EPA 600/2-75-005
APRIL 1975
                       Environmental Protection Technology Series
                   Water Pollution Control
                   for 1974

                                Office of Research

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               RESEARCH REPORTING SERIES
Research reports of the Office of Research and Development,
Environmental Protection Agency, have been grouped into five
series.  These five broad categories were established to
facilitate further development and application of environmental
technology.  Elimination of traditional grouping was consciously
planned to foster technology transfer and a maximum interface
in related fields.  The five series are:

     1.  Environmental Health Effects Research
     2.  Environmental Protection Technology
     3.  Ecological Research
     4.  Environmental Monitoring
     5.  Socioeconomic Environmental Studies
This report has been assigned to the ENVIRONMENTAL PROTECTION
TECHNOLOGY series.  This series describes research performed
to develop and demonstrate instrumentation, equipment and
methodology to repair or prevent environmental degradation
from point and non-point sources of pollution.  This work
provides the new or improved technology required for the
control and treatment of pollution sources to meet environmental
quality standards.

This report has been reviewed by the Office of Research and
Development.  Approval does not signify that the contents
necessarily reflect the views and policies of the Environmental
Protection Agency, nor does mention of trade names or commercial
products constitute endorsement or recommendation for use.
Document is available to the public  through the National  Technical
Information Service, Springfield, Virginia  22151.

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                                      EPA-600/2-75-005
                                      April 1975
   MUNICIPAL WATER POLLUTION CONTROL


            ABSTRACTS  FOR 1974
                   By

            Joanne S. Murphy
          Grant No. R803046-01
         Program Element 1BB033
            Roap/Task PEMP 08
            Project Officer

            Patrick M. Tobin
  Municipal Pollution Control Division
Control and Treatment Integration Branch
    Environmental Protection Agency
        Washington, D.C.  20460
              Prepared for
   Office of Research and Development
  U.S. Environmental Protection Agency
        Washington, D.C.  20460

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                              ABSTRACT
     The Franklin Institute Research Laboratories, Science Informa-
tion Services Department has prepared for the Environmental Protec-
tion Agency a monthly current-awareness abstracting bulletin, the
Municipal Technology Bulletin (MTB) , Volume 2, 1974, which deals
with methods of municipal waste water treatment, problems of water
quality, and water pollution control.  Under the same grant, the
Science Information Services Department has provided 360 MTB
abstracts, as well as 1440 additional abstracts, to the WRSIC data
bank as sole supplier of municipal waste water treatment input and
center of competence for Water Resources Scientific Information
Center.  The Municipal Technology Bulletin informs researchers,
consultants, engineers, and government officials of current develop-
ments described in over 4000 technical journals, both domestic and
foreign.  The topics covered in MTB, Volume 2, and in the WRSIC
input include:  storm water runoff; tunnel technology and sewer
systems; biological, chemical, and physical methods of waste water
treatment; waste disposal alternatives; treatment plant operation
and automation; analytical techniques for water quality measure-
ment; mathematical, statistical, and simulation model studies; and
construction and equipment for pollution control.
     The 1800 abstracts representing 1974 input to the WRSIC data
bank have been arranged in chronological order by accession number
within subject areas.  A list of those 360 abstracts which ap-
peared in the Municipal Technology Bulletin is provided.  Included
also are a subject index, author index, and journal list.
     This report was submitted in fulfillment of grant number
R803046-01 by The Franklin Institute Research Laboratories under
the sponsorship of the Environmental Protection Agency.  Work was
completed as of March 10, 1975.

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                               CONTENTS




                                                             Page



  Abstract                                                    ii


  Acknowledgements                                            i-V



  Section


  I.   Introduction                                             1

 II.   Municipal Technology 'Bulletin Abstract
      List                                                     6

III.   Abstracts from MTB and Input to
      WRSIC                                                    7

 IV.   Subject Index                                          910

  V.   Author Index                                           947

 VI.   Journal List                                          1007
                                   ^^^

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                          Acknowledgement s

Rochelle H. Prague was responsible for the technical editing for
the entire project, including both the bulletin issues and all
the input to WRSIC.

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                              INTRODUCTION






     By continuously surveying the United States and foreign technical




literature and by maintaining close liaison with various research organi-




zations, The Franklin Institute Research Laboratories, Science Information




Services Department, abstracts current information in the area of municipal




waste water pollution control for the Office of Research and Development of




the Environmental Protection Agency.  The abstracting service concentrates




on the following major subject areas dealing with municipal waste water




pollution control:  hydrologic aspects, sewer systems, tunnel technology,




treatment methods, analytical techniques, sampling and instrumentation,




model studies, patents, and legislation.  Significant abstracts are high-




lighted in the Municipal Technology Bulletin which is prepared and distri-




buted on a monthly basis.  In addition, approximately 1800 abstracts are




provided for input to the Water Resources Scientific Information (WRSIC)




Data Service, Department of the Interior.  This report is a compilation of




the abstracts for 1974.






     The Municipal Technology Bulletin is a monthly current-awareness ab-




stracting bulletin dealing primarily with municipal waste water treatment




methods.  It is an outgrowth of several preceding publications which were




prepared by the Franklin Institute for EPA:  Selected Storm Water Runoff




Abstracts.,  1970-1972, and the Municipal Technology Bulletin, Volume 1, 1973.




Each of these publications was begun in response to the need of officials,




researchers, and engineers to monitor and digest the proliferation of




published material on runoff and waste water.  Since it had become increas-




ingly difficult for these people to stay aware of recent developments by

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scanning the literature individually, especially foreign literature gath-




ered from worldwide sources, EPA awarded grants to the Franklin Institute




to gather and disseminate this information.  The Municipal Technology Bulle-




tin serves as a starting point for further exploration of the literature




presented that interests the environmental researcher and administrator.






     Literature for the Municipal Technology Bulletin comes from regularly




scanning over 4000 publications, both domestic and foreign.  These documents




are technical journals, government reports, industrial reports, newsletters,




patent gazettes, design manuals, conference proceedings, recent disserta-




tions, and textbooks.  Screening of the material was done at The Franklin




Institute Library and at several other Philadelphia libraries.   Additional




screening was done at The Franklin Institute's facilities in Munich, Ger-




many and Tokyo, Japan.  Each month 30 documents pertaining to the latest




municipal technology were selected for inclusion in Municipal Technology




Bulletin.  Specific subject areas covered during 1974 were (1)  waste water




treatment methods relating to facilities, land application, utilization of




sludge, waste water reuse, plant automation, mechanical and chemical de-




vices; (2)  biological, chemical, and physical analytical techniques; (3)




storm water runoff, including urban runoff, runoff forecasting, flood




routing, rainfall-runoff relationships, catchment basins, and surface




runoff; (4) sewer systems, including combined, separated, outfall and




interceptor sewers, storm drains, infiltration-inflow, materials and equip-




ment; (5) patents for methods and equipment pertaining to waste water




treatment,  waste water reuse, and waste water disposal; (6) mathematical,




statistical, or simulation model studies; (7) tunnel technology, such as

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tunnelling methods, construction problems,  and tunnelling equipment;  and




(8) hydrologic aspects involving parametric hydrology,  sewer hydraulics,




and drainage.






     In 1974, the Municipal Technology Bulletin was distributed monthly




free of charge to 610 selected recipients whose names were supplied by the




EPA Project Officer, or who were added as a result of a direct request to




the Franklin Institute to be placed on the mailing list pending EPA Project




Officer approval.  There was an increase of about 140 names in 1974 over




1973.






     Through this EPA grant, The Franklin Institute serves as a center of




competence for municipal waste water pollution control.  More than 1,800




abstracts on municipal waste water treatment methods are provided annually




to the Water Resources Scientific Information Center (WRSIC), Office of




Water Research & Technology, Department of the Interior.  These are publish-




ed in their Selected Water Resources Abstracts3 their semi-monthly abstract-




ing journal.  Literature is chosen for input to WRSIC using essentially the




same criteria as for the Municipal Technology Bulletin.  Screening proce-




dures were the same.  These abstracts provide over 95% of data base in




municipal waste water treatment for the users of the WRSIC services.






     This final report is a compilation of the 1974 abstracting services




on municipal waste water pollution control accomplished by the Franklin




Institute.  It includes all abstracts which appeared in Municipal Technol-




ogy Bulletin or were forwarded to WRSIC, a detailed subject index, complete

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author index, and journal list.   The abstracts are arranged by topic,  and




are numbered within the topics,  chronologically.   Topic headings are:   Storm




Water Runoff, Sewer Systems, Patents, Treatment Methods, Analytical Tech-




niques, Model Studies, Tunnel Technology, Hydrologic Aspects,  Miscellaneous,




and Radioactive Wastes.  The format of each abstract is explained on the




following page.

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FIRL ACCESSION NUMBER

TITLE OF THE ARTICLE

NAME OF THE AUTHOR(S)

AFFILIATION OF SENIOR AUTHOR

BIBLIOGRAPHIC DATA:  JOURNAL, VOLUME, NUMBER, PAGINATION, DATE,
FIGURES, TABLES, REFERENCES

ABSTRACT OF THE ARTICLE
DESCRIPTORS:  THOSE WORDS FOUND IN THE WATER RESOURCES THESAURUS
WHICH BEST DESCRIBE THE ARTICLE'S CONTENTS.  ASTERISKS INDICATE
MOST IMPORTANT TERMS.

IDENTIFIERS:  THOSE WORDS NOT FOUND IN THE WATER RESOURCES
THESAURUS WHICH BEST DESCRIBE THE ARTICLE'S CONTENTS.

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            MUNICIPAL TECHNOLOGY BULLETIN ABSTRACT LIST
ACCESSION NUMBERS   PAGES
ACCESSION NUMBERS   PAGES
001A-013A
017A-023A
026A-027A
029A
031A
033A
001B-018B
033B-036B
041B-044B
052B-053B
058B-060B
065B-066B
069B-074B
081B-084B
090B-093B
001C-028C
040C-046C
089C-091C
143C-149C
222C-225C
240C-245C
259C-264C
283C-288C
001D-037D
053D-059D
120D-124D
192D-199D
282D-290D
309D-312D
368D-371D
423D-429D
8-14
16-19
20-21
22
23
24
26-34
42-43
46-47
51-52
54-55
58
60-62
66-67
70-72
76-89
95-98
120-121
147-150
186-188
195-198
205-207
217-219
230-248
256-259
289-291
325-329
370-374
384-385
413-415
441-444
001E-008E
011E-016E
024E-026E
049E-051E
066E-068E
106E-112E
119E-123E
142E-146E
165E-169E
001F-007F
013F-016F
019F-020F
034F-038F
059F-062F
085F-089F
094F-097F
001G
005G-006G
010G
001H-003H
007H-009H
015H-016H
029H-032H
046H-048H
051H-056H
057H-059H
070H-073H
078H-080H
482-485
487-489
493-494
506-507
514-515
534-537
541-543
552-554
564-566
572-575
578-579
581
588-590
601-602
614-616
618-620
630
632
634
636-637
639-640
643
650-651
658-659
661-663
664-665
670-672
674-675

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Abstracts from Municipal Technology Bulletin




            and Input to WRSIC

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                           STORM WATER RUNOFF



001A

BETTER STORM DRAINAGE FACILITIES—AT LOWER COST,

Poertner, H. G. and Asce, F.

Bolingbrook, Illinois

Civil Engineering-American Society of Civil Engineers, Vol. 43, No. 10,
p  67-70, October, 1973.  2 fig.

Successful and economical applications of  detention facilities for
stonnwater are described for use in open spaces, parking lots and rooftops.
The design of the storrawater drainage system at Indian Lakes Estates in
Illinois is illustrated.  Two lakes detain stormwater runoff and make
the area more attractive.  One of the lakes is manmade and its existence
has increased property value for adjoining acreage.  In Earth City,
Missouri, the Missouri River bottomland was developed with intersecting
finger lakes providing stormwater detention.  The lakes are an esthetic
and recreational asset to the community.  A specially designed ponding ring
surrounds a roof drain conductor head on some buildings in Denver.  The
device slows runoff and is used for rainfall detention on the roof.  In
the layout of Melvina Ditch reservoir, a paved area prevents erosion at
the inlet, and is used for recreational purposes.

Water Storage, Storm Water, *Storm Runoff, Drainage Systems, *Reservoir
Storage, Missouri, Missouri River, Illinois, Colorado, *Recreation

Indian Lake Estates, Denver, Melvina Ditch Reservoir
002A

PIONEERING PLANT PROVIDES COST-SAVING ALTERNATIVE TO
SEPARATING SEWERS,

The American City, Vol. 88, No. 10, p 90-92, October, 1973.  2 tab.

A modified contact stabilization process to produce a high quality
effluent under stormflow conditions was utilized in Kenosha, Wisconsin.
The runoff is degritted, mixed with activated sludge solids, clarified,
and stabilized in four additions to the existing waste treatment plan:
grit tank, contact tank, final clarifier, and stabilization plant.  The
entire process is automated and directed from the plant's main control
board.  Wet weather conditions are signalled by a level indicator in
the dry weather grit tank's Parshall flume when the flow rises above
21 mgd.  Biological adsorption was used because the first flush of the
storm contains a high ratio of particulate organic matter to soluble
organlcs.  In the first year of operation, the wet weather plant was
activated 23 times with more than 92 million gallons of combined
sewage treated.  As a result, 91.5 percent of the suspended solids,
82.5 percent of the BOD, and 79.8 percent of the total organic carbon
in that waste stream was kept out of Lake Michigan.

Waste Treatment, *Water Treatment, Runoff, *Storm Runoff, Lakes, *Cities,
Wisconsin, *Combined Sewers

Kenosha

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003A

DEVELOPING OF A REFERENCE RAIN SYSTEM FOR THE DIMENSIONING OF
SEWER NETWORKS (Entwicklung eines Berechnungsregens fuer
die Bemessung von Kanalnetzen),

Sifalda, V.

GWF - Wasser/Abwasser, Vol. 114, No. 9, p 435-440, September, 1973.
3 fig., 4 tab, 7 ref.

The rain intensity distribution with respect to time was studied on the
basis of systematic pluviographic recordings conducted in Prague, Brno,
and Pilsen for the estimation of the storage capacity of sewer networks,
i.e., of the sewer load prevailing prior to the main rain period.  Studies
of rain profiles characteristic of the Elba watershed area in Czechoslovakia
revealed high rain peak in the first half of the rainfall period as the
basic type of rain, and equal frequency of rains with regular and irregular
intensity distribution.  All heavy rains were subdivided into an inital,
a main, and a final period.  The initial rain period, suitable for
calculations in the dimensioning of sewer systems, has the same duration
as the main rain does, and has an average intensity amounting to 25 percent
of that of the main rain.  Runoff was found to be most intense at the
end of the main rain period.

Rainfall Intensity, Rain, Rates, Runoff, *Rainfall-Runoff Relationships,
*Sewers, *Watersheds (Basins)

Prague, Brno, Pilsen, Czechoslovakia
004A

ALUMINUM PIT DOORS PROVIDE EASY ACCESS TO A RETENTION
BASIN,

Water and Sewage Works, Vol. 20, No. 10, p 62-63, October, 1973.

The use of aluminum pit doors to provide easy access to the 50 million
gallon underground stormwater retention basin in Warren, Michigan is
discussed.  The 42 heavy plate doors float on compression spring operators
and automatically lock open, providing safety and easy handling.  The
five foot pit doors are completely watertight and provide a flush surface
for walkover traffic.  The channel frames trap surface water which is
directed to a drywell.  Doors are built for a minimum live load of 300
psf.  The lock opens at 90 degrees, but can be released with one hand.
The two large, special size roof scuttles were installed to permit
installation and removal of large equipment.

*Storm Drains, Michigan, *Storm Water, Storage, Water Storage, *Retention

Doors, ^Aluminum Doors

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005A

RAIN RESERVOIRS AND RAIN OVERFLOWS (Regenbecken und
Regenentlastungen),

Muntz, W.

Gas-Wasser-Abwasser, Vol. 53, No. 9, p 293-300, September, 1973.  7 fig,
1 tab, 7 ref.

Problems of the design and dimensioning of rain reservoirs and rain
overflows are discussed.  Canal overflows without rain reservoirs serve
to release stormwater directly into the recipient whenever a critical
throughflow is reached.  Rain overflow basins bypassing the wastewater
treatment facility assume a similar role, -while rain overflow basins
connected in series with the wastewater treatment facility serve to
protect the latter to preserve its purifying capacity.  Rainwater
retention basins retain stormwater for subsequent treatment.  While most
stormwater overflow basins are currently designed for a minimum critical
rain intensity of 15 liter/sec, this critical value should be now
increased to 25-30 liter/sec, and even to 40-50 liter/sec for especially
protected recipients and for water capture areas.  Rain reservoirs should
be designed for flow times of 5 to 15 minutes.  Increased flow time
results in increased reservoir volume per ha, but also in reduced final
pollutant concentration.  Attenuation of the initial pollutant load
peak in plain watershed areas was determined.

*Rainfall-Runoff Relationships, *Rainfall Intensity, Rain, Rates,
Runoff, Sewers, *Watersheds (Basins), Canals, Treatment
006A

COMPUTER SIMULATION OF STORM WATER RUNOFF,

Offner, F. F.

Northwestern University, Evanston, Illinois.

Journal of the Hydraulics Division, Vol. 99, No. HY12, p 2185-2194,
-December, 1973.  4 fig, 5 ref.

The development and application of a computer program for estimating stormwater
runoff are presented.  Most of the intuition used or experience required in
calculating stormwater runoff by the classical rational method is eliminated.
The program gives an approximate solution of the partial differential flow
equation over the area.  The area considered is divided into a grid of squares,
with the elevation and soil condition  (flow coefficient, initial surface
retention, infiltration rate) tabulated for each grid element.  Often, all
these may be considered constant except elevation.  Typical rainfall data are
centered, and the program gives the runoff into drainage lines as a function
of time.  Depth of water standing in the area is also computed.  Copies of
the FORTRAN program are available.

Model Studies, *Storm Water Runoff, *Computer Models, *Rainfall-Runoff
Relationships, Mathematics

FORTRAN
                                          10

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007A

STORM WATER SAMPLING MACHINE,

Dainty, S. H.

Department of Public Health Engineering, Greater London
Council, London, England

Water and Waste Treatment, Vol. 16, No. 10, p 17, October, 1973.

The operation of the stormwater sampling machine being used by the Greater
London Council (GLC) is described.  The GLC samples the stormwater flows from
gravity outlets which are discharged into the Thames at various manned sampling
points.  The problem of sampling during a storm condition and the subsequent
time lapse before the collection of the sample bottles is solved.  During a
storm flow condition the equipment is actuated for a 15 minute cycle of
operation.  The sampling pump circulates stormwater from the sewer through a
loop and back to the sewer while a small amount of lithium chloride solution
is injected into the sewer 120 meters upstream of the sampling point, where
is disperses into the stormwater.  The sample pump stops, and the loop which
is full of fresh stormwater and traces of lithium chloride (the concentration
of which enables the stormwater volume and rate of flow to be ascertained)
discharges into the first sample bottle.  The exact time of sampling is
recorded, and the apparatus automatically resets itself.  The machine has a
capacity of 24 bottles which enables a convenient time schedule for collection
and transportation to the laboratories.

*Storm Water, Instrumentation, *Sampling, Sewers, *Mechanical Equipment

*London, England
008A

FLOOD RUNOFF SYSTEMS WITH COLLECTOR CHANNEL AND FAST DISCHARGE
FOR DAMS  (Volgyzarogatak gyujtocsatornas, surrantos
arapasztoi),

Szakatsits, G.

Vizugyi Kozlemenyek, No. 3, p 342-350, 1973.

Hydrologic, hydraulic, and engineering aspects of collector channels designed  to
collect,  guide, and attenuate the runoff from runoff weirs to fast discharge
facilities  in dams were studied.  Free overflow at maximum water yield, minimum
possible  dimensions of the collector channel, and hydraulically smooth,
attenuated  flow in the collector channel are the principal requirements of
overflow  -  collector channel systems.  Model studies of different configurations
and designs of overflows, collector channels, and fast discharge facilities
revealed  the superiority of the conventional lateral overflow design to all
other systems, and the positive economical and hydraulic advantages of trapezoid
profiles  for collector channels.  The broadening of the collector channel
does not  give noteworthy additional advantages.  Also, existing collector
channels  were found to be unnecessarily overdimensioned regarding channel
depth.

Engineering Structures, *Weirs, Dams, *Storm Runoff, *Model Studies,
Channels, Channel Improvement, Flood Control

*Collector Channels
                                      11

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   009A

   EFFECT OF AIRCRAFT DEICER ON AIRPORT STORM RUNOFF,

   Schultz, M., and Comerton, L. J.

   Ministry of Transport, Ottawa, Canada

   Journal of the Water Pollution Control Federation, Vol. 46, No. 1, p 173-180,
   January, 1974.  3 fig, 1 tab, 3 ref.

   The effect of aircraft deicer on airport storm runoff was investigated, and
   the airport storm characteristics at Dorval, Montreal's International Airport,
   were determined from February 1 to April 15, 1972.  The aircraft deicers which
   are approximately 50 percent water, 50 percent ethylene and/or propylene
   glycol, and have a high biochemical oxygen demand  (BOD) are the major pollutants
   in apron storm runoff during the winters.  The anticipated apron runoff for an
   airport, where the storm sewer system is designed  to accept relatively little
   snow melt and no surrounding water, can be calculated by adding rainfall data
   and all daily snow falls less than one inch.  At Dorval the precipitation was
   4.60 inches.  If storm sewers do not drain the water table or adjacent snow
   melt areas, separate evaluations are necessary.  The organic loading ratio of
   storm to sanitary waste was 4:1 during the winter.  The BOD to glycol relation-
   ship for all BOD values greater than 200 microgram/liter is equal to -50 + 0.85
   glycol.

   Canada, *Deicers, Biochemical Oxygen Demand, *Storm Drains, *Storm Runoff

   Montreal, *Dorval International Airport, *Aircraft Deicer, Ethylene Glycol,
   Propylene Glycol
010A

REALIZATION OF THE DANUBE FLOOD PROTECTION PROJECT FOR VIENNA
(Das Werden des Projektes fuer den Donauhochwasserschutz von
Wien),

Grzywienski, A.

01Z, Vol. 16, No. 11, p 379-385, November, 1973.  4 fig, 45 ref.

The flood protection project being constructed in the Vienna, Austria, area
is described.  The dams will be elevated, and double protection will be
consequently built up around Vienna to meet floods occurring at an estimated
frequency of one in every 10,000 years.  A flood release channel diverts up
to 5,000 cu meters water per second whenever the yield in the Danube exceeds
5,000 cu m/sec.  The areas around Vienna not belonging to the urban agglomeration
will have a flood protection system designed for a flood frequency of one in
every 1,000 years.

*Flood Protection, Dams, Flood Recurrence Interval, Channels, Flood Control,
Flood Routing

*Vienna, *Austria
                                       12

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011A

TUNNELS MAY STORE STORMWATER FOR LATER TREATMENT,

The American City, Vol. 88, No. 12, p 75, December, 1973.

A study of a proposal to build 20 miles of tunnels in bedrock under Milwaukee
to store overflow from a combined sanitary and storm sewer system was approved
by a Southwestern Wisconsin Regional Planning Commission committee.  The
tunnels would measure about 30 by 40 feet each, would be 250 feet below the
surface, and would connect 112 outfalls of three rivers.  If the three-year,
$2.3 million study is approved, the Federal government would pay 75 percent
of the $175 million cost, the state 12.5 percent, and the sewerage commission
12.5 percent.

*Wisconsin, *Tunnels, *Storm Water Runoff, Subsurface Drainage, *Storm
Drains, Underground Storage, Combined Sewers, Sanitary Sewers

*Milwaukee
012A

SEWAGE AND STORMS GET THE FULL TREATMENT,

Ganley, R. J.

Albany, New York

Water and Waste Engineering, Vol. 11, No. 1, p 30-31, 37, January, 1974.

The construction of a $2.2 million sewage treatment plant capable of handling
both storm and sanitary discharges in Catsklll, New York, is described.  A
trickling plant was proposed with modifications to include the use of pre-
aeratlon tanks equipped for the return of activated sludge, and recirculation
pumping rate controlled inversely to the raw sewage inflow rate.  The plant
can achieve 90-95 percent BOD removal through the use of high rate activated
sludge pretreatment, and flow regulation to the primary tanks and trickling
filters.  The instrumentation and variable speed pumping equipment combining
raw with recirculated sewage helps provide the desirable constant flow rate
to the primary settling tanks and trickling filters.  The plant capacity of
1.5 mgd allows for the present Catskill population and its projected growth
requirements.  The plant is designed to allow a flow, including recirculation,
of 3.8 mgd to pass through the primary clarifier and trickling filters
before any of the flow is restricted to the filters and bypassed to the final
clarifier.  To avoid upsetting aerated pretreatment, the pretreated portion of
the flow is restricted to approximately 50 percent of the dry weather flow which
allows maintenance of the filterability of the raw sludge on the vacuum filters.
The plant's raw sewage pumping capacity is 9.0 mgd.

Waste Treatment, Sewage, *Sewage Treatment, *Storm Water, *New York, Activated
Sludge, Municipal Wastes

Catskill


                                      13

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013A

EROSION CONTROL SAVES SOIL NUTRIENTS,

Agricultural Research, Vol. 22, No. 7, p 6-7, January, 1974.  1 fig.

The application of soil erosion control methods in eliminating fertilizer nitrogen
and phosphorus as pollutants in surface runoff is described.  In a three-year
study on adjacent watersheds near Treynor, Iowa, it was demonstrated that when
corn was fertilized at two and a half times the recommended rate, only one
thirteenth as much nitrogen and one tenth as much phosphorus was lost in runoff
when erosion was effectively restricted as when it was not.  The corn was
grown on the watershed protected by level terraces, on two watersheds farmed
on the contour, and on a fourth watershed which was bromegrass pasture.  Terracing
was the more effective means of restricting runoff and soil eriosion on cropped
land.  Average annual loss of nitrogen in all forms was 28.8 pounds per acre
with contouring, 2.7 pounds with terracing, and 2.1 pounds with grass.
Significantly, 92 percent of the total nitrogen loss from contour-farmed
watershed, and 86 percent from the terraced watershed, was associated with
sediment.  A critical period for nutrient losses was during seedbed preparation
and the establishment of crop.  Differences in phosphorus losses from the
four watersheds were similar to those for nitrogen.

*Erosion Control, *Contour Farming, *Cover Crops, Erosion, Soil Conservation,
Soil Management, *Terracing, Vegetation Establishment, *Surface Runoff,
*Nutrient Removal
014A

HYDROLOGICAL ASPECT OF SURFACE RUN-OFF,

Bose, B. and Bandyopadhyay, M.

Science and Culture, Vol. 39, No. 6, p 248-252, June, 1973.  1 fig, 1
tab, 5 ref.

The problems associated with the hydrologic aspect of surface runoff with
particular reference to the city of Calcutta, India are discussed briefly.  A
model based on rainfall-intensity-frequency was obtained from the available
data.  This model then was used to estimate the runoff by the rational method,

*Hydrologic Aspects, *Surface Runoff, *Model Studies, *Rational Formula,
Rainfall Intensity, Frequency Analysis, Estimating Equations,
*Runoff Forecasting

India
                                      14

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015A

CONTROLLED INSTANTANEOUS APPLICATION OF FREE WATER TO A POROUS
SURFACE,

Swartzendruber, S. D. and Asseed, M. S.

Soil Science Society of America Proceedings, Vol. 37, No. 6, p 967-968,
November-December, 1973.  1 fig.

Instantaneous application of free water to a porous-medium surface is achieved
essentially by a device in which the central feature is a plastic plate
perforated with small holes.  The pressure head of the water can be controlled
at a preselected value between 0 and 1 cm.  Water enters the porous medium
at essentially zero external flow resistance, while volume and time of entry
can be measured accurately.  No lateral flow of free water occurs, thus
eliminating the disturbing effects of such flow on the porous-medium surface.

*Porous Media, *Infiltration, Seepage, *Flow Measurement, Control Systems,
Pressure Head

Water Application
016A

CONTRIBUTION TO WATER POLLUTION FROM AGRICULTURAL AND URBAN
SOURCES IN THE COACHELLA VALLEY,

Oertli, J. J. and Bradford, G. R.

California Agriculture, Vol. 27, No. 7, p 4-6, July, 1973.

To obtain quantitative data on the contributions of agricultural and urban
sources to water pollution, an investigation was initiated in the Coachella
Valley on the chemical composition of drainage water from cropped fields
under various agricultural managements and the effluents from the Indio
sewage treatment plant.  Research emphasis was on those nutrients suspected of
playing a major role in eutrophication.  Of the ten sampling station study
fields, three were in citrus, two in grapes, one in dates, one in carrots,
one in asparagus, and two in corn.  Surface runoff and subsurface drainage
of a large feedyard were also sampled.  Results indicate that the drainage water
from corn, carrots, and asparagus fields contains the largest amounts of
nitrates and that the most significant contributor to phosphates in the White
Water River Is the Indio sewage treatment plant.  With respect to total salinity,
the water quality was best from the sewage effluent and surface runoff from
the feedyard.

*On-Site Data Collections, Water Pollution Sources, *Urban Runoff, *Agricultural
Runoff, Chemical Properties, Effluents, Nutrients, Nitrogen, Investigations,
Phosphorus, Salinity, *Surface Runoff, Subsurface Waters, Drainage Water,
*Water Quality

Coachella Valley, California


                                        15

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017A

CROSS-SPECTRAL ANALYSIS OF RAINFALL AND RUNOFF FOR
RARITAN AND MULLICA RIVER BASINS IN NEW JERSEY,

Bourodimos, E. F., and Oguntuase, A. M.

Department of Civil and Environmental Engineering,
State University of New Jersey, New Brunswick, New Jersey

Journal of Hydrology, Vol. 21, No. 1, p 61-79, January, 1974.  9 fig, 1 tab,
11 ref.

Cross-correlation and cross-spectral analysis were used in analysis of rainfall
and runoff in the Raritan and Mullica River basins in New Jersey.  Cross-
covariance and coherence -were studied in the correlograms for the following
correlation cases:  (a) rainfall - runoff for each basin separately;
(b) rainfall - rainfall analysis for two main meteorological stations in each of
the basins; (c) runoff - runoff for two main gaging stations in each of the basins.
From the estimates of the coherence at various frequencies the cross-spectral
analysis shows a highly nonlinear relationship between rainfall and runoff in
these basins.  A poor coherence observed at the annual cycles for each basin makes
it difficult to predict the annual oscillations of runoff from those of rain-
fall by a linear regression model.  An accurate prediction on a linear basis
may be made within the same basin for rainfall or runoff when comparing two
stations within the same basin.

*Rainfall-Runoff Relationships, Rainfall, Runoff, New Jersey, Basins,
*River Basins, Model Studies, *Computer Models, *Mathematical Models

*Raritan River Basin, *Mullica River Basin
018A

LABORATORY EXPERIMENTS WITH SURFACE RUNOFF,

Muzik, I.

Hydrology, Technical Services Division, Department of
the Environment, Government of Alberta, Edmonton,
Alberta, Canada

Proceedings of the American Society of Civil Engineers, Vol. 100,
No. HY4, p 501-516, April, 1974.  12 fig, 2 tab, 22 ref.

Experimental testing by laboratory catchment of two theoretical concepts of
overland surface flow caused by rainfall, instantaneous unit hydrograph and the
kinematic wave concept, was carried out.  Simulated and observed hydrographs
of runoff from a laboratory catchment were compared.  An attempt was made to
test the performance of the instantaneous unit hydrograph and the kinematic wave
models of surface runoff when idealized conditions were satisfied.  Nonlinearity
of the rainfall-runoff relationship was investigated particularly with regard
to the linear approximation by the instantaneous unit hydrograph model.  It
was concluded that runoff from an impervious surface generated by rainfall is
a highly nonlinear process: linear analysis of the process does not strictly
apply.  Term IUH or any other linear model can be considered only as a linear
approximation of the rainfall-runoff process for a given rainfall intensity.
As the deviation in the rainfall intensity increases, the particular linear
approximation becomes progressively worse.  Results of experiments with runoff
from surfaces of varying slopes support the kinematic wave theory.  The effect
of the surface roughness has not been investigated experimentally.  The
apparent time to equilibrium is a function of rainfall intensity.  There is a
good correlation between it and the time to equilibrium predicted by the
kinematic wave model.  The kinematic wave model sometimes overestimates discharge.

*Model Studies, *Mathematical Models, *Runoff, *Rainfall, *Rainfall-Runoff
Relationships, Hydrographs, Overland Flow

Kinematic wave concept
                                      16

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019 A

ESTIMATION OF IMPERVIOUSNESS AND SPECIFIC CURB LENGTH FOR FORE-
CASTING STORMWATER QUALITY AND QUANTITY,

Graham, P. H., Costello, L. S., and Mallon, H. J.

Metropolitan Washington Council of Governments,
Washington, D.C., Department of Health and Environ-
mental Protection

Journal of Water Pollution Control, Vol. 46, No. 4, p 717-725,
April, 1974.  5 fig, 4 tab, 14 ref.

A model for stormwater runoff is explained, which is useful as a planning
aid for estimating imperviousness and specific curb length for future time
periods.  The data produced by the estimation technique is combined with
demographic data in order to predict nonpoint source pollutants added
from urbanizing watersheds adjacent to receiving water.  The analysis and
estimations presented may be applied to give data on stormwater quality and
quantity for projected time periods.  Mentioned specifically are storm-
water runoff, dry weather waste water flow, waste water routing, and waste
water storage and treatment.

*Storm runoff, *Model studies, *Mathematical models, *Water quality, Waste
water, Water flow, Storm water, Biochemical oxygen demand, Watersheds, Waste
water treatment, Water storage

*Demography, Storm water management model
020A

ARTIFICIAL AQUIFER STOPS STORM POLLUTION,

The American City, Vol. 89, No. 5, p 106, May, 1974.

Akron, Ohio has solved the problem of combined storm and sanitary sewers by
an underground, plastic-encased artificial aquifer.  This is both effective
and inexpensive.  Stormflows are diverted into a clarifier where waste water
is settled and chlorinated.  It is then stored in the plastic aquifer until
it can be accepted at the sewage treatment plant.  Surface land above this
underground cell may still be used for other purposes, thus eliminating land
acquisition costs.

*Combined sewers, *Aquifers, *Plastlcs, *Waste water treatment, *Storm runoff,
*Sewage treatment, Ohio, Municipal wastes, Cities, Storm water, Stormflow,
Costs, Clarification

*Stormflow treatment, Clarification-chlorination basin
                                        17

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021A

CHLORINATION AND LEAD IN URBAN SNOW,

Oliver, B. J., Milne, J. B., and LaBarre, N.

Ottawa University, Water Quality Research
Division

Journal of Water Pollution Control, Vol. 46, No. 4, p 766-771, April, 1974.
5 tab, 24 ref.

In both Canadian and American cities, chlorine contamination is a problem
where salting is used to keep roads clear of snow in the winter.  Localized
lead pollution is an additional problem for public health.  Levels of both
lead and chloride in snow and runoffs in the city of Ottawa were measured
in winter and spring 1972.  Various snow melting and snow disposal methods
were compared in order to evaluate environmental effects.

*Snow, *Lead, *Chlorine, *Snow removal, Salt, Waste water treatment,
Water pollution sources, Water pollution effects, Canada, Cities, Water
quality, Pollution

*Urban snow, Chloride contamination, Chlorination, Street salting
02 2 A

WATER POLLUTION AND ASSOCIATED EFFECTS FROM STREET SALTING,

Field, R., Struzeski Jr., E. J. Masters, H. E., and Tafuri, A. N.

National Environmental Research Center,
Cincinnati, Storm and Combined Sewer Technical Branch

Journal of the Environmental Engineering Division, Vol. 100, No. EE2,
p 459-477, April, 1974.  7 fig, 3 tab, 100 ref.

A state-of-the-art review of highway deicing practices is given, with their
associated environmental effects.  In addition future quantitative analyses
are listed, and plans for the writing of A DEICER'S USE MANUAL are mentioned.
Summaries on available information are given for:  methods, equipment, and
materials used for snow and ice removal; chlorides found in winter rainfall
and municipal sewage; salt runoff from highways and streets; deicing compounds
found in surface streams, public water supplies, groundwater, farm
ponds, and lakes; special toxic or nutritious additives; vehicular corrosion
and deterioration of highway structures due to salting; and effects of
deicing compounds on roadside soils, vegetation, and trees.

*Water pollution, *Reviews, *Environmental effects, *Deicers, Snow,
Chlorides, Municipal water, Municipal wastes, Highway icing, High
effects, Groundwater, Toxins, Snow removal, Runoff

*Environmental Protection Agency, *Street salting
                                   18

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023A

WATER POLLUTION ASPECTS OF STREET SURFACE CONTAMINANTS,

Sartor, J. D., Boyd, G. B., and Agardy, F. J.

URS Research Company,
San Mateo, California, Environmental Systems Division

Journal of the Water Pollution Control Federation, Vol. 46, No. 3, p 458-469,
March, 1974.  I fig, 1 tab, 4 ref.

A study was undertaken to investigate and define the water pollution impact
of urban stonnwater discharge and to develop alternate approaches suitable
for reducing pollution from this source.  Problems to be solved included:
direct pollution of receiving waters, overloading of treatment facilities, and
impairment of sewer and catch basin functions, all caused by hydraulic over-
loading and by the various pollutants contained within the runoff.  It was con-
cluded that street surface contaminants contain high concentrations of materials
known to cause water pollution problems.  It was recommended that public works
departments should monitor their street cleaning operations carefully and
examine current practices by a cost-effectiveness model.  In-depth analysis
by individual cities was seen as necessary,

*Water pollution sources, *Storm water runoff, *Street runoff, *Public works,
Reviews, Sewers, Storm sewers, Combined sewers, Treatment facilities,
Pollutants, Costs

*Street cleaning, Street surface contaminants, Hydraulic overloading,
Cost-effectiveness models
02 4A

EFFECT OF VARYING THE ON-OFF TIME OF RAINFALL SIMULATOR NOZZLES
ON SURFACE SEALING AND INTAKE RATE,

Sloneker, L. L. and Moldenhauer, W. C.

U.S. Department of Agriculture, Morris, Minnesota

Soil Science Society of America Proceedings, Vol. 38, No. 1, p 157-159,
January-February, 1974.  1 fig, 2 tab, 8 ref.

The possible effects of nozzle on-off time on rainfall simulator results
were investigated at Morris, Minnesota during the winter of 1972-1973.
Many erosion studies have been conducted using water drops formed by
sprinkler irrigation nozzles.  Rainfall intensity is controlled by vary-
ing the on-off time.  After a certain point, the energy to initiate
runoff is increased as application rate is increased even though runoff
is taking place.

*Irrigation, *Simulated rainfall, *Runoff, Investigations, Infiltration,
Nozzles, Operation, Kinetics, Energy
                                    19

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025A

EFFECT OF GRAZING ON RUNOFF FROM TWO SMALL WATERSHEDS IN
SOUTHWESTERN WISCONSIN,

Sartz, R. S., and Tolsted, D. N.

U.S.D.A. Forest Service, North Central Forest Experi-
ment Station, La Crosse, Wisconsin

Water Resources Research, Vol. 10, No. 2, p 354-356, April, 1974.  3 fig, 2
tab, 1 ref.

The purpose of this study was to determine how land use affects runoff.
Storm runoff from two small open pasture watersheds was measured for 11 years;
during the first 7 years both were grazed, and during the last 4 years only
one was grazed.  Their runoff behavior was similar when both were grazed, but
by the third year after cessation of grazing, runoff from the ungrazed water-
shed had dropped sharply.  The ungrazed/grazed ratio for mean total flow had
dropped from 1.17 to 0.10 and for mean peak flow from 0.82 to 0.03.  It was
concluded that even moderately grazed sloping pastures in the unglaciated re-
gion contribute to floods but that runoff is reduced sharply within three
years after grazing is stopped.

*Storm runoff, *Pasture management, Pastures, Agricultural watersheds, Flow
rates, Land use, Investigations, Continuous grazing, Rotation grazing, Soil

Mean flow, Wisconsin
026A

NUTRIENT LOADING FROM A SEPARATE STORM SEWER IN MADISON,
WISCONSIN,

Kluesener, J. W., and Lee, G. F.

Bechtel, Incorporated, San Francisco, California

Journal of the Water Pollution Control Federation, Vol. 46, No. 5, p 920-936,
May, 1974.  16 fig, 3 tab, 14 ref.

A study was undertaken to explore implications of nutrient loading from separate
storm sewers and characteristics of nutrients in urban runoff.  To this end the
following determinations were attempted:  rainfall-runoff relationships for
a selected basin in Madison, Wisconsin; seasonal and storm-duration variability
of nutrient concentrations; annual nutrient loading; sampling requirements for
nutrient loading quantification; significance of urban runoff with respect to
other known sources of nutrients influent to a lake in Madison.  Percent
runoff was found to be equivalent to the area of the basin covered by streets,
and varied as a function of rainfall amount.  High nutrient and SS concentra-
tions were during the early stages of a runoff event; high phosphorus occurred
during the spring and fall, while nitrogen was high during the spring.  The
major source of inorganic-N was rainfall, whereas phosphorus was generated by
litter arid possibly by auto exhaust.  Preference for sampling procedures
are in the following order:  flow-proportioned sampler, and characterization
of a basin by collection of flow and chemical data over fairly short time
intervals for several storms.

*Urban runoff, *Separated Sewers, *Rainfall-runoff relationships, Nutrients,
Lakes, Basins, Nitrogen, Phosphorus, Flow, Rainfall, Sampling, Storm water,
Storm runoff, Wisconsin, Storm sewers

*Nutrient loading, Chemical data, Madison, Wisconsin
                                   20

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027A

UNRECORDED POLLUTION FROM URBAN RUNOFF,

Whipple, W., Hunter, J. V., and Yu, S. L.

Water Resources Research Institute
Department of Civil and Environmental Engineering,
Rutgers University, New Brunswick, New Jersey

Journal of the Water Pollution Control Federation, Vol. 46, No. 5, p 873-885,
May, 1974.  6 fig, 2 tab, 22 ref.

A study has been done on unrecorded pollution caused by concentrations of ur-
ban populations.  It was concluded that in the case of developing urban areas
when the stage of secondary treatment of recorded wastes is arrived at, the
unrecorded pollution sources will account for more than half of the pollution
in streams.  These unrecorded wastes will be found too large to he ignored
in planning.  An approximation of unrecorded BOD loading of 0.02 to 0.03 lb/day/
person may be used for clean residential urban development.

*Urban runoff, *Urban planning, *Waste disposal, *Water pollution sources,
Pollution, Wastes, Streams, Biochemical oxygen demand, Planning

Waste recording
02 8A

STREET RUNOFF AS A SOURCE OF LEAD POLLUTION,

Newton, C. D., Shephard, W. W., Coleman, M. S.

Oklahoma Department of Health,
Oklahoma City,
Water Duality Control Service

Journal of the Water Pollution Control Federation, Vol. 46, No. 5, p 999-1000,
May, 1974.  4 ref.

In 1972, a surface water survey conducted by the Oklahoma State Department of
Health indicated excessive amounts of lead in the upper portions of the Deep
Fork branch of the North Canadian River in Oklahoma County.  No point source
could be located for this contamination until publication of a recent report
showed that lead from automobile emissions accumulates on the surface of
streets during dry periods and is washed into surface waters during storm run-
off.  It is known that automobile emissions deposit large amounts of lead
close to the source primarily on or near the roadbed.  Samples of snow, ice, and
water were taken from several sites along heavily traveled highways and ana-
lyzed for lead content by use of an atomic absorption spectrophotometer.
Average concentration of lead in samples from road bed edges was 5.5 mg/liter
(range 3.6-8.5 mg/liter).  Concentrations of lead decreased in samples as
distance from the roadbed increased.  The lowest concentration was found in the
middle of an open field surrounded on three sides by heavily traveled roads.
The lead level was 0.09 mg/liter.

*Lead, *Urban runoff, *Surface runoff, *Water pollution sources, Oklahoma,
Water pollution, Spectrophotometry, Analytical techniques

Automobile emissions, Roadbeds
                                       21

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029A

RUNOFF CONDITIONS, CALCULATION METHODS, DIMENSIONING CRITERIA
(ABFLUSSVERHAELTNISSE, BERECHNUNGSMETHODEN, DTMENSIONIERUNGS-
GRUNDSAETZE),

Stetefeld, W.

Wasser-und Energiewirtschaft, Vol. 66, No. 4/5, 1974.  1 fig, 1 tab.

Runoff conditions, as well as calculation methods and dimensioning criteria
for flood protection are discussed with special regard to the conditions
prevailing in Switzerland.  The runoff as part of the overall water budget
is influenced by such factors as climate, the nature of the underground and
rocks, vegetation, and topography.  Rocks and ground have a certain
buffer capacity for water runoff, while vegetation tends to intercept
precipitation.  A general formula for flood calculation determines runoff
quantity as a product of the specific runoff and the surface of the water
capture area.  The storm runoff is determined as the product of the runoff
coefficient, surface area, and rain intensity.  Runoff and flood protection
systems in Switzerland are dimensioned for floods with a probability of
occurrence of one every 100 years.  The freeboard for flood protection systems
is usually set at one m with respect to waves, sediment formation, ice drift
and other phenomena impeding normal runoff.  (Takacs-FIRL)

*Runoff forecasting, *Model studies, *Flood protection, Floods, Sediment,
Topography, Climatic data, Precipitation (atmospheric)

*Switzerland, Calculations
030A

POINT PROCESS OF SEASONAL THUNDERSTORM RAINFALL. 3. RELATION
OF POINT RAINFALL TO STORM AREAL PROPERTIES,

Smith, R. E.

United States Department of Agriculture Southwest
Watershed Research Center, Agricultural Research
Service, Tucson, Arizona

Water Resources Research, Vol. 10, No. 3, p 424-426, June, 1974.
3 fig, 8 ref.

A two-part study of the stochastic nature of thunderstorm occurrence and the
probability of daily rainfall depth indicated the importance of point rainfall
information to areal rain distribution.  A probabilistic expression was
developed for the relationship between the point depth of rainfall, the local
probability distribution of storm cell maximum depth, and the dimensionless
expression of storm depth-area pattern.  The expression was successfully
used to reproduce point rainfall depth probability from storm maximum depth
distribution and depth area data in Tombstone, Arizona.

*Synthetic hydrology, *Thunderstorms, Weather data, Probable maximum
precipitation, Depth-area-duration analysis, Mathematical studies

*Point rainfall, Tombstone, Arizona
                                   22

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031A

DETERMINATION OF THE RAIN RUNOFF WITH SPECIAL
REGARD TO THE RUNOFF FROM INDIVIDUAL PLOTS.
PART 2: APPLICATION OF ASSUMED RAIN DURATION
TO SMALL AREAS—METHOD OF SUMMATION OF RUNOFF
LINES—STORAGE CAPACITY IN MIXED RAINWATER SEWERS,

Pfeil, K.

Heizung Leuftung Haustechnik, Vol. 25, No. 4, p. 131-134,
1974.

Problems of the determination of storm runoff from small
catchment surfaces such as individual plots by the calcula-
tion rain and the cumulative curve methods are described.
Rainfall durations over 15 minutes should be considered
for urban sewer systems and for large catchment areas
only.  The dimensioning of pipelines is often based upon
actual precipitation statistics for the given area rather
than on general formulae.  The exponential runoff curves
for circular catchment areas fall very slightly in the
period immediately after the end of the rainfall and drop
very rapidly later.  The cumulative curve procedure
permits the determination of the flood waves in the
individual sewer sections and of the storm runoff for the
entire catchment area.  It has been demonstrated lately
that the storm runoff is shifted in time rather than
reduced by the sewer volume.

*Runoff, *Equations, Models, Rainfall-runoff relationships,
Floods, Sewers, Combined sewers, Pipelines

Rainwater sewers
032A

USE HIGHWAY FUNDS TO TREAT STREET RUNOFF,

Janicki, V.

The Metropolitan Sanitary District of
Greater Chicago, Illinois

Water and Sewage Works, Vol. 121, No. 6, p 82, June, 1974

It is the contention of the author that an amendment to the Motor Fuel
Revenue Act be initiated so as to redistribute federal tax monies to
include municipal sewerage agencies whose waste treatment plants and
sewer systems collect and treat highway runoff.  The greater Chicago
area, Cook County, is shown as an example of the misuse and overuse of
a sewerage system.

*Taxes, *Sewerage, Federal government, Highway effects, Storm runoff,
Urban runoff, Waste water treatment, Treatment facilities, Sewers

Chicago, Illinois
                                  23

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033A

SCREENING MODEL FOR STORM WATER CONTROL,

Krishen, P. H., and Marks, D. H.

Massachusetts Institute of Technology, Water
Resources Division, Department.of Civil Engineering

Journal of the Environmental Engineering Division, Vol. 100, No. EE4,
p 807-820, August, 1974.  1 fig, 2 tab, 8 ref.

A case study was done on the Bloody Run Drainage Basin in Cincinnati, Ohio,
to test a new screening model for the planning of control of storm water
in combined sewer systems.  This simulation model determines the areas
of local flooding and appropriate storm design for overflows and runoff.
Controls screened are treatment and storage facilities and relief sewers.
The screening model is then run to determine if the operating policy is
feasible and close to optimal.  For the Ohio basin, the best configuration
suggested by the screening model and sensitivity analysis results was
analyzed in detail on simulation model.  From the information obtained,
design details may be implemented.

*Storm water, *Planning, *Combined sewers, *Sewer systems, Model studies,
Simulation models, Overflows, Runoff, Design criteria

*Bloody Run Drainage Basin, Cincinnati, Ohio
034A

URBAN RUNOFF AND COMBINED SEWER OVERFLOW,

Field, R., and Szeeley, P. J.

Environmental Protection Agency, Edison Water
Quality Laboratory Advanced Waste Treatment Research
Laboratory, Edison, New Jersey

Journal of the Water Pollution Control Federation, Vol. 46, No. 6,
p 1209-1226, June, 1974.  228 ref.

As significant contributors to water pollution, stormwater runoff
and combined sewer overflows have become increasingly important to
the Envrionmental Protection Agency as an area for concern and con-
trol.  This article reviews the characteristics of stormwater run-
off and various management practices such as control systems, flow
models, soil infiltration and runoff predictions.  The control of
combined sewer overflows, infiltration, storage, and the beneficial
use of stormwater are outlined.  Finally, the various treatment methods
for stormwater and combined waste water are presented.

*Reviews, *0verflows, *Storm runoff, *Storm water, *Urban runoff,
Combined sewers, Water pollution sources, Management (Applied),
Control systems, Flow characteristics, Infiltration, Storage,
Waste water treatment
                                    24

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035A

WATER QUALITY CHARACTERISTICS OF STORM SEWER DISCHARGES
AND COMBINED SEWER OVERFLOWS,

Kothandaraman, V.

National Technical Information Service Report PB-214 507, 1972.
19 p, 1 fig, 49 ref, 7 tab, 49 ref.

The paper, which reviews pertinent case studies, emphasizes the water quality
aspects of urban storm runoff rather than the quantity of storm water and
combined sewer overflows.  The characteristics of combined and separate
storm sewer discharges, the storm water pollution load estimates and models,
the impact of storm runoff on receiving waters, and methods and estimated
costs for pollution abatement are summarized.  The basic considerations
needed for developing a preliminary prediction model encompassing the
characteristics of storm water runoff in a river basin are reviewed.  However,
the inputs such as topography, soil type, and land use will have to be
developed for each area.

*Pollution abatement, *Storm runoff, *Urban runoff, Water quality control,
Models, Combined sewers, Separated sewers, Costs, Reviews, River basin
036A

A SIMILARITY DURING EARLY STAGES OF RAIN INFILTRATIONS,

Ahuj a, L. R., and Romkens, J. M.

Hawaii University, Honolulu, Hawaii
Department of Agronomy and Soil Science

Soil Science Proceedings, Vol. 38, No. 3, p 541-544, May-June, 1974.  4 fig,
10 ref.

A similarity during early stages of rain infiltration into a relatively dry
soil is shown in which the diffusivity varies exponentially with the water
content.  This similarity permits simple expressions for the description of
the wet-front progress and the water-content change at the soil surface.
The wet-front equation describes well the experimental data for four different
soils.  This approach can be utilized in some cases of rainfall when the
intensity is time-dependent, and to infiltration with transient surface
sealing.

*Watershed hydrology, *Sprinkler irrigation, *Rainfall, Soil properties,
Surface sealing, Diffusivity, Infiltration, Moisture content

*Wet-front progress, *Wet-front equation
                                    25

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                              SEWER SYSTEMS




001B

INSERTED PIPE REPAIRS OUTFALL IN 3 1/2 DAYS,

Western Construction, Vol. 48, No. 11, p 53,  64,  November,  1973.

A relining project using 2600 feet of 32 inch diameter high density
polyethylene pressure pipe in a deteriorating ocean outfall is described.
The operation was completed in only three and one-half days, during which
one hundred feet of existing concrete cylinder pipe was cut out close
to the shore to provide a point of access from which to insert the new
pipe.  The pipe called Sclairpipe has a wall  thickness of .978 inch.
Sixty feet lengths of plastic pipe were butt-fused together.  A steel
cable running from a steel spider band through a  pulley attached  to the
concrete cylinder pipe was pulled by a tractor feeding the  polyethylene
pipe into the outfall.  A special steel nosecone  was attached to  the
lead end to keep the pipe from snagging.  The back flow of  effluent from
the concrete diffuser into the annular space  between the polyethylene
and concrete pipes was prevented by keeping the space filled with water
under enough pressure to hold back the effluent.

Outlets, *0utfall Sewers, Plastic Pipes, *Concrete Pipes, Shores, *Linings

*Sclairpipe, *Relining Project
002B

 'PIG' BRINGS BACK CAPACITY,

Glasson, H. H.

Denver, Colorado Water Department

Water Wastes Engineering, Vol. 10, No. 11, p 33-35, November 1973.

Two raw water conduits supplying Denver's water supply were cleaned using
a device called a pig and designed by the utility's maintenance personnel,
Ralston Reservoir has a storage capacity of 11,252 acre-ft and supplies
raw water  through two cylinder-type reinforced concrete pipelines to the
treatment  plant.  There was a substantial buildup of colloidal clay on
the inner  surface of the pipe, ranging in thickness from approximately
l/16th to  3/8th inches through most of the 8.7 miles.  A two sectional,
eight bladed mechanical cleaner was designed and coupled to the plug or
pig type cleaner like a trailer.  A flexible coupling designed to allow
for flexibility through the bends in the conduit attached this assembly
to the pig.  Operational capacity after cleaning increased from less than
52 mgd to  over 67 mgd.  New operational criteria based on reevaluation
of design  capabilities were established.

Colorado,  Reservoirs, *Conduits, *Maintenance, Clays, Colloids

*Denver, Ralston Reservoir, *Cleaning
                                   26

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003B

HOW TRIPLE SIPHON SOLVED SEWAGE TRANSFER ACROSS WELLAND
RIVER,

Webster, L.

Engineering and Contract Record, Vol. 88, No. 10, p 54-55, October, 1973.

The use of a novel triple siphon system across the Welland River on
Ontario's Niagara Peninsula is described.  Sanitary wastes originating
on one side of the river are conveyed to the City of Niagara Falls
pollution control plant across the river for treatment and disposal.
Excavations were required for large manholes on each bank of the river,
one to serve as an inlet structure, the other an outlet structure,
for the siphons.  A dewatering system was designed to secure the excavations
against the hydrostatic pressure from the underlying silt layer.  The use
of polyethylene pipe for the siphons to effect the actual river crossing
contributes to a substantial savings over a design calling for the
underwater installation of more conventional materials.

Rivers, Canada, *Sanitary Engineering, Treatment, Disposal, *Plastics

*Welland River, Niagara Falls
 004B

 RURAL WATER SYSTEM  DESIGNED FOR SUBURBAN USE,

 Public Works, Vol.  104, No. 11, p  77, November,  1973.

 The organization  of the non-profit Del-Co Water  Company  to build and operate
 a rural water system designed  for  suburban use near Columbus, Ohio is
 described.  The company was financed by a membership  fee and a loan of
 $225,000  from the Farmers Home Administration.   There are more than 1,550
 members in Del-Co,  which consists  of a basic water plant and 122 miles of
 distribution lines.   An additional 80 miles of distribution piping will
 complete  the project.  The source  of supply is the Olentangy River, the
 water of  which is hard and contains iron.  A processing plant was built
 using the usual processes of coagulation, sedimentation, and filtration.
 Initially it will handle 1 1/4 mgd, but can be expanded to 3 mgd.  An
 0-ring joint system connects the vinyl pipes.

 Water Supply Development, Water Management, *Rivers, Ohio, Economics,
 *Financing, Loans,  *Rural Areas, Suburban Areas

 Olentangy River,  Del-Co Water  Company, Farmers Home Administration
                                     27

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  005B

  NEW SEWER OUTFALL WILL SPAN THREE BRIDGES,

  World Construction, Vol.  26, No.  10,  p 53-54,  October,  1973.

  The Johannesburg's diepsloot outfall  sewer  contract is  described.  It is
  unusual because of the use of large diameter spun concrete piping, fissures
  in an ancient granite which imposed difficulties in tunnel construction,
  and the bridging of three valleys to  carry  the sewer near the outfall end.
  The value of the design was $4.51 million.   Standardized bridge construction
  was used because of the short completion dates:  bridge 1, 16 months;
  bridge 2, 18 months; and bridge 3, 20 months.   The layout is  based on a
  module of 20 meter spans for the bridge decks.  Dolomitic aggregate was
  used to control the pattern of corrosion of tunnel concrete,  and shotcrete
  construction was used for the fissures.

  Sewers, Engineering Structures, *0utfall Sewers, *Tunnels, Corrosion,
  Inhibition, *Concrete Pipes, Gunite,  Africa, *Bridges

  South Africa, Johannesburg, Diepsloot
006B

ENGINEERING AND CONSTRUCTION PRACTICES FOR GRAY AND DUCTILE
CAST-IRON PIPE,

Smith, W. H.

Cast Iron Pipe Research Association, Oak Brook, Illinois

Journal of the American Water Works Association, Vol. 65,  p 788-791, December,
1973.  2 fig, 2 ref.

Gray cast iron pipe and ductile cast iron pipe were designed using realistic
assumptions for earth load, trench support, superloads,  impact internal pressure,
and water hammer or surge.  A wide range of joints is available for both pipe
materials, from flanged joints, which are ideal for plant  and pump station
installations, to standard mechanical and push-on joints,  which are reliable
in allowing reasonable deflections, and subaqueous pipe  joints, which allow
for extreme deflection.  Restrained joints resist thrust due to internal
pressure.  Corrosion resistance of ductile cast iron pipe  is somewhat better
than that of gray cast iron pipe, and only a small percentage of the soils
in the United States is corrosive to either.  Proven, inexpensive corrosion
prevention can be accomplished in any severely corrosive soils using loose
polyethylene encasement.

Engineering Structures, Pipes, *Water Hammer, *Casings,  *Metal Pipes

*Cast Iron Pipes, Superloads, *Joints (Connections)
                                        28

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007B

AMERICAN COCKROACH FEEDING IN SEWER ACCESS SHAFTS ON PARAFFIN
BAITS CONTAINING PROPOXUR OR KEPONE PLUS A MOLD INHIBITOR,

Wright, C. G., McDaniel, H. C., Johnson, H. E., and Smith,
C. E.

North Carolina State University, Raleigh, North Carolina


Journal of Economic Entomology, Vol. 66, No. 6, p 1277-1278, December, 1973.
1 tab, 2 ref.

The control of the American cockroach, Per-iplaneta amerisana, in sewer
access shafts was investigated by adding baits containing 0.125% Kepone
(decachlorooctahydro-l,3,4-metheno-2H-cyclobuta(cd)pentalene-2-one)
or 2 percent propoxur, with or without p-nitrophenol mold inhibitor, and
embedded into paraffin cakes to the infested shafts.  Cockroaches did not
feed on propoxur baits.  Feeding occurred on some Kepone baits with and without
mold inhibitor, but they did not feed on Kepone baits after mold became
visible.  Addition of the mold inhibitor reduced the molding of propoxur
and Kepone baits.  There was a reduction in cockroach numbers in baited sewer
access shafts; however, dead cockroaches were observed only in shafts containing
Kepone baits with visible feeding signs.  Cockroach numbers increased in
shafts with paraffin check cakes.  Baits in moist shafts increased in weight
by absorbing ambient moisture, and disintegrated in humid shafts with high
ambient temperatures.

*Sewers, Eradication (Pests), *Insect Control, Attractanta, Insects, *Pestlcides,
*Insecticides

*Cockroach, Periplaneta ameriaa.no., *Kepone, *Proxopur
  008B

  INSTALLATION OF LARGE-DIAMETER FIBER-GLASS FLEXIBLE PIPE IN
  MUNICIPAL SYSTEMS,

  Hutchison, R. M.

  Johns-Manville Corporation, Denver, Colorado

  Journal of the American Water Works Association, Vol. 65 p 791-793,
  December, 1973.  8 fig, 2 ref.

  Installation considerations for fiber-glass pipe are discussed with special
  emphasis on the value of proper installation and handling practices for
  flexible pipes.  The soil surrounding the pipes must be capable of being
  compressed to a density of greater than or equal to 85 percent standard
  proctor, or be that dense in its natural state.  A maximum 3/4 inch diameter
  crushed rock is ideal for backfill and bedding material.  Installation can
  be evaluated by measuring the initial deflection with full load on the pipe.
  The anticipated ring deflection caused by axial bending, plus ring deflection
  induced by soil load, can be calculated.  Initial deflection should not exceed
  5.0 percent and long-term, full-load deflection should not exceed 7.5 percent.
  In municipal systems elastomeric gaskets (bell and spigot) are the preferable
  joint.  Compression of the gasket should be present in the full offset position
  plus a minimum 5.0 percent initial deflection.  Resin-rich inner surfaces
  with and without aggregate type fillers and thermoplastic liners are in use
  in pipes serving municipal markets.  A major benefit to the utility is chemical
  and abrasion resistance.

  Engineering Structures, Pipes, *Joints (Connections), *Linings,
  Municipal Water

  *Fiber-glass Pipes, Flexible Pipes, Fillers, Gaskets

                                        29

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009B

UNGRADED GLASS TO SEWER PIPE,

Steinberg, M.

Brookhaven National Laboratory, Associated University, Inc.,
Upton, New York.

The Glass Industry, Vol. 54, No. 13, p 14-15, 22, December, 1973.

The development and use of sewer pipes made from ungraded bottle glass bonded
with polymers in a municipal sewer line in Huntington, Long Island are described.
The monomer concentration for ungraded glass is 13-16 percent by weight
compared to 9-10 percent for graded glass.  Ambient promoter catalyst systems
are used in production, and silane is included to promote adhesions to the
glass.  Glass polymer composite (GPC) curing was carried out at 70°C for
4-8 hours.  The GPC cured material is 2-4 times stronger than ordinary concrete;
its chemical durability surpasses concrete; and it is resistant to sulfuric
acid.  The costs associated with it are competitive with other materials,
particularly in the 8-24 inch size range.  A sewer pipe was chosen as the
first application because of possible savings in landfill.  There appears
to be a good match between the waste glass generated in an urban community
and the market for sewer pipe.

New York, Pipes, *Sewers, *Recycling, *Cities, City Planning

Hungtington, Long Island, *Glass Pipes, Ungraded Glass Pipes, *Glass Polymer
Composite
   010B

   DATA ACQUISITION AND COMBINED SEWER CONTROLS IN CLEVELAND,

   Pew, K. A., Callery, R. L., Brandstetter, A., and Anderson, J. J.

   Department of Public Utilities, City of Cleveland, Ohio

   Journal of the Water Pollution Control Federation, Vol. 45, No. 11, p 2276-2289,
   November, 1973.  10 fig, 9 ref.

   The development of a system for the comprehensive control of combined sewer
   overflow pollution in the Southerly Sewerage District of Cleveland, Ohio,
   is described.  The project will acquisition and analyze real time rainfall
   and sewer system load information, and will operate by closed loop
   automatic control.  The control system will operate an optimum combination of
   control, storage, treatment, and conveyance facilities.  Automatic wastewater
   samplers have been purchased, and automated chemical analyzers are being
   acquired to analyze chemical oxygen demand, total Kjeldahl nitrogen, sulfate,
   phosphate, nitrate, ammonia, and chloride.  Mathematical models were developed
   and used as analytical tools for the design and control of the sewer system
   improvements, and remotely operated regulators were designed.  The construction
   cost has not yet been estimated, but should be in the order of $60 million or
   approximately $300/acre ($7400 ha), less than the cost of sewer separation.

   *Combined Sewers, *Rainfall-Runoff Relationships, Storm Runoff, Water
   Treatment, *Model Studies, *0hio, Water Storage

   *Cleveland

                                         30

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 011B

 DISCHARGE RELATIONS FOR  SUBMERGED WEIRS,

 Varshney, R.  S.  and Mohanty,  S. K.

 U. P.  Irrigation Department,  R.E.O., Bhubaneswar,
 Orissa.

 Indian Journal of Power, Vol.  23, No.  7, p  225-228, July,  1973.
 3  fig, 9 ref.

 Mathematical  formulae are  presented for submerged  flow  over  sharp-crested  and
 broad-crested weirs during floods based on  experimental studies.  Dimensional
 analysis shows that the  flow  over a weir in submerged condition  is mainly
 governed by three dimensional paramters:  Froude Number, P/H1, and H2/H1.
 P  stands for  the height  of weir from the river bed; HI  and H2 are depths of
 water  over weir  crest upstream and downstream, respectively.  All three
 parameters can be neglected.   The effect of P/H1 can also  be eliminated by
 suitably choosing the ratio P/H1 such  that  the approach depth does not affect
 the coefficient  of discharge.  Thus it is the ratio H2/H1  which  is mainly
 governing the submerged  flow  phenomenon.  A correlation between  this  ratio SI
 and the discharge ratio  Q/Q1  was used  to establish the  mathematical relationship.
 The different types of weirs  were broadly divided  into  the sharp-crested
 and broad-crested weirs, and  two mathematical relations were suggested for
 evaluating stream flow in  practical cases.   The simplifying assumptions made
 may involve slight errors,  but these are of no major significance to  the
 field  engineers.  Therefore,  the equations  can be  adopted  in practical cases.

 Engineering Structures,  Hydraulics, *Weirs,  *0verflow,  Flow, Mathematical
 Studies, *Mathematical Models, *Floods, Municipal  Wastes

 *Submerged Flow
012B

EXPERIMENTAL FIELD STUDIES REQUIRED FOR THE DESIGN OF
DRAINAGES, (Studii experimentale in teren, necessare
proiectarii drenajelor),

Wehry, A.

Hidrotehnica, Vol. 18, No. 11, p 586-589, November, 1973.  2 ref.

Calculation methods necessary for conducting experimental field studies before
designing drainage systems are presented.  Numerous figures in the text present
views of the drainage structures, pressure loss representation, the nomogram
for calculating the value according to Hooghoudt, the ground water level
representation during and after irrigation and the experimental value H=f(t)
representation.  In order to calculate the distance between drains, Hooghoudt
and Ernst's methods are most often used.  In order to apply the nomograms,
it is necessary to know hydraulic conductivity of the earth layer.  This value
can be obtained only by a field study.  Also, porosity and drainage intensity
must be known.  Equations are provided for various field situations and
examples of calculations are given.

Engineering Structures, *Drainage Systems, *Drainage Engineering, Irrigation
Ditches, Lateral Conveyance Structures, Model Studies, *Mathematical
Studies

*Hooghoudt's Method, *Ernst's Method
                                    31

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013B

THREE-ELEMENT FORMING SPEEDS CONCRETE PIPE JOB,

Etheridge, D. C.

Construction Methods and Equipment, Vol. 55, No. 12, p 54-56, December, 1973.

The in-place production of a large diameter concrete storm drain on a nearly
continuous basis is described.  The 66-inch-ID pipeline advances 320 feet each
4-5 hour work day, formed externally up to its springline in a 12-foot deep
smooth-walled trench; crowned by a slipforming machine; and shaped internally
to 6 1/2 inch wall thickness by a tough, adjustably inflatable sausage-shaped
balloon 325 feet long.  The Fullerform process of the Lomar Company works best
in firm, clayey, rock-free soil, and demands both backhoe and slipform
operator skill, and machine dependability.  The presence on any site of
excessive amounts of sand or stone would rule out this approach.  A backhoe
with specially toothed and round-lipped bucket excavates trench to finished
pipeline OD and grade.  Slipform alignment is controlled by a U-shaped shield.
A raised portion at the rear houses concrete hopper with diverter that splits
concrete between invert and crown.  Reinforced polyurethane Inflataform is
unfolded and laid along the trench, inside the slipform, prior to filling
it with air.  The pipeline can be installed with just eight men, including a
superintendent.

Engineering Structures, *Storm Drains, Pipes, *Concrete Pipes, Municipal Wastes

Lomar Company, *Inflataform, *Slipform
014B

CHECKING THE SIZE OF SEWERAGE INFILTRATION AND LEAKS OCCURRING
UNDER OPERATING CONDITIONS, (Verificarea marimii infiltratiilor
si exfiltratiilor din canalizari in timpul exploatarii),

Blitz, E and Tatu, G.

Hidrotehnica, Vol. 18, No. 6, p 283-288, 1973.  6 ref.

Some simple tools for checking the degree of infiltration of sewage systems as
well as calculation methods are presented.  Sewage infiltration and leaks under
operating conditions can affect the functioning of the sewage system and the
neighboring constructions.  Since not all sewers can be provided with improved
modern checking devices, simple verification and calculation methods had
to be devised.  Calculation methods are given for both ovoidal and circular
sewage sections, using both mathematical formulae and tables.

*Sewers, Engineering Structures, Municipal Wastes, Mathematics, *Infiltration,
*Mathematical Studies
                                      32

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015B

ANOTHER UNUSUAL SEWERAGE PROBLEM SOLVED WITH DUCTILE IRON
PIPE,

Cast Iron Pipe News, Vol. 40, No. 3, p 8-9, Third Quarter, 1973.  3 fig.

The use of ductile iron pipe in the construction of a new sanitary sewage
collection and treatment system for a large lumber mill in Oregon is described.
Domestic sewage of the company will be treated in a new stabilization pond and
by chlorination.  The sanitary sewer system of the mill was deteriorating
for a number of years because of excessive crushing wheel loads generated
from heavy operating equipment and septic attack.  Breaks in the system not
only were contributing to the already heavy groundwater infiltration from
around the joints, but also prevented the passage of a television camera
through the lines for purposes of inspection.  The decision to use ductile
iron pipe with its high beam strength, its great resistance to crushing, and
the water tightness of its push-on joints was baped on excessive wheel loads
from trucks and heavy equipment, the desire to keep infiltration in the new
line to zero, the volcanic type soil conditions with deposits of cinders and
cemented gravels, and a high ground water table in the desert area of the
mill.  The lines were constructed with cast iron tees to connect the six-
inch ductile iron services to the eight-inch ductile iron laterals and mains.
Tees were also placed at strategic locations in the lines with the six-inch
opening plugged for possible future service connections.

Engineering Structures, Pipes, Sewers, *Separated Sewers, *Metal Pipes,
Infiltration

*Ductile Iron Pipe
   016B

   LARGE DIAMETER POLYETHYLENE FORCE MAINS INSTALLED QUICKLY,

   Lash, R. W.

   Safety-Service Director, Fremont, Ohio

   Public Works, Vol. 105, No. 1, p 45-47, January, 1973.  4 fig.

   The use of large diameter polyethylene pipe as a sewage force main in Fremont,
   Ohio, is described.  The installation was p^rt of a sewerage system improvement
   program with the capacity to handle up to SiOOO new homes.  Under the double
   force main design, 12- and 24-inch force mains run from a new pumping station
   with each main discharging into separate existing gravity sewer manholes
   located along the main business street.  Both force mains start adjacent to
   each other at the new pumping station and run 1500 feet along the street where
   the 12-inch force main terminates and the 24-inch pipe continues for another
   1,200 feet.  The force mains were laid mainly under the sidewalks to minimize
   excavation in the street and interference from other underground utilities.
   Due to the design, the project called for many special bends.  Polyethylene
   pipe was chosen over other plastic pipes because it could be installed without
   the use of special fillings since it can bend at a 45 degree angle without
   damage.  Up to 190 feet of pipe a day was installed.

   Engineering Structures, Pipes, *Plastic Pipes, Ohio, *Sewers

   *Polyethylene Pipes, *Mains, Fremont
                                         33

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   017B

   USER LIGHT USED TO LAY PIPE,

   Gautreau, J.

   Water and Pollution Control,  Vol.  112,  No.  1,  p 34-35,  January,  1974.   1 fig.

   The application of laser beams for the  alignment of  sewer pipe,  storm drains,
   and other gravity conduits is discussed.   Productivity  can be increased by
   as much as 50 percent, alignment accuracy enhanced to within 1/8 of an inch, and
   surveying greatly simplified.   In laying  sewer pipe, both the pipe crew and
   backhoe operator are simply guided by a pencil-thin  ray of red laser light
   through or beside the pipe onto a target  for precise positioning.   One of
   the lasers currently used in  Canada is  the Laser-Beam Aligner made by Laser
   Alignment, Inc.  Accuracy of  this unit  on a Quebec storm drain job was
   reported as only a 6-inch drop along an 0.7 mile long line.  Another feature
   making this model popular is  that the average  set-up time is only about ten
   minutes.  Once set up, the device operates essentially  unattended.

   Engineering Structures, Sewerage,  *Sewers,  Equipment, *Construction Equipment,
   Canada

   *Lasers, *Laser-Beam Aligner,  Quebec
018B

PRESSURE SEWER DEMONSTRATION,

Carcich, I. G., Hetling, L. J., and Parrel, R. P.

New York State Department of Environmental Conservation, Albany, New York

Journal of The Environmental Engineering Division, Vol. 100, No. 1, p 25-40,
February 1974.  5 fig, 4 tab, 17 ref.

The pressurized wastewater collection concept was evaluated by installing 12
Grinder Pump (GP) units in a pressurized sewer system and observing their operation
for a 13-month period.  The wastewater was collected and conveyed in the normal
manner by the building drainage system to the grinder pump unit's tank.  From
the grinder pump unit it was discharged through a 1 1/4 inch plastic pipe pressure
lateral to an outside plastic pressure main, 1 1/4 to 3 inches in size.  The
pressure main received the macerated wastewater from all 12 units and simply
discharged it into a gravity system within the city.  The hydraulic design is
a critical facet of any new pressure sewer system.  Some grease accumulation can
be expected, but when design velocities are kept between two fps and five fps,
excessive accumulations will apparently be prevented.  Commercially available
shut-off valves should be installed immediately downstream on the discharge pipe
in order that the GP unit can be isolated from the pressure system for maintenance
and repair work.  The costs for the different components and installation can
vary from $1,620 to $3,438 per unit depending on specific needs.  It is concluded
that GP units are meant to be a supplemental tool in any wastewater collection
system and not a replacement for the conventional (gravity-fed) wastewater col-
lection system.

*Sewers, Pipes, Engineering Structures, Drains, Sewage Disposal

*Gravity Sewers, *Pressure Sewers


                                               34

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019B

STORMFLOW POLLUTION CONTROL IN THE UNITED STATES,

Field, R. and Tafuri, A.

U.S. Environmental Protection Agency
Edison Water Quality Research Laboratory
National Environmental Research Center-Cincinnati.
Edison, New Jersey

U.S. Environmental Protection Agency Report No. EPA-670/2-73-077,
November, 1973.

The problem of storm water discharges and combined sewer overflows is discussed
in relation to the Federal Government's involvement.  This overview details
wet-weather flow pollution as classified in the categories of combined sewer
overflows, storm water discharges, and non-sewered runoff.  As a result of
program research, development, and demonstration projects, it is maintained
that sewer separation in most cases is not the logical course of action for
pollution abatement.  Therefore the following approaches are being explored:
control, treatment, and combinations of the two.  These approaches are
discussed under the topic of flow regulation, storage, porous pavement, new
sewer systems, auxiliary biological treatment, microscreening, flotation,
filtration separation, flow measurement, and management models, as well as
the necessary equipment and instrumentation involved.  It is concluded that
in view of the tremendous quantities of pollutants bypassed during rainfall
from the combined sewer system, it is not reasonable to debate whether
secondary treatment plants should be designed for high BOD or suspended solids
removal, since bypassing at regulators during wet-weather flow occurs.
Rather, wet-weather standards must be instituted at various regulatory levels.

*Storm Water, Storm Runoff, Combined Sewers, *0verflow, Pollution Abatement,
Water Pollution Sources, Water Quality Control, Standards, Discharge  (Water),
Water Treatment, Treatment Facilities, Equipment, Methodology, Federal
Government
020B

PREVENTION AND CONTROL OF INFILTRATION AND INFLOW,

Sullivan, R.

American Public Works Association

U.S. Environmental Protection Agency Report No. EPA-670/2-73-077, November, 1973.

Some of the major findings of an APWA Foundation report bearing the same title
as the above are reviewed together with guidelines for the establishment of
a survey to determine the nature and extent of infiltration and some of the
factors to be used in making an economic analysis of desirable corrective
actions.  Steps involved in the complete infiltration-inflow analysis are
outlined.  Detection methods, equipment, and economic justification with
respect to controlling pollution are disclosed.

*Infiltration, Documentation, Reviews, Surveys, Economic Justification,
Water Pollution Control, *Inflow, Methodology, Instrumentation
                                       35

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 021B

 COMBINED SEWER OVERFLOW REGULATOR FACILITIES,

 Sullivan, H.

 American Public Works Association

 U.S. Environmental Protection Agency Report No. EPA-670/2-73-077, November, 1973.

 As a result of investigative programs conducted by the APWA in such fields
 as the pollution of storm water, the extent of combined sewer facilities,
 the design, operation, and maintenance of combined sewer overflow regulators,
 and the prevention and correction of excessive Infiltration and inflow to
 sewers, it has been shown that storm water is polluted whether or not it is
 carried in separate or combined sewers.  Thus, to meet receiving water quality
 standards, treatment or control facilities may be necessary and therefore
 such equipment must be examined.  Decision guidelines are presented for
 the consideration of the combined sewer overflow regulator facility as a
 possible means for pollution abatement.

 *Storm Water, Water Pollution Sources, Sewers, *Water Quality Control,
 Water Treatment, Equipment, Combined Sewers, *0verflow, Treatment Facilities
 02 2B

 PRESSURE SEWERS,

 Carich, I.

 New York State Department of Environmental Conservation
 Environmental Quality Research Unit
 Albany, New York

 U.S. Environmental Protection Agency Report No. EPA-670/2-73-077, November, 1973.

 The pressure sewer concept deals with a wastewater collection system that
 utilizes a newly developed grinder pump unit and small diameter plastic
 or metallic piping systems.  Results of a 13-month study undertaken to
 evaluate the functional specifications of the pumping units and to gain operat-
 ing experience on the mechanical performance, use pattern, operating cost, and
 maintenance requirements for said units, are reported.  A description of the
 grinder pump unit and the test results are given.  Results indicate used
 plastic pipes and fittings, functioned well for the duration of the demonstration
 project.  It is recommended that pressure sewer systems be considered as
 available engineering technology for use where applicable.

*Plastic Pipes, Investigations, Waste Water Treatment, Treatment Facilities,
Evaluation, Pumping, Performance, Operation and Maintenance, *Sewers

*Pressure Sewers, Grinder Pumps
                                       36

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02 3B

APPLICATION OF MICROSTRAINING TO COMBINED SEWER OVERFLOW,

Glover, G.

Cochrane Division-Crane Company

U.S. Environmental Protection Agency Report No. EPA-670/2-73-077, November, 1973.

Studies initiated to determine the performance of microstrainers in removing
suspended solids are reported.  A flow rate of 2.0 cfs/'acre was used as the
required instantaneous capacity of the treatment facility.  A drawing of
the microstrainer tested as well as the operational procedure are given.
Test results indicate that the microstrainer will reduce suspended solids
from 50-700 mg/liter down to 40-50 mg/liter at flow rates of 35 to 45
gpm/sq ft of gross submerged screen area, that being 42-54 gpm of unimpeded
submerged area.  These flow rates have been routinely achieved within an
arbitrary limitation of 24 inches of water differential between inlet and
outlet liquid levels.  The removal of organic and other oxygen demanding
material is 25-40 percent confirmed by BOD, COD, and TOC measurements performed.
Microstraining had negligible effect on the coliform content of the storm
water.

Performance, Investigations, Suspended Solids, Flow Rates, Treatment
Facilities, Organic Matter, Conforms, *Storm Water, Water Treatment

*Microslrainers
 024B

 HIGH-RATE  MULTI-MEDIA  FILTRATION,

 Harvey,  P.

 U.S.  Environmental  Protection Agency
 Region  II,  26  Federal  Plaza
 New  York,  New  York

 U.S.  Environmental  Protection Agency Report  No.  EPA-670/2-73-077,  November,  1973.

 To evaluate the  applicability and  effectiveness  of  the  high  rate  filtration
 process  in  removing contaminants from combined sewer  overflows, a  testing
 program  was undertaken at  Cleveland,  Ohio's  Southerly Wastewater Treatment
 Plant, beginning in 1970.  The  two major  process units  used  in  the proposed
 treatment  system were  the  drum  screen followed by the deep bed, dual  media
 filter.  The testing program was conducted in two phases:  1) evaluation
 and  selection  of system media and  filtration rates; and,  2)  optimization
 of the filtration process  via coagulants  and polyelectrolyte addition prior
 to filtration.   Estimated  total construction costs  of a filtration plant
 which discharged waste screenings  and filter backwash to  the municipal treatment
 system,  ranged from $830,000 for the  25 mgd  capacity  to $3.754 million for
 200  mgd  capacity at a  design rate  of  24 gpm/sq ft.  Annual cost estimates
 ranged from $97,270 to $388,210.   High treatment efficiencies, automated
 operation,  and limited space requirements are the principal  advantages of
 the  proposed system.   The  high  rate  filtration process  was also evaluated,
 elsewhere,  in  terms of its capacity  for polishing secondary  effluent.   Test
 data  has confirmed  the applicability  of this media  to reducing suspended
 solids,  BOD, and phosphate to low  residuals.

 Evaluation,  Performance, Application  Methods, *Filtration, *Combined  Sewers,
 *0verflow,  Treatment Facilities, Screens, Filters,  Optimization, Construction
 Costs, Operating Costs, Tertiary Treatment,  Automation, Operation  and
 Maintenance, Efficiencies

 Cleveland,  Ohio


                                      37

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025B

SCREENING/DISSOLVED-AIR FLOTATION TREATMENT OF COMBINED
SEWER OVERFLOWS,

Gupta, M., and Agnew, R.

Environmental Sciences Division
Envirex, Inc. - A Rexnord Company

U.S. Environmental Protection Agency Report No. EPA-670/2-73-077, November, 1973.

A major portion of the pollutional substances in combined sewer overflows is
particulate in nature indicating that an efficient solid/liquid separation
process can be expected to provide an effective treatment.  Thus an effective
and economical separation process was designed, tested, and developed on a full-
scale basis by the Environmental Sciences Division of the Rexnord Inc.  Two
full-scale screening/dissolved-air flotation systems have been installed
in Racine, Wisconsin for treatment of combined sewer overflows.  Design
criteria for each of the various elements is tabulated; systems were designed
for completely automatic startup, operation, and shutdown.  To insure optimum
use of the system, a floodgate was installed in one of the overflow sewers
to provide approximately 600,000 gallons of in-system storage.  In addition,
the system has been equipped to be completely self-draining thus enabling
use of the system during periods of snowmelt and cold weather.  The cost of
the Racine system is $30,000 per mgd installed capacity.

*Combined Sewers, *0verflow, Treatment Facilities, Water Treatment, Design
Criteria, Automation, Operation and Maintenance, *Equipment, Capital Costs,
Operating Costs, Laboratory Tests, Pilot Plants, Evaluation, Performance,
Suspended Solids

*Screening/Dissolved-Air Flotation, Racine, Wisconsin
026B

HIGH-RATE DISINFECTION OF COMBINED SEWER OVERFLOW,

Glover, G.

Cochrane Division-Crane Company

U.S. Environmental Protection Agency Report No. EPA-670/2-73-077, November, 1973.

Work on disinfection of combined sewer overflows has been performed in pilot
size contact chambers at a constant flow rate by the Cochrane Division-Crane
Company.  A bacteria kill of 99.99 percent was achieved with chlorine dosages
of 10 ppm in 120 seconds under a flow rate of 20 gpm.  The design chambers
were designed to ensure that the hypochlorite was promptly and well mixed
with stormwater as well as to ensure a high degree of small eddy turbulence
in the passages of the contact chamber.  The extraordinarily high kill rate
of these chambers is attributed to the turbulence during contact time.  The
performance of the pilot units, the preliminary design scheme, and the plans
of a 92 cfs chamber designed according to this scheme are detailed.  The
installed cost of such a chamber has been calculated at about $53,000 (in
1969 dollars).  The inherent advantage of increased turbulence economically
induced in this type of installation to enhance reaction rates makes the
system applicable to many situations.

*Disinfection, *Combined Sewers, Overflow, Water Pollution Control, Flow Rates,
*Pilot Plants, Chlorine, Turbulence, Design Criteria, Treatment Facilities

Bacteria Kill
                                       38

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02 7B

THE SWIRL CONCENTRATOR AS A COMBINED SEWER OVERFLOW REGULATOR,

Sullivan, H.

American Public Works Association

U.S. Environmental Protection Agency Report No. EPA-670/2-73-077, November, 1973.

As a result of laboratory tests and mathematical modeling, significant portions
of settleable and floatable solids can be removed from combined sewer
overflows using a swirl concentrator.  Advantages of this system include
low capital cost, absence of primary mechanical parts, and construction with
inert material; operation of the facility is automatically induced by the
inflowing combined sewage so that operating problems will be infrequent.
Consideration of the use of a swirl concentrator as a combined sewer overflow
regulator facility requires evaluation of many factors.  The following factors
are discussed:  hydraulic head differential, hydraulic capacity of collector
sewer, design flow, dry-weather flow and interceptor sewer capacity, and
amount and character of settleable solids.

*Combined Sewers, *0verflow, Capital Cost, Construction Materials, Operation and
Maintenance, Treatment Facilities, Automation, Design Criteria, Model Studies

*Swirl Concentrator
028B

THE EPA STORMWATER MANAGEMENT MODEL:  A CURRENT OVERVIEW,

Huber, W., Heaney J., and Sheikh, H.

Department of Environmental Engineering Sciences
University of Florida
Gainesville, Florida

U.S. Environmental Protection Agency Report No. EPA-670/2-73-077, November, 1973.

The problem of loading by combined and separate storm sewer overflows on
streams and other receiving waters has led to the development of a compre-
hensive mathematical computer simulation program that models quantity (flow)
and quality (concentrations) during the total urban rainfall-runoff process.
The present Storm Water Management Model (SWMM) is descriptive in nature and
will model most urban configurations encompassing rainfall, runoff, drainage,
storage-treatment, and receiving waters.  It does not define nor determine
any decisions for the system or consider alternative methods for efficient
economic comparisons.  This paper presents an overview of the SWMM by
illustrating its use in Lancaster, Pennsylvania.  Major revisions to the
Model have been made to include urban erosion prediction, modeling of new
treatment devices and biological treatment facilities, monitoring of signifi-
cant pollution sources, flexibility in modeling new areas, new and improved
cost functions for treatment and storage options, and a modest hydraulic
design capability as well as minor programming changes and slight format
revisions.

Loads (Forces), Combined Sewers, *Storm Water, Overflows, *Storm Runoff, Urban
Runoff, *Mathematical Models, Computers, Simulation Analysis, *Rainfall-Runoff
Relationships, Drainage, Storage Requirements, Model Studies

Lancaster, Pennsylvania
                                      39

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029B

THE DESIGN, PLANNING AND CONSTRUCTION OF A 45 INCH DIAMETER
WATER MAIN ACROSS A CONGESTED AREA OF WEST BROMWICH,

Burgess, D. E.

Journal of the Institution of Water Engineers, Vol. 27, No. 7, p 365-376,
October, 1973.  3 fig.

The paper describes the design, planning, and construction of a 1145 mm
nominal diameter steel water main laid through the County Borough of West
Bromwich.  The design of the main, which includes pipe bridges over the
river Tame and the Walsall Canal, and two thrust bores, is explained and the
problems encountered during construction are described.  The main was tested
in three sections.  On completion, the main was drained down and the end
connections were then completed.  The main was recharged and brought into
commission after samples had been passed.

Design Criteria, *Project Planning, *Sewers, Construction Materials, *Steel
Pipes, Testing

Great Britain, *Pipe Bridges, Thrust Bores
030B

A SIMPLE METHOD FOR RETENTION BASIN DESIGN,

Yrjanainen, G. and Warren, A. W.

Water and Sewage Works, Vol. 120, No. 12, p 35, 41-42, December, 1973.

Due to the development of land for agrarian, residential, commercial, or
industrial use, the temporary storage of storm runoff in an onsite retention
basin has become essential because of inadequate outlets for the increased
storm runoff created.  Because of over increasing construction costs and  the
infeasibility of installing large-diameter storm drains, the concept of
ultimate design or improvement of collector storm water systems is impractical.
Thus, retention basins that meter or restrict flow are adequate alternatives.
Design methods, mathematical derivation for an orifice outlet, derivation for
a constant rate outlet, and the  retention basin design criteria are given.

*Storm Runoff, Retention, Design Criteria, *Mathematical Studies, Outlets,
*Storage Requirements

*Retention Basins
                                       40

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031B

HYDRAULICS OF CULVERT OUTLETS,

Callander, R. A.

New Zealand Engineering, p 261-265, September 15, 1973.  5 fig, 3 ref.

Spreading of a jet from a culvert outlet is analyzed to yield depth, breadth,
and velocity in terms of distance from the outlet, with the subsequent
solution being presented in the form of design charts.  These data facilitate
design of a stilling basin to dissipate excess energy, and selection to prevent
scour.  For the latter purpose, the Manning-Strickler formula is used with
the Shields criterion for stability.

*Jets, *Culverts, Data Collections, *Design Criteria, Energy Dissipation,
Settling Basins, Outlets, *Mathematical Studies, *Mannings Equation

Jet Spreading
03 2B

LEAKAGE IN SEWER LINE CAUSES CAVE-IN,

Public Works, Vol. 105, No. 1, p 96, January, 1974.

A property owner filed suit against the City of St. Petersburg for injuries
sustained when he fell in a sink hole located in an alley behind his home.
In Moore v. City of St. Petersburg, 281 So 2d 549  (Fla., September 14, 1973)
the court entered judgment for the defendant city, notwithstanding a jury
verdict for the plaintiff.  The court held that under Florida law, the city
can not be liable when its agents or employees commit a tort in performance
of a governmental function, if there was no direct transaction or confrontation
between one against whom the tort or injury was committed and the agent or
employee of the city.

*Erosion, *Sewers, Leakage, Florida, *Legal Aspects, Legislation, Local
Governments

St. Petersburg, Florida
                                     41

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033B

EPOXY TAR LINES BIRMINGHAM'S TRUNK,

Hayward, D.

New Civil Engineer, p 40-41, January 31, 1974.  3 fig.

To deal with the problem of chemical attack and corrosion, Birmingham, England,
is trying a new method of coating the inside of its sewer tunnel's smooth precast
concrete lining with epoxy tar.  The coating was developed by Spun Concrete
and consists of fiber glass tissue sandwiched between two layers of epoxy tar.
The fiber glass is for strength and abrasion resistance.  A trowel is used to
apply the coating.  The 35 percent increase in cost will be offset by reduced
maintenance and replacement.  The tunnel is 1.5 meters in diameter and runs
through rock riddled with coal seams, ironstone and fireclay.  The coal
seams had been worked and were open or filled with debris, presenting the
danger of local subsidence.  To accommodate this probable eventuality flexible
pipes and linings were used (Flexilok - Extraflex segments made by Spun Concrete).
The epoxy coating survived the construction process well.

*Sewers, *Tunnels, *Linings, Engineering Structures, Concrete Pipes, *Epoxy
Resins, Protective Coatings

Epoxy Tar, Fiber Glass
034B

RECOMMENDATIONS FOR INSTALLING PVC GRAVITY SEWER PIPING,

Durazo, R.

Plastics Pipe Institute

Public Works, Vol. 105, No. 4, p 80-81, April, 1974.  2 fig.

Procedures for installing PVC sewer pipe to get the best results include:
the pipe should be bedded true to line and grade with uniform and continuous
support from a firm base; blocking should not be used to bring the pipe to
grade; lateral restraint should be provided by properly placed and compacted
backfill material; appropriate material should be used for bedding, haunching,
and initial backfilling.  In addition, care should be taken during excavation
to provide as narrow a trench as practical at a point level with the top of
the pipe.  Well points or underdrains may be required when excavating below
ground water level.  USCS Soil Classification, System (FHA Bulletin No. 373)
is described, and haunching and initial backfill procedures during various
conditions and for the various soil classifications are described.

Pipes, Engineering Structures, *Sewers, *Plastic Pipes, *Pipe Foundation

PVC Pipes
                                    42

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      035B

      USE OF PIPELINES AS AEROBIC BIOLOGICAL REACTORS,

      Koch, C. M., and Zandi, I.

      General Electric, Philadelphia, Pennsylvania

      Journal of the Water Pollution Control Federation,  Vol.  45,  No.  12,  p 2537-
      2549, December, 1973.  2 fig,  1 tab,  19 ref.

      Sewerage systems of many cities comprise both pressure and gravity lines.   It
      has been suggested that these  lines may be used as  aerobic biological reactors
      to reduce the biochemical oxygen demand on treatment facilities.   The utilization
      of the pipelines as a treatment facility to stabilize the organic portion
      of solid waste while it is being conveyed in slurry form has also been proposed.
      Stabilization of the combined  solid waste and wastewater is another  possibility.
      If the converted conduits are  relatively long, the  BOD reduction may be
      considerable.  An analysis of  pressure pipeline reactors, sometimes  called
      tubular reactors, with the view towards utilizing pressure pipelines as
      aerobic biological treatment facilities is presented.  A mathematical model
      and a case study are developed.  Parameters considered are wastewater flowrate,
      initial pressure head, seed inoculum  concentration, pipe diameter, gas flow
      rate, air to slurry ratio, DO  concentration, gaseous oxygen concentration,
      initial BOD, temperature, pumping station location  with respect  to pressure,
      and gas injection commencement when the DO levels fall below a given value.
      Also considered were the biological kinetic constants for municipal  wastewater.
      The economic practicality of this form of treatment was not considered,
      but it was shown that BOD reduction could he effected.

      Engineering Structures, *Sewers, *Treatment Methods, *Biochemical
      Oxygen Demand, Water Pollution, Municipal Wastes, *Aerobic Treatment
036B

SEWER-WITHIN-SEWER SAVES CITY $400,000,

Nester, A. W.

City Engineer, Flint, Michigan.

The American City, Vol. 89, No. 2, p 45-46, February, 1974.

The city of Flint, Michigan effected the separation of 1800 feet of combined
sewers by putting a pipe within a pipe, thus saving the city $400,000.  The
cost of open-cut or tunneling for separating the sewers was $600,000.  A 14-
inch sanitary sewer line was laid in the invert of the old pipe, a cast-in-
place, elliptical concrete pipe 60 inches high and 40 inches wide.  The sanitary
sewer connections were tied into it, and the line was covered with concrete.
First, the combined sewer was cleaned; working from manhole to manhole, a
Transite asbestos-cement pipe was placed one eight foot section at a time.
The sections were connected with pressure joints.  Sanitary leads from
buildings were tapped into the new sewer; new leads were routed along the
interior wall contour of the old pipe and were fastened with stainless steel
straps and anchors.  Quick-set mortar sealant prevented leakage of sanitary
sewage into the storm sewer during construction.  When the sewer was in
place, it was concreted over with 3500 psi concrete.

Engineering Structures, Sewers, *Combined Sewers, *Separated Sewers, Manholes,
Pipes, Storm Drains, Tunnels, Urban Drainage, Michigan

Flint, Michigan
                                        43

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037B

THE FRICTION FACTORS OF OSCILLATING PIPE FLOWS,

Hirose, K., and Nobunaka, M.

Okayama University, Department of Mechanical
Engineering

Memoirs of the School of Engineering, Okayama University, Vol. 8, No. 2,
p 44-51, December, 1973.  10 fig, 3 ref.

In this study, the penduluation of water column in the special vertical U-tube
which has about a 2-meter long horizontal straight foot pipe is utilized as
the oscillating pipe flow.  Experimental results indicate that the momentary
friction factors in the accelerating state are smaller and in the decelerating
state are larger than that in steady state for each Reynolds number.

"""Investigations, *Pipe Flow, *Reynolds Number, *Roughness (Hydraulic),
*Turbulent Flow, Steady Flow, Mathematical Studies
038B

RELIEF CONCEPT CONCERNING MIXED SEWERS (ENTLASTUNGS-
KONZEPTIONEN IN MISCHSYSTEM) ,

Munz, W.

Gas- und Wasserfach - Wasser/Abwasser, Vol. 114, No. 11, p 525-529, 1973.
4 fig, 11 ref.

The installation of rain catchment basins to protect the receiving streams
from overflowing combined sewer systems has been an accepted practice for many
years.  These basins have the purpose of holding certain quantities of water
during a rainfall, which is later returned to the purification plant for
treatment.  Calculation methods for construction of rainfall catchment basins
are tabulated.

*Combined Sewers, *0verflow, *Watersheds (Basins), Rainfall, Storm Runoff

*Sewer Overflows
                                  44

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039B

RECONSTRUCTING AN EGG-SHAPED SEWER,

Surveyor, Vol. 143, No. 3258, p  24-26, January  18,  1974.   8  fig.

The reconstruction of  the Bowling Beck and  the  trunk  sewer on Nelson  St.  in  the
City of Bradford is described.   The major part  of  the city lies  in  a  bowl with
only a single outlet to the valley of the River Aire.  This  means that  the
sewers as well as the  natural becks and watercourses  all pass through the
center of the city.  The redevelopment of the central area has necessitated
many diversions and reconstructions of the  drainage system.  The beck
construction consisted of about  110 lin yd  of 10 ft by 7 ft  6 in in situ  RC
culvert at the downstream end as an extension to the  culvert constructed  in
1963.  Upstream of this culvert  some 500 lin yd of  segmental tunnel were  driven
south where a similar  10 ft by 7 ft RC culvert  was  constructed,  80  lin  yd length,
to pick up the west branch of the Bowling Beck.

*Sewers, *Water Supply, Construction, Tunnel

Great Britain, Becks
040B

UTILITARIAN LEISURE FOR BURNHAM-ON-SEA,

Surveyor, Vol. 143, No. 4263, p 9, February, 1974.  4 fig.

The proposed drainage scheme for Burnham-on-Sea UDC is described.  The main
drainage scheme is complete and is the first phase of a complete resewerage of
the district.  The entire plan includes a new regional sewage purification
works and the abandonment of all existing untreated crude discharges to sea.
Large areas of unused claypits were featured in the scheme to provide surface
water storage capacity during tidelock conditions as an alternative to pumping
arrangements.

*Drainage systems, *Sewage Treatment, *Sewers, Surface Waters, Water Storage
                                 45

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041B

SEWER LINE DESIGN BASED ON CRITICAL SHEAR STRESS,

Yao, K. M.

World Health Organization Professor of Sanitary Engineer-
ing, West Pakistan University of Engineering and Techno-
logy, Lahore, Pakistan

Journal of the Environmental Engineering Division, Vol. 100, No. EE2, p 507-520,
April, 1974.  8 fig, 14 ref.

An investigation of all practical aspects in applying the critical shear stress
approach for the hydraulic design of circular sewers was carried out.  The
minimum velocity approach was compared to the critical shear stress approach
in terms of their effectiveness in achieving self-cleaning action, and their
relative effects on the engineering design.  Also, a procedure was developed
for the application of the critical shear stress approach in practical design
of circular sewers.  The following conclusions were reached:  a critical shear
stress in the range of 0.02 psf to 0.04 psf seems to be adequate for sanitary
sewers, while 0.06 psf to 0.08 psf applies to storm sewers; design equations
based on Manning's formula have been developed using the critical shear stress
approach; using a constant minimum velocity for all sewer sizes tends to
underdesign large sewers and overdesign small ones; critical shear stress
approach provides a more economical design in the case of partially full flow
with the flow depth less than 0.4 of the sewer diameter; a design chart and a
proposed design procedure are provided for practical use using the design
equations for the critical shear stress approach.

*Model Studies, *Mathematical Models, *Sewers, *Hydraulics, Engineering Structures

*Critical Shear Stress
042B

DAMAGED SEWAGE PIPE REMOVED BY DIAMOND SAWING,

Industrial Diamond Review, p 102-103, March, 1974.  4 fig.

During the process of aligning eight-foot long by 108 inch o.d. sections of
concrete sewer pipe underground, one of the lead sections was accidentally
damaged.  The problem of removing the damaged section in the shortest possible
time was solved by diamond sawing.  The pipes were being aligned with hydraulic
jacks when one of the units in the lead section was badly mangled.  It was
felt that jackhammers would be too slow.  A standard wall saw unit was adapted
for sawing the circular surface by a firm that specializes in sawing and drilling
concrete structures.  A rig was adapted to the inside of the large pipe and was
operated by a two-man crew.  A 20-inch diameter diamond blade made an initial
slice, followed by a 26-inch blade that cut through the final two inches.
The saw was powered by a nine h.p. motor; the blades rotated at 1400 rpm, and
were water cooled.

*Sewers, *Pipes, *Concrete Pipes, *Engineering Structures

Diamond Sawing
                                 46

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04 3B

NOMOGRAPHS CALCULATE DISCHARGE FROM OPEN, HORIZONTAL PIPE,

Zanker, A.

Haifa, Israel

Heating/Plping/Air Conditioning, Vol. 46, No. 4, p 69-70, April, 1974.  3 fig.

The California pipe flow method for estimating the discharge of water requires
that a pipe be horizontal and at least 6 pipe diameters in length.  No orifice
or nozzle is required for this method, and the only two necessary measurements
are the inside diameter of the pipe, and the distance from the inside top of the
pipe to the surface of the flowing water.  Although the California method is
very simple, It may become troublesome to calculate because of the fractional
exponents involved.  Two nomographs are given which solve the equation within
a matter of seconds.

*Environmental Engineering, *Hydraulics, *Discharge (Water), *PIpes,
Mathematical Models, Model Studies

*California Method, Nomographs
044B

CAPITAL COST MINIMIZATION OF DRAINAGE NETWORKS,

Dajani, J. S., and Hasit, Y.

Assistant Professor of Civil Engineering, Duke University,
Durham, North Carolina

Journal of the Environmental Engineering Division, Vol. 100, No. EE2, p 325-337,
April, 1974.  3 fig, 2 tab, 18 ref.

Three formulations of the drainage network design problem based on variations
of and extensions to standard linear programming suggest a feasible design
methodology for the selection of pipe size and slope combinations for a
given network layout.  The minimum cost design under given assumptions is
produced by this methodology.  Full-conduit flow and a continuum of pipe sizes
is assumed by the first formulation.  The second maintains the full-flow
assumption and limits feasible pipe sizes to discrete commercially available
diameters.  The third allows partial flow and discrete diameters.  The first
is a separable convex variation of linear programming; the second and third
a separable-convex mixed-integer programming model.  The practicality of
mixed-integer programming Is demonstrated, and costs are compared.

*Model Studies, *Mathematical Models, *Engineering Structures, *Pipes,
Environmental Engineering, Drainage Engineering
                                    47

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045B

TUNNEL FAILURE DELAYS SEWER SYSTEM STARTUP,

Engineering News-Record, Vol.  192, No.  2,  p  12,  January 10,  1974.

Operation of a 170 mgd-sewage pumping station in lower Manhattan,  under construc-
tion since 1967, will be delayed until 1975  because of the failure of two
sections of interceptor sewer tunnel that have been completed since 1961, wait-
ing to feed the station.  The failure of the 300 ft of 9 ft diameter concrete
lined interceptor appears related to the construction of the pumping station.
The tunnel sections that failed were driven  in soft ground under compressed
air about 40 ft below the street.  Their primary lining is cast iron segmen-
tal rings with steel rib support.

*Pumping plants, *Sewage, Tunnels, Sewers, Concrete pipes, *Failures
      046B

      TECHNICAL DEVELOPMENTS,

      Pipes and Pipelines International, Vol. 18, No. 1, p 39, November, 1973.

      Technical developments in the pipe and pipeline industry are summarized.  An
      orbital welding machine consisting of an argon arc welding head carrying a
      tungsten electrode which rotates about the pipe joint was developed by Start-
      rite Designs, Ltd., Gillingham, England.  The machine practically eliminates
      underbread in the pipe bore, so that flow patterns can be considerably im-
      proved.  An ICI traveling exhibition toured Great Britain to show how pipes
      made from Propathene, Id's propropylene, have solved many industrial pipework
      problems for drainage and disposal systems.  A combined infill/carrier pipe
      for road and underground drainage was developed from the Turnall asbestos
      cement pipe of TAG Construction Materials, Ltd., Manchester.  A new range of
      horizontal magnetic particle crack detectors was designed by Vitosonics, Ltd.
      Current is passed through the test piece to detect longitudinal defects, and
      magnetic flux generated by a circumferential coil for transverse defect indi-
      cation.

      *Pipes, *Pipelines, *Welding, Welded Joints, Plastics, Drainage System

      Great Britain, Magnetic Crack Detectors
                                         43

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047B

EXAMPLES OF SEWAGE SLUDGE INCINERATION IK THE UK,

Camp, I. C.

J. D. & D. M. Watson

The Institution of Civil Engineers, Vol. 56, Part 1, p 49-62, February,
1974.  4 fig, 4 tab, 6 ref.

Multiple hearth, rotary hearth, and fluidlzed bed Incinerators for sludge
withdrawn from municipal sewage are described followed by an account of the
installation now under construction for the Esher Urban District Council.
Reference is made to similar schemes for the new City of Milton Keynes, the
Royal Borough of Caernarvon, and the Borough of Banbury.  The annual cost
of incineration is shown to range from $3.75 to $12.50 {$2.50 = 1L) per person
served by the system, the amount being dependent on the size of the installation
and the hours run each day.

*Sludge treatment, *Sewage sludge, *Incineration, *Treatment facilities,
Municipal wastes, Operating costs

Great Britain
048B

PINCH VALVES TAKE HOLD ON THE INDUSTRY,

Schneider, L.

Red Valve Co., Inc., Carnegie, Pennsylvania

Water 6, Sewage Works, Vol. 121, No. 3, p 50, 51, 60, March, 1974.  4 fig.

Pinch valves are now being used with increasing frequency in sewer systems
because of their design simplicity.  Pinch valves cannot jam by debris,
eliminate the need   for periodic maintenance or lubrication, and are available
in a great variety of materials and design—pneumatic pinch mechanical pinch,
combination valve designs, and materials that include many elastomers.  Pinch
valves often come with a service life of ten years or more.

*Engineering structures, *Sewers, *Valves, Flow control

Pinch valves
                                 49

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      049B

      GUIDELINES FOR DESIGNING PLANT SEWERS,

      Merrill, W. H., Jr.

      Bissell, Merrill, and Associates, Williamsville
      Plant Engineering, Vol. 28, No.  7, p 95-97,  April 4,  1974.
      4 fig, 1 tab.

      Design criteria for plant sewers are presented.  They should be based on
      information, obtained by a formal waste water survey that details probable
      waste material to be discharged  into the sewer and estimates expected flow:
      maximum surges, minimum flow, and average flow.  Sewer ordinances and health
      codes may establish additional design criteria.  A plan should be made of
      the area and contain:  a plan and a profile  of the project  area, both the
      location and elevation of all structures and underground items near the
      proposed sewer line, and the point of inlet  and point of discharge for the
      proposed line.  Key elements of  good sewer design procedures include:
      alignment, velocity, pipe joints, manholes,  cross connections, pipe strength,
      corrosion problems, corrosion control, pipe  material, and project plans.

      *Design criteria, *Sewers, Sewerage, Estimates, Wastes, Inflow, Flow,
      Legislation, Public health, Discharge lines, Velocity, Pipes, Pipelines,
      Pipe flow, Joints (connections), Manholes, Strength of materials, Corrosion,
      Corrosion control, Planning

      Alignment
050B

UNDERGROUND WASTE MANAGEMENT—A PEOPLE PROBLEM,

Frye, F. C.

Illinois State Geological Survey, Urbana, Illinois

The American Association of Petroleum Geologists Bulletin,
Vol. 58, No. 4, p 749-752, April, 1974.  1 ref.

The application of earth science to underground waste management is discussed.
There are four categories of wastes:  man made refuse, industrial liquid
wastes, high-level radioactive wastes, and sewage effluents and some
agricultural wastes.  Sewage effluents are becoming increasingly important
in the total waste management problem.  Subsurface disposal is one problem
in the management of wastes.  There is clearly a trend toward spreading sludge
on the surface, and at least one major metropolitan area has started a system
of rock tunnels for transporting and storing combined sewage and storm water.
It is estimated that 8.8 billion pounds of suspended solids from the sewer
serviced population of the United States is transported annually.  Other
problems include:  the landfill problem, the purpose of a monitoring system,
whether only naturally safe disposal sites can be used, the recycling of
relatively inert and nonhazardous solid wastes, and the disposal well problem.

Underground waste disposal, *Land management, *Geology, Wastes, Liquid wastes,
Industrial wastes, Radioactive wastes, Sewage effluents, Farm Wastes, Waste
storage, Suspended solids.
                                       50

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051B

CORROSION-RESISTANT PIPE AT WALT DISNEY WORLD,

Water and Sewage Works, Vol. 121, No. 4, p 52-53, April, 1974.

The chilled water and sewer distribution system burried beneath the ground at
Walt Disney World is discussed.  The area's high water table and stringent
demands for performance resulted in the use of new and unusual corrosion re-
sistant pipe materials.  A drainage system keeps the ground stabilized, but
pipe inside the trench is often submerged in water.  The 24 in diameter Temp-
Tlte pipe consists of an outer jacket of corrosion resistant asbestos cement
pipe, a closed cell polyurethane foam insulation, and an inner core pipe of
epoxy lined a-c pipe that carries the water.  It is a factory fabricated pre-
insulated design that does not require expansion joints.  The pipe system is
connected by ring type joints providing a tight seal and allowing for pipe
expansion and contraction.  Thrust blocks are required.  The pipe is not
affected by corrosive soil and does not require cathodic protection.  Water
supply is plentiful in the Orlando area, and seven wells were built to handle
all water needs.

*Sewers, *Water cooling, *Water distribution (applied), Florida, Pipes,
Corrosion control, Pipes, Wells, Water supply

Walt Disney World
052B

GIGANTIC PIPE RESCUES A TOWN FROM FLOODING,

Excavating Contractor, Vol. 68, No. 4, p 20-21, April, 1974.

As rural areas are developed and land runoff becomes a problem, large dia-
meter pipes may provide a viable solution.  In the suburbs of Detroit, a
former flood plain which is now residential was previously perennially flooded.
To relieve this problem, the Henry-Graham Storm Drain was constructed.  This
is a mile-long segment of a steel-reinforced pre-cast concrete pipe, 17 feet
in diameter.  Its design outlet capacity is 2000 cu ft per second.  This
pipe successfully carries incredible water capacities and allows the entire
system to be effective, preventing flooding,

*Floodproofing, *Concrete pipes, Floodplains, Pipes, Rural areas, Storm drains,
Storm runoff, Cities, Costs, Control structures, Drainage engineering

*Land runoff, *Henry-Graham Storm Drain, Pre-cast concrete
                                 51

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 053B

 FLOW SMOOTHING IN SANITARY SEWERS,

 Click, C. N., and MIxon, F. 0.

 Illinois Environmental Protection Agency, Springfield,
 Illinois

 Journal of  the Water Pollution Control Federation, Vol. 46, No. 3, p 522-531,
 March, 1974.  16 fig, 2 tab, 11 ref.

 A study of  municipal waste water systems was undertaken to assess the feasi-
 bility of flow smoothing compared with additional piping as a method of  in-
 creasing the capacity of existing sewerage systems.  It was concluded that
 flow smoothing in sanitary systems does offer an economically attractive
 alternative to relieve sewers needing additional capacity, particularly  if
 the length  of the outfall pipe needing relief exceeds about three miles.
 Flow smoothing also is favored by increasing peak-to-average flow ratios and
 interest rates and by increasing slopes, construction costs, pipe diameters,
 and design  depth of flow.  In addition, capacity increase by flow smoothing
 will result in a proportionate capacity increase in all downstream piping
 and equipment.

 *Municipal  waste water, *Mathematical studies, *Flow, *Pipes, *Sewage systems,
 Costs, Construction costs, Sanitary engineering, Piping, Equipment

 *Flow smoothing, Sewage systems capacity, Flow ratios
054B

NEW RUBBER EXPANSION JOINTS FOR PIPELINES,

Water Services, Vol. 18, No. 935, p 21, January, 1974.

Rubber expansion joints for pipelines are being marketed in the United
Kingdom by United Flexible Metallic Tubing Company, Limited.  The joints
are available in a variety of qualities of rubber and can be fitted for
aggressive chemicals.  They have a strong multi-ply nylon fabric carcass
with wire reinforced collars and a weather proof external cover.  Sizes
range from 32-300 mm bore.  The over length is 130 mm.  Total axial move-
ment possible is + or - 30 mm from the normal free length.  Maximum lateral
offset is from 20-30 mm depending on diameter.  The joints provide a
versatile and economic means of achieving flexibility in pipelines con-
veying fluids under pressure or vacuum.  All forms of movement can be
compensated for, and they also serve to dampen vibrations and prevent the
transmission of noise.

*Expansion joints, *Rubber, Pipelines, Design data, Flexibility

United Kingdom
                                  52

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055B

VACUUM SEWAGE TRANSPORT AND TREATMENT IN RURAL AREAS IN
DENMARK,

Jespersen, F.

A/S Electrolux
Denmark

In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, Institute of
Northern Studies, University of Saskatchewan, p 287-304, August 22-24, 1973.
6 fig, 11 ref.

The article reviews the advantages and potential applications of vacuum sewer
systems in Denmark.  Two of the major arguements presented are: by use of the
vacuum system household water demand could be reduced by as much as 50 percent
and since black water  (e.g. water plus human wastes) is the major source of
pathogenic bacteria and nutrient salts, if one separates its handling from
grey water, great economies in collection and treatment costs could be
realized and improved water quality.  If collected separately sewage
waste volume could be reduced to 5 percent the present level.  Incineration or
chemical treatment could be used to dispose of this black water concentrate.

*Sewage treatment, *Waste disposal, *Water conservation, Bacteria, Water
demand, Cold regions, Water reuse, Water quality

*Demark, *Black water, *Grey water, *Vacuum sewage, Waste water collection
056B

VACUUM SEWER SYSTEMS FOR NORTHERN APPLICATIONS,

Averill, D. W. , and Heinke, G. W.

Project Planning Associates Limited
Toronto, Canada

In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, Institute of
Northern Studies, University of Saskatchewan, p 258-286, August 22-24, 1973.
5 fig, 21 ref.

Where water is scarce, construction materials expensive, and topography and
soil conditions incompatable with required grade lines for conventional
sewer systems, the vacuum sewer system can be a practical alternative for waste
water collection.  Use of this type of system to date in the Bahamas, Canada,
and plans for use in Alaska are reviewed.  Also included is a section on vacuum
transport theory as well as operations, maintenance, and capital costs.  Advan-
tages cited for this type of system include:  horizontal and upgrade transport,
flexibility, water savings.   Vacuum toilets use about one quart of water per
flush as compared with conventional toilets using 2 to 4 gallons per flush.

*Sewerage, *Soil properties, *Topography, *Maintenance costs, *0perating
costs, *Capital costs, Cold regions, Canada, Alaska

*Bahamas, *Vacuum sewer system, *Vacuum transport theory, Waste water collection
                                      53

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057B

STEEL PIPELINE DESIGN,

Hughes, R. C., DeKeyser, W. R., Elder, L. L., and
Wilson, G. R.

Crest Engineering Company, Tulsa, Oklahoma

Civil Engineering- American Society of Civil Engineers, Vol. 44,
No. 3, p 64-67, March, 1974.  1 fig.

Design criteria differ for steel pipelines used for four major purposes.  These
subfields are slurry, liquid petroleum, gas, and water.  Experts in each area
discuss differences between them.  Slurry refers to long distance transportation
of a designed slurry, giving both liquid and solid stresses.  Corrosion/erosion
resistant linings are essential for reducing required wall thickness.  For
liquid petroleum pipelines, criteria for internal and external pressures are
the minimum rather than the limits for the engineer.  Factors to be considered
in design are temperature, fluid temperature, dynamic effects, longitudinal
stress, corrosion, threading and grooving, and wall thickness and defect toler-
ances.  Gas pipelines follow similar criteria, with additional limitations
due to possible internal corrosion.  Water pipelines included those buried for
water supply and transmission pipelines with pipe in diameter 24 inches and
larger.  Stress was based upon internal pressures, external loads and pro-
tective linings and coatings, cathodic protection, and types of field joints.
Standardized symbols in coding as well as communication between engineers
in these sub-fields was deemed necessary,

*Pipelines, *Petroleum, *Design criteria, Standards, Slurries, Temperature,
Fluid temperature, Corrosion, Pressure, Structures, Engineering structures,
Communication, Research

*Steel pipelines, *Liquid petroleum, Water pipelines, Stress
05 8B

CLEANING WATERMAINS USING POLYURETHANE SWABS,

Water and Pollution Control, Vol. 112, No. 5, p 34-36, May, 1974.  4 fig.

A watermain near Toronto, Canada, was cleaned by forcing a polyurethane foam
swab through the main via regular water pressures.   First, the main valves
were closed to isolate the section; the swab was inserted into the top of a
compression-type hydrant which had its internal workings previously removed.
Water pressure from a fire hose on the hydrant supplied the pressure while
the nearest main valve was opened and the swab moved at 100 feet per minute to
an open hydrant at the far end of the line.  The chance of a swab becoming
lodged in a main is small, and can be corrected by a reverse flow.  Insertion
of the swab is not difficult; most of Ontario's hydrants are of the compression
type.  For small mains up to 10 inches in diameter there is no problem—it is
necessary, however, to ensure the plugging of drain holes.  The greatest need
for swabbing is commonly at municipalities using low pH surface water supplies
where filtration treatment is not provided.  Detritis removed by swabbing may
be conducive to bacterial growth, and swabs are often treated with disin-
fectant .

*Pipes, *Cleaning, *Water pressure, *Hydrants, Canada, Municipal water,
Drainage, Bacteria, Disinfection

*Polyurethane, *Water mains, Compression, Toronto, Swabs, Mains, pH
                                 54

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059B

RAIN RETENTION BASINS AND RAINWATER DISCHARGES (REGEN-
BECKEN UNO REGENENTLASTUNGEN) ,

Munz, W.

Gas - Wasser - Abwasser, Vol. 54, No. 3, p 98-110, April, 1974.  40 fig,
13 tab, 2 ref.

Examples for the calculation of rainwater retention basins and compound ba-
sins, a combination of retention basin and settling basin, for complex sewer
systems are presented.  While both rainwater retention and settling basins are
usually designed for a rain intensity of 40 liter/sec that occurs at a proba-
bility of about 10 times yearly, it is acceptable to reduce this value to 30
liter/sec to cut investment costs.  Detailed calculations of runoff yield,
inlet canal, heights of basin and canal, settling basin surface area, over-
flows, flow rates, and retention volumes are described.  Runoff inlet should
be along the longitudinal axis of the basin, or baffle walls should be used
to prevent the content from circulation within the basin.

*Rain water, *Settling basins, Sewer systems, Flow rates, Canal design,
Costs, Design criteria

*Rain water discharges, *Rain retention basins, Runoff yield
060B

WHAT'S HEW IN WATER AND SEWER PIPE?,

Godfrey, Jr., K. A.

Editor, Civil Engineering, New York, New York

Civil Engineering-ASCE, Vol. 44, No. 5, p 72-73, May, 1974.  1 fig.

For a savings of time and money, steel channels were used to line a tunnel
for a ten foot OD sanitary sewer in Staten Island, New York.  The steel tun-
nel lining was designed to carry permanent loading, permitting the contractor
to place the cast-in-place concrete liner before holing the tunnel.  Wide
steel channels (24 inches) were made and welded flange to flange, then pressed
to conform to the tunnel shape.  The length of the job is 17,000 feet, and
is characterized by having a wide segment width of 48 inches to ensure rapid
tunnelling and being the first major tunnel in New York City using neoprene
gaskets which are factory applied.

*Tunnel linings, *Sewers, *Steel pipes, Construction materials, Channels,
Concrete

Staten Island, New York, Steel tunnels, Steel channels, Neoprene gaskets
                              55

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061B

THE DUAL FUNCTIONING SWIRL COMBINED SEWER OVERFLOW
REGULATOR/CONCENTRATOR,

Field, R.

U.S. Environmental Protection Agency, Storm & Combined
Sewer Technology Branch, Edison Water Quality Research
Laboratory, National Environmental Research Center —
Cinn., Edison, N.J.

Environmental Protection Agency Report No. EPA 670/2-73-059, September,
1973.  49 p, 16 fig, 2 tab, 13 ref.

A hydraulic laboratory pilot project was run in conjunction with mathematical
modeling to refine and demonstrate the swirl flow regulator/solids-
liquid separator.  The simple, annularly shaped device requires no moving
parts and provides the dual function of regulating flow by a central cir-
cular weir while simultaneously treating combined waste water by a swirl
action.  The low-flow concentrate is diverted via bottom orifice to the
sanitary sewerage system for subsequent treatment at the municipal works
while the relatively clear liquid overflows the weir into a central down-
shaft and receives further treatment or is discharged to the stream.  The
device is capable of functioning efficiently over a wide range of combined
sewer overflow rates, and can effectively separate suspended matter at a
small fraction of the detention time required for conventional sedimentation
or flotation.

laboratory testa, *Separation techniques, *Mathematical models, *Waste
water treatment, Overflows, Combined sewers, Flow control, Weirs, Design
criteria

*Swirl regulator/concentrator
06 2B

CORNWALL'S NEW PVC TRUNK MAIN,

Pawson, J. M.

Chemidus Wavin Limited,
Meadowfield, Durham,
England

Water  Services, Vol. 78, No. 938, p 124-125, April, 1974.

A description of a large plastic 24 inch water main is given as well  as  details
on  local drinking water treatment, reservoir operation, costs  and  capabilities
of  the new water main.  Demand for additional water due to  an  increase in  resi-
dential population, immigration, and seasonal tourism hhas  risen in the  town  of
Cornwall, as it has in much of England.  This new facility  offers  a possible
solution.

*Water distribution, *Water resources development, Water storage,  Water  supply,
Costs

*Polyvinyl chloride, Great Britain  (Cornwall)

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06 3B

THE PRESSURE SEWER:  A NEW ALTERNATIVE TO THE GRAVITY
SEWER,

Carcich, I. G., Hetling, L. J., and Farrell, R. P.

New York Dept of Environmental Conservation, Albany,
New York

Civil Engineering-ASCE, Vol. 44, No. 5, p 50-53, May 1974, 6 fig.

The key to a new pressure sewer system is the grinder pump.  Placed in the
basement of the house, the pump grinds up large particles in the household
sewage and discharges this fluid to a small diameter pressure sewer.  The
chief advantages gained by use of such a system are the reduction in sewer
installation costs (the pipe need only be laid just below ground level);
and elimination of groundwater infiltration.  In testing performed in the
Albany area it was found that pressure-sewer waste was 100 percent stronger
on a concentration basis yet 50 percent less contaminants were in the water
on a gm/capita/day basis than in conventional gravity sewer waste water.
Sewage volume was 2/3 lower on a per capita basis than for conventional sys-
tems, primarily due to the elimination of groundwater infiltration.  The small
diameter pressure sewer appears to be a proven technology.  More than 20
projects using this type of system are either in operation, under construc-
tion, or being designed.

*Sewers, *Waste disposal, *Facilities, *Costs, Groundwater, Infiltration,
Pressure, New York

*Pressure sewer
064B

THE SEWAGE SYSTEM OF THE CITY OF RANGOON,

Singh, G. P.

The Public Health Engineer, No. 9, p 96, May  1974.

The existing sewerage system was installed in the year 1874 during  the
British regime covering an area of 3.4  square miles of central Rangoon,
Burma.  From 1915 to 1924 the system was extended, bringing the  total
area covered to 6.3 square miles.  The  remaining 44 suburbs have no sewerage
at present, but are served with bucket  and pit latrines.   The contents of
both collecting chambers flow into the  main sewers which discharge  into
the eastern end of the Irrawaddy River.  Municipal sewage  is discharged
into the main sewers by ejector stations at the roadside.  Water consumption
in the city is about 35 gallons per head per  day or 70 million gallons per
day.  The supply is insufficient and authorities have begun the  construction
of a water reservoir project at Pugyi,  32 miles from Rangoon.

*Water supply, *Sewerage, *Sewers, Municipal  wastes, Waste treatment, Water
utilization, History

Burma
                                    57

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065B

SURFACE WATER POLLUTION BY THE DISCHARGE OF COMBINED SEWER
SYSTEMS (POLLUTION DES EAUX DE SURFACE PAR LE DECHARGE DES
RESEAUX D'EGOUT UNITAIRES),

Bex, J.

Techniques et Sciences Municipales, Vol. 69, No. 4, p 185-189, April, 1974.
2 fig, 1 tab, 12 ref.

Problems of the pollution of receiving waters by the discharge of storm runoff
in combined sewer systems, and methods for the design of storm overflows in
such sewer systems are discussed.  In combined systems, all or part of the
storm runoff, far exceeding the quantity of dry-weather runoff, is directly
discharged into the receiving waters without treatment.  This is likely to
cause pollution surge in the latter due to its inherent pollution, and to the
entrainment of municipal effluent and sewer sediments.  The dilution method,
previously used for the calculation of storm overflows, is unacceptable
since the overflow is polluted, and it is not possible to evaluate the pollutant
load caused in the receiving waters.  Instead, storm overflows should be
calculated on the basis of a judiciously chosen critical rain, usually varying
from 15 to 25 liter/sec.  The pollutant load of the receiving waters due to
storm water runoff can be abated by the use of retention basins, or by partial
purification of the storm runoff.  (Takacs-FIRL)

*Sewer systems, *Storm runoff, *Combined sewers, Municipal wastes, Storm water,
Effluents, Path of pollutants, Rainfall-runoff relationships

*Receiving waters, Storm overflows, Pollutant load, Retention basins
066B

INCREASING THE EFFICIENCY OF THE USE OF GUIDE CORDS IN THE
MAINTENANCE OF A GIVEN SLOPE (Povysheniye effektivnosti
ispol'zovaniya kopira-niti pri podderzhivanii zadannogo uklona),

Beylin, D. K., and Strautin, U. F.

Gidrotekhnika i Melioratsiya, Vol. 3, No. 4, p 65-68, April, 1974.  3 fig.

A method for the elimination of errors occurring during digging operation due
to the sag of the guide cord is described.  The guide cord is acted upon by
a force that is equal to the force causing the sag but opposite in direction
in the point of its contact with the depth feeler.  The lifting mechanism
can be in the form of a two-arm lever with an adjustable balance weight at
one end and with a hook at the other.  The use of the lifting mechanism
permits the inter-support distance to be increased from 10 m to 60-100 m.
(Takacs-FIRL)

*Mathematical studies, *Equations, *Slope protection, Operation, Soil
mechanics, Design

*U.S.S.R, Guide cord, Digging
                                   58

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067B

EFFECT OF URBAN STREET PATTERN ON DRAINAGE,

Kao, S. E.

Arizona University

Dissertation Abstracts International, B, Vol. 34, No. 12, p 6099,
June, 1974.

Tradeoffs between alternative street patterns with respect to urban
drainage has been investigated.  The study area is confined to residential
subdivisions where the subdivision boundary is assumed to be the watershed
boundary.  The cost-effectiveness technique is employed to give an objective
evaluation for the three alternative patterns; those being rectangular,
curvilinear, and dendritic.  A framework of a distributed system model
has been constructed for simulating the runoff hydrographs and flow depths
at certain points on the streets.  Results indicated that the dentritic
pattern appears to be the best type of street arrangement in terms of
urban drainage.  This pattern has the smallest percentage of street
intersections occupied by water during a storm; time of occupation of high
water stages at street intersections is much shorter in the dentritic
pattern; and, the development cost for the dentritic pattern is the lowest.

*Roads, *Urban drainage, *Storm runoff, Drainage systems, Evaluation,
Simulation analysis, Model studies, Cost analysis

*Dentritic patterns
068B

ICE VISITS EDINBURGH'S L 22m TUNNELLED SEWER SYSTEM,

Wade, S.

New Civil Engineer, No. 92, p 24, May 16, 1974.

An interceptor sewer system which will intercept the flow from Edinburgh
and direct it for primary treatment on reclaimed land in the Seafield Bay
area will be 18 km long when completed in 1976.  The greater part of the
system is being tunnelled with a primary lining of standard segments and
a secondary lining formed with in situ concrete.  The treatment works will
provide primary treatment although space has been allowed in the total
area of reclamation for extension to further treatment should it ever be
required in the future.

*Sewers, *Tunneling, Construction materials, Tunnel linings, Treatment
facilities

England
                                  59

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069B

PIPELINE NETWORK CALCULATIONS USING SPARSE
COMPUTATION TECHNIQUES,

Mah, R. S. H,

Northwestern University,
Evanston, Illinois

Chemical Engineering Science, Vol. 29, No. 7, p 1629-1638, 1974.
8 fig, 10 ref.

Computation to determine steady-state conditions in pipeline
networks can be facilitated using sparse computation techniques.
Three network algorithms for direction assignment, node-arc
ordering and construction of a minimal length cycle set are
given.  These algorithms are readily implemented using list
processing techniques, making it unnecessary for program users
to supply similar information.  Using these algorithms, it is
possible to obtain substantial reduction in computing time
and core storage.  Computational accuracy may also be enhanced
by reduced number of rounding errors.  The reduction of com-
puting time is particularly dramatic.  Estimates based on opera-
tion counts are partially verified by actual computational ex-
perience.  For a given network the benefit of a single appli-
cation of these algorithms is multiplied many times with itera-
tions and different parametric values.  The development demon-
strates substantial advantages of applying graph-theoretic
techniques directly to increase data processing efficiency.

*Pipelines, *Algorithms, Construction, Computation, Computers,
Models, Data Processing, Networks
 070B

 EFFECTS  OF PIPE MATERIALS  ON QUALITY  OF WATER  SAMPLES,

 Tabatabai, M. A., and Fenton, T. E.

 Iowa  State University
 Ames,  Iowa,
 Department of Agronomy

 Journal  of Soil and Water  Conservation, Vol. 29, No.  3,  p.  125-126,
 May/June, 1974.   2 tab,  5  ref.

 Studies  for  evaluating  the effect  of  metal  (iron) wells  on  ground-
 water  quality in  Iowa have shown that water samples collected
 from metal wells  contained markedly lower concentrations of
 orthophosphate-P  and sulfate-S  than did samples collected from
 wells  constructed with  plastic  pipes.  Rust which formed in
 the metal wells caused  precipitation  of the orthophosphate  and
 sulfate  present in groundwater.  Studies  to evaluate  the use of
 galvanized metal  runoff-collection tanks  for nutrient loss  by
 surface  runoff experiments showed  that orthophosphate-P  con-
 centration in water collected in such tanks decreased with  time.
 No effect of time of water sampling from  the runoff-collection
 tank  on  the  nitrate of  sulfate  concentration was observed within
.48 hours.

 *Pipes,  *Water quality,  *Construction materials, *Metals, Runoff,
 Water  sampling, Plastic pipes

 Iowa,  Iron wells


                                    60

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071B

COMPACT WASTE WATER PUMPING SYSTEMS WITH HIGH CAPACITY
(KOMPAKTE ABWASSERPUMPWERKE GROSSER LEISTUNG),

Jaggi, H.

Schweizerische Bauseriung, Vol. 92, No. 22, p 541-544, 1974.
5 fig, 1 ref.

Compact waste water pumps with high capacity are described
with special regard to cooling systems.  In pump shafts with
no flooding hazards, vertical or horizontal assemblies with
a short drive shaft and conventional electric engines are
used.  However, it is also possible to use compact comonobloc
systems incorporating splash-proof submerged pumps that should
be provided with efficient cooling systems.  Air cooling is
not feasible due to the limited space of the collection shaft.
Effective cooling can be achieved by the use of oil-filled
electric motors with oil cooling in a separate cooler cooled
by waste water.  Such pumps are available for capacities
up to 150 kWatts.

*Waste water, *Pumps, Cooling systems, Equipment

Air cooling, Oil cooling
07 2B

DRAIN CONSTRUCTION UNDER HIGH GROUNDWATER LEVEL CONDITIONS
(0 STROITEL'STVE DRENAZHA V USLOVIYAKH VYSOKOGO URONNYA
GRUNTOVYKH VOD),

Kaziyev, B. M.

Gidrotekhnika i Melioratiiya, No. 2, p 81-82, 1974.

Factors influencing the cave-in of trench walls in areas
with high groundwater level were studied.  In most cases,
cave-in did not extend over the entire depth of the trench,
but started out from the depth with the highest moisture
content.  In relatively dry sections, cave-in extended
over the entire height, and was often preceded by cracks
parallel to the trench wall.  Cave-in was found to be con-
ditioned by the non-linear motion of the excavator.  Also,
cave-in occurred most frequently on the side of the spoil
bank.

*Groundwater, Draining, Sewer systems

*Cave-ins
                                    61

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073B

INVESTIGATION OF THE OPTIMAL LIFE OF FIXED CAPITAL IN WATER
SUPPLY AND SEWER SYSTEMS  (AZ ALLOESZKOZOK OPTIMALIS ELET
TARTAMANAK VIZSGALATA A VIZELLATAS ES CSATORNAZAS TERULETEN) ,

Magony, L.

Hidrologiai Kozlony, Vol. 54, No. 1, p 10-14, January, 1974. 7  tab.

Considerations concerning the determination of the optimal life
of fixed capital in water supply and sewer systems are presented.
Records on the maintenance, repair, and overhaul of water supply
and sewer systems should give information on both the costs  and
on the expectable life of the facility.  Such records should
also permit the determination of the optimum time for replacement
of a given facility.  The life of such facilities is determined
by physical wear and economic considerations.  A given facility
should be replaced as soon as the costs of repair and overhaul
for a given period of time in the future exceed the total of the
earlier repair and overhaul expenditures.  Or, replacement may
be desired at a time when the anticipated costs of overhaul are
nearly equal with the value of a new, modern facility.  The
quantification of these factors is possible by the introduction
of a so-called factor of usefulness, i.e., a sum of scores
determined by various criteria, e.g., weight, specific weight,
power and fuel consumption, reliability and write-off.

*Sewer systems, *Capital costs, Maintenance costs, Water supply,
Facilities

Modernization
074B

DESIGN OF A COMBINED SEWER OVERFLOW REGULATOR CON-
CENTRATOR,

Field, R.

Water Quality Research Laboratory,
National Environmental Research Center,
Environmental Protection Agency,
Edison, New Jersey

Journal of the Water Pollution Control Federation, Vol. 46, No. 7,
p 1722-1741, July, 1974.  24 fig, 2 tab, 15 ref.

A new type of combined sewer overflow regulator/concentrator was
developed under the auspices of EPA, Edison.  The swirl unit which
resulted offers potential control of both quantity and quality of
overflows.  Mechanical breakdown and power requirements and cor-
rosion complications are eliminated to a great extent, and detention
times are very short.  It is simple to design, but requires evalu-
ation of the following factors:  hydraulic head differential
between the collector and interceptor sewers, hydraulic capacity
of collector sewer, design flow, dry weather flow and capacity
of interceptor sewer, and amount and character of settleable
solids.

*Combined sewers, *Environmental Protection Agency, *Design
criteria, *Hydraulic design, Sewer systems

Dry weather flow, Settleable solids
                                   62

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075B

COMPUTERIZED REPORTS IMPROVE SEWER MAINTENANCE,

Van Natta, W. S.

The American City, Vol. 89, Mo. 6, p 81-83, June,  1974.
2 fig.

Accurate and accessible records are essential in the efficient  operation of  sewers,
and in the inexpensive operation of the same.  Information  is needed  on each
separate length of sewer in the city's system, and  the development of  the  sorts
of records most helpful to those needing the information.   A statistical record
evaluating the efficiency and progress of overall maintenance is  required  for
administrators and engineers, and a detailed record which would reflect each
individual maintenance action and the expense to that individual  portion sewer
system is necessary.

*Sewerage, *Costs, *Municipal wastes, Statistics,  Sewer systems,  Maintenance

Records
076B

EXPERIENCE WITH BUTTERFLY VALVES,

Popalisky, J. R.

Division of Water Supply, Kansas City, Missouri

American Water Works Association, Vol. 66, No. 6, p. 349-351,
June, 1974.  4 fig, 1 tab.

The use of rubber—seated butterfly valves is elucidated.  The valves are employed
in low-pressure applications at a water treatment facility in Kansas City,
Missouri.  Experience with these valves has been generally favorable except for
30 in a group of 32 associated with a raw-water pump discharge-and-distributions-
control system for a treatment facility.  The valves had gum-rubber seats and
stainless-steel disc edges.  The isolated seat failures were attributed to the
substitution of inferior rubber compounding material and the use of the seats
in a non-disinfected raw-water environment.

*Butterfly valves, Water treatment, Equipment, Water supply

*Raw-water pump discharge-and-distributions-control system
                                    63

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077B

SOME INVESTIGATIONS CONCERNING UPVC WATER AND SEWER
PIPES AND FITTINGS,

Janson, L.-E., and Valimaa, P.

VBB, Consulting Engineers and Architects, Stockholm,
Sweden

Journal of the American Water Works Association, Vol. 66, No. 6, p 360-368,
June, 1974.  18 fig, 10 ref.

Developmental work conducted in Finland on long-term behavior of pipes and
fittings as a function of raw material properties and manufacturing  techniques
is discussed.  Results show that the raw material properties for UPVC pipes
are far more important for the long-term strength than has been recognized in
most international standards.  As for pressure pipes, the permissible tensile
stress can easily be raised if proper requirements of the raw material are
formulated and an adequate testing method is introduced.  Even for sewer pipes
the raw-material properties are of great importance for the long-term behavior
of the total installation.

*Pipes, Construction materials, Pressure conduits, Sewers, Testing,
Performance

Fittings
078B

STATIC CALCULATION OF SEWAGE PIPES MADE FROM HIGH-PRESSURE
POLYETHYLENE (STATISCHE BERECHNUNG VON ABWASSERROHREN ADS
POLYAETHYLAN) ,

Gaube, E., Mueller, W., and Falcke, F.

Kunststoffe, Vol. 64, No. 4, p 193-196, April, 1974.  5 fig, 2 tab, 9 ref.

Static calculations of high-pressure sewage pipes in different types of
soil are presented.  Separate calculations are given for polyethylene
pipes laid over or under the groundwater level or in riverbeds.  Pipes
laid under the groundwater level or in riverbeds should be calculated
both for deformation by soil pressure and for buckling due to the exter-
nal overpressure of the groundwater or river water.  Formulae for the
determination of elliptical deformation due to soil pressure and for the
buckling are presented.  Pipes laid in soils with the properties of vis-
cous liquid (such as in marshlands) should be calculated for buckling a-
gainst the external liquid pressure.  When using polyethylene pipes for
relining existing canals, the buckling behavior of the pipes should be
taken into account.

*Sewage pipes, *Soil pressure, Soils, Calculations, Canals, Polyethylene,
Groundwater

*Static calculations
                                    64

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079B

NEW DESIGNS OF PIPELAYING IMPLEMENTS FOR DRAIN BAGGERS
(Novyye konstruktsli truboukladyvayushchikh prisposoblenly dreno-
ukladchikov),
Naryshkina, V. L., and Nedokuchayev, B. N.

Gidrotekhnika i Melioratsiya, Vol. 3, No. 4, p 68-71, April, 1974.
3 fig, 3 ref.

Tendencies in earthenware pipelaying technology for drainages are
outlined on the basis of a review of foreign patents.  Pipelaying
equipment providing for circular cushioning layer should have forced
pipe feeding to prevent the pipes from separating.  For great depths,
up to 4 m, pipelaying equipment should be provided with adequate im-
plements for the correction of the height and angular position.  To
reduce friction and resistance during pipe feeding, the frictional
pipe feeding mechanism should have roller bed guides rather than slid-
ing guides.

*Drainage, *Patents, *Equipment, *Pipes

Pipelaying, Earthenware pipes
    080B

    THE DESIGN OF FILTER ADAPTERS FOR IRRIGATION PIPES (0
    konstruktsii prisoyedineniya fil'tra k polivnomu trubo-
    provodu) ,
    A. G. Vasil'ev

    Gidrotekhnika i Melioratsiya, Vol. 3, No. 4, p 61, April, 1974. 3 fig.

    New design of filter adapters for irrigation pipelines is presented.
    The filter, 20 mm in diameter and 175 mm in length, is placed in a
    pipe section with increased cross section at the beginning of the
    pipeline.  The cross-section of the pipeline is equal to the annular
    cross section formed between the section of increased diameter and
    the tubular filter.  The new design of the filter adapter reduced
    the coefficient of local resistance and the pressure by up to 6 to 8
    times as compared with the conventional adapter -without increased dia-
    meter.  The filter is suitable for the retention of particles larger
    than 0.8 mm that are susceptible of clogging the sprinklers.

    Irrigation, *Pipelines, *Filters, Pipes, Sprinklers

    *Filter adapter
                                        65

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081B

SUBMERSIBLE PUMPS IN THE SEWAGE SYSTEM,

Fries, H.

Royal Institute of Technology, Stockholm, Sweden

The International Technical Review, No. 95, p 246-250, 1974.  8 fig, 8 ref.

Sewage is being pumped over long distances in many countries.  Choice of
pump types and design of pump stations is discussed, with the criteria
depending on the type of treatment that the sewage will receive at the treat-
ment plant.  Too long a retention time in peripheric pump stations can give
a septic water that is hard to treat, especially in warm countries.  Pumps
should be sufficiently wear resistant to handle sand and gravel and should
be designed for a mild action only if necessary for the pump function, so
that the efficiency of automatic strainers at the treatment plant is not
adversely affected.  Small pump stations can be designed with tangential
inlets and steeply sloping bottoms for optimum aeration and minimum cleansing
demand.  For large pump stations, however, model testing is necessary to
determine the best inlet conditions to the pump.  In addition, multipump
stations are discussed, which offer the possibility of equalized feeding of
treatment plants, but must be equipped with not only step-wise start but
also step-wise stop of the pumps.

*Pumps, *Sewage, *Equipment, *Pumping, Design criteria, Waste water
treatment, Sewage treatment, Pumping stations, Automation, Cleansing

*Treatment plants, Multipump stations, Model testing
082B

PLANNING AND CONTROL OF COMBINED SEWERAGE SYSTEMS,

Glessner, W. R., Cockburn, R. T., Moss, F. H., and Noonan, M. E.

City and County of San Francisco, San Francisco,
California, Department of Public Works

Journal of the Environmental Engineering Division, Vol. 100, No. EE4,
p 1013-1032, August, 1974.  6 fig, 4 tab, 2 ref.

A detailed study of the San Francisco Bay area led to the preparation of a
Master Plan for Wastewater Management, applying systems engineering to the
use of combined waste water control and management of combined sewer over-
flows .  Three waste water treatment plants with a combined average daily
sanitary capacity of 100 mgd and an interceptor system of approximately 300
mgd peak capacity to service 43 separate combined sewer districts were
investigated.  Problems included control of the massive and dynamically
variable wet weather periods of short duration and control of the smaller
volume of dry weather flow.  Water quality standards and planning alter-
natives were considered.  It was concluded that a combined sewer system with
added storage and enlarged treatment to reduce overflows will provide a
higher level of water quality protection than separate storm and sanitary
systems.

*Waste water treatment, *Combined sewers, *Management, Planning, Overflows

*Treatment plants, *San Francisco, California, Master Plan for Wastewater
Management


                                     66

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083B

SLOTTED DRAIN IS DESIGNED FOR SAFETY,

Morris, G. E.

Armco Steel Corporation,
Metal Products Division

Public Works, Vol.  105, No. 9, p 76-77, September, 1974.

Design engineers at the Armco Steel Corporation have produced a recessed
drainage pipe with  a continuous opening that is flush with a highway surface.
This prevents ponding and sheeting of rainwater along roadways, and is both
economical and safe.  This  Slotted Drain pipe  is a welded-seam, helically
corrugated steel pipe.  Proper backfill material plus the fact that the pipe
is  installed in the firm foundation of a roadbed add to  the structural
integrity of the Slotted Drain.  Applications  include installation along
median barriers of  superelevated highways,  installation  next to curbs on
residential streets, and use in paved parking  lots and airport ramps.  Tests
showed that this drain does not freeze at temperatures as low as  -45 F and
with its continuous operation, sheet flow is intercepted and disposed of
before it can clog  the pipe.

*Pipes, *Design, Engineering structures, Highways, Drainage, Installation,
Drain pipes, Municipal runoff, Rainfall, Storm runoff

Armco Steel Corporation, Slotted Drain
084B

PUMPS FOR SEWAGE TREATMENT PROCESSES,

Sowden, W. H.

The International Technical Review, No. 93, p 240-243, June, 1974.  7 fig.

A wide scope of biological and chemical treatments of sewage utilize pumps
and pumping stations.  Design features differ for pump impellers and casings.
Services on which pumps must be used include:  movement of untreated, coarse
screened or comminuted sewage; storm water pumping; sludge transfer and
sludge circulation services; water pumps for treated effluent pumping; and
water pumps for high pressure effluent hosing.  In a sewage pumping station,
care is needed in the layout of pumps to avoid problems caused by suspended
matter.  Flow measurement, adequate ventilation, and precautions against
hydraulic surges are dependent upon the type of plant requirements.  Pump
stations cover a range of a few meters cubed per day to nearly half a million
meters cubed per day.  Design features are becoming more specific according
to the type of sewage treatment facility.

*Pumps, *Pumping stations, *Design criteria, Sewage treatment, Circulation,
Sewage sludge, Water pumps, Flow measurement
                                  67

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085B

PVC SEWER PIPE MEETS TIGHT SPECIFICATIONS,

Public Works, Vol. 105, No. 7, p 84, July, 1974.

Twenty-five sewer construction projects are under way in New Castle
County, Delaware, in anticipation of a rise in population.  Johns-
Manville Rlng-Tite PVC sewer pipe in 8-inch to 12-inch sizes are being
selected due to their availability and reliance in meeting the strict
infiltration/exfiltration limitations.  Also the pipe's light weight
and 20-foot lengths allow trenches to be opened and closed quickly.

*Plastic pipes, *Sewers, Construction materials, Delaware, Water
pollution control
086B

SEWER PIPE:  INFILTRATION IS THE ISSUE,

Fairweather, V.

Civil Engineering-ASCE, Vol. 44, No. 7, p 79-83, July, 1974.  4 fig.

Due to the 1972 amendment of the Water Pollution Control Act, the
infiltration/inflow rates to sewers is becoming an important con-
sideration for applicants proposing new sewage treatment facilities.
A three-phase procedure for complying with regulations requires a
preliminary infiltration/inflow analysis, a sewer system evaluation
survey, and sewer rehabilitation and/or construction or expansion of
treatment plants.  The problems, economics, and technology associated
with this legislative requirement are reviewed.

*Pipes, *Sewers, *Infiltration, *Inflow, legislation, Repairing,
Federal Water Pollution Control Act, Sewage treatment, Treatment
facilities
                                     68

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087B

THE NEATH VALLEY SEWERAGE SCHEME,

Pipes and Pipelines International, Vol. 18, No. 3, p 25-26, June, 1974.  1 fig.

The development of 1200 mm diameter ductile iron pipe made available large
diameter pipe with the strength of steel but possessing corrosion-resistant
qualities better than those of gray steel.  The Neath Valley Joint Sewerage
System, Neath Valley, Great Britain, will use 2200 m of this pipe with a
concrete lining.  This pipe will receive the effluent from a pumping station
equipped for grit removal and the screening of solids, and will convey the
effluent to a submarine outfall.  The pipes are being laid on a bed of
crushed lime-stone aggregate and sand is used to surround the pipes.
Polyethylene sleeves provide additional protection against corrosion.  The
pipes are connected by Stantyte joints, which are specially shaped rubber
gaskets which fit in the sockets; the joints are completed by pushing the
spigots into the sockets of mating pipes.

*Pipes, *Pipelines, *Sewers, *Metal pipes, Joints (connections), Water
conveyance, Sewerage, Hydraulic structures, Engineering structures,  Great
Britain

Neath Valley, Iron pipe, Stantyte joints
    088B

    IMPROVING HAILSHAM'S  SEWERAGE,

    Surveyor, No.  4285, p 37,  July,  1974.   1  fig.

    New sewerage facilities  are  described  including  combined  schemes  for  the  pro-
    vision of sewerage and pumping  stations for  the  northern  drain  of  Hailsham,
    Sussex.  Over the past ten years,  several schemes  have been  implemented to
    provide regional sludge  treatment  facilities from  various works.   Previous
    sludge processing facilities were  designed for a larger area with a population
    of 38,700 and include a  sludge  heater  house, two primary  digestion tanks, a
    gas holder, two thickening tanks,  and  pressing plant.  The most recent
    facility includes 6 km of  sewers and a pumping station.   The present  popula-
    tion served is 10,200, but the  facilities were designed for  ultimate  expansion
    to 16,500.

    *Combined sewers, *Treatment facilities,  Construction, Design criteria,
    Pumping stations, Drain  areas

    Hailsham, Sussex, Sludge processing, Population  expansion, Regional treatment
                                        69

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089B

WASTEWATER COLLECTION,

Tara Singh, H. D.

Nottingham and Associates, McLean, Virginia

Journal of the Water Pollution Control Federation, Vol. 46, No. 6, p 1191-1195,
June, 1974.  43 ref.

A review of waste water collection is presented.  Topics covered include
strategies of the Water Pollution Control Federation, sewer design and con-
struction, sewer monitoring and maintenance, and economic considerations.
Pressure sewers, computer programs for design and cost, a modified dynamic
program of collection, and infiltration rates and materials of sewer construc-
tion are discussed.  Techniques for measuring flows in sewers, preventive
maintenance programs, television inspections of sewers, smoke testing of
sewers, and insertion techniques to use polyethylene pipe to repair defective
sewers are presented.  Various ways in which communities have saved money with
their sewer systems are reported.

*Sewers, *Design, *Construction, *0peration and maintenance, Flows, Pipes,
Costs, Computer programs, Water Pollution Control Federation, Reviews

*Waste water collection
090B

SPECIAL METHODS OPEN STORM-BLOCKED PIPELINE,

Water and Sewage Works, Vol. 121, No. 8, p 60-61, August, 1974.

New techniques for cleaning out storm-blocked sewer pipes were developed and
implemented by the Robinson Pipe Cleaning Company.  Several miles of 42-inch
main interceptor sewer line were disabled, in an area from western Baltimore
suburbs to their sewage treatment plant, as a consequence of Tropical Storm
Agnes.  After damage to the line was repaired, a five-mile portion had to be
cleaned, unseen debris removed, and hidden defects located.  Specialized small
equipment was used, including high-pressure jets, bucket pullout machines,
augurs, and trash pumps.  To facilitate cleaning, water was pumped through
jet-equipped trucks at pressures of 1500 psi to break up bulk material;
trash pumps disposed of the slurry created; heavier objects were handpicked
from the line; brick and brick-sized stone were bucketed through the line
and removed through manholes.  After final jetting and pumping to flush fine
material, the pipes were checked visually, using miner's helmet lights and
torches.  The line was then functionally operative.  These methods saved costs
and time ranging up to 90 percent of those of replacing the pipe system.

*Pipelines, *Sewage treatment, Equipment, Costs, Storm sewers, Pumping,
Waste disposal

Sewage treatment plants, Pipe cleaning
                                     70

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09 IB

TV INSPECTIONS SLASH SEWER COSTS $300 PER REPAIR,

McLaughlin, S. J.

Metropolitan St. Louis Sewer District,
St. Louis, Missouri

The American City, Vol. 89, No. 9, p 51-52, September, 1974.

A preventive maintenance program at the Metropolitan St. Louis Sewer District
was found to reduce costs of sewer repair drastically.  In the last year,
2.1 million feet of sewer lines were inspected by closed-circuit television
cameras in order to find the causes of failures such as cave-ins and backups.
The previous cost of digging up a trouble area was about $400; each television
inspection costs $33, with average repairs costing $40.  This saves over $300
per problem.  In addition, some critical areas for regular line cleaning
operations were identified and computerized.  For example, a leaf burning ban
is a major cause of expected sewer blockage in the fall when leaves are swept
into gutters.  Preliminary inspections are also made of each sector of pipe
to be cleaned.  Wet weather information is obtained from measuring devices
placed through manholes.  Sewers are cleaned by rodding equipment or bucket
machines.  By the combination of preventive maintenance, flow surveillance,
and equipment improvement, costs of repairs have been cut by about $150,000
per year.

*Maintenance, Sewer systems, Pipes, Equipment, Construction, Flow, Planning,
Costs

*Sewer repair, *Television inspection, Preventive maintenance
092B

UPDATING AGING SEWERS WITHOUT TRENCHING,

St. Onge, H. S.

Cliffside Pipelayers,
Scarborough, Ontario, Canada

Engineering and Contract Record, Vol. 87, No. 7, p 40-41, 44, July, 1974.

Technology for sewer renewal without excavation costs less, avoids public
nuisance such as construction noise and inconvenience, and prevents problems
of damage to gas and water lines.  Major causes of trouble in sewers are
protruding laterals, calcite buildup, and root infestation obstructions
which reduce cross-sectional area and produce turbulent flow, as well as
deterioration of the pipe walls.  In the city of Toronto, a reaming operation
was designed to increase pipe flow capacity by first removing obstructions.
Renewal is effected by using inserted close-tolerance polyethylene pipe.
A video-reaming technique was successful, whereby the operator of the reamer
could observe, on closed circuit television, the size and shape of objects
encountered in order to pull and cut with the proper amount of pressure.
Once reaming is complete, the length of sewer is cleaned with a high pressure
jet spray vehicle; the close fitting pipe is pulled by a vibrating nose
cone; and the plastic liner is inserted by means of a hydraulic power winch
truck positioned over a manhole.  A final process involves remote lateral
cutting and grouting to insure leakproof connections.

*Sewers, *Plastic pipes, Pipelines, Materials, Construction, Maintenance,
Canada

*Reaming, Pipe repairs
                                     71

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093B

MORE THAN A MYRIAD,

Engineers Notebook, No. 173, p 355-356, August, 1974.

The metropolitan sewage system of Melbourne, Australia has been expanded
to include a modern waste treatment plant southeast of the city.  As part
of the pollution controls, an effluent outfall line was constructed to
discharge purified effluent from the plant out to the ocean.  Construction
of this line involved 35 miles of trenching, manufacture of an equivalent
length of large-diameter concrete pipe sections, installation, backfilling,
and landscaping.  Joint seals of Neoprene for the 90 to 100 inch diameter
outfall pipe sections were chosen because of its properties of long-term
retention of resilience and sealing integrity.  Special pipe sections -were
designed where topography necessitated bends in the line.  When the system
is fully operable, it will serve 175 square miles and handle 50 million
gallons of waste water per day.

*0utfall sewers, *Municipal wastes, Waste treatment, Construction, Pipes,
Materials, Equipment, Installation, Concrete pipes

Neoprene joint seals, Australia
094B

THE DESIGN AND CONSTRUCTION OF AYCLIFFE SEWAGE
WORKS EXTENSIONS,

Brooksbank, H. R., and Dyson, J. M.

Water Pollution Control, Vol. 73, No. 4, p 367-368, 1974.  1 tab.

In 1941, the Aycliffe sewage works was constructed to serve a Royal
Ordinance Factory, later to be taken over after the war by the Board of
Trade as an industrial estate.  From this estate, sewage was discharged to
the sewage works.  When the land was bought by the Darlington Rural District
Council to provide sewage treatment facilities for Newton-Aycliffe in 1950,
the works contained 1 screen, 3 rectangular sedimentation tanks, 4 biological
filters, 4 humus tanks, 2 pumping stations, 4 sludge storage tanks and
sludge-drying beds, with a capacity of 2.275 x 1000 cu m/d DWF.  These sewage
works were modified in 1964 to service the population of 20,000 in the new
town, with an increased water flow from the industrial estate.  A separate
plant was built to the north to enable a gravity system to be used.  This
new operation comprised preliminary treatment, storm tanks, 2 circular sedi-
mentation tanks, 4 biological filters, 2 humus tanks, recirculation pumping
station, heated sludge digestion and sludge-drying beds.  The new capacity
was 3.68 x 1000 cu m/d DWF.  When the town's population was increased to
45,000 in 1966, an increase in the industrial estate was expected.  Therefore,
the Darlington Rural District Council made the above provisions for indus-
trial development.

*Sewage treatment, *Waste water treatment, *Water pollution, *Industrial
wastes, Water quality control, Biological treatment, Sludge treatment,
Domestic sewage, Effluent control

*Biological filters, *Sedimentation tanks, *Humus tanks, *Sludge storage
tanks, *Sludge-drying beds, Heated sludge digestion, Recirculation pumping
station, Storm tanks
                                    72

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095B

TWENTY-FIVE PERCENT SAVINGS WITH STEEL STORM SEWER,

Water and Sewage Works, Vol. 121, No. 7, p 63, July, 1974.

In a suburb of Oklahoma City, the choice of 8000 feet of  storm sewer gave
the city some 25 percent savings.  Smooth-flow corrugated galvanized steel
pipe was the basis of an important sewer project in Bethany, Oklahoma.
Through a bond issue in 1970, financing for a storm sewer was approved
along two miles of a heavily-traveled avenue.  Before bids were submitted
on this project, corrugated steel pipe fabricators modified city specifi-
cations to include smooth-flow, which is a process in which galvanized
steel culvert pipe is dipped twice into bituminous material.  This material
reduces the turbulence of the flow and preserves the steel pipes' inherent
flexibility.  This pipe can be installed without disturbing traffic and
business.  The standard 20 foot lengths of 78 inches diameter of galvanized
steel pipe weigh much less than the standard 8 foot sections of other
materials.  This lighter weight means less expensive equipment and fewer
laborers needed in installation.  With the proper coating, the corrugated
steel pipe will last as long as other materials.

*Storm sewers, Drainage systems, Equipment, Sewerage, Steel pipes,
Pipelines, Pipes, Separated sewers, Materials, Oklahoma

*Corrugated galvanized steel pipes
096B

MEASURING SEWAGE FLOW USING WEIRS AND FLUMES,

Mougenot, G.

Technical Services Station, Project Operations
Branch, Ontario Ministry of the Environment,
Ontario, Canada

Water and Sewage Works, Vol. 121, No. 7, p 78-81, July, 1974.  2 fig,
10 ref.

Two basic problems when considering flow measurement by means of weirs and
flumes are the primary device and the method for the "head" measurement.
Although the primary and secondary devices are joined as an installation,
they are usually separately manufactured, with the installation consisting
of a check of the relationship of the datum point of the one device to that
of the other.  These devices have been popular in irrigation systems, how-
ever, most weirs and flumes are not installed in hydraulic situations approx-
imating those in irrigation for which rating tables were made, when being
used in sewage works.  A "V" notch weir is used where head loss is tolerable,
and must not be used where the fluid flow contains entrained materials which
could plug the notch.  Settleable materials might degrade the performance
of this weir if the materials collect on the upstream side.  The fluid flow
through the notch should clear the downstream side of the bulkhead, leaving
air under the "nappe".  The head/flow ratio at low heads is greater than at
high heads.  Installation costs are less than those for the Venturi flume.
Parshall flume accuracy is dependent upon the accuracy of construction,
with strict adherence to the dimensions given a necessity.

*Sewage disposal, *Waste water treatment, *Weirs, *Flumes, Hydraulics

"V" notch weirs, Rectangular weirs, Parshall flumes


                                          73

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097B

INFILTRATION SMOKED-OUT,

Bexson, J.

Water and Sewer Department, Village of Gardner, Illinois

Water and Wastes Engineering, Vol. 11, No. 9, p 59-60, September, 1974.

The Village of Gardner, Illinois, solved their problems of sewer overloads by
smoke testing.  Although the sanitary system in the town was less than 10 years
old and completely separated from the storm sewers, overloads occurred every
time even a moderately heavy rain fell.  The overloads caused floods in many
home basements, and forced bypass of any sanitary treatment.  Smoke testing
of the sewers was chosen because of its ability to locate problem areas in
mains, laterals, and building drains.  Actual testing was done by the National
Power Rodding Corporation.  Advance notice was given to the residents before
the testing started.  It was explained that smoke entering houses indicated
faulty plumbing that should be corrected because sewer gas could back up the
same way.  The equipment for the test consisted of a portable 1500 cfm blower
placed on each manhole and a plywood manhole ring lined with a 0.75 inch thick
sponge rubber gasket for sealing the connection.  Smoke was forced through
the sewers.  The smoke was a high-moisture zinc chloride which created a dense,
grayish white or white appearing mist.  The smoke issued from all downspout
gutters connected to the sewer, from breaks, storm sewer connections and
cracked house laterals.  All household violators were required to attend a
meeting and had the trouble explained.  All but 10 households have satisfactorily
repaired their violations.  Repair of broken lines and illegal connections has
reduced the maximum overload on the treatment plant from 1.5 mgd to 300,000 gpd.
Electricity and chlorine usage have also been reduced.

*Sewers, *Pipelines, *Sewerage, Plumbing, Separated sewers, Storm drains

*Smoke testing


098B

WATER OR AIR, WHICH DO YOU PUMP?,

Hoeppner, S.

FMC Corporation, Indianapolis, Indiana,
Pump Division

Water and Wastes Engineering, Vol. 11, No. 9, p 67-68, 70, September, 1974.
1 fig.

In an efficiently designed system, vapors of air or gas should not be allowed
to enter centrifugal pumps.  When air or gas do get into the pump, liquids are
displaced and the pump becomes air bound, wearing out rings, bearings, shafts,
and even impellers from lack of lubrication.  In addition, if carbon dioxide
from water  in deep wells is allowed  to escape,  these gas bubbles form a film
of highly concentrated carbonic acid.  This acid corrodes  the vital metal parts
of a pump,  causing severe damage.  Solutions to problems of pumping and deep
wells are discussed.  For horizontal pumps, installation techniques are
stressed.   To prevent formation of air pockets  on the suction side of a pump,
an eccentric increaser should be used, suction  piping should be  laid out so
that no high spots exist where air might collect, and all  suction piping joints
or connections should be air tight.  In deep well situations, falling water
must be  eliminated, either by construction of wells with no well casing
perforations or by the installation  of baffles  or of a liner within the well.
When gas of any type does become entrained in well water,  one special suction
device may  be used to separate the gas from the water.  This is  a normal
suction pipe enclosed in a second pipe, useful when the well is  of sufficient
diameter.   Other modifications to the pump and  its impeller to prevent gas
from entering the systems are described.

*Pumps, *Centrifugal pumps, Air, Deep wells, Deep well pumping,  Installation,
Pipes, Corrosion

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099B

DOLLAR GAIN TO TOP COST CLIMB IN 1975 SEWERAGE
CONSTRUCTION,

Engineering News Record, Vol. 195, No. 15, p 14-15, October 3, 1974.  1 fig,
1 tab.

Contracting plans were reported by 75 major sanitary districts in the United
States, with about $5 billion in new work being bid for fiscal year 1975-1976.
Despite inflation close to 20%, the Environmental Protection Agency anticipates
dollar gains, related to sewerage construction cost indices.  Many of the
projects scheduled for contracts in the next year are hold-overs from previous
years, where federal grants had been postponed.  Construction costs have
increased up to 30% for treatment plants and about 15% for interceptor plants.
However, the financing needed to activate the contracts may be easier to
obtain this fiscal year than in 1975.  State and municipal bond sales for
sewerage construction have increased 66%, a rate more than double the increase
of a year ago.  Much of the 1975 sewerage construction is dependent upon
federal aid, with EPA grants projected to total $3.5 billion, as opposed to
1974's $2 billion.

*Construction costs, Municipal water, Sewerage, Construction, Costs

*Treatment plants, Federal grants, Environmental Protection Agency
                                   75

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                                 PATENTS
001C

APPARATUS FOR RELEASING CHEMICALS CLEARING AND CLEANING
WASTE PIPES,

Stalnaker, R. M.

Newton, Hopkins, and Ormsby, Atlanta, Georgia

United States Patent 3,771,968.  Applied July 7, 1971.  Issued November
13, 1973.  Official Gazette, Vol. 196, No. 2, p 617-618, November 13, 1973.

An apparatus for releasing chemicals that clears and cleans waste pipes is
described.  An elongated tubular-shaped dispenser with a plurality of
axially and circumferentially spaced openings is attached to a rotational
support plug.  The dispenser releases chemicals in predetermined amounts
in response to flushing water.  It is capable of destroying, clearing,
and cleaning obstructions located in the waste pipe.  A chemical capable
of aiding in the control of pollution could also be utilized in the
disperser.  The disposable dispenser is replaced after the chemicals are
released.

*Pipes, Engineering Structures, *Sewers, *Cleaning, Treatment, Patents

Apparatus
002C

METHOD FOR TREATING WATER CONTAINING SUSPENDED SOLIDS FROM
A SANITARY SYSTEM,

McKibbe, J. W., Goodman, B. L., and Higgins, R. B.

Ecodyne Corporation, Chicago, Illinois

United States Patent 3,770,624.  Applied December 14, 1970.  Issued November 6,
1973.  Official Gazette, Vol. 196, No. 1, November 6, 1973.

An  improved method and apparatus for treating water containing suspended
solids from a sanitary system are described.  The water is aerated and
delivered to a screen with a directional component across the screen surface
and a directional component through the screen.  The screen has openings
large enough to pass the majority of the solids suspended in the water,
and has the ability to hold a coating of these solids on its upstream side.
The flow of water is controlled so that a coating of the suspended solids
from the water is formed on the screen surface.  The delivery of water
containing these suspended solids to the screen is continued with a
directional component across the screen and a directional component through
the screen, in order to filter solids from the water passing through the
coating and screen.  The relationship between the directional components
across and through the screen is controlled to maintain the coating on
the screen.  The water that is passed through the screen is stored, and
is  recycled to the sanitary system.

Suspended Solids, Treatment, *Separated Sewers, *Recycling, *Aeration,
Patents

Apparatus


                                       76

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003C

LINER INSERTING MACHINE FOR PIPELINES,

Reed, R. R.

Modesto, California

United States Patent 3,774,286.  Applied April 24, 1972.  Issued November 27,
1973.  Official Gazette, Vol. 916, No. 4, p 1229, November 27, 1973.

A liner-inserting machine for underground pipelines used in irrigation or
sewer systems is described.  Liner pipe sections are thrust into the
pipeline by the patented machine.  The machine includes a frame in an
excavation adjacent to the open end of the pipeline.  The frame supports
a power actuated, reciprocable pusher head in axial alignment with the
open end of the pipe.  It forcefully thrusts the liner pipe sections in
end-coupled relation.

Sewers, *Pipes, *Linings, Irrigation, Patents, Equipment

*Liner-inserting Machine, Apparatus
004C

APPARATUS FOR TREATING WASTE FLUIDS BY MEANS OF DISSOLVED
GASES,

Hurst, George E.

Pollution Control Engineering,  Inc., Downey, California

United States Patent 3,773,179.  Applied September  28, 1971.   Issued November  20,
1973.  Official Gazette, Vol. 916, No. 3, p 932, November  20,  1973.

An apparatus for treating wastewater to remove suspended pollutants is
described.  It consists of a tank with a plurality  of compartments through
which the fluid is repeatedly pumped from one compartment  to the next.
At each pumping station, gas is injected at the suction side of the pump and
back pressure is maintained in  the discharge line to force more gas into
solution.  Effluent from each compartment is taken  near the bottom and
the discharge is located midway of the height, confined to a small area,
and then deflected by a deflector plate.  Clarified water  is removed
by a riser tube from the bottom of the final compartment and flows over
a weir.  The floated matter is  removed from the fluid surfaces in each
compartment by skimming or other methods.

*Suspended Load, Suspended Solids, *Waste Disposal, Patents, Equipment

Apparatus
                                       77

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005C

SHEAR-RESISTANT FLEXIBLE PIPE JUNCTION FOR SEWERAGE AND
DRAINAGE,

Eoechst Australia Ltd.

p;dwd Waters and Sons,
Australia

Australian Patent 439,581.  Applied July 2, 1969.  Issued September 6, 1973.
Australia, Official Journal of Patents, Trade Marks and Designs, Vol. 43,
No. 33, p 3557, September 6, 1973.

A shear-resistant flexible pipe junction for sewerage and drainage is
described.  It consists of a pipe joint collar fitting of substantially
flexible thermoplastic material either rotationally cast, or made by some
other process, in the form of cylindrical collar sections.  Two
adjoining plain pipes abutt the collar sections.  The collar includes
two or more axially-spaced internal annular spaces, one in each section
to accommodate a resilient sealing ring for sealing the pipes.  There
is an external circumferential groove extending between the internal spaces.
The flexibility of the groove permits a pair of adjoining pipes to
undergo relative angular movement without pipe or seal breakage.

*Sewers, Conduits, Engineering Structures, *Plastic, *Pipes,
Equipment, Patents

Collar Sections, Apparatus
006C

PRIMING UNIT FOR DISTRIBUTING PRIMING WATER TO MULTIPLE
SEWER LINE WATER TRAPS,

Watts, J. B.

Precision Plumbing Products, Inc., Portland, Oregon

United States Patent 3,776,269.  Applied April 7, 1972.  Issued December 4,
1973.  Official Gazette, No. 1, p 144, December 4, 1973.

A priming unit for distributing priming water to multiple sewer line water
traps is described.  It consists of a case of compact dimensions which
are coupled to the priming water.  A plurality of water outlet pipes
penetrate the case floor by a predetermined distance to permit use of the
water contained in the case to measure the level condition of the unit.
There is substantially equal distribution of priming water through all
the pipes to the various sewer line water traps.

Conduits, Water Transfer, *Sewers, *Conveyance Structures, Equipment;,
Patents

*Priming Water, Apparatus
                                           73

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007C

METHOD AND FILTER MEDIA FOR THE TREATMENT OF SEWAGE AND
WASTE WATERS,

Choun, J. M.

Golden, Colorado

Canadian Patent 938,226.  Applied November 5, 1970.  Issued December 11, 1973.

A method and filter media for the aerobic treatment of sewage and wastewaters
using a trickle filter are described.  The filter media consists of thin wall
capsules or shells of polymeric resin of sufficient rigidity as to be self-
supporting in the filter bed.  The shells are reticulated by comparatively
large diameter openings which permit a trickling flow of liquid and a free
circulation of air both about and within the capsules.  The structural
arrangement of the filter media permits the filtering process to include the
steps of forming both small puddles and unwetted portions throughout the
filter media.  A small amount of anaerobic activity apparently occurs within
the puddles, and psychoda flies, finding dry perching places, live within the
filter media itself.  These combined factors result in a more effective
filter media and better performance by the media.

Sewage, *Waste Water Treatment, *Filtration, *Aerobic Treatment, Filters, Patents
008C

METHOD AND APPARATUS FOR USE IN TUNNELLING,

Patin, P.

58 rue de Sevres, Boulogne-sur-Seine, France

United States Patent 3,788,087.  Applied April 25, 1972.  Issued January 29,
1974.  Official Gazette, Vol. 518, No. 5, January 29, 1974.

A method and apparatus for use in tunnelling are described in which the terrain
is supported by an annular fluid mass under pressure moved either continuously
or stepwise.  A lining compound is introduced outside the fluid mass and
sets to form a tube.  The tube may then be internally coated.

Engineering.Structures, Tunnels, *Tunnelling, *Tunnelling Machines, Tunnel
Construction, *Pipes, Municipal Wastes, Patents
                                         79

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009C

DRAINAGE GRATING,

Basev, P. D., Ipatova, K. G., and Shirior, I. S.

Soviet Patent 374,424.  Applied May 10, 1971.  Issued April 25, 1973.  Soviet
Inventions Illustrated, Section III, Mechanical and General, U(47), p 3,
December 27, 1973.

A grating of half-cylindrical form designed to retain litter and general rubbish
being carried along by storm water and sewage is described.  The concept is
similar to a radio tuning-coil, in that a sector composed of plates can be
rotated inside the main grating.  The closed section can therefore be altered
so that it always faces the direction of flow thus retaining the rubbish, while
the water passes through the open section.  The unit consists of a flat
framework with semi-circular plates forming a grating.  Interposed between
the plates are further plate sectors connected to an operating rod.  The
rubbish carried along by the rain or sewage flow is separated from the water
by rotating the plates to face the water flow.  Stops are provided to prevent
overtravel of the swinging sector.

Storm Water, *Storm Drains, Intakes, *Urban Drainage, Sewers, Municipal Wastes,
Patents

*Grating
(HOC

ION EXCHANGE PURIFICATION PLANT - ESPECIALLY FOR REMOVAL
07 ANIMAL AND VEGETABLE MATTER FROM SEWAGE,

Viscose Development Company

Belgian Patent 808,402.  Applied June 2, 1972.  Issued October 1, 1973.  Belgian
Patents, Food, Disinfectants, Detergents (451), p 3, January 24, 1974.

The purification of liquids by an ion exchange process particularly adaptable
for removing animal and vegetable matter from sewage is described.  The liquid
to be purified is mixed thoroughly by a variety of mechanical methods in one
01: more treatment tanks in series and/or parallel with granulated (50-100 H. S. S
mesh size) activated regenerated cellulose or cellulose derivative material.
The ion exchange process extracts the unwanted Impurities from the liquid
which is then separated by a variety of methods from the ion exchanger material
which is exhausted, and at the same time, laden with the impurities.  Some of
those impurities are then stripped out of the exchanger material by regenera-
tion using the same activate as that used initially.  The regenerated ion
exchanger wholly or partially is fed back into the plant for reuse after
beiing flushed through.

*lon Exchange, Water Treatment, *Treatment Methods, Waste Water  (Pollution),
Liquid Wastes, *Sewage, *Cellulose, Municipal Wastes, Patents
                                             80

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one

HYDRAULIC SEWER PIPE LINE CLEANER,

Latall, R. C.

Conco Inc., Mendota, Illinois

Canadian Patent 939,459.  Applied April 23, 1971.  Issued January 8, 1974.
Canadian Patents, Vol. 102, No. 2, p 76, January 8, 1974.

A skid-mounted jet-propelled, hydraulic, pipeline cleaner is described which
is activated from a stationary high pressure water pumping unit to which it
is connected by a flexible hose.  The cleaner includes:  a novel skid arrange-
ment of extreme rigidity and a selectively positionable wate/ jet capable
of assuming either a propelling position or a tool flushing position.  A
jet propulsion system was designed so that the jet discharges directly into
the pipeline void and does not impinge against any portion of the pipeline
cleaner as a whole so that no retarding influence is offered to the free
forward motion of the cleaner.

*Pipes, Pipelines, Pumping, *Sewers, Municipal Wastes, Patents

*Pipe Cleaner
012C

SEWAGE TREATMENT PLANT - USING COMBINED FLOCCULATION AND
AERATION,

IMB-Holland B. V.

Netherlands Patent 7,217,163.  Applied June 2, 1972.  Issued December 4, 1973.
Netherlands Patents, Food, Disinfectants, Detergents (451), p 1, January 24,
1974.

A sewage treatment plant is described which combines flocculation and aeration.
The raw sewage and a flocculating agent are fed into the inlet chamber of the
plant together with some recycled liquid and a bleed fraction from the main
compressed air line.  The resultant mixture overflows a weir and goes into
a preseparation and flocculation tank with an internal convection circuit.
On the surface is a floating plastic inlet nozzle and manifold assembly which
is connected to the suction side of a pump.  It feeds the extracted liquid
into a pressure vessel whose lower part is a set of air distributor nozzles
fed by the main compressed air line.  The resultant air-saturated liquid is
expelled by the pressure build up into sets of distributor nozzles in the final
separation tank of the plant.  The air raises the flakes to the surface where
they are trapped and the clear effluent is drained via a baffled compartment
from the base of the separator tank.  The nozzles for the super-aerated liquid
are in two tiers, those above having higher mass flow than those below.  There
is a relatively high treatment capacity and high purification efficiency
in terms of extraction of those dissolved impurities which are bonded
by the flocculation agent.

*Sewage, *Waste Treatment, Flocculation, Aeration, Treatment Methods,
Recycling, Patents

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013C

SEWAGE PHOSPHATES EXTRACTION - USING ACTIVATED SLUDGE,

Biospherics, Inc.

Netherlands Patent 7,207,517.  Applied June 2, 1972.  Issued December 4, 1973.
Netherlands Patents, Food Disinfectants, Detergents (451), p 1, January 24,
1974.

A process for the extraction of sewage phosphates using activated sludge
is described.  Raw sewage is passed through a presedimentation tank and then
mixed with activated sludge.  The resultant slurry is stored in an aeration
tank for 1-8 hours where the micro-organisms in the activated sludge digest
the phosphates.  Some are absorbed into the sludge, while insoluble particles
are precipitated.  The slurry is then passed to a sedimentation tank where the
sludge with digested and precipitated phosphates is fed to a stripping tank
into which a stoichiometric quantity of phosphate stripping and dissolving
agents is fed so that the sludge can be recycled.  The effluent from the
final separator can be passed on for subsequent treatment and has significantly
reduced BOD.

*Sewage, *Phosphates, *Activated Sludge, *Recycling, Precipitation,
Sedimentation, Biochemical Oxygen Demand, Effluent, Patents
014C

WASTEWATER TREATMENT USING ELECTROLYSIS WITH ACTIVATED
CARBON CATHODE,

Kawahata, M. and Price, K. R.

General Electric Company, Schenectady, New York

United States Patent 3,788,967.  Applied February 3, 1969.  Issued January 29,
1974.  Official Gazette, Vol. 518, No. 5, January 29, 1974.

An improvement in the electrolytic treatment of wastewater is described
in which the reduction of oxygen on an activated carbon cathode is
employed to form hydrogen peroxide.  The peroxide oxidizes the organic carbon
pollutants in the wastewater.  The oxygen is fed to the activated carbon cathode
from outside the electrolytic cell.  The cathode is part of the enclosure
for feeding the gas to the surface, which forms part of the boundary of
the cell compartment.

Waste Water, *Electrolytes, *Activated Carbon, *Waste Water Treatment,
*0xidation, Municipal Wastes, Patents

*Reduction

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015C

CIRCULATION SYSTEM WATER PURIFICATION - BY TREATMENT WITH
AMMONIA SUBSEQUENTLY RECOVERED BY MEANS OF ION EXCHANGE RESIN,

Koganovskii, A. M., Semenyuk, V. D., and Chepurnaya, G. S.

Water Supply and Sewage Design Institute

Soviet Patent 365,326.  Applied February 17, 1969,  Issued June 6, 1973.  Soviet
Inventions Illustrated, Section J-Chemical,  (U49), January 10, 1974.

The purification of a circulation water system by treatment with ammonia
and its recovery by an ion exchange resin are described.  The process is simpler
and more economical than the conventional treatment with alkalis, which
results in periodical discharge of water when the 9ontent of chemicals exceeds
the admissible level (thus chemicals are lost) .   Ammonia is recovered in the
H-form on cationic filters which are regenerated by washing with nitric acid.
Water is then neutralized by passing through an OH-ionite filter, regenerated
with ammonia water.  The filter washing solutions can be used as liquid
fertilizers.  For example, water loss in a recirculation system is replenished
with river water, which is treated with ammonia in an amount of 40
milligrams/liter milligram equivalent of the temporary hardness.  The pH rises to
9.5-10, and calcium carbonate, magnesium hydroxide, and ferric hydroxide are
precipitated.  Ammonia is recovered on a H-cationite filter.  A part of the
water that passed through this filter (1/3-1/5) is directed to an OH-
anionite filter.  The regeneration of both filters is carried out with
25 percent nitric acid or 10 percent ammonia solution, respectively.

Waste Water, *Recycling, *Recirculated Water, Water Reuse, *Ion Exchange,
*Resins, Filtration, *Ammonia, Municipal Wastes, Patents
016C

WASTE WATER PROCESS TANK CONTROL FACILITY,

Boschen, W. 0. and Grieshaber, 0. A.

Ralph B. Carter Company, Hackensack, New Jersey

United States Patent 3,788,472.  Applied February 3, 1972.  Issued January
29, 1974,  Official Gazette, Vol. 518, No. 5, p 1847, January 29, 1974.

A control facility for a wastewater process tank having a normal operating
mode is described.  On malfunction, the system shuts down and indicates "fault".
The system provides a stepped, sequential trouble-shooting procedure for
determining the fault, and provides for temporary operation or partial operation
of the system until the fault is corrected.  The system is directed toward
use in wastewater treatment plants which utilize liquid mixing and/or heating
tanks.

Waste Treatment, *Waste Water Treatment, Municipal Wastes, *Control, Patents

*Trouble-Shooting
                                    83

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017C

VACUUM SEWAGE CONVEYING WITH VACUUM OPERATED VALVE,

Burns, B. C.

P. 0. Box 254, Woodbridge, Virginia

United States Patent 3,788,338.  Applied June 29, 1971.  Issued January 29, 1974.
Official Gazette, Vol. 518, No. 5, p 1812-1813, January 29, 1974.

A method and apparatus for conveying sewage by vacuum-induced plug flow are
described.  The sewage is drawn from a sewage-collecting region into a vacuum
line pipe through a valve, and moves toward the source of vacuum by vacuum-
induced plug flow caused by the interposition of volumes of air between
plugs of sewage.  A control zone in an operator portion of the vacuum valve is
controllable by a low-pressure reservoir for opening the valve.  The reservoir is
maintained at a low pressure through a vacuum tap conduit communicable with
the reservoir and the vacuum line conduit.  The sewage-collecting region may
be an underground collecting tank which contains equipment for controlling
operation of the vacuum valve which may be located outside the collecting
region in a separate housing just below grade.  Electrical power used at the
collecting region may be supplied solely from a central panel through cable
laid in a trench along the vacuum line conduit.  A rigid pipe assembly in
the collecting tank is connected several feet above the tank bottom, but
below grade, to a pipe assembly of the vacuum valve, and the orientation
may be such as to permit disconnection of pipes at the vacuum valve without
causing leakage in the region where workmen must stand.

Pipes, Engineering Structures, *Sewage, *Pipelines, *Sewage Disposal, Patents

*Vacuum Sewage Conveyance
Q18C

FILTER - FOR CLARIFYING NATURAL AND WASTE WATERS,

Petrov, E. G., Gorodisher, Z. Ya., and Novikov, M. G.

Leningrad K. D., Pamfilov Communal Agriculture Academy
Research Institute

Soviet Patent 376,104.  Applied March 15, 1971.  Issued July 6, 1973.  Soviet
Inventions Illustrated, January 24, 1974.

A filter for clarifying natural and waste waters is described which includes
a body with a filtering charge, system of entry and exit, and vibrators.
The degree to which the filter medium can clean the waters is increased and
consumption of wash water is reduced by establishing vibrators directly in the
first layers of the filter medium commensurate with the direction of liquid
flow.  Water comes in through the distribution system and is fed to the
charge of filter material.  The clean water runs through the collector and pipe.
As wash water is admitted through the system, the vibrators are switched on,
thus helping to dislodge the entraped Impurities.  The wash water flow is
directed upwards through the entire thickness of the bed, taking the impuri-
ties with it.  The rate of feed is 4-5 liters/sec/square meter.

Effluents, Water Treatment, *Treatment Methods, *Filtration, *Equipment
Patents

Clarification
                                        84

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 019C

 GROUND WATER  LEVEL  CONTROL,

 N. V. Heidemaatschappij Beheer

 German Patent 1,784,335.  Applied July  29,  1968.   Issued December  13,  1973.
 German Patents Abstracts, Vol.  6 U, No.  51, pi, January 1974.

 A ground water level  control near a pipe trench  is described which uses  filter
 pipes and  suction  pipes introduced be  fore the  trench  excavation  and  with
 connected  suction pumps.  These pipes are introduced  into  the ground under
 the bottom of the graded trench so that  the filter pipes lie approximately
 horizontal behind each other, parallel  to the  trench  line.  Each corresponding
 suction pipe  connected to a pump is passed sideways out of the line and
 projects sideways out of the ground.

 Engineering Structures, *Pipes, *Pumps,  *Groundwater, *Water Table, Patents
020C

SEWAGE AERATOR - WITH SUBMERGED MOTOR CARRIED BY FLOATS,

Sydnor Hydrodynamics, Inc.

German Patent 1,957,793.  Applied November 18, 1969.  Issued December 13, 1973.
German Patents Abstracts, Vol. U, No. 51, p 1, January, 1974.

A sewage aerator with a submerged motor carried by floats is described.  The
motor, and the vane wheel mounted above it and driven by it, are enclosed in
common by an open-ended sheathing ring between which are the motor and guide
walls.  When seen in cross section, the walls run radially relative to the motor.
Preferably, the upper open end of the rings consist of a mouthpiece which
widens toward the outside.

*Sewage, *Equipment, *Aeration, Patents, Treatment Methods

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021C

WATER PURIFICATION - USING ELECTROLYSIS TO RELEASE OXYGEN,

McMenamin, S. H.

French Patent 7,107,184.  Applied October 27, 1971.  Issued September 25, 1973.
French Patent Abstracts, January 31, 1974.

A reduction process for the electrolytic purification of water is described.
A sufficient amount of electrolyte is added to the water to make it conduc-
tive, and the water passes a pair of electrodes.  A direct current releases
a predetermined volume of oxygen at the cathode to injure micro-organisms
in the water.

Patents, Treatment Methods, *Water Treatment, *Disinfection

*Reduction, *Electrolytic Purification
02 2C

ELECTROLYTIC WATER TESTER - FOR DETERMINATION OF OXYDANT OR
REDUCING AGENT CONTENT,

Mines de Potasse D'Alsace S. A.

Belgian Patent 800,283.  Applied April 30, 1973.  Issued November 30, 1973.
Derwent Belgian Patents, January 31, 1974.

An electrolytic water tester for the determination of oxydant or reducing
agent content is described.  It consists of an outer shell with an insul-
ating plug at one end to support a reference.  An indicating electrode is
at the other end and has the connecting leads from those electrodes passing out
of it.  The electrode probe is placed within a flow of the water to be ana-
lyzed at the axis of flow.  The indicator electrode is of precious metal
(platinum or gold) and the reference electrode a metal wire (silver or
copper); the two electrodes are concentric and have a longer life than
probes using calomel as electrode material.  The tester is especially used
for control information and signals to determine or regulate rate of addition
of neutralizing agent in water treatment plants.

Equipment, Patents, "^Instrumentation, Treatment Methods, *Water Treatment

*Electrolytic Water Tester
                                      86

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023C

SURFACE SCUM EXTRACTOR - FOR RECTANGULAR FLOTATION TANK IN
SEWAGE WORKS,

Degremont Society Generate D'Epuration et D'Assainissement

Belgian Patent 801,156.  Applied June 20, 1973.  Issued October 15, 1973.
Derwent Belgian Patents Reports, January 31, 1974.

A surface scrum extractor for a rectangular flotation tank in sewage works
is described.  A bridge structure running on parallel rails along the sides
of the tank carries a rotating drum in the form of two end checks between
which are a number of horizontal dredger bucket cross-section scraper blades.
These move in the opposite direction to that of the bridge as it traverses the
length of the tank, and discharge by gravity into a coaxial worm and trough
extractor, or conveyor belt or sloping gutter.  At the rear of the bridge is a
hinged pusher plate which forces the floating matter forwards on to the
blades as the bridge moves forwards.  By placing a similar pusher on the
front of the bridge and operating them differentially, along with the use of
double profile bucket blades, the system may be made bidirectional.

*Sewage Treatment, *Flotation, Treatment Methods, Patents, *Scum, Equipment

*Tanks
024C

FLUID POLLUTION MONITORING APPARATUS AND METHOD,

Hayre, H. S.

10 Legend Lane, Houston, Texas.

U. S. Patent 3,791,200.  Applied September 9, 1971.  Issued February 12, 1974.
Official Gazette, Vol. 919, No. 2, p 471, February 12, 1974.

A new and Improved method and apparatus for monitoring fluids to determine the
presence of pollutants In the fluids are described.  The type and quantity
of pollutants are identified by analysis of the acoustic impedance properties
of the fluid.

Equipment, Treatment Methods, Instrumentation, *Acoustics, Patents, *Effluents
                                         87

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025C

METHOD AND APPARATUS FOR CONVEYING SEWAGE,

Burns, B. C. and Albertsen, H. C.

Woodbridge, Virginia

Canadian Patent 940,011.  Applied April 2, 1971.  Issued January 15, 1974.
Patents/Brevets, Vol. 102, No. 3, p 191, January 15, 1974.

A method and apparatus for conveying sewage from sewage sources such as
residences to a remote location are described.  The sewage is initially
conveyed by gravity flow from the source into a collecting tank and by
vacuum-induced plug flow to a vacuum receiver tank at the remote location.
The sewage may be discharged from the remote location, preferably under
positive pressure, into another line such as a vacuum line for further
vacuum-induced plug flow or a gravity flow conduit.  The final location to
which the sewage is conveyed may be the sewage treatment facility.  Sub-
stances for treating the sewage may be advantageously introduced into the
system and mixed with the sewage during conveyance.  Self-scouring tanks, ro-
tation-imparting plug reformers, and several alternative ways of introduc-
ing controlled amounts of air at or above atmospheric pressure into the
vacuum portion of the system are provided.

Patents, Treatment Methods, Conduits, *Sewers, Engineering Structures, *Pressure
Conduits, Hydraulic Conduits
026C

METHOD OF FILTRATION,

United States Atomic Energy Commission.

Australian Patent 441,682.  Applied April 1, 1969.  Issued November 8, 1973.
The Australian Official Journal of Patents, Trade Marks, and Designs, Vol. 43,
No. 42, p 4491, November 8, 1973.

An improved hyperfiltration process is described for purifying water by re-
moving solute impurities from an aqueous solution.  An inert non-solute
rejecting filter aid material is deposited to a bed depth of from 0.1 to
100 microns on a porous substrate which contains pores large enough to
allow water to pass through.  The material has a particle size in the range
of 0.01 to 100 microns.  The solution is passed over the surface of the bed
in cross flow to form a solute-rejecting membrane of the material on the
bed.  A sufficient velocity and pressure drop is maintained across the
bed to force the solution through and to allow the filtered material to
collect.

Patents, *Treatment Methods, *Filtration, *Water Treatment, Municipal Water

*Hyperfiltration
                                       88

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027C

ACTIVATED SLUDGE SEWAGE THEATER,

Passavant Werke Michelbacher Huette

German Patent 2,043,148.  Applied August 31, 1970.  Issued November 22, 1973.
German Patents Abstracts, Vol. U, No. 48, p 2, January, 1974.

An activated sludge sewage treater is described which has at least one baffle
extending transversely of the longitudinal flow in the annular closed aera-
tion tank.  The baffle top edge is below the water level, and the baffle
is inclined downward toward the flow to deflect part of it.  Preferably the
tank has two straight sections joined by curved ones.  The aerator is in a
curved section at the end of the partition separating the straight sections.
The baffle is at the beginning of the straight section downstream of the
aerator.

Patents, Treatment Methods, Sewage, *Sewage Treatment, *Activated Sludge,
Aeration
028C

METHOD AND APPARATUS FOR INCINERATING POLLUTED LIQUIDS AND MUD,

Pariel, J. M. and Robic, G.

Societe Anonyme Heurtey and ELF-Union, Paris, Seine, France

Canadian Patent 940,279.  Applied April 19, 1971.  Issued January 22, 1974.
Patents/Brevets, Vol. 102, No. 4, p 270, January 22, 1974.

A method and apparatus for incinerating polluting liquids and mud are
described.  The pollutants are sprayed inside a reaction chamber in the pre-
sence of an oxidizer with a mixture formed by the mutual dispersion of
non-miscible phase containing the pollutants and a liquid.

Patents, *Equipment, Pollutants, *Incineration, *Liquid Wastes, *Mud, Oxidation
                                      89

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029C

APPARATUS AND METHOD FOR TREATING SEWAGE,

Freese, R.

Official Gazette, Vol. 920, No. 4, p 1202, March 26, 1974.  United States
Patent 3,799,346, Applied July 22, 1971, Issued March 26, 1974.

An Improved sewage treatment plant Is described having a primary waste receiving
and mixing vessel, an aeration vessel, and a settling tank.  Material from
the primary mixing vessel is pumped into a bottom region of the aeration vessel
by means of a pump and a venturi aerator is provided for introducing air into
the stream of sewage being pumped into the aeration vessel which contains a
series of downwardly inclined baffles arranged to trap pockets of air and
circulate the sewage along a tortuous path across said air pockets.  A portion
of the aerated sewage is recycled from a top region of the aeration vessel back
Into the primary mixing vessel for mixing with the raw, unaerated sewage and
a second recycling system is provided for recycling a portion of aerated sewage
from an upper region of the aeration vessel into the stream being pumped into
the lower region of the aeration vessel.

*Sewage Treatment, *Treatment Facilities, *Patents, *Equipment, Mixing, Aeration,
Settling Basins, Design Criteria, Recycling, Methodology, Pumping, Waste
Water Treatment
030C

SEWAGE AERATION TURBINE,

Envirotech Corp.

Derwent Belgian Patents Report, Vol. 5, No. 6, p 2, March 14, 1974.  Belgian
Patent 805,018, Applied September 19, 1973.  Issued January 16, 1974.

The blades of the axial flow turbine are closely surrounded by the throat of the
Venturi tube and at least some of them are hollow with orifices at their tips.
The drive shaft from the external motor also is hollow and has holes in its walls
leading to an annular space connected by one or more pipes to the atmosphere.
The number and shape of blades and the motor speed produce safer cavitation at
the tips.

*Venturi Flumes, *Patents, *Axial Flow Turbines, Aeration, Sewage Treatment,
Cavitation
                                          90

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031C

FURNACE FOR BURNING SEWAGE AND LIKE RESIDUES,

Stribling, J. B.

Lucas Furnace Developments Limited,
Wednesbury, England

Official Gazette, Vol. 920, No. 4, p 1131, March 26, 1974.  United States
Patent 3,799,074, Applied October 26, 1972. Issued March 26, 1974.

A furnace for burning sewage comprising a chamber enclosing a pool of the
sewage and a burner directed downwardly onto the pool to bathe the entire surface
of the pool in flame has been developed.  The pool has a floor which is conical
in two stages so tha  the area of liquid subject to flame can be controlled
by varying the level of the liquid relative to the conical area.

*Patents, *Burning, *Sewage Treatment,  Equipment

*Furnaces
032C

AERATION TANK,

Dolobovskaya, A. S., Nevzorov, M. I., and Sherenkov, I. A.

Water-Conservation Industrial Division Water-Supply
Cain Canalisation, Hydraulic Enf. Const. & Eng.
Hydrogeology Research Institute

Soviet Inventions Illustrated, Vol. 5, No. 5, p 1, March 7, 1974.
U.S.S.R. Patent 381,611. Applied May 22, 1973.  Issued August 14, 1973.

The system consists of a rectangular storage tank fitted with filters,
water admission and withdrawal channels, sludge-duct, and screens.  The mass-
transfer conditions are improved and the purifying process is Intensified by
creating flows of air and water  in opposite directions, the screens in pairs
forming diffusers.  The sludge mixture is continuously circulated from the
bottom of the tank via adjacent  corridors along the diffusers upwards and passed
into the corridors from above.   In this way the sludge mixture comes downwards
against the rising flow of ait coming in through the filter channels.

*Aeration, *Treatment Facilities, *Storage Tanks, *Waste Water Treatment,
*Filters, *Screens, *Sludge Treatment
                                            91

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03 3C

NATURAL FERTILIZER PRODUCTION,

Kratzer, B. P.

Derwent Belgian Patents Report, Vol. 5, No. 6, p 1, March 14, 1974.  Belgian
Patent 805,042. Applied September 19, 1973. Issued January 16, 1974.

The fertilizer is prepared from mixtures of aqueous waste and animal excrement
by adjusting the pH of the animal excrement, optimally after mixing with water,
to 0.1-2 with mineral acids and agitating the mixture to disintegrate it for 24
to 60 hours separating the liquid phase from the solid material and adjusting
the pH of the liquid to at least pH 5.  Said fertilizer is suitable for
domestic gardens, horticultural, and agricultural use.  It has no odor, is
hygienically acceptable, and is storage stable.

*Patents, *Fertilizers, *Farm Wastes, *Waste Water Treatment, Hydrogen Ion
Concentration, Separation Techniques, Application Methods
 034C

 WATER PURIFICATION  COAGULANT PRODUCTION,

 Kulskii, L. A., Dontsova, M. I., and Medvedev, M. I.

 Colloid and Water Chemistry Institute of  the
 Academy of Sciences, Ukraine, SSR

 Soviet Patent  357,808.  Applied July 7, 1969.  Issued August 31, 1973.  Soviet
 Inventions Illustrated, Vol. 5, No. 6, p  1, March, 1974.

 The preparation of  an active, hygienic, and economical coagulant to be used in
 water purification  is described.  A mineral acid is added to a water purification
 process sludge until the hydroxide gel is converted to a solution.  The sediment
 is separated from the solution, and the organic matter is oxidized.  The point
 at which the gel becomes a solution is determined by potentiometric or conducti-
 vity  measurements.  The oxidation of organic material is preferably carried
 out with a powerful oxidizer so that the  solution is completely decolorized.
 In an example, 0.5  liters of mud obtained from a water purification process
 is treated with 1 liter amounts of 0.1 N  HC1 after 20 min, and then five times
 every subsequent hour, then after 13 days, and after 1 mo and 8 days.  The
 degree of peptization is determined from  the amount of insoluble sediment
 resulting.  The coagulant obtained is treated with ozone and its technological
 properties are tested.

 *Water Purification, *Coagulation, *Patents, Sludge, Inorganic acid

 *Russia
                                      92

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035C

SEWAGE PHOSPHATES EXTRACTION,

Biospherlcs, Inc.

French Patent 2,183,605.  Applied May 12, 1972.  Issued December 21, 1973.
French Patents Abstracts, Vol. 5, No. 7, p 1, March, 1974.

An extraction method for sewage phosphates is described which uses activated
sludge.  Raw sewage is passed through a presedimentation tank and then mixed
with activated sludge.  The resultant slurry is stored in an aeration tank for
1-8 hr where the microorganisms in the activated sludge digest the phosphates
being precipitated.  The slurry then passes to a sedimentation tank where the
phosphated sludge is fed to a stripping tank into which a stoichometric quantity
of phosphate stripping and dissolving agents is fed so that the sludge can be
recycled.  The effluent from the final separator can be passed for subsequent
treatment and has significantly reduced BOD.

*Sewage Treatment, *Phosphates, Activated Sludge, Separation Techniques,
Recycling, Effluents, *Patents

France
 036C

 AERATOR,

 Autorol Corporation

 French Patent 2,184,068.   Applied May 10,  1973.   Issued date not given.   French
 Patents Abstracts,  Vol.  5, No.  7, p 3,  March,  1974.

 A rotatable,  biological  surface contact aerator  is  described for treating
 activated sludge effluent.  It  has a series  of elements mounted on  and spaced
 along a shaft and is partly emmersed in the  effluent to be  purified.   The
 elements  are  a series of  discs  delimiting  both a number of  mutually spaced,
 separate internal coaxial channels opening at  each  end into a radial channel.
 Adjacent discs delimit and extra series of separate, coaxial channels also
 opening at each end into  a radial channel.

 *Activated Sludge,  *Effluents,  Waste Treatment,  Aeration, Equipment,  *Patents

 Aerator,  France

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037C

TREATMENT OF INDUSTRIAL EFFLUENTS,

DuPont of Canada, Ltd.

Netherlands Patent 7,310,574.  Applied July 31, 1973.  Issued February 4,
1974.  Derwent Netherlands Patents Report, Vol. 5, No.  7, p 3, March, 1974.

The treatment of Industrial aqueous effluents of pH less than 6.0 containing
nitrogenous and carbonated minerals is described.  The  effluent is entered into
an anaerobic zone of treatment containing an anaerobic  activated sludge at a
rate of flow so that the concentration of nitrate and nitrite ions in the
treatment zone are held at low values, less than 3 mg/liter,  preferably less
than 1 mg/Hter.  The effluents from the anaerobic zone are pumped to a second
treatment zone which may be a clarification zone or an  aerobic treatment zone.
The treated effluent may be recycled.  The process is applicable for the
treatment of industrial effluents, particularly from chemical works as from
nylon production.  The nitrogen content is reduced to a very low figure.

*Nitrogen, *Nitrates, *Nitrites,  *Industrial Wastes, *Effluents, Carbonates,
Minerals, Denitrification, Activated Sludge, *Waste Water Treatment, Chemical
Wastes, Patents

*Netherlands, Canada
038C

WASTE WATER PURIFICATION,

Sterling Drug, Inc.

French Patent 2,177,843.  Applied March 23,  1973.   Issued November 9,  1973.
French Patents Abstracts, Vol. 5, No.  1, Feb. 7,  1974.

A method of purification of sewage and other waste water is described which
comprises removal of suspended solids  and decomposition of nitrogen containing
substances.  An adsorbent, preferably  powdered activated carbon,  and an oxygen
containing gas are introduced into a reservoir in which the waste water and  a
growing biomass have been stored for 3 days.  Aerobic conditions  are maintained
until the whole ammonical nitrogen is  oxidized to nitrites or nitrates.  The
solids are separated by sedimentation.  The  liquid phase is passed into an
anaerobic zone to which another portion of the adsorbent and an organic carbon
source, preferably methanol, is added.  The  nitrites and nitrates are reduced
to elemental nitrogen and the solids are separated by sedimentation.  High
rates of denitrification are achieved.

*Sewage Treatment, *Waste Water, *Water Purification, *Suspended Solids,
*Nitrogen, Adsorption, Activated Carbon, Aerobic Conditions, Nitrates, Separation
Techniques, Oxidation, Denitrification, Nitrites, Nitrates, Sedimentation,
*Patents

*France, Methanol
                                          94

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039C

FILTRATION OF DRAINAGE ELEMENT,

Bayer, A. G.

Belgian Patent 802,943.  Applied July 30, 1973.  Issued January 30, 1974.
Derwent Belgian Patents, Vol. 5, No. 7, March, 1974.

A filtration or drainage system for ground and surface water around foundations
and in embankments is described.  It consists of two mutually parallel textile
articles of large surface formed from synthetic or other rot resistant fibers
with a water discharge zone between them.

*Filtration, *Drainage Systems, *Groundwater, *Surface Water Fabrics, *Patents

Belgium
040C

PIPELINE PIG OR SWIPE,

Girard, H. J.

Houston, Texas.

Canadian Patent 994,109.  Applied July 20, 1971.  Issued March 26,  1974.
Patents/Brevets, Vol. 102, No. 13, p 1062, March 26, 1974.

A patent has been issued for a pig or swipe for use in cleaning pipe lines and
for maintaining fluids separated while being transmitted through the line.  It
is adapted to be propelled through the line by a pressure gradient.  The  pig
includes a sponge-like body of foamed plastic material, having an external
coating of durable material (unfoamed plastic) in which reenforcing material
(wire mesh or glass fabric) may be embedded to increase resistance  to wear.
The covering is applied to leave openings through which the sponge-like body
may project into wiping contact with the surrounding internal surface of  the
pipe.  The pig also has a barrier layer at one end positioned to close the
sponge-like body against the passage of fluid, and to form a fluid  tight  seal
with the surrounding pipe.  The invention includes a method and apparatus for
making the pigs or swipes.

*Patents, *Pipes, *Sewers, *Cleaning, Pipelines

Swipes
                                       95

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041C

PROCESS FOR THE TREATMENT OF ACTIVATED SLUDGE,

Komline, T. R.

Komllne-Sanderson Engineering Corporation,  Peapack,
New Jersey

U. S. Patent 3,803,806.  Applied September  28, 1972.   Issued April 16,  1974.
Official Gazette, General and Mechanical, Vol 921,  No.  3,  p 913,  Acril  16
1974.  1 fig.

Hot flue gases containing suspended solid particles,  oxygen and other water
soluble and insoluble components are injected beneath the  surface of  sewage
sludge.  Heat and the above components are  transfered from the gases  to the
sludge, providing oxygen for activating the sludge.

*Patents, *Activated Sludge, treatment Methods,  *Sewage
042C

SAMPLING AND FLOW MEASURING DEVICE,

Dieterich, P. D.

2927 Summit Drive, Michigan City, Indiana.

U. S. Patent 3,803,921.  Applied March 5, 1971.  Issued April 16, 1974.
Official Gazette, General and Mechanical, Vol. 921, No. 3,  p 943, April 16, 1974.
1 fig.

A device has been patented for sampling the fluid flow in a pipe.  It is comprised
of a probe extending into the flow system.  The probe has an outer conduit of
blind inner and outer ends extending diametrically across the pipe and having
a plurality of laterally spaced openings facing the flow.  It also has an inner
conduit extending from exterior of the pipe to the axial center of the
outer conduit from one end.  This provides the sole communication from the
interior of the outer conduit to sample gathering means external of the pipe.
The lateral openings sample the stream of fluid at several areas across the
diameter of the pipe, carrying the respective samples into the interior of the
outer conduit which constitutes a mixing plenum, so that a representative
sample is drawn off from the inner conduit.  Instead of drawing the sample off,
the sample is passed through a flow sensor and then returned to the pipe to
measure the rate of flow of the fluid.

*Patents, *Pipes, *Analytical Techniques, *Water Sampling, Pollutant Identifica-
tion, Flow
                                    96

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043C

PROCESS OF DEWATERING SEWAGE SLUDGE AND CONVERTING THE
SAME TO A USEABLE PRODUCT,

Baler, R. E.

Calspan Corporation, Buffalo, New York

U. S. Patent 3,804,753.  Applied December 7, 1972.  Issued April 16, 1974.
Official Gazette, Chemical, Vol. 921, No. 3, p 1149, April 16, 1974.

A process of dewatering sewage sludge and converting it to a useable product
has been patented.  The sludge is placed in a porous container and saturated
with a water displacing ingredient (such as technical grade butanol).  After
dehydration, the container pores are closed, and a polymerizable material is
added.

*Patents, *Sludge, *Sewage, *Treatment Methods, *Waste Water Treatment
044C

DRAIN FOR WASTEWATER,

Ernst Rechsteiner lankraumisolation & Feuchtigkeits Schutz

German Patent 2,248,970.  Applied December 3,  1972.  Issued February 2,  1974.
German Patents Abstracts, Vol. 5, No. 2,  p 3,  March, 1974.

A patent has been issued for a drain for wastewater in the foundation of a
building made of thermoplastic material and enclosed in the concrete.
Leaking of underground water is prevented by a flexible collar on the drain
which is supported by radial metal rods,  embedded at one end in the drain and
bent around the collar at the other end.

*Engineering Structures, Buildings, *Dralnage  Engineering, *Plastics, *Patents

Thermoplastics, *Drains
                                      97

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045C

CORRUGATED DRAINAGE PIPE,

Maroschak, E. J.

Plastic Tubing, Inc., Roseboro, North Carolina

U. S. Patent 3,802,202.  Applied February 23,  1973.   Issued April 9,  1974.
Official Gazette, Vol. 121, No. 2,  p 498, April 9,  1974.   1 fig.

A corrugated plastic drainage pipe  has been patented.   The pipe has spaced  apart
annular ribs, certain ribs being interrupted and having a set of  three
circularly arranged spaced apart arcuate rib segments.   The segments  define a
series of three drainage holes positioned between the ends of adjacent rib
segments where the rib segments are of such extent and so arranged as to
position the drainage holes around  the bottom of the pipe.  This  provides a
visual means of aiding in installing the pipe in the ground with  all  of the
drainage holes located below the horizontal center line of the pipe and with
the intermediate drainage holes occupying the lowermost position.

*Engineering Structures, *Pipes, *Drainage Engineering, *Plastics, *Patents

Drains
046C

SAFETY INSTALLATIONS FOR THE PREVENTION OF POLLUTION
THROUGH LEAKAGE IN A PIPELINE,

Wittgenstein, G. F.,

29 Champrond Way, Lausanne, Switzerland

U. S. Patent 3,802,456.  Applied December 6, 1972.  Issued April 9, 1974.
Official Gazette, General and Mechanical, Vol. 121, No. 2, p 563, April 9,
1974.  1 fig.

A safety installation for protecting the environment from leakages in pipelines
has been patented.  It comprises a fluid-tight jacket which surrounds the
pipeline and forms an intermediate space containing inserts which are separated
by ducts sealed with a liquid or gas.  The inserts are joined together by
cables or wires and there is provided at least one tank towards which the
leakage liquid flows through the ducts.  A liquid leakage detector acts to
remotely control the pumps and valves of the pipeline.  The jacket is formed
from short rigid runs connected by flexible joints; breaks between the runs
contain separation bands and are covered by a flexible fluid-tight structure
resting on the inserts and projecting onto the ends of the runs.  The length
of one run in the curves of the line is proportional to the radius of
curvature of the contained pipe.  At least one insert is grooved externally,
and adjacent longitudinal edges of the jacket are distorted by a tool and then
turned down into the groove.  Thus, connection between the edges and the groove
is fixed in position and made fluid-tight by filling the groove with a mass
which solidifies on drying.  A means is provided to enable the sections of the
inserts to deform to a variable extent along the inserts in the curves of the
line.  These inserts mainly rest on the inner wall of the runs.

*Patents, *Pipes, *Pollution Abatement, *Engineering Structures, Environmental
Engineering
                                      98

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047C

TREATMENT OF AN AQUEOUS WASTE STREAM CONTAINING AMMONIUM
HYDROXIDE,

Urban, P., and Rosenwald, R. H.

Universal Oil Products Co., Des Plaines, Illinois

Canadian Patent 941,528.  Applied October 23, 1970.  Issued February 5, 1974.
Patents/Breves, Vol. 102, No. 6, p 513, February 5, 1974.

The treatment of an aqueous waste stream containing ammonium hydroxide to
produce elemental sulfur and ammonia is described.  The aqueous stream is
catalytically treated with oxygen at oxidizing conditions effective to pro-
duce an effluent stream containing ammonium hydroxide, (NH4)2S203, and elem-
ental sulfur or ammonium polysulfide.  The sulfur and ammonia are separated
from the effluent stream containing (NH4)2S203.  That stream is catalytically
treated with hydrogen at reduction conditions effective to form a substantially
thiosulfute free aqueous stream.

industrial Streams, *Ammonia, Sulfur, Oxygen, Hydrogen, Catalysts, *Efflu-
ent Streams, *Waste Water Treatment, Patents

Canada, *Ammonium Hydroxide
048C

DRAINAGE BODY AND BIOLOGICAL FILM SUPPORT,

Geiger, H.

Firme Maschinenf AB

Belgian Patent 802,025.  Applied July 20, 1972.  Issued November 5, 1973.   Der-
went Belgian Patents Report, Vol. 5, No. 1, p 4, February 7, 1974.

A drainage body and biological film support for sewage treatment are described.
The drainage body consists essentially of an assembly of elements having a
large surface area which serves for the growth of the biological film.   At
infrequent intervals this film is detached, independently of the water  and
sewage feed, by means of scrapers.  This is done before the mass becomes de-
tached by itself so that it is not entrained in the water.  Regular operation
of the drainage body and maximum degradation of the sewage is obtained  in
minimum possible space and with the largest possible purification capacity.

*Sewage Treatment, *Drainage Area, Microorganisms, *Biological Treatment,
Biodegradation, *Waste Water Treatment, Patents

Belgium

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049C

CHAIN EXTENDED POLYELECTROLYTE SALTS AND THEIR USE IN
FLOCCULATION PROCESSES,

Witt, E.

Polysar International, S.A.,  Fribourg, Switzerland.

Canadian Patent 941,539.  Applied May 17, 1971.  Issued February 5,  1974.
Patents/Brevets, Vol. 102, No. 6, p 516, February 5,  1974.

The preparation of chain extended polyelectrolyte salts is  described for use
in flocculation processes.  Water soluble poly (quaternary  ammonium)  polyether
polyelectrolyte salts containing quarternary nitrogen atoms in the polymer
backbone and chain extended by ether groups are prepared by treating the poly-
meric reaction product from an N,N,N', N'-tetraalkyl-hydroxy substituted
diamine and an organic dihalide such as a dihaloalkane or a dihalo ether with
and epoxyhaloalkane.  These polyelectrolytes are used in processes for floccu-
lating particles dispersed in aqueous media, e.g., white water clarification,
clay flocculation, sewage treatment, and wet-end addition,  by adding the
polyelectrolyte to the aqueous media in amounts sufficient  to flocculate the
dispersed particles.

*Polyelectrolyte, *Flocculation, Nitrogen, Polymers,  Water  Purification, Clays,
Sewage Treatment, Dispersion, *Waste Water Treatment, Patents

Canada
050C

COALESCING OIL/WATER DISPERSIONS,

Continental Oil Co.

French Patent 2,176,682.  Applied March 17, 1973.   Issued November 2,  1973.
French Patents Abstracts, Vol. 5, No. 1, p 1,  February 7, 1974.

A dispersion of a hydrocarbon oil and water is coalesced by slow passage
through a bed of polyurethane foam which has been equilbrated relative to the
absorption of the oleophilic liquid.  The layers of oil and water are  then
separated at a density of 0.012-0.12 kg/cu dm, temperature of 0-100 C, and
at a pressure sufficient to keep the oil in a liquid state.  Applications in-
clude pollution prevention recovery of oils from residual water  in oil drilling
operations, separation of phenolics in wood treatments, etc.  By using an
equilibrated polyurethane foam a separation squeezing process for the  oil is
eliminated.

*Dispersion, Coalescence, *0il, Water, *Separation Techniques, Pollution
Abatement, *Waste Water Treatment, Patents

France, Polyurethane Foam
                                        100

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051C

REMOVING OIL SPILLS FROM WATER,

Grantley Co

French Patent 2,177,100.  Applied March 23, 1973.   Issued November 2,  1973.
French Patents Abstracts, Vol. 5, No.  1, p 2,  February 7, 1974.

A method of removing oil spills  from water by  absorbing the oils in pieces of
foam polystyrene in which the cells have been  opened by shredding is described.
The polystyrene has a density of 1.4-2.0 Ibs/cu ft, average cell size 1.0-3.0
mm, and is capable of adsorbing about 19 times its weight of crude oil.   The
oil can be subsequently recovered by treatment with a solvent (MED, MIBK,
acetone, benzene, toluene, xylene, carbon tetrachloride, perchloroethylene or
trichloroethylene) to dissolve the polymer. The polymer particles are pre-
ferably coated with a fire retardant before use.  The method may also be used
for cleaning contaminated sand,  for transportation of oil and emulsified oils,
and tank cleaning.

Adsorption, *0il, *Water, Solvents, Organic Compounds, Sand, Cleaning,
*Waste Water Treatment, Patents

France, Polystyrene Foam
052C

WATER TREATMENT ION-EXCHANGE VESSEL,

Madern, J. P.

French Patent 2,179,573.  Applied April 10, 1972.  Issued November 23,  1973.
French Patents Abstracts, Vol. 5, No. 3, p 1, February 21, 1974.

A water treatment ion exchange vessel is described which continuously
regrades the resin bed by circulating resin material.  Water for  treatment
is brought in at the bottom of the vessel where it passes through an ejec-
tor to entrain bed material which is carried up a vertical pipe to be re-
turned to the top of the bed while the water runs down through the bed.
Back washing is eliminated.  The vessel can also be used as a granular
filter unit.

*Filters, Water Treatment, *Ion exchange, Water purification, *Resins,
*Waste Water Treatment, Patents

*France, Backwash
                                      101

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053C

SEWAGE TREATMENT PLANT,

Kaelin, J. R.

Belgian Patent 801,708.  Applied July 2, 1972.  Issued October 15, 1973.  Der-
went Belgian Patents Report, Vol. 5, No. 1, p 3, February 7, 1974.

A sewage treatment plant with partial recirculation is described which uses aero-
bic biodegradation.  A central closed top cylindrical mixer tank is subdivided
by concentric cylindrical walls, and is staggered in height to form an elonga-
ted zigzag path for raw sewage fed into the outer annulus of the mixer tank at
its top and pretreated with injected pure oxygen or gas mixture containing it.
From the base of the center compartment of the mixer tank, a number of pipes
lead to the base of an outer concentric buffer tank and discharge in a peri-
pheral direction into that buffer tank.  A limited feedback of liquid with
activated sludge is taken from the surface of the buffer tank into the mixer
and treated effluent is extracted from the buffer tank.

*Recirculated Water, *Sewage Treatment, *Biodegradation, Aerobic Conditions,
Activated Sludge, Sewage Systems, Facilities, *Waste Water Treatment, Effluent,
Patents

Belgium
054C

LIQUID POLLUTION MEASUREMENT,

Procedyne Corp

French Patent 2,177,336.  Applied March 19, 1973.   Issued November 2,  1973.
French Patents Abstracts, Vol. 5, No.  1, p 3,  February 7, 1974.

A method of measuring liquid pollution is described in which the liquid is
continuously evaluated in terms of total oxygen demand.  A continuously metered
flow sampled from the liquid is mixed with a measured proportion of oxygen
and the mixture is fed into an incinerator, e.g.,  a fluidized bed of aluminum
oxide powder, at > or = 816 C.  The exhaust vapors are condensed, separated,
and dried to produce a dry residual gas which is measured for oxygen content
in an analyzer preferably calibrated to read T. 0. D. values.

*Measurement, *Liquid Wastes,  *0xygen Demand,  Incinerator, Oxygen, Patents

France, *Aluminum Oxide
                                    102

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055C

WASTE WATER PURIFICATION,

Siren, M. J. 0.

French Patent 2,177,843.  Applied March 21, 1973.  Issued November 9, 1973.
French Patents Abstracts, Vol. 5, No. 1, p 7, February 14, 1974.

A sewage and waste water purification method is described which comprises re-
moval of suspended solids and decomposition of nitrogen containing substances.
An adsorbent, preferably active carbon, and an oxygen containing gas are
introduced into a reservoir in which the waste water and a growing biomass
have been stored for > or = 3 days.  Aerobic conditions are maintained until
the whole ammoniacal nitrogen is oxidized to nitrites or nitrates.  The solids
are separated by sedimentation and the liquid phase goes into an anaerobic
zone to which more adsorbent and an organic carbon source, preferably metha-
nol, are added.  The nitrites and nitrates are reduced to elemental nitrogen
and the solids are separated by sedimentation.  High rates of denitrification
are achieved.

*Sewage Treatment, Waste Water, *Water Purification, *Suspended Solids, Ni-
trogen, Adsorption, Activated Carbon, Aerobic Conditions, Nitrates, Separation
Techniques, Oxidation, *Denitrification, Nitrites, Nitrates, Sedimentation,
*Waste Water Treatment, Patents

France, Methanol
056C

DETERMINING OIL CONTENT IN WATER,

Salen and Wlcander AB

French Patent 1,278,618.  Applied March 2, 1973.   Issued November 9,  1973.
French Patents Abstracts, Vol. 5, No.  2, p 3, February 14,  1974.

A method for determining oil content in water by  concentrating the water sample
and measuring the oil content in the concentrate  is described.  The oil is  con-
centrated by passing a definite amount of water per time through a definite
surface of a filter material which absorbs or separates the oil.   A photoelec-
tric device is used to determine the color change of the oil absorbing filter
material.  After the passage of the water, either the degree of color change
is used as a measure for the oil content, or the  dielectric constant of the
oil absorbing filter material is determined.  The measurement is used to de-
fine the oil content.  The water is passed twice  through the filter material in
opposite flow directions so that the greater part of rust and the solid par-
ticles are removed from the filter material.  The filter material consists  of
a thin strip of polypropylene wool.  Simple reliable determination of the oil
concentration in the water is effected even at oil/water ratios below
1/100,000.

*0il, *Water, Filter, *Filtering, Color, *Separation
Technique, Patents

France, *Dielectric Constant
                                       103

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0.5 7C

LIQUID WASTE STABILIZATION PLANT,

General Signal Corp

French Patent 2,179,712.  Applied December 29, 1972.  Issued November 23, 1973.
French Patents Abstracts, Vol. 5, No. 3, p 1, February 21, 1974.

A two stage liquid waste stabilization plant with massive recirculation capabili-
ties is described.  Each stage is a discrete tank, free from internal obstacles
and connected in cascade with a feedback from the intertank connection via an
injector for oxidizing agent to the suction side of the main feed pump for
sewage or sludge into the first stage.  Approximately 85% (> or = 75%) of the
flow from the first stage tank is recirculated.   For maximum efficiency the
first stage tank is recirculated.  For maximum efficiency the pressure in the
first stage is maintained at one level by the throttling effect of the jet
pump and in the second stage at another level by a reverse pressure centrifugal
pump in its outlet side.

*Recirculated Water, *Facilities, Sewage, Sludge, Sewage Treatment, Liquid
Wastes, Stabilization, *Waste Water Treatment, Patents

France
058C

SEWAGE TREATMENT,

Sanitas Co., Ltd

French Patent 7,205,271, Applied August 1, 1972.  Issued October 15, 1973.
French Patents Abstracts, Vol. 5, No. 2, p 1, February 14, 1974.

A sewage treatment is described in which the sewage is flushed from several
receivers to form a mixture of liquid arid sewage.  The mixture is separated into
high solid  content and high liquid content proportions.  The solid matter
is separated from the liquid in the part with high liquid content.  A chemical
composition is maintained in the liquid so that the liquid is a disinfectant
and deodorant.  A bleaching action is maintained in the liquid so as to have
a decolorizing effect.  The liquid is recycled and reused.  The solid particle
is reduced  and the high solid content portion is stored until all the solid has
been chemically broken down by the liquid.

*Sewage Treatment, *Separation Techniques, *Recycling, Disinfection, Water
Purification, Liquid Wastes, Solid Wastes, *Waste Water Treatment, Patents

France
                                        104

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059C

WASTE WATER PURIFICATION,

Sterling Drug, Inc

French Patent 7,301,794.  Applied March 14, 1973.  Issued November 7, 1973.
French Patents Abstracts Vol. 5, No. 2, p 2, February 14, 1974.

The purification of waste waters by simultaneous removal of organic carbonaceous
material and biological oxidation of the reduced nitrogenous forms in waste
waters followed by subsequent reduction of the oxidized nitrogen to elemental
nitrogen is described.  An aqueous suspension of a suitable adsorbent is added
to a vessel containing waste water and a developing active biomass having a
sludge age of > and = 3 days.  Aerobic conditions are maintained to oxidize the
ammoniacal nitrogen to nitrite or nitrate nitrogen.  The adsorbent, associated
adsorbed organic material, and biological solids are separated, and the solids
are returned to the vessel.  The liquid phase goes into an anaerobic zone to
which further adsorbent and a source of organic carbon is added.  The oxidized
nitrogen forms are reduced to elemental nitrogen and the mixture goes to a
quiescent zone where the adsorbent and associated organic material are removed
from the waste water.

Waste Water, Water Purification, *0rganic Matter, *0xidation, Reduction, Nitro-
gen, Adsorption, Sludge, *Biological Treatment, *Aerobic Conditions, Organic
Compounds, *Waste Water Treatment, Patents

France
060C

WASTE WATER PURIFICATION,

Esso Research and Engineering Co

Belgian Patent 801,541.  Applied June 27, 1973.  Issued December 27, 1973.
Derwent Belgian Patents Reports, Vol. 5, No. 3, p 4, February 21, 1974.

A method of waste water purification using active carbon with aerobic growth
control by oxygen treatment is described.  Suspended and dissolved organic
impurities are removed from sanitary municipal or industrial waste water, in-
cluding petroleum refinery effluents, by passing the water preferably upward
through one active carbon bed.  The bed is treated with 0.04-0.07 kg oxygen for
each 0.45 kg oxygen consumed by chemical oxygen requirement-impurities removed
from waste water.  The active carbon bed is preferably rinsed periodically by
passing water upward at a sufficiently high rate to diminish biological growth
collection on active carbon.  In a preferred process, 0.02-0.5 kg oxygen are
supplied for each 0.45 kg oxygen consumed by chemical oxygen requirement im-
purities removed from waste water.  During rinsing the active carbon is treated
at intervals with an oxygen containing gas stream.

*Water Purification, *Waste Water, *Activated Carbon, Suspended Solids,
Organic Matter, Municipal Wastes, Industrial Wastes, Adsorption, Oxygen,
Growth Rates, Control, Patents

*Belgium
                                         105

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061C

REMOVING OIL SUBSTANCES FROM WATER, ROADS, TOOLS AND MACHINES
ETC.- WITH HALOHYDROCARBONS CONTAINING NON-IONIC SURFACTANTS,

Or, II., T., and Watanabe, M.

French Patent 2,172,336.  Applied February 16, 1972.  Issued September 28, 1973.
French Patents, Food, Disinfectants, Detergents (U50),  p 4, January 17,
1974.

The preparation of a mixture of halohydracarbons containing non-ionic sur-
factants and their application in removing oily substances from water, roads,
tools, and machines are described.  The composition consists of a mixture of
not less than two percent of methylene chloride, perchloroethylene, trichloro-
ethylene, and carbon tetrachloride with 3-12 percent of the total composition,
of a nonionic surfactant of the polyoxyethylene type.  The composition has
high emulsifying, dispersing, and stripping power, is nonflammable and can be
stored safely.  A homogeneous, stable, emulsified dispersion of oils is
formed in (sea) water.  The composition can be used to disperse oil on the
sea or other water surfaces, to remove oil from roadways, or to remove oil
from tools and machine.

*Treatment methods, Waste treatment, *Waste water (pollution), *0il spills,
Liquid wastes, *0il wastes, Municipal wastes
062C

FLOWMETER AND MONITOR,

German Patent 1,930,497, Applied June 16, 1969, Issued February 28, 1974.
German Patents Abstracts, Vol. 5, No. 10, p 2, April, 1974.

Designed and patented for use with liquids and gases, this monitoring system
has a membrane arranged to vibrate in front of a jet of the flowing liquid and
a microphone behind to act as a transducer to derive an electrical signal
representing the  flow characteristics.

*Patents, *Monitoring, *Instrumentation, *Flow measurement, *Flow characteristics
                                       106

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063C

SEPARATING SOLIDS FROM LIQUID,

German Patent 2161-310, Applied December 15, 1970, Issude February 21,
1974.  German Patents Abstracts, Vol. 5, No. 9, p 2, April, 1974.

Solid particles are settled from liquid in successive steps in which the
separated particles and depleted liquid are conducted along an inclined
trapping surface.  The horizontal components of the migration speeds in
adjacent stages are altered in direction by more than 90 degrees with the
mixture being separated into parallel spaces.  The downward migrating com-
ponent enters one of two adjacent spaces in the next stage; the rising com-
ponent of the neighboring space to this flows to the successive stage in
the same space of the preceding stage, so that the layer of migrating par-
ticles is rolled around over the whole width of its migration path.

*Patents, *Separation techniques, Suspended solids, Liquid wastes
064C

FILTER FOR PURIFICATION OF EFFLUENTS,

German Patent 1484-841, Applied November 18, 1974.  Issued February 21, 1974.
German Patents Abstracts, Vol. 5, No. 9, p 1, April, 1974.

Plants are embedded into the filter medium, that being either gravel or sand
devoid of nutrients, in such a way that their roots extent parallel to the
direction of flow of the effluents through the filter medium.  An aerator
supplies fine bubbles below some of the roots.  The preferred plants are
plaited bulrushes.

*Filters, *Effluents, *Plant groupings, *Patents,  *Bulrushes

*Treatment methods
                                     107

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065C

ELECTROLYTIC FLOTATION APPARATUS,

Austin, E. P., Kemp, G. D., Modesto, F. A., and
Marshall, I.

Simon-Hartley, Ltd. Staffordshire, England

U. S. Patent 3,793,178.  Applied May 1, 1972.  Issued February 19, 1974.
Official Gazette of the U. S. Patent Office, Vol. 919, No. 3, p 962,
February 19, 1974.  1 fig.

An electrolytic flotation apparatus is described for the treatment of activated
sludge and other liquids.  The suspended material, which may include solids,
is carried to the surface of the tank by a bubbled gas to form a layer of
thickened material.  The liquid is separated from the thickened material by
electrolytic action,

*Flotation, *Electrolysis, *Patents, *Equipment, *Separation techniques,
Activated sludge, Liquid wastes, Waste treatment, Suspended solids

England
 066C

 OIL-POLLUTION DETECTOR,

 Texaco  Development  Corporation

 Belgian Patent  803,742.   Applied August  17,  1973.   Issued February  18,  1974.
 Derwent Belgian Patents  Report, Vol.  5,  No.  9, p  1,  April,  1974.

 An oil  pollution detector is  described for detection of  a liquid  contaminant
 in a  stream of  liquid of a different  density.  The  stream enters  a  U-tube
 having  an outlet limb at a predetermined height.  The level of  the  liquid
 is detected and the variations  in  level  are  determined and  show the presence
 of liquid contaminant in the  stream of liquid.  The liquid  contaminant  is
 preferably petroleum and the  uncontaminated  stream  of liquid is water.

 *0il  pollution, *Patents, *Density, Equipment, Water, Oil,  Water  levels

 *Detector, Belgium
                                         108

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067C

FILTER AND SLURRY METERING SYSTEM,

King, J. A., and Maxam, D. R.

Stauffer Chemical Company, New York, New York

Canadian Patent 944,590.  Applied August 26, 1971.  Issued April 2, 1974.
Patents Brevets/Canadians, Vol. 102, No. 14, p 1165, April, 1974.

A aystem for measuring the solids content on a dry basis in a filter aid
water slurry and pumping the filter aid back into a filter is described.
The system*circulates the filter aid water slurry through a density gauge
and flow meter to measure the dry weight of solids.  Then, the slurry is
pumped back into the filter for reuse.

*Filters, *Slurries, *Patents, *Measurement, Circulation, Weight

*Solids, Canada
068C

FLOATAGE COLLECTING APPARATUS AND METHOD,

Farrell, J. H., Biahchi, R. A., and Johanson, E. E.

JBF Scientific Corporation, Burlington, Massachusetts

U. S. Patent 3,804,251.  Applied March 6, 1972.  Issued April 16, 1974.
Official Gazette of the U. S. Patent Office, Vol. 921, No. 3, p. 1027,
April 16, 1974.  1 fig.

An apparatus and method for removing floating material from the surface of
a body of liquid and for collecting the material are described.  The apparatus
has an endless belt type materials transport mounted with a lower flight
inclined downwardly from above the liquid surface at a frontal location to
below the surface at a rearward location,.  A collection well is contiguously
behind the rearward location.  The transport is driven to advance the lower
flight in the direction from the frontal location to the rearward location.
This motion carries floating material from the liquid surface downward and
rearward under the lower flight of the transport and releases it at the
rearward location to float upward into the collection well.  A method for
floatage collection by steps is also included.

*Equipment, *Patents, Separation techniques

*Floatlng material
                                           109

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069C

METHOD FOR CONTROLLING FLOW OF AQUEOUS FLUIDS IN
SUBTERRANEAN FORMATIONS,

Routson, W. G.

Dow Chemical Company, Midland, Michigan

Canadian Patent 944,548.  Applied February 22, 1971.   Issued April 2, 1974.
Patents Brevets, Vol. 102, No. 14, p 1156, April 2, 1974.

The formation of colloidal, water-insoluble, inorganic compounds in the
presence of high molecular weight organic polyelectrolytes in dilute aqueous
solution provides aqueous compositions having improved resistance to flow
through porous subterranean formations.  The use of these compositions
provides a method for diminishing or shutting off water production in oil
wells, for controlling the mobility of aqueous fluids in zones of higher
permeability in such formations and for plugging subsurface leaks as in
earthern dams.  This method provides a useful adjunct in the control of
thief zones in oil well drilling and in secondary recovery of petroleum by
water flooding techniques.

*Flow control, *Patents, Colloids, Subsurface flow, Inorganic compounds,
Resistance, Porous media

Polyelectrolytes, Canada
070C

APPARATUS AND METHOD FOR TREATING WASTE LIQUID,

Ross, D. S.      i

Hydro-Clear Corporation, Avon Lake, Ohio

U. S..Patent 3,792,773.  Applied September 30, 1971.  Issued February 19, 1974.
Official Gazette of the U. S. Patent Office, Vol. 919, No. 3, p 867, February
19, 1974.

An apparatus and method for treating waste effluent from a sewage treatment
plant using a filter unit having a backwash arrangement are described.  After
backwashing, the liquid is subject to flocculation, coagulation, and
settlement to produce a supernatant.  The supernatant enters directly into
the inlet of the filter without returning the backwash liquid to the sewage
treatment plant.  The solids in the backwash liquid are concentrated and
removed without being reintroduced into the sewage treatment plant.

*Waste water treatment, *Sewage effluents, *Filtration, *Patents, Equipment,
Flocculation, Coagulation, Sewage treatment, Treatment plant

Backwash, Settlement
                                      110

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071C

METHOD AND MEANS OF CONTROLLING DEPOSITION OF PARTICLES
IN A LIQUID,

Woodhouse, D. A.

Phillips, Ormonde, and Fitzpatrick,
Melbourne, Victoria, Australia

Australian Patent 445,189.  Applied September 3, 1969.  Issued February 14,
1974.  Official Journal of Patents, Trade Marks, and Designs, Vol. 44,
No. 5, p 483, February 14, 1974.

A method of treating a liquid to promote coagulation of particles in the
liquid is described.  A self-induced e.m.f. is produced at a section of a
supply conduit through which the liquid flows.  It is effective to alter
the Zeta potential of particles and ions present in the liquid contained
in or passing through that section of the conduit.

*Liquids, *Coagulation, *Patents, Flow, Zeta potential, Electrochemistry

*Electromagnetic force, Australia, Deposits
072C

TESTING LIQUID SAMPLES,

Victors, Ltd

Australian Patent 444,506.  Applied December 21, 1970.  Issued January, 1974.
Official Journal of Patents, Trade Marks and Designs, Vol. 44, No. 2, p 178,
January, 1974.

An apparatus for use in testing samples of liquids is described.  It consists
of a multi-outlet chamber and a methods for producing suction within the
chamber.  The liquid is drawn through the chamber inlet into the chamber and
along the first fluid path until the liquid reaches the first capillary.  The
level of liquid in the chamber rises while gas is drawn from the chamber via
the second fluid path.  The chamber is subsequently emptied of liquid by
connecting the third fluid path to connect the first outlet to the suction
producing means in the chamber bypassing the portion of relatively high
resistance of the first path.

*Equipment, *Patents, *Testing, *Liquids

Suction, Australia
                                        111

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073C

CRUDE OIL SWEEP DREDGE,

Kllney, E.

Canadian Patent 943,871.  Applied June 8, 1971.  Issued March 19, 1974.
Patents/Brevets, Vol. 102, No. 12, p 1010, March 19, 1974.

An apparatus for removal of oil and sludge from the surface of water is
described.  The apparatus can be mounted on a vessel and has an endless
bucket conveyor supported by an arm structure which extends into the water
at one end and to a discharge area in the vessel at the other end.  A drive
moves the conveyor so it picks up oil and sludge and carries it to the
discharge area.  A means of supply heat is adjacent to the discharge area
and aids the discharge of oil and sludge from the buckets.

*Equipment, *0il, *Sludge, *Patents, *Water, Water purification, Dredging

Canada
074C

APPARATUS FOR DREDGING DIVIDED SOLIDS SUBMERGED IN
LIQUID,

Duval, L. A.

U. S. Patent 3,800,949.  Applied September 23, 1971.  Issued April 2, 1974.
Official Gazette of the U. S. Patent Office, Vol. 921, No. 1, p 172, April 2,
1974.  1 fig.

Ar. apparatus for removing finely divided solids collected in a sump or pit
in association with water is described.  A main frame supports the apparatus
above the pit.  There are two guides; the first guide is supported in the
frame for vertical reciprocation.  The second guide is supported within the
first guide for rotation about a vertical axis.  A boom extends outwardly and
downwardly from the lower end of the second guide.  The boom is tillable about
a horizontal pivot axis.  There is a dredging head at the outer end of the
boom which is adapted to reach various parts of the pit by manipulation of
the apparatus.  A pump is mounted inside of the second guide with an intake
line communicating to the dredge head so that the loosened solid material
in somewhat of a slurry is able to be pumped out of the pit.

*Equipment, *Patents, *Dredging, *Liquids, Pumps, Rotations, Pumping,
Slurries

*Solids, Boom
                                       112

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 075C

FLUID SAMPLE ANALYSIS SYSTEM,

Durrum, E. L., Forge, C. 0., Lee, P. L. Y., and
Mackinnon, K. L.

Durrum Development Corporation,
Palo Alto, California

U.S. Patent 3,806,321.  Applied September 2, 1971.  Issued April 23, 1974.
Official Gazette of the U.S. Patent Office, Vol. 921, No. 4, p 1577, April 23,
1974.  1 fig.

A fluid sample analysis system is described which is characterized by an ion
exchange column which operates on a time basis.  A reagent supply line under
substantial positive pressure discharges reagent into the eluent of the ion
exchange column for mixing reagent and eluent.  There is a back pressure
resistance to passage of fluid which is substantially matched to the back
pressure resistance provided by the ion exchange column.  The system is further
characterized by means for the mixing the eluent and reagent and by a tubular
reaction coil.

*Patents, *Liquids, *Analytical techniques, *Ion exchange, Separation tech-
niques, Mixing, Pressure, Tubes

Reagent, Eluent
076C

METHOD FOR DRYING SLUDGE AND INCINERATING ODOR BODIES,

Keller, F. R.

U. S. Atomic Energy Commission,
Washington, D.C.

U.S. Patent 3,805,715.  Applied October 26, 1972.  Issued April 23, 1974.
Official Gazette of the U.S. Patent Office, Vol. 921, No. 4, p 1421, April
23, 1974.

A process for drying sewage sludge and eliminating its odors is described.
The sludge is dried in a fluidized bed dryer while the odors are eliminated by
incinerating them in a fluidized bed incinerator.  The hot exit gases from
the incinerator are employed to preheat both the sewage sludge feed and
the fluidizing air stream for the fluidized bed dryer.  The dryer contains
a heat exchanger submerged in the fluidized bed which provides the heat for
drying from the low pressure exhaust steam exiting from an extraction turbine.
The condensate and exhaust from the dryer heat exchanger are recycled to the
incinerator heat exchanger for generation of high pressure steam.  The output
of the extraction turbine is used to drive air blowers for the two fluidized
beds.  The fluidized bed incinerator is fluidized with the stream of off
gases and odor bodies from the fluidized bed dryer, the fuel value of the off
gases and odor are effectively used in the incinerator where heat is generated
by fuel combustion.

*Drying, *Patents, *Sewage sludge, *0dor, Control, Incineration, Gases,
Turbines, Equipment

*Fluidized bed


                                          113

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077C

SEWAGE FLOW CONTROL SYSTEM,

Smith, S. F.

U.S. Patent 3,805,817.  Applied December 13, 1971.  Issued April 23, 1974.
Official Gazette of the U.S. Patent Office, Vol. 921, No. 4, p 1447, April
23, 1974.  2 fig.

A sewage flow control system is described for a sewage piping complex.  Flow
stabilizing stations are counted in a series of sections, each including means
for constricting and means for accelerating flow to maintain selected pressures
and flow rates in the controlled sections.  This process obtains maximum use
of the cubical volume of the piping complex to maintain the piping full of
fluid to provide overall even flows of sewage during both normal peak and
low volume flows and sufficient internal piping pressure to inhibit ground
water influx.

*Patents, *Sewage, *Flow control, Pipes, Stabilization, Flow rates, Groundwater
078C

APPARATUS FOR AND PROCESS OF TREATING LIQUIDS WITH
A GAS,

Armstrong, E. T.

U.S. Patent 3,805,481.  Applied December 21, 1970.  Issued April 23, 1974.
Official Gazette of the U.S. Patent Office, Vol. 921, No. 4, p 1359,
April 23, 1974.  1 fig.

A gas-liquid mixing system for selective bacterial reduction, generalized
disinfection sterilization or other gas treatment of the liquid is described.
The system utilizes essential gravitational head and/or pumps in conjunction
with a process flow line which may operate under a hydraulic pressure gradient.
It has an inlet at one end for receiving the untreated liquid and an outlet
at its opposite end, one or more local areas of high momentum exchange, and
one or more injectors for the introduction of a gas into the process line.
The injectors are located so as to introduce the gas into the liquid down-
stream from the areas of high momentum exchange where the static pressure is
at least partially regained.  The gas may consist of air, oxygen, or an
oxygen ozone mixture, either alone or mixed with a carrier gas.

*Gases, *Patents, *Liquids, *Mixing, Disinfection, Separation techniques,
Equipment, Flow, Oxygen, Ozone, Flow

Sterilization, Bacterial reduction
                                       114

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079C

RADIOACTIVE WASTE TREATMENT SYSTEM,

Mertens, J.

Nuclear Waste Systems Company,
Campbell, California

U.S. Patent 3,085,959.  Applied June 3, 1971.  Issued April 23, 1974.  Official
Gazette of the U.S. Patent Office, Vol. 921, No. 4, p 1483, April 23, 1974.

A radioactive waste treatment system is described for solid radioactive
process waste from nuclear reactor power plants.  The wastes consist of
filter sludges and demineralized resins or ion exchange resins.  The wastes
are moved to large tanks where they are collected.  The backwash water and
floor drain water wastes are percolated throuth settled solids by gravity.
In doing so, the wastes are prefiltered and predemineralized.  The waste
waters are then polished in the water treatment system and returned to a
condensate storage tank.

*Waste water treatment, *PatentS, *Radioactive wastes, Solid wastes, Sludges,
Resins, Storage tanks, Separation techniques, Percolation, Waste disposal
080C

FRAME FOR A SEMI-PERMEABLE MEMBRANE ASSEMBLY,

Butruille, Y. and Mourlan, J.

Rhone-Poulene S. A., Paris, France

U.S. Patent 3,805,960.  Applied July 1, 1971.  Issued April 23, 1974.  Official
Gazette of the U.S. Patent Office, Vol. 921, No. 4, p 1483, April 23, 1974.
1 fig.

Frames for clamping together the plane membrane and interposed plates of a
semi-permeable membrane stack are described.  The frame comprises two frame
plates interconnected by tie bars extending from onye of the plates to pass
through orifices in the other plate.  The orifices are countersunk in such a
way that the tiebars may be deformed in the orifices to limit subsequent
increases in the distance between the two frame plates, so that the semi-
permeable membrane stack is held tightly together.

*Semipermeable membranes, *Patents, Equipment

*Frames, France
                                       115

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081C

SEWAGE AND WATER TREATMENT WITH MODIFIED QUARTERNARY SALTS
OF VINYLPYRIDINE COPOLYMERS,

Doss, R. C. and deary, J. W.

Philips Petroleum Compnay,
Bartlesvllle, Oklahoma

U.S. Patent 3,806,450.  Applied December 20, 1971.  Issued Arpil 23, 1974.
Official Gazette of the U.S. Patent Office, Vol. 921, No. 4, p 1604, April 23,
1974.

A sewage and water treatment system is described in which the sewage
and water are chemically conditioned with modified quaternary salts of
vinylpyrldine copolymers.  Coagulation, flocculation, and filtration in
sewage and water treatment processes are significantly improved by the
use of the salts.

*Patents, *Sewage, *Water treatment, Salts, Coagulation, Filtration,
Flocculation

*Vlnylpyridine, *Quarternary salts
082C

AUTOMATIC VALVES, PARTICULARLY FOR USE WITH FILTERS,

Cullis, J. C.

Engineering Components, Limited,
Liverpool, England

U.S. Patent 3,807,561.  Applied September  13, 1971.  Issued April  30,  1974.
Official Gazette of  the U.S. Patent Office, Vol. 921, No. 5, p 1909, April
30, 1974.  1 fig.

An automatic valve of the poppet or mushroom type  is described for use with
a filter.  It  is molded as an integral unit from glass fibre reinforced nylon
and has a head and a stem consisting of  two parallel limbs formed  at their
free ends with lateral hook-like projections.  The limbs can be pressed
together  to enable the projections to pass through a port in a ported  member.
They then can  be allowed to spring back  to their normal configuration, engaging
a spring  interposed  between the projections and ported member.

*Patents, *Valves, *Filters, Equipment

England
                                     116

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083C

DEVICE FOR CONDUCTING WASTE LIQUID FROM A RECEPTACLE TO
A PNEUMATIC LIQUID DISPOSAL SYSTEM,

Svanteson, S. E. A.

Aktiebolaget Electrolux, Stockholm, Sweden

U.S. Patent 3,807,431.  Applied November 21, 1972.  Issued April 30, 1974.
Official Gazette of the U.S. Patent Office, Vol. 921, No. 5, p 1874, April
30, 1974.  1 fig.

An apparatus for conveying waste liquid from a hold receptacle to a vacuum
sewage disposal system is described.  The waste liquid is conducted through a
transport conduit to which atmospheric air is able to enter.  The air-waste
liquid provides for a more efficient moving of the waste.

*Equipment, *Liquid waste, Sewage, Waste disposal,  Air

*Liquid waste transport, Sweden
 Q84C

 METHOD AND APPARATUS FOR REMOVING SOLIDS,

 Pentz, H.  L.,  Pakhani,  C.,  and Majeron,  F.

 FMC Corporation,
 San Jose,  California

 U.S.  Patent 3,807,560.   Applied January  12,  1972.   Issued April  30,  1974.
 Official Gazette  of  the U.S.  Patent  Office,  Vol. 921, No. 5, p 1908-1909,
 April 30,  1974.   1 fig.

 A method and apparatus  for  removing  a  varying  depth layer of settled solids
 from the bottom of a sedimentation tank  is described.  The apparatus includes
 a plurality of spaced education means  supported on  a bridge that  is  movable
 transversely between spaced inlets and outlets for  the tank to remove settled
 solids from associated  zones  in the  tank bottom.  The apparatus provides a
 range of flow  capacity  between a minimum and maximum for each zone.   The
 flow of sludge can be adjusted to remove all deposited solids from each zone
 during each pass  of  the bridge.   A sensing mechanism maintains a  substantially
 uniform solids concentration  in the  sludge being removed.

 *Separation techniques,  *Patents, *Equipment,  *Bottom sediments,  Settling
 basins, Sludge treatment

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085C

METHOD AND APPARATUS FOR DETERMINING POLLUTION INDEX,

Brainard, E. C., II.

Environmental Devices Corporation,
Marion, Massachusetts

U.S. Patent 3,807,860.  Applied January 31, 1973.  Issued April 30, 1973.
Official Gazette of the U.S. Patent Office, Vol. 921., No. 5, p 1986, April
30, 1974.  1 fig.

A method and apparatus for providing an index of the concentration of pollutant
in water is described.  The index is determined according to the difference
between two different measures of the salinity of water.  In a preferred
embodiment the two measures of salinity are measures of electrical conductivity
and of refractive index.

*Patents, *Water pollution, Methodology, Equipment, Saline water, Salinity,
Refractivity

*Pollution index
086C

FILTRATION APPARATUS AND METHOD,

Australian Patent 445, 653.  Applied May 9, 1968.  Issued May 5, 1969.  Official
Journal of Patents, Trade Marks and Designs, Vol. 44, No. 7, p 669, February 28,
1974.

Separation of a solid medium from a liquid medium is accomplished by a cylindri-
cal inner wall for the housing, a cylindrical core with a longitudinal bore,
and an axially moveable core which makes up a filtration apparatus.  A pressure
chamber is provided by a flexible tube diaphragm within the housing, located
within the annular cavity.  A deformable lip is joined to the body portion
but is free from the core, adapted to come into sealing contact with a co-operating
portion of the housing in the operative position of the core.  A liquid-
solid inlet is defined; and a third portion of the housing defines a fluid in-
let leading into the pressure chamber between the inner wall and the outside of
the diaphragm.  A fourth and final portion of the housing defines a fluid out-
let leading from the pressure chamber to outside the housing, with means for
exerting a fluid pressure on the outside of the diaphragm via the fluid inlet,
pressure being releasable via the fluid outlet.

*Patents, *Filtration, *Separation techniques, Liquids, Pressure, Equipment,
Flow, Pressure

Solids

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087C

SLUDGE BLANKET FOR WATER TREATMENT,

Australian Patent 445,755.  Applied November 8, 1968.  Issued November 4, 1969.
Official Journal of Patents, Trade Marks and Designs, Vol. 44, No. 7, February
28, 1974.

Water treatment is achieved using chemical agglomeration of impurities followed
by separation of the chemically formed floe-suspension by filtration.  A fully
fluidized sludge blanket is comprised of sludge concentration or compartment, over-
flow openings, and walls of substantially cylindrical vessels arranged horizon-
tally.  A slot along the whole length of the lower part of the sludge blanket
connects to a distribution channel for the treated liquid.

*Sludge, *Water treatment, *Patents, Liquids

*Sludge blanket, Floe-suspension
088C

PROCESS FOR REMOVING PROTEIN FROM WASTE EFFLUENT,

Australian Patent 445,712.  Applied July 15, 1968.  Issued July 14, 1969.  Of-
ficial Journal of Patents, Trade Marks and Designs, Vol. 44, No. 7, p 682, Febru-
ary 28, 1974.

A substantially protein-free liquid is recovered after passing waste effluent
through a bed or beds of ion exchange material, and regenerating the ion ex-
change material for future use.  These ion exchange groups are cross-linked
by the residues of a cross-linking agent which is bifunctional and capable of
reacting with two hydroxyl groups to form covalent bonds.

*Patents, *Effluent, *Proteins, Wastes, Waste treatment, Ion exchange, Liquids

Hydroxyl groups
                                        119

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089C

METHOD AND APPARATUS FOR THE TREATMENT OF INFLUENT WATERS SUCH
AS SEWAGE,

Neel, M. E.

Port Arthur, Texas

United States Patent 3,808,123.  Applied December 14, 1971.  Issued April
30, 1974.  Official Gazette, Vol. 921, No. 5, p 2047, April 30, 1974.  1 fig.

A method and apparatus has been patented for treating influent waters such
as sewage, waste water, discharges from petroleum or chemical plants, or
other materials requiring oxidation.  It utilizes a pressure vessel into which
the influent waters are moved under pressure.  The pressure within each vessel
is maintained within a desired range, and an oxygen stream is pumped into the
influent waters.  To insure proper contact with the oxygen, detention time
within the vessel is provided; fine bubble diffusers are used to inject the
oxygen stream; and these diffusers are spaced at various locations and if de-
sired at varying levels within the vessel.  Means are provided to vary the
quantity of the oxygen stream introduced into the vessel at various points,
as well as to vary the percentage of oxygen in the oxygen stream itself.
The apparatus and method may be employed at various locations in a sewer system
as intermediate steps to prevent excessive build-up of odor or corrosion,
or with additional equipment, such as tapered aeration tanks, or aeration
tanks, or aerobic digesters, to form a complete treatment plant.

*Patent, *Waste water treatment, *Treatment methods, *0xidation, *Sewage
treatment, Aeration, Odor
090C

MEMBRANES FOR REVERSE OSMOSIS,

Walmsley, D.

United Kingdom Atomic Energy Authority, London, England

United States Patent 3,807,571.  Applied April 9, 1973.  Issued April  30,  1974.
Official Gazette, Vol. 921, No. 5, p 1911, April 30, 1974.  1 fig.

A patent has been granted for a cellulose acetate reverse osmosis membrane, a.
method of making such a membrane by casting, and a solution suitable for use
in casting such a membrane.  The particular features of the invention  lie  in
the selection of a narrow range of acetyl values for the cellulose acetete,
obtained by blending cellulose acetates having acetyl values falling outside
the selected range, and in the composition of the casting solution which in-
cluded acetone dioxan and formamide.  The membranes of the invention are
further characterized in having Indices of Performance (I.O.P.) of at
least 50; frequently the I.O.P. is higher than 100.

*Patent, *Reverse osmosis, *Waste water treatment, *Membranes, *Cellulose,
Treatment method

"Cellulose acetate
                                          120

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091C

METHOD OF TREATING SUBTERRANEAN FORMATION TO IMPROVE PERMEABILITY,

Thigpen, A. B., and Tate, J. F.

Texaco, Inc., New York, New York

United States Patent 3,807,500.  Applied March 12, 1973.  Issued April 30,
1974.  Official Gazette, Vol. 921, No. 5, p 1893-1894, April 30, 1974.  1 fig.

A method has been patented for treating subterranean formations containing
water sensitive clays which have sustained permeability damage due to contact
with fresh water.  To increase the permeability of the subterranean formations
a solution of potassium chloride is injected into the formation via wells
drilled into the formations.  Treatment with a heated fluid including steam
having a temperature of at least 300°F for several hours follows.  The forma-
tion is then further treated with mud acid or retarded mud acid.

*Patents, *Aquifer management, *Permeability, *Subsurface drainage, *Arti-
ficial recharge, Infiltration, Clays
 09 2C

 FILTERING PROCESS,

 Goldfield,  J.  and Greco, V.

 Johns-Manville Corporation,
 New York,  New  York

 Canadian  Patent 943,079.  Applied March  16,  1971.   Issued March  5,  1974.
 Patents/Brevets, Vol.  102, No.  10,  p  844, March, 1974.

 A process  for  filtration of submicron liquid and solid particles  from  large
 volumes of  gas in which the particles are carried  is described.   The gas
 is passed  through a  filter medium made up of fibers having an  average
 diameter  of up to about 10 micron at  a velocity of at least  300  ft/min
 and at a  pressure drop not greater  than  40 inches  of water to  remove at
 least 80%  of such particles.

 *Patents,  *Filtration, Filters, Liquids, Solid wastes, Gases,  Pressure, Canada

 *Submicron  particles,  *Purification
                                          121

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 093C

 LOW-TEMPERATURE PURIFICATION OF FLUIDS,

 Hays,  G.  E.,  and Albright,  M.  A.

 Phillips  Petroleum Company,
 Bartlesville,  Oklahoma

 Canadian  Patent 943,055.  Applied May  10,  1971.   Issued March  5,  1974.
 Patents/Brevets, Vol. 102,  No.  10,  p 839,  March,  1974.

 An absorption process for the  low temperature  purification  of  fluids  is
 described.  Liquids or  gas  streams  are purified at  a  temperature  at or
 below  the freezing point of the constituents to be  purified.   Operating
 at or  below that temperature greatly increases the  adsorption  capacity of
 the adsorptive material.

 *Patents, *Absorption,  Liquids, Gases, Streams, Temperature, Canada

 *Purification
094C

WATER QUALITY MEASURING APPARATUS,

Benckiser Wasser Technik

Belgian Patent 806,020.  Applied October 12, 1972.  Issued February 1,
1974.  Derwent Belgian Patents Report, Vol. 5, No. 8, p 1, March, 1974.

A water quality measuring apparatus is described for drinking water,
swimming baths, and process effluent.  The oxygen absorbed value of a
liquid is automatically measured by the instrument using platinum/calomel
electrodes as a composite, one piece probe in an amplified measuring
circuit.  The probe fits into a pocket through which only a fraction of
the flow in a main pipe is diverted.  The fraction is regulated by a flow
control valve and flowmeter upstream of the pocket which discharges at
negligible pressure.  The instrument can be easily disconnected from the
main pipeline in order to clean or renew the electrode without inter-
fering with flow through the main pipeline.  Since the electrode is not
subjected to main pipeline flow and pressure conditions, it can be con-
structed as a cheap, lightweight unit.

*Patents, *Instrumentation, *Measurement, *Water quality, Potable water,
Swimming pools, Effluents, Oxyben, Electrodes, Flow control, Flow
measurements, Pipes, Pipelines

Belgium, Platinum, Calomel

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095C

PURIFYING POLLUTED EFFLUENT,

Stengelin, V.

Netherlands Patent 7,310,800.  Applied August 3, 1973.  Issued February
7, 1974.  Derwent Netherlands Patents Report, Vol. 5, No. 8, p 3,
March, 1974.

A separation technique for purifying polluted effluent is described.  The
incoming effluent is split into two fractions of which the major, about
80-95% of the whole, is put into the first stage while the balance of
untreated effluent is divided between the second and subsequent stages.
This increases the decomposition rate in later stages.

*Patents, *Separation technique, *Waste water purification, Effluent,
Water pollution treatment

Netherlands
 096C

 AERATION DIFFUSER,

 Martin Marietta  Corporation

 French Patent  2,184,426.  Applied May  16,  1972,   Issued February  1,
 1974.  French  Patents Abstracts, Vol.  5, No.  8,  p 1, March,  1974.

 An aeration diffuser was  developed  for the diffusion of a  gas  into a
 relatively large volume of liquid,  particularly  diffusion  of air  or oxygen
 into polluted  lakes or rivers  deficient in dissolved oxygen.   The gas  is
 delivered into the liquid by a small aperture to form a small  bubble.
 The bubble is  driven into the  mass  of  liquid  before its formation is
 complete by a  flow of liquid past the  aperture at a speed  which is
 preferably less  than that of the liquid past  the aperture.

 *Patents, *Aeration, *Diffusion, Gases,  Liquid,  Air, Oxygen, Water puri-
 fication, Lakes, Rivers,  Water pollution treatment, Equipment

 *Aerator, France
                                       123

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09 7C

METHOD FOR INSTALLING AERATION SYSTEMS IN SEWAGE TREATMENT
TANKS,

Thayer, P. M.

Water Pollution Control Corporation,
Milwaukee, Wisconsin

U.S. Patent 3,802,676.  Applied August 3, 1971.  Issued April 9, 1974.
Official Gazette of the U.S. Patent Office, Vol. 121, No. 2, p 619-620,
April 9, 1974.

A method of installing an aeration system in a sewage treatment tank is
described.  It includes the following steps:  prefabricating headers having
transversely extending connectors longitudinally spaced along the header;
supporting the header in a tank to extend horizontally; adjusting the posi-
tion of support of the header to obtain a desired uniform depth in the
tank for the header; leveling the header; rotating the header on its axis
to level the connectors; and attaching air diffusers to the connectors.

*Patents, *Installation, *Aeration, *Sewage treatment, Sewerage, Equipment
098C

DEVICE FOR CONTINUOUSLY TREATING LIQUIDS,

Plura, G.

L and C Steinmuller GmbH, Gummersbach, Germany

U.S. Patent 3,802,568.  Applied October 31, 1972.  Issued April 9, 1974.  Official
Gazette of the U.S. Patent Office, Vol. 121, No. 2, p 593, April 9, 1974.
1 fig.

A trisectional device for continuously treating fluids in an ion exchange
bed is described.  The device consists of a column like hollow body, the
ends of which are closed off with lid like elements, distribution elements
within the device, supply and discharge conduits for the fluid, the
fluid, the fluid treating medium, and tubes within the hollow body and
parallel to its longitudinal axis.  The free ends of the tubes are
firmly connected with intermediate plates.  The uppermost tube is
provided with cutouts extending all the way through.  A smaller tube
is concentrically arranged within the uppermost tube and flows into
cutouts preferably radially extending through the uppermost tube.  In
the treating area of the middle bed section the tubes continue as"
solid rods, again forming tubes in the lower bed section.  Cutouts are
provided in the connecting region between the solid rod and the lower
tube section.

*Patents, *Ion Exchange, *Equipment, *Design data, Waste water treatment,
Equipment

Germany
                                          124

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099C

WATER PURIFYING DEVICE,

Sasaki, S. and Nishikawa, T.

Matsushita Electric Industrial Compnay, Limited,
Osaka, Japan

U.S. Patent 3,802,563.  applied December 20, 1971.  Issued April 9, 1974.
Official Gazette of the U.S. Patent Office, Vol. 121, No. 2, p 592, April
9, 1974.  1 fig.

A water purifying device is described which consists of a filter unit
with a filter element within it and a purified water discharge tube connected'
to it.  There is a directional control valve unit with two water outlet
ports and an externally operable valve ball.  A hose connects one of the
water outlet ports with the filter unit.  The directional control valve
is mounted on a faucet and the valve ball is externally operated to
alternately open and close the water outlet ports to obtain purified, city
water.

*Patents, *Water purification, *Filter, *Filtration, *Municipal water,
Design data, Valves, Equipment

Japan
100C

WATER INTAKE SCREEN,

Hughes, R. G. and Evard, W. M.

FMC Corporation, San Jose, California

U.S. Patent 3,802,565.  Applied May 22, 1972.  Issued April 9, 1974.
Official Gazette of the U.S. Patent Office, Vol. 121, No. 2, p 592, April
9, 1974.  1 fig.

A traveling intake water screen installation is described for removing
debris and fish from a flowing stream of water.  It includes a screen
movable through a vertically closed loop.  The screen is suspended from
a pair of dual material head sprockets and comprises multiple screen
trays interconnecte/d by endless dual material side chains.  Each screen
tray has flexible end plates for preventing passage of debris around the
sides of the screen.

*Patents, *Intake structures, Water purification, Fish, Solid wastes,
*Screens, Flexibility, Installation, Streams
                                       125

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101C

PROCESS FOR REMOVAL OF ORGANIC CONTAMINANTS FROM A FLUID STREAM,

Sutherland, G.

AWT Systems, Incorporated,
Wilmington, Delaware

U.S. Patent 3,803,033.  Applied November 6, 1972.  Issued April 9, 1974.
Official Gazette of the U.S. Patent Office, Vol. 921, No. 2, p 704, April
9, 1974.  1 fig.

A process for the removal of organic contaminants from a fluid stream is
described.  A magnetically susceptible iron carbon complex is dispersed
in the stream until a substantial amount of contaminants have been ad-
sorbed from the stream.  The dispersion passes through a magnetic filter
to separate the dispersion into a fluid stream having a reduced concen-
tration of contaminants and an adsorbed complex containing contaminants.
Regeneration of the adsorbed complex may be accomplished by heating the
complex in an inert atmosphere at a temperature sufficient to desorb and
vaporize the contaminants.

*Patents, *0rganic matter, *Waste water treatment, Iron, Carbon, Dis-
persion, Adsorption, Filters

*Magnetic complexes, Iron-Carbon complex
 102C

 EFFLUENTS BIOCHEMICAL PURIFICATION,

 Smirnov,  D.  N.,  Dmitriev,  A.  S.,  and Gumbatov,  R.  T.

 Water Works  and  Sanitation Research  Institute,
 Bulgaria

 Sovient Patent 385,929.   Applied  February 18,  1971.   Issued September
 20,  1973.  Soviet  Inventions  Illustrated,  Vol.  5,  No.  9,  p  2-3,  April,
 1974.  1 fig.

 The  maintenance  of a stable purification process  is  controlled by con-
 tinuous monitoring of oxidation regeneration potential of drainage water
 flowing into aeration tanks and recirculation  of  sludge and supply of
 air  into the tank  automatically adjusted in accordance with test results.
 The  concentration  of contaminated drainge water is checked  by test unit
 which is used to control the  air  flow through  a valve.  The test unit is
 also used to control the water level in the sedimentation tank.   Sludge
 in the tank is recirculated through  a regulated valve to the tank.

 *Patent,  *Water  water purification,  *Maintenance,  Activated sludge,
 Monitoring,  Drainage water, Aeration, Water level, Automatic control,
 Tanks, Valves

 U.S.S.R.
                                        126

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10 3C

AEROBIC DRYING OF ORGANIC WASTE,

Gujer, H.

Australian Patent 445,094.  Applied December 2, 1968.  Issued February, 1974.
Official Journal of Patents, Trade Marks and Designs, Vol. 44, No. 5,
p 460-461, Februar, 1974.

An aerobic method for continuously dewatering organic waste matter of a
water content of more than 40% by weight is described.  Aerobic precom-
posting proceeds to a water content permitting aerobic compositing of
the water waste matter while simultaneously precomposting the waste matter
arranged in a bed of substantially uniform thickness.  The waste matter
with more than 40% by weight water is periodically admixed through pro-
portionately progressive addition to the total bed mass which consists
essentially of precomposted waste matter of the same type, in a maximum
quantity of 20% by weight of the bed mass per day.  The entire bed mass
is circulated several times daily during the continuous precomposting
process and as much precomposted, dewatered waste matter is removed from
the process as new waste matter of a water content of more than 40% by
weight is added.

*Patents, *Aerobic conditions, *Dewatering, *0rganic wastes, Water drying,
Waste water

Australia
104C

CISTERN,

Gramall Industries Pty Limited

Australian Patent 444,625.  Applied March 11, 1970.  Issude January 31, 197
Official Journal of Patents, Trade Marks, and Designs, Vol. 44, No. 3,
p 259, January 31, 1974.

A cistern is described which has walls and a base forming a container, a
weir, or a dividing wall, joining walls at Its ends and extending upwardly
from the base to divide the cistern into two parts.  There is a ball
valve part and a float part which connect above the weir.  The upper edge
of the weir or dividing wall is below the upper edges of the walls.  A pair
of float operated valves are carried by the cistern and positioned above
the ball valve part of connected to mains supply.  An outlet conduit ex-
tends downwardly from the first pair of valves and passes through the
cistern base.  A by pass tube places the conduit in fluid flow connec-
tion near the base with the float part of the cistern and constitutes an
ejector inlet conduit.  A short outlet conduits depending from the second
pair of valves, each valve has a valve operating arm pivoted to it with
floats attached to it.  The floats are positioned in the float part of
the cistern.

*Patents, *Cisterns, *Design data, Weir, Valves, Floats, Operation,
Conduits

Australia
                                            127

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105C

PROCESS FOR REGENERATING SPENT ACTIVE CARBON IN A SUSPENSION-
DISPERSION TRANSPORT SYSTEM,

Joseph, R. T.

FMC Corporation, New York, New York

U.S. Patent 3,801,514.  Applied June 9, 1971.  Issued April 2, 1974.
Official Gazette of the U.S. Patent Office, Vol. 921, No. 1, p 306,
April 2, 1974.  1 fig.

A process for regenerating spent active carbon in a suspension dispersion
transport system is described.  The carbon, recovered from secondary
sewage treatment and from beer and sugar refining, is regenerated by
rapidly heating it in the dip dispersed phase in the presence of an
activating atmosphere.  The activating gases are preferably steam or
carbon dioxide or both.

*Patents, *Activated carbon, Carbon dioxide, Steam, Sewage treatment,
Heating, Suspension

*Regeneration, Suspension dispersion transport system
106C

SEWAGE TREATMENT,

Luck, E.

Thornhill, Ontario, Canada

U.S. Patent 3,801,499. Applied August 25, 1971.  Issued April 2, 1974.
Official Gazette of the U.S. Patent Office, Vol. 121, No. 1, p 54, April
2, 1974.

A method of treating liquid sewage is described which includes the pre-
cipitation of heavy metals which may have been previously settled, fil-
tered, or otherwise treated so as to remove a large proportion of the
solids content.  The pH is raised to over 11 to destroy pathogenic or-
ganisms and to release the enzymes from bacteria in the sewage.  The pH
is then lowered so that it is in a range in which the enzymes digest
components of the sewage.  Microorganisms are added to the sewage to
assist in decomposing organic components and are then killed and removed.
The remaining solution is neutralized and treated with ion exchange
resins to remove the anions and cations.  The water produced is of
drinking water quality and the process by which it is made is apprecia-
bly faster than present commercial sewage treatments.

*Sewage treatment, *Patents, *Water purification, *Chemical precipitation,
Heavy metals, Hydrogen ion concentration, Enzymes, Biological treatment,
Sewage bacteria, Biodegradation, Ion exchange, Resins, Water quality,
Potable water, Canada
                                       128

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10 7C

ACTIVATED SLUDGE WASTE WATER PURIFIER,

See Soc D'Epuration SA

Belgian Patent 806,205.  Applied October 17, 1973.  Issued February
15, 1974.   Derwent Belgian Report, Vol. 5, No. 9, p 2, April, 1974.

An activated sludge waste water purifier is described which combines
blower aeration and stabilizing vessels in a single underground tank.
Domestic or industrial waste water is treated in order that it may be
discharged as an effluent without pollution hazard into a cylindrical
underground tank.  The tank is divided into an aerating section and a
stabilizing section and separated by a partition penetrated by a pipe
leading to the liquid surface.  The installation preferably has a manhole,
covered by a metal grid which provides access to the blower and both
sections of the tank.  Water is fed to one end of the tank in aeration
section, and pure water is recovered via perforated surface collection
pipes.  The unit may be installed close to residences, is not noisy,
and is not susceptible to contamination with vegetation.

*Patents, *Waste water treatment, *Water purification, Equipment, Activated
sludge, Sludge treatment, Domestic wastes, Industrial wastes, Effluents,
Aeration, Underground structures

Belgium
 108C

 ACTIVATED  SLUDGE  TREATMENT  IN TANK AERATOR,

 United  Kingdom Electricity  Council

 Belgium Patent 806,582.   Applied  October  26,  1973.   Issued  February
 15,  1974.   Derwent  Belgiun  Patents Report, Vol.  5,  No.  10,  p  2,
 April,  1974.

 An activated  sludge treatment tank aerator is described which used
 multiple jet  pumps  driven by  a common rotary  pump.   Either  an external
 electric motor driven impeller pump with  suction side connected  to the
 lower part of the circular  treatment  tank, or an immersed pump may be
 used.  From the delivery  side of  that pump either a curved  horizontal
 pipe or the body  of the main  immersed pump, feeds a number  of radially
 spaced  nozzles in the form  of Venturis, so that  turbulence  is created
 in the  tank contents. Each Venturi has a vertical air  inlet  pipe at
 its  throat leading  to above the maximum liquid level especially  above
 the  tank roof. Thorough  mixing of activated  sludge with the  sewage
 especially farmyard,  combines with oxygenation.

 *Sludge treatment,  *Patents,  Activated sludge, Pump, Nozzle,  Sewage,
 Oxygenation,  Agricultural wastes, Venturis

 *Aerator,  Belgium,  Great  Britain

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109C

WATER SAMPLING DEVICE,

Hagenuk Vormals Neufeldt

French Patent 2,186,132.  Applied April 11, 1973.  Issued February 8,
1974.  French Patents Abstracts, Vol. 5, No. 9, p 5, April, 1974.

A water sampling device for the supervision of water supplies is described.
The device takes samples of definite intervals of time and detects the
presence of impurities.  The apparatus has reservoirs and can be used on
buoys supported on a support at the bottom of a lake or fixed on stakes
or piles.  Compared with previous devices, all that is required is a
rotating arm for shearing glass capillary tubes at the inlet of the
reservoirs.  The samples can be preserved indefinitely in the containers
in a definite order.  Once removed from the magazine their contents
cannot be altered in any way and they can be tested by means of various
probes to determine the degree of pollution.

*Patents, *Sampling, *Water, Water supply, Buoys, Equipment, Water
pollution

France
HOC

PREPARATION OF ION EXCHANGE RESINS BASED ON AGAROSE,

Institute de Biochimie

German patent 1,916,107.  Applied March 28, 1969.  Issued February 28,
1974.  German Patents Abstracts, Vol. 5, No. 10, p 1, April, 1974.

Basic ion exchange resins are prepared from agarose or cross linked
glyceryl agaroses by treatment with equimolar amounts of epichlorhydrin
and triethanol-amine in a basic medium for 30 rain at 75-80 C.  The
products are useful for the isolation and purification of viruses,
proteins, nucleic acids, nucleotides, nucleoprotides, and enzymes.
*Ion exchange, *Resins, Proteins, Viruses, Enzymes

*Agarose, Germany, Nucleic acids, Nucleotides, Nucleoprotides
                                      130

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me

MULTIPLE RE-USE OF WATER,

Cyapman, W. H., and Eichelmann, J. F.

El Paso Southern Company,
El Paso, Texas

Canadian Patent 944,875.  Applied March 8, 1971.  Issued April 2, 1974.
Patents/Brevets, Vol. 102, No. 14, p 1224, April 2, 1974.

A process for the treatment of saline, brackish or other high mineral
content water to provide effluent waters for domestic and industrial
usage and for the treatment of the domestic and industrial waste water
for multiple reuse so as to solve both water supply and waste water
pollution problems is described.  A deminerallzation system is combined
with a system utilizing a relatively nonvolatile fluidizing liquid and
capable of operating on a waste waters of relatively high solids con-
tent.  The latter system receives high mineral content effluent from
the demineralizer as well as waste waters from the industrial and/or
domestic sources.  Potable water and low mineral content waters for
industrial use are produced and substantially all water is reused
except that lost by evaporation to the atmosphere or by use in irriga-
tion.  The system is particularly well adapted for small communities
having an adjacent industrial plant.

*Patents, *Waste water treatment, *Demineralization, *Water reuse,
Mineralogy, Saline water, Water purification, Brackish water, Water
pollution control, Waste water disposal, Effluents, Industrial water,
Potable water, Irrigation, Municipal water, Water supply, Water supply
resources, Evaporation, Canada
112C

SLURRY PUMP,

Katzer, M. F. and Routson, W. G.

Dow Chemical Company,
Midland Michigan

U.S. Patent 3,804,556.  Applied September 28, 1972.  Issued April
16, 1974.  Official Gazette of the U.S. Patent Office, Vol. 921, No. 3,
p 1105-1106, April 16, 1974.  1 fig.

A two cylinder pump adaptable to pump mud and silt or other slurrled
material is described.  While one cylinder is pumping, the other is
filling with mud.  Each cylinder has a piston in it which separates the
mud from the hydraulic fluid (oil or oil-water).  The hydraulic fluid
is pumped out of one cylinder and into the other.  The floating piston
is drawn away from oe end of the first cylinder, thereby drawing in
the mud under vacuum plus the differential barometric head.  At the
same time an equal volume of hydraulic fluid is pumped into the other
cylinder causing the piston to eject mud through a mud line.  At the
moment that one piston reaches on extreme of its stroke, the other one
reaches the other extreme of its stroke.  At this moment there is a
switching of the direction of flow of the fluid and the discharge of
the mud from one cylinder to the other.  This fluid reversal and shifting
will generally take place several times per minute.

*Pump, *Patents, *Mud, *Slurries, Silt, Pistons, Equipment

Cylinders
                                    131

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113C

FILAMENT WOUND REVERSE OSMOSIS TUBES,

Riggleman, B. M. and Young, W. L., Ill

United States of America, Washington, D.C.,
Department of Interior

U.S. Patent 3,804,259.  Applied January 23, 1973.  Issued April 16,
1974.  Official Gazette of the U.S. Patent Office, Vol. 921, No. 3,
p 1029, April 16, 1974.  1 fig.

An improved resin bonded filament wound support tube for membranes
used in reverse osmosis processes is described.  The support tube is
in the form of a curved composite structure and contains at least 20-30%
by weight of a thermosetting resin.  The tube has interior plies of
helical filament windings which result in a smooth interior surface for
the tube and high strength.

*Patents, *Tubes, *Reverse osmosis, Resins

Filament
114C

PROCESS AND APPARATUS FOR THE SEPARATION OF LIQUID MIXTURES,

Rishel, R. C.

U.S. Patent 3,804,252, Applied January 3, 1972.  Issued April 16, 1974.
Official Gazette of the U.S. Patent Office, Vol. 921, No. 3, p 1027,
April 16, 1974.  1 fig.

A process and apparatus for the separation of liquids of different
specific gravities is described.  A horizontal cylindrical tank is divided
into compartments, into one of which the mixture to be separated is
introduced, forms distinct layers, and flows over a weir into a
second compartment.  The heavier, lower layer enters at a point remote
from the inlet of the mixture into the first compartment, into a conduit
which directs the heavier liquid through a hydraulic trap into a third
compartment.  The heavier liquid is maintained at a level lower than
that of the mixture of the liquids in the initial settling compartment
and subsequently removed.

*Patents, *Separation techniques, *Specific gravity, *Liquids,
Equipment
                                            132

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115C

MOLECULE SEPAKATOR,

Ryhage, E. R.

LKB-Produkter AB, Bromma, Sweden

U.S. Patent 3,803,811.  Applied November 6, 1972.  A Issued April 16,
1974.  Official Gazette of the U.S. Patent Office, Vol. 921, No. 3,
p 914, April 16, 1974.  1 fig.

A molecular separator is described which acta according to the let principle.
It consists of at least one separation stage with an evacuation chamber,
connected to a pump provided with two coaxially arranged nozzles for the
gas phase subject to separation.  One of the nozzles is axially displace-
able.  There is a method of controlling the distance between the nozzles
from outside the separator while it is in operation.

*Patents, *Separation techniques, Pump, Nozzle, Equipment

*Molecular separator, Sweden
116C

ION EXCHANGER PURIFICATION PLANT,

Viscose Development Company

French Patent 2,186,289.  Applied June 1, 1973.  Issued February 15, 1974.
French Patents Abstracts, Vol. 5, No. 10, p 2, April 1974.

An ion exchanger purification plant is described in which the liquid to
be purified is mixed thoroughly by a variety of mechanical methods.  The
mixing occurs in treatment tanks in series and/or parallel with granulated
activated regenerated cellulose or cellulose derived material.  The ion
exchanger process extracts the unwanted impurities from the liquid
which is then separated again by a variety of methods from the ion ex-
changer material.  A part at least of those impurities are then stripped
out of the exchanger material by regeneration especially using the same
activator as that used initially and the regenerated ion exchanger wholly
or partially fed back into the plant for reuse after being flushed through.
The plant is especially useful for removal of animal and vegetable matter
from sewage.

*Patents, *Sewage treatment, *Ion exchange, Waste water purification,
Cellulose, Organic wastes, Mixing

France
                                        133

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117C

EFFLUENT SLUDGE TREATMENT,

Wibau Westdeutsche Ind

Netherlands Patent 7,304,173.  Applied March 26, 1973.  Issued February
14, 1974.  Derwent Netherlands Patents Report, Vol. 5, No.  9, p 2, April,
1974.

Effluent sludge is treated by passing it through a scrubber or other wet
washing process which increases the surface area by contacting it with
combustion gases at 600-800 C.  The gases are made by trioxide, hydrogen
chloride and small amounts of hydrogen fluoride, so that the effluent
is acidified and proteinaceous material is precipitated.  The tempera-
ture is preferably less than 50 C during the treatment.  The process
allows treatment of effluent sludges containing about 99 wt % of water
without using conventional precipitating agents.

*Patents, *Sludge treatment, Chemical precipitation, Effluents, Proteins,
Acidity

*Wet scrubbers, Netherlands, *Combustion gases, Sulfur dioxide, Sulfur
trioxide, Hydrogen chloride, Hydrogen fluoride
 118C

 FILTER HAVING A FLEXIBLE WALL FOR FILTERING LIQUIDS,

 Fournier, E.

 Australian Patent 44,975.  Applied June 18, 1970.  Issued February 7,
 1974.  Official Journal of Patents, Trade Marks, and Designs, Vol. 44,
 No. 4, p 385, February 7, 1974.

 A filter with a flexible wall for filtering liquids is described.  It
 consists of two discs, one of which is connected to a support and which
 has a fluid outlet aperature connected as a means of suction.  The second
 disc member is coaxial with an axially movable relative to the first disc
 member.  A flexible filter sleeve extends between the two discs and
 is connected to them.  There is a gravity activated ballast means which
 biases the discs away from each other and tenses the flexible filter sleeve
 to approximately cylindrical form when no suction is applied.  The discs
 flex inwardly when the apparatus is immersed in a fluid-containing solids.
 The solids are deposited on the filer filter when suction is applied.

 *Patents, *Filter, *Flexibility, *Liquids, Separation techniques, Equip-
 ment, Operation

 Suction, Australia
                                        134

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119C

BIOLOGICAL SEWAGE TREATMENT PLANT WITH CENTRIFUGAL AERATOR AT
WATER SURFACE,

German Patent 1759861.  Applied February 7, 1974.  Issued March 21, 1974.
German Patents Abstracts, Vol. 5, No. 7, p 1, March, 1974.

A partition between two straight troughs forming the oxidation tank
reaches solely up to the aerator/circulator, which rotates about a
vertical axis at one of the curved sections connecting the troughs.  The
partition is curved near the aerator toward the channel side in which
the sewage flows down toward the aerator.

*Sewage treatment, *Patents, *Biological treatment, *Treatment plants,
Channel

Oxidation tank, Biological sewage treatment plant, Sewage flow, Aerators,
Germany
120C

SEWAGE PURIFIER WITH DROP BODY AND SUMP TROUGH FOR
ACTIVATED SLUDGE,

Mead Corporation

German Patent 2028047.  Applied February 7, 1974.  Isgued March 21, 1974.
German Patents Abstracts, Vol. 5, No. 7, p 2, March, 1974.

A central mixing zone is bounded by walls reaching on all sides above the
liquid surface in the trough.  It extends out from into the trough,
from the settling zone between these walls and the inner side of the
trough's bounding wall.  The raw sewage inlet ducts, the drop body
drain, and the branch duct for the returned settled sludge and liquid
open into the mixing zone.  The settling zone is divided into separate
zones to interrupt the horizontal movement of liquid.

*Patents, *Sewage, *Water purification, *Activated sludge, Sumps

*Sewage purification, Central mixing zone, Settling zone, Sump trough,
Drop body, Germany
                                        135

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me

APPARATUS FOR CLEANING MUDDY WATER,

Stewart, F. I.

Huntsville, Alabama

United States Patent 3,799,349.  Applied July 3, 1972.  Issued March 26,
1974.  Official Gazette of the U.S. Patent Office, Vol. 920, No. 4, p 1203,
March, 1974.  1 fig.

A conduit, channel or other passageway forming means is disposed in the
bottom of a body of water with perforations in at least a portion of the
passageway forming means to enable mud, sediment, and silt to collect
in the conduit, channel or passageway.  This forms means together with a
structure moving through the conduit, channel or passageway to remove the
collected mud, sediment and silt for depositing it on the bank of the
body of water or in any other desired location thereby enabling contin-
uous removal.  The apparatus and the associated technique may be employed
in a stream, river, lake, pond or any body of water whether the water be
moving or still.

*Patents, *Cleaning, *Mud, Clarification, Conduits, Channels, Sedimen-
tation, Silt, Stream, River, Lake, Pond, Equipment
122C

BIOLOGICAL PURIFICATION OF SEWAGE,

French Patent 2190-739.  Applied July 4, 1973.  Issued March 8, 1974.  French
Patents Abstracts, Vol. 5, No. 13, p 6, March, 1974.

Purification is carried out using three reservoirs of which greater or
equal to 2 serve as feed reservoirs for the sewage water, and one as a
clarification reservoir.  The sewage water in the first feed reservoir
is circulated aerobically for part of the time and anaerobically for
the rest of the time.  It is then discharged to the clarifying reservoir
through the third reservoir where it has aerobic treatment.  The feed
reservoir may be connected to the clarifying reservoir directly during
its aerobic period, and to the third reservoir during its anaerobic period.
The functions of the two feed reservoirs are changed over periodically.
Precipitation takes place in the presence of inorganic compounds, in
particular of nitrates, which may be produced.

*Patents, *Purlfication, *Sewage, Biological treatment, Reservoirs, Sewage
water, Anaerobic conditions, Nitrates, Clarification

*Biological purification, Feed reservoirs, France
                                       136

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123C

METHOD AND APPARATUS FOR TREATING SEWAGE,

Brociner, H.

FMC Corporation,
San Jose, California

Canadian Patent 944,089.  Applied December 6, 1971.  Issued March 19, 1974
Patents/Brevets, Vol. 102, No. 12, p 1057, March, 1974.

Elimination of heavy solids, such as grit, from sewage streams prior to
introduction into treatment tanks is necessary as such solids interfere
with normal operations.  Substantially all of the heavy solids are re-
moved by a process and apparatus where raw sewage is introduced into a
tank with the bottom sloping downwardly from the far side to a trough
adjacent a first sldewall, with even distribution along the first side-
wall.  A predetermined small range of liquid level variation is main-
tained by flowing effluent sewage over a weir extending above the full
length of the top of the sidewall opposite the first sidewall.  Air is
introduced with even distribution through and along the first sidewall
to induce circulatory flow of liquid and light-weight solids upwardly
and then in the direction of the opposite sidewall.  This turns the cir-
culatory flow direction downwardly toward the tank floor by a baffle
spaced from the opposite sidewall and positioned transferse to the direc-
tion of liquid flow through the tank, to effect separation of light-
weight solids and flowing the sewage suspension under the baffle and
upwardly for removal by flow over the weir.

*Patents, *Solids, *Sewage, *Sewage treatment, Streams, Effluents,
Canada, Flow, Liquids, Weirs

Effluent sewage, Heavy solids
124C

ANAEROBIC EFFLUENT TREATMENT,

Belgian Patent 803-949.  Applied August 23, 1973.  Issued February 25,
1974.  Derwent Belgian Patents Reports, Vol. 5, No. 11, p 1, April 18,
1974.

Anaerobic microbiological purification of effluent is supplied tangentially
to a rotationally symmetrical purification tank containing a microbiolo-
gical sludge, by introducing the effluent below the surface of the water
through greater or equal to 1 device.  The outermost of these lies at
a distance from the edge of thy tank corresponding to 0.5-1.0 times the
height of the water, at a velocity such that the tangential flow velo-
city at any point in the tank is 0.5-2 m/sec and more especially 0.2-1 m/sec.
The water containing the micro-biological sludge is discharged after
resisdence in the tank through an opening in or near the center of the
tank.

*Patents, *Purification, *Sludge, Tanks, Flow, Microbiology, Effluent
treatment, Anaerobic conditions, Water purification

*Microbiological purification, Belgium
                                       137

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125C

SEWAGE DISPOSAL,

French Patent 2190-738.  Applied June 28, 1972  Issued March 8, 1974.
French Patents Abstracts Vol. 5, No. 13, p 6, March, 1974.

Liquid and solid waste materials of sewage are allowed to separate in a
settling tank.  The solids are removed and are heated in a non-oxidizing
atmosphere to the point of destructive distillation.  The gaseous pro-
ducts are treated by passing them through a flame curtain to remove any
noxious odors.  The final product is a finely powdered ash which
may be removed and easily disposed.

*Patents, *Sewage disposal, *Solid wastes, *Liquid wastes, Distillation,
Sewage

Settling tanks, France
 12 6C

 FLOATING MIXER  FOR WASTE WATER  TREATMENT TANK,

 Richards of Rockford,  Incorporated

 French  Patent 2187-399, Applied June  7, 1973.   Issued  February  22,  1974.
 French  Patent Abstracts, Vol. 5, No.  11, p 5, February,  1974.

 A  float filled  with  foamed polyurethane, carries  an  electric motor,  and
 is  tethered by  cables  on the surface  of a tank  for waste water  treatment.
 The motor  drives  a helical impeller,  shrounded  by vertical  cylindro-conic
 tube; flow may  be upward or downward.   It is deflected radially by  a
 baffle, formed  by the  bottom of the float, or by  a cone  in  line with
 bottom  of  shround.   The motor is protected from liquid by an intercepting
 plate at bottom of float through which  the shaft  passes; leakage between
 shaft and  interceptor  is returned to  the tank by  horizontal radial  channels
 through a  float.  The  liquid level maintained above  interceptors prevents
 air entrainment and  consequent  cavitation at the  impeller when  flow is
 downwards.  The mixer  automatically adjusts to  level of  the tank liquid
 and is  easily relocated or removed from cleaning.

 *Patents,  *Waste  water treatment, *Liquids, Mixing,  Tanks

 France, Floating  mixer, Tubes
                                       138

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127C

CONTINUOUS SEEDING AND ACTIVATING DEVICE,

French Patent 2190-742.  Applied July 3, 1972.  Issued March 8, 1974.
French Patents Abstracts, Vol. 5, No. 13, p 6, March, 1974.

A seeding and activating device for septic tanks consists of a cylindrical
recipient with a movable, inclined cover with holes acting as a strainer.
The device is placed below the pipe which feeds the effluents into the tank;
it is fixed to this pipe or to the wall of the tank and dips into the liquid
layer.  The recipient is fitted with an overflow pipe.  The culture medium
in the device can be fed with fresh organisms and natural nutritive substances
which are added as required.  At the same time a certain amount of mixing and
agitation is effected in the culture medium itself.

*Patents, *Septic tanks, Activation, Purification, Effluents

Culture media, Activating devices, Biological purification, France
128C

WASTE WATER TREATMENT CHEMICAL REACTOR,

French Patent 2187-398.  Applied June 6, 1972,  Issued February 22, 1974.  French
Patent Abstracts, Vol. 5, No. 11, p 5, February, 1974.

The reactor, separated by a perforated partition from an overhead "plug flow"
reaction chamber, has a bottom inlet below a convergent/divergent blending
nozzle.  The throat is fed a reagent, such as a coagulant or a flocculant.
The reactor has a low pressure drop (.2-.5 bar), low power requirement, re-
duced dead space, and is not subject to by-passing reaction.  It may be
controlled in response to sensors (pH detectors) in upper and lower chambers.
The reactor is especially useful for treatment of waste water, such as with
lime or H2S04 to control pH.

*Patents, *Waste water treatment, Chemical reactions, Pressure, Power, Lime

*Chemical reactors, pH, H2S04, France
                                       139

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129C

ACTIVATED SLUDGE PURIFICATION STATION FOR WASTE WATER AND
SEWAGE TREATMENT,

Nardonnet Soc

French Patent 2187-705.  Applied June 15, 1972.  Issued February 22, 1974.
French Patents Abstracts, Vol. 5, No. 11, p 6, February, 1974.

The station consists of a tank in the form of a body or revolution, with a
horizontal axis and is divided internally by partitions which form the
boundaries of a primary settlement chamber.  The partitions also form, with
the end walls, two volumes, one of which acts as a secondary settlement chamber.
An injection chimney for the activated sludge has its lower, bell-mouthed end
provided with an air nozzle to keep the liquid rising in the chimney.  The
upper part of the secondary settlement chamber includes an undisturbed fil-
tration area, with an outlet for the purified water.  The incoming sewage is
seeded immediately in the injection chimney and is mixed with the stream of
activated sludge; any abnormal flows can be dealt with satisfactorily.

*Patents, *Activated sludge, *Waste water treatment, *Sewage treatment,
Stations, Water purification

France
130C

ION EXCHANGE WATER TREATMENT,

Abwassertechnlk Kunststo

French Patent 2187-703.  Applied June 12, 1973.  Issued February 2, 1974.
French Patents Abstracts, Vol. 5, No. 11, February, 1974.

An ion exchange plant for softening and demineralizing water is described.
Part of the resin bed is periodically set aside for regeneration and  then re-
turned to the bed.  Water for treatment is directed down through a first sec-
tion of the resins bed, then turned and redirected up through a second section,
at the top of which resin can be separated off for regeneration.  Subsequently
it is relntroduced at the top, upstream end of the first section.  Even when
fully automated, this plant does not require complex controls.

*Patents, *Ion exchange, *Demineralization, Automation, Beds, Water treatment,
Streams

France, Resins beds, Ion exchange plant
                                         140

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131C

EFFLUENT WATER TREATMENT,

Heidrich A.

French Patent 2184-917.  Applied May 16, 1973.  Issued February 1, 1974.
French Patents Abstracts, Vol. 5, No. 11, February, 1974.

Effluent water is treated with an agent consisting of (a) chlorisocyanuric
acid or salts of this, (b) Na aluminate, (c) NaOH and (d) Na tripolyphosphate
or Na hexametaphosphate and Mg sulphate or Mg chloride or Mg oxide.  The
agents, when added to contaminated water containing fats, or oil emulsions,
or humic acid colloids, give excellent proportion of the impurities and
purification of the water.  The process is especially effective with oil emul-
sions if the treated water is also subjected to an electric field between two
electrodes to give a rapid proportion of the oil as a sludge.

*Patents, *Effluents, Salts, Water quality, Waste water treatment, Sludge

Chlorisocyanuric acid, Na aluminate, NaOH, Na tripolyphosphate, Oil
emulsions, Huraic acid colloids, France
132C

SEWAGE LIFT STATION GAS TRAP,

Wilson, R. E.

Bossier City, Louisiana

United States Patent 3,807,901.  Applied November 18, 1968.  Issued April
30, 1974.  Official Gazette of the U.S. Patent Office, Vol. 921, No. 5,
p 1997, April 30, 1974.  1 fig.

A sewage lift station includes a variable volume breathing assembly which nor-
mally isolates the interior of the sewage tank from the surrounding atmosphere
and eliminates the escape of offensive gas.  The assembly traps the sewer
gas in the tank as the effluent level rises and falls between predetermined
limits.  This effects relatively innocuous venting of a portion of the sewer
gas from the tank to the atmosphere if excessive amounts accumulate over a
period of time or if an abnormal rise in the effluent level occurs resulting
in a rise in the pressure of the trapped gas exceeding ambient atmospheric
pressure.

*Patents, *Sewage, Sewers, Effluents, Pressure, Equipment

Sewer gas, Sewage lift station
                                      141

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133C

MULTI-STAGE ELECTROSTATIC PRECIPITATOR,

Vincent, J. H.

Canadian Patent 943,872.  Applied April 30, 1970.  Issued March 19, 1974.
Patents/Brevets, Vol. 102, No. 12, p 1010-1011, March 19, 1974.

The first section of this invention may include one or more pairs of positively
chargev vertical plates.  Between each pair are positioned a plurality of
negatively charged vertical wires.  The second section, which is contiguous
to the end of the first section, includes a plurality of grids parallel to
each other and perpendicular to the plates of the first section.  Thus a cover
electrical precipitator is composed of these two tandem electrostatic sections,
arranged to eliminate dust or dirt or any form of particulate matter, which may
be conveyed with air or gas or any fluid medium.

*Patents, *Electrical currents, *Cleaning, Fluids

*Precipitator, *Multi-stage electrostatic precipitator, Dust removal, Dirt
removal
134C

WATER DESALTING,

Johnson, J. S., Kraus, K. A., and Martsinkovskii, A. E.

Soviet Patent 381195.  Applied April 15, 1973.  Issued March, 1974.  Soviet In-
ventions Illustrated, Vol. 5, No. 8, p 1, March, 1974.

High pressure filtration through a porous membrane accomplishes water desalting
after the addition of surfactants.  These include neutral organic polymers,
polyelectrolytes, organic and inorganic ion-exchangers, and multi-valent metal
salts, which may be added as solutions, suspensions, or emulsions.  The method
proposed may be used for sea, industrial, and radioactive water.  Water is
passed at pressure 1000 psi through a porous membrane such as a metal filter,
charcoal, or cellophane.  The additives form a film on the membrane which re-
pulses soluble materials.

*Filtration, *Patents, *Water desalting, Membranes, Porous media, Ion exchange,
Metals, Salts, Organic matter, Solutions, Solubility, Suspensions, Pressure

Inorganic materials, Multi-valent metal salts, U.S.S.R.
                                          142

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135C

SEWAGE TREATMENT PLANT,

Ingenieursbureau Kuipers

Netherlands Patent 7212-429.  Applied September 13, 1972.  Issued March 15,
1974.  Derwent Netherlands Patents Reports, Vol. 5, No. 13, p 1, May 13,
1974.

Raw sewage is passed through initial sand filter beds and is then fed from a
trough into a tank from which an Archimedian screw rises upwards within a
semicircular floored gutter.  The purpose is to segregate suspended particles
of specific gravities.  The shaft of the work is in bearings at both ends and
is driven at an adjustable speed.  A washing water spray is fitted above the
upper part and there is a compressed air feed into the lower part of the gutter
for breaking up caked sand deposits.  The lighter organic material in suspension
in the filtered raw sewage is carried over with the effluent for subsequent
treatment.

*Patents, *Sewage treatment, *Suspended solids, *0rganic matter, Washing, Ef-
fluents, Tanks, Waste treatment, Worms, Specific gravity

Archimedian screw, Netherlands
136C

CONTINUOUS EFFLUENT TREATMENT PLANT,

Burdon Engineers Limited

Belgian Patent 806-044.  Applied October 12, 1973.  Issued February 1, 1974.
Derwent Belgian Patents Report, Vol. 5, No. 8, p 2, March, 1974.

A container with a floor, external walls and > or = one internal partition
with two opposed faces having one vertically spaced means of communication in
each face comprises the apparatus for the continuous treatment of liquids.  These
are designed specifically for aqueous effluent from electrical treatment, pick-
ling, or photographic processes.  The container is connected by an internal pas-
sage in the partition which extends horizontally over the whole width to ensure
laminar flow of the liquid.

*Patents, *Liquids, Equipment, Effluents, Laminar flow, Treatment facilities,
Liquid wastes

Belgium
                                   143

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137C

INDUSTRIAL WASTE WATER TREATMENT,

French Patent 2185-594.  Applied April 23, 1973.   Issued April 1, 1974.   French
Patent Abstracts, Vol. 5, No. 9, p 3,  April,  1974.

Principal parallel plate electrodes form two side walls of a cell between which
are a number of rows of parallel bar auxiliary electrodes.  These increase
the effective area of the electrochemical active surface so that the voltage
applied can be reduced, giving higher efficiency and reduction of gases.  The
bars are supported in an open box structure.   They are especially alternated car-
bon for the extraction of the cyanide, a metal alloy which dissolves electrical-
ly the hydroxide of its own metals for the extraction of heavy metal ions.

*Patents, *Waste water treatment, industrial wastes, Equipment, Heavy metals,
Electrodes, Gases, Electrochemistry, Ions

*Cyanide, France
138C

TREATMENT OF WASTE WATER,

Zuckerman, M., and Molof, A.

Phillips, Ormonde and Fitzpatrick, Melbourne, Victoria,
Australia

Australian Patent 444,933.  Applied May 11, 1970.  Issued February 7, 1974.
Official Journal of Patents, Trade Marks and Designs, Vol. 44, No. 4, p 375,
February 7, 1974.

A process for the treatment of non-biologically treated waste water containing
high molecular weight soluble organic materials is comprised of two steps.
These are:  hydrolyzing the high molecular weight soluble organic material in
the waste water to yield a hydrolyzed product containing low molecular weight
soluble organic materials; and removing at least part of the soluble low mole-
cular weight organic material from the waste water.

*Patents, *Waste water treatment, Organic matter, Hydrolysis, Solubility,
Molecular weight

Australia
                                         144

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139C

TREATMENT OF AQUEOUS WASTE STREAMS CONTAINING A WATER-
SOLUBLE SULFIDE COMPOUND,

Universal Oil Products Company

Australian Patent 444,809.  Applied October 27, 1970.  Issued February 7, 1974.
Official Journal of Patents, Trade Marks and Designs, Vol. 44, No. 4, p 349,
February, 1974.

A method for the treatment of aqueous waste streams containing a water-soluble
sulfide compound was comprised of three steps.  These are:  to contain the aqueous
waste stream and oxygen in an amount less than 0.5 moles of 02 per mole of the
sulfide compound with a first solid oxidizing catalyst at oxidizing conditions,
including a relatively low pressure and temperature, sufficient to form a first
effluent stream containing a water-soluble polysulfide, to contact the first
effluent stream and oxygen with a second solid oxidizing catalyst at oxidizing
condition, including a temperature greater than the melting point of sulfur and
pressure to maintain a portion of the first effluent stream in liquid phase;
and to separate the liquid sulfur from the second effluent stream to produce a
treated aqueous stream which is substantially free of the sulfide compound.

*Patents, *Aqueous solutions, *Sulfides, Oxidation, Catalysts, Effluents, Li-
quids, Streams

*Waste streams, *Water-soluble compounds, Polysulfides, Australia
140C

DEHYDRATION OF SOLIDS BY CHEMICAL FRACTIONATION,

Boeing Company

Netherlands Patent 7312-586.  Applied March 13, 1974.  Issued May 13, 1974.
Derwent Netherlands Patent Report, Vol. 5, No. 13, p 2, May, 1974.

A surface layer of impurities are separated from a liquid, such as in separating
an oil film floating on water, in which a flow of liquid is directed downwards
onto the surface layer at sufficient speed to entrain the impurities.  These
are conducted to a non-contaminated region beneath the surface, where at the
least the impurities are collected in a submerged opening connected to a suction
source.  This may be used also for removing floating scum from water purifica-
tion tanks or other industrial plants.

*Patents, *Water purification, *Separatlon techniques, Liquids, Oil, Indus-
trial plants, Equipment

Water purification tanks, Netherlands
                                       145

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141C

WATER PURIFICATION AND STERILIZATION,

Solvay and CIE

Belgian Patent 804-425.  Applied September 4, 1973.  Issued March 4, 1974.  Der-
went Belgian Patents Report, Vol. 5, No. 13, p 1, March, 1974.

A significant improvement occurs in terms of pH control compared with conven-
tional methods where active chlorine source is added before the flocculants.  A
quantity of active chlorine used is sufficient to overcome the reaction threshold
and reacts with ferrous salts to form other ferrous compounds.  The flocculant
salt or salts, the optional oxidation promoter and the source of active chlorine
may be added simultaneously, especially as a premixture.  The ferrous salt
used is ferrous chloride, the oxidation promoter is HC1 and the source of active
chlorine is sodium hypochlorite.  The pH value of the finished product is 7.5-8
when the last is added after the other additives.  If premixed simultaneously,
the pH value is 6-7, closer to 6.

*Water purification, *Disinfection, *Chlorine, Salts, Flocculation, Sterilization,
Oxidation

*pH, Ferrous chloride, Oxidation promoter, Belgium
142C

EFFLUENT WATER TREATMENT BY CONTACTING WITH PLANT TISSUE,

Hitachi Limited

Netherlands Patent 7312-237.  Applied September 4, 1973.  Issued March 3, 1974.
Derwent Netherlands Patents Report, Vol. 5, No. 12, p 4, March, 1974.

Water is contacted such as in a column or a stirred vat with plant tissue
(stalks and leaves of barley, rice, wheat, sugar cane, soya beans, saw dust,
shavings, twigs of cut woods, pampas grass, nettles, wisteria).  The process ab-
sorbs impurities and gives excellent removal of heavy metal compounds, basic
and direct dyestuffs and surfactants such as alkylbenzenesulphonates.

*Patents, *Effluents, *Water treatment, *Plant tissues, Heavy metals, Equipment,
Waste removal, Water purification

Alkylbenzenesulphonates, Netherlands
                                          146

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143C

WATER PURIFICATION,

Lynch L D

French Patent 2193-783.  Applied July 20, 1973.  Issued March 29, 1974.
French Patent Abstracts, Vol. 5, No. 17, p 3, May 31, 1974.

Chelate compounds are formed when contaminated water is purified and clarified
by the addition of an element.  These chelates with ligands in the liquid
adsorb the contaminations in the liquid.  For example, the ions are iron or
carbon cations, formed by applying potential to an iron or carbon electrode
immersed in the water.

*Patents, Contamination, *Water purification, *Clarification, *Chelation,
Liquids, Ions, Water treatment, Adsorption

Ligands
 144C

 OIL RECOVERY FROM OIL-CONTAMINATED WATER,

 Rafael, J.

 Netherlands Patent 7313-109.  Applied September 24, 1973.  Issued March 27,
 1974.  Derwent Netherlands Patents Report, Vol. 5, No. 15, May, 1974.

 Purification of water, such as from oil slicks at sea, is accomplished by an
 apparatus with a floating body and inlet openings as well as a collecting
 chamber for the contaminated water.  This chamber has a cover which comes
 partly or wholly into contact with the oil-contaminated water surface and is
 provided with an oil uptake device.  The cover is arched and the oil uptake
 device may be a discharge channel or a suction unit, which is installed at
 the crest of the arch.

 *Patents, *Water purification, *0il spills, *0ceans, *Water pollution, Equip-
 ment, Contamination

 Oil slicks
                                        147

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14 5C

OIL RECOVERY FROM SPILLS ON WATER,

Union Oil Company

Netherlands Patent 7212-980.  Applied September 26, 1972.  Issued March 28,
1974.  Derwent Netherlands Patents Report, Vol. 5, No. 15, May, 1974.

A box-like structure, supported on detachable buoyant pontoons along each side,
contain inlet equipment:  an oil water separation zone; an oil collection sump;
and water outlet facilities.  This floating oil skimmer is easily dismantled and
transported for recovering oil from water surfaces.  An inlet at the open front
end of the skimmer is arranged so that the skimmed water-oil mixture runs
back down a slope from an adjustable lip device.  The separation zone includes
an adjustable weir at the bottom of the slope over which the separated oil
can flow.

*Patents, *0il, *0il spills, Floating, Equipment, Weir, Flow, Water pollution

*011 recovery, Floating oil skimmer
 146C

 LIQUID WASTES  TREATMENT  METHOD,

 Cessna, J.  0.  H.

 Del-Pak Media  Corporation,
 Oakland, California

 Canadian Patent 945,695.  Applied  September  16,  1971.   Issued April  16,  1974.
 Patents/Brevets,  Vol.  102,  No.  6,  p  1404-1405, April,  1974.

 A two stage high-rate, activated biological  filter  system is used, involving
 a primary clarifier for  treatment  of liquid  wastes.  Activated  floe  and  biolo-
 gical slime are sloughed  off  from  the biological filter and returned to  a
 primary clarifier.   The  activated  floe  is built  up  in  the biological filter by
 the recycling  of  substantial  quantities of aerobic  sludge from  a  secondary
 clarifier to the  biological filter and  by the metering of solids  wasted  from
 the treatment  system.  This maintains the mixed  liquor,  suspended solids level
 in the filter  effluent in excess of  about 1500 mg/liter.   Underdrain flow from
 the secondary  clarifier  is  a  substantial percentage of plant influent flow.
 This is recycled  without  extended  mixing with plant influent or aeration prior
 to distribution over the  biological  filter.

 *Patents, *Liquid wastes, Clarification, *Waste treatment, *Aeration, *Recy-
 cling, Flow, Filters,  Sludge, Activated sludge,  Solids,  Biological treatment,
 Suspended solids, Effluents,  Secondary  treatment, Primary treatment, Mixing,
 Canada
                                         148

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147C

CARBON-CONTAINING WASTE WET-OXIDATION,

Barber-Colman Company

Netherlands Patent 7312-989.  Applied September 20, 1973.  Issued April 2, 1974.
Derwent Netherlands Patents Report, Vol. 5, No. 16, p 1, May, 1974.

A horizontal reactor is subdivided into several cylindrical, interconnected
compartments for the wet-oxidation of carbon-containing waste material.  This
process involves contacting an aqueous dispersion of the waste material within
an oxidizing gas.  The dispersion is introduced continuously into one end of the
reactor and moved through, from compartment to compartment.  For one to thirty
minutes, dispersion is kept at acid pH (2-7) and 204 C to 246 C.  Rapid oxida-
tion of the carbon-containing waste material is effected by strong stirring,
movement, and distribution of the oxidizing gas and thus forms an ecologically
acceptable effluent.  This process is suitable for municipal and small-scale
sewage processing.

*Patents, *Municipal wastes, *Carbon, *0xidation, Gas, Ecological effects,
Effluents, Sewage, Dispersion

*Carbon-containing wastes, *Wet-oxidation, Netherlands
14 8C

AERATION PLANT FOR LIQUIDS,

Purator Klaranlagen

Belgian Patent 807-372.  Applied November 16, 1973.  issued March 15, 1974.
Derwent Belgian Patents Report, Vol. 5, No. 14, p 3, March, 1974.

Waste water and sewage are treated by aeration with compressors operating
below the liquid surface.  The plant has a main air pipe and branch pipes which
lead to this aerator, each provided with perforations through which air can
escape.  At regular intervals the air feed pipes are connected to the main feed
and supplied with compressed air by a motor driven machine.  This compressor
assembly is mounted on slides so that it can be lifted clear of liquid for
maintenance.  Since these compressors operate below the liquid surface, no
cooling systems are needed and noise is reduced.

*Patents, *Aeration, *Liquids, *Waste water treatment, *Sewage treatment,
Maintenance, Treatment facilities, Air

*Compressors, Treatment plants, Belgium
                                        149

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149C

WASTE WATER TREATMENT PLANT,

Laurent S 0 R

French Patent 2191-945.  Applied July 17, 1972.  Issued March 15, 1974.  French
Patents Abstracts, Vol. 5, No. 14, p 2, March, 1974.

Non-biodegradable impurities in effluents are separated by flotation methods,
using microbubbles of hydrogen produced by the reaction of water with activa-
tion aluminum.  Impurities are skimmed from the surface while cleared water
is extracted by syphoning.  The plant design is a single flotation
tank with a sump for heavy precipitated sludge.  The raw sewage inlet is at
about half the height of one side wall with plates of activated aluminum amal-
gam being placed below the level of the Inlet.  Overflow runoff for any partly
treated effluent can be further treated by aerobic methods.

*Patents, *Waste water treatment, *Treatment facilities, *Flotation, *Alumi-
num, Sewage, Precipitation, Sludge, Syphoning, Aerobic treatment, Effluents,
Design, Separation, Equipment

^Treatment plants, Aluminum amalgam, France, microbubbles
 150C

 FATTY OIL-WATER  SEPARATION PROCESS,

 Keller, H.  F.

 GBK Enterprises,  Incorporated,
 Placentia,  California

 United-States Patent 3,803,031.  Applied July 12, 1972.  Issued April 9, 1974.
 Official Gazette of the U.S. Patent Office, Vol. 921, No. 2, p 702, April,
 1974.

 Aqueous systems  containing fatty constituents and particulate solids and
 having a pH from about 1 to about 4.8 are filtered through a finely divided,
 acid and alkali  resistant filter media having a particle mesh size range
 from about  12 to about 60 at a rate from about 1 to about 50 gallons per minute
 per square  foot  of filter media surface area.  Fatty constituents and parti-
 culate solids are retained by the filter media and the effluent is clarified
 water.  The filter media is periodically regenerated by:  agitating the
 media in the presence of a saponifying alkaline solution to extract fatty
 constituents; withdrawing the alkaline solution from the filter media; passing
 fresh water through the filter media in the same direction of flow as that
 of  the aqueous system to remove residual water soluble materials; and
 backwashing the  filter media with fresh water to remove insoluble and non-
 dispersible particulate solids.

 *Patents, *Separation techniques, *Filters, Flow, Acidity, Alkalinity,
 Clarification, Effluents, Fats

 Oil-water separation, Fatty constituents, pH, Filter media
                                        150

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151C

BIOLOGICAL WASTE TREATMENT PROCESS,

Smith, L. G., and Hood, J. W.

Montclair, New Jersey

United States Patent 3,806,448.  Applied November, 1971.  Issued April 23, 1974.
Official Gazette of the U. S. Patent Office, Vol. 921, No. 4, p 1603, April 23,
1974.  1 fig.

A method of treating waste material containing biodegradable matter and non-
biodegradable matter is described.  This involves an aerobic treatment step
and a final clarifier in which a final sludge is separated.  The final sludge
is disintegrated and separated into a first fraction containing the biodegradable
material and a second fraction containing inert material, which is discarded.
The first fraction is returned to the aerobic treatment unit with or without
microbial biolysis.

*Patents, *Waste treatment, *Biodegradation, *Aerobic treatment, *Clarification,
*Sludge treatment, Microbiology, Separation

Microbial biolysis
152C

RESTRAINING TUBE FOR SEWER ROD,

Caperton, C. B.

Springlake, New Jersey

United States Patent 3,805,462.  Applied February 22, 1973.  Issued April 23,
1974.  Official Gazette of the U. S. Patent Office, Vol. 921, No. 4, p 1354,
April 23, 1974.  1 fig.

A rigid restraining tube is provided for use in manholes for restraining the
sewer rod.  This is used in clearing sewer obstructions, against the reaction
forces which are set up when the forwardly driven sewer rod encounters the
obstruction.  The restraining tube is a series of short sections connected
together by rigid links.  Each section is split in half axially, forming a
series of section halves, adapted to be wound up on opposing reels for storage
and transportation.  The sections of tube need not abut against each other
since they are connected rigidly by the links.

*Patents, *Sewers, Equipment, Manholes, Storage, Transportation

*Sewer rods, *Sewer restraining tubes
                                       151

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153C

PROCESS FOR FLOCCULATING SOLID PARTICLES FROM AN AQUEOUS
SUSPENSION THEREOF,

Webb, F. J., and Tate, D. P.

The Firestone Tire and Rubber Company,
Akron, Ohio

United States Patent 3,801,500.  Applied September 13, 1971.  Issued April 2,
1974.  Official Gazette of the United States Patent Office, Vol. 921, No. 1,
p 305, April 2, 1974.

The process for preparing water-soluble polymers from polydienes having a
substantial amount of repeating units with pendent vinyl groups, such as high-
vinyl polybutadiene is explained.  The process involves the anti-Markownikoff ad-
dition of hydrogen bromide to the pendent vinyl groups to give the primary
bromide derivative groups, which upon the addition of a tertiary amine, give
quanternary ammonium groups.  These impart water solubility to the polymers.
The products are particularly useful for the flocculation of solids from
suspensions such as elutriated sewage.

*Patents, *Solubility, *Polymers, Ammonium, Flocculation, Solids, Suspensions,
Sewage

*Water-soluble polymers, Vinyl, Anti-Markownikoff process, Hydrogen bromide
15 4C

METHOD AND APPARATUS FOR TREATING WASTE PRODUCTS,

Stephanoff, N. N.

Fluid Energy Processing and Equipment Company,
Hatfield, Pennsylvania

United States Patent 3,802,089.  Applied April 2, 1973.  Issued April 9, 1974.
Official Gazette of the United States Patent Office, Vol. 921, No. 2, p 469,
April, 1974.  1 fig.

The treatment of sewage, industrial waste, and other vegetable and animal wastes
by drying and dehydrating this waste material in a fluid energy drying appara-
tus is accomplished.  An illustration indicates the way that the waste matter
is subjected to the heat energy of high-temperature gases while being whirled
through a curved path, where dried particles are centrifugally separated
from the less-dried particles.

*Patents, *Industrial wastes, *Sewage, *Animal wastes, *Dehydration, Equipment,
Heat, Energy, Temperature, Gases, Separation, Centrifugation
                                    152

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155C

SEWAGE AND INDUSTRIAL WASTE COAGULATION,

Nalco Chemical Company,
Sydney, New South Wales

Australian Patent 444,072.  Applied September 14, 1972.  Issued January 1974.
Official Journal of Patents, Trade Marks and Designs, Vol. 44, No. 1, p 34,
January, 1974.

A method of thickening or dewatering solids from municipal sewage or industrial
wastes has been patented.  It includes the addition of an aqueous solution
of a water-soluble vinyl addition polymer, by the inversion of a polymeric
latex, to sewage under floe forming conditions.  The solids are allowed to
settle from sewage to provide a clear aqueous supernate, where polymeric
latex is produced by the steps of forming a water-in-oil emulsion and heating
emulsion under free radical forming conditions to polymerize the water-soluble
ethylenic unsaturated monomer forming a polymeric latex.

*Dewatering, *Sewage, *Industrial wastes, *Patents, Polymers, Floe, Solids,
Municipal wastes

Water-in-oil emulsions, Latex
 156C

 SYSTEM FOR MONITORING AND CONTROLLING SUBSTANCES IN  FLUID BODIES,

 Emmons, D. R., and Beverly, W. C.

 Orlando, Florida

 United States Patent 3,809,922.  Applied November 10, 1972.  Issued May 7, 1974.
 Official Gazette of the United States Patent Office, Vol. 922  No  1  p 338
 May, 1974.  1 fig.

 The addition of substances, such as chlorine, to fluid bodies is controlled and
 the concentration of such substances is monitored by a special system.  A tem-
 perature compensated probe measures the concentration, and electronic means
 responsive to outputs of the probe add the substance, as needed, to the desired
 level.

 *Patents, *Chlorine, *Monitoring, *Automatic control, Temperature,
Concentration, Electronic equipment, Liquids, Measurement
                                     153

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157C

SELECTIVE ADSORPTION OF PHENOLS FROM SOLUTION IN WATER,

McCoy, F. C., and Schlicht, R. C.

Texaco Incorporated,
New York, New York

United States Patent 3,812,031.  Applied September 20, 1972.  Issued May 21, 1974.
Official Gazette of the United States Patent Office, Vol. 922, No. 3, p 896,
May, 1974.

A method for the extraction of phenolic materials from aqueous solutions was
patented.  This utilizes polyurethane foam for selective adsorption of these
phenols.

*Patents, *Solutions, *Aqueous solutions, *Phenols, *Adsorption, Extraction

*Polyurethane foam
158C

PROCESS FOR TREATING DOMESTIC AND INDUSTRIAL LIQUID WASTES,

Chappeil, G. M.

United States Patent 3,812,032.  Applied August 6, 1971.  Issued May 21, 1974.
Official Gazette of the United States Patent Office, Vol. 922, No. 3, p 896, May,
1974.  1 fig.

A process for treating domestic, municipal, or industrial liquid waste to reduce
BOD of the waste consists of adding a sufficient amount of an acid formula and
a sufficient amount of an alkaline formula to the waste.  This causes evolution
of heat and flocculation of solids, and separates the resulting solids from the
liquid.  The novel acid formula and alkaline formula are disclosed.  Liquid
wastes treated by the process of this invention can be safely discharged into
rivers, lakes and streams.  In addition the process is extremely efficient since
flocculation is rapid, and in many instances starts immediately upon the addition
of eithe/ formula to the liquid waste.

*Domestic wastes, *Patents, *Munlcipal wastes, *Industrial wastes, *Biochemical
oxygen demand, Acidity, Alkalinity, Heat, Flocculation, Solids, Liquid wastes,
Discharge, Rivers, Lakes, Waste treatment

Treatment methods
                                     154

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159C

APPARATUS FOR COLLECTING SURFACE PARTICLES ON BODY OF WATER,

Carter, L.

United States Patent 3,811,325.  Applied October 30, 1972.  Issued May 21, 1974.
Official Gazette of the United States Patent Office, Vol. 922, No. 3, p 722,
May, 1974.  1 fig.

An apparatus for sampling and collecting floating particulate matter on the
surface of a body of water has parallel spaced longitudinal floats supporting
a rigid tubular frame.  Secured to the frame are two parallel, horizontal
hydrofoil bodies spaced apart from each other to form an intake opening.  A
funnel-shaped net with its wide end secured to the intake opening and its
narrow end terminating in a collecting screen, collects surface particulate
matter.  This matter is caused to flow into the intake opening as the appara-
tus is towed on a body of water.  The lower hydrofoil body maintains the
intake opening at a predetermined depth below the water surface, while the
upper hydrofoil body enables the apparatus to ride over swells.

*Sampling, *Patents, Floating, Particulates, Hydrofoils, Screens

*Surface particles, Particle collecting, Hydrofoil bodies, Particulate matter
160C

TEMPERATURE-CONTROLLED FLUID MANIFOLD FOR A FLUID SYSTEM OF AN AUTOMATED SAMPLE ANALYZER,

Diebler, H. G., Gyori, S. A., and McCandless, W. J. C.

Technicon Instruments Corporation,
Tarrytown, New York

United States Patent 3,811,842.  Applied June 7, 1972.  Issued May 21, 1974.
Official Gazette of the United States Patent Office, Vol. 922, No. 3, p 856-857,
May, 1974.  1 fig.

A temperature-controlled fluid manifold for a fluid system of an automated
sample analyzer was designed for analyzing a series of liquid
samples flowing seriatum.  The basic elements of the temperature-controlled
manifold may be permanently combined with a wide variety of other components
to meet the requirements of many different chemistries, each suited for analy-
sis of a different constituent of a sample, such as blood.  In each individual
manifold, the sample may be treated by combination and mixing with any appro-
priate reagent or reagents under temperature-controlled conditions for subsequent
analysis such as a colorimeter.  The basic manifold elements comprise a therm-
ally conductive plate or block heated by conduction from a temperature-
controlled source of heat.  The plate has an outer, exposed surface of sub-
stantial area and an appropriate number of appropriately configured fluid
passageway portions, such as helical mixing or helical time-delay paths.

*Patent, *Analyzers, *Sampling, *Temperature control, Fluid movement,
Automation, Analytical techniques, Chemistry, Colorimetry, Conduction

*Fluid manifold, Fluid svstems, Blood, Reagents
                                       155

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161C

PROCKSS FOR TREATING OIL SLICKS USING CHEMICAL AGENTS,

Ferm, R. L.

Chevron Research Company,
San Francisco, California

United States Patent 3,810,835.  Applied February 25,  1971.   Issued May 14,  1974.
Official Gazette of the United States Patent Office,  Vol. 922,  No. 2,  p 503,
May, 1974.

A process has been patented for the treating of an oil slick to contain it
and prevent its uncontrolled spreading.  A chemical agent which repulses the
oil spill is applied to open water areas in the vicinity of  the spill.  With
care, the oil slick can be gathered into a limited area which facilitates
cleanup.  The chemical agent is selected from the group consisting of N,N-
dialkyl amides; n-alkyl and n-alkylene monoethers of ethylene glycol and poly-
ethylene glycol; polyethylene glycol monoesters of n-alkyl acids; and n-alkyl
and n-alkylene monoesters of propylene glycol.

*Patents, *0il, *Chemical treatment, Oil spills, Cleaning,
Water purification, Pollution abatement

Amides, Monoethers, Monoesters
162C

TREATMENT OF WATER OR AQUEOUS SYSTEMS,

Jones, T. I., Richardson, N., and Harris, A.

Ciba-Geigy Corporation,
Ardsley, New York

United States Patent 3,810,834.  Applied November 26, 1971.  Issued May 14, 1974.
Official Gazette of the United States Patent Office, Vol. 922, No, 2, p 593,
May, 1974.

Hydrolyzed polymaleic anhydride is used for the treatment of water or aqueous
systems containing dissolved salts of metals.  This serves two functions:  to
cut down the rate at which insoluble salts are formed; and to modify their
nature.

*Patents, *Water treatment, Metals, Salts

*Insoluble salts, *Dissolved metal salts, *Hydrolysed polymaleic anhydride,
Aqueous systems
                                         156

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163C

MOBILE PURIFYING PLANT FOR WASTE WATER,

Lundqvlst, B. 0.

Gustavsbergs Fabriker,
Gustavsberg, Sweden

United States Patent 3,810,543.  Applied April 20, 1972.  Issued May 14, 1974.
Official Gazette of the United States Patent Office, Vol. 922, No. 2, p 522,
May, 1974.  1 fig.

A purifying plant for waste water consists of a mobile housing of a size
transportable on public highways.  The housing contains means for the
biological purification of the waste water, means for mixing aluminum sul-
phate into the biologically purified water, a separator to separate the
deposited particles from the water, and a tank to collect the particles
separated in the separator.  The various apparatuses are situated at one
wall of the housing, and create a compact plant.

*Patents, *Water purification, Biological treatment, Waste water treatment,
Highways, Separation, Tanks, Aluminum

*Aluminum sulfate, Treatment plants, Mobile housing  (equipment)
 164C

 FLUIDISED BED REACTOR,

 Laporte Industries,  Limited,
 Sydney, New South Wales,  Australia

 Australian Patent 447,304.  Applied January 12,  1970.   Issued April  11,  1974.
 Official Journal of  Patents,  Trade  Marks  and Designs,  Vol.  44, No. 13, p 1343,
 April,  1974.

 A fluidised bed reactor comprises a vessel  and has  a base arranged to support
 a bed of particulate material within the  vessel.  This is formed with a
 multiplicity  of perforations  for the admission of fluidising gas, conduit
 means for supplying  fluidising  gas  to the reactor,  a first  set of tubes  of
 which each tube communicates  at one end with the supply conduit means, and
 a closable valve located  between the supply conduit means and the orifice.
 Openable closure means  are  located  on the side of the  orifice, remote from
 the  supply conduit means.   The  closure means are arranged to permit  clearing
 of the  orifice when  the closure means is  open.  A second set of tubes is pro-
 vided.   The number of tubes in  each set is  equal to the number of perforations
 and  each tube of the second set has a closable valve and communicates at one
 end  with a different one  of the tubes of  the first  set.

 *Patents,  *Equipment, *Liquids, Gas,  Waste  treatment

 *Fluidised bed reactor, Australia

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165C

DREDGE AND SLUDGE ALEMBIC,

Kiss, G. S.

Lombard, Illinois

United States Patent 3,810,549.  Applied November 24,  1972.   Issued May 14, 1974.
Official Gazette of the United States Patent Office,  Vol.  922, No.  2,  p 524,
May, 1974.  1 fig.

A sludge alembic is comprised of a sludge receiving tank with vibratory means
in its interior for settling out the sludge solids or residue, and  a screen
means through which discharged water must flow.   This alembic, which may be
stationary, portable, or mounted on a barge or dredge, permits the  location
of a conveyor means beneath it for transporting slurry.  The unit is called
a combination dredge and sludge alembic.

*Patents, *Dredging, Tanks, Sludge, Settling, Screens, Discharge, Slurry

*Sludge alembic, *Combination dredge and sludge alembic
 166C

 FLOATING APPARATUS FOR LIQUID COMPOSTING,

 Blough, R. S.

 Fairfield Engineering and Manufacturing Company,
 Fairfield, Iowa

 United States Patent 3,810,548.  Applied January 26, 1973.  Issued May 14,
 1974.  Official Gazette of the United States Patent Office, Vol. 922, No. 2,
 p 523-524, May, 1974.  1 fig.

 A floating apparatus for aerating and circulating animal waste material was
 designed for use preferably in a relatively deep reservoir.  This liquid
 composting equipment is comprised of an outer float assembly for floating
 support of the apparatus on the surface of the material in the reservoir;
 a rotatable hollow shaft extending down into the material, the lower end
 being adapted to permit air to exit; an axial thrust propeller rigidly at-
 tached to the lower end of the shaft; and a drive means for rotating the
 shaft and propeller to draw air down out of the lower end of the shaft to
 generate small bubbles, which are propelled into the material.  The apparatus
 also has a barrier including a hollow cylinder concentrically surrounding
 the drive means and shutting off the supply of air at the upper end of the
 hollow shaft.

 *Patents, *Animal wastes, *Liquid wastes, *Equipment, *Aeration, Flotation,
 Waste treatment, Circulation, Reservoirs

 *Liquid composting equipment, Floating apparatus
                                           153

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167C

FLUID ANALYZER WITH VARIABLE LIGHT PATH,

Shea, J. J.

Gam Rad Incorporated,
Detroit, Michigan

United States Patent 3,810,695.  Applied December 14, 1972.  Issued May 14,
1974.  Official Gazette of the United States Patent Office, Vol. 922, No. 2,
p 561, May, 1974.  1 fig.

A turbidimeter or fluid analyzer was patented.  The length of its light path
is selectively variable so that different ranges of turbidity or contamination
can be detected.

*Patents, *Analyzers, *Instrumentation, *Contamination, Liquids, Turbidity

*Turbidimeter, *Fluid analyzer, Pollution detection
168C

FILTER SYSTEMS,

Armstrong, A., and Fletcher, G. C.

Sutcliffe, Speakman, and Company, Limited,
Lancashire, Great Britain

United States Patent 3,810,544.  Applied June 21, 1972.  Issued May 14, 1974.
Official Gazette of the United States Patent Office, Vol. 922, No. 2, p 523,
May, 1974.  1 fig.

A filter and water reclamation system is described.  It is comprised of two
filter beds in series, one containing sand and one containing activated car-
bon granules.  Half a charge of water in a cycle passes through only the
sand filter, the other half passes through the sand filter and the activated
carbon.  The water in the system remains at a substantially constant volume.

*Patents, *Filtering systems, *Sand, *Activated carbon, Water reuse,
Filters

*Filter beds, *Water reclamation
                                       159

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169C

PURIFICATION PROCESS,

Nicklin, T.

North Western Gas Board,
Rochdale, England

United States Patent 3,810,833.  Applied August 24,  1972.   Issued May 14,
1974.  Official Gazette of the United States Patent  Office, Vol. 922, No.  2,
p 593, May, 1974.

An effluent pufivication process was patented for removing vanadium salts,
sodium anthraquinone disulphonates and di-hydroxyanthraquinones from effluent
liquors which have been used in processes for removing hydrogen sulphide
from fuel gases or liquid hydrocarbons.  The process comprises passing the
liquor through an adsorbent bed to remove the anthraquinone compounds and
through an ion exchange material to remove the vanadium compounds.

*Patents, *Effluents, *Purification, *Salts, Liquids, Hydrocarbons, Gases,
Ion exchange, Removal

*Fuel gases, *Vanadium compounds, Sodium anthraquinone disulphonates,
Effluent liquors, Adsorbent beds
170C

DEVICE FOR REMOVING A SLUDGE FROM A SURFACE,

Shibata, K., Seika, Y., Sakamoto, I., Yamada, K., and
Kondon, S.

Mitsubishi Jukogyo Kabushiki Kaisha,
Tokyo, Japan

United States Patent 3,808,631.  Applied March 1, 1972.  Issued May 7, 1974.
Official Gazette of the United States Patent Office, Vol. 922, No. 1, p 21,
May, 1974.  1 fig.

A device for removing a sludge from the surface of a liquid or from a floor
such as a deck of a tanker is described.  This includes a shovel which is
adapted to be moved along the sludge with its opened mouth positioned to
receive the sludge.  The construction includes a connection for directing
a high velocity liquid jet into the shovel in the vicinity of the mouth
to impinge upon the sludge and to break it up into a slurry.  In addition,
means are provided for withdrawing the slurry upward through a conduit for
discharge at a remote location.  The discharging connection consists of a
liquid ejector which is operated partly by the conduit connected for supplying
the high velocity jet of liquid to the shovel.  This is connected to the shovel
for providing a withdrawing suction or pumping action on the slurry which
forms in the shovel.  In a further embodiment, the interior of the shovel
is provided with a screen or grate across the shovel interior onto which the
slurry is directed and against which the high velocity liquid jet is directed.
The action breaks up the slurry elements into finer elements for withdrawal
through the discharge conduit.  A still further embodiment includes an
intermediate chamber at the rear of the shovel and a plurality of turning
water streams.  These are directed in a whirling flow to cause a rotation
and further pulverizing of the slurry material before it is delivered through
the discharge conduit.

*Patents, *Sludge, *Jets, Liquids, Slurry, Waste treatment, Discharge,
Conduits, Liquid wastes

*Sludge removal, shovel


                                        160

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me

PURIFYING PLANT FOR SEWAGE,

Bosje, J.

United States Patent 3,809,242.  Applied July 25, 1972.  Issued May 7, 1974.
Official Gazette of the United States Patent Office, Vol. 922, No. 1, p 178,
May, 1974.  1 fig.

A purifying plant for sewage according to the active sludge method comprises
an open tank provided with a partition.  Its shape is that of a closed
aerating circuit with a supply conduit, a discharge conduit and at least one
surface aerator.  The aerating circuit has a curved shape such that it sub-
stantially encloses a space in which at least one after-settling tank and at
least one thickening pond are provided.

*Sewage treatment, *Patents, *Activated sludge, ^Settling tanks, Purification,
Water supply, Aeration, Conduits

Thickening ponds, After-settling tanks, Surface aerator
 172C

 ROTARY  COUNTERCURRENT  SOLID-LIQUID  EXTRACTION APPARATUS,

 Duchateau,  G.  F.

 Raffineri"  tirlemontoise,  Brussels,  Belgium

 United  States  Patent 3,809,538.  Applied  June 28,  1971.   Issued May  7, 1974.
 Official  Gazette  of the  United  States  Patent Office, Vol.  922, No. 1, p  255,
 May,  1974.   1  fig.

 A method  was designed  for  extracting,  by  means  of  a liquid, products which
 are part  of solids in  a  partitioned rotating extractor.   The  flow of the
 liquid  fraction,  separated from the solids  fraction, is slowed down by
 baffles and the liquid fraction is  spread over  the length and width relative
 to the  new  solids fraction.

 *Patents, *Extraction, Liquids,  Solids, Equipment, Waste  treatment, Flow

 *Rotary countercurrent apparatus, *Solid/liquid extraction, Liquid fraction,
 Solids  fraction
                                        161

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173C

SEWAGE TREATMENT APPARATUS,

Kennedy, S. R.

Bridgeton, Missouri

United States Patent 3,809,245.  Applied January 31,  1972.  Issued May 7,  1974.
Official Gazette of the United States Patent Office,  Vol. 922, No. 1, p 179,
May, 1974.  1 fig.

A sewage treatment apparatus was patented which has an aeration circulation
system for separating sludge from sewage.  Sewage is  circulated around an
outlet port shielded by a circulation guide member.  This circulating sewage
causes solid matter to move radially away from the outlet port so that liquid
entering the outlet port is essentially free of solids.

*Sewage treatment, *Patents, *Aeration, Sewage, Circulation, Liquids, Solids,
Waste treatment, Equipment

*Aeration circulation system
174C

FUEL SEDIMENT BOWL ASSEMBLY,

Jackson, J. E.

Deere and Company,
Moline, Illinois

United States Patent 3,809,244.  Applied December 14, 1972.  Issued May 7, 1974.
Official Gazette of the United States Patent Office, Vol. 922, No. 1, p 179,
May, 1974.  1 fig.

A fuel sediment bowl assembly is described.  The assembly is built between a
source of fuel and a fuel pump.  A hand pump cooperates with appropriate
valving for pumping fuel into the sediment bowl when separated water in the
bowl Is being drained.  The action of the pump effects the replacement of the
volume formerly occupied by the water by fuel such that no air will be
introduced into the system.  The sediment bowl assembly also Includes a
baffle at the top.  This aids in the separation of water from the fuel which
is drawn through.

*Patents, *Fuel, Pumping, Sediment, Separation, Equipment

*Fuel sediment bowl assembly, Fuel pumps, Valving
                                          162

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175C

FLUID SEPARATION APPARATUS AND MEMBRANE SUPPORT FRAMES
THEREFOR,

Niogret, G.

Lyon, France

United States Patent 3,809,246.  Applied December 15, 1972.  Issued May 7, 1974.
Official Gazette of the United States Patent Office, Vol. 922, No. 1, p 179,
May, 1974.  1 fig.

A fluid separating apparatus has a support frame for placement between the
membranes.  The frame comprises a generally rectangular plate, with two faces
and two ends.  At least one cell forming a recess is formed in each face,
and at least one orifice extends through the thickness of the plate adjacent
to the ends of the plate for the passage of fluid to be treated.  A duct
exists for the removal of fluid which is passed through the membrane supported
by the plate over each of the cells forming recesses.  An aperture passes
through the plate and is positioned between at least one of the orifices
and the cell forming recess.  The aperture has a detachable clamp to clamp
membranes disposed on each of the faces in a fluid-tight manner against a
rules surface of the rectangular plate.

*Separation, *Patents, *Membranes, *Liquids, Equipment, Waste disposal,
Liquid wastes

*Fluid separation
176C

OIL/WATER SEPARATION ACCELERATION MEDIA,

Rhodes, H. M.

Oil Mop, Incorporated,
New Orleans, Louisiana

United States Patent 3,810,832.  Applied June 1, 1972.  Issued May 14, 1974.
Official Gazette of the United States Patent Office, Vol. 922, No. 2, p 593,
May, 1974.  1 fig.

Media is directed to an apparatus for accelerating the separation of oil from
oil/water mixtures.  This brings the oil to the surface over as short a
linear distance as possible in a linear flow of a mixture of oil and water.
The process is accomplished by directing the oil/water mixture through a
barrier of filaments of polypropylene arranged across the path of the mixture
flow; the barrier is anchored at its base at the bottom of the fluid confining
means by an API oil separator, a ditch, or a canal.  The free ends of the strips
of polypropylene are directed upward, forming an inclined plane up which the
oil droplets amalgamate.  These are assisted by the buoyancy of the oil and
the force flow vector of the mixture passing through the fluid confining
means.

*Separation, *0il, *Patents, Flow, Equipment, Filaments

*Polypropylene, Acceleration media, Flow vector, Linear flow, Oil-water
separation
                                       163

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177C

BOD MEASURING APPARATUS,

Fleischmann, L. W.

Randallstovm, Maryland

United States Patent 3,810,738.  Applied August 14, 1972.  Issued May 14, 1974.
Official Gazette of the United States Patent Office, Vol. 922, No. 2, p 573,
May, 1974.  1 fig.

The BOD of a waste water sample is measured by continuously recirculating
an oxygen-containing gas through a closed loop gas passageway.  The equipment
is adapted to pass the gas in series through the waste water sample, a
carbon dioxide absorber, and an oxygen partial pressure sensor.  A make-up
gas containing oxygen in a predetermined proportion is admitted to the closed
loop passageway in an amount so that the oxygen partial pressure in the circula-
ting gas remains constant.  Inert gas in the make-up gas causes pressure in
the system to build as additional oxygen is consumed.  The BOD in a given
sample is therefore indicated by measuring the gas pressure in the closed
loop passageway.

*Patents, *Biochemical oxygen demand, *Sampling, *Measurement, *0xygen, Gas,
Pressure, Waste water

*Closed loop gas passageway, Oxygen partial pressure sensor, Make-up gas
 178C

 METHOD FOR TREATING OIL-CONTAINING WASTES,

 Ohta, M.

 Kyoto-shi, Kyoto-fu, Japan

 United States Patent 3,809,631.   Applied March 8,  1973.   Issued May 7,  1974.
 Official Gazette of the United States Patent Office,  Vol. 922,  No.  1,  p 274-
 275, May, 1974.   1 fig.

 A method for treating industrial wastes containing oils  and surfactants com-
 prises adjusting the pH of such wastes to 3 or less.   The wastes are also
 subjected to an electrolytic treatment using an anode composed  of an acid-
 resistant electrode material and a cathode composed of an ordinary electrode
 material.  The process separates the oil phase from the aqueous phase where
 the surfactants are dissolved.  The aqueous phase, separated from the oil
 phase, is subjected to an electrolytic treatment using an anode and a cathode
 composed of aluminum which precipitates the surfactants as sludge separated
 from water.

 *Industrial wastes, *0ils, *Waste treatment, *Patents, *Anodes, *Cathodes,
 *Surfactants, Electrolysis, Aqueous solutions, Separation, Aluminum

 pH, Electrolytic treatment, Oil phase, Aqueous phase

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179C

AERATION DEVICE FOR THE SURFACE AERATION OF LIQUIDS,

Kaelin, J. R., and Seeburg, V.

Buochs, Switzerland

United States Patent 3,811,662.  Applied September 5, 1972.  Issued May 21,
1974.  Official Gazette of the United States Patent Office, Vol. 922, No. 3,
p 809, May, 1974.  1 fig.

An aeration device for the surface aeration of liquids has supporting legs
which, in the rotor-bearing unit end, are forked and hinged to a cage-like
supporting frame.  The frame surrounds the rotor-bearing unit so that the
height of the unit can be adjusted by adjusting means provided on or adjacent
to the axis of the supporting legs.

*Patents, *Aeration, Liquid wastes, Equipment, Waste treatment

*Aeration devices, Surface aeration
180C

APPARATUS FOR CONTROLLING A POLLUTING LIQUID,

Oxenham, J.  P.

Shell Oil Company,
New York, New York

United States Patent 3,810,546.  Applied March 28, 1973.  Issued May 14, 1974.
Official Gazette of the United States Patent Office, Vol. 922, No. 2, p 523,
May, 1974.  1 fig.

The apparatus examined removes a pollutant or polluting liquid floating on
the surface of a body of water.  The invention uses a skimmer utilizing liquid
movement to facilitate separation of the polluting liquid from the water.  The
skimmer is arranged to remove the polluting liquid from all directions.  Further,
the apparatus has means for circulating water adjacent to the polluting liquid/
water interface.  This presents moving liquid to the skimmer approaching from
all directions.

*Patents, *Liquids, *Pollutants, Liquid wastes, Oil, Oil/water interfaces.
Water treatment, Removal, Equipment
                                          165

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181C

TREATMENT OF BIOLOGICAL SLUDGE,

Australian Patent 446,556.  Applied May 11, 1970.  Issued March 28,  1974.
Official Journal of Patents, Trade Marks and Designs, Vol. 44,  No. 11,  p 1079,
March, 1974.

A method of treating an aqueous biological sludge is described.  This comprises
the steps of feeding the slurry through an evaporator plant where it is subjected
to heat treatment and a part of its water content is removed by evaporation.  The
slurry which has passed through the evaporator plant is filtered, and the aqueous
filtrate is recycled for further treatment with the slurry in the evaporator plant.


^Patents, *Biological treatment, *Slurries, *Sludge, *Sludge treatment,
*Aqueous solutions, Filtration, Evaporation, Recycling

*Treatment plants
 182C

 DETECTING PARTICLES  IN  LIQUIDS,

 Emhart  Corporation,  Sydney, New  South Wales, Australia

 Australian Patent  446,177.  Applied  January 26,  1972.  Issued January  4,  1973.
 Official  Journal of  Patents,  Trade Marks  and Designs, Vol.  44, No.  9,  p 900-901,
 March 14,  1974.

 A method  of inspecting  transparent liquid filled containers for  foreign particles
 comprises  the  steps  of:  spinning the container to  cause  the liquid  contents  to
 swirl;  stopping the  container while  the liquid contents  continue to swirl; generating
 a first video  voltage pattern as a result of scanning the container and contents
 with a  video camera; providing timed digital voltage pulses corresponding to any
 peak portions  of the first video voltage  pattern which exceed a  predetermined
 threshold voltage; and  storing the timed  pulses  for subsequent recall  from a
 memory  device.  Following this,  methods involve: generating a suceeding video
 voltage pattern as a result of scanning the container and contents  with a
 video camera at a  later instant  of time;  altering  the threshold  voltage during
 the succeeding voltage  pattern so that the threshold voltage is  decreased at the
 location  corresponding  to each peak  portion of the first video voltage pattern;
 digitizing the succeeding video  voltage pattern  to provide  a voltage trace with
 pulses  corresponding to peak  portions; synchronizing the first and  succeeding
 digitized video voltage patterns; and comparing  the first and succeeding  digitized
 voltage patterns by  electronically comparing one to the  other.

 *Liqulds,  *Computers, *Patents,  Automation, Inspection,  Monitoring

 *Detection, *Video voltage patterns
                                             166

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183C

TREATING A WATER STREAM CONTAINING A WATER SOLUBLE SULFITE,

Australian Patent 446,540.  Applied February 8, 1971.  Issued March 21,  1974.
Official Journal of Patents, Trade Marks and Designs, Vol. 44, No.  10, p 1027,
March, 1974.

A method for treating an input water stream containing a water soluble sulfite
compound in order to reduce its total sulfur content while minimizing the formation
of sulfate by-products, is comprised of three steps.  First, the input water
stream is contacted with a reducing agent selected from the group consisting of
finely divided sulfur, a polysulfide compound, a water-soluble sulfide compound
and mixtures at thiosulfate production conditions selected to form a thiosulfate-
containing effluent stream.  Next the effluent stream is reacted from the previous
step with carbon monoxide at reduction conditions selected to produce a sulfide-
containing aqueous effluent stream.  Finally hydrogen sulfide is stripped from
the aqueous effluent stream to form a substantially sulfate-free treated water
stream which is substantially reduced in total sulfur content relative to the
input water stream.

*Patents, *Water treatment, *Sulfites, *Streams, Sulfur, Sulfates,  Effluents,
Hydrogen sulfide, Aqueous solutions

Water soluble sulfite, Treatment methods
184C

A PROCESS FOR PURIFYING WATER AND NATURAL HYDROCARBON GAS,

Australian Patent 446,481.  Applied August 26, 1970.  Issued March 21, 1974.
Official Journal of Patents, Trade Marks and Designs, Vol. 44, No. 10, p 1014,
March, 1974.

A process for purifying water and natural hydrocarbon gas includes reacting an
impure water feedstock with a natural gas feedstock to form solid hydrocarbon
hydrates.  Also described is an impure water residuum having an enhanced
impurity content, which separates the solid hydrates from the water residuum, and
washes the solid hydrates to remove adhered impurities.  In addition, the washed
hydrates are decomposed to form purified water and a purified gaseous
hydrocarbon product.

*Patents, *Water purification, *Hydrocarbons, Hydrates

*Natural hydrocarbon gas, Impure water feedstock, Natural gas feedstock
                                      167

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185C

REVERSE OSOMOSIS WATER PURIFYING DEVICE,

Australian Patent 445,989.  Applied August 12, 1970.  Issued March 7, 1974.
Official Journal of Patents, Trade Marks and Designs, Vol. 44, No. 8, p 794,
March, 1974.

A water purifying device includes a treatment chamber with a feed water inlet
for connection to a source of water to be purified and a reverse osmosis water
purifying element in this chamber, having a feed water outlet and a product
water supply outlet.  A reservoir has a compressible container whereby the inner
volume of this container communicates with the product water supply outlet
for storing product water and a transfer passage between the feed water outlet
and the volume of the reservoir outside the comprehensible container.  Means
for selectively opening the transfer passage allow feed water pressure to be
exerted on the product water, discharging product water through a product water
discharge outlet.

*Patents, *Water purification, *Reverse osmosis, *Water supply, Water pressure,
Equipment, Reservoirs

Product water supply outlet, Treatment methods
 186C

 OIL RECOVERY  PROCESS,

 Shephard,  C.  A. Y.

 Mobil Oil  Corporation,  New York

 Canadian Patent 947,644.  Applied May  25,  1972.   Issued May  21,  1974.
 Patent Office Record, Vol. 102, No.  21,  p  21-41,  May  1974.

 Disclosd is a process of  recovering  oil  from an oil-containing  reservoir
 having a gas  cap.   In accordance with  this process  a  fluid is injected  into
 the gas cap that is miscible with the  oil  in the  reservoir and  gas  in the
 gas cap.   Also injected into the reservoir are gas  and water in an  amount no
 greater than  that amount  which  can be  maintained  within the  gas cap without
 flowing into  the oil zone.  Oil is produced from  the  reservoir  from locations
 that  are structurally lower than the gas cap.

 *Patents,  *0il, Gas, Reservoirs, Pollution abatement

 *0il  recovery, *0il zone, Miscibility
                                        168

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187C

APPARATUS FOR DISINTEGRATING AND SEPARATING MATERIAL IN FLUID
SUSPENSION,

Improved Machinery Incorporated, Nashua, New Hampshire

Canadian Patent 947,705.  Applied March 17, 1972.  Issued May 21, 1974.
Patent Office Record, Vol. 102, No. 21, p 21-54, May 1974.

An apparatus was patented comprising a chamber containing a centrifugal pump
arranged to pump material in fluid suspension.  The material is pumped to an
accepts discharge, and a screen which limits the size of the material supplied
by the pump to the accepts discharge is mounted with the pump to be rotatably
driven.  This causes disintegration of coarse material in the suspension.  Baffle
means adjacent to the screen feed face divide the chamber into communicating
inner and outer portions.  Suspension is supplied to the screen through the
chamber inner portion; and rotary vanes induce vortex flow of suspension in the
chamber outer portion.  Thus heavy material is separated from the suspension by
centrifugal separation.  The heavy rejected material is discharged from the
chamber through a discharge outlet.  Lighter particles of coarse material
rejected by the screen may be discharged from the chamber through a discharge
conduit which is arranged to receive such particles from the chamber's inner
portion.

*Patents, *Pumps, *Separation, *Suspensions, Equipment, Discharge

Vortices, Baffles
188C

METHOD AND APPARATUS FOR DENITRIFICATION OF TREATED SEWAGE,

Savage, Elton S.

Dravo Corporation, Pittsburgh, Pennsylvania

Canadian Patent 947,886.  Applied July 2, 1971.  Issued May 21, 1974.  Patent
Office Record, Vol. 102, No. 21, p 21-93, May, 1974.

A method and apparatus are given for denitrification of aqueous nitrate-containing
solutions.  Specifically the invention provides for denitrification of the effluent
from an activated sludge sewage treatment process.  Effluent from the settling zone
of such a process containing nitrogen compounds such as nitrates and nitrites, is
passed through a deep bed filter.  The filter medium has been inoculated with
bacteria that convert the nitrogen compounds to nitrogen gas.  The filter, in
addition to removing the nitrogen compounds, removes any suspended solids from the
settling zone effluent, so that the final effluent from the filter is concurrently
clarified and denitrified.  By controlling the backwash of the filter, bacteria are
retained so as to enable continuous use of the filter for denitrification.


*Patents, *Denltrification, *Sewage treatment, *Activated sludge, Effluents,
Nitrogen, Nitrates, Nitrites, Filters, Bacteria, Suspended solids, Clarification

Deep bed filter, Settling zone
                                       169

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189C

SEWAGE TREATMENT UNIT,

Light, D. J.  N., and Devries,  J.

Pollution Control Systems Limited,  Thornhill,  Ontario,
Canada

Canadian Patent 946,990.  Applied October 29,  1969.   Issued May 7,  1974.   Patent
Office Record, Vol. 102, No.  19, May,  1974.

One treatment method for sewage involves aerating the raw sewage in a storage
tank provided with means for recirculating the sewage and subsequently passing
aerated sewage to a blending tank.  There it is mixed with a flocculating or
coagulating agent and the sewage is then passed to a filtering or clarifying
assembly.  This is provided with a filtering medium, adapted to move through the
mixture and receive suspended solids.   Means are provided in the assembly to receive
the filtering medium for subsequent disposal and an outlet is provided to dispense
the filtrate.  This filtrate may then be subjected to further aeration or bacteria
removing treatment.

*Patents, *Sewage treatment, *Aeration, *Storage tanks, Circulation, Flocculation,
Coagulation,  Filtering, Suspended solids, Disposal,  Bacteria
190C

FLOAT MOUNTED EJECTOR WASTE TREATMENT APPARATUS,

Mandt, M. G.

Kimberly Clark Corporation,
Neenah, Wisconsin

Canadian Patent 945,275.  Applied July 20, 1971.  Issued April 9, 1974.
Patent Office Record, Vol. 102, No. 15, p 1311, April, 1974.

A system is described for the removal of B.O.D. and suspended solids from aqueous
waste.  It operates by the use of ejectors which are supported by a float.
Advantages include improved mobility, reduced piping, and low maintenance
requirements.  In one such system a venturl effect is used to supply air to the
ejectors placed near the surface of the aqueous waste to provide aeration.

*Patents, *Biochemical oxygen demand, *Suspended  olids, Aqueous solutions, Wastes,
Piping, Maintenance, Aeration

*Venturi effect, *Removal, *Floats
                                         170

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191C

EJECTOR AERATED OXIDATION DITCH FOR WASTE TREATMENT,

LeCompte, A. R.

Kimberly-Clark Corporation,
Neenah, Wisconsin

Canadian Patent 948,797.  Applied November 2, 1972.  Issued June 4, 1974.  Patent
Office Record, Vol. 102, No. 23, p 23-97, June, 1974.

A patent was issued for an oxidation ditch system for the removal of B.O.D. and
suspended solids from aqueous waste.  This involves the use of ejectors to aerate
the liquid and to move the liquid as the propelling force around a closed-loop circuit.
Advantages include reduced horsepower requirements and the use of deeper, high-
volume ditches without reducting aeration effectiveness.

*Patents, *0xidation, *Biochemical oxygen demand, *Suspended solids, Aqueous
solutions, Aeration, Liquids, Equipment

*Ejectors, *0xidation ditch system
FLUID FILTERING DEVICE,

Brown, C. A., and Thomas, J. F.

Parker-Hannifin Corporation,
Cleveland, Ohio

Canadian Patent 948,562.  Applied April 19, 1971.  Issued June 4, 1974.  Patent
Office Record, Vol. 102, No. 23, p 23-46, June, 1974.

A fluid filtering device has a housing with a cavity in which a cylindrical filter
element is disposed.  This defines an annular chamber between the outer wall of
the filter element and the interior of the housing, the annular chamber registering
with an inlet port.  One end of the filter element registers with an outlet port so
that the normal path of fluid flow is from the inlet port into the annular chamber,
radially through the walls of the filter element, axially through the interior
of the filter element and externally of the filtering devide by the outlet port.
When the filter element becomes clogged by a predetermined amount, a valve
mechanism disposed at the opposite end of the filter element causes the fluid to
bypass the filter element.  The valve mechanism includes a cover member which in
turn closes the housing cavity.  Indicators are connected to the valve mechanism
for determining the filtering condition of the filter element.

*Patents, *Filtering, *Equipment, *Fluids, Valves

Fluid filtering device, Filter elements
                                        171

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19 3C

PROCESS FOR PURIFYING WATER CONTAINING OILS AND SOLIDS,

Beavon, D. K.

Canadian Patent 945,479.  Applied March 26, 1971.  Issued April 16, 1974.  Patent
Office Record, Vol. 102, No. 16, p 1356, April, 1974.

Water containing oil and particulate solids, such as oil-wet solids, is filtered
through a filter media, such as a sand for purification.  Particulate solids
are retained, thus yielding clear water or a mixture of solids-free oil and
water, which will readily separate by gravity.  The filter media is periodically
regenerated by steam stripping to remove retained oil.  It is then backwashed
to remove oil-free particulate solids.

*Patents, *011, *Filter media, Sands, Clarification, Separation, Gravity

*Backwashing, *Particulate solids
194C

METHOD FOR THE MONITORING OF LIQUID FLOW AND AN AUTOMATIC
FLOW CONTROLLER TO BE USED FOR THIS METHOD,

Canadian Patent 948,737.  Applied August 25, 1971.  Issued June 4, 1974.  Patent
Office Record, Vol. 102, No. 23, p 23-84, June, 1974.

A method is detailed for the monitoring of a liquid flow by means of two pressure
detectors installed in different horizontal planes of a non vertical pipe.  These
pressure detectors trip an alarm system by comparing their outputs if a given flow
value is not attained.  The invention also concerns an automatic flow controller
comprising two resistance strain gauges which are installed in a pipe.  These
are arranged one above the other and an electronic alarm circuit supplying the
resistance strain gauges compares their data and trips an alarm system as soon as
the liquid content of the pipe falls below a specified value.

*Patents, *Monitoring, Liquids, Flow, Pressure, Pipes, Automation, Control,
Installation

*Pressure detectors, Alarm systems
                                           172

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195C

PURIFIER DEVICE,

Sana, N.

United States Patent 3,815,753.  Applied June 18, 1972.  Issued June 11,  1974.
Official Gazette of the United States Patent Office, Vol. 923, No.  2, p 550-551,
June, 1974.  1 fig.

A liquid purifier device for immersion in a body of liquid  includes an annular
canister with a through central column or main duct.  The canister has inlet
and outlet means in spaced relation so that there is a flow path  through  the
canister interior or secondary duct.  A purifying medium is located in this
flow path.  When submerged, all of the inlet means are at a higher pressure
level than the exit means.  Thus, whenever a flow of air is introduced into the
lower end of the column, a pressure differential is created.  A tube is provided
to introduce a flow of air into the lower end of the column when  it is submerged
so that the differential of pressure created in the column  acts as a lift tube
pumping means to cause a flow through the purifying medium,  The  purifying medium
preferred is activated charcoal.  The canisters may also be adapted for
stacking and use in combination with a filtering device.

*Patents, *Water purification, Equipment, Filtering, Pumping, Liquids, Flow

*Activated charcoal
196C

WASTE WATER TREATMENT METHOD,

Tate, J. F.

Texaco, Incorporated,
New York, New York

United States Patent 3,817,859.  Applied March 29, 1972.  Issued June 18, 1974.
Official Gazette of the United States Patent Office, Vol. 923, No. 3, p 1067,
June, 1974.

A method of disposing of certain process effluent waste streams by injecting
them into subterranean formation is described.  This entails inhibiting the
formation of solid precipitates which plug the subterranean formation.  The
method of Inhibition involves lowering the pH of the mixed streams and optionally
removing any organic phase created before injection.

*Waste treatment, *Patents, *Effluents, *Precipitates, Waste disposal, Streams,
Organic matter, Solids

*pH, Subterranean formation
                                  173

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197C

APPARATUS FOR TREATING NOXIOUS EFFLUENTS,

Solomon, R. L.

Trayler and Trayler,
Edmund, Ohio

United States Patent 3,812,793.  Applied April 19, 1972.  Issued May 28, 1974.
Official Gazette of the United States Patent Office, Vol. 922, No. 4, p 1091-
1092, May, 1974.  1 fig.

An uncomplicated structure which lends itself to unskilled manual operation for
treating the output of a furnace or burner is described.  The furnace output
is cooled, directed and forced into a treating tank containing a scrubbing
fluid, and exposed to a burner flame before being discharged into the atmosphere.
The system is of particular use in ensuring that the output from the burner or
furnace contains no noxious effluents.

*Patents, *Waste treatment, Effluents, Burning, Discharge, Liquids, Toxicity,
Treatment facilities

*Furnace, *Burner, Scrubbing fluid
 198C

 REMOVAL OF MERCURY FROM MERCURY CATHODE SLUDGE,

 Rachor, D. G., and Perry, R. A.

 Environmental Protection Agency,
 United States

 United States Patent 3,814,685.  Applied April 27, 1973.  Issued June 4, 1974.
 Official Gazette of the United States Patent Office, Vol. 923, No. 1, p 264,
 June, 1974.

 Mercury is recovered from mercury cathode sludge by treating the sludge with
 acid and then roasting.  The mercury content of the residue becomes
 significantly lower by this process than when the acid treatment step is
 omitted.

 *Patents, *Mercury, Acid, Treatment

 *Mercury cathode sludge, *Acid treatment, roasting
                                   174

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199C

WATER PURIFICATION SYSTEM,

Johnson, W. E., and Fraser, J. H.

Avco Corporation,
Cincinnati, Ohio

United States Patent 3,813,892.  Applied August 23, 1971.  Issued June 4, 1974.
Official Gazette of the United States Patent Office, Vol. 923, No. 1, p 62-63,
June, 1974.

A water purification system is described with uses including desalination of
saline water.  Water is crystallized in saline solution through the use of an
appropriate refrigerant to form a slurry of ice crystals and brine, which is fed
to a wash column for separating the brine from the ice crystals.  The ice
crystals form a porous ice bed for movement through the column.  This bed is
washed by a wash liquid flowing in direction counter to the ice bed movement.
Ice is removed at one end of the column and brine and wash water is removed
through an intermediate permeable port of the column.  The ice is preferably
being melted by indirect heat exchange with vaporized refrigerant.  The pressure
relationships at the input end of the ice bed, at the intermediate permeable
port, and at the output end of the ice bed are controlled independently of the
pressures at the crystallizer and at the melter units of the system.  This
provides for maximum ice output from the column and minimization of wash liquid
loss.

*Patents, *Water purification, *Desalination, Ice, Slurry, Crystallization,
Equipment, Heat, Pressure
     200C

     REMOVING MERCURY FROM WASTE BRINE,

     Imperial Chemical  Industries Limited,
     Great Britain

     Australian Patent  446,563.   Applied February 9, 1971.  Issued March  28, 1974.
     Official Journal of Patents, Trade Marks and Designs, Vol.  44, No.  11, p 1081,
     March 28, 1974.

     A process for  the  removal of mercury from chlorine containing waste brine from a
     mercury cell has been patented.   It comprises adding sulfide or hydrosulfide
     ions to the brine  in sufficient amount to produce a redox potential of the
     brine, relative to a saturated KCl-Calomel electrode, of a  value more negative
     than +0.45 volts whereby mercuric sulfide is precipitated.  Also,  the
     precipitated mercuric sulfide is  removed by passing the brine through a filter
     which comprises at least two directly superimposed layers of granular filtration
     material, the  average size of the particles of granular material in the
     successive superimposed layers decreasing and the specific  gravity  of the
     granular material  increasing from the top of the filter downwards.

     *Patents, *Mercury, *Brines, Chemical precipitation, Chlorine, Filtration,
     Sulfides

     Mercury removal
                                        175

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201C

SPINNING TOP FOR LIQUID AERATION,

Kaelin, J. R.

Shelston Waters, Sydney, New South Wales, Australia

Australian Patent 445,817.  Applied Nov. 26, 1969.  Issued March 7,  1974.
Official Journal of Patents, Trade Marks and Designs,  Vol. 44,  No.  8,  p 752,
March 7, 1974.

A vertical axis spinning top of internal blade type has been developed for the
ventilation of liquids.  It comprises a rotor member which diverges  from a
lower axial intake portion to an upper peripheral outlet portion.  This rotor
member has a number of blades to define a number of ducts for conveying the
liquid to be ventilated from the intake portion to the outlet portion.  Each  of
duct has a longitudinal slot in the wall facing the inside of the spinning top
which extends along the entire length of the duct.  The slot has a width similar
to the distance between consecutive blades at the intake end with the  width of
the slot being substantially constant along its length.

*Patents, Equipment, Aeration

*Spinning top, Liquids ventilation
 2Q2C

 DEEP TANK AERATION USING EDUCTOR TUBES OF ELONGATE
 CROSS-SECTION,

 Walker, J. D.

 Chicago Bridge and Iron Company,
 Aurora, Illinois

 Canadian Patent 946,991.  Applied March 4, 1971.  Issued May 7, 1974.
 Patent Office Record, Vol. 102, No. 19, p 19-94, May 7, 1974.

 Eductor tubes have been patented which allow efficient aeration of huge
 quantities of sewage in very deep tanks.  Air is liberated at only a moderate
 depth, the tubes extend downwardly from only slightly above the level of
 liberation, and the tubes are elongated in horizontal cross-section for
 effective utilization of the full cross-section.  There is a baffle at
 surface level above the tubes.

 *Patents, *Aeration, Equipment, Sewage treatment

 Deep tanks, Eductor tubes, Baffles
                                          176

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203C

FEED NOZZLE FOR SCREENING DEVICE,

Riesbeck, L. J., and Blackwell, W. A.

Midwestern Industries, Incorporated,
Massillon, Ohio

Canadian Patent 947,793.  Applied October 28, 1971.  Issued May 21, 1974.
Patent Office Record, Vol. 102, No. 21, p 21-73, May 21, 1974.

A device for controlling the flow of a fluid material at a screen of a
conventional material separator which isolates any solids consists of an
adjustable baffle plate within a conical hood member.  The input fluid is
directed against the baffle plate and deflected against the hood member which
is suspended over the screen.  The fluid then follows along the hood member
and falls to the screen as an annular sheet of fluid material.  The precise
configuration of the sheet of fluid material is controlled by adjusting the
axial location of the baffle plate, moving it toward and away from the
direction of the flow of the input material.  The solids which are unable to
pass through the screen are transmitted to a discharge chute located at the
periphery of the screen.

*Screen, *Patents,  Flow control, Separation techniques

*Feed nozzle
 204C

 AERATING LIQUIDS,

 Platz,  R.,  Fuchs, W.,  and  Nagel,  0.

 Badische Anilln-and Soda-Fabrik Aktiengesellschaft,
 Ludwigshafen,  Germany

 Canadian Patent  947,639.   Applied May  7,  1970.   Issued  May  21,  1974.
 Patent  Office  Record,  Vol. 102, No.  21, p 21-40,  May  21,  1974.

 Aeration of liquids present in a  container and  premixing  of the air  to  be
 introduced  into  the liquid is  performed by means  of a stream of liquid
 issuing from a nozzle  into a mixing  zone  provided within  the container  with
 a portion of the liquid present in the container. Discharge into  the
 remainder of the liquid follows.

 *Patents, *Aeratlon, *Liquids, Equipment

 Treatment methods,  mixing  zone
                                       177

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205C

METHOD AND APPARATUS FOR RECOVERING A SUBSTANCE FLOATING
AS A SHEET ON THE SURFACE OF A LIQUID MASS,

Mourlon, J., and Dubois, E. M. R.

Bertin and Cie,
Paris, France

Canadian Patent 948,120.  Applied December 22, 1969.  Issued May 28, 1974.
Patent Office Record, Vol. 102, No. 22, p 22-48, May, 1974.

A process is described for recovering a substance, such as a hydrocarbon,
spread as a thin sheet and floating on the surface of a liquid.  The liquid
is, in the vicinity of its surface, subjected to a local rotating movement
so as to bring about the formation of a vortex-type cavity.  The cavity is open
and has a vertical axis, and in which the substance originating from the sheet
accumulates, and from this cavity the accumulated substance is extracted.  The
amount extracted is automatically replaced, as it is being extracted, by
further substance emanating from the sheet.

*Floating, *Patents, *Liquids, *Hydrocarbon, Recovery, Extraction

Treatment methods, Liquid masses
 206C

 HIGH CAPACITY FLUID TREATER EMPLOYING CONCENTRATED
 ELECTRIC FIELDS,

 King, A. S.

 Prairie Village, Kansas

 Canadian Patent 948,159.  Applied April 14, 1971.  Issued May 28, 1974.
 Patent Office Record, Vol. 102, No. 22, p 56-57, May, 1974.

 A  fluid treater has multiple flow paths in order to treat large quantities of
 water utilizing an electric field without substantial pressure drop.  The
 treater is provided with an intake manifold having a configuration which causes
 essentially  laminar flow of the water in the manifold along a spiral path
 which has convolutions of successively reduced diameter.  Outlet ports of the
 manifold are spaced along this path and are in communication with tubular,
 outer electrodes.  Water passes through these to a similarly arranged discharge
 manifold where the plural paths are recombined.  The water in each path is
 subjected to a radial electric field in the annular passage defined by its
 respective inner and outer electrode pair.  The tubular wall of each outer
 electrode.is inset to concentrate the electric field in the annular passage.
 The inner electrode has an electrically conductive outer surface at least
 coextensive  with the tubular wall.  The construction permits any of the inner
 electrodes to be readily replaced without disassembling the treater.

 *Patents, *Water treatment, *Pressure, *Fluids Flow, Laminar flow, Electrodes,
 Construction

 *Electric fields, *Flow paths, *Fluid treater
                                          178

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207C

METHOD OF FILTERING,

Hirs, G.

Hydromation Filter Company,
Livonia, Michigan

United States Patent 3,814,247.  Applied August 21, 1972.  Issued June 4, 1974.
Official Gazette of the United States Patent Office, Vol. 922, No. 1,  p 155,
June, 1974.  1 fig.

A liquid filtering method for operating an apparatus comprises a deep  bed of
dual, vertically separate, granular filter media beds.  The first filter media
bed has relatively coarse grains-in the size range of 0.050 to 0.375 inches-
which have a specific gravity in the range of 0.9 to 1.6.  The second  filter
media bed, which underlies the first bed, has finer grains which have  a specific
gravity greater than 2.1.  Upon backwashing, the first bed is slurried and
turbulently recirculated through a path external of the retaining vessel, while
the second bed is only expanded.  After backwashing, the filter media  beds
assume their original respective orientations.

*Patents, *Filters, *Filter media, Specific gravity, Recirculated water

Deep bed filters, *Backwashing
 208C

 LIQUID  COLLECTING AND  FILTERING DEVICE,

 Le  Roy,  R. F.

 Upjohn  Company,
 Kalamazoo, Michigan

 United  States Patent 3,814,079.  Applied April  28,  1972.   Issued June 4, 1974.
 Official Gazette of the  United'States Patent Office, Vol.  923, no. 1, p 112,
 June, 1974.

 A pair  of telescopically arranged  tubes defines an  expansible, closed chamber
 in  which the pressure  is initially and substantially below ambient pressure.
 The inner tube has an  inlet end with a perforable closure  member and an outlet
 end which communicates with the outer tube.  A  cannula is  supported upon the
 inlet end for movement between a position spaced from the  closure member to
 a position penetrating through the closure member to communicate with the
 chamber.   A filter means is disposed in the inner tube so  that liquid moving
 from the inlet end through the outlet end or the inner tube must pass through
 the filter.

 *Patents,  *Filters, *Liquids, *Filtration, Tubes, Pressure, Equipment

 Ambient pressure
                                          179

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209C

APPARATUS FOR EXTRACTING A LIQUID SAMPLE AT VARIOUS
DEPTHS OF A LIQUID STREAM,

Crumal, J.

Nielsen Engineering and Research Incorporated,
Mountain View, California

United States Patent 3,813,945.  Applied November 19, 1971.  Issued June 4, 1974.
Official Gazette of the United States Patent Office, Vol. 923, No. 1, p 76,
June, 1974.  1 fig.

A hollow elongated tube with an opening near its lowest end descends into a
stream.  A plunger within the tube normallyppositioned below the opening rises
upward within the tube after the tube reaches the bottom of the stream.  This
forces a liquid sample out the top of the tube.  A second plunger may be
employed within the tube normally positioned above the opening to act as a
pump plunger descends through the stream of liquid.  The pump plunger travel
may be controlled as a function of height of the opening of the tube within the
stream.  A method has been patented in order to obtain a liquid sample that
contains various constitutents in the same proportion as the liquid stream.

*Patents, *Extractions, *Liquids, *Sampling, Streams, Tubes

Liquid samples, Liquid streams, Pump plunger
210C

APPARATUS FOR FRACTIONATING FLUID SUSPENSIONS,

Young, D. L. G.

Canadian Ingersoll-Rand Company, Limited,
Montreal, Quebec, Canada

United States Patent 3,814,244.  Applied May 30, 1972.  Issued June 4, 1974.
Official Gazette of the United States Patent Office, Vol. 923, No. 1, p 153-154,
June, 1974.  1 fig.

A fractionating apparatus is described which comprises a plurality of annular
walls spaced one inside the other.  At least one of these walls is a screen.
The apparatus includes rotary drive shaft means having a portion connectible to
a driving means and a portion eccentric to such connectible portion.  One of
the annular walls is connected to the eccentric portion of the drive shaft
means.

*Patents, *Fluids, *Suspension, Equipment, Waste treatment

*Rotary drive shaft means, *Fractionation
                                       180

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211C

PROCESS AND APPARATUS FOR TREATING WASTES BY A COMBINED
ACTIVATED SLUDGE AND BIOLOGICAL FILTER BED,

Tymoszczuk, J.

Montreal, Quebec, Canada

Canadian Patent 948,335.  Applied August 10, 1971, Issued May 23, 1974.  Patent
Office Record, Vol. 102, No. 22, p 94, May, 1974.

A process is described for treating wastes in which the wastes are flowed
gravitationally, in sequence, through an activated sludge compartment.  Next
they flow through a single layer biological filter bed compound of filter
media which is aerated continuously from the bottom.  The same air is used to
aerate the activated sludge compartment containing a closed sludge concentrator.
This permits the removal of excess biological sludge.  The concentrator is used
to remove backwash effluent when the biological filter bed is being backwashed.

*Patents, *Waste treatment, *Activated sludge, Equipment, Sludge removal,
Aeration, Filter media

*Biological filter bed, Backwashing
212C

BOX FILTER,

Rosenberg, D. J.

Pall Corporation, Glen Cove, New York

United States Patent 3,815,754.  Applied September 16, 1974.  Issued
June 11, 1974.  Official Gazette of the United States Patent Office, Vol.
923, No. 2, p 551, June 11, 1974.  1 fig.

A disposable box filter is provided which comprises a box, houses at least
two portions, and has a fluid chamber with two fluid ports.  A filter element
in sheet form extends across the fluid chamber and is held at its sides by
the housing across the line of flow between the fluid ports.

*Patents, *Fllters,  Equipment, Flow control

*Box filter
                                        181

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213C

METHOD AND DEVICE FOR COLLECTING SUBSTANCES FLOATING IN
A LIQUID SURFACE,

Bergman, H. L.

Vallatorg, Stockholm, Sweden

United States Patent 3,817,385.  Applied April 1, 1971.  Issued June 18, 1974.
Official Gazette of the United States Patent Office, Vol. 923, No. 3, p 950-
951, June 18, 1974.  1 fig.

A method and an apparatus for collecting substances floating in a liquid sur-
face uses an endless, rotating conveyor band, one end of which is immersed
in the liquid.  A collecting band, which runs from a supply down into the
liquid, is also used and rests'on the conveyor band carrying with it sub-
stances floating in the liquid surface to a collecting device and receives
the collecting band and the substances transported on the band.  Thus,
substances in the liquid surface are lifted up from underneath and removed
out of the liquid by'the collecting band.

*Methodology, *Equipment, *Patents, Separation techniques

Collection systems, Liquid surfaces
214C

WASTE DISINTEGRATOR,

Bradley, E. H.

General Signal Corporation, New York, New York

United States Patent 3,815,827.  Applied September 11, 1972; Issued
June 11, 1974.  Official Gazette of the United States Patent Office, Vol. 923,
No. 2, p 570-571, June 11, 1974.

Under this patent, waste disintegrator for comminuting solid particles in a
fluid has a transverse wall in its housing.  The transverse wall has a cen-
tral opening through which the fluid is channeled and a comminuting means
is mounted in that opening.  A fluid bypass is formed in the transverse wall
in a peripheral area.  Covering this opening is a flapper valve that is
pivotally secured to the downstream side of the transverse wall.  The flapper
valve has one of its ends secured on a shaft that passes through a housing
wall of the disintegrator and to this shaft at its end is attached an arm.
A coil spring that has one of its ends secured to the housing and its other
to one end of the arm provides a relatively constant spring tension on the
arm.  This urges the flapper door to remain in its closed position or to
return to its closed position when the differential pressure across the
transverse wall diminishes to a predetermined level.  Also mounted on the
wall housing is a microswitch which is part of a warning signal circuit.
The switch is in engagement with the arm when the flapper door is closed
and it is under this condition that the switch is open.  As increased dif-
ferential pressure forces the flapper door open, the arm moves away from
the switch closing the circuit, which in turn activates the warning signal.

*Patents, *Waste treatment, Treatment facilities, Equipment, Valves, Flow
control, Waste disposal
                                       182

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215C

THIN WATERFALL SEPARATING AND SCREENING APPARATUS,

Ginaven, M. E.

The Bauer Brothers Company,
Springfield, Ohio

United States Patent 3,815,740.  Applied June 28, 1971.  Issued June 11,
1974.  Official Gazette of the United States Patent Office, Vol. 923, No. 2,
p 547, June 11, 1974.  1 fig.

This invention is directed to screen units and screen assemblies applied
primarily to the separation and reclamation of solids, particularly fibrous
solids, from a fluid slurry.  Each embodiment of the invention is
characterized by a screen section or assembly of screen sections having in
connection a feed system including a variable flow control means.  The
controls provided enable a directed initial feed of a slurry in a thin
waterfall form and in a manner whereby the initial engagement of the slurry
with the flow surface can be variably placed with an impact effect.  The
structural features provided enable oily, fatty and like adherent substances
to be optimally separated from the solids content of the slurry in movement
to and over the flow surface provided by the invention embodiments.

*Patents, *Separation techniques, *Screens, Solid wastes, Slurries, Equipment
216C

APPARATUS FOR AND METHOD OF AUTOMATICALLY REMOVING
POLLUTANTS FROM A FLOWING STREAM,

Dubouchet, J. L.

Societe Generale de Constructions Electriques et
Mecaniques, Grenoble, France

United States Patent, 3,815,742.  Applied March 23, 1972.  Issued June 11,
1974.  Official Gazette of the United States Patent Office, Vol. 923, No. 2,
p 547-548, June 11, 1974.  1 fig.

A patent was issued for a separator located alongside a liquid stream bed,
and a vertical liquid chamber communicating at its bottom with the bottom of
the separator.  Also included are means for permitting the discharge of liquid
from the upper portion of the chamber and means for discharging the separated
pollutant material collected in the separator.

*Patents, *Equipment, *Methodology, Automatic control, Separation techniques,
Streamflow, Water pollution control
                                        133

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2i7c

MULTI-CAPACITY WATER SAMPLER,

Nlskin, S. J.

Miami, Florida

United States Patent 3,815,422.  Applied June 4, 1973.  Issued June 11, 1974.
Official Gazette of the United States Patent Office, Vol. 923, No. 2, p 464, June
11, 1974.  1 fig.

A water sampler device for obtaining samples of ocean water at designated
depths consists of tubular members of identical shape and size clamped together
to form a receptacle of any desired capacity with a closure or valve for
both ends of the receptacle.  This is maintained away from the upper opening
to permit sea water to flow through the receptacle as it is lowered and sinks
to the desired depth of water.  Upon release of a messenger, the closures are
released simultaneously whereby the lower closure passes through the upper
opening to become seated on the lower opening while the upper closure seats on
the upper opening to be locked in position by cams.  The weight of the water
trapped in the receptacle maintains the lower cap in a sealed position on the
lower opening as the sampler is brought to the surface of the ocean.

*Patents, *Water sampling, Sea water, Equipment
 218C

 FILTER FOR REMOVING  SUCH PARTICLES AND MISCELLANEOUS
 DIRT AS  CONTAINED  IN A FLUID,

 Hamano,  T.

 Ichikawa, Chiba Prefecture, Japan

 United States Patent 3,815,341.  Applied September 14, 1971.   Issued June 11,
 1974.  Official Gazette of the United States Patent Office, Vol. 923, No. 2,
 p  442-443, June 11,  1974.  1 fig.

 A  filter consists  of a base member, which is a coarsely woven  or knitted
 fabric or reticulated material with flocked fibers on the surface.  The
 process  of preparation consists of first applying an adhesive  onto the
 base member, in a  manner not to fill the meshes, and then applying the flock
 fibers.  The adhesive is preferably applied in sufficient amount to give a
 layer of 0.3 mm-0.6mm, with a base cloth which is removed after the fibers
 have been fixed.

 *Patents, *Filters,  Equipment, Filtration, Construction materials, Waste
 treatment, Fibers
                                         184

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219C

SEWERAGE TREATMENT SYSTEM,

Delaney, R. E., and Cornish, A. H.

Koehier-Tlayton Incorporated,
New Britain, Connecticut

United States Patent 3,815,159.  Applied November 8, 1972.  Issued June 11,
1974.  Official Gazette of the United States Patent Office, Vol. 923, No. 2,
p 395, June 11, 1974.  1 fig.

A sewerage treatment system comprises a toilet, a bathing facility, first and
second recirculating tanks each including filtering media, means for
selectively directing the effluent flushed from the toilet into the receptacle
compartment of either recirculating tank, means for selectively directing
the effluent from the bathing facility into either recirculating tank, means for
selectively draining either recirculating tank, means for selectively
recirculating the liquid in the filtrate compartment of either recirculating
tank to the toilet for flushing means for operating the system in a first mode
of operation, means for alternately operating the system in a second mode of
operation.  Included also are means for draining the first recirculating tank
and for switching the system from the first mode of operation to the second
mode of operation.

*Sewage Treatment, *Patents, *Treatment facilities, Equipment

Toilet
220C

AEROBIC SEWAGE TREATMENT SYSTEM,

Yost, K. J.

Coate Burial Vault Incorporated,
West Milton, Ohio

United States Patent 3,817,858.  Applied April 5, 1972.  Issued June 18,
1974.  Official Gazette of the United States Patent Office, Vol. 923, No. 3,
p 1067, June 18, 1974.  1 fig.

Liquid sewage from an individual residence is directed tangentially into a
large, flat, and shallow aerobic settlement tank to expose a large surface
area of the sewage per unit volume.  Air is circulated over the surface of
the sewage in a generally spiral direction to effect circulation or turbulence
of the sewage within the tank and diffusion of the air into the liquid.  The
air flow within the tank is produced by connecting the air intoutlet of the tank
to a chimney which projects upwardly adjacent to the outer wall of the residence
and creates a natural draft.  The liquid treated in the aerobic settlement
tank is directed into a similarly shaped aerobic digester and clarifier tank
which also provides for circulation of the treated liquid and diffusion of the
air.  The second tank defines an annular clarifier chamber which receives
the treated liquid before it is discharged.  The discharged effluent may be
directed through a chlorinator formed by a vertical housing which receives a
supply of chlorine crystals.

*Patents, *Sewage treatment, Aerobic treatment, Liquid wastes, Equipment,
Treatment facilities
                                        185

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221C

TREATMENT OF WASTEWATER,

Torpey, W. N.

Autotrol Corporation,
Milwaukee, Wisconsin

United States Patent 3,817,857.  Applied September 29, 1972.
Issued June 18, 1974.  Official Gazette of the United States  Patent Office,
Vol. 923, No. 3, p 1066-1067, June 18, 1974.  1 fig.

The process and apparatus for the oxidation of carbonaceous and nitrogenous
matter in waste water by use of a mixture of biologically active slimes
attached to partially submerged rotating contactors are described.  The
biological contactors are mounted in a single-stage treatment unit and are
supplied with waste water at a controlled rate relative to the surface of the
contactors and distributed substantially evenly over the contactor surface.  A
denitrifying unit, located upstream from the single-stage treatment unit
utilizes biologically active slimes attached to rotating biological contactors
for the removal of carbonaceous matter from the waste water supported by
nitrate oxygen from the recirculated effluent.

*Patents, *Waste water treatment, *0xidation, Equipment, Treatment facilities,
Carbon compounds, Nitrogen compounds, Biological treatment, Denitrification
OIL/WATER SEPARATOR FILTER,

French Patent 2196-187.  Applied August 16, 1973.  Issued April 19, 1974.
Derwent French Patents Abstracts, Vol. 5, No. 20, 1974.

A patent was granted for an oil/water separator filter.  The filter element
consists of a fibrous core in an outer sheath.  The core is made of fibers
coated with a synthetic resin having a higher affinity for oil than for
water.  The fibers in an upper section are of textile material laid up
in thin layers with the fibers side by side and transverse to flow direction.
The resin coating acts as binder within the layers, loosely piled one on the
other.  A lower section significantly thicker than the above layers, consists
of randomly oriented glass fiber or mineral wool.

*Patents, *Filters, *Separation, Textiles, Fibers, Resins

*0il/water separator filter, Oil-water separation, Mineral wool, Glass fibers
                                          186

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223C

WASTEWATER CONCENTRATION,

Talley, W. J. and Wright, H. W.

Sweco, Incorporated, Los Angeles, California

Canadian Patent 948,119.  Applied June 1, 1971.  Issued May 28,  1974.
Patent Office Record, Vol. 102, No. 22, p 47-48, May, 1974.

A patent was issued for equipment and methods for screening and  concentrating
waste water overflow from combined sewer systems.  The equipment includes a
separator employing a cylindrical rotating screen.  Influent is
piped upwardly into the equipment and deflected outwardly toward the inner
surface of the screen.  This manner achieves a desired flow rate and flow
pattern of the influent onto the screen.  The screen is rotated  at a speed to
achieve a desired centrifugal force.  Effluent passes through the screen to an
outlet and the remaining concentrate passes to an outlet.  A certain amount
of the influent splashes from the inner surface of the screen.  This is
received by a backsplash pan and may be recirculated and rescreened.  The
screen has several removable screen panels for replacing damaged screens or
changing screen type or mesh size.  Cleaning is provided by directing a cleaning
fluid periodically at the screen.  The manner in which the influent, effluent,
concentrate and backsplash are handled, and manner in which the  influent is
screened for ultimate disposal is detailed.  A sequence of influent feed and
screen cleaning is also described.

*Patents, *Combined sewers, *Waste water, *0verflow, Screens, Flow rate,
Effluents, Outlets, Influent streams, Cleaning, Centrifugation
224C

LIQUID PURIFICATION ION-EXCHANGE EQUIPMENT,

Van Wijk and Boerma Water

German Patent 1767-705.  Applied June 7, 1968.  Issued April 25, 1974.
Derwent German Patents Abstracts, Vol. 5, No. 18, p 1, June 7, 1974.

Equipment was patented which includes concentric perforated walls which
enclose annular space and contain active resin granules.  A first manifold
chamber is enclosed centrally by the inner perforated wall.  A second,
annular manifold chamber is between the outside perforated wall and the
cylindrical casing.  The flow of water/liquid being treated is radial either
inwards or outwards.  The outer perforated wall extends for most of the
height of the casing.  The apparatus performs liquid purification, using ion
exchange.

*Ion exchange, *Patents, *Equipment, Flow, Water purification

Manifold chamber, Perforated walls, Active resin granules
                                       137

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225C

LAND DRAINAGE PIPE COUPLING,

Khomylov, G. S., Kozlovchunas, E. F., and Mysin, A. V.

A. A. Skochlniskii Mining Institute,
H. S. S. R.

U.S.S.R. Patent 393398.  Applied December 21, 1970.  Issued December 12,  1973.
Soviet Inventions Illustrated, Vol. 5, No. 19, 1974.

A land drainage pipe coupling was patented with segmented seals which lower
resistance to infiltration or water.  This pipe coupling is used for land
reclamation systems and is built up from L.D. or H.D. polyethylene or P.V.C.
segments.  These form domed covers of glass fiber alternating with beaded
gaskets.  The segments are located in holes drilled around projections of
the pipe.  Moisture penetrates the domed covers and passes through the slight
gaps present between the projections.  Improved access to water means that
a reduced number of collection pipes is required as compared with the more
conventional designs.

*Patents, *Design criteria, *Pipes, *Land reclamation, *Land drainage,
Drainage, Equipment

PVC, Pipe coupling
22 6C

STREET DRAIN FOR USE WITH A SEWER SYSTEM,

Thompson, L. B.

South Bend, Indiana

United States Patent 3,815,749.  Applied April 23, 1973.  Issued June 11, 1974.
Official Gazette of the United States Patent Office, Vol. 923, No. 2, p 549,
June, 1974.  1 fig.

A street drain is used with a sewer system and includes a water collection
basin, positioned in the street, and a dry well generally located adjacent
to the street.  The collection basin has two discharge openings.  One of the
openings is placed in communication with the dry well, the other is placed
in communication with the sewer system.  The basin discharge opening which
is connected into the sewer system is located so that water, such as storm
water, entering the collection basin will first pass into the dry well
until the dry well is filled and then will pass into the sewer system.

*Patents, *Drains, *Sewers, Roads, Drainage systems, Storm water

Collection basins, Dry wells
                                      188

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227C

PROCESS FOR THE REMOVAL OF SOLID PARTICLES FROM AN AQUEOUS
SUSPENSION THEREOF AND APPARATUS THEREFOR,

Visser, P., and Haar, L. W.

Shell Internationale Research Maatschappij N. V.,
The Hague, Netherlands

Canadian Patent 948,518.  Applied October 13, 1970.  Issued June 4, 1974.
Patent Office Record, Vol. 102, No. 23, p 37, June, 1974.

A process removes solid particles by adding a water-immiscible, auxiliary
liquid to the suspension and separating a resulting mixture of solid
particles and auxiliary liquid from a water phase.  The auxiliary liquid
is supplied in two stages by adding:  a minor part of the water-immiscible
auxiliary liquid to the aqueous suspension in a mixing stage and imparting
a turbulent motion to form agglomerates of solid particles and auxiliary
liquid in water; and a major part of the auxiliary liquid to the mixture of
agglomerates in water in a separating stage, in which stage a bottom layer
of water and a top layer of auxiliary liquid comprising the agglomerates
are formed.

*Patents, *Separation techniques, Solid wastes, Waste treatment, Methodology,
Equipment
228C

SYSTEM FOR MEASURING BOD BY ELECTROLYSIS,

Young, J. C.

Iowa State University Research Foundation, Incorporated,
Ames, Iowa

Canadian Patent 947,819.  Applied June 6, 1972.  Issued May 21, 1974.
Patent Office Record, Vol. 102, No. 21, p 79, May, 1974.

A reaction vessel containing the sample receives a container of material
for absorbing C02 which is provided with an adaptor.  An electrolysis cell
storing the electrolyte is received in the adaptor.  A cap is placed on
the electrolysis cell with an upper circular covering flange spaced from
the walls of the cell thus providing an annular space communicating with
the electrolyte.  This permits venting of hydrogen while minimizing
evaporation of the electrolyte.  When the level of the electrolyte falls
below a predetermined minimum, indicating a low 02 pressure in the vessel,
a sensing switch energizes a regulated DC current source to start the
electrolysis process to replace the 02 consumed by the sample.  The system
is insensitive to changes in line voltage and electrolyte strength over a
design range.  Apertures in the cap member and the cell may be selectively
aligned by twisting the cap to equalize the pressure in the cell with
atmospheric pressure before starting.

*Patents, *Measurement, *Biochemical oxygen demand, *Electrolysis
                                            189

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229C

DOMESTIC SEWAGE TREATMENT PLANT,

Stone, J. S.

Sanitary Disposal Systems, Incorporated,  Wheat Ridge,
Colorado

Canadian Patent 948,798.  Applied August  14,  1972.   Issued June 4,  1974.
Patent Office Record, Vol. 102, No. 23, p 97,  June,  1974.

The plant comprises a cylindrical tank having an inner truncated conical
baffle in the tank, spaced from the top,  bottom, and side  walls of  the
tank.  The top lip of the baffle is positioned below the normal liquid
level within the tank.  An outer truncated conical  baffle  is positioned
concentrically outside the inner baffle.   The bottom end of the outer
baffle is coextensive with that of the inner baffle, but the top end
extends above the tank's normal liquid level.  The  two baffles form an
annular upflow passage between them.  Air inlets are provided to admit
air into the bottom end of the upflow passage.  A sewage inlet admits
sewage into the top end of the inner baffle.   The introduction of air
into the upflow passage causes the upward movement  of air  and liquid in
the manner of an air-lift pump.  The pump discharges back  into the  inner
baffle with a downward thrust.  The continuous circulation of solids in
this manner results in a reduction of their size, so that  they are  prepared
for further treatment.

*Patents, *Sewage treatment, *Treatment facilities,  Equipment, Domestic
wastes
 230C

 SANITARY DRAINAGE SYSTEM,

 Carlson, H. B., and Pinezich, J. R.

 Andrew Carlson and Sons, Incorporated,
 Kings Park, New York

 United States Patent 3,817,864.  Applied June 2, 1972.  Issued
 June 18, 1974.  Official Gazette of the United States Patent Office,
 Vol. 923, No. 3, p 1068, June 18, 1974. 1 fig.

 A novel and improved sanitary drainage system was patented.  The
 Septic tank of the system is fabricated from Fiberglas which has
 advantages over the use of pre-cast concrete or other material pre-
 viously used.  It is non-corrosive, impervious, and light and strong
 with some flexibility.  The Fiberglas septic tank has a generally
 hemi-spherlcal, furstoconical or polygonal shape.

 *Patents, *Septic tanks, *Sanitation, *Drainage, Materials,
 Precast concrete construction

 *Sanitary drainage system, *Fiberglas
                                    190

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231C

WASTE TREATMENT SYSTEM,

Milotich, F. J.

General Electric Company,
New York, New York

United States Patent 3,819,053.  Applied October 2, 1972.  Issued
June 25, 1974.  Official Gazette of the United States Patent
Office, Vol. 923, No. 4, p 1378, June 25, 1974.  1 fig.

The bottom of a solids separating tank treats sewage which has been ground,
macerated, and treated with a coagulant.  Solids accumulate in a si idge
blanket below a screen which divides the tank into upper and lower
portions.  Clear liquid passes throughthe blanket and screen.  Sludge
from the sludge blanket is pumped to a sludge concentrating tank where
further liquid is extracted.  The concentrated sludge is periodically
pumped out for incineration or other disposal.

*Patents, *Waste treatment, *Coagulation, *Sewage treatment,
Tanks, Screens

*Sludge blanket
232C

TREATMENT OF SEWAGE OR CONTAMINATED WATER,

Swales, D. A.

Albright and Wilson Limited, Oldbury,
Warwickshire, England

United States Patent 3,814,686.  Applied November 17, 1971.
Issued June 4, 1974.  Official Gazette of the United States
Patent Office, Vol. 923, No. 1, p 264, June 4, 1974.

A method for removing suspended solids from contaminated water by the
addition of a coagulant composition is detailed.  The coagulant composition
is prepared by digesting chrome residue containing 35 to 40 percent by
weight of Fe203, 27 to 32 percent A1203, 13 to 18 percent MgO, and 12
to 17 percent Cr203 with a strong mineral acid selected from the group
consisting of 20 to 36 percent by weight hydrochloric acid and 20 to 100
percent by weight sulfuric acid.  This process forms a solution of
metal salts containing trivalent iron, aluminum, and chromium ions
and magnesium ions.

*Sewage treatment, *Suspended solids, Coagulation, Acidity, Removal

*Contaminated water, Chrome residue
                                       191

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23 3C

SEWER RELIEF VALVE,

Oberholtzer, J. V.

Dallas, Texas

United States Patent 3,815,629.  Applied October 26, 1972.  Issued
June 11, 1974.  Official Gazette of the United States Patent Office,
Vol. 923, No. 2, p 518, June 11, 1974.  1 fig.

A patent was granted for a sewer relief valve for installation in the
cleanout connection to a sewer line.  A flapper opens to release
sewage water when the water rises in the sewer line.  This flapper
is self-closing when the water pressure has been relieved on the line
so as to seal the gases in the sewer line.  The valve unit is molded
of a relatively rigid plastic material.  The sealing face of the
flapper is formed of a softer inserted piece of nylon plastic and
forms a gas type seal to the sewer line when the valve is in the
normally closed position.

*Patent, *Sewers, *Water pressure, Installation, Plastics

*Sewer relief valves, Sewer lines
 234C

 SINGLE BASIN AERATED SEWAGE LAGOON WITH SPRING TIME
 INTENSIFIED AERATION,

 Murphy, D. S.

 Atara Corporation,
 Montreal, Quebec,  Canada

 Canadian Patent  948,334.  Applied September  8, 1970.
 Issued May 28, 1974.  Patent Office Record,  Vol. 102, No. 22,
 p  93-94, May 28,  1974.

 An aerated sewage lagoon provides a much increased earation in the
 spring, reduced  aeration in the  summer, and  still further reduction
 in the winter.   In winter there  is an area of high intensity aeration
 near the sewage  intake, and little or none elsewhere.   In spring
 there is a second high intensity area to cope with the  suddenly
 increased demand due to winter dormancy.  In summer  the high inten-
 sity aeration  is followed by an  area over which the  aeration conti-
 nues but at gradually reduced intensity as the sewage moves down-
 stream to the  outflow.

 *Patents, *Sewage lagoons, *Aerated lagoons, *Aeration,
 Seasonal, Sewage treatment, Streams, Basins

 Winter, Summer,  Spring season
                                       192

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235C

PROCESS FOR TREATMENT OF WASTE LIQUIDS CONTAINING
DIFFICULTLY DECOMPOSABLE CYANO-COMPLEX,

Ichiki, M., and Ishii, M.

Mitsui Mining and Smelting Company,
Tokyo, Japan

United States Patent 3,816,275.  Applied February 8, 1973.
Issued June 11, 1974.  Official Gazette of the United States
Patent Office, Vol. 923, No. 2, p 673, June, 1974.

A process for treating a waste liquor containing a difficultly
decomposable cyano-complex such as ferrocyanldes and ferrie-
yanides and/or cyano ions is described.  It comprises electrolyzing
the waste liquor by employing iron as an anode to form a water-
insoluble colloid.  The colloid is floated and concentrated by
an action of bubbles formed during the electrolysis.  The material
is converted to a scum, and the scum is removed from the waste liquor
in an electrolytic cell.  A purified liquor free of cyano-component is
obtained.
*Patents, *Colloids, *Scum, Iron, Floating

*Cyano-complexes,  Waste liquor, Anodes, Electrolytic cells
236C

METHOD AND APPARATUS FOR SEPARATION OF SLUDGE,

Sako, F. F., and Chandler, S. S.

FMC Corporation

United States Patent 3,822,204.  Applied June 12, 1970.  Issued
July 2, 1974.  Official Gazette of the United States Patent
Office, Vol. 924, No. 1, p 107, July, 1974.

An apparatus was designed for separating a sludge-containing
liquid medium produced by the processing of sewage into a
clarified liquid and a sludge concentrate.  Companion electrodes
in the bottom of the container produce gas by electrolysis
of water.  The water rises as dispersed bubbles and upon
occlusion to sludge particles floats the particles to the
liquid surface.  Sludge concentrate floating adjacent to the
surface of the liquid medium is moved out of the container
by a skimmer.  Clarified liquid is discharged from the
lower portion of the container.

*Patents, *Sewage, *Clarification, *Sludge,
*Electrolysis, Liquids, Floating
                                          193

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237C

REMOVAL OF DISSOLVED OR SUSPENDED SOLIDS IN WASTE WATER,

Anderson, H. T.

Swift and Company,
Chicago, Illinois

United States Patent 3,816,274.  Applied October 20, 1971.
Issued June 11, 1974.  Official Gazette of the United States
Patent Office, Vol. 923, No. 2, p 673, June, 1974.  1 fig.

Waste water containing oil and water emulsions and dissolved
or suspended solids is de-emulsified and clarified by creating
a three dimensional anolyte stream.  It was designed by care-
ful placement of anodes and by impressing direct or galvanic
current through the water.  Waste water is first contacted
with an anode system in a restricted zone so as to give sub-
stantially all of the waste water a rapid p change of several
units.  Water is then conveyed to a second zone where a three
dimensional anolyte stream is formed causing the oily particles
to float to the surface of the water where they can be skimmed
off.

*Dissolved solids, *Emulsions, Oily water, Waste water

*Anodes, *Anolyte stream, pH changes
238C

CLARIFICATION OF TAR SANDS MIDDLINGS WATER,

Schutte, R.

Gulf Oil Canada Limited,
Atlantic Richfield Limited, Canada

United States Patent 3,816,305.  Applied December 23, 1971.
Issued June 11, 1974.  Official Gazette of the United States
Patent Office, Vo. 923, No. 2, p 678, June, 1974.

A patent was issued for a process which involves the addition
of  an acid to water to accelerate clarification of the water
and to reduce required sludge settling pond area.  This process
is  useful for treating tar sands to cause flocculation or
coagulation of the clays and other small solids particles
produced from the hot water process and present in middlings
and tailings streams.

*Flocculation, *Coagulation, *Clays, Waste water treatment,
Settling ponds

*Tar sands, Middlings, Tailing streams
                                      194

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239C

METHOD AND APPARATUS FOR DETECTING PARTICULATE
MATERIAL IN FLOW STREAM,

Baldwin, W. F., and Mullins, L. D.

Mobil Oil Corporation,
New York City, New York

United States Patent 3,816,773.  Applied October 12, 1972.
Issued June 11, 1974.  Official Gazette of the United States
Patent Office, Vol. 923, No. 2, p 771, June, 1974.

A system was patented for detecting the presence of particulate
material such as sand, in a fluid stream flowing through a
conduit.  The system comprises an acoustical probe which is
positioned directly into the flow stream.  The probe has a
housing in which a transducer  (piezolectric crystal) is sus-
pended.  The housing is filled with oil to acoustically
couple the transducer to the housing.  Particulate material
in the flow stream gives up kinetic energy upon striking
the housing of the probe which in turn excites the transducer
to generate an output signal having a representative frequency
component.  The system includes circuitry which amplifies
and filters the output signal  to provide an alarm, activated
when a certain sand content condition in the flow stream is
exceeded.

*Patents, *Flow, *Fluids, *Sand, Automation, Systems

*Particulate matter, Detection
240C

SEWAGE AND EFFLUENT TREATING SYSTEM,

Briltz, R. P.

Canadian Patent 951,035.  Applied July 6, 1971.  Issued July 9, 1974.
Patent Office Record, Vol. 102, No. 28, p 96-97, July, 1974.

A patent was issued for a sewage and effluent treatment system.
Effluent is pumped from the primary sewage treatment location
through an agitating module at which time a flocculating agent
is introduced into the sewage.  This module includes a casing,
an intake header at one end, an outlet baffle chamber at the
other end, and a plurality of conduits extending between the
header and chamber.  The sewage and flocculent are agitated
and thoroughly mixed in this flocculent module, and the maj-
ority of the flocculated material is separated out by baffles.
The deflocculated effluent then passes to conventional first
and second stage filtering tanks.  Means are provided to
back flow the modules to remove the flocculated material
and cleanse the modules when necessary.

^Patents, *Effluents, *Sewage treatment, Pumping, Flocculents,
Conduits, Canada
                                       195

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241C

OIL SPILL RECOVERY VESSEL,

Netherlands Patent NL 7315-128.  Applied November 5,  1973.
Issued May 8, 1974.  Netherlands Patent Report,  Vol.  5,  No.  21,  p 1,
June 28, 1974.

Oil floating on water is recovered using a vessel with a cyclone
chamber into which a skimmed layer is admitted via a  lateral
opening, one edge of which is defined by an adjustable skimmer
or weir plate, the inflow to the chamber being solely dependent
on the translational speed of the vessel.  The oil is tapped
from the larger diameter end of the chamber while separated
water is discharged from the smaller diameter end.  The chamber
may have a horizontal or vertical axis.

*Patents, *0il spills, *Recovery, Pollution abatement, Equipment,
Oil, Floating, Weirs

Netherlands
242C

CLARIFYING TANK FOR EFFLUENTS,

German Patent DS 1658-054.  Applied May 10, 1967.  Issued
May 16, 1974.  German Patent Abstracts, Vol. 5, No. 21, p 1,
June 28, 1974.

A patent has been issued for clarifying tank for effluents
which consists of a flocculation space, surrounded by a ring
on which rests the vessels containing the flocculant fluid
bed and the solid filter.  This supporting ring has passages,
and covers a flushing trough.  Flushing holes join the latter
to the passages to keep them clean.  An external girder
ring supports the ring.

*Patents, Clarification, *Tanks, *Effluents, Flocculants, Filters,
Equipment
                                      196

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243C

PRECIPITATING AGENT FOR WATER PURIFICATION PROCESSES,
AND A METHOD OF PREPARING SAME,

Kawert, K. G. K.

Aktiebolaget Gullhogens Bruk,
Skovde, Sweden

United States Patent 3,827,984.  Applied June 1, 1972.  Issued
August 6, 1974.  Official Gazette of the United States Patent
Office, Vol. 925, No. 1, p 240-241, August, 1974.  1 fig.

An agent for purification of water by precipitation, and a
method for preparing this precipitating agent has been patented.
The water is purified to such an extent that raw water becomes
potable and suitable for cooking and food preparing, and
sewage must be cleaned so that it can be released into receiving
waters with no deleterious effects.  The substances to be re-
moved are primarily iron, manganese, aluminum and various
phosphates, but the water may also contain copper, lead and
mercury.  The precipitating agent comprises a mixture of
minerals which, after a previous burning, have different
solubility products.  The mixture has a mole ratio of 1.0-
5.0 between basic and acid oxides, and a content of 5-40 percent Si02,
5-15 percent A1203, 3-12 percent Fe203, 15-70 percent CaO and 0.1-20
percent MgO in an ignited sample.  In the preparation of the precipitating
agent sufficient mineral formation is obtained, and the burnt mixture
contains minerals of different solubility products having a mole ratio
between basic and acid oxides of 1.0-5.0 and the above-mentioned analysis
data.  The product is subsequently ground to a powder having a fineness of
10-20 percent by weight greater than 60 micrometers and 0-2 percent by
weight greater than 90 micrometers.

*Patents, *Water purification, *Potable water, Metals, Minerals
Solubility, Precipitation (Chemical)
244C

WATER TREATMENT FILTER BED FOR SEWAGE SYSTEMS,

Bergles, J. L. , and Nelson, M. A.

United States Patent 3,823,825.  Applied June 15, 1973.  Issued
July 16, 1974.  Official Gazette of the United States Patent Office,
Vol. 924, No. 3, p 543, July, 1974.  1 fig.

A patent was granted for a trickle-type water treatment filter bed
formed in the ground for receiving water of a sewage plant.  Its
absorption bed has a drain wall around its sides, and functions
to prevent saturation of the absorption bed.  The drain wall
means for the absorption bed is useful in soils of poor perme-
ability.  The drain walls have tile means located at a depth
lower than the tile means in the absorption bed.  The drain
walls function to prevent surface water from running into the
absorption bed and contributing to its saturation, and also
function to drain off excess water in the absorption bed to
permit the absorption bed to function properly.

*Patents, *Water treatment, *Filters, *Sewage treatment, *Absorption,
Sewage systems

*Treatment plants, Trickle-type filters
                                          197

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245C

STRAINER DEVICE FOR LIQUIDS,

LeBlanc, H. P.

United States Patent 3,823,831.  Applied November 19, 1971.  Issued
July 16, 1974.  Official Gazette of the United States Patent Office,
Vol. 924, No. 3, p 545, July, 1974.  1 fig.

An invention for straining has been patented.  It relates to an
in-line strainer without interrupting the fluid flow, meanwhile
allowing backflushing.  The strainer device comprises a ball-
shaped strainer element rotably mounted within a strainer body,
the strainer element being provided with an inlet into which
the debris containing fluid is directed.  The debris is con-
tinuously collected within the ball-shaped strainer element.
Screen closure means are provided within the strainer element
whereby its inlet can be closed off to retain the debris
within the strainer element which is back flushed by rotation.
During rotation the fluid stream is continued to be strained.
Clean out means are provided in conjunction with the ball-
shaped strainer element whereby the debris can be collected
in a sump resevoir, after which the ball-shaped strainer
elements is returned to its normal straining position.

*Patents, *Liquids, *Solids, *Separation, *Strainers, Equipment,
Flow, Waste water treatment
24 6C

TARGET SYSTEM FOR LAYING SEWER PIPES,

Roodvoets, R. J., and Stapert, J. Jr.

Laser Alignment, Incorporated,
Grand Rapids, Michigan

United States Patent 3,815,250.  Applied September 30, 1971.  Issued June 11, 1974.
Official Gazette of the United States Patent Office, Vol. 923, No. 2, p 419, June
11, 1974.  1 fig.

An adjustable target is described which has use in aligning pipes with a laser
beam or an other similar collimated light beam which is projected axially with the
pipe.  The target has a base member, a level carried by the base member, and an
upright target carried by and vertically adjusted relative to the base.  Extension
means for the base member extend the base laterally to permit the target to be
employed in larger pipes.

*Patents, *Sewers, Pipes, Installation, Equipment

*Sewer pipes, *Lasers
                                          198

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247C

PROCESS FOR THE REACTIVATION OF POWDERED CARBON,

Corson, F. L.

CPC International Incorporated,
Englewood Cliffs, New Jersey

United States Patent 3,816,338.  Applied February 8, 1971.  Issued June 11, 1974.
Official Gazette of the United States Patent Office, Vol. 923, No. 2, p 683-684,
June 11, 1974.  1 fig.

A process was patented which describes a method for the reactivation of spent
powdered carbon for purification of waste waters as well as other liquids.  The
invention describes a continuous process for the reactivation of spent powdered
carbon containing adsorbed organic matter.  Particle sizes are smaller than about
100 mesh, and have a reactivation efficiency of at least about 80 percent, and a
product yield of at least about 90 percent by weight.  This process comprises
dispersing the spent carbon in water to form an aqueous suspension with a solids
content of from about 20 percent to about 35 percent by weight.  The suspension
is atomized with steam and the atomized suspension is passed in an atmosphere
substantially free of oxygen through a radiantly heated reactor vessel, with a
wall temperature of from about 1200 F to about 1900 F.  A time period of from
about 5 to about 30 seconds is used.  The carbon to and from the reactor is
handled in a slurry form, which eliminates dust losses.

*Patents, *Carbon, *Liquids, Purification, Waste water, Organic matter, Suspension,
Slurry

*Reactivation
 248C

 UNIVERSAL BASIN FOR USE  IN A SEWER SYSTEM,

 Johannessen,  J.  M.

 Pontoppidan Sorensen,  Solrod Strand,  Denmark

 United  States Patent 3,815,748.  Applied  September  26,  1972.   Issued  June  11,  1974.
 Official Gazette of the  United  States Patent  Office, Vol.  923, No.  2, p 549, June  11,
 1974.   1 fig.

 A patent was  issued for  a  basin  to be used  in a sewer system.  The  equipment has
 a draining device designed as a  cover and consists  of a housing with  a submerged
 inlet opening and a centrally located outlet  opening.   The housing  contains an
 outlet  chamber with a  circular or  helical sidewall.  An inlet  tube  opens tangen-
 tially  along  this sidewall into  the outlet  chamber.  When  the water level  in the
 basin rises,  the water flowing into the outlet chamber  circulates so  that  it works
 as a centrifugal brake and retards the water  flow.

 *Patents,  *Equipment,  *Sewers, *Baslns, Flow

 *Sewer  systems
                                      199

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249C

FLUID FILTER,

Firth, R. L.

Donaldson Company, Incorporated,
Minneapolis, Minnesota

United States Patent 3,819,052.  Applied September 15, 1972.  Issued June 25, 1974.
Official Gazette of the United States Patent Office, Vol. 923, No.  4, p 1377, June
25, 1974.  1 fig.

A fluid filter was patented where a first cylindrical filter housing has an open
top and is at least partially surrounded by a second housing.  This forms a passage-
way.  A baffle with a central opening is mounted in the open top and a cylindrical
filter element is biased against the baffle member in the first housing.  A dome-
shaped cover is attached on top of the second housing to provide a flow path for
fluid into the filter element.  This gives passage through the filter element and
then through an opening in the second housing.  A combination bypass-indicator
member is attached to the top of the movable filter element for guided sliding
movements in the central opening of the baffle member.

*Filters, *Patents, Equipment, Flow, Liquids

*Fluid filters
 250C

 PROCESS FOR TREATING WASTES CONTAINING CHROMATES AND/OR
 COMPLEX IRON CYANIDES,

 Henley, T. D., and Reeves, R. F.

 Amchem Products, Incorporated,
 Ambler, Pennsylvania

 United States Patent 3,819,051.  Applied August 31, 1972.  Issued June 25, 1974.
 Official Gazette of the United States Patent Office, Vol. 923, No. 4, p 1377, June
 25, 1974.

 Dissolved hexavalent chromium and dissolved complex iron cyanide [Fe(CN)6] are
 removed from a liquid waste effluent by adding a reducing agent with an anion
 capable of reducing the hexavalent chromium to trlvalent chromium and a cation
 which forms a solid or precipitate with the complex iron cyanide.  The preferred
 reducing agent is zinc hydrosulfite (ZnS204).

 *Waste treatment, *Patents, *Liquid wastes, Effluents, Anions, Precipitates

 *Chromates, *Iron cyanides
                                       200

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251C

METHOD OF MAKING AND PIPELINE TRANSPORTING A NON-CORRO-
SIVE SULPHUR-WATER SLURRY,

Horvath, R. J.

Canadian Patent 950,944.  Applied September 27, 1971.  Issued July 28,  1974.
Canada Patent Office Record, Vol. 102, No. 28, p 76, July, 1974.

A method of making and transporting a sulphur-water slurry by pipeline
is described.  This maintains a non-corrosive and non-clogging process
by keeping a passivating film of ammonia between the sulphur-water slurry
and the interior wall of the pipeline or contacting equipment.  Ammonia
is injected into the slurry line under such conditions that a passivating
film of ammonia is maintained between the interior of the pipeline wall
and the sulfur-water slurry transported in the pipeline.   By this pre-
caution, hot corrosion and clogging of the pipeline can be inhibited or
prevented.

*Patents, *Pipelines, *Slurries, Ammonia, Equipment

*Sulphur-water slurries, Transport
252C

POLLUTED WATER PURIFICATION,

Box, E. O., and Farha, F.

United States Patent 3,823,088.  Applied March 2, 1973.  Issued July 9, 1974.
Official Gazette of the United States Patent Office, Vol. 924, No. 2, p 342,
July, 1974.

Organically polluted waters are purified by contacting them with a
catalyst of zinc aluminate promoted with at least one metal active
for initiating oxidative reactions in the liquid or gaseous phase
under oxidizing conditions.  In one case, an aqueous stream obtained
from the effluent of an oxidative dehydrogenation containing contami-
nating oxygen-containing organic materials was subjected to oxidizing
conditions in the presence of a promoted zinc aluminate catalyst.  This
converted the water to a potable aqueous product.

*Patents, *Water purification, *Water pollution control,
Oxidizing, Oxygen, Potable water
                                        201

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253C

METHOD AND APPARATUS FOR LAYING A PIPELINE,

Menzel, R.

United States Patent 3,827,155.  Applied July 27, 1972.   Issued August
6, 1974.  Official Gazette of the United States Patent Office, Vol. 925,
No. 1, p 33, August, 1974.  1 fig.

A method and apparatus for laying a pipeline in which the pipes are
aligned along a preselected path with a collimated light beam is de-
scribed.  Air is forced through the pipeline in a helical spiral to
prevent gases from building up within the pipeline as the pipes are
being laid.  A blower unit coupled to an outlet nozzle has a clamp for
clamping the nozzle to the pipe at an angle to the longitudinal axis
of the pipe.

*Patents, Pipelines, Equipment, Pipes

*Collinated light, Pipelaying
254C

METHOD AND APPARATUS FOR LAYING A PIPELINE,

Roodvoets, R. J., and Applegate, M. J.

United States Patent 3,827,156.  Applied September 30, 1968.  Issued
August 6, 1974.  Official Gazette of the United States Patent Office, Vol.
925, No. 1, p 33, August, 1974.  1 fig.

A method is described relating to the apparatus for laying a pipeline
in which the pipes are aligned along a preselected path with a collimated
light beam.  Air is blown through the pipeline as the pipes are being
laid to prevent the build up of gas within the pipeline.  A blower unit
and a flexible conduit are provided for this purpose.

*Patents, *Pipelines, Pipes, Equipment

*Pipelaying
                                         202

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 255C

 AUTOMATED FLUID  INJECTOR,

 Harris, R. J.

 United States Patent  3,824,859.  Applied February  16, 1973.   Issued July  23,
 1974.  Official  Gazette of  the United States Patent Office, Vol. 924, No.
 4,  p  818-819, July, 1974.   1  fig.

 An  apparatus was  patented for accurately measuring and  injecting quantities
 of  fluid specimens, or samples, as received from a flowing sampled stream,
 into  various media.   Such media include a receptacle or inlet of a modern
 analytical instrument.  The automatic fluid injector, or continuous flow
 analyzer, is comprised of:  a support means; a  tubular  mounting member,
 generally mounted on  the support means; a needle syringe, including a
 barrel and a plunger  reclprocable within the barrel, and the bore of a
 needle for insertion  into the axial opening; and an associated cylinder
 piston unit, the  needle syringe of which is mounted on  the forward end of
 the piston.  Both the plunger of the syringe and piston of the cylinder
 piston unit are  reciprocable.  On actuation in  response to automatic control
 means, they accurately measure, trap, and then  inject fluid specimens from
 the flowing stream, as desired.

 *Patents, Water  samples, Automation, Fluids, Experimentation, Streams

 Fluid injection
256C

FILTERING AND CONCENTRATING MEANS AND METHOD,

Smith, E. W.

Canadian Patent 950,837.  Applied December 23, 1970.  Issued July 9, 1974.
Patent Office Record, Vol. 102, No. 28, July, 1974.

An apparatus for filtering and concentrating liquid slurries is provided and
consists of a container with an encircling filter screen mounted about an
axis.  Means are provided for torsionally oscillating the screen with
respect to the container; thus, liquid is removed from a liquid particle
mass in the container after it passes through the screen.  The particles
remain in the mass with little or no tendency to clog the screen.

*Filters, *Patents, Slurries, Equipment, Particles, Screens

Oscillation
                                      203

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257C

SAMPLING DEVICE,

Anderson, P. L.

Kaiser Aluminum and Chemical Corporation,
Oakland, California

United States Patent 3,823,602.  Applied November 20, 1974.  Issued July
16, 1974.  Official Gazette of the United States Patent Office, Vol.
924, No. 3, p 485, July, 1974.  1 fig.

An improved centrifuge sampling device for the capture and size segregation
of particles less than two microns in diameter from a fluid has been
patented.  The device consists of a rotating body and cap which define a
spirally shaped conduit having from 1.5 to about 2.5 convolutions.  The
particulate-laden fluid is split by the sampler into a large stream and
a small stream.  The large stream is directed to the beginning of the
spiral conduit where entrained particles are removed by centrifugal forces.
The smaller stream is introduced into the larger stream when nearly all
particulate matter has been removed from the larger stream and the flow has
become laminar.

*Sampling, *Water sampling, *Patents, *Centrifugation, *Conduits,
Equipment, Analytical techniques

Particulate matter segregation
25 8C

DEVICE AND APPARATUS FOR TREATING LIQUIDS SUCH AS
DRINKING WATER AND WASTE WATER,

Chappal, P.

United States Patent 3,823,923.  Applied January 11, 1972.  Issued July
16, 1974.  Official Gazette of the United States Patent Office, Vol. 924,
No. 3, p 569, July, 1974.  1 fig.

A device was patented which is comprised of a tube, immersed in the liouid
of a tank.  This communicates at Its upper end with treating gas-supply
means.  A diffuser with radial vanes fixed to a rotating disc is connected
with the lower end of the tube.  A pump disposed under and coaxial with
the diffuser pumps the liquid from the tank through passages in the disc
into chambers defined by the vanes.  This forms an emulsion of the gas
and liquid in the chambers which is then ejected into the liquid in the
tank.

*Patents, *Tanks, *Pumps, Equipment, Potable water, Waste water treatment,
Liquids, Gases

France
                                       204

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25 9C

BIOLOGICAL DEGRADATION SEWAGE TREATMENT PLANT,

French Patent FR 2201-259.  Applied September 28, 1973.  Issued May 31,  1974.
Derwent French Patent Abstracts, Vol. 5, No. 27, p 3,  August, 1974.

A patent was granted for a biological degradation sewage treatment plant.
Its main treatment tank has feed pipes along one side for partly processed
raw sewage.  These are parallel to the surfaces of the discs and effluent
pipes of the other side.  The effluent is completely recycled once to three
times through a preceding denitrification tank, into which the settled/decanted
sewage is fed simultaneously.  The handling capacities of both stages are
related to disc area.  In the case of the main tank, the capacity is 1.6 to
10.0 cu cm per sq cm per day, where the atmosphere above the sewage is oxygen
enriched to 30 to 60 volume percent.  In the denitrif ication tank, capacity
is 16 to 64 cu cm per sq cm per day.

*Patents, *Denitrification, *Sewage treatment, *Biological degradation,
Treatment, Effluents, Tanks

Treatment plants, Tank capacities
26 OC

WATER PURIFICATION PLANT,

Belgian Patent BE 810-790.   Applied February 8,  1974.   Issued  May 29,  1974.
Derwent Belgian Patents Report, Vol. 5,  No.  26,  p 1, August,  1974.

A water purification plant, using multi-cellular single tanks, with  each
cell in a concentric, circularly symmetrical configuration within a  common
pit was patented.  The plant consists of a flocculation chamber which  widens
as it deepens, communicating via a gap with a filtration compartment which
widens from the base upwards.  This in turn is connected by a  weir with a
sedimentation tank and guide walls.  Clear water is collected  in a common
chamber above the filtration chambers.  The arrangement is useful for  large
scale water treatment.

*Patents, *Water purification, Water treatment,  Flocculation,  Filtration,
Sedimentation tanks, Weirs

Treatment plants
                                     205

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 261C

 TWO SECTION WATER CLARIFICATION COLUMN,

 Netherlands Patent NL 7316-894.  Applied December 11,  1973.   Issued June 17,
 1974.  Derwent Netherlands Patents Report,  Vol.  5, No.  26,  p 2,  June,  1974.

 A patent was Issued for the clarification of water, comprised of a container
 delimiting a clarification chamber with a first  section connected at its
 lower end to an adjacent second section, and a device  for feeding the water
 to be clarified to the first section of the clarification chamber at a point
 above its lower end.  In addition, devices remove solids and liquids from a
 space near the upper end of the first section of the chamber, and supply gas
 bubbles to the chamber between the water feed and the water discharge devices.
 A second section of the chamber is wider than the lower end of the first
 section.  The corresponding part of the second section thus projects outward
 in the opposite direction to the lower end of the upper first section.

 ^Patents, *Water clarification, *Equlpment, Solids, Liquids, Removal
26 2C

DRINKING WATER TREATMENT PLANT,

French Patent FR 2200-202.  Applied January 12, 1973.  Issued April 19,  1974.
Derwent French Patents Abstracts, Vol. 5, No. 25, p 3,  July,  1974.

A compact, economically maintained unit was patented and is particularly
useful in domestic situations.  The unit consists of a  housing with a
detachable lid,'containing a first set of columns filled with activated
carbon.  These absorb excess chlorine; the water inlet  is fed there at the
base, followed in the purification circuit by a detachable container of
regeneration agent for the ion exchanger resin.  This fills a second set of
columns, again bottom fed, and from whose top the softened water of improved
taste is fed to the outlet pipe.  Interconnections between the internal  ele-
ments are by flexible hoses and the sets of columns are retained by elastic
straps.

*Patents, *Water treatment, *Potable water, Equipment,  Chlorine, Pipes

Treatment plants
                                          206

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 26 3C

 CONDUIT WITH INTERNAL DRAIN,

 Huggins, H. D.

 Modine Manufacturing Company,
 Racine, Wisconsin

 Canadian Patent 953,287.  Applied June 29, 1972.  Issued August 20, 1974.
 Patent Office Record, Vol. 102, No. 34, p 52, August, 1974.

 A patent for a conduit with an internal drain was granted .   An apparatus
 drains away a liquid from an interior wall surface of a conduit by gravity
 flow.  The conduit has located within it a capillary drain  with spaced
 gravity drain portions, each of a small cross sectional area in contact
 with the wall surface at spaced locations.  The portions are sloped so as
 to provide gravity drain away from the surface.  Liquid condensate will be
 drawn by gravity capillary flow down the conduit wall, contacting portions
 to an intermediate portion.  From there it is conducted down out of contact
 with the wall surface and the condensate will not interfere with heat
 transfer through the conduit wall.

 *Conduits, *Patents, *Drains, *Drainage, *Gravlty, Condensate,  Equipment
264 C

SEWAGE TREATMENT SLUDGE CONCENTRATING PLANT—WITH IM-
PROVED HEAT RECOVERY FROM TREATED CONCENTRATE TO
INCOMING RAW SLUDGE,

Belgian Patent BE 808-258.  Applied December  5,  1973.  Issued  June  5,  1974.
Derwent Belgian Patents Report,  Vol. 5,  No.  25,  p 1,  July,  1974.

A patent was issued for a sewage treatment concentrating plant with improved
heat recovery from the treated concentrate to the incoming  raw sludge.   The
raw sludge is pumped at high pressure by an indirect  heat exchanger into a
reactor vessel.  This vessel delivers treated sludge  back through  the  heat
exchanger to yield heat to Incoming raw sludge.   A pressure reducing device
is then fitted between the heat exchanger and the reactor so that  the  pres-
sure of incoming sludge can be held well above the reactor  pressure.   The
sludge in the heat exchanger can also be raised  to a  correspondingly higher
temperature without danger of blocking.

*Patents, *Sewage treatment, *Heat recovery,  *Sewage  sludge,  Pressure,
Equipment, Temperatures, Concentration

Sewage sludge treatment plants,  Concentrating plants
                                         207

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265C

AMMONIA ELIMINATION SYSTEM,

Caldwell, D. H., and Earth, E. F.

United States Patent 3,824,185.  Applied September 5, 1972.  Issued
July 16, 1974.  Official Gazette of the United States Patent Office,
Vol. 924, No. 3, p 631, July, 1974.  1 fig.

A patent was granted for a process where the nitrogen content of
waste water is removed by air stripping ammonia from waste water.
The ammonia is then absorbed in water containing nitrifying micro-
organisms.  Thus the ammonia is oxidized in the absorber water.  The
absorber and nitrifier water becomes far more concentrated in nitro-
gen than the original waste water and can be denitrified by denitri-
fying microorganisms in a small reactor.  Air and water are recycled
within this system.

*Patents, *Microorganisms, Water purification, Nitrogen, Ammonia,
Waste water treatment, Oxidation, Water recycle, Nitrification,
Denitrification
 266C

 LIQUID FILTER SYSTEM HAVING AUTOMATIC FILTER BACK
 WASH CONTROL AND METHOD OF OPERATION,

 Walters, T. M., and Brown, C. H.

 United States Patent 3,826,368.  Applied August 9, 1972.  Issued
 July 30, 1974.  Official Gazette of the United States Patent Office,
 Vol. 924, No. 5, p 1218, July, 1974.  1 fig.

 A filter for removing solid particles from a fluid was patented in
 which an inlet supplies the fluid to be filtered to one side of the
 screen.  An outlet carries away the filtered fluid from the other
 side of the screen, where means coupled to the outlet are responsive
 to an absolute drop In normal pressure.  These introduce a higher
 pressure back wash into the outlet.  Additional means are coupled
 to the inlet responsive to an Increase in normal pressure in the
 inlet for terminating the flow of back wash into the outlet.

 *Filters, *Patents, *Pressure, Solids, Liquids, Equipment, Screens

 *Back wash
                                       208

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267C

APPARATUS FOR SAMPLING LIQUIDS,

Weasels, G. R.

The Dow Chemical Company, Midland,- Michigan

United States Patent 3,826,144.  Applied June 25, 1973.  Issued
July 30, 1974.  Official Gazette of the United States Patent Office,
Vol. 924, No. 5, p 1160, July, 1974.  1 fig.

Equipment was patented for collecting liquids, particularly water.
Included is a platform which supports one or more open-end containers.
A rigid bar is positioned upright to the platform and the lower end
of the bar is fastened into the platform.  A line is used to raise
and lower the unit into a liquid body to collect the sample in the
containers.  As the liquid fills each container, the apparatus is
raised to the surface and a hinged closure assembly seals the open
end of each container.

*Patents, Liquids, Equipment,  Water sampling

Containers
268 C

NUTRITIONAL IRON-PROTEIN COMPLEXES FROM WASTE
EFFLUENTS,

Jones, S. B., Kalan, E. B., Jones, T. C., and Hazel,  F.

United States Patent 3,823,127.  Applied June 7, 1972.  Issued July 9,  1974.
Official Gazette of the United States Patent Office,  Vol.  924, No.  2,  p 348,
July, 1974.

Proteins may be precipitated and recovered from industrial waste effluents
such as whey by the addition of Ferrlpolyphosphate to the effluents.  The
recovered product, a Ferripolyphosphate-protein complex in powder form,
contains from 8 to 15 percent iron from 15 to 50 percent protein.  It is
highly nutritional and highly assimilable, and has great potential as an
iron-protein enriching additive in food and other products.

*Patents, *Proteins, Iron, Industrial wastes, Effluents, Water reuse,
Food

Ferripolyphosphates, Food additives
                                        209

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269C

METHOD OF SEPARATING METALLIC CHLORIDES FROM AN
AQUEOUS MIXTURE THEREOF,

Aue, A. I., Relnhardt, H., Rydberg, J.  H.  A., Frolunds,
B., and Skjutare, L.

Gullspangs Elektrokemiska A B, Gull spang,  Sweden

United States Patent 3,824,161.  Applied October 8,  1971.   Issued  July 16,
1974.  Official Gazette of the United States Patent  Office,  Vol.  924,  No.
3, p 625, July, 1974.  1 fig.

A method for separating one or more metallic chlorides from an acid
aqueous mixture was patented.  It employs a multi-stage,  selective
extraction process and a water immiscible extraction agent which con-
sists of a solution of an amine capable of forming extractable compounds
with the metallic chlorides.  Subsequently the metallic chloride or
chlorides are washed out of the mixture.

*Patents, *Mixtures, *Chlorldes, Metals, Extraction

Metallic chlorides
 27 OC

 FULL FLOW FLUID FILTER,

 Troth, L., Hagler, R., and Keller, 0.

 California Institute of Technology, Pasadena, California

 United States Patent 3,827,568.  Applied January 12, 1973.  Issued August
 6,  1974.  Official Gazette of the United States Patent Office, Vol. 925,
 No. 1, p 138-139, August, 1974.  1 fig.

 A filter has been designed to remove particulate impurities from a
 fluid.  It IB a hollow, generally cylindrical housing having axial
 fluid channels along the inner surface and open opposite ends forming
 an  inlet and an outlet for the filter.  Several annular, generally
 disc-shaped filter elements are tightly stacked within the housing.
 The outer edges of the filter elements bear on the inner surface of
 the housing and combine to form the axial fluid channels while the in-
 ner edges of the filter elements combine to form a hollow Inner core
 communicating with one of the open ends of the housing.  Each filter
 element Includes radial channels between the axial channels and the
 hollow inner core.  Each channel has a low-velocity pocket for trap-
 ping particulate impurities in a fluid flowing along.  One end of
 the hollow inner core is blocked so that the path for fluid flowing
 between the inlet and outlet is through the axial and radial channels
 and the hollow inner core.

 *Patents, *Filters, *Flow, Fluid mechanics, Equipment, Filtration, Sediments,
 Detritus, Sediment load, Sedimentation, Suspended load. Suspended solids,
 Water pollution sources, Water pollution treatment, Water treatment

 *Partlculate impurities removal
                                        210

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271C

APPARATUS FOR REMOVAL OF CONTAMINANTS FROM WASTES,

Okubo, K., and Ueno, A.

Tokyo, Japan

United States Patent 3,827,964.  Applied April 23, 1973.  Issued August 6, 1974.
Official Gazette of the United States Patent Office, Vol. 925,  No.  1,  p 236-237,
August, 1974.  1 fig.

This apparatus consists of an electrolytic cell partitioned by a membrane into
two electrolytic chambers.  The chambers are filled with electric conductors
in a granular or fibrous form with positive and negative major electrodes
respectively thereby forming an anode chamber and a cathode chamber in abut-
ting relation through the membrane.  The anode chamber or the cathode chamber
which are filled with the granular or fibrous conductors with major electrodes
may be replaced by a porous conductive metal sleeve.

*Patents, *Waste treatment, Seperation techniques, Equipment, Electricity,
Electrolytes, Suspended load, Suspended solids

*Contaminant removal, Electrolyte cell
 27 2C

 METHOD OF INTRODUCING OXYGEN INTO A LIQUID  TO BE
 CLARIFIED AND DEVICE FOR CARRYING THE METHOD  INTO  EFFECT,

 Kaelin, J.

 Buochs, Switzerland

 United States Patent 3,827,679.   Applied August 14,  1972.   Issued  August
 6, 1974.  Official Gazette of the United States Patent  Office,  Vol.  925,
 No. 1, p 168, August, 1974.  1 fig.

 A method of introducing oxygen into a liquid  located in an activation
 tank of a clarification plant is described.  The liquid is circulated
 in toroidal flows.  Oxygen or air is then bubbled  through.

 *Patents, *0xygen, Aerobic treatment, Water pollution treatment, Water  treatment,
 Sewage, Sewage treatment,  Oxidation, Sanitary engineering, Water supply

 Clarification plants, Activation tanks
                                       211

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27 3C

METHOD FOR THE DISPOSAL OF COMBUSTIBLE AMD
DILUTE AQUEOUS WASTES,

Grlmmett, E., and Lamont, P.

United States Atomic Energy Commission

United States Patent 3,827,946.  Applied June 5, 1972.  Issued August 6, 1974.
Officical Gazette of the United States Patent Office, Vol. 925, No. 1, p 233,
August, 1974.  1 fig.

There is a new method for the disposal of combustible and dilute aqueous
wastes.  This method produces both potable water and useful power.  Com-
bustible waste, together with conventional fuel, is burned in a fluidized-
bed steam generator; the steam produced is used to evaporate dilute aqueous
wastes in the first stage of a two-stage fluidized-bed evaporator.  The
steam in the first stage is used to evaporate dilute aqueous wastes in the
second stage of the two-stage fluidized-bed steam generator; the steam pro-
duced in the secorri stage is used to  generate power.  Spent steam  from the
first and second fluidized-bed evaporators is condensed as potable water.

*Patents, *Water reuse, *Potable water, Reclaimed water, Evaporators,
Equipment, Water pollution  treatment, Water supply, Steam

*Steam power, *Aqueous waste disposal, Steam generator, Potable water
production
 274C

 FLUID SYSTEM FOR INCLUSION IN A TOTAL AUTOMATED FLUID
 SYSTEM OF A SAMPLE ANALYZER,

 Smythe, W. J., Bellinger,  S. L., Diebler,  H.  G.,  and
 Dannewitz, R.

 Technicon Instruments Corporation,
 Tarrytown, New York

 United States Patent 3,826,615.   Applied June 9,  1972.   Issued  July 30,  1974.
 Official Gazette of the United States Patent  Office, Vol.  924,  No.  5  i  1282-
 1283, July 30, 1974.  1 fig.

 A fluid system, serving to  dilute each sample for  subsequent  division  into
 a large number of parts, has been developed for inclusion  in  an automated
 fluid system for analyzing  a series  of liquid samples flowing seriatim.
 Involved in the patented system  is  the same and equal dilution  treatment
 of each sample as the series.  Also  involved  in the  system is the effective
 inhibition of cross contamination of  samples  from  the point of  introduction
 of the samples into the dilution system to the point, after division of  the
 samples,  where the samples  flow  into  the respective  ones of the analysis
 subcomblnations.

 *Patenta,  *Dilution,  Sampling, Analytical techniques, Instrumentation
 Automatic  control
                                          212

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275C

WATER QUALITY ANALYSIS SYSTEM WITH MULTICIRCUIT SINGLE
SHELL HEAT EXCHANGER,

Houser, E. A., and Schwlndt, B. W.

Beckman Instruments, Incorporated, Fullerton, California

Canadian Patent 948,881.  Applied March 20, 1972.  Issued June 11, 1974.
Canadian Patent Office Record, Vol. 102, No. 24, p 18, June 11, 1974.

A modular water quality analysis system for steam electric power generating
plants is disclosed which includes a novel single shell multicircuit heat
exchanger that varies the rate of flow of cooling water through each of the
multiple circuits.  The heat exchanger has a physical construction such that
it can be mounted on top of the system rack thereby replacing a plurality of
individually manifolded and valved heat exchangers formerly mounted at the
back of the rack.  The flexibility of design in the modular system also per-
mits the same basic apparatus to be adapted to a large variety of different
sizes and types of power generating plants having different analysis re-
quirements .

*Patents, *Analytical techniques, *Instrumentation, *Water analysis, Water
quality. Power plants. Flow rate, Cooling water
276C

METHOD OF BLEACHING WOOD PULP,

Lincoln, R. M., and Meyers, J. A.

Atlantic Richfield Company, New York, New York

Canadian Patent 949,263.  Applied May 26, 1971.  Issued June 18,  1974.
Canadian Patent Office Record, Vol. 102, No. 25, p 3, June 18, 1974.

A method to prevent both atmospheric and water pollution in the pulp and
paper industry has been patented.  Under this process,  pulping and bleaching
of wood chips is accomplished in a single stage using tertiary butyl hydro-
peroxide in an aqueous alkaline medium.

*Pulp and paper Industry, *Patents, *Water pollution control,  Pulp
wastes, Bleaching, Methodology

Butyl hydroperoxide
                                        213

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277C

SEWAGE TREATMENT SYSTEM,

Long,  H. G.,  and Long,  V.  E.

United States 3,819,054.   Applied September  8,  1971.   Issued  June  25,  1974.
Official Gazette  of the  United  States Patent Office,  Vol.  923,  No.  4,
p 1378, June 25, 1974.  1 fig.

A recently patented sewage treatment system  especially adapted  to  be a
conversion unit for existing  septic tanks is comprised of  the following
equipment.  An inner tank to  receive raw sewage is within  the septic tank
and spaced from the walls with its upper surface open  above the liquid
line.   An air diffuser  system delivers compressed air  within  the inner
tank and draws activated  solid  portions settling from  the  clarifier  zone
in the outer tank toward  the  sludge zone at  the bottom and  through the  means
is attached to the outer  wall of the inner tank.  Lastly,  a float  skimmer
means is provided to insure the return of floating solids  from the clarifier
zone to the interior of the inner tank for retreatment.

*Sewage treatment, *Treatment facilities, *Equipment,  *Patents,  Septic
tanks, Weirs

Float skimmer, Air diffuser
27 8C

FILTRATION PROCESS AND FILTRATION EQUIPMENT,

Murata, K., Ikeda, H., Ashida,  K., and  Sato,  U.

Yuasa Battery Company Limited,  Hakuhaicho,  Tokotsuki City,
Osaka, Japan

United States Patent 3,826,369.  Applied December  18, 1972.   Issued  July 30,  1974.
Official Gazette of the United  States Patent  Office, Vol.  924,  No. 5,  p 1218-1219,
July, 1974.  1 fig.

This invention provides a filtration process  capable of intermittent repeti-
tion.  The prefilt is fed under pressure through a filter  medium to  one
section of a pair of containers compressed  to a  watertight closure and the
filtrate is discharged from another section of the containers.   The  filtrate
is fed under pressure in the reverse direction of  the filtration process,
while the filtration process is suspended,  to remove plugging of the filter
medium.  The filtration and backwash processes are alternately  repeated a
predetermined number of times.

*Patents, *Filters, *Filtration, Equipment, Separation techniques, Water
treatment, Pressure

Backwash


                                         214

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279C

TOTAL MKRCURY MONITOR,

Capuano, I. A.

Ionics, Incorporated, Watertown, Massachusetts

United States Patent 3,826,614.  Applied May 17,  1972.   Issued July 30,  1974.
Official Gazette of the United States Patent Office, Vol.  924, No.  5,  July,
1974.  1 fig.

An apparatus and method are described for analyzing liquid streams  for their
mercury content including elemental mercury, ionic mercury and undissociated
mercury compounds.  The sample is automatically measured and treated with an
acidic metal salt reagent containing an oxidant for oxidizing elementary
mercury in the sample to ionic mercury.  It is then treated with hydrazine
to form a catalytic colloid.  Elementary mercury is formed by the action of
hydrazine and the catalytic colloid on the ionic and combined mercury.  The
results are indicated and/or recorded by transferring the elemental mercury
to a photometric detector.

*Patents, *Mercury, *Analytical techniques, *Equipment, Monitoring

Total mercury monitor
 28 OC

 APPARATUS  FOR AUTOMATICALLY  EFFECTING VACUUM CONCENTRATION
 AND RECOVERY OF  WASTE LIQUID,

 Takayasu,  K.

 United  States Patent 3,826,718.  Applied March  23, 1973.  Issued July 30, 1974,
 Official Gazette of the United States Patent Office, Vol. 924, No. 5, July,
 1974.   1 fig.

 An apparatus  which will automatically effect vacuum concentration and the
 recovery of waste liquid is  described.  It consists of an evaporating vessel
 of a relatively  small volume and which is topped by a steam riser tube con-
 taining a  vapor  separator and a condenser.  A waste liquid is supplied to the
 evaporating vessel and Is heated by a steam heater.  The steam produced is
 discharged through a drain tank to the outside.  The liquid level in the
 evaporating vessel, the water level in the drain tank and the liquid level
 in the  waste  liquid recovery tank are controlled by relays so that the evapora-
 tion and concentrating operations and discharge of the distilled water are
 automatically repeated for a given number of times,

 *Patents,  *Reclaimed water,  *Liquid wastes, Equipment, Waste water treatment,
 Distillation, Water treatment, Evaporation, Evaporators
                                       215

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281C

RECOVERY OF RESIDUAL AMMONIA FROM WEAK AQUEOUS
SOLUTIONS THEREOF,

M&vrovic, I.

United States Patent 3,826,815.  Applied October 15,  1973.   Issued  July  30,  1974.
Official Gazette of the United States Patent Office,  Vol.  924,  No.  5,  July,
1974.  1 fig.

A method for recovering ammonia from a waste liquid effluent composed  of a weak
ammoniacal aqueous solution is described.  The solution is  stripped with steam
and an inert gas in a fractionator at specific conditions.   Substantially all
of the ammonia is recovered in a gaseous product and  a liquid product  is re-
covered that is substantially free of ammonia.

*I'atents, *Ammonia, *Equipment, Aqueous solution, Waste water treatment,
Liquid wastes, Water treatment

Ammonia recovery
 28 2C

 CARBONATION SYSTEM FOR RECOVERY OF SODIUM BASE PULPING
 LIQUOR,

 Anderson, C. G.

 Owens-Illinois,  Incorporated, Cincinnati, Ohio

 United States Patent 3,826,710.  Applied April 21, 1972.  Issued July 30, 1974.
 Official Gazette of the United States Patent Office, Vol. 924, No. 5, July,
 1974.  1 fig.

 An  integrated closed carbonation system for recovering sodium base sulfite
 pulping liquor has been invented.  The system includes:  smelt solutions which
 contain from one third to  two thirds mol percent sodium sulfide with the
 balance primarily sodium carbonate; self-sufficiency in carbon dioxide for
 displacement of  the sulfide; temperatures during carbonation from 140 to 180
 degrees F; an intermediate concentration of carbon dioxide for carbonation;
 and systems for  cycling different gas streams to conserve and reuse carbon
 dioxide.  The system also produces gases containing hydrogen sulfide suitable
 for direct combustion to sulphur dioxide and purges gases relatively free of
 hydrogen sulfide or sulphur dioxide.

 *Patents, *Liquid wastes, *Equipment, *Pulp wastes, Sodium compounds, Sulfite
 liquors, Sulphur compounds, Carbon dioxide, Waste treatment

 Carbonation system


                                          216

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283C

AERATING EFFLUENT AND KEEPING SLUDGE IN SUSPENSION,

Netherlands Patent 57251V/32.  Applied January 29,  1973.   Issued July  31,
1974.  Derwent Netherlands Patents Report, Vol.  5,  No.  33,  p 2,  September  24,
1974.

A patent was Issued for a process by which effluent Is  aerated and activated
sludge Is maintained in suspension by jets of water obliquely striking the
surface.  The vessel used is circular, elliptical,  or polygonal in shape
and of constant cross-section through the greater part  of its height.
The jets strike the surface at not more than 60 degrees,  preferably 10 to
20 degrees to the surface with a speed of 3 to 12 m/sec.   The horizontal
component of the tangent is in the general direction of flow.

*Patents, *Equipment, *Aeration, *Effluents, Sludge, Suspension, Jets,
Flow, Activated sludge, Sludge treatment
 284C

 SOLID BOWL CENTRIFUGAL SEPARATOR,

 Peck, W. H., and Collier, S. A.

 United States Patent 3,829,009.  Applied March 15, 1973.   Issued August 13,
 1974.  Official Gazette of the United States Patent Office,  Vol. 925,
 No. 2, p 514, August, 1974.  1 fig.

A centrifugal separator for the removal of solids from slurry was patented.
A high speed bowl rotates about a vertical axis and is centrally fed with
 slurry in its upper region.  A circular ceiling plate above  the level  of
 slurry feed establishes a narrow annulus with the cylindrical upper rim section
 of the bowl.  This becomes sealed with sludge as the solid constituents build
 up in the vicinity.  A series of plows advance slowly around the annulus and
 through the sludge seal and elevate the sludge above the  ceiling plate, into
 the path of a series of rotatable buckets.  These buckets assume outside
 ecliptic positions where they scoop wads of sludge from the  sludge seal,
and assume inside ecliptic positions where their directional relationship
 is reversed ao that centrifugal force dislodges the wads, causing them to
be flung radially over the rim of the bowl.  The liquid constituent of
 the slurry is then forced out through an outlet in the bowl  bottom wall.

*Patents, *Centrifuges, *Slurries, *Solids, Equipment

 Treatment methods
                                         217

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285C

FLUID AERATING MEANS,

Canadian Patent 949,239.  Applied July 6, 1971.  Issued June 11,  1974.
Patent Office Record, Vol. 102, No. 24, p 93, June, 1974.

A patent was granted for a method of fluid aeration.  Sewage,  particularly
when flowing, is aerated by many downwardly directed spaced air Jets in a
submerged deformable plastic tube, preferably one of circular  transverse
cross-section.  The tube is held down by a subjacent shot-filled  anchor
tube held spaced by an underside connecting strip.   When air is not holding
the tube inflated, the unstressed shape of the tube together with the pressure
against the outer lateral surface portions by the ambient  water occlude water
and air, preventing the interior of the tube from becoming clogged.

*Patents, *Aeration, *Equipment, *Sewage treatment, Flow,  Jets, Pressure

Fluid aeration
28 6C

SYSTEM FOR DETECTING PARTICULATE MATTER,

Hofstein, S. R.

Princeton Electronic Products, Incorporated,
North Brunswick, New Jersey

United States Patent 3,830,969.   Applied  October 14, 1971.   Issued August 20,
1974.  Official Gazette of the United States Patent Office,  Vol.  925,  No. 3,
p 1000, August, 1974.  1 fig.

A system and method for detecting and graphically visualizing partlculate
matter present in a fluid sample was patented.  The liquid  sample is held
in a transparent container and agitated by spinning the container for  a
limited time period.  This places the particles in transient motion relative
to the then stationary container.  A television camera forms a time con-
tinuous image of the illuminated container and scattered points of light
from the moving particles.  This television image is processed by a signal
converter tube.  The processed image, now retaining only the light points
corresponding to the moving particles, can be displayed on  CRT equipment.
The processed image signal may also be furnished to an electronic particle
detector and analyzer, which will examine the particulate matter  for
characteristics such as movement, distribution, dimensions,  and number or
concentration.

*Patents, *Waste identification, Liquids, Analyzers, Sampling, Matter

*Particulate matter, *Television image
                                         218

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28 7C

APPARATUS TO COUNT PARTICLES SUSPENDED IN LIQUID,

German Patent E1837V/25.  Applied January 11, 1967.  Issued June 12, 1974.
Derwent German Patents Abstracts, Vol. 5, No. 25, p 2, July 30, 1974.

Equipment was patented which counts particles suspended in liquid.  The
apparatus is comprised of two vessels, permitting liquid to flow successively
in opposite directions, to give two measurements.  The liquid is contained
in one vessel in which a second measuring vessel stands upright.  Suction
is applied by means of a bellows which permits liquid to be drawn into the
upright measuring vessel.  Inside a measuring chamber are two electrodes
at different heights, which enter it from above through a wall of the
channel projecting from the circular chamber.  Measurements are made twice
in succession on the same liquid by drawing it up initially by the bellows
and subsequently releasing it to flow back into the lower containing vessel.

*Patents, *Partides, Liquid, Suspension, Flow, Measurement

Particle counts, Bellows, Measuring chambers
288C

TREATMENT OF WASTE WATER FROM DOMESTIC SEWAGE,

Smith, A. W.

Western Mechanical Incorporated,
Melbourne, Victoria, Australia

Australian Patent 449,369.  Applied October 29, 1969.  Issued June 13, 1974.
Official Journal of Patents, Trade Marks and Designs, Vol. 44, No. 21,
p 2265, June, 1974.

An apparatus and a continuous process for treatment of waste water from
domestic sewage was patented.  Its goal is to recover usable water from
sewage, of sufficient purity for normal agricultural and domestic purposes,
including human drinking purposes.  The method of treating this waste water
consists of the following steps:  vigorously passing a controlled amount
of sulphur dioxide through the waste water, together with an amount of
gaseous oxygen greater than that needed to saturate the treated waste water;
bringing the treated waste water into contact with a source of metallic iron;
subjecting the source of metallic iron and treated waste water to continuing
vigorous passage of gaseous oxygen; and, monitoring the acidity of the
treated waste water.  In addition, the amount of sulphur dioxide passed
through the waste water is controlled in response to the monitoring of the
treated waste water to maintain the monitored acidity at a level adequate
to insure bacterial kill; the treated waste water is neutralized by addition
of an alkaline material; and the vigorous agitation of the neutralized waste
water is continued by passing an amount of gaseous oxygen through it in
excess of that needed to saturate the neutralized waste water.  The final
result is a separation of liquid and solid components of the waste water.

*Patents, *Waste water treatment, *Potable water, Domestic wastes, Sewage
treatment, Sulphur dioxide, Acidity, Liquids, Solids, Separation, Iron,
Equipment, Monitoring, Neutralization

Domestic sewage, Bacteria kill           „,„

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289C

SLIME CONTROL COMPOSITIONS CONTAINING PHENOLIC COMPOUNDS
AND THEIR USE,

Brink, R., Shema, B. F., Justice, R. L., and Swered, P.

Betz Laboratories, Incorporated, Trevose, Pennsylvania

United States Patent 3,829,305.  Applied July 6, 1971.  Issued August 13, 1974.
Official Gazette of the United States Patent Office, Vol. 925, No. 2, p 588-589,
August, 1974.

Water used in pulp and paper manufacture and water used in coling water systems
and other industrial waters, provide environments which are favorable to
slime formation.  Slime is considered undesirable from an operational and/or
an aesthetic point of view.  Compositions have been patented that are useful
for inhibiting and/or controlling the growth of slime in water.  These mix-
tures exhibit synergistic activity against microorganisms, including the
bacteria, fungi and algae which produce slime in aqueous systems.  The growth
of slime is inhibited by the biocldal action of the compounds in the mixture.
The mixture is composed of phenolic compounds such as phenol, ortho-
phenylphenol, 2,3,4,6-tetrachlorophenol, 4-chloro-2-cyclopentylphenol and
2-chloro-4-phenylphenol.

*Patents, *Slime, *Phenols, *Bacteria, *Fungi, *Algae, Inhibition, Water
quality control, Industrial water, Pulp and paper industry, Industrial wastes
 290C

FLUID FILTER DEVICE,

Brown, C. A.

Parker-Hannifin Corporation, Cleveland,  Ohio

Canadian Patent 952,440.  Applied April  15,  1971.   Issued  August 6,  1974.
Patent Office Record, Vol. 102,  No.  32,  p 40,  August,  1974.

A fluid filter apparatus is described.  It consists of a fluid chamber with
the first two inlet portions connected to a fluid  inlet and  an intermediate
portion connected to a fluid outlet.  A cylindrical filter element is in the
intermediate portion; fluid flows from the inlet portions  into the interior
of the filter element, radially through its walls and  into the intermediate
portion.  In response to a predetermined pressure increase in the inlet
portions, the filter element moves and opens fluid communication between the
inlet portions and the intermediate portion.  Fluid then flows from the
fluid inlet to the fluid outlet and bypasses the filter element.

*Patents, *Filters, *Filtration, *Separation techniques, *Waste water treatment,
Equipment, Pressure
                                    220

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 291C

METHOD AND APPARATUS FOR TREATING EFFLUENT,

Hopwood, A. P.

Mono Pumps Limited, London, England

Canadian Patent 952,237.  Applied October 13,  1971.   Issued  July 30,  1974.
Patent Office Record, Vol. 102, No. 31,  p 88,  July,  1974.

A method and apparatus for treating raw effluent such as sewage are described.
The effluent is sent through a vessel containing media.   The media are
suitably short lengths of plastic tubing.  Air is passed through the effluent
and media.  A two stage process is possible by passing the effluent through
two containers of plastic tubing.  The treated effluent  then goes to settlement
tanks.

*Patents, *Sewage treatment, *Aerobic treatment, *Tubes, *Sewage effluents,
Liquid wastes, Waste water treatment, Settling basins
 29 2C

 METHOD AND APPARATUS FOR MEASURING PARTICLE CONCENTRATION
 IN A FLUID SUSPENSION OF PARTICLES,

 Hogg, W. R., and Longman, M. D.

 Canadian Patent 952,193.  Applied April 28, 1972.  Issued July 30, 1974.
 Patent Office Record, Vol. 102, No. 31, p 78, July, 1974.

 Particle concentration in a fluid suspension is measured by the generation of
 a signal each time a particle traverses a sensing zone; the duration of the
 signal or particle pulse is related to the time occupied by the particle in
 suspension while traversing the sensing zone.  Concentration is proportional
 to the percentage of time the particles are in the sensing zone to the total
 time it takes the suspension to pass through the sensing zone.  The apparatus
 Includes electrical circuits for measuring the duration of a predetermined
 portion of each particle pulse between two points.  The direct current
 component of these duration-measuring pulses averaged over the time during which
 they occurred is proportional to the concentration and can be found with a
 d.c. meter.  The meter can be calibrated in terms of particle concentration.

 *Patents, *Suspension, *Fluid mechanics, Sediment load, Suspended load,
 Suspended solids, Analytical techniques, Equipment, Water quality control,
 Current meters, Direct currents
                                           221

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  293C

OXYGEN-HYDROGEN GENERATION AND SEWAGE TREATMENT METHOD
AND SYSTEM,

Wesley, R. B.

United States Patent 3,829,368.  Applied March 2, 1972.  Issued August 13, 1974.
Official Gazette of the United States Patent Office, Vol. 925, No.  2, p 602,
August, 1974.  1 fig.

A system to produce potable water from sewage is described.  It is  a regenera-
tive sewage treatment method which decomposes sewage into its constituent
elements,  including oxygen and hydrogen gases.  The elemental gases and the
recombination of these gases generate almost enough energy to make the system
self-supporting.  Potable water is produced when the elemental gases recombine.
The system consists of a high-pressure electrolytic unit for producing
pressurized gases of decomposition, a pressure engine and mechanical electrical
generator  for converting the potential energy of the gases to kinetic and
electrical energy, an oxygen-hydrogen fuel cell for producing potable water,
and an external energy source for supplying initial start-up energy.

^Patents,  *Potable water, *Sewage treatment, *Energy conversion, *Water supply,
Hydrogen,  Oxygen, Energy
 294C

SEWAGE TREATMENT SYSTEM,

Corniah, A. H., DeLaney, R. E.,  and Davis,  R.  B.

Koehler-Dayton, Incorporated, New Britain,  Connecticut

United States Patent 3,831,534.   Applied July  2,  1973.   Issued  August  27,  1974.
Official Gazette of the United States Patent Office,  Vol.  925,  No.  4,  p  1180,
August, 1974.  1 fig.

A sewage treatment system is described.   A surge  tank receives  the  effluent
from a recirculating toilet or similar structure.   The  effluent received by
the surge tank is selectively and periodically delivered  to  a housing  in an
incinerator.  The incinerator contains a combustion chamber  that directs a
flame down against the top surface of the sewage  in the housing.  The  liquid
part of the effluent evaporates  and passes through a  stack on the combustion
chamber.  The incinerator is turned off  automatically when the  level of  the
effluent in the housing drops to a predetermined  level.

*Patents, * Incineration, *Sewage treatment,  *Burning, *Liquid wastes,
Sewage effluents, Waste water treatment
                                       222

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  295C

 REDUCTION OF WATER POLLUTION  BY  BIOLOGICAL
 DENITRIFICATION,

 Hashimoto,  S.

 Union Oil Company  of  California,  Los Angeles,  California

 United States Patent,  3,829,377.  Applied February  7,  1973.  Issued August 13,
 1974.  Official Gazette  of  the United  States Patent Office, Vol. 925, No. 2,
 p  604, August,  1974.   1  fig.

 A  process to biologically denitrify water that contains soluble nitrates has
 been  patented.  Anaerobic bacteria is  added to the  water and a normally
 gaseous Cl  to C3 hydrocarbon  for  a long enough time so that the nitrate ions
 can be biologically degraded  to  nitrogen.

 *Patents,  *Nitrogen,  *Denitrification, *Nitrates, *Biological treatment,
 Anaerobic bacteria, Waste water  treatment, Nutrient removal, Chemical
 reactions
 296C

FILTER ASSEMBLY,

Thomsen, J. W.

Everpure, Incorporated, Oak Brook, Illinois

Canadian Patent 952,041.  Applied May 5, 1970.  Issued July 30,  1974.
Patent Office Record, Vol 102, No. 31, p 43, July,  1974.  1 fig.

A filter assembly has been patented that consists of a head with a built-in
shut-off valve and is adapted to be mounted in the line supplying the  fluid
to be filtered.  A replaceable filter unit is held  by a clamping collar
to the head.  Interacting cam means on the clamping collar and head engage
or disengage the filter unit to or from the head,

*Patents, *Filters, *Equipment, *Filtration, Waste water treatment,
Separation  techniques
                                        223

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 297C

APPARATUS FOR FLUID TREATMENT,

Maroney, W. J.

Sybron Corporation, Rochester,  New York

United States Patent 3,812,969.   Applied October  16,  1972.   Issued May  28,  1974.
Official Gazette of the United  States Patent Office,  Vol.  922,  No. 4, p 1137,
May, 1974.  1 fig.

An apparatus has been designed  for treating fluid in  which the  fluid passes
through a bed of solid particles such as filter media or  ion exchange resins.
The apparatus provides better support and improved backwashing  of  the bed.
An inner container with an open bottom is positioned  over  the bottom of an
outer container with a closed bottom.  The bed of solid particles  is supported
by the bottom of the outer container and extends  into one  of the containers,
covering the opening between the inner and outer  containers.  Support items
such as underdrains and strainers are not required because the  bed is
supported by the outer container.  Fluid enters one of the containers,  passes
through the bed and into the other container.  One of the  containers should
have a closed top and an outlet conduit located at an intermediate level.
Fluid accumulates in the container with the closed top, trapping air above  it.
The trapped air is compressed by restricting the  outflow.   Backwashing  is
effected by releasing pressure  on the inlet side  of the bed;  the compressed
air forces the accumulated fluid back through the bed and  through  a backwash
outlet conduit.  During the backwash cycle, air may be withdrawn from the
pocket of compressed air and injected into the bed, so that a mixture of air
and fluid will scour the particles in the bed.

*Patents, *Filters, *Filtratlon, *Equipment, *Waste water  treatment, Ion
exchange. Separation techniques, Packed beds. Water treatment
  298C

 METHOD AND  DEVICE FOR WASHING A CONTINUOUS FILTER WITH
 A HORIZONTAL  FILTRATION  SURFACE AND CELLS,

 Davister, A.

 Societe  de  Prayon,  Prayon  (Commune de Foret), Belgium

 United States Patent 3,830,658.  Applied June 13, 1972.  Issued August 20, 1974.
 Official Gazette of the  United States Patent Office, Vol. 925, No. 3, p 942,
 August,  1974.  1 fig.

 A method has  been patented  for washing a continuous filter with a horizontal
 filtration  surface  and cells.  Washing is done after the discharge of the
 filtration  cake.  Water  jets of high kinetic energy and/or heavily turbulent
 water flows are used to  cause a mechanical scouring of possible sediments and
 scales formed on the walls  and cloths of the filters during filtration.  The
 wash water  is supplied inside the cells.

 *Patents, *Filters, Filtration, Water treatment, Waste water treatment,
 Equipment,  Sediments
                                       224

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  299C

  CORRUGATED DRAINAGE TUBE WITH RESTRAINING SCREEN,

  Slxt, M.  E.

  Advanced  Drainage  Systems, Incorporated,
  Waterville, Ohio

  United  States Patent  3,830,372.  Applied April 19, 1972.  Issued August 20,
  1974.   Official Gazette of the United States Patent Office, Vol. 925, No. 3,
  p 867,  August, 1974.   1 fig.

  A flexible  corrugated drainage tube has been patented that consists of
  alternating annular peaks and annular valleys with walls connecting the peaks
  and valleys.  Openings in selected valleys  of  the tube  are arranged trans-
  versely to  the longitudinal  axis of the tube so  that liquid water can drain
  into the  tube  through the openings.  A water permeable  restraining screen
  surrounds the  tube and engages the peaks.   The screen prevents waterborne
  particles above  a certain size from entering the tube when water drains
  into the  tube.   The water permeable screen  allows waterborne  silt and clay
  to pass through,  which keeps the  screen from becoming clogged with these
  particles.

  *Patents, *Separation techniques,  *Drainage, Water  treatment, Tubes,
  Filtration,  Equipment
  300C

ACTIVATED CARBON CHEMICAL ADSORPTION ASSEMBLY,

Economy, J. and Lin, R. Y.

The Carborundum Company, Niagara Falls, New York

United States Patent 3,831,760.  Applied June 28, 1972.  Issued August 27, 1974,
Official Gazette of the United States Patent Office, Vol.  925, No. 4,  p 1241
August, 1974.  1 fig.

An apparatus for use in controlling chemical spillage on commercial waterways
is described.  Activated carbon textile has a floating support and a sinking
weight.  The activated carbon chemical adsorption assembly can be constructed
in configurations that are essentially one, two,  or three  dimensional.
Chemical spillage is controlled by the use of a combination of various
configurations.  The more convenient configurations are somewhat less  effective
and the more effective configurations are somewhat less convenient to  use.

*Patents, *Activated carbon, *Chemical industry,  *Equipment,  *Pollution
abatement, Water pollution sources

*Chemical spillage
                                        225

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 301C

 CENTRIFUGAL LYOPHOBIC SEPARATOR,

 Booth, F. W. and Bruce, R. A.

 United States Patent 3,828,524.  Applied August 9, 1971.  Issued August 13,
 1974.  Official Gazette of the United States Patent Office, Vol. 925, No. 3,
 p  390, August, 1974.

 A  centrifugal separator using a lyophobic filter has been patented.  It is
 designed for removing liquid particles from a mixed stream of gas and liquid
 under conditions of negative or positive external acceleration or weightlessness.
 Rotating the filter and inclining it to the entering flow improves the
 lyophobic properties of the filter.  This position allows gross separation of
 larger liquid particles and prevents prolonged contact of liquid droplets
 with the spinning filter.  If prolonged contact of droplets with the filter
 was allowed to occur, the filter properties might be changed or the filter
 could become blocked.

 *Patents, *Filters, *Separation techniques, *Centrifugation, Equipment,
 Waste water treatment, Filtration
 302C

APPARATUS FOR REMOVING SLUDGE FROM A RECTANGULAR
FLOTATION TANK,

Lefur, J., Lauboutin, R., and Savall, V.

Degremont Societe Generale D'Epuration et
D'Assainissement,
Rueil-Malmaison, France

United States Patent 3,831,767.  Applied  May 18, 1973.   Issued  August  27,  1974.
Official Gazette of the United States Patent Office,  Vol.  925,  No.  4,  p 1243,
August, 1974.  1 fig.

An apparatus is described that removes sludge from a  rectangular  sewage
flotation tank.  It is a bridge structure with a horizontal drum  provided
with vanes mounted on a bridge structure.  The direction of the rotation
of the drum and vane assembly is opposed  to the direction  of travel of the
bridge structure when the surface is being scraped.  A  scraper  blade pushes
the sludge toward the front of the moveable vanes of  the drum.  The removed
sludge is fed to a discharge device mounted inside the  tubular  shaft of
the drum.  The sludge is collected in a container fastened to the bridge.

*Patents, *Sewage treatment, *Sludge, *Equipment, Sludge disposal
                                         226

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  303C

 DISCHARGE DEVICE FOR A VACUUM SEWAGE SYSTEM,

 Andersson,  J.

 AB Cenenta, Malmo,  Sweden

 Canadian Patent 952,789.   Applied  December  13,  1971.  Issued August 13, 1974.
 Patent Office  Record, Vol. 102,  No.  33,  p  30, August, 1974.

 A discharge device  for a  vacuum  sewage  system is  described.  It consists
 of a minimum of two sewage collection tanks, each with valve controlled
 inlet and outlet ducts, a vacuum source  and valve controlled passages which
 connect each of the tanks alternatively  to  the  vacuum source and to a source
 of ventilation air.  The  inlet duct  of each tank  is connected  to the vacuum
 sewer which feeds the sewage  to  the  discharge device.  The valve controlling
 the inlet ducts operate so that  at any  time there is at least  one  tank
 receiving sewage and simultaneously  connected to  the vacuum source.  When
 the tank becomes filled with  sewage,  it  is  disconnected from the sewage
 system and  from the vacuum source  and another tank is connected in its
 place.  Removal of  the sewage from the  full tank  is effected by connecting
 it to the source of ventilation  air  and  opening the outlet duct so that
 sewage flows out through  the  outlet  duct.   The  outlet ducts may be connected
 to a collecting tank under atmospheric pressure,  to a sewer pit or to a
 conventional gravity sewer.

 *Patents,  *Sewers,  *Sewerage,  Equipment, Wastes,  Sewage, Water pollution
 sources

 *Vacuum sewers
304C

LIQUID PURIFICATION APPARATUS AND PROCESS,

Humiston, G. F., and Cotton, B. L.

United States Patent 3,837,491.  Applied November 3,  1972.   Issued
September 24, 1974.  Official Gazette of the United States  Patent  Office,
Vol. 926, No. 4, p 1265-1266, September, 1974.  1 fig.

A method was developed for the continuous mechanical purification  of a
liquid containing solid and dissolved pollutants.  A liquid chamber is
charged with polluted liquid which is subjected to centrifugal separation
and vacuum distillation.  The centrifugal separation influences the removal
of pollutants from the chamber, exposing more surface of relatively pure
liquid for the vacuum distillation.  A stationary housing comprises the
purification apparatus, along with a cylindrical, circumferentially per-
forated screen member concentrically arranged within the housing.   Vanes
inside the screen member are mounted for rapid rotation around the axis,
for centrifugation of the liquid .  A vapor outlet in the housing apply a vacuum
to the liquid within the screen member.  A sludge outlet in the housing
provides for the removal of sludge from the housing.

*Patents, *Liquid wastes, *Water pollution, *Water quality control, *Water
purification, Separation techniques, Distillation, Sludge removal

*Centrifugal separation, *Vacuum distillation, Liquid purification
                                     227

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305C

METHOD AND APPARATUS FOR PURIFYING FLUIDS,

Woods, M. D.

United States Patent 3,837,800.  Applied January 11, 1973.  Issued September
24, 1974.  Official Gazette of the United States Patent Office, Vol. 926,
No. 4, p 1347-1348, September, 1974.  1 fig.

A  technique for continuously purifying a fluid by the emission of ultra-
violet rays has been patented.  The apparatus consists of a body with a
series of spaced, parallel, elongated, cylindrical radiation chambers,
elongated, interconnected chambers with a height much less than the diameter
of the radiation chambers, and elongated, ultraviolet ray emitting lamps
mounted in jackets in the radiation chambers, extending from the front to
the rear of the radiation chambers.  Fluid for purification is received in
an elongated chamber and spread into sheet-like flow and passed serially
and transversely between the lamp jackets and the radiation chambers' walls.
The fluid remains in the sheet-like flow between adjacent radiation chambers
by passing through the interconnecting chambers.  The purified liquid is
discharged from the last radiation chamber.

*Patents, *Water purification, *Waste water  treatment, *Ultraviolet
radiation, Irradiation, Waste  treatment, Sterility

*Radiation chambers
 306C

 METHOD AND APPARATUS FOR REMOVING WATER SOLUBLE WASTES
 OR SALTS FROM AN AQUEOUS SOLUTION,

 Wallace, L. J.

 United States Patent 3,833,044.  Applied January 8, 1973.  Issued September 3,
 1974.  Official Gazette of the United States Patent Office, Vol. 926  No  1
 p 98, September, 1974.  1 fig.

 A method and apparatus for removing water soluble salts from aqueous salt
 solutions have been patented.  An unsaturated evaporating medium such as
 unsaturated air is directed across a readily disposable, movable curtain
 which has been saturated with an aqueous salt solution.  The air carries
 away the moisture leaving the salt residue on an expendable screen.   The
 incoming air is heated if its temperature falls below 38 degrees F and/or
 its relative humidity is equal to or greater than 85 percent.  The moisture
 laden air is passed to a condenser where the moisture is condensed and
collected .

*Separation techniques,  *Aqueous solutions,  *Patents, *Equipment,  *Waste water
 treatment,  Industrial wastes, Evaporation
                                       223

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  307 C

 PLANT FOR WASTEWATER TREATMENT,

 Hampton, Q. L., and Matras, E. J.

 JMC Corporation, Chicago, Illinois

 United States Patent 3,828,933.  Applied February 14,  1972.   Issued  August  13,
 1974.  Official Gazette of the United States Patent Office,  Vo].  925,  No.  2,
 p 495, August, 1974.  1 fig.

 A method and apparatus are described for converting a  basic  unitary  tank
 structure into a series of communicating treatment zones.   This is
 accomplished by using a self-supporting modular settling tank which  has
 liquid tillable fillets as part of its structure.  The tank nay be anchored
 in position to provide watertight segments which function as cooperative
 treatment areas.  The modular tank provides the support for the aeration
 apparatus necessary to convert an adjacent tank segment into an aeration
 zone.  It also provides support for the apparatus that removes sludge  from
 the mixed liquor.  Part of the sludge can be returned  to the aeration  tank.
 The rest of the sludge is discharged to any additional treatment processes.
 The clarified effluent is discharged from an upper portion of the modular
 tank.

 *Patents, *Waste water treatment, *Aeratlon, *Sludge,  Sewage treatment,
 Structure, Equipment
308C

FILTERS,

Walker, A. J. W.

United States Patent 3,833,123.  Applied February 16, 1973.  Issued
September 3, 1974.  Official Gazette of the United States Patent Office,
Vol. 926, No. 1, p 119, September, 1974.  1 fig.

A screen filter composed of a perforate and substantially flat screen is
described.  Fluid material to be filtered is supplied to  an outwardly
sloping face of the screen.  Adherence of filtrate to the screen is
reduced and the filtrated is the collected as It falls free of the
screen.

*Patents, *Filters, *Separation techniques, *Waste water  treatment,
*Filtratlon, Screens
                                       229

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                               TREATMENT METHODS




 001D

MAGNETIC CLARIFIER,

Engineering News-Record, Vol. 191, No. 20, p 23, November 15, 1973.

The application of an instream magnetic separation process for cleaning
the bottom waters of Boston's Charles River is described.  The process
has previously been used only in the mining and clay industries.  It
involves distributing very finely ground iron filings throughout water
that has been pumped up through a suction device from the river bottom.
Chemicals are added to coagulate the pollutants and iron filings, and to
improve the electrolytic property of the water.  The water is run through
a high intensity electromagnetic field which attracts the solids.  The
separated material is again put through a magnetic field to recover  iron
filings for reuse.  The treated water is returned to the river while the
sludge is temporarily stored in a barge.

Massachusetts, *Rivers,  Treatment, *Recycllng, Sludge, Mining, *Iron

Magnetic Clarifier, Apparatus, Magnetic Separation, Boston, *Charles River,
Bottom Waters, *Iron Filings
 002D

IRON REMOVAL IN MUNICIPAL TREATMENT PLANTS,

Goswami, S. R.

Diplomats American, Academy of Environmental  Engineers

Water and Sewage Works, Vol. 120,  No.  10,  p 52-55,  82-84,  October,  1973.
7 fig, 2 tab, 7 ref.

The presence of iron in groundwater and  in various  stages  of  treatment  in
selected municipal water treatment plants  was related to field  studies  at
the same locations.  Experimental  parameters  measured were pH,  oxidation-
reduction potential (Eh), temperature, alkalinity,  dissolved  oxygen,  ferrous,
filterable ferrous, and total iron.  Field data at  particular raw water
wells and operational data of raw, aerated, filtered, and  softened  waters
of municipal treatment plants treating iron-bearing groundwaters  were
compiled.  The ranges of Eh for raw and  aerated waters  of  treatment plants
treating iron-bearing groundwaters are between 180  to 370  mv  and  380  to
500 mv, respectively.  The Eh is considerably increased by chlorination at
any stage of treatment.  The range of ferrous iron  concentration  varied
from 1.30 to 9.09 mg.  The Eh appears to be a useful analytical test  in
controlling the various stages of  treatment of iron bearing groundwaters.
There is a general correlation between the increase in  Eh  with  decrease in
filterable ferrous Iron content.  The variation of  Eh from raw  to finished
water is an excellent parameter indicating the efficiency  of  treatment
processes.  The Eh measurements could be incorporated in the  water  treatment
plants as an automatic monitoring  device as used in waste  treatment plants.

Treatment, *Groundwater, *Iron, Waste Water Treatment,  Municipal  Water,
*Monitoring, *Oxidation-Reduction  Potential
                                        230

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003D

THE PHOSPHATE PRECIPITATION IN COMMUNAL WASTE WATERS (Die
Phosphat-Faellung in kommunalem Abwasser),

Gleisberg, D. Kandler, J. and Peantek, G.

Chemie-Ing.-Techn., Vol. 45, No. 20, p 1225-1226, 1973.  2 fig. 1 tab.

The possibility of the chemical precipitation of phosphates and of the
reduction of the BOD and COD values in municipal wastewater was studied at a
wastewater treatment plant serving some 10,000 inhabitants.  Preprecipitatlon,
coprecipitatlon, and direct precipitation were studied.  The precipitants
used were aluminum sulfate containing 15 percent alumina, and ferric sulfate
with about 43 percent ferric oxide.  The precipitation was conducted in a
mixing tank.  The phosphate:Al and phosphate:iron ratios were set at
1:1.27 and 1:2.4, respectively.  The pH value averaged 7.5.  Precipitation
of 80 percent of the orthophosphate ions in about ten seconds was determined.
The efficiency of preprecipitation, coprecipltation, and direct
precipitation in terms of phosphorus removal was 97-99 percent, 93-94 percent,
and 97-98 percent, while mechanical-biological purification without pre-
cipitation had an efficiency of 10 percent only.  The reduction in the BODS
values was 93-99 percent for preprecipitation, 83-88 percent for coprecipitatlon,
and 60-77 percent for direct precipitation, compared to a control value of
94 percent for the case of biological treatment.  The corresponding figures
for the reduction of the COD were found to be 84-91 percent, 60-74 percent,
55-59 percent, and 67 percent.  Water samples taken after chemical precipitation
of the phosphates, and incubated with Anabaena flos-aquae, considerably
inhibited algal growth.

*Phosphates, Treatment, *Biochemlcal Oxygen Demand,  *Chemical Oxygen Demand,
Water Pollution Treatment, Treatment Facilities, *Anabaena, Algae
004D

STUDIES ON THE SUITABILITY OF MICRO STRAINERS FOR THE REMOVAL
OF SUSPENDED MATTER FROM BIOLOGICAL CLEARING FACILITY
EFFLUENTS (Unterauchungen ueber die Eignung des Mikrosiebes
zur Entnahme suspendierter Stoffe aus den Ablaeufen biologischer
Klaeranlagen),

Hanisch, B.

Schweizerische Bauzeitung, Vol. 91, No. 39, p 946-949, September,  1973.
6 fig, 2 ref,

Mlcrostrainers for the removal of suspended matter from biological wastewater
treatment plant effluents, and experiments with such microatrainers, are described.
Microstrainers constitute horizontal rotary drums with very fine steel wire
mesh of 23 or 35 microns on their surfaces through which the purified effluent
passes from  the inside to the outside.  The retained particles form a filter
layer on the inside of the drum, and thus help retain very small suspended
particles.   Zooglea bacteria are controlled by UV irradiation.  The strainer
resistance,  i.e., the water level difference between the inside and the outside
of the drum, ranges from 10 to 15 cm.  Experiments with a mlcrostralner on
the removal  of suspended matter from biological wastewater treatment plant
effluents revealed a retention efficiency of 33-91 percent from an effluent
mixed with return sludge, and a BODS reduction of 26-73 percent.  Purified
effluents from a percolation filter, passed through a microstrainer, experienced
a reduction  in their suspended matter content from 24-164 mg/liter to 5-36
mg/liter, and a BODS reduction from about 110 mg/liter to less than 25 mg/liter.
The straining efficiency and the optimum operating parameters, such as the
rotational and peripheral speeds, strain resistance, and flushing water expenditure,
are basically determined by the properties of the suspended matter and of the
strainer fabric.

*Filters, *Separation Techniques, Bacteria, Suspended Solids, Treatment,
Waste Water  Treatment.

*Mlcr o s traIner s
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 005D

 EXPERIMENTAL HYDROPONIC GARDENING WITH MUNICIPAL WASTE-
 WATER,

 Sias, D. R. and Nevln, T. A.

 Dept. of Oceanography, Florida Institute of Technology,
 Melbourne, Florida

 Bulletin of Environmental Contamination and Toxicology, Vol. 10, No. 5,
 1973.  3 fig, 1 tab, 9 ref.

 The use of hydroponics in a municipal wastewater reuse process was evaluated.
 Tomatoes and radishes were grown in five beds irrigated as follows:  irradiated
 wastewater from a Cobalt 60 facility; potassium nitrate added to wastewater
 before irradiation; KN03 added to wastewater after irradiation, and untreated
 wastewater as a control.  Growth in the chlorinated effluent was one quarter of
 that in the control and was repressed when KN03 was added to irradiated effluent.
 Radishes grown in irradiated wastewater were appreciably heavier than any crops
 other than that grown as the control.  Tomatoes also grew best in irradiated
 wastewater, but seemed to do better when there was a higher concentration of
 nitrogen as nitrate.  They grew poorly in chlorinated wastewater, achieving only
 one third the weight of the controls.  It is concluded that hydroponics, in Its
 present state of development, is readily adaptable to the use of wastewater
 treatment plant effluents, probably removing plant nutrients which might
 otherwise become pollutants, as well as producing foodstuffs economically.
 Further, a repeated use of otherwise lost water can be accomplished.

 *Hydroponics, *Aquiculture, Municipal Wastes, *Waste Disposal, Municipal Water,
 Irradiation, Chlorination, Agriculture, Tomatoes, *Recycllng

 Radishes
006D

CARBON TREATMENT OF A MUNICIPAL WASTEWATER,

Burns, D. E. and Shell, G. L.

Eimico Processing Machinery Division,  Envirotech Corporation,
Salt Lake City, Utah

Journal of the Water Pollution Control Federation,  Vol.  46,  No.  1,  p  148-164,
January, 1974. 8 fig, 13 tab, 21 ref.

The use of powdered carbon for the removal of soluble organics  from municipal
raw wastewater was evaluated in a Salt Lake City, Utah,  pilot plant study.
The carbon treatment system included two  carbon contactors,  a granular media
filter, a gravity thickener, and a vacuum filter.  Solid contact units were
very effective for contacting and removing powdered carbon  for  chemically
treated and gravity clarified municipal wastewater.  The two-stage, counter-
current contacting was more efficient, (requiring less carbon)  than single-
stage contacting.  The total solids recycle and variable area clarification
zone features of the units used were key  factors in providing a significant
level of biological activity without odor problems  and In accomplishing
effective removal of carbon solids.  Effective gravity clarification  of  carbon
suspensions was achieved at overflow rates of up to 0.8  gpm/sq  ft without the
use of flocculation aids.  Granular media filtration effectively removed carbon
particles from carbon contactor effluent.  Alum treatment followed  by a  two-
stage counter-current carbon contacting with 75 milligram/liter dosage would
cost $0.83/1000 gal, including chlorinatlon.  The predicted  plant effluent
quality would be considerably better than a secondary biological treatment
effluent for all parameters, but particularly for phosphorus and suspended
solids.

Utah, *Pilot Plants, Carbon, Waste Water  Treatment, Municipal Wastes,
*Sewage Treatment

*Salt Lake City, *Powdered Carbon
                                       232

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007D

OZONE:  AN ALTERNATIVE TO CHLORINE?

Slither, J. T.

Journal of the Water Pollution Control Federation,  Vol.  46,  No.  1,  p 4-6,
January, 1974.

The advantages of ozone as an alternative to chlorine disinfection  of wastewaters
is discussed.  Beginning in 1977, all municipal treatment plants have to
disinfect their effluent to achieve a fecal coliform level of  200/100 milli-
liter.  Pilot investigations show that ozone is a quicker and  more  efficient
disinfectant than chlorine by a factor of 3,000.   A five milligram/liter
dose of ozone applied for less than two minutes yielded  a significant reduction
in total plate count and fecal coliform levels in wastewater effluent.  Ozone
can reduce the number of viruses, but the techniques are tentative, and actual
reductions uncertain.  Ozone does not leave a residual of compounds toxic  to
aquatic life.  Ozone can reduce the concentration of suspended solids to less
than two milligrams/liter.  Tertiary treatment plants have used  ozone to reduce
the biochemical oxygen demand, the chemical oxygen demand, cyanides, and
phenols.  It requires about two parts ozone to destroy one part  phenol.
Production cost is the largest single item in ozone treatment.  It  would cost
a one mgd plant using ozone for tertiary treatment $0.26/1000 gal;  but a
50 mgd plant, only $0.10/1000 gal.

Municipal Water, *0zone, *Coliforms, Sewage Bacteria, *Disinf ection, Viruses,
Biochemical Oxygen Demand, Chemical Oxygen Demand,  Phenols

Cyanides
008D

A MEMBRANE BIOLOGICAL FILTER DEVICE FOR REDUCING WATERBORNE
BIODEGRADABLE POLLUTANTS,

McClure, G. W.

Boyce Thompson Institute for Plant Research,  Yonkers,
New York,

Water Research, Vol. 7, No. 11, p 1683-1690,  1973.   2  fig,  2 tab,  12  ref.

A membrane biological filter device for reducing waterborne biodegradable
pollutants was modeled by a laboratory system.   A phenylcarbamate-degrading
population of microorganisms reduces the concentration of the herbicide
isopropylphenylcarbamate (IPC) in a continuously flowing stream.   The
microorganisms are kept separate from the feed  stream  by an ultrafilter
membrane which retains the microorganisms,  but  allows  passage of all  smaller
materials.  As the feed stream passes through the device, IPC is  transferred
to the bath of microorganisms and metabolized.   The percentage reduction of  IPC
in the feed stream depends primarily on the efficiency of transfer across
the membrane, the velocity of the feed stream,  the quantity of microbes
retained in the bath, and the factors affecting their  activity.  An
equation is derived relating these variables under  the assumption  of
complete transfer of IPC to the bath and a  constant rate of IPC
degradation per unit of microbes.  Problems and improvements are  discussed.

Filtration, Membranes, *Biological Membranes, Membrane Processes,
*Herbicides, *Biodegradation

*Isopropylphenylcarbamate


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  009D

  ALTERNATIVE STRATEGIES FOR MANAGING WASTEWATER,

  Howe, R. S.

  Indiana University, Bloomington, Indiana

  Journal of Soil and Water Conservation, Vol. 28, No. 6, p 252-255,
  November/December, 1973. 2 tab, 10 ref.

  Strategies for managing wastewater are discussed; they include activated sludge,
  physical-chemical treatment, and land disposal.  The activated sludge procesf
  consists of pretreatment, primary clarification, and single stage biological
  treatment.  The process requires some means for disposing of sludge, as
  through dewatering at the plant and then transporting the dried solids to
  a land disposal site, or it may entail transport of liquid sludge by barge,
  truck, or pipe to a land disposal site.  The physical-chemical process
  requires a means for disposal of the substantial quantities of solids that
  are generated.  Chemicals frequently used are lime, alum, and iron salts.
  land disposal systems can be categorized as infiltration systems (recharge
  tasins, septic tanks, absorption fields, spray disposal, and ridge and furrow
  basins) or irrigation systems (spray irrigation, flood irrigations, and the
  living filter).  Advantages of the activated sludge system include small land
  area, lower initial capital investment, removal of certain toxic materials,
  and ability to handle overload situations, and greater immunity to the
  vagaries of weather.  Disadvantages include higher operating costs, more
  difficult operation, and use of chemicals that may introduce trace quantities
  of impurities that result in water quality standard violations.

  *Water Management (Applied), *Water Treatment, *Activated Sludge, *Land
  Management, Land Use

  *Physical-Chemical Treatment, *Land Disposal
01OD

SMALL TOWN SPENDS A BIG $8 MILLION,

Hickeman, R. E.

Whitman and Howard, Inc., Boston, Massachusetts

Water and Wastes Engineering, Vol. 10, No. 12, p 42-44, December, 1973.

The design and operation of the secondary waste treatment plant in West Warwick,
Rhode Island are described.  Renovation and enlargements were made on existing
plants to provide a 5.0 mgd facility to help clean up the Pawtuxet River.
The $2.5 million treatment plant can provide conventional complete mix
activated sludge and step aeration methods of secondary treatment depending
on the quality, quantity, and characteristics of the raw wastewater.
Septic from individual homeowner cesspools and septic tanks is delivered by
tank trucks In a daily volume ranging from 6,000 to 25,000 gallons.  The
septage Is passed to a receiving tank, chlorinated for odor control, degritted,
and stored.  There are four square aeration tanks each with one 7.5 hp
fiberglass mechanical surface aerator which register BOD levels ranging from
1000 milligrams/liter to 350 milligrams/liter.  The system readily adjusts
to varying demands while maintaining a mixed liquor concentration between
2.900 and 4.700 milligrams/liter and dissolved oxygen levels between 2.0
and 3.0 milligrams/liter.  The digester was converted into a post-chlorine
contact tank which pumps the excess activated sludge into two sludge flotation
thickeners.  The thickened sludge is then dewatered.

*Water Treatment, *Rhode Island, Activated Sludge, Aeration, Septic Tanks,
Waste Treatment

West Warwick, Pawtuxet River, *Secondary Treatment
                                           234

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011D

CHEMICAL ADDITION TO TRICKLING FILTER PLANTS,

Nlckerson, G. L., Robson, C. M., Morrison, R. D., and
Clinger, R. C.

Arthur Beard Engineering, Inc., Chevy Chase, Maryland

Journal of the Water Pollution Control Federation, Vol. 46, No. 1, p 133-147,
January, 1974. 9 fig, 7  tab, 3 ref.

The application of a chemical addition system for increasing the overall BOD
and SS removals at two Fairfax County, Virginia, trickling filter wastewater
treatment plants is described.  Ferric chloride was added at the influent and
of the grit chamber and  cationic polymer was added in the Parshall flume,
just before the flow enters the primary clarlfiers.  These additions achieved
approximately 85 percent SS and 60 percent BOD removals.  Hydraulic capacity
was increased by raising the wall levels of critical manholes and structures
where overflows had previously occurred, but this correction frequently
caused an overflow at another.  A total chemical cost to treat the liquid
flow averaged approximately $85 per million gallons at one plant and $71
per million gallons at the other plant.  Increased sludge handling problems may
be expected when chemical addition to the liquid stream is practiced for
increased removal of oxygen demanding materials.  Existing sludge handling
facilities should be carefully reviewed for adequacy.  Any necessary improvement
should be made before liquid stream chemical addition.  Further, addition
of chemicals to the sludge handling system may be required to enhance
thickening and dewatering operations.

*Filtration, *Virginia, Water Treatment, *Biochemical Oxygen Demand,
*Suspended Solids, *Hydraulic Engineering, *Chemical Engineering

Fairfax County
012D

COAGULATION OF STORMWATERS AND LOW ALKALINITY WASTEWATERS,

Ketchum, L. H., Jr, and Weber, W. J., Jr.

University of Notre Dame, Notre Dame, Indiana

Journal of the Water Pollution Control Federation, Vol.  46,  No.  1,  p 53-62,
January, 1974.  17 fig.

The clarification of low alkalinity wastewaters was investigated by the
chemical combination of lime and activated silica.  To facilitate control
and to study significant variables, synthetic systems were  made  by  adding
known quantities of selected substances to water to produce the  desired
experimental characteristics.  Studies of stormwaters and wastewaters were
subsequently conducted to confirm the observation made on the synthetic
systems.  The lime and activated silica were effective.   Low alkalinity
wastewater can be coagulated with  .002 moles/liter of lime  or .00075 moles/liter
moles/liter of lime plus 3.75 milligrams/liter of activated silica.  Based
on these prices and dosages, the cost per million gallons of wastewater
treated using lime alone and lime plus activated silica  are $11.92  and $8.72,
respectively.  This chemical cost savings and the decreased  sludge  to be
handled make the use of activated silica economically advantageous  when
alkalinity is in the ranges indicated.

*Chemical Engineering, Water Treatment, *Storm Water, Hydrogen Ion  Concentration,
*Alkalinity, *Waste Water Treatment, Lime, Silica

Activated Silica

                                          235

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 013D

 A CASE  STUDY OF CHLORINE CONTACT TANK INADEQUACIES,

 Araman, V. K. and Evans, R. L.

 Illinois  State Water Survey, Water Quality Section

 Public  Works, Vol.  105, No. 1, p 59-62, January, 1974.  3 fig, 2 tab, 11 ref.

 The physical, chemical, and bacteriological performance characteristics of
 the chlorine contact tank of the Pekin, Illinois, waste treatment plant
 were  evaluated under air agitated and quiescent conditions.  The hydraulic
 flow  characteristics were determined by adding Rhodamine-B dye at the outlet
 end of  the circular launder of the secondary settling tank.  Samples were
 taken at  the outlet end.  Simultaneously samples were obtained from the inlet
 and outlet ends of  the chlorine contact tank for pH and temperature measurements,
 residual  chlorine determinations, and bacteriological analyses.  The injected
 dye took  five to ten minutes to be completely mixed, depending upon the
 rate  of flow through the tank.  Chemical and bacterial performance characteristics
 of the  chlorine contact tank with and without air agitation were determined.
 The dissolved oxygen at the outlet was high (3.3 to 6.0 milligrams/liter)
 even  though the dissolved oxygen content of the settling tank effluent in
 the collecting launder was zero or 0.1 milligrams/liter.  The residual
 chlorine  of the effluent samples was relatively high, varying from 1.6 to
 3.6 milligrams/liter.  The fecal coliform count, which is the controlling
 parameter, was higher than the desired limit in six out of eight samples.
 It was  concluded that the residence time distribution of the flow-through
 in a  contact tank is important in obtaining satisfactory bacterial quality.

 Waste Treatment, *Water Treatment, *Treatment Facilities, *Illinols, *Dissolved
 Oxygen, Coliforms,  *Chlorine, Municipal Wastes

 *Chlorine Contact Tank
OUD

EVALUATION OF THE ACTIVATED SLUDGE QUALITY WITH RESPECT TO THE
TECHNOLOGY OF WASTE WATER TREATMENT,  (Az eleveniszap-minoseg
ertekelese tisztitas-technologiai szempontbol) ,

Caanady, M.

Hidrologiai Kozlony, Vol. 53, No. 9-10,  p 406-417,  September-October,  1973.
16 ref.

A systematic analysis of activated sludge quality data obtained  for  biological
wastewater treatment plants in Hungary shows persistent impairnent of  the
quality of the activated sludge during the last several years.   The  findings
also show the great Influence of the quality of the activated  sludge on  the
quality and nature of the wastewater.  Wastewater treatment plants handling
typical domestic effluents feature activated sludge concentrations of  6-7
g/liter in the recirculation, and 3-3.5 g/liter in  the aeration  tank at  100
percent recirculation.  The corresponding values were found to be 10-12  g/liter
and 5-6 g/liter in municipal wastewater treatment plants handling also
inorganic, mostly industrial, effluents.  In industrial wastewaters  with
high organic loads, e.g., such as those generated by dairies and other food
processing industries, sludge with poor settleability is obtained even with
normal specific sludge loads, which considerably reduces the sludge
concentration, and requires increased aeration  tank volume if  the necessary
purification efficiency is to be maintained. As the prescribed  sludge con-
centration of four g/liter in oxidation ditches is  reached only  exceptionally,
a lower value of three g/liter is recommended for design purposes.   The
settling of sludges with poor settleability can be  increased through
increasing the settling time, or by means of adequate sludge thickening
facilities.

*Activated Sludge, Municipal Wastes,  *Treatment Methods, Domestic Wastes,
Effluents, *Biologlcal Treatment

*Hungary

                                        236

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 015D

 BIOLOGICAL WASTEWA.TER TREATMENT SYSTEM DESIGN.   PART  I.
 OPTIMAL SYNTHESIS,

 Mlshra, P. N.,  Fan,  L-T.,  and  Erickson,  L. E.

 Kansas State University, Manhattan,  Kansas

 The Canadian Journal of  Chemical Engineering, Vol.  51,  No.  6,  p 694-701,
 December,  1973.  1  fig,  1  tab, 45 ref.

 The optimization of  both the structure and design of  a  biological wastewater
 treatment system was Investigated using the  structural  parameter system
 synthesis technique.  The  system was composed of a  trickling  filter, an
 activated sludge aeration  vessel, and  a secondary clarifler.   The results
 of optimal synthesis Indicate  that the activated sludge system by itself is
 the most economical  wastewater treatment system for the chosen set  of parameters.
 This was to be expected  as activated sludge  systems have been observed to
 be generally more cost effective than  trickling filter  systems for  high
 degrees of treatment.  It  can  be concluded that systems generated by optimal
 synthesis are consistently the same and do not  possess  different structures
 even if the general  structures from which they  are  deduced  are different.
 Trickling filters have certain operational advantages,  and  combinations
 of trickling filter  systems and activated sludge systems may  be optimal for
 a different set of  parameters.  Results may  be  different if operating
 costs are also accounted for.

 *Waste Water Treatment,  Municipal Wastes, *Biological Treatment, *Trickling
 Filters, Activated  Sludge, Aeration

 Clarifier, *Structural Parameter System Synthesis
016D

BIOLOGICAL WASTEWATER TREATMENT SYSTEM DESIGN.   PART II.   EFFECT
OF PARAMETER VARIATIONS ON OPTIMAL PROCESS SYSTEM STRUCTURE AND
DESIGN,

Mishra, P. N., Fan, L-T., and Erickson, L. E.

Kansas State University, Manhattan, Kansas

The Canadian Journal of Chemical Engineering, Vol. 51,  No.  6,  p 702-708,
December, 1973.  10 fig, 1 tab, 8 ref.

The effects of parameter variations on optimal  process  system  structures
and designs for biological wastewater treatment systems were investigated.
The strategy employed was to synthesize the system for  different  sets  of
parameter values and examine the corresponding  changes  in the  system structure
and design.  The results indicate that optimal  system structure and  design
are sensitive to variations in the rate constants and feed  concentration.
Some of the process flowsheets deduced are innovative and have surprisingly
low total costs.  The process system structure  and designs  developed merit
careful consideration in the future planning of new wastewater treatment
plants and In the expansion of existing wastewater treatment facilities.  The
results were based on capital costs alone, and  operating  costs were  not
taken into account.  Capital costs themselves can vary  to a certain  extent
and this may lead to different structures and designs for the  biological
wastewater treatment system.

*Waste Water Treatment, Municipal Wastes, *Costs, Biological Treatment,
Trickling Filters, Activated Sludge, Aeration

*Structural Parameter System Synthesis
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 017D

 EFFICIENCY TESTS FOR MICROSTRAINER WASTE TREATMENT,  (Maikuro
 sutorena ni yoru shorisui kojo shiken),

 Iwata, Y., Ito, Y., and Kamata, 0.

 Nagoya Municipal Government Department  of Sewage Works.
 (Japan)

 Mizu Shori Gijutsu, Vol. 14, No. 2, p 45-50,  October,  1973.   14  ref.

 Experiments were conducted for evaluating the efficiency of 510-mesh micro-
 strainer using the secondary treatment water  of a sewage treatment  plant,  and
 a mixture of primary settling pond sewage screened by  60-mesh net and  the
 secondary treatment water.  The drum rotation speed,  cleansing water pressure,
 and SS concentration were varied to see  the turbidity, SS, BOD,  permanganic
 acid COD, and coliforms, by sampling water every two hours for 24 hours.
 The most important point in the function of a microstrainer is the  setting
 of filter loss head, which has a close relationship with the  SS  and BOD
 elimination rates.  When a film is formed on the mesh, smaller SS can  be
 eliminated, and the elimination rate of  a given mesh  Improves.  Therefore,
 to get a maximum elimination efficiency, the loss water head  must be set for
 quick film formation; yet, if the loss water head is  too great,  the film
 will be destroyed and the elimination rate will decrease. If SS concentration
 of the treatment water is constant, the  relationship  among loss  water  head
 and the drum rotation speed, and cleansing water pressure can be calculated.
 If the filter speed and cleansing water  pressure are  constant, the  slower
 the rotation speed, the greater will be  the loss water head.   The results
 of the experiments showed that when SS was 7 ppm, the filter  index  was 7/m
 with the secondary treatment water; with the mixed sewage water  of  15  ppm
 SS, FI was 5.2/m.  Loss water head and  SS-BOD elimination rates  have close
 relationships, but the elimination conditions are quite different.  With
 the secondary treatment water, when loss head was 19mm, SS elimination rate
 was 42.3 percent, but BOD elimination with H (loss head) 12 mm was  31.2 percent.
 And when H (loss head) increased, BOD elimination decreased.   In the mixed
 sewage, with the loss head increase, BOD elimination  rate decreased, but
 SS elimination rate increased gradually.  The maximum COD elimination  rate
 in any case was 10 percent; the microstrainer seemed  ineffective for COD.

 *Sewage Treatment, Water Treatment, Treatment Methods, Municipal Wastes,
 *Biochemlcal Oxygen Demand, *Suspended  Solids.

 *Microstrainer
018D

SOLIDS THICKENING IN OXYGEN ACTIVATED SLUDGE,

Speece, R. E. and Humenick, M. J.

University of Texas, Austin, Texas

Journal of the Water Pollution Control Federation, Vol. 46, No. 1, p 43-52,
January, 1974.  9 fig, 2 tab, 6 ref.

The solids thickening limitation, which exists when oxygen activated sludge
Is designed according to conventional air activated sludge principles,  was
analyzed.  The mixed liquor suspended solids (MLSS) concentration characterizing
the crossover point where the thickening  function governs the  area requirements
of the final clarifier instead of clarification was defined.   The increased
capital costs for the aeration tank and  final clarifier were demonstrated
for municipal wastewaters in the region beyond the crossover point.  A
suggested design rationale was outlined  to take advantage of some of the
options inherent in commercial oxygen activated sludge.  Solids separation
can be achieved within the aeration tank  by confining  the turbulence within
the DBCA.  The resulting relatively quiescent  conditions within the  sludge
blanket permit clarification in the region above the sludge blanket  recycle
intake.  Thus, solids separation can be achieved in an  integrated aeration
solids separation system.  The thickening function and  its inherent  limitation
are thereby eliminated, opening up the possibility of eliminating the final
clarifier.  Savings of 33 percent in capital cost are projected for  an
integrated aeration solids separation system over a conventional  system.
The process is patented.

*Activated Sludge, Aeration, Suspended Solids, Waste Treatment, *Waste  Water
Treatment, Municipal Wastes

*0xygen Activated Sludge, *Mixed Liquor Suspended Solids

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019D

THE BEHAVIORS OF HEAVY METALS IN THE REGENERATION PROCESS OF
SEWAGE TREATMENT ACTIVATED CARBON,  (Gesui short kasseltan no
kanetsu salseiji nl okeru jukinzoku no kyodo) ,

Urano, K and Nakamura K,

Yokohama National University (Japan), School of Engineering;
Fuji Chemical Co., (Japan), Department of Liquid Treatment

Gesuido Kyokai-shi, Vol. 10, No. 115, p 19-22, December, 1973.  6 ref.

The possibility of causing air pollution as a secondary pollution during the
regeneration of particulate activated carbon by a heating process utilized
in the tertiary tests of various sevage treatment plants was examined by
measuring the heavy metal content released from the carbon.  Six kinds of
activated carbons used at various treatment plants were dried, packed in
quartz tubes, and heated at various temperatures between 200!j and 960^ C
for 10 to 80 minutes.  After heating, the carbon was cooled in nitrogen, and
100 ml of 25 % nitric acid was added.  After boiling for two hours the
carbon was filtered, diluted by distilled water, and analyzed for copper,
chromium, manganese, lead, zinc, and mercury by atomic absorption.  The
results showed that activated carbon utilized in sewage treatment contained
(per 1 kg of dry material), 800-1700 mg of Cu, 150-1800 mg of Cr, 15-80 mg
of Mn, 5-20 mg of Pb, 500-1700 of Zn, and 0-5 mg of Hg.  Since activated
carbon before being used for sewage treatment contained almost no heavy
metals, it was assumed that metals adsorbed on carbon due to the treatment
process was considerable.  Hg compounds at 200% C or more, and Zn and Pb
compounds at 800JjC are gasified when regenerating carbon.  Since part of
these metals will be released in the flue gas, it is necessary to install
flue gas treatment system for reactivating used activated carbon.

Sewage Treatment, *Activated Carbon, *Tertlary Treatment, Metals, Treatment
Methods,  *Heavy Metals, Municipal Wastes

*Secondary Pollution, Reactivation
020D

ALUMINUM IN FLUORIDATED DRINKING WATER:  ANALYTICAL AND
PHYSIOLOGICAL PROBLEMS,

Ruzicka, J, A. and Mrklas, L.

The Institute of Dental Research, Prague, Czechoslovakia

American Water Works Association Journal, Vol. 66, No. 1, p 53-55, January,
1974.  2 tab, 12 ref.

In a laboratory test mice drunk solutions and suspensions of sodium fluoride
and aluminum sulphate with controlled pH.  The tests revealed the effects of
different forms of aluminum and of different pH levels on the utilization by
human beings of fluoride in drinking water.  Aluminum that is used in the
coagulation process for treating drinking water is usually present in tap
water at various concentrations.  Relatively firm complexes of aluminum Ions
with fluoride are formed at a ratio of up to six fluorine per one aluminum.
There is a decreased utilization of fluorine in solutions with a lower pH.
At high pH levels the utilization of fluorine gradually  Increases.  The
fluorine interacts with the aluminum flocculant present  in the solution.
The fluorine concentration used was approximately 25 times higher than that
currently used for fluorldation of drinking water.  The  consequent increase
In the ratio between the complex bound fluorine and the  free fluoride ion
was recognized, and it accounts for the  difficulty that  may arise in the
process of utilization of fluorine by mice.  The coagulation process used
In drinking water treatment by means of  aluminum salts does not diminish
the effectiveness of dental-caries prevention achieved by fluoridatlon of
drinking water.

Water, *Water Utilization, *Domestic Water, Consumptive  Use, *Aluminum,
*Hydrogen Ion Concentration, Municipal Wastes

*Fluoridatlon

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D21D

TOXIC WASTE HANDLING BECOMES CHEAPER,

Materials Reclamation Weekly, Vol. 124,  No.  1,  January 5,  1974.

A process for the fixing of toxic wastes such as heavy metals in solution
so that the final solid product can be used  as  impervious  landfill  with very
low leaching levels is being introduced  into the United Kingdom.  The Chemfix
process involves the use of a 40 foot  mobile road trailer  in which  reagents
are housed for metering into the toxic waste and pumping the fixed  product,
which sets hard after a certain length of time, to the discharge point.
Costs for the system, including disposal, but excluding hauling  charges,
were quoted at between 1.8 and 3.8 p/gallon, (approximately 4.3  to  9,1
cents/gallon) depending on the waste being processed.   The process  is
being operated wherever quantities of  waste, either in lagoons or storage
tanks, exceed 50,000 gallons.  In the  United States, the process was  developed
to handle a wider range of materials and to  cope with more frequent occurrence
of homogenous wastes than those found  in the United Kingdom.  For economic
reasons it is preferred that the suspended solids are  in a five  percent or
more proportion to the liquid, and that the  wastes contain appreciable
amounts of inorganic sludge and suspended solids, particularly heavy  metals.

Waste Disposal, *Landfills, *Waste Water Disposal, Metals, *Heavy Metals,
Waste Storage, Municipal Wastes

*Chemfix, *England, Mobile Trailer
022D

SPEED UP WATER PLANTS,

Camp, J. R., and Kreske, W. J.

1705 Grand Drive, Deerfield, Illinois

Water and Wastes Engineering, Vol. 11, No. 1, p 27-29, January, 1974.  1 fig.

A process to condition floe for filtration is described that eliminates
sedimentation, reduces the needed size of flocculation units, and cuts chemical
costs, while giving faster throughput.  The basis for the Thomas R. Camp
process is the relationship of floe volume concentration to mean velocity
gradient.  The method as claimed in the patent, U.S. 3,660,284, applied
to  operating conditions whereby water or wastewater is treated with from 6-50
ppm of floe-forming chemical in a mixing chamber operating at a mean velocity
gradient G corresponding to values of floe volume concentration between 50-300
ppm.  The G values necessary to achieve the floe volume concentrations desired
vary from about 150 to 1000 per second, and flocculation is essentially complete
after five minutes of mixing at these speeds.  A ten-month field test in New
Bedford, Massachusetts, indicated that the Camp process was commercially
feasible when applied to the highly colored water currently being used at
New Bedford.  The process saved New Bedford $1.75 million in capital for a
new 30 mgd facility by eliminating the need for sedimentation basins.
Savings in annual operating costs of a minimum of $15,000 could be achieved
from reduced chemical requirements.

Water Treatment, Flocculation, *Filtration, *Pre-Treatment (Water), Costs,
''Monetary Benefits, Pilot Plants, *Massachusetts, Municipal Wastes

*Thomas R. Camp process, New Bedford

                                         240

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  02 3D

  SELECTION  OF  THE  IRON  AND  MANGANESE REMOVAL  PROCEDURES  TO  BE
  USED  IN  SMALL WATER  TREATMENT  PLANTS,  (Alegerea  schemelor  de
  deferizare si demanganizare  a  apel la  statlile de  tratare  mici),

  Nitescu, S.

  Hidrotehnica, Vol. 18,  No. 11, p  573-578,  November,  1973.   13  ref.

  A simplified  method  for selecting the  iron and manganese removal  procedures
  to  be  used in small  water  treatment plants is presented.   Usually the  removal
  procedures are  selected by means  of a  pilot  station.  The  cost of a  pilot
  plant  at a small  treatment plant  is high,  due to the fact  that the cost  of
  the pilot  station is almost  equal to the cost of the production installation
  itself.  Various  factors have  been verified  which  allows its elimination.
  The removal procedures  are selected on the basis of  physico-chemical indices
  which  are  described  and discussed.  The procedures under consideration are
  aeration of water, oxidation of ferrous and  manganese compounds,  treatment with
  substances which  increase  the  water's  alkalinity,  treatment of water with
  coagulant  substances,  decantation and  filtration.  Methods for differentiation
  of  waters  containing iron  and  manganese, treatment of waters with mineral
  content, treatment of  water  with  alkaline  substances, or oxidizing substances,
  as  well  as methods for treatment  of waters with  humic iron and manganese
  compounds, are  presented.  After  selection of removal method,  it  is  necessary
  to  experiment on  models in order  to determine the  optimum  filtration para-
  meters and chemical  doses.

  Effluents, Municipal Wastes, treatment Methods, *Pilot Plants, Aeration,
  Oxidation, Metals, *Iron,  ^Manganese
 024D

THE LAND TREATMENT PROCESS FOR WASTEWATER RENOVATION,

Hlnesly, T. D.

University of Illinois, Urbana, Illinois

Public Works, Vol. 105, No. 2, p 62-66, February, 1974.

The land treatment process for wastewater renovation is discussed with emphasis
on spray irrigation.  There are three distinct types of land treatment systems:
overland flow, rapid infiltration/percolation, and crop irrigation.  An
overland flow land treatment system is used for soils with very low infiltration
and/or percolation capacities.  Rapid Infiltration/percolation systems are
used where deep permeable soil materials are available.  The crop irrigation
system may embody various methods of applying secondary-treated effluents
by spray applications or flooding on land through furrows or borders.  Spray
irrigation has the greatest applicability to different soil types and cultural
practices.  This treatment may be used on varying terrain, requires less land
preparation, and is less labor Intensive when compared to other methods of
irrigation.  Maximum benefits are realized from the plant and animal nutrients
recycled in growing plants, which is a most important reason for choosing
irrigation over other systems.  Maintaining a water^unsaturated aerobic zone
in the soil surface ensures more complete filtering and adsorbing of wastewater
pollutants.  The site should be selected so that the frequencies and rates
of water applications will be limited by the soil's capacity to filter,
absorb, and precipitate pollutants, rather than by soil hydraulic characteristics.

Land Management, Land Use, *Soil Management, *lrrlgation, *Mist Irrigation,
Infiltration Rates, *Infiltration, *Percolation, *Water Treatment, Municipal
Wastes
                                       241

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 025D

 A CHLORINE DEMAND  STUDY  OF  SECONDARY  SEWAGE EFFLUENTS,

 Lin, S.  and Evans,  R.  L.

 Illinois State Water  Survey,  Peorla,  Illinois

 Water and Sewage Works,  Vol.  121,  No.  1, p 35-44, January, 1974.
 1 fig,  4 tab,  10 ref.

 Samples of sewage  effluent  from  three types of  secondary sewage treatment were
 chlorinated with calcium hypochlorite and chlorine water at dosages through
 12 milligrams/liter chlorine.  Chlorine demands were ascertained by periodic
 determinations of  residual  chlorine during a time span of 60 minutes.  The
 chlorine demands were  observed to  be  influenced by the initial dosage, contact
 time, and the  source  of  chlorine.  In general,  the higher the dosage, the
 greater the demand.  The demand  of the sewage effluents was consistently
 less when using calcium  hypochlorite  compared to chlorine water.   The demands
 also varied from run  to  run and  with  the types  of sewage treatment.  Two
 geometric expressions, one  for contact times of 1-12 minutes, and  the other
 for times of 12-60 minutes, were useful for predicting the chlorine demands of
 domestic sewage.  These  expressions utilize the weight ratio of the chlorine
 dosage and the ammonia-N concentration of the sewage effluents.

 *Sewage Treatment,  *Chlorination,  Mathematical  Studies, Municipal  Wastes,
 Chlorine

 *Chlorlne Demand,  Calcium Hypochlorite
026D

DISINFECTION PRACTICES IN THE SAN FRANCISCO BAY AREA,

White, G. C.

Wallace and Tiernan Division of Pennwalt Corp.,
San Francisco, California

Journal of the Water Pollution Control Federation,  Vol.  46,  No.  1,  p 89-101,
January, 1974.  7 fig, 1 tab, 11 ref.

The disinfection of wastewater in the San Francisco Bay  area,  based on an
Investigation of 36 treatment plants over a six month period in  1972 is discussed.
The data collected included:  type of treatment process, characteristics of
Influent wastewater, chlorine dosage, chlorine consumption,  chlorine residual,
biochemical oxygen demand of influent and effluent, suspended  solids in the
effluent, contact time, contact chamber configuration, MPN of  coliform in
effluent, dye studies of contact chambers, pH, ammonia nitrogen,  mixing at
point of application, type of chlorine control system, monitoring if any,
reliability of operation, and method of measuring chlorine residual.  The
data are organized in groups characterized by the basic  treatment process:
11 primary, 15 activated sludge, four secondary using highrate recirculatlng
filters, four secondary followed by oxidation ponds, one tertiary,  and one
consisting of oxidation ponds only.  Conclusions drawn from the  study were
numerous.  Mixing was of major importance to good disinfection performance,
the mixing device being well-planned.  The optimum dosage of chlorine for
disinfection of domestic wastewater is between 10 and 15 milligrams/liter.
Thy optimum residual with adequate mixing such as in a hydrualic  jump seems
to be between 3-4 milligrams/liter with not less than 30 minutes  contact
time.

*Disinfection, *Water Treatment, California, *Treatment  Facilities, Domestic
Water, Activated Sludge, Filtration, Oxidation, Chlorine, Recirculated Water,
Municipal Wastes

*San Francisco Bay Area
                                        242

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027D

FULL-SCALE TESTING OF A WATER RECLAMATION SYSTEM,

Horstkotte, G. A., Miles, D. G., Parker, D. S., and
Caldwell, D. H.

Central Contra Costa Sanitary District, Walnut Creek,
California

Journal of the Water Pollution Control Federation, Vol. 46, No. 1, p 181-197,
January, 1974.  3 fig, 10 tab, 17 ref.

The full scale testing of a 300 mgd water reclamation system that will produce
water for industries located along the southern shore of Suisun Bay, California,
is described.  Treatment in the planned plant will consist of lime coagulation-
sedimentation, nitrification, and denitrlfication.  Performance data for a
representative three months of operation were tabulated and indicate that
the performance of the Advanced Treatment Test Facility (ATTF) is stable.
The concentration of organics in the nitrified and denitrified effluents
is low, as measured by BOD and organic carbon.  Operation for complete
nitrification also results in high organic removals.  Suspended matter
concentrations in the nitrified and denitrified effluents are also exceptionally
low.  This is attributed in part to the fact that the sludge has tended to be
in a bulking condition, and effluents from bulking sludges are quite commonly
very clear.  Total nitrogen in the denitrified effluent averages less than 2
milligrams/liter.  More than half of the effluent nitrogen is organic nitrogen,
much of which will be removed by effluent filtration.  Total phosphorus is
below the one milligram/liter limit.  Based on the three months of performance,
it is concluded that the system can dependably produce the quality of
effluent required by Contra Costa County Water District.

Water Treatment, *Pilot Plants, *Coagulation, *Sedimentation, *Nitrification,
*Denitrification, Effluents, Municipal Wastes

*Advanced Treatment Test Facility
028D

SUCCESSFUL APPLICATION OF GRANULAR CARBON SOLVES QUALITY
PROBLEMS,

Bowling, R.

Water Works Superintendatit, Paris, Kentucky

Public Works, Vol. 104, No. 1,  p 70-71,  December, 1973.

The successful application of granular carbon in the four filters  at the 1.5
mgd water treatment plant at Paris, Kentucky is described.  Off taste and odor
appeared at Paris irregularly and could  last from a day  or two to  a week or
more.  Efforts to pinpoint the source of the trouble were never completely
successful.  The plant had previously used powdered carbon,  but switched to
granular because the granular appeared to offer a more efficient use of
adsorptive capacity of the carbon, decreased need for monitoring the raw
water, no capital expenditures requirements and suitable hydraulic
characteristics.  During a two-week period 50,000 pounds of  granular activated
carbon were loaded into four filters, each of 275 square feet.  The carbon/sand
combination of dual media filtration increased the filter capacity.  The
number of backwashes is less, but the volume of water used is not  as low as
the frequency would Indicate because the filters are washed  somewhat longer
than before.  At 8 and 12 months the measurement of carbon bed depth revealed
no measurable loss of carbon due to the backwashlng.  The minimum  life of the
carbon is estimated at three years; it costs each of the 9,000 customers a
fraction of a cent per day for a dramatic improvement in water quality.

*Water Quality, *Filtration, Kentucky, Treatment Methods, Odor, Taste,
*Activated Carbon, Costs

*Granular Carbon

                                       243

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 029D

 DRUG RESISTANT COLIFORMS CALL FOR REVIEW OF WATER QUALITY
 STANDARDS,

 Grabow, W. 0. K., Prozlesky, 0. W., and Smith, L. S.

 National Institute for Water Research,  South African
 Council for Scientific and Industrial Research,
 P.O. Box 395, Pretoria, South Africa

 Water Research, Vol. 8, No. 1, p 1-9, 1974.  1 tab, 126 refs.

 The need for a reevaluatlon of the role of coliforms in water quality is
 discussed.  The therapeutic value of antimicrobial drugs is diminishing
 due to the rapid increase of resistant bacteria.  A current prominent type of
 resistance is mediated by R factors (extrachromosomal nucleic acid elements)
 which may cause high level resistance to many drugs.  These factors may also
 provide resistance to other antibacterial agents such as ultraviolet light,
 heavy metals, bacteriocins, and phages, and may enhance the virulence
 and infectivity of pathogens.  Evidence is presented that sewage-polluted
 water may play an important role in the spread of coliform and other
 bacteria-carrying R factors.  Since coliforms have joined forces with bacteria
 increasingly involved in disease, they can no longer be regarded as harmless
 indicators of fecal pollution.  This calls for reevaluation of water quality
 standards and for more advanced purification of sewage prior to discharge
 into the environment.

Water Treatment,  *Sewage Treatment,  Coliforms,  Microorganisms, Bacteria,
 *Water Quality, Water Pollution,  *Water Pollution Control

 *Fecal Coliform
 030D

 NTA REMOVAL IN SEPTIC  TANK AND  OXIDATION  POND  SYSTEMS,

 Klein,  S.  A.

 University of California,  Berkeley,  California

 Journal of the Water Pollution  Control  Federation, Vol.  46,  No.  1, p  78-88,
 January, 1974.  11 fig,  2  tab,  12  ref.

 The biodegradability of  trisodium  nitrilotriacetate  (NTA)  in pilot scale  septic
 tanks and  leaching field systems was investigated  to  determine  its potential
 as a replacement for phosphate  builders in synthetic  detergents.  The removal
 of NTA averaged 21.8,  23.3, and 23.1 percent in three septic tanks during the
 nine months of operation.   Effluents from the septic  tanks flowed into
 percolation fields contained in a  four-compartment box.   Five to seven weeks
 were required for biological slimes to  develop  and become acclimated  to NTA
 in the fields.  In normal  aerobic  percolation fields  all the NTA was
 essentially degraded  from influents containing concentrations up to 60
 milligrams/liter.  Totally anaerobic fields degraded  ten percent NTA, but
 under nearly anaerobic conditions  NTA degradation  was virtually 100 percent.
 The presence of NTA had  no noticeable effect on performance of  septic tank
 percolation fields or  sewage treatment systems.  In  aerobic soil columns,
 NTA was nearly 95 percent degraded from influent concentration  of  40  and
 100 milligrams/liter.   In anaerobic soil columns,  degradation ranged  from
 10-15 percent for the three influent NTA concentrations examined.   In oxidation
 ponds, after a two-month acclimation period, steady  state removal  of  NTA
 was in excess of 90 percent when influent concentrations were in the  range
 normally expected in wastewater.

 Leaching,  *Septic Tanks, *Blodegradatlon, *Pilot Plants, *Nitrogen Compounds,
 Oxidation Lagoons

 *Leaching Fields, Nitrilotrioacetate

                                         244

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031D

ENHANCED NITRIFICATION BY ADDITION OF CLINOPTILOLITE TO
TERTIARY ACTIVATED SLUDGE UNITS,

Sims, R. C. and Little, L. W.

University of North Carolina, Chapel Hill

Environmental Letters, Vol. 4, No. 1, p 27-34, 1973.  2 fig,  2 tab, 15 ref.

A new technique for improving the efficiency of the nitrification process in
the treatment of wastewater is described based on the surface sorption property
of a natural zeolite, Hector Clinoptilolite.  The process utilizes the zeolite
as a solid phase in an activated sludge unit.  The zeolite selectively sorbs
ammonium ions from wastewater and therefore provides an ideal surface for the
attachment of nitrifying bacteria which oxidize ammonium ion to nitrate ion.
The removal of the adsorbed ammonium ion from the zeolite by nitrifying bacteria
allows regeneration of the zeolite surface and thus enables the same zeolite to
be used repeatedly.

*Nitrification, Water Treatment, *Sorption, *Activated Sludge, Oxidation,
Bacteria, *Zeolites

*Hector Clinoptilolite
032D

WATER AND POLITICS IN COASTAL CALIFORNIA - THE DIABLO
CANYON EXPERIENCE,

Lee, K. N.

University of Washington, Seattle, Washington

Science and Public Affairs, Vol. 30,  No. 2, p 29-35,  February,  1974.

The relationship between public utilities and public  opinion is illustrated
through a discussion of the Diablo Canyon desalting facility of central
California.  The primary capacity of  the plant would  have been  the production
of fresh water.  One of its secondary capacities would have been to use some
of the waste heat from a neighboring nuclear power plant.  Less desirably,
the desalting plant would have altered the pattern of land use  on its  small
part of the California coast.  The plant would have been a strong incentive
for population growth and would have provided important engineering and
technical benefits in terms of water  decontamination  and in giving the
United States a valuable International advantage.  Environmental groups
opposed the desalting plant and aroused public opinion to the extent  that
the voters passed an initiative requiring close scrutiny of future coastline
development plans.  Eventually, the federal government cancelled the
construction of the plant due to budget restrictions  and the announcement
of a similar plant being built in Hong Kong that would provide  equivalent
learning benefits to the engineering  community.  The  project failed because
it did not recognize that utilities have social consequences and responsibilities
that cannot be ignored.

Water Treatment, *Municipal Water, *Desalination, Treatment Facilities,
California, Social Impact, *Social Values, *Nuclear Powerplants, *Recycling
                                        245

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033D

CHLORINE FOR EFFLUENTS IN SHORT SUPPLY,

Journal of the Water Pollution Control Federation, Vol. 46, No. 1, p 2-4,
January, 1974.

The chlorine shortage is discussed as it relates to the disinfection of
wastewater effluent, and solutions are suggested.  The total sanitary usage
for chlorine for 1973 is estimated at 460,000 tons. Manufacturers prefer
industrial contracts to municipal ones because many cities are restricted by
their charters from advertising for contracts that extend longer than one
year or provide for periodic price escalations.  Municipal buyers frequently
include requirements for free extras (as containers) in their bid forms.
Legislation may be required to allow manufacturers to break long-term industrial
contracts in order to fill sanitary chlorine requirements preferentially.
Manufacturers are generally committed by contract to 100 percent of their
production and cannot legally allocate any fractions off the top to mun-
icipalities.  The current policy is to supply 1973 contractees again in 1974,
allowing reasonable increases.  The questions of how to handle either new
users or greatly increased demands on the part of old users have not been
resolved.

*Chlorine, Water Treatment, *Disinfection, *Municipal Water
  034D

  THERMAL DRYING OF MECHANICALLY DEHYDRATED URBAN SEWAGE SLUDGE
  IN A BOILING LAYER SYSTEM (TERMICHESKAYA SUSHKA MEKHANICHESKI
  OBEZVOZHENNYKH OSADKOV GORODSKIKH STOCHNYKH VOD V KIPYASHCHEM
  SLOYE),

  Yakovlev, S. V., Kalitsun, V.  I., and Varlygin, A. P.

  Vodosnabzheniye a Sanitarnaya Tekhnika, No. 12, p 5-9, 1973.   4 fig,  4 ref.

  The thermal drying of mechanically dehydrated urban sewage sludge in  a slot
  type fluidized-bed drier was studied.  Small pieces of mechanically dehydrated
  sewage sludge were fed into an upright cylindrical space and  were kept suspended
  over a slot by hot gas stream entering the cylinder through that slot.  The
  dried sludge particles entrained by the hot gas stream were separated by a
  cyclone.  Slot type fluidized-bed driers were found highly suitable for the
  drying of urban sewage sludge at thermal efficiencies  of 57-58 percent, at an
  initial moisture content of 60-65 percent and for particle sizes not  larger
  than 20 mm.  The fluidized-bed height should not be less than 250 mm, and
  the hot gas temperature should be between 450 and 500  C.  The specific fuel
  expenditure was found to range from 1,200 to 1,250 kcal/kg evaporated moisture.
  The drying capacity, determined for final moisture contents of 20-30  percent
  and 6-10 percent, amounts to 500-550 kg/cu m. h and to 600-650 kg/cu  m. h,
  respectively.

  *Sewage, *Sludge, *Treatment Methods, *Dehydration, Forced Drying, Steam,
  Municipal Wastes

  Fluidized-bed Drier
                                        246

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 035D

EFFECTS OF EQUALIZING WASTEWATER FLOWS,

LaGrega, M. D. and Keenan, J. D.

Drexel University, Philadelphia, Pennsylvania

Journal of the Water Pollution Control Federation,  Vol.  46,  No.  1,  p 123-132,
January, 1974.  6 fig, 5 tab, 8 ref.

The effects of equalizing wastewater  flows on treatment  efficiency  was
investigated in a full scale study at the Newark,  New York,  activated sludge
plant.  The plant treats an average flow of approximately 1.8 mgd.   The first
phase of the study characterized plant operation during  normal flow conditions
by reducing the plant to marginal operating conditions.   During the second
phase, the raw flow was diverted to the second aeration  tank for equalization.
The total volume of the equalization  tank was 412,000 gallons with  an effective
depth of 12 feet.  The raw wastewater in the equilization tank was  aerated
to prevent sedimentation and avoid septic conditions.  The results  of a diurnal
sampling program indicate rather poor primary removals in the first phase.
Overall removal of BOD approached 90  percent, while COD  and  SS removals were
about 75 percent.  Primary removals of BOD and COD  were  only 12 percent,
while SS were reduced by 23 percent.   The only substantial difference in
phase two was in the SS and VSS data.  If the influent to the primary
clarifier is compared with the effluent, the SS removal  efficiency  was
47 percent.  It is concluded that the most significant change of composition
occurring in the equalization tank is the reduction in diurnal variability
and maximum concentration.

*Activated Sludge, Municipal Wastes,  Municipal Water, Treatment Facilities,
New York, *EffIciencies, Sanitary Engineering, Aeration, *Biochemical Oxygen
Demand, *Chemical Oxygen Demand

*Wastewater Flow
03 6D

SMALL TOWN GETS AN EFFICIENT WASTE SYSTEM,

Geisinger, D. W. and Mastropietro, M. A.

C. T. Male Associates P. C., Schenectady,  New York

Water and Wastes Engineering, Vol. 11, No.  1, p 32-34,  January,  1974.

The efficient secondary wastewater treatment facilities installed  in Nlskayuna,
New York, are described.  The new plant is rated at 1.5 mgd capacity,  uses
the conventional activated sludge process  with anaerobic digstion  of waste
sludges, and supplements the original plant constructed in 1966,   The  improved
facility consists of a coarse bar rack, aerated grit chamber,  comminutor
chamber, primary settling tanks (2),  aeration tanks(2), parshall  flume
meter chamber, secondary settling tanks (2), chlorine contact  tanks  (2),
air flotation thickener, anaerobic sludge  digesters (2), and sludge  drying
beds.  The existing primary settling tanks were converted to secondary
settling tanks by minor modifications.  A  second anaerobic digester  was
added with floating gasholder to provide the added sludge handling capacity.
The cost totaled $980,000 with construction amounting to $894,750.   The
plant serves approximately 5,000 people, or 1/3 of the design  population.
The only problems with start up were grit  removal and freezing in  the  winter.
All secondary sludge was continuously returned at an average rate  of 50 percent.
Within two weeks, the MLSS was up to  2,000 ppm, and BOD and suspended  solids
removal were in excess of 80 percent.  In  the first five months  of 1973,
BOD efficiency ranged from 90-95 percent,  while SS removal efficiency  ranged
from 89-97 percent.

Treatment Facilities, *Activated Sludge, *Anaerobic Digestion,  *Aeration,
*Costs, Biochemical Oxygen Demand, Suspended Solids, *Sewage Treatment, New
York, Municipal Wastes

Niskayuna
                                        247

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037D

DENITRIFICATION IN GRANULAR CARBON AND SAND COLUMNS,

English, J. N., Carry, C. W., Masse,  A. N., Pitkin, J. B.,
and Dryden, F. D.

National Environmental Research Center, Cincinnati, Ohio

Journal of the Water Pollution Control Federation, Vol. 46,  No. 1, p 28-42,
January, 1974.  13 fig, 5 tab, 1 ref,

The devitrification of secondary effluent in granular carbon and sand columns
was investigated in a four stage, fixed bed, 0.3 mgd pilot plant.  The effect
of denitriiication on column operation, COD removal efficiency, and carbon
regeneration was determined.  Supplementary nitrate was added to secondary
effluent during two carbon column adsorption sequences to obtain average
concentrations of 25.8 and 21.8 milligrams/liter N03-N.  There were removals
of 80 and 92 percent, respectively, with most of the denitrification occurring
in the first stage (ten minutes detention time)  and 3-4 milligrams/liter
N03-N removed, without methanol in the subsequent stages.  The methanol
requirement was 1.9 times the N03-N removed plus 1.1 times the dissolved
oxygen removed.  There was no significant impairment of the carbon's ability
to remove COD in either adsorption sequence, and removals of 72 percent of
COD in the first sequence and 66 percent in the second were within the
expected range.  Biological growth made backwashing necessary twice a day and
headlosses average 30 to 50 psi after  less than 12 hours of operation.
The total cost of a 10 mgd plant using sand as the media was estimated
at $71/million gallon.   If denitrif ication is combined with dissolved organic
removal in an activated carbon system, the additional  cost for denitrification
was estimated to be $25/million gallon.

*Pilot Plants, Effluents, Waste Treatment, *Sewage Treatment, Carbon,
*Denitrification, Chemical Oxygen Demand, Municipal Wastes

*Granular Carbon, *Sand  Columns, Regeneration
  038D

  CYANIDE WASTE TREATMENT UTILIZING CATALYTIC OXIDATION,

  Woolhiser, and Clark, D.

  Air Force Weapons Laboratory Report No.  AFWL-TR-73-37, October, 1973.

  Two major sources of liquid cyanide wastes are electroplating operations
  and color photograph processing having waste streams that vary in concentration
  from under one mg/liter to over 100,000 mg/liter.  To meet state effluent
  standards which range from 0.25 mg/liter to undetectable levels, a system
  utilizing a proprietary cobalt-based catalyst and chlorine-producing electro-
  lytic cells was evaluated with actual photographic and electroplating wastes.
  A prototype catalytic oxidation system capable of treating 0.25 gpm of 2000
  mg/liter total cyanide waste produced effluent streams containing undetectable
  amounts of cyanide with copper plating and nickel strip feeds.  Treatment of
  photographic wastes produced an 87 to 94 percent reduction of total cyanide.
  Effluent cyanate levels were generally under 10 mg/liter for copper solutions
  and ranged from 4 to 42 mg/liter for nickel strip solutions.  The catalytic
  oxidation system has a strong potential for decreasing the operation costs
  of cyanide destruction systems.  System designs are given for two full-scale
  cyanide waste treatment systems.

  Waste Treatment, Liquid Wastes, Effluents, Evaluation, Standards, Effluent
  Streams, Design Criteria, Operating Costs, Industrial Wastes, Treatment
  Facilities

  Electroplating, Photographic Processing, *Catalytic Oxidation, *Cyanides
                                         243

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039D

REMOVAL OF PHOSPHATES FROM WASTEWATERS WITH ELECTRO-
CHEMICALLY GENERATED GADOLINIUM IONS,

Onstott, E.

U.S. Atomic Energy Commission

A method of electroprecipitation of phosphates from secondary sewage effluents
with anodically generated GD3+ was investigated using a gadolinium metal anode
and stainless steel cathode.  At the anode Gd was oxidized to Gd3+, which
precipitated phosphates, and at the cathode H2 gas was evolved.  For electro-
lysis  times in excess of theoretical, removal of soluble orthophosphate was
greater than 99 percent to concentrations of about 0.02 mg/liter P; soluble
condensed phosphate removal was more than 90 percent to about 0.04 mg/liter P;
and, removal of soluble organic phosphate was greater than 80 percent to
about  0.07 mg/liter P.  The electrolytic treatment increased the pH of
product filtrates and a fraction of  the bicarbonate was converted  to carbonate
depending on electrolysis  times.   Some Zn2+ and carbonate, if  the  concentration
of  carbonate exceeded 30 mg/liter, were precipitated by this electrolytic
 treatment.

*Electrochemistry,  Chemical Precipitation, *Phosphates, Sewage Effluents,
Anodes, Cathodes, Waste Water Treatment, Hydrogen  Ion Concentration,
Electrolysis,  Zinc, Bicarbonates

 Phosphate Removal,  *Gadolinium
04 OD

WASTE WATER TREATMENT IN COMMERCIAL FISH PROCESSING:  REDUCING
STICK WATER LOADINGS,

Stiuber, D., and Quigley, J.

University of Wisconsin Sea Grant Program and National Sea Grant Program
Report No. WIS-SG-72-401, November, 1972.

A wastewater disposal problem involving the inadequate treatment of wastewater
resulting from the processing of alewives for fish meal was investigated.
Inplant practice was examined to determine whether process revisions could
be made to reduce the amount of lipids, protein, and other suspended solids
in the discharge.  A further processing step was developed to remove more
solids and to increase product recovery.  The resulting wastewater discharge
was studied for purposes of improving treatment practice.  Owing to the
complexity of the material in the discharge, an anaerobic treatment stage
was found to be required with subsequent design focusing on combination
anaerobic-aerobic systems,   Laboratory scale studies on both glutaraldehyde
and lime coagulation methods were made.  Both processes were subjected  to
cost analysis with generally comparable results.  Preliminary analysis  conducted
on waste water effluent indicated that resulting effluents had comparable
chemical oxygen demand and biochemical oxygen demand values.

Lake Michigan, *Waste Water Disposal,  Liquid Wastes, Waste Water Treatment,
*Commercial Fish, Treatment Facilities, Industrial Plants, Suspended Solids,
Laboratory Tests, Cost Analysis, Coagulation, Design Criteria

Lime Coagulation, *Glutaraldehyde Coagulation, *Anaerobic-Aerobic  Systems,
Fish Processing


                                       249

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 041D

 PHOSPHORUS REMOVAL TREATABILITY  STUDIES AT  C. F. B. BORDON,
 PETAWAWA,  TRENDON AND  UPLANDS,

 Shannon, E.,  and  Rush,  R.

 (Canadian) Environmental Protection  Service and  (Canadian) Department of National
 Defense; Technology Development  Report EPS  4-WP-73-5, December, 1973.

 Results of phosphorus  removal treatabillty  studies  carried out at Canadian
 Forces Bases Borden, Petawawa, Trenton, and Uplands during 1971 and  1972
 are reported.  Traditional  phosphorus precipitants  such  as ferric chloride,
 alum, and  lime, were evaluated with  respect to phosphorus removal efficiency
 via standard jar  testing procedures. Also  the waste-water characteristics and
 diurnal variations at  each  Base  were determined  and discussed.  Costs for
 phosphorus removal at  each  Base  were estimated and  recommendations made
 regarding  the type of  full-scale system  that should be  Installed.  The
 impact of  the phosphorus removal system  on  the receiving waters was  evaluated.

 Canada, *Phosphorus, On-Site Tests,  Efficiencies, Evaluation, Waste  Water
 Treatment, Estimated Costs, Environmental Effects,  *Treatment Facilities, Lime

 *Phosphorus Removal, Waste  Water Characteristics,  Diurnal Variations,
 Treatment  Methods, Alum,  Ferric  Chloride
042D

USE AND PRODUCTION OF IRON SALTS FOR PHOSPHATE REMOVAL,

Scott, D.

Canada-Ontario Agreement on Great Lakes Water Quality Report No  72-3-5
June, 1973.

The principal objective of this study was an assessment of the supply and
probably cost of iron salts for use as phosphate removal chemicals in
wastewater treatment.  The use of iron salts for the precipitation of
phosphate from wastewaters is discussed.  Evidence is reviewed which suggests
that ferrous and ferric salts behave in an equivalent manner due to rapid
oxidation of the former in neutral solutions.  A summary is given of the
nature, source, composition,  and reactivity with dilute sulfuric acid of
major iron containing waste materials available in Ontario, Canada.  The
costs of manufacture of ferrous and ferric sulfate at different production
capacities from a number of theae materials has been estimated.  Treating
coats for phosphate removal using iron sulfate could be as low as 10-20
dollars per million gallons.   For almost all circumstances, the use of
locally manufactured iron sulfates should be competitive with or cheaper than
either alum of imported salts.

*Salts, *Waste Water Treatment, Phosphates,  Chemical Precipitation, Canada,
Sulfates,  Estimated Costs

*Phosphate Removal, Iron Sulfate, Sulfuric Acid
                                      250

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 04 3D

 AEROBIC DIGESTION OF ORGANIC SLUDGES CONTAINING  INORGANIC
 PHOSPHORUS PRECIPITATES:   PHASE  I,

 Ganczarczyk,  J.  and Hamoda,  M.

 Canada-Ontario Agreement  on  Great Lakes  Water  Quality,  72-5-4, June,  1973.

 Three series  of  laboratory batch and semi-continuous  experiments carried
 out at 20!j C  on  the aerobic  digestion of activated  sludges  containing
 aluminum salts or ferric  salts  used  for  phosphorus  precipitation were
 investigated. Treatment  responses measured were digested sludge charac-
 teristics, such  as volatile  solids destruction,  oxygen  uptake, settleability,
 and dewaterability, and supernatant  characteristics,  including total  organic
 carbon, soluble  nutrients, and  suspended solids. The only  variable  that
 was controlled for all experiments was the sludge hydraulic detention time.
 The aerobic digestion of  conventional activated  sludge  was  not affected to
 any significant  degree by the presence of ferric of aluminum precipitates.
 For both the control and  chemically  precipitated sludges an aeration  period
 of 10 to 15 days was required for stabilization. Release of soluble  organic
 carbon and nutrients during  the aerobic  digestion of  activated sludges
 was not altered  appreciably  in  the presence of the  chemical precipitates.
 At the higher chemical dosages  there was a reduction  in nutrient release
 in the supernatant.  Dewaterability  and  settling characteristics of  control
 and chemically precipitated  digested sludges  did not  differ significantly.

 Laboratory Tests, *Aerobic Treatment, *Activated Sludge, Salts, Phosphorus,
 Chemical Precipitation, Aeration, Nutrients,  Organic  Compounds, Carbons,
 Suspended Solids

 Total Organic Carbon Soluble Nutrients,  Dewaterability, Settleability,
 Oxygen Uptake, Volatile Solids  Destruction, Ferric  Salts, Aluminum Salts
04 4D

REVERSE OSMOSIS PROCESS AND ITS APPLICATION,

Mori, K. and Tsuge, H.

Kobe Steel Engineering Reports, Vol. 24, No. 1, p 20-26, January  1974.
12 fig, 2 tab, 54 ref.

The present status of research on reverse osmosis is briefly reviewed.   Recent
work conducted at Kobe Steel Ltd. which includes preparation of semipermeable
membranes and separation of heavy metal ions from plating rinse water  is
discussed .

*Research and Development,  Reverse Osmosis,  *Heavy Metals,  Separation
Techniques, Reviews, Industrial Wastes, *Membrane Processes

Japan
                                         251

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04 5D

AUTOMATION OF THE CONTROL AND OPERATION OF WATER POLLUTION
CONTROL WORKS,

Cotton, P.

Water Pollution Control, Vol. 72, No. 8, p 635-657, 1973.
25 ref.

The development of automation in the sphere of water pollution control does
not appear to have matched that in many other industries due mainly to the
following factors:  inadequacy in fundamental process design knowledge; lack
of investment and hence development in process-control equipment; lack of
coordination between plant designers and plant operators; relatively wide
range of flow rates coupled with the rapid changes in character and strength
of crude sewage; and, methods of financing both capital and running expenses
of sewage treatment.  Existing and potential system of automation of individual
process units are discussed with respect to their coordination in providing a
greater degree of automatic operation.  The function and expected advantages
of the computer-controlled system at Norwich, England is described with the
purpose of providing evidence and data for future development and for providing
a greater store of operating and maintenance data.

*Automation, Equipment, *Water Pollution Control, Data Collections, Operation
and Maintenance, *Coraputers, Computer Programs, Control Systems, Filtration,
Sedimentation, Equipment, Activated Sludge, Sludge Treatment, Sludge Disposal,
*Sewage Treatment, Biological Treatment

Great Britain
04 6D

REDEVELOPMENT OF HAVEN SEWAGE-TREATMENT WORKS,  COLCHESTER,

Suriyadasa, R.

Water Pollution Control, Vol. 72, No.  8, p 693-704,  1973.   6  tab,  1  ref.

Redevelopment of the Haven sewage treatment works,  constructed  in  1884, was
initiated in 1901, completed in November 1970,  and  stressed mainly the ex-
tensions to the main drainage system and sewage treatment works.   Topics  in
reference to this redevelopment scheme, discussed herein, include  the  low-
level pump house, sewage treatment,  sludge treatment and disposal, power
generation, central control, aesthetics, and costs.

*Sewage Treatment, Treatment Facilities, Equipment,  Pumping Plants,  Storage
Tanks, *Storm Runoff, Sedimentation,  Biological Treatment,  Activated Sludge,
Tertiary Treatment, Sludge Treatment,  Sludge Disposal,  Powerplants,  Control
Systems, *Costs

Great Britain,  *Facillties Extension
                                       252

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047D

LIME STABILIZATION OF PRIMARY SLUDGES,

Farrell, J. B., Smith, Jr., J. E., Hathaway, S. W., and
Dean, R. B.

Journal of the Water Pollution Control Federation, Vol. 46, No.  1, p 113-122,
January, 1974.  3 fig, 9 tab, 15 ref.

Preliminary studies conducted on sludges supplied by the Lebanon, Ohio
wastewater treatment facility's pilot  plant operation Indicated  that costs
of lime treatment would be low, pathogens and odor greatly reduced, and
filterability improved.  These findings led to lime treatment of sludge on
a plant scale during alum and iron addition experiments and to documentation
of the results.  The following results are reported from this investigation:
lower sludge solids are obtained when alum and iron are added to the primary
clarifier; the addition of lime to alum and Iron chemical-primary sludges
increases  the vacuum filter yields to  reasonable rates; lime addition does
not make the sludges chemically stable and that the pH eventually falls
and surviving bacteria may return if conditions are favorable, yet the
microbiological portions of this Investigation indicate that lime treatment
of sludge raising it to a pH of 11.5 reduces bacterial hazard to a negligible
value.

*Sludge Treatment, Treatment Facilities, *Pilot Plants, Investigations, Iron,
*Lime, Pathogenic Bacteria, Aluminum,  Filtration, Hydrogen Ion Concentration,
Odor, Waste Water Treatment, Water Pollution Control, Effluents

Chemical Treatment
  048D

  NEW SLUDGE  PROCESSING  PLANT  OF  THE  BEESTON AND  STAPLEFORD
  URBAN  DISTRICT  COUNCIL,

  Water  and Water Engineering,  Vol. 77,  No. 931,  p  341-343,  September,  1973.

  After  completing investigations involving pilot plants,  long-term  analytical
  work,  and negotiations with  industrialists,  it  has been  recommended that  the
  installation  of a mechanical  dewatering plant be  undertaken  and  that  provision
  be  made  for the tankerlng  of  sludge to this  central  location.  In  the case  of
  the Beeston installation,  a  system  of  chemical  conditioning  followed  by filter
  pressing was  recommended.  The  chemicals are mixed with  the  sludge to promote
  easier separation of water from solid  matter.   The filter  pressing involves
  straining water under  pressure  through a fine fabric to  leave a  cake  on the
  fabric.

  *Sludge  Treatment,  *Dewatering, Treatment Facilities,  *Chemicals,  Mixing,
  Separation  Techniques, Filtrat-ion,  Equipment, Construction Costs

  Great  Britain
                                       253

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 04 9D

 MAJOR WASTEWATER TREATMENT PLANT TO BE UPGRADED,

 Foster, J. H.

 Public Works, Vol. 104, No. 12,  p 47-50,  December,  1973.   2  fig,  3 tab.

 Cleveland, Ohio's Southerly Treatment Plant,  in meeting the  most  cost  effective
 solution, is an example of designing to meet  high effluent quality standards
 where major financial investments were required to  modify facilities  that  have
 been outmoded according to present regulations.  As a prelude to  finalizing
 design concepts and selection of unit treatment processes, prototype  and
 bench scale studies, reported herein, were made to  determine process  parameters
 for nitrification and phosphorus removal.  Based on these studies and  evaluation
 of data on current and future conditions, a treatment system was  selected
 consisting of primary sedimentation, a two-stage activated sludge process, and
 effluent polishing by filtration and disinfection.   A summary of  the  basic
 design criteria for the expanded facilities now under design is tabulated.
 Construction of facilities is planned to start during 1974 at an  estimated
 cost of approximately $160 million.

 *Sewage Treatment, *Treatment Facilities, Economic  Efficiency, *Construction
 Costs, Nitrification, Laboratory Tests, Phosphorus, *Design Criteria,
 Sedimentation, Activated Sludge, Filtration,  Disinfection

 Cleveland, Ohio, Phosphorus Removal
050D

CARTMEN DEVISES TECHNIQUE FOR DISPOSING OF 3.5 MILLION GALLONS
OF LIQUID DISCARDS ANNUALLY,

Solid Waste Management, Vol. 17, No. 1, p 12-13, 24, 80, 105,  January,  1974.

In order to accommodate the disposal of the vast quantities of liquid and
sludge wastes generated by an excess of 6500 containerized commercial and
industrial accounts in Canada's Ontario Province, the Superior Sanitation
Services, Ltd. installed a modified Carver-Davis incinerator at its plant.
It was not long after the plant opened that difficulties became evident in
the hauling, burning, and handling aspects of the enterprise.   As a result
of experimentation, watertight modular containers have been constructed and
equipped with various systems of pipes, valves, and sieves designed for screening
out the foreign solid objects as the unit is either filled or  emptied.   To
compensate for the differences in Btu properties of the various kinds of refuse
handled, to reduce the incidence of necessity for supplemental support  fuel,
and to maintain the more-evenly burning mixture in the combustion chamber,  the
storage tanks have been equipped with control gauges and metering valves for
blending appropriate proportions of each type of liquid.

*Liquid Wastes, *Waste Disposal, Canada, *Incineration, Equipment,  Treatment
Facilities, Storage Tanks, Screens, Gages, Measurement, Instrumentation, Sewage
                                      254

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  05 ID

 TREATMENT METHODS  FOR HEAVY METAL-CONTAINING  LIQUID WASTE
 (Text in Japanese),

 Ishihara,  T.

 PPM,  Vol.  5,  No.  2 p  26-33,  February,  1974.   10  fig,  7  tab, 13 ref.

 Neutralization,  sulfurization,  reduction,  oxidation,  biological  treatment, ion
 flotation,  and adsorption are discussed with  respect  to heavy metal-containing
 liquid wastes.   The neutralization method,  in which metal  ions in  sc lution are
 settled and form hydroxides, is the most widely  used  for recovering  heavy
 metals.  Other methods are usually applied  in combination  with the neutraliza-
 tion  method either as pretreatment (biological,  oxidation, or reduction), or
 post-treatment (adsorption or sulfurization)  methods.

 Reduction  (Chemical),  Oxidation,  *Blological  Treatment, Adsorption,  Flotation,
 Neutralization,  Liquid Wastes,  *Heavy  Metals, *Waste  Treatment

 Sulfurization
05 2D

THE TREATMENT OF WASTE WATER FROM INDUSTRIES AND COMMERCE
IN PUBLIC PURIFICATION PLANTS (Text in German),

Ott, R.

Industrieabwaesser, p 8-11, 1973.  6 ref.

Most domestic wastewater can be treated in public purification plants without
problems and in these mechanical-biological plants a balance can be maintained
which is disturbed only by the entry of industrial wastewater.  Thus industrial
wastewater must be analyzed and its effect on the purification process studied
prior to its discharge to an existing facility if feasible.  If the facility
Is inadequate, the wastewater goes to a regional purification plant.  For
joint treatment of industrial and domestic wastewater, certain condition
procedures and requirements, detailed herein, must be followed.

*Waste Water Treatment, Treatment Facilities, *Ac.tivated Sludge, Domestic
Wastes, *Industrial Wastes, *Feasibility Studies, Efficiencies
                                       255

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 053D

A NOVEL DEVICE FOR IMPROVED AIR AH) LIQUID MIXING (UJ
TIPUSU KESQULEK FOLYADEKOK ERINTKEZTETESERE ES KEVERESERE
LEVEGOVEL),

Nagy, Z., Kovacz, A., Rauschenberger, J., and Hupka, G.

Magyar Kemikus Kapja, Vol. 28, No. 11, p 560-565, 1973.  6 fig, 1 tab, 16 ref.

In silty sewage purification processes, industrial aerobic fermentation
processes, and in purification of industrial waters containing emulsified oil
or fat, it is necessary to provide an intensive contact between the air and
the agitated liquids which contain large quantities of dispersed particles.
According to a new process, the potential energy of the air introduced through
the bottom of the vertical tubes immersed in the liquid is used for the intensive
agitation of the liquid.  The material transfer rate (one to five kg 02/cu m
hour in the sodium sulf ite solution) obtainable in the equipment designed in
this way depends not only on the quantity of air, but also on the velocity
distribution obtained as a result of liquid agitation.

*Fermentation, Sewage, *Sewage Treatment, Industrial Wastes, *Aerobic
Treatment, *Aeration

Silty Sewage
  05 4D

  PURE WATERS PROJECT INCLUDES RESTORATION,

  Dyment,  R.

  Water and Sewage Works,  Vol. 121,  No.  3, p 52-53,  March,  1974.

  Monroe County, New York  began a pure waters program in 1970 which will cost
  $400 million by the time it is completed  in 1975.   It includes  the laying of
  hundreds of miles of sewer lines,  constructing four treatment plants,  tearing
  up streets  and private land, and restoring whatever was disturbed to its
  original state.  Lake Ontario and  other water bodies in Monroe  County  are
  polluted to degrees ranging from severe to moderate, with population growth
  increasing  rapidly, thus adding to the pollution problems.   The county was
  divided into four regions according to drainage basins, and sewer networks and
  treatment plants constructed accordingly.   The new treatment plants will provide
  a minimum of secondary treatment of wastewater.  Attempts have  been made to
  minimize the ecological  disruptions during the construction of  the sewers and
  treatment plants.

  Water Pollution, *Water  Resources  Development, Water Treatment, *Project
  Planning, Projects, Management *Water  Management (Applied), Treatment
  Methods, New York *Lake  Ontario, Great Lakes, Sewers

  Monroe County, New York
                                       256

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    05 5D

    LINEARLY VELOCITY - DECREASING WEIRS,

    Chandrasekaran, D., and Rao, N. S. L.

    Hydraulics and Water Resources Department, College
    of Engineering, Madras, India.

    Surveyor, No. 4263, p 30-32, February, 1974.  3 fig, 3 ref.

    The problem of settling of sediment particles is important in sewage treatment
    units as in grit chambers, water purification works and the treatments of
    a variety of industrial wastes.  Among the many factors that affect settling,
    the mean velocity of flow can be readily controlled by the designer by fixing
    suitably designed weirs at the outlets of sedimentation chambers.   This paper
    presents the exact design of such a weir.  The type of proportional weirs pre-
    sented in this paper have potential as velocity controlling devices and are
    capable of trapping sediments to a removal efficiency of 60 to 85  percent.

    Engineering Structures, Sewers, *Weirs, *Control,  *Sediments, Treatment
    Methods

    *Proportional Weirs
056D

DIRECT-FILTRATION STUDIES FOR METROPOLITAN TORONTO,

Tredgett, R. G.

The Proctor & Redfern Group
Toronto, Ontario, Canada

Journal of American Water Works Association, Vol. 66, No. 2,  p 103-109,
February, 1974.  6 fig, 5 tab, 17 ref.

The Municipality of Toronto will solve an unusual water treatment requirement
with a plant addition of modified design for $4.8 million less than the cost
of a conventionally designed plant.  The old 72-mgd plant, located on an
offshore island in Lake Ontario, is to be doubled in size.  The plant has
been operating since 1911 but now only operates seasonally to meet peak summer
demands.   It has kept detailed records of the raw water quality.  Analysis
of these, assisted by a computer, supported the possibility of direct
filtration.  Pilot studies confirmed that efficient filtration at high rates
was feasible and that the flocculation and settling basins could be eliminated .
The new plant will incorporate these features with significant savings.
The size and quality of the floe produced for filtration is critical to this
design.  Whereas settling requires a large flow, high-rate direct filtration
requires a strong, pinpoint floe barely visible to the eye.  Although the
requirements of the new plant are unusual, the principles leading to its
design are quite basic and may be of interest in the Great Lakes area or
any area with good quality raw water.

*Water Treatment, Treatment Methods, *Filtration, *Municipal
Wastes,  Vater Quality, * Flocculation, *Lake Ontario, Great Lakes,
Computers, Data Processing, Canada, *Waste Water Treatment

Toronto
                                        257

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057D

BA3S TO CLEAN UP SEWAGE,

New Scientist, Vol. 61, No.  890,  p 754,  March, 1974.

An emergency sewage treatment system that kills cholera bacteria  and  dysentery
amoeba has been developed by James Howard,  a public health engineer  working
for Oxfam.  It involves passing sewage into four or more seven meter  diameter
sausage-shaped neoprene bags filled with water and linked  in series by plastic
pipes.  The water presents air getting to the microorganisms which settle
in the sludge at the bottom of the first neoprene section  and die within a
week or two.  Howard envisages a  single seven meter section being used then
buried at the end of 24 hours, in the case of an emergency, such  as an earthquake.

*Sewage, Municipal Wastes, *Water Treatment, Treatment Methods, Microorganisms,
*Bacteria,  Sewers, Pipes, Plastic Pipes, *Waste Water  Treatment

Cholera Bacteria, Dysentery Amoeba, * Emergency Treatment
 058D

 SOUND,  OZONE ZAP GERMS,

 Water and Wastes Engineering,  Vol.  11,  No.  3,  p  56, March,  1974.

 A wastewater treatment system  combining ultra-high frequency  sound  and  ozone  is
 as effective as conventional methods  of disinfection  and may  be  superior,
 according to some scientists at Ibtre Dame  University.  Dr. Gary  Burleson's
 research showed that treatment with sonicatlon,  ultra high  frequency  sound,
 and ozone totally inactivated  each  of three virus  types in  15 seconds and
 six different bacteria,  which  cause such diseases  as  dysentery and  cholera,
 in a minute or less.  When sonication is teamed  with  ozone  a  synergistic
 effect seems to occur.  A pilot plant using Sozone treatment  has  been in
 operation on the Notre Dame campus  since 1971.   Plans for further research
 on the ozone-sonication technique are being made to test the  technique's
 effectiveness on other bacteria and viruses.

 Water Ibllution, V&ter Treatment, Treatment Methods,  *Disinfection,
 *0zone, *Pilot Plants, *Sound  Waves,  *Waste Water  Treatment

 Ultra High Frequency Sounds,  Sonication,  *Sozone Treatment
                                      258

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  059D

  PLANT GETS NEW PROCESS,

  Jeris, J. S., and Flood, F. J.

  Ecolotrol, Inc., Bethpage, New York

  Water and Wastes Engineering, Vol. 11, No. 3, p 45-48, March, 1974.  2 fig,
  2 tab.

  A novel biological denitrification process has been added to Nassau County's
  wastewater renovation plant.  Combining the demands of the increased population
  with the growth of industry over  the past 20 years, the amount of high quality
  water needed and the corresponding quantity of wastewater requiring treatment
  has more than tripled.  The ground water table has been declining due to the
  increased demand for water, with  a corresponding evidence of salt water in-
  trusion, high nitrate-nitrogen concentrations as well as other contaminants.
  Protection of the ground water was incorporated into a master plan which
  included a 500,000 mgd  advanced wastewater treatment plant.  A physical-
  chemical treatment system was built on the site of Nassau County's 60 mgd
  wastewater treatment plant at Bay Park.  The goals of this plan were to learn
  what quality water could be obtained using this advanced water renovation plan,
  to determine the ability and ramifications of recharging this treated water
  into the aquifer, and to obtain the cost of this extensive treatment and
  recharge operation.  Nitrate- and nitrite-nitrogen removal is encouraging,
  the fluidized granular  bed denitrification system being used showing promise
  in supplanting  the biological denitrification processes being used in the
  field today.

  Water Pollution, Water  Treatment, Treatment Methods, Groundwater, *Water
  Table, Aquifers, New York, *Aquifer Management, *Groundwater Recharge,
  Saline Water Intrusion, *Waste Water Treatment

  Nassau County,  New York
06 OD

AN EXPERIMENTAL IRRADIATION FACILITY FOR THE STERILIZATION
OF SEWAGE SLUDGE (EINE VERSUCHSBESTRAHLUNGSANLAGE ZUR
HYGIENISIERUNG VON KLAERSCHLAMM),

Suess, A., Moetsch, H., Bosshard, E., Schurmann, G.,
and Luescher, 0.

Bayerische Landesanstalt fuer Bodenkulter und
Pflanzenbau, Muechen und Freising

Kerntechnik, Vol. 16, No. 2, p 65-70, 1974.  4 fig, 11 ref.

An experimental plant for sterilization of sewage sludge by irradiation with
a 120k Ci-Co 60 source is described.  The main components of the facility are
the irradiation shaft with a built-in central tube in which the sludge is
recirculated during irradiation, and the recirculation system which consists of
an accessible pump shaft with recirculation and evacuation pumps, the necessary
shutoff and regulation valves, and pipework.  In this system untreated digested
sludge Is pumped from the conventional part of the sewage treatment plant to an
above ground silo in which a voiding valve opens and allows a metered quantity
of sludge to flow into the irradiation chamber upon signal.  In said chamber the
sludge is recirculated and forced to flow past both sides of the radiation
sources for a certain predetermined time.  The filling and voiding times of the
irradiation chamber are at present about six minutes each.

*Pilot Plants, *Sewage Sludge, *Sludge Treatment, *Irradiatlon, *Treatment
Facilities, Cobalt


                                       259

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  0610

  VIRUS REMOVAL BY DIATOMACEOUS-EARTH FILTRATION - PART 1,

  Brown, T. S., Malina, J. F., Jr., and Moore, B. D.

  Gibbs and Hill, Incorporated, New York, New York

  Journal of the American Water Works Association, Vol. 66, No. 2, p 98-102,
  Feb., 1974.   3 fig, 6 tab, 11 ref.

  This study,  involving the removal of bacterial viruses from water using
  diatomaceous earth filter aids, covers the comparative properties of uncoated
  and polyelectrolyte-coated products as they affect the process.   The work is
  based on studies using bacteriophage T2 for Escherichia coli.  The removal
  eff ciencies presented were calculated to represent only that removal due to
  attachment to the diatomaceous earth and filtration through the  filter aid.
  The optimal  T2 recovery required attachment at pH 6.25 and desorption at pH 9.55.
  The procedure for coating the filter aid with inorganic coagulants affects
  the efficiency of T2 virus removal.

  *Diatomaceous Earth, *E. Coli, *Viruses, *Bacteriophage, *Filtration,
  Desorption,  Hydrogen Ion Concentration, Efficiencies, Waste Water Treatment

  *Virus Removal
06 2D

THE CHEMICAL TREATMENT OF MUNICIPAL WASTE WATER (ZUR CHEMISCHEN
BEHANDLUNG VON STAEDTISCHEN ABWASSERN),

Bouveng, H. 0.

Schwedisches Forschungsinstitut fuer Wasser- und
Luftreinhaltung, Stockholm, Sweden

Staedtehygiene, Vol. 25, No. 11, p 260-261, 1973.

The Swedish government has adopted a policy of financing 50 percent of the
construction costs of municipal purification plants provided a 90 percent
reduction of BOD and of the total phosphorus is achieved.  This action has
spurred the addition of chemical stages to the mechanical biologic purification
plants since this stage has a higher BOD reduction capability.  In Switzerland
and Finland, simultaneous treatment through chemical precipitation is the most
common practice.  Incorporation of this phase into the existing purification
plant scheme allows for better phosphorus concentration.

*Chemical Precipitation, *Waste Water Treatment, *Municipal Wastes, Treatment
Facilities, Biochemical Oxygen Demand, Phosphorus

Sweden, Switzerland, Finland
                                       260

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063D

POTABLE-WATER SUPPLY BY MEANS OF UPFLOW FILTRATION
(L'EAU CLAIRE PROCESS),

Haney, B. J., and Steimle, S. E.

Tulane University, Civil Engineering Dept.,
New Orleans, Louisiana

Journal of the American Water Works Association,  Vol.  66,  No.  2,
p 117-123, Feb., 1974.  8 fig, 5 tab, 15 ref.

Upflow filtration is a recent development in the history of water  filtration.
By using polyelectrolytes and progressively finer filter media a potable  water
can be produced that compares favorably with waters treated by conventional
methods that require flocculatlon, sedimentation, and  filtration.   The L'Eau
Claire process is a water treatment method that uses both of these developments.
To recognize the potential of upflow filtration in potable-water production,
an upflow research project was initiated using a 4-foot  diameter upflow filter
in the evaluation.  Test results indicate that the process with effluent
disinfection can be used as a means of potable water treatment of  surface supplies,
yielding excellent quality water under continuing operation.  It should be noted
that at turbidities above 280 Jtu the utility  of the process is limited by very
short filter runs.  However, process parameters and plant configuration can
be altered to compensate for this deficiency.

*Filtration, *Evaluation, *Polyelectrolytes, *Potable  Water, *Water Supply,
*Waste Water Treatment, *Performance, *Fllters, Turbidity, Water Quality,
Treatment Facilities

*Upflow Filtration, *L!Eau Claire Process
 064D

 COST EFFECTIVENESS IN SEWAGE TREATMENT,

 Ramsden, I.

 Manager, Lincolnshire Sewage Division,
 Anglian Water Authority, Great Britain

 Surveyor, Vol. 143, No. 4263, p 28-29, Feb., 1974.

 The effects of the removal of slag media from filter beds at the East Kesteven
 RDC and subsequent replacement with plastic filter media are described.
 It is maintained that the capacity of the beds has been increased by at  least
 two-fold.  This la an example illustrated by the author to stimulate cost
 effectiveness ideas for the sewage treatment industry.

 *Cost Analysis, *Project Planning, Optimum Development Plans, Project Purposes,
 Sewage Treatment, Pipes, Personnel Management

 Great Britain
                                        261

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  065D

  OXYGENATION SYSTEM FOR ACCELERATED SEWAGE TREATMENT,

  Weber, R. B.

  Environmental Equipment Division, MAROX Diffusion
  Systems, FMC Corporation, Englewood, Colorado

  Mechanical Engineering, Vol.  96,  No. 3, p 28-33,  March,  1974.   7 fig,  4 ref.

  The use of pure oxygen in sewage  treatment has been investigated for several
  years; however, the acceptance of a pure oxygen system has  been delayed due to
  a lack of satisfactory methods of diffusion oxygen into  the sewage.   The two
  types of diffuser systems detailed herein are designated as the passive
  system and the active system.   The passive system has recently been  installed
  at a waste treatment facility  which handles a relatively high  BOD waste.
  Testing of said system has demonstrated that excellent bubble  quality  exhibiting
  greater than 95 percent efficiency of oxygen transfer in deep  water  is provided
  and that bubble quality does not  degrade with time because  of  plugging or
  corrosion.  The active system  is  being evaluated  for  performance in  aerobic
  digestion of  waste activated sludge.  Results of  batch and  flow-through tests
  indicate superior wastewater  treatment performance at a  lower  capital  expenditure
  and lower operating cost when  compared to existing systems.

  *Sewage Treatment, *0xygenation,  *Waste Water Treatment, Performance,  Capital
  Costs, Testing, Operating Costs,  Treatment Facilities

  *0xygen Diffusion, ^Passive Diffuser System, *Active  Diffuser  System
06 6D

ADVANCED WASTE TREATMENT PROCESS SELECTION, PART TWO,

Gulp, G. L., and Hamann, C. L.

Culp/Wesner/Culp, Clean Water Consultants,
Corona Del Mar, California

Public Works, 10 Vol. 105, No. 4, p 69-74, April, 1974.  5 fig, 3 tab.

The use of chemical oxidation and adsorption for removal of organics and
application of coagulants for phosphorus reduction are discussed.  It is main-
tained that chemical oxidation processes showing any potential for economic
use are limited to ozonation as the technique available at lowest cost, and
that chemical oxidation steps are unacceptable for application to removal of
organics from raw sewage.  Carbon adsorption may be applied to raw sewage for
removal of organics rather than using biological processes, or it can be
applied to secondary effluents.  Powdered carbon and granular carbon adsorption,
regeneration, and reuse are compared.  Chemical coagulants for phosphorus
removal may be added to the primary clarifier influent, the activated sludge
aeration tank, or a tertiary chemical clarifier.  The use of iron and aluminum
salts as coagulants in the aforementioned treatment stages is discussed.

*0xidation, *Phosphorus, *Adsorption, *0zone, *Chemicals, Economics,
Activated Carbon, Iron, Aluminum, Application Methods, Sewage Treatment,
Waste Water Treatment, Organic Wastes, Coagulation, Salts

Powdered Carbon, Granular Carbon, Phosphorus Removal
                                          262

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067D

CHEMICAL-PHYSICAL PURIFICATION PROCESSES FOR RESIDUAL
WASTEWATER AND CIRCULATING PROCESS WATER IN CARDBOARD AND PAPER
MILLS,

Morgeli, B.

Sulzer Technical Review, Vol. 55, p 205-212, March, 1974.  5 fig, 1 tab, 1 ref.

Chemical-physical processes such as flocculation, filtration, ozone oxidation,
and activated charcoal adsorption are discussed in relation to each method's
treatment of circulating and residual wastewater in paper and cardboard manu-
facture.  The salient points of the individual processes are taken up with
examples employed to explain their action singly and in combination with
other processes.

*Reviews, *Flocculation, *Filtration, *0zone, *0xidation, *Actlvated Carbon,
*Adsorption, Methodology, Waste Water Treatment, Pulp Wastes, Pulp and
Paper Industry, Industrial Water
 068D

FURNACE CONSTRUCTIONS FOR INCINERATION (OFENKQNSTRUKTIONEN
FUER DIE ABFALLVERBRENNUNG),

Wasser, Luft and Betrieb, Vol. 18, No. 1, p 28-30, 1974.  4 fig.

Various kinds of furnaces for incineration of a wide variety of waste products
such as odorous wastes gases, communal and industrial sludges, and solid
wastes are described.  Such incineration processes include a fluidized bed
furnace, radiation recuperators, a rotary kiln, and a fourth process for the
specific treatment of liquid  and gaseous wastes.  In this process, waste
products are injected to the combustion chamber via concentrically arranged
burners after which fuel is injected through fine nozzles in a ring around the
burners.  As combustion products, sulfur dioxide and hydrogen chloride develop
apart from water vapor and carbon dioxide which are removed in scrubbers.

*Treatment Facilities, *Incineration, *Waste Treatment, *Liquid Wastes,
Sewage Sludge

Rotary Kiln, Fluidized Bed Furnace, Radiation Recuperators
                                         263

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06 9D

NEW METHODS TO DISPOSE OF USED METALWORKING EMULSIONS, (NEUE
VERFAHREN ZUR BESEITIGUNG GEBRAUCHTER METALL-BEARBEITUNGS-
EMULSIONEN) ,

Moeller, U. J., Boor, U., and Runge, G.

Esso AG Forschungszentrum, 21 Hamburg 90,
Moorburger Strasse 21, West Germany

Erdoel und Kohle-Erdgas-Petrochemie, Vol. 27, No. 2, p 70-71, 1974.  11 fig,
11 tab, 32 ref.

A new method, flame evaporation, has been developed to separate emulsion into
water and oil phases with the aid of heavy fuel oil.  The water content of the
emulsion is converted to steam and removed through the stack.  Simultaneously,
the oil phase and the auxiliary fuel oil is combusted to C02 and water.  The
consumption of the heavy fuel oil is low; the heat of combustion of the
emulsion and auxiliary fuel can be utilized.  Disposal of emulsion by the landfill
method includes the absorption of the oil phase onto aluminum hydroxide and
the placement of the oil floe/water mixture in earth pits having a water
permeable lining.  The oil is converted to a usable compost by means of
microorganistic activity or through use of activated  sludge within six
months.

*Emulsions, *Separation Techniques, *0ily Water, *Burning, Landfills,
Waste Disposal, Absorption

*Flame Evaporation
  070D

  THE AUTOMATIC FILTER PRESS FPAKM (DIE AUOTOMATISCHE
  :?ILTERPRESS FPAKM) ,

  Ermakov, I. S., and Mesengisser, M. J.

  Institut Urkniichimmasch, Charkov, Ukraine, SSR

  Chemische Technik, Vol. 26, No. 1, p 32-33, 1974.  3 fig, 2 tab.

  An automatic chamber filter press with horizontally arranged filter plates
  Chat can be moved electromechanically or hydraulically up and down is described.
  The endless filter band is conducted over rollers back and forth through the
  filtering chambers which are formed by the filtering plates.  The upper section
  of the filtering plates forms the chamber for draining off the filtrate, the
  lower section forms an open frame which upon closing of the filter plates forms
  the chamber for formation of the filtering cake.  Between upper and lower
  sections of the filter plates a rubber membrane is installed for separation of
  the liquid phase by water or compressed air.  The operating time for opening,
  cake discharge, and closing takes about one to two minutes.  The application
  of the chamber filter for sludge-containing industrial and communal wastewater
  is being tested.  In Japan as well as the Soviet Union, this filter press is
  used for dewatering of sewage sludges.

  *Filters, *Automation, *Sludge Treatment, Sewage Sludge, Application Methods,
  Equipment

  *Filter Press, *Filter Plates
                                             264

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07 ID

REVERSE OSMOSIS AND ULTRAPILTRATION - A SURVEY OF AUXILIARY
APPARATUSES AVAILABLE IN THIS FIELD  (tIMGEKEHRTE OSMOSE UNO ULTRA-
FILTRATION - EIN UEBERBLICK UEBER DIE AUF DIESEM GEBIET
VERFUBSBAREN APPARATIVEN HILFSMITTEL) ,

Murkes, J,

Firma Alfa-Laval AB, Tumba, Sweden

Chemische Technlk, Vol. 25, No. 10, p  601-603, 1973.  4 fig.

The principle of reverse osmosis  is explained and a  survey of the following
apparatuses for  said method given:  plate and frame modules, tubular modules,
spiral modules, capillary fiber modules, and ultraf iltration modules.   In plate
and frame modules, round membranes are fastened to a porous supporting material
and stacked in a pressure-resistant casing.  With tubular modules, membranes are
inserted into a tubular permeable supporting  structures similar to the spiral
modules but with a smaller membrane  surface.  Capillary fiber modules are
comprised of many aromatic polyamide fibers wLth a large  specific membrane
surface and whose throughput  is smaller than with plane or tubular cellulose
acetate membranes.

*Reverse Osmosis, *Membrane Processes, *Surveys, Application Methods

Frame Modules, Tubular Modules, Spirial Modules, Capillary Fiber Modules,
Ultraf iltration
07 2D

BEST EFFLUENT THE GOAL,

Cotter, J. E.

Daniel, Mann, Johnson, and Mendenhall, Los Angeles


Water and Wastes Engineering, Vol. 11, No. 2, p 46-49, February, 1974.
4 fig.

The advanced control system which is being installed to aid water reuse at the
Sepulveda Water Reclamation Plant is described.  The plant will provide secondary
treatment by an activated sludge process.  In addition, the effluent from the
final settling tanks will be passed through filter beds for final polishing in
order to make it suitable for its end use.  Raw sewage in amounts up to 40 mgd
will enter the headworks of the plant through screw pump lift stations.  The
plant will have a distinctive control system Jn that almost all control outputs
will be derived from direct digital control logic supplied by a central computer
system.  In addition, all inputs and outputs to the process will be multiplexed
remotely in the field and transmitted in serieal digital form to the computer
center over a common communications cable.

*Effluent, Automatic control, *Water Reuse, *Water Treatment, *Waste Water
Activated Sludge, Sewage, Facilities, Filters,  Computers, Instrumentation,
Engineering, *Waste Water Treatment

* Plant Design

                                      265

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073D

RIPPON SQUASHES CENTRAL WASTE TREATMENT PRECEDENT,

Shwer, M.

Surveyor, Vol. 143, No. 4263, p 10, February, 1974.

A decision regarding the site of a chemical waste treatment plant near
Birmingham, England is discussed.  Environment Minister Geoffrey Rippon refused
the site because local residents put up a strong opposition to a waste treatment
plant on the grounds they had suffered from previous industrial development.
The proposed plant was to have handled up to 10 tons of solids and 45,000
gallons of concentrated aqueous wastes per week by chemical treatment.  A
further two tons of both liquid and solid wastes were to have been incinerated
per hour, adding up to 350 tons per week incinerated.  This last figure is the
equivalent of 80,000 gallons a day of  solvents.  The chemical plant effluent
would have been about 10-20,000 gallons per day, and residues were expected
to amount to some 20 tons per week from chemical treatment and 60-70 tons
per week from incineration.

^Administrative Decisions, *Chemical Wastes, *Waste Disposal, Sites, Waste
Treatment, *Waste water treatment

Great Britain
074D

AUTOMATIC PROCESS CONTROL OF SEWAGE TREATMENT WORKS,

Casling, R. H.

Bolivar Treatment Works, South Australia

PACE, Vol. 26, No. 12, p 14-19, December, 1973.  7 fig.

The sewage treatment processes employed in the new major plants to be found in
the principal cities of Australia are described including the steps being taken
t:o instrument and control them.  Such plants, designed to process the sewage
from populations in excess of 50,000 people can be economically instrumented
and automated.  Conventional sewage treatment is a combination of mechanical,
physical, and biological processes.  The intimate contact between the oxygen
and sewage which is the essential part of secondary treatment is achieved in
one of two ways.  In activated sludge plants, the air is provided by air com-
pressors with capacities of thousands of cubic feet of air per minute at
pressures of approximately 6-8 Ib/sq in.  In filter plants, the settle sewage
is distributed over thick beds of  stone of graded size by some type of
distributor fitted with spreading nozzles.  The process parameters measured
and used in treatment works can be classified as those concerned with
physical quantities and those termed fluid characteristics as dissolved oxygen
level, suspended solids, and BODS.  Automatic controls are used which havee
reduced the operating costs at the major treatment works while giving a standard
of control which is closer to the optimum than can be achieved by manual
neans.

^Sewage Treatment, *Automatic Control, Activated Sludge, Filtration, *Sewage
Disposal, Operating Costs, Instrumentation, Aeration, *Wastewater Treatment

^Australia


                                         266

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07 5D

ALL COSTS MUST BE COUNTED.. .,

Kalinske, A. A.

Camp Dresser and McKee, Boston,  Mass.

Water and Wastes Engineering, Vol. 11,  No.  3,  p 49-51,  March,  1974.   2  fig.

The determination of the costs of sludge and sidestreams is  discussed.   Often
these costs are not properly identified, especially when relatively  polluted
streams are recycled.  Recycling can significantly affect the  loading on the
process generating the stream and other processes, both directly and indirectly,
To ensure that all pertinent costs are  recognized, design engineers  should
consider the use of a complete flow diagram which quantitatively identifies
all the recycled streams.  By analyzing overall costs according to  this scheme,
it is possible to determine proper loadings, under equilibrium conditions, on
various processes and equipment in the  treatment plant.  The analysis involve
mass balance and a knowledge of the biological, physical, and  chemical  conversion
processes.

*Waste Water Treatment, *Costs,  *Sludge, *Engineering,  Sludge  Treatment,
Costs Analysis, Recycling
 07 6D

DISINFECTION OF WATER USING CHLORINE DIOXIDE,

Malpas, J. F.

Wallace and Tiernan, Ltd.

The Journal of the Society for Water Treatment and Examinations,  Vol.  22,  No.  3,
p 209-221, 1973. 1 tab, 14 ref.

The use of chlorine dioxide for  the disinfection of water  is discussed.  Although
chlorine dioxide is widely used  as a water treatment chemical for the  specific
purpose of taste removal, it is  not generally thought of as an alternative to
chlorine for disinfection.  It is pound for pound far more expensive than  chlorine,
yet does not appear to have outstanding germicidal properties.  There  does appear
to be three areas in which chlorine dioxide could be used  advantageously as an
disinfectant:  firstly, in the potable water field, where abstraction  from
rivers high in ammonia makes break point chlorination impossible, or difficult;
secondly, for the disinfection of sewage effluents; and lastly,  in swimming
pools because chlorine dioxide reportedly does not cause eye irritation.

*Dislnf ection, Sewage Treatment, *Swimming Pools, Potable Water,  Water Purification,
*Waste Water Treatment

*Chlorine dioxide. Great Britain
                                         267

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07 7D

NEW TERTIARY SEWAGE PROCESS NEEDS NO CHLORINE TO DISINFECT,

Engineering News-Record, Vol. 192,  No.  8,  p 23,  February  21,  1974.

A tertiary wastewater treatment process was developed  that combines  ultrahigh
frequency sound with ozone and could replace chlorlnation for  disinfection.
Chlorine leaves a toxic residue that can be harmful to aquatic life.   The cost
of an entire 1 mgd physical/chemical plant using the process would be  competitive
with an activated sludge plant the same size.  It would be feasible  to expand
the process for use on plants in the 50 mgd range.  The process kills  most
viruses within 15 sec, as compared  to 1-2  min when using  ozone alone.   Currently,
a 27,000 gpd pilot plant is in operation,  with plans for  a 600,000 gpd sonozone
plant.

*Tertiary Treatment, *Disinfection, *Waste Water Treatment, Water Purification,
Ozone, Ultrasonics, Aquatic Microorganisms

*Ultrahigh Frequency Sound
07 8D

COUNTERCURRENT WASHING TURNS THE TIDE AGAINST RISING EFFLUENT
COSTS,

Pier son, H. G. W.

Pier son and Co., Ltd., Manchester,  England

Progress Engineering, p 47,  February, 1974.   2 fig.

The use of countercurrent washing to reduce  the volume of  effluent  by  half  and
so reduce treatment cost is  discussed.  The  countercurrent washing  process
is illustrated for a long slab like filter cake.  The filter cake  travels from
left to right while the successive washes are piped  the other  way.  Each of
the three portions of the cake is washed three times.   At  each washing the
filter cake has a higher concentration of soluble solids than  the  wash water
and so the concentration of  impurities in the cake is decreased at  every
washing.  A 1% level of impurities can be obtained in a three  stage counter-
current washing compared to  a four stage countercurrent washing process.

*Cleaning, *Filtration, Effluents,  Treatment, Costs, *Waste water  treatment

*Great Britain, Countercurrent Washing
                                       263

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07 9D

THOSE NASTY PHOSPHATIC CLAY PONDS,

Environmental Science and Technology, Vol. 8,  No. 4,  p 312-313,  Aprtl,  1974.
2 fig.

Methods of dewatering phosphate slimes are discussed.  There are about  40,000
acres of active and inactive settling areas of phosphate slimes  that are
surrounded by over 300 miles of earth dams.  Since 1942, some 20 dam failures
occurred, releasing large amounts of phosphate slimes, and seriously, although
temporarily, polluting surrounding waters.  Two dewatering methods are  deemed
technically feasible and economically promising.  One is mixing  with tailings
sand, and the other is chemical flocculation together with coagulation  with
tailings sand.  Other possible feasible methods include filtering and the use
of a cross flow fluid bed dryer.  The possibility of  utilizing the slime is also
being explored in areas of fertilizers, bricks, and sewer pipes.

*Phosphates, *Slime, *Dewatering, Flocculation, Coagulation, Dryers, Economics,
Feasibility, Sands, Flocculation, Filtration
080D

THE PROS AND CONS OF AUTOMATED FILTERS,

Froman, C. A., Jr.

Gary-Hobart Corp., Gary, Ind.

Water and Wastes Engineering, Vol. 11, No. 3, p 43-44, 48, March, 1974.  1 tab.

The advantages and disadvantages of automated filters are discussed.  An
automated filter is defined as a filter with numerous automated features and is
run without an operator who routinely inspects the filter during operation and
is not in attendance during the backwashing function.  Some common problems
that have been associated with filter plant operations are filter bed clogging,
cracks in filter bed, air binding, gravel shifting and sand boils, and loss of
filter media.  Some of these problems could be avoided if an operator were in
attendance, therefore, the biggest disadvantage of automated filters is the
loss of direct operator observation and control of process.  Other disadvantages
include the investment required, high maintenance costs and depreciation.
Advantages include economy in operation and maintenance consistency of opera-
tion.  One plant estimates its total annual savings at $17,500.

*Filtration, *Economics, Water Treatment, Filters, Automation, Operation and
Maintenance, *Maintenance Costs, *Wastewater Treatment
                                       269

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08 ID

AUTOMATION COMES TO L.A.,
Flanagan, M. J. and Jones, G. M.

Brown and Caldwell, San Francisco, Calif.

Water and Wastes Engineering, Vol. 11, No. 2, p 41-46, February, 1974.  7 fig.

An expandable automated control system which will permit the addition of improved
processing techniques as they become available is being installed in a Los
Angeles waste water plant.  The Hyperion sewage treatment plant provides primary
treatment for an average dry weather flow of 420 mgd and a peak wet weather
flow of 720 mgd.  Secondary treatment by the activated sludge process is provided
to a constant flow of 100 mgd.  Under dry weather flow conditions, primary and
secondary effluent are mixed and discharged to Santa Monica Bay through a 5 mi
long outfall.  When excessive wet weather flows impose too great a load on the
5 mi conduit, effluent from the activated sludge process is discharged through
the plant's original 1 mi outfall.  Solids from the treatment process are
discharged through a 7 mi outfall after reduction by the anaerobic digestion
process.

^Automatic Control, *Waste water Treatment, Facilities, *Sewage Treatment,
Activated Sludge, Effluents, Computers, Digestion
082D

PRIMARY SLUDGES PRODUCED BY THE ADDITION OF LIME TO RAW WASTE
HATER,

Mlnton, G. R. and Carlson, D. A.

Washington University, Seattle, Wash.

Water Research, Vol. 7, No. 12, p 1821-1947, 1973.  10 fig, 8 tab, 45 ref.

Information compiled on the primary sludge produced by the addition of lime
to the raw waste water is summarized.  The removal of moisture content of
primary sludges containing lime will vary significantly with the waste water
hardness/alkalinity, insolubilization, pH, and possibly the phosphorus
concentration.  The recommended minimum insolubilization pHs to ensure satisfactory
thickening, vacuum filtration, sand bed drying, and centrifuging are tabulated.
The minimum insolubilization pH required for satisfactory clarification cor-
responds to the minimum insolubilization pH for satisfactory removal of sludge
moisture content with the possible exception of vacuum filtration.  The degree
to which the capacity and/or operating hours of the existing moisture removal
processes must be increased to handle the new sludge will depend upon the
aforementioned waste parameters and the existing operating characteristics,
solids contents, and loading rates of the facility,  Lime will significantly
alter the quantity, composition, and quality of the solids and sludges produced
by the treatment process.

*Sludge, Waste Water, *Lime, Hydrogen Ion Concentration, *Waste Treatment,
Water Purification, Activated Sludge, Dewatering, Review, *Waste Water
Treatment
                                         270

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083D

SEWAGE TREATMENT AND DISPOSAL,

Water and Water Engineering, Vol. 77, No. 934, p 495-498, December, 1973.
2 fig.

New sewage treatment and disposal facilities and projects are summarized.
A water management study on treating sewage at Melbourne is being conducted.
New sewers are being proposed for Banstead UDC and Bedworth UDC.  Four
automatic pumps were installed at the Faversham Sewage Works.  New facilities
have opened at the Isle of Sheppey, Northallerton RDC, Village, Rugby Newbold,
Spalding RDC, Stokesley RDC, Winchester RDC, and Zambia.  In the United States,
the Rosemont Treatment plant is being evaluated by the Environmental Protection
Agency.  A recent ruling made it unlawful to prohibit the discharge of sink
waste from boats on streams in the area of the Lancashire River Authority.
An important water management scheme is being developed in Greece to control
the irrigation of local farmland.  A flood relief scheme is being planned
for South West Bristol.

Facilities, *Sewage Treatment, *Waste Water Treatment, Water Management
(Applied), Waste Disposal, Irrigation Systems, Flood Damage, Boating


*Flood Relief, *Great Britain, *Greece
084D

LETCHWORTH WATER POLLUTION CONTROL WORKS,

Taylor, E.

The Public Health Engineer, No. 7, p 21-34, January, 1974.  1 fig, 8 tab.

The extension of the Letchworth Water Pollution Control Works to a 4-5 mgd
facility based on the diffused air activated sludge process is described.  The
numbers, dimension, and capacities of the following individual units are
tabulated:  inlet works, sedimentation tanks, aeration tanks, final settlement
tanks, sludge pumps, sludge digestion tanks, sludge filter presses, biological
filter beds, scavenge pumping stations, the administration building and com-
pressor house, and tank washout and washdown facilities.  The construction costs
of the extension are tabulated and total about $3 million.

*Facilities, *Water Pollution Control,  *Costs Activated Sludge,  Intakes,
Sedimentation, Separation Techniques, Sludge Digestion, Sludge Disposal,
Sludge Treatment, Filters, Filtration,  Waste Water Treatment, Pumps, Pumping
Plants, Equipment


Great Britain, *Letchworth, England
                                       271

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 085D

PLANT EXPANDED FOR ADVANCED WASTE TREATMENT,

McDuff, D. P. and Ward, D. B.

URS Forrest and Cotton, Inc., Dallas, Texas

Public Works, Vol. 105, No. 3, p 56-59, March, 1974.  4 fig.

The expansion of the sewage treatment facility at Garland, Texas is described.
It will feature a new and innovative treatment unit in parallel with an existing
trickling filter plant in order to meet the demand for high quality waste
effluent.  The plant is designed to increase the capacity from 7.5 to 30 mgd
and to provide treatment objectives of reducing both BOD and suspended solids
to a concentration of less than 10 mg/liter.  The proposed additional treatment
processes at the existing plant include:  equalization and aeration, pretreatment,
chemical clarification, recarbonation, filtration, carbon adsorption, dis-
infection, sludge dewatering, and scum disposal.

*Sewage Treatment, *Facillties, *Trickling Filters, *Water Quality,
Pre-Treatment (Water), Filtration, Aeration, Adsorption, Disinfection

Sludge Treatment, Dewatering, Waste Water Treatment, Biochemical Oxygen Demand,
Suspended Solids, Water Purification, Scum


Recarbonation
 08 6D

PHOSPHATE REMOVAL BY MAGNETIC FILTRATION,

Bitton, G., Mitchell, R.,  Latour, C. de, and Maxwell, E.

Harvard University, Cambridge, Massachusetts, Division of
Engineering and Applied Physics

Water Research, Vol. 8, No. 2, p 107-109, 1974.  2 fig, 2 tab, 12 ref.

The removal of phosphate from natural water by magnetic separation was inves-
tigated under carefully controlled conditions.  Water from the Charles River,
Boston, was sampled at three different locations and was treated by magnetic
filtration to reduce its phosphate content.  The removal of phosphorus approached
the 90 percent level in the three locations.  The suspended solid content and
the color of the Charles River samples were reduced significantly.  The efflu-
ents obtained by magnetic filtration were all very clear and did not contain
any trace of montmorillonite.  It is concluded that magnetic filtration is a
rapid process that requires only a few minutes retention after the addition of
magnetite, alumn, and clay to the water samples.  The process could be used as
an alternative to settling tanks in the tertiary treatment of wastes.

*Phosphates, Investigations, *Filtration, Sampling, Color, *Rlvers, *Separa-
tion Techniques, Suspended Solids, Tertiary Treatment, Clays, Montmorillonite,
Effluents

*Charles River, Magnetic Separation, Magnetite, Alum

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 087D

 DIRECT FILTRATION:  AN ECONOMIC ANSWER TO A CITY'S WATER
 NEEDS,

 Sweeney, G. E., and Prendiville, P. W.

 Municipal Water Works, Springfield, Mass., Water Dept.

 Journal of American Water Works Association, Vol. 66, No. 2, P 65-71, February,
 1974.  4 fig.

 The history of the Springfield, Mass., water system and the background of
 engineering investigations are descirbed.  The first community water supply in
 the city was developed in 1848.  The city took over operations in 1872, and the
 reservoir had a yield of 10 mgd.  The total average daily water consumption
 increased from 17 mgd in 1940 to 41 mgd in 1971.  Currently about 33% of the
 supply is used by industry.  An engineering report of 1970 recommended the im-
 mediate construction of a 60 mgd direct filtration plant, to be operated in
 conjunction with the slow sand filters.  It was also recommended that the new
 facilities be designed to facilitate expansion of the plant to an ultimate capa-
 city of 180 mgd.  The report set a reasonable budget and schedule for the pro-
 ject.  The plant is scheduled to go into operation in early 1974.  The construc-
 tion cost of the direct filtration facilities is now estimated at about $88,000/
 mil gal of capacity, considerably lower than expected for a plant of this
 size.

 *Municipal Water, *Filtration, *Waste Water Treatment, Facilities, Water Works,
 History

 *Springfield (Mass.)
088D

RESEARCH ROUND UP,

Effluent and Water Treatment Journal, Vol. 13, No. 12, p 791-792, December,
1973, 1 fig.

Current research in waste and water treatment is summarized.  Studies on the
kinetics of packed bed denitrification at the University of California con-
cluded that the denitrification process can be operated near the maximum unit
removal rate and still obtain acceptable nitrogen conversion, regardless of
the reactor configuration.  A bacterial mutant was isolated at the Canadian
Centre for Inland Waters from waste water after ultraviolet mutagenisation and
penicillin selection and was shown to have higher affinity for nitroiltriacetic
acid using concentrations up to 2.5 percent as sole carbon, nitrogen, and
energy source over a wide temperature and pH range, without acclimatization.
At the National Environmental Research Center in Cincinnati, pilot-plant ex-
periments on the effect of waterworks sludge on the activated sludge process
show there are no adverse effects.  The Central Public Health Engineering
Research Institute at Hagpur successfully substituted bituminous coal for an-
thracite for use with sand for dual media filtration.  A pressure and flow con-
trol pump manufactured by the Etruscan Engineering Co., Ltd. for use on appli-
cations involving sludges and sluries was developed.

*Waste Water, *Water Treatment, *Denitrification, Nitrogen, Packed Beds,
Nitrilotriacetic Acid, Investigations, Bacteria, Sludge, Activated Sludge,
Sand, Filtration, Coals, Sluries

England, India, Canada, Mutants

                                             273

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089D

TURNKEY CONTRACTS FOR SEWAGE TREATMENT PLANTS?,

Pinnell, S.

Civil Engineering-ASCE, Vol. 44, No. 1, p 86, January, 1974.

The disadvantages of turnkey contracting procedures for sewage treatment plants
are summarized.  Conventional contracting can provide better organization of
pollution control efforts.  The direct costs of turnkey contracting will normally
be substantially higher than conventional contracting.  Turnkey contracting does
not generally result in design innovation unless special provisions are written
into the design construction contract.  Turnkey contracts would tend to limit
competition to large design constructors.  This restriction is too serious to
justify the use of turnkey contracting in public works, especially when other
contractual arrangements or improvements in conventional contracting could
produce similar time reduction and at less cost.

Contracts, Sewage, Facilities, Costs, Utilities


Turnkey Contracts
090D

CITY OF BRADFORD WATER DEPARTMENT CHELLOW HEIGHTS TREAT-
MENT PLANT,

Water and Waste Treatment, Vol. 16, No. 11, p 21-22, November, 1973, 3 fig.

The Chellow Heights water treatment plant is discussed.  A filter building was
constructed to replace, with a higher capacity, the existing outmoded filters,
and the provision of a precipitation tank to increase existing precipitation
capacity.  Maximum throughput was designed to be 40 mgd (1.60 cu m/sec).
A covered service water reservoir is currently under construction and has a
capacity of 140,000 cu m (30.8 mg).  It is based on the prime elements of a
reinforced concrete walls, reinforced concrete columns, and a reinforced con-
crete roof.

*Water Treatment, *Filtration, *Reservoirs

Great Britain
                                              274

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09 ID

HERE AND THERE,

Effluent and Water Treatment Journal, Vol. 13, No. 2, p 751-752, December, 1973.

Research and newsbriefs on effluent and water treatment throughout the world
are summarized.  The question whether industry should use public sewers or
provide its own treatment plants is being debated.  There is renewed interest
in the United States in the use of land as a means of disposing of sewage.
The growth of the use of synthetic polymers in the dewatering of sludges il-
lustrates that it takes a long time to prove the worth of chemicals that are
gradually replacing those inorganic chemicals as precipitants and flocculants
that greatly increase the amount of sludge to be handled.  A consultant group
convened by the WHO International Reference Centre for Community Water Supply
recommends that polyelectrolytes should be employed in the purification of water
for public supply only after careful consideration of possible toxic hazards.
The Water Research Association and the Testing and Research Institute of the
Netherlands Water Undertakings will hold a conference to discuss improvements
in techniques for the distribution of drinking water.

*Effluents, *Water Treatment, Industrial Wastes, *Sewage Disposal, Land Use,
Sludges, Dewatering, Organizations, Polymers, Polyelectrolytes, Flocculation,
Water Purification, Potable Water, Water Resources

*Great Britain
092D

DEEP-BED FILTRATION,

Jung, H., and Savage, E. S.

BAMAG Verfahrenstechnik GmgH, Butzbach, Germany

Journal of American Water Works Association, Vol. 66, No. 2, p 73-78, February,
1974.  10 fig, 2 tab, 5 ref.

The advantages and disadvantages of deep bed filters which are utilized in
Europe and other parts of the world are illustrated.  Their chief advantage is
their high specific loading.  They make possible long filter runs and more fin-
ished water per wash than do shallower systems.  They need less backwash water
than do other systems.  In some cases pretreatment can be reduced or elimina-
ted.  A disadvantage of deep bed systems is that deeper filter vessels are re-
quired which may preclude using such a system.  In general, the trend is toward
the deeper vessels because they avoid negative head loss in the filters at the
end of each cycle.  With deep beds and air water backwash, coarse media and low
head loss filter bottoms may be used.  The overall head loss is no more than
generally experienced with shallower filters and in many cases may be less.
Special consideration should be given to deep bed systems for process and po-
table water filtration when filter optimization is desired or the quantity of
backwash water generated must be held to a minimum.

*Design Standards, *Filtration, Filters, Potable Water, Water Treatment

*Germany, Deep Bed Filters, Backwash
                                             275

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 09 3D

 DEVELOPMENT TRENDS IN POLLUTION-FREE PROCESSES,

 Chemical Economy and Engineering Review, Vol. 5, No, 67, p 59-60, November,
 1973.  2 tab.

 The development of closed systems of production in Japan as a method of pollu-
 tion control is discussed.  Central to this system is the recycling of materials
 used in the production process.  According to a survey made by the Agency of
 Industrial Science and Technology, the process accounts for 31.9% of pollution
 abatement devices now being developed.  The share is likely to increase to
 42.5% five years later.  There are plans to recover urban sewage as industrial
 water or to utilize gypsum by-produced from the desulfurization of flue gas.  The
 closed system is designed to prevent secondary and tertiary pollution.  As
 such it is part of a comprehensive system of pollution control.  Efforts to
 clean the environment also involve attempts to change the sources of heat and
 some of the raw materials and, more importantly, to change the nation's indus-
 trial structure.

 *Recycling, Industrial Production, *Pollution Abatement, Sewage, Water Reuse.

 Japan
094D

TALE OF TWIN CITIES CUTTING THE HIGH COSTS OF POLLUTION
CONTROL,

Instrumentation, Vol. 27, No. 1, p 12-15, 1974, 5 fig.

The centralized waste water treatment facility of the Twin Cities area in Min-
nesota is described.  It serves a 3000 sq mile area with a population of over
2 million people and a commercial/industrial population equivalent to an addi-
tional million persons.  The plant is completely integrated, meaning that its
processes include secondary as well as primary treatment, sludge incineration,
and chlorination of the effluent prior to discharge into the Mississippi River.
Average flow capacity through the plant today is 218 mgd.  A major expansion
program over the next five years will boost this to 290 mgd in a first step,
with a potential flow capacity of 350 mgd in the long range future.

*Waste Water, *Water treatment, *Facilities, *Sewage Treatment, Aeration,
Sludge Disposal, Incineration, Effluents, Chlorination, Flow

Minnesota, St. Paul, Minnesota, Mineapolis, Minnesota
                                     276

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095D

MID CALDER WATER BOARD OPENS TWO NEW TREATMENT WORKS,

Water Services, Vol. 78, No. 935, p 22-24, January, 1974.

Two new water treatment plants with a total capacity of 9 mgd have been opened
by the Mid Calder Water Board, England.  The plants employ sodium hydroxide,
ferrous sulfate, and chlorine for conditioning of raw water, followed by
clarification using sludge blanket tanks, and final processing by rapid
gravity filtration.  Dirty water after backwashing is delivered to the waste
water recovery plant.

*Water treatment, *Treatment facilities, *Coagulation, *Filtration, Chemicals,
Waste water treatment

Great Britain
096D

DEVELOPMENTS IN THE TREATMENT OF SEWAGE FROM SMALL
COMMUNITIES,

Department of the Environment Notes on Water Pollution, No. 60, p 1-4,
March, 1973.  14 ref.

The treatment of sewage from small communities is discussed and recent
developments are described.  Many of the problems of small treatment plants
relate directly to the fact that small plants can normally provide little
supervision or maintenance and privately owned plants are especially liable
to serious neglect.  Before 1960, there was essentially only a combination
of septic tanks and percolating filters for treating sewage from small
communities.  During the last decade a variety of modified activated sludge
systems has been actively developed particularly for small scale use.  Three
forms of plant have evolved:  extended aeration, contact stabilization, and
the oxidation ditch.  Purification plants using rotary disc biological
contactors have recently been introduced into the United Kingdom.  Extended
filtration and submerged bed aeration plants have been commercially developed
to a small scale as small package plants.  The main developments in effluent
polishing for small systems have been with the simplest systems:  grass
plots, upward flow clarifiers; and slow sand filters.  The use of separate
aerobic digestion plants to stabilize raw or septic tank sludge at central
collection works has overcome the problem of sludge disposal.

*Sewage treatment, *Treatment plants, *Rural areas, Maintenance, Septic tanks,
Percolation, Activated sludge, Aeration, Stabilization, Oxidation lagoons,
Biological treatment, Filtration, Effluents, Suspended solids, Filters,
Digestion tanks, Sludge disposal

United Kingdom
                                     277

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09 7D

WASTEWATER SYSTEM ALTERNATES:  WHAT ARE THEY. . .AND WHAT
COST?

Monti, R. P. and Silbermann, P. T.

Anderson Nichols and Company, Boston, Massachusetts,
Environmental Sciences Division

Water and Wastes Engineering, Vol. 11, No. 4, p 36-40, April, 1974.
5 fig, 1 tab.

Alternatives to conventional secondary waste water treatment that will meet
the best possible practical treatment requirements of 1983 are discussed.
Because the Federal requirements are not entirely clear on BOD, ammonia,
and suspended solids, an additional treatment step is proposed.  If land is
available, the least costly treatment may be a polishing pond.  If no land is
available, rapid sand filtration columns could be used.  A microstraining
device could remove additional suspended solids and their associated BOD
from treatment plant effluents.  The most economical method of ammonia removal
is single stage nitrification.  This biological process converts ammonia to
nitrates in an aeration tank.  The most troublesome of the pollutants is
nitrate which has a maximum allowable groundwater limit of 10 mg/liter.  If
ground disposal is chosen, the most reasonable type of denitrification process
would be a packed column reactor added after conventional treatment and using
methanol addition as a source of carbon for the denitrifying organisms.  In
the case of land disposal, there are three basic techniques for surface
application of waste water effluent to the land:  spray irrigation, overland
runoff, and rapid infiltration.

*Waste water treatment, *Alternate planning, Ammonia, Suspended solids,
BOD, Waste disposal, Filtration, Filters, Nitrification, Nitrates,
Denitrification, Effluents, Infiltration, Irrigation, Runoff

Polishing pond, Microstraining device
098D

USE OF LIME FOR PHOSPHORUS REMOVAL,

Le Clair, B. P., and Ladouceur, E.

Wastewater Technology Centre, Canada Centre for
Inland Waters, Burlington, Ontario, Canada

In:  PHOSPHORUS REMOVAL DESIGN SEMINAR, Canada-Ontario Agreement on Great
Lakes Water Quality, May 28-29, 1973.  15 p, 6 fig, 3 tab, 7 ref.

Process design information and operating experience on the use of lime,
including the direct use of dry unslaked lime for phosphorus removal, are
summarized.  Of the three methods demonstrated at full scale, the method in-
volving dry hydrated lime storage in a silo and batch continuous slurry make-
up is preferred.  Approximately 25 percent chemical cost saving should be
realized with the method as well as fewer operating difficulties.

*Lime, *Design criteria, *0peration and maintenance, *Cost comparisons,
Waste water treatment, Chemical precipitation

*Phosphorus removal
                                        278

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099D

ACTIVATED SLUDGE CHARACTERIZATION AND SETTLING,

Zaloum, R.

Environmental Protection Service

In:  PHOSPHORUS REMOVAL DESIGN SEMINAR, Canada-Ontario Agreement on Great
Lakes Water Quality, May 28-29, 1973.  15 p, 6 fig, 6 ref.

This study is a portion of a sludge dewatering and reduction project aimed
at the characterization of sludges with respect to physical, chemical, and
biological properties and the correlation of these properties with various
process units.  Some of the progress achieved in this area is presented and
discussed.  The methods presently used for the determination of clarifier
areas is evaluated.  Only typical results are presented as the data from all
tests yielded similar trends.

*Activated sludge, Physical properties, Chemical properties,
Biological properties, Investigations

*Sludge characterization, *Phosphorus removal
100D

A CURSORY LOOK AT THE IMPACT OF PHOSPHORUS LADEN SLUDGES ON
CONVERSION PROCESSES,

Villiers, R. V.

In:  PHOSPHORUS REMOVAL DESIGN SEMINAR, Canada-Ontario Agreement on Great
Lakes Water Quality, May 28-29, 1973.  20 p, 6 tab, 14 ref.

Conversion processes alter sludge constituents to make them inoffensive,
nonviable, or unextractable to permit reuse or return of the sludge to the
environment.  Such processes include heat treatment, incineration, anaerobic
digestion, aerobic digestion, chlorination, or lime treatment.  All processes
are temperature and pH dependent; sensitive to change in loading, time,  and
mixing; sensitive to change in air and food supply; and concerned with organic
matter destruction or stabilization.  Cause-effect relationships between
the process and phosphorus-sludge are predicted by relating the following
three categorizations to the various conversion processes.  The categorizations
are:  changes in sludge characteristics; process operating parameters; and,
changes in sludge components during conversion.

*Sludge treatment, *Heat treatment, *Incineration, *Anaerobic digestion,
*Aerobic treatment, *Chlorination, *Lime, *Phosphorus, Temperature, Hydrogen
ion concentration, Mixing, time, Organic matter, Operations

*Phosphorus removal, *Sludge characteristics, Loading
                                    279

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10 ID

LAND APPLICATION OF PROCESSED ORGANIC WASTES,

Wood, G. M.

Ministry of the Environment, Waste Management
Branch, 880 Bay Street, Toronto, Ontario, Canada

In:  PHOSPHORUS REMOVAL DESIGN SEMINAR, Canada-Ontario Agreement on
Great Lakes Water Quality, May 28-29, 1973.  29 p 2 tab.

Under the authority of the recent amendments to REGULATION 824 of the REVISED
.REGULATIONS OF ONTARIO, 1970, the Ministry of the Environment is undertaking
the certification of haulers, organic waste management systems, and
organic soil conditioning sites for the disposal of processed organic waste.
According to the amendment, "No person shall use, operate, establish, alter,
enlarge, or extend a waste management system or a waste disposal site" unless
governmental approval has been received.  Standards for the location, main-
tenance, and operation of an organic soil conditioning site which include such
topics as site location, land characteristics, site management, and sludge
application rates are discussed.

*Regulation, *Governments, *0rganic wastes, *Waste disposal, *Waste treatment,
*Soil disposal fields, Soil engineering, Sites

*Phosphorus removal
102D

PHOSPHORUS REMOVAL COSTS,

Powell, G., and Crawford, P.

Gore & Storrie Limited

In:  PHOSPHORUS REMOVAL DESIGN SEMINAR, Canada-Ontario Agreement on Great
Lakes Water Quality, May 28-29, 1973.  38 p, 9 fig, 2 tab, 8 ref.

A significant factor to phosphorus removal costs pertaining to waste water
plants is the designer's familiarity with the effect of the phosphorus removal
chemicals on the treatment processes.  Insufficient data is presently available
for accurate costs on phosphorus sludge disposal and the effect of lime on the
biological treatment at elevated hydrogen ion concentrations.  As effluent
standards are made more stringent to safeguard waters, treatment costs will
increase.  Thus, with higher and more sophisticated degrees of treatment,
a better understanding of the operation and the economics of the treatment
processes involved will result.

*Costs, *Economic efficiency, *Waste water treatment, Lime, Sludge disposal,
Data collections, Water quality control, Effluents, Treatment facilities,
Chemical precipitation

*Phosphorus removal
                                         280

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103D

PHOSPHORUS REMOVAL ON SECONDARY EFFLUENTS,

Shannon, E. E.

Wastewater Technology Centre,
Environmental Protection Service

In:  PHOSPHORUS REMOVAL DESIGN SEMINAR, Canada-Ontario Agreement on Great
Lakes Water Quality, May 28-29, 1973.  16 p, 7 fig, 30 ref.

Phosphorus precipitation by chemical addition to the secondary effluent requires
the addition of separate equipment onto the existing facility and reduces the
effluent total phosphorus levels in the order of .1 to .5 mg/liter and reduces
the BOD to less than 10.  Some alternatives for post-precipitation are depicted,
with the individual components being flash mixing, flocculation, and clarifi-
cation, or the three combined in a reactor clarifier, pH adjustment, and fil-
tration.  Design aspects of the various stages in post precipitation are
discussed.

*Chemical precipitation, *Phosphorus, Equipment, Biochemical oxygen demand,
Mixing, Flocculation, Hydrogen ion concentration, Filtration

*Phosphorus removal, Clarification
104D

CHEMICAL PRECIPITATION FOR BIOLOGICAL AND POSTBIOLOGICAL
TREATMENT,

Norman,  J.  D.

Pollutech Pollution Advisory Services, Limited

In:  PHOSPHORUS REMOVAL DESIGN SEMINAR, Canada-Ontario Agreement on Great Lakes
Water Quality, May 28-29, 1973.  14 p, 6 fig.

Chemical precipitation at full-scale treatment plants in several plants in
Ontario, Canada has been observed.  Comments are made on some of the factors
(chemical choice, point and rate of application, control of chemical feed,
and the effect of plant operation) affecting the performance of chemical pre-
cipitation processes and the effect or lack of effect of several variables
tested.   Conclusions resulting from this investigation suggest the following:
chemical solutions are not difficult to obtain, the jar testing procedure
is consistent for a given waste, equipment for chemical application is inexpen-
sive and portable, systems should also provide improved effluent quality, and
system optimization requires a longer testing period than eight weeks.

*Chemical precipitation, *0n-site testing, *Treatment facilities, *Performance,
Equipment, Effluents, Optimization, Efficiencies, Canada

*Phosphorus removal
                                           281

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105D

PHOSPHORUS REMOVAL BY CHEMICAL ADDITION USING PRIMARY
TREATMENT,

Wilkes, A.

James F. MacLaren Limited

In:  PHOSPHORUS REMOVAL DESIGN SEMINAR, Canada-Ontario Agreement on Great Lakes
Water Quality, May 28-29, 1973.  17 p, 1 fig.

Phosphorus removal by chemical addition ahead of primary clarification is a
vaiable technique for controlling phosphorus discharges at sewage treatment
plants.  For the purposes of this study, primary treatment for phosphorus
removal is defined in terms of the point of addition of chemical.  The types
of phosphorus compounds present in sewage such as ortho-phosphates, polyphos-
phates, and organic phosphates are discussed.  The mechanism of phosphorus removal
which includes precipitation of phosphorus compounds, chemical reactions,
and solids flocculation, together with practical considerations and experience
are mentioned.

*Chemical precipitation, *Sewage treatment, *Phosphates, Chemical reactions,
Flocculation, Methodology

*Phosphorus removal
106D

PHOSPHORUS REMOVAL IN ONTARIO,

Van Fleet, G. L.

Ministry of the Environment, Sanitary Engineering
Branch, 135 St. Clair Avenue, West, Toronto M3V1P5,
Ontario, Canada

In:  PHOSPHORUS REMOVAL DESIGN SEMINAR, Canada-Ontario Agreement on Great
Lakes Water Quality, May 28, 29, 1973.  25 p, 1 fig, 6 ref.

The integration of chemical treatment into existing waste water treatment plants
in Ontario has necessitated thy development of a research methodology capable
of providing in a very short time period sufficient design information to
successfully implement the Province's phosphorus removal program.  This metho-
dology has involved both treatability studies and intensive research investi-
gations.  The treatability studies are proceeding at all waste water treatment
plants requiring phosphorus removal and it is expected that the resultant data
will contribute to the design of the most efficient and economical chemical
process for each particular plant within the required timing.  Research and
demonstration projects have made it possible to demand permanent facilities to
meet the required percent phosphorus removal or effluent quality criteria.
Continuing investigations will produce more accurate information on sludge hand-
ling and disposal and will improve upon existing waste water treatment tech-
nology.

*Research and development, *Waste water treatment, *Treatment facilities,
*Methodology, Data collections, Design criteria, Economics, Efficiencies,
Chemical precipitation, Canada

*Phosphorus removal


                                         282

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10 7D

GUIDELINES FOR CONDUCTING TREATABILITY STUDIES FOR PHOSPHORUS
REMOVAL AT WASTEWATER TREATMENT PLANTS,

Rupke, J. W. G., and Van Fleet, G. L.

Ministry of the Environment,
135 St. Clair Avenue,
West, Suite 400, Toronto M4V1P5, Ontario, Canada

In:  PHOSPHORUS REMOVAL DESIGN SEMINAR, Canada-Ontario Agreement on Great
Lakes Water Quality, May 28-29, 1973.  24 p, 1 fig, 2 tab.

An information brief for consulting engineers and municipal officials as well as
a supplement to GUIDELINES FOR INITIATING TREATABILITY studies is given.  These
guidelines are designed to assist personnel involved in carrying out phosphorus
removal treatability studies in determining the most efficient and economical
means to implement phosphorus removal through chemical addition at existing
waste water treatment plants.  The methodology, which includes both jar testing
and pilot study phases, allows the prediction of the prime coagulant best
suited for phosphorus removal at any particular treatment facility and a
determination of whether the chemical used has any affect on the existing
waste water treatment process, facilities, method of sludge treatment, and
subsequent sludge disposal practices.  The choice of chemical is limited to
the process most compatible with sewage characteristics and the existing
facilities, taking into account the physical layout of the plant and the
delivered cost and availability of the particular chemical.

*Waste water treatment, *Treatment facilities, Investigations, Coagulation,
Chemical treatment, Pilot plants, Methodology, Sludge disposal, Sludge
treatment

*Phosphorus removal, Investigation guidelines
108D

THICKENING AND DEWATERING SLUDGES PRODUCED IN PHOSPHATE
REMOVAL,

Knight, C. H., Mondoux, R. G., and Hambley, B.

Canadian EVT Limited

In:  PHOSPHORUS REMOVAL DESIGN SEMINAR, Canada-Ontario Agreement on Great
Lakes Water Quality, May 28-29, 1973.  17 p, 4 fig, 7 ref.

The effect of adding 80 percent phosphate removal facilities on the
capacity and efficiency of dewatering processes is examined.  Material and
water balances and average capacity figures are developed for the various
dewatering processes and different chemical additions.  It is noted that
no two sludges are alike and that bench scale and plant scale tests are
desirable to confirm critical design conditions.  The various treatment methods
studied include gravity thickening, flotation thickening, nozzle discharge
disc centrifuge thickening, vacuum filtration, and conveyor type centrifuge
dewatering.

*Treatment facilities, *Efficiencies, *Dewatering, *Sludge treatment,
*Chemical precipitation, Water balance

*Phosphorus removal, *Sludge thickening, *Treatment methods
                                       283

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109D

INSTRUMENTATION AND AUTOMATIC CONTROL OF PHOSPHORUS REMOVAL
PROCESS,

Daniels, S. L.

Environmental Control Systems, The Dow Chemical
Company, 2020 Dow Center, Midland, Michigan

In:  PHOSPHORUS REMOVAL DESIGN SEMINAR, Canada-Ontario Agreement on Great Lakes
Water Quality, May 28-29, 1973.  21 p, 7 fig, 1 tab, 17 ref.

Significant reductions of all phosphorus species present in municipal waste
water are technically feasible in existing treatment plants before effluents are
discharged into receiving waters.  These reductions are accomplished by modify-
ing conventional precipitation and flocculation processes.  Instrumentation
in both coagulation and flocculation processes has been limited to controlling
the storage and preparation of chemicals, the metering of chemical additions,
and the monitoring of influent and effluent qualities.  Comparisons of typical
flocculant preparation systems, flocculant addition systems, and coagulant
addition systems for five ranges of total plant flow are summarized.

*Waste water treatment, *Phosphorus, *Chemical precipitation, *Flocculation,
Instrumentation, *Control systems, Monitoring, Measurement

*Phosphorus removal
HOD

SOME PLANT DESIGN CONSIDERATIONS IN PHOSPHORUS REMOVAL
FACILITIES,

Aldworth, G. A.

James F. MacLaren Limited

In:  PHOSPHORUS REMOVAL DESIGN SEMINAR, Canada-Ontario Agreement on Great Lakes
Water Quality, May 28-29, 1973.  19 p, 2 fig.

Described herein are areas related to detailed design for phosphorus removal
with the following topics being explored:  effects of encrustation and corro-
sion; representative chemical feed systems; and, the effect of chemicals on
plant elements such as air diffusers, pumps, tanks, and piping.  Emphasized
are schemes involving the storage and feeding of large amounts of chemicals
received in bulk form.  A summary of guidelines for the use of lime treatment
and alum or ferric chloride treatment in phosphorus removal is included

*Design criteria, *Phosphorus, *Chemical treatment, Equipment, Corrosion,
Treatment facilities, Lime, Aluminum, Chlorides, Iron

*Phosphorus removal, Feed systems
                                         234

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 HID

 DESIGN CONSIDERATION IN THE IMPLEMENTATION OF ONTARIO'S
 PHOSPHORUS REMOVAL PROGRAMME,

 Boyko, B. I., and Rupke, J. W. G.

 Ontario Ministry of the Environment,
 Research Branch, Toronto,
 Ontario, Canada

 In:  PHOSPHORUS REMOVAL DESIGN SEMINAR, Canada-Ontario Agreement on Great Lakes
 Water Quality, May 28-29, 1973.  34 p 8 fig, 5 tab, 10 ref.

 The predictive methodology, operational results, problem areas, and design
 considerations that have resulted from the full scale phosphorus removal studies
 conducted at waste water treatment facilities ranging in size from 0.05 to
 24.0 mgd capacity are discussed.  Also, the results of studies involving
 phosphorus removal through continuous chemical addition to waste stabilization
 pond systems are disclosed.  The following conclusions have resulted from this
 investigation:  a satisfactory predictive technique was developed that allows
 a rational selection of prime coagulant to be used for phosphorus removal at
 a treatment facility; phosphorus removal was readily implemented with minimal
 capital expenditure; satisfartory effluent quality was attained by the
 activated sludge process and its modifications when phosphorus removal was
 practised; increased sludge production was experienced at all systems; and,
 anaerobic digestion of chemical sludges associated with phosphorus removal
 was successful with no significant phosphorus release being observed.

 *Waste water treatment, *Phosphorus, *0n-site testing, *Treatment facilities,
 *Chemical precipitation, Coagulation Activated sludge, Effluents, Anaerobic
 digestion, Sludge treatment

 *Phosphorus removal
112D

PHOSPHORUS REMOVAL IN SEASONAL RETENTION LAGOONS BY BATCH
CHEMICAL PRECIPITATION,

Graham, H. J., and Hunsinger, R. B.

Ontario Ministry of the Environment, Research Branch,
135 St. Clair Avenue, West, Toronto, Ontario, Canada

In:  PHOSPHORUS REMOVAL DESIGN SEMINAR, Canada-Ontario Agreement on Great
Lakes Water Quality, May 28-29, 1973.  25 p, 4 fig, 1 tab, 12 ref.

Alum, ferric chloride, and lime have been tested as a means of phosphorus
removal in the batch chemical treatment of seasonal retention lagoons.  The
required dosages were determined by jar tests, a highly reliable method in
predicting the post-treatment results in a lagoon.  Lagoon discharge was usually
begun the day after treatment and continued for an average of eight days.
Both alum and ferric chloride produced a high quality effluent, low in
phosphorus and BOD.  The lime application initially produced a higK quality
effluent, but deteriorated rapidly over the drawdown period.

*Aluminum, *Lime, *Chlorides, *Iron, *Testing, *Chemical precipitation,
Effluents, Phosphorus, Biochemical oxygen demand, Performance

*Phosphorus removal
                                        285

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 113D

 CHLORINE RESIDUALS  IN TREATED EFFLUENTS,

 Snoeyink, V. L., and Markus, F.  I.

 Illinois University, Urbana-Champaign, Illinois,
 Department of Civil Engineering

 Water and Sewage Works, Vol. 121, No. 4, p 35-38, April, 1974.  3 tab,
 16 ref.

 Toxicity studies on chlorine residuals in treated effluents are reviewed and
 the results of a field survey is presented wherein the concentration and type
 of chlorine residual present in  treated effluents were determined.  Chlorine
 residuals in the concentration range of 1-5 mg/liter as C12 are being dis-
 charged to receiving waters in central Illinois as a result of chlorination
 of effluents for disinfection.   The residual is predominantly monochloramine
 and in most instances it is being discharged to streams which provide little
 dilution.  Other research has shown that chlorine residual imparts a definity
 toxicity to the discharge; stream crtieria of 0.002 to 0.2 mg/liter total
 chlorine residual have been recommended depending on the. type, of fish to be
 protected in the receiving water and on whether the residual is continuously
 or intermittently present.  Dechlorination can be achieved by use of sulfur
 compounds or by activated carbon.  The carbon will also remove any ammonia.

 *Chlorine, *Toxicity, *Effluents, *Streams, Inlet, Illinois, Chlorination,
 Reviews, Ammonia, Water pollution, Water pollution sources, Water pollution
 control, Activated carbon, Sulfur compounds, Investigations, Waste water
 treatment

 Dechlorination, Sulfur dioxide
114D

NEW ARIZONA WASTEWATER PLANT TO ALLEVIATE PROBLEMS,

Roll, E.

John S. Collins and Associates,
Tucson, Arizona

Water and Sewage Works, Vol. 121, No. 4, p 60, April, 1974.

The Tuscon, Arizona $1.5 million waste water reclamation plant now under con-
struction is described.  The new, nearly constant flow (1,417 gpm) plant will
have automatic sampling equipment, electronic metering and control, and will
automatically record pH and chlorine residual levels.  It will utilize automatic
air injection and solids control for the aeration basin.  The control building
also has a small but efficient facility for on site laboratory analysis and an
equipment maintenance shop.  The activated sludge biological process will be
used in handling an average flow of 1.5 mg/d and a peak of 2.0 mg/d.  Influent
to the reclamation system has 180 mg/liter of suspended solids and 200 mg/liter
of biological oxygen demand.  The cost of the plant is estimated at $84,293
per year of $154 per million gallons of reclaimed water produced.

*Reclaimed water, *Waste water treatment, *Treatment plant, Equipment,
Automation, Automatic control, Activated sludge, Biological treatment,
Suspended solids, Biological oxygen demand, Costs, Measurement
                                                                       Flow,
                  Biological oxygen demand,  Costs,  Measurement

*Tucson, Arizona



                                         236

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 115D

 TURBIDITY CONTROL BY AUTOMATIC DIVERSION,

 Markalunas, J. J.

 Treatment and Supply,
 Aspen, Colorado

 Water and Sewage Works, Vol.  121, No.  2, p  44-45, February,  1974.

 The automatic raw water diversion system and automatic  chemical dosage  system
 for turbidity control at  the  Aspen,  Colorado treatment  plant are described.
 At times the water  supply for Aspen  (Castle Creek) becomes highly  turbid and
 high in iron content.  To assure that  this  water does not enter the  city's
 reservoir, a system was devised to turn off the raw water diversion  and restore
 the raw water pipeline to service after the water cleared up.  An  intake
 diversion dam on Castle Creek conducts the  flow through a pipe line  to  a
 structure where a 30 in diameter butterfly  valve is located.  When the  valve
 is closed, the flow passes over a weir and  returns to the creek.   When  the
 valve is open, the  water  flows on through the  pipe line to the water treatment
 plant some 2 miles  away.   This unit  has an  automatic alarm system  that  enables
 the operator to maintain  a chemical  dosage  for a limited range of  turbidities
 and also increases  the length of filter fruns.  The raw water storage reservoir
 does not silt up as quickly and the  net water  production of  the plant is
 greater.

 *Diversion structures, *Turbidity, *Automatic  control,  *Chemical treatment,
 Treatment facilities, Water purification, Iron compounds, Industrial wastes,
 Water

 Aspen, Colorado, Turbidimeters
116D

THERMAL SLUDGE CONDITIONING IN KALAMAZOO, MICHIGAN,

Swets, D. H., Pratt, L., and Metcalf, C. C.

Jones and Henry Engineers, Toledo, Ohio

Journal of the Water Pollution Control Federation, Vol. 46, No. 3, p 575-581,
March, 1974.  5 fig, 5 tab.

Economic advantages of thermal sludge conditioning over chemical conditioning
are shown.  Costs of operating and actual system performance indicate a close
correlation.  These relate to reducing labor costs, as certain operator
training processes are no longer required.  With partial oxidation as a part
of the process, a sterile end product is produced, particularly useful for
communities with diverse industrial wastes.  The process of this conditioning
as well as its effects on the chemical and physical structures of waste water
sludge are explained.

*Waste water treatment, *Sludge, Cost analysis, Costs, Economics, Sewage sludge

*Thermal sludge, Chemical sludge conditioning,  Labor costs
                                           287

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117D

EVALUATION OF A ROTATING DISK WASTEWATER TREATMENT PLANT,

Antonie, R. L., Kluge, D. L., and Mlelke, J.  H.

Autotrol Corporation, Milwaukee, Wisconsin, Bio-systems
Division

Journal of the Water Pollution Control Federation, Vol. 46, No. 3, p 498-511,
March, 1974.  11 fig, 4 tab, 5 ref.

After nine out of twelve months of an evaluation period, a 0.5 ragd (1.9-mil
liter/day) rotating disk municipal waste water treatment plant has been highly
successful.  Capability is shown of achieving high degrees of biochemical
oxygen demand and suspended solids removal and nitrification.  The variables
investigated included rotational disk velocity, hydraulic loading, and exposure
to different climatic conditions.  The plant  exhibited stable operation under
conditions of fluctuating hydraulic and organic loading and waste water tem-
perature.  High density of sludge solids indicate significant potential savings
in treatment plant construction and operating costs.

*Waste water treatment, *Biochemical oxygen demand, *Nitrification, *0rganic
loading, *Suspended solids, Hydraulics, Sludge treatment

Waste water treatment plant, Hydraulic loading, Treatment plant construction,
Sludge solids
USD

THE BALANCE BETWEEN WASTE TREATMENT AND WASTE DISCHARGE
IN THE U.S., 1957-2000,

Wallis, I. G.

Monash University, Clayton, Australia, Department of
Mechanical Engineering

Journal of the Water Pollution Control Federation, Vol. 46, No. 3,  p 438-457,
March, 1974.  3 fig, 11 tab, 54 ref.

If overall river quality level is to improve, treatment efficiency  must in-
crease even faster than the rate of increase of waste generation.  The treat-
ment level required to maintain a constant level of waste discharge is esti-
mated for years 1970 to 2000.  Two ubiquitous wastes are phosphorous wastes—
generated primarily from domestic and agricultural sources, and oxygen deman-
ding wastes—produced from industrial sources.  Factors for increase in phos-
phorus wastes were population increase, growth in detergent use, expansion of
the sewerage system, and increased rural runoff of phosphoric fertilizers.
High costs of waste treatment include changing raw material input,  production
process, recovering materials from the effluent, and transforming effluents into
a useful by-product.  This broad analysis gives, impressions about the techno-
logical advances necessary to reduce waste discharge and hence improve water
quality, a feasible but costly process.

*Waste water treatment, *Water quality, *Phosphorus, Agrucultural wastes,
Domestic wastes, Human population, Costs, Effluents, Waste treatment, Waste
water treatment, Sewage systems, Oxygen demand
                                          288

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119D

CONTROL OF BIOLOGICAL SOLIDS CONCENTRATION IN EXTENDED
AERATION,

Yang, P., and Gaudy, A. F.

Cornell University, Ithaca, New York

Journal of Water Pollution Control Federation, Vol. 46, No. 3, p 543-553,
March, 1974.  10 fig, 2 tab, 7 ref.

A 200-day test period showed that extended aeration activated sludge process
with total sludge recycle can be operated successfully using hydrolytic assist
to control the mixed liquor biological solids concentration.  Thus, the process
was made independent of natural periods of accumulation and de-accumulation
of biological solids and showed a good ability to accept shock loading.  Sludge
carbohydrate and protein were within ranges indicating a metabolically active
biomass, and the unit respiration activity of the sludge (endogenous 02 uptake
values) were slightly higher than those obtained using total cell recycle with-
out hydrolytic assist.  Pilot plant operation using the process is still in
progress to provide design and design and operating guidelines.

*Pilot plants, *Activated sludge, *Aeration, Recycling, Carbohydrates, Solids,
Biomass, Hydrolysis, Waste treatment

Sludge proteins, Biological solids, Hydrolytic assist
120D

METHANE PRODUCTION FROM WASTE,

Stafford, D. A.

University College, Cardiff

Effluent Water Treatment Journal, Vol. 14, No. 2, p 73-75, 77, 79, February,
1974.  4 fig, 4 tab, 15 ref.

Much of the fundamental microbiology is not yet known for the organisms in-
volved in the production of methane.  In order to use domestic sewage as a
source of power, research must be done to solve the practical problems of
operating a two stage hydrolysis/gas production anaerobic digesting plant.
The methane bacteria all have the reaction:  4H2 + C02 yields 2H20 + CH4,
common to different species of anaerobic organisms in degrading organic car-
bon.  Discussed here are the nutrient requirements of the bacteria, practical
applications of anaerobic  digestion, inhibitors of digestion gas production,
and the financial considerations and market potential for the use of these
processes.

*Methane, *Sewage treatment, *Microbiology, Domestic wastes, Costs, Decomposing
organic matter, Anaerobic bacteria, Anaerobic digestion, Organic wastes, Methane
bacteria, Biochemistry

Hydrolysis/gas production, Digester gas production
                                        209

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121D

DIGESTION BY-PRODUCT MAY GIVE ANSWER TO ENERGY PROBLEM,

Goeppner, J., and Hasselmann, D. E.

Knoerle, Gender, Stone & Associates, Chicago, Illinois

Water and Wastes Engineering, Vol. 11, No. 4, p 30-35, April, 1974.  6 fig,
1 tab.

The methane gas which is produced during the anaerobic digestion of sludge is
discussed as a possible source of energy.  The volume of methane generated in
anaerobic digestion is dependent upon the nature and volume of the wastes.
Current data indicates that 15 to 20 cubic feet of gas are produced per pound
of volatile organic material destroyed.  The gas produced by fermentation con-
tains about 60-70 percent methane, carbon dioxide being the predominant
remaining constituent.  It is estimated that from 100 gallons of sewage it
would be theoretically possible to obtain more than one cubic foot of combustble gas
 having a heating value of 650 BTU.  Construction costs of digestion
units are integral in determining economic feasibility of such an energy source.
It was found that for fuel generation alone anaerobic digestion would not
be economically possible.  However, the process can be used to affect the
use of outside procured energy to operate the treatment plant.  The possi-
bility of using this process with animal wastes is explored.  The estimated
electrical power capacity potentially available from the wastes of 12 million
beef cattle represents >about one percent of the total U.S. capacity.  Assets
of this system of energy production are ease of storage of digester gas, and
ease of transport.  Anaerobic digestion facilities at existing sewage treatment
plants incorporate design features which are compatible with adoption of gas
recovery systems.

*Energy, *Methane, *Anaerobic digestion, *Sludge digestion, Sewage, Waste
treatment, Treatment methods, Waste disposal

*Energy sources
122D

OZONE TREATMENT OF SECONDARY TREATMENT LIQUID (Niji shorisui
no ozon shorl),

Goda, T., Munemiya, I., and Kawahara, 0.

Gesuido Kyokaishi, Vol. 10, No. 122, p 14-27, September, 1973.  28 fig, 2 tab,
6 ref.

Basic studies were made on various characteristics of the strong oxidation pro-
perty of ozone in tertiary treatment.  Experiments were conducted on the ef-
fects of ozone oxidation on secondary treatment water (treated sewage water
from the Kyoto Municipal Sewage Treatment Plant).  The procedure consisted of
sampling water for 24 consecutive hours, preparing a composite sample with
four time segment samples, filtering, ozone treatment for 5, 10, 20, and
40 minutes each, filtering by a 0.45 micron mlllipore filter, vacuum con-
centration at 39 C, gel filtering, fraction sampling, and preparation of a
composite.  The total COD of the treated waste water and the pH time change
pattern were measured and presented in tables.  The composition of organic
substances in the treatment water was clarified.  The molecular weight dis-
tribution of less-than-0.45 micron substances and other peaks were examined.
The findings were as follows:  the organic substances in treatment water gen-
erally revert to lower molecules by ozone treatment; BODS increases temporarily
and then decreases; BOD5/COD(Cr) increases as a result of decrease of COD(Cr);
these phenomena are closely related to the transformation of the molecular
weight distribution; substances of molecular weight of about 1200 mainly re-
main after an ozone treatment, and these substances are mostly susceptible to
biological degradation.

*0zone, *Waste water treatment, treatment Methods, *Sewage treatment,
Disinfection, Water purification, Water treatment


                                            290

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123D

ODOR ELIMINATION BY OZONE (Ozon-ho ni yoru akushu jokyo),

Azuma, T.

Kankyo Sozo, Vol. 4, No. 2, p 79-84, February, 1974.  10 fig, 2 tab, 13 ref.

Ozone deodorlzation process is achieved by both oxidation and neutralization of
bad odor elements.  Oxidation is enhanced by coexistence of steam, and ozone
reacts to many organic substances quickly - the reaction to inorganic sub-
stances is believed to be instantaneous.  Most effectively neutralized or
decomposed odors ary mercaptans, sulfides, amines such as trimethylamine and
dimethylamine, phenol, and low class nonsaturate hydrocarbons.  Ozone deodoriza-
tion is effective in emission sources which emit the above mentioned odor ele-
ments, such as sewages, Kraft pulp mills, and fishmeal processing plants.  The
reaction chemical formulas are presented. Odor emission sources in the actual
environment in all cases produces complex odors, and ozone oxidation seldom
achieves complete deodorization.  The process therefore is often combined with
a pre-or post-treatment system.  The most common combination is with a scrubber.
The basic structure of a deodorization system comprises an aeration tank, an
ozone aeration tank, an ozonizer, and a neutralization tank with alkaline
solution.  Various odors were tested by a special deodorization system com-
prising a scrubber with ozone and alkaline solution, a demister, and an
activated carbon layer.  The scrubber absorbed amine and other soluble odors,
and the liquid interface achieved oxidation decomposition; activated carbon
oxidized and adsorbed sulfides and other nonsolubles, and decomposed excess
ozone.  The results showed that an appropriate amount of ozone (5 ppm) could
deodorize 98.7 percent of 15 ppm triethylamine, 90-95 percent of 4.5 ppm hydro-
gen sulfide, and close to 100 percent of 3.2 ppm methylmercaptan.  This system
was applied to the treatment of exhaust from the trickling filter of a sewage
treatment plant.  The gas odor concentration of 400-1000 can be reduced to
8-16 by 5 ppm of ozone.

*0zone, *Sewage treatment, *Waste water treatment, *0dor, *Water pollution
effects, *Treatment methods
 124D

 REMOVAL OF AMMONIA-NITROGEN AND HEAVY METAL  ION BY ZEOLITE
 FROM  SEWAGE WATER  (Zeoraito ni yoru osuichu  no anmoniasei chisso oyobi
 jukinzoku ion no jokyo),

 Sanko, S. Takahashi, H., and Kurata, Y.

 Gesuido Kyokai-shi, Vol. 11, No.  616, p  2-8, January, 1974.  12 fig, 1 tab,
 2  ref.

 Experiments were conducted on removal of ammonia—nitrogen in sewage using various
 kinds of natural and synthetic zeolites.  The results on ten zeolite specimens
 showed that, in general, the greater the concentration of NH3-N in sewage water,
 the greater was NH3-N absorption.  When  the  initial  concentration of NH3-N was
 greater than 100 mg/liter, all zeolite specimens showed a tendency to approach
 the saturation adsorption point (ion exchange capacity).  Ordinary urban sewages
 contain about 20-40 mg/liter of NH3-N.  The  absorption varied from 2.5 to
 7  mg/g.  Tests were given to one  natural zeolite, repeating the performances
 by recovering activity by heating zeolite in a furnace at 600 C for 30 minutes.
 The NH3-N removal  rate was 53.6 percent initially with 5,000 mg/liter of new
 zeolite; the rate  improved to 73  percent after the first recovery treatment.
 After that, the rates ranged from 30 percent to 60 percent for six consecutive
 repeated tests.  The results of two series of tests  averaged 49.5 percent removal
 rate with the adsorption quantity of 3.59 mg/g.  Repeated heat recovery only
 slightly decreased the removal rate.  Of the ten zeolite specimens, five
 natural zeolites had 28.8 percent to 50 percent of removal rates, whereas
 three synthetic ones had 50 percent to 73 percent removal rates, and two had
 very low rates.  Cadmium ion in sewage was removed more than 90 percent with
 a  relatively small amount of zeolite with stirring of the liquid for 30 minutes
 when concentration is about 100 mg/liter, high removal rates for copper, zinc,
 and cadmium ions can be obtained.

 *Waste water treatment, *Treatment methods,  *Zeolites,

 *Denitrification, Ammonia, Nitrogen, Sewage
                                        291

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125D

SEVEN ARCHES WORKS,

Walton and Weybridge U. D. C.

Water and Waste Treatment, Vol. 16, No. 12, p 20-22, December, 1973.

Sewage treatment works are described at Seven Arches, Weybridge, Surrey; the
Borough of Mossley in Lancashire, and at Kitwe, Zambia.  At Seven Arches no
storm water Is discharged into the River Wey.  Overflows pass through two storm
water tanks.  The supernatant liquor is mixed with the primary sedimentation
tanks effluent and then passes through the filters.  An average of 15/15 stan-
dard is being achieved.  At Mossley, the existing works were reconstructed and
modernized due to increases in domestic and industrial wastes in the 1950's.  By
1972 there was need for further extension or modernization.  As a temporary
measure a Flocor Roughing Filter Tower Is being incorporated between the sedi-
mentation tanks and the percolating filters.  This substantially reduces the
BOD content of the sewage whi^h enables the existing filter beds to produce a
much improved quality of effluent.  The new works at Zambia are based upon the
treatment of sewage in a two stage activated sludge process, where the first
stage consists of biological filters which are intended to act in parallel with
the secondary aeration tanks.

*Treatment facilities, *Sewage treatment, Rivers, Storm water, Filters, Storage
tanks, Sedimentation, Water purification, Water quality standards, Percolation,
Filters, Biochemical oxygen demand, Activated sludge, Sludge treatment, Aeration,
Suspended solids

Kitwe, Zambia; Borough of Mossley, Lancashire, England; Seven Arches, Weybridge,
Surrey, England; Great Britain
126D

STUDY ON THE REMOVAL OF INORGANIC AND ORGANIC MERCURY IN
WASTE WATER BY THE FLOTATION METHOD,

Mukai, S. and Nakahiro, Y.

Kyoto University, Kyoto, Japan, Department of Mineral
Science and Technology

Memoirs of the Faculty of Engineering Kyoto University, Vol. 35, No. 4, p 361-
380, October, 1973.  20 ref.

The removal of inorganic and organic mercury in waste water by the flotation
method was investigated as a part of the intensive studies of the water pollu-
tion control.  Inorganic mercury was efficiently removed by the Fe(OH)3 copre-
cipitation flotation method with 80 mg/liter cumulative addition of ferric
ions in the pH about 0 after the third stage flotation using sodium oleate as
a collector.  Sodium sulfide was added to the waste water to completely preci-
pitate the mercury.  Organic mercury was removed by decomposing the compound con-
taining the organic mercury into inorganic mercury with gaseous chlorine, fol-
lowed by the Fe(OH)3 coprecipitation-flotation method and the Fe(OH)3 copreci-
pitation Na2S precipitation flotation method.  The optimum conditions were at a
pH below 1.  The removal of excess chlorine in the flotation pump is important
for a successful flotation of the precipitates.  The excess chlorine was elimi-
nated by 8 g/liter sodium thiosulfate or the aeration over 40 min.  Mercury de-
composed by C12 gas was completely removed by the flotation method with an addi-
tion of 50-100 mg/liter ferric ions and 1 equivalent of sodium sulfide to the
total amounts of mercury at the pH 5.0-9.5.

*Waste water treatment, *Flotation, Chemical precipitation, Water pollution con-
trol, Hydrogen ion concentration, Investigations, Organic compounds, Inorganic
compounds, Chlorine,  Water purification

*Mercury compounds, Japan, Iron hydroxide, Sodium sulfide, Sodium thiosulfate
                                        292

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127D

THE DEVELOPMENT OF A NEW WATER TREATMENT,

Finan, M., and Atkinson, A.

CIBA-GEIGY (UK) Limited, Water Treatment Application and
Technical Service

The Steam and Heating Engineer, Vol. 43, No. 507, p 6-10, February, 1974.  4 fig,
3  tab.

The techniques used by CIBA-GEIGY  (UK) Ltd. to develop, from laboratory to
full scale use, the new Belgard range of water treatment formulations are des-
cribed.  The laboratory tests included:  magnesium hydroxide deposition on heat
transfer surfaces:  static conditions; magnesium hydroxide deposition on heat
transfer surfaces:  flowing conditions; activities in simulated water recircu-
lating.  The additional following  laboratory tests are described:  threshold
effects of various scale forming salts; crystal modification effects; calcium
carbonate deposition on heat transfer surfaces:  flowing conditions; and acti-
vities in simulated water recirculating cooling systems.

*Waste water treatment, Salts, Crystals, Laboratory tests, Methodology, Heat
transfer, Magnesium hydroxide, Flow, Calcium carbonate, Recirculated water,
Cooling water, Boilers

*Belgard water treatment formulations, United Kingdom
128D

AN EXPERIMENTAL IRRADIATION FACILITY FOR THE STERILISATION
OF SEWAGE SLUDGE  (VERSUCHSBESTRAHLUNGSANLANGE ZUR HYGIEN-
ISIERUNG VON KLARSCHLAMM),

Suss, A., Moetsch, H., Bosshard, E., Schurmann, G., and
Luescher, 0.

Bayerische Landesantalt fuer Bodenkultur und Pflazenbau,
Muehchen und Freising, Germany

Kentechnik, Vol. 16, No.  2, p 65-70, January, 1972.  4 fig, 11 ref.

An experimental irradiation facility for the sterilization of sewage sludge was
designed and built at the sewage treatment plant of the Ampergruppe in Geisel-
bullach.  It is at present: equipped with a 120 kCi Co 60 source and can process
a daily flow of about 30  cu m sewage sludge at an exposure of 300,000 R.  The
treatment capacity of the facility can be raised for four or five times the
present level without any structural alterations by using a stronger source.
The main components of the facility consists of the irradiation shaft with a
built in central tube in which the sludge is recirculated during irradiation and
the recirculation system  consisting of an accessible pump shaft with the  re-
circulation and evacuation pumps the necessary shutoff and regulation valves
and pipework.

*Sludge treatment, *Treatment facilities, *Radiation, Agriculture, Design data,
Sewage sludge, Sterilization, Waste water purification, Equipment, Evaluation,
Costs

Ge rmany

                                         293

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129D

SURFLEET SEWERAGE SCHEME,

Water Services, Vol. 78, No. 935, p 13-14, January, 1974.

The design and construction of the Surfleet sewage works is described.  Because
of the typical fenland topography, the area is served by a system of sewers, in-
corporating six pumping stations and associated rising mains.   The bulk of the
sewage flow discharges into the first pumping station at the center of the vil-
lage from which point it is pumped to the sewage treatment works.  A total of 5500
m of 225 mm diameter and 150 mm diameter pipes were laid to serve an existing
population of 845 persons.  The sewers have been designed on the separate sys-
tem so that storm water has been excluded as far as it is possible.  A new
sewage treatment works has been constructed to the North of the village and
consists of inlet works, settlement tanks, hoppers, pumping stations, filter
beds, and humus tanks.  Provision has been made for incorporating tertiary treat-
ment in the future.

*!>ewage treatment, *Treatment facilities, Pumping plants, Filters, Topography,
Ssiwers, Pipes, Sludge, Equipment, tertiary treatment

Surfleet, England
130D

LONGBRIDGE SEWAGE TREATMENT WORKS,

Water Services, Vol. 78, No. 936, p 44-47, February, 1974.

The design and operation of the new joint sewage works at Longbridge for the
Boroughs of Warwick and Leamington Spa, England are described.  The works re-
places the existing Warwick sewage works and will treat up to 60% of the flow
from Leamington Spa.  The works operates on the double filtration system of
treatment involving two successive applications of settled sewage on to two
sets of biological filters with intermediate sedimentation.  The facilities
consist of the following:  inlet unit, flow separation and storm sewage treat-
ment, primary sedimentation tanks, high level pumping station and main control
room, primary filters and humus tanks, secondary filters and humus tanks, outfall,
and sludge dewatering plant.  The plant will meet the effluent standards pre-
scribed by the Severn River Authority.

*Sewage treatment, *Treatment facilities, Sludge treatment, Dewatering, Water
quality standards, Effluents, Filtration, Flow, Sedimentation, Biological
treatment, Pumping plants, Filters

England, Warwick, England, Leamington Spa, England
                                           294

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131D

CONTACT STABILISATION—A PROCESS WITH A FUTURE?

Goddard, J. E.

Permutit Company, Limited

Water Services, Vol.  78, No. 935, p 16-17, January, 1974.

The contact stabilization process, which was one of the earliest developments
in the application of biochemical engineering to sewage treatment, is described.
The process employs two aeration zones separated by a secondary clarification
tank.  Raw sewage and activated sludge are aerated together in the first zone,
known as the contact  zone, for a short period after which the mixed liquor is
passed to the settlement stage.  At this point the treated sewage can be dis-
charged, being below  the normal Royal Commission standard of 20/30 i.e., BODS
less than 20 mg/liter and suspended solids less than 30 mg/llter.  Most plants
give an effluent of around the 10/15 standard.  The sludge from the settlement
stage is returned for further aeration before being mixed with more raw sewage
in the contact zone.  Such a plant is smaller than an equivalent conventional
plant by a factor of nearly two.  The development of the process was somewhat
empirical but was based on the observation that the initial removal rates of or-
ganic matter by activated sludge was  very high.  The most important factor
in the contact stabilization process is that the two phases of the reaction are
separated and this leads to more efficient and quicker purification.

*Sludge treatment, *Biochemical oxygen demand, Suspended solids, Water quality
standards, Activated sludge, Aeration, Sewage treatment, Chemical oxygen demand,
Nitrification, Engineering

*Contact stabilization, England
132D

i500,000 SLUDGE TREATMENT PLANT,

Water and Waste Treatment, Vol. 16, No. 12, p 17, 19, December, 1973.

The design and operation of the recently completed sludge treatment and pres-
sing plant at the Motney Hill Treatment Works of the Rochester, Chatham, and
Gillingham Joint Sewage Board (England) are described.  The installation will
chemically condition and press the sewage sludge separated out at the treatment
works.  The sludge pressing plant forms part of the program of major extensions
to the Motney Hill sewage treatment works to enable it to cater for the expan-
ding population of the Medway Towns.  The existing works serves a current popu-
lation of approximately 215,000 and provides for comminution, grit removal, pre-
aeration and primary settlement of the sewage before it is discharged to the
River Medway.  Additions are scheduled for the primary and sludge treatment
facilities and the construction of a partial secondary treatment plant designed
to hold the pollution load on the estuary at its present level.  The following
processes at the plant are described:  existing sludge treatment, new sludge
treatment arrangements, screening and copperas conditioning, lime conditioning,
filter presses, sludge feed to the presses, sludge disposal, liquor treatment,
conditioning agents, and the building services.

*Sludge treatment, *Treatment facilities, Filtering, Lime, Sludge disposal,
Water pollution control, Estuaries, Design data

England, Iron sulfate
                                        295

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133D

ALL PROCESSES CENTRALLY CONTROLLED AND MONITORED, NORWICH
CORPORATION,

Water and Waste Treatment, Vol. 16, No. 12, p 11, 13, December, 1973.

The sewage treatment facilities at Norwich, England which are currently being
extended to treat 55,000 cu m/day DWF of sewage from a contribution population
of 197,000 persons is described.  There are two treatment plants.  One has cir-
culation sedimentation radial flow tanks, biological filters and humus tanks
with effluent pumping facilities, and the other has circular radial flow sedi-
mentation tanks, diffused air activated sludge plant, and final settlement.  The
processes have been automated and interlinked into one central control system.
The system is the Kent K70 system which has a complete range of both hardware
and software for computer process control   The system is compatible with most
digital computers.

*Sewage treatment, *Treatment facilities, *Automation, Computers, Sludge treat-
ment, Equipment, Monitoring

England
134D

TECHNICAL TOUR FEATURES LULU ISLAND SEWAGE PLANT,

Water and Pollution Control, Vol. 112, No. 3, p 26-27, March, 1974.

The design and operation of the Lulu Island sewage plant of Greater Vancouver,
Canada are discussed.  The treatment plant serves an area of over 16,000 acres
with a system of lateral sewers draining to local pump stations and pumping
through shallow force mains to a truck sewer.  The plant was designed for an
average dry weather flow of 13.45 mgd in 1980, with provisions for expansion
to handle an estimate of 29 mgd by 2021.  The plant was designed to reduce BOD
by a minimum of 60%.  Primary treatment includes influent sampling, prechlorina-
tion, pumping from a subsurface wet well to an above ground screen room housing
multiple barminutor units, preaeration and grit removal, sedimentation, sludge
removal followed by thickening, dewatering, incineration, and sterile ash dis-
posal.  Post chlorination in chlorine contact tanks has a one hour detention
time and automatic chlorine residual control.  There is provision for sampling
and metering of effluent.  The plant was also designed to accomodate possible
future construction of secondary treatment facilities.

*Treatment facilities, *Sewerage, Canada, Sewers, Sewage treatment, Biochemical
oxygen demand, suspended solids, Sludge, Pumping plants, Equipment, Dewatering,
Sludge treatment, Construction, Operation, Costs

Lulu Island, Canada
                                     296

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 135D

 COMPUTERISED SEWERAGE SCHEME,

 Measurement and Control,  Vol.  7,  No.  3,  p  83-84,  March,  1974.

 The  computerized sewerage scheme  which serves  the Boru Borough of  Motherwell
 and  Wishaw in Lanarkshire,  England  is described.   It  consists  of a new man  sew-
 age  works  with a processing capacity  of  682,500  cu m/day of  raw sewage and  two
 outlying works with  capacities  of 68,200 cu  m/day and 6800 cu  m/day.   All
 three works are supervised  through  a  computerized telemetry  and control system.
 The  system provides  a high  degree automatic  control for  two  works  each of which
 are  controlled on three push buttons.  Without the facilities  of the  computer
 based system,  298 push buttons  would  have  been needed for control  of  the outly-
 ing  works.   A major  feature of  the  control system philosophy is the amount  of
 information processing carried  out  by the  computer.   The plant is  run on the
 management  by exception principle,  only  information about deviations  from nor-
 mal  are presented to the  operator.  The  control  system will  also initially  be
 used in a  data gathering  mode  to  amass information about the performance of
 the  plant  in a variety of situations.

 ^Computers,  *Sewerage, Treatment  facilities., Automatic control, Sewage,
 Data collections, Water pollution control

 England
136D

80/80 STANDARD INTO BRISTOL CHANNEL YEO VALLEY MAIN
DRAINAGE SCHEME,

Water and Waste Treatment, Vol. 16, No. 12, p 7-9, December, 1973.

The Yeo Valley Main Drainage Works at Kingston Seymour, Clevedon, Somerset are
described.  The effluent discharges to an estuary into the Bristol Channel.  The
works has been designed hydraulically to handle a maximum rate of flow of 1578
liters/sec or six time ultimate dry weather flow to allow for storm flows from
the old combined sewerage systems connected into the new regional scheme.  The
treatment consists of maceration, grit removal, filtration through high rate
polyvinyl chloride filters, sedimentation and discharge through an effluent
pipeline to the head of the Kingston Pill.  Sludge is disposed of by heat
treatment sludge conditioning followed by Filter pressing to produce a sterile
sludge cake with a moisture content of 50% suitable for disposal to tip.  Speci-
fically described are the sewage treatment processes, biological oxidation,
settlement, sludge disposal, inlet pipes, inlet pumping station, recorders,
barminutors, detritors, filters pumping station, filters, humus tanks, booster
pumping station, outfall pipeline, sludge pumping station, sludge holding tanks,
transfer sludge pumping station heat treatment plant, administration building,
and the remote control system,  and the electricity supply and services.

*Sewerage, *Treatment facilities, Design data, Equipment, Filtration, Sedimen-
tation, Sludge treatment, Activated sludge, Biological treatment, Pumping sta-
tion, Filters, Sewage, Storage  tanks, Organic matter, Pipelines, Remote con-
trol, Electricity

Barminutors, Recorders, Detritor, Great Britain
                                         297

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 137D

 RESPIRATION AND DENITRIFICATION  STUDIES ON LABORATORY AND
 WORKS ACTIVATED SLUDGES,

 Clayfield, G. W.

 Upper Tame Main Drainage Authority, England

 Water Pollution Control, Vol.  78, No. 1, p 51-76, 1974.  13  fig,  20  tab, 46 ref.

 The respiratory, denitrifying, and dehydrogenase activities  of activated sludges
 from full scale and laboratory scale plants were investigated.  The  activated
 sludges were always washed  to  remove soluble and weakly absorbed  substrates.
 Synthetic sewage was used to facilitate comparison of the estimated  potential
 activities of the sludges.  Measurement of carbonaceous metabolic activity,
 nitrification and denitrification of activated sludges from  the various sources
 made the examination of the interrelationship and dependence on operating
 variables such as BOD possible.  An attempt was also made to account for oxy-
 gen uptake and to use the relationship obtained to suggest a means of estima-
 ting the quantity of surplus activated sludge produced during treatment.  Among
 the conclusions are these:  it is advantageous to operate at low  loadings; de-
 nitrifying ability tends to fall with decreasing BOD loading; endogenous res-
 piration is a variable and  depends upon the history of the sludge; respiration
 rates support the view that conventional activated sludges are low in viable
 bacteria; and respiration rate measurements could profitably be included in the
 examination of activated sludge.

 ^Activated sludge, *Respiration, *Denitrification, Investigations, Biochemical
 oxygen demand, Sludge treatment, Nitrogen, Ammonia, Chemical oxygen  demand,
 Equipment, Sewage bacteria

 *Dehydrogenase activity, Great Britain
COMPUTER OPERATED SEWAGE TREATMENT AT NORWICH,

Effluent and Water Treatment Journal, Vol. 14, No. 2, p 79, February, 1974.

The annual report of the City of Norwich Sewage Purification Works is summarized.
Figures are given for total volume of sewage received at the works during the
year, the average daily volume of raw sludge removed from the sedimentation
tanks, average rate of application of settled sewage to biological filters,
average daily volume of recirculated final effluent, solids loading of the
sludge digestion plant, overall average reduction in total solids fed to the
digestion plant, and the average daily flow of trade effluent.  The final ef-
fluent quality failed to comply with the River Authority/s relaxed limits for
most of the year.  It was anticipated that the commissioning of four new humus
tanks late in 1972 would contribute to some improvement.

*Sewerage, *Treatment facilities, *Administration, Waste water purification,
Sewage treatment, Sludge digestion, Sludge disposal, Effluents, Solid wastes,
Maintenance

Norwich, England
                                           298

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 139D

 IN CONFERENCE:   METROPOLITAN TORONTO'S EXPERIENCE IN
 PHOSPHATE REMOVAL,

 Baldock,  E. H.

 Water and Pollution Control Division,  Toronto,  Canada

 Water and Pollution Control, Vol.  112, No.  3,  p 47-51,  63,  March,  1974.

 The results of  laboratory studies  to establish  the phosphate balance of  the
 North Toronto Sludge Treatment Plant streams are discussed.   Plant trials  were
 made with iron  and  aluminum salts.   Total phosphorus reduction to  meet a mini-
 mal requirement of  80% was achieved with both  salts.  The total phosphorus re-
 duction to meet a minimal requirement  of 90% was achieved with the iron  salt and
 could have been achieved with the  aluminum salt with a  slight increase in  dose
 rate.  The total phosphorus reduction  to meet a requirement  of less than 1
 mg/liter  was achieved with both salts.  The best results  were achieved when
 the precipitant salts were added at the end of  the aeration  tanks.   The  final
 effluent  had higher values for suspended solids and BOD when both  salts  were
 used than before the test period.   Digester performance remained satisfactory
 with a slight increase in gas production,  an increase in  digested  sludge solids,
 and a decrease  in supernatant solids.   No adverse effects were experienced in
 the sludge dewatering process using a  coil  type vacuum  filter.   This improve-
 ment is more marked with the use of ferric  chloride than  with alum.

 *Sludge treatment,  *Treatment facilities,  *Phosphates,  Investigations, Alumi-
 num, Salts,  Iron, Phosphorus, Effluents,  Suspended solids, Biochemical oxygen
 demand, Digestion

 Ferric chloride,  Toronto,  Canada
140D

BIOLOGICAL TREATMENT OF AIRPORT WASTEWATER CONTAINING
AIRCRAFT DE-ICING FLUIDS,

Jank, B. E., Guo, H. M., and Cairns, V. W.

Environmental Protection Service, Ontario, Canada, Waste-
water Technology Centre

Report No. EPS-4-WP-73-5, July, 1973.  113 p, 26 fig, 43 tab, 7 ref, 2 append.

The feasibility of treating a combination of de-icing fluids and airport
waste water using an activated sludge process was investigated to provide in-
formation for the design of treatment facilities at the new airport at St.
Scholastique, Quebec, and for assessing alternatives at other airports across
Canada.  The first part of the study was a bench scale activated sludge study
to determine the optimum loading condition and to obtain design parameters
for the treatment of de-icing fluids and municipal sewage at low temperatures.
A 131 cu m/day IGPM pilot plant was operated at the optimum organic loading
to verify the results from the laboratory scale study and determine whether
there were any operational problems.  The second part of the program bioassay
studies was carried out to determine whether the aircraft de-icing fluids and
process effluents were acutely toxic to rainbow trout.  The results show
that an activated sludge system treating a combination of de-icing fluid and
domestic sewage at less than 10 C produces an effluent have BOD and suspended
solids concentrations not exceeding 20 mg/liter and 25 mg/liter respectively
at a loading of 0.15 kg BOD/kg MLSS/day.  Growth of filamentous microorgan-
isms and the resulting bulking condition were responsible for the low loading
condition.

*Waste water treatment, *Deicers, *Activated sludge, Investigations, Pilot
plants, Air temperature, Canada, Design criteria, Bioassay, Rainbow trout,
Toxicity, Domestic wastes, Biochemical oxygen demand, Suspended solids,
Microorganisms, Organic wastes, Effluents, Aeration, Equipment, Nutrients,
Oxidation
                                        299

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 141D

 TERTIARY PHOSPHORUS REMOVAL AND LIMITING NUTRIENT STUDIES
 AT C. F. S. LAC ST. DENIS,

 Shannon, E. E., and Salvo, J.  M.

 Environmental Protection Service,  Ontario,  Canada,  Waste-
 water Technology Centre

 Report No.  EPS 4-WP-74-1,  February,  1974.   60 p,  16 fig,  16 tab,  24 ref.

 Pilot plant experiments on the treatment of the stabilization pond effluent from
 C. F. S. Lac St. Denis are described.   The  plant  was a 10 Igpm chemical treat-
 ment system consisting of  chemical coagulation, flocculation, tube settling,
 and mixed media filtration components.   Various alum and  polymer  feed condi-
 tions were evaluated over  the  10 mo  period  of continuous  operation.  Algal
 assays were carried out on the receiving water, Lac Depatie,  to determine the
 limiting nutrient and to ascertain the  effect of  treated  and  untreated pond ef-
 fluent upon algal growth.   Because of seasonal variations in  the  quality  of
 the stabilization pond effluent, it  was observed  that the recommended summer
 alum dosage level of 100 mg/liter  must  be increased to 150 mg/liter to achieve
 equivalent  phosphorus removal.  Filter  backwash requirements  and  backwash
 sludge production and characteristics were  determined.  For several chemical
 feed conditions the pilot  plant demonstrated a limited capability for zinc, lead,
 iron, and nitrogen removal and a high efficiency  for coliform removal. Phos-
 phorus was  shown to be the probable  limiting nutrient in  Lac  Depatie and  the
 planned efforts to reduce  phosphorus loading to the lake  from C.  F. B. Lac St.
 Denis should significantly reduce  the present eutrophic conditions.  Chemical
 operating costs are estimated  at 5.3 cents/1000 I gal.

 *Waste water treatment,  *Pilot plants,  *0xidation lagoons,  Chemical treatment,
 Coagulation, Flocculation, Filtration,  Algae, Nutrients,  Growth, rates, Efflu-
 ents, Filters, Phosphorus, Investigations,  Zinc,  Lead,  Iron,  Nitrogen, Coliforms,
 Eutrophication, Operating  costs, Canada

 Alum, Backwash, C.  F.  B. Lac St. Denis,  Canada


142D

DOMESTIC WASH WATER RECLAMATION  FOR REUSE AS  COMMODE WATER
SUPPLY USING A  FILTRATION—REVERSE OSMOSIS SEPARATION
TECHNIQUE,

Hall, J. B., Jr., Batten, C. E., and Wilkins, J. R.

NASA Langley Research Center, Hampton,  Virginia

Report No. NASA TN-D-7600,  April, 1974.   34 p,  3 fig, 9 tab, 17 ref.

A combined filtration reverse osmosis water recovery system was evaluated  to
determine its capability to reclaim domestic wash water for reuse as a commode
water supply.  The system produced water that met all chemical and physical
requirements established by the U.  S. Public Health Service for drinking
water with the exception of carbon chloroform extractables, methylene blue
active substances, and phenols.  It is  thought  that this water is  of sufficient
quality to be reused as commode supply  water.  The filters were not capable of
removing particles less than 1 micron in size from the waste water.  The pro-
cess rate of the reverse osmosis unit was degraded by approximately 46.9%  for
the 2.7 cu m of filtered wash water processed.  Treatment of the process water
with 5 ppm chlorine was sufficient to reduce the microorganisms in  the. commode
tank to zero.  Efficient dissemination  of chlorine was required in order to
rapidly inhibit microorganisms in the processed water tank.  The use of the
combined process for wash water recovery will require a maintenance filter  to
remove solid materials including those  less than. 1 micron in size from the
wash water.  The reverse osmosis module, if sufficiently protected  from plug-
ging, is an attractive low energy technique for removing contaminants from do-
mestic wash water.

*Reverse osmosis, *Filtration,  *Water reuse, Water supply, Potable water,  Phe-
nols, Carbon, Chlorine, Chlorination, Water purification,  Sewage bacteria,
Investigations, Evaluation, Waste water treatment, Water conservation, Water
pollution, Domestic wastes, Operation,  Water quality standards

Commode water supply, Methylene blue, Chloroform
                                       300

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14 3D

REPLACES NEW WORKS 1900 INSTALLATION,

Water and Waste Treatment, Vol. 16, No. 12, p 13, 15, December, 1973.

The complete reconstruction of the sewage disposal works at Faversham (Kent,
England) is described.  Before the reconstruction, the works were mainly as
they had been constructed just after 1900 and tanks.  Sludge settled out in
the main pumping station and was desludged manually once a week and put into
open sludge lagoons with no underdrainage.  In 1971 alterations began on the
existing pumping station involving work below Ordnance Datum and the increase
in pumping capacity at that station to avoid the storm overflows functioning.
The existing rising main was found to be adequate for the new  flows at an
increased velocity.

*Sewage disposal, treatment facilities, Sludge, Pumping plants, Construction,
Design, Filters, Filtration, Sludge treatment

England
 144D

 PHYSICO-CHEMICAL TREATMENT OF STRONG MUNICIPAL WASTEWATER,

 Rebhun, M., and Streit,  S.

 Israel Institute of Technology, Haifa,  Israel
 Environmental Engineering Laboratories

 Water Research, Vol. 8,  p 195-201, March, 1974.  3  fig, 5  tab, 14 ref.

 Direct chemical flocculation—clarification of strong new waste water  followed
 by adsorption on activated carbon has been investigated.  The fate of  specific
 organic components  (low  organic acids,  carbohydrates, proteins, fats as well
 as BOD and COD) in the chemical treatment process  was also studied.  Excellent
 removals of phosphates,  fats and suspended solids  and a clear effluent were
 obtained in the chemical treatment.  The clear 'primary chemical' effluent is,
 however, of high soluble organic content, the largest fraction being the soluble
 (low) organic acids and  carbohydrates.  Adsorption of the chemically treated
 waste water on activated carbon gave a  60 percent  removal and a final effluent
 of a relatively high organic content including BOD.  The  high concentration of
 remaining organics is ascribed to poor  adsorbability of the low organic acids
 anions on activated carbon.

 *Municipal waste water, *Biochemical oxygen demand, *Chemical oxygen demand,
 Waste water treatment, Suspended solids, Effluents, Phosphates, Fats, Carbo-
 hydrates, Organic acids, Flocculation,  Clarification

 *Physico-chemical treatment, Israel
                                             301

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145D

OXYGEN ACTIVATED SLUDGE SELECTED BY PHILADELPHIA,

Nelson, M. D.

Philadelphia Water Department, Philadelphia, Pennsylvania,
Water Pollution Control Division

Civil Engineering, American Society of Civil Engineers, Vol.  44, No.  4, p 42-45,
April, 1974. 3 fig, 1 tab.

The Philadelphia Water Department compared three different pilot treatment fa-
cilities at one site.  These were an oxygen activated sludge  unit, a conven-
tional activated sludge unit, and a physical-chemical plant.   Design criteria
for the future were determined.  It was felt that either biological plant could
meet the effluent standards with the air plant giving more marginal performance.
The oxygen activated sludge plant was also slightly lower in  installed and
operating costs.  In a proposed site plan for the future plant,  aerator tanks
using pure oxygen will be placed downstream of existing primaries.  The expanded
plant will be highly automated, with on-site direct digital computer to monitor
all processes of plant operation.

*Waste water treatment, *Pilot plants, Design criteria, Activated sludge, Ef-
fluents, Aeration, Planning, Computers, Municipal wastes, Treatment facilities


*Philadelphia, Pennsylvania, Oxygen activated sludge, Physical-chemical plants,
Effluent standards
14 6D

TREATMENT AND DISPOSAL OF WASTEWATER SLUDGES,

Vesilind, P. A.

Duke University, Durham, North Carolina,
Department of Civil Engineering

Science Editor, p 1, Spring 1974.

A book review is given for a new publication,  to be used by both the student
and the practicing engineer.  Solids (sludge)  treatment as an operating cost
of waste water treatment is the focus of the book.  It is said to be design-
oriented, including practical data for conducting laboratory tests.

*Sludge treatment, *Solids, *Costs, Reviews, *Sludge disposal, Waste water
treatment, Universities, Municipal wastes, Treatment facilities, Data collec-
tions, Publications

*Book reviews, Municipal engineers, Ultimate disposal, Data calculations
                                         302

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147D

PROCESS DESIGN MANUAL FOR CARBON ADSORPTION,

Environmental Protection Agency

National Technical Information Service, PB-227 157, October, 1973.  79 fig, 29 tab.

The use of activated carbon for removal of dissolved organics from water and
waste water is one of the most efficient organic removal processes available
to the engineer.  Both the great capability for organic removal and the
overall flexibility of the carbon adsorption process have encouraged its ap-
plication in a variety of situations.  Activated carbon adsorbs a great vari-
ety of dissolved organic materials including many which are nonbiodegradable.
Biological degradation occurring on the granules complements the adsorption
process in removing dissolved organic material.  Carbon in certain configura-
tions also functions as a filter.  The greatest cost within the carbon treat-
ment process is the cost of the carbon itself.  Thermal regeneration of the
spent carbon makes the process economically feasible.  The most important
design parameter is contact time.  Hydraulic loading, within the ranges nor-
mally used, has little effect on adsorption.  The basic process configurations
of the physical plant include upflow or downflow, either under force of gra-
vity or pump pressure, with fixed or moving beds, and single (parallel) or
multi-stage (series) arrangement.  Data from both pilot and laboratory tests
are given.  Procedures for preliminary tests are discussed and the character-
istics of some full-scale plants, planned or operating, are presented.

*Activated carbon, *Waste water, *0rganic matter, Biodegradability, Filters,
Costs, Hydraulics, Pilot studies, Laboratory tests, Data, Plants, Flow

*Dissolved organics, Carbon adsorption, Hydraulic loading, Organic removal
processes, Upflow, Downflow


1480

DESIGN AND PERFORMANCE CRITERIA FOR SETTLING TANKS FOR
THE REMOVAL OF PHYSICAL-CHEMICAL FLOGS,

Heinke, G. W.

Toronto University, Toronto, Ontario Institute of Envi-
ronmental Sciences and Engineering

Research Program for the Abatement of Municipal Pollution Within the Provisions
of the Canada-Ontario Agreement of Great Lakes Water Quality, Research Report
No. 10, Vol. 1, March, 1973.  82 p, 20 fig, 12 tab, 44 ref.

The objective of this research was to study, both on a laboratory and full-scale
plant basis, the settling behavior of physical-chemical suspensions and to pro-
duce design and performance criteria for mixing—coagulation and settling tanks
in waste water treatment plants.  Approximately 50 long and short tube settling
tests were carried out at the university laboratories on Humber Sewage Treat-
ment Plant raw waste water, without and with chemical addition (alum, ferric
chloride, lime, polymers).  Plant studies at Sarnia over a period of eight
months and at Windsor for one month only were carried out.  Long tube settling
tests were carried out at the plants for comparison of plant to test results.
The results are presented in relation to type and dosage of chemical used, ef-
fluent suspended solids and BOD, overflow rate, and detention time.   Results
of the laboratory tests show that all three coagulants (alum, ferric chloride,
lime) used in this study increased settling rates of solids, but to varying
degrees.  Lime produced fastest settling floes, ferric chloride intermediate
and alum slowest rates.  Addition of polymer and recycling of sludge further
increased settling rate.  For the Sarnia clarifiers a scale-up factor of 2.0
was determined, meaning that laboratory settling rates (or overflow rates)
must be halved for plant design to allow for the effects of turbulence in the
clarifier.  Variations in plant overflow rate between 300 to 600 gpd/sq ft (15
to 30 cu m/sq m/day) effected effluent quality only slightly.  Work will be
continuing in 1973/74 on this study.

*Settling, laboratory tests, *Pilot plants, Suspensions, Physicochemical
properties, Mixing, Design criteria, Sewage treatment, Lime, Biochemical oxy-
gen demand, Effluents, Suspended solids, Coagulation, Overflow, Canada

*Settling tanks, Ferric chloride, Alum, Polymers, Toronto University, Toronto,
Ontario

                                       303

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149D

TO ESTABLISH VIABLE METHODS OF MAINTAINING WASTE TREAT-
MENT FACILITY EFFICIENCIES WITH REFERENCE TO FLOW VARIA-
TIONS,

James F. Maclaren Limited, Environmental Engineers and
Scientists, Willowdale, Ontario

Research Program for the Abatement of Municipal Pollution Within the Provisions
of the Canada-Ontario Agreement on Great Lakes Water Quality, Research Report
No. 11, 1974.  91 p, 34 fig, 13 ref.

Equalization of sewage flow variations has several major benefits:  reduced
unit size requirements for treatment facilities; more stabilized process oper-
ations; and, reduced bypassing of the incoming flow.  Limited attention has been
given to these aspects.  The first step was to develop a methodology for sizing
equalization facilities taking into account diurnal, daily and seasonal varia-
tions in sewage flow.  Actual flow data from a treatment plant having a 40-50
MIGD (million imperial gallons per day) capacity were used in development of
methodology.  The significance of flow equalization to the design of treatment
facilities was developed by revising design criteria for sizing treatment
facilities.  These were established using basic design concepts incorporating
modified hydraulic characteristics of equalized sewage flow into the design.
The methodology was then applied to sizing treatment facilities for a plant of
similar size to the selected plant operating under equalized and varying
flow conditions.  It was found that a saving in capital costs would be realized
by installing equalization facilities.  In conclusion, the study verified
the need for further investigation into the potential benefits of flow equali-
zation.

*Sewage, *Flow, Waste water, Treatment facilities, Design, Hydraulics,
Costs, Methodology, Data Efficiency, Canada


*Flow equalization, *Sewage flow, *Treatment plants, Process operations,
Ontario
150D

INTEGRATION OF PHYSICO-CHEMICAL AND BIOLOGICAL WASTEWATER
TREATMENT PROCESSES,

Dryman, W. R., and Haycock, D. H.

Waterloo University, Research Institute

Research Program for the Abatement of Municipal Pollution Within the Provisions
of the Canada-Ontario Agreement on Great Lakes Water Quality, Research Report
No. 7, 1973.  112 p, 23 fig, 37 tab, 7 ref.

Alum was added to an activated sludge process for phosphorus removal.  The
effects on the operation and performance of the process were investigated.  Two
pilot plants, each with a design capacity of 2.0 mgd, were operated in parallel
at various hydraulic loadings.  One plant was operated as a control and 100
mg/liter of Alum and 4 rag/liter Activated Silica were added to the aeration
tank of the other for phosphorus removal.  Laboratory studies were also per-
formed with continuous flow bench-scale models to gain information unobtain-
able from the pilot plant operations.  The effects of the Alum addition on
phosphorus removal, organic and solids removal, general plant operation, oxygen
utilization and transfer, and sludge production and characteristics were
evaluated at 1.5 mgd, 2.0 mgd and 2.5 mgd hydraulic loadings.

*Pilot plants, *Hydraulics, Design, Phosphorus, Organic matter, Sludge,
Operation, Silica, Models, Physicochemical properties, Biological treatment,
Waste water treatment, Canada

*Alum, *Phosphorus removal, Hydraulic loading, Organic and solids removal,
Bench scale models, Ontario


                                     304

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 151D

 SEWAGE TREATMENT METHODS IN FINLAND,

 Vlitasaarl,  M.

 Research Institute, National Water Board of Finland,
 Helsinki,  Finland

 In:   SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, Institute of Northern
 Studies, University of Saskatchewan, p 29-44, August 22-24, 1973.  10 fig,
 2 tab, 4 ref.

 The  Finnish  Water Conservation Policy is reviewed in this paper.  The goals
 and  achievements of using different treatment methods (e.g. simultaneous pre-
 cipitation,  direct precipitation, final coagulation, stabilization ponds,
 mireinfiltration) are discussed and compared.  Four examples of various treat-
 ment plants' reduction of BOD in percent vs.  monthly average temperatures are
 given.  Long term BOD studies were done to compare the effects of treated
 and  untreated  effluent.   It was shown that untreated effluent exerts a two
 stage BOD  on receiving waters, the second stage coming after approximately 30
 days.  Treated effluent was found to have a low and constant BOD value.

 *Sewage treatment, *Chemical precipitation, *Biological oxygen demand,
 *Temperature,  Oxidation ponds, Infiltration,  Cold regions

 *Simultaneous  precipitation, *Direct precipitation, *Final coagulation,
 *Mireinfiltration, *Finland
152D

SWEDISH EXPERIENCES IN SEWAGE TREATMENT,

Ulmgren, L.

National Environmental Protection Board,
Solna, Sweden

In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, Institution of
Northern Studies, University of Saskatchewan, p 45-64, August 22-24, 1973.
6 fig, 6 tab.

Various methods of sewage treatment are compared including:  chemical vs
biological treatment; precipitation with lime (slaked or un-slaked) as compared
with alum (aluminum sulphate) or iron salts; and various types of sludge
treatment.  Design guidelines are provided and a recommendation that any plant
located in an area with more than 30 days where the temperature is below -10 C,
should be covered.  It is also recommended that in the colder areas chemical
treatment is superior to biological treatment.

*Sewage treatment, *Temperature, *Lime, Biological treatment, Chemical
treatment, Chemical precipitation, Cold regions

*Sweden, *Alum, *Iron salts
                                 305

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1531)

SEWAGE TREATMENT IN THE NORTHERN AREAS OF THE U.S.S.R.,

Alferova, L. A., Sklrdov, I. V., Ponomarev, V. G., Hudenko,
B. M., and Gladkov, B. A.

All - Union Scientific Research Institute,
VODGEO Komsomolsky Prospect, Moscow, U.S.S.R.

In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, Institute of
Northern Studies, University of Saskatchewan, p 64-74, August 22-24, 1973.
3 tab.

Various types of treatment units are discussed with special reference to
compact units for small settlement areas.  Temperature effects on biochemical
processes are reviewed.  It was found that as the temperature was reduced the
biochemical purification of activated sludge was reduced and the specific
oxidation rate of organic substances was decreased.  The number of bacterial
types also decreases with a drop in temperature.  Numbers and activity of
bacteria associated with the second phase of nitrification showed a reduction at
temperatures above 37 C or below 15 C, especially below 10 C.

*Treatment facilities, *Temperature, *Biological treatment, Specific oxidation,
Nitrification, Bacteria, Cold regions

*U.S.S.R., *Qu unit, *MOCVODOKAMALNIIPROJECT, *Apt units, *0xitank,
Specific oxidation
154D

EXTENDED AERATION, CLARIFICATION AND ANAEROBIC TREATMENT
CYCLE,

Hughes, C. D.

City of Brandon,
Manitoba

In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, Institute of Northern
Studies, University of Saskatchewan, p 85-98, August 22-24, 1973.  3 fig,
3 tab.

The City of Brandon, Manitoba required a sewage treatment facility to handle
4 to 5 million gallons of industrial and domestic sewage per day during a 4
month winter period.  Test results indicate that a mixed system with effectiva
clarification and sludge return is very effective and not drastically affected
by temperature, oxygen variation, or sludge quantity.  Twenty hours extended
aeration, followed by anaerobic treatment in cold temperatures, can give
an economical method of treating sewage and give BOD reductions of 92 percent
or better.  Some design criteria were included.

*Aeration, *Temperature, *Anaerobic digestion, *Anaerobic conditions,
Treatment facilities, Sewage treatment, Biological oxygen demand, Cold regions,
Design criteria, Costs

*Extended aeration, Clarification, *Manitoba (Brandon), Mixed system
                                            306

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155D

FURTHER FIELD INVESTIGATION ON AERATED LAGOONS IN THE CITY
OF WINNIPEG,

Girling, R. M., Pick, A. R., and Van Es, D. W.

City of Winnipeg, Manitoba,
Waterworks, Waste, and Disposal Division

In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, Institute of Northern
Studies, University of Saskatchewan, p 89-124, August 22-24, 1973.  12 fig, 7
tab, 5 ref.

The City of Winnipeg made modifications to several of its aerobic-anaerobic
lagoons to operate them in series and test effectiveness of this method.
Included was a test of reduction in total solids during a no feed period.
Results obtained:  good BOD reduction (82 percent for system, 50 percent'for
first lagoon); suspended solids decline through system; dissolved oxygen was
generally above 1 mg/liter in all system parts; temperature decreases through
the cell sequence; total organic carbon decreases through the cell sequence;
observed significant nitrification well below 10 C; the four month no feed
period  (aeration) had a negligible effect on reducing sludge accumulation;
effluent was determined to be satisfactory.

*Aerated lagoons, *Aerobic conditions, *Anaerobic conditions, *Nitrification,
*Temperature, Cold regions, Sludge digestion, Biological oxygen demand,
Carbon, Aeration, Suspended solids, Performance

*Total organic carbon, Winnipeg, Manitoba
 156D

 THE EFFECTS OF WATER TEMPERATURE AND ELEVATION UPON AERATION,

 Hunter, J. S. and Ward, J. C.

 Colorado State University
 Ft. Collins, Colorado, Civil Engineering Department

 In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, The Institute of
 Northern Studies University of Saskatchewan, p 125-169, August 22-24,
 1973.  8 fig, 2 tab, 24 ref.

 A laboratory scale mechanical aeration system simulating near perfect mixing
 conditions was used to study variation in oxygen transfer rates into water as
 a function of changes in water temperature (0-40C) variation in overall
 volumetric mass transfer coefficient for aeration systems which varies linearly
with temperature and can be predicted from equation provided.  This equation in
 conjunction with others is usable to construct diagrams of combined effects
 that elevation and water temperature have on aeration.  These diagrams show
 that factors related to increasing altitude which reduce aerator output pre-
 dominate over these factors tending to exhaust aerator output.

 *Water temperature, *Aeration, *Elevation,  Cold regions Mass transfer,
 Colorado,  Efficiencies, Equations
                                         307

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 157D

DIFFUSION SYSTEMS FOR COLD CLIMATE LAGOONS,

Christiansen, C. D., and Smith, D. W.

Environmental Protection Agency
College, Alaska
Arctic Environmental Research Laboratories

In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, The Institute of
Northern Studies, University of Saskatchewan, p 170-206, August 22-24, 1973.
13 fig, 2 tab, 34 ref.

Studies to compare coarse and fine bubble aerators were carried out at the
Fort Greely lagoon.  Dissolved oxygen levels were monitored in both water and
sludge.  Horsepower requirements of different systems were calculated.
Conclusions reached were that fine bubble diffusers are more efficient in
oxygen transfer than coarse bubble diffusers, but not necessarily more eco-
nomical; power requirements in Ib 02 per horsepower-hour may be higher for
fine bubble diffusers; maintenance requirements are higher for fine bubble
diffusers.  Oxygenation efficiencies published in the literature may be used
for aerated lagoon design but where ice fog is a problem, one must use a
larger number of diffusers at increased spacing.

*Diffusion, *Cold regions, *Aerated lagoons, Alaska, Dissolved oxygen,
Efficiencies, Costs, Maintenance, Ice fog

*Fine bubble diffuser, Coarse bubble diffuser
158D

WASTE TREATMENT PERFORMANCE DATA AT PRINCE ALBERT PULP
COMPANY,

Aschun, 0. K.

Prince Albert Pulp Company,
Prince Albert, Saskatchewan, Canada

In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, The Institute of
Northern Studies, University of Saskatchewan, p 207-219, August 22-24, 1972.
8 fig, 3 ref.

This paper is a presentation of steady state waste treatment data gathered
over an 18 month period.  These data illustrate the effects of long term
trends in production changes and seasonal effects.  There was a marked
decrease in BOD during the warm summer months attributed to higher water
temperatures.  Toxicity tests and results are given.

*Pulp and paper industry, *Pulp wastes, Waste treatment, Biological oxygen
demand, Cold regions, Toxicity, Performance

*Saskatchewan (Prince Albert)
                                         308

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159D

SURFACE AERATION OF DOMESTIC WASTES SECTION 1 - THE
BONNYBROOK SEWAGE TREATMENT PLANT,

Meckelborg, E. I.

The City of Calgary
Bonnybrook Treatment Plant, Alberta, Canada

In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, The Institute of
Northern Studies, University of Saskatchewan, p 220-229, August 22-24, 1973.
4 fig, 1 tab.

The article is a description of the Bonnybrook plant and some problems in
the secondary treatment facilities during winter months.  Aerator icing
emerged as the number one problem.  Frozen scum on final clarifiers appears
to be infrequent.  A minor problem is dense fog over aeration tanks.  Ana-
lysis of the performance data indicate that during winter months (final
effluent temperature below 52 F) there was an increase in BOD removal effi-
ciency with an increase in final effluent temperature.

*Water temperature, *Ice fog, *Aeration, Canada, Waste treatment, Biological
oxygen demand, Efficiencies, Cold regions, Performance


Alberta (Calgary), Clarifier
160D

SURFACE AERATION OF DOMESTIC WASTES OPERATING EXPERIENCES AT RED
DEER, ALBERTA, SECTION II,

Lawson, P. D.

Reid Crowther and Partners Limited
Calgary, Alberta, Canada

In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, The Institute of
Northern Studies, University of Saskatchewan p 230-239, August 22-24, 1973.
6 fig.

A description of lagoon treatment facilities at Red Deer is given, along with
conclusions concerning temperature effects.  There is a rapid initial drop
in temperature in aerated lagoons when there is a large thermocline from
air to water.  Ice cover reduces temperature loss.  Equilibrium (thermal)
is quickly reached.

*Water temperature, *Ice, Cold regions, Aerated lagoons, Canada, Efficiencies,
Performance

*Alberta (Red Deer)
                                            309

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161D

ON THE COMBINED TREATMENT OF DOMESTIC SEWAGE AND WASTE WATER
FROM WOOD INDUSTRIES,

Airaksiner, J. U.

Oulu University, Finland

In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, The Institute of
Northern Studies, University of Saskatchewan, p 241-257, August 22-24, 1973.
4 fig, 3 tab, 15 ref.

A review of wood industries' contribution to the waste load of Finnish waters
is presented.  Eighty-eight percent of Finland's BOD is a result of wood
industry processes.  Combined treatment of domestic and wood industry ef-
fluent is discussed as to its advantages and disadvantages.  Results of three
pilot plant investigations are presented.  The three treatment methods are:
activated sludge process, extended aeration method, and waste ponding.
Results show good standards can be achieved by combined treatment of domestic
and wood industry effluent.  Temperature has a strong effect on efficiencies,
especially in waste ponding where the volume of the ponds must be increased
to achieve the desired results.

*Pulp and paper industries, *Pulp wastes, Domestic wastes, Waste treatment,
Water temperature, Performance, Efficiencies, Activated sludge, Cold regions

*Finland, Extended aeration, Waste ponding, Wood industries
162D

PSYCHROPHILES IN WASTE TREATMENT,

Henry, J. G.

Toronto University, Toronto, Canada
Department of Civil Engineering

In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, The Institute of
Northern Studies, University of Saskatchewan, p 305-331, August 22-24, 1973.
3 fig, 4 tab, 32 ref.

A study of the relationship between low temperature, psychrophilic bacteria
and their metabolic activity is compared to mesophiles.  The study was
divided into four areas:  full scale treatment plants, pure culture batch
tests, continuous mixed culture model studies, and identification of bac-
teria from model systems.  One outcome of study was the lack of a distinct
line separating psychrophiles from mesophiles.  It was also found that psychro-
phlles are present in substantial numbers in activated sludge plants, at
normal operating temperatures (7 C to 27 C).  Also, the relation between
microbial activity and temperature is non-linear.  A decrease in activity
accelerates at the lower temperatures.  Psychrophilic species include
Pseudomanas, Flavobacterium, Achromobacter, and Vibrio.

*Bacteria, *Temperature, *Metabolism, Treatment facilities, Models,
Canada, Cold Regions, Pseudomanas, Actinomycetes, Activated sludge, Waste
treatment

*Psychrophiles, *Mesophiles, Flavobacterium, Vibrio, Achromobacter
                                             310

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163D

BIO-PROCESSES OF THE OXIDATION DITCH IN A SUB-ARCTIC CLIMATE,

Murphy, R. S., and Rananthau, K. R.

Dames and Moore,
Fairbanks, Alaska

In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, The Institution of
Northern Studies, University of Saskatchewan, p 332-357, August 22-24, 1973.
7 fig, 6 tab, 12 ref.

Waste treatment in Arctic areas shares the same problems as treatment needs
world wide, that is:  climate, economics, and low population.  The extended
aeration modification of the activated sludge process appears to be a highly
suitable alternative for the treatment of small volumes of waste.  This paper
examines one form of the extended aeration process, the oxidation ditch.
One such facility at College, Alaska was studied during 1967-1968 and showed
a 90 percent BOD and suspended solids reduction at 50 percent loading.  It
was also found that biological processes operated at essentially the same
rate at low temperatures as at higher temperatures in more moderate climates.
Some design criteria are also included.

*Biodegradation, *Temperature, *Cold regions, Waste treatment, Alaska,
Activated sludge, Aeration, Costs, Biological oxygen demand, Suspended solids,
Design criteria, Treatment facilities

*0xidation ditch, *Extended aeration
164D

LOW TEMPERATURE EXTENDED AERATION THROUGH THE USE OP1 A FLOATING
TUBE SETTLER AND WOOD STAVE TANKAGE,

Buzzell, T. D., Sherwood, C. R., and Wilbur, P. F.

U. S. Army Corps of Engineers,
Hanover, New Hampshire,
Cold Regions Research and Engineering Laboratories

In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, The Institute of
Northern Studies, University of Saskatchewan, p 358-379, August 22-24, 1973.
8 fig, 1 tab, 12 ref.

A single tank extended aeration system is described which provides satisfac-
tory secondary treatment performance, reduces logistics problems, lowers costs,
and does not require encapsulation.  The system consists of a 2000 gallon
redwood stave tank, dual low head air blowers, dual cycle time clocks,
necessary air flow piping, a Marlof Rollmix Air Diffuser Assembly, and a
floating tube settler.  The most significant development is that of the
floating tube settler which provides automatic adjustment to peak flow de-
mands, and significantly reduces retention time as compared to typical
clarifier units.  Design criteria are included.

*Cold regions, *Aeration, *Temperature, *Design criteria, "Treatment facilities,
New Hampshire, Waste treatment, Biological oxygen demand, Suspended solids,
Performance, Clarification

*Floating tube settler, *Air diffuser, Low head air blower
                                           311

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165D

LOW TEMPERATURE DENITRIFICATION OF WASTEWATER,

Sutton, R. M., Murphy, K. L., and Dawson, R. N.

McMaster University,
Ontario, Canada

In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, The Institute of
Northern Studies, University of Saskatchewan, p 380-403, August 22-24,
1973.  9 fig, 4 tab, 29 ref.

A study was done to determine the rate of denitrification under various con-
ditions of loading and temperature to ascertain the practicability of the
biological denitrification process.  The experimental design employed five
temperature levels, and two levels of sludge in a stirred tank reactor,
as well as five detention time intervals in packed columns.  Results showed
the stirred tank method providing water with a concentration of less than
1 mg/liter nitrate plus nitrite N2 at temperature 10 C or higher, whereas
packed columns required temperatures of 20 C to 25 C to achieve the same
results.  Packed columns did appear to be superior to the stirred tank in
suspended solids reduction.

*Denitrification, *Temperature, *Cold regions, Waste water treatment,
Treatment facilities, Canada, Performance, Efficiences, Nitrates, Nitrites

*Stirring tanks, *Packed columns
166D

A DESCRIPTION OF SOME RECENT RESEARCH WORK OF PARTICULAR
INTEREST FOR THE INTRODUCTION OF NEW WASTEWATER TREATMENT
METHODS IN NORWAY,

Abrahamsen, J.

Ministry of Environment,
Norway

In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, The Institute of
Northern Studies, University of Saskatchewan, p 403-422, August 22-24, 1973.
7 fig, 6 tab, 8 ref.

A review is made of Norway's PRA program which has been surveying the theore-
tical and practical knowledge of different processes of waste water treatment.
Areas in which PRA has concentrated its efforts include:  chemical removal
of phosphorous salts; operation and study of mechanical, chemical, and bio-
logical effects on different recipients of different treated water, and
aerobic stabilization of sludge.

*Waste water treatment, *Treatment facilities, *Nutrient removal, *Biologi-
cal treatment, *Chemical treatment, Performance, Efficiencies, Design, Cold
regions, Costs, Sludge treatment, Phosphorous

*Norway, *Mechanical treatment
                                          312

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  167D

AN OVERVIEW OF THE PROBLEMS OF DISINFECTION,

Chambers, C. W.

U. S. Environmental Protection Agency,
Cincinnati, Ohio,
Advanced Waste Treatment Research Laboratories

In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, The Institute of
Northern Studies, University of Saskatchewan, p 423-437, August 22-24, 1973.
4 fig, 1 tab, 15 ref.

A variety of disinfectants are discussed, with primary emphasis on factors
having major impacts on the effectiveness of the physical and chemical agents
being considered, especially low temperatures.  Among the disinfectants con-
sidered are chlorine, iodine, bromine and bromine chloride, chlorine dioxide,
ozone, ultraviolet light, and heat.  Chlorine exhibited lowered disinfectant
potency at low temperatures and high pH values.  Bromine and bromine chloride
exhibit similar responses.  Chlorine dioxide would appear unfeasible for
Arctic use.  Ozone seems a. promising alternative but needs more testing.
Excess lime creates the need for pH adjustment before release of the effluent.
Ultraviolet radiation and heat may have cost constraints.

*Disinfection, *Chlorination, *Environmental sanitation, *Temperature, *Cold
regions, Costs, Performance, Efficiencies, Bromine, Chlorine, Ozone, Lime,
Ultraviolet radiation, Heat

*Bromine chloride, *Chlorine dioxide
 168D

 CHLORINE DISINFECTION OF WASTEWATER,

 Gordon,  C.  R.,  Davenport,  C.  V.,  and  Reid,  B.  H.

 U.  S.  Environmental  Protection Agency
 College,  Alaska
 Arctic Environmental Research Lab

 In:   SYMPOSIUM  ON WASTEWATER  TREATMENT  IN COLD CLIMTATE,  Institute  of
 Northern Studies,  University  of Saskatchewan,  p 438-481,  August  22-24,
 1973.   11 fig,  7  tab,  35 ref.

 A two-phase study was  carried out to  determine if  chlorination could provide
 satisfactory disinfection  of  waste water  at temperatures  less than  1 C.   The
 first  phase consisted  of batch treatment  with  rapid  chlorination and continuous
 stirring.   Four effluents  were tested (primary sedimentation system, a  15 day
 detention time  aerated lagoon,  and two  extended aeration  systems).  The  tests
 were run  at less  than  1 C  with controls run at 25  C.   Effective  disinfection
 was  achieved in all  four effluents at less  than 1  C  with  a 60 minute contact
 time and  no more  than  1 mg/liter  residual chlorine.  The  second  phase of
 the  study consisted  of running primary  sedimentation effluent through a  well
 baffled  flow-through chlorine  contact chamber  at less  than 1 C.   Acceptable
 reduction of coliforms was not reached  in the  flow-through chambers at  less
 than 1 C  until  residual chlorine  reached  2  mg/liter.   Doubling contact  time
 to 120 minutes  allowed proper  disinfection  with only 0.5  to 0.6  mg/liter.
 Conclusions are drawn,  the most important being that contact time appears
 to be  as  important as  maintenance of  a  particular  chlorine residual level.

 *Disinfection,  *Chlorination,  *Temperature,  *Toxicity, Environmental sanitation,
 Cold regions, Performance, Efficiencies,  Alaska, Hydraulic structures,
 Design flow

 Batch  flow,  Contact  time,  Plug flow
                                        313

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16 9D

LIME DISINFECTION OF SEWAGE BACTERIA AT LOW TEMPERATURE,

Morrison, S. M., and Martin, K. L.

Colorado State University
Ft. Collins, Colorado
Department of Microbiology

In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, Institute of Northern
Studies, University of Saskatchewan, p 482-506, August 22-24, 1973.
9 fig, 3 tab, 21 ref.

Studies were conducted to determine:  the effects of high pH on raw and treated
sewage bacteria at low temperatures (1 C to 15 C); degree of BOD removal from
waste water at high pH and low temperature; effectiveness of lime as a precipi-
tator of orthophosphate from sewage at low temperature.  Results showed
that raw domestic settled sewage and secondary sewage effluent could be dis-
infected to a relatively safe level by lime contact for less than 90 minutes
at a pH of 11.5 or higher.  The high pH lime systems also significantly reduced
both BOD and orthophosphate concentrations.  Recommendations for additional
studies are made.

*Disinfection, *Temperature, *Lime, *Biological oxygen demand, *Phosphates,
Performance, Efficiencies, Environmental sanitation, Waste treatment,
Colorado, Cold regions


*0rthophosphate
170D

OZONE DISINFECTION OF WASTEWATERS AT LOW TEMPERATURES,

Kinman, R. N.

Cincinnati University
Cincinnati, Ohio
Department of Civil and Environmental Engineering

In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, Institute of Northern
Studies, University of Saskatchewan, p 507-521, August 22-24, 1973.  2 fig,
6 tab, 12 ref.

In this study 03 was used to disinfect poorly treated effluents and well treated
effluents under low temperature (1 C and above) conditions.  The pH effect was
also tested under these conditions.  The study revealed that 03 is more inde-
pendent of pH effects or temperature effects than any other readily available
disinfectant.  03 was found to destroy coliform, total bacteria and Fecal
streptococci more rapidly at any pH or temperature than chlorine or iodine.
Problems with the use of 03 for arctic treatment facilities are:  power costs
of generation, need for onsite generation; and the difficulties of 03 transfer
from gas to liquid medium.

*Disinfection, *Hydrogen ion concentration, *0zone, *Temperature, Performance,
Efficiencies, Environmental sanitation, Waste treatment, Cold regions,
Water quality control, Ohio, Coliforms

Fecal streptococci


                                         314

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171D

FEASIBILITY OF PHYSICO-CHEMICAL TREATMENT OF RAW SEWAGE
AT LOW TEMPERATURES,

Maqsood, R. and Benedek, A.

McMaster University
Hamilton, Ontario
Department of Chemical  Engineering

In:  SYMPOSIUM ON WASTEWATER TREATMENT  IN COLD CLIMATES,  Institute of Northern
Studies, University of  Saskatchewan, p  523-548, August 22-24, 1973.  14 fig, 24
ref.

The article is a discussion of the effects of low  temperatures on the per-
formance of Physico-Chemical treatment  plants.  These units operate after
the large particles are removed from the effluent  and after it has been treated
with metallic coagulents  (alum, etc.) and polymeric  flocculants.  The PTC
method employs either Granular Activated Carbon (GAC) or  Powdered Activated
Carbon (PAC).  The use  of PAC requires  an additional step, the separation by
sedimentation of the PAC particles from the sewage.  Powdered carbon sludge is
not currently susceptible to regeneration though GAC is,  by thermal means.
The advantages of PTC over biological treatment include:  delivery of 10 mg/
liter BOD and 30 mg/liter COD on a continuous basis; insensitivity to hydraulic
and organic variations  of influent; improved removal of phosphorous and
heavy metals.  Disadvantages of PTC include:  high operating costs and
inadequate design and operational experience.  Conclusions drawn include:
chemical coagulation is influenced by temperature  but not to the extent of
infeasibility.  PAC absorption is little effected  by low  temperature; and
kinetics are temperature dependent but  less sensitive than biological pro-
cesses.

*Water quality control, *Temperature, *Chemical treatment, Performance,
Efficiencies, Canada, Cold regions, Biological oxygen demand, Chemical oxygen
demand, Water quality control, Environmental sanitation

*Granular activated carbon, *Powdered activated caron, *Physico-Chemlcal
treatment

172D

PHOSPHORUS REMOVAL BY LIME ADDITION TO A CONVENTIONAL AN-
AEROBIC STABILIZATION FACILITY,

Lechner,  L. J., and Davis, E.

Department of Environment
Regina, Canada
Air Pollution Control Branch

In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES,  Institute of Northern
Studies,  University of  Saskatchewan,  p 570-586,  August 22-24,  1973.   8 fig,
9 ref.

An investigation was conducted to determine the  phosphorous removal  capacity
of three  different dosages of lime in an anaerobic lagoon.  Secondarily,  it  was
hoped that a determination might  be made of the  effect of lime on the removal of
carbonaceous material.   The lime used in this study was a high calcium chemi-
cal grade hydrated lime.  The efficiency of phosphorous removal at a dosage  of
187.5 ppm and 100 ppm were similar,  about 82 percent, and little effected by
temperature.  Removal efficiency at 50 ppm was considerably below the other
levels.  Percent BOD removal for all three dosages was similar and not above
10 percent greater than the conventional untreated anaerobic process.   COD
removal was also similar for all three dosage levels.  Only the highest
dosage produced any increase in the removal of total carbon over that of the
untreated lagoon process.  The high dosage removed 93 percent  of the SS,  while
the moderate dosage removed 89 percent.   The untreated lagoon  and the low
dosage both removed 84  percent of SS.   All dosages appeared to be temperature
independent in SS removal.

*Phosphorous,  *Lime,  *Anaerobic digestion,  *Temperature,  Water quality control,
Cold regions,  Canada,  Performance,  Efficiencies,  Biological oxygen demand,
Chemical  oxygen demand,  Carbon,  Suspended solids

*Anaerobic stabilization, Phosphorous  removal,  Carbonaceous material
                                        315

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173D

REFINERY EFFLUENTS NEED EFFICIENT CONTROL,

Energy Digest, Vol. 3, No. 1, p 37-39, January/Febraury, 1974.  2 tab.

Refineries share the major problem of effluent control.  Three components make
up effluent water:  process steam, mixed with oil vapors which condense and
separate into oil and water; rain water in drainage areas which must be treated
to separate the oil they have picked up enroute; and water employed for cooling
purposes.  These three water streams are generally treated separately, by
gravity separation, flocculation with chemicals, biological treatment, acti-
vated sludge treatment, or air flotation plants.  The type and degree of water
treatment required is dependent upon the volume of the water, the quality, and
the size of the receiving water.  In addition, radioactive material can be a prob-
lem.  Considered too, are problems relating to pollution by the gas industry and
lack of effective sulphur legislation.

*Effluents, *0il, Flocculation, Waste water treatment, Sewage treatment, Acti-
vated sludge treatment, Aeration, Separation techniques, Gas, Water pollution,
Sulphur, Legislation, Biological treatment, Water quality

*Refineries, Effluent control
174D

WASTEWATER SYSTEM ALTERNATES:  WHAT ARE THEY. .  . AND
WHAT COST?

Monti, R. P., and Silbermann, P. T.

Water Quality Management Group, Anderson Nichols & Com-
pany, Boston, Massachusetts, Environmental Sciences
Division

Water and Wastes Engineering, Vol. 11, No. 5, p  40-48, 75, May, 1974.  10 fig.

As the third article of four, this presentation  describes objectives and ac-
tions for achieving zero discharge and effecting better waste water treatment
methods.  To achieve the high degree of BOD reduction and nutrient removal to
reach required discharge levels, a two-stage chemical precipitation with alumi-
num and ferric salts, and three-stage aeration followed by sand filtration, car-
bon column filtration, disinfection, and final effluent aeration is recommended as
a waste water treatment.  Phosphorus removal systems are discussed and a chemi-
cal system of removal was agreed upon as most efficient.  Ozonation and its ad-
vantages and potentials are also summarized.  All of the waste water treatment
processes outlined are facilities oriented to comply with the 1985 discharge limi-
tations to navigable waters mandated by Congress.

*Waste water treatment, *0zonation, *Biochemical oxygen demand, Aeration, Fil-
tration, Phosphates, Effluents, Standards, Chemical precipitation, Aluminum,
Salts, Legislation, Navigable waters

*Zero discharge, *Phosphorus removal, Congress
                                      316

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175D

FILTRATION MECHANISMS DURING THE REMOVAL OF CONTAMINANTS
FROM NITRIC ACID,

Rybakov, K. V., Kovalenko, V. P., and Rozanova, L. M.

International Chemical Engineering, Vol. 14, No. 2, p 263-264, April, 1974.  2
fig, 2 ref.

It is known that the filtration process can proceed with complete clogging
of the pores according to some intermediate law, with sludge formation, as well
as with a simultaneous or sequential combination of the above-mentioned phenome-
na.  In order to determine the filter surface area for clarification by filtra-
tion, it is necessary to establish the mechanisms which describe the process un-
der given specific conditions.  Illustrated are graphic methods for calculating
the nitric acid filtration process using various filter media.  The process is
found to take place by a sequential two-stage mechanism.  This involves first,
the partial clogging of the pores of the filter media and second, the sludge
formation.

*Filtration, *Sludge, *Clarification, Simulation, Mathematical studies, Inves-
tigations, Nitrogen, Filters, Pores, Removal, Contaminants

*Nitric acid, Sludge formation, Filter media
176D

ADVANCED WASTE TREATMENT PROCESS SELECTION, PART THREE,

Gulp, G. L., and Hamann, C. L.

Corona Del Mar, California

Public Works, Vol. 105, No. 5, p 71-14, May, 1974.  3 fig.

As the concluding part of a study of modification of existing waste water treat-
ment plants to meet higher effluent standards with respect to discharge of
suspended solids and aquatic growth nutrients such as nitrogen and phosphorus,
this deals with ammonia stripping, chlorination, ion exchange, and solids re-
moval by coagulation/filtration processes.  Ammonia stripping is the only one
of the three physical-chemical techniques which has been actually tried on a
full plant scale.  The process consists of raising the pH of water to 10.8 to
11.5; formation and reformation of droplets in a stripping tower; and providing
air-water contact and droplet agitation by circulation of large quantities of
air through the tower.  This method is effective and reliable for nitrogen re-
duction in climates which are not too cold.  For areas of cold weather, other
methods such as breakpoint chlorination are necessary.  This is a method whereby
chlorine is added to waste water containing ammonia nitrogen and reacts with
hypochlorous acid to produce chloramines.  Six United States plants are planning
to use this process.  Its advantages are low capital costs, assurance of dis-
infection, and conversion of ammonia to elemental nitrogen with no disposal
problem.  Disadvantages are the large increase in total dissolved solids.
Selective ion exchange uses zeolites which are selective for ammonia relative to
calcium, magnesium, and sodium.  It is still in the pilot stage but seems to re-
move nitrogen without adding objectionable quantities of other materials, and
is effective in cold weather.

*Ammonia, *Chlorination, *Ion exchange, *Suspended solids, *Treatment facilities,
Coagulation, Filtration, Waste water treatment, Nitrogen, Chlorine, Cold,
Disinfection, Zeolites, Pilot plants, Phosphorus

*Ammonia removal, *Solids removal, pH, Treatment plants, Breakpoint
chlorination

                                       317

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 17 7D

 HIGH  RATE  FILTRATION MEDIA CONCEPTS,

 Morey,  E.  F.

 The Taulman Company, Atlanta,  Georgia,
 Turbitol Division

 Public  Works,  Vol.  105,  No.  5,  p  80-83,  May  1974.   3  fig.

 High  rate  filtration has become a viable alternative  to  conventional  silica
 sand  media filters.  Five types of filter media are in existence.   These are:
 silica  sand only, where  grain  size is  distributed  from fine  to  coarse from
 top to  bottom; the  so-called "ideal filter"  with grain size  gradually decreases
 throughout bed depth;  the conventional dual-media  filter incorporating an anthra-
 cite  coal  layer on  top of silica  sand;  the mixed or tri-media concept, uti-
 lizing  a  combination of  anthracite, silica sand and garnet or ilmenite; and
 the uniform dual-media filter  comprised of highly  uniform anthracite  and silica
 layers.  The last three  are  approaches to the so-called  ideal filter  bed
 design.  Three plants  throughout  the country were  compared using dual, uni-
 form  dual, mixed media,  and  one inch caps (a slightly modified  conventional
 sand  filter).   Based upon their data,  uniform dual-media and mixed media fil-
 ters  exhibited better  performance than conventional dual media  filters.
 The efficiency increase  from significantly longer  filter runs will offset costs
 of installation.

 *Filtration, *Water treatment, *Filters, *Sand, Silica,  Design criteria, Pilot
 plants, Experimentation, Costs, Installation

 Filter  bed, Dual filters, Uniform dual filters, Mixed media filters,
 One inch  cap filters
 178D

 MARKETS FOR CHEMICALS GROW AND GROW,

 Gross, A. C.

 Cleveland State University and Predicasts, Incorporated,
 Cleveland, Ohio

 Environmental Science and Technology, Vol. 8, No. 5, p 414-418, May, 1974.
 1 fig, 2 tab.

 The economics of chemical companies in the antipollution field is discussed.
 Although inflationary forces will raise costs of these chemicals to perhaps
 15 percent by 1980, growth of water and waste water treatment chemicals is
 expected to exceed the growth rate of the economy.  Specific chemicals will
 significantly increase.  Polyelectrolytes should grow more rapidly than inor-
 ganic coagulants, membranes faster than other filter media, ion exchange resins
 faster than lime, with oxygen used more widely than air.  The industry is frag-
 mented; six specialty firms control almost half of the formulations.  These are
 Betz Laboratories, Chemed, Mogul, Merck, Nalco, and United States Filter.
 Chemical filter materials, pH neutralizers and salts, biological action chemi-
 cals, and internal water preparations are discussed.  Waste water treatment
 chemicals seem to forecast a larger market than water treatment, but both will
 be on the increase.

 *Costs, *Chemicals, *Waste water treatment, *Water treatment, Costs, Coagula-
 tion, Membranes, Polyelectrolytes, Lime, Ion exchange, Resins, Filters,
 Forecasting


 Economic markets, Betz, Chemed, Mogul, Merck, Nalco, U. S. Filter, pH,
Manufacturers
                                       318

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179D

HIGH-RATE FILTRATION,

Rice, A. H.

Journal of the American Water Works Association, Vol. 66, No. 4, p 258-261,
April, 1974.

High filtration rates for improved filtered-water clarity are a trend in
industry.  Practices of filtration vary widely because of a number of variables
in design and mechanisms of filters.  Filters become steadily finer as materials
deposit and head loss increases exponentially.  By being sure that filter-media
grain size is too large to permit straining to occur, this is prevented; and
removal is therefore by chance adhesion of the relatively small suspended
particles onto the relatively large surface of the filter media or previously
deposited material.  Flow rate, kind and amount of suspended solids, desired
effluent quality, and water temperature are the major variables in filtra-
tion.  Depth of filter and media size also influence head-loss, floe penetra-
tion, and water quality.  While the majority of United States watei-filter plants
use a sand filter, dual media filters with anthracite coal and three-media
filters with garnet or ilmenite are described.  In the use off multi-media fil-
tration, materials with different specific gravities are necessary, and the
materials must be relatively inexpensive and durable under filter conditions.
An additional problem in filtration, seasonal variabion of floe, has been solved.
Polyacrylamides and activated silica as floe-strengthening agents are a ne-
cessary part of new methods of high-rate filtration.

*Filtration, Clarification, *Water quality, *Filters, Water temperature,
Effluents, Suspended solids, Flocculation, Head loss, Silica, Design criteria

Polyacrylamides, High rate filtration, Floe penetration, Anthracite coal,
Filter-media
180D

THE DIRECT REUSE OF RECLAIMED WASTEWATER:  PROS, CONS,
AND ALTERNATIVES,

Phillips, W. J. II.

John Carollo Engineers, Walnut Creek, California

Journal of the American Water Works Association, Vol. 66, No. 4, p 231-237,
April, 1974.  9 tab, 21 ref.

Both sides of the waste water reuse issue hav,e been represented.  Reuse is
defined as the general use of a reclaimed resource and recycle is defined as
the use of a reclaimed waste water in a domestic water supply.  The argu-
ments in favor of waste water recycling are illustrated by ongoing research
and projects including:  treatment methods such as utilizing industrial waste
heat in adding treatment processes, polyelectrolytes to complex heavy metals
for removal, and activated carbon to remove organic contaminants such as
refractories and petroleum products; and measurement techniques such as gas
chromatography for monitoring drinking water supplies, or detection of
organisms by filter fluorescent antibody techniques.  The negative aspects
of water reuse are the unknowns in the areas of bacteriology, parasitology, and
virology both because of system unreliability and possible catastrophic break-
downs leading to epidemics and because of viruses, bacteria, and new chemicals
which may be toxic and resistant to treatment methods.  Alternatives to waste
water reuse are in the areas of water salvage—control of seepage, evapora-
tion control, vegetation management, water harvesting, desalination,disposal—and
water conservation.  Control and development of either water reuse or water con-
servation are seen as applicable to regional governments and public insti-
tutions on a large scale.

*Water reuse, *Recycling, AWaste water treatment, *Dotnestic water, Polyelec-
trolytes, Activated carbon, Petroleum products, Monitoring, Potable water, Fil-
tration, Bacteria, Toxicity, Water conservation, Public health, Evaporation
control

*Waste water reuse, Treatment methods, Parasitology

                                       319

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 181D

FACTORS IN REGIONAL ASSESSMENT OF WASTEWATER REUSE,

Horsefield, D. R.

Camp Dresser and McKee, Incorporated
Boston, Massachusetts

Journal of the American Water Works Association, Vol. 66, No. 4, p 238-239,
April, 1974.

Feasibility of waste water reuse in any region should be evaluated on the
basis of specific local conditions of quality, quantity, and economics.  The
North Central Texas Council of Governments assessed their area by asking what
the needs for present and future supplemental water supplies were, what
the best method of reuse for the region might be, what the potential markets
for renovated waste water were, and what water quality criteria for beneficial
uses needed to be.  The Texas Water Plan is long range and takes into account
methods of water reuse aside from domestic reuse twenty years from now.  These
include groundwater recharge, agricultural irrigation, recreational lakes,
industrial process water, and cooling water.  Disease prevention is foremost
as a consideration.  The only currently marketable method of the five above is
cooling water for steam-electric power plants.  If these operate at capacity,
for 1990, with recycled cooling water (high quality effluent), the make-up
requirement could be reduced by up to 40 fold.  Advantages of waste water
reclamation are in economics and in long-range planning.

*Water reuse, *Waste water disposal, *Recycling, *Cooling water, Water quality,
Standards, Water supply, Planning, Costs, Domestic water, Groundwater,
Recharge, Agriculture, Recreation, Industrial wastes, Diseases, Electricity,
Effluents, Power plants


Texas Water Plan, Texas, Waste water reclamation, Economics
18 2D

SELECTING MIXING FOR TREATMENT OPERATIONS,

Winter, R. L.

Philadelphia Mixers Corporation,
King of Prussia, Pennsylvania

Journal of the American Water Works Association, Vol. 66, No. 4,  p 262-264,
April, 1974.  5 fig.

Designs for mixers in water treatment and waste treatment vary according to
particular applications but basic operating principles are the same.  Waste
treatment is broken down into primary, secondary, and tertiary treatment.
Primary treatment removes solids with the aid of some type of liquid-solid
separation mechanism.  In secondary treatment, a biochemical process is
usually involved to get rid of undesirable bacteria and other impurities.
In tertiary treatment, this water is converted to a reusable state.  Mixers
are used for each phase, and vary in speed as well as size.  An additional
application of mixers in industrial operations are in automatic control of
pH value of waste water by a response valve which allows control of the flow
of lime.  Costs and flexibility determine the type mixer for any application.
Factors for consideration are speed changes, power changes, impeller changes,
gear-reducer load ratings, and agitator and support bearings.

*Mixing, *Water treatment, *Waste treatment, *Design criteria, Costs,
Liquids, Solids, Biological treatment, Tertiary treatment, Industrial wastes,
Lime, Waste water treatment, Separation, Equipment

*Mixers, pH
                                             320

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 183D

 FEASIBILITY  OF WATER REUSE AT HIGHWAY REST  STATIONS,

 Parker, C. E.

 Virginia Highway Research Council,
 Virginia Department of Highways,
 Charlottesville, Virginia

 Journal of the American Water Works Association, Vol.  66, No.  4,  p  247-249,
 April, 1974.  4 tab, 9 ref.

 Work was done to determine the  current  effluent quality  from an existing  rest
 station, the treatment required to upgrade  the waste water  from the rest
 area for recycle,  the requirements of the rest area, and the response  ne-
 cessary for  a recycle system to meet peak demands.  Water use  was correlated
 with rest area use and traffic  flow.  Waste water was  examined from an area
 employing an extended aeration  system and a holding pond, and  evaluated re-
 garding requirements for toilet flushing at peak needs.   It appears that  by
 changing the flow  scheme and storage and disinfection  scheme,  the present
 effluent could be  used for flushing toilets.  Capital  costs were  compared
 with the necessary system for effluents which are free from phosphorus and
 low in organic carbon.  This recycling  alternative would save  about $35,000
 per rest area.  On a test basis,  it is  indicated that  waste water reuse for
 flushing toilets at highway  rest areas  offers an alternative to releasing
 high-quality effluent to a stream.  Further demonstration projects  are
 needed for more conclusive statements.

 *Water reuse, *Water recycle, *Effluents, *Costs, *Waste water treatment,
 Water quality, Phosphorus, Organic carbon,  Aeration

 *Flush toilets, *Highway rest areas
184D

MERCURY CONTAMINATION OF VEGETATION DUE TO THE APPLICATION
OF SEWAGE SLUDGE AS A FERTILIZER,

Van Loon, J. C.

Toronto University, Toronto, Canada,
Institute of Environmental Sciences and Engineering
and the Departments of Geology and Chemistry

Environmental Letters, Vol. 6, No. 3, p 211-218, 1974.  1 tab, 7 ref.

Vegetation grown on sludged and control plots were tested for mercury con-
tent.  Washed and unwashed samples were also tested.  Of various plants,
leaves and seeds of wild barley and quack grass; tomato roots, plants and
fruit; bean roots plants and pods; carrot roots and tops and lettuce leaf,
only tomato fruit showed increase of mercury levels for the washed plant
material from the sludged plot.  In this case, levels up to fifty times higher
compared to specimens from unsludged plots were found.  In addition, further
investigation is recommended for surface contamination of vegetation by
mercury containing dusts and soils which can cause elevated levels in un-
washed material.

*Vegetation, *Mercury, *Sewage sludge, *Contamination, Soil contamination,
Experimentation, Soil surfaces, Tomatoes

Washed materials
                                           321

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185D

KINETICS OF ACTIVATED SLUDGE OXYGENATION,

Humenick, M. J., and Ball, J. E.

Texas University, Austin, Texas,
Department of Civil Engineering

Journal of Water Pollution Control, Vol. 46, No. 4, p 735-747, April, 1974.
10 fig, 2 tab, 31 ref.

The purpose of this study was to determine the basic causes for reported
greater sludge settleability, higher kinetic rates, and lower sludge produc-
tion using oxygenation.  It was determined that high purity oxygen is, in
fact, a realistic alternative to conventional aeration in the activated
sludge process.  The additional costs for production, distribution, and
utilization of oxygen may be justified by the benefits of an oxygenation
system.  However, these benefits seem to be derived not from metabolic change
in the organisms but from the ability to transfer oxygen rapidly across the
gas-liquid interface at low turbulence and to meet high oxygen uptake demands
per unit volume of mixed liquor.  Conclusions were that no significant dif-
ferences were found in the sludge yield coefficient, decay coefficient, or
substrate removal kinetics under aeration or oxygenation; no significant
difference was found in the initial settling velocity of activated sludge
developed in the zone settling range of mean cell retention time, suspended
solids concentration, and mixing history in the zone settling range; and
the choosing of oxygenation over aeration must depend on overall economic ana-
lysis.  Specific benefits of oxygenation include ability to supply oxygen
demands at the influent end of a reactor, significant DO concentration in the
plant effluent, and the reduced size of sludge processing equipment.

*Aeration, *0xygenation, *Costs, *Activated sludge, *0xygen, Experimentation,
Effluents, Influents, Sludge, Liquor, Treatment facilities, Gas, Liquids,
Settling, Kinetics, Waste water treatment, Equipment

Treatment plants
186D

OCEAN INCINERATION OF TOXIC WASTES,

Public Works, Vol. 105, No. 4, p 46-47, April, 1974.

Chlorinated hydrocarbons and other toxic wastes may be destroyed by a new
method, the incineration at sea.  A converted German cargo vessel was specially
constructed so that its combustion chambers may take toxic wastes from British,
Dutch, and Scandinavian companies.  An American counterpart is proposed for
1975.  The ship, named "Vulcanus", reduces the cost of incineration to nearly
one half of land incineration.  Chlorinated hydrocarbon wastes are disposed
of by incineration at 1400 C.  This temperature consumes 99 percent of the
materials; fumes settle in the ocean and are converted into mild hydrochloric
acid, which can be absorbed into the marine life without harm.  Burning is
done in combustion chambers in the rear of the ship and fumes fall astern
into the wake.  Burning in the North Sea is done fifty to sixty miles away
from the nearest coastline, and clear of shipping lanes.  Disposal is checked
for keeping within government regulations after each trip.

*Hydrocarbons, *Toxicity, *Incineration, *0ceans, Burning, Ships, Hydro-
chloric acid, Marine animals

*Toxic wastes, *0cean incineration, Combustion chambers, Vulcanus
                                         322

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187D

CHARACTERISTICS OF MUNICIPAL EFFLUENTS,

Pound, C. E., and Crites, R. W.

Metcalf and Eddy, Incorporated

In:  Proceedings of the Joint Conference on Recycling Municipal Sludges and
Effluents on Land, July 9-13, 1973, Champaign, Illinois, The National Associa-
tion of State Universities and Land-Grant Colleges, University of Illinois,
p 49-61.  12 tab, 19 ref.

A summary of the characteristics of municipal waste water and effluents from
common treatment processes is given.  The range of constituents varies from
weak to strong, and involves pre-treatment, primary, or secondary treatment
accordingly.  Characteristics of waste water are physical, chemical, or
biological.  Physical properties include total solids content, color, and
odors; chemical characteristics are organic matter, inorganic matter, and
gases; microorganisms, predominantly bacteria, make up the biological charac-
teristics.  Pre-treatment involves screening and sedimentation which yields
primary effluent.  Primary treatment by coarse screens and grit chambers does
not affect the biological characteristics.  These must be removed by secon-
dary treatment, biological oxidation and flocculation, as well as secondary
sedimentation.  Disinfection, or the selective destruction of disease-causing
organisms, is a final technique.  Decisions for application of effluents to
the land must take into account all water and soil quality data as well as
environmental conditions.  Irrigation systems can be designed using available
technology for the various treatment processes, depending upon the waste water
constituents.

*Municipal water, *Municipal wastes, *Irrigation, *Waste water treatment, Ef-
fluents, Biological treatment, Chemical treatment, Sedimentation, Screens,
Flocculation, Biological oxidation, Pre-treatment (water), Primary treatment,
Secondary treatment, Bacteria
 188D

ORGANICS,

Broadbent, F. E.

University of California

In:  Proceedings of the Joint Conference on Recycling Municipal Sludges and
Effluents on Land, July 9-13, 1973, Champaign, Illinois, The National Associa-
tion of State Universities and Land-Grant Colleges, University of Illinois,
p 97-101.  1 fig, 3 tab, 5 ref.

Sludge from domestic and industrial sewages may contribute to soil improvement
by affecting soil properties such as moisture holding capacity, structural
stability, and cation retention.  Organic components include partly undecom-
posed substances and partly microbial cells and by-products synthesized during
the treatment process.  Most are biodegradable, and are readily converted to
water, carbon dioxide, and other inorganic substances during aerobic treatment.
Little is known, of the nitrogen transformations attendant to sludge applica-
tion on soils and this area of research should be expanded.

*Domestic wastes, *Industrial wastes, *Soil properties, *0rganic matter,
Soil microbiology, Biodegradation, Aerobic treatment, Nitrogen, Soils, Soil
treatment, Carbon dioxide, Sewage sludge, Research

Soil holding capacity, Cation retention
                                       323

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189D

THE PROPERTIES OF SLUDGES,

Dean, R. B., and Smith, J. E. Jr.

Environmental Protection Agency
Cincinnati, Ohio

In:  Proceedings of the Joint Conference on Recycling Municipal Sludges and
Effluents on Land, July 9-13, 1973, Champaign, Illinois, The National Associa-
tion of State Universities and Land-Grant Colleges, University of Illinois,
p 39-47, 2 fig, 8 tab, 33 ref.

Because a typical digested sludge contains about twenty tons of water associa-
ted with each ton of solids, the major cost of sludge treatment and disposal
is related to dewatering and drying processes of this water.  Types of
sludge are categorized by the contaminants removed from waste water by physi-
cal, biological, and chemical treatments.  Raw primary sludge consists of
readily settleable fine silt and organic matter.  Waste-activated sludge (WAS)
is the biological multiplication of microorganisms feeding on suspended
and soluble organic matter in the presence of dissolved oxygen.  Controlled
putrefaction of either type sludge is known as anaerobic digestion.  This pro-
cess is easily upset by various toxic influents, and aerobic digestion to
stabilize sludge is often used as well.  Chemical precipitation by lime, alum,
or iron slats is frequently used for agricultural sludges, especially for
phosphate removal.  Toxicity caused by heavy metals is an additional problem.

*Sewage, *Sludge treatment, *Sludge disposal, *Biological treatment, *Chemlcal
treatment, Aerobic digestion, Anaerobic digestion, Lime, Alum, Heavy metals,
Agricultural wastes, Phosphates

Waste activated sludge (WAS)
190D

ENGINEERING AND ECONOMICS OF SLUDGE HANDLING,

Bauer, W. J.

Bauer Engineering, Incorporated

In:  Proceedings of the Joint Conference on Recycling Municipal Sludges and
Effluents on Land, July 9-13, 1973, Champaign, Illinois, The National Associa-
tion of  State Universities and Land-Grant Colleges, University of Illinois,
p  161-167.  1 fig, 2  tab.

It  is difficult and costly to dewater municipal sewage sludge and an alterna-
tive method is transportation and land application.  One such project was
the excavating and transport of over one million wet tons and land application
of over  half a million wet tons of sewage slurry from the Metropolitan Sanitary
District of Greater Chicago.  By open and competitive bidding, land application
could be an economically  feasible alternative  to incineration and make use of
the organic potential of  sludge.  Transport systems suggested include truck,
rail, pipeline, and barge.

*Costs,  *Dewatering,  *Incineration, Municipal  wastes, Sewage sludge, Pipelines,
Planning, Slurry

*Sewage  transport, *Land  application, Chicago, Illinois  (Metropolitan Sanitary
District of Greater Chicago)
                                            324

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 191D

 RECYCLING MUNICIPAL SLUDGES AND EFFLUENTS ON LAND,

 Williams, T.  C.

 Williams and  Works

 In:  Proceedings of the Joint Conference on Recycling Municipal Sludges and
 Effluents on  Land, July 9-13, 1973, Champaign, Illinois,  The National Associa-
 tion of State Universities and Land-Grant Colleges,  University of Illinois,
 p 169-173.

 Williams and  Works has designed schemes  involving land treatment involving
 pre-treatment considerations, energy requirements, and costs of operation.
 Pre-treatment processes include:   no pre-treatment other  than maceration;
 primary treatment; trickling filters; activated sludge; aerated lagoons, and
 anaerobic-aerobic pond systems.  Methods for land application, using spray ir-
 rigation, utilize equipment such  as center pivot machines,  winched pulled  guns
 that travel back and forth across the field, portable aluminum pipe systems,
 and solid set systems.  Research  needs are listed.  These include:  air
 pollution around treatment plants; inflow and outflow quality comparison on
 mature pond systems; quality of ice on ponds; muck and peat soils; swamp
 irrigation; entomology; animals,  thermal studies; movement  of groundwater  in
 the unsaturated  zone; pond recirculation; dissolved  oxygen  in the effluent;
 and study of  the quality of the drinking water supply system.

 *Municipal wastes, *Effluents, *Recycling, Pre-treatment  (water), Primary
 treatment, Trickling filters, Activated  sludge, Aerated lagoons, Ponds, Irri-
 gation, Equipment, Pipes,  Air pollution, Treatment plants,  Ice, Groundwater,
 Dissolved oxygen, Potable  water,  Water supply

 *Land applications, *Treatment methods
19 2D

HIGH-RATE LAND TREATMENT I:  INFILTRATION AND HYDRAULIC
ASPECTS OF THE FLUSHING MEADOWS PROJECT,

Bouwer, H., Rice, R. C., and Escarcega, E. D.

U. S. Water Conservation Laboratory, Phoenix, Arizona

Journal of the Water Pollution Control Federation, Vol. 46, No. 5, May, 1974.
3 fig., 5 tab., 11 ref.

An experimental high-rate land treatment system, the Flushing Meadows project,
was initiated to study renovation of secondary sewage effluent for irrigation,
recreation, and some industrial uses.  The project attempted the renovation
through high-rate infiltration basins in the bed of the Salt River.  It was
found that infiltration rates decreased linearly during flooding and were re-
stored sigmoidally during drying of the basins.  One acre of basin area could
renovate 0.36 mgd of effluent due to a hydraulic loading of 400 feet per year
obtained by 20 to 30-day flooding periods alternated with 10-day drying periods
in summer and 20-day drying periods in winter.  The bottom conditions most
desirable for high infiltration rates was mature grass stand, followed by
bare soil and then gravel.  A deep, nonvegetated basin is thought to be most
conductive to high infiltration rates over the long run.  A uniform, aniso-
tropic aquifer was assumed and showed good agreement with horizontal and verti-
cal hydraulic conductivities obtained by a resistance network analog from
groundwater level response to recharge and those obtained by well tests.  The
existence of active and passive flow regions was inferred by the effective
transmissibility for recharge of twelve percent of the transmissibllity for
the entire saturated height of the unconfined aquifer.  The hydraulic conduc-
tivity of the aquifer was not noticably affected by groundwater recharge with
sewage effluent.

*Secondary treatment, *Infiltration rates, *Flooding, Basins, Effluents,
Irrigation, Recreation, Water reuse, Hydraulics, Aquifers, Groundwater, Flow,
Sewage effluents

High-rate infiltration, Flushing Meadows Project, Phoenix, Arizona


                                        325

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193D

HIGH-RATE LAND TREATMENT II:  WATER QUALITY AND ECONOMIC
ASPECTS OF THE FLUSHING MEADOWS PROJECT,

Eouwer, H., Lance, J. C., and Riggs, M. S.

I. S. Water Conservation Laboratory, Phoenix, Arizona

Journal of the Water Pollution Control Federation, Vol. 46, No. 5, p 844-859,
May, 1974.  9 fig., 3 tab., 15 ref.

Water quality and economic aspects of the Flushing Meadows project in Phoenix,
Arizona, were investigated.  The filtration of the secondary effluent through
the gravel and sand resulted in almost complete removal of SS, BOD, and fecal
coliforms, but total organic carbon was still present in concentrations of
about five mg/liter.  No fecal coliforms were encountered after 300 feet of
horizontal travel.  Total nitrogen load at the design hydraulic loading rate
of 300 feet per year was 24,000 pounds per acre.  Cyclic flooding and drying
periods of several days each yielded essentially complete conversion of the ni-
trogen in the effluent to nitrate in the renovated water, but no removal of
nitrogen.  With flooding and drying periods of two weeks each, ammonium was
adsorbed in the soil during flooding and nitrified; it was partially denitri-
fied during drying.  This yielded a net nitrogen removal of about 30 percent,
which could be doubled or almost tripled by addition of organic carbon, recyc-
ling part of the renovated water, or by reducing the hydraulic loading rate.
Phosphate removal was about 50 percent after 30 feet of underground travel,
as was fluoride.  Copper and zinc were removed by about 80 percent.  Dissolved
E:alts of the renovated water was about two percent higher than that of the
effluent.  The pH was lowered from 8 to 7.  It was concluded that high-quality
renovated water suitable for unrestricted irrigation and recreation can be ob-
tained.  Cost was about $5.3/acre-foot which is significantly less than the
cost of equivalent in-plant tertiary treatment required to produce a water of
similar quality.

*Water quality, *Costs, *Filtration, *Secondary treatment, Suspended solids,
Biochemical oxygen demand, Coliforms, Flooding, Nitrogen, Recycling, Recrea-
tion, Irrigation, Water reuse, Ammonium, Tertiary treatment

*Hydraulic loading, Organic carbon, pH
 194D

 BIOLOGICAL  TREATABILITY  OF LANDFILL LEACHATE,

 Boyle,  W. C.,  and  Ham, R. K.

 Department  of  Civil  and  Environmental  Engineering,
 The University of  Wisconsin,  Madison,  Wisconsin

 Journal of  the Water Pollution  Control Federation,  Vol.  46,  No.  5,  p  860-872,
 May,  1974.   4  fig, 14 tab, 5  ref.

 A substantial  portion of the  organic pollutants  in  sanitary  landfill  leachate
 can be  removed by  biological  treatment.   Anaerobic  treatment of  raw leachate
 provided more  than 90 percent BOD  reduction  for  hydraulic  detention times
 greater than ten days at temperatures  of  23  to 30 C.   Aerobic polishing of
 the anaerobic  effluent produced BOD values proportional  to surface  water dis-
 charge.  Leachate  can be added  to  domestic waste water in  an extended aeration
 activated sludge plant at a  level  of at least  five  percent by volume  without
 serious impairment of quality.   At greater than  five  percent, leachate addi-
 tions caused substantial solids production,  increased oxygen uptake rates,
 and poorer  mixed liquor  separation.

 *Blological treatment, *Biochemical oxygen demand,  *Landfills, Pollutants,
 Organic matter, Anaerobic treatment, Domestic wastes, Activated  sludge,
 Oxygen, Solids, Liquors, Effluents, Waste water  treatment

 Landfill leachates,  Organic  pollutants


                                         326

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 19 5D

JET AERATOR HAS HIGH OXYGENATION CAPACITY,

Chemical Engineering, Vol. 81, No. 10, p 70, May 13, 1974.

A jet aeration system has been developed which consumes less power and is
much cheaper than pure-oxygen processes.  Its system design is based on oxygena-
tion capacities calculated from temperature, solids concentration, basin
geometry, BOD, COD, and equipment efficiencies.  The Eddy-Mix Jet Aeration
system features fiber-glass ductwork, submersible heavy-duty pumps and large-
diameter jets, and can be used in waste lagoons, oxidation ditches, or aera-
tion tanks.  Compressed air and recirculatlng liquor are brought into the jet
and form small, entrained bubbles.  The mixture is discharged on the bottom in
a horizontal stream.  Plumes are formed which provide turbulence.  Unlike
surface aeration systems, mixing is not limited by tank depth.

*Jets, *Aeration, *0xygen, Basins, Biochemical oxygen demand, Chemical oxygen
demand, Equipment, Efficiency, Pumps, Lagoons, Oxidation, Liquors, Streams,
Mixing

*Jet aeration, Basin geometry, Tank depth
I960

VORTEX CLARIFIER ACHIEVES FAST SEPARATIONS,

Canadian Chemical Processing, Vol. 58, No. 4, p 32-33, April, 1974.  1 fig.

A new clarifier has been designed by Queen's University Engineering Department,
Kingston, Ontario and will have its first commercial use and installation
by 1975.  This clarifier will process 200 gallons per minute or more of li-
quids which contain less than 1 percent solids.  It is designed to bridge the
gap between centrifuges and settling tanks used for this purpose.  The Bird Mach-
ine Company will use this "forced vortex" in which the liquid in the cone ro-
tates as if it were a solid body, minimizing fluid shear and hence turbulence.
By applying large rotational accelerations (500 to 2000 g) the particles
quickly agglomerate and reduce retention time to 40 seconds (rather than hours
in a settling tank).  Applications being considered are in recovering fibers
from paper mill effluents and the reduction of water pollution.  Possible
future uses include separation of immiscible liquids.

*Separation, *Clarification, Vortices, Installation, Liquids, Solids, Water
pollution control, Equipment,, Canada, Solids

Vortex clarifier, Kingston, Ontario, Forced vortex, Retention time,
Acceleration, Immiscible liquids
                                            327

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19 7D

GAMMA RADIATION AS AN EFFECTIVE DISINFECTANT,

Murphy, K. L.

McMaster University, Hamilton, Ontario, Canada,
Department of Chemical and Civil Engineering

Water and Pollution Control, Vol. 112, No. 4, p 24, 26, 28, April, 1974.
5 fig, 7 ref.

Gamma radiation has not been used as a disinfectant for waste waters primarily
because of costs.  However, while chlorine is currently the most widely used
disinfectant for potable water treatment, serious questions have been raised
about both its effectiveness and its possible toxicity over time.  A further dis-
advantage of chlorine is its high energy consumption,  especially in time of
energy shortages.  By laboratory studies, gamma radiation from radioactive
cobalt 60 has been demonstrated to be an effective disinfectant; it
cannot induce radioactivity or add to contaminants present.  A pilot plant in
Georgetown, Ontario was designed to test reactor efficiency, disinfecting
ability of radiation, reactor performance, effect on soluble organics,  and
toxicity effects.  Significant results on effectiveness of treatment and re-
production of an effluent non-toxic to fish were shown.  Costs of cobalt are
presently half the price of ten years ago.  This coupled with a lower energy
consumption as compared to chlorine, could make gamma radiation a viable al-
ternative as a waste water disinfectant.

*Gamma rays, *Cobalt radioisotopes, *Disinfection, *Chlorination, Chlorine,
Potable water, Water treatment, Laboratory tests, Energy, Contamination, Pilot
plants, Toxicity, Fish, Waste water treatment, Canada

*Gamma radiation, Cobalt 60, Laboratory studies, Energy consumption, Ontario
19 8D

BRANDON SEWAGE PLANT FEATURES NOVEL CLARIFIER,

Brandon, Manitoba, City Engineering

Water and Pollution Control, Vol. 112, No. 4, p 50-52, April, 1974.

Specific problems exist in cold regions such as Brandon, Manitoba, where biologi-
cal sewage treatment processes were difficult to maintain by conventional anaero-
bic lagoon methods.  The new treatment facility is essentially an extended
aeration plant, incorporating an aeration tank in which Penberthy jets are in-
stalled.  These produce a stream of water and air simultaneously, and react to
produce a fine bubble.  These jets promote complete mixing action and are not
prone to freezing, as the aerator is always submerged.  Using a pilot plant, it
was found that a completely-mixed system with effective clarification and sludge
return is a very efficient system; it should not be critically affected by
temperature variation, sludge quantity, or variation in oxygen content.  An ad-
ditional feature of the Brandon plant is a clarifier which removes settleable
solids.  This is done by a tube or set of tubes or a channel with flushing in
the direction of the flow with flushing water either directed to a separate
basin or returned to the original basin.  Essentially, 100 percent of the sludge
from the clarifier is returned to the aeration tank and eventually will be waste
into the lagoon system.  A full cycle of sewage treatment will consist of 24
hours of aeration, followed by clarification before discharge to a lagoon for
three weeks storage, then cascading down an open channel to re-absorb a maximum
oxygen before discharge to the river.

*Sewage treatment, *Biological treatment, *Aeration, *Anaerobic treatment, *Jets,
Lagoons, Treatment facilities, Pilot plants, Clarification, Oxygen, Solids,
Sludge, Temperature, Rivers, Bubbles, Canada, Cold regions

Settleable solids, Anaerobic lagoons, Aeration tanks, Penberthy jets, Brandon,
Manitoba, Fine bubbles


                                         323

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19 9D

FURTHER PURIFICATION OF BIOLOGICALLY TREATED WASTE WATER
TREATMENT PLANT EFFLUENTS BY MEANS OF MICROSTRAINERS (WEI-
TERREINIGUNG BIOLOGISCH BEHANDELTER KLAERANLAGENABLAEUFE MIT
HILFE VON MICROSTRAINERN) ,

Hanisch, B.

Gas-Wasser-Abwasser Vol. 54, No. 3, p 75-77, April, 1974.  6 fig.

The principle and the use of microstrainers for the reduction of the suspended
matter content in biologically purified effluents in waste water treatment
plants are described.  The microstrainer is composed of a horizontal, slowly
rotating drum covered by fine wire mesh serving as filter.  It emerges to two
thirds into the effluent which passes through it from the inside to the outside.
The suspended matter settling on the inside of the drum acts as an additional
filter.  The proliferation of Zooglea is prevented by UV irridation.  Experi-
ences from the practical use of microstrainers in connection with biological
waste water treatment plants and percolation bodies show that microstrainers are
able to retain up to 60 percent of the suspended matter content, and to reduce
the residual BOD content by about 50 percent.  While the suspended matter reten-
tion efficiency of microstrainers is lower than that of rapid sand filters, mi-
crostrainers are superior to the latter in terms of lower investment costs and
reduced susceptibility to great load variations.

*Water purification, *Waste water treatment, *Filtratlon, *Biological treatment,
*Equipment, Suspended solids, Retention, Biochemical oxygen demand, Ultraviolet
radiation, Filters, Costs

*Microstrainers, Treatment plants, Suspended matter, Germany
200D

WASTE TREATMENT:  UPGRADING METAL-FINISHING FACILITIES TO
REDUCE POLLUTION,

U. S. Environmental Protection Agency,
Washington, D.C.

Environmental Protection Agency, Technology Transfer, July, 1973.  27 p,
6 fig, 1 tab, 25 ref.

Metal processing in manufacturing includes a number of finishing steps
that improve and condition the surface for further processing for the
intended final purpose of an article.  Most of these finishing steps employ
wet processes and require rinsing steps.  Water pollution is caused by
the deliberate or accidental discharge of the processing solutions and
the contaminated rinse water.  In an activity centered around various pro-
cesses employing water as a solvent, it is evident that water pollution
problems will be encountered whenever an effluent is discharged.  The
severity of the pollution naturally will depend on the source of waste,
the type of process employed, the size of the installation, and the
relative concentration of the effluent.  These aspects as well as
commonly used waste treatment systems, economic considerations, metal
recovery, and process-solution regeneration and recovery are discussed.

*Waste treatment, Industrial wastes, Water pollution sources, Waste water
(pollution), Ion exchange, Reverse osmosis, Evaporation, Economics

*Treatment methods, Metal recovery, Metal processing
                                      329

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 201D

 ROYAL  SEND-OFF FOR  SEVERN  SCHEME,

 Surveyor, Vol. 142, No.  4245, p  30-31, October 19,  1973.   5  fig.

 The Severn  Scheme is  the largest undertaken by the  Bristol Waterworks
 Company  of  England  since its formation, and when completed will yield  a
 total  of 61 mgd.  For phase I of the scheme,  four vertical-spindle pumping
 units  were  installed  which deliver water  from the treated-water reservoir
 to the new  Puckelchurch  reservoir through a 46-inch diameter  steel trunk
 main.  Surge protection  is by means of a  conventional  small  surge
 vessel at the pumping station and an atmospheric feed  tank at  the highest
 intermediate point  of the main.  Phase II of  the scheme will  supply  an
 extra  12 mgd bringing the  combined Purton throughput to 61 mgd.

 *Water resources development, Water storage,  Pumping plants,  Future
 planning  (projected), Waterworks, Treatment  facilities,  Equipment

 Great  Britain
202D

THE LAND CAN BE RETURNED,

Water and Pollution Control, Vol. 112, No. 4, p 18-19, April, 1974.
1 tab, 4 ref.

Research at Guelph University in Ontario, Canada includes field trials
directly incorporating shredded garbage onto land alone, or in combina-
tion with sewage sludge and poultry manure, and the application of lime,
alum, and iron-precipitated sludges.  Corn corps were then planted.
Results in terms of corn yields and soil nitrate-nitrogen distribution
during the tests have been promising.  A general summary of the data shows:
a sludge application of 0.5 acre-inches was sufficient to produce 112
bu/acre corn; up to 30 percent of the total nitrogen applied as sewage
sludge remained in the cultivated soil layer as residual solids; zinc
levels were highest in treatment involving solid waste or poultry manure;
the greatest cadmium level found in the corn stover from the highest
application of milled refuse and sludge; maximum lead level in corn
grain was related to the treatment of milled refuse plus poultry manure;
and, levels of metals in crops of corn and rye after one application of
waste did not appear to reach toxic concentrations.

*Sewage sludge, *Waste disposal, Crop production, Farm management,
Nitrogen, Corn (field), Sludge treatment, Farm wastes, Solid wastes,
Zinc, Cadmium, Lead, Metals, On-site tests, Canada
                                         330

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203D

MAKING POLLUTION CONTROL EASIER:  PART 2 - WATER
TREATMENT & CONTROL,

Bacchetti, J. A.

General Electric Company, Environmental Protection
Operation, Schenectady, New York

Automation, Vol. 21, No. 5, p 56-60, May, 1974.  1 tab.

A brief description of the legal aspects cited from the Federal Water
Pollution Control Act, 1972 Amendment is given together with regulations
now being proposed and promulgated by the Environmental Protection Agency
to implement this water act.  Design criteria for treatment facilities
and methodology must be consistent with present and future regulations
always operating within specification and consistent with the daily
effluent standards specified in the permits.  Such criteria are explored
for the following potential pollutants:  heavy metals and other inorganics,
nutrients, and water flow regulation.

*Legal aspects, *Federal Water Pollution Control Act, Regulation, Design
criteria, Treatment facilities, Methodology, Heavy metals, Nutrients,
Flow control, Inorganic compounds, Environmental Protection Agency
 204D

 COSTS OF CONSTRUCTION OF PUBLICLY-OWNED WASTEWATER
 TREATMENT WORKS.   1973 'NEEDS'  SURVEY,

 U.S. Environmental Protection Agency, Washington, D.C.

 Report to the Congress,  Prepared Pursuant to Sections 205 and 516, Public
 Law 92-500,  1973.   14 p, 4 tab.

 In conformance with Section 516(b)  (2)  of the 1972 Act, the 1973 Survey
 asked local  authorities  to report the costs for construction of municipal
 treatment and collection facilities which were eligible for Federal fund-
 ing under the 1972 Act and the guidelines published by the Environmental
 Protection Agency  for construction  grants, and which met definitions and
 criteria established in  the survey  and  outlined herein.  Costs were re-
 ported for facilities in five categories, two for treatment and three for
 sewer systems.  The limitations  of  the  survey as well as survey results
 and possible allocation  formulae are presented.

 *Surveys, Construction  costs,  *Treatment facilities, *Sewers, Municipal
 wastes,  Federal Water Pollution  Control Act, Grants, Federal project policy,
 Cost allocation, Environmental  Protection Agency, Costs
                                            331

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20511

AUTOMATIC CONTROL OF AN ACTIVATED SLUDGE REACTOR,

Kiel, H. E., Sundstrom, D. W.

Connecticut University, Storrs, Connecticut,
Department of Chemical Engineering

Journal of the Water Pollution Control Federation, Vol. 46, No. 5, p 993-998,
May, 1974.  9 fig.

Biological reactors, and activated sludge reactors in particular, can be
difficult to control.  Part of the problem is in the long residence times (1
to 8 hr).  Other characteristics of these facilities that create difficulties
include:  nonlinear reaction kinetics; undefined mixing; autocatalytic nature
of the processes, and mixed nature of both substrate and bacteria.  To maintain
consistent water quality with biological treatment procedures it is important
to detect a change in the process as soon as possible by measuring input pro-
perties rather than waiting until the change becomes apparent in the output
stream.  A feed forward control system was constructed and demonstrated on a
pilot activated sludge reactor using primary effluent from a municipal
sewage treatment plant.  This control system can be used to both control air
and recycle solids rates to the reactor to compensate for increases in the
carbon level of the feed stream.  When the test system was operated at residence
times comparable to those of a municipal plant, the effluent concentration was
held constant when the return rate of recycle solids was controlled as a func-
tion of the input of the carbon level.  Lower conversion and residence times
produced unsatisfactory results.

*Waste water treatment, *Biological treatment, *Activated sludge, *Automatic
control, Monitoring, Treatment facilities, Pilot plants


*Connecticut
206D

ACTIVATED CARBON ADSORPTION OF PETROCHEMICALS,

Giusti, D. M. , Conway, R. A., and Lawson, C. T.

West Virginia University,
Morgantown, West Virginia,
Department of Civil Engineering

Journal Water Pollution Control Federation, Vol. 46, No. 5, p 947-965,
May, 1974.  10 fig, 5 tab, 46 ref.

Activated carbon adsorption is an advanced method for the removal of residual
organic compounds from waste water.  There are two stages of waste treatment
where the adsorption technique can be employed:  a tertiary treatment stage
for removing refractory organics after conventional secondary (biological)
treatment; or application at the source of the specific pollutant emission.
This study was conducted to test the adsorptive capacity of various carbons
under differing physico/chemical parameters.  Among the findings of the study
were:  when the molecular weight of the compounds increases, and as the
solubility, polarity and branching decrease, the adsorptive capacity of the
carbon increases in a predictable fashion; aromatics showed the greatest tendency
to be adsorbed; the adsorptive capacity of the various carbons was higher at
high pH values.  The following sequence of susceptibility to carbon adsorption
for straight chained hydrocarbons of 4 carbons or less was determined; from
most to least susceptible the sequence is:  undissociated organic acids
greater than aldehydes greater than esters greater than ketones greater than
alcohols greater than glycols.

*Activated carbon, *Adsorption, *Waste water treatment, *Tertiary treatment,
Aromatic compounds, Alcohols, Esters, Aldehydes, Organic acids, West Virginia

Ketones, Glycols


                                            332

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207D

AIR DIFFUSION UNIT,

Aberley, R. C., Ratray, G. B., and Dougas, P. P.

Caldwell Connell Engineers,
Melbourne, Australia

Journal of the Water Pollution Control Federation, Vol. 46, No. 5, p 895-910,
May, 1974.  18 fig, 3 tab, 11 ref.

A description of the design criteria, final design, and performance testing
of a prototype air diffusion unit and aeration system for an activated sludge
treatment facilities is given.  Seven different diffuser arrangements were
studied.  Results of testing showed that the initial assumption of complete
mixing was justified by the uniform DO levels at all sampling points for each
run.  Testing also showed that flat porous plates arranged in a closely spaced
pattern over the entire floor of an aeration tank produces a bubble and cir-
culation pattern resulting in very high oxygen transfer efficiencies (13-19
percent at a submergence of 15 ft).  This oxygen transfer efficiency greatly
increased at air flow rates of 40-50 cfm.  It was also discovered that sodium
metabisulphate is unsuitable for oxygen uptake tests.

*Aeration, *Diffusion, *Circulation, Activated sludge, Waste water treatment,
Design criteria, Design standards, Pilot plants, Efficiencies, On-site tests,
Performance

*Australia, *Air diffusion unit, *Aeration system
208D

WATER QUALITY AND TREATMENT OF DOMESTIC GROUNDWATER,

Gibb, J. P.

Illinois State Water Survey,
Urbana, Illinois

Circular 118, 1973.  17 p, 3 fig, 1 tab, 21 ref.

Each year the Illinois State Water Survey receives numerous requests from
individuals for advice on locating, developing, or treating home or farm water
supplies.  This report on water quality and treatment presents basic information
on water quality and treatment of domestic and farm groundwater supplies.  It
describes tests and practices that assure a safe sanitary water quality, and
discusses in detail the common minerals and natural gases that are of concern
to home water supplies in Illinois.  Described also are water treatment procedures
and equipment for disinfection, iron removal, softening, methane and hydrogen
sulfide gas removal, and their costs.

*Water quality, *Water treatment, *Groundwater, *Water supply, Costs, Domestic
water, Illinois, Agriculture, Tests, Disinfection, Methane, Sanitation, Water
softening

Iron removal, Hydrogen sulfide gas removal, Domestic groundwater supply
                                       333

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  20 9D

THE DEVELOPMENT OF A TEST FOR THE POTABILITY OF WATER
TREATED BY A DIRECT REUSE SYSTEM,

Christian, R. T.

Cincinnati University, Cincinnati, Ohio

National Technical Information Service Report No. AD-771 131, September, 1973.
27 p, 11 fig, 12 tab.

A test system was developed to determine the potability of direct reuse water.
The test system is composed of both a biological and chemical test.  Mammalian
cell culture is the technique employed in the biological test system.  The
cell culture system has been shown to be capable of distinguishing between direct
reuse waters which have received different degrees of treatment.   Cytotoxicity
of certain metals included in drinking water standards has been demonstrated.
The level at which such toxicity occurs is within an order ot magnitude of
the level specified in the standard.  An analytical laboratory for the analysis
of inorganic and organic contaminants in direct reuse water has been stablished.
Gas chromatography - mass spectroscopy analysis has identified five compounds
that ary present in reverse osmosis permeate of direct reuse water:  methanol,
ethanol, acetone, isopropanol, and acetic acid.  Several methods for precon-
centration of such waters were studied.  Promising techniques include adsorp-
tion and freeze concentration.  Included for study were group of mono- and
dihydroxy-substitute phenolic compounds - hydroquinone, xylenols and pyrogallol.
The report includes the plans for a bench scale water reuse system to supply
water for chemical and biological test systems and to determine the effective-
ness of the various unit processes.

*Water reuse, *Testing procedures, *Systems analysis, *Water treatment, *Potable
water, Treatment methods, Toxicity, Gas chromatography, Mass spectroscopy,
Chemical analysis, Concentration


*Direct reuse water, Biological testing, Chemical testing
210D

FILTER PRESS FOR SLUDGE TREATMENT,

Matsuno, Y., Nishi, K., Kawazoe,  S.,  and Uratsuka,  K.

Technical Review, Vol. 11, No. 1, p 49-60, February, 1974.   15 fig,  4 tab,
3 ref.

Products of dewatering equipment  now available include not  only the vacuum
press and centrifuges, but also the filter press.  The filter press appears to
be the most powerful in dewatering performance of these types of dewatering
equipment.  Demand for the filter press is due to the future Act of Water
Pollution Control which will prohibit the discarding into rivers of the sludge
produced in the course of treatment of both industrial and  municipal waters.
The Act will also prohibit discarding the sludge cake containing a large amount
of water (over 85 percent).  In addition, when sludge cake  is treated by
burning, the lower its water content, the lower the treating cost.  On the
basis of the technique developed  for the soy bean sauce press now under mass
production, the filter press was  developed.  It was planned to treat every
kind of sludge in order to get a  lower water content in the sludge cake.
Water content has been reduced to below 70 percent, a level previously unat-
tained by the other types of dewatering equipment.

*Dewatering, *Equipment, *Sludge  treatment, *Filters, *Water pollution control,
Rivers, Sludge, Vacuum, Industrial wastes, Municipal was.tes, Waste water
treatment, Water Pollution Control Act, Centrifuges, Municipal water

*Vacuum press, *Filter press, Sludge cake



                                        33 it

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211D

CHLORINATION EFFECTS ON ORGANIC CONSTITUENTS IN EFFLUENTS
FROM DOMESTIC SANITARY SEWAGE TREATMENT PLANTS,

Jolley, R. L.

Tennessee University

Oak Ridge National Laboratory Report No. ORNL-TM-4290, October, 1973.

Sensitive radioactive tracer monitoring was used to determine the effects of
chlorination in the chlorinated effluents by coupling chlorination by 36C1
radioactive tracer with separation by high-resolution anion-exchange chroma-
tography.  Chlorine-containing stable organic constituents are present after
chlorination of effluents from domestic sanitary sewage treatment plants.
Effects of these effluents on the receiving water ecosystems and upon mankind
need to be assessed.  Seventeen of these organic compounds were identified and
quantified at the 0.5 to 4.3 microgram/liter level; none had been so identified
previously.  Based on these results, it is roughly estimated that 1,000 tons
of chlorine in the form of stable chlorine-containing organic compounds are
discharged annually from sewage treatment plants to American waterways.

*Chlorination, *Monitoring, *Radioactive tracers, *Effluents, *0rganic com-
pounds, Discharge, Sewage treatment, Water pollution, Chromatography, Anion
exchange

Chlorine-containing organic compounds, Treatment plants, 36C1, Sensors,
Chlorination effects
 212D

 OPERATION  CONTROL PROCEDURES FOR THE ACTIVATED SLUDGE PROCESS,
 PART  I, OBSERVATIONS,

 West, A. W.

 National Field  Investigations  Center,
 Cincinnati, Ohio

 National Technical  Information Service  Report No.  PB-228  741, April,  1973.
 11  fig.

 Aeration tanks  and  final  clarifiers are described  and illustrated.   Informative
 physical characteristics  which help identify sludge  quality  and  process  are
 given.  Particular  clues  indicate  the type  of control adjustments needed to
 achieve optimum plant  performance.  Inferences from  these findings  supplement
 the results of  more specific control tests, which  dictate direction and
 magnitude  of  the essential  control adjustments.

 *Aeration, *Control systems, *Sludge, *Quality control, Analytical  techniques,
 Clarification

 *Aeration  tanks, Final clarifiers, Plant performance
                                        335

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213D

OPERATIONAL CONTROL PROCEDURES FOR THE ACTIVATED SLUDGE PROCESS,
PART II, CONTROL TESTS,

West, A. W.

National Field Investigations Center
Cincinnati, Ohio

National Technical Information Service Report No. PB-228 742, April, 1973.
3 fig.

Control tests reveal sludge quality, process status, and final effluent quality
at intervals throughout each 24-hour cycle.  By results of a settleometer, centri-
fuge, and final clarifier sludge blanket, calculations may be made for solids
distribution ratios between the aeration tanks and the final clarifiers, as
well as sludge detention time in the final clarifiers and other factors which
influence process performance.  By coordinating results of the full test
series—flow records, turbidity, and dissolved oxygen test data—one deter-
mines the return sludge flow, excess sludge wasting and air discharge rates
which are necessary to maintain or restore excellent final effluent quality.

*Control systems, *Quality control, *Centrifuge, *Sludge, Tests, Turbidity,
Dissolved oxygen, Discharge, Aeration, Measurement

*Final clarifier, *Calculations, *Final effluent quality, *Sludge blanket,
Sludge wasting, Aeration tanks, Settleometer
214D

FEASIBILITY OF OZONE DISINFECTION OF SECONDARY EFFLUENT,

Greening, E.

Illinois Institute for Environmental Quality

National Technical Information Service Report No. PB-228 524, January, 1974.
40 p, 10 fig, 13 tab, 33 ref.

The use of ozone in treating secondary waste water effluents was studied.
The use of ozone rather than chlorine for secondary disinfection has the
advantage in removal of viruses; ozone was shown to be more effective as a
viricide than chlorine.  Higher levels of ozone were required for disinfection
and reduction of the parameters measured in the study than previously expected.
Also, ozone-iron induced flotation was not as efficient as was expected.
Although ozone was a good viricide, its use as a disinfection method for
secondary treated effluents was not recommended for Illinois.

*0zone, *Secondary treatment, *Effluents, Waste water treatment, Chlorine,
Viruses, Flotation, Illinois

Ozone-iron induced flotation, Secondary effluents, Viricides
                                          336

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  215D

  COSTS OF DISSOLVED AIR FLOTATION THICKENING OF WASTE
  ACTIVATED SLUDGE AT MUNICIPAL SEWAGE TREATMENT PLANTS,

  McMichael, W. F.

  Environmental Protection Agency, National Environmental
  Research Agency, Cincinnati, Ohio,
  Advanced Waste Treatment Research Laboratory

  National Technical Information Services Report No. PB-226 582, February, 1974.
  9 p, 4 fig, 2 ref.

  Presented are estimated capital and operating costs and operation and main-
  tenance labor man hours.  These are associated with flotation thickening.
  Equipment supplied by Komline-Sanderson Engineering Corporation and Rex-Chain-
  belt Incorporated was used for cost analysis.  Capital costs were determined
  by loading rates, operating schedules, and excess capacity factors.  Operation
  and maintenance costs were made up principally of labor, electric power, and
  chemical (polymer price and dosage) costs.

  *Capital costs, *0peratlng costs, *0peratlon and maintenance, *Maintenance
  costs, Labor, Polymers, Electric power costs, Equipment

  Polymer dosage, Polymer costs, Komline-Sanderson Engineering Corporation,
  Rex-Chainbole Incorporated
216D

CHLORINE RESIDUALS IN TREATED EFFLUENTS,

Snoeyink, V. L.

Illinois Institute for Environmental Quality,
Chicago, Illinois

National Technical Information Service Report No. PB-227 268, August, 1973.
59 p 7 fig, 8 tab, 37 ref.

The occurrence and effect of residual chlorine in treated waste water effluents
was discussed.  A field study which Involved analysis of effluents from 20
waste water treatment plants In Central Illinois showed total chlorine
residuals ranging from 1 to 5 rag/liter.  Most of these plants discharged to
streams which have 7-day 10-year low flows of zero.   A study was made of the
rate of decay of residuals in receiving waters, and this rate proved to be
an important function of the type- of residual (free or combined) and the
amount of sunlight.  Free chlorine in secondary effluent exposed to bright
sunlight decayed most rapidly.  Chlorine residual can be eliminated by
chemical reduction of the residual either by sulfur compounds (S02, HS02,
S03) or activated carbon.

*Chlorine, *Effluents, *Waste water treatment, Treatment facilities,
Discharge, Decay, Sulfur compounds, Activated carbon, Waste water, Illinois,
Streams

*Zero discharge, Residual chlorines, Sunlight exposure, Treatment plants
                                           337

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217D

VACUUM DISTILLATION/VAPOR FILTRATION WATER RECOVERY,

Honegger, R. J., Remus, G. A., and Krug, E. K.

General American Transportation Corporation,
Niles, Illinois,
General American Research Division

Technical Report, CARD Project No. 1528, Contract No.  HAS 8-27467,  July,
1973.  104 p, 28 fig, 14 ref.

A vacuum distillation/vapor filtration (VD/VF) water recovery system was
designed, fabricated, and tested.  The system employs  vacuum distillation,
vapor-phase catalytic oxidation, and condensation as the basic processes for
recovering potable water from urine.  Both the evaporator and condenser utilize
a rotating impeller to create an artificial gravity for separation of liquid
and vapor in zero gravity.  Each impeller is driven through a magnetic coupling,
thus eliminating shaft seals.  A six-day performance test indicated good
system thermal efficiency.  Water recovered from urine was of good quality as
determined by selected analyses.  Daily analysis of recovered water were made.
Total organic carbon was less than 12 mg/liter, pff varied between 6.0 and 6.9,
turbidity was below one Jackstm Unit, and ammonia concentration was less than
1 mg/liter.

*Vacuum, *Filtration, *Water reuse, Oxidation, Evaporation, Condensation,
Equipment, Potable water, Tests, Analytical techniques, Organic carbon,
Ammonia, Distillation, Water quality, Turbidity

*Vacuum distillation, *Vapor filtration, pH, Water recovery, Zero gravity
  218D

  TUCSON TACKLES TWO PROBLEMS,

  Water and Wastes Engineering, Vol. 11, No. 5, p 66, May, 1974.

  A $1.5 million waste water reclamation plant, now being built by the city of
  Tucson, Arizona, will hopefully eliminate two problems for that city.  First,
  the new plant will help relieve the present overload on one of the main 10"
  sewer lines serving the rapidly growing southeast side of the city.  Secondly,
  it will provide irrigation water for the city's two golf courses.  Currently,
  irrigation water for these golf courses is purchased from the city water de-
  partment.  The new practice will be cheaper and will conserve 547.5 million
  gallons per year of precious groundwater supplies in this desert region.  A
  brief summary of the plant's operation and hardware is included.

  *Water reuse, *Waste water treatment, *Irrigation, *Municipalities, Costs,
  Efficiencies, Water Conservation, Arizona, Facilities
                                          338

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 219D

ANDOVER GIVES SHOT TO SUPPLY,

McQuade, R. E., Fuller, C. E.

Andover, Massachusetts
Public Works Department.

Water and Wastes Engineering, Vol. 11, No. 5, p 32-37, May, 1974.
11 fig.

Andover, Massachusetts recently completed construction of a new drinking
water filtration plant with an ultimate capacity of 24 mgd.  The plant cur-
rently draws water from Haggets Pond to supply the town's 24,000 residents
and commercial and industrial users.  In the future it is planned to augment
this supply by drawing water from the Merrimack River.  Included in the
report are the costs breakdown of building as well as basic design data,
equipment used in the plant, and estimated operating costs for 1974.

*Water treatment, *Municipal water, treatment facilities, *Design criteria,
*Costs, Filtration, Construction, Engineering, Water supply, Massachusetts

Public works
 220D

 PICKIHG THE BEST COAGULANT FOR THE JOB,

 Brodeur, T. P., Bauer, D. A.

 Daytona Beach, Florida, Water and Wastewater
 Plants

 Water and Wastes Engineering, Vol. 11, No. 5, p 52-55, May, 1974.  4 fig.

 The problem was raised as to which chemical is most cost-effective in coagula-
 tion application.  This article reports the findings of a study done to try to
 resolve this problem.  Alum has been used with great success by the municipali-
 ties of Daytona Beach, Florida for over 40 years.  This study was conducted not
 so much to find something better than alum as it was to alleviate some of the
 drawbacks of its use.  Typical problems with alum use are:  dry power causes
 handling problems; soluble alumina which carry through into the distribution
 system can cause fouling and dirty water; increased lime dosages are needed
 to counter the acidifying characteristics of alum; carryover of light floe
 reduces filter runs by formation of gelatinous layers on the bed; and sludge
 production with increased water flow causes crowding in the save-all tank and
 lagoons.  The study compared plant-scale applications of aluminum sulphate,
 activated silica, and a high molecular weight anionic polymer (Nalcolyte
 8174).

 *Coagulation, *Alum, *Costs, *Sludge, Waste water treatment, Silica, Florida,
 Filters

 Nalcolyte 8174, Daytona Beach, Florida
                                       339

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 221D

 NIAGARA FALLS WATER PLANT CONVERTS GRAVITY FILTERS
 HYDRAULICALLY,

 Water and Pollution Control, Vol. 112, No. 4, p  66-67, April,  1974.
 3  fig.

 Niagara Falls  (Ontario) sewage treatment plant of 16 rapid  gravity  filters  and
 maximum capacity of 40 million Imperial gallons  per day was having  its  output
 impeded by  a sluggish rate of filtration.  It was necessary to improve  this
 rate without sacrificing water quality.  Consulting engineers  recommended  that
 the 8 new filters in the expanded portion of the plant be operated  at 4 gal/
 sq ft/minute  (twice the original rate); the eight older filters be  operated
 at 1 gal/sq ft/minute; and each of the two settling tanks be operated at
 rates that would give comparable effluent quality.  The new filters were con-
 verted to the dual media type.  The dual media configuration gives  the  fol-
 lowing structure:  anthrafilt on top, a layer of sand below this, a layer  of
 gravel below the sand which is underlaid by the  draining system.  Unfortunately,
 in this case the anthrafilt was already in place and it was necessary to de-
 vise a way  of introducing the sand layer beneath the anthrafilt with minimum
 disturbance to the filter.  This was done by placing sand on top of the
 anthrafilt  and then using a backwash flow  (gradually increasing in  rate
 with time)  to fluidize the two media which then  sorted themselves properly
 with the sand ending up beneath the anthrafilt.

 *Filters, *Hydraulics, *Gravity, Water treatment facilities, Sand,  Gravel,
 Canada, Municipal water, Sewage treatment

 *Dual media filters, Niagara Falls, Anthrafilt system
222D

PROBLEMS ON POLLUTION AND WATER RESOURCES IN THE NEW YORK
CITY METROPOLITAN AREA,

Lang, M.

New York City,
Department of Water Resources

Hudson River Colloquium, Annals of the New York Academy of Sciences, Vol.
250, p 178-181, May 24, 1974.

The size and scope of New York's sewage treatment effort are discussed.  The
City has made substantial progress toward its goal of high-degree secondary
treatment.  Of the 1.5 billion gallons/day of sewage in the city, 75 percent
currently receivessecondary treatment.  The other 25 percent is discharged
untreated into the estuary, principally from the west side of Manhattan.  The
city has currently embarked on a program to construct two new treatment plants
and upgrade 12 existing ones, the cost of which is estimated to be $2.3 billion.
Plans for a storm water treatment plant on the shore of Jamaica Bay are dis-
cussed as well as a comprehensive ecological analysis and monitoring program
for the bay and parts of the estuary.  A more detailed breakdown of expendi-
tures on the basis of Federal, state, and local shares is also given.

*Waste water treatment, *Storm drains, *Storm water, *Ecosystems, Financing,
New York, Costs, Municipal wastes, Sewage treatment

*Ecological Analysis, *Ecological monitoring
                                    340

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 223D

 APPLICATION OF BIOLOGICAL FILTERS IN WATER TREATMENT
 SYSTEMS,

 Hurley, T. L., Bambenek, R. A.

 Chemtric, Incorporated

 Nasa Tech Brief, B73-10404, November, 1973.

 Regular bacteria filters tend to accumulate bacteria and, when nutrients
 become available the bacteria, increase exponentially, which increases the
 possibilities of a breakthrough.  Present effective lifetime of most filters
 is about 10 days.  If a bactericide is used to kill bacteria near the filter,
 the lifetime of the filters can be extended.  Silver chloride placed on or
 close to the barrier will kill the bacteria as they arrive.  Dead bacteria
 accumulate linearly rather than increasing exponentially and hence filter
 life can be extended to up to 30 days.

 *Bacteria, *Filters, *Bactericides, Equipment, Water treatment

 *Silver iodide, NASA
224D

FILTER AND CENTRIF GES FOR THE DEHYDRATION OF WASTE WATER
SLUDGES (FILTER HND ZENTRIFUGEN FUER DIE ENTWAESSERUNG
VON ABWASSERSCHLAEMMEN) ,

Rueb, F.

Wasser Luft und Betrieb, Vol. 18, (5/6), p 279-289, 1974.  9 fig.

Thin sludges left from various water purification processes must be thickened
for deposition in sanitary landfills or other kinds of disposal including
reuse.  This had frequently been accomplished by drying in drying beds.
Machines such as filter presses, drying drums, belt filter presses and sludge
centrifuges gained recent increasing interest.  Filter presses proved very
efficient with dewatering sludges from pickling stations or galvanizing
stations.  A special construction is the tower filter press comprising two
vertical filtering belts.  The thin sludge enters on top and proceeds down-
ward between the two belts which in the lower section exert a pressure of 1.8
to 2.5 bar.  The filter cake falls out at the bottom.  The tower filter press
combines hydrostatic and mechanical pressure.  The operating principles of
drum filters, the belt filter press and the centrifuge are reviewed and illus-
trations of these machines are given.

*Dehydration treatment facilities, *Filters, *Centrifugation, *Sludge,
Solid wastes, Waste water treatment

Germany
                                             341

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22.5D

PURIFICATION PLANT EUTIN, APPLICATION OF SIMULTANEOUS
PRECIPITATION FOR PHOSPHATE ELIMINATION, (KLAERANLAGE
EUTIN, ANDWENDUNG DER SIMULTANFAELLUNG ZUR PHOSPHAT-
ELIMINIERUNG,)

Mudrack, K. and Stobbe, G.

Wasser Luft und Betrieb, Vol. 18, No. 5/6, p 289-292, 1974.  4 fig, 2 tab, 2 ref.

In the city of Eutin, Germany, treating the sewerage of a population of over
17,800, waste water from a military caserne, a police training camp, and
the usual small trade, the possibilities of phosphate-elimination and of in-
fluencing the sludge index by addition of iron sulfate into the activation
basin were studied.  This was done both in the laboratory and in practical
operation of the cities mechanical-biological treatment plant.  Amounts of
16g Fe/cu m, 23g/cu m and 46g/cu m were added.  Phosphate elimination rates
of about 80 to 90 percent were achieved, leaving a residual concentration
of 2 to 5mg/liter of phosphate.  The sedimenting properties of the sludge
were improved and the volume of surplus sludge was reduced.  The purification
efficiency of the plant, as measured by BOD and KMn04 consumption, was im-
proved.

*Phosphates, *Precipitation, *Iron compounds, Sludge, Waste water treatment,
Efficiencies, Biochemical oxygen demand

*Simultaneous precipitation, *Iron sulphate, *Germany
22.6D

THE EFFECT OF SURPLUS ACTIVATED SLUDGE IN FILTER PRESS
PERFORMANCE,

Brade, C. E., and Sambidge, N. E. W.

Mansfield Sewage Works Manager, England

Water Pollution Control, Vol. 73, No. 2, p 138-149, 1974.  10 fig, 7 tab,
6 ref.

Experiments to press raw primary and humus sludge, raw mixed sludge which
contains surplus activated, digested mixed sludge, and elutriated digested
mixed sludge are recounted.  Test results led to the following conclusion:
raw primary/humus sludge was readily dewatered using batch conditioning
techniques; the poor cakes were due to aging after addition of the conditioner;
raw mixed sludge could be pressed more satisfactorily using an in-line con-
ditioning system when proportions of activated sludge were not high; and,
the mixed sludge, after digestion and elutriation, was easily pressed in a
short time and gave excellent cakes.

*Sludge treatment, *Dewatering, Activated sludge, Treatment facilities, Diges-
tion, Filters

*Filter press, Filter press cakes, Elutriation, Treatment methods, Great
Britain
                                           342

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227D

INVERSE SEPARATION OF HEAT-TREATED SLUDGE,

Rotsides, C., and Everett, J. G.

University  College, Department of Mechanical Engineering,
Cardiff, England

Water Pollution Control, Vol. 73, No. 2, p 210-213, 1974.  6 fig, 7 ref.

An examination of the problem of floating sludge was undertaken with experi-
ments showing that agitation and air entrainment of heat-treated sludge may
play a part in causing sludge to float.  It was found that the amount of
floating sludge is not influenced by either temperature or period of heat
treatment but that solids concentration does have a pronounced effect on the
settling of the sludge.  Continuous operation of the decanter also may in-
fluence sludge floating.

*Sludge treatment, *Heat treatment, Air entrainment, Temperature, Settling,
Laboratory  tests

*Floating sludge, Solids concentration
228D

THE EFFECT OF HEAT TREATMENT ON THE SOLUBILIZATION OF
HEAVY METALS, SOLIDS AND ORGANIC MATTER FROM DIGESTED
SLUDGE,

Everett, J. G.

University College, Department of Mechanical Engineering,
Cardiff, England

Water Pollution Control, Vol. 73, No. 2, p 207-209, 1974.  4 tab, 9 ref.

The effect of heat treatment on the solubility of five metals and other di-
gested sludge components has been investigated.  Nitrogen was found to be
more soluble than most sludge components and metals were found to be the
least soluble.  This has important implications for the use of the liquor as
an agricultural fertilizer.  The liquor solids averaged 12 percent of the
toxicity of the sludge.  For equal applications of nitrogen the liquor was
only six percent as toxic as the sludge.

*Heat treatment, *Sludge treatment, *Heavy metals, *Solubility, Effluents,
Nitrogen, Fertilizers, Organic matter, Zinc, Copper, Nickel, Chromium, Lead,
Sludge digestion, Solid wastes

Great Britain
                                      343

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  229D

  A STUDY OF CONDITIONING SEWAGE SLUDGES WITH LIME,

  Webb, L. J.

  D. Balfour and Sons, Consulting Engineers

  Water Pollution Control, Vol. 73, No. 2, p 192-206, 1974.  7 fig, 7 tab,
  12 ref.

  The following two project objectives were investigated with respect to lime
  treatment of sewage sludges:  to understand further the mechanism of lime
  conditioning of sewage sludges with a view to improvements in process effi-
  ciency and to compare various lime conditioning systems on a variety of sludge
  types.  It is shown that lime with copperas is the most effective conditioning
  system on typical examples of primary, digested, and activated sludges.
  There is a much larger variation in the liquid phase lime demand than in the
  solid phase demand.  And, the great efficiency of lime in conditioning pri-
  mary sludges is attributed to its interaction with the fat/grease content of
  the sludge.

  *Sludge treatment, *Sewage sludge, *Lime, Efficiencies, Investigations,
  Liquids, Solids

  *Lime conditioning, *Copperas
230D

THE SSP-BELT FILTER FOR THE DEHYDRATION OF COMMUNAL AND
INDUSTRIAL SEWAGE SLUDGES (DAS SSP-BANDFILTER KUR ENTWAS-
SERUNG KOMMUNALER UND INDUSTRIELLER SCHLAMME) ,

Emrath, E. E.

Wasser Luft Und Betrieb, Vol. 18, No. 3, p 154-157, 1974.  2 fig, 3 tab.

A new sludge dewatering machine is described, the SSP band filter, whose ini-
tials indicate the processes of sifting, suction and pressing, performed by
the band filter.  The arriving sludge is mixed intensely with flocculents.
Cationic flocculents usually lead to good results with most sludges, the mole-
cular weight and the amount of cationic substance being of major importance.
With certain industrial sludges the use of anionic flocculents brought better
results.  In stjme cases only the combination of two flocculents brings the
desired results.  The sludge which Has been mixed with the adequate flocculent
passes to the sifting band by way of a distributor.  The sifting band glides
over a perforated synthetic plate.  The mesh width of the sifting band should
match the size of the sludge flake.  The band proceeds with the sludge to the
sifting zone where the free water flows off.  In the suction zone a slight
vacuum prevails.  Here the sludge is dewatered to the extent that the sludge
layer contacting the band is dry while most of the fine water is removed from
the top layer.  In the following pressing zone the water from the sludge
surface is pressed out.  The throughput varies greatly and depends on the kind
of sludge to be dewatered.  If sodium perchlorite is to be added for deodoriza-
tion the flocculent consumption will rise.

^Dehydration, *Dewatering, *Sludge, *Equipment, Pressure, Industrial wastes,
Domestic wastes, Flocculents, Vacuum, Oil, Odors

*Band filter, Suction, Sifting, Sludge dewatering
                                          344

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  231D

SOURCE CONTROL KEY TO WASTE SYSTEM,

Chapman, W. A.

City of Palo Alto, California

Water and Wastes Engineering, Vol. 11, No. 3, p B-20-B-22, March, 1974.

The city of Palo Alto, California, considers source control to be the basis
of its program to treat industrial wastes.  Industrial disposal problems were
anticipated by the city, and an industrial waste treatment works was designed
and built at the waste water treatment plant.  Concentrated chemical wastes
and septic tank sludge will be transported by truck to this facility for
special treatment and disposal.  A questionnaire was sent to 68 businesses
in the area to ascertain monthly volumes of deleterious wastes they produce
and interest in a pick-up and disposal service.  On the basis of their response
the treatment plant was planned, and proposed rules were drafted.

Industrial wastes, *Municipal wastes, *Waste treatment, *Water pollution
sources, *Chemical treatment, Septic tanks, Waste disposal, Treatment facili-
ties, California, Planning

Treatment plants, Chemical wastes, Septic tank sludge
232D

POSSIBILITIES AND LIMITATIONS IN THE COMBINED PURIFICATION
OF DOMESTIC AND INDUSTRIAL WASTE WATERS (MOCGLICHKEITEN UND
GRENZEN DER GEMEINSAMEN REINIGUNG HAEUSLICHER UND GEWER-
BLICHER ABWAESSER),

Irhoff, K. R.

VDI-Berichte, No. 207, p 93-101, 1973.

Possibilities and limitations of the combined treatment of domestic and indus-
trial waste waters are discussed.  Joint treatment is economically motivated by
the fact that the specific costs of treatment sharply reduce with increasing
throughput capacities, especially up to 100,000 inhabitant equivalents.  The
combined treatment creates no particular problems provided that the industrial
waste waters are non-toxic and their share does not exceed 30 percent of the
total volume to be treated.  Most industrial waste waters require mechanical-
chemical pre-treatment, such as precipitation and neutralization prior to their
discharge into the municipal sewer system.  The addition of industrial waste
water is also essential for establishing the correct nutrient balance of the
waste water for efficient biological purification.  Waste waters that are too
concentrated should be treated anaerobically rather than by the aeration
method due to the limit capacity of the latter.  Special waste waters may
require two-stage biological purification with separate sludge systems and
different kinds of bacteria.  Examples demonstrating the combined purification
of domestic and pre-treated industrial waste waters are presented.

*Domestic wastes, *Industrial wastes, *Waste water treatment, *Costs, Pre-
treatment, Sewer systems, Nutrients, Aeration, Biological treatment, Chemical
treatment, Precipitation

Joint treatment (municipal/industrial)
                                         345

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 233D

 VACUUM FILTRATION EQUIPMENT INNOVATIONS,

 Bosley, R.

 Stockdale Engineering Limited,
 Bollington,  Macclesfield,  Cheshire

 Filtration and Separation,  Vol.  11,  No.  2,  p 138-148,  March/April,  1974.   31 ref.

 Recent developments were made in the design and  application of all  types  of
 vacuum filters.   Equipment  dealt with includes rotary  drum, rotary  disc,  ro-
 tary table,  rotary multi-tipping pan filters, single tipping pan, linear  belt
 and other cake filters.  Rotary  drum precoat, and  other media type  vacuum
 filters were described.  The cost and influence  on design of new materials of
 construction for vacuum filtration equipment is  reviewed.   The mechanical de-
 sign and features of very  large  vacuum filters (drum filters of 150 sq  m  and
 disc filters of  5 m diameter), and the development of  automatic control systems
 for vacuum filtration equipment, were considered.   The influence of improved
 mechanical  design features  on processing,  including cake washing, drying,
 discharge systems and filter cloth washing  techniques  is discussed.  New  pro-
 cess applications can now be economically handled  by vacuum filtration  because
 of wider range of equipment, improvements  in design, new materials  of construction,
 and new filter media.

 *Deslgn criteria, *Equipment, *Filters,  *Vacuum  drying,  Construction costs,
 Construction materials,  Drying,  Discharge

 *Vacuum filters, Cake washing, Filter media
234D

REMOVAL OF AMMONIA FROM RIVER WATER,

Short, C. S.

Water Research Association, Ferry Lane,
Medmenham, Marlow, Bucks,
Treatment Group

Water Services, Vol. 78, No. 937, p 81-85, March, 1974.  10 fig, 2 tab, 3 ref.

An evaluation of the performance and costs of ammonia removal processes was
undertaken by the Water Research Association (WRA) as part of research into
problems of river water quality.  Pilot-scale investigations of three promising
processes—biological sedimentation, biological filtration and air-stripping—
were carried out over a period of 18 months.  Capital and operating costs of
these processes and of breakpoint chlorination were estimated.  Biological
sedimentation was found to be effective and considerably cheaper than the
alternative processes.

*Costs, *Ammonia, *Capital costs, *0perating costs, Chlorination, Sedimentation,
Filtraton, Methodology

*Ammonia removal, *Water Research Association, Pilot investigations, Biological
filtration, Biological sedimentation, Breakpoint chlorination, Air-stripping
                                        346

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235D

DEEP BED AUTOMATIC CARBON FILTER IN OPERATION,

Koppers Company,
Pittsburgh, Pennsylvania,
Environmental Systems Division

Water and Sewage Works, Vol. 121, No. 4, p 40, April, 1974.

The town of Amesbury, Massachusetts has the first deep bed (48 inch media
depth) automatic backwash carbon filter (ABW).  This type of filter eliminates
costly time of maintenance and permits automatic cleaning of the filter media
without interrupting the water processing.  Filter media of either sand or
granular carbon are available; carbon controls tastes and odors better.  The
ABW filter bed operates in the following manner:  clean filtered water is
forced up through one cell, sweeping particulate matter into a hood which
is suspended from the automated carriage above the cell; washwater is discharged
to waste; as the carbon media is cleaned, the hood and carriage move to an
adjacent filter cell; and while one cell is being backwashed, the others contin-
ue to filter.

*Filters, *Automation, *Maintenance, *Costs, *Sand, *Carbon, Waste water treat-
ment, Filtration, Water purification, Carbon filters, Filtering systems

*Automatic backwash carbon filter (ABW), Backwashing, Filter media
236D

MALEIC RECOVERY PROCESS OFFERED BY UCB,

Chemical Age, Vol. 108, No. 2855, p 15, April 5, 1974.

The recycling of valuable wastes from treatment plants has economic advantages
over traditional disposal methods.  The UCB process in Brussels has tested pro-
duction plants for the recovery of maleic anhydride (MA) from effluent streams
of plants producing phthalic anhydride by the catalytic oxidation of naphthalene
or oxylene.  Maleic anhydride can be recovered as polyester grade product
or for use in processes such as the production of fumaric acid and maleic
esters.  In addition, products contained in the effluent stream from phthalic
anhydride production (phthalic anhydride, citraconic anhydride, benzoic acid,
or traces of maleic anhydride) can be separated off as anhydrous melt for
disposal by incineration.  Investment costs for the recovery are low and
the market value is attractive in view of rising benzene prices.

*Recycling, *Waste treatment, *Waste disposal, Effluents, Costs, Oxidation

*Maleic anhydride, *Benzene, *Polyesters, Investment costs
                                         347

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237D

SHORTAGES:  WATER POLLUTION CONTROL FACILITIES FACE THE
CRISIS,

Sliter, J. T., and Ward, P. S.

Journal of the Water Pollution Control Federation, Vol. 46, No. 4, p 616-622,
April, 1974.

Waste water treatment plants are faced with recent shortages of energy and
materials.  Uncertainty about delivery times for fuel and its availability
for running sludge incinerators has created crises in several areas of the
United States.  In addition, materials to build and operate the plants are
in demand, and costs are a particular problem.  This holds true for high
prices of not only oil and gas but also chlorine.  One remedy proposed for
fuel shortages is the use of methane gas generated by anaerobic digestion of
waste water sludge.  The concept of digester gas was used previously and has
already been instituted at several plants, at least as a supplementary re-
source.

*Waste water treatment, *Energy, *Fuel, *0il, *Chlorine, *Methane, Recycling
Costs, Materials, Sludge, Resources, Anaerobic digestion

*Digester gas, *Sludge gas, *Energy shortages, Treatment plants, Treatment
methods
238D

NEW DEVELOPMENTS IN FILTER PLATES AND FILTER PRESSES,

Cherry, G. B.

Fletcher Filtration Limited,
Mirifield, Yorks, Great Britain

Filtration and Separation, Vol. 11, No. 2, p 181-192, March/April, 1974.
3 fig.

The whole concept of filter press utilization has changed because of innova-
tive mechanical developments and a reduction in manual labor requirements.
Cleanliness of operation has been achieved by using rubber moulded plates with
a high degree of compressibility, and synthetic cloths sealed on the gasket
surface.  Good cake release properties without leakage have resulted as well.
The interaction of press plate size, cake thickness, dead time for opening,
closing, and cake removal and labor utilization were improved with the transi-
tion from manually to automatically operated plate and frame presses.

*Filters, *Filtering systems, *Automation, Labor, Equipment, Treatment
methods, Treatment facilities, Plastics

*Filter press, *Filter plates, Cake removal, Great Britain
                                        348

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239D

CATFIELD, LUDHAM, AND POTTER HEIGHAM SEWERAGE AND SEWAGE
PURIFICATION WORKS,

Whimster, K. W.

John Dosser and Partners, The Moors, Worcester, Great
Britain

Water Services, Vol. 78, No. 937, p 77-79, March, 1974.  5 fig.

A new sewerage and sewage purification system was opened which serves three
villages in the Norfolk Broads region of England.  The area needed this addi-
tional facility to accomodate a summer population of about 9000 visitors as
well as the residents.  The purification works are conventional in their treat-
ment methods, removing solid matter and oxidizing the liquid.  Solids are
disposed of on land and the liquid is discharged to the river.  Sludge is de-
watered by a rotating disc vacuum filtration plant and disposed of to farmers
or tipped.

*Sewage treatment, ^Treatment facilities, *Water purification, Waste disposal,
Solid wastes, Liquid wastes, Dewatering, Sludge

*Treatment plants, Great Britain, Vacuum filtration plant, Tipping
240D

RECOVERY OF HEAVY METALS FROM WASTE ACID (HAISAN KARA NO
JUKINZOKU NO KAISHU),

Matsumura, A., Matsuda, Y., Masuyama, K., Murakami, K.,
and Imamura, T.

Sumitomo Denki, No. 108, p 20-26, March 1974.  12 fig, 3 tab.

The treatment of waste acid containing heavy metals has posed a problem in Japan
even prior to the initiation of environmental control.  A method for treating
such acid waste has been investigated which permits the recovery of such
valuable metals as copper, nickel, and chromium.   Described is a process for
separating nickel and iron by stepwise neutralization and recovering this nickel
by electrolysis.

*Heavy metals, *Nickel, *Chemical wastes, Waste treatment,  Separation tech-
niques, Iron, Neutralization, Electrolysis, Copper, Chromium

*Japan
                                                 349

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241D

SLUDGE CHARACTERISTICS OF MUNICIPAL SOLIDS,

Kaplovsky, A. J., and Genetelli, E.

Rutgers University, College of Agriculture and Environ-
mental Science, Department of Environmental Sciences,
New Brunswick, New Jersey

In:  Proceedings of Conference on Land Disposal of Municipal Effluents and
Sludges, March 12-13, 1973, Rutgers University, New Brunswick, New Jersey,
p 3-18.  6 tab.

The practice of land disposal is analyzed historically emphasizing that the
degree of sophistication is dependent upon the local, social, and economic
conditions as well as the sludge characteristics.  The formation of sludge
from municipal wastes and solids handling are reviewed with the composition
of this sludge being calculated.  It is concluded that in light of existing
constituent composition found in waste sludges, the inherent concentration
variability and the many factors which must be considered for crop management
indicate that the true feasibility and economics of land disposal are largely
unanswered.  More specifically, the practices of ultimate disposal, its
management, and economic and social implications are directly or indirectly
related to the composition and character of the material requiring disposal.

*Sludge, *Sludge disposal, Landfills, Municipal wastes, Economics, Farm
management, Feasibility

*Sludge characteristics
242D

DISPOSAL AND REUSE OF SLUDGE AND SEWAGE:  WHAT ARE THE
OPTIONS?

Dean, R. B.

Environmental Protection Agency, National Environmental
Research Center, Advanced Waste Treatment Research Labora-
tory, Ultimate Disposal Research Program, Cincinnati,
Ohio

In:  Proceedings of Conference on Land Disposal of Municipal Effluents and
Sludges, March 12-13, 1973, Rutgers University, New Brunswick, New Jersey,
p 19-30.  1 fig, 1 tab, 8 ref.

Some of the properties and quantities of municipal waste solids are reviewed
briefly.  Sludge when applied to the land is discussed in general with regards
to water, organic matter, and inert minerals, and specifically nitrogen,
phosphorus, potassium, zinc, lime, heavy metals, and salts.

*Sludge disposal, Landfills, Water reclamation, Organic matter, Minerals,
Nitrogen, Phosphorus, Potassium, Zinc, Lime, Heavy metals, Salts

*Sludge characteristics
                                     350

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243D

SOILS AS SLUDGE ASSIMILATORS,

Evans, J.0.

U. S. Department of Agriculture, Forest Service, Washing-
ton, D. C., Division of Forest Environment Research

In:  Proceedings of Conference on Land Disposal of Municipal Effluents and
Sludges, March 12-13, 1973, Rutgers University, New Brunswick, New Jersey,
p 31-52.  1 tab, 10 ref.

General concepts concerning factors which determine the relative ability
of soils as sludge assimilators are presented.  Soil properties that facili-
tate sludge assimilation such as ion exchange capacity and buffer capacities,
soil filterability and microbial transformations, as well as various applica-
tion techniques are mentioned.  Physical factors relating to sludge assimi-
lation (sludge characteristics, physical soil characteristics, climatic,
biotic, and land influences, and loading rates), and the sludge chemical
analysis and soil chemistry, and micro- and macro-organisms are discussed.

*Soil chemical properties, *Soil physical properties, *Sludge, Soil disposal
fields, Soil microorganisms, Soil management, Soil investigations, Soils
244D

MODES OF TRANSPORTING AND APPLYING SLUDGE,

Bauer, W. J.

Bauer Engineering, Incorporated, Chicago, Illinois

In:  Proceedings of Conference on Land Disposal of Municipal Effluents and
Sludges, March 12-13, 1973, Rutgers University, New Brunswick, New Jersey,
P 53-66.  1 fig, 2 tab.

Alternative methods for dewatering, transporting, and applying sludges re-
sulting from treatment of municipal sewage are discussed.  Sludge characteris-
tics, costs of dewatering, and hydraulic characteristics are generalized.
Pipeline, truck, barge, and rail transportation systems are discussed.  Five
application methods are presented with the preferred being the plowing in of
a slurry fed continuously through a hose to a moving plow.  Illustrated are
various combinations of systems indicating their economic significance.

*Sludge disposal, *Application methods, Transportation, Dewatering,  Pipelines,
Barges, Roads, Railroads, Economics,  Comparative costs, Comparative benefits
                                            351

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24 5D

SOME CONSTRAINTS OF SPREADING SLUDGE ON CROPLAND,

Dotsoii, G. K.

Environmental Protection Agency, National Environmental
Research Center, Advanced Waste Treatment Research Laboratory,
Ultimate Disposal Research Program, Cincinnati, Ohio

In:  Proceedings of Conference on Land Disposal of Municipal Effluents and
Sludges, March 12-13, 1973, Rutgers, University, New Brunswick, New Jersey,
p 67-79.  15 ref.

The composition of sewage sludge is discussed emphasizing nitrogen, metals,
and pathogens.  The various aspects of soil nitrogen include mineralization,
digestion, denitrification, plant uptake, and runoff removal.  The fate of
heavy metals, trace elements toxicity, and the permissive levels of trace
elements also are reviewed.  Methods of pathogenic destruction are mentioned
as well as the application of sewage sludge to soil for crop production and/
or scil improvement.

*Sludge disposal, *Farm management, *Nitrogen, *Toxicity, Heavy metals, Trace
elements, Pathogenic bacteria, Sewage sludge, Application methods
24 6D

METHODS OF LIQUID FERTILIZER APPLICATION,

Lynam, B. T., and Carlson, R. 0.

Metropolitan Sanitary District of Greater Chicago,
Illinois

In:  Proceedings of Conference on Land Disposal of Municipal Effluents and
Sludges, March 12-13, 1973, Rutgers University, New Brunswick, New Jersey,
p 81-90a.  3 fig, 1 ref.

The Metropolitan Sanitary District of Greater Chicago, Illinois applies anaero-
bically digested sewage sludge to strip mine land to restore its organic matter
content and to supply plant nutrients for crop production.  The methods of
application used include:  a tank truck equipped with a manifold across the
rear end; various irrigation systems; and an incorporation method that is
being developed.  Each of the systems used is described briefly.

*Sewage sludge, *Sludge disposal, Organic matter, Crop production, Nutrients,
Irrigations systems, Fertilizers, Flood irrigation, Transportation, Appli-
cation methods

Chicago, Illinois
                                             352

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247D

EQUIPMENT FOR INCORPORATING SEWAGE SLUDGE AND ANIMAL
MANURES INTO THE SOIL,

Reed, C. H.

Rutgers University, Department of Biological and Agricul-
tural Engineering, New Brunswick, New Jersey

In:  Proceedings of Conference on Land Disposal of Municipal Effluents and
Sludges, March 12-13, 1973, Rutgers University, New Brunswick, New Jersey,
p 91-100a.  6 ref.

The incorporation of wastes directly into the soil is superior to surface
spreading because there is no odor, no opportunity for flies or other pests
to feed or breed, and no runoff or surface erosion of wastes.  Also, the wastes
are placed in the best possible media for immediate degradation to plant nu-
trients and utilization by plants.  The design of an effective land treatment
system and the selection of appropriate equipment necessitates the considera-
tion of many factors, some of which are outlined.  Presented are equipment
and devices used for such application techniques as the rldge-and-furrow
method, sub-sod-injection, and plow-furrow-cover.

*Equlpment, *Sewage sludge, *Sludge disposal, Farm wastes, Soil disposal
fields, Application equipment

*Land application
248D

SLUDGE DISPOSAL STUDIES AT BELTSVILLE,

Walker, J. M.

USDA, ARS, AEQI, Biological Wastes Management Laboratory,
Beltsville, Maryland

In:  Proceedings of Conference on Land Disposal of Municipal Effluents and
Sludges, March 12-13, 1973, Rutgers University, New Brunswick, New Jersey,
p 101-116.  2 fig, 3 tab.

Results of four different field studies and a number of laboratory studies on
the use of dewatered sewage sludge for soil improvement are highlighted.  The
primary concern has been with what limits the amount of sludge can be safely
applied to soils.  These limitations were grouped into categories:  short-term
limitations including the initial toxicity of sludges to plants, pathogen pre-
sence and survival, and excessive quantities of nitrogen; and, toxicity from
heavy metals such as zinc, cadmium, copper, and nickel.  The research goal
has been to use sewage sludge to improve soils at a reasonable cost, with
minimum hazard to health, and with minimum soil and water pollution.

*0n-slte tests, *Laboratory tests, *Sewage sludge, *Sludge disposal, *Soil
management, Crop production, Toxicity, Pathogenic bacteria, Nitrogen, Zinc,
Nickel, Cadmium, Copper, Soil disposal fields
                                       353

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249D

MERCHANDISING HEAT-DRIED SLUDGE,

Wilson, C. G.

Sewerage Commission, Milwaukee, Wisconsin

In:  Proceedings of Conference on Land Disposal of Municipal Effluents and
Sludges, March 12-13, 1973, Rutgers University, New Brunswick, New Jersey,
p 117-123.

Employing the activated method of municipal sewage disposal since 1920, the
city of Milwaukee, Wisconsin has used heat-dried sludge,  named Milorganite,
to help offset costs.  In merchandizing such sludge, the  following points
have been found important:   knowledge of what the byproduct can and cannot
do in growing plants; national market to balance seasonal and climatic vari-
ables; sales based on agronomic service; and, a strong distribution system.

*Sludge disposal, *Activated sludge,  *Byproducts

*Sludge merchandising, Milwaukee, Wisconsin
250D

OCEAN COUNTY SEWERAGE AUTHORITY WASTEWATER SOLIDS
UTILIZATION ON LAND DEMONSTRATION PROJECT,

Gritzuk, M.

Ocean County Sewerage Authority, New Jersey

In:  Proceedings of Conference on Land Disposal of Municipal Effluents and
Sludges, March 12-13, 1973, Rutgers University, New Brunswick, New Jersey,
p 125-132.  2 fig.

Ocean County, New Jersey will soon start construction of a sewerage system
that will produce about 25,000 dry tons of sludge annually.  A demonstration
project has been initiated to determine if sludge reuse is possible, economi-
cally feasible, and environmentally desirable for the County.  A description
of the following project aspects are outlined:  sludge characteristics for
reuse; project goals; project activities such as site selection, application
methods, hydrologic and geologic characteristics, soil conditions and vegeta-
tion, atmospheric and meteorological monitoring, loading rates, aesthetic
evaluation, and, a cost comparison.

*Pilot plants, *Sludge disposal, Application methods, Sites, Monitoring,
Comparative costs, Evaluation, Soil disposal fields, Sewage sludge

*0cean County, New Jersey
                                     354

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25 ID

EPA VIEWPOINT ON LAND APPLICATION OF LIQUID EFFLUENTS,

Trax, J. R.

Environmental Protection Agency, Office of Research and
Monitoring, Municipal Technology Branch, Treatment and
Control Optimization Section, Washington, D. C.

In:  Proceedings of Conference on Land Disposal of Municipal Effluents and
Sludges, March 12-13, 1973, Rutgers University, New Brunswick, New Jersey, p 133-
142.

For purposes of this paper, land treatment is intended to be used in its broad-
est context and confined to its use for treatment and renovation of municipal
waste water.  Land treatment can be divided into the following categories:
infiltration-percolation, cropland irrigation, spray-runoff, and solids bene-
faction.  Approximately 14 percent of the total budget for fiscal 1974 for
the Municipal Technology Research Program, or about $1.2 million, is planned
for development of land treatment technology which includes sludge application
to the land.  The philosophy behind the Program is outlined.

*Municipal wastes, *Latid management, Federal project policy, Irrigation systems,
Crop production, Infiltration, Overland flow, Application methods, Waste dis-
posal, Liquid wastes

Environmental Protection Agency, Opinions, Land application
25 2D

LAND TREATMENT AND ENVIRONMENTAL ALTERNATIVES,

Reid, B.

Project on Clean Water Natural Resources Defense Council

In:  Proceedings of Conference on Land Disposal of Municipal Effluents and
Sludges, March 12-13, 1973, Rutgers University, New Brunswick, New Jersey,
p 143-150.

Statistics and examples of problems of water pollution and its control are
presented as a general introductory statement emphasizing the need for zero
discharge of pollutants and proposing land disposal as a viable, natural alter-
native.  Land treatment is defined as a complex system which must be carefully
planned and engineered to assure that the rate of application of treated
waste water conforms to local climate so as not to overload the desired treat-
ment levels.  Questions are raised on the following four considerations of
land treatment:  performance; costs, in terms of capital, operations, outlays,
and returns or profits; political acceptance; and, public health.

*Water pollution control, *Land management, *Waste water treatment, Waste
disposal, Performance, Costs, Public health, Political aspects
                                      355

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253D

NEW YORK STATE'S VIEW OF LAND DISPOSAL,

Bogedain, F. 0.

New York State Department of Environmental Conservation,
Bureau of Municipal Wastes

In:  Proceedings of Conference on Land Disposal of Municipal Effluents and
Sludges, March 12-13, 1973, Rutgers University, New Brunswick, New Jersey, p 151-
164.  2 tab, 7 ref.

A history of the initiation and implementation of the land disposal method
for waste water is described briefly.  Municipal, industrial, and individual
system statistics are mentioned.   The following conclusions are drawn as re-
garding the State of New York and its position on land disposal.  Land disposal
is an established method of waste disposal, but is little used.  Numerous
problems can be encountered with this approach even when competent planning,
design, construction, and operation stages are not omitted.  More detailed
studies of the increasingly larger installations are needed to assist in
decisions involving the use of land disposal.

*Land management, *Waste disposal, Waste water treatment, *New York, Sewerage,
Research and development, Municipal wastes, Industrial wastes

Viewpoint, Land disposal
25AD

MUNICIPAL EFFLUENT CHARACTERISTICS,

Hunter, J. V.

Rutgers University, College of Agriculture and Environ-
mental Science, Department of Environmental Sciences,
New Brunswick, New Jersey

In:  Proceedings of Conference on Land Disposal of Municipal Effluents and
Sludges, March 12-13, 1973, Rutgers University, New Brunswick, New Jersey,
p 165-180.  9 tab, 16 ref.

The physical and chemical characteristics of secondary effluents are presented
with results of the following investigations statistically tabulated:  total
solids distributions for an activated sludge effluent, variation in effluent
quality of an activated sludge plant, organic parameter distributions for an
actual sludge effluent, chemical composition of soluble-colloidal organic
matter in a trickling filter effluent, composition of trickling filter efflu-
ent particulates, average inorganic composition of municipal secondary ef-
fluents, general composition of secondary treatment plant effluents, and
heavy metal constituents of secondary treatment plant effluents.  It is noted
that although there have been extensive investigations into the nature of the
organic constituents of effluents, most of the particulate organics are still
unknown and even the soluble organics have only been classified by solubility
and extractive procedures rather than by molecular species present.

*Municipal wastes, *Effluents, Investigations, Chemical properties, Physical
properties, Activated sludge, Organic matter,  Heavy metals, Inorganic com-
pounds

Waste characteristics
                                          356

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  255D

FATE OF MATERIALS APPLIED,

Thomas, R. E.

Environmental Protection Agency, Robert S. Kerr Environ-
mental Research Laboratory, National Water Quality Control
Research Program, Ada, Oklahoma

In:  Proceedings of Conference on Land Disposal of Municipal Effluents and
Sludges, March 12-13, 1973, Rutgers University, New Brunswick, New Jersey, p 181-
200.  15 ref.

The fate of suspended solids, major plant nutrients of environmental concern,
and other selected constituents of waste water when this waste water is applied
to the soil are summarized.  Methods of application include the crop irriga-
tion, infiltration, and spray-runoff approaches to waste water management.
An insight into the mechanism involved and the practical aspects involved in
the treatment or renovation of waste water by applying the waste water to the
land is presented.

*Suspended solids, *Nutrients, *Waste water treatment, Infiltration, Irriga-
tion systems, Land management, Waste disposal, Overland flow

Crop irrigation
   256D

   EXPERIENCES WITH LAND SPREADING OF MUNICIPAL EFFLUENTS,

   Thomas, R.  E., and Harlin, C. C., Jr.

   Environmental Protection Agency, Robert S. Kerr Water Re-
   search Center, National Water Quality  Control Research
   Program, Ada, Oklahoma

   In:  Proceedings of Conference on Land Disposal of Municipal Effluents and
   Sludges, March 12-13, 1973, Rutgers University, New Brunswick, New Jersey,
   p 211-225.   1 tab, 8 ref.

   The Environmental Protection Agency's  involvement in land spreading of munici-
   pal effluents for treatment and/or reuse is summarized.  Coverage of the many
   research projects introduced has been  limited and selective in order to high-
   light the objectives of this presentation.  The three areas of interest In-
   clude infiltration-percolation, cropland irrigation, and spray-runoff which
   have well-defined differences regarding land area requirements and the resul-
   ting interactions with the plant, soil, and water components of localized
   ecosystems.

   *Land management, *Municipal wastes, *Waste disposal, Waste water treatment,
   Waste water disposal, Water reuse, Irrigation systems, Soil-water-plant rela-
   tionships,  Research and development, Federal project policy, Overland flow

   *Envlronmental Protection Agency, Crop irrigation, Infiltration-percolation
                                          357

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257D

NATIONWIDE EXPERIENCES IN LAND TREATMENT,

Pound, C. E., and Crites, R. W.

Metcalf & Eddy, Incorporated, Palo Alto, California

In:  Proceedings of Confernece on Land Disposal of Municipal Effluents and
Sludges, March 12-13, 1973, Rutgers University, New Brunswick, New Jersey,
p 227-244.  1 fig, 6 tab, 21 ref.

The three basic modes of land application of waste water are crop irrigation,
overland flow or spray-runoff, and infiltration-percolation.  The methods are
presently being studied to determine the following project objectives:  key
parameters for design, effects on the environment, health and safety risks,
costs, and additional study areas.  Site and waste water characteristics are re-
viewed and general statistics are given for the three modes.  A detailed des-
cription including design, management, costs, and health aspects, is included
only for the crop irrigation systems.

*Waste water disposal, Waste water treatment, Overland flow, Investigations,
Design, Environmental effects, Costs, Administration, Public health, Safety,
Sites

Crop Irrigation, Infiltration-percolation, Site characteristics, Waste water
characteristics
258D

A SURVEY OF LAND APPLICATION OF WASTEWATER FACILITIES,

Sullivan, R. H.

American Public Works Association

In:  Proceedings of Conference on Land Disposal and Municipal Effluents and
Sludges, March 12-13, 1973, Rutgers University, New Brunswick, New Jersey,
p 245-261.

A field survey of 100 facilities where land application of domestic and indus-
trial waste water effluents was utilized gave the following results:  communi-
ties generally use their land application system on a continuous basis; ground
cover utilized for municipal systems is divided between grass and crops;
land application systems are generally used on a daily basis; and application
rates for crop irrigation are very low in terms of inches of water per week.
Many types of soils were used, with sand, loam, and silt being the most common.
Most operating agencies are planning to expand or continue their installations;
industries surveyed treat their total waste flow by land application; secondary
treatment is generally provided by municipalities prior to land application;
spray irrigation is the most frequently used method of application.  Land
use zoning for land application sites is predominantly classified as farming.
Waste water generally is transported to the application site by pressure lines;
many community land application facilities have been in use for several years,
more than hair over 15 years.  Renovated waste water is seldom collected by
underdrains.  Land application facilities do not make efforts to preclude pub-
lic access and water, soil uptake, and crop uptake monitoring is not carried
out with any consistency.

*Surveys, *Waste disposal fields, Municipal wastes, Industrial wastes, Land
management, Application methods, Soil types, Installations, Irrigation systems
                                      358

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259D

STUDY ON MECHANICAL SURFACE AERATOR,

Shiramasa, I.

Mitsui Zosen Giho (Mitsui Shipbuilding Technical Review), Vol. 85, p 61-66,
January, 1974.  9 fig.

Mechanical aerators have become widely used in the activated sludge process
due to their simplicity of design and construction and superiority in
oxygen transfer capacity per unit horsepower.  Hydraulic and oxygen-transfer
tests were conducted with the following results being obtained.  Oxygen
transfer efficiency is directly proportional to the horsepower, and oxygen
transfer capacity is approximately equivalent to 2.5 kg 02/kWH.  The shape
of the blade is very important in controlling oxygen transfer capacity
by change in the depth of its submergence.  Aerator speed must be between
3 and 6 m/sec at the extremity of the blade.  A baffle must be provided
for the aeration tank to prevent surging.  A change in the number of blades
plus a change in the depth of submergence results in a change in the oxygen
transfer coefficient.

*Aeration, *Equipment, *Activated sludge, Design criteria, Oxygen requirements,
Efficiencies

*Mechanical aerators, Oxygen transfer
260D

TREATMENT OF OILY WASTE WATER USING ACTIVATED CARBON,

Matsumoto, T., Inoue, M., Takeuchi, T., and Sugimoto, E.

Mitsui Zosen Giho (Mitsui Shipbuilding Technical Review), Vol. 85, p 1-10,
January, 1974.  14 fig, 1 tab, 6 ref.

Experiments were carried out on the treatment of oily waste water using
activated carbon with about 10 ppm oil at the inlet and less than 1 ppm
at the outlet of the fluidized bed adsorption column.  Results are
presented in mathematical formulas.

*Waste water treatment, *0ily water, *Activated carbon, Adsorption, Mathematical
studies
                                      369

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261D

VARENNES WATER PLANT PLANNED FOR EXPANSION,

Water and Pollution Control, Vol. 112, No. 5, p 16-17, May, 1974.

The city of Varennes, located on the south shore of the St. Lawrence River
opposite Montreal, Canada, has recently completed a major expansion of
its water supply facilities.  Designed with an initial capacity of 2.0 mgd
with provision for expansion to 6.0 mgd, the facility provides for flocculation,
sedimentation, plus rapid sand and anthracite filtration.  Built at a cost
of $1.25 million, the new plant also incorporates a laboratory equipped
with sample taps to analyze raw, mixed, flocculated, pre- and post-filtered,
and finished water.  Instrumentation and equipment includes a Zeta potential
meter, filterability plague, void pump, and turbidimeters.   Polyelectrolite
can be added to assist filtration.  Chlorine dioxide is used to help
remove occasional taste and odor.  Lime can be incorporated to correct
pH, and fluor is also available.

*>Tater supply, *Treatment facilities, Canada, Design criteria, Flocculation,
Sedimentation, Filtration, Construction costs, Instrumentation, Equipment,
Sand, Lime


Anthracite filtration, pH
262D

RECOVER ALUM TO REDUCE WASTE-DISPOSAL COSTS,

Fulton, G. P.

Metcalf and Eddy, New York, New York

Journal of the American Water Works Association, Vol. 66, No. 5, p 312-318,
May, 1974.  4 fig, 2 tab, 1 ref.

Alum is widely used in water treatment, but current investigations of
other coagulants to be used were held, due to the difficulty in disposing
of alum sludge.  A relatively easy, inexpensive method that makes possible
pre-treatment of alum sludge so that it can be dewatered and reused is
described.  This convertible alum-recovery process offers several advantages.
The aluminum hydroxide-raw-water suspended-matter wastes are relatively
easy to separate from the discharge carrier flow.  This leaves a supernatant
of good quality for recycling through the water plant.  Since an alternative
method of waste disposal is mandatory for any type of waste recycle, alum
recovery is the most economical to install and to operate.  The reduced
need for new or make-up alum decreases both delivery handling and delivery-
truck traffic.  In addition, the use of alum as a coagulant without affecting
well-established water treatment methods is retained.

*Aluminum, *Water treatment, *Sludge treatment, Dewaterlng, Recycling,
Waste disposal, Methodology, Costs, Treatment facilities, Equipment
                                          360

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   263D

WATER-TREATMENT-PLANT WASTES DISPOSAL - PART 1,

Westerhoff, G. P., and Daly, M. P.

Malcolm Plrnle, Incorporated, Consultant Environmental
Engineers, Paramus, New Jersey

Journal of the American Water Works Association, Vol. 66, No. 5, p 319-324,
May, 1974.  6 tab, 4 ref.

The Sturgeon Point Water Treatment Plant, located about 15 miles south of
Buffalo, New York, treats raw water from Lake Erie and is the principal
source of potable water for the Erie County Water Authority.  The water
authority presently serves about 426,100 persons and is constructing and
evaluating primary concentration facilities for achieving a zero discharge
of waste water to Lake Erie.  The first phase of the program was to con-
struct primary waste water-concentration facilities for interim lagooning
until the second phase could be designed and constructed.  Phase 1 facilities
included a 210 x 60-foot one-story waste water treatment building, two
holding basins, two 200 x 200 x 10-foot and one 150 x 200-foot earth lagoons,
three 40-foot-diameter clarifier-thickeners equipped with upflow clarifiers,
two 15.5-foot high x 7-foot-diameter sludge holding tanks, and various pumps,
piping, and valves for transferring the wastes between the various treatment
units.  These facilities are designed to achieve a degree of liquid-solids
separation.  The liquid phase of the waste water is returned to the plant
raw water; the solids are concentrated and stored in lagoons.

*Treatment facilities, *Waste water treatment, Construction, Equipment,
Design criteria, Filters, Sludge treatment, Investigations, Polyelectrolytes
                                                        Vol.  11,  No.  5,
 264D

BIODEGRADATION OF MIREX BY SEWAGE SLUDGE ORGANISMS,

Andrade, P. S. L., Jr., and Wheeler, W. B.

Florida University, Gainesville, Florida, Pesticide
Research Laboratory

Bulletin of Environmental Contamination and Toxicology,
p 415-416, May, 1974.  1 tab, 3 ref.

Uniformly labelled 14C-Mirex was incubated in the dark with 100 ml of
sewage sludge in 250 ml Erlenmeyer flasks under aerobic and anaerobic con-
ditions at 30 C.  Controls composed of 14C-Mirex in sterilized sludge were
maintained for both aerobic and anaerobic samples.  After 2.5 months of
incubation all samples were extracted.  The autoradiograms of the thin-
layer plates showed two distinct spots for the anaerobic samples but only
one spot for the aerobic samples and the controls.  The data indicate
that under experimental conditions sewage sludge microbes degrade Mirex
under anaerobic conditions.

*Microbial degradation, *Sewage sludge, Laboratory tests, Aerobic conditions,
Anaerobic conditions

*Mirex
                                           361

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265D

PACKAGE TYPE WASTE WATER TREATING APPARATUS,

Technical Review, Vol. 11, No. 1, p 83-84, February, 1974.  3 fig, 1 tab.

A package type apparatus can be widely used for effective treatment of waste
water by the chemical flotation method including the treatment of oily
wat€:r, that of waste water arising from the marine products processing
industry, and that of non-precipitating waste water containing suspended
solids.  For treating oily water, a coalescer is used for the primary
tres.tment behind which this apparatus is installed to be used for the
seccndary treatment to guarantee that the final oil content in the waste
water treated is below 1 ppm.  For other waste water treatment, the coales-
cer is not required.  Examples of the performance of this waste water
trea.tment apparatus against various kinds of waste water are tabulated.

*Equipment, *0ily water, *Waste water treatment, Flotation, Treatment
faci.lities, Performance
 266D

EMULSIFIED OILY WATER TREATING EQUIPMENT,

Technical Review, Vol. 11, No. 1, p 79-82, February, 1974.  6 fig, 3 tab.

Mitsubishi Heavy Industries has recently developed systems for treatment of
waste water contaminated with soluble cutting oil.  These systems have been
effectively utilized on practical scales, and are illustrated.  An outline
of t'ite systems for treating such waste water is provided.

*0ily water, *Waste water treatment, *Treatment facilities, Equipment
                                             362

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 267D

REVERSE OSMOSIS CUTS SOLIDS,

Burns, V. T., Jr.

Gibbs and Hill, New York, New York

Water and Wastes Engineering, Vol. 11, No. 5, p C-6 - C-12, May, 1974.  2 fig,
3 tab.

A new reverse osmosis unit with a capacity of 250 gpm is reducing total
dissolved solids while providing water to the Harrison Power Station near
Haywood, West Virginia.  The station consists of three 600 MW units with
steam design conditions at 3675 psig with reheat to 1000 F.  The primary
fuel is pulverized coal which is normally delivered by overland conveyor
from a nearby mine.  Water supply for make-up to recirculating cooling
systems is from the West Fork River.  Two natural draft towers serve  the
three units.  Water for make-up to the thermal cycle, potable use, fire
head tank, and filtered water for miscellaneous service is designed for
supply from an existing reservoir.  Emergency backup comes from the West
Fork River.  This emergency backup supply of 650 gpm is taken from the
36-inch pipelines providing make-up supply to cooling systems.

*Reverse osmosis, *Waste water treatment, Industrial water, Dissolved
solids, Treatment facilities, Water supply, Coal, Equipment
    268D

    STATE  OF  THE  ART-ACTIVATED  CARBON  TREATMENT  OF WASTEWATER,

    Suhr,  L.  G.,  and  Gulp,  G. L.

    CH2M/H111 Engineers,
    Reston, Virginia

    Water  and Sewage  Works, p 104-108,  110-112,  April  30,  1974.   3  fig,  6  tab,
    17  ref.

    Currently there are two approaches  for  the use of  granular activated carbon
    in  waste  water treatment.   One approach is to use  activated carbon in  a
    tertiary  treatment sequence following conventional primary and  biological
    secondary treatment.  Another approach  utilizes activated carbon in  a  physical-
    chemical  treatment (PCT) process in which raw waste water is  treated in a
    primary clarifier with  chemicals prior  to carbon adsorption.  Filtration
    and disinfection  also may be included in PCT, but  biological  processes are
    not used.  The PCT approach seeks  to make maximum  use  of granular activated
    carbon by extending its function of removing refractory dissolved organics
    to  adsorption of  biodegradable organics as well.   In some cases, the granular
    bed of carbon is  used as a  filter  to remove  suspended  and colloidal materials.
    The capabilities  of PCT must be evaluated in light of  specific  effluent
    quality requirements to determine  its applicability.

    *Waste water treatment, *Activated  carbon, *Tertiary treatment, Adsorption,
    Suspended solids, Waste treatment

    Physical-chemical treatment
                                            363

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 269D

 WASTE PLANT CORROSION MUST BE TREATED WITH CARE,

 Lopata, J. R., and Leutwiler, C.

 Carboline Company, St. Louis, Missouri, Pollution Control
 Division

 Water and Sewage Works, Vol. 121, No. 5, p 46-47,
 May, 1974.

 The protection of steel and concrete in waste treatment plants should be
 a matter of increasing concern to design engineers and operating personnel.
 These plants have been given the additional burden of processing highly
 corrosive industrial wastes previously directed into rivers and streams.  The
 South Charleston Waste Treatment Plant in West Virginia is an example of
 the advantages and long range economics of proper corrosion control planning
 and execution.  Most of the protective coating systems and tank linings used
 on steel in this new facility consist of modified phenolic, epoxy-amine, and
 epoxy-polyamide basins, submerged steel, interiors and exteriors of pipes,
 industrial clarifiers, steel in the aero-accelerator activated sludge
 basins, and floors of flumes.  After ten years of operation, complete repainting
 of the plant has never been necessary.  In some isolated areas the coatings
 that were damaged mechanically were spot repaired.

 *Treatment facilities, *Corrosion control, Protective coatings, *Linings,
 Industrial wastes, Waste  treatment, Repairing, Design criteria
270D

DESIGN FOR JOINT TREATMENT OF MUNICIPAL AND PAPER MILL
WASTE AT LYNCHEURG, VIRGINIA,

Clingenpeel, W. H., and Jones, M. K.

Wiley & Wilson, Incorporated, Enginerers-Architects-
planners, Lynchburg, Virginia, Environmental Department

Water and Sewage Works, p 12, 14, 18-19, 24-25, April 30, 1974.  3 fig, 6 ref.

In order to upgrade the existing primary treatment facility in Lynchburg,
Virginia to secondary treatment, the city was requested to consider joint
treatment with the Mead Corporation's Paperboard Plant.  In complying with
this request, the investigation of joint treatment of pulp and paper wastes
with municipal wastes involved the following:  a close evaluation of the
existing Lynchburg treatment facilities: a study of the Mead Corporation's
waste sources and characteristics; an investigation of joint treatment results
elsewhere.  Also included were: study of combined Mead and Lynchburg waste
treatability; the development of a joint treatment process concept; and, design
of the joint treatment facility.  The Lynchburg Project has demonstrated
that: in many instances municipal and industrial wastes are compatible for
joint treatment that is mutually beneficial.

*Treatment facilities, *Design criteria, *Sewage treatment, Pulp wastes,
Municipal wastes, Pulp and paper industry, Investigations

Joint municipal-industrial waste treatment
                                             364

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271D

A SLUDGE CAKE INCINERATION PROCESS AND AIR POLLUTION
CONTROL SYSTEM,

Cho, P.

Environmental Protection Agency, Region V, Chicago,
Illinois, Surveillance and Analysis Division, Air
Surveillance Branch, Air Data and Analysis Section

Water and Sewage Works, p 76-80, April 30, 1974.  2 fig, 4 tab, 4 ref.

A study was completed in 1970 on basic design data for the proposed Secondary
Treatment Facilities for Fort Southworth Sewage Treatment Plant in Kentucky.
The proposed facility was designed to provide for a minimum BODS removal of
90 percent and to effect comparable suspended solids removal and peak flow
disinfection.  The following design alternative was accepted by the City of
Louisville and Jefferson County:  five trains of oxygenation tanks designed
to operate with pure oxygen generated by on-site units; twenty final settling
tanks with 14-foot SWD; a return sludge pumping station; chlorination facilities
and chlorine contact tanks; a final effluent pumping station; and a building
containing sludge thickener tanks, sludge vacuum filters, chemical handling
facilities, and three multiple hearth incinerators; and, miscellaneous
structures and facilities.   The sludge treatment phase using the Zimpro wet
air oxidation units as well as computer simulation techniques employed are
described.

*Design criteria, *Sewage treatment, *Treatment facilities, Equipment, Biochemical
oxygen demand, Suspended solids, Sludge treatment, Simulation analysis,
Computers, Incineration


*Sludge cakes, Air pollution control
272D

TRICKLING FILTER VERSUS ACTIVATED SLUDGE:  WHEN TO
SELECT EACH PROCESS,

Kincannon, D. F., and Sherrard, J. H.

Oklahoma State University, (School of Civil Engineering)
Stillwater, Oklahoma

Water and Sewage Works, p 32-34, 36, April 30, 197.4.  1 fig, 4 tab, 9 ref.

Secondary treatment of waste waters containing biodegradable organic matter
usually requires a choice between the trickling filter process and the
activated sludge process.  An attempt has been made to offer a reasonable
basis for comparison of these two biological processes.  To accomplish this
objective, a comparison of process similarities and differences is presented,
a discussion of process modifications is made, and a criteria for process
selection established.  Results indicate that if activated sludge and trickling
processes are compared on an equitable basis, effluent quality and operational
characteristics are similar.  Therefore, a rational selection procedure should
be based on desired treatment objectives and then on economic and operational
considerations.

*Sewage treatment, *Waste water treatment, *Trickling filters, *Activated
sludge, Biological treatment, Comparative analysis, Effluents, Operation and
maintenance, Performance, Methodology
                                            365

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273D

FE WASTES HELP REMOVE PHOSPHATES,

Canadian Chemical Processing, Vol. 58, No. 5, p 44-46, May, 1974.  3 fig.

Environment Canada sponsored a study on available waste products that could
be used for phosphate removal.  Results indicate that both carbide lime and
pickle liquor, or heptahydrate crystals, consistently removed phosphates
from sewage plant effluent, and at doses matching commercial iron and lime
coagulants.  Meanwhile, the Canada Centre for Inland Waters located in
Burlington, Ontario, set up a joint venture with three Ontario municipalities
which house metal processors with waste pickle liquor.  For the cost of
haula.ge, the liquor was taken to the town sewage plant where it was mixed with
secondary effluent.  Results to date are e-ncotiraging.  Currently li-me, ferric.
chloride, and alum are the main coagulants for use in phosphate removal.
Lime has produced worker opposition at sewage plants and is limited by pH
specifications on released water.  The Fe and Al salts generally are preferred
with iron winning most of the new business.  Cost of the materials are
computed.

*Waste treatment, *Phosphates, *Industrial wastes, Coagulation, Iron, Aluminum,
Costs, Canada, Lime


Phosphate Removal
 274D

 ADSORPTION-BIOOXIDATION PROCESS FOR REMOVAL OF ORGANIC
 AND NITROGENOUS  COMPOUNDS FROM WASTEWATERS,

 Besik, F.

 Ontario Research Foundation, Ontario, Canada,
 Department of Applied Chemistry

 Water and Pollution Control, Vol. 112, No. 6, p  24-29,  37-39, June,  1974.   5
 fig, 1 tab.

 Results of the Ninth Canadian Symposium on Water Pollution Research  are presented
 with an explanation of a new process for treatment of domestic and municipal
 waste waters.  This method removes suspended and dissolved organic and
 nitrogenous compounds from waste waters in one stage without addition of
 chemicals or an external source of energy.  The process was tested on a pilot
 scale: with sewage  flow rates from 7000 to 10,000 GPD.   The name of this process
 is Acsorption-Biooxidatlon or A-B and refers to action whereby the activated
 carbon is not consumed and does not require external reactivation.   The flowsheet
 is described and allowed a 96-day virtually unattended  and maintenance-free
 operation.  Except for ammonia, all contaminants were efficiently removed  from
 the start up of  the plant.  Ammonia was efficiently removed after 10 to 14
 days of system operation.  Applications of the A-B process are in water
 renovation and reclamation, particularly for the design of small to  medium
 sized package systems.

 *Waste water treatment, *Municipal waste waters, *0rganic compounds, *Nitrogenous
 compounds, Adsorption, Canada, Contaminants, Ammonia, Energy, Activated carbon,
 Flow, Pilot plants, Water reclamation

 *Adsorption-Biooxidation process, Sewage flow rates
                                             366

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  275D

  CYANIDE  DISPOSAL  BY  OZONE  OXIDATION,

  Garrison,  R.  L.,  Mauk,  C.  E.,  and  Prengle,  H.  W.

  Houston  Research,  Incorporated,
  Houston, Texas

  N.T.I.S. Report No.  AD-775 152,  99 p,  33  fig,  7  tab,  10 ref.

  Aqueous  cyanide and  complex metal  cyanide wastes  from the Air Force's  routine
  electroplating operations  and  color photographic  film processing reauire extensive
  treatment  to  satisfy stringent water quality standards.   No proven process
  existed  which was  effective for  the complete destruction of total cyanide
  influent as high  as  100,000 mg/liter,  or  below one  mg/liter,  to  produce  an
  effluent with total  cyanide below  the  limit of detection.  A process was
  developed  by  laboratory experimentation.  This used ozone for the total
  destruction of cyanide  and metal cyanide  complexes.   It was found that the
  destruction of concentrated cyanide was limited by  mass  transfer of ozone from
  the gas  to liquid  phase, and the destrction of dilute cyanide was limited by
  the chemical  reaction rate. Mass  transfer  and kinetic rate constants  were
  determined by experimentation.  It was found that ozone alone reacted  with  the
  iron  cyanide  complexes  (found  in all photographic and electroplating wastes)
  much  too slowly for  practical  application,  but ozone  at  slightly elevated
  temperature in the liquid  became much  more  effective, and ozone  with
  ultraviolet light  became effective enough to permit the design of a successful
  system.  Using the laboratory  data, a  pilot scale prototype was  designed,
  fabricated, and operated to destroy actual  Air Force  cyanide wastes.   A
  conceptual design  of a  full scale  system  to treat electroplating waste is included.

  *0zone,  *0xidation,  *Waste disposal, *Waste treatment, *Water quality  standards,
  Pilot  plants, Laboratory data, Mass transfer,  Temperature

  *Cyanide disposal, *Metal  wastes,  Electroplating, Iron cyanite,  Photographic
  wastes,  Ultraviolet  light
276D

FLUORIDATION ENGINEERING MANUAL,

Bellack, E.

Environmental Protection Agency, Washington, D. C., Office
of Water Programs

N.T.I.S. Report No. PB 228 371, 94 p., 19 fig, 6 tab, 55 ref.

Quality of fluoridation of water supplies is dependent upon proper use of the
facilities and the organization of the water plant.  Accurate feed rates, choice
of chemical, and choice of equipment are equally important.  In this manual
are described compounds used in controlled fluoridation, feeders used for adding
fluorides, preparation of fluoride solutions, selection of the optimal fluori-
dation system, and control and surveillance methods.  In addition, maintenance,
safety and hazards in handling fluoride chemicals, and the technical problems
attributed to fluoridation are discussed.

*Fluoridation, *Water supply, *Treatment facilities, *Equipment, *Manuals,
Chemicals, Design criteria, Maintenance, Safety

*Fluoride chemicals, Fluoride engineering
                                           367

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277D

LAKD DISPOSAL...WHAT'S THE REALISTIC VIEW?

Michel, H. L., Gilbert, P. H., and Creed, H. K.

Parsons Brinckerhoff Quade and Douglas,
New York

Water and Wastes Engineering, Vol. 11, No. 6, p 30-35, June, 1974.  6 tab.

One. of the first comprehensive study programs in the field of land application
has been completed with facts emerging to offer a much clearer outline of the
concept.  The study area for this program encompassed the 12-county San
Francisco Bay-Delta Area of California,  approximately 10,000 square miles.
The application areas were to be drawn from the 12-county study area and from an
additional 27 counties in the central portion of California.  To approach the
problem five broad areas were explored:   site selection, process effectiveness,
benefits, environmental impact and unknown problems, and implementation and
costs.  Results of these investigated topics are disclosed.

*Investigations, *Land management, Waste water treatment, *Waste disposal,
Sites, Landfills, Performance, Cost-benefit analysis, Environmental effects


*Ls.nd application
27SD

ENIi-OF-PIPE TREATMENT AND DISPOSAL DOMINATE CONFERENCE,

Tappi, Vol. 57, No. 6, p 22-24, June, 1974.

The 1974 Environmental Conference held in New Orleans, Louisiana drew a record
attendance of over 400 delegates.  Reports included alternates for capture
and disposal of pollutants for air emission control, color reduction,
biotreatment, sludge disposal, and local environment impact.  Only two of the
twenty technical papers dealt in a direct manner with in-plant water reuse
and recycle.  The main theme of this conference was the disposal of the
residues which cannot be eliminated by in-plant methods.

*Conferences, *Environmental effects, *Waste disposal, Water reuse, Recycling,
Biological treatment, Reverse osmosis, Sludge disposal, Pollution abatement

New Orleans, Louisiana
                                            368

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279D

WASTEWATER SYSTEM ALTERNATES:  WHAT ARE THEY. . .AND
WHAT COST?

Monti, R. P., and Sllbermann, P. T.

Anderson Nichols and Company, Environmental Sciences
Division, Water Quality Management Group,
Boston, Massachusetts

Water and Wastes Engineering, Vol. 11, No. 6, p 52-56, June, 1974.  3 fig.
2 tab.

Because the increment of inorganic ions added to waste water during average
use is much higher than background levels of these constituents in water, an
additional demineralization process is required beyond the advanced treatment
scheme.  The ion exchange process is from 85 to 95 percent efficient but
generates a considerable quantity of waste brines which pose a disposal
problem.  Distillation has always been and is currently a prohibitively
expensive operation.  Presently reverse osmosis (RO) can efficiently
remove 85 to 90 percent of dissolved minerals in waste water with conversion
ratios of 80 percent.  The RO process has the advantage of being able to
tolerate higher organic wastes water loadings than ion exchange without
experiencing operating problems.  It is stressed that because RO is relatively
new, it is almost certain that operation will become more efficient and costs
will decrease as time goes on.  The capital and operating costs for RO
treatment of highly treated effluent and the total costs for RO applied to a
biological waste water treatment plant with ozonation are summarized.

*Waste water treatment, *Reverse osmosis, *Demineralization, Operating costs,
Capital costs, Project planning, Inorganic compounds, Treatment facilities,
Biological treatment
 280D

ELECTROKINETIC AND CHEMICAL ASPECTS OF WATER
FILTRATION,

Wnek, W.

IIT Research Institute,
Chicago, Illinois

Filtration and Separation, Vol. 11, No. 3, p 237-238, 240-242, May/June, 1974.
3 fig, 54 ref.

The role of electrokinetic and chemical phenomena in liquid filtration,
particularly water filtration, is discussed in terms of colloid chemistry.
The effects of surfactants, pH, and ionic strength on filter efficiency
are explained.  These provide a basis for selecting conditions which
enhance operation.

*Filtration, *Colloids, Physical properties, Chemical properties, Zeta
potential, Hydrogen ion concentration, Surfactants, Ions, Efficiencies

pH
                                                 369

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IILTRAPURE WATER AND REVERSE OSMOSIS TECHNOLOGY,

Kohout, R.

Microsystems International Limited,
Ottawa, Canada

Solid State Technology, Vol. 17, No. 6, p 60-65, June, 1974.  4 fig, 2 tab,
14 ref.

The new concept of treatment plants incorporating the reverse osmosis process
has proved to be capable of producing water of greater purity.  Evaluated are
the attributes of the new technology, the problem areas experienced in the
field, and the contribution of reverse osmosis to the state-of-art in
production of high-purity water.  Operating results of two water treatment
systems representing the two technologies (classical and RO) are compared
product water purity and its effect on fabrication of various generations of
semiconductor devices.  It is suggested that the old concept of what constitutes
ultrapure water may have to be reinvestigated in the era of LSI devices.

*Reverse osmosis, *Water purification, Evaluation, Reviews, Treatment
facilities, Operations, Performance, Coagulation, Filtration, Ion exchange,
Water treatment

*Semiconductor devices
 282D

 STUDY OF THE WATER PURIFICATION BY MEANS OF ELECTROLYZER WITH
 ALUMINUM ANODE  (ISSLEDOVANIYE PROTSESSA OCHISTKI VODY V ELEKTROLIZERE
 S ALYUMINIYEVYM ANODOM) ,

 Strokach, P. P., Slipchenko, V. A., Kul'skiy, L. A., and
 Belaya, V. P.

 Bilektronnaya Obrabotka  Metallov, No. 4, p 41-45, 1973.  3 fig, 3 tab, 16 ref.

 The physicochemical, electrical and hydrodynamic factors influencing the
 efficiency of the electrocoagulation method of water purification in the
 removal of silicon, iron, and oxygen from water were studied in laboratory
 experiments, using aluminum anode.  The optimum pH values for the removal
 of silicon and  iron, as well as phytoplankton and suspended matter were found
 to be 6.5-9, 8.2 and over, and 4-7, respectively.  Finely dispersed clay
 particles increased the purification efficiency, while humus matter interfered
 with the purification.  The increase of the water flow rate in the electrode
 zone from 1.6 to 70 m/sec had practically no effect on the efficiency of the
 removal of silicon and  iron, and the efficiency was largely determined by the
 quantity of the aluminum hydroxide available for adsorption.  The increase in
 the flow rate decreased the efficiency of oxygen removal.  Increased current
 density resulted in reduced efficiency of iron and silicon removal, and in
 slight increase in the  efficiency for oxygen removal.  The optimum values
 of the current  density  and of the electrode potential were found to be
 1-2 mA./sq cm and 2.5-4  V, under which conditions economical removal of
 pollutants, such as silicon, iron, coloring contaminants, suspended matter,
 phytoplankton,  and oxygen was possible at an efficiency of 60-80 percent.
 (Takacs-FIRL)

 *Water purification, *Aluminum, Flow rate, Pollutants, Iron, Suspended solids,
 phytoplankton

 *Electrocoagulation, *Electrolyzers, Oxygen removal
                                         370

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283D

STABILIZATION OF HIGHLY CONCENTRATED ORGANIC WASTE WATERS AND
SEWAGE SLUDGES BY AEROBIC-THERMOPHILIC DECOMPOSITION PROCESSES
(STABILISIERUNG HOCHKONZENTRIERTER ORGANISCHER ABWAESSER UNO
ABWASSERSCHLAEMME DURCH AEROB-THERMOPHILE ABBAUPROZESSE) ,

Loll, U.

Gas-Wasser-Fach - Wasser/Abwasser, Vol. 115, No. 4, p 191-198, April,  1974.
10 fig, 4 tab, 15 ref.

The stabilization of highly concentrated organic waste waters and sewage
sludges with BODS values ranging from 8,000 to over 100,000 mg/liter by
aerobic-thermophilic decomposition was studied.  Exothermal stabilization
of highly concentrated organic waste waters and sludges was found possible
by aerobic-thermophilic treatment for which the necessary energy is
supplied by the aerobic microorganisms participating in the metabolic
processes.  The process temperature is spontaneously stabilized over 45 C.
The quantity of heat released amounts to 3.5 kcal per one g COD.  Of the
identified microorganisms participating in the stabilization process,
Bacillus stearothermophilus, Bacillus coagulants and related bacilli are
dominant.  The magnitude of the rise in temperature above the initial
substrate temperature increases with increasing initial BODS value and with
increasing rates of decomposition.  The pH value tends to end values of
8.7-9.5 by the end of the stabilization process that requires 2.5-7 days.


*Thermophilic bacteria, *Sewage sludge, *Aerobic treatment, *Microorganisms,
Temperature, Stabilization, Biochemical oxygen demand, Chemical oxygen
demand, Waste water treatment

*pH, *Aerobic-thermophilic decomposition
 284D
 SECURITY MEASURES  AGAINST  PRESSURE SURGE FOR THE  CLEANED  WATER
 OUTLET RUHLEBEN-TELTOWCANAL  OF THE BERLIN SEWAGE  PURIFICATION
 PLANT (DRUCKSTOSSSICHERUNGSMASSNAHMEN FUER DIE  KLARWASSER-
 ABFLUSSLEITUNG RUHLEBEN-TELTOWKANAL DER BERLINER  ENTWAESSERUNGS-
 WERKE),

 Franke,  P.

 Wasserwirtschaft,  Vol.  64, No.  6,  p 174-181,  1974.   8  fig,  3 refs.

 The  outlet  system  and  the  water hammer of the 15  km  long  cleaned water outlet
 Ruhleben-Teltowkanal of the  Berlin sewage purification plant was investigated
 under transient conditions to  determine adequate  security measures against
 pressure surge.  The security  measures should be  designed for the outflow
 of all pumps  in the discharge  line.   As security  measures against water
 hammer,  either an  increase of  the  mass of the rotating system, an air chamber,
 or a surge  tank are possible.   Each of these measures was computed and
 compared.   Because of  specific local conditions,  a surge  tank installed
 at the outlet system of the  sewage purification plant was chosen as  the best
 solution.   Trial runs  have shown that the surge tank prevents the water
 pressure from exceeding the  rated  pressure of the discharge line and from
 falling  below the  atmospheric  pressure.

 *Sewage  treatment, *Water  purification, *Pressure, *Surges, Surge tank,
 Pump,  Outlet  works, Discharge,  Atmospheric pressure

 *Purification plants,  Treatment methods
                                             371

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285D

EXPERIENCES WITH TWO LAYERS OF ION EXCHANGERS IN FULL DESALINATION
PLANTS (ERFAHRUNGEN MIT SCHLICHTBETTAUSTAUSCHERN IN VOLLENTSAL-
ZUNGSANLAGEN) ,

Brunner, R. E., and Hoffmann, W.

VGB Kraftwerkstechnik, Vol. 54, No. 4,  p 235-242, 1974.   10 fig,  6 tab,  7 ref.

Experiences with the use and regeneration of two-layer ion exchangers In full
desalination are presented.  Two-layer  anion exchangers,  composed of strong
and weak acidic exchangers, especially  suitable for the  separation of sodium
ions, are regenerated in counterflow.   These use 0.7-1 percent sulfuric  acid
for the weak acidic exchanger, and 1.5-5 percent sulfuric acid for the strong
acidic exchanger.  If regeneration is  done with hydrochloric acid, its
concentration should not exceed 5 percent.  The use of hydrochloric acid-
regenerated counterflow two-layer ion  exchangers is the  most economical
solution for waters with high carbonate hardness.  Counterflow-regenerated
anion exchangers, composed of a strong  basic and another weak basic exchanger,
are an ideal solution for full desalination.  However, the elution of chlorine
ions from the strong basic exchanger is problematic.

*Ion exchange,  *Anion exchange, *Desalination, Carbonates, Acidity


Counterflow, Hydrochloric acid, Chlorine ions, Elution
286D

THE PROBLEMS OF THE DISCHARGE AND OF THE TREATMENT OF THE WASTE
WATERS OF THE PARIS URBAN AGGLOMERATION (LES PROBLEMES D'EVACUATION
ET DE TRAITEMENT DES EAUX USEES DE L'AGGLOMERATION PARISIENNE),

Olives!, J.

Industrie Minerale, Vol. 56, No. 3, p 118-123, March, 1974.  5 fig.

The waste water treatment and disposal method adopted at the Acheres waste
water treatment facility servicing the Paris urban agglomeration is outlined.
The waste waters received at the treatment plant are first pretreated for
the mechanical removal of sand and voluminous objects, after which the
supernatant is eliminated by decantation.  The waste water thus pretreated is
then subjected to two-stage biological treatment using aeration and activated
sludge.  The purified effluent is discharged into the recipient.  The sewage
sludge is digested, then conditioned thermally by exposing it to steam at
200 C for 15 minutes, and after dehydration in vacuum press, it is disposed
of on a sanitary landfill.

*Waste disposal, *Treatment facilities, *Urban areas, Pre-treatment,
Biological treatment, Sewage sludge, Aeration, Activated sludge, Vacuum
drying, Landfills

*Paris, France, Treatment plants, Thermal conditioning
                                             312

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287D

EVALUATION OF THE EXPERIENCES GAINED DURING THE OPERATION OF THE
AEROBIC SEWAGE SLUDGE TREATMENT PLANT IN NYIREGYHAZA (A NYIREGYHAZI
AEROB ISZAPKEZELO BERENDEZESSEL SZERZETT UZEMI TAPASZTALATOK
ERTEKELESE),

Olah, J.

Hidrologiai Kozlony, Vol. 54, No. 1, p 41-48, January, 1974.  5 fig, 3 tab,
10 ref.

Experiences gained with a partly oxidizing aerobic sewage sludge stabilizing
plant are evaluated.  Comparative experiments and economic considerations
concerning the anaerobic and aerobic stabilization of excess sludge and raw
sludge mixtures revealed the superiority of aerobic treatment.  The excess
activated sludge or the mixture of the raw and activated sludge was treated
in a 700 cu m earth basin by means of an Abtaerator aerator of 2.4 m in
diameter in semicontinuous operation, using purified waste water as wash
liquid.  The aerator organic matter load was maintained at 1.54-1.95 kg/cu m/day
at an excess activated sludge concentration of 15 kg/cu m and at a hydraulic
hold time of 6.8 days, and a reduction by 17-20 percent in the organic matter
content was achieved.  The treated sludge could be easily dehydrated in drying
beds without decomposing of odors.  During the treatment of the excess
sludge, foam and suspension formation was observed after 3 weeks operation
that could be controlled by increasing the wash liquid expenditure.  To
maintain the aerator temperature above 10 C in the winter period, it is
necessary to increase the wash liquid expenditure by 10 times.

*Aerobic treatment, *0rganic matter, *Sewage sludge, *Stabilization, Activated
sludge, Waste water, Dehydration

Stabilizing plant
288D

TREATMENT AND DIGESTION OF SEWAGE SLUDGE PRODUCED BY WASTEWATER
TREATMENT PLANTS (TRATTAMENTO E SMALTIMENTO DEI FANGHI PRODOTTI
DAGLI IMPIANTI DI DEPURAZIONE DELLE ACQUE DI SCARICO),

Songa, T., and Aveni, A.

Ingegneria, No. 2, p 81-93, February, 1974.  7 fig, 7 tab, 11 ref.

The complex system of the treatment and disposal of sewage sludge produced
by waste water treatment plants is surveyed.  The sewage sludge, a mixture of
different sludges generated by the different waste water treatment processes
steps, is either sterilized by pasteurization or chlorination, or conditioned
thermally or chemically for the conversion of colloids to settling floccules
by aggregation, or digested anaerobically or aerobically.  Anaerobic digestion
at a constant temperature for 20 to 30 days, and especially between 16 and 38 C
(mesophilic digestion) is the most commonly used digestion process, as compared
with aerobic digestion.  Conditioned sludge is subjected to dehydration on
drying beds, by centrifugation, vacuum filters, or filter presses, while
anaerobically digested sludge is dried on drying beds, in rotary furnaces, in
fluidized beds, and in the form of atomized suspension.  After drying and
dehydration, the sludge can be incinerated in multistage or rotary furnaces,
in fluidized-bed furnaces, and atomization furnaces, or stabilized by
composting or the Zimpro process.  Following such treatment, the ashes and
sludge can be disposed of safely, and the compost obtained, possibly mixed with
peat, can be used for agricultural purposes.

*Sewage sludge, *Sludge disposal, *Anaerobic digestion, *Aerobic digestion,
Chlorination, Dehydration, Incineration

Mesophilic digestion, Agricultural uses, Sludge conditioning, Treatment methods
                                              373

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289D

NEW HIGH-EFFICIENCY METHODS FOR THE DESALTING OF NATURAL WATERS
AND FOR THE PURIFICATION OF WASTEWATERS (NOVYYE VYSOKOEFFEKTIVNYYE
METODY OPRESNENIYA PRIRODNYKH I OCHISTKI STOCHNYKH VOD) ,

Yasimov, A. A., and Mayzlik, D. L.

Khimicheskaya Promyshlennost', No. 3, p 182-189, 1974.  7 fig, 3 tab, 52 ref.

The uses and advantages of reverse osmosis and ultrafiltratlon by means of
semipermeable membranes, especially those made of acetylcellulose membranes,
in seawater desalination and in the purification of industrial effluents are
surveyed.  These methods often are less expensive than conventional treatment
methods.  Modern multistage reverse osmosis units are suitable for the
effective and inexpensive desalination of seawater even, with high salt contents.
Reverse osmosis and ultrafiltration are suitable for the purification of
effluents in the pulp and paper industry, electroplating industry, and for the
removal of pathogenic germs, viruses, microorganisms, surfactants and enzymes
from water.  Ultrafiltration is suitable for the concentration and removal of
substances with high molecular weight, but also of low-molecular substances
such as urea, phenol, acetone from protein, nucleic acid and polypeptide
solutions, and for the separation of aqueous solutions of glucose, lactose,
maltose, ethyleneglycol, and propyleneglycol.

*Reverse osmosis, *Waste water purification, *Pulp and paper industry,
*Semipermeable membranes, Desalination, Water purification, Separation,
Industrial wastes, Proteins, Microorganisms, Enzymes


*Ultrafiltration
29 OD

TERTIARY TREATMENT OF SEWAGE TREATMENT PLANTS,

Kato, S., and Araki, Y.

Sewerage Bureau, Tokyo Metropolitan Government,
Tokyo, Japan

Mitsubishi Denki Giho, Vol. 48, No. 4, p 444-451, April, 1974.  6 fig, 1 tab.

Tertiary treatment is seen as a new treatment method from the perspective of
prevention of water pollution and effective utilization of water resources.
There are several types of tertiary treatment under development, depending on
the. objects of removal and the removing rate.  In Morigasaki Treatment Plant,
a tertiary treatment plant has been constructed  for treated water by high speed
sand  filtering method on secondary treated water from  the activated sludge
method.  This plant intends to supply water for  miscellaneous purposes, such
as pumps sealing water, and to gather data of a  tertiary treatment plant.
Installations and ongoing experiments are described.

*Tertiary treatment, *Water quality control, Treatment facilities,
Filtration, Activated sludge, Sand

Morigasaki Treatment Plant  (Japan), High speed sand filtration
                                            374

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 291D

 BALTIMORE HAS A  LOT  GOING  FOR  IT  -  INCLUDING  ITS WATER,

 Ramsay, A.  St. A.

 National Engineer, Vol.  78, No. 5,  p  11-12, May, 1974.

 In Baltimore as  in other sections of  the country where the mineral content
 of the raw  water is  low, the basic  treatment  procedure as outlined below
 is used for the  two  Montebello plants and the Ashburton plant.  Chlorine
 as a sterilizing agent is  applied to  the water immediately after it passes
 through a meter  which measures and  records the rate of flow.  Alum is
 used as a coagulating agent to collect the mud and suspended material in
 the raw water.   The  alum reacts with  the alkalinity in the water and forms
 aluminum hydroxide which will precipitate as  a floe.  After mixing, the
 water moves into the settling basins.  The basins are designed so that
 sufficient  time  elapses in the passage of the water for the particles of
 floe with their  absorbed materials  to settle  to the bottom.  The last step
 in clarifying the water is accomplished by passing it through about 20 inches
 of sand.  Fluoridation of  the water supply was begun in 1952.  So as to
 counteract  corrosiveness,  lime is added to the filtered water in the amount
 of approximately one half  grain per gallon.

 *Treatment  facilities, *Water treatment, Chlorination, Lime, Aluminum,
 Filtration, Fluoridation,  Corrosion control,  Equipment

 *Baltimore, Maryland
29 2D

KEEPING WATCH ON WASTEWATER,

Rogers, M. E.

Camp, Dresser and McKee, Boston, Massachusetts

Water and Wastes Engineering, Vol. 11, No. 6, p 38-40, June, 1974.  2 fig.

Lower first cost and the integrating of data handling and modern process
control into the existing operating staff are two of the advantages of a
new computer installation at one New York City waste water plant.  The
modern instrument and computer-based data handling system is being provided
in connection with the upgrading and enlarging of the Tallman Island
pollution control plant serving the Borough of Queens area.  The plant
was designed to use a computer-based data handling system with advanced design,
solid-state electronic instrument systems.  Only the minimum number of
recording instruments and several spare recorders are used.  In this way,
any of the process variables or derived values can be assigned for trending.

*Computers, *Instrumentation, *Waste water treatment, New York, Data storage
and retrieval, Treatment facilities, Design criteria
                                               375

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29 3D

THE MINI-SIZE TREATMENT PLANT,

Excavating Contractor, Vol. 68, No. 6, p 25, June, 1974.

Practical sewage treatment systems are now available for small community
waste treatment application.  A privately owned sewage plant installed
near Lakewood, New Jersey is described.  The question of concrete or steel
construction materials is debated mentioning problems such as corrosion,
space, and maintenance.  Both precast and poured methods for concrete
construction are discussed.

treatment facilities, Construction materials, *Steel, *Concrete,
Sewage treatment
29 4D

SONICS PLUS OZONE A WINNER?

Heckroth, C. W.

Water and Wastes Engineering, Vol. 11, No. 6, p 41-44, June, 1974.

Sonics has been combined with ozonation in a quick-step tertiary treatment
at Indlantown, Florida to yield a fully-acceptable effluent.  The complete
system, using chemical/mechanical, filtration, and sonics/ozone steps,
inactivates pathogenic viruses and kills bacteria detrimental to public
health within two hours.  The Sonozone system encompasses a primary stage
of settling and contact with coagulants, followed by a filtration system
to remove microsized solids and organics, and finally the tertiary step
that takes the waste stream through ultrasonic bombardment and ozonation.
All equipment is back-flushed using effluent and the back-flush water is
recycled through the plant.  Residual ozone and dissolved oxygen appear
in the treated effluent.  The sludge is sent to sand beds and the excess
sludge liquid is recycled to the plant.  The dried sludge is collected
and periodically transported to a sludge disposal area.

*Waste water treatment, *Sewage treatment, *0zone, *Tertiary treatment,
Effluent stream, Equipment, Treatment facilities, Sludge treatment

*0zonation, *Ultrasonic bombardment, Indiantown, Florida
                                             376

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295D

HOUSTON SUBURBS PROFITS FROM BUILDING THE STATE'S BEST
WASTE WATER TREATMENT PLANT,

Water and Sewage Works, p 38-40, April 30, 1974.

The unincorporated area, Montgomery County Fresh Water Supply District
No. 2, produces a clean effluent by one of Texas' first three-stage
sewage treatment plants.  The district installed a big, advanced plant
then sold excess capacity to neighboring districts.  Within two months of
starting plant operation, (in September 1971) the district had found
buyers for 700,000 of the plant's one mgd capacity.  The plant is a
factory-built field-erected system whose major components were built by
Ecodyne Corporation's Smith and Loveless division.  The secondary stage
of the treatment system employs a contact stabilization type of activated
sludge biological treatment.  The tertiary step is gravity filtration,
in which secondary effluent filters through layers of anthracite and sand.
Instruments in the plant's control station continuously monitor effluent
flow volume, pH, chlorine residual and other key operating indicators.
Switches at a single panel permit control of aeration tank blowers, settling
basin skimmers, sludge concentrator and filter pumps.

*Treatment facilities, Texas, Sewage treatment, Tertiary treatment,
Equipment, Filtration, Activated sludge, Biological treatment,
Instrumentation, Economics, Operating costs.
296D

EXPANSION SPARKS NEW DESIGN,

Westerhoff, G. P.

Malcolm Pirnie, Incorporated, White Plains, New York

Water and Wastes Engineering, Vol. 11, No. 6, p 44, 46, 66, June, 1974.
1 fig, 1 tab.

A report outlining a program for the evaluation and testing of plant
pre-treatment on a full plant scale including a six-month study program
was initiated in conjunction with the reviewing authority in 1973 at the
Sturgeon Point, New York plant.  Results of the study and the recommendations
for future plant operations are presented.  The water treatment processes
at Sturgeon Point consist of aeration, chemical addition, rapid mixing,
flocculation and sedimentation, followed by filtration and chlorinatlon.
The study program required turbidity measurements at several critical
points and used continuous-sampling and recording turbidimeters to measure
turbidity.  Examinations for total microscopic count were made during the
filtration study as an additional indicator of water quality during the
testing program.  Based on the results of the one-year filtration study
program, filtered water quality goals were established for the Sturgeon
Point Water Treatment Plant.  These goals should be met consistently,
with the existing standard pre-treatment presently approved by the State
Department of Health.

*Pre-Treatment (water), *Project planning, *Evaluation, Treatment
facilities, New York, Operations, Waste water treatment, Turbidity,
Filtration
                                            377

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29 7D

BOD:  A RE-EVALUATION,

Clark, D. W.

Wastewater Treatment Plant, Las Cruces, New Mexico

Water and Sewage Works, Vol. 121, No. 5, p 68-69, May, 1974.  9 ref.

There Is growing dissatisfaction with the standard five-day biochemical
oxygen demand (BOD) determination as a basic control parameter for waste-
water treatment plant operation.  Limitations associated with BOD include:
the length of time it takes for test analysis, difficulties in correlating
results with observed conditions, and uncertainty as to what is actually
being measured.  Chemical oxygen demand (COD) testing was an attempt to
improve upon the speed and precision of the BOD.  It utilizes dichromate to
oxidize the organic materials under harsh conditions.  The COD includes
not only carbonaceous oxygen demand, but other forms as well.  Total
organic carbon (TOC) analysis improves upon organic and inorganic source
differentiation by measuring a different parameter.  It does not rely
upon oxygen demand; rather it measures the carbon dioxide produced upon
complete oxidation of the organic material in the waste.  By using BOD,
COD, and TOC results, a descriptive profile of a waste can be accumulated
which includes the specific concentrations of organics in the waste, the
rate at which these organics will be decomposed, the oxygen required to do
this, and finally the portion of organic material which will remain inert.

*Biochemical oxygen demand, *Chemical oxygen demand, *Analytical techniques,
Waste: water treatment, Water analysis, Treatment facilities, Operations

*Total organic carbon
298D

OIL RECOVERY SYSTEM OPERATES EFFECTIVELY IN ROUGH WATER,

Gascciigne, P,

World Oil, Vol. 178, No. 7, p 93-94, June, 1974.

A versatile type of oil spill pickup equipment has been developed by MARCO
Pollution Control Corporation, Seattle, Washington.  The equipment is an
oil skimmer which can operate efficiently even under bad weather conditions.
The skimmer vessel is 58 feet long, 24 feet wide, weights 35 tons and is
driven by twin 210-hp diesel engines.  Oil is pumped into storage tanks
by two 250-gpm guiding-type screw feed pumps.  Special features of the
system include oil sump heat exchangers, materials handling crane, screw
conveyors in sumps, bow thrusters, combustible gas detection, and high
intensity lighting.

*0il spills, *Skimming, *Equipment, Storage tanks, Water pollution control
                                             378

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299D

DESIGN OF BASIN COLLECTION TROUGHS,

Boyle, W. H.

Envirex Incorporated, Rexnard Companu, Waukesha, Wisconsin

Water and Sewage Works, p 136-137, April 30, 1974.

Collection troughs have a direct bearing on both the process and the economic
aspects of a facility.  The process aspect of collection troughs involves
the requirement to handle a maximum specific flow rate.  They must be
sized properly so the hydraulics of the troughs will not adversely affect
the intended unit process design and must be designed properly so that
flooding of the weirs does not occur.  Another important aspect of the
design of the collection trough would be that of economics.  A proper
economic sizing of the trough should be a compromise between an economic
determination of the cost of the trough, versus the cost of handling
additional headless.  Finally, it  is important for the design engineer to
determine if the collection trough will have free or submerged discharge,
and size accordingly.

*Economics, *Design criteria, *Conduits, Treatment facilities, Flooding,
Weirs, Mathematical studies, Flow  rates
300D

WATER TREATMENT PLANT DESIGN IS FLEXIBLE,

Bolllnger, K. A.

City Manager, Allegan, Michigan

Water and Sewage Works, p 116-118, April 30, 1974.

In 1968 the city of Allegan, Michigan began construction of a water treatment
system that would replace the hard water supplied by natural wells located
in the valley of the Kalamazoo River.  The treatment plant was designed
by Williams and Works of Grand Rapids, Michigan.  The design capacity is
3 mgd, the hydraulic capacity is 4 mgd.  The plant flow sheet provides
flexibility in hardness removal, as either a split or straight lime
system.  For most of the year, the split treatment provides softening to
130 mg/liter, iron removal, taste and odor control and disinfection.  The
plant can be operated by means of manual, automatic, or remote control
methods.  The control panel is located in the laboratory so that the
equipment and processes can be under constant observation.

*Water treatment, *Treatment facilities, Hardness (water), Design criteria,
Operation and maintenance, Equipment, Automation

Michigan
                                                379

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301D

FOAM SEPARATION OF LEAD(II) AND CADMIUM(II) FROM WASTE
WATER,

Ferguson, B. B., Hinkle, C., and Wilson, D. J.

Vanderbilt University, Nashville, Tennessee,
Department of Chemistry

Separation Science, Vol. 9, No. 2, p 125-145, 1974.  18 fig. 2 tab, 21 ref.

Feasibility studies were conducted to evaluate the efficiencies of lead(II)
and cadmium(II) removal from contaminated waste water using foam separation
techniques.  Variables such as pH, ionic strength, collector concentration,
and interfering ions were studied to determine their effects on ion
flotation.  Adsorbing colloid flotation gave excellent results; lead sulfide
and cadmium sulfide were adsorbed to ferrous sulfide which was then removed by
foaming with hexadecyltrimethylammonium bromide.  Lead(II) levels were
reduced from 0.80 to 0.025 ppm in 34 minutes foaming with 15 ppm iron(III)
added.  Cadmium(II) levels were reduced from 1.0 to 0.008 ppm in 45 minutes
foaming with 25 ppm iron(III) added.

*Foam separation, *Feasibility studies, Evaluation, Waste water treatment,
Lead, Cadmium


Ion flotation
WASTE WATER RENOVATION THROUGH SOIL PERCOLATION,

John, M. K.

Research Station, Canada Department of Agriculture,
Agassiz, British Columbia, Canada

Water, Air, and Soil Pollution, Vol. 3, No. 1, p 3-10, March, 1974.
3 tab, 12 ref.

A laboratory experiment simulating high-rate effluent renovation by soil
percolation involved leaching secondary sewage effluent through columns of three
differing soils.  Analyses of phosphorus in 22 leachate collections and
distribution of both organic and inorganic phosphorus in column sections
revealed the mechanisms of phosphorus removal, the influence of differing soil
properties, and the effect of continuous utilization.  The leachate N03-N levels
were lower than the original N03-N content of effluent for the first ten
leachings but N03-N enrichment occurred for the last effluent percolations
through all three soils.

laboratory tests, *Simulation analysis, *Waste water treatment, *Percolation,
Soil physical properties, Sewage treatment, Phosphorus, Leaching, Water
pollution control

*Phosphorus removal
                                           380

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303D

PRODUCTS AND PROCESSES FOR THE TREATMENT AND CONDITIONING
OF WATER (PRODUITS ET PROCEDES DE TRAITEMENT
ET DE CONDITIONNEMENT DES EAUX),

La Technique Moderne, Vol. 66, No. 4, p 38-40, April, 1974.

Chemicals and processes for the preparation of drinking water and industrial
waters, and for the purification of municipal and industrial waste water
are described.  Following mechanical separation of bulky materials, water
is further purified by coagulation and flocculation by means of ferric
chloride, and aluminum sulfate for the preparation of drinking and industrial
water.  Drinking water is further purified by filtration and adsorption by
means of activated silica or carbon, and sterilization by means of chlorine
dioxide.  Algal proliferation can be prevented by the addition of polyamides,
quaternary ammonium salts, and chlorine dioxide in industrial waters.  To
prevent encrustation and corrosion in pipelines, precipitation-retarding
agents, such as polyphosphates, dispersing agents, and film-forming
metasilicates are added.  Cyanides are neutralized by means of sodium
hypochlorite, and chromates are oxidized by sodium metabisulfite and ferrous
sulfate.  Dilute effluents can be concentrated by ion exchange resins,
electrolysis, evaporation, or reverse osmosis.

*Potable water, *Industrial water, *Water purification, Chemicals,
Separation techniques, Waste water treatment, Coagulation, Filtration,
Adsorption, Corrosion control
304D

THE FATE OF PHENOL1CS IN WASTEWATER - DETERMINATION BY
DIRECT-INJECTION GLC AND WARBURG RESPIROMETRY,

Baird, R. B., Kuo, C. L., Shapiro, J. S., and Yanko,
W. A.

The County Sanitation Districts of Los Angeles County,
San Jose Creek Water Quality Laboratory,
Whittier, California

Archives of Environmental Contamination and Toxicology, Vol. 2, No. 2,
p 165-178, May, 1974.  6 fig, 4 tab, 13 ref.

The effects of phenol, cresol isomers, and chlorinated phenols on the
respiration of activated sludges have been studied using Warburg techniques.
The biodegradability of these materials under simulated treatment conditions
in activated sludge also was determined.  Results show that less than
10 mg/liter concentrations of phenol and chlorophenols, while being biodegraded,
proved toxic to sludges unacclimated to phenolics.  The toxic effects of the
cresols were not so severe for the sludges tested.  Phenolic analysis in these
studies was accomplished employing GLC techniques with a new column packing,
dinonylphthalate on Chromosorb G.  This chromatographic technique was
effective in rapidly identifying phenolic materials in activated sludge,
treatment plant effluents, and industrial discharges.   Separation of all
isomers tested, except m- and p-chlorophenol,  was possible using this
technique.

*Activated sludge, *Biodegradation, *Respiration, Simulation analysis,
Phenols, Toxicity, Analytical techniques, Chromatography,  Effluents,
Industrial wastes

Cresol isomers, Chlorophenols, Warburg technique
                                         381

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   305D

   SATISFYING VENEZUELA'S QUALITY WATER REQUIREMENTS,

   Rohm and Haas Reporter, Vol. 32, No. 2, p 20-23, Summer, 1974.

   A large and sophisticated conditioning plant that produces up to 780
   gpn of ultra-high-quality water has been developed for a $50 million
   petrochemical complex near Moron, Venezuela.  The system consists of
   three activated carbon filters for removal of organic matter; three cation
   exchange columns to remove sodium and hardness elements such as calcium
   and magnesium; a degasification tower to remove carbon dioxide; three
   anion exchange columns to remove mineral acidity by cation exchange resin
   treatment; and, two final polishing units to totally remove traces of
   silica and other mineral salts.  The Illinois Water Treatment Company
   supplied part of the equipment and assisted in the design and installa-
   tion phases.   All of the cation exchange columns are charged with Amberlite
   IR-120 and the anion exchange columns contain Amberlite IRA-402.  The
   final polishing units contain a mixture of Amberlite IR-122 and Amberlite
   IRA-900.

   *Treatment facilities, *Water treatment, *Water quality control,
   Industrial plants,  Equipment, Filters, Activated carbon, Organic
   matter, Installation, Cation exchange

   Venezuela
306D

LIFTING THE LID OFF PITSEA,

Surveyor Public Authority Technology, No. 4275, p 13, May 17, 1974.

The lagooning area at the Pitsea, England landfill site consists of a
series of long, narrow interlinked trenches dug in surveyed positions in
fully composted refuse.  The trenches have a shallow weir constructed
where they join and the waste is introduced from the pipeline at one
end of the system.  It then flows along the first trench over the weir
and then along the rest of the system.  Phase separation of the oily
wastes using acids to aid the separation is a feasible proposition on a
large scale showing that mixing and dilution of suitable wastes resulted
in pumpable sludge, acceptable for site disposal.  Finally, it is noted
that the most efficient way of disposing of liquid wastes at Pitsea is
to utilize the high potential evaporation from the site rather than
rely on groundwater flow away from it.

*Landfills, *Lagoons, Waste storage, Trenches, Waste treatment, Treatment
facilities, Liquid wastes, Evaporation, Separation techniques, Oil wastes

Great Britain
                                              382

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307D

U. S. NAVY JETTISONS 'HEAVE-HO1 HANDLING OF
PACKAGING ITEMS AT SEA,

Solid Wastes Management/RRJ, Vol. 17, No. 6, p 22-23, 57-58, 66, 70,
June, 1974.
72,
In compliance with executive orders, an environmental protection program
has been initiated in a major effort to reduce or eliminate the wastes
accumulated by Naval ships and currently disposed of at sea.  The Navy
has set a goal of reducing the amount of packaging materials going aboard
ships by 50 percent over the next five years and by 75 percent in 15
years.  Maximum usability will be sought for anything judged absolutely
essential.  Guidelines for hazardous materials, disposability and com-
pactibility ratings of materials, as well as the feasibility of incinera-
tion approaches and establishing rough ratings are discussed.

*Environmental control, Solid Wastes, Navigable waters, Water pollution
control, Waste disposal

United States Navy
 30 8D

WASTE INTO WEALTH,

Searle, S. S., and Kirby, C. F.

Melbourne and Metropolitan Board of Works Farm,
Victoria, Australia

Water Spectrum, Vol 945, No. 36, p 15-21, January, 1973.  2 fig.

About twenty-two miles outside of the city of Melbourne, Australia,
a combination beef cattle ranch and sewage treatment facility functions.
The ranch, called the Board of Works Farm, is systematically irrigated by
waste waters of the highly industrialized city.  Suspended material is
filtered by the soil and transformed into humus and plant food by the action
of soil micro-organisms.  The total flow includes domestic wastes,
industrial wastes, and groundwater infiltration into the sewers.  Industrial
waste water provides about half the biochemical oxygen demand and suspended
solids.  Channels, drains, and ditches were carefully constructed and are
inspected daily by laboratory analyses.  The efficient disposal by soil
filtration depends on the grasses being kept short; sheep and cattle both
have the role of grass mowers.  The farm remains highly productive, eco-
nomically sound, as well as an efficient waste water treatment project.

*Municipal wastes, *Farms, *Sewerage, Sewage treatment, Costs, Industrial
wastes, Waste water, Irrigation, Soil

*Melbourne, Australia, *Board of Works Farm, *Land treatment, Cattle
                                              333

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 30 9D

 STUDY OF  THE EFFICIENCY  OF  THE  REMOVAL  OF  BENZO
 (A)PYRENE FROM URBAN WASTE  WATER BY  BIOLOGICAL
 PURIFICATION,

 Yershova,  K. P.,  Nefedov, Y.  I.,  Kanunnlkova, L.S.,
 and Krylova, M. G.

 Gigiyena  i Sanitariya, No.  2, p 102-103, 1974.   1  tab.

 The efficiency of the  removal of benzo(a)pyrene  and  ether-soluble  petroleum
 products  from municipal  wastewater by biological purification was  studied
 in  full-scale and laboratory experiments.   The mechanical  purification
 step comprising the sand trap had an efficiency  of about 40  percent  in  the
 removal of benzo(a)pyrene.  Total biological  treatment  in  the activated
 sludge aeration basin  and an after-treatment  basin resulted  in a rate of
 benzo(a)pyrene removal of 77.5-98.6  percent averaging 91.2 percent.  The
 efficiency of the biological treatment  in  the removal of ether-soluble
 hydrocarbons ranged from 62.9 to 88.4 percent.   Some correlations  between
 the rates of removal of  benzo(a)pyrene  and ether-soluble hydrocarbons
 were observed.   The efficiency  of the biological treatment was found to
 gradually decrease in  the course of  aeration.  The reduction of the
 benzo(a)pyrene content in the waste  water  during the biological treatment
 was partly due to absorption on the  activated sludge particles and partly
 to  metabolism.

 *Municipal waste  water,  *Petroleum,  *Biological  treatment, *Purification,
 Laboratory tests, Waste  water treatment, Absorption, Activated sludge,
 Hydrocarbons

 Benzo(a)pyrene, Ether-soluble petroleum
310D

EXAMPLES OF THE EFFECTIVE USE OF PLASTIC MATERIALS
IN A MUNICIPAL WATER SUPPLY AND WASTE WATER TREAT-
MENT PLANT (BEISPIELE DER EFFEKTIVEN PLASTANWENDUNG
IN EINEM VEB WASSERVERSORGUND UNO ABWASSERBEHANDLUNG),

Koehler, D.

Wasserwirtschaft-Wassertechnik, Vol. 24, No. 3, p 95-98,
1974. 4 fig.

Examples of the various uses of plastic materials in municipal water supply
and waste water treatment in East Germany are presented.  Compared with
conventional materials, plastics excel by their long useful life, reduced
production and maintenance costs, light weight, and increased resistance to
physical and chemical effects.  Venthole covers, instrument cabinets, waste
water pipes, sludge manifolds for sludge drying rows, percolation bodies
for waste water treatment, and insulating layers are made of PVC, while
polyethylene is used for coating tanks and pipes.  Epoxy resin as filler is
used for the repair of pump blades damaged by cavitation, of surfaces exposed
to wear, and of concrete pipes, as well as for coating tanks.  Polyester
resin is used as construction material for tanks, and for the repair of
broken pipes.

*Plast:ics, *Municipal water, *Water supply, Waste water treatment,
Germany, Materials, Percolation, Pipes, Construction materials

*Treat:ment plants, PVC
                                               384

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311D

MODEL PROCESS FOR BIOLOGICAL PHOSPHATE ELIMINATION FROM
COMMUNAL WASTE WATER II. BIOLOGICAL PHOSPHATE ELIMINATION
FOLLOWING DENITRIFICATION OF THE WASTE WATER NITROGEN
BY MEANS OF METHANOL,

Bringmann, G., and Kuehn, R.

Gesundheits-Ingenieur, Vol. 95, No. 5, p 135-138, 1974.  1 fig, 8 tab.

Biological phosphate elimination from municipal waste water in connection
with and following denitrification by means of methanol in a model bio-
logical waste water treatment plant is described.  The first stage of
the treatment plant constitutes an aerated nitrifying tank for the quanti-
tative nitrification of the ammonium nitrogen in the waste water.  The
methanol denitrification in the second stage has an efficiency of 94.8 percent
with respect to an initial nitrate content of 65.3 mg/liter.  One mg
nitrate-nitrogen required 3.3 mg methanol for its denitrification.  The
effluent from the third stage (trickling body) showed a secondary in-
crease in the residual nitrate-nitrogen content.  However, the nitrate-
nitrogen consumption in the fourth stage (phosphate elimination) re-
sulted in a residual nitrate-nitrogen level of 2.35 mg/liter, corres-
ponding to a total nitrate-nitrogen elimination rate of 96.4 percent.  The
phosphate elimination in the nitrification was dependent on the waste
water quality: while there was practically no phosphate elimination
at neutral pH, phosphate elimination at akaline pH reached efficiencies
of up to 74.1 percent.  Depending on the phosphate content in the nitrifica-
tion effluent, the efficiency of phosphate elimination in the denitri-
fication stage ranged from 80.35 to 41.3 percent.  Relative to the trickling
body effluent, the phosphate elimination was 92.7-89.5 percent.  Following
filtration of the effluents from the phosphate elimination stage by
means of ferrooxidizing bacteria at neutral pH, a residual phosphate
content of 0.006-0.007 mg/liter, corresponding to an overall efficiency
of 99.96 percent, was achieved.

*Phosphate, *Biological treatment, *Municipal wastes, *Waste water
treatment, Denitrification, Methanol, Model studies, Aeration

*Treatment plants
312D

CLEAR-SPAN DOMES COVER WATER TANKS,

Public Works, Vol. 105, No. 7, p 90, July, 1974.  1 fig.

The installation of Geodesic-type domes on two potable water
storage tanks brought the City of Bend, Oregon, into compliance
with State water storage regulations.  The city had experienced
problems with pollen, pine needles and other objects falling
into the open-topped 1.5 MG steel tanks.  Temcor all-aluminum PolyFrame
Domes were selected to roof the tanks.  They are made of aluminum struts
and gussets assembled to form a fully triangulated space truss, and are
covered with triangular closure panels of 16-gauge aluminum sheet.  An
all-aluminum vent with bird screen and a 3 by 3-ft. aluminum access hatch
completes the structure.  The domes were assembled at ground level and
hoisted into position atop and riveted steel tanks with a crane.  Cost
of the two domes was $95,380 installed.  Little maintenance cost is
anticipated since the domes require no painting.

*Tanks, *Potable water, *Water quality control, *Aluminum,
Construction materials, Pollution abatement, Maintenance costs,
Installation

Bend, Oregon

                                                385

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313D

THIS WATER FILTER CLEANS ITSELF,

Medlar, S.

Whitman and Howard, Incorporated, Engineers and
Architects, Boston, Massachusetts

The American City, Vol. 89, No. 6, p 63-65, June, 1974.  1 tab.

Burlington, Massachusetts uses a new water treatment technique.  Using an automatic
backwash carbon filter, the town's 6.0-mgd filtration plant treats water from its
new 500-million gal reservoir for color, iron, taste, odor, turbidity, bacteria,
corrosiveness and contamination.  The plant's two filters are a silica sand with
an effective size 0.60 mm, and an 8 x 30 mesh granular activated carbon.
(Leibowitz-FIRL)

*Filtration, Water treatment plant, Contamination, Bacteria, Turbidity, Iron,
Reservoirs, Filtration
314D

JOINT TREATMENT OF MUNICIPAL AND PULP MILL EFFLUENT,

Voelkel, K. G., Martin, D. W., and Deering, R. W.

Charmin Paper Products Company and the Green Bay
Metropolitan Sewerage District

Journal of Water Pollution Control, Vol. 46, No. 4, p 634-656, April,
1974.  14 fig., 11 tab., 11 ref.

The Green Bay Metropolitan Sewerage District and four paper product companies
undertook a project in 1966 of experimentation on the treatment of municipal and
pulp irill effluents.  Four activated sludge treatment processes were tested.  The
combined wastes included calcium-based bisulfite pulping, de-inking waste water,
Whitewater from paper machines, neutral sulfite semi-chemical pulping, domestic
sewage, waste water from two large meat packing plants, and effluent from a
pickle processing plant.  Of all methods tried, the contact stabilization was
most successful in treating combined wastes; filamentous sulfide bacterial growth
in the mixed liquor was controlled by adding 5 to 10 mg/liter of chlorine to the
returned activated sludge nitrogen and phosphorous additions were demanded for
satisfactory biological activity.

*Wast& water treatment, Sewage, Effluent, Pulp mill wastes, Municipal wastes,
Pulp & paper industry, Activated sludge

* Joint: wastes
                                               336

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315D

SLUDGE DEWATERING WITH THE AID OF CONTINUOUSLY OPERATING PRESS-
TYPE FILTERS (SCHLAMMENTWASSERUNG MIT KONTINUIERLICHEN PRESSFILTERN),

Reuter, I. J., and Beckrath, H.

Aufbereitungs-Technik, Vol. 15, No. 5, p 253-259, May, 1974.
10 fig, 3 tab, 14 ref.

For the past eight years the filter belt press has been applied as a continuously
operating press-type filter for dewatering municipal and industrial sludges.
Recently, additional continuous press-type filters have been developed and tested.
These include the tower press, the angle-type press, and the drum-type filter
press.  The machines differ primarily with regard to the operating direction of
the filtering belts and the pressure to which the sludge is exposed while being
dewatered.  The paper quotes practical results.  However, the figures available
do not allow a direct, reliable comparison of the results and cost of sludge
dewatering by using the four machines is compared.

*Filters, *Municipal wastes, *Industrial wastes, *Costs, Equipment
316D

WATER TREATMENT PLANT  (1140 CU M/HR) FOR SUNABEDA,

Mishra, B., Joshi, S. R., and Savalappan, K. N.

Government of Orissa,
Public Health Department

Journal of the Institution of Engineers (India), Vol. 54, Part PH2, p 61-65,
February, 1974.  6 fig.

The location of an industry is often governed by the availability of an adequate
quantity of water.  The various unit operations involved in the 1140 cu m/hr
water treatment plant at Sunabeda  (Orissa) are discussed.  Details of units and
the design parameters of units are also given.  Merits and demerits of separate
flocculation and clarification versus combination of both unit operations in one
unit are shown.  Construction and operation of an unconventional rapid sand
gravity filter underdrainage system is described.  One-year performance of the
plant is graphically shown with emphasis on clarified water turbidity and filtered
water clarity.

*Water treatment, *Water quality control, Clarification, Flocculation, Water
quantity, Industrial water, Design criteria, Turbidity

*Treatment plants, *India, Sunabeda, India
                                           387

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 317D

 BERRY SEED SHELL AS FILTER MEDIA,

 Bhole,  A.  G.,  and Nashikkar,  J.  T.

 Visvesvaraya Regional College of Engineering,
 Nagpur, India

 Journal of the Institution of Engineers (India),  Vol.  54,  Part PH2,  p 45-47,
 February,  1974.   5 ref.

 It was  found experimentally that berry seed shell satisfies the criteria required
 for a dual media filter.   Conventional sand filtration involves the  flow of
 materials  from fine to coarse media.   Its  drawbacks  include filter clogging and
 shorter filter runs.  Ideally the flow should  be  from coarse to fine, giving
 longer  filter runs.  Upflow filters can not be universally used.   For backwashing
 of an ideal filter, coarse media must remain at the  top,  even after  fluidization.
 This is achieved by density differences between the  two materials.  Denser
 materials  like sand can be of fine size which  settles  at  the bottom.  For the top
 layer,  many lighter materials have been tried.  Anthracite is most commonly used
 as coarse  and light medium, but  was replaced by coal because of its  higher cost.
 A locally  available berry seed is described which resembles anthracite in almost
 all characteristics.

 *Sand filtration, *Flow,  Filtration,  Filters,  Dual media  filters,  Anthracite,
 Backwashing, Design criteria

 *Berry  seed shell
318D

LOOE SEWERAGE AND SEWAGE-TREATMENT SCHEME,

Martin, C.

L. G. Mouchel and Partners,
Bath, Great Britain

Water Pollution Control, Vol. 73, No. 3, p 331-335, 1974.  1 fig.

Since 1955, sewerage facilities in Looe have been planned.  Treatment and disposal
has been a problem,  enlarged by different populations in summer and winter.  Storm
sewerage overflows have also been necessary to complement the combined sewer sys-
tems.  The Cornwall County Council has agreed to make a substantial contribution to
the cost.  Looe is a holiday resort and discharge of sewage into its harbor cannot
continue.  Design and location of the works in an enclosed valley and removal of
sewage pollution are detailed.

*Sewerage, *Combined sewers, *Sewage treatment,  Storm runoff, Pollution abatement,
Sewage districts, Planning, Costs

Cornwall County Council, Great Britain, Treatment methods
                                        388

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 319D

 CHEMICAL AND BIOLOGICAL  QUALITY  OF  SEWAGE EFFLUENTS,

 Hunter, J. V., and Kotalik, T. A.

 Rutgers University, Department of Environmental
 Sciences, New Brunswick, New Jersey

 In:  Conference on Recycling Treated Municipal Wastewater Through Forest
 and Cropland, August  21-24, 1972, The Pennsylvania State University,
 University Park,  p 6-27.   14 tab, 70 ref.

 The chemical and  biological composition of effluents  reflects  the quality
 of the waste water entering the  plant and the changes  that occur during the
 physical, chemical, and  biological  processes in  the plant.  The chemical
 changes that occur during  treatment reflect the  biological removal of
 80-90 percent of  the  organic matter and the production of more oxidized
 organics.  Interest in the removal  of microorganisms  during treatment
 lies mainly in the area  involving the efficiency of pathogen removal.  In
 addition to waste water  bacteria, viruses that have persisted  through
 the plant, large  numbers of protozoa and nematodes can be developed during
 biological treatment.  Interest  here has centered on  the nematodes which
 can ingest pathogens  and thus have  public health significance.  Effluent
 chlorination is largely  for disinfection; however, actual practice may not
 always achieve this end.   Excessive chlorination without dechlorination may
 lead to toxicity  problems  in receiving waters.

 *Waste water treatment,  *Sewage, Effluents, Water quality, Microorganisms,
 Chlorination, Public  health, Biological properties, Chemical properties


 *Effluent composition
 320D

 CHEMICAL AND BIOLOGICAL QUALITY OF MUNICIPAL SLUDGE,

 Peterson, J. R. , Lue-Hing, C., and Zenz, D. R.

 The Metropolitan Sanitary District of Greater Chicago
 Illinois

 In:  Conference on Recycling Treated Municipal Wastewater Through Forest
 and Cropland, August 21-24, 1972, The Pennsylvania State University,
 University Park, p 28-39.  3 tab, 16 ref.

 Sewage sludge is derived from the organic and inorganic matter removed from
waste water at sewage treatment plants.  The nature of sludges depends on
 the waste water sources and the method of waste water treatment.  If waste
 solids are to be evaluated as a soil amendment or as a fertilizer, it is
 important to understand their chemical and biological properties.  A
 comparison of sludge analyses from various treatment plants would be
 confounded by the individual treatment processes; therefore, some of the
more common waste water treatment methods are described.

*Sewage sludge,  *Municipal wastes, Waste water treatment, Chemical properties,
Biological properties,  Sludge treatment, Treatment facilities, Methodology
                                              389

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321D

SITE SELECTION CRITERIA FOR WASTEWATER DISPOSAL —
SOILS AND HYDROGEOLOGIC CONSIDERATIONS,

Parizek, R. R.

The Pennsylvania State University, Department of
Geosciences and The Mineral Conservation Section

In:  Conference on Recycling Treated Municipal Wastewater Through Forest
and Cropland, August 21-24, 1972, The Pennsylvania State University,
University Park, p 95-130.  5 tab, 48 ref.

Site selection criteria for sewage effluent spray irrigation sites are
discussed.  Soils, geology, hydrology, topography, project management,
and other factors are considered to maximize the chances for achieving
a high degree of renovation of waste constituents while at the same time
minimizing secondary environmental problems that can result.  Site con-
ditions suitable and unsuitable for groundwater recharge and reuse are
pointed out as are factors to be considered when designing monitoring
programs necessary to prove the degree of treatment being achieved.
Finally, the importance of the hydrogeologic-soil condition is discussed
for the benefit of administrators who are responsible for defining
environmental procedures to be used for waste water irrigation projects.

*Sites, Irrigation systems, Soil, Geology, Hydrology, Topography,
Project planning, Waste treatment, Recycling, Environmental control

*Spray irrigation
322D

RENOVATION OF MUNICIPAL WASTEWATER THROUGH LAND DISPOSAL BY
SPRAY IRRIGATION,

Kardos, L. T., and Sopper, W. E.

The Pennsylvania State University, Department of
Agronomy

In:  Conference on Recycling Treated Municipal Wastewater Through Forest
and Cropland, August 21-24, 1972, The Pennsylvania State University,
University Park, p 131-145.  8 tab, 3 ref.

In a Penn State project soil solution samples were extracted with suction
lysimeters installed at various depths in the soil profile.  The chemical
quality of the chlorinated secondary treated waste water was monitored by
obtaining a composite of the waste water being applied through the sprinkers
during each irrigation sequence.  Average annual concentrations of various
constituents in the applied waste water are shown for the corn rotation area
for 1963-1970 and are representative of the concentrations in waste water
applied to the other areas.  The extent of renovation of the applied waste
water may be expressed as the change in mean annual concentration of a
particular constituent in the applied waste water when compared with that
found in the soil solution in the suction lysimeters.  The data allow one to
conclude that with appropriate management of nitrogen loads to maximize
utilization by the vegetation and with hydraulic loads adjusted to the soil site
to maximize denitrification it should be possible to recharge water of
drinking water quality into the aquifer below a waste water disposal site.

*Soil disposal fields, *Irrigation systems, Data collections, Evaluation,
Waste disposal, Waste water treatment, Groundwater recharge, Potable water,
Water reuse

*Spray irrigation
                                       390

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323D

RESTORATION OF ACID SPOIL BANKS WITH TREATED SEWAGE SLUDGE,

Lejcher, T. R., and Kunkle, S. H.

United States Department of Agriculture, Forest
Service, Shavmee National Forest, Eastern Region

In:  Conference on Recycling Treated Municipal Wastewater Through Forest and
Cropland, August 21-24, 1972, The Pennsylvania State University,
University Park, p 165-178.  4 tab, 15 ref.

Preliminary results of a strip mined reclamation demonstration project in
Southern Illinois are detailed.  The initial observations indicate that
treated municipal sludge, when applied to the spoil in sufficient amounts,
improves spoil pH, allows establishment of vegetation, and reduces acidity
and concentrations of some of the chemicals in the runoff issuing from
the tract.

*Sludge treatment, *Spoil banks, Municipal wastes, Investigations, Hydrogen
ion concentration, Vegetation establishment, Acidity,  Chemcontrol, Runoff,
Illinois, Strip mines, Sewage sludge
324D

EFFECTS OF LAND DISPOSAL OF WASTEWATERS ON SOIL
PHOSPHORUS RELATIONS,

Hook, J. E., Kardos, L. T., and Sopper, W. E.

The Pennsylvania State University, Department of
Agronomy

In:  Conference on Recycling Treated Municipal Wastewater
Through Forest and Cropland, August 21-24, 1972, The Pennsylvania State
University, University Park, p 179-195.  5 tab, 11 ref.

The movement and fixation of phosphorus, a major constituent of many
waste waters, are important considerations in land disposal systems.  In
the Wastewater Renovation and Conservation Research Project at The
Pennsylvania State University, the fate of phosphorus has been monitored
as treated municipal sewage effluent was applied to cropland and forested
areas.  Ten years of monitoring has indicated a high degree of efficiency
of the soil-plant system to retain and use phosphorus.  The chemical forms
in which the phosphorus was being retained and to what depth in the soil
it was accumulating are described.  It is concluded that when the system
is properly managed most of the added phosphorus remains in the soil at
the disposal site or leaves as a nutrient in harvested crops.

*Phosphorus, Soil disposal fields, Landfills, Monitoring, Sewage effluents,
Municipal wastes, Forests, Farm management, Agronomy, Nutrients

*Land disposal
                                              391

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   32 5D

EFFECT OF LAND DISPOSAL OF WASIEWATER ON EXCHANGEABLE
CATIONS AND OTHER CHEMICAL ELEMENTS IN THE SOIL,

Kardos, L. T., and Sopper, W. E.

The Pennsylvania State University, Department of
Agronomy

In:  Conference on Recycling Treated Municipal Wastewater Through Forest
and Cropland, August 21-24, 1972, The Pennsylvania State University,
University Park, p 196-203.  1 fig, 1 tab, 7 ref.

In a literature review by Ivor K. Edwards (1968) it was indicated that
most of the concern with respect to soil chemical changes was with respect
to changes in the amounts of sodium relative to the other exchangeable
cations in the soil.  In soil samples taken in 1966 Edwards found no
significant change in the status of the exchangeable cations from that
found in 1963 after 48 inches of waste water had been applied.  By 1966
the exchangeable sodium percentage (ESP) in the waste water treated areas
had increased with respect to the control area about 4-fold in the upper
foot and 1.5 to 2-fold in the next four feet.  However, the maximum ESP
value in 1966 was only 3.3 and occurred in the upper foot of the 2-inch
per week treatment area.  The present report extends the information
through the soil sampling in 1969 and also reports on changes in the status
of exchangeable Mn, adsorbed chloride and boron, kjeldahl nitrogen, and
organic matter in the crop rotation area and in some of the forested areas.

*Reviews, *Sampling, *Sodium, Cations, Waste water treatment, Forests,
Rotations, Boron, Chlorides, Nitrogen, Organic matter

*Excharigeable sodium percentage
326D

FACTORS AFFECTING NITRIFICATION-DENITRIFICATION
IN SOILS,

Broadbent, F. E.

California University, Department of Soils and
Plant Nutrition, Davis, California

In:  Conference on Recycling Treated Municipal Wastewater Through Forest
and Cropland, August 21-24, 1972, The Pennsylvania State University,
University Park, p 204-214.  5 tab, 18 ref.

Nitrifying bacteria are present in almost all soils and are active over
a wide range of moisture and temperature conditions.  Variations on the
theme that nitrification and denitrification can and do occur simultaneously
in the same soil lake, pond, or stream, often in locations which are
physically separated by only very short distances, are examined.

*Nitrification, *Denitrification, Soils, Soil chemical properties,
Bacteria
                                                392

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327D

MICROBIAL HAZARDS IN DISPOSING OF WASTEWATER ON SOU.,

Foster, D. H., and Engelbrecht, R. S.

Illinois University, Department of Civil Engineering

In:  Conference on Recycling Treated Municipal Wastewater Through Forest
and Cropland, August 21-24, 1972, The Pennsylvania State University,
University Park, p 217-241.  4 tab, 74 ref.

The public health dangers that may arise from the ultimate disposal of
wastes on land are explored; public apprehension concerning health hazards
are assessed.  This work was undertaken to provide officials with the
type of information that will allow a rational, unemotional, and realistic
assessment of the potential public health problems associated with the
application of waste water to land.  It is shown that the literature is
quite unusual in the paucity of information available on irrigation-caused
epidemics, reflecting either an absence of a problem despite other evidence
indicating that significant quantities of pathogens are placed on soil
by this practice, or that prejudices wnich regard only significant outbreaks
of disease are worthy of investigation.

*Reviews, *Public health, Waste disposal, Irrigation systems, Waste water
treatment, Investigations
328D

VEGETATION RESPONSES TO IRRIGATION WITH TREATED MUNICIPAL
WASTEWATER,

Sopper, W. E., and Kardos, L. T.

The Pennsylvania State University, School of Forest
Resources

In:  Conference on Recycling Treated Municipal Wastewater Through Forest and
Cropland, August 21-24, 1972, The Pennsylvania State University, University
Park, p 242-269.  19 tab, 7 ref.

The Penn State waste water renovation and conservation project is reviewed.
Under this plan, treated municipal sewage effluent has been spray irrigated on
cropland and in forest stands for a 10-year period.  Effluent has been applied
in various amounts ranging from one inch per week to six inches per week and
over various lengths of time ranging from 16 weeks during the growing season on
cropland to the entire 52 weeks in forests.  Rates of application varied from 0.25
to 0.64 inch per week.  Types of crops irrigated with effluent were wheat,  oats,
corn, alfalfa, red clover,  and reed canary grass.  Forested areas irrigated con-
sisted of a mixed hardwood forest, a red pine plantation, and a sparse white
spruce plantation established on an abandoned old field.  It is shown that
sewage effluent irrigation during the past ten years has produced beneficial vege-
tation responses.  Crop yields and tree growth were significantly increased.  In
addition the value of the vegetation as a renovating agent has been demonstrated
to be a vital part of the system.  For year-round operations a combination  of
cropland and forestland provide the greatest flexibility in operating a system
using the living filter concept.

*Irrigation systems, *Sewage effluents, *Waste water treatment, Water reuse,
Investigations, Application techniques, Forests, Farm management, Crops

Spray irrigation


                                                 393

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3 29D

ANATOMICAL AND PHYSICAL PROPERTIES OF RED OAK AND RED
PINE IRRIGATED WITH MUNICIPAL WASTEWATER,

Murphey, W. K., Brlsbin, R. L., Young, W. J., and
Cutter, B. E.

The Pennsylvania State University, School of Forest
Resources

In:  Conference on Recycling Treated Municipal Wastewater Through Forest and
Cropland, August 21-24, 1972, The Pennsylvania State University, University
Park, p 270-285.  6 tab, 24 ref.

The technique of using the forest to ameliorate treated sewage plant effluent
while charging the groundwater can alter the properties of the wood being pro-
duced.  Primarily this study was concerned with the utility of wood grown in
such a forest for pulp wood.  The morphology of the pulp fiber is important
in the strength and conformity of the paper sheet and, therefore, the utility
of the pulp.  Alteration of the dimensions of the pulp fibers by the waste
water were such as to enhance their use as a raw material for paper.  The lack
of a separate control area restricted the findings.   The results of these
experiments indicate that a 1-inch spray enhanced the fiber properties of red
pine.  A 2-inch application of the effluent was beneficial if red oak is used
as a pulp species.

*Forests, *Sewage effluents, Waste disposal, Groundwater recharge, Pulp and
paper industry, Waste water treatment

*Spray irrigation, Pulp fibers
 330D

 DEER  AND  RABBIT RESPONSE  TO  THE  SPRAY  IRRIGATION  OF
 CHLORINATED  SEWAGE  EFFLUENT  ON WILD  LAND,

 Wood,  G.  W.,  Simpson,  D.  W.,  and Dressier,  R.  L.

 The Pennsylvania State University, School  of  Forest
 Resources

 In:   Conference on  Recycling Treated Municipal Wastewater  Through  Forest  and
 Cropland, August 21-24, 1972,  The Pennsylvania State  University, University
 Park,  ? 286-298. 6 tab.

 The  first efforts in evaluating  the  effects of sewage effluent  irrigation treat-
 ment  areas on wild  animals have  been directed toward  the principal game species,
 the cottontail rabbit and the white-tailed deer.   Experimental  results  indicate
 that  the  spray irrigation of chlorinated sewage effluent at  the rate of two
 inches per week appears to have  a favorable influence on the nutritive value  of
 rabbit and deer forages.   Generally  the crude protein,  P,  K, and Mg can be
 expected  to  be raised in  these forages while  the  Ca is  lowered. Reed canary-
 grass, the only forage tested for changes  in  digestibility due  to  treatment,
 showed no significant response with  respect to digestible  dry matter and  pro-
 tein. Studies using the  lead deer technique  to determine  preference for  or
 avoidance of irrigated sites and forage from  these sites indicate  that  the deer
 use  treated  sites at least  as readily  as untreated sites.   During  the winter
 period wild  deer do not avoid the area but appear to  use it  quite  readily for
 resting and  feeding.

 *Evaluation,  *Sewage effluents,  Irrigation systems,  Deer, Wildlife, Forages

 *Rabbits, Spray irrigation,  Forage nutrition


                                               394

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331D

SPRINKLER IRRIGATION SYSTEMS:  DESIGN AND OPERATION
CRITERIA,

Myers, E. A.

The Pennsylvania State University, Department of
Agricultural Engineering

In:  Conference on Recycling Treated Municipal Wastewater Through Forest and
Cropland, August 21-24, 1972, The Pennsylvania State University, University
Park, p 299-308.  1 fig, 2 ref.

Waste water must be applied uniformly over the land surface at the proper rate
in inches per hour and the appropriate amount in inches per week if adequate
renovation is to be expected.  Two areas which greatly affect this judicious
application are proper design and diligent management.  This paper first
lists the variables involved in the design of an irrigation distribution sys-
tem, then discusses a number of factors which affect the choice of specific
value for each variable.  Comments concerning the various management decisions
that must be made when operating the system are included.

*Waste water treatment, Water reuse, Application techniques, Design criteria,
Administration, Irrigation systems, Operations, Land management
   332D

   COST OF  SPRAY  IRRIGATION  FOR WASTE WATER RENOVATION,

   Nesbitt,  J.  B.

   The  Pennsylvania State  University, Department  of
   Civil Engineering

   In:   Conference  on  Recycling Treated Municipal Wastewater Through Forest and
   Cropland,  August 21-24, 1972, The  Pennsylvania State  University,  University
   Park, p  309-314.  2 fig,  1  tab,  1  ref.

   The  net  cost of  effluent  disposal  by spray  irrigation is  dependent upon the
   system required  to  do  a specific job, at a  specific location,  at  a specific
   time, as  well  as the procedures  adopted for management of the  spray field.
   Since different  situations  require different designs  and  management pro-
   cedures,  no  general overall cost information can  be given; however, if certain
   basic assumptions are  made  about design and management, a rough cost estimate
   can  be made.  The figures presented are based  on  work done by  Allender with
   estimated cost of hypothetical systems  carrying flows of  one,  five, and ten
   million  gallons  per day being presented. The  figures are based on certain  assump-
   tions regarding  design  and  management.   These  assumptions may  or  may not fit
   another  specific situation  but they will define the basis of the  estimates
   discussed under  the general areas  of pumping system,  delivery  system, and
   operation.

   *Estimated costs, Irrigation systems,  *Design criteria,  Land  management,
   Operations,  Waste disposal

   Spray irrigation, Pumping system,  Delivery  system
                                             395

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333D

FINANCING MUNICIPAL WASTE WATER TREATMENT FACILITIES,
INCLUDING LAND UTILIZATION SYSTEMS,

Seabrook, B. L.

Environmental Protection Agency, Division of Municipal
Waste Water Programs

In:  Conference on Recycling Treated Municipal Wastewater Through Forest and
Cropland, August 21-24, 1972, The Pennsylvania State University, University
Park, p 315-321.

A continuing need for pollution abatement facilities will always exist after
standards have been achieved to compensate for a growing population, obsoles-
cence, and industrial expansion.  Accomplishing this goal will require the
cooperation of industry and dedication at all levels of government.  Herein
detailed are General Accounting Office (GAO) studies, recent Federal regula-
tions, industrial waste cost recovery guidelines, and clean water bills.

*Pollution abatement, *Regulations, *Investigations, Industrial wastes,
Waste water treatment, Water reuse, Costs, Legislation, Treatment facilities
   334D

   LARGE  WASTEWATER IRRIGATION SYSTEMS:   MUSKEGON COUNTY,
   MICHIGAN  AND  CHICAGO  METROPOLITAN REGION,

   Bauer,  W.  J., and Matsche,  D.  E.

   Bauer  Engineering, Inc.

   In:  Conference  on Recycling Treated  Municipal Wastewater Through  Forest and
   Cropland,  August 21-24,  1972,  The Pennsylvania State  University, University
   Park,  p 322-341.  1 tab.

   The capital and  operating costs  for the  Muskegon County,  Michigan  project and
   for the Chicago  Regional  Wastewater plan are  presented  in a form useful for
   making comparisons with  alternative systems.   Auxiliary uses of land irrigation
   sites  are  described briefly and  the approximate potential revenues from each
   estimated.   The  operating costs  of the system would be  largely, if not en-
   tirely, offset by using  the same  land irrigation site for many other purposes
   in addition to that of renovating the wastewater.   No discussion of the
   benefits  of treating  the  waste water  to  drinking water  standards is presented
   as these  benefits would be  comparable for any other system which would achieve
   the same  end  result.

   *Capital  costs,  Operating costs,  *Irrigation  systems, Project planning,
   Waste  water treatment, Land management,  Water reuse,  Michigan, Illinois
                                                  396

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335D

UTILIZATION OF SPRAY IRRIGATION FOR WASTEWATER DISPOSAL
IN SMALL RESIDENTIAL DEVELOPMENTS,

Williams, T. C.

Williams and Works, Incorporated

In:  Conference on Recycling Treated Municipal Wastewater Through Forest and
Cropland, August 21-24, 1972, The Pennsylvania State University, University
Park, p 362-374.  3 tab.

Williams & Works has designed sixteen pond and irrigation waste water treatment
systems for various governmental units in Michigan.  Designs for the systems
developed include:  two facultative ponds designed to operate either in
parallel or in series at the discretion of the operator; a series of ponds,
consisting of an anaerobic cell followed by at least three facultative cells;
and, mechanically aerated ponds followed by holding ponds.  Performance and
application of these systems are discussed.

*Waste water treatment, *Treatment facilities, Michigan, Irrigation systems,
Ponds, Performance, Design criteria
336D

MUNICIPAL WASTEWATER DISPOSAL ON THE LAND AS AN ALTERNATE
OF OCEAN OUTFALL,

Cowlishaw, W. A., and Roland, F. J.

Bauer Engineering, Incorporated

In:  Conference on Recycling Treated Municipal Wastewater Through Forest and
Cropland, August 21-24, 1972, The Pennsylvania State University, University
Park, p 387-399.  1 tab.

Land treatment as an alternative to ocean disposal of partially treated indus-
trial and municipal wastes is examined.  The specific decision choice for
Falmouth, Massachusetts, is used to highlight the political, engineering, and
resource management factor of decisions that juxtapose land treatment and ocean
disposal.  Analysis indicates that the land disposal-spray irrigation alter-
natives for managing waste water would better serve the needs of the Falmouth
region for its effects in treating waste water; the spray irrigation system
is superior.  Its pollutant removal efficiency clearly exceeds the ocean out-
fall system in its effective removal of pollutants.  In addition to the effi-
ciency and reliability of this system for purifying waste water, it provides
numerous related benefits applicable to the regional water resources.  These
include:  a large percentage return of the treated waste water to the ground-
water resources; flexibility for retrieving and transferring treated water;
provision of usable crops from the irrigation of marginal land for agricultural
purposes; no adverse affect on any marine life or on the recreational value of
the waters; and, an integration of the spray irrigation site with numerous
other publicly funded projects.

*Land management, *Waste disposal, Waste water treatment, Irrigation systems,
Massachusetts, Groundwater recharge, Water pollution control, Project
feasibility
                                               397

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337D

THE ROLE OF LAND TREATMENT OF WASTEWATER IN THE CORPS
OF ENGINEERS WASTEWATER MANAGEMENT PROGRAM,

Johnson, J. F.

United States Army Corps of Engineers, Wastewater
Management Task Force

In:  Conference on Recycling Treated Municipal Wastewater Through Forest and
Cropland, August 21-24, 1972, The Pennsylvania State University, University
Park, p 400-409.  14 ref.

The continuing problems of environmental degradation, particularly that caused
by the discharge of a broad spectrum of pollutants into water courses, have
prompted the Corps of Engineers to assist state, regional, and local govern-
ments in developing waste water management plans toward their solution.  As a
part of its urban studies program, the Corps will develop an array of plans
in consonance with local planning agencies from which the people of the region
could choose the specific plan which best meets their needs.  The role of land
treatment is discussed with particular emphasis upon its relationship to the
planning process, the impacts associated with land disposal, and certain re-
search needs related to land disposal of waste water.

*Project planning, *Land management, *Waste water treatment, Waste disposal,
Project feasibility, Project purposes

U.S. Army Corps of Engineers
338D

RESEARCH NEEDS — LAND DISPOSAL OF MUNICIPAL SEWAGE
WASTES,

Evans, J. 0.

United States Department of Agriculture, Forest Service,
Washington, D.C.

In:  Conference on Recycling Treated Municipal Wastewater Through Forest and
Cropland, August 21-24, 1972, The Pennsylvania State University, University
Park, p 435-442.  1 fig, 6 ref.

A review of topics discussed throughout the conference is presented.  Immediate
research needs with regards to municipal sewage waste disposal are discussed.

*Reviews, Conferences, Research and development, Municipal wastes, Sewage
disposal, Recycling, Soil disposal fields
                                                393

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339D

DEGRADATION OF ORGANIC NITROGENOUS COMPOUNDS BY
PSYCHROPHILIC BACTERIA,

Prasad, D., and Jones, P. H.

Toronto University, Department of Civil Engineering,
Canada

Journal of the Water Pollution Control Federation, Vol. 46, No. 7, p 1686-1691,
July, 1974.  4 fig, 25 ref.

The proteolytic activity and other physiological activity of a mixed bacterial
population adapted to a peptone feed In a laboratory model of the activated
sludge process operating at 2 C has been studied.  The environment was
selective for psychrophiles.  The physiological activity of organisms inhabit-
ing this sludge was considered to be a measure of psychrophilic activity.  Re-
sults indicate that in spite of the apparent metabolic stability of proteins
at low temperatures, the psychrophilic bacteria may use other nitrogenous
compounds such as urea, amino acids, and creatinine as a nitrogen source.  The
comparative degradation rates of various organic compounds by psychrophilic
bacteria at 20 and 2 C indicate that these microorganisms play an important
role in the stabilization of organic matter in the biological waste treatment
processes.  However, their activity at 2 C is lower indicating that biological
waste treatment processes can operate at low temperatures provided sufficient
time is allowed for these organisms to degrade the organic wastes.

*Laboratory tests, *Model studies, *Aerobic bacteria, Activated sludge, Nitrogen
compounds, Microbial degradation, Organic compounds, Biological treatment,
Microorganisms, Temperature

*Waste stabilization, *Psychrophilic activity, *Psychrophiles
340D

BIOLOGICAL TREATMENT OF WASTEWATER USING ALGAE AND
ART EMI A,

McShan, M., Trieff, N. M., and Grajcer, D.

Texas University, Medical Branch, Galveston, Texas

Journal of the Water Pollution Control Federation, Vol. 46, No. 7, p 1742-1750,
July, 1974.  4 fig, 6 tab, 21 ref.

A new system for controlled eutrophication for either waste water or high
organic wastes, such as shrimp ponds, has been researched.  This system
utilizes algae and brine shrimp as its main components.  In such a system
the algae fix the organic and mineral components by using a light source;
the brine shrimp graze on the algae, thus keeping the algae at a constantly
high productivity level.  The choice of brine shrimp is based on their
ability to withstand wide fluctuations in salinity and pH and to remain
there.  The system is adaptable to coastal and inland communities and the
produced brine shrimp could offset some of the costs of the system.

*Waste water treatment, *Biological treatment, *Algae, *Brine shrimp,
Methodology, Operating costs, Biomass
                                             399

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341D

PHOSPHATE REMOVAL FROM DUCK FARM WASTES,

Loehr, R. C., and Johanson, K. J.

Cornell University, Civil and Agricultural Engineering,
Ithaca, New York

Journal of the Water Pollution Control Federation, Vol. 46, No. 7,
p 1692-1714, July, 1974.  10 fig, 7 tab, 6 ref.

Studies of phosphate removal from industrial waste water resulting from
the production of ducks for slaughter are detailed.  These studies were
conducted over a period of two years, initially in the laboratory and subse-
quently in two full-scale field systems.  The most effective chemicals,
predictive relationships for chemical dosages, operating costs, and sludge
production levels were evaluated.

Investigations, *Phosphates, *Industrial wastes, *Waste water treatment,
Farm wastes, Chemicals, Operating costs, Evaluation


*Phosphate removal, Sludge production
  342D

  INJECTING HIGHLY TREATED SEWAGE INTO A DEEP-SAND
  AQUIFER,

  Faust,  S. D., and Vecchioli, J.

  Rutgers, The State University, New Brunswick, New
  Jersey, Department of Environmental Sciences

  Journal of the American Water Works Association, Vol. 66, No. 6, p 371-377,
  June, 1974.  9 fig, 12 tab, 20 ref.

  The growth in population in Nassau County, L.I., over the past twenty years
  has greatly increased the demand for water.  At the same time, urbanization
  has reduced the recharge capacity of the local aquifer.  In an effort to
  solve the problem, a series of.artificial-recharge experiments are being
  carried out which examine the feasibility of injecting reclaimed water into
  a network of wells.  The effect on the resultant water quality is discussed.

  *Water  quality, *Water demand, Urbanization, *Aquifers, *Artificial recharge,
  Feasibility studies, Water reuse, Sewage disposal, Injection wells
                                            400

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343D

EFFLUENT TREATMENT AT PLESSEY CO LTD,

Metal Finishing Journal, Vol. 20, No. 233, p 147-150, June, 1974.

As part of an extensive expansion and modernization program, a new electro-
plating and metal finishing department was recently put into service at The
Plessey Company's headquarters in Ilford, England.  A very wide range of
processes are utilized, including nickel, cadmium, tin, silver, and gold
plating, in addition to the usual vapor and aqueous degreasing, derusting,
and chromate passivation processes.  Fume extraction is provided for all
process tanks, and a temperature controlled ventilation system delivers
filtered air at a controlled rate to the entire plating shop.  This ensures
exceptional cleanliness and pleasant working conditions.

*Treatment facilities, *Industrial plants, Effluents, Automatic control,
Water reuse, Waste water treatment, Polyelectrolytes, Equipment, Metals


Great Britain
     344D

     WASTE TREATMENT PLANT MINIMIZES EFFLUENT,

     Modern Power and Engineering,  Vol.  68,  No.  4,  p 50-51,  83-84,  April,  1974.

     A waste treatment plant at Air Canada's new 500,000 square foot  maintenance
     base provides efficient waste  treatment to  a wide  variety  of liquid effluents
     from cleaning,  stripping,  electroplating, surface  metal finishing,  heat
     treatment,  and machining of aero engine parts.   The system handles  500,000
     pounds of alkalies,  12,000 pounds of cyanides,  4500 pounds of  potassium
     permanganate, and 4000 pounds  of hexavalent chrome each year.  Toxic  chemical
     wastes from the maintenance processes are destroyed,  neutralized, or  extracted
     before the plant's liquid wastes are discharged into the sewage  system.
     Design features and  performance of  the  system  are  detailed.

     *Treatment facilities, *Waste  water treatment,  Industrial  wastes, Waste
     treatment,  Performance, Chemical wastes, Design criteria,  Effluents
                                           401

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345D

CHEMICAL TREATMENT OF LEACHATES FROM SANITARY LANDFILLS,

Ho, S., Boyle, W. C., and Ham, R. K.

Wisconsin University, Department of Civil
and Environmental Engineering

Journal of the Water Pollution Control Federation, Vol. 46, No. 7,
p 1776-1791, July, 1974.  4 fig, 12 tab, 5 ref.

The treatability of leachate by physical-chemical methods has been studied.
The objective of the study was to evaluate the ability of various chemicals
to remove key contaminants from leachate; the approach was to determine the
potential usefulness of each class of chemicals that conceivably could be
used to treat leachate.  The results of this study should not be considered
adequate for design purposes.  Because of variations in leachate composition,
treated water quality objectives, and site limitations, it is expected that
more detailed laboratory testing should be conducted prior to final design
for any given installation.  Results of this study can be used in determining
which of the various treatment schemes available should be examined further.

*Leachate, *Evaluation, Chemical reactions, Water quality, Laboratory tests,
Chemicals, Landfills

*Treatment methods, *Physical-chemical treatment
34 6D

WASTE WATER TREATMENTS INCLUDING OZONATION PROCESS,

Suzuki, S., Mizukami, Y., Kuji, Y., Morikawa, M.,  and
Matsuoka, H.

Mitsubishi Heavy Industries, Head Office

Mitsubishi Denki Giho, Vol. 48, No. 4, p 405-417,  April, 1974.  37 fig,
14 tab, 13 ref.

The characteristics of ozonation are described and various practical treatment
systems presented.  Cases and experimental results of ozonation of phenol and
cyanide containing water for sterilization are reported.  Finally, results at
a tertiary treatment test plant for reuse of sewage water are disclosed.

*0zone, *Waste water treatment, Water purification, Tertiary treatment,
Water reuse

*0zonation, Japan
                                       402

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347D

DEODORIZATION WITH OZONE,

Azuma, K., Doi, K., Morikawa, M., and Kose, M.

Mitsubishi Heavy Industries,
Central Research Laboratory

Mitsubishi Denki Giho, Vol. 48, No. 4, p 431-437, April, 1974.  19 fig,
3 tab, 11 ref.

The theory of deodorization using ozone is outlined and examples of successful
deodorization of exhaust gas and waste water from kraft pulp factories and
marine product processing plants are given.  Similar treatment of exhaust
gas from  food processing works also is discussed.  The possibility of
accelerating the reactions on the surface of activated carbon with ozone in
the case  of mercaptan and hydrogen sulfide in which gas phase oxidation is
too slow  is explored.  Finally, the manufacture of a deodorizing apparatus
consisting of a scrubber with ozone dissolved water as an absorbent is
examined.

*0zone, *Waste water treatment, Industrial wastes, Pulp and paper industry,
Activated carbon, Equipment, Performance


*Deodorization
348D

ELECTROCHEMICAL TREATMENT OF INDUSTRIAL WASTE WATER,

Kuji, Y., Kato, T., and Maeda, M.

Mitsubishi Heavy Industries,
Nagoya Works

Mitsubishi Denki Giho, Vol. 48, No. 4, p 418-423, April, 1974.  16 fig,
6 tab, 4 ref.

In the past a drawback to the electrochemical treatment of industrial waste
water has been the accumulation of scale on the surface of the electrode which
prevents current from flowing, thus stopping the function device.  Mitsubishi
Industries has developed an epochal electrochemical treatment device with
minute gap high speed flow to eliminate this problem.  The features of the
unit and examples of its application are presented.  Basic theory of electro-
chemical flocculation is also explained.

*Equipment, *Electrodes, Electrochemistry, Application techniques, Industrial
wastes, Waste water treatment

Electrochemical flocculation, Japan
                                          403

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 34 9D

BASIC CHARACTERISTICS OF OZONIZERS AND EVALUATION OF
"'MITSUBISHI OZONIZER",

Tabata, N., Yagi, S., Inoue, S., Noda, S., and
Koikawa, S.

Mitsubishi Heavy Industries,
Central Research Laboratory

Mitsubishi Denki Giho, Vol. 48, No. 4, p 424-430, April, 1974.  17 fig,
4 tab, 7 ref.

Ozonizers are recognized effective devices for purification of water and
air.  Their systemizing has become increasingly important with their efficiency
and enlargement of scale.  The basic concept of discharge physics with regards
to ozonizers developed by Mitsubishi Industries is examined.  Fundamental
data regarding ozone generating efficiency are presented; the type and
construction of Mitsubishi ozonizers marketed together with ozone generation
characteristics are included.

*0zone, *Equipment, *Water purification, Data collections, Construction
materials, Performance

*0zonizers, Japan
350D

STUDIES ON THE PURIFICATION OF PETROLEUM REFINERY-
GENERATED EFFLUENTS BY PRESSURE FLOTATION WITH RE-
AGENTS (issledovaniya v oblastl stochnykh vod NPZ meto-
dom reagentnoy napornoy flotatsii),

Sokolov, V. P., and Pusteseleva, Z. I.

Neftepererabotka i Neftekhimiya, No. 2, p 11-13, 1974.  1 fig, 1 tab, 3 ref.

Possibilities of increasing the efficiency of the purification of
petroleum refinery-generated effluents by pressure flotation by means
of reagents, combining flocculation and flotation, were studied in
laboratory and full-scale tests.  The efficiency of the removal of
mechanical impurities and petroleum products from such waste waters
was found to be determined primarily by the formation of metal hydro-
xide floccules which in turn adsorb the petroleum products.  Low-in-
tensity aeration, low flow rate from the flocculator Co the flotator,
and reclrculation of part of the purified effluent at a rate of about
50 percent are required for efficient purification.

*Purification, laboratory tests, *Flocculation, Flotation, Effluents,
Petroleum, Industrial wastes

Pressure Flotation
                                          404

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351D

THE SEWAGE PURIFICATION PLANT AROSA  (DIE ABWASSERRENINIGUNGSANLAGE
AROSA),

Schweizerische Bauzeitung, Vol. 92, No. 22, p 534-536, 1974.  2 fig.

The municipal waste water treatment plant of the ski resort Arosa in
Switzerland, established at 1,618 m over sea level, is described.  The
basins for mechanical separation and biological treatment are built as
one unit, and are then roofed over.  The treatment is conducted in two
pre-treatment stages, two aeration basins, and two biological after-
treatment basins.  The sludge is stabilized by anaerobic digestion at
33 C in two stages with dwell times of 18 and 26 days, respectively.
The sludge is then conditioned by means of polyelectrolyte and pressed
in filter presses.

*Municipal waste water, Waste water treatment, Pre-treatment,
Aeration basins, Biological treatment, Polyelectrolytes

*Sewage purification plants, *Filter press, Switzerland
352D

PLANT EXPANDED FOR ADVANCED WASTE TREATMENT,

Public Works, Vol. 105, No. 7, p 86, July, 1974.

Expansion of the sewage treatment facility at Garland, Texas, will feature
a new and innovative treatment unit in parallel with an existing trickling
filter plant in order to meet the demand for high quality waste effluent.
The proposed additional chemical-physical treatment processes are equali-
zation and aeration, pre-treatment, chemical clarification, recarbonation,
filtration, carbon adsorption, disinfection, sludge dewatering, and scum
disposal.  The process control system is designed for automated plant
operation with all unit systems within the complex either directly con-
trolled or monitored for optimization purposes.

*Sewage treatment, *Treatment facilities, Equipment, Automatic control,
Tertiary treatment, Monitoring, Optimization


Garland, Texas
                                          405

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35 3D

FERRIC CHLORIDE INCREASES WATER PLANT EFFICIENCY,

Hess, A. F., and Schervin, E. J.

Philadelphia Water Department, Torresdale Plant,
Pennsylvania

Public Works, Vol. 105, No. 7, p 77-78, July, 1974.

The Philadelphia Water Department has reduced costs and increased effic-
iency towards planned automation, of water treatment by substituting fer-
ric chloride for alum.  Corrosion of water treatment equipment has been
reduced, the ability to control the pH in the plant effluent has been im-
proved, and the entire operation simplified by converting to the ferric
chloride system at one plant.  The basic ferric chloride treatment system
includes prechlorination and presedimentation, ferric chloride and lime
treatment, flocculation, sedimentation, filtration, and post-chemical
treatment.  217 million gallons of raw water are processed per day at the
Torresdale plant and an average of 80 pounds of ferric chloride are used
for every million gallons.

*Treatment facilities, *Chlorides, *Water treatment, Equipment, Hydrogen ion
concentration, Corrosion control, Operations, Flocculations, Sedimentation,
Filtration, Automation

*Ferric chloride, *Philadelphla, Pennsylvania, Prechlorination, Presedimenta-
tion, Post-chemical treatment, Lime treatment
 354D

 NITRIFICATION IN THE BIOLOGICAL FIXED-FILM ROTATING DISK
 SYSTEM,

 Weng,  C.  -N., and Molof,  A.  H.

 Buck,  Seifert and Jost,  Inc.,  Englewood  Cliffs,  New Jersey

 Journal  of the Water Pollution Control Federation,  Vol.  46,  No.  7,  p  1674-
 1685,  July, 1974.  10 fig,  2 tab,  13 ref.

 The biological fixed-film rotating disk  (BFFRD)  system consists  of  a  series
 of reactors each of which contains a number of closely spaced  rotating ver-
 tical  disks partially submerged in the waste water.   It is  used  as  a  support-
 ing media for biological growth, as a mechanism for aeration,  and as  a means
 of contacting the microorganisms with the  waste water.  Although many advan-
 tages  of this process enhance the possibility of its selection over the
 trickling filter and the activated sludge  process,  additional  basic studies
 are required to provide data for the optimum design and operation, of  waste
 water  plants that oxidize ammonia to nitrate.  This investigative work con-
 centrates on the use of a single rotating  disk in each reactor in a six-stage
 system.   Among conclusions established,  it is shown that the BFFRD  system is
 an efficient treatment unit for nitrification.

 *Biological treatment, Waste water treatment, Nitrification, Equipment,
 Investigations, Efficiencies, Design criteria, Operations


 BFFRD  system
                                          406

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 355D

 OZONATION OF LACTIC ACID FERMENTATION EFFLUENT,

 Walter, R. H., and Sherman, R. M.

 Cornell University, New York State Agriculture Experiment
 Station, Geneva, New York, Department of Food Science

 Journal of the Water Pollution Control Federation, Vol. 46, No. 7,
 p 1800-1803, July, 1974.  2 fig, 1 tab, 10 ref.

 Lactic acid fermentation of cabbage to produce sauerkraut generates a
 strongly buffered, acidic brine that is not conducive to stabilization
 by conventional biological methods.  Because of its high oxidation po-
 tential, rapid reactivity, and almost complete removal of carbon by car-
 bon dioxide evolution, ozone is investigated as a possible treatment
 method for sauerkraut brine.  Preliminary calculations showed that the
 ratio of ozone consumed to chemical oxygen demand reduced in a 72-hour
 period was approximately 2.0.  It is concluded that where ozone genera-
 tors already have been installed in the food processing industry and where
 small batches of refractory effluents are not ammenable to biological
 stabilization, ozonation may be applied as a chemical alternative.

 *0zone, *Waste treatment, Food processing industry, Chemical reactions,
 Fermentation

 Lactic acid, Sauerkraut brine
356D

THE SOLUBILITY PRODUCT OF FERROUS PHOSPHATE,

Chen, P.-J., and Faust, S. D.

Rutgers, The State University, New Brunswick,
New Jersey, Department of Environmental Sciences

Environmental Letters, Vol. 6, No. 4, p 287-296, 1974.  3 fig, 2 tab, 5 ref.

Experimentation on the chemical precipitation of phosphate using ferrous iron
indicates that the solubility product constant of ferrous phosphate can be mea-
sured as 1.07 x 10 to the minus of 29th power at 0.1 M ionic strength and 25C.
The free energy of the dissolution reaction of ferrous phosphate was calculated
as 39.8 Kcal/mole; the free energy of formation of ferrous phosphate was com-
puted as -590.0 Kcal/mole.

*Chemical precipitation, *Laboratory tests, *Phosphates, *Iron,
Solubility, Free energy
                                        407

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35 7D

REVERSE OSMOSIS TREATMENT WITH PREDICTABLE WATER QUALITY,

Luttinger, L. B., and Hoche, G.

The Permutit Co., Paramus, New Jersey

Environmental Science and Technology, Vol. 8, No. 7, p 614-618, July, 1974.

A review of the reverse osmosis process is detailed.  Areas of consideration
include:  treating water contaminants, such as particulate matter, calcium
sulfate, iron and manganese, and colloids; handling contaminants such as
dissolved organics, bacteria and their metabolic products, and silica and
silicates.  Methods for judging the effectiveness of a chemical pre-treatment
step are mentioned.

*Reverse osmosis, *Reviews, Water quality, Waste water treatment,
Contaminants
358D

REGIONAL PLANT SOLVES SMALL-TOWN WASTEWATER PROBLEM,

Cuttica, H. C., and Armstrong, R. A.

Gloversville-Johnstown Sewer Board, New York

The American City, Vol. 89, No. 7, p 31-33, July, 1974.  3 fig.

In 1967, the towns of Gloversville and Johnstown built an interceptor sewer
and treatment plant to purify both the domestic and industrial wastes, having
a population equivalent to about 200,000.  The plant, designed for treatment
of 13 mgd, uses two-stage biological treatment which includes a high-rate
trickling filter and activated sludge.  Wet-air oxidation of sludge is fol-
lowed by dewatering on vacuum filters with final disposal at a landfill.
Hazard warning devices include a Mine Safety Appliance combustible gas detec-
tion cell and two Solvay chlorine leak detectors.  Sewer service charges have
been levied to retire the debt and to operate and maintain the facilities.
The charge amounts to 75 percent of the water bill for residential consumers;
commercial and industrial users pay surcharge on the water bills, depending
upon the strength of their waste.


*Waste water treatment, *Treatment facilities, Interceptor sewers, Biological
treatment, Trickling filters, Activated sludge, Sludge treatment, Dewatering,
Landfills, Equipment, Control systems, Taxes, New York
                                     408

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   359D

   WASTEWATER TREATMENT FOR SMALL COMMUNITIES:   PART ONE,

   Tchobanoglous,  G.

   University of California,  Davis,  California,
   Department of Civil Engineering

   Public Works, Vol.  105,  No.  7, p  61-68,  July,  1974.   2 fig,  9 tab,  12 ref.

   Seventy-five million people  in the United States  are served  by small treatment
   systems of various  design, and the problems  associated with  these plants are
   becoming apparent.   Some of  these general problems are defined, and alterna-
   tive treatment  processes usable by small communities with some design consid-
   erations of major importance for  small plants  are reviewed.   The alternative
   treatment processes are  compared  from an economic standpoint.

   *Treatment facilities,  Operation  and maintenance, Trickling  filters,
   Activated sludge, Oxidation  lagoons, Irrigation,  Overland flow, In-
   filtration, Operations,  Performance, Design  criteria, Equipment

   Imhoff tank, Biological  rotating  disks
360D

EXPERIMENTAL STUDIES ON A KINETIC MODEL FOR DESIGN
AND OPERATION OF ACTIVATED SLUDGE PROCESSES,

Gaudy, A. F. , Jr., and Srinivasaraghaven, P..

Oklahoma State University, Bioengineering Laboratories,
Stillwater, Oklahoma, School of Civil Engineering

Biotechnology and Bioengineering, Vol. 16, No. 6, p 723-738, June, 1974.
6 fig, 5 tab, 16 ref.

Previous laboratory experimentation has shown that the classical theory
developed for continuous growth of pure cultures in completely mixed
aerobic systems in which the recycle cell concentration factor is a selec-
table system constant, did not provide a suitable model for the hetero-
geneous populations of the activated sludge process.  Another model was
derived in which the recycle cell concentration was employed as a system
constant and computational analysis was performed.  Laboratory pilot plant
experimentation was undertaken in order to determine whether a steady state
in aerator biological solids concentration and substrate concentration
could be approached under this mode of operation.  It was found that the
model approached the steady state condition with heterogeneous populations
more closely than did the classical model, and the high degree of treatment
efficiency predicted by the model was demonstrated experimentally.

*Laboratory tests, *Growth rates, Activated sludge, Model studies, Pilot
plants, Aerobic conditions, Cultures, Cultural control, Efficiencies,
Waste treatment

Recycle cell concentration
                                           409

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36 ID

OPERATING A SMALL CONTACT STABILIZATION PLANT,

Black, R. D., and Anderson, W. C.

Weedsport Department of Public Works, New York

Water and Sewage Works, Vol. 121, No. 6, p 78-81, June, 1974.   2 ref.

Operating experiences at the Weedsport, New York waste water treatment
plant are recounted.  The problems encountered and the solutions
implemented are offered as suggestions for the design, construction, and
operation of other such treatment facilities.   A description of the
community and the waste water treatment plant is detailed with specific
mention of the aeration, solids handling, and chlorination steps in the
plant.  Equipment purchasing and costs are mentioned and the performance
of the facility is indicated.

*Waste water treatment, *Treatment facilities, Design criteria, Equipment,
Aeration, Chlorination, Solid wastes, Performance, Economics
362D

DECONTAMINATE WATER BEFORE IT GETS INTO THE GROUND,

Miller, D. W.

Geraghty and Miller, Consulting Ground Water Geologists

Water and Sewage Works, Vol. 121, No. 6, p 51-53, June, 1974.

Some of the principles governing movement of a water body containing
pollutants within the groundwater system are reviewed.  The principal
factors involved in the difficulty of monitoring the safety of groundwater
resources in any particular region and of providing a means for adequate
warning against use of waters that may be harmful are presented.  The
author advocates increased research directed toward developing new methods
for the correction of groundwater contamination problems; the development
of new strategies directed toward the control of potential future problems;
and a greater appreciation of the importance of protecting this resource
from water quality degradation.

*Groundwater, *Groundwater movement, Water pollution sources, Water
pollution effects, Monitoring, Research and development, Aquifers, Water
quality control, Water pollution control
                                       410

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363D

ORGANICS,

Mineat, R. A., and Pagoria, P. S.

Tennessee  University,
Knoxvllle, Tennessee, Department of Civil Engineering

Journal of the Water Pollution Control Federation, Vol. 46, No. 6,
p 1058-1100, June, 1974.  2 tab, 434 ref.

A review of the 1973 literature concerning various organic material is
grouped into several categories.  These include oxygen demand and organic
carbon, detergents and surfactants, oils and greases, pesticides, and
other organic species.

*Reviews, *0rganic matter, Detergents, Surfactants, Oil, Pesticides

Oxygen demand, Organic carbon, Grease
364D

ANAEROBIC PROCESSES,

Ghosh, S., and Conrad, J. R.

Institute of Gas Technology, Chicago, Illinois

Journal of the Water Pollution Control Federation, Vol. 46, No. 6,
p 1145-1161, June, 1974.  98 ref.

An increasing interest in investigating the microbiology and biochemistry
of some of the non-methanogenic processes has been indicated through a
review of the 1973 literature.  Specifically, significant advances were
made to elucidate the mechanism of the following reactions:  cellulose
degradation; reduction of inorganic and organic sulfur compounds; photo-
synthetic and non-photosynthetic hydrogen production; anaerobic nitrogen
fixation; and anaerobic denitrification.  In the areas of process develop-
ment and process application, much effort had been directed toward the
development of anaerobic digestion-based systems capable of reclaiming the
intrinsic energy content of municipal, industrial, and agricultural liquid
and solid wastes.

*Reviews, *Anaerobic conditions, *Anaerobic digestion, Nitrogen fixation,
Denitrification, Waste treatment, Liquid wastes, Energy

Cellulose degradation, Sulfur compound reduction, Photosynthetic
hydrogen production
                                          411

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365D

DETERGENTS,

Banerji, S. K.

MCA Engineering Corporation, Baltimore, Maryland

Journal of the Water Pollution Control Federation, Vol. 46, No. 6,
p 1140-1145, June, 1974.  26 ref.

A review of the literature reported in 1973 indicates a continued interest
in detergent builder compounds.  Major topics include the control of
phosphorus, environmental effects from the use of nitrilotriacetic acid
(NTA); the influence on the major cation mobilization by STPP, NTA, or
ethylenediaminetetraacetic acid (EDTA); aquatic effects such as fertility
and toxicity from exposure to surfactants; microbial metabolism of alkyl-
benzene sulfonate (ABS); blodegradation and recovery of nonionic surfac-
tants; and, the biodegradation of cationic surfactants in activated sludge
pilot plants.

*Reviews, *Detergents, Phosphorus, Environmental effects, Nitrilotriacetic
acid, Aquatic environment, Toxicity, Surfactants, Biodegradation, Pilot plants

EDTA, ABS, STPP, Cation mobilization
366D

PHYSICO-CHEMICAL AND TERTIARY TREATMENT,

Evers, D.

D. Evers and Associates, Lichfield

Water and Waste Treatment, Vol. 17, No. 5, p 13-14, May, 1974.

Through a simple physico-chemical treatment, dyes of all types can be
removed successfully from water along with the elimination of remaining
substances.  Gaschromatograms of the compounds taken from the water
treated prove the effectiveness of this treatment.  The purification effect
can be controlled and continued until drinking water quality is reached.
The process is insensitive to disinfectants, temperature, and intermittent
discharge.  There is no feed-in phase, and the water may be recirculated.
Cost is very low, and the space needed amounts to approximately 6x3x3 m for
a 5 cu m/hr. unit.  The sludge produced is firm and may be further processed
to obtain scatter manure with no odor.  No long pipe-lines are needed.
Minimal attendence is required.

*Tertiary treatment, *Water purification, *Effluent control, Water
pollution, Dyes, Sewage treatment

Physico-chemical treatment
                                        412

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36 7D

CHEMICAL AND TERTIARY TREATMENT UNITS,

Inka Division, A. Johnson Construction Company Limited,
Scotland

Water and Waste Treatment, Vol. 17, No. 5, p 20, May, 1974.

Various systems have been developed to utilize chemical and tertiary treatment
for waste water purification by the Inka Division of the northern Scotland
company.  The treatment process has three main steps, which are:  1)
mechanical operations of screening and grit removal, 2) biological acti-
vated sludge treatment followed by settlement, 3) and chemical dosing,
flocculatlon and precipitation.  The separated sludges are fed into aerobic
digesters before sludge processing.  This form of treatment will generally
produce an effluent quality better than 10/10 standard with 90 to 95 percent
total removal of phosphorus.  Currently being used by the A. Johnson Con-
struction Company is a biological sewage treatment plant with tertiary
treatment and nutrient reduction.  The effluent discharged into a small
stream necessitated a high effluent quality.  The nutrient removal prevents
unwanted algal growth.

*Waste water treatment, *Tertiary treatment, *Nutrient removal, Sludge
treatment,  Flocculation, Precipitation, Sewage treatment, Water pollution

Chemical dosing
368D

NITROGEN MOVEMENT RESULTING FROM SURFACE APPLICATION
OF LIQUID SEWAGE SLUDGE,

King, L. D., and Morris, H. D.

University of Georgia Agricultural Experimental Station,
College Station, Athens, Georgia

Journal of Environmental Quality, Vol. 3, No. 3, p 238-243, July-September,
1974.  5 fig, 6 tab, 15 ref.

There is increased interest in applying liquid sewage sludge to soil both
as a disposal method and as a method to increase crop production.  One of
the limiting factors on the rate at which sewage sludge can be applied to
soil is the speed at which Inorganic N is formed and the fate of that
inorganic N.  A greenhouse lysimeter study was initiated in order to quantify
some of the sinks into which nitrogen from sludge applications might move.
It was found that NH4-N in the liquid fraction of the sludge was susceptible
to volatilization, more so on bare soil than on sod.  Leaching losses of
N03-N were increased by increasing water rates and decreased by the presence
of grass.  A. Grass-F treatment, imposed in an effort to increase denitrifica-
tion, did not reduce leaching loss of N03-N.

*Sewage disposal, *Crop production, *Denitrification, Leaching,. Nitrogen

*Soil application, *Land disposal
                                        413

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36 9D

HANDLING, PREPARATION, AND APPLICATION OF
POLYELECTROLYTES,

Elphick, A., and Lake, L. J.

Effluent and Water Treatment Journal, Vol. 14, No. 5, p 378-382, July, 1974.
3 fig, 5 ref.

A wide range of polyelectrolytes and polymer emulsions are available for use
in Great Britain.   Differing compounds were examined for their feedability,
ease of mixing with water, and solubility, as well as parameters for the
resulting solution such as viscosity and pH.  Natural polyelectrolytes in-
clude the alginates, modified starches and cellulosic materials.  Synthetic
polyelectrolytes are usually based on polyacrylamide and its co-polymers
with polyacrylic acid.  The function of polyelectrolytes in industry and
waste water treatment include clarification aids in potable water and effluent
treatment, conditioners in sewage and other sludge thickening, and filter
aids in processed materials.  In all cases, the polyelectrolytes act to bring
about a cohesion between particles in the water.  Most recently, the intro-
duction of liquid polyelectrolytes in the form of emulsions has occurred.
Their application and preparation techniques include aging, metering, and
dilution, the same steps necessary for preparation of previously used
solutions made from powder.

*Polyelectrolytes, *Sewage treatment, *Polymers, *Emulsions, Fillers,
Cohesion

Great Britain, Liquid polyelectrolytes
 370D

 COLUMNS REPRESENTING MOUND-TYPE DISPOSAL SYSTEMS FOR
 SEPTIC TANK EFFLUENT:  II.  NUTRIENT TRANSFORMATIONS
 AND BACTERIAL POPULATIONS,

 Magdoff, E. R., Keeney, D. R., Bouma, J., and Ziebell, W. A.

 Wisconsin University, Madison, Wisconsin,
 Soil Science Department

 Journal of Environmental Quality, Vol. 3, No. 3, p 228-234, July-September,
 1974.  6 fig, 4 tab, 15 ref.

 The purification of liquid wastes is associated with health problems
 relating to the occurrence of pathogenic bacteria and viruses or a high
 nitrate concentration in potable waters, and eutrophication of ground and
 surface waters due to nutrients from the effluents.  Carbon, nitrogen, and
 phosphorus transformations and bacterial populations were studied in columns
 representing a mound disposal system.  Total nitrogen, total phosphorus,
 and the chemical oxygen demand (COD) of the influent (septic tank
 effluent) averaged 41, 21, and 257 mg/liter, respectively.  It was concluded that soil
 materials, arranged as 60 cm of fill over 30 cm of silt loam to simulate a
 mound, considerably improved the quality of percolating septic tank effluent.
 Techniques for applications to remove COD, nitrogen, and phosphorus are
 currently being developed both in field and laboratory experiments.

 *Septic tanks, *Effluents, *Liquid wastes, Potable waters, Eutrophication,
 Public health, Nitrogen, Phosphorus, Chemical oxygen demand, Soil,
 Laboratory experiments, Bacteria

 Mound-type disposal systems
                                          414

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371D

DESIGN OF A MULTILAYER FILTER FOR USE IN THE WATER
TREATMENT INDUSTRIES,

Fox, G. T. J., and Metcalf, S. M.

Imperial College, London, Great Britain,
Department of Public Health Engineering

Filtration and Separation, Vol. 11, No. 4, p 383-386, July/August, 1974.
2 fig, 1 tab, 4 ref.

The inherent size grading resulting from backwashing a bed of material of
the same density but slightly differing sizes is a major problem in the
improvement of water filters of the "packed bed" variety.  It is practically
infeasible to obtain large quantities of single sized grains, and a size
gradation of small-to-large in the direction of filtration is found in a
sand bed after backwashing.  The effect of this on the operating efficiency
of such a water filter is discussed, and the way in which these problems
can be overcome by the use of a multiplicity of layers composed of materials
of differing sizes and densities is outlined.  While a filter with a gradation
of large-to-small in the direction of filtration, produced by using more than
one material, may be more efficient, it is also much more difficult to de-
sign.  The conclusion reached was that the best method of design is one
which uses maximum removal by the center layer.  Possible flow rates are also
discussed.

*Water treatment, *Backwashing, *Filters, Filtration

*Multilayer filters, Grain size
372D

STUDY OF THE REMOVAL OF COPPER ION AND CADMIUM.
ION FROM WASTE WATER BY FLOTATION METHOD UTI-
LIZING XANTHATE,

Hasebe, S., Sato, H., and Sugata, Y.

Department of Mining and Civil Engineering,
Iwate University

Report on Technology of Iwate University, No. 26, p 41-46,
November, 1973.  9 fig, 1 tab, 13 ref.

A small number of cadium and copper ions are occasionally contained
together with ferric and zinc ions in waste water.  Research was done
to investigate the removal of copper and cadium ions from waste water
by flotation using xanthate.  Copper ion was found to be easily removed
as copper xanthate by adding about 2 or 3 equivalents of methyl or ethyl
xanthate with cadium ion being removable by the adding of 2 or 3 equiva-
lents of butyl or amyl xanthate.  The removal of the cadium or copper
ions was influenced by the peripheral speed of the impeller; the scum
being stabilized by adding frother such as methyl iso-butyl carbinol.
Copper or cadium ions were reduced by the secondary treatment method,
in artificial waste water, from 10 mg/liter of copper and 1 mg/liter of
cadium ions to less than 0.1 mg/liter each, and it was determined that
the co-existence of zinc and ferrous ions prevented the removal of that
copper and cadium of xanthate salt from the waste water.  It is required
that ferric ions be turned into ferric hydroxide by adding calcium car-
bonate, because xanthate ion is oxidized by ferric ion, when ferric ion
is contained in waste water.

*Copper, *Cadmium, *Waste water treatment, *Flotation, Zinc, Water
pollution

*Xanthate, *Calcium carbonate, Ferric ions
                                   415

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373D

A BASIC STUDY OF BIOLOGICAL NITRIFICATION AND
DENITRIFICATION,

Yamanouchi, T., and Sugata, K.

Mitsubishi Heavy Industries Technical Review, Vol. 11, No. 3, p 87-95,
May, 1974.  13 fig, 11 ref.

Advanced ways of treating waste water and sewage are increasingly in
demand, because of the phenomenon of eutrophication.  The total re-
moval of nitrogen is the most significant problem facing these treat-
ments for nutrient removal.  Biological nitrification and denitrifica-
tion systems are investigated as nitrogen removal methods.  The study
is summarized by:  biological nitrification and denitrification being
subjected to such environmental conditions as pH value and temperature,
nitrifying bacteria and denitrifying bacteria being domesticated easily,
and these systems considered as a total biological treatment systems
would be the most effective method.

*Nitrification, *Denitrificatlon, *Waste water treatment, Nitrogen,
Nutrients, Eutrophication, Biological treatment

*Biological nitrification, Biological denitrification
374D

MIXING AND TRANSPORT,

Ditmars, J. D.

Delaware University, Newark, Delaware,
Department of Civil Engineering and
College of Marine Studies

Journal of the Water Pollution Control Federation, Vol. 46, No. 6,
p 1991-1604, June, 1974.  126 ref.

Dispersion and mixing in open-channel flow was reviewed by Fisher.
The theoretical bases for the one-dimensional, cross-sectionally
averaged concentration equation and the longitudinal dispersion co-
efficient were also investigated.  Lab and field data were provided
for both vertical and transverse turbulent mixing coefficients.  The
effect of sinuous channel geometry on longitudinal dispersion was ex-
plored experimentally along with the relationships between the bulk
flow and channel geometry parameters and the longitudinal dispersion
coefficient.  Using lab and natural stream data, the dispersion and
decrease with increases in bend length and mean depth.  Solutions
were found to the convective-diffusion equation for point and line
sources in rivers.  Integral transform techniques were used to arrive
at the solution, and accounted for the presence of surface, bottom,
and bank boundaries, assuming constant values for the longitudinal
vertical, and lateral turbulent diffusion coefficient, and for the
longitudinal current.

*Mixing, *Transport, Streams, Rivers, Lakes, Reservoirs, Bays,
Estuaries, Coastal areas, Dispersion, Open channel flow, Current,
Water pollution, Waste water treatment, Jets, Plumes

Sinuous channel geometry, Longitudinal dispersion, Transverse turbulent
diffusion, Dissolved oxygen
                                    416

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375D

TREATMENT FOR OILY WASTE WATER USING
MAGNETIC POWDER,

Water Purification and Liquid Waste Treatment, Vol. 15, No. 7,
p 37-44, July, 1974.  9 fig, 1 tab, 3 ref.

Chemical coagulation processes are often used to treat waste water
that contains fine oil droplets.  When these processes are performed
by the addition of fine magnetic powder, suspended in oily waste
water layers, the produced flocks containing oil droplets include
these magnetic powders.  Coagulated flocks containing oil droplets,
metal hydroxide and magnetic powder are tightened and sedimented in
magnetic field.  These sediments are easily removed with the moving
of the magnetic belt or rotation of the magnetic drum.

*Waste water treatment, *0ily water, *Coagulation, Water pollution

*Magnetic powder
376D

THE THREE SLUDGE SYSTEM FOR NITROGEN AND
PHOSPHORUS REMOVAL,

Mulbarger, M. C.

Office of Research and Monitoring, Environmental
Protection Agency, Advanced Waste Treatment Research
Laboratory

National Technical Information Service Report PB-213 778, April, 1972.
57 p, 16 fig, 29 ref.

The three sludge (carbon removal, nitrification and denitrification)
system with alum added was evaluated for the effectiveness of phosphorus
and nitrogen removal.  Eight months of performance data from a pilot
plant was obtained.  The data included measurements of pH, temperature,
substrate concentration, COD removal, phosphorus removal, nitrification
and nitrogen removal, solids production, solids characteristics, effluent
suspended solids, nitrification inhibition, alkalinity losses, dissolved
solids introduction, aeration and mixing requirements, chemical addition,
clarifiers, solids wasting, spray water, disinfection, instrumentation, and
costs.  The following conclusions were made: the three sludge system is
preferred over other biological nitrogen removal systems; nitrification
and denitrification are temperature dependent and are pH dependent in non-
acclimated cultures; phosphorus removal to a high level can be easily
obtained with split alum addition and pH optimization; good removals of
soluble COD and carbonaceous BOD5 are achieved with two-stage nitrifi-
cation system; negative or small solids production values occur in the
nitrification system and the values are temperature dependent; and alka-
linity dependent addition for the pH optimization should be automated to
insure maximum system dependability.

*Waste water treatment, *Phosphorus, *Nitrogen, Activated sludge,
Water pollution treatment, Waste treatment, Sewage treatment, Teri-
ary treatment

*Phosphorus removal, *Nitrogen removal, *Three sludge system
                                     417

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405D

AEROBIC DIGESTION OF EXTRACELLULAR MICROBIAL
POLYSACCARIDES,

Obayashi, A. W. and Gaudy, A. F.

Oklahoma State University, Stillwater, Oklahoma,
School of Civil Engineering, Bioenvironmental
Engineering Laboratories

OWRR Official Research Report A-035-OKLA, May, 1972.  32 p, 5 fig, 2 tab,
30 ref.

The extended aeration, or total oxidation, sludge process is based on the
premise that the increase in biological solids resulting from metabolism
of the incoming waste is balanced by the decrease in biological solids due
to their aerobic digestion.  The question about this method is whether all
the organic constituents of the cell, such as those in the cytoplasm, the
walls and membrane and the capsular slime layer, can be metabolized and con-
verted to carbon dioxide.  The slime layer is usually complex heteropoly-
saccharides.  This investigation was made to determine whether extracellular
heteropolysaccharides of microorganisms can be used as sources of organic
carbon for the growth of other microorganisms.  The results show that
extracellular polysaccharide cannot be considered biologically inert material
and that it can metabolized.  These results support the idea of total oxida-
tion of biological solids.

*0xidation, *Microorganisms, *Sludge, *Waste treatment, Aerobic treatment,
Aeration, Bacteria, Organic matter

Total oxidation, Extended aeration, Polysaccharides, Slime layer
406D

PROBLEM DEFINITION STUDY:  EVALUATION OF HEALTH AND
HYGIENE ASPECTS OF LAND DISPOSAL OF WASTEWATER AT
MILITARY INSTALLATIONS,

Sorber, C. A., Schaub, S. A. and Guter, K. J.

United States Army Medical Environmental Engineering Research Unit Report
Number 73-02, August, 1972.  32 p, 72 ref, 5 append.

The most important variables in the health and hygiene aspects of waste water
treatment by land disposal are:  the ultimate use of the contaminated waste
water; the method of  application; and the degree of pre-treatment.  These
variables have physical, biological, and chemical effects.  The United States
Army studied waste treatment by land disposal and drew the following conclu-
sions:  many detrimental health and hygiene effects of land disposal would
be reduced by proper waste water pretreatment; biological contamination of
groundwater could be  avoided by choosing a disposal site with five to ten
feet of continuous fine soil.  There exists a significant probability of
inhaling pathogenic aerosals near a spray irrigation site; chemical components
of sewage can increase the viability of bacteria, virus and protozoans in
aerosols; pathogenic  microorganisms may survive longer in sewage aerosols and
in soil than common indicator organisms.  More mosquito breeding is an effect
of ponding in disposal areas; and, if land disposal is the first step in a water
recycle program, total dissolved solids, sodium and nitrate ion build-up in
the groundwater can be problems.

*Waste water disposal, *Aerosols, Pathogenic bacteria, Microorganisms,
Pre-treatment, Public health, Waste water treatment, Waste disposal,
Application methods,  Bioindicators

Land disposal, United States Army
                                          432

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407D

MIXING IN ANAEROBIC DIGESTION,

Verhoff, F. H., Tenney, M. W. and Echelberger, W. F.

Biotechnology and Bioengineering, Vol. 16, No. 6, p 757-770, June, 1974.
6 fig, 4 ref.

The efficiency of this technique is highly influenced by the mixing of the
anaerobic digester.  Hydraulic dead zones are hazardous to the reaction
kinetics involved in anaerobic digestion.  An analysis of the significance
of thermal fluid movement in the digester to those caused by fluid inflow
and outflow is discussed.  The principles are exemplified in a digester at
the South Bend Wastewater Treatment Plant, South Bend, Indiana.  The
theoretical estimations are confirmed by experimental measurements.  Differ-
ent types of optimization can be achieved on this operation.  One example is
the application of this mixing to gas lift mixers.

*Anaerobic digestion, *Mixing, Thermal properties, Hydraulics, Waste water
treatment, Flow


Hydraulic dead zones, Reaction kinetics, Fluid inflow and outflow, Thermal
fluid movement
408D

APPLICATION OF MICRO-CONTROLLERS MELMIC 100 TO WATER
TREATMENT FACILITIES,

Moriguchi, Z.

Mitsubishi Denki Giho, Vol. 48, No. 6, p 750-765, June 1974.  11 fig, 3 ref.

Complication of city water service and sewage treatment facilities has in-
creased with the upgrading of public welfare and municipal development.
Electric equipment makes it necessary to emphasize the reliability and ease
of operations.  Micro-controllers MELMIC 100 has been developed and manu-
factured as a static sequence controller with arithmetic counting apparatus.
This process promotes the serviceability of the facility.  Examples of
application are presented for consideration of water treatment systems.

*Water treatment, *Water supply, *Sewage treatment, Water quality control

*Micro-Controllers MELMIC 100
                                           433

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409D

TREAT WASTEWATER LIKE DOWNTOWN TRAFFIC,

Martin, R. J.

The American City, Vol. 89, No. 8, p 61-62, August, 1974.

A 340,000 gpd waste water treatment plant in Sherburne, New York is a
single-stage, high-rate trickling filter operation that has held costs to
a minimum, obtained quality results, and reduces labor requirements by
installing a process controller.  All steps involved in handling sludge or
supernatant are started and stopped by a Tenor preset controller system.
The program interval is controlled by a timer that can be set from one
hour to 60 hours.  Any malfunction will either return all units to the "at
rest" mode or permit the program to continue, if it is safe to do so.  The
cost of the complete system is around $25,000.

*Automatic control, *Control systems, *Waste water treatment, Equipment,
Sludge treatment, Costs, Performance
410D

EXTENSIONS TO HANNINGFIELD WORKS OF ESSEX WATER COMPANY,

Water Service, Vol. 78, No. 940, p 190-196, June, 1974.  6 fig.

The extensions to the Hanningfield Reservoir, Essex, Great Britain, were
opened on May 10, 1974.  The present situation, the new works, and future
plans are discussed.  Figures and a schedule of technical data are included.
The new extensions are:  effluent pipelines; aqueducts; a pilot plant;
vertical flow tanks; accelerators; a chemical house; a chemical plant;
electrical and control stations; a carbon dioxide generator; gravity filters;
pumping stations; filtered water tanks; wash water tanks; and, roads and
drains.  The new works cost approximately four million pounds and are the
first two phases of Stage 1 of works required to deal with the additional
yield of 12 mgd from the Ely-Ouse-Essex scheme at Hanningfield.

*Water supply, *Reservoirs, *Water supply development, *Facilities,
Pipelines, Pumps, Filters, Chemicals, Equipment, Costs

Great Britain, Water works, Essex
                                       434

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411D

THEY'RE FOREVER BLOWING BUBBLES,

Compressed Air, Vol. 79, No. 8, p 10-11, August, 1974.

One of the simplest and most effective air diffusers for sewage treatment is
the so-called inverted reservoir type developed and manufactured by Sanitaire
Water Pollution Control Corporation of Milwaukee, Wisconsin.   In this mech-
anism air passes from a header into the diffuser with exit ports being two
rows of holes, one on each side of the air reservoir.  Below the diffuser's
open base, a V-shaped deflector plate directs the flow of waste liquor up
along its outer wall.  As the air comes out, it is sheared into relatively
small bubbles and then well distributed throughout the waste water in the
basin.  Determinations influencing the design of the Sanitaire diffuser are
outlined.

*Equipment, Design criteria, Waste water treatment, Sewage treatment,
Bubbles, Liquid wastes

*Air diffusers
412D

VIRUS REMOVAL BY DIATOMACEOUS EARTH FILTRATION,

Chaudhuri, M., Amirhor, P., and Engelbrecht, R, S.

Indian Institute of Technology, Kanpur, India,
Department of Civil Engineering

Journal of the Environmental Engineering Division, Vol. 100, No. EE4, p 937-953,
August, 1974.  9 fig, 1 tab, 34 ref.

Diatomaceous earth filters have been increasingly employed by municipalities
for water filtration, and their effectiveness in removing viruses is eval-
uated.  Previous research in this area is reviewed.  Methods and materials
used in the experimental study of the effectiveness of DE Filter media
(flux-calcined) in virus removal, the ability of polyelectrolyte coated DE
filter media to remove viruses, and the influence of certain operational
parameters on virus removal by DE filtration were discussed and results
analyzed.  It is concluded that DE filter media coated with water soluble
cationic polyelectrolyte can efficiently remove virus particles.

*Diatomaceous earth, *Viruses, *Filters, *Filtration, Potable water, Water
treatment, Evaluation

Cationic polyelectrolyte, Flux calcined
                                      435

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417D

SAFE TO DRINK TREATED WASTEWATER?,

Civil Engineering-ASCE, Vol. 44, No. 8, p 63-64, August, 1974.

The problems associated with direct reuse of water for domestic purposes are
discussed.  The bases for deciding whether or not to reuse treated waste
water focus on cost and relative risk.  To decide the risk factor one must
find biologically and chemically what and how much is in the water and then
decide how safe the water is.  Pollutants of concern when estimating risk
include:  viruses; pesticides that might be carcinogenic; inorganic chemicals
such as arsenic, asbestos, selenium; organometallic forms of metals that
become concentrated as they move up the food chain; enteric organisms; spore
formers such as tetanus and borulinum; and ova and cysts.  Two particular ways
of treating waste water were particularly interesting:  granular and diato-
maceous filters when combined with chemicals such as alum and polyelectrolytes
can do a good job of removing small asbestos fibers and the usual particles
such as bacteria and viruses; and filtration of waste water through activated,
granular carbon can be very effective in removing dissolved chemical pollutants.

*Water reuse, *Domestic water, *Water quality, *Costs, Reclaimed water,

Recirculated water, Activated carbon, Pesticides, Chemicals, Metals, Viruses,
Waste water treatment, Filtration
418D

BIOLOGICAL FILTERS,

Bunch, R. L.

Environmental Protection Agency, Cincinnati,  Ohio,
Advanced Waste Treatment Research Laboratory

Journal of the Water Pollution Control Federation, Vol. 46, No. 6, p 1121-1123,
June, 1974.  25 ref.

A review of the current literature demonstrates that the emphasis last year
was on upgrading trickling filters to meet the more stringent effluent
requirements and to remove nutrients before discharge.  Biological filters
were used for nitrification and denitrification.  Expressions for the perfor-
mance of trickling filters were developed.  The use of corrugated polyethylene
sheets and PVC grids as packing for a biofilter were studied.  Industrial
applications for trickling filters were found.  Mathematical models of the
rotating biological disk process were formulated, with equations for both the
dynamic and steady-state models.

*Trlckling filters, *Filters, *Water quality, *Reviews, Industries,
Model studies, Water Pollution Control Federation, Nitrogen, Plastics


Rotating biological disk process
                                        438

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419D

WATER ECONOMY ANNUAL REPORT-RHEINLAND PALATINATE,

Wasser und Boden, Vol. 26, No. 6/7, p 202-207, 1974.  4 fig.

The sludge purification and incineration plant of the city of Kaiserlautern,
Federal Republic of Germany, is described.  The purification plant serves a
population of about 120,000 plus a population equivalent of 130,000 from
commerce and industry.  The purification plant yields daily 430 cu m fresh
sludge which first goes to the sludge digestion station.  After a residence
time of 20 days the sludge is dewatered by added flocculants which reduce the
sludge volume to one fifth of the original volume.  The dewatered sludge is
continuously supplied to the incinerator with a capacity of 7.5 ton/hour.
The ash, at a rate of 8 cu m/day, is transported to containers and tipped.
The flue gas stack has a height of 50 m, the flue gases are cleaned with
water from the post purification basin.  The scrubbing water is then returned
to the purification plant.  Total expenditures for the incinerator amounted
to 4 mill. DM.  The biological sewage sludge digestion plant in Lambsheim/
Palatinate, Federal Republic of Germany is also described.  The essential
part of the plant is bio-reactor made of heat insulated steel on concrete
foundation.  It has a diameter of 5.55 m and a height of 4.30 m.  The resi-
dence of the dewatered sludge is about 14 days.  The sludge passes through
six zones of different temperatures.  For the zone with the highest temperature
of 70 to 75 C the sludge needs two to three days to pass through.  The oxygen
is supplied according to need.

*Sewage treatment, *Facilities, Sludge treatment, Biological treatment, Costs,
Foreign countries, Water purification

Federal Republic of Germany
420D

WATER PURIFIERS,

Product Finishing, Vol. 27, No. 7, p 32, July, 1974.

Paterson Candy International Limited has made available two models of water
purifiers.   The purifiers operate on the reverse osmosis principle and can
reduce the dissolved solids content of brackish or mains water by more than
90 percent.  The reverse osmosis process is continuous, requires no regenera-
tion, needs little or no chemical addition, is bacteria resistant, and will
operate over a wide pH range.  Model series 01 has an output of 4500 liters
per day and series 02 has an output of 9000 liters per day.  The purifiers
are expected to be used in installations requiring absolutely pure water.

*Water purification, *Reverse osmosis, *Potable water, *Equipment, Water
treatment,  Water quality control, Membranes, Dissolved solids

*Water purification, Paterson Candy International Limited
                                  439

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421D

WATER RECLAMATION AND REUSE,

Kugelman, I. J.

National Environmental Research Center, United States
Environmental Protection Agency, Cincinnati, Ohio,
Treatment Research Laboratory

Journal of the Water Pollution Control Federation, Vol. 46, No. 6, p 1195-1201,
June, 1974.  61 ref.

A renewed interest in the area of waste water renovation and reuse has been
the result of the 1972 amendments to the Federal Water Pollution Control Act
which stated that the discharge of pollutants to the nation's waterways must
be ended by 1985.  This article reviews the current literature on reuse in
water resource planning, industrial reuse of treated municipal waste water,
irrigation and groundwater recharge, indirect reuse resulting from the dis-
charge of waste waters to rivers or lakes that are used as sources of water
supply, direct potable reuse, and development of reuse technology.

*Water reuse, *Planning, *Reviews, Irrigation water, Reclamation, Recharge,
Potable water, Water Pollution Control Federation, Federal Water Pollution
Control Act
422D

SILVER GETS THE BUGS OUT,

Chemical Week, Vol. 115, No. 6, p 37-38, August 7, 1974.

Better Living Laboratories, Memphis, Tennessee, has designed a portable
water purifier that utilizes a silver-impregnated filter system to kill coli-
form bacteria.  The purifying system consists of fine particulate silver
forced into the pores of activated carbon.  The carbon removes impurities
including odor-causing contaminants and the silver enters solution at a
steady rate of less than 50 ppb, killing coliform bacteria that can cause
cholera, dysentery and typhoid.  The unit will purify one gallon of water
in five minutes and will purify up to 750 gallons of water and is then dis-
carded.  Iron-rich water cannot be treated (the iron would clog the filter)
and neither can water with a high level of hydrogen sulfide.

*Potable water, *Water purification, *Activated carbon, *Filters,
Coliforms, Bacteria, Equipment,, Water quality
                                       440

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42 3D

KINETICS IN OZONE TREATMENT OF SECONDARY SEWAGE EFFLUENTS
(Ozon short ni okeru sokudoron—nlji shorlsui no baal),

Goda, T., Kawahara, 0., and Eda, M.

Gesuido Kyokai-shi, Vol. 11, No. 123, p 41-49, August, 1974.  20 fig, 3 ref.

The absorption of ozone in water, the autodegradation of ozone, and the
oxidation of ozone are some phenomena not yet satisfactorily explained.  As
a basic study for the ozone treatment of secondary treatment liquid waste,
the question of kinetics was examined.  The experimental apparatus consisted
of a batch bubble tower which was made of an acryl cylinder with a glass
filter at the bottom where ozone from the ozone producer was supplied.  The
liquid and ozone were contacted there.  The emitted ozone was measured
between the bubble tower and emission exit.  The test liquid sample was
taken every hour for 24 hours from the secondary treatment water of a Kyoto
sewage treatment plant; from four time belts, equal amounts were taken and
a composite test material was prepared.  The water was filtered to remove
suspended substances before the ozone treatment.  The measurements were
taken for BODS, COD(Cr), COD(Cr) removal speed, ozone consumption/COD
removal, and BOD5/COD(Cr).  The COD(Cr) removal process was satisfactorily
explained by a hypothetical model for multiple reactions of different
speeds and an equation induced from COD removal speed data.  The relation-
ship between ozone consumption and COD removal was experimentally confirmed
to be about 2, and the ratio increase with the progress of treatment was
theoretically clarified.  The initial five minutes of BODS increase had a
correlation with COD(Cr) removal.

*0zone, *Secondary treatment, *Sewage treatment, Effluents, Models,
Biochemical oxygen demand, Chemical oxygen demand, Absorption, Filters,
Measurement

Japan, COD removal
  424D

  STATE OF THE ART OF THE WATER PREPARATION TECHNOLOGY IN
  THE USSR (DER GEGENWAERTIGE STAND DER WASSERAUFBEREITUNGS-
  TECHNOLOGIE IN DER UDSSR),

  Bagozkij, J. B.

  Wasserwirtschaft-Wassertechnik, Vol. 24, No. 6, p 184-187, 1974.
  6 fig, 2 tab.

  Latest achievements in the drinking-water preparation technology in the USSR
  were surveyed.  The use of new flocculants and flocculation aids, design
  improvements, the use of new filter materials and layer filter designs,
  as well as the use of modern integrated analytical instruments for automatic
  process control are the basic trends of the technological development.
  Aluminum sulfate with 14-15 percent active alumina, and, less often, iron
  chloride are used as flocculants, combined with activated silicic acid
  and polyacrylamide as flocculation aids.  The minimum interval between
  the flocculant and flocculation dosaging is 30 to 90 seconds, depending
  on the water temperature.  The aggressivity of the water as caused by
  the flocculants is eliminated by slaked lime.  Ozone is used as a reagent
  for the elimination of slight coloration and turbidity in the ozonization -
  filtration - ozonization or chlorination scheme, or for the improvement of
  the organoleptic properties of the drinking water.  Ozonization alone is
  sufficient if the turbidity and coloration of the raw water do not exceed
  6 mg/liter and 60 degrees, respectively.  The sludge contact process and
  reverse filtration for the better utilization of the sludge retention
  capacity of the filter are among principal equipment design improvements.

  *Potable water, *USSR, *Flocculation, Design criteria, Filters, Ozonation,
  Lime sludge, Equipment, Ozone, Turbidity, Aluminum sulfate, Color
                                          441

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425D

THE RECLAMATION OF WATER FROM SEWAGE EFFLUENTS BY
REVERSE OSMOSIS,

Bailey, D. A., Jones, K., and Mitchell, 0.

Water Pollution Research Laboratory of the Department
of the Environment,
United Kingdom

Water Pollution Control, Vol. 73, No. 4, p 353-366, 1974.  8 fig,
3 tab, 40 ref.

A major water supply source in the United Kingdom is provided by river waters;
the problem of reclamation of this source of water from effluents for direct
reuse is discussed.  Several techniques have been considered for reclaiming
water of sufficiently high quality from secondary sewage effluents.  These
include treatment with activated carbon, chemical treatment, treatment with
ozone, ion exchange, and thermal and membrane processes.  A recently used
type of membrane process is described in detail, the process of reverse
osmosis.  A reverse-osmosis system gives adequate mechanical support to a
membrane while providing suitable hydrodynamic conditions for the process
water to reach and be removed from the membrane surface.  The process re-
moves organic and inorganic substances present in solution.  The efficiency
of removal of each species depends on ionic charge, molecular weight, and
chemical properties.  Bacteria and viruses can be removed from solution
by this treatment method.  In economic terms, the performance and useful
life of membranes critically affects the costs of a reverse-osmosis plant.
The maximum flux which can now be economically maintained is of the order
of 0.5 cu m/d.  Further study, however, is being conducted on developing
membranes with increased permeability without loss of desalinating properties.

*Water supply, *Reverse osmosis, *Effluents, *Sewage treatment, Water reuse,
Reclamation, Costs

Reverse osmosis plant, Secondary treatment
426D

THE EFFECT OF THE CHEMICAL WATER TREATMENT TECHNOLOGY ON
THE EFFICIENCY OF FILTERS (Vliyaniye tekhnologii reagentnoy
ochistki vody na effektivnost' raboty fil'trov),

Nakorchevskaya, V. F., and Kul'skiy, L. A.

Vodosnabzheniye i Sanitarnaya Tekhnika, No. 5, p 16-18, 1974.  1 fig,
2 tab, 5 ref.

The effect of aluminum sulfate as a coagulant and activated silicic acid
as a flocculant on the efficiency of sand filters was studied.  Aluminum
sulfate is generally used for pre-treatment of water before filtration.
The maximum possible duration of the protective action of the sand filter
may exceed the minimum duration by a factor of two to seven.  However,
the duration of the efficient filter operation decreases with the increase
in the contact time between aluminum sulfate and silicic acid.  This
reaction is due to the increase in the size of the aluminum sulfate floccules
with increasing contact time.  Therefore, the contact time should not be
longer than 10 to 20 seconds.  The most durable filtration efficiency is
obtained in heterocoagulatlon or when the flocculant is introduced immediately
after the coagulant.

*Coagulation, *Flocculation, *Filters, *Pre-treatment, Filtration

*Chemical treatment, *Aluminum sulfate, *Sand filters, Silicic acid,
Filter efficiency
                                    442

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427D

A SURVEY OF THE YOKOHAMA MUNICIPAL NANBU SEWAGE TREATMENT
PLANT (Yokohama-shi nanbu gesul shorijo no gaiyo),

Ogura, S.

Gesuido Kyokai-shi, Vol. 11, No. 123, p 54-61, August, 1974.  8 fig, 1 tab.

A total sewage works and treatment plan in Yokohama was Initiated in 1962,
consisting of nine treatment districts and ten sewage treatment plants.  One
of the plants, the Nanbu plant, covers an area of 2965 ha, and services a
population of 670,000.  Construction was started in 1962 and the operation
was begun in July, 1965.  With subsequent gradual expansion plans and
additions, the final plan is to be completed during 1974.  The service area's
constituents are 32 percent commercial, 8 percent industrial or sub-industrial,
and 60 percent residential.  The sewage BOD is about 200 mg/liter, and
suspended solids are about 300 mg/liter, of which 200 mg/liter is settled.
The treatment is designed for a step anaerobic digestion sludge treatment
designed to eliminate 90 percent of BOD—down to 20 mg/liter, and 85 percent
of suspended solids—down to 45 mg/liter.  In the adjacent area is a city
refuse incinerator with the maximum capacity of 450 ton/day, and part of its
steam production is used for heating the sludge digestion tank.  After the
digestion gas is desulfurized, part of it can be used as supplementary fuel
for the incinerator.  Scrub water for the incinerator is supplied with treated
sewage water, and the waste water is returned to the plant for treatment after
a pre-treatment.  The main facilities of the plant are:  settling ponds,
electrical machinery rooms, initial precipitation ponds, aeration tanks, final
precipitation tanks, chlorine mixture tanks, return sludge pump rooms, sludge
condensation pump rooms, sludge condensate tanks, blowers, sludge treatment
rooms with deodorization systems, sludge digestion tanks, sludge scrubbers,
and sludge dryers.

*Planning, *Municipal wastes, *Sewage treatment, Construction, Equipment,
Design criteria, Sludge, Waste treatment, Biochemical oxygen demand, Suspended
solids

*Sewage treatment plants, Japan, Nanbu Sewage Plant
428D

FIRST INSTALLATION IN THE WORLD FOR THE STERILIZATION OF
SEWAGE BY GAMMA RAYS (PREMIER INSTALLATION DU MONDE POUR
L'HYGIENISATION DES BOUES D'EPURATION AUX RAYONS GAMMA),

Gas-Wasser-Abwasser, Vol. 54, No. 5, p 170-171, May, 1974.  1 fig.

A new installation for the sterilization of sewage sludge by gamma rays,
developed by Sulzer Company, and installed in the Munich area, West Germany,
is described.  The batch type sterilizer is composed of an underground,
concrete irradiation shaft, and uses Co-60, Cesium-137, and other radioactive
wastes from nuclear reactors for irradiation of a predetermined duration.
The closed circuit design and the automatic control of the charge and
discharge processes guarantee maximum radiation protection.  The irradiated
sewage sludge, which cannot itself become radioactive, is subsequently
dewatered and used as manure on farmlands.

*Sewage treatment, *Gamma rays, Radioactive wastes, Dewatering, Water reuse

Munich, Germany, Sewage treatment plants, Sterilization
                                   443

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 429B

 PLASTIC FILTER TRICKLING BED WASTE WATER TREATMENT
 (Purasuchikku sansul rosho ho ni yoru haisui shori shisutemu),

 Otsuka, Y.

 Shokuhin Kaihatsu,  Vol.  9, No.  7,  p 32-35,  July,  1974.   2 fig,  4 tab.

 The trickling filter bed method of waste water treatment utilizes propagation
 of aerobic  bacteria on a filter of large mesh, thus contacting  bacteria with
 organic waste water.  The system is similar to other types of biological
 treatment,  but compared with the activated  sludge method which  results  in
 0.4-0.6 kg(SD)/kg BOD, the trickling bed method gives 0.3-0.4 kg(SD)/kg BOD.
 Pretreatment is necessary if suspended solids and oil content are large, to
 reduce oil  to about 30 ppm; if an oil film  does not form, there is no  problem.
 If nutrients are lacking in the waste water, about 5 portions of nitrogen and
 one portion of phosphorus should be added to 100 of BOD; however, this  should
 be kept to  a minimum to avoid eutrophication.  When using a plastic filter
 packed bed, the waste water is mixed with already treated water and sprayed
 over the bed.  Aerobic bacteria multiply rapidly and eliminate  BOD(COD)
 efficiently.  The water is returned to the  circulation tank and part of it is
 discharged.  The circulation ratio is determined by waste water concentration,
 treatment water concentration and the filter bed load.   With the plastic bed,
 M3/M2/day is 30-200.  In an open aeration tank, a natural ventilation (for
 oxygen) always takes place because of the different temperatures of the air
 and water;  but in an enclosed air-tight bed, ventilation should be forced
 by fans.  The number of stages for trickling beds depends on the initial cost,
 maintenance, and the running cost, but usually two or three stages are used.
 The amount of sludge is very small and its  high self-digestion  eliminates the
 necessity for large quantity sludge treatment.

 *Trickling filters, *Waste water treatment, Plastics, Biochemical oxygen
 demand, Sludge treatment, Aeration, Biological treatment
 430D

 ADSORPTION PROCESSES,

 Weber,  W.  J.

 Michigan University, Ann Arbor,  Michigan,  College  of
 Engineering

 Pure  and Applied  Chemistry, Vol.  37, No. 3, p 375-392, 1974.  6 fig  1 tab
 15  ref.                                                                    '

 Adsorption  is a basic process in  the physiochemical treatment of municipal
 waste water.  This treatment can  economically meet the higher effluent
 standards and water reuse requirements of  today.  Activated carbon is
 the most effective adsorbent for  this method.  Expanded-bed contact systems
 are the  most efficient means for  utilizing granular carbon for waste
 treatment.  Augmentation of the adsorption process occurs as an in-situ
 partial  regeneration resulting from biological growth on the surfaces of
 the carbon.  The  system produces  high levels of treatment and has a
 high degree of stability and reliability.  It is very resistant to shock
 loads and toxic waste constituents.  The advantages of a physicochemical
 system over a biological system include:  less land is required; a lower
 sensitivity to diurnal variation  exists; it is unaffected by toxic
 substances; and the former has a  potential for significant removal
 of heavy metals.  In addition, a  physicochemical system gives excellent
 removal  of phosphates and organic waste constituents and greater flexibility
 in design and operation.

 *Waste water treatment,  *Adsorption,  *Activated carbon,  Biological
 treatment,  Water reuse,  Costs,  Municipal wastes,  Effluents,  Organic loading,
Toxicity, Heavy metals,  Phosphorus, Design, Operation and maintenance

*Physicochemical treatment
                                      444

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431D

DESALINATION-NEW WATER FOR OLD (FRISCHWASSERVERSORGUNG
UND ABWASSERAUFBEREITUNG),

Pugh, 0.

United Kingdom Atomic Energy Authority, London,
Great Britain

Meerestechnik, Vol. 5, No. 4, p 119-123, August, 1974.  7 fig.

Previously desalination has been used to provide an essential commodity for
man—potable water.  It is now apparent that the newer desalting processes
are becoming more important in waste treatment.  Desalination technology,
which has been mainly distillation processes, contributes to only one
aspect of the complete watercycle.  The advent of the reverse-osmosis
system introduces the technology to the area of protection of clean
water resources from the discharge of polluting waste.  Reverse-osmosis
can also be used for the renovation of waste water.

*Desalination, *Potable water, *Reverse osmosis, *Waste water treatment,
Distillation, Water quality control, Water resources, Water reuse
432D

MEMBRANES AND MODULES FOR THE WATER DESALINATION WITH
REVERSE OSMOSIS (MEMBRANEN UND MODULE FUR DIE WASSER-
ENTSLZUNG MIT UMGEKEHRTER OSMOSE),

Ermert, U., and Bauermann, H. D.

Meeresteckik, Vol. 5, No. 4, p 125-128, August, 1974.  6 fig, 4 ref.

Beginning with the demarcation line between reverse osmosis (hyperfiltration)
and ultrafiltration, the structure and materials of the usual types of
membranes are discussed.  The membranes are presented as complete modules.
A comparison is made between the different modules including the plate
and frame module, the wound spiral module, the pipe module, and the
hollow fiber module.  The various aspects of choosing membranes and
modules are considered.

*Reverse osmosis, *Filters, *Membranes, *Separation techniques, Desalination,
Waste water treatment, Filtration, Equipment, Design

Ultrafiltration, Plate and frame module, Wound spiral module, Pipe
module, Hollow fiber module
                                          445

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433D

COMBINED CHEMICAL-BIOLOGICAL TREATMENT STUDIES,

Bouveng, H. 0.

Swedish Water and Air Pollution Research Laboratory,
Stockholm, Sweden

Pure and Applied Chemistry, Vol. 37, No. 3, p 329-341, 1974.  10 fig.

The OECD study of chemical treatment of urban sewage is discussed with
special reference to the relation between cost and performance of alternative
processes.  The application of combined chemical and biological treatment
processes is discussed with emphasis on the factors which influence the
stability of performance.  It was concluded that considering chemical
treatment of urban sewage only as a method for phosphorus removal is
an unjustified limitation of its field of application.  Chemical pre-
cipitation of urban sewage is a profitable alternative when an effluent
having a low and stable level of residual BOD is desired.  Chemical treatment
is a useful supplement to biological treatment of industrial waste water
when the latter is not able to achieve the required effluent quality.

*Sewage treatment, *Biological treatment, Chemical precipitation,
Phosphorus, Biochemical oxygen demand, Waste water treatment, Costs,
Municipal wastes, Industrial wastes


*Chemical treatment
434D

HIGH RATE BIOLOGICAL DENITRIFICATION USING A GRANULAR
FLUIDIZED BED,

Jeris, J. S., Beer, C., and Mueller, J. A.

Manhattan College, Bronx, New York, Civil Engineering
Department

Journal of the Water Pollution Control Federation, Vol. 46, No. 9,
p 2118-2128, September, 1974.  11 fig, 4 tab, 11 ref.

Using fluidized, small media for biological removal of contaminants in
a reactor has the advantages of greater surface area available for
growth per unit of reactor volume, very small head loss, no danger of
clogging, and easier carrier removal procedure.  A fluidized bed is a
solid, granular carrier medium in a columnar reactor suspended in an
upflowing fluid.  An experimental apparatus was designed and tested for
denitrification capabilities.  A major problem with the process was the
continual growth of the organisms on the carbon particles.  This caused
bed expansion and necessitated the removal of part of the biologically
coated carbon torevent bed overflow.  The idea of achieving a balance
between growth and washoff similar to that found in a trickling filter was
dropped because increasing the- flow failed to affect the growth on
the media.  It was estimated that the chemical costs would be slightly
over $0.02/1000 gal for removal of 25 rag/liter nitrate nitrogen.  The
nitrogen removals obtained ranged from 257 to 424 Ib inorganic nitrogen/
day/1000 cu ft of reactor capacity.  When the hydraulic loading was
12 gpm/sq ft, the superficial detention time required was about seven
minutes for removal of 20 to 35 mg/liter nitrogen.  The fluidized biological
bed concept has demonstrated the ability to remove more nitrogen than the
activated sludge process and requires less detention time than other
biological waste treatment systems.

*Biological treatment, *Activated sludge, *Carbon, *Nitrogen, Research
and development, Microorganisms, Microbial degradation, Equipment, Trickling
filters, Waste water treatment, Nutrient removal

Granular fluidized bed

                                   446

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435D

COMPARISON OF COMPLETELY MIXED AND PLUG FLOW
BIOLOGICAL SYSTEMS,

Toerber, E. D., Paulson, W. L., and Smith, H. S.

Fehr and Graham Consulting Engineers, Freeport,
Illinois

Journal of the Water Pollution Control Federation, Vol. 46, No. 8,
p 1995-2014, August 1974.  26 fig, 9 tab, 3 ref.

The performance of a completely mixed activated sludge system and
the performance of a plug flow system under parallel operating conditions
were compared.  The two systems were tested with waste from Freeport,
Illinois.  It was found that under normal operating conditions both the
completely mixed and the plug flow systems had similar removal efficiencies.
If there were separate operating conditions and constant influent flow
rates, both systems showed a rapid leveling off of removal efficiency
after a nominal aeration detention time of 2 to 3 hours.  The completely
mixed system exhibited an overall removal efficiency ten percent greater
than the plug flow system when both were subjected to a severe shock
load.

^Activated sludge, *Waste treatment, Evaluation, Flow rates, Organic loading,
Construction, Design, Illinois, Biochemical oxygen demand, Chemical
oxygen demand

*Completely mixed system, *Plug flow
436D

BACTERIAL PRODUCTION OF ENZYMES IN ACTIVATED
SLUDGE SYSTEMS,

Handin, L. and Sands, D. C.

The Connecticut Agricultural Experiment Station,
New Haven, Connecticut, Biochemistry Department

Journal of the Water Pollution Control Federation, Vol.  46, No.  8,
p 2015-2025, August 1974.  14 tab, 14 ref.

The five important stages (raw Influent, primary effluent, mixed liquor,
activated sludge, final effluent)  in four activated sludge treatment
facilities were examined to determine the numbers and percentages of bacteria
capable of producing specific enzymes.  It was found that the activated
sludge contained the greatest total number of bacteria,  followed by the
number in the mixed liquor.  A 17- to 93-fold increase was evident
between raw influent and mixed liquor and activated sludge.  It  appears
that there is not a selective removal of any one specific bacterial
type in the primary effluent stage.  From the primary effluent to the
mixed liquor stage, a selective process seems to occur which favors
bacteria with certain enzymatic capabilities.  Bacteria in enzyme categories
not readily precipitated in the sludge appear in higher numbers  in the
final effluent.  The fact that the increase of bacteria from the mixed
liquor and the activated sludge was not greater than was found may
indicate that activated sludge contains more undegraded material than
bacterial cells or, if the sludge is predominately bacteria, that they
are dead cells.  The lack of significant difference between these two
stages may mean that the percentage of active bacteria tends to  equalize
in the aeration step.  Information obtained in this study could  be useful
when considering the possible use of stabilized enzymes in lieu of,
or in addition to, microorganisms.

*Sludge treatment, *Waste treatment, *Bacteria, *Activated sludge,
Enzymes, Biological treatment, Microbial degradation, Sludge, Effluents,
Biodegradation, Microorganisms

                                 447

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437D

TREATMENT FACILITY INCORPORATES UNIQUE DESIGN FEATURES,

Lynch, G. P.

John Carollo Engineers, Santa Ana, California

Public Works, Vol 105, No. 9, p 106-107, September, 1974.  3 fig.

The city of Redlands, California, is currently upgrading and increasing
the capacity of their existing waste water treatment facilities.
Two unique design features of the new system include a digester
supernatant degasification facility to allow further concentration
of supernatant following high rate primary-secondary anaerobic
digestion and a peaking pond to limit peak flow rates to existing
secondary treatment facilities and to third-stage ammonia conversion
facilities.  The new facilities are two rectangular tanks with a
bottom width of 21 feet and length of 11 feet, side slopes at 3
to 1 covered with 4 inches of concrete, a normal working depth of
6 feet, and 2 feet of freeboard.  A decant box pump at one end, with
a scumbaffle and adjustable overflow weir, return the decanted liquid
to the plant influent flow.  A sump at the opposite end from the
decant box collects the concentrated sludge.  Effects of the facilities
which have not yet been evaluated include:  optimum process control of
third stage biological facilities due to more uniform flow rates; greater
effluent solids control caused by reduction of peak flow rates on
second and third-stage sedimentation facilities; equalization of
organic loadings; and, operational flexibility.

*Waste water treatment, *Facilities, *Design, Digestion, Flow rates,
Sedimentation, Operation and maintenance, California, Municipal wastes

Degasification, Peaking pond
438D

LIME SLUDGE:  SOME PROBLEMS — SOME SOLUTIONS,

Hazelswatts, D. E.

Municipal Water Plant, C-rand Rapids, Michigan

Water and Sewage Works, Vol. 121, No. 7, p 72-73, July 1974.  3 fig.

The Grand Rapids municipally owned water system operates from two sources
of supply, Lake Michigan and Grand River.  Lime-softened river water produces
2260 pounds of solids per million gallons, producing at maximum rate 90,400
pounds of sludge per day.  When the sludge was put in sewers to be dewatered,
lime precipitates formed a pasty sludge heavier than sewage, causing the
machinery to break down.  After investigation, a Bird 36x72 inch solid bowl
centrifuge with a spiral scraper was installed.  Flocculant was injected
through a 3/4 inch diameter pipe inside the feed pipe; however, results with
the flocculant were no better than without; the flocculant pipe had broken.
The baffle hole surrounding the flocculant pipe was enlarged; the machine is
still operant.  Because of problems of dissolving the sludge and also poor
working conditions caused by the accumulation of the powdered flocculant on
walkway surfaces, a new liquid flocculant from Nalco was tried.  The liquid
flocculant probed as effective as the dry flocculant, but it twice the
amount was required.  However, the cost of the required quantity of liquid
is about half.  Therefore the overall cost is the same, and the convenience
and safety are much improved.  The cake produced by the centrifuge is hauled
to a driving yard.

*Waste water treatment, *Sludge, *Centrifuges, *Flocculant, Costs, Lime


*Lime sludge, Grand Rapids, Michigan, Grand River, Bird centrifuge, Nalco
"Instant" polymer
                                 448

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 439D

 UPFLOW FILTRATION IMPROVES OXIDATION POND EFFLUENT,

 McGhee, T. J.  and Patterson, R. K.

 Engineering Research Center, College of Engineering and
 Technology, Nebraska University, Lincoln, Nebraska

 Water and Sewage Works, Vol. 121, No. 7, p 82-83, July 1974.  3 fig, 11 ref.

 Oxidation ponds are an effective, uncomplicated and economical way of treating
 domestic sewage and certain industrial wastes.   The system requires no skilled
 operator or maintenance.  Through evaporation and seepage the total reduction
 in BOD through an oxidation pond can approach 95 percent, although the actual
 concentration of BOD and suspended solids may not meet the new standards of
 30 mg/liter monthly average, and 45 mg/liter weekly average determined for
 secondary treatment.  The material which contributes to the BOD effluent
 and suspended solids of oxidation ponds is largely algal cells utilizing
 inorganic byproducts of the bacterial oxidation of the waste.  Techniques
 listed for removal of algae include coagulation with alum, coagulation with
 alum and polyelectrolytes, flocculation and aggregation on cationic exchange
 resins, chlorine disinfection, anaerobic rock filters, fly ash slurry
 filtration, pressure filtration through a diatomaceous earth filter, and
 sand filtration.

 *0xidation lagoons, *Effluent treatment, Sewage treatment, Water quality
 control, Filtration, Biochemical oxygen demand, Coagulation, Alum, Secondary
 treatment, Flocculation, Aggregation, Polyelectrolytes, Algae

 *Upflow filtration
440D

TREATMENT OF WASTE-WATER CONTAINING SURFACE ACTIVE SUBSTANCES,

Hagiwara, K. and Murakami, Y.

Bulletin of the Government Industrial Research Institute, Osaka, Vol. 24,
No. 4, p 325-330, December, 1973.  8 fig, 3 tab, 5 ref.

A condensed product of polyhydric phenol and polysaccharose was discovered to
be effective for removal of nonionic surface active substances, in a new
method of waste water treatment.  This can also be used in the treatment of
emulsified oil.  The condensed product is added to waste water and ferric or
aluminum ion is added as a coagulant, with the pH value of the solution
adjusted to between 5 and 6.  The solution is filtered and the sludge
treated by a method such as burning.  The treatment's efficiency is dependent
upon the number of ethylene glycol molecules in the surface active substance.
Efficiency decreases as the number of ethylene glycol molecules increases.
The solubilities of the reaction product of the surface active substance and
the condensed product of polyhydric phenol and polysaccahrose increases as
the ethylene glycol molecule increases.  With the surface active substance
at a concentration of 1,000 ppm, more than 90 percent of the surface active
substance was removed.

*Water pollution, *Waste-water treatment, *Sludge disposal, Hydrogen ion
concentration (pH)

*Polyhydric phenol, *Polysaccharose, *Ethylene glycol molecule, *Surface
active substance, Ferric ion, Aluminum ion
                                       449

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 441D

 CONCENTRATION OF POLARISATION  IN REVERSE OSMOSIS FLOW
 SYSTEMS UNDER LAMINAR CONDITIONS.  EFFECT OF SURFACE
 ROUGHNESS AND FOULING,

 Carter, J. W., Hoyland, G., and Hasting, A. P. M.

 Birmingham University, England, Department of Chemical
 Engineering

 Chemical Engineering Science,  Vol. 29, No. 7, p 1651-1658, 1974.  11 fig,
 3  tab, 18 ref.

 Experimentation in reverse osmosis was conducted under laminar flow conditions
 in a channel of cross-section  3x38 mm.  Solution concentrations giving
 pi f/delta p up to 0.66 and cellulose acetate membranes having high
 rejections and distilled water fluxes of 12-15x 0.0001 cm/sec were employed.
 A  close prediction was made by a numerical solution of the theoretical
 equations of the product fluxes and concentration polarisation.  The effects
 of rough membrane surfaces in  increasing polarisation and decreasing product
 flux were also predicted utilizing a roughness depth determined from a
 profile of the surface irregularities.  A rust layer on the membrane surface
 had like effects on flux and polarisation which were calculable.

 *Reverse osmosis, *Transition  flow, Membranes

 *Cellulose acetate membranes,  *Distilled water fluxes, *Polarization, Rough
 membrane surfaces
442D

NEW CONCEPTS FOR CLARIFICATION OF WATER USING SOME
ALTERNATIVES TO ALUM,

Rao, M. N., and Datta, A, K.

Regional Engineering College, Durgapur, India

Journal of the Institution of Engineers (India), Vol. 54, No. PH2, p 57-60,
February, 1974.  5 fig, 12 ref.

Alum has been fundamental in the clarification of municipal waste water for
drinking purposes for centuries.  The employment of alum as a coagulant in
sophisticated water treatment plants is nearly universal.  New concepts in
the field of clarification of water recommend the use of polyelectrolytes,
foam, and magnesium carbonate as alternatives to alum.  Polyelectrolytes
are polymers with only the cationic being used as prime coagulants.   They
exhibit a high charge density, and when added as a coagulant, the positively
charged polymers are absorbed on the surface of the negatively charged
colloidal impurities of water.  The particle surface charged is reduced
or used sufficiently to allow cohesion and aggregation on collision.  Foam
has only a limited field of application in treatment of turbid water.  A
cationic surfactant is added to and mixed with the raw water, and passes to
a flotation cylinder.  The surfactants are both collector for the colloidal
turbidity particles and frothing agent for carrying particles from the solution.
When using magnesium carbonate as a coagulant, the sludge problem is often
totally eliminated.

*Water purification, *Alum, *Polyelectrolytes, *Magnesium carbonate, *Foaming,
Coagulation, Waste water treatment, Colloids, Bacteria, Dyes

*Cationic polymers
                                         450

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44 3D

U.S. CHECKING UP ON FIRMS' SPILL-PREVENTION, CLEANUP PLANS,

The Oil and Gas Journal, Vol. 72, No, 30, p 117, July 29, 1974.

Spot checks are being taken of possibly hazardous oil facilities by government
agents, in areas of navigable waters or their tributaries which have a
pollution prevention program.  Such programs, certified by registered
professional engineers, were have been completed by July 10, 1974.  These
plans are not required to be filed with the EPA.  Oil companies are requested
to build dikes around storage tanks or any other steps for containment
of oil spills.  If spills should occur, the EPA would probably dictate the
terms of the prevention plan required under the regulations.

*0il spills, *Water pollution, Federal government, Water policy

*Environmental Protection Agency
444D

UNIQUE NEW SECONDARY OXYGEN TREATMENT SYSTEM FOR EFFLUENT,

Paper Trade Journal, Vol. 158, No. 31, p 22-23, August 5, 1974.  2 fig.

A forced free-fall oxygenation (F30) waste water treatment system has been
developed by a unit of Airco Industrial Gases.  This system is designed
for municipal, chemical, pulp and paper waste usage.  Conventional aeration
tank capacity may be doubled or tripled by this system.  It can also be
used in conjunction with new activated sludge plants of existing operations.
The waterfall principle is used in induvidual modular mixing and dissolving
units.  Also developed was a simple pipeline waterfall reactor useful in
black liquor oxidation.

*Effluent treatment, *Waste water treatment, Water pollution, Chemical
wastes, Pulp and paper wastes, Aeration, Activated sludge, Municipal wastes

*Secondary oxygen treatment system, *PIpeline waterfall reactor, *Black
liquor oxidation
                                            451

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44 5D

ANAEROBIC DIGESTION OF ORGANIC MATTER,

Hobson, P. N., Bousfield, S., and Summers, R.

Rowett Research Institute, Bucksburn, Aberdeen,
Scotland

Critical Reviews in Environmental Control, Vol. 4, No. 2, p 131-191, July
31, 1974.  6 fig, 197 ref.

Treatment of waste products is of primary current concern.  The biochemistry
of anaerobic digestion is discussed with regards to anaerobic metabolism in
the rumen and in digesters, to the composition of digester feedstocks,
cellulose digestion, to digestion of nitrogenous and lipid materials,
minor bacterial metabolites in digesters, effects of growth rate,
substrate concentration, and pH, and fermentation.  Theoretical digester
systems and modeling of digester systems are presented with emphasis on the
high rate digester, two-stage digester, and the anaerobic filter system.
The bacterial populations of anaerobic digesters and practical aspects
of anaerobic digestion systems are mentioned.

*Reviews, *Anaerobic digestion, *Waste treatment, Equipment, Models,
Theoretical analysis, Bacteria, Biochemistry
  446D

  APPLICABILITY OF  CONTROL  STRATEGIES TO  THE ACTIVATED
  SLUDGE WASTEWATER TREATMENT PROCESS,

  Lech, R.  F.

  Purdue University

  Dissertation Abstracts  International B, Vol.  35, No. 1, p  211, July,
  1974.

  The potential improvements to be gained by the addition of control
  systems to the activated  sludge waste water treatment process are
  evaluated.  Approximate models for the  important transfer  functions
  in the process are developed.  The applicability of single and multiple-
  loop feedback control systems is evaluated on activated sludge plants
  characterized by  two types of final settler behavior.  It was found that
  the most  significant improvement in performance is achieved by
  feedforward and combinations of feedforward and feedback control systems
  among all the control systems considered.  Also, the applicability of
  control strategies is limited by the design of the process.

  *Activated sludge, *Waste water treatment, Evaluation, Model studies,
  Control systems,  Performance, Design criteria

  Feedforward, Feedback
                                            452

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447D

VIROLOGICAL STUDIES IN WATER SYSTEMS:  NATURAL
OCCURENCE OF REOVIRUSES AND THEIR INACTIVATION BY
PHYSICAL AND CHEMICAL AGENTS,

Mehta, S. C.

Iowa University

Dissertation Abstracts International B, Vol. 35, No. 1, p 284, July,
1974.

Field investigations of two water systems were undertaken to evaluate
the detection of reoviruses in water samples collected from the Cor^lville
Reservoir, Iowa River, and the Cedar River.  A two-phase separation method
was used to concentrate the viruses from the water samples.  L
cells and KB cells were used to propagate the virus.  Iramunofluorescent
staining was employed to Identify the viruses.  Reovirus was found to
be resistant to heat, less resistant to ultraviolet, and least resistant
to chlorine and ozone.  A comparison of resistance to inactivation
between reoviruses and polio and coxsackie viruses exposed to various
physical and chemical agents also is presented.

*0n-site investigations, *Viruses, Water samples, Evaluation

*Reoviruses, Viral resistance
448D

TURBIDITY REMOVAL USING POLYMERS AND ACTIVATED CARBON,

Miller, R. D.

Purdue University

Dissertation Abstracts International B, Vol. 35, No. 1, p 284, July, 1974.

A possible coagulation-adsorption process for turbidity removal has been
investigated.  For clay destabilization using only polycations, optimum
clarity was achieved over a narrow range of polymer dosages.   Residual
polymer concentrations below one mg/liter were determined for polycations
using clay coagulation tests and for polyanions and nonionic polymers using
a filtering technique.  Combined use of carbon and polycations for clay
removal was inferior to the use of polycations alone.   Use of carbon and
polyanions or nonionic polymers for clay removal produced some clarity at
relatively low carbon dosages and nearly complete clarity at carbon dosages
of 5.0 g/liter or higher with a mixing time of thirty minutes and settling
time of ten minutes.

*Turbidity, *Polymers, Coagulation, Adsorption, Activated carbon

*Turbidity removal
                                         453

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449D

SOME EFFECTS OF NITROGEN AND PHOSPHORUS LIMITATION ON A
BIOLOGICAL-CHEMICAL WASTEWATER TREATMENT PROCESS,

Wu, Y. C.

Michigan University, Ann Arbor, Michigan

Dissertation Abstracts International B, Vol. 35, No. 1, p 229, July, 1974.

The effect of nitrogen and phosphorus limitation on substrate removal, sludge
productivity, biochemical behavior of sludge, and capsule and electric charge
production on the surface of treatment organisms has been studied using two
laboratory activated sludge units with heterogeneous populations.  Experimental
results indicate that the treatment efficiency of the biological-chemical
process is highly dependent on the chemical nature of the waste to be treated.
Also, an increase in sludge protein and sludge phosphorus content was observed
as the sludge yield and carbohydrate content decrease.  Finally, results of
chemical flocculation studies showed that lower chemical doses per unit of
effluent biological solids were required at high initial solids and low
initial phosphorus conditions.  The relationship between quantity of chemical
precipitant and percentage of phosphorus removal was not a stoichiometric
function.  Indications are that following phosphorus removal there is a
chemical separation of dispersed microorganisms.

*Nitrogen, *Phosphorus, *Waste water treatment, *Waste treatment, Biological
treatment, Treatment facilities, Sludge treatment, Activated sludge,
Laboratory tests, Efficiencies

Chemical treatment, Charge production
4 500

ALUM RECOVERY FROM WATER AND WASTEWATER TREATMENT PLANT
SLUDGES,

Chen, B. H. H.

Virginia Polytechnic Institute and State University

Dissertation Abstracts International B, Vol. 35, No. 1, p 217, July, 1974.

Under this investigation, the extent of alum recovery achievable is defined,
the effectiveness of recovered alum is demonstrated, the properties of the
remaining sludge are characterized.  The economy of the alum recovery process
in water and waste water treatment systems was also analyzed.   Results showed
that the amount of alum recovered can be controlled by noting the associated
stoichiometric relationship and by pH measurement.  An extensive cost analysis
cf the alum recovery technique developed in the laboratory was conducted with
two illustrative problems demonstrating the economic advantage of this
recovery process.  Alum recovery and reuse may be a viable alternative to
the conventional method of water and waste water treatment.

*Invest!gations, *Alum, *Sludge treatment, Economics, Waste water treatment,
Treatment facilities, Hydrogen ion concentration

*Alum recovery
                                           454

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451D

WATERLESS SANITATION FOR REST .AREAS,

Fullerton, R. W.

Chrysler Corporation Space Division, New Orleans,
Louisiana

Water & Sewage Works, Vol. 121, No. 6, p 86-88, June, 1974.  1 fig, 2 tab.

Since 1970, the Chrysler Corporation's Space Division has been developing
marine and land based sewage disposal systems.  One such system, described
here, is a closed loop no-discharge nonbiological sewage disposal system
which uses mineral oil as the flush fluid to transport human waste instead
of water.  The flushing fluid carries waste from conventional commodes to
a separation tank where the sewage is separated by gravity.  The fluid is
filtered, purified, and reused indefinitely.  Disposal is by burning in a
pollution—free incinerator.

*Sewage disposal, *Sewerage, Separation techniques, Treatment facilities,
Domestic wastes, Waste treatment

Mineral oil
452D

DISINFECTION,

Davis, E. M., Whitehead, L. W., and Moore, J. D.

Texas University, Houston, Texas

Journal of the Water Pollution Control Federation, Vol. 46, No. 6, p 1181-1191,
June, 1974.  102 ref.

The methodology and techniques developed and used in disinfection which have
been reported in recent literature are reviewed.  The need for increased
attention in providing safe water supplies, adequately disinfecting waste
water, and overall research have appeared periodically.  Disinfection kinetics
and other properties as well as chlorine research are highlighted.  The
possibility of using biological filtration and chlorinatlon as tertiary treat-
ment methods and the biological effects of chlorine are mentioned.  Finally,
three patent applications appearing in the literature on disinfection are
discussed.

*Disinfection, ^Reviews, Publications, Water supply, Waste water treatment,
Research and development, Patents, Chlorination, Tertiary treatment
                                           455

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453D

SLUDGE TREATMENT, UTILIZATION, AND DISPOSAL,

Dick, R. I.

Delaware University, Department of Civil Engineering,
Newark, Delaware

Journal of the Water Pollution Control Federation, Vol. 46, No. 6, p 1161-1181,
June, 1974.  220 refs.

A review of the 1973 published literature concerned with various aspects of
sludge treatment and control is presented.  This work outlines the research
and technical achievements as well as on-going projects involved in the
treatment of sludge.  The topics mentioned include conditioning, composition,
thickening, dewatering, combustion and heat drying, reclamation, and
ultimate disposal.  These processes are discussed in view of the impact of
the 1972 Amendments to the Federal Water Pollution Control Act.  The legislation
seems to encourage regionalization but at the same time may increase the
scattering of solids handling problems.

*Reviews, *Publications, *Sludge treatment, Sludge disposal, Dewatering,
Research and development, Legislation

Sludge conditioning, Sludge composition, Sludge thickening, Combustion,
Heat drying, Sludge reclamation
454D

LIQUID WASTE TREATMENT METHOD USING MICROORGANISM AS
ADSORBENT (Blseibutsu o kyuchakuzai to shita haisui
shoriho),

Kobayashi, H.

Gijutsu to Kagai, Vol. 4, No. 4,  p 39-43, July,  1974.   3 fig.

The use of a type of pseudomous bacteria for decomposition of  organic mercury
compounds was developed by the Fermentation Research Institute (the present
Microbiol Industrial Technology Research Institute).  Generally,  continuous
treatment of toxic heavy metals by this method is extremely difficult.  Heavy
metal ions are considered water pollutants because of  their easy  accumulation
in living organisms.  Research was performed on  the ability of yeast, chlorella,
and bacteria to remove heavy metal ions, detergent, and dyes both by adsorption
on the cell surfaces and by internal absorption.   Saccharomyces cerevisiae
(store bought bread yeast) and Torulopsis utilis  (feed yeast)  were used because
of their easy accessibility.  The results showed  that  depending on the
bacterial cell, sodium potassium, potassium bichromate and arsenic oxide were
not adsorbed, but mercury, lead,  cadmium, and other plus metal ions and
aluminum ion were relatively well adsorbed.  Basic dye, which  turns into plus
ion in a neutral solution, was adsorbed well, but acidic dye and  catalytic dye
were not.  These physiochemical reactions are explained and their application
for liquid waste treatment is discussed.  However, at  the present stage of
research, the unsolved problems are too many, the cost of such a  system is
unfeasible, and the development of much less expensive microbial  agents is not
yet foreseeable.

*Bacteria, *Mercury, *Adsorption, *Heavy metals,  *Yeasts, Water pollution
sources, Water treatment, Pollutants, Chlorella,  Liquid wastes, Foreign
research, Foreign countries

Japan, Saccharomyces cerevisiae,  Torulopsis utilis
                                    456

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455D

BACTERIOLOGY OF CHLORINATED AND UNCHLORINATED WASTEWATER
EFFLUENTS,

Silvey, J. K. G., Abshire, R. L., and Nunez, W. J.

North Texas State University, Denton, Texas,
Department of Biological Sciences

Journal of the Water Pollution Control Federation, Vol. 46, No. 9, p 2153-2162,
September, 1974.  1 fig, 1 tab, 20 ref.

Chlorination has not been widely practiced in the treatment of waste water
although chlorination of finished water is standard procedure for the purpose
of eliminating pathogenic bacteria.  The current emphasis on curtailment of
further massive pollution of water by waste products has made necessary a
re-evaluation of waste water treatment methods.  A bacteriological and chemical
study was made on part of the Trinity River in Texas.  High numbers of fecal
coliforms and fecal streptococci were attributed to the presence of waste
effluents.  Chlorination was found to be effective in reducing the quantities
of microorganisms only where the chlorine was directly applied.  Bacterial
populations recovered immediately after chlorination was ended.  Decreasing
susceptibility of microbial organisms to chlorine was, in this order:
beneficial heterotrophic organisms, fecal coliforms, nonfecal coliforms and
fecal streptococci.  Chlorination did not effectively destroy Salmonellae.
The BOD and DO of the effluent improved as a result of chlorination.  The
data obtained in this investigation indicates that chlorination did not
effectively improve the conditions of the river.

*Chlorination, *Pathogenic bacteria, *Waste water treatment, Pollution
abatement, Streptococcus, Coliforms, Salmonellae, Biochemical oxygen demand,
Dissolved oxygen, Microorganisms, Texas, Chlorine

Trinity River, Fecal coliforms, Nonfecal coliforms, Fecal streptococci

456D

WASTEWATER DEGASSING BY ADIABATIC FLASHING,

Wilson, D. B. and Tsao, H. Y.

New Mexico State University, Las Cruces, New Mexico,
College of Engineering, Department of Chemical
Engineering

Journal of the Water Pollution Control Federation, Vol. 46, No. 9, p 2209-2214,
September, 1974.  3 fig, 3 tab, 11 ref.

Aqueous solutions of dissolved gases can result from a variety of industrial
and water treatment operations such as the production of oil from petroleum,
domestic waste water treatment, petroleum refining,  hydroelectric production,
fish-farming operations, and the scrubbing of power plant stack gases.   The
dissolved gases must be removed before the water is  released to the environment
if the gaseous components are corrosive or toxic to  the biological life in the
water system.  These gases can be physically separated either by stripping or
flashing.  Adiabatic flashing is recommended because the equipment is
relatively simple,  a short residence time for phase  separation is provided
and eliminates mist entrainment,  the gaseous solute  produced is in a high
concentration, and the discharge temperature of the  water steam is lowered.
A mathematical analysis of adiabatic flashing was performed.  The analysis
indicated that if the quantity and condition of the  feed,  adiabatic operation,
and the flash temperature are specified, all the other design variables may
be calculated by using the system material and energy balances.  The design
variables include the pressure of the flash, and the ratio of the quantity of
gas phase produced to the quantity of feed.   The recommendation of adiabatic
flashing is based on the results of the analysis, an estimation of economic
costs based on equipment prices,  and estimated operating costs.

*Separation techniques, *Flash distillation, *Waste  water treatment,  Gases,
Aqueous solutions,  Industrial wastes, Domestic wastes, Equipment, Costs,
Economics, Mathematical studies,  Algorithms

Adiabatic flashing
                                     457

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457D

TEMPERATURE-SUBSTRATE INTERACTIONS IN BIOLOGICAL TREATMENT,

Novak, J. T.

Missouri University, Columbia, Missouri, Department of
Civil Engineering

Journal of the Water Pollution Control Federation, Vol. 46, No. 8,
p 1984-1994.  12 fig, 3 tab, 23 ref.

Temperature correction factors are used in biological waste treatment processes
to modify microorganism growth rates or substrate utilization rates to
correspond to variations in the temperature.  The modified Arrhenius equation
is usually used to characterize the temperature correction for these modifica-
tions.  The temperature response of biological processes was found to depend
on the substrate concentration present in the system.  Therefore, the
applicability of the Arrhenius equation is limited because one of its factors
(the temperature coefficient) is substrate dependent.  It was observed that
aerobic processes were nearly Independent of temperature variations at low
substrate levels and anaerobic processes were dependent on temperature at
all substrate levels.  Although temperature models provided reasonable
descriptions of process response, they must be used with care, keeping in mind
the fact that temperature can affect the organism yield coefficient and
decay rate, the dominant organism groups and the availability of nutrients,
which in turn can alter the kinetic response.  The following basic temperature
model clarifies the temperature-substrate relationships present in biological
waste treatment systems:  for aerobic degradation both k and Ks increase
logarithmically with increased temperature; for anaerobic decay k increases
logarithmically with increased temperature and Ks decreases logarithmically
with increased temperature.

*Biological treatment, *Waste treatment, *Kinetics, Aerobic treatment,
Anaerobic treatment, Temperature

Arrhenius equation
458D

WATER TREATMENT PLANT WASTES DISPOSAL-PART 2,

Westerhoff, G. P. and Daly, M. P.

Journal of the American Water Works Association, Vol. 66, No. 6, p 379-384,
June 1974.  3 fig, 6 tab, 5 ref,.

The available alum-sludge treatment and disposal methods were evaluated by
pilot plant studies so that the Sturgeon Point Water Treatment Plant could
be improved in accordance with the Federal Water Pollution Control Act
Amendments of 1972.  Processes evaluated included alum recovery, recycling
of recovered alum, pressure filtration, scroll centrifugation, basket
centrifugation, vacuum filtration, chemical coagulation, a belt-filter-press
system, and artificial freeze-thaw.  It was concluded that the processes or
combinations of processes most feasible at the Sturgeon Point Plant are
pressure filtration, precoat rotary-vacuum filtration, scroll centrifugation,
freeze-thaw plus vacuum filtration, and alum recovery plus horizontal vacuum
filtration.

*Waste treatment, *Waste disposal, *Sludge treatment, *Sludge disposal,
Filtration, Coagulation, Centrifugation, Chemical precipitation, Evaluation

*Alum
                                         458

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459D

NEW APPROACH TO PREVENTING BULKING SLUDGE,

Rensink, J. H.

Agricultural University, Wageningen, Holland, Department
of Water Purification and Waste Water Disposal

Journal of the Water Pollution Control Federation, Vol. 76, No. 8,
p 1888-1894, August, 1974.  4 fig, 2 tab, 26 ref.

One of the problems associated with the activated sludge treatment of waste
water is bulking sludge which settles and compacts poorly.   Bulking sludge
causes the loss of activated sludge and a breakdown in the process.  The
occurrence of bulking sludge in batch, completely mixed, and plug-flow systems
was studied.  It was found the sludge volume index (SVI) of the batch system
was constant at a loading of 300 g BOD5/day/kg MLSS and had a value below 100
(normal).  The SVI of the completely mixed system rose as the loading increased.
If the loading was above 300 g BOD5/day/kg MLSS, the sludge of the batch system
bulked after many days of operation but the completely mixed system bulked
immediately after one or two days.  The SVI at a loading of 100 and 300 g
BOD5/day/kg MLSS in the plug-flow system was low, stable, and similar to the
SVI of the batch system.  The filamentous microorganisms that caused bulking
were Sphaerotilus natans, Flavobacter, Flexibacter, or Haliscomenobacter.
One of the microorganisms usually predominated depending on the initial sludge
and organic loading.  The batch system had more sludge growth than the
completely mixed system.

*Actlvated sludge, *Bulk density, Microorganisms, Organic loading,
Biochemical oxygen demand, Waste water treatment, Biological treatment

*Sludge volume index, *Bulklng
460D

RECOVERY OF ESCHERICHIA COLI FROM CHLORINATED SECONDARY
SEWAGE,

Braswell, J. R., and Hoadley, A. W.

Florida University, Gainesville, Florida, Department
of Environmental Engineering Sciences

Applied Microbiology, Vol. 28, No. 2, p 328-329, August, 1974.  1 fig,
1 tab, 5 ref.

If bacterial assays are to be used to test the efficacy of chlorination of
secondary sewage effluents and if effluent standards are to place limitations
upon discharges of indicator bacteria, then dependable standardiEed methods
must be employed for their enumeration.  This study examined injury to
E. coli that occurred during chlorination and evaluated the current methods
for counting the fecal coliforms in chlorinated effluents.  Methods studied
included most probable number (MPN) determined on 5-tube serial dilutions
in lactose broth and in EC broth incubated at 44.5 degrees C and membrane
filters incubated on m-FC medium and spread plates on Trypticase soy agar.
Decreases in viable counts obtained by all methods tested occurred exponen-
tially.  The decrease in viable count determined by the membrane filter
technique had a higher and more variable rate than the other techniques.
Recovery of unstressed cells occurred equally well by all the methods.  The
results of the study demonstrated that counts of fecal coliforms in chlorinated
secondary effluents must be considered low when measured by currently used
techniques.  The difference between counts made with present methods and
the true viable counts increased with the length of exposure to chlorine.

*Bioassays, *Bioindicators, *Standards, *Coliforms, Chlorination, Sewage
treatment, Disinfection, Chlorine, Bacteria, Analytical techniques

Escherichia coli, Standard methods
                                           459

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461D

OYSTERS, ALGAE AND SEWAGE,

Douglas, J. H.

Science News, Vol. 106, No. 11,  p 170-171, September 14,  1974.   3 fig.

Scientists at the Woods Hole Oceanographic Institution have in the pilot plant
stage a method of removing the inorganic compounds of nitrogen and phosphorous
by using them to grow algae to feed oysters.   The laboratory expects facilities
like their pilot plant to produce about 6,000 bushels of  oysters per acre of
tank per year.  The seaweed that is being grown, Irish moss, is also economi-
cally attractive because it contains carrageenan, a binder used in ice cream
and cosmetic manufacture which has no synthetic substitute.  A crop of 25 to
50 tons of seaweed per acre per year is expected.  It is  estimated that a
facility large enough to provide tertiary sewage treatment for a coastal town
of 50,000 might have an annual income of $4 or $5 million from the sale of
oysters and seaweed.  Problems with the system that have  not been solved
include the presence of viruses which might become concentrated in the oysters
and the removal of heavy metals which will become concentrated in the oysters.

*Tertiary treatment, *Nutrient removal, *0ysters, *Agriculture, *Economic
feasibility, Phosphorus, Nitrogen, Biological treatment,  Sewage treatment,
Heavy metals, Viruses

Seaweed
462D

SUTTON TO SOFTEN WATER BY ION EXCHANGE,

Water and Waste Treatment, Vol. 17, No. 8, p 44, 46, August, 1974.  1 fig.

A 470,000 pound contract for equipment to soften drinking water supplies was
awarded to PD Process Engineering by Sutton District Water Company, Surrey,
Great Britain.  The softening is accomplished by dealkalization which reduces
the total hardness and reduces the dissolved solids.  The water produced
reduces scale and is more acceptable to industry.  The water to be treated
enters a ion exchange resin where the calcium and magnesium hardness salts
are exchanged for hydrogen ions.  Bicarbonates in the water combine with the
hydrogen ions and carbon dioxide is released when the water passes through
a degasser.  Seventy percent of the total flow is treated; the total hardness
is reduced from 290 ppm to 125 ppm.  The treated water is blended with the
remainder.  The ion exchange resins are automatically regenerated after a
set limit of impaired ability is reached.  The final system will consist of
two streams each having three ion exchange resins operating while one is
being regenerated.  The plant is designed to fail safe in the case of a
failure.

*Ion exchange, *Water softening, ^Hardness (water), *Scaling, Water
purification, Water quality, Equipment, Costs, Potable water, Foreign research

Dealkalisation, Great Britain
                                           460

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463D

ACHIEVEMENTS IN WASTE WATER PURIFICATION AND MECHANICAL
SLUDGE DRYING BY MEANS OF SYNTHETIC ORGANIC POLYMERS  (PROGRES
REALISES DANS LA CLARIFICATION DES EAUX RESIDUAIRES ET LE
SECHAGE MECANIQUE SES BOUES PAR L'EMPLOI DE POLYMERES
ORGANIQUES DE SYNTHESE),

Boeglin, J. C.

Institut de Recherches Hydrologiques de Nancy, France

Pure and Applied Chemistry, Vol. 37, No. 3, p 343-374, 1974.  13 fig, 4 tab,
19 ref.

Solid-liquid separation is found in all waste water treatment processes.
Solid-liquid separation eliminates suspended matter from the waste water,
purifying the water before disposal or for reuse in the plant by recycling.
It also allows the maximum concentration of the solids in the form of
slurries or sludges.  The sludges and slurries can undergo a mechanical
dehydration treatment to produce a solid sediment that can be incinerated
or removed with almost no cost and handling problems.  The synthetic
flocculants now on the market greatly improve purification and treatment
methods that include solid-liquid separation.  In order to use these polymers
in an exact manner, the mechanism of their action must be known.  Examples
are given illustrating the actions of flocculants in the different phases
of purifying and treatment processes for waste water and sludges.

*Separation techniques, *Waste water treatment, *Flocculation, *Water
purification, Incineration, Slurries, Sludge, Polymers, Suspended solids,
Dehydration
464D

COLUMNS REPRESENTING MOUND-TYPE DISPOSAL SYSTEMS FOR
SEPTIC TANK EFFLUENT:  1. SOIL-WATER AND GAS RELATIONS,

Magdoff, F. R., Bouma, J., and Keeney, D. R.

Journal of Environmental Quality, Vol. 3, No. 3, July-September, 1974.
8 fig, 4 tab, 15 ref.

Columns were designed to model a mound-type disposal system for receiving
septic tank effluent on problem soils.  The columns were filled with gravel
to represent creviced bedrock, silt loam to represent the original topsoil,
a sand or sandy loam fill representing fill material, gravel to represent
the seepage bed, and another layer of silt loam to represent the mound
cover.  Septic tank effluent was applied to the columns at a rate of 2 cm
every 6 hours.  Until permanent ponding at the fill-gravel interface caused
by crusting occurred, the fill was aerobic and the silt loam representing
the original topsoil was anaerobic.  Higher redox potentials were present
in the fill than in the silt loam.  After the continuous ponding, moisture
tension fluctuations almost stopped, the subcrustal soil became anaerobic,
and the redox potentials greatly decreased and became negative.  When field
conditions were simulated by perforating the column walls, aerobic conditions
were maintained in the subcrustal fill.

*Model studies, *Sewage disposal, *Aerobic conditions, *Anaerobic conditions,
Landfills, Puddling, Methane

*Mound-type disposal system
                                            461

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465D

TWO AWT PLANTS FOR FITCHBURG, MASS.,

Parker, W. H., and Callahan, W. F.

Camp Dresser and McKee Incorporated, Boston,
Massachusetts

Civil Engineering-ASCE, Vol. 44, No. 9, p 90-93, September, 1974.  5 fig.

The city of Fitchburg, Massachusetts, is currently building two advanced
waste water treatment plants.  One plant is a two-stage activated sludge
plant for treating the domestic waste waters of Fitchburg and Lunenburg.
The second plant is a physical-chemical plant using activated carbon to
treat the industrial waste waters of the two large paper companies near
the town which contribute 90 percent of the pollutional load.  The design
a.Ti(l operation of the two plants is described.  Two plants were necessary
for Fitchburg because of the high volume of waste water produced by the
paper companies.  The activated carbon plant was chosen to process the
industrial waste water because pilot plant studies showed that it produces
a better quality effluent with more consistent BOD and COD removal and
better color removal.  The activated carbon was less prone to upsets from
highly variable loads and could be shut down or operated at much less than
full capacity.

*Activated sludge, *Domestlc wastes!, Industrial wastes, *Pulp and paper
industry, Facilities, Biochemical oxygen demand, Chemical oxygen demand,
Massachusetts, Waste water treatment, Design, Pilot plants


*Physical-chemical treatment
 466D

 COAGULATION-FILTRATION PRACTICE AS RELATED TO
 RESEARCH,

 Journal of  the American Water Works Association, Vol. 66, No. 8,
 p  502-503,  August, 1974.   24 ref.

 In the field  of water treatment, clarification generally means the solids-
 liquid separation process  which may include coagulation, flocculation,
 sedimentation, and filtration.  Filtration is merely one step in the total
 process.  The laboratory jar test is the conventional method for determining
 the optimum coagulant dosage for plant operation.  Plants with expert staff
 may also employ zeta potential measurements, filterability test, pilot-
 filter monitoring, residual-coagulant analyses, or interfacial-turbldity
 monitoring.   The jar test  is limited because of the subjective nature of
 the floe evaluation and the difficulty of duplicating conditions of water
 being treated in a plant.  The filterability of a floe is a measurable
 property of the raw water, the equipment, or the floe itself.  Iron floes
 ware discovered to filter  best near the isoelectric point of the floe.  The
 efficiency  of removal of negatively charged clay particles was improved by
 charging the  surface of sand columns electropositively.  It has been found
 the turbidity removal improves with increased electrophoretic mobility of
 suspended clay materials and that coagulating chemicals are required in the
 influent to a filter for the removal of algae and particles of activated
 carbon.

 *Coagulation, *Filtration, *Flocculation, *Sedimentation, *Water pollution,
 *Water treatment, Algae, Activated carbon, Turbidity, Zeta potential

 *Filterability tests, Pilot-filter monitoring, Residual-coagulant analyses,
 Electrophoretic mobility,  Jar test
                                            462

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467D

SPLIT CHLORINATION:  YES7-NO?,

Kothandaraman, V., and Beuscher, D. B.

Water and Sewage Works, Vol. 121, No. 7, p 90-92, July, 1974.  3 tab, 9 ref.

Illinois has made the continuous disinfection of waste water effluents con-
taining fecal coliform bacteria mandatory.  Chlorination is the primary
method used.  Better efficiency results in better economy, and split chlor-
ination has been advocated since 1956 for this reason.  This process consists
of a portion of the total applicable chlorine dosage administered at the
head end of the contact chamber and the remainder being added at another
location along the contact basin.  It has been suggested that split chlor-
ination improves the bacterial kill when it reduces the chlorine demand that
is exerted.  Collins and Selleck concluded that the germicidal activity of
chlorine residual decreases measurably with time, suggesting that chlorina-
tion of waste water effluent at two different points in the contact basin
could improve the efficiency of the process.  A grab sample of about 20 liters
of secondary effluent was gathered each day of an experimental run at the
Greater Peoria Sanitary District treatment plants.  Initial bacterial density
was enumerated prior to chlorination on each sample.  Two batch reactors were
installed in which 2 liters of effluent samples were placed.  Total chlorine
dosage rates and contact time were chosen so that results of bacterial
analyses of the samples could be compared.  It was determined that split
chlorination does not enhance the waste water chlorination process.

*Water pollution, *Waste water treatment, *Effluent control, "^Disinfection,
*Chlorination, Water purification, Sampling, Bacteria membrane processes

*Split-chlorination, Fecal coliform bacteria, Secondary waste effluents
468D

OLD CANAL CONVERTED TO TREATMENT PLANT,

Dutton, C. S.

Procter and Redfern Limited, Toronto, Canada

Water and Pollution Control, p 24-25, July, 1974.  1 fig.

A waste treatment facility was required by the Canada Starch Company, due
to a high-strength effluent.  The BOD readings for its corn wastes was up
to 3000 ppm.  A scarcity in suitable land for a conventional treatment plant,
because of river configuration and the plant's proximity to a village, re-
sulted in a 1968 waste sampling and flow measurement program under the
direction of Procter and Redfern engineers.  In-plant modifications ensued,
with certain process waste streams isolated, allowing a recycling of high-
strength by-products and a collection of the more potent wastes for treat-
ment.  One waste source had a daily BOD equivalent to a town of 20,000 people,
and the volume and type of effluent varied daily.  A single-cell aerobic
facultative lagoon was decided upon, having a low capital cost and a capa-
bility of 85 to 90 percent BOD removal.  This is a dilute biological system
in which the mixed liquor solids developed within the aerated waste do not
exceed a concentration of 100 ppm.  The suspended solids concentration in
the treated effluent just about equals the mixed liquor solids concentration
within the lagoon itself.  There is adequate intensity to maintain the total
supernatant liquid with a positive dissolved oxygen residual.  Anaerobic de-
composition on the bottom of the lagoon results.

*Waste water treatment, *Water pollution, *Effluent control, Biochemical
oxygen demand, Industrial wastes, Lagoons, Biological treatment, Aerobic
treatment, Suspended solids, Activated sludge

*Mixed liquor concentration, Hydrogen sulfide, Sulphuric acid, Low-rate
stabilization pond systems
                                       463

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469D

SEWAGE TREATMENT IN THE POTTERIES,

Banks, P. A.

John Taylor and Sons, Great Britain

The Consulting Engineer, Vol. 38, No. 7, p 41, 44, 45, July, 1974.  4 fig.

At Stoke-on-Trent, Great Britain, a new sewage treatment plant is being
completed to help the redevelopment of Stoke into a city with an expanded
economy with a larger range of social and municipal services.  The reclama-
tion work on derelict clay pits and slag heaps has fostered redevelopment
in industrial towns within their boundaries.  A proposed motorway-standard
link with the M6, along with other new programs, has helped combine what
was once six towns into one.  The Strongford sewage works on the River Trent
is an extension of a plant first constructed on the southern city boundary
in 1930.  A policy of centralization of sewage treatment resulted in the
reduction of the number of works maintained in the general area and the
transfer of flow to Strongford.  The plan to close the Hanley works and
three other smaller works necessitated a sewer 2 m in diameter for the
transfer of up to six times the dry weather flow 5 miles south.  A scheme
to route the link sewer was developed according to an assessment of the
subsidence risk arising from two active coal mines in that area.  The works
require a high effluent standard, including preliminary treatment units and
primary sedimentation arranged in two inter-connected streams.

*Sewage treatment, *Water pollution, *Water quality management, *Municipal
water, Industrial wastes, Effluent control, Rivers, Coal mine wastes

*Preliminary treatment, Link sewer, Clay pits, Slag heaps
 470D

 DISINFECTION:   THE  LAST  LINE  OF  DEFENSE  FOR
 POTABLE WATER,

 White,  G.  C.

 Water and  Sewage  Works,  Vol.  121,  No.  7, p 66-67,  July,  1974.

 A survey by  the Community Water  System revealed  that  77  percent  of water
 treatment  plant operators are inadequately trained in elementary water
 microbiology, with  46 percent deficient  in chemistry  relating  to the
 operation  of  the  facility.  A review of  the  important aspects  of chlorina-
 tion chemistry  was  presented.  In  the  free residual process, free chlorine
 displays the  most powerful  germicidal  ability of all  chlorine  compounds,
 with the exception  of chlorine dioxide.  This process should be  operated  so
 that the HOC1 content of the  final residual  is 85  to  90  percent  of the
 total residual.   Ammonia nitrogen  and  organic nitrogen cause the most inter-
 ference with  the  process.   Ammonia nitrogen  may be removed by  chlorine
 easily,  requiring approximately  10 parts of  chlorine  for each  part of
 ammonia.   Organic nitrogen  compounds can produce a system of unstable
 residuals, with reactions lasting  for  days before  completion,  often re-
 sulting in N-chloro compounds  with taste and odor  problems in  the distri-
 bution  system.  The coliform  concentration is a salient  factor in the
 evaluation of raw water  quality.   At Lake Tahoe, California, a plant pro-
 duces effluent  with a coliform concentration less  than 2.3/100 ml.  This
 potable standard  is achieved  with  chlorine doses of 2 to 3 mg/liter in the
 presence of  2 to  15 mg/liter  of  ammonia nitrogen.

 *Water  pollution, *Water quality management, *Disinfection, *Water
 purification, *Chlorination,  Nitrogen  compounds, Waste water treatment,
 Potability,  Coliforms

 *Free residual  process,  *Ammonla nitrogen, *0rganic nitrogen,  N-chloro
 compounds
                                        464

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471D

PEAT MOSS: AN ALTERNATIVE ADSORPTION MEDIUM,

Water and Pollution Control, Vol. 112, No. 8, p 18, August, 1974.  2 fig.

The University of Sherbrooke, Quebec is studying the application of peat moss
as effective filtration and adsorption medium, as an alternative to activated
charcoal in pollution abatement.  The price of peat at 3 to 4 cents per Ib is
desirable in comparison with that of activated charcoal at 40-60 cents per Ib.
Peat moss is made up of decomposed tissue of various plants, primarily that
of the genus Sphagnum, which can be found over an area of about 37,000 square
miles in Canada itself.  It is a sponge-like, highly porous structure with an
approximate surface area of 200 sq m/g.  It is composed of humic acids, and
provides cationic exchange properties.  On a weight basis, peat moss' adsorptive
capacity is significantly inferior to activated charcoal, but it has a positive
comparison on an economic basis.  This has prompted investigation into low
efficiency application of peat moss in control of agricultural sewage and some
industrial odors.  Studies are being conducted on the possibility of peat
moss filters in the treatment of industrial waste waters, since peat is known
to adsorb oils in amounts 8 to 12 times its own weight.  However, where there
are surfactants in substantial numbers, the adsorptive capacity of peat moss
is greatly diminished.  Also under investigation is the application of peat
moss in the adsorption of metals in industrial wastes.

*Water pollution, *Waste water treatment, *Peat, *Adsorption, Filtration,
Industrial wastes, Agricultural wastes, Activated charcoal, Surfactants,
Dyes, Oil, Mercury, Proteins, Oil spills, Sewage treatment, Hydrogen sulfide,
Iron, Zinc, Nickel, Copper, Ammonia

*Peat moss, Humic acids, Dimethylamine
 472D

 SOLID ADSORBENTS FOR GAS AND LIQUID TREATMENT,

 Pick, P.  E.

 Process and Chemical Engineering, Vol.  27, No. 6, p 23-27, June, 1974.  3  fig,
 2  tab.

 Solid adsorbents such as silica gel and  the synthetic or naturally occurring
 zeolites  called molecular sieves can be  utilized in the purification,
 separation and dehydration of  gases and  liquids.  Davison gel, a pure form of
 silicon dioxide (99.7 percent  S102), which is made under carefully controlled
 conditions from sulphuric acid and sodium silicate results in an amorphous
 polymeric structure with the following percentage composition:  Si as Si02,
 99.7; Fe  as Fe203, 0.03; Al as A1203, 0.10; Ti as T102, 0.09; Ca as CaO, 0.01;
 Na as Na20, 0.02; Zr as Zr02,  0.01; trace elements, 0.03.  This structure
 consists  of beads with pores with a diameter ranging from 20-40 A.  The pore
 size and  particle sizes can be determined by controlling the reaction
 conditions during their manufacture, with the granules being sieved into
 particle-size ranges.  An extrusion process is used in the formation of bead
 form silica gel.  The result is a pure,  chemically inert material which is
 structurally strong with a high attrition resistance.  The total surface
 area will range around 700-800 sq m/g, depending upon pore size.  Silica gel
 has a great affinity for water, and can  hold 40-100 percent of its weight
 as water.  It can adsorb organic molecules, with the selectivity order based
 on polarisability, degree of unsaturation and volatility.  This gel can be
 utilized  in the dehydration of air, carbon dioxide, natural gas, alcohol
 mixtures, aromatics like benzene, and for chromatographically separating
 organic fractions.

 *Silica gels, *Gases, *Liquid  wastes, *Separation techniques, *Purification,
 *Dehydration, Zeolites, Water  pollution, Waste water treatment

 *Solid adsorbents, *Gas and liquid treatment, Silicon dioxide, Sulphuric
 acid, Sodium, Silicate, Amorphous polymeric structure, Extrusion process,
 Molecular sieves
                                           465

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473D

REVERSE OSMOSIS AND ULTRAFILTRATION,

Del Pico, J., and White, P. W.

Abcor, Incorporated, Cambridge, Massachusetts

Metal Finishing, Vol. 72, No. 8, p 29-31, August, 1974.  6 fig.

The practical application of reverse osmosis and ultrafiltration now includes
the concentration, purification and/or fractionation of a large spectrum of
industrial streams.  Both processes utilize a semi-permeable membrane as the
separating agent, and pressure is used for the driving force to achieve
separation.  The semi-permeable membrane is considered a "surface" filter,
allowing the passage of water and some of the smaller sized solutes, while
being capable of retaining larger solutes, particulates and colloidal matter.
A counterpressure is produced, depending on the numerical concentration of
molecules retained by the membrane.  This osmotic pressure must be overcome
before water removal can occur.  The nature of the membrane is the primary
factor in determining which species are retained, and which permitted passage.
Ultrafiltration membranes, on the other hand, are relatively open membranes,
retaining only large molecules and colloidal particles, allowing salts
passage through the membrane with water.  The osmotic counterpressure is low
and operating pressures are usually below 100 psi, and throughput per unit
area is 1 to 10 times greater than with RO membranes.  The size of the
molecule to be retained determines: the type of membrane utilized.

*Reverse osmosis, *Waste water treatment, *Water pollution, Filtration,
Semipermeable membranes, Industrial wastes, Separation techniques,
Colloids, Water purification, Distillation

*Ultrafiltration, Osmotic pressure, Particulate matter, Membrane configuration
474D

PRECOAT FILTRATION ON ROTARY VACUUM FILTER,

Berndt, H.

Aufbereitungstechnik, Vol. 15, No. 3, p 137-140, November 3, 1974.  5 fig,
11 ref.

A pre-coat filter, which was developed from the rotary vacuum filter, operates
continuously to filter suspensions by utilization of gas pressure.  The filter
includes the stationary filter tank where the suspension is introduced,
the filter drum, provided with filter cells subdivided by the chamber division
strips, the control valve, the swinging agitator, the filter cake removing
device, and the driving mechanism.  The pre-coat filter may consist of various
materials.  A detailed description of the pre-coat filtration process is
presented.  Pre-coat filtration on the rotary vacuum filter permits the
separation of suspensions which are unable to be separated into the solid
and liquid phase by other conventional continuous filtration processes.

^Filtration, Water treatment, Separation techniques

*Precoat filters, *Rotary vacuum filter, Gas pressure, Filter cake removing
device, Swinging agitator, Chamber division strips, Stationary filter tank,
Filter drum
                                           466

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475D

TERTIARY TREATMENT:  THE WRONG SOLUTION TO A NON-PROBLEM?,

Stokes, H. W., and Hedenland, L. D.

Civil Engineering-ASCE, Vol. 44, No. 9, p 86-89, September, 1974.  1 fig.

Design criteria and operating techniques are suggested that allow higher levels
of BOD removal than those generally thought to be possible with activated
sludge treatment.  The Tapia Water Reclamation Plant, California, reliably
achieves 98 percent BOD and suspended solids removal by optimizing the
secondary treatment.  The process design for this plant is given.  It covers:
primary treatment; aeration system; process air requirements; secondary
sedimentation tanks; chlorine contact tanks; reaeration tanks; aerobic
digestion; and, designed effluent quality criteria.  The most important
parameters for precise operation are aeration control through the use of
nitrate nitrogen profiles, precise daily solids balance of the aeration
system, and constant activated-sludge return rate.   A secondary sludge plant
that can produce 98 percent BOD removal and nitrify the ammonia, will have
a effluent that contains almost no colloidal material, should not need
filtering, and will have a turbidity of less than one Jackson Unit.  A
properly designed and operated secondary treatment (activated sludge) plant
can adequately remove suspended solids, BOD, ammonia, coliform, and virus.
Tertiary treatment is needed only to remove the heavy metals, phosphorus
and nitrate-nitrogen.

*Activated sludge, *Tertiary treatment, *Design criteria, *0peration and
maintenance, Biochemical oxygen demand, Treatment facilities, Suspended
solids, Heavy metals, Nutrient removal, Water quality control, Biological
treatment, Nitrogen, Phosphorus removal, Bacteria,  Viruses
476D

ACTIVATED SLUDGE BULKING (Kassei odei no barukingu),

Sona, K., and Kyushin, S.

Kemikaru Enjiniyaringu, Vol. 19, No. 7, p 37-41, July, 1974.  6 fig, 2 tab,
12 ref.

The sedimentation ability of activated sludge and bulking, the causes of
bulking, the hypothetical mechanism of filamentous bulking, and countermeasures
for bulking are discussed.  In an operating aeration tank, the maintaining of
MLSS  (mixed liquor suspended solid) concentration at an appropriate level and
the BOD load at a relatively low level (usually less than 0.3 kg BOD/kg
MLSS/day) is important.  The ratio of nutrients in the sludge is important,
and if the ratio of carbon/nitrogen increases, the amount of carbohydrates in
bacteria will increase; one way of preventing bulking.is to add enough
nitrogen.  Chlorine is deleterious to filamentous fungi rather than to
Zoogloea, and the addition of about 0.3-0.6 percent (to dry sludge weight)
in the return sludge can improve the settling of bulking sludge greatly.
To prevent other deleterious effects, chlorine must be carefully measured.
Intermittent adding of other oxidizing agents such as hydrogen peroxide is
reported to be effective; the limits are 20-400 ppm, but less than 20 ppm
will  be ineffective and over 400 ppm will cause partial deflocculation.
Radical changes in the quantity and composition of waste water flow will
induce bulking; for this reason, a pre-treatment of water is desirable.  The
type  of pre-treatment will affect the efficiency of activated sludge greatly.
The  low temperature of aeration tank water can cause bulking both by SVI
increase and the increase of carbohydrate at a lower  temperature.  An
intermittent fill and draw method of waste water flow has been successful in
preventing bulking.

*Activated sludge, *Bulk density, *Settling basins, Nutrients, Biochemical
oxygen demand, Chlorlnation, Pre-treatment, Temperature

*Bulking, Mixed liquor suspended solids  (MLSS)
                                467

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 477D

 DIGESTION AND DEWATERING OF  PHOSPHORUS-ENRICHED  SLUDGES,

 O'Shaughnessy,  J.  C.,  Nesbitt,  J.  B., Long, D. A.,  and
 Kountz,  R.  R.

 Pennsylvania State University,  University Park,
 Pennsylvania,  Department of  Civil  Engineering

 Journal  of the  Water Pollution  Control  Federation,  Vol. 46, No.  8, p  1914-1926,
 August,  1974.   10  fig,  1 tab, 17 ref.

 Chemical-biological treatment for  the removal of phosphorus appears to be
 the  most economical method because it can use the existing treatment
 facilities.   Several aspects of the chemical precipitation of phosphorus are
 discussed:   the effects of aluminum-phosphorus precipitate on the anaerobic
 digestion process;  the identity of the  different forms of phosphorus  and
 the  effects  of  anaerobic digestion on them; whether the excess sulfate ion,
 released into solution during phosphate removal  with alum, increases  the
 production of hydrogen sulfide; and, the effects of the aluminum-phosphorus
 precipitate on the dewatering properties of raw  sludges.  It was found that
 a biological sludge containing  a complex aluminum phosphate precipitate will
 not  harm the anaerobic digestion stage  and will  not be redissolved in the
 digester.  Sulfate ion added during the removal  of  phosphorus did not cause
 hydrogen sulfide to be produced during  anaerobic digestion.  Sludge containing
 the  precipitates of chemical additives  dewaters  more readily than a sludge
 without  these precipitates.  It was concluded that  removal of phosphorus
 from waste water by chemical precipitation with  alum or sodium aluminate and
 the  addition of sludge containing  these precipitates to an anaerobic  digester
 has  no adverse  effect  on the anaerobic  digestion process.

 *Phosphorus  removal, *Chemical  precipitation, *Activated sludge, *Digestion,
 Anaerobic conditions,  Waste  water  treatment, Sludge treatment

 *Alum, Sodium aluminate
478D

BIODEGRADABILITY OF A CARBOXYMETHYLOXYSUCCINATE
DETERGENT BUILDER,

Klein, S. A., and Jenkins, D.

California University, Berkeley, California, Sanitary
Engineering Research Laboratory

Journal of the Water Pollution Control Federation, Vol. 46, No. 9,
p 2107-2117, September, 1974.  10 fig, 4 tab, 7 ref.

Trisodium carboxymethyloxysuccinate (CMOS)  is being used as a detergent
builder that contains no phosphorus or nitrogen.  The fate of CMOS during
waste water treatment by pilot scale septic tank-percolation field systems
and oxidation ponds is discussed.  Septic tanks with a two-day residence
time are ineffective in removing CMOS; 10 percent CMOS removal was achieved
by the septic tanks.  CMOS degradation was  essentially total in aerobic
percolation fields following septic tank treatment.  CMOS degradation in
excess of 90 percent was obtained in anaerobic percolation fields.  The
removal of CMOS is virtually complete when  the dissolved oxygen of the
percolation field effluent is one mg/liter.  Algal oxidation ponds required
an acclimation period of 150 days (about five times average hydraulic
residence times) before significant CMOS removal occurred.  The ponds
receiving 30 mg/liter CMOS acclimated to CMOS slower and achieved lower
levels of CMOS removal than ponds receiving CMOS levels of 15 mg/liter.

*Detergents, *Degradation, *Septic tanks, *Percolation, Biological treatment,
Waste water treatment, Oxidation lagoons
*Trisodium carboxymethyloxysuccinate (CMOS)
                                           468

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479D

GRANULAR FILTERS FOR TERTIARY WASTE WATER TREATMENT,

Baumann, E. R., and Huang, J. Y. C.

Iowa State University, Ames, Iowa

Journal of the Water Pollution Control Federation, Vol. 46, No. 8,
p 1958-1973, August, 1974.  14 fig, 3 tab, 24 ref.

A dual-media filter (coarse anthracite over finer sand) overcomes the problems
of head loss across the filter and no penetration of the solids into the bed
that are present when a normal, graded, single-medium filter is used to filter
the suspended solids left after secondary treatment.  A pilot plant was
constructed and operated at the Ames, Iowa, Pollution Control Plant to test
procedures to be used in the design of tertiary waste water filters and to
determine the effectiveness of granular filtration in reducing the pollution
potential of the effluent from a water pollution control plant.  The results
showed that the final effluent from the control plant should be filtered
through a dual-media filter with 38.10 cm of uni-sized 1.84 mm anthracite
on top of 38.10 cm of uni-sized 0.55 mm sand.  The filtrate suspended solids
should be about 4 to 5 mg/liter, the filtration rate can be as high as
6 gpm/sq ft, and the influent suspended solids can be as high as 40 mg/liter.
The following steps should be included in a design of a pilot plant operation
to determine the optimum economic design of a tertiary filter plant:  determin-
ation of the proper size and depth of anthracite and sand based on the
particular type of waste water; determination of the backwash rate required for
the chosen media size and depth combination; development of curves relating the
net water production to the filtration rate under different run lengths; and,
development of the curves relating run length to the filtration rate at
different suspended solids concentration.

*Filters, *Filtration, *Tertiary treatment, Design criteria, Pilot plants,
Suspended solids, Waste water treatment, Iowa

Dual-media filter
 480D

 TRICKLING FILTRATION OF A WASTE CONTAINING NTA,

 Cleasby, J. L., Hubly, D. W., Ladd, T. A., and
 Schon, E. A.

 Iowa State University, Ames, Iowa, Department of Civil
 Engineering

 Journal of the Water Pollution Control Federation, Vol. 46, No. 8, p 1873-1887,
 August, 1974.  8 fig, 4 tab, 20 ref.

 Interest is being shown in the use of the sodium salt of nitrilotriacetic
 acid (NTA) as a replacement compound for polyphosphate detergent builders.
 However, before NTA can be allowed to replace phosphates in our environment
 its ultimate fate as it goes through the water ways and waste treatment plants
 must be known.  The effect of NTA on a trickling filter and the NTA-removal
 ability of the trickling filter are presented.  There was no effect on the
 efficiency of a trickling filter to remove BOD, COD, and TOC at NTA levels
 of 4, 8, and 16 mg/liter.  Two to three weeks were needed at an NTA feed
 level of 4 mg/liter before substantially complete NTA removal occurred.
 NTA levels of less than 0.5 mg/liter were consistently reached at dosage
 levels of 4 and 8 mg/liter Na3NTA during the summer and fall.  During cold
weather operation, the NTA removal was less complete (less than 2 mg/liter
 in the effluent when the NTA level was 8 mg/liter).  No functional relationships
between NTA removal and the removal of other organic substances were observed.
The NTA had no effect on nitrification efficiency or on the ability of the
 trickling filter to remove heavy metals.

*Trickling filters, *Nitrllotriacetic acid, *Detergents,  Biochemical oxygen
demand, Chemical oxygen demand,  Nitrification, Heavy metals, Waste water
treatment
                                           469

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481D

FLUIDIZED-BED SLUDGE INCINERATOR DESIGN,

Liao, P. B.

Kramer, Chin, and Mayo, Incorporated, Seattle,
Washington

Journal of the Water Pollution Control Federation, Vol. 26, No. 8,
p 1895-1913, August, 1974.  6 fig, 3 tab, 22 ref.

Theories of fluidization and sludge combustion, methods for development of
design criteria, equations, and procedures for design calculations for a
fluidized-bed waste water sludge incinerator are discussed.  The design
criteria and equations derived are the result of the pilot plant operation.
They can be used for prototype incinerator design,  i design method is given
which ranges from determining the amount and rate of sludge to be incinerated
to determining the best air pollution control equipment.   An incinerator
can be designed by using the equations and the relationships between sludge
loadings, air supply, and fuel requirements.  Fluidized-bed treatment is a
sanitary and efficient method of waste water sludge disposal and has a
minimum of detrimental effects on the environment.

*Sludge disposal, *Waste water treatment, *Incineration,  Design, Ultimate
disposal, Design criteria, Pilot plants, Burning, Facilities
 482D

 AMMONIA DESORPTION  BY DIFFUSED AERATION,

 Srinath,  E.  G.,  and Loehr,  R. C.

 Cornell University, Ithaca, New York, Agricultural
 Waste Management Program

 Journal of  the Water Pollution Control Federation, Vol. 46, No. 8,
 p  1939-1957, August, 1974.  12 fig,  2 tab, 18 ref.

 The removal  of nitrogen from waste water  is becoming  increasingly important.
 Since nitrogen in untreated waste water exists as ammonium nitrogen, ammonia
 desorption  is a  viable method of nitrogen control.  Theoretical considerations
 to predict  ammonia  desorption from water  and waste water, experiments on
 removal of  ammonia  from waste water  by diffused aeration, and predictive
 equations relating  ammonia  desorption efficiency to environmental and process
 conditions  are discussed.   The quantity of ammonia desorbed from a solution
 depends on  the concentration of undissociated ammonia, the gas-liquid surface
 area, the mass-transfer coefficient, and  the partial  pressure exerted by
 ammonia in  the gas  phase.   The rate  of diffusion is influenced by pH,
 temperature, and viscosity.  The equations presented  allow better estimates
 of the ammonia loss from artificial  and natural aerated systems to be made.
 Equations were developed to determine the ammonia desorption coefficient
 under quiescent  and aerated conditions and to determine the quantity of ammonia
 lost under  various  environmental conditions.

 *Nitrogen,  *Waste water treatment, *Ammonia, *Waste water, Air-water
 interfaces,  pH,  Temperature, Viscosity, Mathematical  models

 Ammonia desorption
                                           470

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48 3D

BUBBLE SIZE AND CONTACT TIME IN DIFFUSED AERATION
SYSTEMS,

Mavinic, D. S., and Bewtra, J. K.

Windsor University, Windsor, Ontario, Department of
Civil Engineering

Journal of the Water Pollution Control Federation, Vol. 46, No. 9,
p 2129-2137, September 1974.  7 fig, 4 ref.

One of the most common ways of supplying oxygen to aeration basins is by
diffused bubble aeration.  The contact time of air bubbles with the liquid
is one of the most important parameters influencing the efficiency of
diffused bubble aeration.  The procedure for determining bubble contact
time, ways to increase this time, and the effects of different parameters
on this time are discussed.  Four systems were observed:  a simple column of
water; water circulation and an upward cocurrent air-water flow caused by
diffused air; water circulation and counter-current air-water flow caused by
pumping; and, water circulation and downward cocurrent air-water flow caused
by pumping.  The unit contact time in each system was dependent on the air
flow rate and the unit contact time decreased with an increase in air flow.
The unit contact time is independent of the depth for the first three systems.
The total contact time will increase almost linearly with the diffuser
submergence.  System three (water circulation and counter-current air flow
caused by pumping) provides: the highest unit contact time.  This is caused
by the slowing of the air bubbles by countercurrent air-water flow.

*Aerobic treatment, *Activated sludge, *Aerated lagoons, *Aeration, Sewage
treatment, Waste water treatment, Flow, Water circulation, Pumping
484D

REBIRTH OF THE SEWAGE FARM,

The Consulting Engineer, Vol. 38, No. 7, p 49-51, July, 1974.  2 fig.

The Metropolitan Sanitary District of Chicago has developed a land reclamation
program.  Digested sludge has been disposed of mainly by a barge down the
Illinois River to Fulton County, 200 miles from Chicago.  From this location
it is pumped eleven miles underground to reservoirs, where it is sprayed
by sprinklers over a portion of 11,000 miles purchased by the MSD.  More than
1500 M gallons of sewage is treated each day.  The treatment removes 90 percent
of the solids in settling tanks, and high-rate heated digestion treats the
solids and accompanying liquids.  The Chicago district produces approximately
1,000 dry tons of digested sludge.  A new scheme of expansion includes the
construction of deep tunnels and underground reservoirs for storing storm
sewage awaiting treatment.  The Muskegon County Wastewater Management System
of Michigan is pumping sewage from ten towns through a rising main to a
treatment plant north-west of Muskegon.  BOD is reduced 70-90 percent by
conventional primary and secondary treatment.  Vast lagoons store the effluent
where solids settle out.  The lagoons will be dredged in five years.  From
the lagoons the effluent flows to an irrigation system where it is disinfected
with chlorine.

*Sewage treatment, *Waste water treatment, Water pollution, Biochemical
oxygen demand, Sludge removal, Chlorination, Reservoirs, Storm sewage,
Lagoons

*Digested sludge, Settling tanks, High-rated heated digestion
                                        471

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485D

AN OVERLOADED SLUDGE PLANT?  TRY CHEMICAL TREATMENT,

Pearson, S. C., and Soltis, R. G.

Hercules Incorporated, Wilmington, Delaware

Water and Sewage Works, Vol. 121, No. 7, p 56-58, July, 1974.  2 fig, 8 ref.

It has been determined that the solids transport capacity is the sum of two
parts, one of which, the capacity due to sludge withdrawal, is alterable by
the plant operation.  An increase of solids loading on the clarifier from
12 to 16 Ib/sq ft/day necessitates that the sludge recycle be increased
from 50 to 65 percent to prevent solids carryover.  A limited activated
sludge recycle capacity can influence the chemical treatment objectives to
a large extent.  These objectives include the reduction of solids loading
on the final clarifiers and maintenance of good solids capture across the
final clarifiers in the face of flow increase; both objectives depend
upon the accomplishment of maximum BOD removal in the primary basin by
adding an inorganic coagulant and flocculant to the raw sewage and by
adding a flocculant to the mixed liquor to ensure complete clarification.
A flocculant is added to the sludge thickener for the prevention of a
hydraulic overload on the digesters.  The experiment had three different
phases, including the establishment of a baseline by operating the plant
at overload with no chemical treatment; the evaluation of the potential
flocculation of mixed liquor as the only form of treatment; and full chemical
treatment in primary and secondary systems.

*Sludge removal, *Chemical treatment, *Clarification, *Flocculation, Waste
water treatment, Separation techniques, Solid wastes, Mixed liquor,
Digestion, Biochemical oxygen demand

*Solids transport capacity, Inorganic coagulant, Hydraulic overload
486D

TREATMENT OF CRUDE SEWAGE IN TWO HIGH-RATE ACTIVATED-
SLUDGE PLANTS OPERATED IN SERIES,

Boon, A. G., and Burgess, D. R.

Water Pollution Research Laboratory of the
Department of the Environment, Great Britain

Water Pollution Control, Vol. 73, No. 4, p 382-395, 1974.  4 fig, 4 tab,
11 ref.

Experiments by the Water Pollution Research Laboratory of the Department of
the Environment have determined that during the treatment of settled domestic
sewage from Stevenage, England at a temperature of 17 degrees C the growth
rate constant ranged from 0.15 to 0.59 d to the minus first power apparently
as a result of different degrees of inhibition of the nitrifying bacteria
under various conditions of treatment.  Recently it has been shown that when
treating similar sewage, nitrification is achieved consistently when the
wastage rate of the activated-sludge is 0.36 d to the minus first power
corresponding to a sludge age of 2.78 d, when the temperature is in the range
of 16 to 21 degrees C.  The implication is that the growth rate is constant
for Nitrosomonas at more than 0.36 d to the minus first power.  The average
BOD of effluent has been shown to be attainable consistently at 50 mg/liter,
maintaining at the same time a high-rate of treatment with the activated
sludge settling in the final sedimentation stage.  Results confirmed that when
treating settled sewage in the same plant, the high quality of effluent can
be achieved with short periods of aeration of sewage at high sludge loadings,
as long as the rate of treatment is not limited by the concentration of
dissolved oxygen in the mixed liquor.

*Water pollution, *Effluent treatment, *Sewage treatment, *Activated sludge
treatment, Biochemical oxygen demand, Nitrification, Sewage bacteria,
Sedimentation, Aeration


*Settled domestic sewage, *Nitrosomona
                                    472

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487D

FILTRATION ENGINEERING'S SYMPOSIUM ON MEMBRANE
SEPARATION,

Heneghan, W. F.

Filtration Engineering, Vol. 5, No. 5, p 7-8, 10-12, 14-18, 23-24, 26, 28,
July/August, 1974.  7 fig, 1 tab.

Ultrafiltration is defined as a solvent and a solute placed in a pressure side
of a membrane.  A permeate flows through the membrane with a concentrated
solute remaining on the same side of the membrane.  The solute may be solids,
colloids or various organic molecules.  Pore structure and the material of
the membrane influence significantly the efficiency of the separation.  This
is a low-energy separation process, and is an alternative to spray drying,
evaporation, selective precipitation and other fine media filtration processes.
Applications of ultrafiltration cover a large range of particle sizes, ranging
from ten microns on the high side to ten angstroms on the low side.  On the
low side the membranes are similar to reverse osmosis membranes.  Ultrafiltra-
tion 's basic characteristic; however, is that the osmotic pressure is extremely
low in solution and operating pressures are about 50 psi, whereas reverse
osmosis is closer to 500 to 1,000 psi.  The flux per unit area is the same or
higher than the reverse osmosis separation.  Ultrafiltration is less costly
than chemical treatment for the treatment of oil emulsions.  It involves no
chemical usage, therefore adding no pollution to the system.  In the General
Electric system discussed, a 2.0 percent emulsion is concentrated up to about
50 percent, at the point of combustibility.  Because the membrane is only a
physical barrier to the passage of oil droplets, the changes in waste
characteristics have no effect on the Ultrafiltration system's performance.

*Membrane processes, *Filtration, *Separation techniques, Reverse osmosis,
Organic matter, Oil wastes, Colloids, Centrifugation

*Membrane separation, *Ultrafiltration, Hydrocyclones, Oil emulsions
488D

4632 IDS REDUCED TO 322 BY REVERSE OSMOSIS,

Wold, P. B.

Water and Sewage Works, Vol. 121, No. 7, p 67, July, 1974.

Reverse osmosis was used to convert water with 4,000 ppm total dissolved solids
to water of the quality described by the Environmental Protection Agency and
the North Dakota State Health Department as potable.  It was determined that
systems based on the hollow nylon fiber devices were feasible because of the
fiber membrane's resistance to high and low pH and bacterial degradation.
An operating pressure of 400 psig or lower was required.  Smaller space is
needed for a hollow fiber membrane system.  Included in the system was a sand
filter for removing suspended solids from the feed water.  Hardness is removed
by a weak acid ion exchange installation.  The reverse osmosis system can
remove 90 to 95 percent of the dissolved solids, based upon the DuPont
"Permasep" permeaters.  Rejected water is used for the regeneration of the ion
exchange unit and sand filter backwash.  Under consideration is the use of
the reject water for spraying gravel roads for dust control.  The water should
contain over 25,000 ppm TDS, with many being deliquescent in nature.

*Reverse osmosis, *Water pollution, *Memb,rane processes, *Water quality
control, Ion exchange, Bacteria, Electrodialysis

*Hollow nylon fiber membrane treatment system, EPA, DuPont "Permasep"
pemeators, Total dissolved solids (TDS)
                                          473

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 489D

 WASTEWATER TREATMENT,

 DiGiane, F. A., and Scaramelli, A. B.

 Massachusetts University, Amherst, Massachusetts,
 Department of Civil Engineering

 Journal of the Water Pollution Control Federation, Vol. 46, No. 6,
 p  1109-1121, June, 1974.  I.  tab, 131 ref.

 Physical-chemical  techniques  for removing nutrients, biodegradable organic
 and colloidal suspensions were reviewed.  A new physical-chemical plant at
 Rosemount, Minnesota, consists of pretreatment, clarification, filtration,
 adsorption, ion exchange, and disinfection; with a capacity to reduce BOD
 from  200 ing/liter  to 10 mg/liter, and ammonia and phosphorus to one mg/liter.
 Treatment by coagulation, filtration, adsorption, ion exchange, reverse
 osmosis, flocculation, sedimentation, foam separation, and carbon adsorption
 techniques were explored.  In one instance, a mobile 18 process, trailer
 mounted pilot plant was empiloyed to evaluate physical-chemical treatment for
 industrial waste,  using various integrated processes to gain a desired
 effluent quality.  U. S. installations where the removal of phosphorus has
 been  achieved and  European phosphorus removal by coagulation were compared.
 Domestic and paper mill waste treatment  utilizing the low lime process was
 examined in both bench and pilot plant studies.  Eighty-five percent removal
 of suspended solids and complete phosphorus and 60 percent removal of COD
 was accomplished by the addition of lime to pH 10.0 and the recarbonation to
 pH 8.5.  Laboratory tests dealing with the removal of phosphorus from laundry
 wastes indicated that calcium chloride was the most effective precipitant,
 with  optimum removal occurring at pH 10.0.

 *Reviews, *Waste water treatment, *Phosphorus, *Water pollution, *Coagulation,
 *Adsorption, *Nutrients, *Folymers, *Filtration, *Clarification, Ion exchange,
 Reverse osmosis, Disinfection, Biochemical oxygen demand, Ammonia, Solids
 separation, Nitrogen, Membrane processes, Ozone, Pulp wastes

 *Physical-chemical waste water treatment systems, Nonionic polyacrylamide
 polymer, Microstrainers, Sand filters, Ultra-high-rate  filtration

 490D

 ACTIVATED SLUDGE,

 Azad, H. S., and Weddle, C. L.

 Journal of the Water Pollution Control Federation,  Vol.  46, No. 6,  p 1123-1135,
 June, 1974.  124 ref.

 Activated sludge treatment of waste was reviewed.   Yeast was found to be
 effective in the conversion of nitrogen,  phosphorus,  and carbon in domestic
 waste water into a marketable protein,  if sugars were added to the feed.
 Photosynthetic bacteria was utilized in the treatment of certain industrial
 waste water, with excess sludge used as food for animals and fish.   Hydrogen
 peroxide was discovered as  a.n effective source of oxygen in activated sludge
 treatment.   After acclimation, the H202-fed sludge  showed a BOD reduction
 of 385 to 15 mg/liter.   The contact stabilization process was examined in
 the treatment of combined sewer overflows, with a reported 82 percent BOD
 removal with 15 minute contact and 2.7  hour aeration period.   Extracellular
 heteropolysaccharides  were  determined to  be readily biodegradable,  verifying
 the theory of total oxidation.  Heat-treatment liquor of activated sludge
was discovered to be as  amenable  to biological treatment as  settled domestic
waste water.  The effect of the addition  of p-amino-benzoic acid on the
biotreatability of coke-oven waste waters was  investigated.   When the acid
was added to the influent  at a few mg/liter,  it accelerated  the biodegradation
 rate of some nitrogenous constituents.   Bio-chemical factors,  including
 p-amino-benzoic acid and glucose,  were  discovered  to  greatly enhance the
 rates of thiocyanate,  cyanide, and ammonia bio-oxidations.   The growth factors
were also determined to  promote the biochemical oxidation of conventionally
 resistant organic bases  like pyridine.

 *Activated  sludge,  *Waste water  treatment, *Water pollution,  Nitrogen,
Phosphorus,  Domestic waste  water,  Yeasts, Biochemical oxygen demands,  Feed,
Industrial  waste water,  Biodegradation, Biological  treatment,  Oxidation,
Bacteria,  Mathematical models, Separation techniques,  Aeration,  Effluents,
Cyanide,  Ammonia

Hydrogen peroxide,  Thiocyanate,  Pyridine
                                    474

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49 ID

SEWAGE SLUDGE CENTRIFUGING GETS SCOTTISH OK,

Surveyer, Vol. 4285, p 39-40, July, 1974.  2 fig.

A report has been published by the Scottish Development Department on full-scale
trials to investigate the efficiency of centrifuging as a means of dewatering
sewage sludges.  The Lockerbie Composting Center has composted partially
dewatered sluo"   with organic residue from domestic waste.  Sludge enters
the center at an average rate of 36.5 cu m per day from many sewage treatment
works and a few septic tanks.  The original vacuum filter dewatering plant,
utilizing wood flour as filter medium, processes sludge at a maximum rate
of 5 cu m per hour.  An hour is required to prime the filter drum, being
effective only 4 1/2 hours.  A machine was installed of the solid bowl scroll
discharge type, with a rated capacity between 6 and 10 cu m per hour.
Polyelectrolyte is added to help flocculation.  It is fed into the machine
so that mixing and floe formation occur within the feed zone.   Experiments
with the sewage sludge centrifuge were performed with various  pond depths,
polyelectrolyte dosing rates and concentrations, centrate quality, and the
applicability of the capillary suction time technique in the assessment of
appropriate polyelectrolyte dosages.  At Lockerbie, sludge cakes are composted
with domestic organics in a biostablilizer.  There has been no apparent
diminuation in composting activity, nor has any biological inhibition from
the usage of polyelectrolytes been noted.

*Sludge disposal, *Centrifugation, *Polyelectrolytes, *Sewage  sludge, Domestic
wastes, Water pollution, Dewatering, Septic tanks

*Sewage sludge centrifuge, Vacuum filter, Capillary suction time
492D

INTERFACING NEWLY DEVELOPED TECHNOLOGY WITHIN PRESENT
WASTEWATER TREATMENT TRAINS,

Belfort, G.

Hebrew University of Jerusalem, Jerusalem, Israel,
School of Applied Science and Technology, Human
Environmental Sciences Program

Journal of the American Water Works Association, Vol. 66, No. 8, p 504-505,
August, 1974.  1 tab, 6 ref.

Much research and pilot plant experimentation is underway to investigate the
usefulness of membrane processes for waste water treatment in the pulp and
paper, mining, photographic, paint, food and pharmaceutical, textile and
electronic industries.  The concern has formerly been with the evaluation of
membrane performance or permeator design with different municipal effluents,
and its longevity.  Advanced processes, being more complicated, cost more to
operate, although their rate of treatment is high and their land utilization
is low.  For conventional processes less external energy is required.
Traditional biological treatment processes have lower operating and maintenance
costs but higher capital investment than the advanced processes including
the pressure-driven membrane processes.  However, the buildup of conservative
constituents resulting from multiple recycling, will have to be taken into
consideration.  Dissolved inorganic ions, refractory organics, and viruses
are among the conservative constituents for normal biological secondary
treatment.  Reverse osmosis is one of the only processes that can totally
remove such conservative constituents from the effluent stream.  There exist
many differences in structure and operation between a specific group of
advanced processes (pressure-driven membrane) and the traditional processes
for waste water treatment.  Research and planning can minimize or avoid
potential problems associated with the integration of diverse methods.

*Waste water treatment, *Membrane processes, *Water pollution, Reverse osmosis,
Pilot plants, Municipal wastes, Effluents, Economics, Biological treatment,
Filtration

*Pressure-driven membrane processes, Inorganic ions, Conservative constituents
                                      475

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493D

CONTAINING THE FLOW OF SEWAGE SLUDGE,

Environmental Science and Technology, Vol. 8, No. 8, p 702-703, August, 1974.
1 fig, 1 tab.

Philadelphia, Pennsylvania, conducted a simple "unit" operation for the con-
tainment of sewage sludge.  The sludge is anaerobically digested and pumped
to a lagoon for thickening: to about 12.5 percent solids.  This thickened
sludge is transferred to a 2 million gallon holding barge which is towed out
to sea.  The discharge of the sludge occurs over a 6 mile course at approxi-
mately 30,000 gpm.  No lasting harmful effects were determined by a joint
study on this process.  Because of an increase in ocean and outfall sludge
dumping, ocean disposal regulations and restrictions have increased to such
an extent that land disposal is expected to increase.  Landfilling sites,
however, are scarce and expensive, precipitating the old technique of land
use of sludge for agricultural needs like soil conditioning and fertilizing
supplementation.  For example, sludge disposal takes care of 80,000 gpd
near Pensacola, Florida.  The optimum rate of sludge application for corn,
sorghum and soy growth was estimated at 1 inch per week.  Cattle fed these
grains for 6 months are to be tested for heavy metal and other toxic sub-
stances in the animals' tissues.  The U.S. Department of Agriculture is
investigating composting and trenching of sludge.  Estimates are that primary
sludge provide only 1 percent of nitrogen usable for agriculture.  Allegheny
County Sanitary Authority introduced vacuum filters for dewatering sludge,
utilizing the maximum heat, so as to generate steam as a final product by
burning a mixture of sewage solids and solid waste materials.

*Sewage sludge disposal, *Digestion, Water pollution, Heavy metals,
Pesticides, Pathogenic bacteria, Landfills, Sewage treatment plants,
Fertilizer, Agriculture, Dewatering

*Sludge incineration, Environmental Protection Agency
49 4D

FLOCCULANTS FLOURISHING,

Chemical Week, Vol. 115, No. 11, p 34, September 11, 1974.

The demand for high-polymer flocculants in Japan in 1974 will be 9000 metric
tons, an increase of 3600 metric tons over 1973.  There is a predicted
30 percent growth in the demand for 1975.  Predicted demand is 15,000 m.t. in
1976 and 18,000 m.t. in 1977.  The major use of Japanese-produced organic
flocculants is for waste water treatment.  Eighty percent of the high-polymer
flocculants used are produced from acrylamide.  The oil crisis of 1973 caused
the price of flocculants to increase to $3.60-4.00/kilogram in the last months
of the year.  Labor cost increases have caused further increases in the
flocculant price to $4.00-4.60/kilogram.  Major producers of chemical
flocculants in Japan include Sanyo Chemical Industries, Sumitomo Chemical,
and Asahi-Dow.  These figures were reported by the Chemical Economy Research
Institute, a private chemical research group generally regarded as a reliable
source of information, particularly for chemicals not covered by statisticians
of Japan's Ministry of International Trade and Industry.

*Flocculation, *Waste water treatment, *Chemical industry, Chemical
precipitation, Coagulation, Foreign research, Costs

*Flocculants, Japan, Chemical Economy Research Institute
                                   476

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495D

TREATMENT OF SERVICE WATER WITH OZONE,

Tabata, N., and Mori, M.

Mitsubishi Denki-Giho, Vol. 48, No. 5, p 639-645, May, 1974.  17 fig, 6 ref.

Ozone treatment of service water is being practiced in European countries.
In Japan, it is being studied as a method to deodorise service water.  Ozone
treatment presents several technical problems which require further investi-
gation because of the differences in conditions of Japanese and European
service water.  The first question asked was whether ozone treatment or
activated carbon treatment is superior in its deodorising effect.  Reports
on the study of this question show that the ozone treatment is more effective
than activated carbon.  Many problems of treatment technique such as the
nitric acid radical, residual ozone in water, and ozone decomposition of
exhaust gas are discussed.  The performance of a contact tank of gas and
liquid which is the most important part of a study of treatment devices is
also discussed.

*0zone, *Activated carbon, Waste water treatment, Chemical treatment

*Service water, *Deodorisation
 496D

 PHILADELPHIA PILOTS — BUILDS OXYGEN ACTIVATED SLUDGE,

 Guarino,  C. F., Nelson, M. D.,  and Edwards, A. B.

 Philadelphia Water Department,  Philadelphia, Pennsylvania

 Journal of  the Environmental Engineering Division, Vol. 100, No. EE4,
 p  919-935,  August, 1974.  14 fig, 7 tab.

 Philadelphia, Pennsylvania, is  expanding all three of  its  large water pollution
 control plants.   The  city has been running oxygen activated sludge  pilot
 plants since March, 1971.  UNOX pilot units were operated  at each plant.
 Comparative cost  studies between air activated and oxygen  activated systems
 were  made.  The construction costs and  annual costs  for the oxygen  system
 were  estimated to be  $11,060,000 and $1,418,000, respectively.  The air
 system would have construction  costs of $13,165,000  and annual costs of
 $1,506,000.  The  extensive pilot work indicates that the activated  sludge
 process using pure oxygen is a  feasible unit process for treating waste water.
 During the  pilot  study, high levels of  treatment were  consistently  achieved
 even  when the organic loading and oxygenation time varied  widely.   The total
 cost  of a system  using pure oxygen is less than using  air  even though using
 air has a lower annual cost in  the aeration part of  the system.  The city
 of Philadelphia has decided to  build activated sludge  facilities using pure
 oxygen at two of  its  plants.  The facilities will have capacities of 150 mgd
 and 210 mgd.

 *Activated  sludge, *0xygen, *Municipal  wastes, *Waste  treatment, Facilities,
 Pilot plants, Pennsylvania

 UNOX, Oxygen activated sludge,  Philadelphia, Pennsylvania
                                      477

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497D

OPERATIONAL ASPECTS OF URBAN SEWAGE WORKS,

Hatfield, J., Ormerod, K., and South, C.

Leyland Urban District Council, Great Britain

Water Pollution Control, Vol. 73, No. 4, p 369-381, 1974.  1 fig, 2 tab.

Sewage treatment and sewerage works of three relatively small local authorities
in Great Britain and their problems of management are discussed.  Included
are details concerning the division of works within the three authorities,
a description of the treatment units at the works, and the management of the
labor force employed.  It was concluded that where competent management
staff are available on sewage works, they should be included in consultations
with the persons responsible for the design of treatment plants.  More stress
needs to be placed on determining the ecologically best method of sludge
disposal and on providing the most appropriate treatment method.  The small
works described can produce results comparable with the results of much
larger units when reasonably designed and well run.  Smaller works also
maintain much of the team spirit and pride of achievement which often can not
be found on larger works.

*Sewage treatment, *Sewerage, *Management, *Design, Facilities, Sewage
districts, Sludge treatment, Sludge disposal
 49 8D

 ASBESTOS REMOVAL  SYSTEMS PERFECTED,

 Water  and Waste Treatment, Vol.  17, No. 6, p 13, June, 1974.

 Scientists  at  the Canada Centre  for Inland Waters have assembled  systems
 that can remove up to  99.8% of the asbestos fibers from drinking  water.
 The treatment  costs an estimated five cents per  1000  gallons.  Ordinary
 sand filtration removes approximately 90% of the asbestos-like fibers
 in water.   However, the remaining 10% consists of very small  fibers
 which  may present the  greatest health hazard.  The most effective system
 for removal of these fibers is coagulation and filtration used together
 with a polyelectrolyte. The  polyelectrolyte acts to  refine the precipita-
 tion and coagulation so that  even the smallest asbestos particles are
 removed.  This work has important implications for the asbestos mining
 industry as well  as for municipalities  on affected waterways.

 *Asbestos,  *Water treatment,  *Potable water, Coagulation, Filtration,
 Polyelectrolytes, Filters, Public health, Costs

 Sand  filters,  Asbestos mining industry, Treatment methods
                                      478

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499D

HIGH-RATE FILTRATION FOR TORONTO'S  ISLAND WATERWORKS,

Tredgett, R. G.

Proctor and Redfern Group

Water and Pollution Control, Vol. 112, No.  8, p  37-39,  41, August,  1974.
2  tab.

Since 1917, Toronto's  old  Island Filtration plant has been operated on
what is loosely  referred to as  coagulation  followed by  direct  filtration.
Alum is added  at  pump  suctions  to raw water which is  then pumped  to the
filters without  flocculation and settling.  The  plant performs acceptably
confirming the idea that good quality raw water  can be  filtered with
minimum treatment.  This fact was of significant consideration in the
design of new  facilities.  Records  of raw water  quality kept by the plant
were analyzed.   Lake Ontario was shown to be  generally  a source of  g< od
quality raw water with isolated occurrences of high turbidity.  Two pilot
studies were performed early in 1971.  The  mechanical mixing required to
produce a satisfactory floe for direct filtration and the direct  filtration
of coagulated  water at rates not less than  4  g/sq ft/min were  examined.
The investigation resulted in the recommendation to build a plant employ-
ing rapid coagulation  followed  by direct filtration.  Plans include
immediate expansion to 60  mgd capacity and  further extensions  to  replace
the old plant  when the demand increases.  Chemical treatment will include
alum, chlorine,  sulphur dioxide, and fluoride which have been  used pre-
viously.  Improvements of  chemical  treatment  include  prechlorination,
addition of ammonia hydroxide and polyelectrolyte filter aids.  The esti-
mated cost for construction of  the  first phase of the extensions  is $9.0
million.

*Water treatment, *Water purification, *Water quality,  ^Facilities, Water
supply, Chlorination,  Coagulation,  Filtration, Chemical precipitation,
Costs, Lake Ontario, Canada

Toronto, Canada
500D

TREATED EFFLUENT GOES  "UNDERGROUND",

Water and Sewage Works, Vol. 121, No. 9, p 60-61, September, 1974.
2 fig.

A new regional water pollution control facility for the City of West Palm
Beach, Florida includes wells to inject treated effluent more than one half
mile underground, rather than disposing of wastes through an ocean outfall.
The secondary treated  effluent will be disposed of by well injection into
the boulder zone of the Floridan aquifer.  A testing phase is now underway;
a 3500 foot deep well  will be constructed so that it can be used for test
injection purposes and later as a monitoring well for the final disposal
system.  In addition,  a 1200 foot deep well will tap an aquifer of saline
water, which will be used as an injection well to dispose of the salt water
that will be produced  when the deep test hole is being drilled.  The wells
are part of an overall plan for treatment facilities capable of handling
up to 128 million gallons of sewage per day.  Separate management of sewage
and storm water for the City of West Palm Beach and the Town of Palm Beach
are planned.  The projects will also test the capabilities of extended
aeration on a very large size municipal treatment plant.  The extended
aeration, with long retention time in the aeration basin, is not subject
to shock loading, and  requires no highly skilled operations, thus reducing
operational costs.  The system has been designed to include growth poten-
tial and to meet federal effluent requirements for advanced treatment,
essentially to the potable water stage by 1983.

*Waste disposal wells, *Injection wells, *Effluents, Sewage disposal,
Water pollution control, Water resources management (applied), Municipal
wastes, Aeration, Operating costs, Legislation,  Potable water, Florida

West Palm Beach,  Florida


                                         479

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•snip

ENVIRONMENT, ENERGY COSTS SUGGEST OXYGEN ACTIVATED
SLUDGE AS WASTEWATER TREATMENT APPROACH,

Kulperger, R. J.

Union Carbide Corporation

Professional Engineer, Vol. 44, No. 10, p 29-31, October, 1974.  4 fig.

The UNOX System technology for an oxygen-activated sludge system for waste
water treatment is currently used by 125 treatment plants in several coun-
tries.  The system consists of a covered, staged aeration or oxygenation
basin where oxygen rather than air is used as the aerating gas.  Feed oxygen,
waste water and return sludge all flow through the basins in the same direc-
tion.  High dissolved oxygen levels (4 to 8 mg/liter) and high solids levels
(4000 to 8000 mg/liter) are maintained in the oxygenation basin.  Treatment
time is reduced and the system possesses high stability to shock organic
loads.  The costs of energy and power in recent years have escalated, and
the UNOX System has an economic advantage in terms of power usage.  Total
power to operate an oxygen activated sludge system compared to a diffused
air system will be reduced from 30 to 50 percent.  For example, in Detroit,
Michigan, both types of plants are operated and the relative annual operating
costs of the UNOX system showed a savings of $311,500 per year, most of which
is the result of reduced power usage.  In addition, the ability of a system
to turn down in response to organic loads imposed on the plant is an important
factor, relative to power usage.  The typical UNOX System reduces average
consumption by 20 percent, calculated by the early design years of a plant
plus diurnal variations at full plant load.  At 1.5 cents per KWH, 100 Hp
costs over $10,000 per year.  The amount of land required for oxygen-activated
sludge systems is also less than that of air diffusion systems because of the
reduced sewage residence time.  The residence time is reduced because of the
high mixed liquor concentrations maintained in oxygenation basins.  With in-
creases in power costs, and decreases in available land, this method is a
viable alternative to traditional air systems for secondary waste water treat-
ment.

*Activated sludge, *0xygenation, *Aeration, Costs, Energy, Power, Dissolved
oxygen, Secondary treatment, Waste water treatment

*UNOX System
502D

WATER FACTORY 21,

Chandler, C. R.

Orange County Water District Board of Directors,
Fountain Valley, California

National Water Supply Improvement Association Journal, Vol. 1, No. 1,
p 23-30, July, 1974.  6 fig, 2 tab, 5 ref.

The Orange County Water District is constructing an advanced fresh water
factory called Water Factory 21 in Fountain Valley, California.  It is a
combination waste water reclamation plant and desalting module with an
ultimate capacity of 30 mgd of high quality domestic water.  The Water Factory
is part of a massive hydraulic barrier project initiated to prevent further
intrusion of seawater into the groundwater basin in Orange County.  The water
produced will be injected into the groundwater basin for replenishment and
will act as a deterrent to seawater intrusion.  The injected water develops
an underground hydraulic pressure mound and creates a false fullness to the
groundwater basin.  Deep well water, imported water, reclaimed waste water,
and desalted seawater were evaluated as potential sources of water for the
injection program.  The source of water adopted is a combination of half re-
claimed waste water and half desalted seawater.  Reasons for choosing this
combination include:  the reduction of 15,000 acre feet of waste discharge
to the ocean annually; the reduction of dependency on northern California and
Colorado River water supplies; and, the addition of ocean brine to waste water
discharge in the ocean, thereby reducing the impact on the marine environment.
Water Factory 21 is providing the design, construction, and operating tech-
nological experience that is needed for the future development of water supply
facilities in different areas throughout the United States.

*Water reuse, *Desalination, *Groundwater recharge, *Water quality control,
Waste water treatment, Facilities, Water management (applied), Groundwater
resources, Design, Construction

Colorado River, Fountain Valley, California

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503D

THE CLOSE LINK BETWEEN WATER SUPPLY AND SEWAGE
PURIFICATION,

van Duuren, F. A.

Die Siviele Ingenieur in Suid-Afrika, Vol. 16, No. 6, p 216-217, June, 1974.

The control and the prevention of pollution are now equally important and
the gap between water supply and sewage purification has narrowed at an
exponential rate; a practical linking of water supply and sewage purification
must occur.  Acceptance of the fact of the indivisibility of water resources
in South Africa is demonstrated by the cooperation shown between the Water
Engineering Division of the South African Institution of Civil Engineers
and the Institute of Water Pollution Control (South Africa).  The problems
of pollution in South Africa are intensifying because of the concentration
of the population and the rapidly increasing industrialization.  Industrial-
ization is the more important cause because of the synthesis of new chemical
compounds being about 400 new compounds are on the South African market
annually.  The treatment of domestic sewage is considerably less difficult
than treatment of industrial wastes because domestic sewage is usually of
known properties and at constant strengths.  It is proposed that treatment
of domestic wastes and industrial wastes should be separate.  Industries
should utilize closed water circuits.

*Waste water treatment, *Domestic wastes, *Industrial wastes, *Water
pollution control, *Water purification, Water quality control, Chemical
wastes, Pesticides, Chemicals, Recirculated water, Sewage treatment

South Africa
                                          481

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                            ANALYTICAL TECHNIQUES
001E

APPLICATION OF REAL-TIME MASS SPECTROMETRIC TECHNIQUES TO
ENVIRONMENTAL ORGANIC GEOCHEMISTRY.  II. ORGANIC MATTER IN
SAN FRANCISCO BAY AREA WATER,

Simoneit, B. R.,  Smith, D. H. Eglinton, G., and Burlingame, A. L.

Space Science Laboratory, University of California, Berkeley,
California

Archives of Environmental Contamination and Toxicology, Vol. 1, No. 3,
p 193-208, 1973.   5 fig, 1 tab, 24 ref.

The solvent soluble (organic) matter passing through a fine fitted filter
was investigated in samples of water taken from the San Francisco and San
Pablo bays, the Carquinez Strait, and an estuary in the confluence of the
Sacramento and San Joaquin rivers.  The petroleum ether extracts (ranging
from 2.5 to 102 microgram/liter) were analyzed using gas chromatography,
computer coupled gas chromatography/mass spectrometry, and high resolution
mass spectrometry.  The organic compounds identified in these extracts are
quite diverse and consist mainly of hydrocarbons from various sources.
Some phthalate esters occur at various sampling sites.  It is concluded
chat the techniques of gas chromatography/mass spectrometry, and high
resolution mass spectrometry are ideally suited to the assessment of some
of the potential interactions of pollutants and other organic compounds
in the aquatic environment.

Rivers, *Bays, Solvents, Solubility, Sampling, Water Sampling, *0rganic Matter,
"Oil Wastes, Gas Chromatography, Mass Spectrometry

*San Francisco Bay, San Pablo Bay, Carquinez Strait, Sacramento River,
San Joaquin River
  002E

  TRACEMETAL CONTAMINANTS,

  Dimensions/NBS, Vol. 57, No. 10, p 244-245, October, 1973. 2 ref.

  The determination of trace levels of toxic metals in natural waters is being
  investigated at the National Bureau of Standards.  A joint study of
  the chemical, biological, and other mechanisms operative in natural water
  systems for mobilization and transport of heavy metal focuses on the
  transformation of inorganic mercury into highly toxic forms.  Field samples
  of sediment and water are being analyzed for total mercury and organic
  mercury by nuclear magnetic resonance and mass spectrometry.  In another
  similar project, cathode ray polarography has led to the development of
  improved methods for determining metals and organic substances, such as
  nitriloacetic acid.  A stable isotope dilution procedure was developed
  using the spark source mass spectrograph for simultaneously determining
  a dozen trace elements in river water samples.  Concentrations in parts
  per billion were determined for mercury, cadmium, lead, and copper.

  Natural Resources, *Water Quality Standards, *Metals, Mercury, *Toxicity,
  Cadmium, Lead, Heavy Metals, Copper, Organic Acids

  Nuclear Magnetic Resonance, Mass Spectrometry, Polarography
                                             482

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00 3E

EVALUATION OF A LOW-COST ARSENIC AND SELENIUM DETERMINATION
AT MICROGRAM-PER-LITER LEVELS,

Caldwell, J. S., Lishka, R. J., and McFarren, E. F.

Environmental Protection Agency, Water Supply Research
Lab, Cincinnati, Ohio

Journal of the American Water Works, Vol. 65, No. 11, p 731-735, November
1973.  2 fig, 7 tab, 9 ref.

New methods and modification of known methods of detecting arsenic and
selenium in water are described.  In a modification, inorganic arsenic and
selenium are converted into gaseous hydrids by moving a balloon, which
serves as an expansion chamber for the generated gas, away from the
reaction vessel and the insertion of a length of vinyl plastic tubing
between them.  A method using atomic absorption spectrophotometry and
data for differentiating between organic and inorganic arsenic are
presented.  An open system was used for selenium.  The balloon was not
needed as an expansion chamber since selenium hydrid is apparently formed
almost instantaneously and the hold was unnecessary.  The procedures can
be performed in a few minutes and permit routine monitoring of water
supplies for arsenic and selenium.

Chemical Wastes, Water Pollution, *Monitoring, *Arsenic Compounds,
Waste Water

*Selenium
 004E

 WATER MONITORING THROUGH  CONTINUOUS  MEASUREMENT  OF  SEVERAL
 PARAMETERS  (Gewaesserueberwachung mit  kontinuierlicher  Multi-
 parametermessung) ,


 Umwelt,  No.  5  p  48,  October-November,  1973.

 Water quality  monitoring  instruments developed by Rheinmetall  GmbH,  Dusseldorf,
 West  Germany,  for measurement  of  several  parameters in  flowing and standing
 waters,  including wastewaters,  are described.  A buoy-secured  instrument is
 designed for the fully  automatic, continuous  measurement  and recording of
 temperature,  oxygen  content, pH value,  and electric conductivity in river
 waters and  in  moving sea  water.   The modular  system permits  extensions for
 the measurement  of additional  parameters, and the instrument can be integrated
 in water quality monitoring networks.   Such monitoring  networks give alarms
 whenever specific pollution limit values  are  exceeded.   Another portable,
 floating instrument  with  analog recording and digital output measures
 the same parameters  in  wastewaters.  It can be powered  by battery or from mains.

 *Water Quality Control, *Rivers,  Instrumentation,  Dissolved Oxygen Analyzers,
 Analog Models, On-Site  Tests

 *West Germany, Dusseldorf,  Rheinmetall GmbH
                                            483

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005E

PROPERTIES OF GB IN WATER,

Epstein, J.

U.S. Dept of the Army, Edgewood Arsenal, Aberdeen Proving
Ground Maryland

American Water Works Association Journal, Vol. 66, No. 1, p 31-37, January,
1974.  5 fig, 3 tab, 28 ref.

The possibility of contamination of water supplies with the nerve gas
isopropyl methylphosphonofluoridate (I), usually referred to as GB or Sarin,
at levels injurious to the consumer is discussed.  It is unlikely that GB
could be used to contaminate the water in the reservoir of any city.  The
hazards in handling GB, because of its high vapor toxicity, preclude the
use of quantities sufficient to contaminate reservoirs with a capacity on
the order of 100 million gallons to levels necessary to cause symptoms of
intoxication of the consuming public.  Although contamination of a small
volume of water is conceivable, it would still be hazardous to accomplish.
Should a water supply become contaminated, adequate methods (enzymatic,
chemical, and bioassay) for detection and analysis of the GB in water, and
treatment procedures to remove or destroy it, are available.

*Water Pollution, *Reservoirs, Cities, Domestic Water, Municipal Wastes

*Nerve Gas, *Isopropyl Methylphosphonofluoridate (I), GB, Sarin
00 6E

PESTICIDE ANALYSIS IN WATER,

Hurley, J. T.

State of Illinois Environmental Protection Agency,
Springfield, Illinois

American Water Works Association Journal, Vol. 66, No. 1, p 27-31, January,
1974.  12 fig.

The detection and analysis of pesticides in drinking water supplies are
discussed.  Pesticides can be divided into several classes according to
their chemical structure as follows:  chlorinated hydrocarbon pesticides,
organophosphorus pesticides, carbamates, and phenoxy herbicides.  In
investigating the levels and types of pesticides in water, it Is important
to know toxicity, extent of usage, persistence in the environment, biomagni-
fication, and sensitivity of detection.  The chlorinated insecticides are one
of the most important groups.  They are widely used, toxic to mammals,
persistent, have a long half-life, and undergo biomagnification, ultimately
being stored in the fatty tissue, of the body.  This gas chromatograph system
consists of five parts:  pressure regulator and flowmeter for the carrier
gas, sample-injection system, a column, a detector, and a recorder.
It is sensitive, selective, and suitable for determining pesticide levels in
water.

Instrumentation, Chromatography, *Gas Chromatography, *Measurement, *Pesticides,
*Chlorinated Hydrocarbons, Organophosphorus Pesticides, Carbamate Pesticides,
Herbicides, Water Pollution, Pollutant Identification, Municipal Wastes

Phenoxy Herbicides
                                        484

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00 7E

ATOMIC ABSORPTION SPECTROPHOTOMETER FACILITIES WATER ANALYSIS,

Water and Sewage Works, Vol. 121, No. 1, p 27, 45, January, 1974.

The use of an atomic absorption spectrophotometer for analyzing water at the
Ben Nesin Laboratory (New York) is described.  The laboratory is one of seven
which analyzes water from 18 reservoirs and four controlled lakes which supply
New York City.  At Ben Nesin, 40,000 samples a year are collected and 400,000
annual analyses performed, checking for 60 different substances, inclusive of
heavy and trace metals.  The atomic absorption technique is baser' on the fact
that the atoms of an element will when vaporized, absorb radiation passed
through them at specific wavelength limits which are different for each
element.  For the detection and measurement of most metals, the instrument
vaporizes the sample by flame in an air-acetylene, or air-propane burner.
Samples being tested for cadmium, copper, cobalt, nickel, and lead are
extracted with sodium hydroxide and hydrochloric acid.  Concentrated solutions
are prepared for analysis of zinc, chromium, strontium, iron, and manganese.
Silver, sodium, cadmium, and magnesium are run without concentration.  The
spectrophotometer is extremely reliable and sensitive, more so than automated
monitoring systems.

*Municipal Water, Instrumentation, *Spectrophotometry, *New York, Municipal
Wastes, Metals

*Atomic Absorption
008E

WATER-SEDIMENT SPLITTER FOR RUNOFF SAMPLES CONTAINING COARSE-
GRAINED SEDIMENT,

Fleming, W. G. and Leonard, R. A.

United States Department of Agriculture
Watkinsville, Georgia

Soil Sciences of America Proceedings, Vol. 37, No. 6, p 961-962,
November-December, 1973.  2 fig, 1 tab.

A water sediment sample splitter was designed and  constructed  for dividing
samples up to 20 liters into three equal and representative smaller  samples  for
chemical and physical analyses.  This funnel-shaped device for  a mechanical
agitator divides samples containing particles up to two millimeters  without
first separating the sediment from the water.  Evaluation showed that  the
splitter divided samples containing coarse sediments into three parts  with a
distribution of 33 percent plus or minus two percent in each.  The device has
application in assuring representative samples of  runoff from watershed  or
similar runoff studies.

Runoff, *Surface Runoff, Watersheds (Basins), *Sediments, *Sampllng,
Ins trumentation

*Sample Splitter
                                         485

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009E

THE DETERMINATION OF HEAVY METALS IN DOMESTIC SEWAGE
TREATMENT PLANT WASTES,

Van Loon, J. C., Lichwa, J., Ruttan, D., and Kinrade, J.

Water, Air, and Soil Pollution, Vol. 2, No. 4, p 473-482, December, 1973.
9 tab, 10 ref.

Atomic Absorption spectroscopy procedures are outlined for the determination
of some important heavy metals in sewage treatment plant solids and liquids.
Problems associated with sample preparation and sample solution interferences
are described.  It is recommended that reference standards and internal
laboratory control samples be used to allow some assessment of the validity of
results.  Sewage treatment plant products both liquid and solid were analyzed
and results given for samples representing a wide range of sewage imput
patterns.

*Spectroscopy, *Heavy Metals, Analytical Techniques, *Sewage Treatment,
Treatment Facilities, Solid Wastes, Liquid Wastes, Waste Treatment, Sampling,
Laboratory Tests, Control Systems
 010E

 INTERDISCIPLINARY MONITORING OF THE NEW YORK BIGHT,

 Egan, W. G., Cassin, J. M., and Hair, M. E.

 Environmental Letters, Vol. 2 No. 4, p 205-215, 1972.  5 fig, 7 ref.

 Measurements were made in the New York Bight during 1969-1970 using in situ
 instrumentation together with associated monitoring devices for performance
 verification.  Feasibility studies indicated that in situ instrumentation can
 measure chlorophyll, bioluminescence, Gellbstoff, hydrogen ion concentration,
 dissolved oxygen, salinity and the location of the thermocline.  It is main-
 tained that in situ instrumentation may be adapted to continuous synoptic
 monitoring of the estuarine and oceanographic parameters necessary for
 mathematical modeling.

 *Measurement, *On-Site Investigations, Feasibility Studies, *Instrumentation,
 Monitoring, Performance, Hydrogen Ion Concentration, Dissolved Oxygen,
 Chlorophyll, Mineralogy, Thermocline, Salinity, *Water Pollution

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011E

CONSTRUCTION AND OPERATION OF A LABORATORY FERMENTER FOR KINETIC
MEASUREMENTS IN WASTE WATERS (BAU UND BETRIEB EINES LABORATORIUMS-
FERMENTORS FUR KINETISCHE MESSUNGEN AND ABWASSERN),

Behrens, U., Ringpfeil, M., Thielemann, H., Klappach, G.,
and Pohland, D.

Institut fur organisch-technisch Chemie der Akademie der
Wissenschaften der DDR.  Leipzig

Fortschritte Der Wasserchemie, No. 15, p 203-215,  1973.  7  fig, 6 ref.

The construction of a laboratory fermenter for  studying biological
purification processes  in wastewaters is described.  It consists of  a  16  liter
suspended vessel of Jena glass having an efficient aeration system.  Bio-
logical wastewater treatment can proceed discontinuously, continuously  and
continuously with sludge return.  Control of temperature and pH value  is
possible.  Carbon dioxide and oxygen are automatically determined in the
outgoing air.

Treatment Methods, *Biological Treatment, *Water Purification, Aeration,
Fermentation, Kinetics, *Waste Water Treatment

*Laboratory Fermenter
012E

A MODIFIED PROCEDURE FOR THE TTC-DEHYDROGENASE TEST IN
ACTIVATED-SLUDGE,

Klapwijk, A., Drent, J., and Steenvoorden, H. H. A. M.

Department of Water-purikfication, Agricultural
University, Wageningen, the Netherlands

Water Research, Vol. 8, No. 2, p 121-125, 1974.  7 fig, 4 tab, 13 ref.

The procedure for the determination of TTC-dehydrogenase activity of activated
sludge has been critically examined with respect to the termination of the
enzyme reaction, the extraction of formazan  (TF), the exclusion of oxygen in
the sample, the incubation temperature and the organic substrate used.  The
dehydrogenase activity measured by a modified TTC test correlates fairly well
with oxygen uptake.  Toxic substances such as zinc, phenol, cyanide and 2-4D
do not influence the oxygen uptake and dehydrogenase activity to the same extent.

*Activated Sludge, *Analytical Techniques, Toxicity, Oxygen Demand, Zinc, Phenols

TTC-dehydrogenase, Formazan, Cyanide
                                     487

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013E

APPLICATION OF THE CARBON CUP ATOMISATION TECHNIQUE
IN WATER ANALYSIS BY ATOMIC-ABSORPTION SPECTROSCOPY,

Dolinsek, F., and Stupar, J.

The 'Jozef Stefan' Institute, University of Ljubljana,
Ljubljana, Yugoslavia

The Analyst, Vol. 98, No. 1173, p 841-850, December, 1973.  8 fig, 8 tab, 16 ref.

A modified, laboratory-made small-scale Massmann carbon cup atomiser is
described, with particular reference to the atomic-absorption determination
of copper, lead, and cadmium in water samples.  Several parameters (sample
volume, time and temperature of the atomisation steps, sample composition)
have been investigated.  It was found that injection of a ten-microliter
sample in one portion is the most convenient technique with respect to sensi-
tivity and speed of operation.  Addition of EDTA causes an enhancement of
sensitivity, considerable when determining lead.  The absorption of these
elements on the polyethylene containers has also been examined in order to
evaluate possible errors that may arise after sample storage.  The detection
limits are 0.45 ng/ml of lead, 1.7 ng/ml of copper and 0.04 ng/ml of cadmium,
and the average precision is + three percent in a single measurement.  The
method permits the direct and rapid determination of these elements in various
water samples.

Water Pollution, *Analytical Techniques, *Spectroscopy, *Copper, *Cadmium,
*Lead, Water Pollution Sources

*Atomic Absorption, EDTA, *Carbon Cup
 014E

 THE DETERMINATION OF VEGETABLE AND MINERAL  OILS  IN THE
 EFFLUENTS AND  SEWAGE SLUDGES OF THE UPPER TAME BASIN,

 Bennett, M., Dee, H. J.,  and Harkness, N.

 Upper Tame Main Drainage  Authority,
 156/170 Newhall Street,
 Birmingham B3  1S#, England

 Water Research, Vol. 7, No. 12, p 1849-1859,  1973.  6 fig,  3  tab,  20  ref.

 A method for the quantitative analysis of vegetable and mineral  oils  in
 effluents and  sewage sludges is described.  The  oils are extracted from  acidi-
 fied effluents by a liquid-liquid extraction, and from acidified dried sewage
 sludges by Soxhlet extraction using carbon  tetrachloride as solvent.  The
 vegetable oil  is transesterified at room  temperature, quantitatively  esti-
 mated by gas-liquid chromatography, and neutralized.  After separation of
 the methyl esters of the  vegetable Foils  on a silica gel column, the  mineral
 oils are qualitatively estimated by gas-liquid chromatographic "fingerprinting"
 analysis, and  quantitatively estimated by infrared spectrophotometric methods.

 Analysis, *Analytical Techniques, *Spectrophotometry, *Chromatography,
 Chemical Analysis, *0il,  *Sewage Sludge

 Liquid-Liquid  Extraction, Soxhlet Extraction

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015E

DETERMINATION OF MERCURY IN WATER BY THE FLAMELESS ATOMIC
ABSORPTION METHOD (Higany meghatarozasa vizben lang nelkuli
atomabszorpclos modszerrel),

Harsanyi, E. G., Polos, L., Bezur, L., and Pungor, E.

Magyar Kemiai Folyoirat, Vol. 79, No. 11, p 471-476, November, 1973.  9 fig,
1 tab, 40 ref.

In comparison with other analytical procedures, the flameless atomic absorption
method has a great advantage in the determination of small amounts of mercury
in water and biological materials because of its simplicity and sensitivity.
A system has been constructed in which mercury is reduced by tin  (II) chloride,
and the vapor is driven into the absorption cuvette by an air stream.  In
a volume of 100 cu cm water the detection limit was four nanograms with a
reproducibility of 2-7 percent.  An enrichment method has also been elaborated.
It is based on the tin (II) chloride reduction technique.  According to the
procedure, mercury is reduced in a volume of 800 cu cm and driven into a
50 cu cm solution volume where it is absorbed under oxidative conditions.
The mercury is then reduced in the smaller volume again with tin  (II) chloride.
The mercury vapor driven out from the solution is measured by the atomic
absorption method.  The detection limit of the technique has been found to
be 0.008 ng/cu cm, its variation coefficient being four percent and the
efficiency of the enriching operation 93 percent.

*Mercury, Metals, Water Pollution, *Analytical Techniques, Water Pollution
Sources

*Atomic Absorption, Flameless Atomic Absorption
016E

CONFIRMATION STUDIES ON POLYCHLORINATED BIPHENYLS  (PCB) FROM
RIVER WATERS USING MASS FRAGMENTOGRAPHY,

Ahnoff, M., and Josefsson, B.

Department of Analytical Chemistry
University of Gothenburn
Fack, S-402 20 Goteborg 5, Sweden

Analytical Letters, Vol. 6, no. 12, p 1083-1093, 1973.

A sensitive method for confirming the presence of polychlorinated biphenyls
(PCB) in river water is detailed.  Mass fragmentography is shown to be a helpful
technique especially when using naturally-occurring stable isotopes of chlorine.
Synthesized tetrachloro-, pentachloro- and hexachloro biphenyls were used to
focus the mass spectrometer at the three selected masses, so-called multiple
ion detection (MID).

*Analytical Techniques, *Mass Spectrometry, Water Pollution, Chlorine,
*Polychlorinated Biphenyls, Water Pollution Sources

*Fragmentography,  Multiple Ion Defection
                                         439

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017E

MEASUREMENT AND MONITORING UNITS FOR WASTE WATER (MESS-
UND UEBERWWACHUNGSGERAETE FUER ABWASSER),

Enke, Chr. Gg.

Wasser, Luft und Betrieb, Vol. 18, No. 1, p 20-25, 1974.  12 fig, 1 ref.

Measurement and monitoring units for wastewater include pH measuring instru-
ments which check the pH of the cleaned water leaving purification plants.
Rake cleaning facilities are used for better operation of the purification
plants and pumping stations with new automatic devices that remove the mater-
ial from the rakes in the opposite direction to the water flow.  Oxygen
measurement mains and battery-operated oxygen analyzers are available whose
measurement ranges between 0 and 30 mg 02/liter and are stabilized against
the ambient temperature,  A COD measuring unit involving the use of bichromate
oxidation is illustrated, with the consumed quantity of bichromate being
the measurement for the COD value.  Descriptions of electric C02 meters and
conductivity analyzers are included.

*Measurement, *Monitoring, ^Instrumentation, *Equipment, Waste Water Treat-
ment, Hydrogen Ion Concentration, Treatment Facilities, Oxygen Requirements,
Turbidity, Conductivity, Chemical Oxygen Demand
018E

AUTOMATED METHOD FOR ORTHO-, ORTHO-PLUS HYDROLYZABLE AND
TAL PHOSPHATE IN SURFACE AND WASTEWATERS,

Osburn, Q. W., Lernmel, D. E., and Downey, R. L.

The Proctor & Gamble Co., Ivorydale Technical Center,
Cincinnati, Ohio

Environmental Science and Technology, Vol. 8, No. 4, p 363-366, April, 1974.
2 fig, 5 tab, 7 ref.

All the titled classifications of phosphates are concurrently measured
colorimetrically as orthophosphate using appropriate modifications of the
Murphy and Riley reagent.  Features of the method include a means of compen-
sating for the high bias effect of turbidity on orthophosphate results and
elimination of a need for neutralization of the acidic sample streams of the
hydrolyzable and total phosphate determinations prior to color development.

*Phosphates, *Measurement, *Colorimetry, *Automation, Methodology, Turbidity,
Neutralization, Surface Waters, Waste Water (Pollution)

Orthophosphates
                                    490

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019E

THE COUNTING OF AEROBIC ACTINOMYCETES IN WATER SAMPLES
(DENOMBREMENT DBS ACTINOMYCETES AEROBIES DE L'EAU),

Eak-Hour, C., and Leclerc, H.
Institut Pasteur, Laboratoir d'Hydrobiologie

Lille, France

Armales de Microbiologle  (Institut Pasteur), Vol. 124, Part B, No. 4,
p 533-546, 1973.  3 tab, 22 ref.

A practical method for the quantification of actinomycetes in water and in
sediments has been determined.  Factors investigated include:  suppression
of bacteria and of fungi by the use of antibiotics; the purification, con-
centration, and homogenization of samples; and, the comparative efficiency
of different culture media.  Techniques for different types of water samples
are suggested.

*Methodology, *Water Sampling, *Soil Analysis, Antibiotics (Pesticides),
Bacteria, Fungi, Efficiencies

*Antinomycetes, Samples Treatment
  020E

  COLIFORM COUNTS OF POLLUTED WATERS:   A COMPARISON OF
  MEDIA AND METHODS,

  Mara,  D.  D.

  Nairobi University,  Dept.  of Civil Engineering,
  Nairobi,  Kenya

  Water  Research,  Vol.  7,  No.  12,  p  1899-1903,  1973.   1 fig,  3 tab,  8 ref.

  Samples of sewage  and polluted  river water were  used to compare various
  media  for the  enumeration  of collform organisms,  including  Escherichia
  coli,  by  the membrane filtration,  pour-plate,  and multiple  tube fermentation
  techniques.  The pour-plate  method with Lactose  teepol agar was found to  be
  at  least  as good as  the  other techniques,  and  is  preferred  as it is more
  economical, both in  terms  of time  and material.

  *Coliforms, *E.  Coli,  *Sewage Bacteria,  *Water Sampling,  Water Pollution,
  Bioindicators,  Economics,  Methodology

  ^Membrane Filtration,  *Pour-Plate  Method,  *Multiple  Tube  Fermentation
                                            491

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 021E

 THE CALIBRATION AND USE OF A CONICAL HOT FILM ANEMOMETER
 PROBE IN RECIRCULATING WATER FLOW,

 Stoy, R. L.

 Connecticut University, Storrs, Connecticut

 Review of Scientific Instruments, Vol. 45, No. 2, March, 1974.  3 fig, 5 ref.

 A calibration for directional sensitivity of a conical hot film anemometer
 probe is described.  It is usually assumed that the conical probe in insensi-
 tive to the velocity vector direction but, in fact, this is not true because
 deviations of + or - 607, of the mean velocity can occur at low water speeds.
 In this study, the probe is aligned at right angles to the velocity vector,
 but the trend of the results applies to probes aligned along  the velocity
 vector.  An application of the conical probe to velocity measurements  in
 a vortical water flow for speeds  from 0.66 to 3 m/sec is discussed.

 *Flow, *Anemometers, Flow Measurement, Calibrations
022E

INSTRUMENTATION IN FULL SCALE SELF-AERATED FLOWS (APPAREILS DE MESURE
DBS CONCENTRATIONS ET DES VITESSES DANS UN COURANT MIXTE D'AIR ET
D'EAU EN GRANDEUR NATURE),

Keller, R. J.

Karlsruhe University, Karlsruhe, Federal Republic
of Germany, Institute for Hydromechanics

Journal of Hydraulics Research, Vol. 11, No. 4, p 325-351, 1973.  8 fig, 1 ref.

The development of field instruments which measure accurately air concen-
trations and velocities at points in the flow of open channels is described.
The development included the design of a field unit by means of which depth
profiles of air concentration and velocity could be obtained at various
locations in the channel.  After extensive use of the instruments, it is
concluded:  the methods used to measure air concentration and stagnation
pressure were satisfactory.  Furthermore, except near the flow surface,
the errors associated with the computer values of tine average air con-
centration, stagnation pressure, and velocity were small.  However, measured
values of air concentration near the fluctuating surface and computed values
of velocity very near the flow surface could not be relied on.

*0pen Channel Flow, *Velocity, *Air Circulation, Flow Measurement,
Instrumentation, Analytical Techniques

Germany
                                         492

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023E

IMPROVING THE ACCURACY OF POINT-GAUGE MEASUREMENT IN HIGH-
VELOCITY FLOWS (AMELIORATION DE LA PRECISION DE LA POINTE DE
MESURE DANS LES ECOULEMENTS RAPIDS) ,

Jayaraman, R. and Sethuraman, V.

Indian Institute of Technology, Madras, India,
Hydraulic Engineering Laboratory

Journal of Hydraulics Research, Vol.  11, No. 4, p 317-323,  1973.   2  fig,
1 ref.

A new instrument was developed  to  improve  the  accuracy  of point-gauge  mea-
surement  in high-velocity  flows.   The Gauge  Contact-Time  Indicator can be
used with any point gauge  to  improve  the accuracy of  depth  measurement.
The instrument indicates the  percentage of time in which  there  is  contact
between the water level prove and  the pulsating water surface.   Since  the
instrument shows a  6 sec moving mean  indication,  the  readings  are  fairly
steady even  in the  presence  of  low-frequency pulsations.  The  unit,  which
is  self-contained and portable, is built inside an  aluminum chassis  and is
powered by four pen light  cells.   The instrument  eliminates the personal
error inherent in point gauge measurement  in high velocity  flows.   With
this instrument, all observers  can get readings within + or -  0.01 cm.

"^Instrumentation, *Measurement, Gauges, Flow,  Water Levels, Depth

*India, High Velocity  Flow
 024E

 PROCESS INNOVATIONS,

 Canadian Chemical Processing,  Vol.  58, No.  3,  p 8-10,  March, 1974.

 Water pollution can be detected at  night by a new airborne instrument.  A blue
 light from a low-powered laser excites fluorescence in the target area, an eight-
 inch telescope focussed on this area collecting the light.  Optical filters
 are used to block the reflected laser light and select pertinent wavelengths
 from the fluorescent spectrum of the target.  This light is converted to an
 electrical signal by a photomultiplier tube, processed and recorded on a strip
 chart.   It has two advantages  over  other systems:  it  is small and light,  and
 does not require a sample of the material to be identified.  The apparatus has
 detected fluorescence from oil refinery wastes and pulpmills'  settling ponds,
 as  well as controlled spills of oils and dyes.  The instrument has measured
 the fluorescence of water at ranges up to 75 meters and detected oil slicks from
 altitudes of 300 meters.   It has also detected rhodamine dye and chlorophyll in
 open water, and lignin sulphonates  in pulpmill ponds.   At ground level, the
 system has been used to examine river water and on board a ship to monitor
 chlorophyll concentrations in  Lake  Erie.

 *Analytical Techniques, *Water Pollution Sources, *Fluorescence, *0il Wastes,
 Oil Spills, Rhodamine,  Dyes

 *Lasers
                                       493

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025E

DETERMINATION OF PENTACHLOROPHENOL IN NATURAL AND WASTE
WATERS,

Chau, A. S. Y., and Coburn, J. A.

Special Services Section, Water Quality Branch, Canada
Center for Inland Waters, Burlington, Ontario, Canada
L7R4A6. •

Journal of the Association of Official Analytical Chemists,
Vol. 57, No. 2, p 389-893, March, 1974.  5 fig, 3 tab, 11 ref.

A sensitive, reliable method for routine determination of pentachlorophenol (PGP)
in natural and wastewaters is described.  PCP is extracted from the sample with
benzene and from the benzene into a potassium carbonate solution.  The addition
of acetic anhydride to the aqueous solution produces the acetate derivative of
PCP.  It is extracted in hexane and analyzed by electron capture gas-liquid
chromatography.  The analysis of PCP in lake water and sewage effluent is
presented, along with the retention times of other phenolic acetates.  As little
as 0.01 ppb PCP in one liter of water can be determined by this method.

*Analytical Techniques, *Gas Chromatography, *Sewage, *Phenols, *Water Pollution
Sources

Pentachlorophenol
  026E

  TRITIUM WATER TRACING,

  Smith, D. B.

  Nuclear Physics Division,  AERE, Harwell

  Water Treatment and  Examinations,  Vol. 22,  No.  4,  p  250-258,  1973.   2  fig,  4  ref.

  Tritium tracing techniques are  a valuable  tool  for groundwater  investigations.
  These techniques  are reliable,  practical,  and  complementary  to  other methods.
  Unique information about  relatively  long-term  movement  and the  behavior of
  pollutants  can be gathered from natural  tritium measurements.   Examples of
  tritium tracer studies  are given for drainage  of water  from  mines  and  for a
  river recharge investigation.

  *Tritium, *Analytical Techniques,  *Radioactivity Techniques,  *Radiochemical
  Analysis, *Tracers,  *Rivers,  Recharge, Mining,  Mine  Drainage
                                      494

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027E

ELECTROANALYTICAL STUDIES OF METHYLMERCURY IN AQUEOUS SOLUTION,

Heaton, R. E., and Laitlnen, H. A.


Hercules Research Center, Wilmington, Delaware

Analytical Chemistry, Vol. 46, No. 4, p 547-553, April, 1974.  6 fig, 31 ref.

The electrochemical reduction of monomethylmercury compounds in solution has
been studied using pulse polarography, cyclic voltammetry, and related tech-
niques.  Reduction of these compounds at a mercury electrode occurs in two
one-electron steps.  The first results in the formation of a methylmercuric
radical on the electrode.  This step is reversible under polarographic condi-
tions, but the polarographic wave is distorted due to involvement of the
methylmercuric radical in subsequent chemical reactions.  Addition of the
second electron results in reduction of the methylmercuric compound to ele-
mental mercury and methane, giving rise to the second polarographic wave.
This reduction is irreversible; the wave is distorted.  The first reduction is
irreversible; the wave is distorted.   The first pulse polarographic wave has
analytical utility arising from a linear peak current vs.  concentration curve
between concentrations of .0000001 and .0001 M.  The analytical implications
of the reduction mechanism are discussed; attention is given to effects of
coordinating agents and to detection limits.

*Electrochemistry, *Polarographic analysis, Analytical techniques,  Methane,
Polarographic Waves

*Monomethylmercury, Electroanalytical techniques, Voltammetry
  028E

  A PROGRAMMED SAMPLER FOR RUNOFF AND BEDLOADS,

  Swanson,  N.  P.

  USDA,  Lincoln,  Nebraska

  Transactions of the ASAE, Vol.  16,  No.  4,  p 790-792,  July-August, 1973.
  5 fig,  5  ref.

  A programmed, automatic sampler that collects  a sequence of composite samples
  of runoff and accompanying bedloads that has been in  use on a feedlot research
  installation near Lincoln, Nebraska, for over  four years is described.  The
  samples consists of an arm and dipper electrically driven by a gear reduction
  motor  through sprockets and a chain, a tipping bucket that collects the samplings
  from several rotations of the dipper and delivers them as a single sample, a.
  turntable holding successive sample containers, a gear reduction motor moving
  the turntable by a friction drive,  and a program timer.  Composites samples
  are collected over five minute sampling periods with  volumes of about three
  liters.  The sampler can be programmed to obtain individual samples for any
  of the 144 five-minute periods during 12 total hours  of actual operation.  The
  runoff need  not be continuous.   The time of collection of each sample is
  recorded  to  relate to the runoff hydrograph and recording rain gage chart.  Bed-
  load particles up to 5/8 inch in diameter can  enter the rotating sampler dipper
  which  passes under the discharge.  The sampler permits both qualitative and
  quantitative analyses of runoff with relation  to time for an event.  Main-
  tenance and  field servicing requirements have  been minimal.

  *Feedlots, *Runoff, *Bed load, Nebraska, Chemical analysis, Samplers, Rain
  gauge,  Hydrograph analysis

  Feedlot research, Quantitative analysis
                                            495

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029E

WATER QUALITY MONITORING EXPERIENCE IN THE SOMERSET RIVER AUTHORITY
AREA,  1968-1972,

Elvlns, B. J.

Water Pollution Control, Vol. 78, No.  1, p 33-40, 1974.  4 fig.

The Somerset River Authority has concentrated its resources on obtaining con-
tinuous information for dissolved oxygen and temperature parameters, sup-
plemented by the use of automatic samplers to give information on other chemi-
cal factors.  The stations are simple and battery-operated, requiring regular
maintenance with the probes being immersed directly in the river.  System dif-
ficulties are maintaining sufficient flow aroung the probe when the water is
penned and the formation of algal and Sphaerotilus growths on the probe, thus
preventing accurate readings.  The chief problem that occurs in the collection
of data from quality stations is the presentation of the information in a form
which can be easily related to other factors in the river.  It is felt that
the two forms of monitoring described when combined with flow measurement and
with regular semi-quantitative biological sampling of rivers, can give most
useful information.

*Dissolved oxygen, *Temperature, *Monitoring, Instrumentation, Gaging stations,
Data collections, Flow measurement

Great Britain
  030E

  USE OF BASE-RUNOFF RECESSION CURVES TO DETERMINE AREAL
  TRANSMISSIVITIES IN THE UPPER POTOMAC RIVER BASIN,

  Trainer, F. W., and Watkins, F, A., Jr.

  Albuquerque, New Mexico

  Journal of Research, U.S. Geological Survey, Vol. 2, No. 1, p 123, 125-131,
  January-February, 1974.  2 fig, 1 tab, 17 ref.

  The recession curve of base runoff is used in geohydrologic study of the upper
  Potomac River basin.  The slope of the recession curve is used with other data
  to estimate average basin values for transmissivity from streamflow data.
  Two general recession curves characterize the tributary basins:  (1) A
  continuous (simple) curve approximately straight on a semllogarithmic plot,
  which represents a constant set of diffusivity values within a basin and
  (2) a discontinuous (compound) curve, composed of a steeper first segment
  and a gentler second segment.  Simple curves represent basins underlain by
  sandstone, shale, or crystalline rock; by combinations of these rocks; or by
  carbonate rock.  Compound curves, which represent basins underlain in part
  by carbonate rock and in part by noncarbonate rock, are believed to reflect
  seasonal changes in relative discharge of these unlike aquifers, with the
  carbonate rock providing most of the ground-water runoff during summer-
  autumn and during drought.

  *Potomac River, *Streamflow, *Data collections, *Transmissivity, *Recession
  curves, *Hydrogeology, Aquifer characteristics, Storage coefficient,
  Groundwater basins, Runoff
                                         496

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031E

CORRELATION BETWEEN TURBIDITY  AND  IRON  CONTENT  OF  THE
FILTER EFFLUENT OF WELL ORIGIN,

Filip, A., Vuskovic, B.,  and Strundjalic,  P.

Department of Water Treatment  Plant  Automation,
Mihallo Pupin Institute Belgrade,  Yugoslavia

Journal of the American Water  Works  Association, Vol.  66,  No.  3,  p  166-168,  March,
1974.  4  fig, 2 ref.

Experimental results indicate  that the  turbidimeter  and  iron  analyzer can be
used for  continuous monitoring of  the filter  effluent  of well-origin water,
except when there are  iron  compounds present  or when there is  any solid phase
other than insoluble iron compounds  suspended in the water.  Turbidimeters
are preferable because they have shorter time constants, are  less expensive,
and are easier to operate and  maintain.

^Laboratory tests, *Monitoring, *Effluents, *Iron, *Turbidlty,  *Instrumentation,
*Well filters, Correlation analysis

*Turbidimeters, *Iron  analyzer
032E

DISCHARGE COEFFIEIENTS OF FLOAT-AREA-TYPE FLOW METERS,

Maki, H.

Tokyo Science University, Noda, Japan

The Japan Society of Mechanical Engineers, Vol. 17, No. 103, p 83-87,
January, 1974.  6 fig, 1 tab, 8 ref.

It is experimentally noted that the commonly used discharge coefficients of
float-area-type flow meters do not always have constant values over a wide
range of characteristics Reynolds numbers even in the region of Re larger than
critical characteristic Reynolds number Rec.  It is shown that floats having
special shapes or geometrical dimensions have constant value discharge
coefficients.  A semi-empirical formula to predict flow rate characteristics
has been obtained and limits of applicability of said formula are explained.

*Flow measurement, *Instrumental ion, *Reynolds nunfcer, *Mathematical studies,
Flow rates, Application methods.

*Discharge coefficient
                                         497

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  033E

  A GAMMA-RAY SPECTRUM ANALYSIS TECHNIQUE FOR LOW-LEVEL
  ENVIRONMENTAL RADIONUCLIDES,

  Wood, R. E., and Palms, J. M.

  Emory University,
  Atlanta, Georgia,  Physics Department

  IEEE Transactions on Nuclear  Science, Vol. NS-21, No. 1, p 536-542,
  February, 1974.   5 fig, 1 tab, 48 ref.

  The requirements for gamma-ray spectra analysis for low level environmental
  radionuclides are reviewed.  Special emphasis is placed on the routine and
  rapid analysis of large numbers of samples.  Pertinent requirements for analysis
  include the system energy and efficiency calibration, the library of gamma rays
  of concern, criteria of establishing the limits of sensitivity,  and techniques
  used for gamma ray intensity  and background determinations.  An analysis code
  (CETUS) used with a Ge(Li) detector and multichannel analyzer interfaced
  to a programmable desk top calculator is described.

  *Spectrometers,  *Gamma rays,  Analytical techniques, Measurements,
  *Radioisotopes,  Reviews,  Equipment

  *Ge(Li) spectrometer
034E

COMPARISON OF GE(LI) AND ANTICOMPTOM SYSTEMS FOR MEASURE-
MENTS OF ENVIRONMENTAL SAMPLES,

Wogman, N. A.

Battelle, Richland, Washington, Pacific Northwest
Laboratories

IEEE Transactions on Nuclear Science, Vol. NS-21, No. 1, p 526-535,
February, 1974.  17 fig, 2 tab, 21 ref.

A variety of sensitive low level counting systems are discussed from an
analyst's viewpoint, centering on a variety of Nal(Tl) and Ge(Li) gamma ray
spectrometers.  The coincident gamma ray emitters are most sensitively detected
through Nal(Tl) multi-dimensional gamma ray spectroraetry, while single gamma
ray emitters are very sensitively detected with Ge(Li) detector systems.
Nal(Tl) detector systems are superior in general for environmental
measurements.

*Spectrometers, *Gamma rays, *Radioisotopes, Measurements, Equipment,
Evaluations

*Ge(Li) spectrometers, Nal(Tl) spectrometers
                                         493

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035E

DETECTION SYSTEMS FOR THE LOW LEVEL RADIOCHEMICAL ANALYSIS OF
IODINE-131, IODINE-129 AND NATURAL IODINE IN ENVIRONMENTAL
SAMPLES,

Brauer, F. P. and Kaye, J. H.

Battelle, Richland, Washington, Pacific Northwest
Laboratories

IEEE Transactions on Nuclear Science, Vol. NS-21, No. 1, p 496-502,
February, 1974.  10 fig, 1 tab, 25 ref.

A procedure based on chemical separation techniques and activation analysis
has been developed for the sequential analysis of low levels of 1131, 1129,
and natural iodine in environmental samples by oxidation.  The separated
iodine is then counted by low level, beta-gated gamma-ray spectrometry for
the measurement of 1131.  The chemical yield for the separation ismeasured
by means of 1125 tracer.  Activation analysis is used for measurement of the
separated natural iodine, 1127 and 1129.  The natural iodine is estimated
from either the 1126 or 1128 activity produced in the sample.  The induced 1130
is used to estimate the 1129 concentration.  Measurements have been made of
iodine radioactivity in the environment at concentrations below the limits
established for radiation protection purposes.

*Iodine radioisotopes, *Neutron activation analysis, *Separation techniques,
*0xidation, Gamma rays, Spectrometers, Measurement

       *I129, *I125, *I126, *I128, *I130
036E

GE(LI) LOW LEVEL IN SITU GAMMA-RAY SPECTROMETER APPLICATIONS,

Phelps, P. L., Anspaugh, L. R., Roth, G. W., Huckabay,
G. W., and Sawyer, D. L.

California University, Livermore, California,
Lawrence Livermore Laboratory

IEEE Transactions on Nuclear Science, Vol. NS-21 No. 1, p 543-552, February
19, 1974.  8 fig, 4 fig, 10 ref.

The application of a Ge(Li) spectrometer for in-situ measurements of radio-
nuclides contained in soil is described.  This is being done at nuclear reactor
sites and in complex radionucllde fields at the Nevada Test Site.  The metho-
dology and precision of the in-site spectrometer techqniue has previously been
established for analysis of radionuclides in soil.  Application of the technique
to gaseous and liquid effluents containing radionuclides has shown a great
deal of promise.

*Spectrometers, *Radioisotopes, *Soils, Measurements, Methodology, Liquid
wastes, Gases, Effluents, Analytical techniques

*Ge(Li) spectrometer
                                            499

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03 7E

FLOC BLANKET CLARIFICATION,

Effluent and Water Treatment Journal, Vol. 14, No. 1, p 51 January, 1974.

Laboratory experiments at the Technical College at Zillna and full scale tests
at Brno in Czechoslovakia have been investigating the floe blanket clarifiers
in terms of hydraulic and chemical characteristics.  In the laboratory a
300 mm diameter by 3 m high column received chemically dosed water entering
tangentially at the base.  At upflow velocities of 1.2 mm/s floe volume con-
centrations were uniform with depth at about 20%, but solids fraction
values increased with depth usually increasing by about 20% from top to bottom.
The actual values of solids fraction depended on the chemicals which had been
added.  River water was utilized at Bmo and when the water temperature
exceeded 10 C the upflow rate was 1.3 mm/s, but during winter the output
fell to about 0.8 mm/s.  Previously, output had been sustained by 25 mg/llter
bentonite, but it was learned that 0.3 rag/liter starch produced the required
results.  Performance was assessed in terms of residual iron in the clarified
water.  The iron could be measured against performance characteristics with
the flocculation product as the most sensitive parameter with an optimal
value of 3000.

*Chemical properties, *Hydraulic properties, Water purification, Equipment,
Flocculation, Iron compounds, Rivers

*Floc blanket clarifiers, *Czechoslovakia
038E

A STOCHASTIC STUDY ON THE CONCENTRATION PROCESS OF RADIO-
ACTIVE SUBSTANCES TO AQUATIC ORGANISMS,

Aoyama, I., and Inoue, Y.

Kyoto University, Kyoto, Japan,
Department of Sanitary Engineering

Health Physics, Vol. 26, No. 2, p 191-198, February, 1974.  9 fig, 7 tab,
9 ref.

A stochastic study using a birth death process is presented on the concen-
tration process of radioactive substances to aquatic organisms.  A. formula
was calculated to show that the concentration step of organisms is in the
concentration step at an arbitrary time.  Using this analytical method, it is
found that the theory can be applied generally to cases in which the concen-
tration in the environmental water varies with time and that the concentration
distribution follows the Poisson distribution whose parameter is equal to the
mean value of the concentration steps.

*Stochastic processes, *Radioactivity, *Aquatic life, Formulas,
Mathematical studies, Analytical techniques

Ireland, Japan
                                        500

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039E

LIGHTING UP THE HAZE OF TURBIDITY MEASUREMENT,

Process Engineering, p 68-71, March, 1971.  4 fig, 1 tab,

The measurement of turbidity and turbidity measuring instruments which utilize
optical methods and operate on several different principles are described.
Some instruments operating on the reflected beam or scattering principles
measure the scattering at 90 degrees and others measure low angle scattering
up to 45 degrees.  In some cases the ratio between the amount of transmitted
light and of scattered light is measured.  Measurement of the intensity of
light transmitted through a liquid is known as turbidimetry and instruments
operating on this principle are turbidimeters.  Measurement of the intensity
of scattered light is known as nephelometry and instruments using this principle
are nephelometers, but instruments measuring the ratio of the transmitted
and scattered light are also often known as turbidimeters.  Diagrams of four
different turbidimeters are illustrated and their operation is explained.

*Turbidity, ^Measurement, *Light, Light intensity, Optical properties,
Instruments

Turbidimeters, Nephelometers, Scattered light, Transmitted light
040E

THE EFFECT OF HYDROMETEOROLOGICAL CONDITIONS ON THE ZETA-
POTENTIAL OF SUSPENDED SOLIDS (Hidrometeorologiai viszonyok
hatasa a lebego anyagok Zeta-potencialjara) ,

Buklai, L., Licsko, I., and Szepkuti, L.

In:  Hidrologiai Kozlony, No. 12, p 557-565, 1973.  6 fig, 4 tab, 2 ref.

The effect of hydrometeorological conditions on th° zeta potential of suspended
solids was investigated in the Danube River.   The colloidal particles had a
negative charge and almost every particle within a sample had a different
zeta potential.  Therefore, it was impossible to describe a particular hydro-
meteorological situation positively and unambiguously by a single zeta
potential value.  An attempt was subsequently made to describe the electro-
static charges of the colloidal particles present by the distribution of the
zeta potential values observed,   The observation data were processed with
the help of a computer, but there was no correlation between either the sus-
pended solids content and zeta potential or between conductivity and zeta
potential.  There was a relationship of limited validity between the number
of algae counted in unit volume and the value of the zeta potential.  At an
increasing alga count the zeta potential tended to zero, whereas decreasing
counts were accompanied by increasing zeta potential values.  A relationship
of similarly limited, but more general validity was found to exist between
river stage and the zeta potential.

*Zeta potential, *Suspended solids, Rivers, *Hydrometeorology, Electric
properties, Conductivity, Water level, Seasonal, Temperature, Algae

*River Danube, Electrostatic charges, River stages, Poland
                                                 501

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04 IE

TURBIDIMETERS MONITOR DUBAI FLOOD WATER,

The Oil and Gas Journal, Vol. 72, No. 15, p 68, April 15, 1974.  1 fig.

Turbidimeters utilizing a forward light scattering technique are monitoring
water purity for waterflooding oil fields in the Arabian Gulf.  The instru-
ments use two modular subsystems, a transmitter and a converter.  The trans-
mitter is mounted in the process line and projects a beam of light through
the process stream.  The turbidimeters are insensitive to color and bubbles
so produce accurate measurements of solids loading.  Linear solid state de-
tectors convert the varying intensity of the light scattered from the parti-
culates into electrical signals.  These signals are processed by the converter
to produce an instantaneous computation and display of turbidity.

*Turbidity, *Measurement, Water quality, Treatment facilities, Waste water
treatment, Equipment

*Hght scattering *Turbidimeters, Dubai
 042E

 ENVIRONMENTAL DOSE MEASUREMENTS  IN THE VICINITY OF NUCLEAR
 FACILITIES,

 Hall, R. M. Jr., and Ross, D. I.

 E. I. duPont de Nemours and Company,
 Savannah River Plant, Aiken, South Carolina

 IEEE Transactions on Nuclear Science, Vol. NS-21, No. 1, p 451-455, February,
 1974.  6 fig, 1 tab, 6 ref.

 The environmental radiation monitoring program for the Savannah River plant
 was recently altered to make more detailed readings at more locations in
 the plant's environs.  Monitoring stations were increased from 40 to about 500.
 Additional stations were selected to improve the delineation and measurement
 of natural radiation.  Monitoring stations near each operating area were
 supplemented by additional stations near effluent streams and at one mile
 intervals along the plant perimeter.  Thirty five towers within a 50 mile radious
 of the plant are used to place monitors up to 80 ft above the ground to aid
 in distinguishing between airborne and terrestrial radioactivity.  Most mea-
 surements are taken quarterly, but several locations are measured biweekly to
 detect short term variations.

 *Monitoring, *Nuclear powerplants, *Radiation, Measurements, Radioactivity,
 Instrumentation, Filters

 *Savannah River Plant (Aiken South Carolina), *Dosimeters, Dosimetry systems
                                      502

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04 3E

AN AIRBORNE GAMMA RAY SPECTROMETER AND ITS APPLICATION  IN
NUCLEAR POWER PLANT SITE SURVEYS,

Fryer, G. E., and Adams, J. A. S.

Rice University,
Houston, Texas

IEEE Transactions on Nuclear  Science, Vol. NS-21, No. 1, p 572-584, February,
1974.  8 fig, 4 tab, 15 ref.

Airborne radiometric surveys  from low flying helicopters have been completed
for three nuclear power plant sites in Texas.  The gamma ray counting data
acquired in the air are converted to ground dose rate and plotted as a  series
of profiles.  A radial flight line pattern provides easy position control and
concentrates sampling density over the plant site.  The 5-8 fold range  of
natural and man made radiation background within 10 miles of the three
plant sites is statistically well characterized by over 14,000 spectra
taken directly from 3.8% of each 314 sq mi survey area.  The aerial dose
estimates agree closely with  thermoluminescence dosimeter data taken on
the ground over 3 mo periods.  The instrumentation system, survey rationales,
data reduction, and analysis procedures are described.  One of the major
complications of the area is  the periodic and extensive flooding of the rice
fields, attenuating the gamma ray flux from the ground.

*Nuclear powerplants, *Gamma rays, *Spectrometers, Monitoring, Air pollution,
Radioactivity, Measurements, Texas, Instrumentation, Surveys, Flooding

Thermoluminescence dosimeters, Helicopters
044E

ACTIVATED  SLUDGE pH SHOCK,

Effluent and Water Treatment  Journal, Vol.  14, No.  3,  p  165, March  1974.

The study  at Oklahoma  State University  on  laboratory  cultures  has as  its  objec-
tives  to characterise  the  response  to terms of biomass and  effluent substrate
concentrations,  types  of microbiol  populations present and  chemical composition
of the biomass.  Guidelines were  obtained  for allowable  pH  in  waste water.  With
severe acid shock, the population changed  from bacterial-protozoan  to one of
filamentous fungi.  Based  on  the  results it was  estimated that pH changes of
no more than one unit  from the  neutral  preshock  range  can be tolerated, without
disrupting the biochemical efficiency of substrate  removal.

*Biomass,  *Effluent, *Waste water,  *Bacteria, *Laboratory analysis, Microorgan-
isms,  Filamentous  fungi, Chemistry,  Analytical techniques

*pH, Bacterial-protozoan,  Biochemical efficiency, Acid shock
                                         503

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045E

DETERMINING THE BIODEGRADABILITY OF ORGANIC COMPOUNDS,

Effluent and Water Treatment Journal, Vol. 14, No. 3, p 161, March, 1974.

Organic carbon in aqueous solution or suspension may be measured by catalytically
oxidizing  it to carbon dioxide, with a Model 915 TOC Analyser by Beckman In-
struments.  Application of the total organic carbon analyser is the determina-
tion  of degradability of various organics by a given culture in the activated
sludge treatment process.  The process incorporates the aerobic oxidation of
organic compounds to simple, harmless inorganics such as carbon dioxide, water,
nitrates,  sulphates, and cellular organic matter.  Because widespread require-
ments for  determining organic pollution of water are increasing, this measure-
ment  of organic carbonaceous matter as a major oxygen-demanding pollutant is
important.  Total organic carbon analyser measurement is rapid and produces du-
plicate results on duplicate samples.  The process is applicable for measure-
ment  of effluents from water pollution control plants, industrial waste treat-
ment  plants, and the measurement of organics in surface waters.

instrumentation, *0xygen demand, *Pollutants, *0rganic compounds, *Biodegrada-
tion, Effluents, Water pollution control, Measurement, Surface waters, Indus-
trial wastes

*0rganic carbon analyser, *Model 915 TOC Analyser, Water pollution control
plants
046E

STREAM STANDARDS:  DEAD OR HIDING?

Wolman, M. G.

The Johns Hopkins University, Baltimore, Maryland, Depart-
ment of Geography and Environmental Engineering.

Journal of the Water Pollution Control Federation, Vol. 46, No. 3, p 431-437,
March 1974.  6 ref.

Water quality is not easily quantifiable, but is rather dependent upon percep-
tion of use.  While the public is attuned to attributes such as algae, murki-
ness, suds, foam, cans, glass, and debris, scientists try to measure river
quality by standard parameters such as dissolved oxygen, acidity, temperature,
dissolved solids, turbidity, and biological measures such as the diversity
of species, size of the population, and complexity of the system.  To translate
quality objectives into standards is quite difficult.  In addition, economic
benefits, as opposed to costs, are vaguely defined.  Every water body has more
than one polluter along with a number of pollutants, and reasonable standards
must vary with perceived use of a particular river.

*Rivers, *Streams, *Stream pollution, *Water quality standards, Water pollu-
tion, Costs, Dissolved oxygen, Dissolved solids, Turbidity, Water quality
standards

Stream standards, Biological measures, Standard parameters
                                       504

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047E

HINDERED SETTLING AND SLUDGE BLANKET CLARIFIERS,

Gould, B. W.

Public Health Engineering, New South Wales University,
Australia

Effluent and Water Treatment Journal, Vol. 14, No. 3, p 131-135, March, 1974.
2 fig, 6 ref.

In the treatment of water and waste water, one common application is in sludge
blanket, or solids-contact, clarifiers.  The theory of hindered settling,
whereby particles are hindered by other particles in the suspension, is es-
sential to this treatment.  The relationship between the sludge flux intensity,
velocities, and concentration distribution, was found to depend upon continu-
ity conditions for a particular sludge.  The stability of flow in fluidized
beds, such as a slurry pool in a clarifier, cannot be achieved unless the in-
coming fluid is mixed as thoroughly and evenly as possible with the settling
sediment.  Thus, efficient mixing at the inlet to a sludge blanket clarifier
is most necessary to obtain efficient operation.

*Waste water treatment, *Water clarification, Flow, Settling, Slurries,
Fluid movement, Water treatment

*Sludge blanket clarifiers, Sludge flux intensity, Hindered settling, Slurry
pool, Fluidized bed, Efficient mixing
  048E

  STABILITY OF LAMINAR FLOW AT SEABED,

  Sleath, J. F. A.

  Cambridge University, Cambridge, England, Department of
  Engineering

  Journal of the Waterways Harbors and Coastal Engineering Division, Vol. 100,
  No. WW2, p 105-122, May, 1974.  11 fig, 13 ref.

  The problem of determining the flow produced by water waves in the boundary
  layer above a two-dimensionally rough bed is studied analytically.  It is ac-
  cepted that at sufficiently high Reynolds numbers, this flow ceases to be lami-
  nar.  Previous work in this field was done by Li and Manohar and the new tests
  are with their results.  By numerical interaction and small-perturbation
  process, this paper concluded that:  at high Reynolds numbers and bottom rough-
  ness, vortices are found during each half cycle of the wave; for a small part
  of each half cycle, an instability occurs in the form of sudden jets of fluid
  in opposite directions at the crest and trough of the bed roughness.  No light
  was shed on the conditions under which turbulence first occurs with a rough
  bed and the study is not intended to imply that turbulence does not develop
  at higher Reynolds numbers.

  *Laninar flow, *Seabed, *Reynolds numbers, Numerical analysis, Jets, Fluids,
  Turbulence

  Li and Manohar, Small-perturbation process
                                          505

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049E

CARBON MEASUREMENTS IN WATER QUALITY MONITORING,

Maier, W. J., and McConnel, H. L.

Minnesota University,
Department of Civil and Mineral Engineering

Journal of the Water Pollution Control Federation, Vol. 46, No. 4, p 623-633.
3 fig, 5 tab, 25 ref.

Review of the literature indicates that continuous monitoring programs to
measure organic and inorganic carbon concentrations in rivers and lakes are
necessary.  In a one-year test program with the State of Minnesota Water Quality
Sampling Program, an instrument for the rapid (2 min/sample) an/ precise
(nearest mg/liter) determination of organic and inorganic carbon was demon-
strated.  Comparison of TOC and BOD measurements indicate different aspects
of the organic pollutant load in natural waters.  These measurements have
three uses:  in pollution abatement work as a simple method for monitoring
pollution levels regarding the accumulation of nonbiodegradable organic materials,
in study of ecology, as quantitative information about the carbon cycle, and
in public health work as a nonspecific measure for monitoring potential toxic
organic materials in drinking water.

*Monitoring, *Carbon, *Water quality control, *Rivers, *Lakes, Biochemical
oxygen demand, Pollutants, Organic loading, Reviews, Biodegradability, Public
health, Ecology, Measurements, Toxicity, Carbon cycle, Minnesota

*0rganic carbon
  050E

  BACTERIOPHAGES AS VIRAL POLLUTION INDICATORS,

  Kott, Y., Roze, N., Sperberg, S., and Betzer, N.

  Israel Institute of Technology, Haifa, Israel,
  Environmental Engineering Laboratories Technion

  Water Research, Vol. 8, p 165-171, March, 1974.  7 tab, 10 ref.

  The use of bacteriophages as viral pollution indicators was investigated.
  2 Phage, attenuated Polio I (LSC) strain introduced daily to a 350 liter ex-
  perimental oxidation pond showed no decrease in bacterial viruses 2 or other
  coliphages or Polio I strain.  Ratios of coliphages to human enteric viruses
  ranged in flood waters from concentrations as low as 1:1 to as high as
  10,000:1; in wastewater at various seasons the ratio was 1,000,000:1; in
  trickling filter effluents in winter it was 100,000:l;in spring 1,000,000:1,
  in summer and fall 100,000:1, in oxidation pond effluents in winter 10,000:1;
  in spring 100,000:1; and in summer and fall 10,000:1.  Out of three epidemics
  in small communities caused by failure of water supply, coliphages were found
  to be positive.  At the same time only two samples of human enteric viruses
  were positive (the third was contaminated with yeasts).  Chlorination ex-
  periments using the experimental oxidation pond showed that 2 was most re-
  sistant. MS2 was very resistant, and coliphages were more resistant than
  attenuated Polio I virus.  Experiments with the oxidation pond effluents
  showed that coliphages were at least as or even more resistant to chlorine
  than human enteric viruses.  For the purposes of routine microbiological
  examinations the use of E. Coll B bacteriophages provides an adequate measure
  of the viral quality of water.

  *Analytical techniques, *Bioindicators, *E. coli, *Enteric bacteria, *Bacterio-
  phage, *Viruses, Water pollution sources, Coliforms

  Coliphages
                                      506

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051E

A PRELIMINARY EVALUATION OF A DISCRETE SAMPLE ANALYZER FOR
CHEMICAL ANALYSIS OF WATER,

St. Jean, R., and Kasatiya, S. S.

Department of Social Affairs,
P. 0. Box 412, Ville de Laval,
Quebec, Canada

Environmental Letters, Vol. 6, No. 3, p 193-203, 1974.  9 fig, 1 tab, 11 ref.

The BECKMAN DISCRETE SAMPLE ANALYSER  (DSA-560)  (KLiNa Accessory) was used to
determine chlorides, fluorides, nitrates, nitrites, sodium, and potassium
in drinking water samples.  It was found to be precise, accurate, and rapid
and was thought to be a potentially useful instrument in environmental ana-
lysis.  However, it is necessary to continually supervise its use and
ensure its careful handling.  It is versatile, and requires small samples.

*Analytical techniques, *Water pollution sources, *Chemical analysis, in-
strumentation, *Pollutant identification, Water analysis, Chemical wastes

Beckman Discrete Sample Analyser
052E

DETERMINATION OF TRACES OF COPPER, LEAD, CADMIUM, NICKEL,
ZINC AND IRON IN SILVER HALIDS BY PULSE POLAROGRAPHY,

Taddia, M., Lippolis, M. T., and Lanza, P.

Chemical Institute "G. Ciamician", Bologna University,
Bologna, Italy

Electroanalytical Chemistry and Interfacial Electrochemistry, Vol. 51, No. 1,
p 221-225, March, 1974.  2 fig, 1 tab, 12 ref.

A method is described for the analysis of traces of copper, lead, cadmium,
zinc, nickle, and iron in sliver halides by pulse polarography with the stan-
dard addition procedure.  Copper, lead, cadmium, nickel, and zinc were deter-
mined after dithizone extraction.  Iron was determined after oxine extraction.
For elements added at 6-1 ppm levels, the accuracy was better than 10%.

*Trace elements, *Polarographic analysis, Copper, Lead, Cadmium, Nickel, Zinc,
Iron, Investigations, Methodology

*Silver halides, *Pulse polarography
                                          507

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053E

THE EFFECT OF ACID CONCENTRATION ON THE DETERMINATION OF
BICHROMATE VALUE,

Stones, T.

City of Salford, Salford, England

Water Pollution Control, Vol. 78, No. 1, p 121-124, 1974.  1 fig, 3 tab, 3 ref.

A procedure for the determination of the dichromate value of sewage was reinves-
tigated to avoid significant losses of dichromate due to decomposition.  The
procedure recommended that the volume of sulfuric acid used should be 1.2 time
the aqueous volume, i.e., 54.5% of the total volume.  Various amounts of water
were added to a series of flasks containing 25 ml of n/4 potassium dichromate
solution, 80 ml of sulfuric acid, and 10 ml of 0.63% W/V of silver sulfate in
sulfuric acid.  After refluxing for 2 hr, the residual amounts of dichromate
•were determined.  The results show that the decomposition of the dichromate,
which begins when the acid concentration exceeds about 45% V/V, increases
rapidly above 55 F and is complete at 80%.  Increasing the acid concentration
leads to an elevation of the boiling point of the solution, and the breakdown
of the dichromate was due to thermal decomposition.  In determining the di-
chromate value of a sewage or an industrial waste water an appropriate correction
must be made for the amount of dichromate decomposed.  This will not be constant
but will be dependent upon the amount of dichromate which is in excess of that
required for oxidation.

*Sewage, Methodology, Investigations, Acidity, Decomposition, Sulfuric acid,
Industrial wastes, Oxidation

*Dichromate value, England, Potassium dichromate
05 4E

THE DESIGN OF SAMPLING PROGRAMMES FOR RIVERS AND EFFLUENTS,

Montgomery, H. A. C. and Hart, I. C.

Water Pollution Research Laboratory, Department of the
Environment

Water Pollution Control, Vol. 78, No. 1, p 77-101, 1974.  7 fig, 7 tab, 39 ref.

Guidelines for the design of sampling programs for rivers and effluents are
discussed based upon a survey of conditions in the United Kingdom.  In develop-
ing a program, it is advisable t:o seek various types of average, percentile
values, or frequency distribution of concentration or load, as well as indivi-
dual values or sequences of values.  Loads and flow weighted concentrations tend
to become more useful than time based average concentrations as the flow be-
comes more variable.  Accidental or illegal incidents of short duration cannot
be detected with certainty by long term sampling programs.  Sampling should
be carried out only where lateral or vertical mixing is complete and sampling
locations should be numerous enough to allow the results to be interpreted
in the manner decided upon.  Six: samples are tentatively suggested as an appro-
priate number for characterizing a cyclic fluctuation or a period of persistently
high or low concentration.  Time of sampling should either be randomized or
arranged so that the frequency of sampling is different from that of any daily,
weekly, or other cyclic fluctuation.  Formulae are proposed for estimating the
number of samples needed to obtain a summary result with a given precision
at a given level of confidence.

*Sampling, *Rivers, *Effluents, *Water sampling, Time, Flow, Water treatment,
Water quality, Water analysis, Methodology, Surveys, Numerical analysis, Mix-
ing, Formulas

United Kingdom
                                         508

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 055E

 ADVANCED  X-RAY  CRAWLER,

 Anti-Corrosion,  Vol.  21,  No.  2,  p  17,  February,  1974.   1 fig.

 Criterion Ltd.  of  Hitchin,  Herts has  built  an  advanced X-ray crawler for pipe-
 line  radiography of  20  in diameter pipes  and above.   One major  feature is a
 central steel chassis with  three afixed parts  to give  added  strength with a
 rigid frame.  This enables  the  crawler to be easily  lifted into and out of
 pipelines.  The component parts  are an x-ray tube,  an  electric  motor, a drive
 mechanism,  an electronic  brain  and a  rechargeable battery unit.  The crawler is
 remotely  controlled  and may be  despatched in forward or reverse.

 *Pipelines, *X-rays,  *Pipes,  *Equipment,  *Measurement

 *X-ray crawler,  Radiography,  Great Britain
056E

RAPID DETERMINATION OF THE PRESENCE OF ENTERIC BACTERIA
IN WATER,

Kenard, R. P., and Valentine, R. S.

Atlantic Research Corporation, Alexandria, Virginia

Applied Microbiology, Vol. 27, No. 3, p 484-487, March, 1974.  10 ref.

A rapid and sensitive method is described for the detection of bacteria in water
and various other natural substrates by the isolation of specific bacteriophage.
By the addition of large numbers of the organism to the sample, the presence
of virulent bacteriophage is demonstrated in as little as six to eight hours.
Fecal coliform, total coliform, and total coliphage counts were determined for o
over 150 water samples from several geographical areas over a period of two
years.  Computer analysis of the data shows a high degree of correlation be-
tween fecal coliforms and the coliphage present in the samples.  With a high
correlation coefficient between fecal coliform and coliphage counts, preduc-
tions of the fecal coliforms may be made by enumeration of the phage.

*Bacteria, *Analytical techniques, *Bacteriophage, Microbiology, Coliforms,
Enteric bacteria, Water sampling

*Coliphage, Virulent bacteria, Computer analysis, Fecal coliforms, Virulent
bacteriophage
                                           509

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057E

CORRELATION BETWEEN BIOCHEMICAL OXYGEN DEMAND (BOD) AND
CHEMICAL OXYGEN DEMAND OF POTASSIUM DICHROMATE (CODcr) IN
THE WASTE WATER FROM BOILED NOODLE (SPAGHETTI AND JAPANESE
NOODLE),

Kadooka, K., Ohata, M., Tsukamoto, M., and Hattori, R.

Journal of  Food Science and Technology, Vol. 20, No. 9, p 426-428, September, 1973.

A method of calculating BOD from COD was determined because the regulation for
the waste water from a boiled noodle plant is generally restricted by BOD whose
measurement is more complicated and lengthy.  The BOD value of the waste water
from boiled noodle was highly correlative with COD value and the equation ob-
tained by a least squares method is BOD = 0.630 times COD + 43.  The correlation
coefficient is 0.99 and it is significant at the one percent level of confidence.

*Biochemical oxygen demand, *Chemical oxygen demand, *Industrial waste water,
Waste water, Potassium compounds, Least squares method, Correlation analysis,
Calculations, Measurement

*Boiled noodle plant, *Potassium dichromate, *Japan
058E

CHEMICAL DOSAGE CONTROL FOR PHOSPHORUS REMOVAL,

Pollutech Pollution Advisory Services Limited, Oakville,
Ontario

Research Program for the Abatement of Municipal Pollution Within the Provisions
of the Canada-Ontario Agreement on Great Lakes Water Quality, Research Report
No. 4, March, 1973.  79 p, 44 fig, 6 tab, 7 ref.

A study was done to determine whether a simple monitoring procedure could be
utilized to control chemical addition in municipal waste treatment plants.
It was intended to demonstrate that proportional control of chemical feeding
would be economically advantageous and to determine which specific parameters
could be monitored to enable chemical dosage control and at which locations
within a treatment plant.  Bench-scale jar studies and measurements at a full-
scale plant were conducted.  Jar-test studies demonstrated that the chemical
dosage required for a 1 ing/liter phosphorus residual can be predicted when jar
tests are repeated on the same waste sample, and that potential savings in
chemicals of 30-40 percent could theoretically be achieved if a controller
capable of measuring chemical requirements to the same accuracy as the jar
test could be developed.  However, no correlations could be established be-
tween the common waste water parameters in raw sewage and phosphorus concen-
trations, or the amount of chemical required to achieve a 1 mg/liter phos-
phorus residual.  Observations taken at a full-scale treatment plant at various
sampling points during chemical addition revealed a reasonable correlation
between final effluent phosphorus and soluble phosphorus in the aeration tank
effluent after chemical addition, i.e., limiting the aeration tank effluent
soluble phosphorus concentration to 0.2 mg/liter, would be expected to result
in a 1 mg/liter phosphorus residual in the final effluent 80 percent of the
time.  It was postulated that the observed phosphorus removal takes place in
three distinct steps with the majority being removed in the aeration tank.
This observation can be extended to postulate that phosphorus must be removed
in the aeration tank by aluminum hydroxide.  It was found that the addition
of alum to mixed liquor results in the immediate precipitation of a fairly
constant percentage of the soluble phosphorus.  Increasing the dosing rate
causes an eventual increase in the amount of phosphorus removed by the system.

*Monitoring, *Municipal wastes, *Treatment plants, Chemical control, Costs,
Laboratory tests, Sewage, Phosphorus, Effluents, Aeration, Alum, Waste water,
Canada

*Phosphorus removal, Chemical feeding, Chemical dosage, Jar-test studies
                                        510

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059E

JUST A MOMENT!,

Wallis, J. R.,  Matalas, N. C., and Slack, J. R.

IBM Research Center, Yorktown Heights, New York

Water Resources Research, Vol. 10, No. 2, p 211-219, April, 1974.  6 fig, 4 tab,
1 ref.

Water resources systems are designed according to decision variables which are
functions of various parameters, including those that characterize the sto-
chastic properties of hydrologic inputs to the systems.  Distribution functions
for the three statistics, the mean, the standard deviation, and  the coeffici-
ent of skewness, were obtained by Monte Carlo experiments for small samples
of various distributions.  Any particular set of hydrologic parameters to be
estimated depends upon the purposes and objectives underlying the proposed
development of the water resource system.  Here sample sizes of  10 (10) 90
were considered, and the distributions used were the normal, Gumbel (extreme
value type 1),  log normal, Pearson type 3 (gamma), Weibull, and  Pareto type 1
(Pearson type 4).  Pronounced skews, biases, and constraints in  the sampling
properties of the statistics were observed.

*Water resources development, *Hydrologic data, *Statistical methods, Monte
Carlo method, Mathematical studies, Sampling, Decision making

Mean, Standard deviation, Coefficient of skewness, Parameters
060E

RESULTS FROM MULTI-TRACE-ELEMENT NEUTRON ACTIVATION
ANALYSES OF MARINE BIOLOGICAL  SPECIMENS,

Guinn, V. P., and Kishore, R.

Scripps Institution of Oceanography, California Univer-
sity, Irvine, California, Department of Chemistry

Journal of Radioanalytical Chemistry, Vol.  19, No. 2, p  367-371,  1974.   6  ref.

Traces of mercury in marine specimens had been previously  investigated  and
this study showed the reproducibility of replicate analyses  of  a  given  sample
and of different samples  (aliquots) of the  same tissue from  a given marine
specimen.  A considerable body of  data was  obtained  on the Hg,  Se, and  Zn
levels for several different spiecies of Pacific Ocean fish and  mammals.  Three
variables which affect the levels  of these  trace elements  include species,
tissue, and size or age of the specimen.  Sample dissection  was carefully
conducted and the data of specimen size was  recorded for a large  number of
specimens.  Whereas Hg, Se, and Zn all appear to concentrate markedly in the
liver of marine mammals such as dolphins and killer  whales (relative to
their levels in muscle tissue), only the latter two  appear to concentrate
appreciably in the liver  of large  fish such  as the albacore.

*Mercury, *Marine fish, *Marine biology, *Radioactivity effects,  Measurements,
Analyses, Sampling, Pacific Ocean, Zinc, Aquiculture

Albacore, Dolphins, Killer whales, Aliquots, Selenium, Trace-element levels,
Muscle tissue, Species
                                           511

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06 IE

ALGEBRAIC BOUNDEDNESS OF SAMPLE STATISTICS,

Kirby, W.

U. S. Geological Survey, Reston, Virginia, Water Resources
Division

Water Resources Research, Vol. 10, No. 2, p 220-222, April, 1974.  2 ref.

Seemingly puzzling results from computer experimentation and simulation study
about random sampling behavior of the sample mean, sample standard deviation
and sample skew coefficient are clarified.  It is shown that the sample skew
coefficient has population-independent bounds depending only on the sample
size.  Similar results are obtained for the coefficient of variation of positive
data, the maximum standardized deviate, and the standardized range.  The upper
bounds of these statistics are summarized in a table.

*Samples, *Statistical methods, *Computer simulation, Computer models,
Simulation analysis

Sample mean, Sample standard deviation, Sample skew coefficient, Sample size,
Algebraic boundedness
062E

A METHODOLOGY FOR PLANNING LAND USE AND ENGINEERING AL-
TERNATIVES FOR FLOODPLAIN MANAGEMENT,

Seisz, R. N.

Arizona University, Arizona

Dissertation Abstracts International B, Vol. 34, No. 8, p 3899, 1974.

Analytical and decision-making methodology is developed in terms of planning land
use and regulations, development policies, and engineering measures.  The ob-
jective of the floodplain management system is to select the most economically
efficient combination of land use and engineering alternatives.  A test applica-
tion and computer study makes decision rules for combining:  spatial and tempor-
al distribution of urban land uses; site elevation through dirt fill; floodproof-
ing; public acquisition of undeveloped land for open space uses; public acquisi-
tion and removal of existing improvements from the floodplain; dams; and channel
improvement.  The methodology can be used to formulate floodplain management
system plans, to evaluate the economic impact of floodplain management system
plans, to perform "with and without" analyses, and to perform incremental analy-
ses of development policy and engineering alternatives.

*Mathematical models, *Land use, *Computers, *Engineering, *Flood plains, Land
management, Floodproofing, Costs, Channels, Dams, Engineering structures, Dis-
tribution

Floodplain management, Land distribution
                                          512

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063E

THE PHOSPHORUS STATUS OF EUTROPHIC LAKE SEDIMENTS AS
RELATED TO CHANGES IN LIMNOLOGICAL CONDITIONS—TOTAL, IN-
ORGANIC PHOSPHORUS,

Wildung, R. E., Schmidt, R. L., and Gahler, A. R.

Environmental Chemistry, Battelle

Journal of Environmental Quality, Vol. 3, No. 2, p 133-138, April-June,
1974.  2 fig, 3 tab, 19 ref.

The role of sediments as a source of phosphorus to lake waters and the
factors which may influence sediment phosphorus release, changes with time
in the phosphorus statement of noncalcareous sediments of a eutrophic lake were
assessed.  These were related to changes in sediment carbon and nitrogen, surface
water composition, pH,  temperature, and phytoplankton growth.  Sediment
phosphorus status and the relationship of these changes to limnological  con-
ditions differed with locations in the lake.  Changes in sediment composition
were greatest in a bay which received agricultural runoff in the early spring,
additional nutrients apparently providing the initial impetus for increased
surface water biological activity in the spring relative to other locations.
s was reflected in increased surface water organic carbon and nitrogen,
turbidity, and phytoplankton growth.  At this location, total sediment
phosphorus, carbon, and nitrogen decreased during the late spring and early
summer  corresponding to the period of exponential growth of the lake phyto-
plankton population.  Results indicate that sediment inorganic phosphorus
is directly related to  the biological productivity of the surface waters, and
in at least one location, sediments serve as a significant source of phos-
phorus to these waters  supporting increased biological growth.

*Sampling, *Phosphorus, *Sediments, *Eutrophication, *Lakes, Carbon, Nitrogen,
Organic matter, Phytoplankton, Runoff, Biological communities, Surface
waters, Turbidity

Biological growth
064E

HISTORY OF METAL POLLUTION IN SOUTHERN CALIFORNIA COASTAL ZONE,

Bruland, K. W., Bertine, K., Koide, M., and Goldberg, E. D.

Scripps Institution of Oceanography, La Jolla,
California

Environmental Science and Technology, Vol. 8, No. 5, p 425-432,
May, 1974.  3 fig, 7 tab, 10 ref.

Measurements were made of the anthropogenic and natural fluxes of elements
into the sediments of the San Pedro, Santa Monica, and Santa Barbara Basins,
off the coast of Southern California.  These included Pb, Cr, Cd, Zn, Cu, Ag,
V, and Mo.  Use of the sedimentary record to reveal metal fluxes to the
environment is dependent upon rapid removal of metal from water following
its entry, as is the case for lead.  Samples were taken; dating techniques
and elemental analyses were performed, including fractional extraction.  By
identifying those elements whose fluxes to the sediments as a result of human
activities are significant compared with natural mobilization rates, traport
paths from the continents to the sediments for individual elements are
indicated.  These account for waste outfalls, river and storm runoff, and
composition of the atmosphere.  Conclusions include marked similarity in the
anthropogenic sedimentary fluxes and the rainfall fluxes, indicative that
atmospheric transport of these metals to the coastal areas and the area
of the Soledad Basin are a possible explanation.

*Metals, ^Pollution, *Sediments, *Measurements, Analytical techniques,
Lead, Zinc, Chromium, Silver, Sampling, Water pollution, Human resources,
Storm runoff, Coastal areas,  Environmental effects,  Atmosphere

California (San Pedro,  Santa Monica, Santa Barbara), Anthropogenic fluxes
                                        513

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065E

MONITORING CONSIDERATIONS FOR MUNICIPAL WASTEWATER EFFLU-
ENT AND SLUDGE APPLICATION TO THE LAND,

Balkeslee, P. A.

Michigan Department of Natural Resources

In:  Proceedings of the Joint Conference on Recycling Municipal Sludges and
Effluents on Land, July 9-13, 1973, Champaign, Illinois, The National Associa-
tion of State Universities and Land-Grant Colleges, University of Illinois,
p 183-198.  2 tab.

Monitoring the performance of the many interrelated systems which are involved
in any project employing waste water or waste water sludge application to
the land is not reviewed as a substitute for a full understanding of system
response prior to project commitment.  The role of an on-going monitoring
program should be to confirm judgments made at the design stage.  Where inadequate
information is currently available about the nature of system response, adequate
safeguards must be provided and assured.  Data presented represent an overview
of current effluent and waste water sludge quality at Michigan municipal
waste water treatment plants.  Additional model guidelines are being used in
Michigan for groundwater monitoring associated with on land disposal systems.

*Monitoring, *Waste water, *Waste water treatment, Treatment facilities,
Effluents, Sludge, Michigan, Systems analysis, Municipal wastes, Municipal
water, Groundwater

*Municipal waste water, *Land disposal, Guidelines
066E

ANALYSIS OF BIOLOGICAL, CLINICAL, AND ENVIRONMENTAL
SAMPLES USING PROTON-INDUCED X-RAY EMISSION,

Walter, R. L., Willis, R. D., Gutknecht, W. F., and
Joyce, J. M.

Duke University, Durham, North Carolina, Department of
Physics and Triangle Universities Nuclear University

Analytical Chemistry, Vol. 46, No. 7, p 843-855, June, 1974.   19 fig, 16 ref.

A 3-Mev beam of protons 2 to 150-nanoampere intensity has been used to excite
x-ray emission from a wide range of environmental and biological samples.
These include human tissue, body fluids, soil extracts, leaves, coal, fly ash,
ion-exchange membranes, and proteins.  The x-rays have been detected using a
Si(Li) solid state detector for the elements P (Z=15) through Pb (Z=82).
Linear response has been demonstrated for the elements Pb, Cu, Zn, Co, and Mn
from 5 ng to greater than 2 micrograms.  A lower limit of sensitivity of approxi-
mately 200 picograms in the irradiated area has been attained with the more
responsive elements when they are deposited on very thin substrates.  The
proton-induced x-ray emission technique seems well suited to  rapid and economical
multielement analyses for samples of environmental and clinical interest.
Data observations give critical evaluation.

*X-rays, *Analytical techniques, *X-ray fluorescence, *Sampling, Coal, Human
pathology, Ion exchange, Membranes, Data collections, Irradiation

*Proton-lnduced x-rays, Solid state detector, Biological sampling, Clinical
sampling, Environmental sampling, X-ray emissions, Durham, North Carolina
                                          514

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067E

THE USE OF AN ELECTRON CAPTURE DETECTOR FOR THE DETER-
MINATION OF PESTICIDES IN WATER,

Uhnak, J., Sackmauerova, M. , Szokolay, A., and Palusova, 0.

Research Institute of Hygiene, Bratislava, Czechoslovakia

Journal of Chromatography, Vol. 91, p 545-547, April, 1974.  10 ref.

An electron capture detector is used for the determination of chlorinated in-
secticide residues in water.  Linear response of the detector was found for
BHC and DDT isomers and metabolites in the range 0.03-1.20 micrograms/ml.
Results for the determination of chlorinated insecticide (alpha-BHC; alpha-
+ beta- +• delta-BHC; DDT + DDE) residues in waters in Slovakia (for the years
1971-72) are given.  BHC and DDT contents in Slovakian rivers ranging from 0.01
to 0.80 micrograms/liter, in the Danube from 0.01 to 0.60 micrograms/liter
and in ground waters from 0.02 to 0.30 micrograms were found.  The DDT content
was lower than the content of BHC residues.  The results agree with the actual
consumption of chlorinated insecticides in agriculture in the area studied.

*Pesticides, *Water pollution, Insecticides, Chlorine, Water pollution sources,
Groundwater, Agriculture, Rivers

*Electron capture detector, Czechoslovakia
 068E

 INVESTIGATION  OF  VOLATILE  ORGANIC  MICROPOLLUTANTS  IN  AIR
 AND WATER USING LOW-TEMPERATURE  CAPILLARY  GC-MS,

 Bergert, K. H., Betz, V.,  and  Pruggmayer,  D.

 Batelle-Institute e.V., Hauptabteilung  Chemie,  Frankfurt
 am Main, Am Roverhof, Bundersrepublik Deutschland

 Chronatographia,  Vol. 7, No. 3,  p  115-121, March,  1974.   6  fig,  24  ref.

 This paper describes a method  allowing  routine  separation and  identification
 of organic micropollutants within  a  concentration  range  10  to  the minus  4th
 power  to 10 to the minus 8th power percent by volume.  Enrichment of  the com-
 ponents occurs in a microgradient  tube.  Separation on glass-thin film open
 tubular columns by linear-programmed low-temperature  gas Chromatography
 (LTGC) and identification by a mass  spectrometer are  coupled to  it.   Evaluable
 mass-spectra are  obtained  for  concentrations as low as 0.02 ppb   .  Analyses
 can be performed  on commercial equipment.

 *Pollutants, *Gas Chromatography,  *Mass  spectrometry, Concentrations,
 Equipment, Analytical techniques

 *0rganic micropollutants, Microgradient  tubes,  Low temperature
                                          515

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069E

PORTABLE DEVICE TO MEASURE INDUSTRIAL WASTEWATER FLOW,

Forester, R., and Overland, D.

North Star Research Institute,
Minneapolis, Minnesota

Journal of the Water Pollution Control Federation, Vol. 46, No. 4,
p 777-778, April, 1974.

Many industrial plants do not have provisions for the installation of
temporary open channel flow recording systems.  Data are often difficult
to interpret because lift pumps, used to move waste water from a pump to
the treatment plant, tend to cycle on and off at frequent intervals
resulting in badly smeared recorder charts.  Herein described is a means
of monitoring the pumps to provide a record of pump operating time which
defines both the total flow and the flow during any time period.  The
data obtained by the pump cycle recorded can be used to proportion in-
dividual samples from an automatic sampler into a composite sample and
also to measure total flow.  The pump cycle measuring device is rugged,
inexpensive, small, lightweight, requires no precision in alignment,
and is easily and rapidly installed by one person.

*Monitoring, *Flow measurement, Data collections, Open channel flow,
Pumps, Instrumentation, Sampling
070E

SPECTROSCOPIC DETERMINATION OF TRACE ELEMENTS IN SEWAGE
SLUDGES,

Beech, G.

The Polytechnic, Wolverhampton WV1 1LY,
Great Britain

Journal of Chemical Education, Vol. 51, No. 5, p 328, May, 1974.  1 tab.

Sewage sludge has many advantages such as  the high organic content, the
presence of trace elements, and its ready  and continued availability.
Yet the use of sludges as fertilizers can  lead to the accumulation of toxic
levels of heavy metals in soils which may  then be picked up in crops and
passed on to man.  Atomic absorption spectrophotometry was used to quan-
titatively analyze samples for copper, nickel, and zinc.  Results for
domestic and industrial sludge samples indicate a total of 7340-7800 ppm
of zinc of which 3100-4760 ppm are extractable; 930-1250 ppm of copper
with 10-19 ppm extractable; and, 280-580 ppm nickel with 252-357 ppm
being extractable.

*Sewage sludge, *Fertilizers, *Copper, *Nickel, *Zinc, *Spectrophotometry,
Analytical techniques, Heavy metals, Toxicity, Domestic wastes, Industrial
wastes

Great Britain
                                             516

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071E

ADSORPTION OF MBAS FROM WASTEWATERS AND SECONDARY EFFLUENTS,

Rlckert, D., and Hunter, J. V.

Rutgers University,
New Brunswick, New Jersey

Journal of the Water Pollution Control Federation, Vol. 46, No. 5, p 911-919,
May, 1974.  5 fig, 2 tab, 13 ref.

In most municipal waste waters, methylene blue active substances (MBAS)
make up a significant part of the potentially adsorbable, dissolved organics.
This study was done to establish the characteristics of MBAS adsorption onto
activated carbon from waste water and secondary effluent.  On the basis of
adsorption behavior observed in this study, it would appear that there are
three groups of MBAS.  One group is observed at low carbon doses, contains
the bulk of the total MBAS, and is readily adsorbable.  A second group is
noted at intermediate dosages, contains little of the total MBAS and is poorly
adsorbable.  At high carbon dosages a third group appears, again making up
only a small portion of the total MBAS.  This latter group is essentially
nonadsorbable.  Freundlich plots of the groups exhibit two stages, with
each high concentration (lower carbon dose) segment corresponding closely to
the range of readily adsorbable MBAS.  By the use of Freundllch equation
constants, the carbon dosages necessary to reduce MBAS over defined concen-
tration ranges were calculated for the readily adsorbable segment of each plot.
The results indicated that organic materials in the systems have a strong
competitive effect on the adsorption of MBAS.  It is postulated that the
greater part of MBAS in waste water is undegraded or slightly degraded linear
alkylate sulfonates, whereas in secondary effluents the bulk of the MBAS is
a mixture of partially oxidized LAS.

*Adsorption, *Effluents, Waste water treatment, Activated carbon, Total
organic carbon, New Jersey, Analytical techniques

*Freundlich equation, *Methylene blue active substances, *Linear alkylate
sulfonates, Secondary effluents
072E

STABILITY OF CRUDE OIL-IN-WATER EMULSIONS,

Chen, E. C.

Inland Waters Directorate,
Environment Canada, Ottowa, Canada

The Journal of Canadian Petroleum, Vol. 13, No. 1, p 38-41, January-March,
1974.  3 fig, 1 tab, 11 ref.

A Coulter counter was used to measure the droplet-size distribution of crude
oil-in-water emulsions.  The stability of the emulsions was determined by the
decrease in oil concentration and the change in specific surface with time.  All
experiments were carried out at room temperature with initial oil to water
volume ratios of 0.005 and 0.01.  Six different types of crude oil were investi-
gated.  All behaved similarly.  Creaming was predominantly responsible for
the instability of the emulsions.  However, all the emulsions finally at-
tained stability with an oil concentration of between .00001 and .001 percent
volume, a specific surface of around 3 x 1000 sq cm/g and a droplet size
below 4 millimicrons.

*Emulsions, *Stability, Oil spills,  Measurements,  Temperature

*0il-in-water emulsions, *Crude oil, *Coulter counter,  Droplet size, Creaming
                                    517

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073E

APPLICATION OF NASA-DEVELOPED TECHNOLOGY TO THE AUTOMATIC CONTROL
OF MUNICIPAL SEWAGE TREATMENT PLANTS,

Hiser, L. L.

Southwest Research Institute,
San Antonio, Texas

National Technical Information Service Report No. N74-11903, November, 1973.
28 p, 8 fig, 6 tab, 4 ref.

A search was made of NASA-developed technology and commercial technology for
process control sensors and instrumentation which would be applicable to
the operation of municipal sewage treatment plants.  Process control con-
cepts were formulated that incorporated specific items into systems to auto-
matically operate municipal sewage treatment plants.  A preliminary design
of the most promising concept was developed into a process control scheme
for an activated sludge treatment plant.  This design included process
control mechanisms for maintaining constant food to sludge mass (F/M) ratio,
and for such unit processes as primary sedimentation, sludge wastage, and
underflow control from the final clarifier.

Instrumentation, *Technology, *Municipal wastes, *Sewage treatment, Clarifi-
cation, Activated sludge, Automation, Control

NASA, Commercial technology, Treatment plants, Municipal sewage treatment,
Process control mechanisms, F/M ration (food to sludge mass), Sensors
074E

INVESTIGATION OF METHODS FOR DETERMINING OPTIMUM POWDERED CARBON AND
POLYELECTROLYTE DOSAGES IN MILITARY WASTEWATER TREATMENT SYSTEMS,

Wang, L. K.

Department of the Army,
Research and Development Center,
Fort Belvoir, Virginia

Calspan Report No. N0-5296-M-5, February 15-November 15, 1974.  109 p.
21 fig, 26 tab, 108 ref.

Physical and chemical characteristics of waste waters generated by typical
field laundries, showers, and kitchens were compiled.  Previous investigations
of the use of polymers and carbon in the treatment of waste waters with
characteristics similar to those generated at military bases were surveyed
and assessed.  Laboratory investigations were conducted to optimize the
controlling parameters of a waste water treatment system involving powdered
carbon adsorption, polymer coagulation and diatomite filtration.  Analytical
studies were conducted to develop the methods and a field test kit necessary
for determining the nature and concentration of pollutants likely to be
present in waste water generated at field laundries, showers, and kitchens.
The test method and the test, kit developed were designed for use in the field
by military personnel with limited training to provide guidance for deter-
mining the optimum carbon-polymer dosages.

*Waste water treatment, *Military aspects, Domestic wastes, Carbon,
Laboratory tests, Coagulation, Filtration, Analytical techniques, Polymers,
Chemical analysis

Powdered carbon, Carbon-polymer dosages, Diatomite filtration
                                    518

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    07 5E

    BIOLOGICAL TREATMENT TECHNOLOGY,

    Ludzack, F. J.

    U. S. Environmental Protection Agency,
    Cincinnati, Ohio,
    Municipal Permits and Operations Division

    National Technical Information Service Report No. PB-228  148, December,  1973.

    A collection  of  instructional materials  to  assist the  student to  upgrade
    performance of biological  treatment  facilities  is provided.  Information
    gathering techniques related to waste water characteristics, concentrations,
    and loading are  described.  The influence of these  data upon common  treatment
    operations and correction  of treatabllity difficulties are  considered.   Opera-
    tional  control to maximize the performance  of existing facilities are dis-
    cussed  along  with selection of add-on operations or design  of new facilities
    to upgrade the treatment system to a performance compliance status.

    *Publications, ^Training,  *Biological treatment, Methodology, Activated
    sludge, Analytical techniques, Cost-benefit theory, Environmental control,
    Disinfection, Laboratory tests, Industrial  wastes,  Measurements,  Municipal
    wastes, Nutrients, Maintenance, Project  planning, Recycling, Safety,
    Separation techniques,  Toxicity, Waste water treatment, Trickling filters

    *Manuals, Treatment operations, Instruction
076E

A GROUNDWATER PROFILE SAMPLER,

Hansen, E. A., and Harris, A. R.

USDA Forest Service,
Cadillac, Michigan,
North Central Forest Experiment Station

Water Resources Research, Vol. 10, No. 2, p 375, April 1974.  I fig, 1 ref.

With increasing concern over groundwater contamination, new data collection
methods are needed.  Analysis of the chemical composition (including contami-
nants) of groundwater at several depths would permit the determination of
the thickness of any contaminated zone and the depth of maximum concentration.
Such profiles collected over an area would then indicate the rate of contami-
nant movement due to groundwater flow and its dissipation (by absorption,
diffusion, or decomposition) in time and space.  To meet this need, a "ground-
water profile sampler" was developed.  The instrument is a series of fiber
glass probes spaced in sandpacked compartments in a screened well point which
permits the collection of a number of discrete groundwater samples from pre-
determined depths in a single borehole.

*Groundwater,  *Sampling, *Data collections, Wisconsin, Analysis, Flow,  Con-
tamination, Profiles, Instrumentation

*Groundwater profile sampler
                                             519

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077E

QUALITY OF BERLIN SURFACE WATERS:  MEASURING SCHEME, (DAS
GUTEMESS PROGRAMS DER BERLINER OBERFLACHENGEWASSER) ,

Frenzel, H., and Sarfert, F.

Umwelthygiene, Vol. 25, No. 5, p 97-99, 1974.  1 fig, 2 ref.

A scheme to measure the quality of Berlin surface waters has "been extended
to a present total of 98 sampling points.  The program includes the examina-
tion of physical/chemical, bacteriological, biological, and partly, radiologi-
cal parameters.  It was necessary to make arrangements between the participa-
ting laboratories as to the methods of analysis to be used.  The resulting
data will be subject to automatic data processing.

*Water quality, *Surface water, *Measurement, *Data processing, Monitoring,
Automation

Physical parameters, *Chemical parameters, *Bacteriological parameters, *Bio-
logical parameters, *Radiological parameters, Berlin
    078E

    HOW TO MEASURE AMBIENT POLLUTION,

    de Veer, S. M.

    Philips Gloeilampenfabrieken
    Eindhoven, Netherlands,
    Department Philips Pollution Measuring

    La Tribune du Cebedeau, Vol. 27, No. 364,  p 129-133,  March,  1974.   5 fig, 6 ref.

    The best way to measure ambient pollution quite often depends on the reason
    why one wishes to measure it.  Efficient control is only possible if the
    feedback control loop "process - measurement - control" is closed and all
    three segments are working optimally.  For adequate pollution control continu-
    ous measurement is required.  Field monitoring is usually done without an
    operator or data processor on hand.  Extra reliability of the monitoring equip-
    ment is therefore essential.  Automatic calibration,  representative sampling,
    proof against environmental influences, and automatic data transmission are
    necessities of remote monitoring.  This paper gives examples of the develop-
    ment of monitors for air and water pollution meeting the above requirements.
    Some remarks are made relative to the application and costs  of monitoring.

    *Monitoring, *Remote sensing, *Data transmission, Costs, Water pollution,
    Water quality measurement, Air pollution,  Automation

    Netherlands, Field measurement
                                            520

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079E

INFORMATION ON THE RECENT PRACTICE OF HYGIENIC QUALIFICA-
TIONS OF SURFACE WATERS, (TAJEKOZTATO A FELSZINI VIZEK
HIGIENES MIOSITESENEK JELENLEGI GYAKORLATAROL),

Schiefner, K., Maar, I., and Rako, J.

Egeszsegtvdomany, Vol. IS, No. 1, p 58-63, 1974.  1 fig, 2 tab, 6 ref.

Based on the results of detailed tests (chemical, bacteriological and biologi-
cal), the authors suggest the extension of parameters for determining the
hygienic quality of surface vaters (as based on oxygen consumption, coliform
counts, and saprobic character).  For this reason they advise the adoption of
"trophic character" which they evaluated by the number of algae they found in
a volume of water.  "Trophic character" determined on the basis of floral or-
ganisms has no direct relationship with the saprobiological feature which
determines the group classification for hygienic surface water utilization.  The
water qualification involving new parameters generally results in a worse
grouping of classifications.  Evaluation of floral microorganisms (algae)
draws attention to biological phenomenon (mass production, flourishing of
water) that influence water consumption primarily from the technological
point of view, and hint at their effects (mechanical, taste and odor effects).
Statistical evaluations also confirm the necessity of adopting the new para-
meters in water qualification.

*Water quality standards, *Trophic level, *Algae, Oxygen demand, Coliforms,
Sampling

*U.S.S.R., *Trophic character
 080E

 COUGHING  FISH MAY MONITOR WATER  QUALITY,

 Chemical  and Engineering News, Vol.  52, No.  20,  p  64, May  20,  1974.

 The tendency of  some  species  of  fish to "cough"  (or  at  least make a  sound
 similar to  it) may be useful  in  monitoring water quality  in lakes and
 streams.  Tests  have  shown  that  concentrations of  copper  and mercury that
 inhibit growth and reproduction  also cause an increase  in  the  frequency
 of coughing.  The coughing  is  a  normal process that  clears the gills of
 debris.   Some fish which are  known  to exhibit this behavior include  blue-
 gill,  sunfish, fathead minnows,  and all trout and  salmon.   Testing is under-
 way on ten  heavy metals and pesticides to see if,  indeed,  this type  of bio-
 assay would be reliable.

 *Fish, *Water quality, *Monitoring,  Bioassay, Mercury,  Copper
                                             521

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   081E

   WATER AND EFFLUENT INSTRUMENTATION MADE SIMPLE,

   Maddinson, C.

   Taylor Instrument Companies (Europe) Limited

   Water Services, Vol. 78, No. 938, p 116-117, April 1974.  5 fig.

   A considerable amount of money will be spent in England during the next few
   years on sewage treatment representing a growth for the instrument industry,
   though instrumentation represents but a small percentage of the expenditures
   anticipated.  Discussed are various sewage flow measurement techniques such
   as level, differential pressure, and venturi measurements or the use of a
   magnetic flow meter.  Also mentioned are pollution control devices and appli-
   cations to pumping and speed control.

   *Sewage treatment, *Instrument:ation, *Flow measurement, *Water pollution con-
   trol, Application methods, Effluents, Pressure

   Great Britain, Magnetic flow meter
082 E

SUSPENDED SOLIDS ANALYSIS USING ERTS-A DATA,

Kritikos, H., and Yorinks, L.

Pennsylvania University, The Moore School of Electrical
Engineering, Philadelphia, Pennsylvania

Remote Sensing of Environment, Vol. 3, No. 1, p 69-78, 1974.  6 fig, 4 tab, 19
ref.

Analysis of magnetic digital tapes of the imagery obtained by ERTS-A for
selected areas of the Potomac River has been carried out with statistical
analysis of all four bands being performed.  Results indicate that band III is
useful in determining the water-to-land interface.  Data on bands II suggest
the existence of three distinct types of water, those having low, medium,
and high reflectivity; the high reflectivity type was identified as having
high concentrations of suspended solids.  Areas of low reflectivity were
identified as having relatively lower concentrations of suspended solids.
A commonly used computer technique with some additional refinements has been
used to generate thematic maps which Identify the above areas and show
their geographic distribution.

^Remote sensing, *Analytical techniques, *Statistical analysis, *Suspended
solids, *Earth-water interfaces, Potomac River, Computers, Water types, Re-
flectance, Data collections
                                           522

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083E

THE SOLVENT EXTRACTION ATOMIC ABSORPTION ANALYSIS OF
EFFLUENTS AND WATER,

Lloyd, A.

Sussex River Authority, England

Water Pollution Control,, Vol. 73, No. 2, p 224-229, 1974.  1 fig, 4 tab,
16 ref.

The application of solvent extraction atomic absorption spectrophotometry
(AAS) to the analysis of effluerts and stream samples provides a rapid and
accurate means of determining a variety of metals at the microgram/liter
level.  The ammonium pyrollidine dithiocarbamate/methyl isobutyl ketone
system, which uses simple AAS equipment, can be applied to an even wider range
of metals including Ag, Hg, and As9.  The most important step in the analysis
is the extraction stage, and potential interferences are likely to be of a
chemical nature involving a lowering of the extraction efficiency of the
chelate.  When wet oxidation is necessary or when the sample contains a diver-
sity of metals at the mg/liter level, a double extraction is required.  How-
ever, for relatively clean samples a single extraction is suitable.  Standard
addition offers the advantage of allowing a single extraction to be applied
to a wide range of sample types.

*Solvent extractions, *Spectrophotometry, *Analytical techniques, *Metals,
Effluents, Effluent streams

*Ammonium pyrollidine dithiocarbamate/Methyl isobutyl ketone system,
Wet oxidation, Atomic absorption spectrophotometry (AAS)
      084E

      SELF-CONTAINED SAMPLING AND MEASUREMENT SYSTEM FEATURES
      RESPIROMETER,

      Robertshaw Controls Company,
      Richmond, Virginia

      Water and Sewage Works, Vol. 121, No.  2, p  53, February,  1974.

      A self-contained sampling and measuring system for use in waste water  treatment
      operations has been introduced by Robertshaw Controls Company.  It utilizes
      a continuous bacterial respirometer and is  designed  to provide municipal and
      industrial sewage treatment plant operators with continuous  information con-
      cerning the treatment process.  The on-line data provided by the respirometer
      is convertible to biochemical oxygen demand (BOD) values.  A waterproof en-
      closure houses the respirometer which  samples from the aeration basin  or pri-
      mary clarifier effluent.  The sample is aerated and  metered  through an internal
      residence chamber at a constant rate.  The  differential oxygen utilized by
      the active bacteria throughout the system is sensed  by dissolved oxygen sensors
      located at both ends of the residence  chamber.  Toxic or  inhibitory materials
      which adversely affect the bacterial metabolism are  identified readily.  The
      system has an automatic cleaning cycle which prevents bacterial growth within
      the system.

      *Sampling, *Measurement, ^Municipal wastes, Industrial wastes, Biochemical
      oxygen demand, Aeration, Clarification, Dissolved oxygen, Bacteria, Monitoring,
      Toxicity, Cleaning

      *Respirometer
                                                  523

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085E

MEASURING OPEN CHANNEL WASTEWATER FLOWS,

Blols, R. S.

Leupold and Stevens, Incorporated
Beaverton, Oregon

Industrial Wastes, Vol. 19, No. 6, p 20-22, November/December, 1973.  3 fig, 2 ref.

Since the 1972 Federal Water Pollution Control Act Amendments, industrial and
municipal wastes must be recorded in terms of amount of discharge.   Measurement
of flow is not only legally required for monitoring pollution, but  is also
economically useful for an individual industry to be able to locate unnecessary
discharge caused by accident such as by the opening of valves in fresh-water
washlines for extended periods of time.  Types of flow measurements include
recording devices such as a weir with a stilling well and recorder.  Other
methods are remote operation, the capacitance type probes, or bubbler devices.
Selection of a feasible method should depend upon site conditions,  expected
flow range, type of liquid (sewage, waste water, water supply for irrigation),
allowable head loss, required accuracy, and allowable expense.

*Measurements, *Flow measurements, *0pen channel flow, *Waste water, Instrumen-
tation, *Federal Water Pollution Control Act, Recording,  Weirs, Water supply,
Sewage, Liquid wastes, Monitoring, Industrial wastes, Municipal wastes,
Discharge, Water pollution, Costs
  086E

PHOSPHORUS STUDIES IN LOWER GREEN BAY, LAKE MICHIGAN,

Sridharan, N., and Lee, G. F.

Wisconsin University,
Madison, Wisconsin,
Water Chemistry

Journal of the Water Pollution Control Federation, Vol. 46, No. 4, p 684-696,
April, 1974.  9 fig, 7 tab, 16 ref.

Green Bay, Wisconsin, receives excessive amounts of aquatic plant nutrients
from municipalities, industries, and agricultural facilities.  Water samples were
collected and analyzed to study the chemistry of phosphorus in lake sediments
of this area.  The Fox River seems to be the major source of the area's phos-
phorus.  Dredge and core methods indicated an association of phosphorus with
iron; mechanisms were proposed to explain the phosphorus release under oxic and
anoxic conditions.  Orthophosphate concentrations in water of lower Green Bay
are quite high, two to three times higher than the critical concentrations for
excessive algal growth.  Despite the reduction of phosphorus input from waste
water sources by 80 percent, algae are not likely to become phosphorus limited.
Water quality problems are complex and include high BOD and turbidity.  However,
by removing  80 percent of phosphorus from waste water sources, Lake Michigan
may be protected from future water quality deterioration.

*Phosphorus, *Lake Michigan, *Municipal wastes, industrial wastes, *Agricul-
tural wastes, Nutrients, Algae, Measurement, Analytical techniques, Biochemical
oxygen demand, Turbidity, Water quality control, Water pollution, Waste
water disposal, Chemistry, Sediments


Orthophosphates, Green Bay, Wisconsin
                                      524

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087E

WATER POLLUTION SAMPLING, MONITORING AND ANALYSIS INSTRU-
MENTATION,

Chermisinoff, P. N.

Newark College of Engineering,
Environmental Engineering Department

Pollution Engineering, Vol. 6, No. 4, p 36-48, April, 1974.  37 fig.

Sampling and monitoring of water quality include on-site measurements and pro-
cedures which remove water from its environment for off-site analyses.  Purposes
cited include:  ensuring proper operating conditions in the process plant;
providing a continuous and permanent record of process and waste water handling;
ensuring efficiency and reliability of manufacturing operations and waste pro-
cessing; providing a basic tool for pollution control; and ensuring that stan-
dards of environmental quality set by regulatory agencies be met.  Types of
samples are the individual grab sample, simple composite sample, sequential
composite sample, continuous sample, hand proportioned composite sample, and
automatic proportioned composite sample.  In analyzing waste water systems,
separation and concentration methods are used.  These include carbon absorption,
ion exchange, freeze concentration, chromatography, and liquid-liquid extraction.
Types of spectrophotometry are detailed.  Physical parameters for water pollu-
tion recorded include temperature, electrical conductance, density, turbidity,
viscosity, volatility, and particulate and dissolved solids.  Temperature is
also measured by varying methods.  A list of about one hundred corporations for
instrumentation is given for additional information about specific methods.

Instrumentation, *Monitoring, *Measurement, *Sampling, *Water quality, On-site
investigations, Recording, Water pollution control, Regulation, Carbon absorption,
Ion exchange, Spectrophotometry, Temperature, Density, Information, Systems
analysis, Reviews

Waste water systems, Corporations
 088E

 THE MEDWAY WATER BOARD TELEMETRY AND TELECONTROL SYSTEM,

 Howard, D. W., and Insley, M. G.

 Westinghouse Brake and Signal Company, Limited,
 Chippenham, Wiltshire, United Kingdom,
 Automation Division

 Water Services, Vol. 78, No. 937, p 90-95, March, 1974.  6 fig, 1 tab.

 Telemetry equipment has been proven in both the United Kingdom and elsewhere,
 using Westinghouse Style F2 "Westronic" equipment.  The County of Kent on the
 River Medway decided to institute a Remote Control and Telemetry scheme which
 employs computer control, visual display by cathode ray tube units, data logging,
 and a closed circuit television link.  The daily log gives outputs in two
 parts, daily water outputs (amounts of flow) and chemical alarms (chlorine,
 pH, temperature, oxygen content, etc.).  Components of the system are:  a com-
 puter controlled master telemetry station capable of expansion to cover future
 phases of the scheme; associated logging and visual display units under the
 computer's control; two Mimic diagrams to cover the "Area of Supply" and the
 "River Medway Scheme"; three outstations at the River Intake, the Treatment
 Works, and the Low Lift pump house; a manual standby panel for obtaining data
 and operating controls when the computer is off line; a private telephone exchange;
 and a closed circuit television system.

 *Equipment, *Control, *Telemetry, Computers,  *Recording (logging), Chlorine,
 pH, Temperature, Rivers,  Treatment facilities, Water supply,  Automatic control,
 Data collection, Equipment

 Great Britain (River Medway, Kent), Chemical alarms, Westinghouse F2 Westronic
 equipment, Telecontrol, Mimic diagrams


                                          525

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089E

DETERMINATION OF THE BREAK-THROUGH VOLUME OF SODIUM
CHLORIDE FOR SOIL COLUMNS IN PESTICIDE LEACHING,

Dannals, L. E., and Kucharczk, N.

Uniroyal Chemical, Division of Uniroyal, Incorporated,
Naugatuck, Connecticut,
Agricultural Chemicals Research and Development

Bulletin of Environmental Contamination and Toxicology, Vol. 11, No. 4, p 348-
351, 1974.  1 fig, 1 tab, 2 ref.

Factors such as column matrix geometry, diffusion, and retardation due to
adsorption and ion exchange influence and mobility of any chemical through a
soil column.  The extent to which pesticides leach in soils is a measure of
potential groundwater contamination.  This can be commonly determined in soil
columns.  A highly-leachable substrate such as NaCl is used for standardization
to determine the breakthrough volume for every column and soil used.  The de-
finition for the break-through volume of sodium chloride is defined as the
volume needed to elute 50 percent of the applied salt out of the column.  This
is determined by 36NaCl and liquid scintillation counting.  In this way, column
leaching studies become more accurate and intercomparable.

*Pestlcides, *Soil leaching, *Soil analysis, *Groundwater, *Sodium chloride,
Contamination, Water pollution, Measurement, Analytical techniques

*Break-through volume, Liquid scintillation, Soil columns, Standardization
 090E

 COLLABORATIVE  TESTS  OF WATER ANALYSIS  (THE  CHEMAQUA
 PROGRAMME),

 Kingsford, M.,  Stevenson,  C. D.,  and Edgerley, W. H. L.

 Department of  Scientific and Industrial Research,
 Lower  Hutt,  New Zealand,
 Chemistry Division

 New Zealand  Journal  of Science, Vol. 16,  p  895-902, March,  1973.   2  tab,  4  ref.

 Sixteen New  Zealand  laboratories  have  analysed two water samples  for various
 inorganic constituents.  The methods used to  determine carbonate  were unsatisfac-
 tory,  and a  better method  is needed to analyse for low levels  of  sulphate.  The
 total  errors for the remaining estimations  were  less than 25 percent.  These
 estimations  could be rated as excellent,  the  most precise being that of con-
 ductivity.

 *Analytical  techniques, *Water supply, *Sampling, *Inorganic material, *Car-
 bonates, Conductivity, Laboratory analysis, Estimating

 *Sulphates,  New Zealand
                                      526

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 091E

 POLAROGRAPHIC DETERMINATION OF 8-HYDROXYQUINOLINATES  AFTER
 EXTRACTION WITH NAPHTHALENE.   TRACE ANALYSIS  OF CADMIUM
 AND LEAD,

 Fujinaga,  T., and Purl,  B.  K.

 Bulletin of the Institution of Chemistry Research,  Kyoto University,  Vol.  51,
 No. 5,  p 253-267, September,  1973.   4 fig,  9  tab,  12  ref.

 A rapid extraction-polarographic method has been developed for the direct  de-
 termination of cadmium and  lead extracted into the  organic phase.   8-Hydroxy-
 qulnolinates of cadmium and lead were extracted with  molten naphthalene in
 the pH  range of 7-10 and 9-12 respectively; as the  temperature was lowered,
 naphthalene separated out as a solid mass containing  the metal-oxinate. This
 solid mass was dissolved in dimethylformamide and the polarograms  were recorded
 using 0.1 M sodium perchlorate-0.1 M perchloric acid  in case of cadmium and
 0.1 M pyridine-0.1 M perchloric acid in case ofead  as the supporting elec-
 trolytes.   Under these conditions, these metal-oxinates gave well  defined  waves
 with E  sub 1/2 of -0.63 V and -0.47 V versus SCE respectively.  The relation be-
 tween diffusion current and concentration is linear in the range of 0.0-112
 micrograms/10 ml for Cd and 0.0-207.0 micrograms/10 ml for Pb.  The interferences
 of various ions had been studied in detail.  The method is simple, rapid,  and
 sensitive, and applicable for the determination of  cadmium, mercury,  and
 lead in various complex materials.

 *Polarographic analysis, *Cadmium, *Mercury,  *Lead, Separation techniques,
 Analytical techniques
 092E

 RAPID METHODS FOR THE DETERMINATION OF FAECAL CONTAMINA-
 TION IN OYSTERS,

 Qadri, R. B., Buckle, K. A., and Edwards, R. A.

 New South Wales University, Kensington, Australia,
 Department of Food Technology

 Journal of Applied Bacteriology, Vol. 37, No. 1, p 7-14, 1974.  6 tab, 15 ref.

 The fact that food poisoning outbreaks are known to result from the consumption
 of fecally contaminated oysters makes it desirable that such products should
 be examined for enteric pathogens.  Two methods for the rapid detection and
 estimation of numbers of fecal coliforms and Escherichia coli type I in oysters
 have been developed.  That for fecal coliforms involves incubation of tubes
 of MacConkey broth for 2 h at 37 F and then for 22-24 hours at 44 F.  The
 second method, a modification of MacKenzie, Taylor & Gilbert's (1948)  specific
 method for E. coli type I, makes use of the same system of incubation, but
 requires the inoculation of tubes of peptone water as well as MacConkey broth,
 the former tubes being used for subsequent testing for indole formation.
 Both methods take only 24-26 hours and are as sensitive and accurate as the
Most Probable Number methods which are in common use and which take upwards
 of 72-96 hours to complete.

 *Escherichia coli, *Incubation, laboratory tests, *0ysters, Contamination,
Analytical techniques,  Food


*Fecal coliforms,  *Enteric pathogens,  Most Probable Number method, MacConkey
broth,  Peptone water, Food poisoning
                                     527

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093E

A MEMBRANE FILTRATION TECHNIQUE FOR THE ENUMBERATION OF
ESCHERICHIA COLI IN SEAWATER,

Halls, S., and Ayres, P. A.

Ministry of Agriculture, Fisheries and Food, Fisheries
Laboratory, Burnham-on-Crouch,  Essex, England

Journal of Applied Bacteriology, Vol. 37, No. 1, p 105-109, 1974.  2 tab, 7 ref.

Membrane filtration has become an accepted method for enumerating Escherichia
coli in water, but little published evidence could be found to judge the
specificity of the method to assess faecal contamination in either fresh or
saline waters.  A laboratory method was used to monitor the extent and degree
of sewage pollution in coastal areas.  There is still need for information
on what proportion of lactose-fermenting colonies from seawater, developing
at 44 F on a 4 percent enriched Teepol medium, are E. coli type I.  A total
of 1352 colonies from seawater was tested for production of indole and for
gas from lactose at 44 F.  In addition, 46 percent of the colonies were screened
by the IMVEC series of tests.  The proportion of colonies tested ranged from
10-100 percent, depending on the number of colonies on the membrane.  Many
of the colonies (81.9 percent)  to which IMVEC tests were applied were E. coli
type I; a further 10.9 percent  were Irregular type I.

*Bacteria, *Escherichia coli, *Sea water, Filtration, Sewage, Pollution,
Contamination, Saline water, Fresh water, Laboratory tests, Monitoring,
Costal areas

*Membrane filtration, *Fecal contamination, Enumeration
094E

LASER LIGHT SPOTS WATER POLLUTION,

Canadian Chemical Processing, Vol. 58, No.  4, p 31-32, April, 1974.

A remote sensing laser fluorometer device has been developed by  the Inland
Waters Directorate of Environment Canada.  This instrument is able to
detect specific substances at a distance, to operate at night, to perform
well in bad weather, to monitor large areas from land, shipboard, or air-
borne platforms, and to run unattended for long periods.  The entire
system, including power supply, weighs 100 kilograms with about 600  watts of
120-volt AC required to run it.  Considerable sophistication is required
to interpret the readout of the instrument.  Other than water quality
monitoring, the laser fluorometer can be applied in looking for oil  pipe-
line leaks and performing airborne forest health surveys.

Instrumentation, *Remote sensing, *Fluorometry, Water quality control,
Application methods, Monitoring
                                  528

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095E

BIO-DEGRADATION OF NON-IONIC SURFACTANTS - II:  BIO-
DEGRADATION ASSESSMENTS (BIODEGRADAZIONE DI TENSIOATTIVI
NON IONICI.  NOTA 2:  MISURE DELIA BIODEGRADAZIONE),

Albanese, P., and Capuci, R.

Montedison, Institute Ricerche "G. Donegani" Dipartimento
problem! ambientali, Novara, Italy

La Rivista Italiana delle Sostanze Grasse, Vol. 51, No. 2, p 70-81, February,
1974.  3 fig, 9 tab, 23 ref.

Research was performed to determine whether the EMPA test could be used
to assess biodegradation in non-ionic surfactants, polyethoxylated alkyl-
phenols, and alcohols using different analytic procedures as appropriate.
Standard-error values were discussed for the test and for concentration
assessments obtained from surface tension measurements.

*Biodegradation, *Surfactants, *Phenols, *Alcohols, Analytical techniques,
Testing, Measurements
096E

INSTRUMENTAL ANALYSIS IN ENVIRONMENTAL CHEMISTRY-
LIQUID AND SOLID PHASE DETECTION SYSTEMS,

Stedman, D. H., and Meyers, P. A.

University of Michigan, Ann Arbor, Michigan, Departments
of Chemistry and of Atmospheric and Oceanic Sciences

BioScience, Vol. 24, No. 6, p 346-349, June, 1974.  5 tab, 47 ref.

Analytical methods which depend upon detection in the liquid or solid phase are
described.  Thus, according to arbitrary separation, methods which analyze
solids or liquids after vaporizing them, such as gas chromatography and mass
spectrometry, are not included in this review.  The object of this review is
general capacities with selected references being mentioned.  Methods discussed
include liquid chromatography, infrared analysis, ultraviolet and visible
analysis, electron spin resonance, nuclear mangetic resonance, electroanalytical
techniques, and neutron activationaand x-ray fluorescence.

*Analytical techniques, *Reviews, Chromatography, Infrared radiation,
Ultraviolet radiation, Nuclear magnetic resonance, Electrochemistry,
Electronics, Neutron activationanalysis, X-ray fluorescence
                                      529

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097E

FLUORIDE VARIATION IN DOMESTIC SEWAGE RELATIVE TO TAP
WATER AND PRECIPITATION,

Hwang, C. P.

Saskatchewan University, Saskatoon, Saskatchewan,
Canada, Civil Engineering Department

Water and Sewage Works, p 138-139, April 30, 1974.  1 fig, 2 tab, 3 ref.

Due to increasing population and lack of adequate water resources it may be
necessary to utilize sewage as reclaimed water for public drinking.  A
knowledge of the variation of fluoride content of sewage can be important for
dental purposes as well as in determining if troublesome sewage is from
groundwater or sewage and estimating the amount of infiltration or direct inflow
to the sewerage system.  The distribution of precipitation and of tap water
and domestic sewage fluoride concentration for one year is tabulated for the
area of Saskatchewan, Canada.  Also the relationships between monthly total
precipitation and average fluoride content in tap water and domestic sewage
is presented.

*Potable water, *Water reuse, *Fluorides, *Precipitation, Domestic wastes,
Sewage treatment, Water pollution sources, Canada
098E

PREDICTION OF EFFLUENT MIXING PATTERNS USING A
BACTERIOPHAGE TRACER,

Statham, M.

University College, Cardiff, England, Department of
Microbiology

Water and Waste Treatment, Vol. 17, No. 3, p 20, 22, 24, March, 1974.
5 fig, 3 ref.

To investigate mixing patterns in water it is necessary to resort to some
tracing technique.  The technique chosen will depend upon the following
factors:  volume of water to be labelled, composition and concentrations of
dissolved solids in the water, quality and quantity of suspended solids in
the water, subsequent use to which labelled water may be put, and information
required from the experiment.  The use of bacteriophage as a water tracer is
a reliable and well tried technique.  The use of a bacteriophage marker to
trace water movement in a fairly turbid estaury is examined.

*Mixing, *Tracers, *Bacteriophage, Water circulation, Discharge (water),
Suspended solids, Hydrogen ion concentration, Volume

Great Britain
                                      530

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 099E

 THE DETERMINATION OF FORMALDEHYDE AND RELATED COMPOUNDS
 IN WATER AND  INDUSTRIAL  EFFLUENTS,

 Afghan,  B.  K.,  Kulkarni,  A.  V.,  Leung,  R.,  and Ryan,  J.
 F.

 Canada Centre for Inland Waters, Water Quality Research
 Division, Burlington, Ontario,  Canada

 Environmental Letters, Vol.  7,  No.  1, p 53-65, 1974.   3  fig,  1 tab,  11 ref.

 The automation of colorimetric  and fluorometric methods  for the determination of
 low levels  of formaldehyde and  related compounds in drinking water,  natural
 water, and  industrial effluents  is described.  The colorimetric method
 utilizes chromotropic acid;  the fluorometric method is based on the  reaction
 of formaldehyde with 2,  4-pentanedione and  ammonia to form a fluorescent
 product. The fluorometric method was found to be much more specific than
 the colorimetric procedure and  both methods are capable  of determining
 formaldehyde  down to 10  mg/liter at a rate  of 10 to 20 samples per hour.   A
 preliminary survey concerning the occurrance of formaldehyde and related
 compounds in  a wide variety of  samples, ranging from drinking waters to
 industrial  effluents was conducted with results indicating that considerable
 quantities  of these compounds are present in some waters receiving industrial
 wastes.   These results also show that samples which contain formaldehyde
 indicate the  presence of other  carbonyl compounds.

 *Analytical techniques,  *Water  analysis,  Industrial wastes, Automation,
 Colorimetry,  Fluorometry, Surveys, Potable  water

 *Formaldehyde,  Carbonyl  compounds
 100E

 MECHANICAL SEPARATION PROCESSES,

 Lehrer, I. H.

 Monash University,
 Department of Chemical Engineering

 PACE, Vol. 27, No. 2, p 21-26, February, 1974.  7 fig, 2 tab, 6 ref.

 Heterogeneous systems which consist of continous phases and dispersed phases
 and which may be treated by mechanical separation processes are discussed.
 Such separation is required for preparation of raw materials and purification
 of products in the complete process.  Applications of mechanical separation
 pertain to waste treatment and water reuse.  Theoretical derivations from
 basic principles are given as a guide in design of equipment.  These derivations
 are shown to be fallible and often the purchaser of such equipment must expect
 modifications to be necessary after installation.  Specific processes for
 which equations are given include sedimentation, filtration, and electrical
 separators.

 *Separation techniques, *Design criteria, *Equipment, Equations, Waste treatment,
Water reuse,  Sedimentation, Filtration, Mathematical studies, Analytical
 techniques

 *Mechanical separation, Electrical separators
                                    531

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10 IE

TRACE METAL CONCENTRATIONS IN BROWN SEAWEEDS, CARDIGAN
BAY, WALES,

Fuge, R., and James, K. H.

University College of Wales, Aberystwtyh,
Department of Geology

Marine Chemistry, No. 4, p 281-293, December, 1973.  2 fig, 4 tab, 24 ref.

Marine algae may be used to monitor coastal water trace-metal concentrations,
as long as a careful sampling procedure is adopted.  Concentrations of zinc,
cadmium, copper, manganese, iron, cobalt, nickel and molybdenum were examined
in brown algae, Fucus serratus and F. vesiculosus, from Cardigan Bay,
Irish Sea, Great Britain.  In both species a seasonal variation in metal content
was observed.  Zinc, cadmium, copper, iron, nickel and cobalt concentrations
were highest in the spring and lowest in the autumn, probably reflecting levels
of metabolic activity and climatic factors.  All the studied elements, except
nickel, reached highest concentrations in harbor specimens from Aberystwyth
and Aberaeron where rivers draining mineralized areas enter the sea.  Outside
the harbors, marked regional variations were observed.  Trace element concentrations
varied among different species from the same locality and also varied according
to position on the shore.

*Monitoring, *Marine algae, *Metals, *Brown algae, Seasonal, Minerals, Sampling,
Coastal areas, Climates, Harbors, Seas, Zinc, Cadmium, Copper, Iron, Nickel,
Cobalt

*Seaweeds, Great Britain, Coastal waters, Metabolic activity
10 2E

MASS SPECTROMETRIC IDENTIFICATION AND DETERMINATION OF
ORGANOCHLORINE HYDROCARBONS IN FISH (MASSENSPEKTROMETRISHE
IDENTIFIZIERHNG UND QUANTIFIZIERUNG VON CHLORKOHLENWASSER-
STOFFEN IN FISCH),

Schaefer, R. G.

Chemiker-Zeitung, No. 5, p 241-247, May, 1974.  10 fig, 3 tab, 27 ref.

Examined was the application of the gas chromatography/mass spectrometry
combination method in the analysis of chlorinated hydrocarbons in marine fish.
The following substances could be detected: p,p'-DDT, p,p'-DDD, p,p'-DDE,
hexachlorobenzene, and several PCB isomers (tetra-, penta-, hexa-, hepta-,
and octachlorobiphenyls).  Lindane, heptachlor, and aldrin were not found.
The detection of dieldrin was excluded by the applied clean-up procedure.
The quantification is carried out by means of mass chromatography using a
dedicated computer system.  The lowest detectable quantities are discussed.

*Mass spectrometry, *Hydrocarbons, *Fish, Polychlorinated biphenyls, Marine
fish, DDT, Dieldrin, Computers, Analytical techniques

*0rganochlorine hydrocarbons, Pollution identification
                                         532

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10 3E

A SIMPLE METHOD FOR INVESTIGATION OF THE BIODEGRADABILITY
OF PRODUCTS AND CONSTITUENTS IN WASTEWATER(EIN EINFACHES
VERFAHREN ZUR PRUFUNG DER BIOLOGISCHEN ABBAUBARKEIT VON
PRODUKTEN UNO ABWASSERINHALTSSTOFFEN),

Zahn, R., and Wellens, H.

Chemiker-Zeitung, No. 5, p 228-232, May, 1974.  4 fig, 2 tab, 5 ref.

A description Is given of a simple, cost-saving, method of testing the
biodegradability of products and the constituent substances of effluent.  Various
test parameters, the form of degradation curves, and the results of adaptation
tests are discussed.  The method described is readily reproducable and is
compared with other test methods.

*Biodegradation, *Costs, Analytical techniques, Tests,
Effluents, Waste water

*Biodegradability, Germany, *Degradation Curves, Test parameters
104E

POLLUTION CONTROL STARTS WITH ANALYSIS,

Automation, Vol. 21, No. 6, p 84-85, June, 1974.

Analytical instruments detect the presence and/or quantity of elements and
chemical compounds in a sample.  Presence is detected by comparing one or more
uniquely distinctive physical properties of the sample with those of known
standards.  Spectroscopy is a highly reliable and versatile analytic
technique.  It can be employed in several ways to detect and measure certain
constant physical characteristics of materials which produce predictable
patterns.  These can be matched against a known spectrum and thus be
identified.  The following spectrometric methods are described:  atomic
absorption spectrometry, infrared, ultraviolet, and visible spectrometry,
fluorescence spectrometry, gas chromatography, and mass spectrometry.

*Analytical techniques, Spectrometers, "^Instrumentation, Mass spectrometry,
Gas chromatography, Fluoresecence, Infrared radiation, Ultraviolet
radiation

Atomic abosrption spectrometry
                                      533

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    105E

    ATOMIC ABSORPTION SPECTROSCOPY,

    Braun, R. D., and Sapio, J. P.

    University of Michigan,
    Ann Arbor, Michigan

    Chemistry, Vol. 47, No. 6, p 9-13, June, 1974.  5 fig, 14 ref.

    Atomic absorption analysis is a relatively simple, inexpensive, sensitive,
    and accurate method to determine trace amounts of numerous chemical elements.
    It has become a useful analytic method in clinical chemistry, geology, and
    pollution analysis.  The methodology, theory, instrumental components, cells,
    light detection system, and interference are described.  These include
    spectral, chemical, and ionization, with regard to atomic absorption analysis.

    *Analytical techniques, Instrumentation, Methodology, Absorption, Water
    pollution sources

    *Atomic  absorption analysis
106E

DEVELOPMENT OF A SIMPLE AND INEXPENSIVE METHOD FOR THE DETERMINATION
OF ORGANICALLY BOUND CHLORINE ON ACTIVATED CARBON IN WATERWORKS
FILTERS (ENTWICKLUNG EINER EINFACHEN UND BILLIGEN METHODE ZUR
BESTIMMUNG VON ORGANISCH GEBUNDENEN CHLOR AUF AKTIVKOHLE VON
WASSERWERKSFILTERN),

Mainka, E., Coerdt, W., von Baeckmann, A., and Kuehn, W.

Gas-Wasser-Fach - Wasser/Abwasser, Vol. 115, No. 4, p 178-181, April, 1974.
2 tab, 2 fig, 9 ref.

A simple, inexpensive procedure for the determination of organochlorine
substances, including pesticides, adsorbed on activated carbon in water works
filters, is described.  The activated carbon samples, to be stored deep-frozen
in aluminum containers to prevent adsorption, are washed with twice distilled
water for the desorption of inorganic chlorides, after which the sample is
dried at 60 C for 48 hrs, and then milled for homogenizatlon.  The organic
chlorine is then released by hydropyrolysis at temperatures of up to 1,000 C
in water vapor-saturated oxygen stream.  The test solution is then combined
with twice distilled water, and thermostatized at 25 C for the determination
of organically bound chlorine by means of an ion-specific chloride electrode,
using a double-junction reference electrode as counter-electrode.  The
potential is changed by th-? addition of a standard solution with known chlorine
concentration.

*Activated carbon, *Adsorption, *Chlorine, Pesticides, Filters, Water works,
Aluminum, Hydropyrolysis, Analytical techniques

*0rganochlorine substances
                                          534

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 107E

 AERIAL  INFRARED THERMOGRAPHS  IN  THE  SERVICE  OF WATER PROTECTION:
 AN EXAMPLE:  THE  CASE OF  CHARENTE  (LA  THERMOGRAPHIE INFRAROUGE
 AEROPORTEE AU  SERVICE DE  LA PROTECTION DES EAUX:  UN EXEMPLE:
 LE CAS  DE LA CHARENTE),

 Dechambenoy, C.,  Pontler,  L.,  Sirou, F.,  Vouve, J., and
 Pouget, E.

 Techniques et  Sciences Municipales,  Vol.  69,
 No. 4,  p 175-185, April,  1974.   12 fig,  4 ref.

 The thermal pollution of  the  Charente  river  in France was  studied by  aerial
 infrared thermography, using  an  infrared  radiometer with a rotary mirror
 for scanning at 500  m altitude.  The temperatures recorded on magnetic  tape
 are displayed  either in the form of  temperature listing for automatic data
 processing, or in the form of coded  listing  for the study  of details.   The
 presence of thermal  anomalies in the waterflow can be indicative of flow
 anomalies, thermal pollution,  and  subsurface  obstacles.  The purified effluent
 from a  waste water treatment  plant was detected as a homogeneous cloud  with
 a temperature  slightly above  the mean  water  temperature of the  river.


 *Water  pollution  sources,  Thermal  pollution,  Thermal water, Temperature,
 Flow measurement, Effluents,  Automation,  Analytical techniques

 *Thermography, *Radiometers,  *Infrared radiometers, *Charente River,  France,
 Aerial  thermography
10 8E

THE GEOPHYSICAL BEHAVIOR OF THE ENVIRONMENTAL ISOTOPES AS A BASIS
FOR MODEL CALCULATIONS IN ISOTOPIC HYDROLOGY (DAS GEOPHYSIKALISCHE
VERHALTEN DER UMWELTISOTOPE ALS BASIS FUER MODELLRECHNUNGEN IN
DER ISOTOPENHYDROLOGIE),

Oeschger, H., and Gugelmann, A.

Oesterreichische Wasserwirtschaft, Vol. 26, No. 3/4, p 43-49, April, 1973.
11 fig, 6 ref.

The geophysical behavior of natural and anthropogenic radioactive isotopes in
the environment is discussed with respect to their use for hydrological
studies, especially for the dating of waters.  For practical purposes, input
concentrations of natural isotopes such as tritium, 14C, 32Si, 39Ar, 81Kr,
and 36C1 may be regarded as constant for the time before 1954, the year of
the first A-bomb test.  The isotope ratios 180/160, deuterium/H, and
tritium/H were found to exhibit seasonal variation which is to be considered
in isotope dating.  The 85Kr concentration in air and water has been linearly
increasing for the last two decades.  The A-bomb and H-bomb tests have
resulted in tritium and 14C concentrations now exceeding the natural levels
measured before the tests.  Natural radioactive isotopes are suited to the
determination of the age distribution of water in hydrological systems
either by the piston-flow model, excluding the mixing of waters of different
ages, or by the exponential model allowing for mixing of different water
bodies.

*Isotopes (radioactive),  *Environmental effects, *Radioactive dating,
Hydrology, Model studies, Hydrologic models, Flow models, Analytical techniques

Piston-flow model, Water dating (isotopic)
                                       535

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109E

THE DETERMINATION OF RESIDUAL CHLORINE IN WATERS  (LA
DETERMINAZIONE DEL CLORO RESIDUO NELLE ACQUE),

Bodrito, P.

Inquinamento, Vol. 16, No. 3, p 26-28, March, 1974.  2 fig, 1 tab, 11 ref.

A colorlmetric method for the determination of chlorine in water by means of
o-tolidine is described.  The total chlorine  content is measured by the
addition of one ml o-tolidine to 50 ml water.  The sum of chlorine,
hydrochloric acid, and chlorine dioxide is determined by the additional use
in the test solution of arsenite for the prevention of the color reaction
of the chloramines.  The interference by free chlorine and chloramines is
prevented by the addition of malonic acid.  The colorimetric method has a
sensitivity of 0.02-0.05 ppm.  The interference by iron is prevented by
preliminary precipitation by sodium pyrophosphate.  The nitrite content in the
test solution should be less than 2 ppm for no interference to occur.
(Takacs-FIRL)

*Chlorlne, *Colorimetry, Analytical techniques, Nitrites, Iron

Residual chlorine, Chloramines, Hydrochloric  acid
110E

DETERMINATION OF INORGANIC POLLUTANT CATIONS BY THIN-LAYER
CHROMATOGRAPHY (DETERMINAZIONE DI CATIONI INORGANICHI
INQUINANTI MEDIANTE CHROMATOGRAFIA SU STRATO SOTTILE) ,

Frache, R., Drago, M., and Cescon, P.

Inquinamento, Vol. 16, No. 3, p 23-25, March, 1974.  1 fig, 16 ref.

Thin-layer chromatographic method for the determination of inorganic cations
as water pollutants, such as bivalent mercury, zinc, cadmium, nickel, copper,
manganese, lead and barium ions, and trivalent iron and chromium ions is
described.  The samples to be analyzed are first concentrated on nitric acid-
treated 20-50 mesh Dowex 50WX8 ion exchange resin.  Silicagel, alumina, and
cellulose can be used as thin layer, while the best results were obtained by
means of microcrystalline cellulose layer of 400 micron thickness.  A
40:40:20:20 ratio of acetone, butanol, 0.4N hydrochloric acid and water is
used as eluent.

*Chromatography, *Inorganic compounds, Water pollution sources, Metals,
Analytical techniques, Sampling, Ion exchange, Cellulose

*Thin-layer chromatography, Inorganic cations
                                       536

-------
HIE

MERCURY DETERMINATION IN WATER AND WASTE WATER BY FLAMELESS
ATOMIC ABSORPTION (QUECKSILBER-BESTIMMUNG IN WASSER UND
ABWASSER MIT HILFE DER FLAMMENLOSEN ATOMABSORPTION),

Dujmovic, M., and Winkler, H. A.

Aus der Abteilung Anwendungstechnik der Beckman
Instruments, GmbH, Munich, Germany

Chemiker-Zeitung, Vol. 98, No. 5, p 233-235, May, 1974.  4 fig, 1 tab, 8 ref.

Flameless atomic absorption spectroscopy has been shown as a suitable method
for the determination of mercury in water.  Organic bound mercury must be
exposed to ultraviolet radiation before its determination.  The reliability
of the method was tested by application to different types of water.  An
analytical differentiation between inorganic and organic bound mercury was
shown.

*Mercury, *Spectroscopy, Analytical techniques, Waste water, Water pollution
sources, Ultraviolet radiation

*Flameless atomic absorption spectroscopy
112E

GEL- AND ULTRAMEMBRANE FILTRATION OF AQUATIC HUMUS:  A
COMPARISON OF THE TWO METHODS,

Gjessing, E. T.

Norwegian Institute for Water Research,
Blindern, Norway

Swiss Journal of Hydrology, Vol. 35, No. 2, p 286-294, 1973.

Analytical water chemistry methods are discussed.  Fractionation as an
approach for obtaining information about the complex composition of aquatic
humus is detailed.  For this purpose, gel filtration has been used over
the last decade.  More recently ultramembrane filtration as a technique of
fractionation has been found useful.  The two techniques are compared and
results of combined use of ultramembrane filtration and gel filtration are
reported.  The results show a poor correspondence regarding molecular size.
Due to an interaction between the gel used (Sephadex) and humus, the ultra-
membrane filtration technique proved to be preferable for desalting and for
molecular size fractionation of aquatic humus.

*Fractionation, *Filtration, Aquatic plants, Aquatic life, Humus, Desalting,
Analytical techniques, Water chemistry

*Ultramembrane filtration, *Gel filtration (Sephadex), Aquatic humus
                                        537

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113E

MEASURING ELECTRODE POTENTIALS IN ANAEROBIC DIGESTION
WITH STAINLESS STEEL ELECTRODES,

Blanc, F. C., and Molof, A. H.

Water and Sewage Works, Vol. 121, No. 5, p 64-66,  74, May, 1974.  5 fig.
13  ref.
The successful use of stainless steel as a replacement for such metals as
gold and platinum as an inert electrode under anaerobic conditions is
examined.  Experimental results show that stainless steel electrodes
exhibited the same electrode potential readings and behavior as the commonly
used, more expensive platinum electrodes in both acetate-fed methane
fermentation units and in the sewage sludge-fed anaerobic digestion unit.
This identical behavior of both metals was also observed during periods  in
which the electrode potentials varied considerably and during  the initial
electrode adjustment periods after  first immersion of the electrodes.

*Stainless steel, *Electrodes, Anaerobic conditions, Fermentation,
Anaerobic digestion

Electrode potential
114E

PERCOLATION TESTS IN STRATIFIED SOIL,

Manke, A.

Fayetteville, New York

Water and Sewage Works, p 42, 44, 46, April 30, 1974.  2 fig.


Percolation tests can easily produce varying results when the hole is filled
with water and allowed to soak in order to saturate the soil before determining
the final percolation data.  Where the soil is of the same consistency or
homogeneous for the entire depth of the 30-inch hole, this method of
saturating the soil does not encounter the difficulties which are inherent
where two or more defininte layers of widely differing soil are present.
Results obtained when three definite layers of soil were encountered in
digging a hole to a depth of 30 inches to perform a percolation test are
presented.  Another test was undertaken to determine if the percolation rate
of 116 minutes was due to saturation or to silt from the top layer getting
into the pores of the lower soil layer.  Results indicate that a different
approach should be used to obtain a percolation test in a reasonably well-
saturated area where the soil for the 30-inch hole has layers which are of an
entirely different nature.  These tests also show the importance of avoiding
silting action in the drainage trench, particularly when the trench is located
in a stratified soil of this type.

*Percolation, Percolating Water, Testing, Data collections, Soil types,
Saturation,  Silts
                                        538

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 115E

 MAGNETIC FLOWMETER THAT KEEPS  ITS NOSE  CLEAN,

 Neish, D.

 Taylor Instruments Companies  (Europe) Limited,
 Water Treatment and Pollution  Control Department

 Process Engineering, p 61, May, 1974.


 Taylor Instruments has designed a self-cleaning electrode with the following
 three basic different features:  the leading edge is a gentle slope while
 the trailing edge is steep; the actual  conductive part of the electrode
 is a small eye in the center of the leading edge; and, the remainder of
 the electrode is coated with a tough insulating material called Nucerite.
 This electrode is embodied in  a new range of magnetic flowmeters designed
 for use in sewage, sludge, and effluent treatment.  The electrodes are made
 of Carpenter 20 Cb3, a corrosive-resistant stainless steel.  The flowmeters,
 designated the Mag-Pipe 1210L  series, have additional junction boxes that
 plug into the side of the transmitter unit.  This enables the customer to
 install his field wiring in the junction boxes and then seal them to be
 watertight.  If flooding occurs, the transmitter is rendered temporarily
 inoperative without damaging the instrument.

 *Instrumentation, ^Electrodes, *Flowmeters, Construction materials,
 Sewage treatment

 Transmitter unit
116E

DETERMINATION OF ZINC AND CADMIUM IN ENVIRONMENTALLY
BASED SAMPLES BY THE RADIOFREQUENCY SPECTROMETRIC SOURCE,

Talmi, Y.

Oak Ridge National Laboratory,
Oak Ridge, Tennessee,
Analytical Chemistry Division

Analytical Chemistry, Vol. 46, No. 8, p 1005-1015, July, 1974.
1 fig, 5 tab, 16 ref.

The applicability of the radiofrequency furnace (RFF) spectrometric source
to the analysis of trace amounts of cadmium and zinc in environmental samples
is described.  Modifications in the original design of the system enhanced
sensitivity and reduced interferences.  Both atomic absorption (AA) and
atomic emission (AE) spectrometric modes have been sucessfully used with
samples pre-treated by various methods.  These included wet ashing, on-
substrate wet ashing and Soluene solubility, and direct analysis.  Samples
such as coal, fly ash, gasoline, bovine liver, bunker oil, soil, orchard
leaves, and fish gonad were analyzed.  The rate of analysis was five per
minute.  The average overall accuracy was 6.8 percent and reproducibility
was 5.5 percent.  With the AA mode, detection limits for Cd and Zn were
5 picograms and 6 and 8 picograms with the AE mode.  Relative sensitivi-
ties were in the 0.001-0.5 ppra range.  Interferences in the two modes
were also compared.

*Spectrometry, *Cadmium, *Zinc, Environmental effects, Analytical
techniques, Sampling, Pollutants

*Radiofrequency furnance, *Atomic absorption, *Atomic emission
                                          539

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 117E

 WATER POLLUTION  TELEMETRY  SYSTEM,

 Kitahara, S., Takeno, K.,  and Omura, A.
 Communication.   Equipment Works

 Mitsubishi Denki Giho, Vol. 48, No. 4, p 452-458, April, 1974.
 5 fig, 4 tab, 6  ref.

 Waste water produced by industries and urban expansion is on the increase
 and pollution of water of rivers and lakes around cities is being
 aggravated.  A water pollution telemetry system was built for the
 purpose of studying the water pollution.  The Ministry of Construction
 (of Japan) tries to standardize the specifications of water pollution
 telemeters and has given more stringent standards for the water quality.

 *Telementry, *Water quality standards, *Water quality control,
 *Water pollution, Measurement, Systems, Urbanization, Rivers, Lakes,
 Municipal water

 *Japan
118E

DDT RESIDUES IN SOIL, WATER, AND FAUNA FROM NEW YORK
APPLE ORCHARDS,

Kuhr, R. J., Davis, A. C., and Bourke, J. B.

New York State Agricultural Experiment Station,
Geneva, New York,
Department of Entmology

Pesticides Monitoring Journal, Vol. 7, No. 3/4, p 200-204, March, 1974.
2 tab, 15 ref.

Five commercial apple orchards which had not been sprayed extensively with
DDT for twelve years were surveyed in 1972 for residues of DDT and its
metabolitles.  In addition to the parent compound, DDE and ODD were
almost recovered, but no dicofol was detected in any soil sample.  Total
residues in  the top 6-inch soil layer underneath the trees ranged from
21.8 to 259  Ib/acre.  Between the rows of trees the levels were consider-
ably lower;  they ranged from 7.3 to 78.5 lb/6-inch acre.  In one heavily
contaminated orchard, researchers also analyzed stream water, stream-
bottom mud,  and animals.  Very low amounts of DDT (0.32 ppb) and ODD
(0.042 ppb)  were found in the water.  Residues in stream-bottom mud
totaled less than 1 ppm.  Worms, slugs, snails, tadpoles, fingerling
fish, and frogs all contained ODD, DDE, and DDT.

*Pesticides, *Soils, *Streams, *DDD, *DDE, *DDT, *Pesticide residues,
Aquatic life, Pollutants, Animals, Sampling
                                         540

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 119E

 THE PLATEAU B.O.D.—MEASUREMENT AND SIGNIFICANCE
 (DER PLATEAU-BSB-MESSUNG UND AUSSAGEKRAFT),

 Hartmenn, L.

 Unwelthygiene, Vol. 25, No. 5, p 99-102, 1974. 6 fig.

 The measurement and significance of the plateau BOD value in
 waste water are described.  The BOD curves are the result of
 a series of biologic al reactions.  As shown by experiments,
 only the very first reaction is caused by  the aerobic degra-
 dation dissolved organic matter.  Consequently, only this first
 reaction has significance for the biological treatment of sew-
 age.  This BOD, termed as plateau-BOD, is  established in 18
 to 24 hrs (or in much shorter time depending on the bacteria count
 and the temperature).  While this plateau-BOD considers the oxygen
 demand for the primary oxidation elimination of dissolved organic
 substances, the BODS additionally considers endogeneous respira-
 tion and other secondary reactions.  A new instrument, Pollumax,
 developed by Pollux, permits the automatic determination of the
 plateau-BOD value by converting the vacuum into electrical signals.
 These in turn can be used in control circuits by computer.  The
 automatic measurement of the plateau-BOD values indicates new
 automation of activated sludge waste water treatment plants.

 *Measurements, *Biochemical oxygen demand, *Biological treatment,
 Sewage treatment, Dissolved organics, Automation, Activated sludge,
 Waste waters, Analytical techniques

 *Plateau BOD values
120E

DETERMINATION OF CHROMIUM IN WATER AND WASTE WATER
(BESTIMMUNG DES CHROMS IN WASSER UND ABWASSER) ,

Wendel, H.

Gas-und Wasserfach-Wasser Abwasser, Vol. 115, No. 5, p 227-229,
1974.  6 refs.

Methods for the qualitative and quantitative determination of
chromium in waste water are described.  For qualitative deter-
mination, the evaporation residue is fused with sodium carbonate
and potassium nitrate or sodium peroxide.  The cold fused mass
is dissolved in the acetic acid.  Upon addition of silver nitrate,
reddish brown silver chromate is obtained.  Yellow lead chromate
is precipitated fay the addition of lead acetate.  If the cold
fused mass is treated wit sulfurous acid and hydrogen peroxide,
ether-soluble deep blue chromium peroxide is obtained.  For quanti-
tative determination, the fused mass obtained from the evaporation
residue is purified and treated with sulfuric acid and phosphoric
acid, after which the solution is titrated with 0.In-ferrous
sulfate solution after addition of diphenylamine solution until
color shift from violet to green occurs.  In another photometric
method reddish purple color is obtained by the reaction of chromate
ions with diphenylcarbazide in acid solution.

*Chromium, *Waste water,  *Analytical techniques, Pollutant
identification,  Analytical techniques

*Quantltative determination,  *Qualitative determination
                                             541

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121E

DETERMINATION OF THE CHEMICAL OXYGEN DEMAND BY MEANS 0?
VANADATE SULFURIC ACID (DIE BESTIMMUNG DBS CHEMISCHEN
SAURSTOFFBEDARFS MITTELS VANADATSCHWEFELSAEURE),

Rettmer, S., and Straten, G.

Wasser-und Abwasser-Forschung, Vol. 7, No. 2, p 57-62, 1974.
2 tab, 26 refs.

Disadvantages of COD determination by dichromate-sulfuiric acid,
and a new method of COD determination by means of vanadate-sul-
furic acid are described.  Oxidation of chlorides and disinte-
gration of dichromate are the basic disadvantages of the dich-
romate method.  These disadvantages are eliminated by the use of
vanadate-sulfuric acid.  For COD determination by this method,
mercury sulfate, silver sulfate and sulfuric acid are combined,
after which vanadate-sulfuric acid is added for boiling the
sample under addition of silver sulfate and sulfuric acid.  Then,
ammonium ferric sulfate solution and o-phenanthroline indicator
are added until color shifts from bluish green to reddish blue.
Comparative determinations of COD values of pure organic compounds
revealed oxidation rates of 93 percent, 87 percent, and 33 percent
for dichromate, vanadate, and permanganate methods, respectively.

*Chemical oxygen demand, *Sulfuric acid, *Water quality, Oxidation,
Analytical techniques

Vanadate sulfuric acid, Dichromate method, Permanganate method
122E

EXEMPLARY WATER LEVEL AND RUNOFF MEASURING DEVICES
IN MOUNTAIN WATER STREAMS (VORBILDLICHE WASSERSTANDS-
UND ABFLUSSMESSANLAGEN IN GEBIRGSWAESSERN),

Hinrich, H.

Die Bautechnik, Vol. 51, No. 4, p 131-133, April, 1974. 7 fig, 2 ref.

Two simple water-level and runoff gauges installed in the El
Rincon and Benetez rivers in the Conlara Valley in Argentina
are described and compared with a sophisticated water-level
gauge in the Massa river in Switzerland.  In the mountain creeks
in Argentina, the gauging section is concreted in the bed with
a transversal slope of 1 : 20.  Water-level and runoff measre-
ment are done by simple hydrometric vanes fastened to support on
the banks.  The highly sophisticated and expensive gauging sta-
tion on the Massa river in Switzerland, composed of artificial
weir, stilling basin and measuring canal, is suitable also for the
measurement of glacier water on the basis of preliminary model
experiments.  The simple gauging stations in Argentina are especi-
ally suitable for measurement  of the dry-weather runoff.

*Runoff, *Measurement, Streams, Rivers, Gauges, Weirs, Basins,
Canals

Argentina, Switzerland, Water  level gauge
                                            542

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123E

THE USE OF CHELATING ION EXCHANGE IN CONJUNCTION WITH
RADIOISOTOPE X-RAY SPECTOMETRY FOR DETERMINATION OF TRACE
AMOUNTS OF METALS IN WATER,

Holynska, B.

Radiochemistry and Radloanalytical Letters, Vol. 17, No. 5/6.
p 313-324, June 20, 1974.  6 fig., 1 tab, 11 ref.

The chelatlng Ion-exchange resin Chelex-100 was applied for
collection of trace amounts of several metal ions from aqueous
solutions.  The kinetics of the exchange reaction has been
measured, as well as the influence of pH of the solution and
calcium or sodium ions concentrations on the metal collection.
The radioisotope X-ray fluorescence method has been applied
for determination of metal ions sorbed on the resin.

*Chelation, *Ion exchange, *Trace metals, *Spectrometry, Analytical
techniques, Kinetics, Radiolsotopes, Fluorescence, Calcium,  Sodium

Resin
124E

MONITORING 2,4-D RESIDUES AT LOXAHATCHEE NATIONAL WILDLIFE
REFUGE,

Schultz, D. P., and Whitney, E. W.

Southeastern Fish Control Laboratory, Fish and Wildlife
Service, Bureau of Sport Fisheries and Wildlife, U.S.
Department of the Interior, Warm Springs, Georgia

Pesticides Monitoring Journal, Vol. 7, No. 3/4, p 146-152, March, 1974, 4 tab,
11 ref.

In the Loxahatchee National Wildlife Refuge in Florida, more than 7,000 acres along
the Hillsboro perimeter canal were sprayed with 2,4-D(DTA-2,4-D) at a rate of 4.48
kg acid equivalent per hectare to control waterhyacinth (Eichornia crassipes) in
1971.  Samples of fish, water and mud were collected at the three stations along
the canal for water quality monitoring and residue analysis.  The first application
of 2,4-D, supported by spot treatments of DTA-2.4-D and/or the dimethylamine salt
of 2,4-D (DMA-2,4-D) controlled waterhyacinth very well.  The day after the initial
treatment saw the highest residue level of 2,4-D in water (0.037 mg/1).  Three to
15 days after treatment saw the highest occurrence of hydrosol (0.005 mg/kg).  In
60 samples of fish, 3 showed herbicide residue exceeding 0.010 mg/kg, 16 showed
less than 0.010 mg/kg,  and the remaining samples appeared to be free of any notice-
able residue.  Residue levels of 0.30 mg/kg and 0.675 were detected in Florida gall-
inules a day after spraying.  No bad effects were found to occur in the hatching
of boat-tailed grackle eggs or fledgling development from herbicide use.


*Herbicides,  Pesticide residue, Waterhyacinth, Fish, Sampling, Monitoring, Water
quality control

*2,4-D, DTA-2,4-D,  2,4-D(DMA-2,4-D), Florida gallinules, Boat-tailed grackle
                                             543

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125E

LIQUID SCINTILLATION COUNTING FOR PLUTONIUM IN ENVIRONMENTAL
SAMPLES,

D. L. Bokowski

Products and Health Physics Research, Dow Chemical U.S.A.,
Rocky Flats Division, Golden, Colorado.

American Industrial Hygiene Association Journal, Vol. 35, No. 6, p 333-344, June,
1974.  9 tab, 21 ref.

A liquid scintillation counting technique which is applicable to the conventional
analysis of plutonium in environmental and biological samples is discussed.  A
presentation is made of methods for improving the specificity and sensitivity for
plutonium.  This method was compared to the anlon exchange chromatography-alpha
plus height spectrometry technique, and made valid by means of a t-test.  Procedures
for sample preparation are given for air filters, water and soil.  Expediency in
preparation is shown.  Overall mean recovery of plutonium from the different types
of samples was greater than 95 percent.  Detectable activity at the minimum for
100-minute counts is 0.18 pCi.

*Environmental control, Chromatography, Soil

*Plutonium, Liquid scintillation, Environmental samples
 126E

 THE WORK AND  FACILITIES OF THE BRIXHAM LABORATORY OF IMPERIAL
 CHEMICAL INDUSTRIES LIMITED,
Water Pollution Control, Vol. 73, No. 3, p 336-340, 1974.  4 fig.

The Brixham Laboratory of the Imperial Chemical Industries has facilities and
services available both to ICI and for outside industry.  These enable work to be
done on any operation normally encountered in effluent and pollution control.
Analytical services use modern instrumental methods such as radioactive tracer
techniques, gas-liquid chromatographs, and a special technique for analysis of
total carbon.  Areas of treatment include chemical and physical treatment, pilot
investigations of biological treatment and ancillary processes, tertiary treat-
ment, and work site surveys.  Disposal research includes field surveys, biological
surveys of fauna and flora samples, bacteriological surveys, and bioassays.


laboratory tests, Industrial wastes, *Effluents, *Analytical techniques,
*Biological treatment, *Pllot studies, *Chemical treatment, Surveys, Sampling,
Investigations, Research

*Brixham Laboratory, Imperial Chemical Industries
                                         544

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127E

PHOSPHORUS AND NITRATE LEVELS IN GROUNDWATER AS RELATED
TO IRRIGATION OF JACK PINE WITH SEWAGE EFFLUENT,

Orie, D. H.

United States Department of Agriculture, Forest Service,
North Central Forest Experiment Station

In:  Conference on Recycling Treated Municipal Wastewater Through Forest and
Cropland, August 21-24, 1972, The Pennsylvania State University, University
Park, p 157-164.  2 tab, 5 ref.

The North Central Forest Experiment Station has begun research on the effects
of sewage effluent on groundwater nutrient levels.  Results from an initial
test conducted near Cadillac, Michigan are discussed.  This exploratory test
was conducted to gain background information on the methods useful in conduct-
ing field tests of sewage effluent renovation where only small volumes of
effluent are available.  The single plot test illustrates that the nitrates
added in sewage effluent irrigation may reach shallow water tables under sand-
soil, forest conditions.  Phosphorus renovation was complete during the initial
year.  Public health considerations may limit the permissible dosage levels in
such highly permeable soils.  Experience with this single plot test has re-
sulted in the adoption of a different type of field test in locations where sew-
age effluent must be trucked to the test site.  Tests now in progress utilize
plots about 0.001 hectare in area using gravity methods of application.  Tension
lysimeters are being used instead of wells to test the degree of renovation
under various treatments.

*Nutrients, *Groundwater, *Phosphorus, *Nitrates, Testing, Sewage effluents,
On-site tests, Irrigation, Public health, Water table, Soil types, Waste
water treatment, Lysimeters
128E

BIOTOXIC ELEMENTS IN SOILS,

Hinesly, T. D., and Jones, R. L.

Illinois University, Department of Agronomy

In:  Conference on Recycling Treated Municipal Wastewater Through Forest and
Cropland, August 21-24, 1972, The Pennsylvania State University, University
Park, p 215-216.

Application of stabilized municipal waste treatment plant residues on agricul-
tural lands is the most economically viable solution to a growing solids dis-
posal problem.  Yet, it is a small problem from the standpoint of its utiliza-
tion by agriculture.  Only enough sludge solids would be available to treat
slightly more  than 0.2 percent of the 465 million acres of cropland or slightly
less than 0.06 percent of the total 1904 million acres contained in the United
States.  It is recognized that the solids from many small waste water treatment
plants will probably continue to be recycled to cropland.  Thus it is necessary
to attempt to  identify those chemical elements which tend to be ubiquitously
present in relatively high concentration in municipal waste waters and sludges
and might accumulate in soils in forms available to crop plants at concentra-
tions which may be injurious to plants or to animals consuming the produce.

*Sewage effluents, *Municipal wastes, Waste treatment, Tertiary treatment,
Chemical properties, Water pollution control, Environmental control
                                            545

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 129E

 DETECTION  OF DILUTE ORGANIC ACIDS  IN WATER BY
 INELASTIC  TUNNELING SPECTROSCOPY,

 Skarlatos, Y., Barker, R. C., Haller, G. L., and
 Yelon, A.

 Yale University, New Haven, Connecticut,
 Department of Engineering and Applied Science

 Surface  Science, Vol. 43, No. 2, p 353-368, June, 1974.  9 fig, 2 tab,
 14 ref.

 Oxidized aluminum films were exposed to acetic, formic, and cynoacetic acid
 and covered with a lead film.  These form junctions which carry electrical
 current by electron tunneling.  The technique of inelastic electron tunnel-
 ing spectroscopy, which reveals the characteristic vibration spectra of the
 molecules adsorbed on the oxide surface, was used to detect the presence of
 the organic molecules in the parts per million range.  The intensity of the
 spectral lines, which is dependent upon the competition between water and
 the organic molecules for the adsorption sites on the alumina surface, appears
 to saturate in the 10 to 1000 ppm range.  From the spectra obtained, one can
 distinguish between different molecules with similar structure and between
 different surface bonding configurations.  The method should be applicable
 to the detection of low concentrations of other, similar organic molecules
 that adsorb readily on the alumina surface.

 *Water chemistry, *Analytical techniques, *Spectroscopy, *0rganic acids,
 Application techniques

 *Inelastic electron tunneling spectroscopy
130E

 AN ADAPTED DETERMINATION OF PHOSPHATE IN SEAWATER
FOR USE WITH THE HYBRID AUTOMATIC ANALYSER,

Pugh, K. B., and Gibbs, C. F.

University College of North Wales, Menai Bridge,
Anglesey, United Kingdom, Marine Science Laboratories

Chemosphere, Vol. 13, No. 3, p 103-105, June, 1974.  1 fig, 3 ref.

Inorganic phosphate dissolved in seawater and beach groundwater has been
determined using the method of Chan and Riley on a hybrid automatic three
channel analyzer.  The reagents used were as described by Chan and Riley
with a number of minor modifications found to improve the effectiveness
of this manifold.  Statistical results are included.

*Phosphates, *Analytical techniques, Water analysis, Instrumentation,
Performance, Data collections, Temperature, Mixing, Automatic control
                                        546

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131E

A HYBRID AUTOMATIC ANALYSER,

Pugh, K. B., and Chubb, L. W.

University College of North Wales,  Menai Bridge,
Anglesey, United Kingdom, Marine Science Laboratories

Chemosphere, Vol. 13, No. 3, p 97-101, June, 1974.  1 fig, 5 ref.

The construction materials and procedures of a three channel analyzer
for ammonium-,nitrate-, and nitrate-nitrogen determinations are pre-
sented.  The system, detailed here, comprising a sampler, proportioning
pump, glassware, heating bath, colorimeters, and recorders has been in
satisfactory use for over two years.  The system is fully adaptable so
that manifolds for the determination of other chemical species are
easily constructed.

*Analytical techniques, *Instrumentation, Ammonia, Nitrates, Nitrites,
Nitrogen, Water analysis, Sea water, Equipment
 132E

MERCURY DETERMINATION IN WATER AND WASTE WATER WITH THE AID
OF FLAMELESS ATOM ABSORPTION (QUECKSILBER BESTIMMUNG IN WASSER
UND ABWASSER MIT HILFE DER FLAMMENLOSEN ATOMABSORPTION),

Mira, D., and Winkler, H. A.

Chemiker-Zeitung, Vol. 98, No. 5, p 233-235, 1974.  4 fig, 1 tab, 8 ref.

A quantitative method for the determination of total and inorganic mercury
in water by flamless atomic absorption is described.  For the determina-
tion of inorganically bound mercury, the water sample is combined with po-
tassium permanganate solution, nitric acid, sulfuric acid, and hydroxylam-
monium chloride, after which tin chloride solution in sulfuric acid is added
for the spectrometric determination.  For the determination of the total
mercury content, the sample is exposed to UV irradiation for 2 hrs for the
digestion of organically bound mercury.  The organic mercury content is
determined from the difference of the total mercury and inorganic mercury
levels.  Actual measurements of the mercury levels in surface waters in
Switzerland and West Germany revealed total mercury levels one order of
magnitude below the maximum allowable concentration of 1 microgram/liter,
and organomercurlal contents amounting to 80 percent of the total mercury.

*Mercury, *Atomic absorption, Sampling, Measurement, Surface waters

Germany, Flameless atomic absorption
                                           547

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 133E

 POSSIBILITIES OF WATER DATING BY MEANS OF INERT GAS
 ISOTOPES (AUBSLICK AUS DIE WASSERDATIERUNG MIT HILFE
 VON EDELGASISOTOPEN),

 Oeschger,  H., and Gugelmann,  A.

 Oesterreichische Wasserwirtschaft,  Vol.  26, No. 3/4, p 54-56,  April,  1974.
 2 fig,  2 tab, 7 ref.

 Possibilities of water dating in hydrology, oceanology and  glaciology by
 means of inert gas isotopes,  and actual dating performed by this  method are
 described.   The inert  gas isotopes  suitable for dating water of different
 ages are 37Ar, 39Ar,  81Kr, and 85Kr with the respective half-life periods
 of 35 days;  269 yrs;  210,000  yrs, and  10.6 yrs.  For water  dating,  the water
 sample is  first heated to 85-100 C  under atmospheric pressure  for the sepa-
 ration of  the gases.   Krypton and argon are then separated  from oxygen and
 nitrogen by  oxidation of the  latter over hot copper followed by fractionated
 distillation.  Argon  and krypton are then separated from each  other by a
 chromatographic method.   The  radioactivity is measured by means of proportional
 counter.  Water dating by means  of  such inert gas isotopes  is  suitable for
 the determination of  the age  and age distribution of water,  of the motion and
 turbulence of water masses in oceans,  and of the age of different layers of
 glaciers.

 *Argon, *Krypton radiosotopes, Hydrology, Turbulence, Oceans,
 Water sampling, Glaciers

 *Water dating, Gas isotopes
134E

MEASUREMENT OF THE ALLUVIAL DEPOSIT TRANSPORT BY MEANS OF
RADIOACTIVE TRACERS (MESSUNG DBS FLUSSEDIMENTRANSPORTES MIT
HILFE RADIOACTIVER MARKIERUNG),

Erdelysky, Z.

Oesterreichische Wasserwirtschaft, Vol. 26, No. 3/4. p 89-92,
March-April, 1974.  6 fig.

The propagation of alluvial deposit of different particle sizes in
Danube river was studied by radioactive tracers.  Four different radio-
active isotopes with characteristic gamma-components and intensities
(Zn-65, Zr-95, Hf-181 and Sb-124) were embedded in pebbles of different
sizes and sealed by araldit resin.  The pebbles were laid in the river
and their propagation was followed up by systematic scanning of the
riverbed by means of scintillation detectors.  The pebbles were found
to be carried away by the water stream in a narrow strip of 2.5 m in
width, maintained even after a path of 1,600-2,000 m.  At a flow rate
of 0.75 m/sec measured near the riverbed, a 3 mm-particle had a velocity
of 0.21 m/sec.

*Alluvial deposit, *Radioactive tracers, Radioisotopes,
Analytical techniques, Flow rates

Transport
                                             543

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135E

THE INFLUENCE OF SURFACTANTS ON FLOW AT WIND-BLOWN
WATER SURFACES,

Mansfield, W. W.

CSIRO Division of Applied Chemistry,
Melbourne, Australia

Chemical Engineering Science, Vol. 29, No. 7, p 1592-1600,
1974.  4 fig, 24 ref.

The effect of an air-stream on a closed channel of water has been examined
by chemical engineers in modelling two-phase flows containing both mass
transfer and surface effects.  When air blows over a closed channel of
water, a steady surface velocity develops, as part of a flow extending to
the channel bed.  Different flows are produced, depending on the concen-
trated solution of surfactants.  The surface velocity increases with the
downwind distance and the flow is confined to a boundary layer adjacent
to the surface.  This boundary layer flow is a new type, and is related
to that generated by a solid surface moving through a quiescent fluid.  The
characteristics of this flow are determined experimentally and
theoretically,

*Surfactants, *Mathematical equations, Channels, Channel beds, Flow rates,
Liquids, Experimentation
136E

WATER CHARACTERISTICS,

Ghosh, M. M., and Brown, W. P.

Maine University, Orono, Maine

Journal of the Water Pollution Control Federation, Vol. 46, No. 6,
p 1050-1058, June, 1974.  72 ref.

Considerable attention was focused in 1973 on the development and refine-
ment of analytical techniques for determination of various water character-
istics .  Monitoring and measurement methods and equipment for analysis of
parameters such as temperature, suspended solids, hydrogen ion concentra-
tion, electrolytic resistivity, polybasic acids activity coefficients, and
turbidity, are reviewed.

*Analytical techniques, *Reviews, Monitoring, Measurement, Methodology,
Equipment, Laboratory tests

*Water characteristics
                                           549

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13 7E

TESTING OF METHODS FOR DETERMINATION OF URBAN RUNOFF,

Chien, J.-S.

Dalton-Dalton-Littie-Newport, Incorporated,
Cleveland, Ohio

Journal of the Hydraulics Division, Vol. 100, No. HY 7, p 1081-1082,
July, 1974.  2 ref.

A state-of-the-art in urban hydrology is challenged with regards to the
estimation of infiltration parameters and sewer routing procedures.  Chien
maintains that the following factors be considered in addition to the
efforts endorsed by the authors:  the adoption of individual hyetographs
for each event with its associated catchment as input instead of using the
average Thiessen hyetograph; field verification of Manning's n in the
sensitivity study; consideration of possible backwater conditions from
the downstream interceptor under high flow situation; groundwater infiltra-
tion and other inflows as part of the flow monitored.

*Urban hydrology, Estimating equations, Infiltration, Distribution patterns,
Hyetographs, Mannings equation, On-site investigations, Flow rates,
Monitoring, Groundwater, Backwater, Reviews


Sewer routing
 138E

 SYSTEM ANALYSIS,

 Loucks. D.  P.

 Cornell University,  Ithaca,  New York

 Journal of  the  Water Pollution Control  Federation,  Vol.  46,  No.  6,
 p 1604-1611, June,  1974.   59 ref.

 The literature  dealing with  the development  and  application  of  systems
 analysis techniques  for assistance  in the  evaluation  of  alternative water
 pollution policies  in 1973 can be divided  into the  following categories:
 general reviews;  regional  water quality management  studies;  economic
 incentives;  data  requirements and problems;  water reuse  analysis;  the
 design and  operation of waste water treatment plants,  instream  artificial
 aeration devices, and flow augmentation systems; and  the analysis  of speci-
 fic pollution problems attributed to acid  mine drainage, DDT, nitrogen
 and thermal waste water.

 *Systems Analysis,  *Water  quality management, *Water,  Aeration,  Water
 pollution,  Mine drainage,  DDT,  Nitrogen, Thermal waste water, Waste water
 treatment

 Instream artificial  aeration devices
                                            550

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139E

HEAVY METALS AND OTHER TRACE ELEMENTS,

Leland, H. V., Copenhaver, E. D., and Corrlll, L. S.

University of Illinois, Urbana-Champalgn, Illinois

Journal of the Water Pollution Control Federation, Vol. 46, No. 6,
p 1452-1576, June, 1974.  257 ref.

Trace elements like heavy metals are natural constituents of aquatic
environments.  If more of the elements are added to water through the
activities of humans and result in changed chemical composition of the
environment, the natural cycling processes are upset.  Mine wastes
contribute to such an imbalance, along with many waste water treat-
ment plants and heavy metal particles from smelters and other industrial
processes.  Some elements present at trace concentrations have been
determined dangerous and extremely toxic at unnatural exposure con-
centrations.  A possible relationship has been shown between concentra-
tion of some waterborne trace elements and dental caries.  Chronic
poisoning due to As was reported in Argentina.  Cd intoxication has
been determined to result in kidney failure.  Methylmercury poisoning
was reported in epidemic proportions in Iraq in 1972.  Analyses of speci-
fic parameters for determining the condition of health of aquatic organ-
isms has been recommended.  Hematological alterations are multiplied
when there is the introduction of sublethal concentrations of toxic metals
in aquatic environments.

*Aquatic environments, *Public health, *Water pollution, *Heavy metals,
Trace elements, Hematology
140E

VARIABLES TO BE MEASURED IN WASTEWATER TREATMENT PLANT
MONITORING CONTROL,

Roesler, F., and Wise, R. H.

The Environmental Protection Agency, Cincinnati, Ohio

Journal of the Water Pollution Control Federation, Vol. 46, No. 7,
p 1769-1775, July, 1974.  23 ref.

Process control can be interpreted as the adjustment of key process
variables on a continual or intermittent basis of maximum performance
while minimizing cost.  The control of the key variables affects
quality, while control of the other variables only reduces cost.
Automatic backwashing of rapid sand filters responding to head loss
through the filter is an example of control with an indirect affect
on effluent quality and cost.  The key variables in biological
waste treatment processes are classified into four categories: sub-
strate variables, physical and chemical variables, suspended solids
variables, and biological activity variables.  These groups are dis-
cussed in terms of their limitations and relationships to each other,
plant performance and process control strategies.

*Waste water treatment, *Effluent control, *Biological waste treatment,
Automation, Suspended solids

^Process control, Automatic backwashing, Rapid sand filters, Substrate
                                         551

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141E

DETERMINATION OF AMMONIA LEVELS IN WATER AND
WASTEWATER WITH AN AMMONIA PROBE,

Evans, W. H. and Partridge, B. F.

Laboratory of the Government Chemist,
Cornwall House, Stamford Street, London,
Department of Trade and Industry

The Analyst, Vol. 99, No. 1179, p 367-375, June, 1974.  7 ref.

An ammonia probe application was investigated for discrete measurement
of ammonia levels in a laboratory containing a variety of waters.   A
response was exhibited for the range of 0.2 to 40 mg/liter of am-
moniacal nitrogen In a stirred sodium hydroxide solution (0.1)  con-
taining 0.01 M ethyl enediaminetetraacetic acid.  A precision of 4 per-
cent was determined by recoveries of added ammonia and repeated cali-
brations of the study, for ammoniacal nitrogen concentrations above
0.4 mg/liter and 0.015 mg/liter for concentrations less than 0.4 mg/
liter.  The statistical limit of detection 0.03 mg/liter.  Agreement is
reached with existing methods based on distillation and spectrophoto-
metric measurement for more sample ranges, but the detection limit and
precision at low levels indicate that accuracy in potable waters would
be difficult.  Albuminoid nitrogen can be determined by this probe by
taking the difference between the ammoniacal nitrogen and total free
and albuminoid nitrogen obtained by distillation.  Values arrived  at
in this manner agree with those gathered by existing methods, subject
to the acceptability of the probe.

*Ammonia, *Waste water treatment, *Water pollution, Distillation,
Spectrophotometry

*Ammoniacal nitrogen, Albuminoid nitrogen
 142E

 ARSENIC IN WATER BY FLAMELESS ATOMIC ABSORPTION
 SPECTROPHOTOMETRY,

 Tarn, K. C.

 Freshwater Institute, Winnipeg, Manitoba, Canada

 Environmental Science and Technology, Vol. 8, No. 8, p 734-736,
 August, 1974.  1 fig, 2 tab, 16 ref.

 Chronic poisoning has been reported to be caused by the utilization of
 drinking water containing 0.21 to 10.0 mg/liter of arsenic.  The United
 States Public Health Service and the Canadian Joint Committee on Drink-
 ing Water Standards have both recommended an acceptable concentration of
 0.01 mg/liter and a maximum permissible limit of 0.05 mg/liter.  Arsenic
 in water was extracted with diethylammonium diethyldithiocarbamate in car-
 bon tetrachloride and determined by atomic absorption Spectrophotometry
 using the carbon rod atomizer.  The method determines arsenate, arsenite,
 and any organoarsenic compounds soluble in carbon tetrachloride.  By using
 ultraviolet photooxidation to decompose organoarsenic compounds, the method
 determines total arsenic.

 *Potable water, *Poisons, *Arsenic, Atomic absorption, Spectrophotometry,
 Analytical techniques, Public health

 Photooxidation, United States Public Health Service, Canadian Joint Com-
 mittee on Drinking Water Standards
                                           552

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USE

ASBESTIFORM AMPHIBOLE MINERALS: DETECTION AND MEASURE-
MENT OF HIGH CONCENTRATIONS IN MUNICIPAL WATER SUPPLIES,

Cook, P. M., Glass, G. E., and Tucker, J. H.

National Water Quality Laboratory,
Environmental Protection Agency,
Duluth, Minnestoa

Science, Vol. 185, No. 5154, p 853-855, September 6, 1974.  2 fig, 18 ref.

Asbestiform amphibole minerals, which have been demonstrated to be
associated with human health problems, were detected in substantial
quantities in municipal water supplies taken from western Lake Superior
water.  The total concentration of amphibole minerals in the Duluth,
Minnesota, water supply, was measured by x-ray diffraction of daily samples
of suspended solids.  They averaged 0.19 milligram per liter with large
fluctuations due to seasonal and climatological effects on lake circula-
tion.  Electron microscopic examination of these water samples confirmed
the presence of asbestiform amphibole fibers.  A conservative estimate of
the fiber count for 1973 Duluth water supply samples is one to thirty mil-
lion amphibole fibers identifiable by electron diffraction per liter of
water, with a mass concentration of one to thirty micrograms per liter.

*Pollutants, *Water supplies, *Municipal water, Lake Superior,
Measurements, Fibers, Detection, Sampling

*Asbestlform amphibole minerals, Duluth, Minnesota
 144E

 AUTOMATIC  DOSAGE  OF SULFATES  BY  AN  IMPROVED NEPHLO-
 METRIC  METHOD  (DOSAGE  AUTOMATIQUE DBS  SULFATES  PAR UNE
 METHODE NEPHELOMETRIQUE  AMELIOREE),

 Verduyn, G., and  Derouane,  A.

 Institute  of Hygiene and Epidemiology,
 Brussels,  Belgium

 Atmospheric Envrionment, Vol.  8, No.  7,  p  707-715, July,  1974.
 6 fig,  1 tab,  15  ref.

 An automatic nephelomatric  method  for  the  determination of  low  con-
 centrations of sulfate is described.   It permits  the  determination
 of concentrations as low as 0.1  microgram  per cu  cm.   Sulfate ions
 are precipitated  by means of  barium perchlorate and  fifty samples  can
 be analyzed in an hour.   This method  is  applicable to the determina-
 tion  of sulfate amounts  in  rain  water.   The  equipment used  is called
 a Technicon Auto  Analyser,  connected with  a  two monochromators  spectro-
 fluorimeter.

 *Automation, Sulfate,  Measurement,  Analytical techniques, Equipment,  Rain water

 *Nephelometric methods,  Dosages, Technicon Auto Analyser
                                       553

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145E

DETERMINATION OF N.N-DIALKYL DITHIOCAKBAMATES IN WASTE-
WATER BY THIN-LAYER DENSITOMETRY,

Onuska, F. I.

Canada Centre for Inland Waters,
Burlington, Ontario, Canada

Analytical Letters, Vol. 7, No. 5, p 327-334, 1974.  1 fig,
2 tab, 20 ref.

The increasing awareness and importance of very small amounts of various
herbicides in waste water has greatly stimulated refinement and extension
of analysis pertaining to water media.  The quantitative determination of
N,N-dialkyl dithiocarbamates tetramethylthiuram disulfide and tetramethyl-
thiuram monosulfide in waste water was studied by thin-layer densitometry
of their copper complexes.  A densitometer provides a simple and rapid means
to quantify these compounds.  N,N-dialkyl dithiocarbamates were analyzed
in microgram quantities using this method.

*Herbicides, *Waste water, Analytical techniques, Copper

N,N-dialkyl dithiocarbamates, Densitometry
146E

SPHERE METHOD TURBIDIMETER,

Sato, K.

Chemical Economy and Engineering Review, Vol. 6, No. 5, p 26-30, May, 1974.  7 fig.

The presence of suspended matter in pre-treated effluents poses some problems
such as an increase in fluid resistance and fluid film thickness.  To remove
solids attached to the membrane, it is important to measure and control the
suspended matter in a given sample.  A new instrument, the Poic Sphere-Method
Turbidimeter, is useful in analysis of fine amounts of impurities.  It operates
on the principle of measuring both dispersive and parallel transmissions and
comparing the two readings:  turbidity = Td/Tp x 100 percent.  Experiments in
Japan used the Turbidimeter to control the quality of seawater and to analyze
regional differences in the suspended solids of different seawater.  A positive
relationship was found to exist between turbidity and solid suspension.  Ap-
plications of this instrument include pollution control by measuring suspended
solids, oil concentration, and activated sludge after pre-treatment; atmos-
pheric research by measuring particulate concentrations; and, a variety of
applications in petrochemical and petroleum industries, pharmaceutical indus-
tries, and high polymer industries.

*Turbidity, *Suspended matter, Instrumentation, Effluents, Pre-treatment,
Measurement, Activated sludge, Polymers

*Turbidimeter
                                  554

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147E

INSTRUMENTATION IMPROVES WATER TREATMENT PLANT OPERATION,

Water and Sewage Works, Vol. 121, No. 6, p 96-99, June, 1974.  1 fig, 4 tab.

Water analysis at the Loveland, Colorado water plant used jar tests in
conjunction with a laboratory turbidimeter and a very sensitive spectro-
photometer to indicate optium operation and lowest overall costs.  Clari-
fication equipment, load conditions, and key water quality tests, such as
turbidity, color, and pH, were studied most.  The data were then examined
for cause and effect relationships which suggested optium feed rates or
equipment changes.

*Instrumentation, *Water analysis, Optimization, ^Operations, *Costs,
Performance, Testing, Turbidity, Color, Hydrogen ion concentration,
Spectrophotometry

Jar tests
USE

HANDBOOK FOR ANALYTICAL QUALITY CONTROL IN WATER AND
WASTEWATER LABORATORIES,

National Technical Information Service Report PB-213 884, June, 1972.
107 p, 17 fig, 15 tab,

This handbook is designed to aid laboratory directors, leaders of field
investigations, and other personnel who bear the responsibility for water
and waste water data.  Information is offered such that the reader is able
to start, or reinforce, a program of analytical quality control which em-
phasizes recognition, prevention, and correction of problems which might
distort the data.  Topics covered include the importance of quality control,
laboratory services, instrumental quality control, glassware, reagents, sol-
vents and gases, control of analytical performance, data handling and report-
ing, special requirements for trace organic analysis, and skills and training.

*Quality control, laboratory equipment, Laboratories, Laboratory tests,
Research and development, Analytical techniques, Water analysis, Scientific
personnel, Data collections, Data processing

*Handbook
                                    555

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149E

AN IMPROVED CHEMICAL DELIVERY APPARATUS FOR USE IN
INTERMITTENT-FLOW BIOASSAYS,

Chandler, J. H., Sanders, H. 0. and Walsh, D. F.

United States Bureau of Sport Fisheries and Wildlife,
Warm Springs, Georgia, Southeastern Fish Control Laboratory

Bulletin of Environmental Contamination and Toxicology, Vol. 12, No. 1,
p 123-128, July, 1974.  1 fig, 4 ref.

Flow-through systems for measuring toxicological and physiological effects
of pesticides in aquatic organisms are an improvement over the static
systems.  A chemical delivery apparatus is described that is an improvement
over many of the intermittent-flow toxicant systems previously devised.
The apparatus does not require the use of a Mariotte bottle and is designed
to replace the metering devices on existing intermittent flow systems
without altering their basic function.  It has no moving parts, consists
of materials commonly found in well-equipped laboratories, and delivery
of different volumes of toxicant is easily produced by changing the
volume of the apparatus.

*Bioassay, *Laboratory equipment, *Pesticide toxicity, Pesticides,
Equipment, Toxicity, Aquatic life, Analytical techniques, Water pollution
sources

*Intermittent-flow bioassays, New equipment
150E

IMPROVED LIQUID SCINTILLATION TECHNIQUE FOR ENVIRONMENTAL
MONITORING OF IRON-55,

Moghissi, A. A., Whittaker, E. L., MacNelis, D. N. and
Lieberman, R.

National Environmental Research Center, Las Vegas,
Nevada

Analytical Chemistry, Vol. 46, No. 9, p 1355-1356, August, 1974.  2 tab,
1 ref.

Iron-55 is an important radionuclide, produced by nuclear weapons and
reactors.  Some methods for low-level counting of iron-55 are proportional
counting, X-ray spectrum counting, and liquid scintillation counting.  The
preferred method of liquid scintillation is simpler in sample preparation
and automatic operation.  The separated sample iron was electrodeposited
on a copper disk where experimenters used proportional counting.  On a
2-inch disk as much as 80 mg of iron can be electrodeposited for propor-
tional counting without exceeding the half-value layer for the 5.9 KeV
X-ray of iron-55.  The amount of sample or sample plus carrier iron that can
be fitted in a 25-ml counting vial, without significant loss in efficiency,
is limited to 20-30 mg (20 mg, E=0.161; 30 mg, E=0.108, 40 mg, E=0.067;
50 mg, E=0.032).

*Nuclear wastes, *Iron, *Environmental control, Chemical pollution, X-Ray
spectroscopy, Radioisotopes, Nuclear reactors, Nuclear fallout

*Liquid scintillation, *Counting methods, Proportional counting,
Solubilization


                                             556

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151E

THE MORPHOEDAPHIC INDEX, A FISH YIELD ESTIMATOR-
REVIEW AND EVALUATION,

Ryder, R. A., Kerr, S. R., Loftus, K. H., and
Regier, H. A.

Ministry of Natural Resources,
Fish and Wildlife Research Branch,
Thunder Bay, Ontario, Canada

Journal of the Fisheries Research Board of Canada, Vol. 31, No. 5,
p 663-688, May, 1974.  6 fig, 107 ref.

This paper reviewed and evaluated the morphoedaphic index  (MEI), a fish yield
estimator.  Background papers leading to the development of the MEI and more
recent advances were discussed.  The MEI was defined and its criteria for use
examined.  The significance of its components -  total dissolved solids and
mean depth - were explained.  A comparison between the MEI and  related models
was also made.  The global range of the MEI was  outlined as well as restrictions
on its use.  Sustained fish yields at different  MEI values for various climatic
regions were predicted.  Several special applications of the MEI include:
prediction of angling yield in north-temperate lakes; prediction of commercial
fish yield on a newly created reservoir; indication of ecological stresses and
changing environments; and contrasting responses to cultural eutrophication in
the littoral and profundal zones of lakes.  The  implications of the MEI for
ecological theory were discussed.

*Dissolved solids, *Yield equations, *Fish populations, Statistics, Depth

*Morphoedaphic index, Angling yield, Commercial  fish yield, Mean depth
152E

THE ULTRASONIC METHOD OF RIVER GAUGING,

Herschy, R. W.

Water Data Unit, DOE,
Reading Bridge House, Reading, Great Britain

Water Services, Vol. 78, No. 940, p 198-200, June, 1974.  3 fig.

The ultrasonic method of river gauging was designed to more accurately measure
river flow in areas, such as rivers influenced by navigation and locks, where
existing methods of river gauging are unsuitable.  The ultrasonic method
measures the velocity of flow at a certain depth by simultaneously trans-
mitting sound pulses through the water from transducers on both sides of
the river.  The average velocity of the water at the depth of the trans-
ducers is directly related to the difference between the time of travel of
the pulses crossing the river in an upstream direction and those travelling
downstream.  By incorporating an area factor in the electronic processor
and relating the average velocity at the depth of the transducers to the average
velocity of flow of the whole cross section, an output of discharge can be
determined.  Studies were done at River Pang at Pangbourne and at the River
Thames at Sutton Courtenay and the calibration and accuracy of the system
were found.

*Flow, *River flow, Rivers

River Gauging, Ultrasonic methods, Great Britain
                                            557

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153E

SIMULTANEOUS DETERMINATION OF CU2+, PB2+, CD2+, and
ZN2+ IN FRESH TOWN-WATER BY ANODE STRIPPING POLAROGRAPHY,

Yamazaki, Y.

Journal of the National Chemical Laboratory for Industry,  Vol. 69, No. 5,
p 154-161, May, 1974.  8 fig, 6 tab, 13 ref.

A procedure for the simultaneous determination of copper,  lead, cadmium, and
zinc ions in fresh municipal water which has been retained in water-pipes for
a period of 24 to 72 hours is examined.  The ions were electrodeposited on a
Balanced Head Stationary Hanging Mercury Drop Electrode at -1.5 volts vs. Hg
pool for about 5 minutes while being stirred at 300 rpm in 0.5 M sodium
acetate +0.1 M potassium tartrate supporting medium.  Anodic dissolution
curves were recorded by changing potential linearly over the range of -1.5
volts to 0 volt vs. Hg pool at a scan rate of 50 mV/sec.  Relationships
between the dissolution peak currents and pre-electrolysis potential, the
effects of foreign cations on Cd (1 x 10 to the minus seventh power M) and
Pb (1 X 10 to the minus seventh power M), and the surface  active substance
effects on Cu, Pb, Cd, and Zn were elucidated.  Approximately 0.006 to 0.017
ppm of Cu, 0.003 to 0.017 ppm of Pb, 0.05 to 0.2 ppb of Cd, and Q.Q06 to
0.04 ppm of Zn were discovered in the fresh municipal water.

*Polarographic Analysis, *Municipal water, *Water pollution

*Cu2+, *Pb2+, *Cd2+, *Zn2+, *Anodic stripping polarography, Anodic dissolution
curves, Surface active substance, Balanced Head Stationary Hanging Mercury
Drop Electrode, Sodium acetate, Potassium tartrate supporting medium
154E

DICHROMATE REFLUX CHEMICAL OXYGEN DEMAND:  A PROPOSED
METHOD FOR CHLORIDE CORRECTION IN HIGHLY SALINE WASTES,

Baumann, F. J.

Pomeroy, Johnston and Bailey, Pasadena, California

Analytical Chemistry, Vol. 46, No. 9, p 1336-1338, August, 1974.  1 fig, 3 tab,
4 ref.

Chloride interferes with methods which attempt to determine chemical oxygen
demand by strong wet oxidative means in saline wastes.  Mild oxidizing conditions
inhibit chloride oxidation, but only at the expense of inefficient oxidation
of organic matter.  The dichromate reflux method uses acid concentrations and
heating times which oxidize about 85-95 percent of the organic matter present,
while oxidizing the chloride ion by 100 percent as well, in the determination
of COD.  The chloride interference can be greatly inhibited through the addi-
tion of mercuric sulfate to form unionized mercuric chloride.  The complexing
method using a weight ratio of HgS04:Cl at 10:1, yields reproducible results at
chloride concentrations up to 5,000 mg/liter.  Chloride interference problems
occur in wastes of low to moderate COD with chloride concentrations approaching
that of seawater.  True values for oxygen consumed from dlchromate. are deter-
mined in highly saline wastes and seawater By the employment of the chlorine-
recovery method, without the requirement of prior chloride determination or
dependence on an excess of mercury which does not achieve complete sequestra-
tion of chloride.

*Water pollution, *Salinity, *Chlorides, *Waste water treatment, *0xidation

*Dichromate reflux method, *Chemical oxygen demand, Mercuric sulfate,
Chloride oxidation, Saline wastes
                                         558

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155E

METHOD FOR DETERMINATION OF SELENIUM, ARSENIC, ZINC,
CADMIUM, AND MERCURY IN ENVIRONMENTAL MATRICES BY
NEUTRON ACTIVATION ANALYSIS,

Orvini, E., Gills, T. E., and LaFleur, P. D.

Activation Analysis Section, Analytical Chemistry
Division, National Bureau of Standards,
Washington, D.C.

Analytical Chemistry, Vol. 46, No. 9, p 1294-1297, August, 1974.  6 tab, 6 ref.

Selenium, arsenic, zinc, cadmium, and mercury present a serious pollution
problem as heavy metal contamination in our environment.  Neutron activation
analysis has the high sensitivity necessary for the detection of these ele-
ments.  However, the most sensitive of reactions involve short half-lived
isotopes of As, Zn, Cd, and Hg, requiring chemical separation of these
elements from the activated matrix.  A combustion technique used for mercury
and selenium separation does not require the previous dissolution of the
matrix.  The technique has been altered and extended to separate quantita-
tively As, Zn, and Cd in addition to Hg and Se from different biological
materials and materials of environmental concern.  This procedure has been
used in the determination of Se, As, Zn, Cd, and Hg concentrations of certain
Standard Reference Materials under development at the National Bureau of
Standards.

*Arsenic radioisotopes, *Zinc, *Cadmium, *Mercury, *Neutron Activation
Analysis, Heavy metals, Water pollution, Separation techniques

*Environmental matrices, *Selenium, Standard Reference Materials, National
Bureau of Standards
 156E

 DETECTION OF WATER POLLUTANTS BY A C02 LASER,

 Kraus, G., Maier, M. and Kaiser, N.

 Physik-Department der Technischen Universitat,
 Munich, Germany

 Optics Communications, Vol. 11, No. 2, p 175-177, June, 1974.  1 fig, 5 ref.

 The concentration of S04 ions in the sewage of a textile plant was measured
 by the infra-red absorption of a cw C02 laser.  The detection sensitivity was
 determined at about 50 mg/liter.  Infra-red absorption spectroscopy is an effective
 technique in the detection of small concentrations of organic and inorganic
 molecules.  The molecules' vibrational and rotational absorption bands are
 the identifying factors.  Spectroscopic techniques have lately been used for
 detecting the quantitative measurement of air pollutants' concentration.  In
 dealing with water pollution, many common inorganic anions exhibit character-
 istic absorption bands in the wavelength region between 6 and 11 micrometers.
 The major difficulties in measuring the concentration of pollutants dissolved
 in water are:  that pure water has a high absorption in the infra-red region;
 and that the concentration of the pollutants is generally very small, ranging
 from 1 mg/liter or less in clean lakes and rivers to about 1000 mg/liter in the sewage
 of industrial plants.  These concentrations are not measurable with conven-
 tional infra-red light sources and spectrometers where detection of several
 g/liter is achieved.   A cw C02 laser in conjunction with a sensitive two-beam
method resolves the difficulty.

*Water pollution,  *Lasers, *Infrared radiation, *Absorptlon, *Spectroscopy,
Industrial pollution, Sewage,  Lakes,  Rivers

*Cw Co2 laser,  Inorganic anions,  Absorption bands,  Vibrational and rotational
absorption bands,  S04 ions
                                            559

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 157E

 DETERMINATION OF PARTS PER BILLION SULFIDE IN WATER
 WITH THE SULFIDE-SELECTIVE ELECTRODE,

 Baumann, E.

 E.  I. DuPont de Nemours and Company,
 Savannah River Laboratory,
 Aiken, South Carolina

 Analytical Chemistry, Vol. 46, No. 9, p 1345-1347, August, 1974.  1 fig, 2 tab,
 5 ref.

 The sulfide-selective electrode is helpful in the routine determination of
 total sulfide in water due to the simplicity of measurement and absence of
 interferences.  A procedure developed by Orion Research Incorporated, with
 a sulfide antitoxicant buffer of sodium salicylate, ascorbic acid, and sodium
 hydroxide, determines sulfide contents as low as 0.1 ppm.  This sensitivity
 was extended to 30 ppb by the removal of heavy metals from the sodium sali-
 cylate by dithizone extraction.  A preconcentration step was incorporated
 In  the process because this sensitivity was still inadequate for the deter-
 mination of sulfide concentrations in natural waters; extending the deter-
 mination to a lower ppb range.  The sulfide was separated as ZnS, copreci-
 pitated with Zn(OH)2, and dissolved in alkaline EDTA-ascorbic acid solution
 for potentiometric measurement with the sulfide-selective electrode.  Higher
 concentrations of sulfide were determined without the preconcentration step.

 *Sulfides, *Water pollution, Electrodes, Chemical Wastes, Heavy metals,
 Potentiometric levels

 *Sulfide-selective electrode, Sodium salicylate, Dithizone extraction,
 Ascorbic acid, Alkaline EDTA
1.58E

EXTRACTABLE AND PLANT-AVAILABLE ZINC IN HORIZONS OF
SEVERAL FRASER RIVER SOILS,

John, M. K.

Canadian Journal of Soil Science, Vol. 54,  No.  2, p 125-132,  May, 1974.   6 tab,
15 ref.

Recent emphasis on mineral requirements for cattle and reports of zinc deficiency
in crops indicated need for study of zinc in soils and its availability  to plants.
One case was Fraser River, Canada, where the total zinc and seven measures of
extractable zinc in horizons of seven soil  profiles declined  with increasing
depth of sampling within the profile.  Some extractants removed more zinc from
the deepest horizons of some profiles than from the horizon sampled immediately
above.  This distribution pattern was more  pronounced for extractable than total
zinc.  From 27 horizon samples containing an average of 108 ppm total zinc, 2 N
MgC12, DTPA, North Carolina, Morgan, N KC1, acidic NH4Ac, and 0.01 M CaC12 ex-
tractants solubilized an average of 4.14, 3.77, 3.37, 1.99, 1.82, 1.64,  and 0.69
ppm zinc, respectively.  Zinc concentrations in corn and in oats grown on the
horizon samples were best correlated with amounts extracted by 2 N MgC12, acidic
NH4Ac, and N KC1.  Regressions on extractable Zn and soil pH accounted for as
much as 74 and 55 percent of variations in zinc content of corn and oats,
respectively.

*Soil profiles, *Zinc, *Alluvial soils, *Rivers, Extractions, Crops, Minerals

Fraser River, Canada, pH
                                            560

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159E

REVIEW OF RAPID BOD TEST METHODS,

LeBlanc, P. J.

Eco-Research Limited, Pointe Claire, Quebec, Canada,
Analytical Services

Journal of the Water Pollution Control Federation, Vol. 46, No. 9, p 2202-2208,
September, 1974.  35 ref.

Rapid BOD test methods, as opposed to the standard five-day BOD test, are con-
sidered.  Time-temperature methods, special innoculation methods, correlation
methods, manometric methods and plateau value methods are all reviewed and
evaluated.  It is concluded that current rapid procedures cannot replace the
standard five-day test, although the one-day, 37 degrees centigrade test and
the TbOD test have some practical validity.  It is also suggested that the
short-term AT test be further developed.

*Biochetnical oxygen demand, *Incubation, *Chemical oxygen demand, Analytical
techniques, Laboratory tests, Organic loading, Organic matter

Oxygen-carrying capacity, Total organic carbon, Total oxygen demand, Inocula,
Plateau value, Manometric techniques
160E

ELECTROCHEMICAL FILTRATION OF DILUTE COLLOIDAL HYDROSOLS,

Liberman, S. J., Inoue, M., and Mason, S. G.

Buenos Aires University, Argentina,
Department of Inorganic and Analytical Chemistry

Journal of Colloid and Interface Science, Vol. 48, No. 1, p 172-175, July,
1974.  2 tab, 7 ref.

In the use of bimetallic coalescence filters consisting of granular beds of
pairs of electrochemically dissimilar metals as a simple method of clarifying
fine ultradilute emulsions, the filtering action is ascribed to electrophoretic
deposition of the electrically charged droplets in the self-generated electrical
fields between each pair of dissimilar metal granules.  It is demonstrated that
exposure of dilute hydrosols of solid particles to granulated metals can be used
for removal of the particles and that the technique offers promise as a simple
method of water clarification.  Using monodisperse cationic and anionic poly-
styrene latex hydrosols as model systems, particle removal has been studied by
compacted granular beds and stirred suspensions of simple metals or in pairs.
Measurements of the removal efficiency or particles in the presence of various
electrolytes and metal combinations, coupled with the observation that the
method can be made to work with single metals, cast doubt on the validity of
the aforementioned mechanism.

*Electrochemistry, *Filtration, *Laboratory tests, *Hydrosols (dispersions),
*Emulsions, *Methodology, *Water purification, Metals
                                        561

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161E

THE ABSORPTIOMETRIC DETERMINATION OF ALUMINIUM IN WATER.
A COMPARISON OF SOME CHROMOGENIC REAGENTS AND THE
DEVELOPMENT OF AN IMPROVED METHOD,

Dougan, W. K., and Wilson, A. L.

Water Research Centre, Medmenham Laboratory,
Medmenham, Marlow, Buckinghamshire, Great Britain

Analyst, Vol. 99, No. 1180, p 413-430, July, 1974.  3 fig, 15 tab, 21 ref.

The properties of chromogenic reagents used for the absorptiometric determina-
tion of aluminium in water are compared, and an experimental comparison of
catechol violet, Eriochrome cyanine R, and stilbazo has been made.  Catechol
violet is considered to be the most suitable and a method involving the use
of this reagent has been developed.  With the exception of fluoride, substances
normally present in treated waters did not cause important interference.  The
method is simple and rapid; ten samples can be analyzed in approximately 1.5
hours.  The method has advantages over other commonly used methods, and is
recommended for use in water analysis laboratories.

*Water analysis, *Aluminum, *Analytical techniques, Methodology, Sampling

*Absorptiometric determination, *Chromogenic reagents
162E

LET'S UPGRADE THE BOD TEST,

Arthur, R. M.

Arthur Brothers Company, Incorporated, Fond du Lac,
Wisconsin

Water and Sewage Works, Vol. 121, No. 6, p 100-102, June, 1974.  2 fig,
11 ref.

The manometric method of performing the BOD test as opposed to the dilution
method is discussed.  The problems with the technique of the dilution method
BOD, the BOD variables, the advantages and disadvantages of the dilution BOD
are delineated.  A new method of determining BOD using modern Instrumentation
is recommended and explained.  The new method has the following advantages:
it is a biochemical test; the simplest of manipulative skills are required;
it: requires a low capital investment for equipment and less daily labor costs;
it is similar to the dilution techniques and can be accepted as a Standard test;
and large undiluted samples are used.  In addition, it simultaneously measures
rate as well as total oxygen demand; a shorter time is needed to provide infor-
mation about the strength of a waste; and the results are more accurate than
the dilution method.

*Biochemical oxygen demand, *Analytlcal techniques, Laboratory equipment,
Standards, Instrumentation, Water pollution, Biochemistry, Water Analysis

*Manometric method of BOD
                                           562

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 163E

 CONTINUOUS MONITORING, AUTOMATED ANALYSIS, AND SAMPLING
 PROCEDURES.

 Brezonlk, P. L.

 Florida University, Gainesville, Florida

 Journal of the Water Pollution Control Federation, Vol. 46, No. 6, p 1100-1109, June,
 1974.  94 refs.

 A review of  the literature published during 1973 dealing with analytical aspects of
 water pollution and its control is presented.  The general areas of discussion include
 inorganic substances analysis using electrometric and spectrometric methods of
 detection;  organic matter, oxygen demand, and bioassays; radioactivity; and,
 sampling methods  including sample preservation, samplers, and concentration/extraction
 methods.

 *Reviews, *Publications, *Monitoring, *Automation, *Analytical techniques, *Sampling,
 Inorganic compounds, Organic matter, Oxygen demand, Bioassays, Radioactivity
164E

SYSTEMS ANALYSIS OF CENTRALIZED REACTIVATION OF EXHAUSTED
CARBON IN WASTEWATER TREATMENT,

Hsu, J. S-y.

Michigan University
Ann Arbor, Michigan

Dissertation Abstracts International B, Vol. 35, No. 1, p 404, July, 1974.

A system in which industrial and/or municipal waste water treatment plants of a
region transport their exhausted carbon to one or more central furnaces for
reactivation can result in savings in the total cost of carbon reactivation.  Such a
system is the topic of this dissertation.  Based on empirical data, four major costs
are estimated and expressed as mathematical functions of the reactivation demand.
From these cost functions two location models were constructed.  Some numerical
results were obtained based on a region of 150-mile radius.  Results indicate that
regionalization of carbon reactivation for small plants can result in large savings
in the total cost of carbon reactivation.

*Waste water treatment, *Activated carbon *Tertiary treatment, Regional economics,
Mathematical studies, Model studies, Numerical analysis, Estimated costs

*Carbon reactivation
                                       563

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165E
AUTOMATION OF FILTER IN PURIFYING DEVICES IN WATER PIPES
(Avtomatizatsiya fil'trov na vodoprovodnykh ochistnykh
sooruzheniyakh),

Shimkovich, V. V.

Vodosnabzheniye i Sanitarnaya Tekhnika, No. 4, p 9-11, 1974.  2 fig, 4 ref.

Critical review is given of automatic control systems for water filters in
municipal and industrial water supply systems.  The rates of filtration are
controlled primarily by the water levels or by the flow rates of the filtrates,
by means of electric or hydraulic, and sometimes pneumatic automatic control
systems.  The automatic control systems act upon electrically or hydraulically
powered sluice valves.  Poor hydraulic characteristics of conventional sluice
valves make their replacement by rotary valves necessary.  The automatic
sequential switchover of the filters to flushing is possible by a pulse from
a limit switch.  Switchover is a function of the limit value of the pressure
loss, and a function of the turbidity which is controlled by a turbidimeter.

*Filters, *Automation, *Hydraulics, Flow rates, Water purification,
Filtration, Turbidity, Equipment

*Water pipes, Rotary valves
166E

TELEMETRY IN WATER POLLUTION CONTROL,

Holmes, J. R.

South Yorkshire Metropolitan County Council,
South Yorkshire, Great Britain

Water Pollution Control, Vol. 73, No. 4, p 433-442, 1974.  11 fig.

Telemetry and data transmission are applicable to water and sewage treatment.
The use of sophisticated computer equipment is described, in which both analysis
and treatment are made by remote control.  A total feedback loop is not
presently possible, one by which equipment would monitor the incoming effluent,
select the appropriate treatment, and direct the sewage treatment machinery
with outfall instrumentation.  Parts of this system, however, are feasible.
Described are multiplexing, transmission media, autodialling monitoring
systems, the operational outstation, and the operational master station.
Basic principles are outlined, terminology is defined, with reference to use
in water pollution control.

*Telemtry, *Water pollution control, Sewage treatment, Computers,
Automation, Equipment, Monitoring
                                          564

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167E

DESCRIPTION OF A NEW WASTE WATER ANALYZER FOR LABORATORIES
(RESPIROMETER) (Uj laboratoriuml szennyvizvizsgalo
keszulek (Respirometer),

Fleps, W.

Hydrologiai Kozlony, No. 5, p 217-221, 1974.  5 fig, 11 ref.

New batch type and flow-through respirometers were developed in Hungary for
complex laboratory analysis of waste waters and activated sludge regarding
the parameters which determine the biological purification of waste waters.
An oxygen supply is automatically controlled by oxygen displacement from a
burette which permits visual checkup and also automatic recording of the
oxygen consumption in both the batch type and flow-through respirometers.
The batch type respirometer is suitable for the determination of the complete
BOD curve, the rate of carbon dioxide formation, the sludge growth,
and, by means of two respirometers, the total biochemical oxygen consumption,
including that for endogenous respiration.  The flow-through respirometer
with a peristaltic pump for water supply and discharge at preset rates is
suitable for the determination of:  the rate of oxygen consumption of the
mixture of waste water and activated sludge; the specific oxygen demand;
the specific endogenous and substrate respiration; the specific sludge
formation; the waste water toxicity; and, the total BOD.

*Analytical techniques, *Water purification, *Analyzers, *Laboratory
equipment, Waste water, Biochemical oxygen demand, Sludge


*Respirometer, Hungary
 168E

 CONTINUOUS WATER QUALITY MONITORING,

 Best, G. A.

 Clyde River Purification Board,  Scotland

 Effluent and Water Treatment Journal,  Vol.  14,  No.  7,  p 357-367,
 July, 1974.  6 tab, 16 ref.

 Despite widespread international usage there has been  a general dissatisfac-
 tion with the performance of water quality  sensors  currently marketed.   The
 Clyde River Purification Board in Scotland  has  experienced many varied
 problems in the operation of one of their two water quality monitoring
 stations.  Continuous water  quality monitoring  stations are expensive to
 build, equip, and maintain,  and  require constant attention by a competent
 staff.  If continuous water  quality monitoring  equipment Is purchased for
 pollution measurement rather than water supply  protection, it would be  useful
 for a certain measure of mobility to be introduced  into the station. In
 that way, areas of special interest to the  river board could be investigated
 from time to time.  It was suggested that monitoring equipment could be
 installed on a purpose built caravan and towed  to various sites of a river
 basin.  One new development  by EIL is  a submersible dissolved oxygen and
 temperature recorder, model  8050.  The reliability  of  the instrument has
 not yet been proven,  but its compact design and the use of well tried sensors
 suggest definite promise for water quality  measurement.

 *Water quality control, *Monitoring, Costs, Construction, Measurement,
 Water Supply, Dissolved oxygen,  Equipment

 Clyde River Board, Scotland
                                           565

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169E

AUTOMATIC WATER QUALITY METER BY SPECTROSCOPY FOR LIQUID
WASTE MANAGEMENT (Haisui shori kanrl no tame no bunko
sokutei nl yoru suishitsu jido keisoku),

Sakai, A.

Preprint, Japan Spectroscopic Society, p  29-33, Spring, 1973.   3 fig.

Process control factors for treatment of  suspended substances  and dissolved
organic matter in waste water are discussed.  The treatment depends on an appro-
priate amount of oxygen supply and organic substance load suitable for bacteria
degradation speed, the nutritional balance, pH, and the temperature.  For good
results, sludge must have good flocculation and easy separation.  The floccula-
tion capacity decreases greatly if the sludge concentration and organic sub-
stance load are not suitable and if the nutritional balance is poor.  There-
fore, the most important control factors  are the oxygen in the aeration tank
and the organic substance load.  Dissolved oxygen measurement  can be taken
easily by an automatic continuous electrochemical meter.  For  the control
of chemical additive coagulant, infrared  and ultraviolet absorption
spectrophotometry was examined, using dye waste water.   When a coagulant is
added and floe is formed, the turbidity can be measured by infrared ray and
the remaining color can be simultaneously measured by a visible light.  In
this study, wave lengths were examined for various dye  solutions; generally,
yellow could be measured at 420 nm, and blue and red groups could be measured
at 550 nm.  For turbidity, a 970 nm single ray was used.  Even when coagulation
is complete and transparency is achieved, the remaining color  can bring error.
Measurement was therefore made after the  formed floe was completely separated,
with the use of a z layer filter.  Possible further improvements and ultra-
violet absorption were also discussed.

*Water quality control, *Liquid wastes, *Spectroscopy,  Automation,
Organic matter, Flocculation, Dissolved oxygen, Waste water treatment,
Turbidity
 170E

 TOTAL PHOSPHORUS ANALYSIS:   PERSULFATE OR ASHING?,

 Gupta,  K.,  and Zanoni,  A.  E.

 Havens  and  Emerson Limited,
 Cleveland,  Ohio

 Water and  Sewage Works,  Vol.  121,  No.  7,  p 74-77,  July,  1974.   5  fig,  17  ref.

 A combination of oxidation,  using  potassium persulfate,  K2S08  as  an  oxidizing
 agent and hydrolysis  of the  sample in  an  acid  medium followed  by  a colorimetric
 determination of phosphorus  is  a new method for analyzing  phosphorus.   In
 another technique,  KN03-NaN03 eutectic melt is utilized, while still another
 employs 50  percent hydrogen  peroxide solution.  Harwood  compared  five  oxidation
 procedures  for total  phosphorys analysis.   A procedure was developed by
 Harvey  which samples  are acid hydrolyzed  under pressure  with an autoclave
 at 140  C for 5 hours.  In the persulfate  method,  10  ml of  standard solution
 was oxidized with different  amounts of K2S208  using  30 percent sulfuric acid,
 and adding  distilled  water to increase the volume  to 50  ml.  In the  dry ashing
 method, 10  ml of standard solution was treated with  a volume of 13.67  percent
 MgC12.6H20  solution,  then evaporated to dryness on a steam table.

 *Phosphorus, *0xidation, Hydrolysis

 *Total  phosphorus analysis,  *Persulfate method, *Dry ashing method,  Sulfuric
 acid, Percholic acid  digestion, Eutectic  melt, Environmental Protection
 Agency
                                         566

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171E

DETERMINATION OF FENITROTHION, PHOSPHAMIDON AND
DIMETHOATE IN NATURAL WATER,

Ripley, B. D., Hall, J. A., and Chau, A. S. Y.

Water Quality Branch, Canada Centre for Inland Waters,
Burlington, Ontario, Canada

Environmental Letters, Vol. 7, No. 2, p 97-118, 1974.  4 fig, 6 tab, 16 ref.

Fenitrothion, phosphamidon and dimethoate are organophosphorus pesticides
being used for the protection of Canadian forests from defoliators.  A
method for determining residues of these chemicals in natural waters was
investigated.  Because fenitrothion and phosphamidon were not resolved
on several GLC columns used in the laboratory, the separation was
accomplished through serial solvent extraction using different solvents before
GLC analysis.  The step of solvent partitioning serves to a certain extent
as confirmation of the identity of the pesticide.  Storage effects on these
pesticides in distilled and natural waters were elucidated.  Only 0.01 ppb
of fenitrothion and dimethoate and 0.05 of phosphamidon in one liter of water
is determinable.

*0rganophosphorus pesticides, Forest management, Natural waters, Separation
techniques, Water pollution

*Fenitrothion, *Dimethoate, *Phosphamidon, *Serial solvent extraction,
GLC analysis
172E

TERTIARY PLANT HAS SUPPLIER-INSTALLED AUTOMATIC CONTROL
SYSTEM,

Instrumentation, Vol. 27, No. 2, p 9-11, 1974.

A Honeywell control system has been installed at the new Chino Basin Municipal
Water District's advanced waste water treatment facility near Ontario,
California.  The control system incorporates automatic processes.  The filter
beds are backwashed automatically, activated either by a loss-of-head or a
timer if the head-loss point is not reached.  All critical variables are
indicated and recorded at the central control panel.  Pump control switching
is also done at the central control panel.  Flow control is designed to
assure a constant throughput.  Chemical additions include chlorine, alum,
and polyelectrolyte.  The addition of the polymer has cut alum requirements
and reduced the chloride and sulfate content in the final effluent.  Sludge
is on a pre-programmed schedule.  The control systems were designed for
efficient and safe operation, easy operator training, and minimum maintenance.

*Waste water treatment, *Municipal wastes, *Automatic control, *Facilities,
Operation and maintenance, Filters, Pumps, Chemicals, Sludge, Equipment,
California

Honeywell control system
                                       567

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173E

WATER QUALITY BY PHOTOGRAPHIC ANALYSIS,

Klooster, S. A., and Scherz, J. P.

Photogrammetric Engineering, Vol. 40, No. 8, p 927-935, August, 1974.
10 fig, 1 tab, 15 ref.

Five years of research have resulted in a workable and practical aerial
reconnaissance technique for correlating water quality parameters to aerial
photographs.  A positive correlation was determined between reflectance of
water and the water quality parameter of turbidity.  This relationship is
permanent for any particular waste.  At certain times other parameters such
as suspended solids, correlate to turbidity and may be mapped.  Proper
analysis of aerial photographs in determining water reflectance requires a
standard reflectance panel somewhere in the frame.  For such investigation
color and color-infrared film are utilized and analyzed with a color
microdensitometer which, with some modification, is employed to analyze
reflectance of water samples.  Noise in the analysis consists of bottom
effects, reflection from the air-water interface, and path luminance; all
of which may be dealt with by proper techniques.

*Water  quality management, *Water pollution, *Aerial photography, Turbidity,
Air-water interfaces, Reflectance, Suspended solids, Sampling

*Infrared film, *Microdensitometer, Bottom  effects, Path luminance
 174E

 DEVELOPING WATER SAMPLING STANDARDS,

 Environmental Science and Technology, Vol. 8, No. 9, p 786-787  September
 1974.

 The consensus of opinion at the D-19 Symposium on Aquatic Sampling and
 Measurement for Water Pollution Assessment held in Washington, D. C., in
 June, 1974, was that no standard sampling equipment or technique exists
 for determining how polluted a given waste water stream is.  One of the
 most difficult sampling jobs is to obtain representative samples from storm
 or combined sewers.  Different methods for sampling sewers include discrete
 samples, simple composite samples, flow-proportional composite samples, and
 sequential composite samples.  Equipment and sampling standards are in a
 formation stage; standards should emphasize intake, transport, tubing and
 piping, sample size, flow control, power sources, and temperature control.
 An ideal sampler should operate on batteries weighing less than 40 pounds
 which are capable of reliable sampling for three days in a standard manhole
 with uniform atmosphere and protection from vandalism.  It should have the
 ability to:  take flow-proportional and time-composite samples; separate
 the sample from all metal; purge the intake; vary the intake from 2 to
 10 ft/sec; multiplex; vary the collection intervals from ten minutes to
 four hours.  The sampler should be explosion proof, have a watertight exterior
 case, a security lock, a 2 1/2 gallon capacity, and a lift of 20 feet.

 *Equipment, *SampIing, *Water analysis, Quality control, Water sampling,
 On-site data collection, Data collection, Variability
                                         568

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175E

NEW SPECTROPHOTOMETRIC METHOD FOR THE ESTIMATION
OF HEXAVALENT CHROMIUM IN WATER,

Prasad, R., and Ramanujam, S.

Research and Industry, Vol. 19, No. 1, p 26-29, March, 1974.  1 fig, 7 tab,
6 ref.

The blue color developed with 0-tolidine hydrochloride-tartaric acid reagent
in the presence of aqueous sodium fluoride, is the basis for a quantitative
method for the spectrophotometric evaluation of hexavalent chromium in
drinking water at 600 millimicrons.  Hexavalent chromium is a toxic inorganic
element in potable water.  The maximum amount permissible is 0.05 ppm.  The
standard hexavalent chromium solution consists of the dissolving of 0.1414 g
Analar potassium dichromate in distilled water, making the volume up to
100 ml.  Twenty ml of this solution were made up to 1000 ml to create the
standard solution consisting of one microgram hexavalent chromium per ml.
0-tolidine hydrochloride tartaric acid was prepared by dissolving 0.5 g
freshly prepared pure 0-tolidine hydrochloride and 0.5 g pure tartaric acid in
distilled water, making a volume of 100 ml.  One g pure sodium fluoride
dissolved in water made up to 100 ml and kept separately.  The null balance
method in a one centimeter cell of Unicam SP 500 series 2 ultraviolet and
visible spectrophotometer in the visible range utilizing tungsten lamp
was used to determine the optical density measurements.  The hexavalent
chromium solution was treated with one ml of 0-tolidine hydrochloride-tartaric
acid reagent and one ml of sodium flouride solution, making up to 10 ml with
distilled water.  The blue color was stable for about one hour.  The solution
was measured in the spectrophotometer for 26 to 30 minutes at wavelengths
ranging from 400 to 650 millimicrons.

*Spectrophotometry, *Chromium, *Toxicity, Water pollution, Water quality
standards, Metals, Potability, Water quality control

*Hexavalent chromium, *0-tolidine hydrochloride-tartaric acid reagent,
Analar potassium dichromate, Sodium fluoride, Beer's Law
176E

AN AUTOMATED METHOD FOR THE DETERMINATION OF
FORMALDEHYDE IN SEWAGE AND SEWAGE EFFLUENTS,

Musselwhite, C. C., and Petts, K. W.

Water Pollution Research Laboratory of the Department
of the Environment

Water Pollution Control, Vol. 73, No. 4, p 443-448, 1974.  4 fig, 7 tab,
3 ref.

The discharge of sewage from pleasure boats has been cited as an increasing
source of pollution.  Control of this discharge requires the mandatory use
of chemical toilets which will be discharged for treatment ashore, probably
to be treated in combination with other sewage.  Since some of the chemical
additives to the toilets contain a high proportion of formaldehyde, which is
toxic to some fish at levels above 50 mg/liter, it is necessary to know the
formaldehyde content of this treated sewage before it is discharged to water.
A procedure is described for using a Technicon Auto Analyzer to quickly and
accurately monitor the formaldehyde level.  The method utilizes the reaction
of formaldehyde with acetylacetone in the presence of an excess of an
ammonium slat to form a yellow compound, diacetyldihydrolutidine, which
is measured colorimetrically.  The methods outlined will give reproducible
results in the range of 0.10 to 25.0 mg/liter of free and combined
formaldehyde and in the range of 0.05 to 10.0 mg/liter of distilled
formaldehyde.  It is proposed that the automated processes should be used
for the routine monitoring of total formaldehyde present in sewage and sewage
effluents.

*Sewage, *Analytical techniques, *Monltoring, *Water quality control,
Boating, Water pollution sources, Boats, Boating regulations, Automation

*Formaldehyde, Technicon Auto Analyzer

                                   569

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 177E

 DESIGN AND APPLICATION OF A MULTIPURPOSE MANAGEMENT
 INFORMATION SYSTEM FOR DRINKING WATER QUALITY ASSESS-
 MENT IN DISTRIBUTION SYSTEMS,

 Kovacs, S.

 Drexel University,  Philadelphia, Pennsylvania

 Dissertation Abstracts International B,  Vol.  35,  No.  4,  p 1725,  1974.

 A computer based multipurpose management information  system,  MMIS,  for
 drinking water quality data has been designed.   The City of Philadelphia,
 Pennsylvania was used as a prototype model.   Degradation of water quality
 can be a public health hazard and cause  aesthetic problems of discoloration,
 taste, and odor.  An MMIS is necessary to provide correct and available
 information on water quality indicators  in distribution  systems.   The  MMIS
 can be utilized in the research of cause and  effect relationships of water
 quality deterioration and also for managerial and operational decision-
 making.  Statistical techniques which are appropriate for the study of water
 quality deterioration and for the empirical definition of water  quality
 are presented.  The MMIS can be adapted  by a  municipal water utility to meet
 its specific information requirements.  The MMIS  can  also be used as a
 modular subsystem of an overall water utility management information system.

 *Computer models, *Water quality control, *Domestic water, *Water
 management (applied), Public health, Operations,  Management,  Mathematical
 models, Water supply

 Multipurpose management information system (MMIS)
178E

DETERMINATION OF SUBMICROGRAM QUANTITIES OF MONOMETHYL
MERCURY IN AQUATIC SAMPLES,

Bisogni, J. J., and Lawrence, A. W.

Cornell University, Ithaca, New York,
Department of Environmental Engineering

Environmental Science and Technology, Vol. 8, No. 9, p 850-852, September,
1974.  4 tab, 8 ref.

The discovery of high concentrations of mercury in some aquatic organisms
has prompted the investigation of methods of testing for the presence of
organomercurials.  The method described combines modifications of several
different schemes to analyze for monomethyl mercury in aqueous solution,
biomass, or in inorganic and organic sediment.  The procedure Involves
essentially these steps:  the separation of the organic mercury from inorganic
mercury by benzene extraction; the identification of the separated organo-
mercury by thin-layer chromatography; and, measurement of the amount of
separated organomercury from a calibration curve using the flameless atomic
absorption technique.  This monomethyl mercury analysis is accurate and
precise with recovery efficiencies greater than 90 percent and standard
deviation less than 4.1 percent for spiked inorganic and organic matrices.
Extraneous organomercurials interfere with the measurement; samples with
high concentrations of extraneous organomercurials should not be analyzed
by this method.  Interfering agents such as inorganic mercury, organic
solvents, and chloride can be readily eliminated.  The apparatus required
to perform this analysis costs about $1500.

*Mercury, *Analytical techniques, *Water pollution sources, *Water
pollution, Public health, Assay, Testing, Water analysis, Heavy metals

Organomercurials, Monomethyl mercury
                                      570

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179E

AUTOMATED MONITORING OF RECOVERED WATER QUALITY,

NASA Tech Brief No. B74-10029, May, 1974.  2 fig.

A laboratory prototype water quality monitoring system is described.  The
system provides an automatic method for online monitoring of the chemical,
physical, and bacteriological properties of recovered water and for
identifying a malfunction in the water recovery system.  Parameters moni-
tored are chloride ion concentration, ammonium ion concentration, pH,
specific conductance, total organic carbon, and E. coli.  The system is a
practical method to assess the potability of reclaimed water and utilizes
commercially available sensors that can be suitably modified.  The bacter-
iological quality of recovered water is monitored by a chemiluminescence
produced by the catalytic action of bacterial porphyrins, specifically
hematin, on a luminol-hydrogen peroxide mixture.  An eighteen-step pro-
grammer performs most of the process control.  During each step twenty
functions can be controlled.  Signals are sent to the processing electronics
from the photo-multiplier and provide a readout to be used for permanent
records and analysis of data.

*Potable water, *Reclaimed water, *Monitoring, *Equipment, Testing, Water
analysis, Quality control, Analytical techniques, Regulation, Maintenance,
Data analysis
180E

AUTOMATED WET CHEMICAL MICROCOULOMETRIC ANALYZER
FOR CHLORIDE ION,

Ott, D. E., and Gunther, F. A.

California University, Riverside, California,
Department of Entomology

Bulletin of Environmental Contamination and Toxicology, Vol. 12, No. i,
p 161-166, August, 1974.  3 fig, 6 ref.

An automated system for the rapid and reproducible analysis of the presence
of chloride ion in aqueous solution is described.  The apparatus is a
combination of a Technicon Auto Analyzer and Dohrmann microcoulometric
titration modules.  The chloride analyzer is designed to detect chloride
ion resulting from the degradation of organochlorine pesticides, but is
useful in any analytical situation requiring accurate and rapid analysis
of chloride ion.  The experimental results showed a mean operation effi-
ciency of 97 plus or minus one percent and 96 plus or minus 3 percent.
This chloride analyzer can be used for low-level aqueous chloride ion
determinations as long as interferences such as bromide, iodide, and
fluoride ions are not present.

*Chlorine, *Analytical techniques, *Pollutant identification, *Aqueous
solutions, Water pollution sources, Equipment, Pesticides

Technicon Auto Analyzer, Dohrmann microcoulometric titration modules
                                        571

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                         MODEL STUDIES
001F

PROBLEMS IN PHENOLICS-MODELING METHODS IN THE OHIO RIVER
AT WHEELING,

McMichael, F. C. and Vigani, F. C.

Department of Civil Engineering, Carnegie-Mellon
University, Pittsburgh, Pennsylvania

Journal of the American Water Works, Vol. 65, No. 11, p 725-731, November, 1973.

Problems in phenolics modeling methods in the Ohio River at Wheeling, West
Virginia are described.  A method of fitting a time series model to historical
data on raw water quality was found unsuitable for describing what was
occurring in the river, but revealed activities of the operators in the
treatment plant.  An analysis of data showed the effect of operator bias
on the reported data.  When the operator bias is removed,  there is
essentially no structure to the residuals, which indicates no apparent
physical or assignable cause relationship in the phenolics concentration
data.  The problem that very high concentrations of phenolics affect water
quality remains.  A measure of the occurrence of these extraordinary
values is tabulated for the five highest daily concentrations reported
at Wheeling in 1963-1968.  Major pollution control efforts should be
directed toward eliminating these high and apparently random values.
The extreme values of phenolics concentration may be caused by:
analytical problems, slugs of nonindustrial origin, and extraordinary
industrial discharges.

*Phenols, Chemical Wastes, Chemicals, Industrial Wastes, Water Pollution
Sources, Rivers, Ohio River, *Treatment Facilities, *Model Studies
002F

STORM DRAINAGE SYSTEMS DESIGN MADE ADAPTABLE FOR COMPUTERS,

Dillon, M.

Austin Company, Roselle, New Jersey.

Building System Design, Vol. 70, No. 7, p 27-29, October/November,  1973.

The Rational Method of Storm Design is described and applied to a computerized
design of storm drainage systems for 2 to 200 acre commercial and industrial
sites.  The Rational Method states that the peak discharge rate in cubic
feet per second is approximately equal to the drained area in acres; time
runoff coefficient, times the average rainfall intensity in inches
per hour.  It is necessary to know the time of concentration for
proper design of a storm drainage system.  The time of concentration is the
sum of overland flow time, plus time of flow in pipe above the design section.
Overland flow time is the.longest period of time, measured from the
beginning of a theoretical design storm, for runoff to travel from the most
remote point of the collection area, along a path perpendicular to contour
lines, down to the design section, usually an inlet.

*Model Studies, Storm Runoff, *Drainage Systems, *Storm Drains, Rainfall
Intensity

*Rational Method of Storm Design
                                        572

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003F

ALLOCATION OF FUNDING FOR WASTEWATER TREATMENT FACILITIES,

Hunter, J. S., Ill

Colorado State University, Fort Collins, Colorado.

Journal of the Water Pollution Control Federation, Vol. 46, No. 1, p 18-27,
Janaruy, 1974.  2 fig, 17 ref.

The allocation of funding for wastewater treatment facilities is discussed,
and a systems analysis approach is presented.  The process of fund allocation
cannot be any more rational than the information processing system used.
The priority systems now used for allocating wastewater treatment plant
construction funds leave much to be desired.  More attention must be given
to the actual benefits obtained from water quality management projects.
Existing procedures do not ordinarily attempt an explicit weighing of costs
and benefits, nor do they provide for a full and flexible consideration
of alternatives.  A systems analysis approach is outlined which gives
explicit attention to all the relevant factors involved.  These factors
are the nature of the water resource, its uses, and the interrelationships
among all these resources characteristics and uses.  Water resource includes
time, quantity, location, and quality.

*Systems Analysis, *Water Treatment, Waste Treatment, Model Studies, *Costs
004F

MASTER PLANNING METHODOLOGY FOR URBAN DRAINAGE,

Bishop, H. F.

Leornard Rice Consulting Water Engineers, Inc., Denver,
Colorado.

Journal of the Hydraulics Division, Vol. 100, No. HY1, p 189-199, January,
1974.  4 fig, 12 ref.

A comprehensive systems process for managing urban drainage and flood
control is described based on the integrated development of evaluation
criteria and existing situation model.  One of the principal elements of
the urban system is that of water resource management which included urban
drainage and flood control.  A systems engineering methodology was developed for
master planning of the major drainage system in the Denver area under Project
REUSE (Renewing the Environment through Urban Systems Engineering).  The
methodology incorporates a functional description of the urban drainage
system, and a systematic process of data acquisition, runoff analysis,
concept identification and selection, and master plan development and
implementation.

*Flood Control, Drainage Systems, *Urban Drainage, *Model Studies, Water
Resources, Systems Analysis, Colorado

*Denver, Project REUSE
                                             573

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005F

HYDRAULICS OF A WATER SUPPLY SYSTEM WITH FLUCTUATING WATER
DEMAND,  (Hydraulik eines Wasserversorgungssystems mit
fluktuierenden Bedarfstfengen),

Cembrowlcz, R. G.

Angewandte Informatlk, No. 11, p 481-488, 1973.  8 ref.

An algorithm has been developed using systems analysis techniques for the
hydraulic dimensioning of a water supply system with counterpressure tank
for fluctuating water demand.  The pump characteristics and the water-level
fluctuations in the taflks are taken into account in the model.  The dimensions
of the system components are given by the hydraulic equilibrium conditions
as a function, of parameters defined as pressure heads and pressure differences.
The reference pressure of the pump stand, and the pressure head occurring at
the feed-in point of the municipal network in the main pipe during the peak
demand interval were found to be sensitive principal parameters of the
water supply in sensitivity tests of the system for different fluctuations
in the water demand.  The hydraulic equilibrium in the tanks can be fully
restored by adequate reduction of the pressure head during drops in the
water demand.

*Algorithms, Mathematical Studies, *Model Studies, *Systems Analysis, Sewer
Systems, Engineering Structures, Pipes, Water Supply
006F

COMPUTER DATA FLOWS SMOOTHLY FOR SMALL WATER AUTHORITY,

Kingsley, F. H.

Monroeville Water Authority, Monroeville, Pennsylvania.

Public Works, Vol. 105, No. 1, p 52-53, January, 1974.

The computerized data processing procedures at the Monroeville, Pennsylvania,
Water Authority Plant are described.  The plant has 7,548 customers who use
an average of 2.7 million gallons a day.  An IBM System/3 Model 6 computer was
installed, and does all water billing accounting work including payroll
and general ledger as well as far-ranging management reports.  The computer
provides vital water consumption analyses for rate structures purposes and
allows billing on a monthly, quarterly, or on a regular budget basis.  Other
services and reports include:  trial balance reports giving a complete status
of the business within one hour; water bills turned out at the rate of
eight per minute; sheets for the reader's meter book turned out at the
rate of 40 a minute; an alphabetic listing of customers in two and a half
hours; a tenant listing in rental properties; and a monthly past-due listing.

*Treatment Facilities, *Computer Programs, *Data Processing, *Budgeting,
Planning, Consumptive Use, *Pennsylvania, Municipal Wastes

Billing, *Monroeville

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 007F

 INORGANIC NITROGEN REMOVAL IN A COMBINED TERTIARY TREATMENT-
 MARINE AQUACULTURE SYSTEM—I.  REMOVAL EFFICIENCIES,

 Goldman,  J.  C.,  Tenor,  K. R., Ryther,  J. H.,  and Corwin,  N.

 Woods Hole Oceanographlc Institution,  Woods Hole,
 Massachusetts

 Water Research,  Vol.  8, No. 1, p 45-54, 1974.   5 fig,  6 tab,  34 ref.

 The transformation of nitrogen and phosphorus  were observed  during the Summer
 and Fall  of 1972 in a prototype process consisting of  growth systems  for
 marine algae, oysters,  and seaweed, joined in  series  and  fed secondarily-
 treated wastewater diluted 1:4 with seawater for 11 weeks.   During tlis time
 95 percent of the influent Inorganic nitrogen  was removed by algal assimilation.
 The oysters in turn removed 85 percent of the  algae,  but  regenerated  as soluble
 ammonia 16-18 percent of the  nitrogen originally bound in the algal cells.   All
 of the regenerated nitrogen was removed in the seaweed system so that the total
 inorganic nitrogen removal efficiency of the system was 95  percent.
 Phosphorus removal was  not nearly as complete  as only  45-60  percent was
 removed.   The process has the capability of being expanded  to include
 additional tropic levels in an integrated and  highly  controlled food  chain
 system to serve the dual function of tertiary  wastewater  treatment and
 waste recycling through the production of shellfish and seaweeds.

 *Recycling,  Water Conservation, *Water Pollution Treatment,  *Water Reuse,
 Sewage Treatment, *Tertiary Treatment, *Food Chains,  Food Webs, *Ecosystems,
 Algae, Oysters
 008F

 THE DEVELOPMENT OF A MATHEMATICAL MODEL TO PREDICT
 RUNOFF WATER QUALITY FROM WATERSHEDS;,

 Malouf, J. B.

 Texas A and M University, College Station, Texas

 Dissertation Abstracts International B, Vol. 35, No. 4, p 1651, 1974.

A mathematical model, the Qual Model, to predict the quality of watershed
 runoff has been developed.  Runoff that moves over a basin and the pollu-
 tants that are dissolved or suspended in it is evaluated.  The pollutants
are substances generally deposited as a result of human activity within the
basin that are present on streets, surfaces, sidewalks, driveways, roofs,
grassed areas, alleys, gutters, and storm drains.  The model is based on
 the assumption that the rate of pollutant removal by surface runoff is
proportional to the amount of pollutant remaining and to the runoff intens-
ity.  The pollutants found on the basin before rain are obtained from
literature and used to evaluate the quality of runoff with respect to
 time from any watershed.  The simulation of urban runoff considers the
 urban runoff process as composed of precipitation, runoff, and quality
which interact to predict the quality found in urban storm water runoff.
The model may be applied to any watershed if the basic hydrographic data
and surface characteristics are known.  Improvements need to be incor-
porated into this model as more data and a further understanding of the
basic mechanisms involved become available.

^Mathematical models, *Urban runoff, *Water quality, *Surface runoff,
Storm runoff, Precipitation (atmospheric), Runoff forecasting,
Watersheds (basins), Hydrographs

Qual Model

                                         575

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009F

APPLICATION OF MULTIGOAL WATER QUALITY PLANNING MODEL,

Plngry, D. E., and Whinston, A. B.

Journal of the Environmental Engineering Division, ASCE, Vol. 100, No. EE1,
p 61-75, February, 1974.  2 fig, 9 tab, 8 ref.

An application of the water quality planning model presented by the authors is
considered.  Results of the application to the West Fork White River in Indiana
are presented along with an examination of some of the difficulties involved
in the application of the large-scale models of this type.  A simple descrip-
tion of the nonlinear algorithm used in solving the model is included.  Some
consideration of the role of planning models in decision-making is explained.

*Model Studies, *Mathematical Models, Application Methods, *Water Quality,
*Project Planning, Indiana, *Algorithm

West Fork White River
010F

HYDROLOGY AND STRUCTURAL DESIGN,

Chebotaryov, A. I. and Serpik, B. I.

Meteorologiya i Gidrologiya, No. 10, p 45-54, 1973.  3 fig, 5 ref.

A summary of the Guide to Determination of Design Hydrological Characteristics
is given.  Errors made in the preparation of certain normative documents are
mentioned and immediate tasks are shown.  It is maintained that said solution
should improve technical norms in the field of calculations of river flow as
applied to the requirements of structural design.

Reviews, Documentation, *Hydrologic Aspects, Structural Design, *Design
Criteria, *Mathematical Studies
                                        576

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011F

HYDROLOGICAL FORECASTING AND WATER MANAGEMENT,

Popov, E. G. and Komarov, V. D.

Meteorologiya 1 Gidrologiya, No. 10, p 37-44, 1973.  8 ref.

Problems Involving the application and efficiency of hydrological forecasting
with respect to water management in the Soviet Union are described.  A brief
survey of forecasting methods and primary tasks and trends of research
in the field of hydrological forecasting are given.

Application Methods, Efficiencies, *Hydrologic Aspects, *Forecasting, *Water
Management  (Applied), Research and Development, Surveys, Methodology

U.S.S.R.
012F

OPTIMIZATION OF STOCHASTIC STORAGE MODELS FORMULATED BY
P.A.P. Moran, and Z. Kaczmarek,

Mitosek, H. T.

Archiwum Hydrotechniki, Vol. 20, No. 3, p 309-335, 1973.  3 fig, 66 ref.

The purpose of this work is presentation of methodology concerned with utiliza-
tion of stochastic storage models for determination of release control
rules under the form of the reservoir operation plan securing optimization
of the economic effects under consideration.  These models allow for evaluation
of the reservoir operation in case the operation plan under the form of the
so-called storage volume transition probabilities matrix is already known.
Such evaluation depends on the assumptions concerning the random properties
of the reservoir inflow process.  The Moran"s model is based on the assumption
of the nonstationary cyclic random process with independent variables, while
Kaczmarek's model is based on the assumption of the nonstationary cyclic
lag-one Markov process.  The investigations based on the empirical material
recorded for the Polish rivers indicate that the process of mean monthly
flows (reservoir inflows) comply with the assumptions made in the Kaczmarek's
model.

Methodology, *Stochastic Processes, *Markov Processes, Reservoir Storage,
Model Studies, Optimization, *Mathematical Models, Reservoir Operation,
Evaluation, Inflow

Poland, *Moran Model, *Kaczmarek Model
                                     577

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013F

QUANTITATIVE ESTIMATION OF DISINFECTION INTERFERENCES,

Hall, E. S.

Water Research Association

Journal of the Society for Water Treatment & Examinations, Vol. 22, No. 3,
p 153-174, 1973.  9 fig, 14 ref.

The inactivation of microorganisms and the reaction of chemical interferences
with disinfectant at rates proportional to their concentration conform with
the equation,-log base 10 (proportional survival of organism or residual
interference) -kD/2.303, where D is the concentration of disinfectant inte-
grated over time and k is a constant.  Experimental data do not usually con-
form with the equation because more than one degree of susceptibility to
disinfection or oxidation prevails.  Within a certain range of values of D,
however, data can be processed to conform and yield a value for k.  The relation-
ship between dose of disinfectant and contact time for a given value of dis-
infection level can then be calculated.  Using exiting constants for ammonia
free chlorine reactions, progress in the formation of chloramines may be
related to disinfection level.  This enables optimum design of plant and
disinfection control systems for a disinfection level appropriate to the
water source.

*Microorganisms, *Disinfection, *Equations, Chlorine, Ammonia, Treatment
Methods, *Mathematical Models

Disinfectants
OUF

A COMPARISON OF PHYSICALLY-BASED INFILTRATION EQUATIONS,

Swartzendruber, D., and Youngs, E. G.

Agricultural Research Council Unit of Soil Physics,
Huntingdon Road, Cambridge, England

Soil  Science, Vol. 117, No. 3, p 165-167, March, 1974.  1 fig, 10 ref.

Three infiltration equations derived from a consideration of  the physics  of
flow  through porous media are compared quantitatively over  time from  zero to
infinity.  Compared with the Green and Ampt equation, the two-term Philip
equation is never more than 15.1 percent higher, while  the  equation arising
out of Philip's linearization analysis is never less than 9.2 percent lower.
For practical use these discrepancies may be ignored.   Because of its
mathematical simplicity and adaptability, the two-term  Philip equation,
however, would be the preferred choice.

*Model Studies, *Infiltration, *Mathematical Studies, Equations

*Infiltration Equations, Green Equation, Ampt Equation, Philip Equation
                                    578

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015F

OPERATIONAL CONTROL CONCEPTS FOR THE ACTIVATED SLUDGE PROCESS,

Sherrard, J. H., and Kincannon, D. F.

School of Civil Engineering, Oklahoma State University.

Water & Sewage Works, Vol. 121, No. 3, p 44, 56, 64, 66, March, 1974.
2  fig, 2 tab, 4 ref.

Control schemes advocated  for recycling activated sludge processes frequently
are based on empirical observation.  Input of scientific knowledge to control
models has been minimal.   As a  result of the use of microbial continuous
culture theory for describing process relationships, several advances toward
the understanding of basic process fundamentals have recently been made.
This article illustrates the effect of altering process control variables
by the development of mathematical relationships that are descriptive of the
activated sludge process,  presentation of data obtained in a laboratory model
activated sludge unit, and integration of data and equations to explain the
consequences of altering process control variables available to the
treatment plant operator.

Model Studies, *Mathematical models, *Activated sludge, Equations,
*Treatment methods, Recycling,  Microorganisms

*Continuous culture theory
016F

DESIGNING?  PLUG IN A COMPUTER,

Brill, F. W.

Spotts, Stevens & McCoy, Wyomissing, Pennsylvania

Water and Wastes Engineering, Vol. 11, No. 2, p 39-41, February, 1974.  2 fig.

Programs can be written in such a way that they can be of help in designing
small installations where it is impossible to determine the design variables
accurately, for example in biological waste treatment plants.  The answers
given by the computers would be approximate, and would allow selected values
to be changed without disturbing any others.  Such a program permits the user
to try many designs on paper and to determine the effect of ranges of values
of design variables.  All this is possible using Basic or Fortran computer
languages in such a way that the user need not know either language.  An
example is given to illustrate this method using the mathematics given
by L.G. Rich in "Unit Processes of Sanitary Engineering."

Automation, Instrumentation, *Waste water Treatment, Engineering, *Computers,
*Plant Design
                                        579

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017F

INFILTRATION INTO A SWELLING MATERIAL,

Smiles, D. E.

CSIRO, Canberra City, Australia

Soil Science, Vol. 117, No. 3, p 140-147, March, 1974.  4 fig, 11 ref.

The process of infiltration into a swelling material is discussed and
some of J. R. Philip's prediction on the properties of flow in swelling
systems are reexamined.  Because of a paucity of experimental data on
these materials Philip's was forced to use plausible arbitrary properties
for his illustrative calculations.  A saturated clay was used and results
in considerable simplification of the mathematics while the essential
characteristics of the swelling phenomenon, in the gravitational field, are
retained.  As Philip predicts, infiltration in swelling materials has more
in common physically with capillary rise than with infiltration in a rigid
soil.  This arises because in a saturated swelling soil infiltration is
accompanied by a net increase in the gravitational potential energy of
the system.  Infiltration in a rigid soil results in a decrease in the
potential energy of the water while that of the solid is unchanged.  The
net increase in the potential energy of the system together with the flow
properties of swelling clays results in the sorption component of the
infiltration process being temporarily more persistent, by several orders
of magnitude, than is the case for rigid soils.

*Infiltration, Flow, Clays, Theoretical Analysis, Soils, Soil Water Movement,
Soil Structure, Soil Texture

Swelling, Soils
018F

COMPARISON OF NUMERICAL METHODS SOLVING FLOW THROUGH POROUS MEDIA
(EIN VERGLEICH VON NUMERISCHEN VERFAHREN ZUR LOESUNG VON
SICKERSTROEMUNGEN),

Luehr, H. P.

University of Karlsruhe, Karlsruhe, West Germany.

La Houille Blanche, No. 5-6, p 433-434, 1973.  2 ref.

Numerical methods of solving flow through porous media are compared and
a cost effectiveness analysis was made.  Digital solution methods generally
are considerably more effective than analytical and analogous methods.
Either finite elements or finite differences can be used in the digital
solution method, and both methods produce discrete solutions of given
problems.  The comparison of both methods is done by significant criteria:
the required core storage, the required computing time, and the flexibi-
lity of the methods approximating the problems.  As the core storage and
the computing time directly depend on the organization technique and the
algorithm solving linear equation systems, special organization techniques
are discussed.  The flexibility is seen in dependence on physical problems.
Finite differences are better than finite elements in terms of organization
and programming and should be used to solve flow problems through porous
media.  For problems involving an automatic search of free surfaces, the
method of finite elements appears to be more suitable.

*Numerical Analysis, *Flow Measurement, *Porous Media, Finite Element
Analysis, Cost-Benefit Analysis

Germany, Finite Differences Analysis


                                             580

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019F

WASTE NEUTRALIZATION CONTROL - DIGITAL SIMULATION SPOTS
NONLINEARITIES,

Richter, J. D., Fournier, C. D., Ash, R. H., and
Marcikic, S.

University of Cincinnati

Instrumentation Technology, Vol. 21, No. 4, p 35-40, April, 1974.  8 fig, 8 ref.

A generalized model to study the effect of influent composition variations on
pH control was designed to study performance in a treatment plant before
installation of equipment.  It was found that in the nonlinear situation
there is no simple functional relationship between concentration of a single
ionic species and pH.  Equilibrium calculations based on mass balances for
each component are required to predict the response.

*Model Studies, Digital Computers, *Hydrogen Ion Concentration, *Waste Water
Treatment, Mathematical Models
020F

WATERHEAD FORECAST POSSIBILITIES ON HYDRAULIC BASIS,

Kozak, M.

Acta Technica Academiae Scientiarum Hungaricae, Vol. 75, No. 1-4, p 219-233,
1973.  4 fig, 4 tab, 21 ref.

Forecasting the water level of rivers is an important water management activity.
General solution of the problem may be arrived at by discussing it on a
deterministic basis.  Economic solution of the differential equation system
describing the phenomenon was made feasible by digital calculation engineering.
The implicit method, combined with an iteration process, is employed for
forecasting.

*Mathematical Models, *Rivers, *Hydraulics, *Water Levels, *River Forecasting,
Digital Computers
                                     581

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021F

NUMERICAL COMPUTATION OF MOMENTUM JETS AND FORCED PLUMES,

Trent, D. S. and Welty, J. R.

Battelle Pacific Northwest Laboratories, Richland, Wash.

Computer and Fluids, Vol. 1, No. 4, p 331-357,  December,  1973.   24 fig,  1 tab,
17 ref.

A numerical study of vertical momentum jets and forced plumes issuing to similar
receiving media is presented.  The complete partial differential equations
governing steady, incompressible, turbulent flow are solved in axisymmetric
coordinates using finite difference techniques.  Solutions were based on the
stream function vorticity transport approach for a Boussineq fluid.   Buoyant
driving forces were coupled to the vorticity equation which included effects
of temperature and other constituents.  Turbulent transport coefficients were
computed iteratively using the Prandtl eddy diffusivity model.   Results  for the
momentum jet, axial, and radial distributions of velocity and concentration,
show excellent agreement with published data.  Forced plume computations are
presented which include similar results for densimetric Froude numbers ranging
from 1 to 1000.

*Mathematical Studies, *Equations, *Model Studies, Turbulent Flow
022F

HOUSEHOLD WASTEWATER CHARACTERIZATION,

Ligman, K., Hutzler, N., and Boyle, W. C.

Baxter and Woodman, Inc., Crystal Lake, 111.

Journal of the Environmental Engineering Division, Vol. 100, No. EE1, p 201-
213, February, 1974.  9 tab, 46 ref.

The types of waste waters generated in a domestic household and their respective
waste water characteristics were defined through the use of a waste water genera-
tion survey, a waste water sampling survey, and literature reviews.  Based on
data collected, a simulated waste loading was adopted for use in waste water
treatment and disposal studies.  The average four person household uses 190
gallons of water a day generating 0.695 Ib/day BOD5 and 0.797 Ib/day of sus-
pended solids.  Current research efforts employing this simulated waste water
loading will define the limitations and operational requirements of given unit
processes to meet a requisite water quality for ultimate disposal.

*Waste Water, *Surveys, *Suspended Solids, *Waste Disposal, Sampling, Domes-
tic Wastes, Biochemical Oxygen Demand, Water Quality
                                           582

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  023F

  THE INVESTIGATION OF BIOGRADABILITY OF BRANCHED NONYL
  PHENOL ETHOXYLATES,

  Rudling,  L.  and Solyom,  P.

  Swedish Water and Air Pollution Research Laboratory,
  Stockholm,  Sweden

  Water Research, Vol. 8,  No.  2,  p 115-119, 1974.  4 fig,  2 tab, 7 ref.

  The biogradability of branched chain nonyl phenol ethoxylates was investigated
  according to a screening test procedure recommended by OECD and by a study con-
  ducted in a laboratory-scale activated sludge system operated with presettled
  municipal sewage under treatment plants.  The results show that there is no
  significant difference between the biogradability of the different nonyl phenol
  ethoxylates containing 8-30  ethylene oxide groups.  The removal of surfactants
  exceeds 90% and no acclimatization was needed in activated sludge treatment
  under plant conditions.

  *Activated Sludge, *Investigations, *Biodegradation, *Phenols, Municipal
  Wastes, Sewage, Surfactants

  *Sweden, *Nonyl Phenol Ethoxylates
024F

ESTIMATION AND EVALUATION OF RADIOACTIVE CONTAMINATION
THROUGH A FOOD WEB IN AN AQUATIC ECOSYSTEM  (1).

Aoyama, I., and Inoue, Y.

Journal of Radiation Research, Vol. 14, No. 4, p 375-381, December, 1973.
11 refs.

A transfer of radioactive substance through a food chain in an aquatic
ecosystem was analyzed through application of modified three compartment
model of Aten's.  The modification consists of an excretion of radioactivity
from Fish-1 (preys) to sea water and an direct uptake of radioactivity by
Fish-2 (predator) from sea water.  In the experimental system, pike cichlids
and minows were used as predators and preys, and the Cesium 137 isotope was
used as a radionuclide in the system.  The accumulation of a 137 Cs in pike
was explained by application of the modified model and various parameters
in the model were determined.  The transfer or a radionuclide through a food
chain can be estimated by knowing the uptake rate and the turnover rate of
the predator.  In econological termonology, they are a daily average ration
and an assimilation rate respectively.

Food chains, Radioactive wastes, Radioactive waste disposal, Aquatic
environment, Fish, Predation, Prey fish, Investigations, Food webs,
Ecosystems, Model studies

Japan
                                            583

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025F

MODEL STUDIES ON REACTIONS OCCURRING IN OXIDATIONS OF LIGNIN
WITH MOLECULAR OXYGEN IN ALKALINE MEDIA,

Kratzl, K., Claus, P., Lonsky, W., and Gratzl, J. S.

Vienna University, Institute of Organic Chemistry, Vienna,
Austria

Food Science and Technology, Vol. 8, No. 1, p 35-49, 1974.  12 fig, 47 ref.

The degradation of lignin in oxidation with molecular oxygen is discussed
emphasizing the radical (hotnolytic) or one-electron transfer-oxidations in
the initial phase of the basic reaction.  The critical oxidation potentials
(COP) according to Ficser represent a useful measure for the ease of
electron release from lignin-related phenolic models.  At low alkalinity
rough correlation were observed between the measured COPs and the initial
oxygenation rates.  The results obtained from quantum mechanical calcula-
tions of critical oxidation potentials are discussed briefly.  The impor-
tance of phenoxy radicals and the hypothetical cyclohexadienone hydroperoxides
as intermediates is outlined in view of such degradation reactions as oxi-
dative side-chain eliminations, demethoxylations, and splitting of aromatic
rings.

*Lignins, Oxidation, *Model Studies, Measurement, Alkalis (Bases),

*Molecular Oxygen, *Critical Oxidation Potentials
  026F

  SOME LESSONS FROM MODEL AND FULL-SCALE TESTS IN RECTANGULAR
  SEDIMENTATION TANKS,

  Price, G. A., and Clements, M. S.

  I.C.I. Ltd., Mond Division, Runcorn, England

  Water Pollution Control, Vol. 78, No. 1, p 102-113, 1974.  8 fig, 11 tab,
  7 ref.

  Results of research into the effects of inlet changes, density and wind-induced
  currents on the performance of rectangular sedimentation tanks are summarized.
  The investigation included experiments on both models and on full-scale
  tanks at six sewage works to test the importance of time ratio and inlet design
  on the efficiency of tanks.  Time ratio is a measure of the streaming through
  the tank and defined as the ratio of effective flow-through time to
  effective settling time with an ideal value of unity.

  *Model studies, *0n-site tests, *Settling basins, Sedimentation, Treatment
  facilities, Efficiencies, Intakes


  Inlet design, Flow-through time, Settling time
                                           584

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027F

STOCHASTIC ANALYSIS OF ORTHOKINETIC FLOCCULATION,

Cockerham, P. W., and Himmelblau, D. M.

Wright-Patterson Air Force Base, Ohio

Journal of the Environmental Engineering Division, Vol. 100, No. EE2,
p 279-293, April, 1973.  8 fig, 1 tab, 7 ref.

The application of a stochastic analysis to orthoklnetic flocculation, a
common operation in water treatment, is illustrated.  Both the unsteady-state
and the steady-sample response could be represented by a normal distribution
regardless of the types of distributions used for the flocculation model
inputs and parameters.  The sample mean response agreed with the deterministic
solution if normal distributions are used for the flocculation model inputs
and parameters, but not otherwise.  Dispersion in the model parameter had
a greater effect on the dispersion of the sample output than did the model
parameters.  Dispersion in G (the root mean squared velocity gradient) had
the least effect on the dispersion of the sample output.  The degree of
dispersion in the process flow rate had little effect on the flocculator
overdesign factor.  The stochastic approach is applicable to the stochastic
analysis of other important processes in water and waste water treatment.
Of particular value is the method of calculating overdesign factors.  The
stochastic approach does not reduce the uncertainty involved in the
processes, but it does allow one to make more objective decisions about the
uncertainty.  This is becoming more and more important as effluent quality
standards become more stringent.

*Stochastic processes, *Flocculation, Water treatment, Model studies,
Dispersion, Waste water treatment, Statistical methods
028F

WINTER-REGIME THERMAL RESPONSE OF HEATED STREAMS,

Paily, P. P., Macagno, E. 0., and Kennedy, J. F.

Iowa University, Iowa City, Iowa, Institute of Hydraulic
Research

Proceedings of the American Society of Civil Engineers, Journal of the
Hydraulics Division, Vol. 100, No. HY4, p 531-551, April, 1974.  9 fig,
1 tab, 13 ref.

The mathematical formulation is derived of a closed form solution of the
unsteady one dimensional convection diffusion equation for the temperature
distribution downstream from the point at which a thermal load is imposed.
It is based on the assumption that complete mixing of the heated water with
the river flow occurs both vertically and laterally at all sections of the
stream, including the discharge section itself.  The river is treated as
uniform.  In the course of the derivation, it is demonstrated that the surface
heat exchange term appearing in the governing equation can be expressed,
without significant loss of accuracy, as a linear function of the mixed
temperature of the stream.  The results may provide slightly increased values
of temperature, since the effect of linearizing the heat loss rate is slightly
to underestimate its magnitude.  The heat of fusion required for the melting
of ice has been neglected in the formulation so that the predicted lengths
of ice free reaches may be overestimated.  The accuracy of the solution to
predict winter time conditions in heated rivers needs to be checked by field
observations.

*Mathematical studies, *Convection, *Diffusion, *Equations, *Teraperature
distribution, Downstream, Rivers, Mixing, Heat transfer, Heater water,
Heat balance, Ice


                                         585

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 029F

 SCALE-UP  OF  SOLID BOWL  CENTRIFUGE PERFORMANCE,

 Vesilind,  P. A.

 Duke University, Durham, N.  C., Department of Civil
 Engineering

 Journal of the  Environmental Engineering Division, Vol. 100, No. EE2,
 p  479-486, April, 1974.  2  fig, 1 tab,  2 ref.

 A  method  for calculating centrifuge  capacities based on data from continuous
 geometrically similar models is proposed.  It is usually not possible  to
 determine from  field test data if performance is limited by hydraulic  or
 solids capacity.  Scale-up  must be in terms of both solids and hydraulic
 loading.   The hydraulic capacity of  a larger solid bowl centrifuge can be
 estimated on the basis of data for a geometrically similar one operating
 on the same  slurry, by  the  relationships:  (Q sub L)sub 2 = (Q sub L/S) sub 1
 (S)  sub 2.   The solids handling capacity can be estimated as (Q sub s) sub 2 =
 (Q sub s/beta)  sub 1 (beta)  sub 2.   Beta is equal to pi delta sigma ADNP.  The
 lowest rate  thus determined  will limit  performance and must be used for
 scale-up.

 *Centrifugation, *Numerical  analysis, *Model studies, *Solid wastes,
 *Waste disposal, Separation  techniques, Hydraulic properties.

 *Solid bowl  centrifuge.
030F

PITFALLS IN PARAMETER ESTIMATION FOR OXYGEN TRANSFER
DATA,

Boyle, W. C., Berthouex, P. M.,  and Rooney, T. C.

Wisconsin University, Madison, Wisconsin

Journal of the Environmental Engineering Division, Vol. 100, No. EE2,
P 391-408, April, 1974.  10 fig, 4 tab, 8 ref.

Some of the pitfalls of methods  of parameter estimation applicable to the
analysis of oxygen transfer data are examined.  The following must be
considered:  know the error structure of the data and apply appropriate
weighting procedures in the analysis of the data; corroborate the value
of the dissolved oxygen saturation concentration employed to estimate the
overall oxygen transfer coefficient (K) through experimental data for a
given physical arrangement of aeration and basin geometry.  Truncation of
an aeration test before reaching saturation can produce substantial error in
estimates of K unless a precise  estimate of the dissolved oxygen concentration
(C)  can be determined.  Truncation of dissolved oxygen data up to 20% will
not effect the precision of the  estimate of K.  The product of KC tends to
compensate for errors in K and C and will normally give reasonable estimates
of the oxygen transfer rate.  Poor estimates of C will tend to produce
substantial error in the calculation of oxygen transfer rates.

*Model studies, *Estimates, *Aeration, Analytical techniques, Numerical
analysis, Oxygen

*0xygen transfer data
                                        586

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031F

VARIATION OF REGIME COEFFICIENTS IN PAKISTAN CANALS,

Mahmood, K.

Colorado State University, Fort Collins, Colorado, Civil
Engineering Department

Journal of the Waterways Harbors and Coastal Engineering Division, Vol. 100,
No. WW2, p 85-104, May, 1974.  9 fig, 4 tab, 15 ref.

The regime theory, assuming that the channel has been self-formed in an inco-
herent alluvium by a steady discharge, is not entirely applicable to man-made
channels.  Here,  the Canal and Headworks Data Observation Program (CHOP) carried
out an extensive  program of data observation on the headworks, silt excluders,
and canals in the irrigation system of Pakistan, to test the  theory.  To inter-
pret regime coefficients, some factors on morphology of a nonbranching alluvial
channel are:  flow discharge; bed material size, gradation, and particle shape,
bed material load inflow, its size and gradation; quantity of fine material
load and its chemical composition; water temperature; and channel bed and bank
maintenance practices.  By studying equations, CHOP data concluded that the
three degrees-of-freedom can be represented by regime coefficients alpha one,
alpha three and alpha four, or by the rigid boundary hydraulics parameters
Froude number of  flow, width-depth ratio of channel section,  and energy gradi-
ent.  The canals  do not adjust their widths rapidly.  There is an inverse rela-
tion between silt factors and alpha four, involving discharge, median bed ma-
terial size, and  kinematic viscosity, but not alpha three.  One degree-of-free-
dom found is related to a silt factor, FVR, and is governed by the bed material
transport function for the channel and the current bed material load.

*Model studies, *Canals, *Alluvial channels, Irrigation systems, Channel mor-
phology, Regime,  Silt, Flow, Beds, Hydraulics

*Pakistan, Canal  and Headworks Data Observation Program, Regime coefficients,
Headworks, Silt excluders
032F

OPTIMAL CONJUNCTIVE USE MODEL FOR INDUS BASIN,

Chaudhry, M. T., Labadie, J. W., Hall, W. A., and Albert-
son, M. L.

Colorado State University, Fort Collins, Colorado, Depart-
ment of Civil Engineering

Journal of Hydraulics Division, Vol. 100, No. HY5, p 667-687, May, 1974.  4 fig,
16 ref.

Proper development and management of water in an arid region such as Pakistan
is important.  The production of food can be maintained if and only if scarce
water resources are properly used.   Optimizing analytical models for the sys-
tem is a complex problem, involving conjuctive use of surface and groundwater
resources.  A mathematical model is presented here, which takes into account
costs and benefits.  It is applicable only to the Indus Basin irrigation
system.

*Costs, *Water management (applied), *Groundwater, *Surface waters, Arid
climates, Irrigation system

*Indus Basin, *Paklstan, Food production
                                    587

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033F

NATIONAL WEATHER SERVICE RIVER FORECASTING SYSTEM,

Monro, J. C., and Anderson, E. A.

National Weather Service, National Oceanic and Atmos-
pheric Administration, Silver Spring, Maryland, Office
of Hydrology

Journal of the Hydraulics Division, Vol. 100, No. HY5, p 621-630, May, 1974.
12 ref.

Major changes are occurring at the National Weather Service in the area of
research and development about river forecasting service.   The purpose, objec-
tives, current components, and proposed additions are given in this paper.
Computer programs for efficient operational use of a conceptual hydrologic
model of forecasting are noted.  A large number of basins  may be calibrated
in a reasonable time; the model has wide applicability.  New plans for including
a snow-pack model and additions to the channel-routing procedure may make it
practical for the whole United States.

*Model studies, *Computers, *Rivers, *Hydraulics, *River forecasting, Hydro-
logic models, Basins, Research and development

*National Weather Service, Basin calibrations
034F

COMPUTER SIMULATION OF WASTEWATER TREATMENT BY CHEMICAL-PHYSICAL
PROCESSES,

Anand, A., Gibbs, J., Laughlin, Jr., W. C., and Sherwood,
R. J.

Envirotech Corporation

Effluent and Water Treatment Journal, Vol. 14, No. 3, p 155-160, March,
1974.  2 fig, 3 tab, 5 ref.

The increasing demand for high-quality effluents and more stringent waste-
water treatment standards have made chemical-physical wastewater treatment
a viable alternative to conventional biological plus tertiary processes.
Experience in chemical-physical treatment is rather limited and the pro-
cesses themselves raise a number of important questions related to design,
operation and costs.  It is both the number and complexity of these questions
that makes the proper analysis of these treatment processes so difficult.
A flow sheet is given which illustrates treatment options in the chemical-
physical treatment of municipal wastewater.  The flow sheet was developed
from a computer simulation model which is accurate, rapid, and flexible.

*Waste water treatment, *Model studies, *Computer models, *Simulation, *Estimated
costs
*Chemical-physical treatment
                                         588

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035F

A FINITE ELEMENT APPROACH TO WATERSHED RUNOFF,

Taylor, C., Al-Mashidani, G., and Davis, J. M.

University College, Swansea, Great Britain,
Department of Civil Engineering

Journal of Hydrology, Vol. 21, No. 3, p 231-246, 1974.

Watershed direct runoff problems are analyzed by a numerical finite
element-based implicit recurrence relationship.   The algorithm is shown in a
two dimensional form for the full momentum and continuity equations.   It is
presented unidimensionally for the kinematic wave theory.  Because the whole
domain is represented and solved as a single set of matrix equations, the
advent of shocks for domains where appreciable changes in slope and/or
resistance to flow occur, is immediately recognizable.

*Model studies, *Slmulation, *Mathematical models, *Watershed management,
*Runoff


*Algorithm
036F

A MATHEMATICAL EXAMINATION OF URBAN RUN-OFF PREDICTION,

Newton, S. G., and Painter, R. B.

Institute of Hydrology, Wallingford

The Institution of Civil Engineers, Vol. 57, Part 2, p 143-157, March, 1974.
11 fig, 12 ref.

A rigorous mathematical examination of the more frequently used methods of
predicting urban runoff is given as a means of assessing their true limitations,
and of indicating where improvements should be made.  The study was prompted by
the problem of prediction of the amount and distribution of storm runoff
from impervious areas and subsequent modifications made in the pipe network.
It was found that the rational formula for determining the peak runoff from
a catchment allows for changes in storage in pipes and for variations with
time of the rainfall.  It can be generalized to give the discharge as a
function of time.  The area-time method allows for the variation in width of
the catchment and the change in slope with position.  A program of theoretical
and experimental research is under way to investigate the surface runoff process
further.

*Model studies, *Mathematical models, *Runoff, *Storm water, *Urban
runoff, *Rational formula, Sewers, Storm drains
                                       589

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037F

DEVICES FOR THE PRE-DILUTION OF SEWAGE AT SUBMERGED
OUTFALLS,

Agg, A. R., and White, W. R.

Senior Scientific Officer, Water Pollution
Research Laboratory

The Institution of Civil Engineers, Vol. 57, Part 2, p 1-20, March, 1974.
15 fig, 4 tab, 7 ref.

An analysis and arrangement of the parameters governing the dilution of
sewage discharged from submerged outfalls is presented.  This form of display
indicates that the most efficient outfall in terms of maximum dilution at the
water surface, operates at a densimetric Froude number of unity.  Six possible
designs for devices to achieve pre-dilution of sewage before discharge from
a submerged outfall are also described, and comparative experiments in a
physical model to assess their performance are reported.  Experiments carried
out subsequently on four variations of the most promising device are also
compared.  The efficiency of the device in increasing dilution at the surface
in different depths of water is discussed.

*Model studies, *Waste water treatment, *Mathematical studies, *0utfall sewers,
Sewers, Sewage treatment, Waste dilution

*Submerged outfalls
038F

A SCHEME FOR ASSESSING THE RELIABILITY OF INTERPOLATED RAINFALL
ESTIMATES,

Kelway, P. S.

The University of Birmingham, Birmingham,
Great Britain, Department of Civil Engineering

Journal of Hydrology, Vol. 21, No. 3, p 247-267, 1974.  5 fig, 9 tab, 8 ref.

Quantification of the significance of variables controlling the reliability
of interpolated estimates of rainfe1,! is attempted.  Alternative ways of
expressing the gauge network and rainfall distribution patterns in a form that
may be used in estimating equations for assessing error in interpolated values
are examined.  A scheme is devised for obtaining equations analytically for any
interpolation method used to derive information; the results of a study
relevant to a specific analysis technique are shown.  The purpose of the
scheme is to enable confidence limits to be placed on interpolated output
during computer processing of rainfall data.  Comparisons may then be made
between available analytical techniques, results being assessed under opera-
tional conditions.  Once a user has selected a suitable method of analysis,
the factors likely to control the accuracy of the information produced are
monitored during processing and likely tolerance limits are given for output
values.

*Model studies, *Computer models, *Stimulation, *Rainfall, *Hydrologic cycle,
Rain gages, Distribution patterns, Forecasting
                                           590

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039F

SEWERAGE SYSTEMS DESIGN,

Computer Aided Design, Vol. 6, No. 1, p 54-55, January, 1974.

An integrated computer based system for the design of sewerage systems and for
the automatic production by computer of drawings and contract documents has
been developed by General and Engineering Computer Services, Ltd., Liverpool,
England.  The programs are totally interlinked which reduces to a minimum the
manual production of information, yet permits the engineer to intervene at all
stages of the design process to overwrite and to amend the computerized design.
There are seven individual program modules:  master file creation and control
programs; optimization; hydraulic calculations; pipe strength and class of bed-
ding; automatic drawings; estimates and K29 form; and bill of quantities.

*Computers, *Sewerage, Data storage and retrieval, Data processing, Documenta-
tion, Optimization, Hydraulic design, Pipes, Automation, Estimating, Data col-
lections

England
040F

ON THE VARIANCE OF THE STATIONARY PROBABILITY VECTOR FOR
A FINITE DAM,

Jarvis, C. L.

Australian National University, Canberra, Australia,
Computer Centre

Journal of Hydrology, Vol. 21, No. 3, p 291-297, 1974.  3 tab, 5 ref.

A method for estimating the variance of the stationary probability vector for
the finite dam is discussed.  The method relies upon the constancy of a gradient
matrix in the vicinity of the solution and a simple numerical differentiation
technique is found to be adequate.  An example of the variance calculation is
given by applying the method to streamflow data previously used in an application
of Moran's theory of dam to the Ord River project.

*Probability, *Dams, *Mathematical models, Streamflow, Numerical analysis,
Rivers

*Stationary probability vector, Ord River, (Australia), Australia, Netherlands
                                         591

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041F

THE DESIGN AND OPERATION OF ACTIVATED SLUDGE FINAL SET-
TLING TANKS,

Hibberd, R. L., and Jones, W. F.

Satec Limited, Crewe, England

Water Pollution Control, Vol. 78, No. 1, p 14-32, 1974.  13 fig,  9 tab,  11 ref.

The design and operation of activated sludge final settling tanks were investi-
gated in laboratory studies.  Three aspects of the tank operation are important:
the production of a clarified effluent under all flow and sludge  conditions;
the return of a concentrated underflow to maintain MLSS concentrations,  and
the prevention of excessive solids retention periods under anaerobic conditions.
The theoretical analysis of sludge thickening overestimates the solids handling
capacity of the final tank.  The error in the prediction can be related  to
sludge bed depth and return sludge rate by conducting laboratory  continuous tes
tests.  The extent to which the laboratory results can be applied to full scale
tank performance depends upon the degree of flocculation obtained in the tank and
the uniformity of flow distribution over the plan area.  A tank design approach
to maintain clarification at all flow conditions is suggested.  This is based
on providing sufficient capacity for dry weather flow loading with shallow bed
depths in the tanks, and ensuring that an excessive increase in bed depth does
not occur during high flows.  The criteria derived will vary with the aeration
unit size and the MLSS concentration required, and assumes that a low bed depth
will be maintained under low flow conditions.

*Activated sludge, *Settling basins, *Evaluation, Design, Operating, Analysis,
Effluents, Anaerobic conditions, Sludges, Laboratory tests, Flow, Suspended
solids
England
042F

VALIDITY OF THE MODIFIED BILHAM EQUATION,

Ashworth, R. G., and O'Flaherty, C. A.

West Riding County Council, England, Highways and
Bridges Department

Institution of Municipal Engineers, Vol. 101, No. 2, p 43-50, February, 1974.
12 fig, 15 ref.

The validity of the modified Bilham equation was investigated to illustrate the
extent to which rainfall intensities associated with different storm durations
and return periods can vary in England.  The results indicate that the modified
Bilham relationship can give intensity results for particular areas of the
country which are significantly different from the true values.  This can result
in the overdesign or underdesign of drainage facilities.  To minimize the was-
tage drainage facilities, more emphasis be placed on local conditions.  Govern-
ment guidelines should be compared with that given for the locality in the
appropriate isopleth diagram.  If the two values differ significantly, the
Meteorological Office should be consulted regarding the advis-ab'ility of using
local rainfall data to determine, more appropriate, intensity values.

*Rainfall intensity, *Forecasting, Storms, Drainage systems, Design

Bilham Equation, England, Isopleth diagrams
                                          592

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043F

THE ANALYSIS OF SOME MONTHLY HYDROLOGIC TIME SERIES,

Torelli, L.

S. Lorenzo in Campo, Pesaro, Italy

Journal of Hydrology, Vol. 21, No. 3, p 269-290, 1974.  7 fig, 3 tab, 9 ref.

The following time series are analyzed:  monthly average temperatures at Urbana,
Illinois (1915-1965); monthly precipitations at Morrisonville, Illinois (1896-
1969); and monthly streamflows in the Sangamon River at Monticello, Illinois
(1915-1969).  The model was previously identified and showed  that a simple
transformation makes the series stationary.  The analysis was completed.  By
a joint use of spectral and regression analysis one arrives at the formulation
of models in which the deterministic process and the variaces are described
by means of trigonometric functions.  This allows a considerable economy of
parameters in comparison with the models based on the 24 sample monthly averages
and variances.  The practical advantages of such an economy of parameters are
discussed.

*Time series analysis, *Monthly, Temperature, Precipitation (Atmospheric),
Streamflow, Hydrographs, Mathematical models

Urbana, Illinois, Morrisonville, Illinois, Sangamon River, Monticello, Illinois,
Italy, Netherlands
044F

A MATHEMATICAL MODEL OF A RIVER PURIFICATION LAKE,

Chapman, B. T.

Severn River Authority, England

Water Treatment and Examination, Vol. 22, No. 4, p 269-291, 1973.  18 fig, 14 ref.

A mathematical model was developed of a river purification lake to predict the
effect of various retention times on the quality of the lake effluent.  The re-
sults showed that doubling the experimental retention time to 9.6 days would not
remove the smallest particles, but halving the retention time to 2.4 days pro-
duced a deterioration in the effluent quality.  The removal of soluble organic
carbon within the lake was 21% of the Influent concentration at 9.6 days reten-
tion and 6% at 2.4 days retention.  The model predicted that, with a retention
time of 9.6 days, by the middle of May the chlorophyll-a concentration in the
lake would exceed 100 mg/cu m and would continue to increase throughout the summer.
If this happened, the water would become extremely dark green with a skin of
algae present on the surface.  A retention period of only 2.4 days meant that the
predicted chlorophyll-a concentration were only slightly greater than the
concentration of the influent, showing that production was taking place only to
a small extent.  The maximum predicted chlorophyll-a concentration was 21 mg/cu
m.  The dissolved oxygen concentration was not predicted to fall below 3 mg/liter
under any retention time.

*Mathematical models, *Retention, *Water quality, *Effluents, *Lakes, Organic
matter, Influents, Chlorophyll, Algae, Dissolved oxygen, Treatment facilities,
Sedimentation, Computers

Great Britain
                                          593

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045F

A PREDICTIVE MODEL FOR SLUDGE CHARACTERIZATION USEFUL TO
DESIGN AND CONTROL OF SLUDGE DEWATERING PROCESSES IN WA-
TER RECYCLE SYSTEMS,

Bobalek, E. G., Durst, R. E., and Yadeta, B.

University of Maine, Orono, Maine, Environmental Studies
Center

Report No. 1-74, Project No. B-008-ME.  110 p, July, 1973.  22 fig, 10 tab, 37
ref.

An empirical correlation was developed relating the filterability of synthetic
slurries to the hydrophilic character of the resulting filter calces and the
filtration driving force.  The hydrophilic character was evaluated by determining
the bound water corresponding to 99% saturation of the filter cake samples as
indicated by the vapor pressure at a fixed temperature, while the driving force
was provided by a differential pressure system.  The experimental data was cor-
related using dimensionless variables and the results indicated that a fixed bound
water the dependence of filterability on the driving force group was almost
linear, while at a constant driving force a one cycle change in bound water
resulted in a two cycle change in the filterability.  It is concluded that
the filterability of synthetic slurries correlates inversely with the hydrophilic
character of resultant filter cakes, where such a characteristic is defined
and measured as the equilibrium bound water in the filter cakes at a standar-
dized temperature.  No single mechanism of water binding is found sufficient
to account for the total bound water in colloid modified solid liquid systems.
The relationship between bound water and filterability is a proper index of
filterability independent of slurry composition.

*Bound water, *Filtration, *Model studies, Slurries, Filters, Industrial
wastes, Municipal wastes, Sludge, Dewatering, Water reuse, Fluid mechanics
046F

WATER POLLUTION BEING FOUGHT BY COMPUTER,

The American City, Vol. 89, No. 5, p 71-72, May, 1974.

The Miami Conservancy District of Dayton, Ohio is collecting massive data on
river use to determine factors that influence water quality.  By using the data
given the computer, both real and projected conditions can be simulated and fore-
cast.  The costs of the program are distributed among 20 municipal and county
treatment plants, 15 paper mills, 20 other industries, 5 power plants and 5
counties, in proportion to how much they discharge into the river.  Each engineer
of the district must do computer operating, collecting printouts.  These are
statistical reports on flow or pollution conditions, with which other factors—
such as influent or effluent rates—may be compared.

*Computer studies, *Models, *Engineers, *Water quality control, Rivers, Ohio,
Simulation, Municipal wastes, Industrial wastes, Costs, Flow, Pollution, Ef-
fluents, Conservation, Data collections, Treatment facilities

River use
                                        594

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04 7F

CONTROL OF ANAEROBIC DIGESTION PROCESS,

Collins, A. S., and Gllliland, B. E.

Combustion Engineering, Windsor, Connecticut, Nuclear
Steam Supply Systems

Journal of the Environmental Engineering Division, Vol. 100, No. EE2, p 487-
506, April, 1974.

Waste water treatment plants are currently based mainly on steady-state rela-
tionships rather than dynamic models.  However, variations occur in biological
processes due to flow rates, organic matter concentrations, and BOD removal
efficiency fluctuations.  A dynamic model for the anaerobic digestion process
has shown to be meaningful by Clemson University.  This process considers pH
response due to organic and hydraulic overloads.  The results are based on the
Andrews-Graef digester model, as simulated using Fortran IV.  It was found
that when predictive flow control is used with feedforward base addition as con-
tinuous compensation, base addition and flow rate are excessive.  Reduction of
the gain of the feedforward controller results in most desireable performance.

*Models, *Waste water treatment, *Anaerobic digestion, Flow rates, Biochemical
oxygen demand, Fortran IV, Plants, Computer studies, Activated sludge, Organic
matter
Overloads, Hydraulic overloads, Organic overloads, Digester model, Dynamic
models, pH
048F

AN APPROXIMATE NUMBERICAL SOLUTION OF A POLLUTANT DISPER-
SION,

Sumitomo, H.

Kyoto University, Kyoto, Japan, Department of Sanitary
Engineering

Transactions of the Japan Society of Civil Engineers, Vol. 4, p 120-121,
November, 1973.  3 fig.

Diffusion equations have often been utilized for describing water quality
transportation.  However, the physical meaning of the diffusion coefficient
is not always clear, especially in turbulent flow with internal shear force.
Therefore, the word "dispersion" is often used for such type of complicated
flow, instead of the "diffusion", and the dispersion is distinguished from the
molecular diffusion.  Here the possibility of employing simpler presentation for
the dispersion is discussed instead of the Reynolds' analogy.  The purpose of
the simplification is to consider more hydraulic characteristics at solving
pollution problems in addition to the mass balance of water quality.

*Pollutants, *Dispersion, *Analytical techniques, Diffusion, Turbulent flow,
Water quality, Reynolds' number, Pollution problems, Hydraulics
on, Reynolds' analogy, Numerical solutions
                                     595

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049F

APPLICATION OF SEASONAL PARAMETRIC LINEAR STOCHASTIC
MODELS TO MONTHLY FLOW DATA,

McKerchar, A. I., and Delleur, J. W.

Purdue University, West Lafayette, Indiana, School of
Civil Engineering

Water Resources Research, Vol. 10, No. 2, p 246-255, April, 1974.  6 fig, 2 tab,
16 ref.

Stochastic linear models are fitted to hydrologic data for two main reasons:
to enable forecasts of the data one or more time periods ahead and to enable
the generation of sequences of synthetic data.  Short sequences of data lead
to uncertainties in the estimation of model parameters and to doubts about
the appropriateness of particular time series models.  A premium is placed
on models that are economical in terms of the number of parameters required.
One such family of models is multiplicative seasonal autoregressive integra-
ted moving average (Arima) models that have been described.  Illustrated is
the process of identifying the particular member of the family that fits loga-
rithms of monthly flows, estimating the parameters, and checking the fit.  The
seasonal Arima model accounts for the seasonal variability in the monthly
means but not the seasonal variability of the monthly standard deviations:
for this reason its value is limited.  The forecasting of flows one or more
months ahead is described with an example.

*Hydrologic aspects, *Flow data, *Model studies, Forecasting, Mathematical
studies

*Stochastic models, Hydrologic data, Parameters, Autoregressive integrated
moving average, Monthly flow data, Logarithms
 050F

 THE ESTIMATION OF VERTICAL EDDY DIFFUSIVITIES BELOW THE
 THERMOCLINE  IN LAKES,

 Powell,  T.,  and  Jassby, A.

 California University, Davis, California, Department of
 Physics  and  Division of Environmental  Studies

 Water Resources  Research, Vol. 10, No.  2, p 191-198, April, 1974.  4  fig,  4  tab,
 44  ref.

 Mathematical models of the spatial and  temporal variation of lakes and
 ocean water  require a quantitative formulation of vertical turbulent  trans-
 port.  Methods of estimating vertical eddy diffusivity coefficients in lakes
 for such substances as temperature, inorganic ions, or biologically active
 materials are briefly reviewed.  One widely used method, the McEwen method,  is
 discussed, and it is shown how this method can lead to erroneous results.  An-
 other method, the flux gradient method, is examined and compared with the
 McEwen method in specific case studies  of thermal energy transfers.  Lack of
 agreement between values obtained by the McEwen method and the flux gradient
 method has led some investigators to postulate a flux of thermal energy into
 the deep layers  of a lake by density currents.  An alternative explanation
 of  the discrepancy is offered by noting that deepwater turbulent mixing may  re-
 sult from a microstructure of layers and sheets caused by, for example, a
 Kelvin-Helmholtz shear instability in the flows or other instability mechan-
 isms.

 *Mathematical models, *Lakes, *0ceans,  Turbulent flow, Temperature, Inorganic
 compounds, Density currents, Eddies

 *McEwen  method,  *Flux gradient method, Diffusivity coefficients, Vertical
 turbulent transport, Quantitative formulations, Deepwater mixing, Vertical
 eddies
                                        596

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051F

SIMULATION OF ALLUVIAL FAN DEPOSITION BY A RANDOM WALK
MODEL,

Price, W. E. Jr.

U. S. Geological Survey, Reston, Virginia Water Re-
sources Division

Water Resources Research, Vol. 10, No. 2, p 263-274, April, 1974.  13 fig, 34 ref.

Alluvial fans are an important source of groundwater and knowledge of spatial
variations in the permeability of water-bearing beds in alluvial beds to geo-
logic processes is useful to estimate acquifer parameters.  This model aids
in the development of data collection systems, the estimation of aquifer
parameters in undeveloped areas, better Interpretation of aquifer tests, and
improvement in the accuracy of test-hole correlations.  The results suggest
that a digital model based on a random walk may be used to simulate alluvial
fan deposition.  The model is in three dimensions, is dynamic in time and space,
and employs two independent stochastic events:  an uplift of the moutain
basin contributing sediments and a storm large enough to result in fan depo-
sition.  A random walk, each step governed by the gradient and momentum of flow,
determines the pattern of deposition.  Results of the simulation are printed
as geologic maps and sections.  The general form of the simulated deposits is
that of an alluvial fan, the pattern of simulated flows resembles that of real
flows, and fan facies show a concentration of debris flows near the apex and
a particle size decrease in water flow deposits downfan.

*Alluvial fans, *Groundwater, Geology, Aquifers, Model studies, Simulation
analysis, Stochastic processes, Flow, Gradients, Data collection

*Random walk model, Geologic maps, Simulated  flows, Digital models
052F

NUTRIENT CONTROL IN SEWAGE LAGOONS,

Pollutech Pollution Advisory Services Limited, Oakville,
Ontario

Research Program for the Abatement of Municipal Pollution Within the Provisions
of the Canada-Ontario Agreement on Great Lakes Water Quality, Research Report
No. 8.  56 p, 23 fig, 2 tab, 7 ref.

This project was initiated to provide documentation on the effects and be-
haviour of precipitated phosphates in sewage lagoons.  Two techniques were
used to simulate lagoon conditions to obtain data for the possible long-term
distribution of phosphates between the solid and liquid phases in treatment
lagoons:  One method utilized laboratory-scale simulators operated under
closely controlled conditions of temperature and loading.  In the second me-
thod, a computational procedure was developed, involving the use of a com-
puter model written to simulate the removal of soluble phosphates by precipita-
tion with alum.  Full-scale lagoons were used for comparative purposes in the
first method.  Two laboratory units were seeded from bottom deposits, and
filled with lagoon effluent taken from the full-scale lagoons.  In each case
one lagoon was operated as a control, and the other received chemical dosing.
In both the full-scale control lagoon and the laboratory control lagoon, it
was observed that, during periods of low dissolved oxygen, both phosphorus and
carbon were resolubilized from bottom deposits.  The phosphorus resolubilization
rate was much less dependent on temperature and lagoon maturity than carbon.
The laboratory simulators indicated that more extensive phosphorus resolubili-
zatoin would occur at higher temperatures, pH was not found to be a governing
factor for phosphorus resolubilization.

*Phosphates, *Sewage lagoons, Laboratory tests, Model studies, Computers,
Solids, Liquids, Dissolved oxygen, Phosphorus, Effluents, Chemical control,
Carbon, Canada

Soluble phosphates, Bottom deposits, pH, Chemical dosages, Ontario
                                    597

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05 3F

DEVELOPMENT OF A MONITOR FOR RECYCLE OF WASTE WATER,

Scharen, H., and Mix, T. W.

Amicon Corporation, Lexington, Massachusetts

Annual Report for period of December 1, 1972 to August 15, 1973, November,
1973.  42 p, 11 fig, 4 ref.

In a pilot eight-month study at Amicon, a Reverse Osmosis (RO) unit was set
up and RO membranes were tested for flux and salt rejection.  Ultrafiltra-
tion (UF) and ozonation studies were performed on various dyes to check their
suitability as candidate tracer material for the various purification
steps of the recycle water.  Efforts were undertaken to decide whether or not
each step must be monitored individually.  In the concluding phase of the pro-
gram efforts were concentrated on a feasibility study of dichromate oxidation
in acid mediums as a monitoring technique, using a spectrophotometer to study
the reaction between organic impurities in water and dichromate.

*Monitoring, *Pilot study, *Reverse osmosis, Recycling, Flux, Membranes,
Water purification, Spectrophotometry,  Research, Tracers, Dyes, Salts

*0zonation, Ultrafiltration, Dichromate oxidation, Dichromate, Amicon Corpora-
tion
 054F

 MATHEMATICAL SIMULATION OF SUBSURFACE  FLOW CONTRIBUTIONS
 TO SNOWMELT RUNOFF,  REYNOLDS  CREEK WATERSHED,  IDAHO,

 Stephenson, G.  R., and Freeze,  R.  A.

 USDA Northwest  Watershed Research  Center,  Agricultural
 Research Service,  Boise, Idaho

 Water Resources Research, Vol.  10, No. 2,  p 284-294,  April,  1974.   10  fig,  2
 tab, 14 ref.

 A mathematic model is presented which  provides a two-dimensional transient
 saturated-unsaturated analysis  of  the  subsurface flow at  the field site.  This
 model of subsurface  flow has  been  applied  to a field  study of snowmelt runoff
 in a small upstream  source area in the Reynolds Creek Experimental Watershed,
 near Boise, Idaho.   The field measurements from an instrumented cross  section
 of this watershed showed that streamflow generation is  subsurface delivery  of
 meltwater over  limited distances through shallow high-permeability low-porosity
 formations of altered and fractured  basalt.  However, such hydrologic  response
 models cannot be used on a regional  scale  due to serious  limitations of data
 availability, funds  for data  acquisition,  and computer  capacity.  In this particu-
 lar study, it is seen that mathematical models consist  of boundary value problems
 which are time  and space dependent upon boundary conditions.  Value of such models
 is their applicability to specific sites.

 *Mathematical models, *Model  studies,  *Subsurface flow, *Hydrologic models, Field
 studies, Basalt, Instrumentation,  Data collections, Measurements, Boundaries,
 Costs, Computers, Snowmelt, Runoff,  Porosity

 Snowmelt runoff, Reynolds Creek Watershed, Idaho
                                           598

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055F

KINETICS OF SUBSTRATE ASSIMILATION AND PRODUCT FORMATION
IN ANAEROBIC DIGESTION,

Ghosh, S., and Pohland, F. G.

Institute of Gas Technology, Illinois,
Institute of Technology Center, Chicago, Illinois

Journal of the Water Pollution Control Federation, Vol. 46, No. 4, p 748-759,
April, 1974.  10 fig, 2 tab, 16 ref.

Process kinetic models were developed to describe the progression of substrate
utilization, growth, and product formation by mixed digester cultures.  Anaero-
bic processes are a two step sequence using two types of microorganisms.  Such
biological processes have three advantages as a treatment method:  low biomass
yield, production of useful gaseous and solid end-products, and good organic
solids destruction efficiency at reasonable costs.  Significant disadvantages
of high-rate anaerobic digesters are the need for long sludge retention times,
often over 15 days.  The roicrobial systems from two groups of microorganisms
must function in harmony in terms of their growth rates and metabolic activi-
ties.  Data revealed that during acid fermentation, about 60 to 76 percent
of the assimilated substrate was used for synthesis, compared to 15 to 19
percent for energy of synthesis and 4 to 26 percent for maintenance energy.
As detention time was increased, digester operations provided enhanced pro-
duction of acidic and gaseous products but decreased production of biomass ari-
sing from the growth of acid-forming organisms.

*Model studies, *Kinetics, *Anaerobic digestion, Microorganisms, Biological
treatment, Biomass, Gases, Solids, Measurements, Acids, Energy

Digester operations
056F

POLYELECTROLYTES AS PRIMARY COAGULANTS FOR POTABLE WATER SYSTEMS,

Robinson, C. N. Jr.

Topeka Water Department, Topeka, Kansas

Journal of the American Water Works Associacion, Vol. 66, No. 4, p 252-257,
April, 1974.  6 fig, 6 tab.

As shown by the Kansas River and its conventional methods of clarification,
improvement in methodology is warranted.  Conventional purification includes
chemical lime-soda ash process causing turbidity and subsequent chlorination,
coagulation with aluminum sulfate (alum), and coagulant aids such as activated
silica.  Disadvantages are found in each; suspended solids content in the Kansas
River requires chemical treatments, each with additional problems.  By pilot
plants and laboratory investigations over a two year period on the river,
polyelectrolytes were shown to be much more effective than the standard coagu-
lants.  Polymer basins promote methods of separating the mud from the chemical
sludge.  In addition, it is simpler to treat water of lower turbidity which
has not artificially hardened with chlorine and alum.  Economic advantages re-
sult from this treatment method as well.

*Model studies, Clarification, *Treatment facilities, *Polyelectrolytes,
Pilot plants, Laboratory studies, Lime, Purification, Coagulants, Polymers,
Chlorine, Alum, Costs, Potable water

Kansas River, Kansas, Economics
                                        599

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057F

ADAPTIVE CONTROL APPLIED TO A WATER QUALITY SYSTEM,

Perils, H. J.

Newark College of Engineering,
Newark, New Jersey

Instrument Society of America Transactions, Vol. 13, No. 1, p 31-34, 1974.
1 fig, 3 tab, 13 ref.

A model system for a crude form of adaptive control has been applied to water
pollution control problems.  Its principle is response to changes in temper-
ature, reacting with a computer.  This is called open-loop adaptive control.
A two-element control vector in a number of reaches of stream (not contiguous)
is used.  Cost/benefit tradeoffs are incorporated into the scheme.  Results
show a reduction in overall theoretical cost and an improvement in 00 level
maintenance and BOD loading.

*Model studies, *Control, *Water pollution, *Computers, Costs, Biochemical
oxygen demand, Dissolved oxygen, Loading, Streams, Temperature, Mathematical
studies, Water quality control, Effluents

Open-loop adaptive control
058F

ECONOMIC ASPECTS OF THE APPLICATION OF MUNICIPAL WASTES
TO AGRICULTURAL LAND,

Seitz, W. D., and Swanson, E. R.

University of Illinois

In:  Proceedings of the Joint Conference on Recycling Municipal Sludges and
Effluents on Land, July 9-13, 1973, Champaign, Illinois, The National Associa-
tion of State Universities and Land-Grant Colleges, University of Illinois,
p 175-182, 5 fig, 22 ref.

Implications of minimizing the cost of waste treatment and of its disposal
on agricultural land are discussed.  Crop returns from application of waste
and of environmental damage are accounted for in cost minimization.  The
optimal rate of application of waste to crops is shown, in principle, to
be influenced by all variables and functions in the system, including the
marginal cost of alternative methods of treatment and disposal.  Given is a
simulation analysis of a particular land-reclamation sludge-disposal project.
The variables found to be most influential in performance of the system in-
cluded:  transport costs for sludge, site preparation costs, assumptions
regarding the nitrogen budget, choice of cropping system, and source of labor
used in site preparation.  Research on these variables will improve decision
making regarding the application of waste to crop land.

*Mathematical models, *Costs, *Municipal wastes, *Simulation, Waste treat-
ment, Waste disposal, Agriculture, Sludge, Nitrogen, Decision making

*Land application, Crop land, Agricultural land, Cost-minimization, Treatment
methods, Land reclamation
                                      600

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059F

STUDIES ON MODELING OF URBAN STORM WATER RUNOFF—ON THE
RELATION BETWEEN THE COMPOSITION OF BASIN MODEL AND THE
EQUIVALENT ROUGHNESS,

Toyokunl, E., and Hagihara, K.

Memoirs of the Ehime University, Section III (Engineering), Vol. 7, No. 1,
p 49-64, 1974.  12 fig, 1 tab, 18 ref.

On the basis of observed hydrological data in the research basin, the relation
between the composition of the basin model in the homogeneous surface and
the equivalent roughness for each model and adaptability of the runoff model
are discussed.  These are studied on the representation of equivalent drainage
area for the heterogeneous area composed of roof, asphalt road, or pervious
ground surface.  Each of three models, one simple and two more complex,
are derived theoretical!}? from the elements of composition in the basin model,
applying the kinematic wave method.

*Storm runoff, *Hydrological data, *Basins, *Model studies, Drainage, Drainage
areas, Surface drainage, Urban runoff

*Kinematic wave method, Urban storm water runoff, Japan
060F

IMPROVED DYNAMIC PROGRAMMING PROCEDURES AND THEIR PRACTI-
CAL APPLICATION TO WATER RESOURCE SYSTEMS,

Mawer, P. A., and Thorn, D.

Medmenham, Marlow, Buckinghamshire, England
Water Research Association

Water Resources Research, Vol. 10, No. 2, p 183-190, April, 1974.  8 fig,
10 ref.
2 tab,
Value iteration dynamic programming and simulation procedures have been brought
together by a general optimization algorithm.  This is used in conjunction
with penalty costs to derive long-term operating policies for water resource
systems.  Two types of problems are illustrated by numerical examples; these
are value iteration procedures dependent upon the nature of transition costs.
For deterministic costs a computational procedure reduces computational effort
to about 8 percent of that required if conventional procedures are adopted.
With probabilistic transition costs, savings in computation are less, but
still substantial.  Feedback from a simulation to the dynamic programming
is achieved by penalty costs, interpreted as Lagrangian multipliers.  Simpli-
fied dynamic programming procedures give practical benefits which outweigh
any theoretical objections.

*Mathematical models, *Costs, *Simulation, *Computers, *Algorithm, Dynamic
programming, Water resources development, Planning

*0ptimizing algorithm, Value iteration, Deterministic costs, Penalty costs,
Probabilistic costs, Lagrangian multipliers, Water resources planning
                                     601

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061F

OPTIMAL TIMING AND SIZING OF A CONJUNCTIVE URBAN WATER
SUPPLY AND WASTE WATER SYSTEM WITH NONLINEAR PROGRAMMING,

Mulvihill, M. E., and Dracup, J. A.

Loyola University of Los Angeles, Los Angeles, Califor-
nia

Water Resources Research, Vol. 10, No. 2, p 170-175, April, 1974.  6 fig., 16 ref.

A conjunctively operated urban water supply and waste water system is formulated
as a mathematical model and applied to the city of Los Angeles.  The objectives
are:  to minimize the cost of supplying water from several sources, including
provisions for recycling reclaimed water; and to determine the capacity expan-
sion schedule of the water and waste water treatment processes.  The water
sources vary in quality, quantity, and cost.  The model formulated consists
of the minimization of a concave objective function subject to linear con-
straints.  A multilevel solution technique is developed to determine the minimum
cost alternative for a selected planning horizon.  The mathematical model is
flexible and can be expanded to include additional water quality constituents,
advanced waste water treatment processes, and variations in water quality
standards.

*Mathematical models, *Urban areas, *Water supply, *Waste water treatment,
Recycling, Costs, Model studies, Planning, Water quality control, Waste treatment,
Water quality standards, California

Los Angeles, California
062F

STUDIES ON RUNOFF CHARACTERISTICS IN CHANNEL NETWORK
SYSTEMS IN LOW LAND,

Toyokuni, E., and Watanabe, M.

Memoirs of the Ehime University, Section III, Engineering, Vol. 8, No. 1, 1974.
23 fig, 1 tab, 10 ref.

The methods of discharge measurement for open-channels in low land, using the
data of water surface gradient and water stage, are discussed with respect to
the fundamental equation for unsteady flow.  These are examined by hydraulic
experiments.  A runoff model of channel network systems is investigated and is
verified.  Using this simulation model, the characteristics of channel flow
associated with inundation and the runoff characteristics are researched by
means of digital simulation, increasing the applications of this model.

*Measurement, *Runoff, *Simulation, *Model studies, Channel flow, Inundation,
Discharge, Surface waters

Channel networks, Japan, Low lands, Water surface gradients
                                      602

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063F

THE MEDWAY WATER BOARD TELEMETRY AND TELECONTROL SYSTEM,

Howard, D. W., and Insley, M. G.

Westinghouse Brake and Signal Company Limited,
Chippenham, Wiltshire, England,
Automation Division

Water Services, Vol. 78, No. 938, p 126-218, April, 1974.  3 fig.

A remote control, automated, computerized system for water treatment facilities
is described in detail.  The main features of the system include a 12,000
word store computer with a 30,000 word store disc, a standby control panel,
closed circuit television, and  power supplies.

*Computers,  *Instrumentation, *Treatment facilities, *Control systems,
*Automatic control, *Telemetry, Automation,Monitoring,  Remote control,
Equipment

*England, *Computerization
  064F

  SEDIMENTATION:  AN INTRODUCTION TO SOLIDS FLUX THEORY,

  Handley, J.

  Water Pollution Control Department, Sheefield, England

  Water Pollution Control, Vol.  73,  No.  2,  p 230-240,  1974.   10 fig,  17 ref.

  An attempt has been made to survey the basic concepts involved in the design
  and operation of settlement tanks  and  thickeners with no presentation of new
  theory on sedimentation or thickening.  Material normally  found in  research
  papers is presented in a way that  the  practicing designer  or operator can
  grasp the concepts developed.   The application of these concepts to the various
  features of tank design and operation  is  described.

  *Reviews, *Design criteria, Operations,  *Sedimentation, Mathematical studies,
  Theoretical analysis, Application  methods

  *Thickeners,  *Settling tanks,  *Solids  flux,  *Flux theory
                                      603

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065F

HISTORICAL DEVELOPMENT OF WATER POLLUTION CONTROL COST
FUNCTIONS,

Tlhansky, D. P.

Environmental Protection Agency, Washington Environmental
Research Center, Washington, D. C., Office of Research and
Development, Economic Analysis Branch

Journal of the Water Pollution Control Federation, Vol. 46, No. 5, p 813-
833, May 1974.  31 fig, 2 tab, 82 ref.

Available information on the derivation and application of cost functions
on water pollution control are summarized.  The state-of-the-art on cost for-
mulations and their development from an historical perspective are described.
The concept of cost function is defined in general terms and its derivation
is related to policy objectives and data requirements with the most important
cost categories subject to functional analysis being discussed.  Determinants
or variables affecting costs are distinguished according to their signifi-
cance in various cost models,  A review of cost studies on municipal versus
industrial waste water control follows, with cost expressions presented in
both mathematical and graphical form.

*Water pollution control, *Cost analysis, *Data collections, *Reviews,
*Mathematical studies, Model studies, Application methods, Municipal wastes,
Industrial wastes

*Cost function, *Functional analysis, State-of-the-art reviews
066F

FACILITIES FOR CONTROLLING THE ACTIVATED SLUDGE PROCESS
BY MEAN CELL RESIDENCE TIME,

Burchett, M. E., and Tchobanoglous, G.

Yoder-Trotter-Orlot and Associates, Walnut Creek,
California

Journal of the Water Pollution Control Federation, Vol. 46, No. 5, p 973-
979, May 1974.  7 fig, 6 ref.

Several methods now being used by operators to control the activated sludge
process are discussed.  The use of the mean cell residence time (MCRT) is
recommended as the most suitable operational control parameter.  The basic
concepts involving the theoretical and practical reasons for controlling
the MCRT are discussed in the first section of this paper, and the physical
features of a control system developed to use this method are presented in
the second section.  The following advantages for the proposed control system
are:  minimum required operator attention, inexpensive capital costs, more pos-
itive process control, and more stable process operation.

*Activated sludge, *Treatment facilities, *Control systems, Automatic control,
Operation and maintenance

*Mean cell residence time (MCRT)
                                        604

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 067F

 HEAPS AND HOLES,

 Surveyor, No. 4261, p 10-11, February, 1974.  2 fig.

 Planning links between waste disposal, land reclamation, and mineral extraction
 are needed for future disposal facilities.  A pilot study for a computer model,
 as well as its limitations, is described.  Strategy was defined as factors
 needed to arrive at a marginal value for waste disposal.  This was given in
 terms of the wastes considered, the holes available, the environmental con-
 straints on which types of wastes can go into which holes, and the pre-treatment
 of the wastes.  Water pollution standards, risks to public health, and location
 of sites were considered in the model.  From the computer results, attractive
 holes can then be reassessed.  Real figures would be given in the form of a de-
 tailed hydrogeological survey, estimates of costs, landscaping, access, and
 screening, and safety with respect to water pollution.  Planning decisions
 for mineral workings in a particular area could then be made.

 *Planning, *Waste disposal, *Model studies, *Computer models, *Water pollution,
 *Mineral industry, Treatment facilities, Public health, Costs, Hydrogeology,
 Landscaping, Pre-treatment

 *Mineral extraction, Land reclamation
068F

A MATHEMATICAL MODEL OF TRANSPORT, DIFFUSION AND DEGRADA-
TION OF ORGANIC MATTER IN A RIVER,

Nalluri, C.

University of Newcastle upon Tyne, Department of Civil
Engineering, England

Journal of the Institution of Engineers (India), Vol. 54, Pt. PH 1, p 1-6,
October, 1973.  15 ref.

A program suitable for solving the diffential equations developed for calcu-
lations in polluted streams using a realistic approach is described.  The nu-
merical method discussed is easily programmable and economical in machine
time and is easily extended to arbitrarily distributed grid points.

*Mathematlcal models, *Model studies, *Rivers, Organic matter, Biochemical oxy-
gen demand, Dissolved oxygen, Heat, Diffusion, Degradation (Decomposition),
Sediment transport, Water pollution control

Great Britain
                                         605

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 069F

 THE CONFLICT BETWEEN CONSUMPTION AND POLLUTION,

 Fleming,  R.  N.,  and  Pantell,  R.  H.

 Stanford  University,
 Stanford,  California

 IEEE Transactions  on Systems, Man,  and  Cybernetics,  Vol.  SMC-4, No.  2,
 p  204-208, March,  1974.   7  fig,  5 ref.

 The United States  is  concerned about controlling pollution without excessive
 decreases  in consumption.   In this  correspondence a  technical  relationship
 between consumption  and pollution is defined.  A utility  function indicates
 the manner in which  consumption  should  vary with time  so  as  to maximize
 utility.   It is  assumed that a specified pollution level  is  to be achieved
 at the termination of a given planning  period, and the problem is to  obtain
 the optimum  path to  this  objective.   As a special case, a steady-state solution
 is obtained,  which specifies the  most desirable constant  levels of consumption
 and pollution.   Critical  parameters  that enter into  this  solution are the
 discount  (or appreciation)  rate  for  the future, the  decay lifetime for the
 pollutant, and the rate of  change of pollution generation with respect to
 consumption.  In addition,  a closed-form solution is obtained  for the low-
 pollution case,  which indicates  that the optimum consumption function decreases
 with increasing  time.  Computer  solutions are given  for the  general  case
 with several different values of  critical parameters.

 *Water consumption,  *Water  pollution control, *Mathematical  models,  *Computers,
 Planning

 *Food consumption, Steady-state  solution, Critical parameters
070F

THE EFFECT OF PHENOLS AND HETEROCYCLIC BASES ON NITRIFI-
CATION IN ACTIVATED SLUDGES,

Stafford, D. A.

University College, Cardiff, Wales, Microbiology
Department

Journal of Applied Bacteriology, Vol. 37, No. 1, p 75-82, 1974.  7 fig, 1 tab,
9 ref.

The optimum conditions of pH, suspended solids concentration, temperature and
age of sludge, for nitrification by activated sludge have been studied.
Activated sludge receiving ammonium thiocyanate (500 mg/liter) was able to
nitrify.  The rate of ammonia oxidation was decreased when less than 3 mg/
liter of phenol (or cresols) was added to the sludge, and at 10 mg/liter was
inhibited completely.  Concentrations of up to 100 mg/liter of phenols did
not affect nitrite oxidation.  The 2- and 4-methyl pyrldine derivatives
inhibited both ammonia and nitrite oxidation.

*Activated sludge, *Phenols, *Nitrification, *Suspended solids, *Temperature,
Ammonia, Oxidation, Mathematical models

Ammonia oxidation, Nitrite oxidation, Heterocyclic bases
                                     606

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071F

TIME OF CONCENTRATION-A KINEMATIC WAVE APPROACH,

Paintal, A. S.

Metropolitan Sanitary District,
Chicago, Illinois,
Sewer Design Section

Water and Sewage Works, Vol. 121, No. 4, p 26-30, April 30, 1974.  2 fig,
10 ref.

A method was outlined for estimating the time of concentration, or overland
flow time, useful in small watershed work and urban storm sewer design.  This
time is governed by rainfall intensity and watershed characteristics.  The
factors used for the mathematical model were rainfall intensity, surface slope,
surface roughness, infiltration, depression storage, and flow distance.

*Mathematical models, *0verland flow, *Urban runoff, Rainfall intensity,
Water resources planning, Watershed management, Infiltration

*Urban storm sewer design
072F

MATHEMATICAL AND OPERATIONAL RELATIONSHIPS FOR THE
COMPLETELY MIXED ACTIVATED SLUDGE PROCESS,

Sherrard, J. H., Schroeder, E. D., and Lawrence, A. W.

Oklahoma State University, Stillwater, Oklahoma,  School
of Civil Engineering

Water and Sewage Works, p 84-86, 88, 91, April 30, 1074.  8 fig, 1 tab, 12 ref.

A simplified approach in describing continuous flow aerobic biological waste
water treatment processes through utilization of the variable observed cell
yield coefficient is presented.  For specific waste water and constant
environmental conditions, the magnitude of the variable observed yield
coefficient is dependent upon net cell growth rate, or its reciprocal, sludge
age or mean cell residence time.  Illustrations are presented to show
interrelationships between the aeration basin hydraulic retention time, the
sludge age, the influent organic concentration, the microbial concentrations
in the waste line and aeration basin, and the mass of waste solids produced
per unit time.  Similar sets of relationships and equations also could be
developed for other fluidized culture microbial processes such as nitrification,
denitrification, and methane fermentation.

*Mathematical studies, *Activated sludge, Aerobic conditions, Waste water
treatment, Biological treatment, Equations, Solid wastes

Cell yield coefficient, Retention time, Sludge age, Influent organic
concentration, Microbial concentrations
                                      607

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    073F

    A FORMULA FOR AERATION TANK DETENTION TIME,

    Sterling, P.

    Water and Sewage Works, Vol. 121,  No. 5,  p 62,  May,  1974.

    A rational approach to elementary  principles  of design and operation of the
    conventional  activated sludge process aeration  tank,  excluding oxygenation,
    is presented.   It demonstrates that:   flow is not a  factor in the determination
    of design aeration detention time;  detention  time varies  directly as BOD
    concentration and inversely as the  product of loading and  mixed liquor suspended
    solids(MLSS)factors;  and,  the product of  loading and  MLSS  factors may be used
    in direct ratio to determine relative system  loading  and/or percentage of
    design capacity utilized.

    *Mathematical studies, *Equations,  Activated  sludge,  Design criteria, Operations,
    Aeration, Storage tanks, Flow, Biochemical oxygen demand,  Loading

    *Detention time, Mixed liquor suspended solids
074F

A SOLUTION OF THE INORGANIC CARBON MASS BALANCE
EQUATION AND ITS RELATION TO ALGAL GROWTH RATES,

Kelly, M. G., Church, M. R., and Hornberger, G. M.

Virginia University
Charlottesville, Virginia,
Department of Environmental Sciences

Water Resources Research, Vol. 10, No.  3, p 493-497, June, 1974.  2 fig,
1 tab, 18 ref.

The mass balance equation describing the dissolved inorganic carbon content of
river water is solved for varying conditions.  These include net community pro-
ductivity, alkalinity, temperature, atmospheric exchange, and accrual of ground-
water to give C02 concentration throughout the day.  Without accrual of ground-
water the C02 concentration must lie in the range where it will influence growth
rate of some plant species.  However, groundwater input prevents this situation
in most rivers.  In lakes, groundwater input and exchange with the aphotic zone
may prevent the influence of C02 on algal growth rates.  In waters with little
groundwater input or little vertical mixing, the C02 concentration may influence
relative growth rates of species but probably not the total plant biomass
produced.

*Algae, *Rivers, *Equations, Inorganic compounds, Alkalinity, Temperature,
Groundwater, Carbon, Carbon dioxide, Lakes, Aphotic zone

*Mass balance equation, Inorganic carbon content, Algal growth rates
                                             608

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075F

MODELING FLOW AND CHEMICAL QUALITY CHANGES  IN AN
IRRIGATED  STREAM AQUIFER  SYSTEM,

Konikow, L. F., and Bredehoeft, J. D.

United  States Geologtcal  Survey,
Lakewood,  Colorado

Water Resources Research, Vol.  10, No.  3, p 546-561, June,  1974.   23  fig,  3
tab, 25 ref.

Salinity increases in  groundwater and surface water in  the  Arkansas River  valley
of southeastern Colorado  are primarily  related to irrigation practices.  A
digital computer model was developed to predict changes in  dissolved  solid
concentration in response to spatially  and  temporally varying hydrologic
stresses.  Equations describing the transient flow of groundwater  and the
transport  and dispersion  of dissolved chemical constituents were solved
numerically.  The model simulates flow  as well as changes in water quality
for both the stream and the aquifer.  Detailed field measurements  made for
a one year period in an 11-mile reach of the valley between La Junta and the
Bent-Otero county line were used to verify  and calibrate the model.  Measured
water levels varied by an average of about  3 ft during  the  study period.
Calculated water table elevations in the aquifer were within 1 ft  of the
observed values approximately 90 per cent of the time.  The specific
conductances of water  samples from five wells in one well field had a standard
deviation  of about 10 per cent of the mean.  Dissolved  solid concentrations
calculated by the model were within 10  per  cent of the  observed values
for both the aquifer and  the stream approximately 80 per cent of the time.

*Mathematlcal models,  *Salinity, *Groundwater, *Surface water, Irrigation,
Aquifers,  Computers, Dissolved solids,  Equations, Streams, Flow, Field investi-
gations, Digital computers

Colorado,  Chemical quality
076F

A COMPUTER MODEL FOR THREE DIMENSIONAL SIMULATION OF
THERMAL DISCHARGES INTO RIVERS,

Anthony, H.

Missouri University,
Colombia, Missouri

Dissertation Abstracts International, Vol. 34, No. 11, p 5505-B, May, 1974.

A digital computer model has been developed for simulating thermal discharges
Into rivers.  This is needed due to anticipated growth of power plants.  The
model is based on the fundamental conservation equations for hydraulic flow
and the model for the computer code COBRA.  Two types of thermal discharges
were simulated, lateral surface and single-port subsurface.  Each was compared
with field data; the lateral surface discharge with the Philip Sporn Power
Plant on the Ohio River and the single-port subsurface with the proposed
Rush Island Power Plant on the Mississippi River.  Results indicated that
this method of determining dispersion of heated effluents might have universal
application to describe the temperature distribution from outfalls into rivers.

*Models, *Simulation, *Computers, *Discharges, Thermal water, Power plants,
Field data, Temperature, Rivers, Mississippi River, Ohio River, Digital
computers

*Thermal discharges, Single-port subsurface discharge, Lateral surface discharge
                                      609

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077F

MAN'S IMPACT ON THE PHOSPHORUS CYCLE IN FLORIDA,

Gilliland, M. W.

Florida University

Dissertation Abstracts International, Vol. 34, No. 11, p 5504-5505, May, 1974

By digital computer simulation, the phosphorus flux in the Peace River Estuary
in Florida showed the relative importance of projected changes in mining and
population.  Natural drainage to the river is high in total phosphorus and daily
mining water discharges have little effect on total phosphorus concentrations.
Periodic spills from slime ponds in the mining district are more serious, as
shown by simulation of slime releases.   The percent effect on the overall
geochemical cycle of the present phosphorus flows in peninsular
Florida was determined by evaluating an overall phosphorus budget model.  With
a systems model of main energy and money flows, the energy budget of Polk
County was also calculated.  At the current rates of stripping land due to
mining, within five to ten years the total energies for the county without
phosphate mining will be higher than with mining.

*Phosphates, *Mining, *Simulation, *Computer models, *Florida, Human population,
Rivers, Drainage, Eutrophication, Slime, Systems analysis, Energy, Costs

*Phosphate mining, Phosphorus flux, Peace River Estuary (Florida)
078F

A COMPUTER MODEL FOR EVALUATING COMMUNITY PHOSPHORUS
REMOVAL STRATEGIES,

Yeaple, D. S., Barnes, D. A., and DiGiano, F. A.

J B F Scientific Corporation,
Burlington, Massachusetts

N.T.I.S. Report No. PB 228 440, 305 p, 25 fig, 14 tab, 60 ref.

A computer model for the evaluation of various treatment and non-treatment
strategies to remove phosphorus from waste water is described.  The cost of
non-treatments such as the elimination of phosphates in detergents can be
viewed in terms of treatment costs at local waste treament plants.  Chemical
precipitation techniques were selected as being the most effective for phosphorus
removal at the present time.  Total user costs are reported in this model of a
selected strategy for the removal of phosphorus.  Over 21 treatment schemes
with several sludge handling methods can be selected and evaluated, each
dependent upon local conditions.  Through use of the computer, the user can
develop a local profile and choose his optimal treatment method.

*Phosphates, *Phosphorus, *Eutriphication, *Costs, *Chemical treatment,
*Computers, *Model studies, *Costs, Precipitation, Treatment facilities, Sludge,
Local governments, Detergents

Phosphorus removal, Treatment methods
                                         610

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079F

CRITICAL OXYGEN DEFICIT FOR BANK OUTFALL,

Rood, 0. E., Jr., and Holley, E. R.

Illinois University, Urbana-Champaign, Illinois,
Department of Civil Engineering

Journal of the Environmental Engineering Division, ASCE, Vol. 100, No. EE 3,
p 661-678, June, 1974.  6 fig, 1 tab, 12 ref.

The two-dimensional mass balance equation has been solved numerically to
investigate the effects of transverse mixing on the DO downstream of a
bank outfall of BOD in a rectangular channel with no upstream BOD or
deficit.  From the numerical results, the magnitude and location of the
critical deficit have been obtained.  Dimensional analysis has been used to
generalize the presentation of the results.  Results are presented in
graphical form and a method is given for predicting the critical deficit for
various situations.  For some situations the solution to the two-dimensional
equation indicates that the magnitude of the critical deficit may be
significantly larger than that predicted by the traditional one-dimensional
equations and that the longitudinal distance between the outfall and the
location of the critical deficit may be only 40-50 percent of that predicted
by the one-dimensional representation.

*Biochemical oxygen demand, *Numerical analysis, Dissolved oxygen, Equations,
Mathematical studies, Channels

Mass balance, Transverse mixing, Bank outfall
080F

WATER QUALITY MODELS USING THE BOX-JENKINS METHOD,

Huck, P. M., and Farquhar, G. J.

Canada Centre for Inland Waters, Wastewater Technology
Centre, Burlington, Ontario, Canada

Journal of the Environmental Engineering Division, ASCE, Vol. 100, No. EE 3,
p 733-752, June, 1974.  9 fig, 7 tab, 13 ref.

Expanding water quality study programs and the advent of improved methodology
for data acquistion have increased both the volume and the scope of the
analysis to be carried out.  An innovative approach to time series analysis
has been developed by Box and Jenkins.  It has time as its basis, which
appears to be superior in certain cases, as opposed to frequency.  A study was
undertaken to examine the applicability of the Box-Jenkins method to the
modeling of water quality data.  It was shown that the Box-Jenkins technique
was able to employ defective data, containing an oscillation believed to
be machine-induced, to obtain a workable model; this indicates the adaptability
of the method.  Also, the Box-Jenkins method provides the water quality analyst
with a new technique or can serve as an alternative approach.

*Data collections, *Water quality, *Time series analysis, Model studies

*Box-Jenkins method
                                        611

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081F

PROBLEMS IN MODELING URBAN WATERSHEDS,

McPherson, M. B., and Schneider, W. J.

American Society of Civil Engineering Urban Water
Resources Research Program, Marblehead, Massachusetts

Water Resources Research, Vol. 10, No. 3, p 434-440, June, 1974.  3 fig,
45 ref.

Modeling of urban watersheds is complicated by the complexities of the hydrologic
system brought about by urbanization, model scale, and client diffusion.
Modeling objectives vary widely, from storm sewer design to management of local
runoff to river basin planning.  Current difficulties in modeling involve
inherent nonlinearities in most methods of processing inputs for linear models,
problems of storm definition, interconnection of urban catchment areas, and
shortage of detailed rainfall-runoff water quality data for calibration.

*Model studies, *Watersheds (basins), Urbanization, Urban hydrology,
Storm sewers, Design criteria, Urban runoff, Water management (applied),
Project planning, Data collections, Rainfall-runoff relationships

*Model scale, Client diffusion, Modeling objectives
082F

WHY IT MAY COST t 100 MILLION TO CLEAN UP MERSEY SHORES,

Appleton, B.

New Civil Engineer, No. 96, p 49-51, June 13, 1974.

The Water Pollution Research Laboratory was commissioned to develop a
mathematical model of the pollution of the Mersey estuary while a private
company, JD & DM Watson investigated present sewage and industrial
waste disposal and recommended remedial action.  Targets of the investi-
gation were: to ensure that the estuary water should at all times
contain a sufficient level of oxygen to obviate odor nuisance; and,
to obviate the fouling of the estuary foreshore and beaches by crude
sewage or solids or fats from industrial effluents.  These objectives
and experimental findings are discussed.

*Mathematical models, *Water pollution, Estuaries, Industrial wastes,
Sewage disposal, Waste disposal, Oxygen requirements, Odor, Water
pollution control, Economics, Research and development.

Mersey estuary, England
                                       612

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083F

THE USE OF A PROCESS COMPUTER IN AN ENVIRONMENTAL
MONITORING SYSTEM,

Krenke, G., and Scholzke, D.

Measurement and Process Engineering Division,
Karlsruhe

Siemens Review, Vol. 41, No. 4, p 170-174, April, 1974.   1 fig.

    The necessity of maintaining or restoring a cleaner environment has
presented a number of problems connected with the measuring of :he
impurities and the automating of the monitoring methods.   A general
concept was developed for a superregional environmental monitoring
system.  The first result of such work is a data aquisition and  pro-
cessing system which incorporates a process computer.  This instrument
plays the part of a central intelligent monitoring and control unit.
The system has proven its value in trial operation, and conforms to the
current ideas about the requirements that must be met by an environmental
monitoring system.  The hardware and software are flexible enough to
satisfy future requirements.

*Monitoring, *Computers, *Environmental effects, *Data processing,
Purification, Pollutants, Control systems, Automation

Computer hardware, Computer software
  084F

  DESIGN AND OPERATIONAL MODEL FOR COMPLETE MIXING
  ACTIVATED SLUDGE SYSTEM,

  McKinney, R. E.

  Kansas University,
  Lawrence, Kansas

  Biotechnology and Bloengineering, Vol. 16, No.  6, p 703-722, June, 1974
  14 ref.

  The complete mixing activated sludge  (CMAS) system is gaining in
  popularity for treating both domestic and industrial waste waters.  A
  simple mathematical model was produced which can be used in both
  the design and the operational evaluation of CMAS systems.  Labora-
  tory pilot plants and full scale field units have furnished basic data
  to confirm the validity of the mathematical model.  Concepts of the
  model are discussed in light of field evaluations as are areas of
  conflict and confusion which had arisen in the past.  Design examples
  and operational evaluations are presented for several different waste
  water systems.

  *Activated sludge, *Domestic waste waters, *Industrial waste waters,
  Mathematical models, Pilot plants, Field studies, Design criteria,
  Microbiology, Treatment facilities

  Complete mixing activate sludge (CMAS), Treatment methods
                                        613

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085F

STOCHASTIC HYDRO-LOGICAL SYSTEM MODELS (STOCHASTIKUS
HIDROLOGIAI RENDSZER-MODELLEK),

Kontur, I.

Hidrological Kozlony, Vol. 54, No. 2, p 87-90, February, 1974.
6 fig, 18 ref.

A stochastic model of hydrological systems taking evaporation,
trickling and runoff into consideration is presented.  The input-
output model of the catchment system is composed of three segments
for atmospheric (precipitation and evaporation) and geologic
(flows to and from the system) communications, and for water
yield, such as, water leaving the catchment system.  The proba-
bilities at which a given quantity of water evaporates or runs
off from the catchment system or remains within the latter during
a given time are determined.  The investigations indicate the re-
duction of the specific water yield with the increase of the
catchment area.

*Hyrdologic systems, *Runoff, Model studies, Flow, Trickling,
Evaporation, Investigations

Stochastic models, Water yield
086F

NUMERICAL ANALYSIS ON UNSTEADY DISPERSION IN RIVER,

Muraoka, K., and Nakatsuji, K.

Technology Reports of the Osaka University, Vol. 23, No. 1121/1154,
p 649-661, April, 1973.  8 fig, 1 tab, 5 ref.

Numerical analysis of the concentration of diffusive materials for
the prediction of water pollution in a river or its estuary are needed.
Numerical errors of some finite difference schemes were quantitatively
evaluated.  It was found that the finite difference scheme with the
accuracy of fourth order gives the satisfactory results of approxi-
mation and is also free from the restriction of selection of mesh
size at the difference scheme.

*Water pollution, *Rivers, *Models, *Numerical analysis, Estuary, Planning

Errors, Unsteady dispersion, Finite difference schemes
                                          614

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087F

GENERALIZATION, TYPIFICATION, AND KINETICANALYSIS OF THE
BIOCHEMICAL OXYGEN DEMAND CURVES BASED ON BOD-EXPERIMENTS
(OBOBSHCHENIYE, TITIZATSIYA I KINETICHESKIY ANALIZ KRIVYKH
POTREBLENIYA KISLORODA PO DANNYM BPK-OPYTOV) ,

Leonov, A. V.

Okeanologiya, Vol. 14, No. 1, p 82-87, 1974.  2 tab, 28 ref.

The established types of BOD curves are generalized on the basis
of published BOD data.  The existing types are arbitrarily divided
into monophasal and multiphasal curves.  Monophasal curves are
sinusal or autocatalytic, parabolic and expontial, while among
the multiphasal curves, linear curves with terminal acceleration,
exponential-autocatalytic, parabolic-linear, exponential-auto-
catalytic-linear, autocatalytic-linear with terminal acceleration,
exponential-linear with terminal acceleration, polyautocatalytic,
exponential-linear and autocatalytic-linear types are distinguished.
Kinetic equations for the 12 different types of BOD curves are given.

*Biochemical oxygen demand, Equations, Kinetics, Mathematical models

BOD curves
088F

CASE STUDY OF REGIONAL ANALYSIS TECHNIQUES FOR DESIGN
FLOOD ESTIMATION,

Kite, G. W.

Canadian Journal of Earth Sciences, Vol. 11, No. 6, p 801-808,
June, 1974.  2 fig, 3 tab, 12 ref.

Regional analysis describes those techniques permitting
estimation of parameters for those areas in which measurements
of the parameters are not available.  Two techniques, index-
flood regional analysis and a simplified square grid method,
were used to estimate design floods for culverts on the pro-
posed Mackenzie highway.  The results of these two techniques
were compared with design floods estimated by the rational
equation, slope-area method and an envelope of recorded ex-
tremes.  Regional analysis techniques give design flows at
least an order of magnitude less than those of other techniques.

*Floods, Regional analysis, Equations, Highways, Estimation, Canada,
Model studies, Design criteria

Mackenzie highway, Slope-area method
                                       615

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089F

TIME-DEPENDENT LINEARIZED INFILTRATION I. POINT
SOURCES,

Warrick, W. W.

Arizona University,
Tusson, Arizona,
Department of Soils, Water, and Engineering

Soil Science Proceedings, Vol. 38, p 383-386, May/June, 1974.
4 fig, 12 ref.

Water flow from a point source was analyzed using a linearized
form of the moisture flow equation.  Time-dependence is assumed
with the results simplifying to those of previous investigators
for steady-state conditions.  Discrete time-distributed inputs
which might occur for trickly or high frequency irrigation are
amenable to the solution.  Numerical simulations include the
advance of wetting front during infiltration, moisture variation
resulting from a cyclic input as during irrigation, and the
matric flux potential field for a two-source problem.

*Flow, *Flow equations, *Moisture, Infiltration, Trickle
irrigation, Water cycles, Irrigation

Time-dependence, Steady state
090F

VELOCITY CONTROL WITH NEW PROPORTIONAL WEIRS,

Chandrasekaran, D., and Rao, N. S. L.

College of Engineering, Guindy,
Madras,
Hydraulics and Water Resources Department

Journal of the Institution of Engineers (India), Vol. 54, Part PH2, p 48-54,
February, 1974.  5 fig, 2 tab, 6 ref.

The design of an outlet weir is detailed and its potentiality to control the mean
velocity of flow is described.  Velocity varies inversely with the depth of flow.
The settling phenomenon of sediment particles is important in sewage treatment
plants, water purification works, and chemical mixing plants.  Of many varied
factors that affect settling, only the mean velocity of flow in a settling tank
can be easily controlled by the designer.  The control of mean velocity can be
readily achieved by fixing suitably designed weirs at the outlets of the settling
tanks or chambers.

*Weirs, *Sediment, *Sewage treatment, *Water purification, *Settling tank,
Flow velocity

*Proportional weirs
                                       616

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091F

EFFECTS OF INTRACELLULAR NUTRIENT POOLS ON GROWTH
DYNAMICS OF PHYTOPLANKTON,

Grenney, W. J., Bella, D. A., and Curl, H. C.

Utah State University, Utah Water Research
Laboratory, Logan, Utah

Journal of the Water Pollution Control Federation, Vol. 46, No, 7, p
1751-1760, July, 1974.  7 fig, 2 tab, 33 ref.

A three-compartment mathematical model has been developed to represent a
phytoplankton population having the capacity to store nitrogen in a nitrate-
limited environment.  Parameters were estimated by fitting the model to
equilibrium data from two chemostat experiments.  The model then was run to
simulate the transient chemostat conditions and the model response was com-
pared with the observed data.  The model is shown to provide a reasonable
representation of the sudden population surges associated with intracellular
nutrient storage.

*Mathematical models, *Model studies, Phytoplankton, Simulation analysis,
Data collections, Aquatic populations, Nitrogen, Nutrient requirements
092F

A PARTIAL AREA MODEL FOR STORM FLOW SYNTHESIS,

Engman, E. T., and Rogowski, A. S.

United States Department of Agriculture, Northeast
Watershed Research Center, Agricultural Research
Service, University Park, Pennsylvania

Water Resources Research, Vol. 10, No. 3, p 464-472, June, 1974.  8 fig,
1 tab, 28 ref.

A storm hydrograph model is described based on the partial contributing area
concept.  It utilizes a physically based infiltration capacity distribution
for computation of rainfall excess, and incorporates two stages of kinematic
routing.  In the first stage, the rainfall excess is routed over a flow plane
to become the lateral inflow hydrograph for the second or channel phase.  The
overland flow plane expands upslope as the infiltration capacity is exceeded
and the size of contributing area and the length of the flow plane are cal-
culated from infiltration curves.  The model attempts to account for the
natural watershed variability in terms of necessary input data and boundary
and initial conditions.  The data requirements are three:  two Manning's n
values, one for the channel and one for the overland flow plane, and the
initial soil water content.

*Hydrographs, *Model studies, *Storm flow, Simulation analysis, Infiltration,
Overland flow, Routing, Data collections, Mannings equation, Soil water
                                          617

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093F

THE BIODEGRADATION OF HYDROCARBONS,

Fasoll, U., and Genon, G.

La Chimica E L'Industria, Vol. 56, No. 3, p 191-195, March, 1974.  7 fig,
3 tab, 8 ref.

Self-purification of surface water is dependent on the ability of its micro-
organisms to decompose organic substances, such as hydrocarbons or amines.
Evaluation of time for the biodegradation and increase in the bacteria popu-
lation is thus a priory.  Two mathematical models, both based on Monod's
growth equation, are presented for the interpretation of experimental results
relating to hydrocarbon biodegradation.  They differ with respect to their
definition of the physical mechanism responsible for transfer of the hydro-
carbon from the water to the bacterial mass.  The numeric coefficients of the
kinetic equations are determined following establishment of the formal struc-
ture of the two mechanisms.  A comparison is also made between the two models
and their possible applications.

*Surface waters, *Self-purification, *Biodegradation, *Mathematical models,
Model studies, Hydrocarbons, Numerical analysis, Application techniques

Monod's equation
09 4F

TWO-DISTRIBUTION METHOD FOR MODELING AND SEQUENTIAL
GENERATION OF MONTHLY STREAMFLOWS,

Singh, K. P., and Lonnquist, C. G.

Illinois State Water Survey,
Urbana, Illinois

Water Resources Research, Vol. 10,  No. 4, p 763-773, August, 1974.
6 fig, 2 tab, 21 ref.

Distribution of observed monthly streamflows at many gaging stations exhibit
slight, moderate, or sharp reverse curvatures.  These cannot be accomodated
by the commonly used classical distributions such as the normal and gamma
(Pearson type 3) distributions applied to flows or their logarithms.  The
two distribution, essentially a bimodal distribution, fits most of these ob-
served distributions very well.  This distribution represents a unique and
versatile method for modeling and sequential generation of monthly stream-
flows.  The distributions of monthly streamflows generated by the two-dis-
tribution method fit observed flow distributions.  Annual flows obtained by
summing generated monthly flows also fit the observed annual flows quite well.

*Modeling, *Streamflow forecasting, *Gaging stations, Distribution patterns,
Flow
Bimodel distributions, Monthly flow
                                        618

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095F

THE PROBLEM OF DETERMINING THE MAXIMUM STORM RUNOFF YIELD
IN SMALL RIVERS (IN PROBLEMA DETERMINARII DEBITELOR MAXIME
DIN PLOT PE RIURI MICI),

Mustata, L.

Hidrotechnica, Vol. 19, No. 5, p 236-241, 247, May, 1974.  2 fig, 2 tab, 15 ref.

The determination of the maximum storm runoff yield in small rivers is based
on the utilization of the maximum runoff modality from the reductional equa-
tion, worked out for 7 various climatic zones, depending upon the climatic
conditions of Romania.  Seven series of module values were transposed on dia-
grams of the accuracy curves by using known empirical security values.  Thus,
the maximum security yield in percent and cu m/sec equals the elementary maxi-
mum runoff, or the maximum intensity of water replacement in cu m/sec sq km
multiplied by the receiving surface in sq km, divided by the receiving surface
plus 1 to the n power.  The maximum elementary runoff must be determined, con-
sidering the other parameters as known.  The n parameter varies from 0.46 in
the southwestern zone of the Southern Carpathians to 0. 5 in the southern part
of the Transylvania Plateau.  The empirical accuracy of the series was calcula-
ted according to the equation: P security value in percent equals m, the number
of the values in the series, divided by n, the number of the yrs of the series
plus 1, all multiplied by 100 percent.  In order to prolong the series of maxi-
mum yields for as long a period of time as possible, 7 climatically similar
zones were delineated.  The method presented permits the determination of maxi-
mum storm runoff yields in small rivers without using the statistical parameters
Cv and Cs.

*Mathematical models, *Storm water, *Storm runoff, Rivers, Climate

Romania
096F

DO-SAG IN OSCILLATING FLOW,

Li, W-H., and Kozlowski, M. E.

Syracuse University, Syracuse, New York,
Department of Civil Engineering

Journal of the Environmental Engineering Division, Vol. 100, No. EE4,
p 837-854, August, 1974.  9 fig, 11 ref.

The model formulae for steady—state concentration of biochemical oxygen
demand and dissolved oxygen in an oscillating flow due to a steady supply
of sewage from an outfall are presented.  When a pollutant is discharged
from an outfall into the tidal reach of a stream, the water passes the out-
fall many times before flowing further downstream, and increases the con-
centration of the pollutant in the water.  Equations were derived for the
maximum BOD and DO-deficit in an oscillating flow due to a steady supply of
BOD from an outfall.  While these computed maximum values serve as upper
bounds for the BOD concentration and DO-deficit in a tidal river with negli-
gible freshwater flow, the effects of freshwater flow on this model need
further investigation.

*Model studies, *Biochemical oxygen demand, *Dissolved oxygen, Pollutants,
Streams, Sewage, Freshwater

Tidal outfall, Steady-state concentration
                                        619

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097F

ON THE CHOICE OF METHODS FOR THE PREDICTION OF THE
WATER-ACTIVITY AND ACTIVITY COEFFICIENT FOR MULTICOMPO-
NENT AQUEOUS SOLUTIONS,

Sangster, J., and Lenzi, F.

Ecole Polytechnique, Montreal University,
Montreal, Quebec, Canada,
Department de genie chimique

The Canadian Journal of Chemical Engineering, Vol. 52, No. 3, p 392-396,
June, 1974.  2 tab, 22 ref.

Two thermodynamic properties of aqueous solutions that are of importance are
the solute activity coefficient (gamma) and the water activity aw.  A number
of methods of predicting solute activity coefficient and water activity for
multicomponent aqueous solutions exist.  These vary by complexity, accuracy,
and applicability.  Methods of prediction discussed are those by Reilly,
Wood, and Robinson (RWR), Robinson and Bower (RB), Meissner and Kusik (MK), and
Zdanovskii-Stokes-Robinson (ZSR).  The first three are limited to solutions
of electrolytes only, while the fourth also applies to solutions containing
non-electrolytes.

*Mathematical models, Solutions, Electrolytes, Solutes, Thermodnamics

Water activity, Solute activity coefficient
098F

MODERN UNSTEADY FLOW ANALYSIS METHODS AND 'APPLICATION
TO PIPELINE DESIGN  ECONOMICS,

Smith, B.

Hydraulic Analysis  Limited

Pipes and Pipelines International, Vol.  18, No.  3, p 20-24, June,  1974.   1  fig.

Traditional methods of  analysis  of the unsteady  flows  in  the  system are
based around  the  graphical method and can, under certain  conditions, give
excellent results.  However, such analysis can riot be  adapted for  use when
compressible  fluids are involved.  Modern analysis methods  are discussed
together with application techniques.  The Rotterdam Scheme in which the
existing valves and pipes were designed  to accept the  surge pressures re-
sulting  from  valve  closure at  the tanks  for the  original  flow low  rates  is
presented.

*Unsteady flow, Flow, Low flow,  Compressible  flow, Analytical techniques,
Application methods, Pipes,  Pipelines, Design criteria

Holland
                                        620

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099F

INDEPENDENT COMPARISON OF THREE URBAN RUNOFF MODELS,

Heeps, D. P., and Mein, R. G.

Monash University, Victoria, Australia,
Department of Civil Engineering

Journal of the Hydraulics Division, ASCE, Vol. 100, No. HY 7, p 995-1009,
July, 1974.  6 fig, 4 tab., 18 ref.

The scarcity of quantitative comparisons of urban runoff models prompted
the initiation of this study in Australia using the following three models:
the Road Research Laboratory (RRL) Method, the Storm Water Management Model
(SWMM), and the Cincinniati Urban Runoff Model (CURM).  These models were
selected for comparison because they were available and represent a range
of techniques and complexity.  They were applied to several storms on two
urban catchments following the recommendations of the developers of each
model.  Conclusions drawn from results reported indicate that:  the degree
of subdivision of the catchment has a significant influence on the peak
discharge predicted by each of the models; the CURM contains several de-
ficiencies; the SWMM was the model with the best overall performance but at
the expense of large computer storage and time requirements; and the RRL
model predicted poorly for storms in which previous runoff was significant
but performed reasonably well for many other types of storms.  A major pro-
blem with using noncontinuous models is the prediction of antecedent con-
ditions.

*Model studies, *Urban runoff, *Storms, Application methods, Performance,
Investigations, Rainfall-runoff relationships

RRL Method, SWMM, CURM
 100F

 EFFECT OF NITRATE AND  SEDIMENT  CONSTRAINTS ON
 ECONOMICALLY  OPTIMAL CLAY  PRODUCTION,

 Onishi, H.  and  Swanson,  E.  R.

 Illinois  Agricultural  Experimental  Station,
 Illinois  University, Urbana,  Illinois

 Journal of Environmental Quality, Vol.  3, No.  3,  p  234-238,  July-September,
 1974.  2  fig, 1 tab, 12  ref.

 Crop systems  and practices  that are economically  optimal  in  a  485.6-ha
 watershed with  a planned reservoir  were ascertained under conditions  of
 differing constraints  on water  quality  in the  reservoir.   Linear programming
 was  the technique employed.   Consideration was  taken of two  requirements
 related to sedimentation and  three  requirements related to N03-N concentration
 in the leachate below  the  root  zone.  Six combinations of restrictions on  the
 choice of optimal crop systems  were fulfilled.  For all sediment introduced
 into the  reservoir  a system of  charges  reduced  erosion, irrespective  of the
 limit put on  N03-N  concentration in the leachate  below the root zone.
 Relaxation of the limit  of N03-N from 10 mg/Hter to no limit  doubled the
 net  income above nonland costs.

 *Nitrate,  *Sediment, *Soil conservation, Linear programming, Optimization,
 Crop production, Erosion,  Watershed management, Root zone

 *0ptimal  crop production,  *Leachate, Conservation village, Nitrogen
 application rate
                                        621

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10 IF

INDUSTRIAL ECONOMIC MODEL OF WATER USE AND WASTE
TREATMENT FOR AMMONIA,

Galloway, J. A., Schwartz, A. K.,  and Thompson, R. G.

Houston University,
Houston, Texas

Water Resources Research, Vol. 10, No. 4, p 650-658, August, 1974.  7 fig,
5 tab, 9 ref.

A. linear programming method, which analyzes the consequences of policy, and
specifically water policy, on utilization of water in the production and
cost of ammonia, is presented.  The model is solved for each policy require-
ment to determine the most inexpensive process for ammonia production,
marginal costs of resource restrictions, and the price of water use and
waste water treatment.  Effects of raising the water charge for water with-
drawal and consequences of systematically reducing each effluent standard
to zero were considered.  Results obtained from application of these two
conditions were discussed.

*Linear programming, *Water policy, Ammonia, Waste water treatment, Effluents,
Model studies, Mathematical models

Economic models, Water withdrawals
102F

MULTILEVEL OPTIMIZATION FOR CONJUNCTIVE USE OF GROUND-
WATER AND SURFACE WATER,

Yu, W., and Haimes, Y. Y.

Case Western Reserve University, Cleveland, Ohio,
Systems Research Center

Water Resources Research, Vol. 10, No. 4, p 625-637, August, 1974.  7 fig,
6 tab, 22 ref.

A general systems analysis method, as opposed to a straight simulation approach,
for dealing with maximum conjunctive utilization of groundwater and surface
water supplies, is developed.  The aquifer system is represented by a two-
dimensional asymmetrical grid network model.  In considering water resource
management for a hypothetical system comprised of several subregions and a
common aquifer basin, it is suggested that the intersubregional aquifer
boundary conditions be regulated by a regional water agency and a pumping tax
be levied on the subregions'  local water boards to finance recharging of the
aquifer basin.  This model could be implemented by a two-level hierarchy with
a decentralized decision-making structure.

*Simulation analysis, *Groundwater, *Surface water, *Aquifer, Basin, Network,
Mathematical models, Recharge

*General systems analysis
                                          622

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10 3F

MULTIOBJECTIVES IN WATER RESOURCE SYSTEMS ANALYSIS:  THE
SURROGATE WORTH TRADE OFF METHOD,

Haimes, Y. Y., and Hall, W. A.

Case Western Reserve University, Cleveland, Ohio,
Systems Engineering Department

Water Resources Research, Vol. 10, No. 4, p 615-624, August, 1974.  4 fig, 1 tab,
36 ref.

The difficulties presented by noncommensurable multiobjective functions in
water resource systems are considered, as well as possible procedures in
multiobjective design theory.  The surrogate worth trade-off method for
solving noncommensurable multiobjective functions and the methods for deriving
these trade-off and surrogate worth functions are developed.  Prominent fea-
tures and advantages of this method are discussed.  Specifically, the trade-
off and surrogate functions are developed in the functional realm, and after
interaction with the decision-maker these are changed into the decision space.
To illustrate application of this method the Reid and Vemuri multiobjective
water resources problem was selected and solved.

*Water resources, *Economics, *Economic efficiency, Mathematical models,
Decision making, Resources

Noncommensurable multiobjective functions, Surrogate worth functions, Trade-off
104F

EFFECTS OF DEPOSIT RESUSPENSION OF SETTLING BASIN,

Takamatsu, T., Naito, M., Shiba, S., and Ueda, Y.

Kyoto University, Yoshida-honmachi, Sakyo-ku, Kyoto, Japan,
Department of Chemical Engineering

Journal of the Environmental Engineering Division, ASCE, Vol. 100, No. EE 4,
p 883-903, August, 1974.  18 fig, 4 tab, 12 ref.

A mathematical model is established to evaluate effects of deposit scouring on
the removal efficiency of a sedimentation basin.  Also, the most desirable
depth of the basin based on the proposed mathematical model is predicted.
The scouring effects are treated as a boundary value problem with the analytical
solution given.  The equation is reduced by averaging the dependent variable
with respect to a cross section to lend a one-dimensional diffusion equation.
With this formula, the existence of the optimum depth of a rectangular settling
basin is theoretically predicted and verified by a model basin experiment.

*Mathematical models, *Model studies, *Deposition (Sediments), Efficiencies,
Settling basins, Theoretical analysis

Scouring, Removal efficiency
                                         623

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105F

MATHEMATICAL MODELING OF HETEROGENEOUS SORPTION IN
CONTINUOUS CONTACTORS FOR WASTEWATER DECONTAMINATION,

Carnahan, R. P.

Clemson University

Dissertation Abstracts International B, Vol. 35, No. 1, p 282, July, 1974.

Because of strict water quality standards legislation, interest has increased in the
use of activated carbon to remove trace water contaminants.  An analytical
description of contactor dynamics as it effects mass transfer was derived.  These
are prerequisite in the development of a predictive model for adsorption of multi-
solutes of activated carbon by a differential contacting system.  Results of the
model studies indicated that the use of the film diffusion expression for adsorption
kinetics and the semi-competitive Langmuir expression provided good agreement with
experimental data at low concentrations.

*Mathematical models, *Adsorption, *Waste water treatment, Activated carbon, Model
studies, Kinetics
 106F

 MATHEMATICAL MODELING OF  UNSTEADY-STATE  THICKENING OF
 COMPRESSIBLE SLURRIES,

 Tracey,  K.  D.

 Clemson  University

 Dissertation Abstracts  International B,  Vol.  35, No. 1, p 286, July, 1974.

 A dynamic mathematical  model  of  the sludge thickening process has been  formulated
 and  the  model is verified by  conducting  laboratory scale continuous thickening
 experiments.   The model was based on the assumption that the downward movement of
 solids in a thickener was the result of  two factors, gravitational sedimentation
 and  bulk flow resulting from  the withdrawal of the underflow.  The model was used
 to simulate the performance of the secondary  clarifier in the activated sludge
 process.  Such similarities served to illustrate the utility of the model as a tool
 in the design and operation of water and waste water treatment facilities.  The
 thickener model should  be coupled with other  process models to simulate unit inter-
 actions.

 *Mathematical models, *Sludge treatment, *Sedimentation, Performance, Simulation
 analysis, Activated sludge, Treatment facilities, Design criteria, Model studies,
 Waste water treatment,  Slurries

 *Sludge  thickening
                                        624

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107F

LATERALLY INTEGRATED NUMERICAL WATER QUALITY MODEL FOR AN
ESTUARY,

Spaulding, M. L.

Rhode Island University,
Kingston, Rhode Island,
Ocean Engineering Department

Journal of Fluids Engineering, Vol. 96, No. 2, p 103-110, June, 1974. 12 fig, 23 ref.

A two-dimensional, laterally integrated, estuarine, numerical water quality model
was developed and applied to dissolved oxygen-biochemical oxygen demand system of
Narragansett Bay, Rhode Island.  It exhibited agreement with the existing data in
predicting vertical structure.  An application of the laterally integrated numerical
water quality model to storm-sewage overflow for the Bay also exhibited a favorable
comparison to the existing data.

*Estuaries, *Water quality, *Water pollution, Biological oxygen demand, Storm drains,
Mathematical models

*Two-dimensional, laterally integrated, estaurine, numerical water quality model,
*Vertical structure
 10 8F

 INVESTIGATIONS  ON FILTER HEADLOSS,

 Rao,  P.  V.,  Sen,  R.N.,  and Bhattacharyya, B.

 IIT,  Kharagpur,  India,
 Department of Civil  Engineering

 Journal  of the  Institution of  Engineers  (India), Vol.  54, No. PH2, p 66-70, February
 1974.  7 fig, 10  ref.

 An  important parameter  of restraint  for  the working of a rapid sand filter is headloss
 development, associated with the retention of suspended solids.  A correlation has
 been  made of the  time rate of  change of  headloss, with sand size and flow rate of a
 filter,  with the  optimization  of filter  performance in consideration.  Darcy's
 permeability coefficient was utilized as a filter performance parameter  in this study.
 The longevity of  a filter may  improved if the rate of  increase of headloss is reduced
 during the filter run by proper combination of sand size and rate of flow.

 *Head loss,  *Darcy's Law, Filtering  systems, Suspended solids, Flow rate, Hydraulics,
 Sands, Hydraulic  gradient

 *Darcy's permeability coefficient, *Rapid sand filter
                                      625

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 109F

 A CONTRIBUTION TO STATISTICAL DEPTH-DURATION-FREQUENCY
 ANALYSIS,

 Cao, C.

 Institute of Hydraulics,
 Cagliari University, Cagliari, Italy

 Journal of Hydrology, Vol. 22, No. 1/2, p 109-129, June, 1974.  8 fig, 4 tab, 9 ref.

 Current methods for evaluating the depth — duration — frequency analysis of point
 rainfall are unsatisfactory because of uncertainty due to the low density of
 recording station networks.  A new procedure is based on the grouping of stations
 exhibiting homogeneous characteristics, and on the use of one-day rainfall data
 available from more numerous non-recording stations.   Station-grouping is by means
 of analysis of variance theory; a rigorous statistical control is used.  A
 statistical criterion relates one-day depth distribution to shorter duration
 characteristics.  On the basis of linear regression theory, a new method of the
 depth-duration frequency is also suggested.  The new method, because of the lack of
 independence between observations, is not completely statistically rational.
However, for the example of application to a rain-gauge network of Sardinia, the
new method was shown to be superior to the conventional ones.

 *Statistics, *Depth, *Duration, Rainfall, Frequency,  Regression analysis,
Mathematics

Depth-duration-frequency,  Point rainfall, Sardinia,  Cagliari, Italy
110F

NONLINEAR LEAST SQUARES TECHNIQUES FOR SYSTEM IDENTIFICATION
IN WATER QUALITY,

Beliveau, J. G., and Mattingly, G.

Columbia University, New York,
Department of Civil Engineering

Journal of Environmental Systems, Vol. 41, No. 1, p 23-27,
Spring, 1974.  3 fig, 2 tab, 9 ref.

The supply of dissolved oxygen (DO) and biochemical oxygen demand (BOD) in
natural surface waters such as rivers and lakes are measurable quantities
which determine water quality.  By the use of water quality modelling systems
and records of these measurable quantities, the parameters governing system
response can be determined, and meaningful sets of pollution controls may
be imposed to keep water quality at or above acceptable standards.  Many
models have been proposed to represent the experimental observations, most
of these being variations of the classical Streeter-Phelps equation for the
oxygen-sag relationship in rivers.  Another model is described which con-
siders such effects—and respective parameters—as sedimentation, photo-
synthesis, runoff, reaeration rate, and the deoxygenation rate.  The method
of nonlinear least squares combined with eigenvalue perturbations and
parametric differentiation is used for parameter estimation for cases with
both BOD and DO data and for DO data only.  Both numerically generated test
cases and actual laboratory experiments were conducted; and the method is
applicable to both simple and complex models.

*Least squares method, *Dissolved oxygen, *Biochemical oxygen demand,
Water quality control, Mathematical models, Laboratory tests, Pollution
control, Surface waters, Parameters

Streeter-Phelps equation


                                          626

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111F

MODELLING OF SURFACE RUNOFF SYSTEMS BY AN ARMA MODEL,

Spolia, S. K., and Chander, S.

Indian Institute of Technology, New Delhi, India,
Department of Civil Engineering

Journal of Hydrology, Vol. 22, No. 3/4, p 317-332, August, 1974.
6 fig, 15 ref.

Autoregressive models have not previously been used for simulating surface
runoff systems because of inherent deficiency of data in short sequences of
rainfall and runoff resulting from a particular storm.  This investigation
was conducted to establish the relationship between deterministic and
stochastic models.  An autoregressive cum moving average (ARMA) formulation
for modelling of the surface runoff behavior of systems is proposed.  It
emerges from a model by Nash, which was found to be a special case of the
(n, n-1) ARMA model.  The proposed formulation corresponds to a conceptual
model of two linear reservoirs in series.  The moving average component of
the ARMA measures degree of persistence while the autoregressive part is
responsible for the distortion of the independence of the output random
variable.  The model was studied for its stability, nature of response
function, and range of parameter values.

*Simulations, *Surface runoff, Data analysis, Parameters, Mathematical
models, Storm runoff

*Autoregressive models, *Autoregressive cum moving average (ARMA),
*Stochastic models, Deterministic models
112F

SIMPLE METHOD FOR PREDICTING DISPERSION IN STREAMS,

McQuivey, R. S., and Keefer, T. N.

U. S. Geological Survey,
Bay St. Louis, Mississippi

Journal of the Environmental Engineering Division, Vol. 100,
No. EE4, p 997-1011, August, 1974.  5 fig, 1 tab, 16 ref.

Dispersion processes of pollution in streams have been studied through the
use of mathematical models.  These are usually based on transport equations
which contain a convective term due to average velocities and a dispersive
term which is the product of a dispersion coefficient and concentration
gradient.  An investigation was conducted to simplify experimental and
theoretical methods for measuring or predicting dispersion.  The purpose of
the study was:  to develop a simple method to predict longitudinal dispersion
coefficients from mean flow parameters; to predict dispersion coefficients
for several streams at various locations; and to compare the predicted dis-
persion coefficients using actual field time of travel studies with the
dispersion coefficients! obtained from Fischer's linear routing method.
From the equations given, it was found that there is an analogy between the
linear one-dimensional solute dispersion equation and the linear one-
dimensional flow equation for predicting longitudinal dispersion coefficients
in streams.  The relation has a standard error of estimate of approximately
30 percent, based on comparative data from 18 streams and 40 time-of-travel
studies.  The advantage of this procedure is that the dispersion of
coefficient can be predicted from existing basic hydraulic and flow
parameters.

*Hydraulics, *Streams, *Longitudinal dispersion, Flow, Parameters,
Mathematical models, Water pollution, Equations

Mississippi

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  113F

  THE APPLICATION OF STATISTICAL TECHNIQUES TO RIVER
  QUALITY MANAGEMENT,

  Oxley, N. C., and Wallis, B. F. J.

  EASAMS, Limited, Camberley,
  Great Britain

  Water Pollution Control, Vol. 73, No. 4,  p 449-455,  1974.   3 fig, 20 ref.

  The applicability of simple mathematical models and statistical techniques
  to water quality management are discussed.  Two main areas of data analysis
  provide the quantification for river management decisions.  These are the
  prediction of future levels of pollutants in a river system, so that
  quality standards may be set and justified and the organization of water
  quality monitoring systems to provide information both on a short term,
  daily basis and on a long term management basis.  A case study of the Thames
  River is described and illustrates that modelling for the physical situation
  provides a basis for the development of economic models to determine
  expenditures necessary for cleaning up polluted river systems and achieving
  maximum benefits.

  *Mathematical models, *Rivers, *Water quality control, *Statistics,
  *Water resources management  (applied), Costs, Pollution abatement

  Thames River, Great Britain
114F

LEAST COST DESIGN OF BRANCHED PIPE NETWORK SYSTEM,

Deb, A. K.

Roy F. Weston, Incorporated, West Chester, Pennsylvania

Journal of the Environmental Engineering Division, Vol. 100, No. EE4,
p 821-835, August, 1974.  4 fig, 4 tab, 8 ref.

A method for optimal analysis of the branched pipe network of known geometric
layout and water demands is described which incorporates different cost
functions.  The total cost of the pipes of the system relates to the distri-
bution of the total head loss among the different pipes in the branched
system.  For a given residual hydraulic head, inlet pumping head is propor-
tional to the total head loss.  Therefore, optimum total head loss produces
optimum pumping head.  The total pipe cost is inversely proportional to the
head loss.  The overall cost of the system decreases with the increase of
total head loss, reaches a minimum value, and then increases with an increase
in the head loss.  The cost functions used in the development of the least
cost design of a branched water main system are valid for England only.
The method given may be used in other countries by incorporating the constants
and exponents valid for their region.

*Pipes, *Pipelines, *Costs, *Head loss, Decision making, Economics

Great Britain, Branched pipe system
                                      628

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115F

THE ROLE OF MODELING IN ENGINEERING DESIGN,

Schaeffer, C. W.

Gilbert Associates, Incorporated, Reading, Pennsylvania

Public Works, Vol. 105, No. 9, p 78-80, September, 1974.  4 fig.

Although engineering models have been well accepted as design and communication
aids by the industrial community, the municipal services industry has only
slowly begun to use models.  The new waste water treatment plants involve
design and construction procedures about as complex as those for a chemical
plant.  Major problems of integrating new plant components arise when older
plants are upgraded to meet new treatment standards and increased influent
volumes.  Detailed reviews of plant design and operation is now required
by a larger number of public organizations and regulatory agencies.  Models
can be utilized in all these situations.  A rough-out or preliminary model,
usually of wood, polyurethane, or polystyrene, is utilized in the earliest
stages of design.  When design is in advanced stages, detailed engineering
models are used to help coordinate all engineering and design efforts.
Models of modular construction allow access to individual units for revision
and inspection.  Access roads, pipeline and utility routes, erosion controls,
landscape, architectural and esthetic factors can be analyzed before construc-
tion begins by using land site models.  Models can be used by the municipal
services industry in all stages of planning and construction of waste
treatment plants or water supply facilities.

Construction, *Design, *Model studies, *Facilities, Engineering, Domestic
wastes, Waste treatment, Environmental engineering, Project planning

*Engineering models
                                           629

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                    TUNNEL TECHNOLOGY



001G

PIPE JACKING — A TECHNIQUE FOR SOFT GROUND TUNNELLING,

Basu, N. K.

Cementation Company Limited,  Calcutta,  India

Indian Concrete Journal, Vol. 47, No. 9,  p 328-334,  343,  1973.   8 fig,  8 ref.

Pipe jacking is a technique which is found to be extremely useful for the con-
struction of sewer lines, pedestrian subways, and irrigation conduits below
ground without disrupting the surface,  particularly  in the case of soft ground
where traditional mining and tunnelling processes may be  difficult.   In addition
to a detailed explanation of the process  and jacking equipment, several examples
of the successful use of this method are  detailed.  It was employed for laying
a reinforced concrete sewer,  36.6 meters  long and 3  to 3.5 meters in diameter,
under railway tracks near Calcutta.  It crossed seven meters below the tracks,
and hardly interfered with the rail traffic.  It was probably the first time
a pipe of that size was jacked in India.

*Sewers, *Tunnels, *Pipes, Conduits, Engineering Structures.

*Jacking, *India, Calcutta
   002G

   GRANGEMOUTH TUNNEL  SEWER,

   Henry, K.

   Tunnels  and Tunnelling, Vol. 6, No. 1, p 25, 29, January-February, 1974.
   4  fig.

   The plans  and  construction of the Grangeoouth tunnel sewer are described.  The
   tunnel was constructed to form part of the Grangemouth Town Council's multi-
   million  dollar project for the modernization and expansion of the drainage
   system of  the  town.  Combined flows of domestic sewage, industrial effluent,
   and stormwater are  conveyed by the tunnel 1.60 km across the town center to a
   pumping  station on  the south bank of the River Carron.  Separate sets of
   raw sewage and stormtfater screws lift the flow nearly 10 m to pass through
   mechanical screens.  After screening, stormwater is discharged straight into
   the River  Carron and raw sewage is pumped by centrifugal pumps a further
   1.60 km  downstream  to the site of a sewage purification works shortly to
   be constructed.

   *Tunnels,  Sewers, Drainage Systems, *Domestic Wastes, Industrial Wastes,
   *Storm Water, Pumping, Construction

   Great Britain
                                        630

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 003G

 METHODS  VARY  ON MWD PIPELINES,

 Western  Construction, Vol.  49, No.  3, p  25-26, March,  1974.   1  fig.

 The four contracts  on the Metropolitan Water District's West  Valley and
 Calabasas Feeders for installing water transmission pipe ranging  in size
 from 54  to  103 inches in diameter are described.  There is a  comprehensive
 set of safety procedures that the contractor must follow which  are aimed at
 curbing  the public  hazards  associated with open trench work.

 *Contracts, Pipes,  *Safety  Factors, *Sewerage
004G

TURBULENCE CHARACTERISTICS IN A SMOOTH OPEN CHANNEL OF CIRCULAR CROSS-
SECTION (CARACTERISTIQUES DE LA TURBULENCE AU SEIN D'UN
ECOULEMENT A SURFACE LIBRE EN CONDUITE LISSE DE SECTION CIRCULAIRE),

Nalluri, C. and Novak, P.

Newcastle upon Tyne University, United Kingdom

Journal of Hydraulics Research, Vol. 11, No. 4, p 343-368, 1973.  10 fig,
1 tab, 24 ref.

Results of recent research dealing with determination of turbulence inten-
sities and energy spectra in water flowing in a smooth open channel of
circular cross section are presented.  In varying the depth in a channel
of circular cross-section a wide spectrum of shapjjs and types of flows is
encountered.  This variation is also clearly reproduced in the distribution
of the turbulence intensities and the shape of the normalized plots.  The
value of the intensities reflect the variation in channel shape particularly
at some distance from the wall and the free water surface.  At bigger depths
the crowning effect of the channel cross section causes an appreciable
increase of turbulence levels towards the free surface.  A detailed com-
parison of turbulence intensities with those recorded by other investiga-
tions in circular pipe flow or rectangular open channel flow shows some
agreement for a varying range of depths depending on the type of normalization
and plots used and confirms that in a channel of circular cross section the
flow changes from two to three dimensional as the depth increased.  The
measurements of the turbulence along 30 degree radial axis are comparable
with those measured along the vertical axis.  This applied also to a lesser
degree to measurements along a displaced vertical.

*Turbulence, *0pen Channel Flow, *Depth, Flow, *Cross-Sections, Numerical
Analysis, Investigations.

*Great Britain, France
                                           631

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Q05G

PRITTLE BROOK DIVERSION TUNNEL,

Trollop, K. S.

Deputy Borough Engineer and Surveyor, Southend-on-Sea

The Institution of Municipal Engineers, Vol. 101, No. 2, p 37-42, February, 1974.
7 figs.

The catchment area of Prittle Brook is described, in addition the character-
istics of the brook itself which is lined with concrete.  Severe storms in 1968
caused flooding.  Consideration was given to several alternatives for minimizing
risks of a similar occurrence in the future.  A tunnel diversion scheme was
chosen to alleviate conditions during storm flows.  The proposed scheme, imple-
mentation procedures, and sewers involved are described.  The tunnel itself
was constructed with little in the way of design problems; mechanical soft rock
tunneling procedures were used.  Excavation was by rotary drum digger and
steering was by hydraulic jack, all built into a shield.  The tunnel lining is
made of precast concrete blocks with a wedge section forced home by a ram.

*Tunnelling, *Tunnel Construction, *Flood Control, *Rivers, Storm Runoff

Prittle Brook
006G

SHOTCRETE AT MEXICO CITY,

Mason, R. E.

Tunnels & Tunnelling, Vol. 6, No. 2, p 59, 61-62, March, 1974.  5 fig, 2 ref.

The Mexico City drainage system includes 102 km of tunnels, in which there are
two interceptors and an outfall.  Most excavation was done by conventional methods
with a horseshoe tunnel section.  The geology is characterized by bentonltes,
lacustrine sandy and silty deposits, volcanics, and hard clays.  The lacustrine
deposits are very changeable  (heavy water flows in sandy beds, fractures in
the more blocky areas) and provided difficulty in tunnelling.  The volcanics
(rhyolotes, dacites, andesites, basalts) were blocky or highly fractured and
were sometimes accompanied by mylonization.  Major faults  in this area were accom-
panied by hydrothermal alteration.  The hard clays were often weakened by shear
or were in some areas blocky.  Shotcrete was used in the tunnelling to increase
the rate of operations.  Fifty-one spraying machines and 48 mixer-transporter
cars sprayed over 200,000 cubic meters of shotcrete dry-mix by mid 1973.  In the
volcanics, the Swedish method of shotcrete support was utilized — covering the
rock surface with a thin shotcrete coat and filling in corners and fractures;
while in the lacustrine deposits systematic patterns of fully-grouted, untensioned
anchors were used in addition to the shotcrete.  When montmorillonite clays were
encountered shotcrete and full section steel sets were used to resist swelling
pressures.  The shotcrete dry-mix was composed of aggregates, cement and
additives.  Under difficult conditions a  fast-setting coat was applied followed
by normal structural shotcrete.  Heavy water flows were dealt with by drainage
tubes and drain holes.  Shotcrete's effectiveness was proven for use in difficult
tunneling projects for the first time on this continent.

*Tunnel Construction, *Tunnel Design, *Tunnelling, *Gunite, Engineering Structures,
Drainage Systems, Mexico
                                    632

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007G

SMALL TUNNELS, LARGE  POTENTIALS,

Gosselin,  C.

Civil Engineering,  p  34-35, March,  1974.   3  fig.

A significant development  coming  out  of England  recently has been  the  intro-
duction of low cost,  small diameter tunneling, particularly the minitunnel,
a strong contender  for  the existing open  trench  market.  Such  tennels  lend
themselves to high  speed mechanization, which may  reflect  lower costs  yet
by eliminating trench digging.  Laser and automated  tunneling  will be  fully
exploited  in the  future.   Pneumatic transportation of  assorted materials is
discussed.

*Tunneling, *Tunneling  machines,  Automation, England

Minitunnel, Small diameter tunneling, Lasers, Pneumatic transportation
008G

FROST PROTECTION FOR WATERLINES,

Effluent and Water Treatment, Vol. 14, No. 1, p 55, January, 1974.

A new approach to the problem of frost protection of water lines has been
provided by the introduction of a self-limiting heater strip available from
Chemelex Heat Ltd.  The heater strip consists of an electrically insulated
polymeric conductive element in contact with two electrodes which are suitable
for direct connection to a power supply.  The current flows from one electrode
to another across the strip in a parallel circuitry configuration such that
the heater strip can be cut to length on site, limited only by the maximum
current rating of 10 amps per circuit.  The self-limiting feature in conjunc-
tion with the parallel circuitry permits the strip to be used in any circuitry
layout including wrapping over itself when tracing valves and pipe fittings.
Each section of the heater strip behaves independently of any other section
and adjusts its heat output according to its local temperature, which will
depend on the balance between heat input and heat loss rates.  These factors
depend on pipe diameter, insulation grade and thickness, and variations in
ambient temperature.  The heater strip may be used on different pipe sizes
in the same electrical circuit.

*Heat treatment, *Pipes, *Frost prevention

*Heater strip, England
                                       633

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 009G

 NORTHERN  ILLINOIS USES  STORAGE EFFECTIVELY,

 Fowler, D.  P.

 Energy Pipelines and  Systems, Vol.  1, No. 4, p 46-47, April,  1974.

 The use of  natural  underground aquifiers by the Northern  Illinois Gas  Co.
 for storage of natural  gas  is described.  The aquifiers are large, water bearing,
 dome  shaped rock layers of  porous sandstone.  The  sandstone spaces hold water
 much  like gigantic  sponges.  Natural  gas is pumped or injected into  the
 sandstone at pressure great enough  to push the water aside, and  then downward.
 An overlying layer  of impermeable caprock, usually shale  or dense limestone
 keeps the gas from  migrating to  the surface.  As more gas is  injected, the
 shape of  the dome provides  the unique trapping mechanism.  The aquifiers deliver
 as much as  25% of the total gas  sold  during the wintertime, and  as much as
 55% of the  gas distributed  on an exceptionally cold day.

 *Sand aquifiers, *Natural gas, *Storage

 Northern  Illinois Gas Company
010G

STRESSES GENERATED IN NON-CIRCIRCULAR TUNNEL CASINGS BY
GROUNDWATER PRESSURE,

Fotiyeva, N. N.

Fiziko-Teknicheskiye Problemy Razrabotki Poleznykh Iskopayemykh,
No. 1, p 18-23, 1974.

A method for the calculation of tunnel casings of irregular
shape (with one symmetry axis) with respect to the stresses
generated by groundwater pressure is presented.  The method
is based on the resolution of the plane contact problem ac-
cording to the elasticity theory on the equilibrium of non-
circular rings.  Formulae for the determination of the boundary
conditions, and of the normal radial and tangential stresses
as generated by groundwater pressure in such tunnel casings
are given.

*Tunnels, *Equilibrium, *Groundwater, Pressure, Equipment

Tunnel casings
                                         634

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011G

TUNNELLING WITHOUT BLASTING,

Water and Sewage Works, Vol. 121, No. 6, p 64, June, 1974.

A sewer outfall tunnel is being bored through solid bedrock underneath
Rochester, New York by the Insana Construction Company.  The new boring
machine, the Mini-Fullfacer, bores a straight-walled 5- x 8-foot tunnel
through solid rock at rates comparable to conventional methods without
the inconvenience of overbreak due to blasting.  A single cutter disc
with cemented Sandvik Coromant carbide bits swings up on a hydraulic
cylinder while at the same time rotating and undercutting the rock.  Cut
and broken rock falls to the tunnel floor and is removed to the rear by
means of a continuous chain conveyor built into the base of the machine.
Mucking machines behind the Mini-Fullfacer trailer remove the rock cut-
tings from the tunnel.

*Construction equipment, *Tunnelling machines, *Tunnel construction,
*Sewers, Tunnelling


Rochester, New York
                                   635

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                           HYDROLOGIC ASPECTS



001H

TWO SUSPECTS IN TASTE MYSTERY,

Water and Pollution Control, Vol. Ill, No. 12, p 26-28, December, 1973.

The source of noxious odors and a taste in the drinking water at Markham,
Ontario, was investigated.  The problem appeared to come from the Sabiston
Well located 700 feet from an industrial refuse disposal site.  Leachate
migrating from the landfill was suspected as the cause.  The groundwater
quality around the site was studied to assess the direction of groundwater
movement and determine whether contaminants were moving from the landfill
to the wells.  The Sabiston and two other wells drew water from a common
aquifer which also stretched under the landfill.  A stream flows over a
portion of the aquifer and apparently recharges the aquifer.  There were
variances in the groundwater chemistry, particularly in chlorides and
hardness.  Due to changes in the level of the water table, the stream
changed from being effluent to influent in the vicinity of the Sabiston Well.
It is concluded that the water quality in the stream could have adversely
affected the well.  The contaminants could reach, and may have reached,
the municipal wells.  But the long travel time (estimated 1.4 feet/day)
plus numerous variables and uncertainties make it difficult, if not impossible,
to connect the landfill conclusively with the reported taste problem.

Canada, *0dor, *Taste, *Leachate, Landfills, Industrial Wastes, *Aquifers,
*Streams, Water Table Aquifers, *Recharge

*Markham, *0ntario, Sabiston Well
  002H

  EFFECTS OF ROAD SALT IN WINTER,

  Van de Voorde, H. , Nijs, M., and Van Dijc, P. J.

  Public Health Laboratory, Catholic University, Louvain,
  Belgium.

  Environmental Pollution, Vol. 5, No. 3, p 213-217, 1973.  1 fig, 2 tab, 10 ref.

  The effect of salt treatment of roads in winter was investigated by
  assaying the salt concentration in three streams and soils over a two year
  period in Louvain, Belgium.  Salt increased the chloride concentration in the
  Doyle River, which crosses  the city, and the Voer River, a rural stream, by
  nearly 20-30 milligrams/liter for only 24 hours.  The mean chloride concen-
  tration for the rivers is irregular.  The fluctuations are due to rainfall
  diluting the salt.  The chloride in the rivers originates principally from
  domestic sewage which gives  fairly constant levels.  The amount of the salt
  deposited on the banks of the roads filters down to the phreatic water and
  locally increases the chloride concentration of the groundwater, but not to a
  concentration which can be  considered harmful to the health of consumers.
  Other minor disadvantages of road salt are damage to ornamental vegetation
  and corroding effect on metallic surfaces.  The hazards of the use of road
  salt are negligible compared with traffic safety benefits.

  Rivers, Streams, Roads, *Highway Icing, *Snow Removal, *Salinity

  Belgium, *Dyle River
                                          636

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003H

COMMENT ON WATER POLLUTION IN LAKE MICHIGAN FROM POLLUTION
AEROSOL FALLOUT,

Skibin, D.

Atomic Energy Commission, Nuclear Research Centre-Negev,
P. 0. Box 9001, Beer Sheva, Israel

Water, Air, and Soil Pollution, Vol. 2, No. 4, p 405-407, December, 1973.  10 ref.

The hypothesis that air pollution is a major source of some water pollution
trace elements in Lake Michigan was reexamlned.  Hazards evaluation techniques
were used to assess the overall transfer efficiency of pollution from air to
the lake.  This efficiency was found to be at least 25 percent which supports
the hypothesis.  Four new trace elements were found:  aluminum, chromium,
sulfur, and iron.  It is recommended that the problem be further studies,
taking into account local mesoscale systems such as a lake breeze,  distribution
of air trajectory, and wind speed.

*Air Pollution Effects, Pollutants, *Water Pollution, *Lake Michigan,
*Metals, Aluminum, Chromium,  Iron, Sulfur, winds, *Trace Elements
004H

THE SNODLAND-IGHTHAM REGIONAL DRAINAGE SCHEME:  DESIGN
AND OPERATION,

Kellock, R. W.

Water Pollution Control, Vol. 72, No 8, p 658-665, 1973.  7 tab.

As a result of investigations since the late 1950's, extension to the treatment
works at the Snodland and Crouch areas has been undertaken.  In the scheme
there are six pumping stations and six ejector stations conveying sewage a
maximum of 16 km.  All the stations are of a standard design, fitted with
dataphonic equipment, and maintained by one crew of two men.  Sewage treatment
is examined together with equipment employed at the facilities.  Sludge
treatment and operational procedures are examined.

*Sewage Treatment, Treatment Facilities, Pumping Plants, Flow Measurement,
Equipment, Sludge Treatment, *0peration and Maintenance, *Data Collections,
Performance

Great Britain, *Facilities Extension
                                        637

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005H

PHYSICAL EFFECTS OF MAINTAINING DRAINAGE CHANNELS IN NORTH
CAROLINA'S COASTAL AREA,

Swicegood, W. R. and Kriz, G. J.

Journal of Soil and Water Conservation, Vol. 28, No. 6, p 266-269, November-
December, 1973.  5 fig, 1 tab.

Results of a study to determine the effectiveness of maintenance programs on
the water carrying capacities of typical eastern North Carolina channels
showed a general trend toward capacity loss at a rate that would require com-
plete channel modification every 10 to 15 years.  The loss appears to be
principally caused by uncontrolled vegetation, which emphasizes the importance
of mowing the bottom and lower sections of channels.

Investigations, Performance, North Carolina, *Channels, Channel Flow,
Vegetation, *Vegetation Effects, *Maintenance, Flow Rates, Coasts

Water Capacity, *Capacity Loss
006H

TEST RESULTS ON BUOYANT JETS INJECTED HORIZONTALLY IN A
CROSS FLOWING STREAM,

Ayoub, G. M.

Water, Air, and Soil Pollution, Vol. 2, No. 4, p 409-426, December, 1973.
12 fig, 1 tab, 5 ref.

Experiments were conducted to study the behavior of axi-symmetric turbulent
buoyant jets injected horizontally in a cross flowing current.  Material
concentration profiles were measured across various sections along jets of
different parametric values.  From these profiles, concentration distribution
curves as well as maximum concentration and diluted values and their variation
with distance along the jet were determined.  Half jet radius values were
calculated to study the expansion of the jet.  Jet boundaries and trajectories
were studied photographically and compared with measured values.   The effect
of the ambient current on the overall shape of the jet was established by the
study of the measured complete concentration section across the jet.

*Simulation Analysis, Investigations, *Turbulent Flow, ^Currents  (Water),
Jets, Distribution Patterns, *Mathematical Studies

Concentration Distribution, Maximum Concentration, Concentration Dilution
                                        638

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007H

ESTIMATING LAND USE CHARACTERISTICS FOR HYDROLOGIC MODELS,

Gluck, W. R.,  and McCuen, R. H.

Rummel, Klepper and Kahl Consulting Engineers,
Baltimore, Maryland

In:  55th Annual Meeting, American Geophysical Union, April 8-12, 1974.
Washington, D. C., p 250.

Many hydrologic models such as storm hydrograph models and continuous hydrograph
simulation models are being developed or redesigned to provide more accurate
analyses of unrbanized watersheds.  Among the data requirements of urban water-
shed models are estimates of land use characteristics, including percentage
of impervious area.  Census tract information, such as population density and
housing density, is available for most urban and suburban areas and is highly
correlated with many important land use characteristics.  Estimates of land
use characteristics obtained from a systematic sampling of aerial photographs
were related to variables obtained from census data.  The nonlinear relation-
ships are useful for predicting land use characteristics required by urban
watershed response simulation models.

*Model Studies, Hydrologic Data, Hydrographs, *Watersheds (Basins),
*Storms, *Land Use, *Infiltration

Urban Watershed Models
   00 8H

   A NEW NATURAL FACTOR IN THE SELF-PURIFICATION OF WATER-
   BASINS (A VIZTAROLOK ONTISZTULASANAK UJ TERMESZETES TENYEZOJE),

   Szidorenko, G. I., Bagdaszarjan, G. A., Talajeva, J. G.

   Egeszsegtudomany, Vol. 17, No. 4, p 350-355, 1973.

   The problems of microbial contamination in open water basins and other
   water sources are discussed with respect to potable water, and increasing
   industrial effects.  Some microorganisms in the water and soil are known to
   kill human pathogens; the most exhaustively studied phenomenon is self-
   purification by Bdellovibrio in water basins.  Culturing, biological features
   and temperate-zone incidence of the Bdellovibrio have been investigated in
   detail by the Sisin Institute since 1968.  The seasonal changes in their
   incidence and occurrance of new strains have been documented.

   Water Pollution, Microorganisms, *Pathogenic Bacteria, *Water Purification

   *Bdellovibrio, Sisin Institute, *Self-Purification
                                            639

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009H

GROUNDWATER RECHARGE WITH TREATED WASTEWATER,

Fetter, C. W., Jr., and Holzmacher, R. G.

Department of Geology, University of Wisconsin, Oshkosh,
Wisconsin

Journal of the Water Pollution Control Federation, Vol. 46, No. 2,
p 260-270, February, 1974.  77 ref.

Artificial recharge of aquifers is a method for the conservation of groundwater
resources.  Research shows that renovated wastewater may be suitable for
recharge.  Usage of stream channels, open basins, and spary irrigation
using present technology is possible with a secondary effluent.  Suspended
solids in the effluent determine the amount of facilities maintenance
necessary; wastewater of high quality is mandatory for artificial recharge
through wells.  Recharge wells may be clogged by slight turbidity or bacterial
growths.  The relationship between rate of well clogging and water quality
merits further research.  In the case of a fine- or medium-grained aquifer,
several hundred feet of travel seems to eliminate problems from pathogenic
bacteria or virus.  This does not hold for a fissured aquifer.  A suggested
area of further research is in thy physical and biological processes that
occur in the soil.

*Aquifers, *Recharge, *Groundwater, *Aquifer Management, Aquifer Characteristics,
Rock Properties, Groundwater Recharge, *Recycling, *Waste Water Treatment,
Wells
010H

THERMODYNAMICS OF SOIL WATER:  IV.  CHEMICAL POTENTIAL OF
SOIL WATER,

Iwata, S.

National Institute of Agricultural Science, 2-1, Nishigahara,
Klta-ku, Japan.

Soil Science, Vol. 117, No. 3, p 135-139, March, 1974.  7 fig, 3 ref.

The relationship between the chemical potential of water adsorbed to K-
montmorillonite and film thickness of adsorbed water was theoretically
calculated by establishing an adsorption model.  This relationship was com-
pared with experimentally obtained results which yielded a good comparison.
In addition, the decrements of chemical potential due to the solute, the
force field, and the electric field were each compared.

Adsorption, Model Studies, *Soil Water, Thermodynamics, Montmorillonite,
Theoretical Analysis, Chemical Potential

Japan
                                        640

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011H

DIRECT MEASUREMENT OF WATER MOVEMENT IN THE ZONE OF AERATION,

Nlelson, D. R. and Corey, J. C.

California University,
College of Agricultural and Environmental Sciences.

Transactions, American Geophysical Union, Vol. 55, No. 4, p 183-186,
April, 1973.  1 fig, 23 ref.

The state of the art of three methods of direct measurement of soil water
movement in the zone of aeration are reviewed.  The approaches include:
monitoring the rate of change of the distribution of soil water content
within the zone; calculating the water movement on the basis of measured
values of the forces acting on the water and the soil transmlssibility co-
efficients; and following the movement of a tracer to identify the direc-
tion and rate of water flow.  Although accurate estimates of water flow
have been obtained by using the three techniques, almost without exception,
measurements have been confined to small plots of land only a few meters
square.  Measurement and predictions are needed that can be applied to large
land areas such as those of a field cultivated for crop production, of
range or forest land, or those of sufficient size to be significant in
managing land and water resources.

*Measurement, *Reviews, *Soil Moisture, Flow Measurement, Water Resources,
Flow, Soil Water, Soil Water Movement, Monitoring, Tracers
012H

THE POTENTIAL APPLICATION OF SATELLITES IN RIVER REGULATION,

Painter, R. B.

Institute of Hydrology, Wallingford, Berks, Great
Britain

Water and Water Engineering, Vol. 77, No. 934, p 487-491,
December, 19731  1 tab. 14 ref.

Some of the problems of efficient operation of regulating reservoirs are
discussed with particular reference to the measurement and transmission of
data.  Remote sensing systems and existing methods of transmission of ground
data via satellites are described, and their potential use in river regula-
tion is discussed.  Satellites are potentially the most suitable platform
for operational remote sensing, due to their capability for repeated
coverage of large areas.  Viability was proven by a rigorous cost/benefit
comparison between a satellite based system and conventional measuring
techniques.  A satellite based system has the potential to be considerably
cheaper than a landline based system.  Whether it will be depends on many
factors, such as required frequency of transmission, which might necessitate
a geostationary satellite.

*Rivers, *Reservoirs, Data Transmission, Measurement, Satellites (Artificial),
Remote Sensing, Cost-Benefit Analysis

Great Britain
                                       641

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 013H

 NEW ROLLER GATE IMPROVES  THE RIVER WALK,

 Public Works,  Vol.  105, No.  4,  p  90,  April,  1974.   1  fig,  6  ref.

 The new water  control  structure which replaced  a dam  at  the  downstream of
 the River  Walk,  a  loop of the San Antonio River in  downtown  San Antonio,
 Tex.,  is described.  It provides  better flow control  and increases  the
 navigable  length of  the waterway.   The two phase project involved the
 addition of a  new water control gate  between the bypass  channel of  the River
 Walk and the main  channel of the  San  Antonio River, plus relocation of an
 existing tainter gate  further downstream on  the river proper.  When water
 in  the main channel  of the San  Antonio River reaches  higher  levels, the
 top section is lowered to prevent  floodwaters from  entering  the River  Walk
 loop.

 *Water Control,  *Hydraulic Structures, Rivers,  Flow Control, Roller Gates,
 *Flood control

 *San Antonio,  Tex.
014H

HYDROLOGICAL EFFECTS OF URBANIZATION,

Heindle, L. A.

United States National Committee for the
International Hydrological Decade

Transactions, American Geophysical Union, Vol. 55, No. 4, p 190-191,
April, 1974.

A total of 54 experts from 23 countries participated in the International
Workshop on the Hydrological Effects of Urbanization.  The workshop com-
pleted its set task of reviewing the draft report.  The report, which will
be published by the time of the End-of-Decade Conference in 1974, describes
the effects of urbanization on the hydrological circle and identifies research
needs for the next few years.  The report is directed primarily at researchers
in hydrology, but will have a special summary of interest to water managers.

Urbanization, *Urban Hydrology, Urban Socioloty, Hydrology, Organizations,
Water Management (Applied), Water Resources Development

*United States National Committee for the International Hydrological Decade
                                         642

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015H

GROUND-WATER FLOW PATTERNS IN CONFINED AQUIFIERS AND POLLUTION,

Klrkham, D., and van der Plieg, R. R.

Director, Iowa State Water Resources Research Institute,
Iowa State University of Science and Technology,
Ames, Iowa

Journal of the American Water Works Association, Vol. 66, No. 3, p 192-197,
March, 1974.  4 fig, 13 ref.

Flow patterns under steady-state conditions in horizontal confined aquifers of
any shape pumped by a well have been developed theoretically.  The aquifer
boundary may be impervious or pervious.  The pervious boundary may have a
variable head distribution.  A number of flow nets are presented and interpreted
with regard to pollution hazards of the pumped well water.  When velocities are
low a source of pollution will not be as dangerous as an equal source at a
location in the pumped aquifer where the velocities are high.  The theory is
valid for any shape of aquifer and any diameter of well for any location of
the well in the aquifer,  The steady-state approximates nonsteady-atate condi-
tions.

*Mathematical Models, *Aquifers, *Water Wells, *Flow Characteristics,
*Groundwater Movement, *Pollution Identification, Pollutants

Flow Nets
016H

GROUND-WATER RECHARGE STRIP BASIN-EXPERIMENTS,

Brock, R. R., and Amar, A. C.

Chairman of Civil Engineering Department, California
State University, Fullerton, California

Journal of the Hydraulics Division, Proceedings of the American Society of
Civil Engineers, Vol. 100, No. HY4, p 569-592, April, 1974.  12 fig. 2 tab,
15 ref.

Experimental results from a laboratory sand model for the case of recharge from
an infinite strip to an initially horizontal water table overlying a horizontal
impervious base are presented.  The dimensionless rise of the water table
depends on many variables.  As the dimensionless recharge rate from the basin
is increased the nonlinear behavior is increased, and the effect of a deep flow
versus a shallow flow is given by increasing the dimensionless depth.  Experiments
in a sand model give results which are summarized in a curve of dimensionless water
table rise plotted against dimensionless time.  Relationships between the many
parameters are detailed.

*Model Studies, *Mathematical Models, *Water Table, *Recharge, Groundwater
Recharge, Water Supply

Recharge Rate
                                      643

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 017H

 DISTRIBUTION OF MOISTURE IN THE UNSATURATED SOIL PROFILE
 ON A PIEDMONT WATERSHED,

 Ligon,  J.  T., and Wilson,  T.  V.

 Clemson University,  Clemson,  S. C.,  Dept.  of Agricultural
 Engineering

 Transactions of the  ASAE,  Vol.  16,  No.  6,  p 1100-1103,  November-December,  1973.
 15 fig,  6  ref.

 The distribution of  moisture  was investigated in the unsaturated soil profile of
 a 0.21  acre plot within a  28.4  acre watershed of the 561 acre Clemson Research
 Watershed  in the Piedmont  area.  Intensive measurements were  made of soil  mois-
 ture to a  depth of 32 ft along  with measurement  of  precipitation, surface
 runoff  and interflow to provide some indications of the nature of the deep seep-
 age groundwater recharge phenomenon in  this region.   It is  apparent that down-
 ward seepage below the zone of  root influence is a  continuous process but  that
 the rate of transfer at a  point increases  rapidly with  increased moisture  con-
 tent.   At  this particular  site, where the  water  table occurs  at a depth of 60-
 65 ft,  there is a considerable  lag  between the occurrence of  excess moisture
 at the  soil surface  and groundwater recharge resulting  from this excess.  The
 extent  of  this time  lag is a  function of initial soil moisture due to the  strong
 dependence of unsaturated  conductivity  upon moisture content.

 *Soil profiles, *Moisture  content,  *Watersheds (Basins), Soil moisture,  Surface
 runoff,  Precipitation (Atmospheric), Subsurface  runoff, Seepage, Root zones,
 Groundwater

 Clemson Research Watershed
018H

THE EFFECT OF DATA DENSITY ON GROUNDWATER CONTOURING
ACCURACY,

Davis, P. R., and Matlock, W. G.

Arizona University, Tucson, Dept. of Water and Engineering

Transactions of the ASAE, Vol. 16, No. 6, p 1112-1116, November-December, 1973.
7 fig, 1 tab, 3 ref.

The effect of different data densities on contour maps representing fairly
uniform data was investigated.  Tests were conducted in California on a ground-
water basin of 780 sq miles.  The Standard Map for the basin was drawn from
445 randomly located data points which covered an Interior area of 411 sq
miles.  Spacings between input points of 1, 4, and 6 miles were analyzed with
three tests each on the 4 and 6 mile spacings.  Tests were also made on a 6
mile triangular grid and a semirandom grid obtained by dividing the area into
squares 6 miles on a side and then randomly selecting a grid interaction within
each square.  The number of tests conducted was insufficient to draw any con-
clusions, but the tests support the belief that the more observations there are,
the more accurately the surface will be defined.  For investigations where
detailed groundwater contour maps are not required,, a data density with approxi-
mately 4 miles between point is suggested.  Additional data points may be added
near the fringes if extended control is necessary.

*Investigations, *Groundwater basins, Contours, Mapping, California

Data density
                                          644

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 019H

 AMERICAN RIVER PLANT ADDS AUTOMATED PUMPING STATION,

 Instrumentation,  Vol. 27, No,  1,  p 6-9,  1974,  6 fig.

 The  Florin  Reservoir and Pumping  Station of the American River Water Treatment
 Plant  is described.   It  is a remote-control, unmanned facility built completely
 underground in Sacramento, Calif.   The Florin  station is equipped with instru-
 mentation which automatically  starts,  stops, or throttles the  appropriate com-
 bination of three horizontal centrifugal split case pumps.   Completion of the
 Florin Station represents a significant  step in Sacramento's master plan  of
 water  system development and expansion to the  year  2030  when the  plant will
 handle 330  mgd.

 *Reservoirs,  *Pumping plants,  *Automatic control, Remote control,  Water supply
 development

 *Sacramento (Calif.), *Florin  Reservoir
020H

QUALITY OF DRAINAGE WATER FROM A HEAVY-TEXTURED SOIL,

Schwab, G. 0., McLean, E. 0., Waldron, A. C., White, R. K.,
and Michener, D. W.

Ohio State University, Columbus, Dept. of Agricultural
Engineering

Transactions of the ASAE, Vol. 16, No. 6, p 1104-1107, November-December, 1973.
2 fig, 3 tab, 11 ref.

Sediment, dissolved solids, nine chemical elements or ions, five pesticides,
electrical conductivity, pH, and BOD in tile drainage effluent and in surface
runoff were measured from one-half acre plots on Toledo silty clay soil near
Sandusky, Ohio, from March 1, 1969 through September 30, 1971.  Rainfall was
above average in 1969 and 1970 and below average in 1971.  Sediment losses were
about the same in the tile effluent and in the surface runoff.  Nitrate nitro-
gen losses were generally low (about 13 to 19 Ib/acre/yr).  With two exceptions,
phosphorus losses were less than 1.5 Ib/acre/yr, but they were greater in the
surface runoff than in the tile effluent.  Potassium losses in the surface
runoff were 10-13 compared to 4 Ib/acre/yr in the tile effluent.  Sodium,
chlorine, and HC03 losses were higher in the tile effluent than in the surface
runoff.  The average electrical conductivity of the tile effluent and the sur-
face runoff from rainfall were about the same (729-1062 micromhos/cm),  The
BOD of the drainage water was insignificant, being less than 0.3 Ib/acre.
*Sediments, *Pesticides, Biochemical

XlXSS )  LJJ.J.L.O ) \JJ-GLJ ) iJUJ-J-u ) J.UA .*.•*.
Nitrogen, Phosphorus, Potassium

Toledo silty clay soil
.ments, *Pesticides, Biochemical oxygen demand, *Dissolved solids,  Inves-
.ions, Hydrogen ion concentration, Conductivity, Surface runoff, Effluents,
 , Silts, Clay, Soils, Rainfall, Chlorine, Sodium, Drainage, Nitrates,
'gen, Phosphorus, Potassium
                                           645

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021H

THE DEVELOPMENT OF MEANDERS IN NATURAL RIVER-CHANNELS,

Hlckin, E. J.

Simon Fraser University, Dept. of Geography,
Burnaby 2, B. C., Canada

American Journal of Science, Vol. 274, No. 4, p 414-442, April, 1974.
8 fig, 3 tab, 4 plates, 20 ref.

Investigations of the meander growth-patterns of the Beatton River in
northeast British Columbia indicate that there is a critical value of the
ratio radium of channel curvature to channel width (rm/w) which, once reached
by a developing meander, exerts considerable control over subsequent direction
and rate of lateral migration.  Furthermore, the critical value of rm/w, which
is readily identifiable from the pattern of flood-plain surface deposits,
appears to be much less variable in nature than is a similar parameter des-
cribed by Leopold and Wolman in 1960.  On the Beatton River the critical
value of rm/w averages 2.11, and standard deviation is only 0.13.  The
pattern of meander growth is discussed in terms of the dynamics of open-
channel flow.  Some implications of the study for river engineering and
palacohydrological investigations also are presented.

*Channels, Flood plains, Channel morphology, Channel erosion, Open channel
flow, Hydraulic engineering, Canada

*Channel migration, Beatton river
022H

MANAGING WATER RESOURCES FROM THE WRONG PLACE AT THE WRONG
TIME,

McCullough, C. A.

Statewide Planning Branch, Division of Resources
Development, Department of Water Resources, Resources Agency,
State of California, Sacramento, California

Journal of the American Water Works Association, Vol. 66, No. 3, p 187-192,
March, 1974.  6 fig, 1 ref.

The economic development of California has been achieved first through the use
of summer flows of streams and drilling of wells in extensive groundwater
basins.  As these sources were overexploited storage of winter flood flows
and massive transportation facilities were constructed with subsequent ex-
tensive water quality control programs being implemented.  The California
Water Plan, which consists of an inventory of the water resources of the
state, an assessment of the water requirements of the state under the assump-
tion of urban or irrigation development of all irrigable land in the future,
and a reconnaissance plan for possible supply, conservation, and transporta-
tion of water resources, was undertaken.  As the first project initiated as
a result of this plan, the California State Water Project, detailed herein,
was started in 1957 and completed in 1973.

California, *Water resources, *Water quality control, *Water supply,
*Water supply development, *Water transfer, *Project planning, Surveys

California State Water Project, California Water Plan
                                           646

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023H

WATER QUALITY AND OTHER ASPECTS OF GROUND-WATER
RECHARGE IN SOUTHERN CALIFORNIA,

Toups, J. M.

Toups Engineering Inc., Santa Ana, California

Journal of the American Water Works Association, Vol. 66, No. 3,
p 149-151, March, 1974.  2 tab.

Groundwater recharge became necessary in southern California during the 1950s
because groundwater levels along the coastline had dropped below sea level
in many places and sea water was intruding into the groundwater basins.  Various
methods of recharge were tried to alleviate the problem.  These methods and
reasons for using them are presented.

*Groundwater recharge, California, *Ponding, Injection wells, Water supply
development, Water spreading, Flood control, Water quality control
024H

THE SEDIMENT-TRANSPORTING CAPACITY OF ALLUVIAL STREAMS,

Bogardi, J. L.

Martirok u. 31-33, 1024 Budapest, Hungary

Acta Technica Academiae Scientiarum Hungaricae, Vol. 75, No. 1-4,
p 59-70, 1973.  3 fig, 9 ref.

No exact method is available today for determining the sediment-transporting
capacity of alluvial streams.  For this reason the work per unit time expended
for keeping the sediment in suspension is related to the full energy consumption
of the sediment-carrying stream in unit time.  The sediment carried in
streams is in general less than the amount pertaining to saturation and thus
the sediment-transporting capacity estimated from observed concentration is
essentially not more than a theoretical transporting capacity related to a
particular gaging section and influenced by the combination of all hydrologic
factors.  Besides the detailed treatment of various relations on sediment-
transporting capacity, a physically well founded parameter is introduced.
The sediment-transporting capacity of the Danube, the Tisza and the Raba
rivers is examined by comparing the values defining the boundary conditions
of channel erosion and saturation.

*Alluvial channels, *Sedlment transport, Sediment load, Suspended solids,
Boundary layers, Boundaries (property), Mathematical studies, Estimating
equations, Hydrologic aspects, Rivers


Danube River, Tisza River, Raba River
                                          647

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 025H

 HYDRAULIC RESISTANCE  IN THE  PROCESS  OF  WATER FILTRATION IN THE
 VEGETABLE SOIL LAYER  (Gidravlicheskiye  soprotivleniya
 pri fil'tratsii vody  v rastitel'nom  sloye  pochvy),

 Altshul,  A.  D., and Tal, N.

 Meteorologiya i Gidrologiva,  No.  12, p  77-84,  1973.   4  fig,  1  tab,  5  ref.

 Expressions  for the determination of the Reynolds number and the  coefficient
 of hydraulic friction for flows  in the  vegetable  soil layer are  suggested  as
 a result  of  the application  of methods  based on the  filtration  theory to the
 computation  of hydraulic friction in said  layer.  Relationships  between the
 generalized  coefficient of hydraulic friction arid generalized  Reynolds number
 for different flow regimes are recommended on the basis of processed data
 obtained  from experiments with two types  of simulated artificial vegetation.

 *Reynolds number, *Hydraulics, *Mathematical studies, *Flow, Simulation
 analysis, Filtration, Friction,  Flow resistance,  Soil properties
026H

DESIGN OF FILTRATION PLANT FOR ROCKVILLE, CONNECTICUT,

Gammon, A.

Metcalf and Eddy, Incorporated,
Boston, Massachusetts

Journal of the New England Water Works Association, Vol. 88, No. 1, p 19-24,
March, 1974.

The design of a rapid sand filtration plant for the Shenipsit Lake Reservoir
in Rockville, Connecticut is described.  Due to the variations in raw water
characteristics such as temperature from winter to summer, color, tastes, and
odors, flexibility of chemical treatment was an important design considera-
tion.  The new low lift pumping station houses two 7.5 mgd vertical turbine
pumps with space to permit the future installation of a third unit.  The
operations building houses all chemical storage and feeding equipment,
with the exception of chlorine gas and sodium hydroxide.  Each of the two
treatment units has a flocculating compartment, a settling compartment, and
a filtering compartment, all arranged concentrically with a 65 ft diameter
circular tank.  Lagoons were built to handle the waste water from filter
backwashing, with sufficient storage volume to allow freezing of the sludge
for ease in handling and disposal.

*Filtration, treatment facilities, *Design, Reservoirs, *Flexibility,
Chemical treatment, Water purification, Pumping station, Buildings, Floccula-
tion, Filters, Oxidation lagoons, Sludge disposal, Sludge storage, Waste
water treatment

Rockville,  Connecticut
                                         648

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02 7H

MEKY RIVER DIVERSION  SCHEME;,

Gusberti, L.,  and Tamburrino, A.

Imperial Ethiopian Government Awash Valley Authority,
(AVA), Addis Ababa

Fascicolo L'Energia Elettrlca, Vol. 1, p  678-684, November, 1973.

Provisions for the diversion of about 200 million cu m of water per year  from
the Galla Lakes basin to  the reservoir created by the Koka Dam are described.
This compensates, in  part,  for the seepage losses from the reservoir, estimated
at around 400  million cu  m  per year.  Alternatives, with their mathematical cal-
culations were studied.   The selected solution involves the pumping of  the waters
to be diverted from Lake  Ziway.  By lowering the mean level of this lake  by
some two meters, through  removal of a rock sill at its outlet end, the  evapora-
tion will be reduced  by the same amount as the volume to be diverted.

*Rlver basins,  *Reservoirs, Mathematical  studies, Hydrologies, Diversion  loss
returns, Pumping, Dams, Seepage, Evaporation control

*Lake Ziway, Addis Ababa, Galla Lakes
028H

DEVELOPMENT AND FUTURE OF DREDGING,

Mohr, A. W.

Department of the Army, Corps of Engineers, South Atlan-
tic Division, Atlanta, Georgia

Journal of the Waterways Harbors and Coastal Engineering Division, Vol. 100,
No. WW2, p 69-84, May, 1974.  4 tab.

Dredging is performed either to gain the bottom material for fill or commercial
use or to create and maintain waterways.  This paper is concerned with the lat-
ter, where the material itself is an unwanted by-product.  The article describes
mechanical and hydraulic dredges with a series of tables, indicating the dif-
ferences between the various types.  Recently dredges, in their new designs,
must take into account the potential ecological damage which they cause, as well
as economic advantages.  Despite the new water quality requirements, both
hydraulic and especially mechanical dredges should continue to have use in the
future.

*Water quality, *Dredging, *Equipment, Ecological balance, Channels, Costs

*Hydraulic dredges, *Mechanical dredges, Waterway maintenance
                                         649

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029H

RENOVATING MUNICIPAL WASIEWAIER BY HIGH-RATE INFILTRATION
FOR GROUND-WATER RECHARGE,

Bouwer, H.

U.S. Water Conservation Laboratory, Agricultural
Research Service, U.S. Department of Agriculture, Phoenix,
Arizona

Journal of the American Water Works Association, Vol. 66, No. 3, p 159-162
March, 1974.   3 fig, 11 ref.

A pilot project in the Salt River bed west of Phoenix, Arizona, has shown
that secondary-sewage effluent can be renovated effectively by groundwater
recharge with high-rate infiltration basins.  Essentially complete removal
of BOD, suspended solids, and fecal coliforms was obtained.  Nitrogen and
phosphate were reduced.  The pilot project is located 1 1/2 miles downstream
from a sewage treatment plant.  Secondary effluent is pumped from the
effluent channel into six basins.  Infiltration rate in the basins is deter-
mined from the difference between the inflow and outflow rates.  The soil con-
sists of a fine, loamy sand underlain by coarse sand and gravel, and a clay
which marks the lower boundary of the aquifer.

*Waste water treatment, *Municipal wastes, *Aquifer management, *Groundwater,
*Artifical recharge, Induced infiltration, Waste water disposal, Pilot plants
   030H

   ONE FORM OF DEEP DRAINAGE OF UNDERGROUND WATERS  (Oh odnoy
   forme glubokogo stoka podzemnykh vod),

   Vartanyan, G. S.

   Doklady Akademii Nauk SSSR, Vol. 214, No. 6, p 1414-1416, 1974.  2 fig, 8 ref.

   The discharge of ascending underground waters into higher recipient horizons,
   and its mathematical relations are described.  The discharge zone in the reci-
   pient horizon has a hydrodynamic cupola formed by the discharge component,
   and the cupola is, in most cases, hydrostatically screened by the water stream
   of the recipient horizon, i.e., this stream flow along a surface of rotation.
   The ratio of the height of the discharge cupola to the overall height of the
   recipient horizon is equal to the ratio of the ascending water yield to the
   water yield of the recipient horizon proper.  The ascending water yield can
   also be determined by multiplying the recipient horizon water yield with
   a proportionality constant whose formula is presented.

   *Model studies, *Mathematical models, *Groundwater, *Aquifers, Hydrologlc
   aspects, Hydrologic systems, Hydrogeology
                                           650

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031H

COMPARISON OF THE EFFICIENCIES OF VERTICAL AND HORIZONTAL
DRAINAGE (Sravnitel'naya effektivnost'  vertikal'nogo i gorl-
zontalnogo drenazha),

Resetkina, N. M., and Dukhovnyy, V. A.

Gidrotekhnika i Melioratsiya, No. 1, p  76-80, 1974.  1 fig, 1 tab.

The efficiencies of vertical and horizontal drain and irrigation systems are
compared on the basis of experiences gained with such systems in the Kirov
and other areas.  Vertical drain systems have advantages over horizontal systems
in that they do not occupy useful farm lands, do not interfere with farming
operations, they can be used year round, permit groundwater stabilization at
any level, and permit the use of groundwater for irrigation.  In addition,
the construction of such vertical systems can be mechanized, and the opera-
tion be automated or remote-controlled.

*Groundwater, *Aquifers, *Hydrologic aspects, *Drainage, *Controlled
drainage, Drainage practices, Subsurface drainage, Drainage engineering
 032H

 SOIL CLOGGING DURING INFILTRATION OF SECONDARY EFFLUENT,

 Rice, R. C.

 United States Department of Agriculture,
 Phoenix, Arizona, United States Water
 Conservation Laboratory, Agricultural Research Service

 Journal of the Water Pollution Control Federation, Vol. 46, No. 4, p 708-716,
 April, 1974.  9  fig, 1 tab, 12 ref.

 Soil clogging during infiltration of secondary effluent was investigated.
 Soil clogging on two soils, a loamy sand and a course sand, was studied in
 soil columns in a greenhouse.  It was concluded that physical clogging caused
 by deposition of SS on the soil surface was the major cause of infiltration
 reduction.  Sparce evidence of surface biological clogging was found.  Main-
 tenance of low SS concentrations in the wastewater was found to be the most
 important factor in optimizing infiltration.  Concentrations below ten mg/liter
 should be maintained.  Low solids concentrations can be obtained by sedimen-
 tation.  Clogging developed below the surface because entrapped gases blocked
 the soil pores during long periods of intermittent inundation.  It is thought
 that this clogging was due to microbial activity.  High hydraulic gradients
 should be maintained in the soil system; the higher initial infiltration rates
 yielded greater total volumes of water than the low gradients.  Drying the
 clogged layer restored infiltration.  Algal growth on the soil surface in-
 creased infiltration rates during inundation because the algal mat became
 buoyant, thereby freeing the surface from clogging materials.

 *Waste water treatment, *Infiltration, *Soil management, *Soil water
 movement, *Effluents, Sewage effluents, Liquid wastes, Waste water disposal
                                        651

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 033H

 FUNCTIONING PROCESS OF DRAINAGE IN HYDROMORPHIC WASHED
 SOIL (SUR LE PROCESSUS DE FONCTIONNEMENT DBS DRAINS EN
 SOL LESSIVE HYDROMORPHE) ,

 Meriaux,  S.

 Centre de Recherches,  I.  N.  R.  A.,  Dijon,  France,  Station
 d'Agronomic

 Annales Agronomiques,  Vol.  24,  No.  6,  p  639-650, 1973.   6  fig,  2  tab,  10  ref.

 Chlorine  marking was used to study  the mechanism of water  movement  during drain-
 age in washed  soil.  The  chlorine never  goes  below a level of 40  cm.   It  is
 eliminated by  drainage In an essentially lateral movement  taking  place before
 remoistening of the  lower layers.   The lower  layers are  moistened by pre-exis-
 ting water in  the  upper layers  of  soil by  vertical movement  independent of
 drainage.   The functioning of drainage in  deep  be^ds,  as  was  shown,  raises a
 problem of duration  of effectiveness.

 *Soil  water  movement,  *Chlorine, Drainage,  Soil water, Soil  structure

 France
034H

THE FILTRATION FLOW OF PURE WATER THROUGH KAOLIN AND DAR-
CY'S LAW (LES ECOULEMENTS DE FILTRATION DANS LE KAOLIN ET
LA LOI DE DARCY),

Habib, J.

Ecole Nationale Superleure Agronomique, Rennes Cedex,
Chaire de Genie Rural

Annales Agronomiques, Vol. 24, No. 6, p 615-637, 1973.  13 fig, 3 tab,
27 ref.

The water permeability of clays was investigated to determine if it is a con-
stant or variable and if a hydraulic gradient threshold exists below which
clay becomes impermeable.  Tests on kaolin provided neither confirmation of
the existence of such a threshold nor any proof of permeability independent of
the hydraulic gradient, since permeability decreases rapidly with the gradient
when it is low.  A relationship was established between permeability, the poro-
sity of a kaolin and the motor hydraulic gradient.

*Clays, *Permeability, Darcy's Law, Hydraulic gradient, Investigations, Kaoli-
nite, Water, Porosity

France
                                          652

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035H

APPLICATION OF GROUNDWATER HYDRAULICS TO A BASALTIC
WATER-TABLE AQUIFER,

Adyaklar, P. G., and Manl, V. V. S.

Central Ground Water Board, Nagpur, India

Journal of Hydrology, Vol. 21, No. 3, p 211-218, 1974.  2 fig, 3 tab, 10 ref.

An analysis of pump test data of open wells in a basaltic water table aquifer
was made with methods based on both equilibrium and non-equilibrium formulae.
The study has indicated that the Thiem's equilibrium formula and the ratio
method of Narasimhan appear to be more suitable as compared with Jacob's and
Chow's methods.  Of the two, Narasimhan's ratio method, which does not require
the graphical procedure, is more reliable than the Thiem's method since the
latter involves an assumption of the value for the radius of influence.  From
the value of T (coefficient of transmissibility) obtained by Narasimhan's me-
thod, it is also possible to calculate the value of the radius of influence
by Thiem's method, which can be used in determining the required spacing
between wells in the basaltic terrain in order to avoid mutual interference.

*Aquifers, *Basalts, Groundwater, Hydraulics, Water table, Hydrogeology,
Investigations, *Pumping, Analytical techniques, Analysis

India, Thiem's formula, Narasimhan's ratio method
036H

EFFECT OF DRAIN DEPTH AND GAP WIDTH ON POTENTIAL FLOW IN
HOMOGENEOUS POROUS SOIL,

Cheeseman, P. C., Hosking, R. J., and Sneyd, A. D.

Waikato University, Hamilton, New Zealand, Department of
Mathematics

Journal of Hydrology, Vol. 21, No. 3, p 219-229, 1974.  5 fig, 1 tab, 8 ref.

The solution of a problem in potential theory is presented in determining the
effect of drain depth and gap width on potential flow in homogeneous porous
soil.  In order to control water saturation in soils, it is common to control
the water drainage.  A two dimensional situation involving a drain is discussed.
Seepage flow from an equlpotential surface into drains of half width gamma at
relative depth is considered to represent the flow through a porous soil either
normal to impervious layers with intervening gaps or perhaps to a single row
of drain pipes.  The equipotential surface may Be the soil surface, with perhaps
ponded water above it, or it may be the level of the water table.  An exact so-
lution for the flux ratio, suitable for numerical computation, is found by
Schwarz-Christoffel confortnal transformation.  An asymptotic expression derived
for the flux ratio is found to be accurate except for quite small relative
depth.

*Potential flow, *Drainage, Soil, Porous media, Numerical analysis, Soil water
movement, Theoretical analysis, Impervious soils

Flux ratio, New Zealand, Netherlands
                                        653

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037H

TOWN 'CAPTURES' NATURAL SPRING: CUTS WATER TREATMENT COSTS,

Loring, B. A.

Allen and Hoshall, Consulting Engineers, Memphis,
Tennessee

The American City, Vol. 89, No. 5, p 65-66, May, 1974.

In order to increase water-supply capabilities by 40 percent, the city of
Elizabethton, Tennessee found that groundwater from springs were useable.  By
building an earth cofferdam around the springs discharge area, a. concrete receiving
reservoir could act as a pump sump.  The operating and maintenance costs for the
1.4 mgd Valley Forge Spring are very low.  The water has a pH of 8.7 and is
noncorrosive, has no bacteria harmful to public health, and should provide ade-
quate supply through 1980.

*Water supply development, *Groundwater, *Water sources, *Springs, Dams, Re-
servoirs, Costs

Capabilities, Tennessee, pH
038H

SNOW ACCUMULATION AND SNOWMELT AS INFLUENCED B^ A SMALL
CLEARING IN A LODGEPOLE PINE FOREST,

Gary, H. L.

U.S.D.A. Forest  Service, Rocky Mountain Forest and
Range Experiment Station, Fort Collins, Colorado

Water Resources  Research, Vol. 10, No. 2, p 348-353, April,  1974.   8  fig,
1  tab,  9 ref.

The study was undertaken to determine some of the interrelations  of snow  ac-
cumulation and snowmelt.  It was postulated that accumulation is  greater
in openings and  clear-cut areas  than under unbroken stand.   Snow  accumula-
tion, was observed under a thinned lodgepole pine stand about 35 feet  tall
and 80  years old for two winter  seasons before and two seasons after  cutting
a  clearing 1 tree height wide and 5 tree heights long.  The  clearing  was  on a
gently  sloping plateau 9000 feet above sea level and was  oriented perpendicu-
larly to the prevailing southwest wind.  The maximum snowpack water equiva-
lent the first year after clearing averaged 13.1 inches in the upwind forest
16.2 inches in the clearing, and 12.2 inches in the downwind forest zone, with
a  similar pattern the second year.  The increased snow catch in the clearing
was offset by the snow deficit in the downwind forest.  The  clearing  affected
the distribution of snow over the area but not the total  amount of  snow water
equivalent.  Melt rates in the clearing were about twice  those in the interior
forest  zones.

*Snowmelt, *Lodgepole pine trees, Winter, Hydrologic aspects, Forests,
Melt water

*Snow accumulation, Snow water,  Forest zones, Melt rates


                                       654

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039H

MORPHOGENETIC STUDY OF TERMINAL TRIANGULAR TRACT OF IN-
LAND STREAMS IN SUTLEJ YAMUNA PLAIN,

Mukerji, A. B.

Punjab University, Chandigarh

Indian Journal of Power and River Valley Development, Vol. 23, No. 10, p 314-
324, October, 1973.  3 fig, 3 tab, 2 ref.

The purpose of this study was to identify and describe a unit feature termed
terminal triangular tract.  This is a geomorphic landscape unit characterised
by its triangular deltaic shape formed by a dichotomic pattern of distributaries
and which is evolved as a consequence of multi-furcation of the main channel.
Also shown is an empirical genetic interpretation in terms of the geometry of
distributary network, surface material, terrain attributes, human interference,
and local topographic details.  Based on field investigations, aerial photo-
graphs and topographical sheets, the Sutlej-Yamuna plains are described.  The
size of the feature is correlated with the size and discharge of the stream,
the angle of divergence, frequency of divergence and number of lower order dis-
tributaries.  The texture of topography is finer near the points of divergence
and becomes coarser away from them.  The network tends to become progressively
more elaborate and complicated through time.

*Streams, *Geomorphology, Plains, Deltas, Landscape, Terrain analysis,
Channels, Rivers, Topography, Investigations, Field investigations, Inland
streams

Multifurcation, Divergence, India, Sutlej-Yamuna plain, India
040H

THE INFLUENCE OF GEOLOGICAL MEMBRANES ON THE GEOCHEMISTRY
OF SUBSURFACE WATERS FROM MIOCENE SEDIMENTS AT KETTLEMAN
NORTH DOME IN CALIFORNIA,

Kharaka, Y. K., and Berry, F. A.

U. S. Geological Survey, Menlo Park, California

Water Resources Research, Vol. 10, No. 2, p 313-327, April, 1974.  11 fig, 3 tab,
40 ref.

The purpose of this paper is to show the degree to which geological membranes
control formation water chemistry Kettleman North Dome oil field in California.
Waters from the Temblor formation (Miocene) are principally meteoric in origin,
as seen by regional hydrodynamics, isotopic data and detailed geology.  Their
concentration relative to meteoric water is attributed to hyperfiltration
through geological membranes as well as to water-rock interactions.  The
chemistry of the waters in each subzone of the Temblor formation is charac-
teristic of that subzone and shows membrane effluent characteristics to a
given subzone with respect to the one stratigraphically below it.  Chemical
relations are attributed to increased efficiency of shale membranes with in-
creased depth of burial.  Membrane behavior of shales controls completely
or in part the distribution of the following ratios:  Li/Na, Rb/Na, NH3/Na,
Mg/Ca, Sr/Ca, Ca/Na, alkallnity/Cl, S04/C1, I/Br, and B/C1.  Some of these ra-
tios are modified by temperature-controlled water-rock interactions but the
K/Na ratios and the Si02 and Ba concentrations are completely dependent on
water-rock interactions.

*Geology, *Shales, *Water chemistry, Alkalinity, Temperature, Meteroltic
water

*Geological membranes, Kettleman North Dome Oil Field, California, Moicene,
Water-rock interactions, Subzones
                                         655

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041H

ISOTOPIC AND CHEMICAL CHARACTERISTICS OF HIGH-LEVEL GROUND-
WATER ON OAHU, HAWAII,

Hufen, T. H., Buddemeier, R. W., and Lau, L. S.

Hawaii University, Honolulu, Hawaii, Water Resources
Research Center

Water Resources Research, Vol. 10, No. 2, p 366-370, April, 1974.  4 fig,
2 tab, 18 ref.

High level dike-confined groundwaters and high-level perched groundwaters on
Oahu, Hawaii, were analyzed for tritium, radiocarbon, carbon 13, and several
chemical constituents.  Discharges from several tunnels that tap dike compart-
ments contain postbomb tritium, indicating the presence of modern (since 1954)
recharge.  The amount of this recharge in samples taken inside one of the
tunnels is a function of the distance between overlying surface and sampling
point.  Chemical and carbon isotopic compositions of dike waters, established
in the soil zone of ther overlying ground surface, remain unchanged while the
water is passing through the basaltic carbonate-free compartments.  Dike water
carbon isotope data are sufficiently consistent to serve as initial values for
the dating of water in the Honolulu basal aquifers.  The radiocarbon data sug-
gest that the maximum value for residence time of the dike waters is of the
order of 100 years.

*Groundwater, *Geohydrology, *Radiocarbon, Tritium, Tunnels, Soil, Isotopes,
Chemistry

*Hawaii, Isotopic compositions, Oahu, Hawaii, Dike waters
042H

EVOLUTION OF THE SON DRAINAGE,

Lakshmanan, S.

Centre of Advanced Study in Geology, Saugar University,
India

Proceedings of the Indian National Science Academy, Vol. 38A, No. 1, 2, p 21-31,
January, 1972.  4 fig, 19 ref.

It is concluded that the present drainage of the Son valley area was superposed
from a Deccan Trap cover, and the course of the Son river has been controlled
by lithology and not by any major faulting.  This was determined from a geologi-
cal study of the western portion of the Son valley where the Son river takes an
abrupt east northeast bend from its northerly course.  Apparently there is a Pre-
Trappean erosion surface at about 1600 ft above sea level, and the drainage
.appears to have originated on the Deccan Traps which were later denuded away to
axpose the underlying older formations.  By a process of differential and head-
ward erosion, all the northward flowing tributaries were finally captured to
Eorm the Son river.

^Drainage, *Rivers, *Faulting, *Drainage systems, Geology, Erosion, Flow, Trib-
utaries, Hydrology


Lithology, Evolution
                                          656

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 043H

 WORLD'S  GREATEST  SOURCE  OF FRESH WATER,

 Waller,  R.  M.

 U.S.  Geological Survey,  Albany,  New York,
 Water Resources Division

 Journal  of  the American  Water  Works Association, Vol.  66, No.  4, p  245-247,
 April, 1974.   2 fig.

 The Great Lakes,  as  the  largest  system of  fresh water  lakes  in the  world,
 offer large supplies, which could be  properly managed  and treated for  reuse.
 Topography, geology, and hydrology of the  region are described.  Two major
 local problems in the Great Lakes basin  are water-short  areas  of poor  water
 quality.  Geological conditions  of low permeability or thin  unconsolidated
 material cause rapid runoff and  provide  little groundwater storage  area,
 particularly  among shale and igneous-rock  areas.   In some bedrock aquifers,
 highly mineralized water is present at relatively  shallow depth and seeps into
 streams  or  is  encountered by wells.   Saline water  problems occur in parts
 of lower Michigan, Ohio, Indiana, New York, and Pennsylvania.   More and more
 cities and  states are adapting by curtailing wasteful  water-use practices
 and evaluating the water supplies.  Lake basins, with  proper management, can
 continue to be a  future  world  water resource.

 *Great Lakes,  *Lake  basins, *Freshwater, Geology,  Hydrology, Water  resources
 development,  Water management  (applied), Water quality,  Aquifers, Groundwater,
 Cities,  Permeability, Saline water, Great  Lakes region

 New York, Pennsylvania,  Ohio,  Michigan,  Indiana, Bedrock aquifers,  Groundwater
 storage
044H

LAND TREATMENT OF LIQUID WASTE:  THE HYDROLOGIC SYSTEM,

Bouwer, H.

United States Department of Agriculture

In:  Proceedings of the Joint Conference on Recycling Municipal Sludges and
Effluents on Land, July 9-13, 1973, Champaign, Illinois, The National Associa-
tion of State Universities and Land-Grant Colleges, University of Illinois,
p 103-111.  5 fig, 12 ref.

Irrigation and drainage theory explain most hydrologic aspects for application
of liquid waste to land.  The most important factors are:  choosing the
most appropriate system for applying the waste water, whether low-rate or
high-rate infiltration; the design application or infiltration rates in rela-
tion to the hydraulic acceptance of the soil, the desired quality improve-
ment of the water, and the intended longevity of the system; and the ground-
water management below the receiving fields.  Local research and pilot sys-
tems should precede large-scale research because of geology of groundwater,
soil, and climate conditions.  Optimum treatment of waste water before ap-
plication to the land must also be analyzed in more detail.

*Hydrologic aspects, Irrigation, *Liquid wastes, *Waste water, *Infiltration
rates, Pilot studies, Groundwater, Drainage, Water quality control, Water
management (applied), Waste water treatment, Geology, Soil properties, Climate,
Waste water treatment

*Land applications
                                        657

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045H

THE PHYSICAL PROCESSES IN THE SOIL AS RELATED TO SEWAGE
SLUDGE APPLICATION,

Epstein, E.

United States Department of Agriculture

In:  Proceedings of the Joint Conference on Recycling Municipal Sludges and
Effluents on Land, July 9-13, 1973, Champaign, Illinois, The National Associa-
tion of State Universities and Land-Grant Colleges, University of Illinois,
p 67-73, 8 fig, 11 ref.

Soil water retention is increased by the addition of sewage sludge and sewage
compost.  Initially addition increases the hydraulic conductivity of a
soil but this conductivity later decreases, apparently due to the clogging of
soil pores by microbial decomposition products.  The structure of the soil
affects soil air, soil water, mechanical impedence, and root distribution.
Soil aggregation is increased by organic matter and the action of micro-
organisms.  Because of sewage sludge, soil atmosphere is greatly modified.
The low oxygen and high carbon dioxide resulting from high sludge applica-
tion reduces root growth, nutrient uptake, and plant growth.  In addition,
gas products of decomposition, such as methane and etheylene, can be detri-
mental to plants.

*Sewage sludge, *Soil water, *Soil mechanics, Oxygen, Carbon dioxide,
Roots, Soil-water-plant relationships, Methane, Organic matter, Microorganisms,
Soil aggregates

Soil water conductivity, Soil atmosphere, Gas products
046H

NEW GLOBAL WATCH FOR POLLUTION EFFECTS,

Industrial Research, Vol. 16, No. 5, p 23, 25, May, 1974.

A global monitoring system is being set up by the United Nations Environment
Program for assessing the worldwide environment and warning of possible hazards.
The system is called EARTHWATCH and will monitor cadmium,  mercury, petroleum
hydrocarbons, fluorides, arsenic in water.  Monitoring stations will be
global, regional, and local.  Existing facilities will be incorporated in the
networks, and some new stations established.

*Monitoring, *Water pollution, *Cadmium, *Mercury, *Hydrocarbons, *Flourides,
*Arsenic, Facilities, Environmental control, Research

*EARTHWATCH, United Nations Environment Program, Monitoring stations,
Global pollution watch
                                         658

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04 7H

FLOOD PLAIN MANAGEMENT IN METROPOLITAN CHICAGO,

Lanyon, R,

Metropolitan Sanitary District, Chicago, Illinois

Civil Engineering, A.S.C.E., Vol. 44, No. 5, p 79-81, May, 1974.  2 fig, 1 tab.

Planning is now underway with cooperation of many levels of government to
control land use and flooding in the Chicago area.  This flooding was divided in-
to three categories:  basement and below grade flooding due to back-up of
sanitary sewers from floodwater entering sewer systems through flood street
manholes; direct entrance of surface floodwaters into lower level garages,
basements, and subgrade surface living areas; inundation of the above grade
frame portions of the structure.  Besides such residential damage, municipal
flooding occurs on parking areas, playgrounds, highways, and streets.  A
watershed plan was developed to reduce flood damages and erosion.  Two remaining
undeveloped flood plain areas were to be placed in public control with the
intention of enforcing ordinances against new developments in identified
flood hazard areas and the enacting of a technical assistance program to
provide floodproofing information where hazards exist.

*Flood plains, *Flood control, *Floodproofing, *Sewer systems, *Land use,
*Flood damage, Flood plain zoning, Municipalities, Urban planning, Water
management (administrative), Governments, Legislation, Hydrologic aspects

Flood plain management, Technical information, Public control
048H

CITY OF MANCHESTER—MAIN DRAINAGE WORK 6,

Young, D. N.

City of Manchester, England

The Institution of Municipal Engineers Journal, Vol. 101, p 109-116, No. 4,
April, 1974.  4 fig.

Developments of main drainage facilities within the city of Manchester since
1885 are given and present measures taken to improve the redevelopment re-
quirements of the Openshaw area are described.  General design based on the
storm overflow, old mine workings, and coal seams from a colliery are taken into
account.  Over the past year, research work by the city engineer and surveyor's
department was done on the volume of flow generated within a catchment area
together with the efficient performance of stilling pond storm water overflows.
Flows will be monitored from this area by an automatic pneumatic depth recorder
for both dry weather and storm water sewers.  Ultimately sampling equipment
will be expanded.  By automatic rainfall intensity recording gauges, theore-
tical and actual runoff will be compared.  In addition, assessment of the
performance of the stilling pond type overflow will be made.  These results
should provide information for further design criteria for sewer systems in
the area.

*Dralnage area, *Urban planning, *Design criteria, History, Flow, Monitoring,
Sampling, Sewer systems, Automation, Recording, Runoff, Gauges, Models

Great Britain (Manchester, Openshaw)
                                         659

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049H

SEDIMENT AND WASTE DEPOSITION IN NEW YORK HARBOR,

Gross, M. G.

State University of New York, Marine Sciences Research
Center, Stony Brook, New York

Hudson River Colloquium, Annals of the New York Academy of Sciences, Vol. 250,
p 112-128, May 24, 1974.  3 fig, 6 tab, 36 ref.

The physical alterations of the Hudson River estuary are discussed with parti-
cular attention being paid to the sediments and waste deposits that covered
much of the harbor bottom and large areas of New York Bight in 1972.  The fol-
lowing topics are mentioned:  recent geologic history, dredging of the Hudson
Estuary, water movements, sediment sources, sand and gravel production in New
York Harbor, sediment and waste deposits, and future changes to the estuary.

*Hudson River, *Estuaries, *Sediments, Wastes, Sediment load, Water circulation,
Geologic history, Sands, Gravels

New York Harbor, Estuarine alterations, Waste deposition
05 OH

WASTE DISPOSAL SYSTEMS FROM A GROUNDWATER HYDROLOGY AND
POLLUTION POINT OF VIEW

Patterson, R. J.

Department of Geology, Tampa, Florida

Water and Sewage Works, p 92, 94-96, 98-99, April 30, 1974.
3 fig, 2 tab, 3 ref.

Disposal and treatment of solid and liquid wastes on land are gaining wider
acceptance.  Numerous methods for dealing with the many types of waste are
available:  solid, depending on the source may be landfilled or spread; while
liquids are handled by systems employing infiltration basins, surface
flooring, and spray irrigation.  The implications of land disposal in terms
of groundwater hydrology and pollution are emphasized.  Spray irrigation is
cited as a specific example and some of the criteria which are essential for
a proper evaluation of the pollution potential of proposed operations are also
discussed.

*Waste disposal, *Landfills, *Groundwater, *Hydrologic aspects, Water
pollution sources, Solid wastes, Liquid wastes, Evaluation

Spray irrigation
                                          660

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051H

THE USE OF ARTIFICIAL RADIOACTIVE TRACERS FOR THE SOLUTION
OF HYDROLOGICAL PROBLEMS  (DIE VERWENDUNG KUENSTLICHER RADIOAKTIVER
MARKIERUNGEN ZUR LOESUNG HYDROLOGISCHER PROBLEME) ,

Batsche, H., and Neumaier, F.

Oesterreichische Wasserwirtschaft, Vol. 26, No. 3/4, p 80-89,
March-April, 1974.  7 fig, 11 ref.

The practical uses of the radioactive tracer technique according to the
single-hole and multiple hole methods for the solution of hydrological
and hydrogeological problems are reviewed.  The radioactive tracer technique
according to the single-hole method was successfully used for the determination
of the flow velocity and the rate of filtration of groundwater, for the study
of the influence of groundwater table lowering on adjacent groundwater sheets,
and for the determination of the vertical upward flow of groundwater.  Such
investigations may be necessary for the planning and underground structures
and dams.  The radioactive tracer method is also suitable for the measurement
of water evaporation from the ground, and of the vertical rate of percolation
of precipitation through different types of soils.  The multiple-hole method
was used for the identification of karst water and groundwater in an area
used both for water capture and waste water disposal.  Good agreement of the
flow rates as determined by the single-hole and multiple-hole methods as well
as those calculated from pumping tests was established.

*Radioactive tracers, *Hydrologic aspects, *Karst hydrology, Groundwater,
Flow velocity, Filtration rate, Precipitation, Soils, Pumping, Flow rates

Single-hole methods, Multiple-hole methods, Percolation
052H

THE SIGNIFICANCE OF ISOTOPIC MEASUREMENTS FOR COMBINED KARST
WATER STUDIES (DIE BEDEUTUNG VON ISOTOPENMESSUNGEN IM RAHMEN
KOMBINIERTER KARSTWASSERUNTERSUCHUNGEN),

Zojer, H., and Zoetl, J.

Oesterreichische Wasserwirtschaft, Vol. 26, No. 3/4, p 62-70, March-April,
1974.  9 fig, 3 tab, 8 ref.

The significance of isotopic tracer measurements is demonstrated by the
example of complex hydrological studies of the karst waters in the Central
Styrian Karst.  It was possible to quantitatively determine the passage
of water from one creek into another and the complex communications among
these creeks in the karst area by tracer investigations using uranine,
tritium and Lycopodium spores.  The tracer technique permitted the determination
of the distribution of precipitation among the creeks and the delimitation of
the individual watershed areas.  A computer model of the individual watershed
systems was set up on the basis of the tritium tracing results.

*Hydrological aspects, *Karst hydrology, Tracers, Watersheds, Computers,
Tritium

Uranin, Lycopodium spores, Water movement
                                     661

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05 3H

THE USE OF ARTIFICIAL RADIOACTIVE TRACERS FOR THE SOLUTION OF
HYDROLOGICAL PROBLEMS.  PART I: METHODS (DIE VERWENDUNG
KUENSTLICHER RADIOAKTIVER MARKIERUNGEN ZUR LOESUNG HYDRO-
LOGISCHER PROBLEME.  TEIL I: METHODIK),

Moser, H.

Oesterreichische Wasserwirtschaft, Vol. 26, No. 3/4, p 75-80, April, 1974.
6 fig, 10 ref.

A general description is given of the artificial radioactive tracing method
suitable for the solution of hydrological problems.  It is possible to
determine the motion of water within unsaturated ground by injecting tritium
and determining the radioactivity of earth samples taken in a vertical
profile.  The results thus obtained allow conclusions on the conditions of
groundwater formation.  The radioactive tracer technique works according to the
single-hole method.  The groundwater flow rate is determined from the dilution
of the radioactive tracer, from the groundwater flow direction by the use of
direction-sensitive scintillation counters, and from the measurement of the
velocity and yield of vertical streams.

*Radioactive tracers, *Hydrologic aspects, *Groundwater movement, Flow rate,
Measurement, Flow velocity, Tritium

Single-hole method, Scintillation counters
054H

CONSIDERATIONS ON ARTIFICIAL GROUNDWATER RECHARGE
(NACHDENKLICHES ZUR KUENSTLICHEN GRUNDWASSERANREICHERUNG) ,

Bettaque, R.

Gas-Wasser-Fach - Wasser/Abwasser, Vol. 115, No. A, p 171-173, April, 1974.
39 ref.

The advantages of artificial groundwater recharge as a means of drinking water
supply are described with respect to a reluctance towards the application
of this process to water supply in West Germany.  Uncertainties concerning the
suitability of various grounds for infiltration, and the frequent failures
of this process due to established anaerobic conditions resulting from high
pollutant loads and inadequate operating conditions have led to the abandonment
of the infiltration technique at many water works.  However, the biological
slow filtration is superior to chemical and physical methods of drinking water
preparation in its capacity to degrade organic matter.  This capacity amounts
to about 75 percent, corresponding to a residual oxidizability of 1-2 mg/liter,
against 50 percent determined for the flocculation process.   The biologically
stable water obtained by the biological filtration impedes the proliferation
of microorganisms in the water mains.  Raw waters with high pollutant loads
require preliminary purification, such as by rapid filtration and flocculation
to prevent anaerobic conditions.

*Groundwater recharge, *Artificial recharge, *Potable water, Water supply,
Infiltration, Anaerobic conditions, Water works, Organic matter, Biological
degradation
*West Germany, Biological filtration
                                          662

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055H

WATER ANALYSIS IN THE KELETI CANAL (VIZVIZSGALATOK A KELETI
FOCSATORNAN) ,

Keve, T. K., Pinter, C., and Munkacsy, T.

Hidrologiai Kozlony, Vol. 54, No. 1, p 32-40, January, 1974.  5 fig, 2 tab,
14 ref.

Results of the systematic water quality monitoring performed in the Keleti
Focsatorna, a 100 km long drain and irrigation canal connected with the
Tisza river in Eastern Hungary are presented.  The water yield of the canal
amounts to 10-40 cu m/sec.  The monitoring was conducted with respect to the
future use of the canal water for drinking water prepared by the percolation
method.  The water quality was found to be determined by that of the Tisza river
on one hand, and by the momentary mode of use of the canal on the other hand.
With the flow velocity in the river exceeding that in the canal, reduction
of the suspended matter content and of the BOD level and an increase of the
clearness of the canal water was observed.  During high-water periods in the
river, seston contents of several hundred mg/liter, and BOD levels of
10-15 mg/liter were measured in the canal water.  Cleaning of the water and
algal proliferation after such high-water periods were observed.  During
periods of high stagnant water yield, increased nitrogen and phosphorus levels,
and change from calcium hydrocarbonate to sodium hydrocarbonate in the canal
water were determined.

*Water quality control, *Monitoring, *Irrigation, *Canals, *Potable water,
Flow velocity, Biochemical oxygen demand, Algae, Nitrogen, Phosphorus,
Hydrological aspects

Percolation
056H
BIOLOGICAL AND BACTERIOLOGICAL INVESTIGATIONS OF A SLIGHTLY
POLLUTED SURFACE WATER (DANUBE) AND OF A HIGHLY POLLUTED SURFACE
WATER (SZILAS CREEK) (BIOLOGIAI ES BAKTERIOLOGIAI VIZSGALATOK
EGY KISSE SZENNYEZETT (DUNA) ES EGY EROSEN SZENNYEZETT
(SZILAS-PATAK) FELSZINI VIZFOLYASBAN),

Hegedus, J., Nemedi, L., and Hegedus, J.

Hidrologiai Kozlony, Vol. 54, No. 1, p 26-31, January, 1974.  5 fig, 11 ref.

Year-round comparative biological and bacteriological investigations of the
water quality in a lightly polluted stream (Danisbe) and in a highly polluted
creek (Szilas-patak) in Hungary are presented.  The bacteriological
investigations were concerned with the total bacteria count between 20 and 37 C,
and the Streptococcus feecalis, Clostridium, Salmonella, and Shigella counts.
The biological investigations covered the study of the qualitative relations
of phytoplankton, and bacteria and fungi that can be determined by microscopic
and saprobiological methods.  The water quality of the Danube was determined
to vary between B-mesosaprobic and a-inesosaprobic with temporary pa-mesosaprobic
periods.  Unlike Szilas creek, the Danube exhibited pronounced seasonal changes
in water quality.  Strong parallelism between the water qualities as determined
by the biological and the bacteriological method was established.  However,
the biological quality was better in summer, and the bacteriological quality
was better in winter in the Danube.  Pathogenic bacteria, such as Salmonella,
were present in Szilas creek almost all the time.

*Surface waters, Investigations, Streams, Bacteria, Phytoplankton, Water
quality, Seasonal, Salmonella, Water pollution sources

Biological investigation, Bacteriological investigation, Danube (Hungary),
Szilas-patak (Hungary)
                                         663

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05 7H

STUDY OF THE REGULATIONS OF INLAND WATER FORMATION AND
RUNOFF IN AN INLAND WATER BAY WITH PERVIOUS GROUND,

Molnar, G.

Hidrologiai Kozlony, Vol. 54, No. 1, p 15-20, January, 1974.
6 fig, 2 tab, 7 ref.

A black box system model of an inland water area with pervious
ground in Hungary is described on the basis of systematic ground-
water level and runoff measurements.  The inland water formation
in plain areas with pervious ground was found to be determined
primarily by the groundwater level.  The general system model also
contains such factors as precipitation, trickling, evapotranspir-
ation, and flow conditions in the drain canal.  In plain areas
with pervious ground, the increase of the drain canal density was
found to lead to increased inland water volume due to the increased
runoff surface area available for the groundwater.

*Models, *Inland water, *Groundwater, *Runoff, Precipitation,
Canals, Measurements, Pervious soils (atmospheric)

Hungary, Pervious ground, Drain canal density
058H

HYDROLOGIC IMPACT OF TROPICAL STORM AGNES,

Engman, E. T., Parmele, L. H., and Gburek, W. J.

U. S. Department of Agriculture,
Northeast Watershed Research Center,
Agriculture Research Center,
University Park, Pennsylvania

Journal of Hydrology, Vol. 22, No. 1/2, p 179-193, June, 1974.
11 fig, 2 tab, 12 ref.

Data from tropical storm Agnes were analyzed with respect to water-
shed yield and return period frequency.  Antecedent conditions and
events preceding the storm are discussed.  The greatest rainfall
amounts from the June 1972 tropical storm that devastated the Sus-
quehanna river valley occurred over the East Mahantango Creek Water-
shed.  This 162-sq. mile area in the Ridge and Valley Province of
eastern Pennsylvania is a densely instrumented research watershed,
operated by the Agricultural Research Service of the USDA.  Instru-
mentation include 33 20-inch capacity, digital recording rain gages
and seven stream gaging sites.  The maximum rainfall in this storm
was 14.9 inches for 24 h and 18.2 inches for the entire storm (3 days).
Partial and complete runoff records are presented.  The peak flow at
the 162-sq. mile point was over 400 csm and at the 10.1-sq. mile
watershed, over 1,200 csm.  The rainfall and runoff events were several
times greater than those expected for return period frequency of 100 years.

*Hydrologic aspects, *Rainfall, *Storm water, Flooding, Watersheds,
Instrumentation, Rainfall-runoff relationships

*Tropical storm Agnes, Pennsylvania, Watershed yield
                                        664

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059H

HYDRAULIC PROBABILISTIC CALCULATION METHOD FOR THE DETERMINATION
OF THE SEAM KARST WATER YIELD,

Schmieder, A.

Banyaszati es Kohaszati Lapok, Vol. 107, No. 3, p 172-183, 1974.
7 fig, 2 tab, 24 ref.

General relationships characterizing the spontaneous karst water
yield in seams were derived from hydraulic-probalistic calculations.
A quadratic relationship between the karst water yield and the
depression was established.  The effect of protective layers can
not be determined from water yield measurements.  The water yield
is proportional to the surface area of the opened-up field and to
the square root of the turbulent depression occurring in the cracked
rock, and is reduced by simultaneity.  The individual yields are
determined by a cross-section area of the cracks connecting the mine
space with the aquifers and by the depth-dependent water pressure
rather than by the paths formed in the karst aquifers.

*Hydrologic aspects, *Water quantity, *Karst, Equations, Pressure,
Aquifers, Turbulence

*Water yield, Depth dependent water pressure
060H

THE SOIL AS A PHYSICAL FILTER,

Thomas, R. E.,

Environmental Protection Agency,
Robert S. Kerr Water Research Center

In:  Conference on Recycling Treated Municipal Wastewater Through Forest
and Cropland, August 21-24, 1972, The Pennsylvania State University,
University Park, p 40-46.  10 ref.

Soil is a mixture of mineral particles, organic material, air, and water.
The pore space occupied by air or water may be as much as 50 percent of
the total volume, and the pathway of movement through these pores is a maze
of varying sized channels.  It is the size distribution and the nature of
this maze which controls the capability of the soil to filter out suspended
solids that are found in treatment plant effluents or industrial waste
waters.  Several approaches to utilize this filtering capability of the
soil for disposal or renovation of municipal effluents and industrial
waste waters include septic tank-soil absorption systems, cropland irrigation
systems, surface disposal systems, and groundwater recharge systems;.
Clogging of the filter and management practices which can be used to extend
the life of the filter are discussed.

*Filters, *Soil amendments, *Soil analysis, Soil physical properties,
Waste disposal, Soil disposal fields, Soil types, Suspended solids
                                         665

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061H

THE SOIL AS A CHEMICAL FILTER,

Ellis, B. G.

Michigan State University, Department of Crop and
Soil Sciences

In:  Conference on Recycling Treated Municipal Wastewater Through Forest
and Cropland, August 21-24, 1972, The Pennsylvania State University,
University Park, p 47-72.  1 fig, 3 tab, 98 ref.

The areas of soil chemistry which are of most importance for the soil
to act as a chemical filter are:  ion exchange, adsorption and precipitation,
and chemical alteration.  This discussion includes the theory of each
process and the importance of each process to waste disposal systems.

*Filters, *Soil chemistry, Ion exchange, Adsorption, Precipitation,
Soil chemical properties, Waste disposal
 062H

 THE  SOIL AS A BIOLOGICAL FILTER,

 Miller, R. H.

 The  Ohio State University, Department of Agronomy

 In:   Conference on Recycling Treated Municipal Wastewater Through Forest
 and  Cropland, August  21-24, 1972, The Pennsylvania State University,
 University Park, p 73-94.  3 tab, 58 ref.

 The  groups of organisms comprising the soil biological filter are bacteria
 actinomycete, fungi,  protozoa, algae, soil micro- and macro-animals,
 and  higher plants.  The various microbial reactions which influence the
 success of soil as a  filter for renovating municipal waste water and sludge
 are  reviewed.  The majority of these activities are beneficial for
 maintaining the integrity and effectiveness of the soil filter.  Only
 one  reaction, nitrification, can be considered detrimental to the success
 of the soil filter when the disposal method maintains adequate soil aeration.
 Also, it should be emphasized that prolonged periods of anaerobiosis must
 be avoided for the proper functions of the microbial component of the
 soil filter.  Finally, proper management of land disposal systems for
 liquid waste regardless of the mode of application must provide for
 periods of adequate aeration.

 *Filters, *Soil bacteria, Municipal wastes, Waste disposal, Nitrification,
 Soil disposal fields, Application techniques, Aeration
                                        666

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063H

RENOVATING SECONDARY EFFLUENT BY GROUNDWATER RECHARGE
WITH INFILTRATION BASINS,

Bouwer, H.

United States Department of Agriculture, Agriculture
Research Service, U. S. Water Conservation Laboratory

In:  Conference on Recycling Treated Municipal Wastewater Through Forest
and Cropland, August 21-24, 1972, The Pennsylvania State University,
University Park, p 146-156.  1 tab, 10 ref.

The Salt River Valley in Central Arizona is changing from a predominantly
agricultural to a predominantly urban valley.  Groundwater currently
supplies about one-third of the municipal and agricultural water needs
in the area of the Salt River Project.  The resulting depletion of the
groundwater can be reduced if the sewage effluent produced by the
increasing population can be reused.  Unrestricted use of sewage effluent
for recreational lakes and irrigation requires tertiary treatment.  A
promising technique for such treatment in the Salt River Valley would be
by groundwater recharge with spreading basins in the Salt River bed.
Because the performance of a land-filtration system depends so much on
the local conditions of climate, soil, and groundwater, a pilot system,
called the Flushing Meadows Project, was installed in 1967.  The findings
obtained and their use in the design of a large-scale system are presented.

*Groundwater recharge, *Pit recharge, Data collections, Design criteria,
Arizona, Performance, Infiltration, Waste water treatment, Tertiary treatment
  064H

  IMPLEMENTING THE  CHICAGO PRAIRIE  PLAN,

  Kudma,  F.,  and Kelly,  G.

  The Metropolitan  Sanitary District  of  Greater  Chicago,
  Illinois

  In:   Conference on  Recycling  Treated Municipal Wastewater Through  Forest
  and Cropland,  August  21-24, 1972, The  Pennsylvania  State University,
  University Park,  p  342-347.

  The Metropolitan  Sanitary District  of  Greater  Chicago  has developed a
  program  for  the recycle and reuse of sewerage  solids,  the by-products
  of the water reclamation process.   It  is  a far-reaching, environmentally
  sound program called  the "The Prairie  Plan".   Based on a principle of
  watershed planning, it utilizes  the ground as  an  immense, natural  filter
  and collection system.   Utilizing a single watershed with known physical
  characteristics as  the basis  for  application,  not only do the soil and
  living parts act  as a filter, but also there  is a natural way to collect
  all of the  filtered runoff at one point for continuous monitoring  and
  water quality control.   The result  is  a flowing stream which is clean,
  free  from silt, and potentially  a valuable resource for recreational,
  commercial,  and industrial development.  The  first  implementation  of
  "The  Prairie Plan"  is being carried out on over 7000 acres  of land in
  Fulton County, Illinois.  A description of the plan is given.

  *Project planning,  *Recycling, *Sewage disposal,  *Watershed management,
  Filters, Application  techniques,  Monitoring,  Water  quality  control,
  Water reuse, Illinois
                                        667

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065H

THE SEALING MECHANISM OF WASTEWATER PONDS,

Chang, A. C., Olmstead, W. R., Johanson, J. B., and
Yamashita, G.

California University, Department of Soil Science
and Agriculture, Riverside, California

Journal of the Water Pollution Control Federation, Vol. 46, No. 7,
p 1715-1721, July, 1974.  5 fig, 5 tab, 11 ref.

The change of hydraulic conductivity in soils under prolonged submergence of
waste water has been determined together with the chemical change of soils
at the bottom of waste water ponds and the mechanism that reduces the rate
of infiltration in these ponds.  Columns of four different soil types re-
covered from the bottom of the pond indicated a quick reduction of soil
hydraulic conductivity and a sharp increase of leachable cations and anions
in all soils studied.  The layer that restricted the movement of water ini-
tially occurred at the surface, two inches into the soil column.  The initial
sealing was caused by the physical entrapment of suspended particles in soil
followed by a secondary mechanism of microbial growth that completely sealed
off the soil from water movement.  The drying of these completely sealed off
columns returned the hydraulic conductivity of columns back to the initial
magnitude thus indicating that the inhibition of water movement in soils w.ns
not caused by the change of cations that cause the deflocculation of soil
particles.

*Soil water movement, *Hydraulic conductivity, *Soil types, Waste storage,
Ponds, Soil chemistry, Cations, Anions, Suspended solids, Microbial
degradation
066H

SEASONAL EFFECTS IN FLOOD SYNTHESIS,

Brater, E. F., Sangal, S., and Sherrill, J. D.

University of Michigan, Department of Civil
Engineering, Ann Arbor, Michigan

Water Resources Research, Vol. 10, No. 3, p 441-445, June, 1974.  6 fig,
3 tab, 8 ref.

The effect of urbanization on flood flows is studied by analyzing inputs and
corresponding flood hydrographs from many watersheds, along with corresponding
inputs and responses from watershed models.  The inputs consist of precipita-
tion plus snowmelt minus infiltration and retention.  Because of the large
seasonal variation in infiltration rates, accuracy was improved by treating
rainfall frequencies seasonally in predicting flood runoff from precipitation
and snowmelt.  A procedure was also developed for including snowmelt with
sinter rains, and the resulting frequency curves of rain plus snowmelt are
presented and compared with conventional rainfall frequency curves.  It was
shown, as example, that a large difference exists between typical winter and
summer patterns in southeastern Michigan.

Urbanization, *Flood flow, *Watersheds (Basins), *Hydrographs, Hydrograph
analysis, Model studies, Precipitation, Snowmelt, Infiltration, Retention,
Seasonal, Storm runoff, Michigan
                                        668

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06 7H

FIELD STUDY OF THE FLOW PROCESSES IN A POROUS
AQUIFER BY MEANS OF TRACER DYES (FELDUNTERSUCHUNGEN
VON FLIESSVORGAENGEN IN EINEM PORENGRUNDWASSERLEITER MITTELS
FARBSTOFFINDIKATOREN),

Atakan, Y., Roether, W.,, Matthees, G., and Muennich, K.

Gas-Wasser-Fach-Wasser/Abwasser, Vol. 115, No. 4, p 159-164,
April, 1974.  8 fig, 1 tab, 10 ref.

The flow rate and the longitudinal dispersion of groundwater in a
porous aquifer (sand) in the Upper Rhine Valley was studied by means
of rhodamine B and uranin at depths of 3.5-5.5 m; 8-9 m, and 13-15
m.  Both the flow rate and the flow direction were found to be prac-
tically identical within this depth range.  The rate of propagation
averaged 40 m per annum.  Increase of the dispersion coefficient
with depth in a range of 0.0005-0.0037 sq cm/sec was determined.

*Flow rate, *Aquifers, Groundwater, Analytical techniques

*Rhine Valley, Tracer dyes, Rhodanine B, Uranin, Dispersion coefficient
068H

EXPERIENCES WITH THE 14C AND TRITIUM METHODS IN APPLIED
HYDROGEOLOGY (ERFAHRUNGEN MIT DER 14C- UNO 3H-METHODE
IN DER ANGEWANDTEN HYDROGEOLOGIE),

Geyh, M. A.

Oesterreichlsche Wasserwirtschaft, Vol. 26, No. 3/4, p 49-54, April
1974.  4 fig, 36 ref.

Experiences gained during the last five years with the application of the
14C and tritium tracing methods in applied hydrogeology are presented.  The
tracer methods proved useful, especially in the study of underground waters
in confined aquifers in loose rocks.  These methods were used primarily for
the determination of the flow velocity and direction, for the localization
of water capture areas and preferred flowpaths, as well as for the explora-
tion of hydraulic communications among different groundwater systems.  In
the case of unconfined aquifers in loose rocks, tracing methods supply
qualitative information on the hydrodynamic conditions.  Reliable, quanti-
tative interpretation of the results is possible.  The interpretation of
tracing data in solid rocks is problematic and even impossible if large
storage spaces are present in the source and capture area.

*Hydrogeology, Radioactive tracers, Aquifers, Flow characteristics,
Hydraulics, Groundwater

C-14 tracing, Tritium tracing, Flowpath
                                      669

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06 9H

AERATION REVITALIZES RESERVOIR,

McCullough, J. R.

Schramm, Incorporated, Aeration Division, West
Chester, Pennsylvania

Water and Sewage Works, Vol. 121, No.  6, p 84-85, June, 1974.   2 fig.

A dual pressure diffusion system, designed by Schraram, Incorporated,  has
been instrumental in mixing the reservoir waters of Prompton Lake, a highly
stratified recreational water body in  Northeastern Pennsylvania.  In the
system air is fed into a primary manifold at 70 to 100 psig and metered into
the diffusers through a patented device at 50-foot intervals.   The air is
released from the diffusers in sufficient volume and with just enough pres-
sure to overcome the hydrostatic head  allowing the air to rise because of its
buoyancy.  Thus it entrains water, mixing the layers of water and, simultane-
ously increases the dissolved oxygen levels in the water.  The system is de-
signed to perform the destratification function with careful attention to ef-
ficiency and keeping the costs down.

*Destratification, *Aeration, *Mixing, *Equipment, Dissolved oxygen,
Performance, Pennsylvania, Patents

*Diffuser
070H

GROUND-WATER QUALITY STUDY,

White, N. F., and Sunada, D. K.

Journal of the Irrigation and Drainage Division, Vol. 100, No. IRS, p 277-292,
September, 1974.  6 fig, 4 tab, 9 ref.

Groundwater contamination was studied at Severance Basin in Colorado.  Water
quality was analyzed for both geologic and hydrologic detail.  Increasing
contamination in the basin was attributed to leaching of applied fertilizer,
drainage from silage pits and feed lots, percolation of contaminants from oil
field brine pits, and geologic contamination of the aquifer.  Data limitations
made it difficult to isolate sources of groundwater contamination.  Major
causes of contamination in this aquifer were concluded to be a combination
of a high rate of evapotransplration and the relatively low surface and ground-
water outflow from the basin.  This resulted in total dissolved solids in the
basin increasing at the rate of 170 ppm per year.  When irrigation was ac-
companied by high evapotranspiration rates, mechanism of pollution proved to
be a major cause of aquifer contamination.

*Groundwater, *Contaminatlon, *Hydrologic aspects, Basins, Drainage,
Aquifers, Data analysis, Evapotranspiration, Irrigation, Dissolved solids
                                      670

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071H

CONTINUOUS SIMULATION MODELS IN URBAN HYDROLOGY,

Linsley, R., and Crawford, N.

Stanford University, Stanford, California

Geophysical Research Letters, Vol. 1, No. 1, p 59-62, May, 1974.  2 fig. 10 ref.

Continuous hydrologic simulation is defined.  The information needs for
urban water management systems are discussed and the use of a continuous
simulation model of hydrologic data in meeting these information needs is
reviewed.  For most planning efforts, data on probability of occurrence of
events is required.  In most urban situations this can only be provided by
use of a continuous simulation model.

*Hydrologic aspects, *Model studies, *Water resources management,
*Simulation models, Urban hydrology

Continuous simulation models
072H

A STUDY:  EFFECTS OF GEOLOGY AND NUTRIENTS ON WATER-
QUALITY DEVELOPMENT,

Stone, L. J.

Cullen College of Engineering
Houston University, Houston, Texas,
Department of Civil Engineering

Journal of the American Water Works Association, Vol. 66, No. 8, p 489-494,
August, 1974.  15 fig, 1 tab, 25 ref.

Two watersheds in northwest Arkansas were studied for geology and land
use in order to relate stream-water-quality development to the environ-
mental factors present in the ecosystem.  Relationships established were
water quality-geology and water quality-nutrient loading.  Analysis in-
cluded pH, alkalinity, calcium hardness, and electrical conductance of the
geological formations.  The areas of study contained low population density
of both humans and animals.  It was projected that any increase in either
population will markedly increase the nutrient loadings in stream flow.  Data
are to be used for future basin management and water quality control.

*Watersheds, *Hydrology, *Water quality control, Environmental effects,
Alkalinity, Geology, Populations, Stream flow, Water resources management
(applied)


Nutrient loading
                                         671

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073H

BINARY TREE MODEL SIMULATION OF THE BEHAVIOR OF URBAN
HYDROLOGIC SYSTEMS,

Surkan, A. J., and Kelton, P.

Nebraska University, Lincoln, Nebraska,
Department of Computer Science

International Journal of Systems Science, Vol. 5, No. 7, p 639-653,
July, 1974.  9 fig, 3 ref.

A simulator of urban hydrologic networks was designed based primarily
on geometric descriptors.  Its application is demonstrated using data
from the Northwood Gaging Installation in Baltimore, Maryland.  The
simulator incorporates a binary tree model of the network, a polygon
representation of the storm geometry, and time-varying rainfall in-
tensity to produce simulated hydrographs of flow.  A comparison between
simulated hydrographs and experimental runoff graphs is made.

*Urban hydrology, *Hydrograph analysis, Model studies, Data analysis,
Flow, Experiments

Northwood Gaging Installation, Baltimore, Maryland, Runoff graphs
074H

THE HYDRAULICS OF WASTE STABILIZATION PONDS:  PART ONE.
THE EFFECT OF HYDRAULIC FLOW CHARACTERISTICS ON TREATMENT
EFFICIENCY; PART TWO.  THE EFFECT OF WIND ON MIXING IN
STRATIFIED AND UNSTRATIFIED PONDS,

Watters, G. Z.

Utah  State University, Logan, Utah, College of Engineering,
Utah  Water Research Laboratory

Office of Water Resources Research Final Report A-008-Utah, June, 1972.
245 p, 81 fig, 9 tab, 65 ref, 1 append.

Biological activity in a waste stabilization pond is greatly influenced
by the environmental conditions of temperature, wind, sunlight, and the
hydraulic flow patterns.  The hydraulic flow characteristics will have
an effect on the dispersion and the average detention time of the waste
and on the BOD and pathogenic organism removal efficiency of the treatment
process.  The effects of hydraulic flow characteristics on the treatment
efficiency were evaluated by using information that is obtained from the
age distribution functions of the fluid particles within a continuous flow
process  vessel.  The report presents the literature reviews, theoretical
developments, experimental procedures, and the presentation and discussion
of results for both sections.  A mathematical model was designed to be
used  in  conjunction with another equation to predict treatment efficiencies.

*Waste treatment, *Hydraulics, *Flow, Hydraulic models, Flow characteristics,
Sewage lagoons, Oxidation lagoons, Biological treatment, Mathematical
models,  Reviews

Stabilization ponds, Hydraulic flow characteristics
                                         672

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075H

FEASIBILITY OF HYDRAULIC TRANSPORT AND TREATMENT OF GROUND
HOUSEHOLD THROUGH SEWERS,

Guzdar, A. R. and Rhee, S. S.

Foster-Miller Associates, Incorporated, Waltham, Massachusetts

National Technical Information Service Report PB-229 256, April, 1974.
200 p, 67 fig, 9 tab, 38 ref, 2 append.

This paper examined the feasibility of hydraulic transport of ground
household refuse through the straight pipes of existing sewers by studying
the gravity flow of ground refuse slurry through inclined pipes.  The
feasibility of treating domestic sewage containing ground refuse was
studied by conducting a laboratory analysis of the sewage-refuse slurry.
From the results of the study, it was concluded that the transport of
ground refuse through existing sewer lines is feasible and that it is
also feasible to treat ground refuse in sewage in at least 0.5 to 1 percent
concentrations, with qualifications.  Additional work must be completed
before implementation.  Areas for future research are suggested.

*Hydraulic transportation, *Sewers, *Solid wastes, Sewage treatment,
Sewage disposal, Cities, Domestic wastes, Municipal wastes, Sewage slurry

*Refuse, *Sanitary sewers, *Ground refuse, Solid waste management
076H

UPTAKE OF INORGANIC MERCURY BY BED SEDIMENTS,

Kudo, A.,  and Hart, J. S.

Journal of Environmental Quality, Vol. 3, No. 3, -p 273-278, July-September,
1974.  7 fig, 21 ref.

The kinetics of inorganic mercury uptake as mercuric chloride by a variety of
freshwater river sediment types typical of Ottawa River sediments have been
studied to determine the influence of mercury concentration in water, hydro-
dynamic effects, sediment depth, aerobic or anaerobic conditions, and two types
of water.  Uptake appears to depend strongly on concentration of mercury in
water and water velocity, and not on sediment depth or water type.  No signi-
ficant difference in uptake rates was observed between aerobic and anaerobic
conditions during the ten days studied.

*Mercury, *Sediment load, Velocity, Kinetics, Chlorides, Freshwater, Canada

*Inorganic mercury, *Uptake rates, Mercury concentration
                                      673

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077H

FILTER BASINS TO HALT POLLUTION CAUSED BY GREAT LAKES
DREDGING,

Engineering News Record, Vol. 193, No. 8, p 20-21, August 15, 1974.

With the construction of huge settling basins contained within dikes the
problem of disposal of polluted materials dredged from the bottom of inland
harbors and channels is being solved in the Great Lakes region.  These rubble
embankments, called filtration walls, consist: of natural stone and sand filter
beds.  The theory behind the design is that: contaminated solids will settle
out, forming new land while the liquids will filter back into the lakes con-
siderably purified and relatively free of suspended solids.  The historical
and technological development of such basins is described.

*Water purification, Filtration, Dredging, Design criteria, Great Lakes,
Technology, Water pollution control, Settling basins

Filtration walls
078H

FLOOD ESTIMATION FOR URBAN AND RURAL CATCHMENTS,

Aitken, A. P.

Snowy Mountains Engineering Corporation,
Hydrology Branch, Australia

Australian Road Research, Vol. 5, No. 3 p 50-71, October, 1973.
5 fig, 38 ref.

Existing and developing procedures for flood estimation of urban and rural
catchments in Australia are surveyed.  A 1958 publication entitled Australian
Rainfall and Runoff, which has been a guide to practicing engineers, is now
being revised.  Criticisms of the publication follow new developments in
hydrology, particularly those of mathematical and computer models.  Methods
for studying urban catchments include the Transport and Road Research
Laboratory Hydrograph Model (TRRL), a British computer model; the Rational
Formula, a statistical model; and mathematical models such as the complex
Storm Water Management Model.  Mathematical models may have indirect or
direct applications.  It was concluded, for urban catchments, that despite
its limitations, the Rational Formula is the most widely used in Australia,
and that additional research is needed, including collection of more urban
rainfall-runoff data.  Methods for investigating flood estimation for rural
catchments include the Rational Formula, the soil conservation method, the
Bureau of Public Roads method, and the tacitly maximised peak method.
Hydrograph techniques and mathematical models are still in developmental
stages for rural areas.  A frequency analysis of stream flow records is the
most used method for Australian rural flood estimation.

*Flood forecasting, *Mathematical models, *Hydrographs, *Rational formula,
*Australia, Computer models, Engineering, Rural areas, Urban areas

Transport and Road Research Laboratory Hydrograph, Storm Water Management
Model
                                     674

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079H

URBAN RUNOFF BY LINEARIZED SUBHYDROGRAPHIC METHOD,

Chien, J-S., and Saiga, K. K.

Dalton, Dalton, Little, Newport, Incorporated, Cleveland,
Ohio

Journal of the Hydraulics Division, Vol. 100, No. HY8, p 1141-1157,
August, 1974.  6 fig, 2 tab, 19 ref.

A review of the general analytical methodologies in urban hydrology and the
development of the Linearized Subhydrographs Method for Urban Runoff
Determination are presented.  The Linearized Subhydrographs Method is
considered a useful tool for the design of a new system and the analysis
of an existing system.  It uses the principle of mass conservation and
simple parameters and functional relationships.  Peak rates of runoff are
computed from the runoff coefficient.  Linear variation of the rising limb
and the receding limb of the subhydrograph for a small basin is assumed.
Kinematic wave time to equilibrium is used as a factor for the determination
of Subhydrographs.  When this method was applied to the typical urban
drainage basin at Oakdale Avenue, Chicago, Illinois, the predicted hydro-
graphs and the recorded hydrographs were in agreement in time synchronization,
and the predicted peak rates of runoff were close to the recorded ones.

*Urban runoff, *Runoff forecasting, *Hydrographs, Runoff coefficient,
Peak discharge, Hydrology, Drainage area

*Linearized Subhydrographs, Mass conservation, Kinematic wave time
080H

ON THE MODELLING OF CORRELATION FUNCTIONS FOR RAINFALL
STUDIES,

Sharon, D.

Hebrew University,
Jerusalem, Israel

Journal of Hydrology, Vol. 22, No. 3/4, p 219-224, August, 1974.
2 fig, 11 ref.

Localized rainfall may be studied by correlation-distance relationships.
Analysis has been applied to network design, with the goal of determining
minimum requirements to obtain accurate averages of precipitation for a
given area.  If correlation analysis is to be applicable to rainfall
situations, the criteria for including days in the sample should allow
for days with localized rainfall.  Also, correlation functions should be
derived separately for groups of days, storms or hours that are homogeneous
with respect to the nature of the precipitation, and the model should be
adapted to non-monotonous correlation functions, for which certain apparent
irregularities may have meterological or climatological significance.
No all-inclusive model is possible for localized rainfall; and there must be
further investigation of the behavior of correlation functions under various
circumstances.

*Rainfall, *Correlation analysis, Model studies, Hydrologic aspects

*Localized rainfall models;, Monotonous correlation functions
                                         675

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    081H

    GEOTHEMAL WELLS IN IMPERIAL VALLEY, CALIFORNIA:
    DESALTING POTENTIALS, HISTORICAL DEVELOPMENT, AND
    A SELECTED BIBLIOGRAPHY,

    El-Ramly, N., Peterson, R. E., and Seo, K. K..

    National Water Supply Improvement Association Journal, Vol. 1, No. 1,
    p 31-38, July, 1974.  1 fig, 1 tab, 26 ref.

    Possible solutions to future water shortages include waste water reclama-
    tion, importation, and desalting of sea or brackish water, but all of these
    are energy-intensive and energy is also in short supply.  A potentially
    important source of readily available energy is geothermal brine, which is
    an underground resource found in abundance in the Imperial Valley, California.
    The background of geothermal well drilling in the Imperial Valley region is
    presented.  Field research is being performed in the areas of heat-exchange
    technology and geothermal desalting.  Brine disposal has been one problem
    holding back geothermal development.  About two pounds of brine are produced
    for every pound of steam generated.  The corrosive and scaling nature of the
    geothermal brines have stopped large scale commercial development so far.
    One process appears to offer promise for future developments; the Magmama
    power process is a vapor-turbine cycle.  Hot brine is pumped up from the
    geothermal reservoir and the phase change of water to steam is suppressed.
    The brine is cooled in a heat exchanger where it heats a secondary fluid
    with a low boiling point, such as isobutane or freon, which is then used to
    drive a turbogenerator in a closed cycle.  The cooled brine is injected into
    a well to maintain the underground reservoir pressures.  The establishment
    of the feasibility of geothermal power in Imperial Valley will provide
    electrical energy and will better the prospects of a dual purpose geothermal
    power-desalting project in the Valley.

    *Geothermal studies, *Desalination, *Energy, *Brines, Brine disposal,
    Corrosion, Scaling, Temperature, Thermal water, Heat transfer, California,
    Potable water

    Imperial Valley, California

082H

UTILIZATION OF THE EARTH'S NATURAL HEATING SYSTEM TO
DESALT GEOTHERMAL BRINES FOR AUGMENTATION OF THE
COLORADO RIVER SYSTEM,

Lundberg, E.  A.

Bureau of Reclamation,  United States Department of the Interior,
Boulder City,  Nevada,  Lower Colorado Regional Office

National Water Supply Improvement Association Journal,  Vol.  1,  No.  1,  p 39-51,
July 1974.   9 fig,  3 tab.

The available surface water supplies in the Colorado River Basin are being depleted
by increasing agricultural demands and by an expanding population which is using
water at a higher per capita rate.  Water quality problems also exist  in the Imperial
Valley,  California, because of the presence of highly saline soils and many saline
springs which add significant quantities of salt to the river.   Geothermal sources
stored in the form of a hot brine underground in the Imperial Valley have the poten-
tial to yield economical new supplies of fresh water by desalting and  also to
yield mineral by-products and the production of electricity.   A program for water
production from the geothermal resources consists of three proposed stages:   the
research and development stage;  the demonstration stage;  and, the large-scale
development stage.   The research and development stage is now in progress and includes
extensive geological,  geophysical, and water chemistry investigations  to determine
the potential and extent of the geothermal resource.   The demonstration stage
would show the viability of large-scale development.   The large-scale  development
stage is the fully operational stage which could augment  the Colorado  River by
several million acre-feet of desalted water annually and  would have an associated
electric power production.   Investigations completed include the drilling of two
geothermal wells,  one to 8030 feet and the other to 6005  feet and the installation
of two desalting test units,  a multistage flash unit and  a vertical tube evaporator.
The proposed next step in the investigations is the construction of a pilot plant
capable of processing 200,000 to 500,000 gallons per day.

*Geothermal studies,  *Desalination, *Brines,  *Energy, Thermal water, Potable
water, Water resources development, Hater quality control, California

Imperial Valley,  California

                                         6Z6

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                         MISCELLANEOUS



001J

PETROLEUM REFINERY EFFLUENT  REGULATIONS AND  GUIDELINES,

(Canadian) Environmental Protection  Service  Regulations,  Codes  and Protocol
Report No. EPS  l-WP-74-1 January,  1974.

As  of November  1973,  regulations  respecting  deleterious substances in  liquid
effluents from  petroleum refineries  were  annexed  to  the Canadian Fisheries
Act.  Specific  substances;  included under  said  regulations  include oil  and
grease, phenols,  sulfide,  ammonia nitrogen,  total suspended matter, and any
substance capable of  altering  the pH of liquid effluent or once-through cooling
water.  Simultaneously  issued  by  the Department of the Environment were guide-
lines respecting  acute  toxicity of liquid  effluents  from  petroleum refineries
and the quality of liquid  effluents  from  existing petroleum refineries.  Also
detailed are  explanatory notes regarding  the regulations  and both guideline
criteria.

*Regulations, Liquid  Wastes, Effluents, *0il Industry, Oil Wastes,
Toxicity, Standards,  Canada, Quality Control,  Oil, Phenols, Sulfides,  Hydrogen
Ion Concentration, Suspended Load, Ammonia Cooling Water
002J

THE EFFECTS OF HOUSEHOLD SANITARY SYSTEMS ON EFFLUENT PHOSPHATE
LEVELS,

La Valle, P.

Canada-Ontario Agreement on Great Lakes Water Quality Report No. 72-5-14
March 1973.

Work conducted to assess the variation of phosphate input to urban water-
ways from residential areas serviced by septic tanks and sanitary systems is
outlined.  Data collected on the population density of each sample area, and
the amount of phosphorus in household detergents as well as lawn and garden
fertilizers is included.  For a number of urban watersheds, the presence of
household septic tank systems played a major role in determining stream
phosphate concentrations accounting for 56-76 percent of the spatial variation
in stream total phosphate levels and 61-77 percent of the spatial variation
in orthophosphate levels.  Rainfall and fertilizer usage inputs were also
statistically significant but secondary to septic tank systems.  Results
suggest that if phosphate pollution abatement is to be practiced, a concerted
effort should be made to serve all urban residential units by an integrated
sewer system with subsequent phosphate removal at the wastewater treatment
plant.  Also that septic tanks are not an efficient means of keeping excessive
quantities of phosphates from local stream systems.

*Phosphates, Sanitary Engineering, *Septic Tanks, *Sewers, Urban Drainage,
Urbanization, Pollution Abatement, Effluents, Canada, Data Collections
                                        677

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00 3J

LAND APPLICATION OF SEWAGE SLUDGE,

Bates, T.

Canada-Ontario Agreement on Great Lakes Water Quality Report No. 71-4-1
September, 1972.

This report details a literature review undertaken to determine the extent of
present knowledge for ecologically safe and agriculturally productive applica-
tion of sewage sludges to farm lands.  It was concluded that sludge is quite
variable in solids and nutrient content from one sewage plant to another
and also on a daily basis.  Nitrogen is likely to control rates of sludge
application which should be restricted to those needed for crop production,
yet leaching of phosphorus into the groundwater is not expected to be a major
problem controlling application rates.  Reports indicate that the raetals
copper, zinc, cadmium, nickel, chromium, and lead are high in some sludges
and may be cause for concern.  Studies are reported on the survival of human
and animal pathogens and viruses whose populations are reduced by anaerobic
digestion and eliminated by heat drying.  No information was found concerning
the land application of sludges resulting from treating sewage with chemicals
for the removal of nutrients.  Little information is available on times and
methods of sludge applications which will prevent or eliminate water contamina-
tion by erosion and runoff.

Reviews, *Sewage Sludge, *Farm Management, Nitrogen, Nutrients, Application
Methods, Copper, Zinc, Cadmium, Nickel, Chromium, Lead, Viruses, *Sewage
Treatment, Sludge Disposal, Pathogenic Bacteria
004J

PHOSPHORUS REMOVAL DESIGN SEMINAR,

Canada-Ontario Agreement on Great Lakes Water Quality, May 28-29, 1973.

The Phosphorus Removal Design Seminar was intended to provide an exchange
of information between consulting engineers and government personnel involved
in the design and approval of phosphorus removal facilities at waste treatment
plants.  The seminar was divided into four sessions covering various aspects of
phosphorus removal and included:  a general session; mechanical and process
design session; costs, instrumentation, and chemical handling session; and,
a sludge handling, treatment, and disposal session.  The papers presented
at each session are contained in the conference proceedings and should
serve as a useful reference for the design of phosphorus removal facilities
at sewage treatment plants.

*Conferences, Documentation, Canada, Phosphorus., Treatment Facilities, Sewage
Treatment, *Design Criteria, Engineering Education


*Phosphorus Removal
                                       678

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 005J

 REGIONAL WATER AUTHORITIES:   ORGANIZATIONAL PATTERNS  -
 PURPOSE OR PROFESSIONAL,

 Nunn,  G. and Hattersley,  R.

 Water  Pollution  Control,  Vol.  72, No.  8,  p 675-692,  1973.   3  fig,  7  ref.

 Since  1967 the need  to  establish  single purpose  regional  authorities  for
 administration of  sewage  purification  services has been evidenced, affirmed,
 and  reaffirmed.  This paper  gives considerable attention  to the  ultimate  form
 the  reorganization will take,  stressing organizational patterns  rather  than
 detailed structures.  The work of the  regional water  authorities  is  discussed
 function by function, the provisional  pattern immediately after  reorganization
 has  been considered,  and  alternatives  put forward based on professional
 grouping.  The resultant  recommendation is a  functional pattern  which should
 ensure that the  regional  water authorities are largely made up of inter-
 disciplinary groups  making  their  careers  in departments having a clear
 functional purpose.

 Administration,  *Water  Management  (Applied),  Regional Development, *Sewage
 Districts, *Planning, Organizations

 Great  Britain
006J

MANAGEMENT PRIORITIES:  NOW AND THE FUTURE,

Snape, T. R.

Water Pollution Control, Vol. 72, No. 8, p 666-674, 1973.  k fig.

In this paper it is maintained that water is a growth industry, and thus has
characteristic problems related to the pace of change.  Said problems of
change are essentially to do with people and their attitudes, their adaptability,
their ability to grasp and exploit new opportunities, and their ability to
plan and control the change.  The validity of this contention is explored
together with management priorities for the future from the consultant's
point of view.

*Personnel Management, *Water Allocation (Policy), Water Management (Applied),
Administration
                                         679

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 00 7 J

 EFFLUENT STANDARDS STRATEGY:   REJUVENATION OF AN OLD GAME
 PLAN,

 Cleary,  E.  J.

 Journal  of  the Water Pollution Control Federation,  Vol.  46,  No.  1, p 9-17,
 January, 1974.  11 ref.

 In this  paper the events that have contributed to the new federal policy of
 placing  primary reliance on uniform effluent standards for the achievement of
 clean water goals are traced.  Merits and limitations associated with the two
 regulatory  concepts are  outlined and earlier applications of effluent standards
 practice by certain state and interstate regulatory agencies are cited.

 *Effluents, Standards, *Water Pollution Control, Application Methods,
 Environmental Control, Water Quality Standards,  Legislation, *Federal Government

 Environmental Protection Agency
00 8 J

RESULTS OF RED TIDE FORMATION IN TOKYO BAY,

Tsuji, T., Seki, H., and Hattori, A.

Journal of the Water Pollution Control Federation, Vol. 46, No. 1, p 165-172,
January, 1974.  6 fig, 2 tab, 9 ref.

The status of eutrophication in Tokyo Bay was investigated from August 1971
to May 1972 with special attention given to the formation of a microaerobic
zone.  This zone appeared in the bottom layer in the region of a gyre of the
coastal water in the inner part of the bay, after the occurrence of the red
tide caused by phytoplankton.  On the basis of measured oxygen consumption
rates, it is suggested that the multiple crops of phytoplankton in a red
tide are transported downward to the bottom layer before their easily decom-
posable fraction has been decomposed in the upper layers.

*Eutrophication, investigations, Coasts, Hypolimnion, Phytoplankton,
*Red Tide, Oxygen Requirements, Degradation (Decomposition)

Tokyo Bay, Japan
                                      680

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009J

CHANGES IN PERIPHYTIC ALGAE FOLLOWING BICARBONATE ADDITIONS
TO A SHALL STREAM,

Dickman, M.

Journal Fisheries Research Board of Canada, Vol. 30, No. 12, p 1882-1884,
December, 1973.  3 fig, 6 ref.

Additions of less than 50 mg/liter sodium bicarbonate significantly increased algal
standing crop on glass slides exposed in the treated portion of a small stream
during a two-month period.  Filamentous green algae dominated the periphyton
community of both bicarbonate treated and control slides when the study was
terminated after 63 days.  A slight shift in species composition toward the
Cyanophycea on  the bicarbonate  treated slides was also noted.

laboratory Tests, *Bicarbonates, Sodium Compounds, *Streams, Chlorophyta,
Cyanophyta, Methodology, Eutrophication
010J

SEASONAL AND SPATIAL CHANGES IN PRIMARY PRODUCTION AND
NUTRIENTS IN LAKE MICHIGAN,

Rousar, D. C.

Water, Air, and Soil Pollution, Vol. 2, No. 4, p 497-514, December, 1973.
17 fig, 1 tab, 31 ref.

Samples were collected from a railroad ferry between Wisconsin and Michigan
over a period of 17 months to determine the spatial and temporal distribution
of primary production and several physical and chemical variables.  Conductivity,
silica, total phosphorus, soluble reactive phosphorus, plant pigments, and
carbon uptake exhibited inshore-offshore differences, and all but silica
were highest at the Wisconsin inshore station, thus suggesting nutrient enrich-
ment of Lake Michigan by Milwaukee.  Temperature, pH, phenolphthalein alkalinity,
nitrate, silica, plant pigments, and C uptake showed varying degrees of
seasonal change.  A bimodal seasonal abundance of phytoplankton was revealed.

*Sampling, Wisconsin, Michigan, *Nutrients, Phytoplankton, Seasonal, Plant
Physiology, Physical Properties, Chemical Properties, Conductivity, Phosphorus,
Silica, *Lake Michigan, Temperature, Hydrogen Ion Concentration, Nitrates,
*Eutrophication, Plant Growth


Carbon Uptake, Plant Pigments, Phenolphthalein Alkalinity
                                    681

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011J

DISTRIBUTION OF PHOSPHATES IN LAKE MARIUT, A HEAVILY
POLLUTED LAKE IN EGYPT,

Saad, M. A. H.

Water, Air, and Soil Pollution, Vol. 2, No. 4, p 515-522, December,  1973.
3 fig, 28 ref.

In  recent years Lake Marlut was subjected  to severe pollution.  The  phosphate
content of  this Lake was exceedingly higher than that  of  the  other Egyptian
Lakes.  The distribution of phosphates in  Lake Mariut  was found to depend  upon
certain factors which  are discussed herein.

*Lakes, *Phosphates, *Distribution Patterns, Seasonal,  Investigations, Water
Pollution,  *Environmental Effects, Water  Pollution Sources


Lake Mariut, Egypt, Phosphate Distribution
012J

LEACHING REQUIREMENT STUDIES:  SENSITIVITY OF ALFALFA TO
SALINITY OF IRRIGATION AND DRAINAGE WATERS,

Bernstein, L. and Francois, L. E.

Soil Science Society of America Proceedings, Vol. 37, No. 6, p 931-943,
November-December, 1973.  4 fig, 10 tab, 17 ref.

Alfalfa was grown in 0.6 by 1.5 meter greenhouse lysimeters and irrigated with
two waters of EC 1 and 2 mmho/cm prepared by adding equivalent amounts of NaCl
and CaC12 to a 0.4 mmho/cm tap water.  Yields showed relatively little effect
of leaching fraction (LF) within the limits consistent with steady-state salt
balance for suction-drained lysimeters but decreased 26 percent at the lowest
LF for gravity-drained lysimeters.  Cessation of leaching or reduction of LF
to levels requiring drainage water salinities for salt balance at steady
state to exceed 35 mmho/cm eventually reduced yields.  Yield response appears
to be related to the calculated mean salinity against which water was absorbed,
which is influenced more by the salinity of the irrigation water than by
the salinity of the drainage water.  LF in the broad range that permitted
nearly maximum growth had essentially no effect on water requirement or on
Na and Cl contents of the harvested alfalfa.  Increasing irrigation water
salinity in the range 0.4 to 2 mmho/cm consistently increased plant Na and
Cl contents, but had no effect on water requirement.  Implications of the
demonstrated lower leaching requirements for irrigation management and
drainage and for water quality assessment are discussed.

*Alfalfa, *Lysimeters, *Leaching, *Water Quality Control, Irrigation Operation &
Management, Irrigation Effects, Salt Balance, Drainage Water, Investigations,
Salts, Chlorides, Soil Profiles, Water Requirements
                                    682

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013J

THE SEVERN SCHEME OF THE BRISTOL WATERWORKS COMPANY,

Water and Water Engineering, Vol. 77, No. 933, p 431-432, November, 1973.

The first phase works described herein augment the Bristol Waterworks Company's
potable water supply by 24 mgd with provision in phase two for extension to
supply a further 12 mgd, thus meeting predicted demands into the 1990's.
The aim has been to provide buildings of a functional, industrial style with
space to accommodate the additional requirements of the second phase extensions.

*Potable Water, *Water Supply, Water Purification, Equipment, *Treatment
Facilities, Construction Materials

Great Britain
014J

TRENT-WITHAM-AN CHOLME SCHEME AND PROJECT OF THE
LINCOLNSHIRE RIVER AUTHORITY,

Hawkins, H. S. and Arrowsmith, J. D.

The Public Health Engineer, No. 6, p 255-272, November, 1973.

A brief description of the organization and establishment of the Lincolnshire
River Authority (LRA) is given.  Regulation of the three titled rivers exists to
enhance the water resources and meet public water supply demands.  An outline
of this conservation scheme together with design criteria and construction
requirements authorized by the LRA are included.

*Water Resources, *Water Demand, *River Training, *Control Systems, Instrumenta-
tion, Pipelines, Design Criteria, Reservoirs, Outlets, Pumping Plants,
Chlorination, Water Quality


Great Britain
                                     683

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 015J

 ACCUMULATION PHENOMENON WHICH TAKES PLACE IN A MUSSEL (MYTILUS
 GALLOPROVINCIALIS LMK)  GROWN IN AN ARTIFICIALLY POLLUTED ENVIRONMENT,
 VERIFICATION OF A SIMPLIFIED MODEL OF THE DYNAMIC EQUILIBRIUM OF
 METAL RIPARTITION BETWEEN MUSSELS AND SEA-WATER,  NOTE II -
 POLLUTION FROM COPPER,

 Majorl,  L. and Petronio, F.

 L'Igiene Modema, Vol.  66, No.  1, p 64-78, January-February, 1973.  7 fig,
 3 tab,  31 ref.

 Research consisting of  the evaluation of the potential damage due to pollution
 by metals using as the  biological indicator, mussels, and its capability to
 act as  a local pollution warning-signal, is explained.  Such evaluations are
 quantified by the use of a dynamic kinetic model of the metal division between
 mussel  and water.  Results of experimental research show that mussel ability
 to accumulate copper in polluted waters thus confirming aforementioned
 research purposes.

 investigations, *Evaluatlon, Metals, *Water Pollution Sources, Mussels,
 *Bioindicators, Model Studies,  *Copper
016J

A NOTE CONCERNING THE ENVIRONMENTAL ACCEPTABILITY OF NITRILO-
TRIACETIC ACID (NTA) :  THE EFFECT OF NTA ON THE GROWTH OF
GYMNODINIUM BREVE,

Doig, M. T. and Martin D. F.

Environmental Letters, Vol. 6, No. 1, p 31-36, 1974.  1 tab, 12 ref.

The effect of NTA on the growth of Gymnodinium breve was determined by a
modification of the flask test.  The response of G. breve to enrichment of
natural waters with NTA alone or NTA in the presence of domestic waste
materials was evaluated in terms of the following four growth parameters:
lag time, growth constant, mean generation time, and maximum cell count.
nta  was not toxic to G. breve at concentrations up to 10 ppm and no
biostimulatory effects were noted.

Nitrilotriacetic Acid, *Gymnodinium, *Analytical Techniques, Domestic Wastes,
Eutrophication, Toxicity, *Growth Rates

Lag Time, Growth Constant, Mean Generation Time, Maximum Cell Count
                                        684

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 017J

 THE USE OF ALGAL ASSAYS FOR DETERMINING THE EFFECT OF IRON AND
 PHOSPHORUS COMPOUNDS ON THE GROWTH OF VARIOUS ALGAL SPECIES,

 Clasen, J. and Bernhardt, H.

 Water Research, Vol. 8, No. 1, p 31-44, 1974.  16 fig, 7 tab, 58 ref.

 Algal assays were performed with unlalgal cultures to determine the productivity
 of the water samples tested.  The productivity of the water samples rich in
 turbid materials and algae was higher in heat sterilized samples than those
 prepared by filtration.  There is a clear correlation between the productivity
 of unfiltered sterilized water samples and their iron and total phosphorus
 content.  Assays proved that the large decrease in productivity is due chiefly
 to the removal of phosphorus compounds and the removal of iron and other
 unknown substances.  There are indications that the amount of iron required
 for growth, as compared with that of phosphorus, varies greatly depending
 on the individual algal species.  The significance of the algal assay and the
 results relating to measures for limiting eutrophication using phosphorus
 removal plants are discussed.

 *Eutrophication, *Bioassays, *Algae, Water Samples, *Testing, Fertility,
 Filtration, Iron, Phosphorus, Growth Rates
018J

INORGANIC NITROGEN REMOVAL IN A COMBINED TERTIARY TREATMENT-
MARINE AQUACULTURE SYSTEM - II.  ALGAL BIOASSAYS,

Goldman, J. C., Tenore, K. R. and Stanley, H. I.

Water Research, Vol. 8, No. 1, p 55-59, 1974.  3 fig, 2 tab, 9 ref.

Algal bloassays, conducted on samples from various components of the combined
tertiary treatment-marine aquaculture process, demonstrated that nitrogen
removal is necessary to prevent increasing the algal growth potential of
coastal marine waters receiving wastewater discharges.  When nitrogen was
removed from secondarily treated domestic wastewater, the wastewater in varying
dilutions with seawater could not support more algal growth than the seawater
alone.  By adding nitrogen back to the treated wastewater the algal growth
potential was increased to that of the untreated wastewater.  This was demon-
strated by assaying samples containing both artificially added nitrogen and
nitrogen regenerated by oysters.  Assays of the effluent from the seaweed
system showed that the removal of regenerated nitrogen reduced the algal
growth potential to that of natural seawater.

*Bioassays, Sampling, *Tertiary Treatment, Discharge (Water), Nitrogen,
*Algal Control, *Waste Water (Pollution), Coasts

Algal Growth
                                       685

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 019J

 THE SCREENING AND SELECTION OF SOLVENTS FOR THE EXTRACTION
 OF PHENOL FROM WATER,

 Kiezyk, P. R. and Mackay, D.

 Department of Chemical Engineering, and Applied Chemistry,
 University,of Toronto,
 Toronto, Ontario, Canada

 The Canadian Journal of Chemical Engineering, Vol. 51, No. 6, p 741-745,
 December, 1973.  1 fig, 1 tab, 23 ref.

 The thermodynamic basis for the selection of solvents for the removal of
 phenol by liquid-liquid extraction from waste water is discussed.  Data are
 presented showing the often marked dependence of distribution coefficient on
 solute concentration at levels of 5 to 100 mg/liter.  Experimental data for
 the infinite dilution activity coefficient of phenol in 26 solvents at 25 C
 are correlated using a Regular Solution approach by assigning a value to an
 interaction energy term dependent on the chemical nature of the solvent.  The
 accuracy is not sufficient for design purposes, but the method can be used for
 screening.  Toxicity and biogradability of the preferred solvents are discussed.

 *Solvents, *Phenols, *Waste Water, *Separation Techniques, Toxicity,
 Biodegradation

 Canada
020J

RESULTS OF EXAMINATIONS OF HOSPITAL WASTE WATER
(ERGEBNISSE VON UNTERSUCHUNGEN VON KRANKENHAUSABWAESSERN) ,

Althaus, H.

Leiter der Wasserhygiene-Abteilung des hygiene-
Instituts des Ruhrgebiets, 465 Gelsenkirchen,
Rotthauser Str. 19

Oeffentliches Gesundheitswesen, Vol. 35, No. 2, p 960-140, Nov., 1973.
4 fig, 3 ref.

Examination of receiving water bodies which receive hospital wastewater
resulted in the following findings.  Pathogenic germs, particularly salmonel-
la, were found in abundance.  However, their presence was at a lesser degree
than from waste water discharged by a residential area, this being attributed
to the fact that disinfectants are used to treat hospital wastewater prior
to its release to the public sewer system.  If the hospital is not located
near a purification plant where waste water receives treatment, then disin-
fection is practiced at the hospital by heating or chlorination before it
is discharged to the receiving streams.

*Hospitals, *Waste Water Treatment, *On-Site Investigations, *Pathogenic
Bacteria, *Salmonella, Treatment Facilities, Disinfection
                                        686

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021J

A BIOASSAY OF TOXICITY USING PROTOZOA IN THE STUDY OF
AQUATIC ENVIRONMENT POLLUTION AND ITS PREVENTION,

Apostol, S.

Catedra de igiena, Institutil de medlclna lasl,
lasi, R. S. Romania

Environmental Research, Vol. 6, No. 4, p 365-372, 1973.  4 fig, 2 tab,
17 ref.

Methods are described for short-term  (acute) and long-term (chronic) toxi-
city evaluation in order to determine the degree of toxlcity of various
water-borne contaminants and to establish the tolerance to these agents.
The technique consists in exposure of cultures of Paramecium caudatum Ehr.
in serial dilution tests for short and extended time intervals.  Results
may be rapidly obtained within a few hours in the acute and within two weeks
in the chronic tests.

*Toxicity, *Bioassay, *Evaluation, *Protozoa, Laboratory Tests, Bioindica-
tors, Water Pollution Control.

*Paramecium
022J

THE RIVER ITCHEN  SCHEME OF THE PORTSMOUTH WATER  COMPANY,

Water and Water Engineering, Vol.  77, No. 934, p 481-485,  Dec.  1973.   1  fig.

Details of the new scheme inaugurated in October 1973  and  designed  to  augment
the potable supplies by 10 mgd initially are  given.  The first  stage works
includes a river  intake, low lift  pumping station,  treatment  works, high
lift pumping station,  8.5 miles  of 40-inch main,  and a 6 million gallon
service reservoir.  The second stage works includes 2.5 miles of 36-inch
main, a 10 million gallon service  reservoir,  and further lengths of 20-inch
and 36-inch connecting mains.

^Treatment Facilities, ^Equipment,  *Design Criteria, Pumping  Plants, Sewers,
Reservoir Storage, Capital Costs,  Potable Water,  Water Supply,  Construction,
Rivers

Great Britain
                                        687

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      023J

      BACTERIAL DEGRADATION OF CYCLOHEXANE PARTICIPATION OF A
      CO-OXIDATION REACTION,

      de Klerk, H., and van der Linden, A. C.

      Koninklijke/Shell-Laboratorium, Amsterdam, the
      Netherlands

      Journal of Microbiology and Serology, Vol. 40, No. 1, p 7-15, 1974.  2  fig,
      1 tab, 6 ref.

      Complete biodegradation of cyclohexane was demonstrated to occur in a system
      containing two strains of Pseudomonad bacteria, an n-alkane oxidizer and a
      microorganism utilizing cyclohexanol.  n-Heptane also is present as a sub-
      strate for the former with neither bacterial strain being capable of utilizing
      cyclohexane individually.  Cyclohexane biodegradation occurs in the follow-
      ing two steps:  first, the conversion of  cyclohexane into cyclohexanol  by
      the n-alkane oxidizer, and second, through utilization of cyclohexanol  by
      the second strain.  Unsuccessful methods  used  to accumulate a bacterium
      which could grow on cyclohexane as its sole source of carbon are described.

      *Biodegradation, *0rganic Compounds, *Pseudomonas, Investigations, Labora-
      tory Tests .


      *Cyclohexane, *Cyclohexanol Utilization
024J

NEUROLOGICAL CHANGES IN CATS FOLLOWING LONG-TERM DIET OF
MERCURY CONTAMINATED TUNA,

Chang, L. W., Yamaguchi, S., and Dudley, A. W., Jr.

Wisconsin University, Dept. of Pathology, Madison,
Wisconsin

Acta Neuropath. (Berlin), Vol. 27, No. 2, p 171-176, 1974.  4 fig, 30 ref.

Kittens of both sexes were fed daily with mercury contaminated tuna containing
about 0.5 ppm mercury.  Neurological disturbances similar to those in Mina-
mata disease or in experimental mercury intoxication were observed after
7-11 months of the experimental course.  Microscopic examination revealed
dcsgenerations of the granular layer and some Purkinje neurons in the cere-
bellum.  Neuronal necrosis was also observed in the cerebral cortex.  This
investigation suggests that fish containing 0.5 ppm mercury may still be po-
tentially hazardous to health when consumed in excessive amounts for prolonged
periods of time.

*Mercury, *Toxicity, *Public Health, *Animal Pathology, *Tuna, Human Diseases,
Investigations, Reviews

*Meurological Disturbances, Cats, Fish Contamination
                                          688

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 025J

 THE ROLE OF DISINFECTION IN THE OPTIMUM ENVIRONMENT,

 Ingols, R. S.

 Georgia Institute of Technology.

 The Journal of the Society for Water Treatment and Examinations, Vol. 22,
 No. 3, p 147-152, 1973.  10 ref.

 A philosophical discussion on the definition of an optimum environment and the
 role of disinfection in achieving it is presented.  Part of the dilemma
 facing today's control agencies lie in the fact that the answer to yesterday's
 major problem is today's enigma.  The best example of confusion in the aquatic
 environment is the required maintenance of high free chlorine residuals
 to kill all bacteria and viruses instantly in public and semipublic swimming
 pools.  Yet, chlorine was added to industrial wastes and failed to reduce
 the bacterial count of collform organisms.  In a report of studies upon
 the bacterial numbers found in the swimming beaches of several small lakes,
 it was found the people who swam there had fewer infections than those
 people who swam in chlorinated pools.  The public health philosophy stresses
 a high free chlorine content, while the ecologists feel that a clear water
 is not more likely to induce disease transmission than personal contact in any
 other environment.

 *Disinfection, *Water Purification, *Swimming pools, Chlorine, Chlorination,
 Industrial Wastes,  Public Health,  Ecology, Environment
026J

WATER RESOURCES:   KEY TO WESTERN FUTURE,

Civil Engineering-ASCE,  Vol. 44, No. 3, p 84-91, March, 1974.   5 fig.

Highlights of papers from the ASCE's 1974 National Meeting on Water Resources
Engineering are presented.   In the area of water reclamation,  papers were
presented on water conservation in Los Angeles; deep well injection of highly
treated municipal sewage in Chicago; cloud seeding in South Dakota; and
cloud seeding and citizen's participation.  Papers on water related con-
struction including the tightening of tunnel regulations; excavation in the
dry in California; dredge spoil and ecology; repair of a quake damaged
underground reservoir in the San Fernando Valley; the first U. S. bulb
turbine; and gravel mining in the Mississippi River.  Professional and
planning papers included those in political contributions, a pension bill
in Congress, and salary guidelines.  Papers on sanitary engineering dis-
cussed the problem in Los Angeles of source control of industrial pollutants;
leachate from landfills; methods of treating sewage sludge; a P-C tertiary
plant in Cleveland; the disposal of waste water into a saline aquifier;
and land and pond treatment around Lake Michigan.  Other topics included the
ecological impact of thermal discharge; surge storage tanks; land use planning
and poor political ecological decisions.

*Water Resources, *Water Reuse, *Water Conservation, *Municipal Wastes,
*Cloud Seeding, *Tunnels, Excavation, Dredging, Reservoirs, Bulb Turbines,
Gravels, Mining,  Salaries,  Sanitary Engineering, Industrial Wastes, Water
Pollution Sources, Pollution Control, Leachate, Landfills, Sludge Treatment,
Tertiary Treatment, Aquifers, Saline Water, Surge Tanks, Land Use, Ecology,
Legislation, Political Decisions

Water Resources Engineering National Meeting
                                         689

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027J

ENVIRONMENTAL RESEARCH AND HIGHWAYS,

Solomon, D.

Public Roads A Journal of Highway Research and Development, Vol. 37, No.  8,
p 297-305, March, 1974.  6 fig.

Environmental research completed, underway, or planned under the Federally
Coordinated Program of Research and Development in Highway Transportation
is described.  Three major research areas are involved in efforts  to reduce
significant water pollution from highway sources.  One is to provide re-
quirements for the quantity of water to be treated and criteria for treatment
of wastes at roadside rest areas.  Physical, chemical, and biological tests
of the water and sewage will determine water quality and effectiveness of
the sewage treatment process.  A second area of research involves  determina-
tion of the type and amount of pollutants, their impact on the environment,
and methods for controlling pollutants contributed by the high system.
Included are such pollutants as rubber, lead, grease, and oil which collect
on the pavement surface and wash into drainage facilities.  A third task has
as its objective the reduction of damage to water resources through acci-
dental spills of chemicals and other materials.  Research on air quality,
noise, esthetics and visual quality, and ecological problems is also
discussed.

*Environmental Effects, *Research and Development, *Highway Effects,
Water Pollution Sources, Water Quality, Sewage Treatment, Waste Treatment,
Pollution Abatement, Air Pollution Ecology

Noise, Esthetics
028J

CLEANUP DOWN BY THE OLD MILL STREAM,

Environmental Science and Technology, Vol. 8, No. 4, p 314-315, April, 1974.

Critical comments from industrial representatives on the Federal Water
Pollution Control Act Amendments of 1972 are presented.  The guidelines are
considered too exact and inflexible to accommodate new pertinent information that
may result from research and development.  Technical people from indus-
try have no opportunities to comment on the proposed guidelines until the
final stages of development.  There does not always appear to be ground
rules for implementation of effluent guidelines.  Little consideration is given
to differences between individual companies or sites.  The 30-day period for
industry and public response is not sufficient for proper technical reviews
and constructive industry input.  A better two way communication between
industry and government is called for so that industry can elicit uniform
definitions, consistently explained regulations, and agreed upon ranges of
numbers, and arrive at intelligent decisions and effect cost/benefit analyses.

*Federal Water Pollution Control Act, *Industrial Plants, legislation,
Administration, Political Aspects, Administrative Decisions, Evaluation

Amendments
                                           690

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029J

A KNOWLEDGE CRISIS  IN  SOLID-FLUID  SEPARATION?,

Chemical Engineering,  Vol.  81, No.  7, p  26,  28, April  1,  1974.   2  fig,
1 tab.

Some  opinions  of world experts in  solid  fluid  separation  on ways to  close  the
solid-fluid-technology knowledge gap  are presented.  There is wider  support
for education  and  research  in England, Japan,  and  Germany than  in  the  United
States because of  greater population  density which overloaded  the  capacity
of  the rivers  and  forced the  technology.   Other countries also  have  closer
ties  between educators and  industry.  Industry in  the  United States  gives
little research opportunities to universities.  Most industrial research is
done  from within the  company.  The industrial  application of solid fluid
separation, including  pollution control, which most needs improvement
includes:  hydrometallurgy, activated sludge separation,  metal-hydroxide
removal, alum  sludge  dewatering, sulfur  dioxide removal systems, pigment
and dyestuff processing, clarification of  liquids  in the  food  and beverage
area, sewage sludge dewatering, radioactive  material concentration,  shale
oil separation, tar sands separation, and  removal  of ash  from  liquefied
coal.

*Separation Techniques, *Research  and Development

Solid-fluid Separation
030J

SMALL BALLS REPEAL SMELL,

Baum, H. E.

Capricorn Industrial Services, Ltd.,
London, England.

Water and Wastes Engineering, Vol. 11, No. 3, p 41-42, March, 1974.  2 fig.

Tests at a British sewage plant show that smell can be virtually eliminated
by covering liquid sewage with a ball blanket, the name given to a closely
packed layer of hollow plastics balls floating on the surface of a liquid.
Special polypropylene balls are used.  A complete layer of balls arranged
in staggered rows always covers 91% of the surface.  The remaining 9% consists
of small air pockets between the balls which can inhibit fume emission from
the surface in a liquid.  Balls of 45 mm diameter were used to cover two
16 sq ft open sludge tanks.  Immediately after the whole surface was
covered, the smell of the sludge became undetectable.  From additional
laboratory tests it appears that the ball blanket encourages the water
separation process.  Other possible uses of balls for sewage treatment are
being considered including their effect on agitated liquids and in reducing
the amount of foaming in the tank.

*Sewage treatment, Activated Sludge, *Liquid Wastes, Waste Water Treatment,
*0dor, Pollution Abatement, Air Pollution

Great Britain, Ball Blanket
                                         691

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 031J

 THE SURPRISE FACTOR IN MARINE POLLUTION STUDIES,

 Goldberg, E. D.

 Marine Technology Society Journal, Vol. 8, No.  2, p 29-34, February, 1974.
 40 ref.

 The ways in which pollution studies have contributed to a deeper understanding
 of biochemistries and of geochemistries occurring within the ocean system
 are described.  Out of a concern to understand  man's impact upon his environ-
 ment, knowledge about the following subjects bearing on marine processes
 have advanced:  the atmospheric transport of large organic molecules from
 the continuents to the oceans,  the role of methyl groups in the mobiliza-
 tion of metals and non-metals in biologic systems, the oceans as a source
 of low molecular weight gases to the atmosphere,  bioaccumulation trace
 substances by marine organisms, and the biodegradability of organic matter.

 *0ceans, Water Pollution Effects,  Marine Biology, Environmental Effects,
 Biochemistry, Geochemistry
032J

STUDIES OF RENOVATION OF PULP MILL WASTEWATER PILOT PLANT
TESTS FOR GRANULAR ACTIVATED CARBON ADSORPTION OF KRAFT
PULP MILL WASTEWATER,

Kabeya, H., Fujii, T., and Kimura, Y.

Government Industrial Research Institute, Sikoku, Japan

Japanese Technical Association Industry Journal, Vol. 27, No. 11, p 543-553,
November, 1973.  10 fig, 7 tab, 7 ref.

Pilot plant tests for adsorption on granular activated carbon were conducted
with lime treated water of unbleached kraft pulp wash waste water (lignin con-
centration 12-26 ppm, COD 25-44 ppm) and pretreated water of bleached kraft
pulp caustic soda extract waste water (lignin concentration 33-120 ppm), treated
by activated sludge and followed by lime.  The: possibility of renovation of
these treated waters was investigated.  At a superficial velocity of 1.7 m/hr
and contact time of 140 min, the carbon usages of lime treated water were 3530
liter/kg air-dried carbon on the basis of lignin breakthrough curve and 3090
liter/kg air-dried carbon on the basis of COD breakthrough curve.  The adsorp-
tion of lignin on activated carbon by lime treatment increases, but the ad-
sorption of COD hardly increases.  These results are consistent with the re-
sults obtained from adsorption isotherms of lime treated water and dilute water.
Similarly, the carbon usage of pretreated water of caustic soda extract waste-
water was 130 liters/kg air-dried carbon on the basis of lignin breakthrough
curve.

*Pulp wastes, investigations, *Adsorption, Activated carbon, Lignins, Chemical
oxygen demand, Activated sludge, Lime, Waste water

Japan
                                     692

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 033J

 TREATMENT  OF BEET  FACTORY-WASTE  WATER BY  ACTIVATED  SLUDGE
 PROCESS  (BIOSORPTION  PROCESS),

 Nogai, M.

 Hokkaido Sugar Co., Ltd., Japan.

 Proceedings  of the Research Society of Japan  Sugar  Refineries's  Technologists,
 Vol.  24, No. 24, p 25-35, August,  1973.   3 fig,  5 tab,  7  ref.

 The purification of the waste water of the Hongetsu beet  sugar factory by an
 activated  sludge process is described. The process was effectively  operated
 for four years, even  in outdoor  temperatures  of  -28 C.  The design standards
 of the installation are described.   The recycle  ratio of  sludge  was  more  than
 70%.  Since  the capacity of the  clarifier was insufficient, it was necessary
 to increase  the up flow rate in  the clarifier over  the  design  rate.   The  dis-
 solved oxygen in the  sludge aeration tanks was 0.4-0.6  ppm. The expected minimum
 elimination  of BODS was attained at 13 C.  The pH level of waste water should
 be kept  at 6-9.  The  elimination ratio BODS obtained was  60-70%  of the expec-
 ted ratio.  The excess sludge  in running  and  final  sludge  were collected  in a
 final pond,  and they  were decomposed by digestion in summer.   When there  was a
 fluctuation  of pH  value and a  drop  in waste water temperature, the activated
 sludge underwent bulking.  The bulking stopped with the addition of  phosphoric
 acid  and it  is concluded that  soil  adhering to beets and  the beets themselves
 contain  some nutrients that effectively activate the sludge.

 *Waste water, *Water  purification,  *Recycling, *Activated  sludge, Biochemical
 oxygen demand, Sugar  beets, Industrial wastes, Design standards, Operation and
 maintenance, Hydrogen ion concentration,  Temperature

 *Japan,  Bulking, Phosphoric acid
034J

OXYGEN UTILIZATION IN BACTERIAL-PROTOZOAN COMMUNITY,

Canale, R.P., and Cheng, F.Y.

Michigan University
Ann Arbor, Michigan
Department of Civil Engineering

Journal of the Environmental Engineering Division, Vol. 100, No. EE1, p 171-185,
February, 1974.  10 fig, 1 tab, 14 ref.

The dynamic relation between oxygen utilization, nutrient consumption, and
bacterium and protozoan growth in bath cultures was investigated with A. aero-
genes and T. pyriforms.  The results were interpreted with a mathematical model
which incorporated the interactions of the bacterium and the protozoan as well
as the effects of nutrient availability and oxygen utilization.  The model has
several unique aspects:  nutrient recycling and refractory carbohydrate accumu-
lation, protozoan bioenergetics, and protozoan cell size variability.  The
experimental and modeling results confirm1the findings of Bhatla and Gaudy that
the plateau observed in BOD tests is a slow bacterial respiration phase.  It
was shown that the second stage oxygen demand in heterotrophic bacterial pro-
tozoan communities is the result of protozoan metabolism.  These findings
should be useful for defining organic matter stabilization pathways in
multicomponent ecological models and for water quality management.

*Biochemical oxygen demand, Investigations, Recycling, Organic matter,
Water quality, Protozoa, Nutrients, Cycling nutrients, Bacteria, *Mathematical
studies, *Model studies, Metabolism

A. aerogenes, T. pyriforms
                                       693

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 035J

 AVAILABLE PHOSPHORUS LEVEL VARIATIONS OCCURRING DURING THE
 RECLAMATION OF AN ALKALINE-SALTY SOIL (VARIACIONES DEL
 TENOR DE FOSFORO ASIMILABLE DURANTE LA RECUPERACION DE UN
 SUELO SALINO-ALCALINO),

 Lavado, R. S.

 Tecnico en Fertilidad de Suelos, Provincia de Rio Negro,
 Spain

 Anales de la Sociedad Cientifica Arcentina, Vol. 5, No. 195, 2nd Series Applied
 Science, No. 33, p 135-141, March-June,  1973.  4 fig, 2 tab, 11 ref.

 The evolution of available phosphorus in a salty-alkaline soil of the Lower
 Valley of the Rio Negro was investigated.  In general, flooding causes an in-
 crease of the available phosphorus in the soil.  Calcium sulfate also seems to
 increase the availability of phosphorus.  Soil was flooded several times with
 big sheets of water after applying gypsum.  The results show that, statistically,
 there were no significant variations in the amount of available phosphorus.

 *Phosphorus, *Soils, Saline soils, Alkaline soils, Calcium sulfate, *Flooding,
 Gypsum

 *Spain, Rio Negro
036J

PHOSPHORUS AND CARBON IN LAKE POLLUTION,

Kuentzel, L. E.

BASF Wyandotte Corp., Wyandotte, Michigan

Environmental Letters, Vol. 2, No. 2, p 101-120, 1971.  41 ref.

Recent laboratory and field tests and literature on the relationship between
algae, phosphorus, and carbon in lake pollution are summarized.  Algae can
develop in waters containing only 10 ppb or less of phosphorus.  Most natural
waters have 10 ppb or more.  Phosphorus is widespread in nature and widely
used by man.  Indications are that it will not be possible to reduce phosphorus
to less than 10 ppb in urbanized areas by eliminating it from only detergents.
It takes two pounds of carbon dioxide to grow one pound of algae.  The amounts
of carbon dioxide available from the atmosphere and the natural alkalinity of
lake water are severely limited by physical and chemical laws.  Algae growth
depending solely on alkalinity and the 'atmosphere for carbon is relatively slow
and limited by a rising pH at about 10.  When adequate organic pollution is
present, bacteria can undergo a massive population explosion, produce large
amounts of carbon dioxide, and cause massive algae growths.  The role of the
organic matter becomes more evident in those cases where algae growth is massive
in the presence of such pollution even though the phosphorus content of the
water never exceeds 10 ppb.  It appears that algae growth will be controlled
only when organic pollution is controlled, regardless of the phosphorus content.

*Algae, *Phosphorus, *Carbon, Carbon dioxide, *Lakes, Alkalinity, Algae control,
Growth rates, Organic matter, Organic wastes, *Water pollution
                                       694

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   037J

 SANITARY IMPLICATIONS OF SMALL BOAT POLLUTION,

 Cassin, J., Smith, K., and Frenke, K.

 Adelphi University, Garden City,  N. Y., Institute of
 Marine Science

 Environmental Letters, Vol. 2, No. 2, p 59-63, 1971.  2 tab,  2 ref.

 The implications of a New York navigational law forbiding sewage discharge by
 small pleasure craft into the water was investigated.   The study indicates that
 coliforms increase in water column and shellfish in direct relation to small
 boat population in three of four recreational areas sampled.

 *Coliforms, *Navigation, ^Legislation, *Shellfish, Recreation, Recreation
 wastes, Boats, Boating regulations, Waste disposal, Pollution

 New York
038J

CRITIQUE OF WATER POLUTION (sic) CONTROL  ACT,

Dorcey, A. H. J., and Fox, I. K.

British Columbia University, Vancouver, Canada

Journal of the Environmental Engineering Division, Vol. 100, No. EE1, p 141-
151, February, 1974.  1 tab, 3 ref.

The approach adopted in the Federal Water Pollution Control Act Amendments of
1972 is discussed.  Specifically examined are the procedures envisioned to apply
nationwide whereby:  effluent and ambient standards are to be established and
enforced; basin, state, and regional plans are to be developed; and water
quality management facilities are to be financed.  It is concluded that Congress
may not be the best representative body to make some of the judgments that were
made in the legislation; the enormous bureaucracy required by the legislation
to achieve national objectives and to plan and implement water quality management
programs is not necessary; and the effectiveness of the grant program is
questionable.

*Federal Water Pollution Control Act, Standards, *Planning, Future planning
(projected), Water quality, Water quality standards, Water management (Applied)

*Canada
                                        695

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039J
UNIVERSITY CREDITS FEEDWATER TREATMENT PROGRAM FOR 50% CUT
IN BOILER CLEANING WORK LOAD,

National Engineer, Vol. 78, No. 2, p 12-13, February, 1974, 5 fig.

The treatment program for boiler feedwater and condensate return lines at
State University of New York at Buffalo is described.  It is proving effective
by keeping three boilers and more than two miles of return lines free of scale
and corrosion.  The program consists of alkalinity adjustment, phosphate soften-
ing, sludge control, iron sequestration, foam control, and return line corrosion
control.  It is estimated there is a 50 percent cut in boiler cleaning work
load.

*Boilers, *Cleaning, Corrosion control, Costs, Scaling,  Alkalinity,  Phosphates,
Sludge, Control

Buffalo, N.Y.
 040J

 ORGANIC MANAGEMENT  REDUCES  LEACHING  OF NITRATE,

 Koepf, H.  H.

 Bio-Dynamics, No.  108,  p  20-30,  Fall,  1973.   4  tab.

 The reduction of nitrate  leaching  by the  application  of  organic manuring fluids
 was investigated and  compared with adjacent  areas  under  orthodox commercial
 farming.   The nitrate concentration  in the  tile  drainage runoff was  determined
 in four  fields  in  Buffalo,  111., from 1969-1973.   The average  monthly nitrate
 concentration is tabulated  when  there was a  runoff from  the  tiles.   It is con-
 cluded that  fertilizing with  commercial nitrogen interferes  with the changes
 which the  nitrogen continuously  undergoes in the soil.   The  drainage outlets
 in the soils under investigation are rather  close  to  the surface.  Although in
 these silt loams it might take several months before  water from the  surface
 arrives  at the  depth  of these tiles, it was  shown by  the tests that  the biolo-
 gical soil processes  are  a  crucial factor which  determines nitrate leaching.
 The cycles of mobilization-immobilization,  nitrate supply for  the crops, etc.,
 seem  to  be different  in soils under  organic  management from  those which are
 treated  chemically.

 *Nitrates, *Farm wastes,  Investigations,  Fertilizers, *Soils,  Drainage, teach-
 ing,  Silts,  Loam,  Runoff

 Organic  management
                                     696

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 041J

 THE USE OF THE  DILUTION WATER EFFECT AS A WATER QUALITY
 CRITERION,

 Cox,  J. L.

 Southeastern Massachusetts University,  Dept.  of
 Biology, North  Dartmouth,  Massachusetts

 Bulletin of Environmental Contamination & Toxicology,  Vol.  11,  No.  3,
 p 256-257, March,  1974.  1 fig,  2 ref.

 A principle difficulty in the toxicology of marine organisms has been  ob-
 taining dilution water that is free from substances which may affect the
 response of a test organism to a toxin.  The possibility of synergism between
 unknown chemical constituents in the dilution water and controlled additions
 of a  toxin suggests an entirely different approach to  assessing water  quality.
 The dose-response relationship for a particular toxin  or pollutant  is  com-
 pared using relatively clean water as a control dilution water  source  and
 water suspected to being polluted as the test dilution water source.  A
 description of  experimental procedures  is detailed.

 *Toxins, Aquatic life, *Water quality,  *Analytical techniques,  Water sources

 *Dilution water
042J

SOME USEFUL IDEAS ON WASTE WATER REDUCTION,

Haralson, R. H.

Western Electric Co., New York, N.Y.

Plating, Vol. 61, No. 4, p 310-313, April, 1974.  5 fig.

The reduction of waste must be made a major design criteria in any process
planning with a minimum of dilution and expense being the primary premises
governing the design.  Exemplified herein is a zinc plating process which con-
sists of cleaning thd surface to be plated, depositing the zinc on the sur-
face, and passivating the surface to increase corrosion resistance.  These
steps of cleaning, rinsing, and fog spraying are discussed.

*Design criteria, *Waste treatment, *Waste water treatment, Cleaning

Rinsing, Fog spraying
                                        697

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04 3 J

PROBLEMS ARISING FROM OVER EXPLOITATION OF THE NATURAL WATER
RESERVOIR IN THE URBAN DISTRICT OF MILAN  (I PROBLEM! POSTI
DAL SOVRASFRUTTAMENTO IDRICO DEL SERBATIO NATURALE NELLA
CONURBAZIONE MILANESE) ,

Mazzarella, S.

Inquinamento, Vol. 15, No. 6, p 25-34, August, 1973.  11 ref.

Problems arising from the overexploitation of the natural groundwater
resources in the urban and industrial districts of Milan are described, and
solutions to this problem are proposed.  The ever increasing industrial acti-
vity, and especially the concentration of large water consuming industries in
a limited area in and around Milan has resulted in a steady, considerable
lowering of the water table.  The phreatic layer has lowered, in one district
of Milan, from about 6 m in 1934 to 41 m  in 1971.  The industries settled
in the Milan area draw from available water supplies in an uncontrolled manner.
The volume of the water drawn for municipal use has not increased at the
same rate as the population.  It is recommended that the major industries,
chiefly responsible for the lowering of the groundwater table in the Milan
area, should be required to adopt adequate techniques for water recycling
to reduce their water consumption, and to use surface wells for water  capture.
They may be allowed to use water from deep layers of transitional and  marine
sediments in a controlled manner.  It is  further recommended that industries
with high potential water consumption should no longer be allowed to settle
in the Milan area.

*Groundwater, *Water resources, *Water table, Cities, Reservoirs

Milan, Italy
044J

SWEDISH TECHNIQUES TO COMBAT POLLUTION,

Isgard, E., and Ehrlen, L.

VBB Consulting Engineers and Architects,
Water and Sewage Department.  Director, Stockholm,
Sweden

Effluent and Water Treatment Journal, Vol. 14, No. 2, p 97-101, February,
1974.  4 ref.

The demand on sewage treatment has increased in the last years in Sweden
due to the increased population and the problems of waste disposal and
subsequent water pollution.  To facilitate the fulfillment of requirements
set by the authorities as a result of the new environmental protection regula-
tions, the national government grants contributions to certain municipal
treatment plants.  As of July 1973, 94 percent of the people living in urban
areas were connected to sewage treatment plants, those facilities using
either biological treatment or both biological and chemical treatment
(estimated at more than 50 percent by 1975).  Different mechanical, bio-
logical, and chemical treatment methods used in Sweden, their operational
results, sludge treatment processes,  operating costs of facilities, and
various filtration and reuse procedures are discussed.

*Sewage treatment, *Treatment facilities, Water pollution control, Methodology,
Regulations, Environmental control, Sludge treatment, Filtration, Operations,
Operating costs, Water reuse, *Waste water treatment

*Sweden
                                    698

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045J

VIRUS REMOVAL  IN WASTE  STABILIZATION PONDS,

Chaudhuri, M.

Indian  Institute of Technology, Department  of
Civil Engineering, Kanpur-16, Uttar Pardesh,
India

Indian  Journal of Environmental Health, Vol.  16, No.  3,  p  171-177,  July,
1973.   1  tab,  32 ref.

A  review  of  the published  data indicates  that waste stabilization ponds  are
effective in reducing the  virus levels of raw waste water  and  treated
effluents.   Presence of algae and bacteria,  chemical  and organic contents
of the  pond  water, detention time and temperature, and sunlight may
play significant roles  in  the removal or  inactivation of viruses.   It  is
maintained that a shallow  pond with a longer detention time may be  more
effective in reducing virus concentrations.

*Reviews, *Data collections, *0xidation lagoons, *Treatment facilities,
*Waste  treatment, *Waste water treatment, *Viruses

*Virus  removal
046J

RECIPIENT CAPACITY TO LIMIT DISCHARGE OF POLLUTANTS
TO RECEIVING WATERS,

Kamath, P. R.

Health Physics Division,
BARC, Bombay-85, India

Indian Journal of Environmental Health, Vol. 15, No. 3, p 200-207,
July, 1973.  2 fig, 2 tab.

Two field studies indicative of techniques which can be suitably adopted to
determine the assimilative maximum of pollutants into an aquatic environment
are presented.  Evaluation of recipient capacity of receiving waters is
very important as a mode of surveillance to indicate if any unacceptable
deterioration in water quality has occurred.  A need for development programs
to look into wastes generation aspects as a part of the total design is
stressed.

*On-Site investigations, *Evaluation, *Monitoring, Aquatic environment,
*Water quality control, *Waste assimilative capacity, Discharge measurement
                                  699

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04 7 J

BITUMINOUS COAL - A SUBSTITUTE FOR ANTHRACITE FILTER MEDIA
IN TWO-LAYER FILTRATION OF WATER,

Paramasivam, R., Gadkari, S. K., Joshi, N. S., and Deshpande, A. W.

CPHERI, Nagpur-20, India

Indian Journal of Environmental Health, Vol. 16, No. 3, p 178-188, July,
1973.  4 fig. 1 tab, 9 ref.

High rate filtration using two-layer and mixed madia filters is finding in-
creasing application in both overloaded conventional filters and new filter
plants.  Work done on the suitability of indigenous bituminous coal as a
substitute material for anthracite filter media, which is not available in
India, is described.  Mention is made of the laboratory and pilot studies which
show that rates up to 50-100 percent higher than, conventional filters can
be achieved by adoption of two-layer filters using bituminous coal.
*Filtration, *Application methods, *Water treatment, *Bituminous Materials,
Filters, Pilot plants, Laboratory tests, *Waste water treatment

India
048J

APPLICATIONS OF WASTE PROCESSING SYSTEMS FOR PRESSURIZED
WATER REACTORS,

Garber  I., and Kearton, W.

Westinghouse Electric Corporation,
Pittsburgh, Pennsylvania

IEEE Transactions on Power Apparatus and Systems, Vol. PAS-93, No. 1, p 149-
157, January-February, 1974.  6 fig, 6 tab, 11 ref.

An introduction ia the application of Waste Processing Systems in the
Westinghouse Pressurized Water Reactor plant is provided.  These systems employ
the techniques of waste product concentration, long term storage, recycling,
and radiation monitoring in order to implement the basic philosophy governing
radioactive releases established by national and international guidelines.

*Waste treatment, *Application methods, *Radioactive wastes, Recycling,
Storage, Monitoring, Radioactive waste disposal, *Waste water treatment

*Reactors
                                    700

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 049J

 CADMIUM UPTAKE AND TIME DEPENDENT ALTERATIONS IN TISSUE LEVELS
 IN THE WHITE CATFISH ICTALURUS CATUS (PISCES:  ICTALURIDAE),

 Rowe,  D.  W., and Massaro,  E.  J.

 New York State University  at  Buffalo,
 Department of Biochemistry,  Buffalo, N.Y.

 Bulletin of Environmental  Contamination &  Toxicology,  Vol.  11, No. 3, p 244-
 249, March, 1974. March, 1974.  1 tab,  18  ref.

 Anatomical differences, compared to centrarchid and salmonid  fishes, coupled
 with the commercial and sport-fishing importance of catfish prompted this
 investigation of the time  dependent distribution of cadmium in white catfish.
 Results indicate that fish were found to regurgitate from 39  to 56 percent
 of the dose solution within  the first hour.   After one hour,  75.1 percent of
 the Cd body load was contained within the  gastrointestinal  tract with
 maximum relative concentrations being attained by the  stomach, esophagus,
 and skin within one hour.  The intestinal  portions attained maximum
 levels at widely divergent times.  Outside the GI tract, the  liver and
 kidney contained the highest  percentages of  the body load at  21 days (ter-
 mination of experiment); these organs may  not have reached  their relative
 maximum concentrations at  this time.

 *Cadmium, *Catfishes, *Laboratory tests, Fish physiology, Water pollution
 effects,  Toxicity

 Time dependent distribution
050J

RESIDUES OF MIREX AND OTHER CHLORINATED PESTICIDES IN
COMMERCIALLY RAISED CATFISH,

Hawthorne, J. C., Ford, J. H., and Markin, G. P.

Gulfport, Mississippi

Bulletin of Environmental Contamination & Toxicology, Vol. 11, No. 3,
p 258-264, March, 1974.  1 fig, 3 tab, 5 ref.

Commercially raised catfish from parts of Mississippi and southern Arkansas
in which the insecticide mirex was used extensively for the control of the
fire ant have been sampled and analyzed.  Results of the analyses show that
mirex was found in none of the 50 samples at the detection level, 0.01 ppm;
however, all samples contained extensive residues of other pesticides.  The
lack of detectable mirex residues indicates that there is no widespread con-
tamination of the catfish and that mirex is probably one of the least of the
chlorinated pesticides to reach humans by consumption of catfish.

*Catfishes, *Mississippi, *Arkansas, *Insecticides, Food chains, Fish physiology

*Mirex
                                       701

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 051J

 THE ACCUMULATION  OF  ORGANIC AND  INORGANIC MERCURY COMPOUNDS BY
 THE EASTERN OYSTER  (CRASSOSTREA  VIRGINICA) ,

 Kopfler, F. C.

 U. S. Environmental  Protection Agency,
 Office of Research and Monitoring,
 Gulf Coast Water  Supply Research Laboratory,
 Dauphin Island, Alabama

 Bulletin of Environmental Contamination & Toxicology, Vol. 11, No. 3,
 p 275-280, March, 1974.  1 fig,  3 tab, 10 ref.

 The presence of mercury contamination in some coastal waters of the United
 States prompted an investigation into the extent of concentration of various
 mercury compounds by shellfish in those coastal waters.  This study was
 designed to investigate the differences in mercury uptake when oysters were
 exposed to specific  environmental levels of inorganic, phenyl- and methyl-
 mercury compounds.   Experimental results indicate that oysters, following
 continuous exposure  to even one  microgram/liter mercury in any of the three
 compounds studied,   rapidly concentrated mercury in their tissues far in
 excess of the 0.5 ppm guideline  established by the Food and Drug Administration.
*Mercury, Oysters, laboratory tests, United States, Coasts, Pollutants,
Fish Physiology

*Mercury uptake
052J

THE LONG-TERM STRATEGY FOR WATER RESOURCES IN THE UK,

Water Services, Vol. 78, No. 936, p 41-43, February, 1974.  1 fig.

A report by the Water Resources Board of England examines the water resources
of England and Wales as a whole and makes recommendations to meet the ex-
pected increase in the demand for water up through thy year 2000.  Findings
indicate that no more than five new strategic reservoirs need by built.  Also,
the report considers a wide range of possible strategies for the Dee Estuary
area where the need for water cannot be met from local sources; a strategy based
on a mixture of inland and estuary storage making use of rivers to carry water
is recommended.  The report is summarized in outline form with project and
research recommendations listed.

*Publications, *Water resources, *Long-Term planning, Project planning, Water
resources development

*Great Britain
                                      702

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053J

FACTORS AFFECTING THE PERSISTENCE OF PESTICIDES  IN THE
SOIL,

Edwards,  C. A.

Rothamsted Experimental  Station, Harpenden,
Hertfordshire, England

Chemistry and  Industry,  No.  5,  p 190-193, March  2, 1974.   1  fig,   48  ref.

The factors  that  influence  the  persistence  of  organochlorine insecticides  in
soil  can  be  separated  into  chemical,  soil,  environmental,  and human  factors.
Under chemical characteristics  the  most  important  factor  is  the intrinsic
stability of the  chemical with  the  solubility  of the pesticide being  of
considerable influence.   Soil type  and particle  size as well as the  amount
of organic matter in a soil greatly affect  how long  the  insecticide will remain.
The most  important  environmental  factors include temperature, rainfall, and
soil  moisture.   Factors  such as cultivation, weathering  of the soil  surface,
and plant selection can  influence  the persistence of insecticides relative
to the management of the soil.

*Insectlcides, *Soil contamination, Soil chemical properties, *Soil  management,
*Soil environment,  Temperature, Rainfall, Soil moisture,  Soil physical
properties,  Soil types
054J

HEAVY METAL CONCENTRATIONS IN MUSEUM FISH SPECIMENS:  EFFECTS
OF PRESERVATIVES AND TIME,

Gibs, R. H., Jr., Jarosewich, E., and Windom, H. L.

Smithsonian Institution, Department of
Vertebrate Zoology,
Washington, D.C.

Science, Vol. 184, No. 4135, p 475-477, April 26, 1974.  2 fig, 5 ref.

Higher concentrations of cadmium, copper, zinc, and sometimes lead, and
lower concentrations of mercury and sometimes lead were found in specimens
of myctophid fish preserved for one month in formalin, ethyl alcohol, and
isopropyl alcohol as compared with unpreserved frozen specimens.  Properties
of the preservatives and species differences in fish tissues both influence
these metal concentrations.  It is believed that until the changes resulting
from preservation are understood, comparisons of concentrations of metals
between museum specimens and unpreserved or frozen specimens must be considered
unreliable.

Cadmium, Copper, Zinc, Mercury,  Lead, Fish physiology, Time

*Metals Concentration, *Preservatives effects
                                       703

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05 5 J

ASPECTS OF WATER POLLUTION IN FERTILISER INDUSTRY,

Mohanrao, G. J., and Subrahmanyam,  P.  V. R.

CPHERI, Nagpur-20, India

Indian Journal of Environmental Health, Vol.  15, No.  4, p 271-282, October,
1973.  1 fig, 5 tab, 13 ref.

There has been a continuous growth in the fertilizer industry in India in
recent years to meet the ever increasing demand.  The processes of manfacturing
different types of nitrogenous and phosphatic fertilizers are des-
cribed briefly.  The volume and characteristics of the waste water discharged
from the industry are indicated.  Said waste  waters contain a variety of
pollutants, such as toxic, unaesthetic, and nuisance causing which include
ammonia, fluorides, arsenic,  phosphate, and urea.  Water pollution potential
of different units in the fertilizer industry is discussed.  The need for
better process control for reduction of water pollution is stressed.

*Fertilizers, *Water pollution sources, Industries, Toxicity, Industrial
water, Waste water (pollution), Water pollution control, Ammonia, Fluorides,
Phosphates, Nitrogen compounds, Arsenic compounds

India
 056J

 SOURCES CHARACTERISTICS OF LIQUID AND GASEOUS EFFLUENTS FROM
 FERTILIZER PLANT,

 Mitra, S. K.

 The Fertilizer Corporation of India Ltd.,
 Trombay Unit, India

 Indian Journal of Environmental Health, Vol. 15, No. 4, p 322-328, October
 1973.  1 tab.

 Environmental pollution caused by the fertilizer industry is discussed with
 regards to gaseous emissions, liquid effluents, and solid wastes.  The sources,
 effects, and possible control measures for pollutants under these categories
 are indicated.

 *Fertilizers, industrial wastes, Industrial plants, Solid wastes, Liquid wastes,
 Water pollution sources, Water pollution effects, Water pollution Control,
 Environmental effects, Dusts, Organic compounds, Oxides, Sulfides, Fluorides,
 Color, Temperature, Odor, Turbidity, Hydrogen ion concentration, Ammonia,
 Arsenic compounds, Phosphorus, Nitrates, Nitrites, Sulfates, Oil, Biochemical
 oxygen demand
                                     704

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057J

STANDARDS FOR EFFLUENTS FROM FERTILIZER INDUSTRY,

Saxena, G. M.

Indian Standards Institution, New Delhi-1, India

Indian Journal of Environmental Health, Vol.  15, No. 4, p 305-321, October,
1973.  7 tab, 7 ref.

The Indian Standards prescribed for the fertilizer effluents for disposal
into inland surface waters onto land for irrigation, and into public sewers
are discussed.  A summary of select fertilizer industries with reference to
characteristics of their effluents and treatment procedures adopted by
them also is presented.

*Fertilizers, *Standards, Effluents, Waste disposal, Industrial wastes,
Surface waters, Sewers, Irrigation, Waste treatment, Ureas, Sulfates,
Phosphates

India
058J

INTERACTION BETWEEN FISHERY MANAGEMENT AND ENVIRONMENTAL
PROTECTION,

Dickie, L. M.

Fisheries Research Board of Canada,
Marine Ecology Laboratory, Bedford Institute of
Oceanography, Dartmouth, Nova Scotia, Canada

Journal of the Fisheries Research Board of Canada, Vol. 30, No. 12, p 2496-
2506, December, 1973.  33 ref.

Assessment of the need to take account of fishery and environmental parameters
in management depends on the precision with which it is possible to predict
fishery yields from fishery and environmental data.  Earlier attempts to
demonstrate simple correlations of yield with various fishing and environmental
indices were frustrated by variability in statistical data, poor definition
of oceanographic and population systems, and ignorance of the responsible
mechanisms.  Recent research results support hypotheses that environmental
fluctuations are major factors controlling year-class success.  There is also
evidence for strong density-dependence of survival of larval fishes, and of
growth in juveniles and adults; however, in some populations effects of the
recent and highest sustained rates of fishing have exceeded the "adaptative"
capacity of the production—compensating mechanisms so that the carrying capa-
city of the environment is now unsaturated.  The main mechanism controlling
fishery productivity fluctuations within areas appears to be the degree of
vertical mixing in oceanographic systems, with the associated nitrogen supplies
and food resources for the early life-history stages of fishes.  There still
exist major unexplained differences between areas in the structure of the
producing communities and the yields from them.  Assessment of the risk of
pollution concentration, and its importance in reducing density-dependent
compensatory production responses, is still frustrated by high-frequency varia-
bility in samples of both biological and physical parameters.  Recent studies
have demonstrated that this variability may be associated with particular types
of generating mechanisms and suggest means of interpreting it.  Recent knowledge
of natural variability, and its interaction with density-dependent mechanisms
controlling production, implies that a new approach involving "discontinuous"
models appears necessary to prediction of ecosystem responses to fishing and
pollution.

*Fish management, *Environmental control, Fisheries, Environmental engineering,
Data collections, Correlation analysis,  Mixing, Aquatic productivity
                                      705

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 059J

 OBJECTIVES AND PROBLEMS OF MANAGING AQUATIC LIVING RESOURCES,

 Alverson, D. L.,  and Paulik,  G.  J.

 Northwest Fisheries Center, National Marine
 Fisheries Service, National Oceanic and Atmospheric
 Administration, Seattle, Washington

 Journal of the Fisheries Research Board of Canada, Vol.  30,  No. 12, p 1936-
 1947, December, 1973.  52 ref.

 In the management of aquatic living resources, conservation  objectives
 are largely concerned with "rational use" concepts, while socioeconomic goals
 may be associated with economic efficiency, resource development, and allo-
 cation of resources between user groups.  A number of problems confront -managers
 of aquatic living resources.  They include the rapidity of the changes occurr-
 ing in fisheries, conflicting objectives, the fragmented and limited juris-
 diction of management agencies, adequacy of scientific input into management
 decisions, difficulties of enforcement, and multiple use interest.  Improved
 management of aquatic living resources will require decision-making machinery
 that is responsive to the dynamic character of modern fisheries, systems to
 resolve potential conflicts in human values, a commitment of governments,
 managers and scientists to assume the responsibilities delegated to
 them, including the promulgation and enforcement of appropriate regulations,
 and a recognition on the part of management that they cannot expect scientific
 unanimity or certainty regarding the status of fish stocks and the nature of
 the actions required to ensure their productivity.

 *Administration, *Aquatic productivity, *Fish management, Economic efficiency,
 Regulation
060J

MARINE AQUACULTURE:  PROBLEMS AND PROSPECTS,

Idyll, C. P.

Department of Fisheries, Food and Agriculture
Organization of the United Nations, Rome, Italy

Journal of the Fisheries Research Board of Canada, Vol. 30, No. 12, p 2178-
2183, December, 1973.

Aquaculture is the technique of raising useful aquatic species under some
control of the organism and its environment.  It is expected to supplement
fishing by adding significantly to supplies of protein food, but it is unlikely
that it will ever replace fishing as the principal means of exploiting the
sea.  Discussions are often confused because there are a number of distinctly
different procedures embraced by the term aquaculture, with different chances
of development into major industries.  Aquaculture has developed with very
little help from scientists, and the solution of technical and engineering
problems would advance its rate of development greatly.  The kinds of problems
that should be solved include:  the search for species suitable for culture;
research on nutrition of cultured animals and development of suitable food;
pathology of cultured animals; studies on the behavior of cultured animals;
engineering studies; studies of pollution and the use of waste substances and
heat; legal research; economic and social research.  It is proposed that a
small number of regional centers for aquaculture be established to study the
most pressing problems.

*Aquiculture, *Foods, Investigations, Animal pathology, Animal behavior,
Research and development, Artificial substrates
                                      706

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061J

55Fe CONCENTRATION AND SPECIFIC ACTIVITIES IN NORTH PACIFIC
MARINE ORGANISMS,

Jenkins, C. E., and Langford, J. C.

Battelle, Pacific Northwest Laboratories,
Richland, Washington

IEEE Transactions on Nuclear Science, Vol. NS-21, No. 1, p 517-521, February,
1974.  8 fig, 16 ref.

Marine organisms have been shown to have up to 1000-fold higher specific
activities of iron-55 than that in seawater; also that iron-55 specific acti-
vities increase 10 to 30-fold in salmon between raid and northern latitudes.
These observations are currently explained on the basis of a different chemical
form for iron-55 in seawater and greater dilution of the iron-55 by stable
iron at mid-latitudes than at the northern latitudes.  The half-time for
iron-55 concentrations in mature harvested salmon at all latitudes is approxi-
mately 10 months, which is comparable to the half-time for movement of strato-
spheric debris to the earth's surface.

*Iron, *Salmon, Marine fish, Sea water, Pacific Ocean, Alaska, Food chains,
Radionuclides, Investigations, Aquatic environment, Environmental effects

Iron-55
062J

MANAGING WATER RESOURCES:  BASIC CONSIDERATIONS AND PROBLEMS,

Medbery, H. C.

San Francisco Water Department,
San Francisco, California

Journal of the American Water Works Association, Vol. 66, No. 3, p 173-175
March, 1974.  8 ref.

The United States has ample water resources for present and near-future needs
provided there is proper management.  A standard plan for all water resources
management cannot be provided since each area has specific problems of its
own.  Thus the selection of a new or additional water source is dependent
upon local conditions and public involvement.  It is the growth patterns,
local requirements, and special-interest groups which will need balancing
and adjusting if proper management is to bS attained.

*Water management  (applied), *Administration, *Water resources, *Water
resources development, Public rights
                                      707

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06 3J

CHEMISTRY OF MODERN WATER CHLORINATION,

Palin, A. T.

Newcastle and Gateshead Water Compnay,
Laboratory, Throckley, Newcastle upon Tyne, NE15 9DT,
England

Water Services, Vol.  78, No. 935, p 9-12, January, 1974.  3 fig, 2 tab, 8 ref.

A review of the present state of chlorine use for the disinfection of water is
presented with emphasis on the chemistry of chlorination.  The forms of chlorine,
which include gas, solutions, solids, and new products, chlorine dissolved
in water, breakpoint  reactions, and definitions of modern chlorination are
discussed.

*Chlorination, *Chlorine, *Reviews, *Disinfection, *Water treatment
064J

CHEMISTRY OF MODERN WATER CHLORINATION,

Palin, A. T.

Newcastle and Gateshead Water Compnay, Laboratory,
Throckley, Newcastle upon Tyne, NE15 9DT, England

Water Services, Vol. 78, No. 936, p 53-56, February, 1974.

This review article is the second of a series which explores disinfection by
chlorine with regards to the effect of the hydrogen ion concentration, the
effect of temperature and time of contact, and the nature of residual chlorine
and minimum safe levels.  Also discussed are topics such as the chemistry
of waste water chlorination, residual chlorine control, and a general guide
to chlorine requirements.

*Reviews, *Disinfection, *Chlorine, *Water treatment,  Hydrogen ion concentra-
tion, Temperature, Waste water treatment, Industrial water

Residual chlorine, Contact time
                                        708

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06 5 J

WATER POLLUTION PREVENTION IN SOUTH WALES,

Cronshaw, H.

Chief Engineer, Directorate of Engineering,
Wales

Water Pollution Control, Vol. 78, No. 1, p 41-50, 1974.  4 fig, 2 tab.

Water pollution prevention in South Wales is particularly relevant in that
the catchment area draining to the Severn Estuary and Bristol Channel contains
almost two-thirds of the population of the Principality and all its major
industries.  Rapid progress is being made to clean up the rivers of South Wales
and there is a much greater awareness of the need for caution in discharging
waste water.  Pollution prevention measures have taken place within a general
policy framework which is sufficiently flexible to meet future demands.

*Water pollution control, *Waste water disposal, *Discharge (Water), Regulation,
Watersheds  (Basins)

South Wales
06 6 J

STUDIES OF THE SEASONAL VARIATION OF THE SUSPENDED
MATTER OF THE MENAI STRAITS.  II. MID STREAM DATA,

Buchan, S., Floodgate, G. D., and Crisp, D. J.

North Wales University College, Marine Science
Laboratories, Menai Bridge, Anglesey, England

Deutsche Hydrographische Zeitschrift, Vol. 26, No. 2, p 74-83, January,
1973.  9 fig, 2 tab, 3 ref.

Surface and bottom inorganic and organic suspended loads in the Menai
Straits were correlated with hydrographic and meteorologic elements which
impart an influence.  Surface inorganic loads correlated significantly with
tidal range, water temperature, and run of wind.  This latter factor did
not relate well with the bottom inorganic fraction.  Significant correla-
tions were evident between surface and bottom organic loads and the tidal
range.  Turbidity and suspended sediment load were also investigated.

Correlation analysis, *Suspended load, Tidal streams, Water temperature,
Wind tides, Organic matter, Inorganic compounds, Bottom sediments,
Turbidity, Sediment load

Surface Sediments, Menai Straits
                                           709

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06 7 J

ACHIEVING WATER POLLUTION ABATEMENT UNDER THE 1972 WATER
POLLUTION CONTROL ACT AMENDMENTS,

Kollar, K. L., and Brewer, R.

Office of Business Research and Analysis, Washington,
D. C., Water Resources and Engineering Program

Industrial Wastes, Vol. 19, No. 6, p IW/10, IW/12-Iw/13, IW/27,
November/December, 1973.  1 fig, 5 tab.

The achievement of water pollution abatement under the 1972 Water Pollution
Control Act Amendments is discussed.  One of the most controversial issues
is the implementation of best practicable technology by July 1977, best
available technology economically achievable by July 1, 1983, and the goal
of eliminating discharge of pollutants by 1985.  The development of area
wide waste treatment management plants by March, 1974 is also a provision.
There is a lack of qualified personnel of the various professional disciplines
required to adequately implement all the technical requirements established
by law at the federal, state, and local levels.  While most industrial plants
will be tying into municipal systems, more than 10,000 plants may be required
in the future to make large capital investments specifically for the treatment
facilities, in connection with their own sizeable industrial water use.  There
is a strong possibility that many plants may attempt to avoid some of the
capital costs they face by tying into municipal treatment facilities.

*Water pollution control, *Water Pollution Control Act, *Industrial wastes,
Water pollution sources, Costs, Municipal wastes, Professional personnel,
Treatment plants, Capital costs, Water utilization

*1972 amendments
06 8 J

EUTROPHICATION OF INLAND WATERS,

Ministry of Technology Notes on Water Pollution, No. 41, 4 p, June, 1968.
1 fig, 2 tab, 12 ref.

The eutrophlcation of inland waters is discussed including assessment,
utilization of nutrients, sources of nutrients, and methods of control.
The degree of eutrophication can be assessed by regular determinations of
the dissolved oxygen content of the water, rates of oxygen depletion,
biological productivity, transparency, nutrients levels, and the chlorophyll
'a' content of surface waters.  A Wisconsin study concluded that eutrophication
will be present if the phosphorus concentration in water exceeds 0.01 mg/liter
and the nitrate-nitrogen exceeded 0.3 mg/liter at the time of the spring
overturn.  The sources of nutrients include phosphate derived from excreta,
detergents, drainage from fertilized agricultural land, and sewage effluents.
The principle methods of control are diversion of nutrient rich waters from
the lake or reservoir where problems have developed or are likely to arise
and removal of nutrients from effluents.

*Eutrophication, *Water pollution sources, *Water pollution effects, *Water
pollution control, Water quality, Biochemical oxygen demand, Oxygen
requirements, Aquatic productivity, Nutrients, Nutrient requirements, Chlorophyll,
Phosphorus, Nitrates, Nitrogen, Organic wastes, Detergents, Farm wastes,
Sewage effluents

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 069 J

 ANTIBIOTIC  RESISTANCE AND R FACTORS  IN COLIFORM BACILLI
 ISOLATED FROM HOSPITAL AND DOMESTIC  SEWAGE,

 Linton,  K.  B.,  Richmond,  M.  H.,  Bevan,  R.,  and Gillespie,
 W. A.

 Bristol  University,  Bristol, England,  Department of
 Bacteriology

 Journal  of  Medical Microbiology,  Vol.  7,  No.  1, p 91-103,  1974.   8 tab,  21  ref.

 One hundred and one samples  from a wide variety of sewers  and water drainage
 channels in Bristol were  examined for  antibiotic resistant coliform bacilli
 and  for  R.  factors.   The  sewers  enclosed  some  that separately drained hospital
 and  domestic  premises. The antibiotic sensitivity patterns of over 3000
 coliform bacilli isolated were obtained and 1000 resistant strains were
 tested for  R  factor transfer.   Hospital sewage contained more coliform bacilli
 with  much higher proportions of  resistant bacteria,  more R factors,  and  a
 greater  proportion of R factors  carrying  multiple resistance, than sewage from
 domestic and  other sources.   Despite these  findings,  it was calculated that
 less  than 5%  of the R factors  in the sewage  output of the  City of Bristol
 originate in  hospitals.   The normal  healthy population appears to be by  far
 the  greatest  reservoir of R factors  in the  community.

 *Coliforms, *Sewers,  *Sewage bacteria,  Domestic wastes, Sewage,  Investigations,
 Sampling

 *Hospital wastes,  *Antlbiotic-resistance-transfer factors  (R factor),
 Bristol, England
070J

BACTERIAL DEGRADATION OF POLYCHLORINATED BIPHENYLS.  I.
IDENTIFICATION OF SOME METABOLIC PRODUCTS FROM AROCLOR
1242,

Kaiser, K. L., and Wong, T. S.

Environment Canada, Canada Centre for Inland Waters,
Burlington, Ontario, Canada

Bulletin of Environmental Contamination and Toxicology, Vol. 11, No. 3,
p 291-296, March, 1974.  2 fig, 1 tab, 11 ref.

The biodegradation of polychlorinated biphenyls (PCB's) was investigated and
their kinetic and mechanistic differences were determined with respect to
different aquatic organisms.  A bacterial culture, isolated from lake water
was shown to degrade PCB's at a relative high concentration of a commercial
mixture, Aroclor 1242.  Several of the metabolites were identified by their
mass spectral and gas chromatographic data.  None of the metabolites seem to
contain any chlorine.

*Biodegradation, *Polychlorinated biphenyls, Aquatic life, Investigations,
Separation techniques, Aquatic microorganisms, Rivers
Metabolites, Aroclor 1242
                                     711

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 071J

 PROTEIN  RECOVERY  FROM PROCESS  EFFLUENTS USING  ION-EXCHANGE
 RESINS,

 Grant, R.  A.

 Tasman Bacinne Laboratory Ltd.,  Ecotech Systems,
 Division,  Balena  Close,  Creekmoor,  Poole,  Dorset,
 England

 Process  Biochemistry,  Vol. 9,  No. 2, p 11-14,  February/March,  1974.
 2  fig, 12  tab.

 A  process  was developed  which  permits the  separate  recovery  of protein  and
 fat from meat, poultry and other food processing effluents,  while  at  the
 same  time  achieves a  large reduction in the BOD level.  The  process uses  a
 recently developed ion-exchange  resin capable  of adsorbing proteins and
 other macromolecules.  The resins can be manufactured in the granular form
 giving excellent  hydraulic properties.  They can be used in  a  conventional
 type  plant with the usual facilities for cleaning the bed by backwashing.
 Both  anion and cation  exchange forms of the resin are available and
 combination of these makes it  possible to  treat water up to  a  very high
 standard,  that is, BOD values  of less than 10  mg/liter have  been achieved.

 *Ion-exchange, *Resins,  *Proteins,  *Effluents, Food processing industry,
 Hydraulic  properties,  Biochemical oxygen demand, Adsorption, Water treatment,
 Industrial wastes, Byproducts

 *Recovered protein
072J

NUTRIENTS AND AQUATIC VEGETATION EFFECTS,

Fuhs, G. W.

New York State Department of Health, Albany, New York,
Division of Laboratory and Research

Journal of the Environmental Engineering Division, Vol. 100, No. EE2,
p 269-278, April, 1974.  1 tab, 14 ref.

The effect of nutrient pollution and nutrient removal on aquatic ecosystems
is discussed.  Because the increase in productivity of streams and rivers
is difficult to control, measures to control eutrophication of inland lakes
and reservoirs must center around control of total phosphorus loadings.
To the extent that excessive phosphorus loadings are in part or totally due
to discharges from point sources, these sources must be controlled.  In
many lakes, however, inputs from natural and other nonpoint sources are
significant.  Such inputs must be determined as a basis for evaluating total
control needs with respect to projected best usage and, in consequence, the
desirability and feasibility of control on nonpoint sources and land use.
It is hoped that continued studies of land runoff will soon provide an
overall view of phosphorus runoff from natural sources, so that runoff
numbers will be available for most watersheds of New York State and other
areas of the United States.  The control of eutrophication in coastal waters
requires the control of nitrogen discharges.

*Eutrophication, *Ecosystems, *Nutrlent removal, *Phosphorus, Aquatic life,
Streams, Rivers, Reservoirs, Water pollution sources, Water pollution control,
Land use, Surface runoff, Nitrogen, Productivity, Soils

*Nutrient pollution
                                     712

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 073J

 COST  OF  ACHIEVING E.P.A.'S  BPCTCA AND  ZERO  DISCHARGE,

 Paper Trade  Journal,  Vol. 158,  No.  15,  p  30-35,  April  15,  1974.   3 fig,  6  tab.

 Highlights from an engineering  estimate study  of the cost  of  meeting selected
 Environmental  Protection Agency national  effluent limitation  levels are
 presented.   Operating costs for achieving zero pollutant discharge were
 estimated at $1.7 billion annually.  An additional capital investment of
 $1 billion by  the pulp and  paper industry will be required to supplement its
 existing external effluent  treatment facility  to meet  the  proposed best
 practicable  control regulations scheduled for  1977.  The investment and
 operating costs for those mills on municipal sewage  treatment and those
 costs associated with compliance to best  practical control technology available
 are in addition to those estimates.  The  energy  requirement is the single
 largest  cost component of the total operating  cost for zero discharge treatment
 for the  pulp and paper industry.

 *Economic impact, *Federal  Water Pollution  Control Act, *Pulp and paper
 industry, Water quality, Effluents, Operating  costs, Capital  costs, Mills,
 Energy

 *Amendments
074J

THE ENVIRONMENTAL IMPACT CONCEPT,

Schleicher, A. R.

Southwest Research Institute, San Antonio, Texas

American Gas Association, Vol. 56, No. 4, p 21-25, April, 1974.

The environmental impact concept and its effect on the natural gas industry
are discussed.  Organizations are required to evaluate anticipated
environmental effects of their actions and decision making processes.  A
draft of the evaluation must be circulated 90 days prior to the action, and
a final statement is due at the Environmental Protection Agency 30 days before
the action is scheduled.  Practically all sectors of the gas industry are
being effected by the new requirements.  Producers may encounter federal
requirements for environmental reports when operations involve federal or
Indian lands, or offshore locations.  Segments of the industry involved
in gas transmission are acutely aware of the influence of environmental
questions, since most of their construction activities involve federal
authorization.  Most companies involved in the environmental impact process
find it necessary to seek the aid of outside consultants.  But, decision
makers in the natural gas industry should develop their own practical
appreciation of the scope and intent of current environmental policies and
the way the system works.

*Environmental effects, *Natural gas, Evaluations, Federal government,
Environmental control

*Environmental impact, statements, *Natural gas industry
                                     713

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 075J

 ECONOMIC IMPACT OF FWPCA WATER EFFLUENT STANDARDS  AND
 GOALS,

 Paper Trade Journal,  Vol. 158, No.  13,  p 34-38,  April 1,  1974.   5 tab.

 The national economic impact  of the Federal Water  Pollution  Control Act
 Amendments on the paper industry in meeting the  water effluent  standards
 and goals is discussed.   A survey was  conducted  to estimate  the additional
 capital and operating costs that the existing paper industry would have to
 incur to achieve the  two assumed water  effluent  control levels.  The water
 effluent control costs over the range  of mill sizes in each  product category
 were compared with current product  prices,  anticipated profit margins for
 high cost mills, and  the costs of competing foreign mills.   It  is estimated
 that $1,200 million will have to be spent for additional  capital expenditures.
 It is estimated the average incremental operating  cost for best practical
 control would increase from $4.50/ton  average to $6.00/ton in 1977.  There
 will be several inflationary effects in water effluent control  expenditures
 especially during periods of tight  supply/demand.   Pulp and  paper price
 increases to the consumer are expected  to amount to 7.5-11%  at  the best
 practical control level and 19-62%  at  the zero discharge  level, depending
 on the product.  Other effects include  mill closure and unemployment,
 increased energy use, and balance of payments.

 *Economic impact, *Federal Water Pollution Control Act, *Pulp and paper
 industry, Water quality, Effluents, Operating costs,  Capital costs, Prices,
 Unemployment, Mills,  Energy

 *Amendments, Blance of payments
076J

FRESH WATER SEAL IN RIVER SLUICE,

New Civil Engineer, No. 78, p 32-33, February 7, 1974.  2 fig.

A unique system of water control machinery is now in operation at Brean
Cross Sluice on the River Axe near Burnham-on-Sea.   It is the latest in a
series of major tidal outfalls constructed for the Somerset River Authority.
Two major sluice openings are provided, each with a tidal flap and a double
sealing vertical lift roller gate.  The structure was designed to accomodate
a further identical gate in each opening to form a well between the two
gates.  Under normal conditions the gates are lifted and discharge is
controlled by the tidal flaps, but during the summer months all gates would
be lowered and the well between the gages pumped full of fresh water from
upstream using a submersible pump and maintaining the water level in the
well above tide level.  This system excludes salt and silt from the fresh
water reservoir upstream.

*Tides, *Drainage systems, *0utlets, *Sluices, Roller gates, Engineering
structures, Reservoirs, Freshwater, Silts, Salts, Sluice gages, Water level,
Rivers

River Axe (England)
                                      7U

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077J

RESTORATION  OF WASTEWATER FACILITIES DAMAGED BY TROPICAL
STORM AGNES,

Ernstrom, E. K.,  Zachos,  G.  H.,  and Braunscheidel, D. E.

U.  S. Environmental  Protection Agency,  Emergency
Operations and Planning

Water and Sewage  Works, Vol.  121, No.  2,  p  42-43,  51-52,  February,  1974.   2  tab.

The recovery and  restoration of  waste  water facilities  damaged by  tropical
storm Agnes  in June,  1972 are described.  The  storm  caused  severe  flooding
in  New York's Southern Tier  counties.   Waste water collection and  treatment
systems  sustained several million dollars worth of damage.   Individual
municipal cases are  discussed along with  the reactions  and  roles of local,
state, and federal officials. The Environmental  Protection Agency assisted
in  the flood relief  and concentrated its  efforts  in  the following  areas:
emergency repairs to  water and sewage  utilities;  removal  of oil and hazardous
materials in the  disaster area;  rendering a preliminary dollar estimate  of
damages  to water  and sewage  utilities  in  all 62 counties; and performing
initial  inspections,  detailed cost estimates,  eligibility determinations,
interim  inspections,  and  final inspections  on  damaged public utilities in
the 26 declared counties.  Top priority was given to restoring the public
water supply systems.  The current total  of eligible damages to environmental
facilities in the declared counties is  $7,218,170, with over 60% of this
damage in Chemung, Steuben,  and  Allegany  counties.

*Flood damage, *Storm runoff, *New York,  Waste water treatment, Treatment
facilities,  Costs, Sewage, Historic floods, Regional flood,  Disasters,
Estimates

*Tropical storm Agnes, Steuben County,  N. Y.,  Chemung County, N. Y.,
Allegheny County,  N.  Y.
078J

CADMIUM TOXICITY AND BIOCENTRATION IN LAREGMOUTH BASS
AND BLUEGILL,

Cearley, J. E., and Coleman, R. L.

Oklahoma University Health Sciences Center, Oklahoma
City, Oklahoma, Department of Environmental Health

Bulletin of Environmental Contamination and Toxicology, Vol. 11, No. 2,
p 146-151, 1974.  4 fig, 7 ref.

The effects of subacute exposure to cadmium in the largemouth bass and bluegill
were evaluated based on observations of behavioral effects, rate of growth,
survival, and tissue and organ accumulation of cadmium.  Exposure to cadmium
in concentrations ranging from 0.0005 to 0.85 mg/liter resulted in accumulation
of the metal in concentrations greater than those of the water.  The quantity
of metal accumulated increased as the exposure concentration increased.  An
equilibrium developed between the concentrations of the metal in the water
and in the tissues after approximately 2 months.  Metal accumulations on the
bass tissues were higher in the internal organs, followed by the gills and
the remainder of the body.  The bass were more sensitive to cadmium than the
bluegill.  Abnormal behavior patterns observed in both species suggested
that the nervous system was the site of damage.

*Cadmium, *Bass, *Sunfishes, Animal behavior, Animal growth, Growth rates,
Environmental effects, Animal diseases, Investigations, Evaluations, Water
pollution effects, Water analysis

Accumulation, Nervous system, Exposure
                                     715

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 079J

 SIMPLE METHOD FOR INTRODUCING ELEMENTAL MERCURY INTO
 BIOLOGICAL GROWTH SYSTEMS,

 Holm,  H.  W.,  and Cox,  M.  F.

 U.  S.  Environmental Protection Agency,  Athens,  Georgia,
 Southeast Environmental Research Laboratory

 Applied Microbiology,  Vol.  27, No.  3,  p 622-623,  March,  1974.   1 fig,  1 tab,
 8 ref.

 The applications of a  simple method for introducing elemental  mercury  into
 closed biological growth systems are described.   A 1 liter Erlenmeyer  flask
 equipped  with a 24/40  standard taper outer joint  was modified  to permit a
 closed system.   The system may be used to  investigate such processes as the
 transformations of mercury  using pure  cultures  of bacteria,  the behavior of
 mercury in sediment water systems,  and the oxidation of  mercury in natural
 waters.  The  apparatus may  be used in  similar applications involving other
 volatile  materials.

 *Mercury,  *Aquatic environment,  Sediment^water  interfaces, Oxidation,
 Equipment,  Natural streams

 *Closed biological growth systems
080J

PLATING POLLUTION:  THE LATEST FROM EPA, Part 1,

Products Finishing, Vol. 38, No. 7, p 141-144, April, 1974.  1 tab.

The stringent limitations proposed by the Environmental Protection Agency
on the electroplating industry were discussed at an American Electroplaters '
Society seminar.  The proposals made by the EPA require that a plater
discharge no more than a stated weight of any contaminant for each unit of
surface area he plates.  The platers must limit concentrations of contaminants
in the rinse water to 1.0 mg/liter or less, depending upon the constituent
(except for suspended solids).  Few, if any, of the pollution control
authorities in the electroplating industry believe that the confcination of
low water usage and low concentrations can be achieved by production plants.
The basis for the proposed regulations is a Battelle Memorial Institute study
which estimated that a water use of 80 liter/sq in could generally be
attained.

*Standards, Water pollution sources, *Water utilization.

*Electroplating industry, Environmental Protection Agency
                                         716

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     081J

     FLASH—FLOOD WARNING SYSTEMS,

     California Geology, Vol. 27, No. 1, p 7, January, 1974.

     The new flash flood warning system of the National Weather Service is described.
     The system has three main elements, linked together by electrical circuitry:
     an automatic water level sensor at an upstream point on the river; an
     intermediate station several miles or more downstream to provide power to the
     sensor; and a community alarm station from which warnings can be spread quickly
     to the public.  The Weather Bureau is planning a major campaign to encourage
     greater use of these life and property saving devices.

     *Flash floods, *Warning systems, Flood control, Rivers, Water level recorders,
     Flood forecasting, Automation, Control systems.

     National Weather Service, Alarm systems.
082J

OVERFED,

Crossland, J., and McCaull, J.

Environment, Vol. 14, No. 9, p 30-37, November, 1972.  2 tab, 30 ref.

The causes, effects, and treatment of eutrophication are discussed.  The
condition stems from overenrichment with nutrients that frequently derive
from human activities.  In a survey of officials of 425 lakes, the problem
in 80% was overgrowth of algae or other aquatic vegetation or some unspecified
eutrophic condition.  In most cases in which the causes had been determined,
the nutrients were in wastes from municipal sewage treatment plants, septic
tanks, or urban drainage.  In studying the causes of eutrophication, it is
necessary to decide not only how nutrients are distributed in the aquatic
environment, but also which are most important for plant growth.  The most
critical nutrients, carbon, nitrogen, and phosphorus are usually required in
a ratio of 106:10:1, respectively.  If even one of these elements is missing,
all the others becomes useless to the plant.  Proposed solutions range from
attacks on the symptom of the problem to alleviation of the root causes.
The most practical and economical chemical treatment is to precipitate or
otherwise reduce the phosphorus content from the waste water.

*Eutrophication, *Water pollution sources, *Water pollution control,
*Phosphorus, *Algae, *Aquatic plants, *Aquatic algae, *Nutrients, Carbon,
Nitrogen, Lakes, Municipal wastes, Sewage, Treatment plants, Septic tanks,
Urban drainage, Chemical precipitation.
                                         717

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08 3J

AGRICULTURAL WASTE MANAGEMENT,

Miner, J. R.

Oregon State University, Corvallis, Oregon

Journal of the Environmental Engineering Division, Vol. 100, No. EE2,
p 363-368, April, 1974.

The role of civil engineering in the management of agricultural wastes is
discussed.  The problems with agricultural wastes ai= different from those
commonly encountered in the management of municipal .istes.  Serious problems
have resulted when municipal waste technology has be_n transferred to the
management of agricultural wastes without due consideration for the differences
of generation characteristics and chemical characteristics of the waste
materials.  The management of animal manures requires the utilization of a
system that somehow resolves the problems of separation of the manure from
the animal, transport, storage or treatment or both and disposal.  Under
current technology, application to cropland is the most widely practices
disposal method.   Treatment is for the purpose of making the manure more
amendable to cropland application or for the purpose of changing its
physical and chemical characteristics to avoid application difficulties or
nuisances attributable to the application.

*Civil engineering, *Farm wastes, *Farm management, *Waste storage,
*Waste disposal,  Chemical wastes, Waste treatment, Water pollution sources,
Pollution abatement, Waste water treatment.
084J

STATE-OF-THE-ART OF WASTE DISPOSAL IN THE COATINGS
INDUSTRY  (AS OF JUNE 1973),

Tackett,  R.

Journal of Paint Technology, Vol. 46, No. 590, p 63-68, March, 1974.  8 tab.

The results of a survey on waste disposal techniques currently in use in
the coatings industry are discussed.  The questionnaire, which was answered
by 558 companies, was divided into four main parts:  vapors,  liquids, dusts,
and solids.  Questions concerning installation of control equipment  and its
operation were asked in each section.  Equipment was installed by 114 companies
for controlling water based liquid wastes.  The most popular  methods of
control were settling tanks, ponds, or basins.  The main problem of  control
methods for all wastes is that  they generate a solid waste  or sludge which
presents  a serious disposal problem.  The coating industry  will have to
develop an alternate method to  landfill  for disposal of solid waste  or sludge.
Reclamation may be most suitable because of the value  of some of the components.

*Survey,  *Waste  disposal, *Coatings,  *Reclamation, Industrial wastes,
Pollution abatement, Equipment, Dusts, Liquid wastes,  Solid wastes,  Gases,
Recycling, Landfills, Sludge  disposal, Alternate planning.
                                        718

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 085J

 SOME HISTORICAL STATISTICS RELATED TO FUTURE STANDARDS,

 Berthouex, P. M.

 Wisconsin University, Madison, Wisconsin

 Journal of the Environmental Engineering Division, Vol. 100, No. EE2,
 p 423-437, April, 1974.  13 fig, 2 tab, 7 ref.

 Areas of uncertainty that have relevance in the current water quality standards
 are discussed including treatment plant construction dilemma and the lack of
 precision in the language of the standards.  Population and demand for
 forecasting have always added an unavoidable element of risk, but it is very
 possible that changing standards are the factor most likely to force redesign
 before the end of the intended design period.  If control programs based
 on rational statistical methods are ever to be developed, it is necessary
 for effluent target levels and permissible variation to be clearly defined.
 In doing so, allowance should be made for natural variations and for
 analytical errors.  Possible skewness in the distribution of results should
 also be noted and given consideration.  When both a mean and upper performance
 level are set, the mean may be redundant if care is not taken to make the
 two levels consistent.  This problem of consistency could be avoided most
 easily by simply using a 95% upper bound as the standard.

 *Water quality standards, *Treatment facilities, Construction, *Engineer
 estimates, *Forecasting, Design standards, Population, Statistical methods,
 Control, Standards
086J

SOUND STANDARDS FOR ENVIRONMENTAL IMPROVEMENTS,

Train, R. E.

Environmental Protection Agency, Washington, District
of Columbia

American Gas Journal, Vol. 56, No. 4, p 26-27, 29, April, 1974.

Environmental standards and their development at the Environmental Protection
Agency are discussed.  The standard setting process begins with the gathering
of all available data on the health and environmental effects of a particular
pollutant.  The proposed standard is first circulated within the EPA and
then in other federal agencies and organizations for comments and criticisms.
After changes are made in the proposed standard, it is then recirculated.
After final approval, the new regulation is published in the Federal Register.
An environmental standard is a norm of tolerance expressed as a numerical
value indicating a concentration of a pollutant for a given duration of time.
Standards should also specify the test method to be used and should include
adjustments which would bring other recognized and feasible test methods into
equivalency with the specified test method.  The sampling method must also
be an integral part of the standard.  A standard statistical technique for
determining the validity of the sample results is also recommended to be
incorporated in the standard.

*Standards, Environmental effects, Regulations, Testing procedures, Sampling,
Statistical methods

Environmental Protection Agency
                                      719

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     08 7 J

     CHEMICAL HANDLING:  THE CHEMICAL FEEDER AND ITS RELATED SYSTEM
     WHEN APPLIED TO ALUM, FERRIC CHLORIDE, LIME AND POLYMERS,

     Fahlenbock, T.


     Control and Metering Limited,
     Toronto, Ontario, Canada

     In:  PHOSPHORUS REMOVAL DESIGN SEMINAR, Canada-Ontario Agreement on Great
     Lakes Water Quality, May 28-29, 1973.  30 p, 7 fig, 3 tab.

     Various characteristics of the chemical feeder or metering pump which include
     basic design, operation, accuracy, sizing, system components, stages of
     design development, and performance specifications, are detailed.  Also dis-
     cussed are the maximum and minimum feed rates for the feeder as well as its
     ability to handle alum, ferric chloride, dry polymers and lime.

     *Chemical precipitation, *Equipment, Measurement, Design criteria, Operation
     and maintenance, Performance, Alum, Iron, Chlorides, Lime

     *Chemical feeder, *Phosphorus removal
088J

NEW OIL SPILL CLEANUP TOOL FOR COMMERCIAL PRODUCTION,

Oil Week, Vol. 25, No. 8, p 30, April 8, 1974.

The first effective tool for containing and cleaning up oil spills in medium to
fast moving waters will shortly go into commercial production.  The Petroleum
Association for the Conservation of theCanadian Environment developed a boom
which consists of two inflated floats cased in a fabric, each about 50 ft
long between which is suspended netting and a special nonwoven material.  It is
placed across the current flow at an angle and some oil is diverted by the lead-
ing float toward the downstream end for recovery.  Most of the oil flows with
the water under the leading float, passes through the netting and flows along
the face of the nonwoven fabric which is designed to permit the water to pass
through, but not the oil.  The oil comes to the surface of the ponded area be-
tween and the two floats, where a tangential current carries it to the downstream
end of the boom where it is collected and recovered.  The boom weighs only 2
Ib/ft and can be shortened or lengthened in sections.

*0il spills, *Water purification, Oil pollution, Water pollution control, Flow,
Floats, Canada

*Boom
                                          720

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089J

ASBESTOS IN DRINKING WATER,

Sargent, H. F.

Vermont Department of Health,
Burlington, Vermont, Division of Environmental Health

Journal of the New England Water Works Association, Vol. 88, No. 1, p 44-57,
March, 1974.  1 tab, 5 ref.

Asbestos fibers were found by light microscopy to be present in 30 of 32
water systems tested in Vermont.  Generally, there is an increase in fiber count
from source to distribution, but it is not known whether the fiber increase
is due principally to breaking apart, concentration through sedimentation,
erosion of A. C. pipe, or field tapping A. C. pipe.  There is no conclusive
evidence to data incriminating asbestos in water as a health hazard at
presently known levels.  Where flushing of the system was instituted following
sampling, the fiber count was substantially reduced.  There is a need for
more research in this area to establish if or at what concentration of fiber
a hazard to health exists.  A standard procedure for identification and
quantifying asbestos in drinking water is needed.

*Asbestos, *Potable water, *Vermont, *Public utilities, *Municipal water,
Investigations, Water pollution, Water pollution sources, Pipes, Erosion,
Sedimentation
090J

SIGNIFICANCE OF ECOLOGICAL ANALYSES IN THE INTERPRETATION OF
ENVIRONMENTAL RELEASES OF RADIONUCLIDES,

Auerfaack, S. I., Vanderploeg, H. A., Kaye, S. V., and
Witherspoon, J. P.

Oak Ridge National Laboratory,
Oak Ridge, Tennessee, Environmental Sciences Division

IEEE Transactions on Nuclear Science, Vol. NS-21, No. 1, p 18-22, February,
1974.  4 fig, 1 tab, 8 ref.

The role of ecological analyses in the collection and interpretation of
environmental measurements that are part of the surveillance programs of
aquatic ecosystems around nuclear facilities is discussed.  Bioaccumulation
factors are used to predict the radionuclide concentrations an organism
accumulates from chronic releases.  The bioaccumulation factor is the ratio of
radionuclide concentration in the organism to that in water.  Bioaccumulation
factors range from less than 1 to greater than 100,000, depending on the
element, organism, and the environmental and ecological factors.  The bio-
accumulation factors of cesium in fishes are illustrated as a function of
potassium concentration in the water, feeding habits and eutrophy.  The
highest bioaccumulation factors are found in piscivorous fishes from oligo-
trophic waters, which are waters of low nutrient and organic content.
Piscivorous fishes are expected to have the highest bioaccumulation factors
because Cs concentration increases with trophic level.  The generally lower
bioaccumulation factors in eutrophic water may result from sorption of Cs to
the more abundant particulate organic matter in these waters.  Particulate
organic matter strongly absorbs many radionuclides.

*Ecology, Analysis, *Radioisotopes, Aquatic environment, Cesium, Fishes,
Potassium, Organic matter
                                721

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091J

WATER UTILITIES OPERATOR TRAINING:  A WORTHY INVESTMENT,

Jobes, H. D.

Texas Water Quality Board,
Austin, Texas, Central Operations Division

Water and Sewage Works, Vol. 121, No. 4, p 58-59,  April, 1974.

A study made for the Environmental Protection Agency on a water utilities
operator training program in Texas is discussed.   Methodology of the study was
to examine treatment plant operations as they existed before employee training
and to examine results after training.  The effectiveness evaluation study
document states in its conclusion that for every  dollar invested in training,
the equivalent of an additional $91 investment in capital plant was activated
in terms of improved performance.  The degree of  reduction of BOD, total sus-
pended solids, and levels of overall improvements  following training indicated
conclusively that for these plants the value of return on training was high
in terms of both dollars invested and cleanliness  of water treatment.


*Training, *0perations, *Evaluation, Personnel, Texas, Water quality,
Investment, Water pollution control, Treatment facilities
 09 2 J

 THE NEED FOR AN  INDICATOR VIRUS  IN  WATER QUALITY  TESTING,

 DeMichele,  E., Burke,  G.  W.,  Jr., and  Shane,  M. S.

 Water Pollution  Control  Federation,
 Washington, B.C.   Technical Services

 Water and Sewage  Works,  Vol.  121, No.  4,  p  39,  April,  1974.

 Water quality problems are discussed and the  need for  an  indicator virus  in
 water quality testing  is  proposed.  The  validity  of  the coliform test  as  an
 indicator of potential pathogenic microbial water pollution  is  being increas-
 ingly questioned.   The fact that laboratory studies  have  shown  enteroviruses
 to  be more resistant to  normal water and waste  water chlorination practices
 than organisms of the  coliform group lends  justification  to  the hypothesis
 that coliform counts may not  adequately  monitor viral  infection of water.   The
 main problem is  knowing  the viruses exists, but being  unable to measure them
 accurately or knowing  which,  if  any, might  cause  infection.   A  test procedured
 is  proposed for  an indicator  virus  to  be developed in  a manner  paralleling
 the use of E. coli as  an indicator  bacterium.   The procedure should provide
 a rational means  of measuring treatment  efficiency in  terms  of  human health
 and well being.   It is not necessary that the virus  be pathogenic, but rather,
 it  should be similar to  infectious  viruses  in terms  of make  up, tolerance,
 and stability.

 *Water quality,  *Viruses, *Bioindicators, Water analysis,  Water pollution,
 Testing, Public  health
                                      722

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 09 3 J

 FORT WORTH WATER SUPPLY  AND  TREATMENT  PLANT  DEDICATED,

 Water  and  Sewage Works,  Vol.  12,  No. 4,  p  46-47,  63,  April,  1974.   5  fig.

 The dedication  and design of the  Cedar Creek Lake Pump  Station and the Rolling
 Hill Water Treatment  Plant of Fort  Worth,  Texas  are described.   The Cedar
 Creek  project consists of the Cedar Creek  Reservoir with  a capacity of 678,000
 acre-ft, the dam being about 85 mi  southeast of  Forth Worth;  an intakye pump
 station  at the  reservoir;  a  72 in pipe line  with appurtenant  pump  stations,
 68.2 mi  in length from the reservoir intake  to a balancing reservoir  at the
 end of the 72 in section of  pipe  line; an  84 in  pipe  line, 6.1 mi  in  length
 from the balancing reservoir to the site of  the  treatment plant; and  the
 balancing  reservoir with a capacity of 150 mil gal.   Designed to handle 80 mgd,
 the $8.7 million Rolling Hills plant will  be able to  treat 100 mgd when trans-
 mission  facilities permit.   Expansion  to 160 mgd will not require  added chemi-
 cal facilities,  administrative or laboratory buildings, or high service pump
 stations.   The  194 acre  sites will  allow expansion to 320 mgd.   Plant design
 permits  ultimate computer control with data  logging.  The water is treated for
 turbidity, taste, and odor control.  Following chemical application propor-
 tional to  flow,  the water is  mixed,  coagulated,  settled,  filtered  and stored
 for delivery.

 *Design  data, *Pumping station, *Treatment facilities,  Pipelines,  Reservoirs,
 Construction, Waste water treatment, Chemical treatment,  Water analysis, Taste,
 Odor,  Sedimentation,  Filtration,  Filters,  Pumps,  Flocculation

 Forth  Worth, Texas, Rolling  Hills Treatment  Plant, Fort Worth,  Texas, Cedar
 Creek  Lake Pump  Station,  Fort Worth, Texas
09 4J

HOW WELL DO ENGINEERS FORECAST DEMANDS?,

Berthouex, P. M., and Thiele, K.

Wisconsin University, Madison, Wisconsin

Water and Sewage Works, Vol. 121, No. 4, p 54-56, April, 1974.  5 fig, 5 ref.

The problems in making accurate engineering forecasts are discussed and
methods to reduce the forecasting errors are suggested.  Engineers face a
difficult task in forecasting population, flows, organic loads, and other design
inputs and then trying to design a treatment facility to accommodate these
loads and have the real plant eventually function to satisfy standards that
may exist, 10, 15 of 20 yr into the future.  Changes in water quality standards
may confront the engineer as an even greater challenge in future planning
than population forecasting.  If effluent standards or stream standards were
clearly stated and the target were fixed, the engineer could plan the develop-
ment of a treatment system in stages, according to a long term coordinated
plan.  He could try to take full advantage of economics of scale, of new
technology, and of new design procedures.  Uncertainty during design works
against the designer accomplishing this goal.  The impact of this uncertainty
on implementation of pollution control technology is great.           *

*Engineering, *Forecasting, *Engineering estimates, Treatment facilities,
Water quality, Water quality standards, Design standards

*Accuracy
                                       723

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 09 5 J

 REVIEW OF PRECAST PRESTRESSED CONCRET WATER STORAGE
 RESERVOIRS,

 Hodgson, K.  0.

 Natgun Corporation,  Wakefield, Massachusetts

 Journal of the New England Water Works Association, Vol.  88, No.  1, p 58-63,
 March, 1974.

 Precast prestressed concrete water storage reservoirs are discussed.  The
 tanks have a low profile, versatality of installation, require no painting in-
 side or outside, and low or minimum maintenance requirements.  The domed
 tanks which are more common than flat tops do not have and do not need columns.
 They do not have to be taken out of service.  There are three types of tanks:
 small tanks in sizes 100,000 to 500,000 gallons of the precast reinforced
 concrete panel type, with diaphragm, but not wire wound or prestressed;  the
 regular precast prestressed concrete tanks in sizes 500,000 gallons and up,
 and the concrete domes for existing circular tanks or for circular reservoirs.
 Exterior architectural treatment is possible for all tanks.

 *Storage tanks, *Water storage, *Reservoir storage, Concrete structures,
 Prestressing

 Precasting
096J

THE WATER SUPPLY INDUSTRY,

Proceedings of the Society for Analytical Chemistry:  Analytical Division,
Chemical Society, Vol. 11, No. 3, p 41-51, March, 1974.  1 tab, 10 ref.

The proceedings of the Analytical Division of the Chemical Society of the
Society for Analytical Chemistry are presented, and the water supply industry
in Great Britain is discussed.  Under present circumstances, water management
in Great Britain is fragmented and lacks uniformity.  With the existing
arrangements the water services are divided into three parts:  water supply,
sewerage and sewage, and river and water resources management.  As the consump-
tion of water for domestic and industrial purposes continues to increase, more
consideration is being given to augmenting existing supplies by the use of
underground sources, river water, treated effluent, and by opening up new
catchment areas.  The recycling and reuse of water will also become common-
place and cheaper alternative supplies of less pure water will be offered
increasingly to industrial users.  It is expected that there will be close
liaison between industry and the new Regional Water Authorities.  Rivers
are also the recipients of surface water, sewage, and industrial wastes,
which, coupled with the growing use of a diversity of new materials and
active ingredients, increases the risk of water supplies becoming polluted
between the source and the consumer.  The need for stricter analytical sur-
veillance is urgent.

*Water supply, *Water supply development, *Water management (applied),
Water pollution effects, Water pollution sources, Water reuse, Sewage, Water
resources, Water conservation, Rivers, Organizations, Technical societies,
Analytical techniques

Meetings, Society for Analytical Chemistry,  Great Britain
                                        724

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  09 7 J

  THE MARINE ENVIRONMENT—USE AND ABUSE,  ORDER OF
  CONFLICT—PART 1,

  Ranken,  M. B.  F.

  Aquamarine International Limited,
  London,  England

  Journal of the Society of Environmental Engineers, Vol. 131, No. 60, p 3-11,
  March, 1974.  1 tab.

  The causes and effect of pollution in the sea are discussed in a comprehensive
  review of the marine environment.  The most important effects of pollutants
  are biological; the sea is a highly effective scavenger of many pollutants,
  but its  capacity to break down and neutralize them is not infinite.  A great
  many pollutants come from sewage outfalls and industrial discharges into the
  tidal waters,  often uncontrolled and illegal; from rivers; from the atmosphere
  brought down by rain; from agricultural runoff; from dumping from ships; from
  exploitation of natural resources; and from other sources.  In pollution
  abatement a difficult and delicate balance must be achieved between the cost
  of what  is done to reduce or abate the pollution and the losses caused by not
  doing so.  There is easy access to the sea for any industry located on an
  estuary or along the coast.  The aim in estuaries must be to reduce pollution
  to levels at which the bottom can support the fauna needed for sea fish, and
  at which migratory fish can pass up or down river, whatever the river or
  tidal levels.   Some of the pollutants entering the sea are listed.

  *Sea water, *Water pollution effects, *Water pollution sources, Industrial
  wastes,  Sewage, Farm wastes, Rivers, Estuaries, Fishkill, Water pollution
  control, Environmental effects, Domestic wastes, Water supply

  London,  England
09 8J

SEDIMENTARY  FLUORITE  IN TAMPA BAY, FLORIDA,

Taft, W. H.,  and Martin, D. F.

South Florida University, Tampa, Florida,
Department of Chemistry

Environmental Letters, Vol. 6, No. 3, p  167-174, 1974.  4  ref.

Water and sediment samples were collected at eight sites in Tampa Bay adjacent
to the southernmost discharge canal of an industrial  company, Gardinier,
Incorporated.  Water  samples were frozen within 4 hours of collection and
sediment samples were dried and prepared for x-ray diffraction.  The results
show:  the existence of sedimentary fluorite; remarkably low pH meter
readings which indicate the buffering capacity of 12  acre meters of estuarine
water was virtually exhausted; the fluoride concentration is as much as 40
times its concentration in normal sea water, undoubtedly because of the com-
plexing by hydrogen ions and silicon; and the temperature differentials in
such relative shallow water are not only significant, but are the inverse of
what wo.uld normally be expected.

*Water sampling, *Sampling, *Sediments, Analytical techniques, Estuaries,
Fluoride, Sea water, Temperature,  Hydrogen ion concentration

Tampa Bay, Florida, Fluorite
                                      725

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099J

DISPOSAL OF COMMUNITY WASTEWATER,

World Health Organization, Geneva, Switzerland

Technical report series Ho. 541, 1974.  72 p, 17 ref.

A report of a World Health Organization Expert Committee on Disposal of
Community Wastewater which met in Geneva from September 25-October 1, 1973
is presented.  The committee emphasized the need for specific research acti-
vities in the following main areas:  alternatives to the water carriage system;
reuse of waste water; removal of deleterious substances; new criteria for
the control of effluent quality; manpower and managerial development; and low
cost collection and disposal systems.  Master plans envisaging feasible
development in stages should be established on a community basis.  An effec-
tive organization should be established at the national, state, regional, or
local level, for the efficient management of the facilities with the emphasis
on a central agency to plan and operate water supply and waste water dis-
posal systems.  The financing of waste water disposal systems should be
integrated with that of water supply systems in the interest of obtaining
higher priority for waste water systems an  better public acceptance of
them.  The waste water disposal system, should, as far as possible, be
self-financing; government subsidies providing the initial impetus, if
required.  Health agencies should continue their activities in the monitoring
and surveillance of water quality and environmental pollution.

*Municipal wastes, *Waste disposal, *Waste water treatment, Alternative
planning, Water reuse, Water supply, Water quality, Control, Effluents,
Water resources development, Water management (Applied), Water costs, Public
health, Monitoring, Water pollution

Geneva, Switzerland
100J

INSPECTION OF NEW TREATMENT FACILITIES,

MacKenzie, W. N.

Rockville Water and Aqueduct Company,
Rockvllle, Connecticut

Journal of the New England Water Works Association, Vol. 88, No. 1, p 1-18,
March, 1974.

The history of the Rockville Water and Aqueduct Company of Rockville, Conn-
ecticut is presented.  A  chronological summary of  construction and events
dating back almost 150 years is presented including a list of people import-
ant to the development of the company.  The company was organized under a
charter granted in April, 1893 as a  result of the  merger of  the Rockville
Water Power Company and Rockville Aqueduct Company.  The company was con-
cerned with controlled water pollution as early as 1907 when Lake Snipsic
and its tributaries were  examined for sources of pollution.  The company
acquired additional land  for the sole purpose of protecting  from pollution
the drinking water supplied to the city.  Anti-pollution rules were esta-
blished in 1911 for those using the  lake shore front.  Organic wastes and
refuse matter were forbidden to be deposited in the lake.

*History, *Pollution  control, Organic wastes, Wastes, Water  quality, Waste
water treatment, Potable water, Lakes

*Rockville Water and  Aqueduct Company, Rockville,  Connecticut
                                    726

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101J

ENVIRONMENTAL TECHNOLOGY AT NORWICH UNIVERSITY,

Pyper, G. R.

Norwich University, Northfield, Vermont,
Department of Engineering and Technology

Journal of the New England Water Works Association, Vol. 88, No. 1, p 32-43,
March, 1974.  3 ref.

The new and innovative 4 yr curriculum in Environmental Engineering Technology
at Norwich University, Northfield Vermont, is described.  The objective of the
program is to produce an environmental technologist who has the technical com-
petence to work with environmental engineers and support environmental activi-
ties with a minimum supervision.  The course of study includes the following
environmental courses:  Environmental Pollution, Air Resource Engineering,
Hydrology and Waste Resources, Water Analysis Instruments, Air Sampling and
Monitoring, Water Pollution Control,  Air Analysis Instruments, Air Field
Lab Problems, and Water Field Lab Problems.  The predominant characteristic
of the technologist who will graduate from this program will be the techni-
cal ability to identify and define the extent of environmental pollution or
establish that no pollution exists.

*Education, *Environmental engineering, Universities

*Course of study, Norwich University (Northfield, Vermont)
 10 2 J

 RIVER AVON COULD CONSIST LARGELY OF SEWAGE EFFLUENT,

 Water and Wastes Treatment, Vol. 17, No. 1, p 13, January, 1974.

 The report of the Bristol Avon River Authority warning that the River Avon
 could consist largely of sewage effluent is discussed.  The basic fact coming
 out of the report is that water supplies are not limitless and the rising
 demand, which stems from increased per capita usage as well as population
 growth, could not only outstrip supply but also have a disastrous effect
 on the River Avon system.  There are two solutions:  water can be imported
 from other areas or local resources can be developed by river regulation and
 developing and optimizing groundwater resources.  Future public water supply
 needs which by the year 2001 will exceed present resources by 66 million pgd
 can be met, by constructing a new reservoir.

 *Water supply, *Water supply develppment, *Water resources, *Water resources
 development, Rivers, Reservoirs, Sewage, Effluents, Water quality, Groundwater
 resources

 River Avon (Great Britain), Bristol Avon River Authority (Great Britain)
                                       727

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10 3J

STARTUP AND OPERATION OF THE ROCKVILLE WATER TREATMENT
PLANT,

McQueen, J. R.

Rockville Water and Aqueduct Company,
Rockville, Connecticut

Journal of the New England Water Works Association, Vol. 88, No. 1, p 25-31,
March, 1974.     »

The startup and operation of the Rockville Water Treatment Plant is
described.  The plant is the result of 2 1/2 yr of planning and $2 1/4
million.  Treatment in Rockville prior to this rapid sand filter plant con-
sisted of chlorination which began in 1929, the addition of caustic soda in
1966 for corrosion control within the distribution system, and fluoridation
required by state law in 1968.  Complete startup took 18 days.  On May 1,
1970 raw water began flowing through the plant and discharging back in Lake
Shenipsit through the overflow piping of one of the clear water storage tanks.
This was followed by chemical treatment stabilization, Board of Health inspec-
tions, and some piping changes.  Five operators work a rotating shift schedule
which requires that each operator be involved in all aspects of the plant's
operation and maintenance.  The plant has effected a great improvement in
water quality delivered to the system.  Water color at the plant has been
reduced from 10-30 to 2 units or less.  Iron and manganese have been removed.
Continuous activated carbon treatment has removed undesirable tastes and
odors from the water.

Treatment facilities, *0peration, Costs, Water quality, Water purification,
Waste water treatment, Iron, Activated carbon, Odor, Taste

Manganese, *Rockville Water Treatment Plant, Rockville, Connecticut, Startup
104J

BORON RELEASE FROM DEIONIZERS,

Paul, J. L., and Thornhill, W. F.

California University,
Department of Environmental Horticulture

Industrial Water Engineering, Vol. 11, No.  1,  p 6, January/February,  1974.

The release of boron from deionized water and its pollution and toxicity effects
are discussed.  When water is used for irrigation, it is necessary to consider
boron concentration in assessing water quality because boron is toxic to plants
at 1 ppm or more in irrigation water.   Deionized water, produced from a mixed
bed unit, was used for irrigating greenhouse plants and scattered but recurring
cases of boron toxicity were noted.  Samples of deionized water collected
just before and during breakthrough and analyzed for boron, pH, and electrical
resistance showed that boron reached a maximum concentration of 15 mg/liter.
Most pljant species die if irrigated continually with this concentration.

*Boron, *Toxicity, *Plant pathology, Water quality, *Irrigation, Water,
Ion exchange, Distillation

*Deionized Water
                                     728

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 105J

 A FOSSIL PLANT ENVIRONMENTAL IMPACT  STUDY,

 Sloth,  E.,  and Locke,  M.

 Nebraska Public Power  District

 Power Engineering,  Vol.  78,  No.  4, p 52-55,  April,  1974.

 The  Environmental  impact  study  made  by  the Nebraska Public  Power  District
 for  the proposed fossil  fuel plant at Sutherland  Reservoir  is  discussed.  The
 studies are of much the  same nature  and scope  as  for  a nuclear plant with a
 few  exceptions: radioactivity  measurement is  deleted, and  programs for base-
 line S02 and particulate  natter measurements and  monitoring are instituted.
 A program of metering, sampling,  counting, analyzing  and  logging  has been
 underway about a year.   It will be about  5 years  before the plant goes into
 operation.   During  that  time, the gathered data and deductions from it will in-
 dicate  the  relative vulnerability of various targets  to various plant in-
 fluences.   The data will  indicate sampling frequencies that should be increased
 or decreased,  and  it will disclose the  presence of  cyclical and irregular
 fluctuations in biota  counts.

 *Fossil fuels,  Sampling,  Reservoirs,  Measurement, Analysis

 *Environmental impact  studies,  Nebraska Public Power  District
106J

IMPACT OF BEACH NOURISHMENT ON DISTRIBUTION OF EMERITA
TALPOIDA, THE COMMON MOLE CRAB,

Hayden, B., and Dolan, R.

Virginia University, Charlottesville, Virginia

Journal of the Waterways Harbors and Coastal Engineering Division, Vol. 100,
No. WW2, p 123-132, May, 1974.  7 fig, 1 tab, 10 ref.

Since the 1969 National Environmental Policy Act was passed, ecological impacts
of engineering projects on such wildlife as the crab have become practical and
legal necessities.  Emerita talpoida was experimented with at a Cape Hatteras,
North Carolina beach-nourishment program.  On the discharge of nourishment ma-
terials it was found:  the sands are transported across and down the beach via
swash and longshore currents; E. talpoida move down the beach, and result in
increased densities at one location; at termination of discharge, recovery takes
between three days and a week or two.  Mole-crab population here experienced a
migration rather than massive mortality.  High hydrogen sulfide levels are
postulated as cause for a temporary drop in population level.  Redistribution of
the population is the significant conclusion.

*Crabs, *Ecological distribution, *Hydrogen sulfide, Beaches, Legal aspects,
Sands, Currents, Wildlife management

*National Environmental Policy Act  (1969), *Ecological impact, Cape Hatteras,
North Carolina, Beach-nourishment, Emerita talpoida  Mole-crabs, Engineering
projects
                                   729

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10 7 J

RECENT DEVELOPMENTS ON WATER POLLUTION LEGISLATION,

Sacks, B. R.

Environmental Protection Agency, Region I, Boston, Massa-
chusetts, Permits Branch

The Journal of the Leather Chemists Association, Vol. 69, No. 4, p 133-142,
April, 1974.

Recent water pollution legislation has changed the approaches to effluent prob-
lems from both a technical and an economic point of view.  The present status
of the Permits Program and industry standards for effluent are reviewed in re-
lation to regulation of the leather industry.  Topics covered include:  history
of pollution legislation, municipal pollution, industrial pollution, national
standards of performance, water quality standards, enforcement, permits and
licenses, tannery wastes, and cost recovery.

*Effluents, *Water pollution, Tannery wastes, legislation, Coats

*Water pollution legislation, Permits Program, Industry standards, Municipal
pollution, Industrial pollution
108J

ENVIRONMENTAL PROTECTION AND ENERGY CONSERVATION GO
HAND-IN-HAND,

United States Energy Resources

Coal Age, Vol. 79, No. 4, p 113-116, April, 1974.  2 fig, 2 tab.

Major energy-environmental interfaces and problems are discussed.  Mining
industries, especially base metal producers such as aluminum, copper, lead,
zinc, are viewed by EPA as major sources of industrial pollution.  The impact of
new "clean" energy sources is proposed.  Auto emmissions standards are a contro-
versial issue, both for tuning up old cars and for the prohibitive consumer
costs of anti-pollution devices for new models.  Shifting patterns in electricity
use and the need for energy conservation, including drastic changes legislated
by Congress are also noted.

*Energy, *Environmental effects, *Mining, Conservation

Environmental Protection Agency, Industrial pollution, Auto emissions standards
                                       730

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109J

A TANNER LOOKS AT THE FEDERAL WATER POLLUTION CONTROL ACT
AMENDMENTS OF 1972,

Smith, W. L.

R. J. Widen Company, North Adams, Massachusetts

The Journal of the Leather Chemists Association, Vol. 69, No. 4, p 157-174,
April, 1974.  3 fig.

Costs and technical requirements as ramifications of the new law must be con-
sidered by the individual tanner at his plant.  This is essential when discharg-
ing into an existing municipal sewage treatment plant or in planning a tie into
a proposed municipal system.  Treatment of effluents by the individual tanner
is discussed in a lengthy transcript of a panel discussion.

legislation, *Sewage treatment, *Ef fluents, *Costs, *Tannery wastes, Municipal
wastes

Federal Water Pollution Control Act, Sewage treatment plant
110J

NITROGEN:  A PROBLEM OF DECREASING DILUTION,

Scorer, R.

Imperial College, London, Department of Mathematics

New Scientist, Vol. 62, No. 895, p 182-184, April 25, 1974.  2 fig.

Nitrogen pollution levels in the Thames and Lee rivers in Great Britain have
risen due to population pressures.  Drinking water must be kept under 11.3
mg of nitrogen per litre in order to be potable for babies.  Adult limits are
about 20 mg nitrogen per litre.  The use of river water in towns and the popula-
tion served by sewage works have both increased.  An additional problem is
warm winters, such as 1973-1974, where a greater fraction of the waste became
nitrate, rather than going into the air as ammonia.  This paper does not propose
any solutions, except that population growth must not continue due to the
danger of nitrogen pollution.

*Nitrogen, *Rivers, *Nitrates, Human populations, Environmental effects, Potable
water, Water pollution

Nitrogen pollution, Thames and Lee Rivers, Great Britain
                                       731

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    111J

    WATER TREATMENT CHEMICALS,

    Indian Chemical Journal,  Vol.  8,  No.  6,  p  40,  December,  1973.

    A new range of water treatment chemicals,  called the Belgard 800  range has been
    introduced by the  Industrial Chemicals division of Ciba-Geigy  (UK)  Ltd.  All,
    except Belgard 880 and 881,  are based on a low molecular weight polymeric car-
    boxy lie acid.  There are  seven chemicals in the range,  two for boiler treatment
    applications and five for use  in  water recirculation systems.  Of the later five,
    types 880 and 861  are for use  as  scale control additives and act  as threshold  and
    crystal distortion agents,  giving a physical as well as  chemical  action;  types
    881 and 883 are corrosion inhibitors  without the inherent disadvantages of
    chromates of polyphosphates; and  type 880  is a pretreatment formulation designed
    to passivate the water wetting surface of  cooling systems, and give rapid con-
    ditioning of the system prior  to  its  treatment with Belgard 881.   The two chemi-
    cals  for steam raising boilers, types 850  and  851, were  developed to deal with
    problems arising from the deposition  of  hardness scale and sludge in the  feed
    system and the boiler.  All  seven grades meet  the modern day requirements of
    industry, such as  ease of application, reliability and economy, and extend the
    inservice operation of the plant  and  reduce downtime for cleaning.

    *Water treatment,  *Chemicals,  Organic acids, Polymers, Boilers, Recirculated
    water, Corrosion control, Water cooling, Sludge

    United Kingdom, India,  Carboxylic acid
112J

ASH-HANDLING SYSTEM ELIMINATES RUNOFF POLLUTION,

Electrical World, Vol. 181, No. 4, p 50-51, February, 1974.   5 fig.

The elimination of runoff from the ash handling operation at Niagara Power Cor-
poration's Dunkirk Station to meet newly adopted local water quality standards
is described.  The water was recirculated to sluice pumps, commercially accep-
table dry ash was generated, and a means for disposing of that ash was provided.
The system is highly automated and requires less operator attention than the
previous ash handling method.  In addition to eliminating pollution, the new
system permits townships to use the bottom ash on roads.   Before installation
of the system, ash from the settling ponds had to be loaded into trucks with
a front end loader which took considerable time.  Now dump trucks can be filled
almost instantaneously.  Most of tfie ash is now used by local municipalities
for road construction, the rest is being used as cover at a fly ash landfill
location.

*Runoff, *Water quality standards, Automation, Solid wastes, Waste disposal,
Sluices, Pumps, Recirculated water, Water pollution control

*Ash
                                        732

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113J

SANITARY LANDFILL THREATENS LAKE,

Water and Pollution Control, Vol. 112, No. 3, p 12-14, March, 1974.

The threat of the sanitary landfill operation of Dartmouth to Black Lake is
discussed.  The landfill could destroy the lake if the landfill is allowed to
continue without safeguards according to the Dartmouth Lakes Advisory Board
(DLAB).  The landfill is located in an area slated to have industries situated
there is the future.  The landfill operation is heading rapidly towards the
lake and could soon be spilling into it unless protective measures are taken.
There are plans to build an earth berm at the bottom of the mound of landfill,
designed to protect the lake, but members of the DLAB do not think that will be
sufficient.  There is evidence that some erosion is taking place and if the
berm is made of raw earth, there would be soil runoff in heavy rains.

*Landfills, *Lakes, *Damages, Erosion, Runoff

Canada, Berm, Black Lake (Canada), Dartmouth, Canada, Dartmouth Lakes Advisory
Board
  114J

  TOXICITY OF SODIUM NITRILOTRIACETATE (NTA) TO THE FATHEAD
  MINNOW AND AN AMPHIPOD IN SOFT WATER,

  Arthur, J. W., Lemke, A. E., Mattison,  V. R., and Halli-
  gan, B. J.

  Environmental Protection Agency,  Duluth, Minnesota, Na-
  tional Water Quality Laboratory

  Water Research, Vol. 8, p 187-193, March, 1974.   7 tab, 11 ref.

  The toxicity of sodium nitrilotriacetate (NTA)  to Amphipods,  Gatnmarus pseudo-
  limmaeus Bousfield and fathead minnows, Pimephales promelas Rafinesque was in-
  vestigated by submitting them to  acute  (96 h) and chronic (generation-cycle)
  bioassays.  All measurements are  reported as Na3NTA.  The average 96 h TL50
  values under flow through conditions were 98 nig/liter NTA for the amphipod and
  114 mg/llter for the fathead minnow. The acute  toxicity of NTA was caused in
  part by the high pH resulting from the  addition  of large amounts of NTA (greater
  than 100 mg/liter) to soft water.   Controlling pH reduced the lethality of NTA
  by at least one half to fathead minnow  larvae.   The chronic no effect level of
  NTA to the amphipods was 19 mg/liter; in fathead minnows, it exceeded the highest
  exposure level (greater than 54 mg/liter).

  *Toxicity, *Amphipoda,  *Minnows,  Bioassays,  Hydrogen ion concentration, In-
  vestigations, Lethal limit, Analytical  techniques

  *Sodium nitrilotriacetate, *Plmephales  promelas  Rafinesque, *Gammarus pseudo-
  limnaeus Bousfield, Exposure studies, Fathead minnows
                                       733

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   115J

   EFFECTS OF COPPER, ZINC AND CADMIUM ON SELANASTRUM CAP-
   RICORfTOTUM,

   Bartlett, L., Rabe, F. W., and Funk, W. H.

   Idaho University, Moscow, Idaho, Department of Biological
   Sciences

   Water Research, Vol. 8, p 179-185, March, 1974.  8 fig, 3 tab, 12 ref.

   The algicidal and algistatic effects of copper, zinc, and cadmium on Selanastrum
   capricornutum, a unicellular green algae were analyzed by using a modification
   of the Algal Assay Procedures Bottle Test.  Algicidal concentrations of  copper,
   zinc, and cadmium were 0.30, 0.70, and 0.65 mg/liter.  Treatment of Selanastrum
   with various concentrations of the metals resulted in similar  growth rates
   characterized by extended lag growth phases.  Combinations of  the metals were
   similar in toxicity to equal concentrations of zinc.  Combinations of  copper
   and cadium resulted in a  greater growth rate  than equal concentrations of  cop-
   per suggesting that cadmium inhibits copper toxicity.  Selanstrum was  able to
   exist in waters from the  upper South Fork and North  Fork of  the Coeur  d'Alene
   River where  zinc and other metals were in low concentration.   However, the
   algae was not able to tolerate zinc concentrations greater than 0.5 mg/liter
   from waters  of other parts of the drainage.   These observations were consistent
   with laboratory findings where 0.7 mg/liter zinc was algicidal and 0.1 mg/
   liter inhibited the growth of Selanastrum.

   *Chlorophyta, *Copper, *Zinc, *Cadmium, Investigations, *Toxicity, Algicides,
   Growth rates, Analysis, Algae

   *Selanastrum capricornutum, Great Britain, Coeur d'Arlene River
116J

DETERMINATION OF NITRATE IN WATER WITH A NEW CONSTRUCTION
OF ION-SELECTIVE ELECTRODE,

Hulanicki, A., Lewandowski, R., and Maj, M.

Warszawa University, Poland, Institute of Fundamental
Problems in Chemistry

Analytical Chimica Acta, Vol. 69, No. 2, p 409-411, April, 1974.  3 tig, 2 tab,
6 ref.

A new design of the liquid state electrode for nitrate ions is proposed.  It
contains a porous wick soaked with the liquid ion-exchanger, and has no internal
reference solution.  This electrode was used for nitrate determination of tap
water at the level 8-10 ppm.  The effects of chloride and hydrogencarbonate
are eliminated by the addition of silver sulfate and a phosphate buffer,
which also maintains constant ionic strength.  Precision of a series of measure-
ments is better than 2%, but the results show differences up to 10% compared
to the colorimetric brucine procedure.

*Nitrate, *Electrodes, Ions, Investigations, Water analysis, Design data, Ion
exchange, Analytical techniques, Phosphates

Poland, Netherlands, Silver sulfate
                                      734

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117J

STUDY OF CARBOHYDRATE  SOLUBILIZATION FROM SEWAGE SLUDGES,

Owen, S. G. H.  and Lamb, R.

Holywell R. D.  C., Flintshire,  England

Water Pollution Control, Vol.  78, No. 1, p  114-120,  1974.   8  fig, 17  ref.

Carbohydrate  solubilization  from sewage sludges was  investigated to examine:
the degree of solubilization of carbohydrates  occurring  from  the sludge  to  the
sewage  liquid;  the changes in carbohydrate  concentration in the liquid isolated
from the sludge;  and some of the factors which may  influence  these processes.
Although dilution was  important, there was  a tendency  for the same concentration
of carbohydrates to dissolve into the liquid no matter what the dilution.   The
time of contact between  the  liquid  and the  sludge was  important, with more  car-
bohydrates solubilizing  out  into the liquid the longer the time of contact, at
least up to the 18th day, if the sludge and liquid were  not mixed.  Mixing  of the
sludge  and liquid was  important, although after an  initial large  increase in
concentration within the first  day,  the rate and pattern of solubilization  in a
mixed sample  was similar to  that in the unmixed sample.   The  age of the  sludge
affected the  quantity  of carbohydrates dissolving into the liquid; the fresher
the sludge, the greater  the  amount  of solubilization.  Temperature had little
effect  on the process, although a low temperature of 2 C tended to slow  down
the process.   The initial pH of the system  was not  important. There  was a
50% reduction in carbohydrate concentration if the  sludge liquid was  kept out
of contact with the sludge for one  day.

*Carbohydrates, *Sewage  sludge, *Solubllity, Investigations,  Sludge,  Mixing,
Hydrogen ion  concentration,  Age, Liquids

England
118J

THE HYDROLYSIS OF UREA IN RIVERS,

Stiff, M. J., and Gardiner, D. K.

Water Pollution Research Laboratory, Department of the
Environment

Water Treatment and Examination, Vol. 22, No. 4, p 259-268, 1973.  4 fig, 3 tab,
4 ref.

Laboratory and field tests were conducted to establish whether the hydrolysis of
urea might occur in rivers during winter conditions when urea would be used to
prevent the formation of ice on airfield runways.  The results show there is a
likelihood that the hydrolysis of urea will take place in rivers in winter time.
The rate of hydrolysis appears to depend on local conditions and at present not
enough is known about the appropriate variables to make any generalization.
Therefore, the rate at which hydrolysis would occur in any particular river can
be estimated only by experiments involving the water and bottom deposits of
that river.  Because of the relatively short residence time of rivers in the
United Kingdom it is unlikely that complete hydrolysis of urea will take place,
in which case the urea nitrogen load would not appear as ammonia at waterworks
intakes.  Further hydrolysis could occur during residence in reservoirs, but
quantification is possible only by examination of particular cases.  In river
waters examined there is invariably a measurable concentration of urea ranging
from 0.01 to 1 mg N/lit:er.  The addition of urea to rivers from airfields will
not therefore introduce any substance foreign to river waters although it could
lead to an unusually high concentration.

*Winter, *Ureas, *Rivers, Laboratory tests, On-site investigations, Ice,
Hydrolysis, Water pollution sources

United Kingdom, Airports
                                      735

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119J

CHEMICAL POLLUTION OF GROUND WATERS,

Kaufman, W. J.

California University, Berkeley, California

Journal American Water Works Association, Vol. 66, No. 3, p 152-159, March,
1974.  8 fig, 6 tab, 21 ref.

The chemical pollution of groundwaters is discussed and the major pollutants are
described.  Direct chemical groundwater pollution results from the introduction
into aquifers of waste waters containing pollutants or substances that may in-
duce chemical changes or that are themselves modified such that pollutants are
generated.  Indirect pollution is generally attributed to overpumping or excessive
depletion of the groundwater source such that unwanted, naturally present min-
eral constituents are drawn into the aquifer from deeper formations.  In this
context, increasing salinity is the most common problem.  There are at least
26 sources of groundwater pollution, essentially all of them are potential
sources of direct or indirect chemical pollution.  From a public health stand-
point, nitrate pollution is probably the most important, although public con-
cern for pesticides has placed them a close second.  Other principal pollutants
are petroleum products, especially gasoline, detergents, and heavy metals.

*Water pollution sources, *Groundwater, *Nitrates, *Petroleum, *Pesticides,
*Heavy metals, *Detergents, Nitrogen, Soils, Aquifers, Organic compounds,
Inorganic compounds, Gasoline, Fertilizers, Waste water, Organic matter, Dairy
industry, Wastes, Mineralogy
120J

NO RADIOACTIVE FISH IN LAKE MICHIGAN,

Industrial Research, Vol. 16, No. 3, p 22, 25, March, 1974.

The results of a study on radioactivity in Lake Michigan are discussed.  Al-
though environmentalists continue to push for greater precautions for nuclear
reactors, a study issued by Environmental Research Group, Inc. reports that,
even if the worst leakage allowed by the AEC were to occur from power plants
around Lake Michigan, radioactivity in the lake's fish would not build up to a.
point higher than half the permissible level.  Radioactivity from most isotopes
in edible fish caught in the immediate vicinity of a nuclear power plant dis-
charge would be practically none by the time the fish was consumed.  In the
case of iodine, for example, the highest level reached would be 5.5% of their
permissible level.  Moreover, the radioactivity would eventually be removed from
the lake waters through burial in sediment or removal in food products.

*Radioactivity, *Lake Michigan, Radioisotopes, Fish, Investigations, Computers,
Water pollution sources, Water pollution effects
                                         736

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  121J

  MANY PURPOSES THE MIAMI CONSERVANCY DISTRICT AS A SOCIAL
  INSTRUMENT,

  Wolman, A.

  John Hopkins University, Baltimore, Maryland

  Journal American Water Works Association, Vol. 66, No. 3, p 139-141, March, 1974.

  The history and purpose of the Miami Conservancy District are discussed with
  emphasis on its application as a social instrument.  The District was formed
  in 1913 after a disastrous flood.  It exemplified an epic of achievements in
  innovating processes of government, of engineering, and of social organization.
  These essential elements for progressive encounter with new goals are still cur-
  rent.  The aims of the District are to plan for the full development of the
  water resources; to develop intelligent bookkeeping of them; to engage in
  stream beautification; and to design, construct, maintain, and operate where
  appropriate waste treatment facilities.  The District will move from a relatively
  static custodial position to a dynamic total river management, and a $100
  million waste water improvement complex.  The District will expand in function
  and in geographic boundary as it is necessary to maintain its purpose.

  *Social function, *Social participation, History,  Florida

  *Miami Conservancy District
122J

AN EXPERIMENT ON DISPOSAL OF METAL WORKING OIL EMULSION
INTO SEWER SYSTEMS (Kinzoku kakoyu no haisui shori ni kan-
suru ichi jikken),

Izumi, K. and Nagamori, H.

Kao Soap Company, Tokyo, Japan, Industrial Research
Laboratories

Junkatsu (Journal of the Japanese Society of Lubrication Engineers), Vol. 19,
No. 3, p 32-40, March, 1974.  6 fig, 4 tab, 12 ref.

An anode oxidation procedure for the disposal of metal working oil emulsion into
sewer systems was developed to decompose emulsifiers followed by short time
settling to separate the oil from the water.  The procedure can be used in
laboratories or in machine shops of small size where small quantities of emul-
sions need to be disposed of and where independent sewer systems of large capa-
city cannot be justified.  A platinum (and/or ruthenium) plated sintered glass
filter was used to make the equipment compact and to reduce man power to re-
place the anode due to corrosion.  There was a 95% removal of organic matter
from the drainage water although the flow rate of the emulsion was too low to be
practical.  Changing the shape and the structure of the electrodes will
probably increase the flow rate.

*Waste disposal, *0il, *Emulsions, Investigations, Sewerage, Industrial wastes,
Equipment, Electrodes, Anodes, Oxidation, Corrosion control, Flow rates, Or-
ganic matter

Japan, Platinum, Ruthenium
                                         737

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123J

FORGING THE MISSING LINK,

Webster, L. F.

Water and Pollution Control, Vol. 112, No. 3, p 42-45, March, 1974.  3 ref.

A study aimed at using high nutrient wastes as an integral part of a contrived
food chain sequence is described.  Dr. John Ryther of the Woods Hole Oceano-
graphic Institution is working on a project which anticipates the controlled
feddlng of raw domestic sewage to a marine environment.  This would promote the
growth of specific types of algae that would be eaten by shellfish.  The
wastes of these shellfish then serve as food for sea worms that are, in turn,
consumed by succeeding orders of fish higher in the food chain which, in turn,
form part of a human diet.  Undesirable elements would be trapped, or removed
from the system elsewhere—viruses through containment in the shellfish;
ammonia, and phosphate growth of other selected algae and seaweeds.  This
would establish a complex, multi-species food chain which would serve the
dual function of a tertiary sewage treatment process and an aquiculture system
producing a primary crop of shellfish and secondary crops of other potentially
valuable marine organisms.

*Food chains, *Nutrients, *Wastes, Ecosystems, Shellfish, Nitrogen, Phosphorus,
Investigations, Sewage, Effluents, Algae, Sea water, Mollusks, Organic wastes,
Domestic wastes, Aquiculture, Tertiary treatment

Woods Hole Oceanographic Institution, Massachusetts
 124J

 OZONE TREATS ARCTIC WATERS,

 Reid, L. C., and Potworowski, H. S.

 Arctic Health Research Centre, Fairbanks, Alaska, Envi-
 ronmental Sciences Branch

 Water and Pollution Control, Vol. 112, No. 3, p 53-55, March, 1974.  6 fig, 2 tab.

 The application of ozone as a useful water conditioner for cold water sources
 was investigated by the Arctic Health Research Centre for water supplies in
 Alaska.  It is feasible to use ozone for iron, manganese, organics, and color
 removal in cold waters.  From the results obtained in the study, it would ap-
 pear that ozone may be the answer to the need for better iron and manganese
 removal from arctic water suppliers.  If the water is of acceptable hardness
 after removal of iron and manganese, the only treatment of the raw water would
 be for ozonation, sedimentation, and filtration.  The resulting water would
 be free of odors and obnoxious tastes, and would be clear.  Staining of clothes
 and fixtures would be eliminated.  A side benefit of the ozonation process would
 be the purification.  It is recommended that an attempt be made to develop a
 pilot ozonation plant that would treat groundwater for removal of iron, manga-
 nese, color, and organics.

 *Water purification, *0zone, *Arctic, iron, Manganese, Organic matter, Color,
Water treatment, Investigations, Filtration, Sedimentation, Tastes, Ground-
water, Alaska
                                         730

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125J

SUBMERGED AERATORS ARE HOT,

Winter, R. L.

Philadelphia Mixers Corporation, King of Prussia, Penn-
sylvania

Water and Wastes Engineering, Vol. 11, No. 3, p 37-38, 69, March, 1974.

The advantages and applications of submerged turbine aerators are described.
The systems are particularly economical to use where land costs are relatively
high because they can provide higher intensities than surface aerators.  The
aerators offer flexibility for changing the performance characteristics of
the installation.  A submerged unit can be easily modified to generate and dis-
tribute a larger volume of air than originally designed for.  The basins take
up considerably less space than surface aerators and they are highly effective
in dispersing oxygen through the aeration basin.  Their oxygen utilization is
at least 20% which is four times as high as the diffused air types.  The
submerged systems are highly efficient due to the combination of pressured
diffusion with that of mechanical mixing, the saturation level of the liquid
being mixed, and the compact design of the basins.

*Waste water treatment, *Aeration, *Waste water disposal, Underground struc-
tures, Costs, Flexibility, Mixing, Oxygenation, Basins

*Aerators
126J

PROJECTS, IDEAS FOR ENVIRONMENTAL MANAGEMENT,

Water and Pollution Control, Vol. 112, No. 3, p 32, March, 1974.

The City of Sudbury, the Ontario Environment Ministry, and the International
Nickle Co. of Canada, Ltd. are currently experimenting together for a means of
disposing of digested sewage sludge for the city's new water pollution control
plant.  About 150,000 gallons of sludge have been dumped each week on test plots.
This is equivalent to 1800 cu yd of sludge spread monthly by trucks working 5
days a wk.  The test plots include both vegetated and nonvegated areas to
enable collecting data on a controlled basis.  The plot sizes vary but all to-
gether encompass approximately 50 acres.  The experiment will evaluate dif-
ferent types of vegetation which may or may not produce 2nd generation growth
mutations.  The organic waste oxidizes slowly and releases nutrients in addi-
tion to acting as a pH control.  Limestone is the principal additive reaching
the tailings area.  Natural composition is mainly silica, iron and those minerals
found in granite rock.  The average depth of sludge penetration into the tail-
sings has yet to be assessed.  There is still uncertainty as to the benefits
which the sludge will contribute.

*Sludge disposal, Treatment facilities, Sewage, Sludge treatment, Sludge,
Investigations, Organic wastes, Oxidation, Limestones

Sudbury, Ontario, Canada
                                        739

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 127J

 PROCESS DESIGN AND OPERATION FOR ZERO EFFLUENT DISCHARGE,

 Hendrickson, E. R., and Oglesby, H. S.

 Environmental Science and Engineering, Incorporated,
 Gainesville, Florida

 Technical Association of the Pulp and Paper Industry, Vol. 57, No. 4, p 71-73
 April, 1974.  8 ref.

 The Federal Water Pollution Control Act Amendments of 1972 declared the national
 goal to be that the discharge of pollutants into navigable waters be eliminated
 by 1985.  This is commonly referred to as "zero effluent discharge."  A kraft
 mill, for example, will require a combination of reduction of waste water gener-
 ation, maximizing reuse of waste water streams, and development and application
 of unique new treatment techniques.  Among the process measures which look
 promising to reduce waste water discharges are:  increasing pulp washing effi-
 ciency, closing brown stock screening, oxygen or other bleaching, increasing
 dilution in washing, stripping condensates, collecting chemical spills, col-
 lecting fiber spills, and dry barking.  It may be possible to maximize reuse
 of waste water streams and recover the chemicals.  Most of these are in the
 early development stages and some consist only of isolated unit processes.


 *Federal Water Pollution Control Act,  *Water pollution, *Effluents, Water
 reuse, Water treatment,  Industrial wastes, Legislation, Washing, Bleaching
wastes, Screening, Dilution, Chemicals,  Treatment,  Waste water

 *Zero effluent discharge,  Water reclamation,  Amendments to Federal Water Pol-
 lution Control Act, 1972,  Pulp washing efficiency
 12 8 J

 METHODS FOR THE DIRECT DETERMINATION OF HEAVY-METAL POL-
 LUTANTS IN THE ENVIRONMENT,

 Wolcott, D. K.

 The Louisiana State University and Agricultural and Me-
 chanical College, Louisiana

 Dissertation Abstracts International, Vol. 34, No. 9, p 4257, March, 1974.

 In order to determine the  concentration of heavy metal pollutants in the eco-
 logical biosphere, large samples must be collected and/or there must be a pre-
 analysis concentration step.  A need exists for experienced personnel.  A de-
 vice has been designed for the direct determination of heavy metal pollutants
 by atomic  absorption spectroscopy.  This uses a carbon bed atomizer for the
 reduction  of metal pollutants to free atoms, and a heated quartz long path
 absorption tube  to maintain  the atoms in the light path in the free atomic
 state.  Use of the instrument includes determination of cadmium in the atmosphere,
 in seawater,  in  biological fluids,  in filter papers, and in plastics.  It is
 also  calibrated  for  air  analysis.   Attempts are being made to eliminate con-
 tamination in calibrating  media.

 *Heavy metals, *Pollutants,  *Ecology, *Cadmium, Liquid wastes, Oxidation-reduc-
 tion, Analytical techniques, Biosphere, Plastics, Filter paper, Fluids

 Pre-analysis  concentration,  Optical paths
                                    740

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129J

METHYLATION OF MERCURY IN LAKE AND RIVER SEDIMENTS DURING
FIELD AND LABORATORY INVESTIGATIONS,

Mohsin, M.

McGlll University, Canada

Dissertation Abstracts International, Vol. 34, No. 9, p 4156, March, 1974.

The objectives of this study were to determine the amount of methyl-mercury
(MeHg) that is produced in the sediments of two contrasting river environments
when these sediments were treated with mercuric or phenylmercuric salts, and
to determine the amount of MeHg formed in dissimilar lake and river sediments
and the characteristics which affect the production and accumulation of MeHg.
On-site experimentation was performed at two river sites by sample retrieval
of bulk sediment.  These samples were analyzed for total Hg using an aqua regia
digest and flameless atomic absorption spectrophotometry.  Results indicate
that Hg losses from stationary sediments are minimal and that sediment trans-
port is the major source of Hg movement in a river system.  In laboratory
tests, intact sediments from two lakes, one oligotrophic and one eutrophic, and
two polluted rivers were treated with PhHgAc and incubated for up to 14 days
under anaerobic or aerobic conditions.  The amount of MeHg formed in the four
sediments differed and seemed to be related to the amount of sulfide present
and the general biological activity of the sediments.  Biological pathways
producing MeHg and methane did not seem to be directly related.

*Mercury, *Methane, *Pollution, *Rivers, Lakes, On-site investigation, Anaero-
bic conditions, Aerobic conditions, Absorption, Biology, Ecology, Laboratory
tests, Sedimentation, Investigation

Methylation, Methyl-mercury, Aqua regia, Oligatrophic conditions, Eutrophic
conditions, Atomic absorption spectrophotometry
130J

QUALITY OF WATER DISCHARGED FROM TWO AGRICULTURAL WATER-
SHEDS IN SOUTHWESTERN IOWA,

Burwell, R. E., Schuman, G. E., Piest, R. F., Spomer,
R. G., and McCalla, T. M.

U. S. Department of Agriculture, North Central Watershed
Research Center, Council Bluffs, Iowa

Water Resources Research, Vol. 10, No. 2, p 359-365, April, 1974.  5 tab,
15 ref.

The quality of water discharged from a 157.5-ha diversified conservation-
farmed watershed in southwestern Iowa was within acceptable limits for po-
table water except for the levels of ammonia, inorganic phosphorus, and coli-
form.  Total coliform levels exceeded the established criteria on two occa-
sions, and fecal coliform once during the study.  Nutrient concentration was
high occasionally, but the nutrient quantities discharged from the watershed
were low, the effectiveness of the level-terrace system in controlled surface
runoff and erosion thus being shown.  Atrazine residue in the runoff and
sediment was detected in only one sample.  Even though several chlorinated hydro-
carbon and organophosphate compounds had been applied to the watershed, none
was detected in runoff or sediment.  A two year study comparing data from a
33.6-ha contour-farmed watershed with the data from a 157.5-ha well-planned
conservation watershed showed the benefits and necessity of using some means
of controlling runoff and erosion to prevent loss of agricultural chemicals
that might degrade surface waters.

*Water quality, *Watershed management, Conservation, Coliform levels, Inor-
ganic compounds, Watersheds, Runoff, Sediments, Data, Ammonia, Agricultural
runoff, Hydrocarbons

Iowa, Inorganic phosphorus, Level-terrace system
                                       741

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131J

THE PUDSEY PROJECT,

Barker, R. P., Hurst, G., and Rock, B. M.

Civil Engineering, p 30-31, April, 1974.

Research and development by the Wool Industry Research Association (WIRA) and
the water pollution control department of the Pudsey Borough Council has been
carried out to see how sewage effluent might be used for wet processes.  It
was generally thought that a very high quality of water was required for wool
textile industry wet processes.  However, the mass of data collected here in-
dicates that sewage works effluent agrees with the specifications—iron 0.5
mg/liter, manganese 0.1 mg/liter, total hardness of 50 to 100 rag/liter as CaC03.
They do not agree reasonably with turbidity, color, and suspended solids.  How-
ever, after suitable filtration and chlorination it seemed that the effluent
waters would meet these standards.  From laboratory and mill based trials,
it was concluded that the wet processes at the mill could be carried out using
effluent from Pudsey Works.

*Water quality, *Effluents, *Sewage, Textiles, Research and development, Water
pollution control, Water quality standards, Suspended solids, Turbidity, Fil-
tration, Chlorination, Mills

Pudsey Works (England), Wool textile industry, Textile mills
132J

REUSE AND RECYCLE OF WATER IN INDUSTRY,

Appleyard, C. J., and Shaw, M. G.

Bostock Hill and Ribgy, Limited, Birmingham, England

Chemistry and Industry, No. 6, p 240-246, March 16, 1971.  2 tab, 10 ref.

Water reuse or recycle both reduces the requirement of raw water and reduces
the volume of effluent which has to be subsequently disposed of as well as the
size of any treatment plant required.  In industry, in order to utilize water
reuse, a balance must be drawn up followed by a detailed survey to indicate:
whether the effluents are suitable for reuse or recycle with or without treat-
ment; whether water is being used unnecessarily; the minimum, average, and
maximum quantity of water required; frequency of use; nature and amount of
contamination picked up; and nature of treatments required.  Industries dis-
cussed include the food industry, the electronic industry, the semi-conductor
industry, the manufacture of television tubes, the textile industries, cooling
water reuse, steel works and problems related specifically to each.  Treat-
ments included removal of particulate matter or phase separation, removal of
dissolved inorganic ions, and removal of soluble organic material.  It was
concluded that in almost every industry recycle or reuse of water must be
accomodated in the future for both economics and conservation.

*Water reuse, *Recycling, *Industries, *Treatment facilities, Food processing
industry, Textiles, Dissolved solids, Costs

"Treatment methods, Phase separation, Organic material removal, Electronic
industry, Television tubes, Steel works
                                     742

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133J

NOVEMBER 1972 FLOODS ON THE LOWER GREAT LAKES,

Brazel, A. J., and Phillips, D. W.

Windsor University, Ontario, Canada, Department of
Geography

Weatherwise, Vol. 27, No. 2, p 56-62, April, 1974.  6 fig, 2 tab, 7 ref.

Public and political outcry was noted in 1972 due to high water levels on
the Great Lakes.  Extensive flood damage had occurred for which individuals,
industries, and governments were blamed in the media.  This study gives a
meteorological analysis of the flooding, wave action, wind set-up and seiche,
both over time and for various portions of specific lakes.  Shoreline damage
and structural weakening of shorefront structures, geomorphological damage,
harmful effects to wildlife, agriculture, and sewer systems cannot be measured
in costs, although measurable damage amounted to over twenty-five million dol-
lars.  The result of this investigation was the establishment of a Lake Level
Advisory and Warning Service in Toronto in 1973.  This forecasts wave heights
and potential inundation levels along the Lake Erie and Lake St. Clair shore-
lines.

*Flooding,  *Flood damage, *Flood forecasting, *Great Lakes Region, Flood waves,
Sewer systems, Costs, Investigation, Forecasting, Agriculture,  Geomorphology,
Meteorology, Canada

Lake Erie,  Lake St. Clair, Toronto
134J

DESIGN AND PERFORMANCE OF CHLORINE CONTACT TANKS,

Kothandaraman, V., and Evans, R. L.

State of  Illinois Water Survey, Urbana,  Illinois, De-
partment  of Registration and Education

Circular  No.  119.  36 p, 13 fig, 19  tab, 17 ref.

Most existing chlorine contact  tanks suffer from  serious  drawbacks  of  dead
spaces, short circuiting, and solids accumulations.  These putrefy  and exert
undue chlorine demand.  Hydraulic model  studies of chlorine  contact tanks
indicate  that air agitated, baffled  contact units have better  flow  character-
istics than just baffled units  or air agitated contact tanks without baffles.
Air agitation does not result in a loss  of total  chlorine residuals, and it
improves  the  bactericidal efficiency of  chlorination.  Air agitation elimi-
nates the problems caused by solids  accumulation  in  the contact  units.  Split
chlorination  does not appear to be an advantageous modification  in  chlorination
practice.

*Hydraulics,  *Chlorine, *Model  studies,  *Flow characteristics, Air,  Solids,
Design criteria, Bacteria, Water purification

*Chlorine contact tanks, Split  chlorination, Solids  accumulation, Baffled contact
tanks
                                        743

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 135J

 SOLUBILITIES OF CALCIUM SULFATE DIHYDRATE AT 25 C IN BRACK-
 ISH WATERS AND THEIR CONCENTRATES: EFFECT OF CALGON AD-
 DITIVE AND PREDICTIONS FOR REVERSE OSMOSIS PROCESSES,

 Yeatts, L. B., Lantz, P. M., and Marshall, W. L.

 Oak Ridge National Laboratory, Union Carbide Corporation,
 Oak Ridge, Tennessee

 Contract No. W-7405-eng-26, September 1973.  64 p, 17 fig, 21 tab, 9 ref.

 the solubility of calcium sulfate dihydrate, a substance which can impede re-
 verse osmosis (RO) processes by saturation precipitation in RO membrane pores,
 was determined at 25 C in three typical brackish water compositions and their
 concentrates.  These waters were synthetically prepared, and corresponded to
 compositions and concentrates of well waters used by the Office of Saline
 Water RO plants at Gillette, Wyoming, and Webster, South Dakota, and those of
 a post-irrigation water from the Wellton-Mohawk Canal in Arizona.  In this pre-
 sent study, a commercial solid polyphosphate preparation, Calgon, was shown when
 added in small amounts (5-40 ppm In unconcentrated solutions) to initially
 produce an apparent increase in the saturation concentration of hydrated CaS04
 (the solid phase).  Later (2-6 days), the solution concentration of CaS04
 decreased to near the expected solubilities in the absence of Calgon.  The
 method of calculation of the solubility of CaS04 and its hydrates in various
 saline waters, which has been used successfully for several years, is found
 to apply equally well to the calculation of saturation limits of hydrated
 CaS04 in the present waters and concentrates.

 *Calcium sulfate, *Reverse osmosis, *Brackish water, Saturation, Precipitation,
 Solids, Solutions, Irrigation water, Saline waters, Solubility

 *Calgon, Commercial polyphosphate, Arizone (Wellton-Mohawk Canal), Gillette,
 Wyoming, Webster, South Dakota
136J

BASE CIVIL ENGINEER SANITARY LABORATORY,

Schultz, S. E.

Air Force Academy, Colorado

National Technical Information Service, Final Report for period September 9,
1971 to April 13, 1972.  December, 1973.  105 p, 4 fig, 49 tab.

A review of research by the U. S. Air Force Weapons Laboratory describes a
number of standard water and waste water testing laboratories.  These are
equipped to support Base Civil Engineering personnel in operating treatment
plants.  An itemized list of equipment, apparatus, and reagents for each test
to be conducted are given.  Included also are floor plan drawings of the labora-
tory and an identification of utility services which are required for operation.

treatment plants, *Waste water treatment, laboratory tests, *Treatment facili-
ties, Laboratory equipment, Reviews, Standards

Reagents, Floor plans, Apparatus, U. S. Air Force Academy
                                    744

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137J

UTILIZATION OF INDUSTRIAL WASTES AND WASTE BY-PRODUCTS
FOR PHOSPHORUS REMOVAL:  AN INVENTORY AND ASSESSMENT,

Fowlle, P. J. A., and Shannon, E. E.

Environmental Protection Service, Environment Canada

Research Report No. 6, June, 1973.  85 p, 11 fig, 22 tab, 15 ref.

An inventory of waste products was compiled and several different types of
waste material produced by 48 separate Ontario and Quebec companies were evalu-
ated for phosphorus removal efficiency by jar testing procedures.  Several wastes
with varying degrees of usefulness were identified—pickle liquors, reclaimed
FeS04.7H20, mill scale, spent mine acid, carbide lime, stack precipitator
dusts, dross, red mud, and certain bag-house dusts and slags.  A dosage of
pickle liquor at 20 mg/liter as Fe gave effluent phosphorus levels consistently
less than 1 mg/liter for influent phosphorus levels varying as high as 9.3 mg/
liter.  The pickle liquor did not affect COD removal efficiency, or cause sig-
nificant changes in effluent pH or heavy metals content.  Ferric sulphate
[Fe2(S04)3] produced from a sludge incinerator ash was evaluated for phos-
phorus removal on a pilot scale (20 Igpm).   It was found that a dosage slightly
in excess of 15 mg/liter as Fe gave effluent phosphorus levels leas than 1
mg/liter.  Again, heavy metals added with the Fe2(S04)3 were accumulated in
the sludge rather than carrying over in the effluent.

*Waste products, Lime, Effluents, Chemical  oxygen demand, Phosphorus, Heavy
metals, Canada, Sludge, Laboratory tests

*Phosphorus removal, *Jar-testing, Ontario, Quebec, Feoric sulphate, Mine
acid, Pickle liquor
 138J

 HEAVY  METALS  IN AGRICULTURAL  LANDS  RECEIVING CHEMICAL
 SEWAGE SLUDGES,

 Van Loon,  J.  C.

 Toronto University,  Toronto,  Canada,  Department  of  Geolo-
 gy, Chemistry, and  The  Institute  of Environmental Sci-
 ences  and  Engineering

 Research Program  for the  Abatement  of Municipal  Pollution Within  the  Provisions
 of  the Canada-Ontario Agreement on  Great Lakes Water Quality,  Research  Report
 No. 9, March,  1973.  37 p,  2  fig, 10  tab,  6  ref.

 Potentially sewage  treatment  plant  sludges could be used as  fertilizers on
 agricultural  lands.  This would be  a  double  benefit acting as  a disposal mechan-
 ism as well as a  source of  plant  nutrients.   However, a variety of  reports have
 urged  caution in  this regard  for  fear of contaimination of the land by  other
 matrix constituents, among  these  the  potentially toxic heavy metals,.  The
 present study emphasizes  the  utilization of  standard and control  samples as
 tools  for  validating the  data obtained.  A series of reports,  most  of which
 have appeared in  the past year, describe the metal  content of  domestic  sewage
 plant  sludges and sewage  sludge fertilizers.  Researchers in several  countries
 are also developing projects  designed to study the  uptake by plants of  heavy
 metals from sludged or  otherwise  metal contaminated soils.   Selections  of
 references to ongoing work  are given  at the  end  of  this report.

 *Waste water  treatment, *Sludge treatment, *Sewage, *Treatment facilities,
 Fertilizers,  Studies, Heavy metals,  Soils, Sewage disposal,  Toxicity, Re-
 search,  Canada

 *Treatment plant  sludges, Metal contaminated soils, Toronto, Canada
                                         745

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139J

SELECTED ABSTRACTS FOR INSTRUMENTATION AND AUTOMATION OF
WASTEWATER FACILITIES,

Movlar, A. E., and Roesler, J. F.

Raytheon Company
Environmental Systems Center, Portsmouth, Rhode Island

Project No. 17110, 1973.

A collection of abstracts summarizing technical articles related to the in-
strumentation and automation of waste water treatment plants was developed.
This literature search encompassed most recognized environmental instrument
and automatic control periodicals, symposium series, and conference proceedings
published from 1967 to 1973.  In addition, scientific and engineering abstrac-
ting publications were researched for pertinent literature.  Approximately
600 abstracts collected during this investigation are classified according
to the following four categories:  Instruments, Control Experiences and Stra-
tegies, Costs, and Support Material.  These categories are further refined
into numerous subcategories.  Each entry contains a title, author, biblio-
graphic citation, abstract, and keywords.  An author index and source list
are also included.

*Instrumentation, *Automation, *Publications, Costs, Waste water treatment,
Storm water, Flow measurements, Sanitary engineering, Control

*Abstract collections, Technical articles
140J

SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES,

Davis, E. D., Editor

Saskatchewan University
Saskatoon, Saskatchewan
Civil Engineering Department

Economic and Technical Review Report EPS 3-WP-74-3, Water Pollution Control
Directorate, Ottowa, Canada, 1973.  595 p.

A collection of 28 articles was collated relating to the problems and possible
solutions of water supply and waste water treatment in cold environments.
Contributions were predominantly from Canada and the United States but five
other countries were represented as well.  Reports include both engineering
research articles, planning discussions, and some quantitative analyses

*Waste water treatment, *Cold regions, *Waste disposal, *Water supply, Sewage
treatment, Temperature, Sewage lagoons, Disinfection, Aeration, Oxidation,
Biological treatment, Chemical treatment, Facilities, Performance, Efficiencies,
Costs, Planning, Denitrification, Elevation, Water quality, Water conservation,
Anaerobic digestion, Canada, United States, Phosphorous, Chlorine, Finland,
Denmark, Sweden, Norway U.S.S.R., Extended aeration, Bubble diffuser,
Vacuum sewer system, Black water, Grey water, Psychrophiles, Mesophiles,
Floating tube settler, Clarification, Mireinfiltration
                                      746

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141J

AN EVALUATION OF WASTE DISPOSAL PRACTICES IN ALASKA VILLAGES,

Alter, A. J.

Alaska Department of Environmental Conservation

In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, Institute of Northern
Studies, University of Saskatchewan, p 1-28, August 22-24, 1973.  12 tab.

The article discusses the special problems associated with the provision
of an adequate water supply and waste disposal in cold climates.  Recommen-
dations are made as to appropriate planning procedures for communities, research
needs in the biological, chemical, and physical performance of existing
waste treatment methods and of non-frost susceptible methods in environ-
mental management, and the development of realistic, reasonable and equitable
methods of finance for supply and treatment systems.

*Water supply, *Waste disposal, *Cold regions, *Waste treatment, Environmental
control, Biological, Chemical, Physical

*Cold climates, *Alaska, Environmental management
142J

PROBLEMS OF THE CANADIAN NORTH,

Hurtubise, F. G.

Water Pollution Control Directorate,
Environmental Protection Service,
Environment Canada, Technology Development Branch

In:  SYMPOSIUM ON WASTEWATER TREATMENT IN COLD CLIMATES, Institute of Northern
Studies, University of Saskatchewan, p 75-84, August 22-24, 1973.

The role of the Canadian Environmental Protection Service is examined.  Certain
projects in the Northwest Territories in which the Environmental Protection
Service is involved with one also outlined.  These include:  a study on the use
of swampland lakes for sewage treatment; the use of vacuum and recirculating
toilet units for sewage collection with subsequent incineration disposal;
feasibility of land disposal of sewage effluent or use as fertilizer in permafrost
areas; the practicability of the use of physical-chemical and rotating bio-disc
treatment plants; the use of lagoon systems to serve isolated institutions;
and the use of plasticized paperbags to replace garbage cans.

*Canada, *Planning, *Swamps, *Lakes, *Lagoons, *Temperature, Sewage disposal,
Incineration, Fertilization, Cold regions

*Bio disc, Plasticized bags, Vacuum toilet, Recirculating toilet
                                         747

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  143J

  ALASKA VILLAGE DEMONSTRATION PROJECTS:   FIRST
  GENERATION OF INTEGRATED UTILITIES  FOR  REMOTE  COMMUNITIES,

  Reid, B.  H.

  U.  S. Environmental Protection Agency
  College,  Alaska
  Arctic Environmental Research Laboratory

  In:  SYMPOSIUM ON WASTEWATER TREATMENT  IN COLD CLIMATES,  Institute of Northern
  Studies,  University of Saskatchewan,  p  549-569,  August 22-24,  1973.   6 fig,
  11  ref.

  Under Section 20., Public Law 91-224, April 3, 1970,  Congress  authorized the
  Secretary of Interior to carry out  the  Alaska  Village Demonstration Projects
  (AVDP) .  The projects were to include,  "provisions  for community safe water
  supply systems, toilets, bathing and  laundry facilities,  sewage disposal
  facilities, and other similar facilities".   The projects  were  assigned to the
  Office of Research and Development  and  the  Arctic Environmental Research La-
  oratory.   In developing the project concept certain objectives were established,
  including:  the provision of a system of facilities that  would be simple,
  reliable, inexpensive, and yet a real improvement over existing conditions;
  provide water for domestic use that met Federal and State quality requirements;
  and treat and dispose of all wastes (air, water, solid) in such a manner as  to
  meet future Federal and State regulations.   In achieving  these goals some of
  the following processes and equipment were  used: vacuum  toilets; separation
  of  grey water from black water; physico-chemical treatment of  waste water with
  reuse in  laundering facilities; incineration of black water residue and sludge
  from waste water treatment; utilization of  incinerator heat for building heat;
  sauna heat, and clothes dryer heat.

  *Rural areas, *Community development, *Cold regions,  *Waste water treatment.
  Facilities, Costs, Water conservation,  Water demand,  Water supply, Water
  distribution, Water utilization, Incineration, Alaska

  *Community facilities, *Vacuum toilets
144J

A SOLUTION TO A SOLUTION PROBLEM,

Effluent and Water Treatment Journal, Vol. 14, No. 2, p 103-104, February,
1974.  2 fig.

Problems of design for treatment of effluents from industry must take into ac-
count costs and rising standards of pollution control.  For example, acid ef-
fluents must be neutralised and a common method of treatment is to mix a solu-
tion of lime or soda ash in correct proportion with the effluent.  The treatment
plant required for this type of process is a nonproductive capital investment.
J. T. Scotney Limited of Hull has developed a packaged unit called the composite
Solution Silo.  This consists of a cylindrical vessel, the upper section being
the powder silo and the lower section forming an insulated plant room, complete
with lockable double doors and interior lighting.  Designs have built-in alarm
systems to provide remote warning of any malfunctions.  Its purpose is to ration-
alize industrial plants and to reduce extraneous installation,  commissioning, and
maintenance costs.

*Effluents, *Industrial effluents, *Costs, *Standards, Water pollution, Treat-
ment plants, Treatment facilities, Lime, Design criteria, Maintenance, Water
pollution control, Solutions

*Solution Silo, Treatment methods
                                    748

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 145J

 SONOCO  OFFERS  NEW APPROACH TO  SULPHITE  CHEMICAL  RECOVERY,

 Paper Trade  Journal,  Vol.  158,  No.  14,  p  22-23,  April  8, 1974.   1  fig.

 A significant  development  was  made  by Sonoco  towards solving  the problem of pol-
 lution  and costs  by recovering its  sodium base spent sulphite liquors and
 marketing products produced from them.  This  spent liquor was acidified and the
 organic acids  extracted.   The  residual  liquor was also sold as a salt cake sub-
 stitute.  Burning of  the liquor was done  in the  solid  state in conventional equip-
 ment, a less costly process than ordinary recovery furnaces, using new aluminum
 complexes.   A  flow diagram explains the many  steps of  the process.  Basic chemis-
 try and required  equipment are  also detailed.  The significant results of this
 system  are that a major portion of  the  chemicals required in the pulping pro-
 cess are reusable;  no significant odors are generated  from the pulping or the
 recovery processes; a new  basic chemistry for recovery of sodium base sulphite
 pulping liquor has been tested  on a plant scale; the process is economically
 competitive.   This  sulphite chemical recovery system should be applicable to
 any independent sodium base neutral sulphite  semi-chemical pulp mill and for
 sodium  base  sulphite  pulp  mills  practicing full  chemical cooking.

 *Sulphite liquors,  *Water  reuse,  *Aluminum, *Sodium, Water pollution, Chemistry,
 Water streams, Pulping and Paper industry, Pulp wastes, Industrial wastes,
 Recovery, Sulphur,  Organic matter

 *Residual liquors,  Sunoco,  Solid  state liquors
146J

DEPOLLUTION TECHNIQUES AND MANAGEMENT IN AN OIL REFINERY,

Chakravarty, S., and Mulchandani, H. K.

Indian Institute of Petroleum, India

Chemical Age of India, Vol. 24, No. 12, p 819-826, 1973.  2 fig, 5 tab, 6 ref.

With increasing demand for petroleum products and an expansion of the refining
capacity of India, associated effects of pollution occur.   Legislation is now
being formulated to stipulate and regulate levels of acceptable pollution.  Dis-
cussed are waste water management, air pollution, and noise pollution.  Refinery
waste streams systems can be classified as:  sanitary water systems, clean water,
oily water, ballast water systems, and foul and oily process water systems.  The
waste water flow scheme for a refinery includes pH control, an API separator for
the removal of oil, flocculation/flotation methods for the removal of suspen-
ded solids and oil, and a biological treatment system for the reduction of BOD.
Treatment and disposal of effluent leads to the following considerations:  sludge
and its disposal and acid sludge disposal by either burning, thermal decomposi-
tion and sulphur recovery, lagooning, or neutralization and dumping.  Apart^from
the waste purification system, plant design is discussed in terms of economics
and reducing the quantity of either waste water or contaminant.

*0il, *Waste water treatment, industrial wastes, *Water pollution, Effluents,
Biochemical oxygen demand, Flocculation, Flotation, Suspended solids, Lagooning,
Sulphur, Air pollution, Noise pollution, Costs, Contaminants

India, Oil refineries, pH
                                     749

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 14 7 J

 THE EFFECT OF DISSOLVED HYDROCARBON GASES IN SURFACTANT
 SOLUTIONS ON FROTH FLOTATION OF MINERALS,

 Somasundaran, P., and Moudgil, B. M.

 Columbia University, New York, New York, Henry Krumb
 School of Mines

 Journal of Colloid and Interface Science, Vol. 47,  No.  2,  p 290-308,  May,  1974.
 5 fig, 1 tab, 23 ref.

 Surface tension properties of hydrocarbon saturated solutions  have been measured
 and indicated absorption of the gas molecules at the solution/air interface.
 Selective effects of the dissolved hydrocarbons on  froth flotation of minerals
 are discussed on the basis of possible changes in the properties of the solution
 surface and the mineral/solution interface.   Mechanisms responsible for the ef-
 fects on flotation were demonstrated;  for example,  methane dissolved  in sodium
 dodecylsulfonate collector solutions was found to increase the flotation of alu-
 mina by 10 to 30 percent.  Flotation of quartz or hematite was not affected by
 the presence of dissolved methane or butane.   A new automated  constant-pressure
 apparatus for dissolution studies showed the  solubility of gases to be lower in
 surfactant solutions than in water when the  surfactant  concentration  was
 low, and higher than in water when the concentration was high.  This  is explained
 on the basis of the predominance of the "salting-out" effect at lower surfactant
 concentrations and the hydrophoblc bond formation between the  hydrocarbon mole-
 cule and the surfactant chains at higher concentrations.

 *Hydrocarbons, *Solutions, *Gases, *Surfactants, *Froth flotation, Minerals,
 Surface tension, Flotation, Methane, Adsorption

 Salting-out effects, Hydrophobic band  formation
148J

CANADA:  SEVERE PROBLEMS,

Paper Review of the Year,  p 74, 76-78,  80, 101,  1973.   1 tab.  1 ref.

Canadian pulp and paper industry has been heavily taxed and has had severe econo-
mic problems due to increasing costs of pollution control measures defined by
governmental legislation.   Improvements described include a fluidised bed reac-
tor which incinerates all  non-usable wastes together with general mill debris and
sludge from the effluent system of the  mill,  without creating atmospheric pollu-
tion.  Also, the reclamation of waste fibre materials  are accomplished by:  li-
quid waste being aerated in collecting lagoons,  monitoring stations,  simulations
of effluent waters in a fish aquarium to check water quality,  or by installation
of a recovery furnace and boiler.  Specific equipment and machinery for these
and other processes are described.

*Pulp and paper industry,  *Canada, *Water pollution control, *Costs,  Legisla-
tion, Pulp wastes, Paper pulp wastes, Aeration,  Lagoons, Monitoring,  Fish,
Water quality control, Recovery, Equipment, Machinery

Fluidised bed reactor, Waste fibers
                                     750

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149J

PLANT TREATS WASTES FROM AIRCRAFT ENGINE TESTING,

Water and Pollution Control, Vol. 112, No. 3, p 34-36, 39, March, 1974.  2 tab.

The expansion of facilities at Air Canada, Dorval, Quebec included the expansion
of the overhaul and maintenance building where jet engines were to be serviced.
This necessitated an effluent handling system designed to deal with toxic inor-
ganic wastes from metal stripping, cleaning, and plating processes.  Wastes
stemmed from two sources, batch solutions into which the metal parts were dipped,
and rinse waters.  They consisted of cyanides, alkaline permanganates, caustic
soda, and a variety of acids.  Due to the variety of processes, chemical solutions,
and tanks, recycling systems were not economically practical and a destruction
treatment was seen as necessary.  Specifically treated were chromate wastes,
cyanide wastes, solutions containing hydrofluouric and phosphoric acids, alkaline
permanganates, concentrated general acids, and concentrated alkalies.  Equipment
is described, all tanks having overflow pipes, controlled by continuous automatic
treatment panels located on the floor above.

*Industrial wastes, *Effluents, *Facilities, Toxicity, Inorganic matter, Alka-
lines, Acids, Chemical solutions, Tanks, Recycling, Equipment, Control

Chromates, Cyanide, Phosphoric acid
 150J

 TRICKLE  IRRIGATION SOIL WATER POTENTIAL AS INFLUENCED BY
 MANAGEMENT OF HIGHLY SALINE WATER,

 Tscheschke, P., Alfaro, J. F., Keller, J., and Hanks, R. J.

 Utah State University

 Soil Science, Vol. 117, No. 4, p 226-231, 1974.  5  fig, 2  tab, 5 ref.

 The purpose of  the investigation was  to experimentally  determine the  soil water
 potential and salt patterns in uniform soil profiles as a  result of four different
 water management  treatments.  Cherry  tomato plants  were irrigated:  daily with a
 volume of water equal  to  that used by the plant on  the previous day;  every other
 day with volumes  of water being equal; below  the water evapotranspired; and
 above the water evapotranspired.  This was done to  test for salt,  for even though
 trickle  irrigation offers the possibility of  good yields when, nontoxic highly
 saline water Is used to irrigate, there may be accumulated salts in the root zone
 as a potential  hazard.  It was seen that soil water potential decreased in the
 soil profile as a result  of salt accumulation with  increased distance from the
 trickle  source.  The highest salt concentration occurred in the profiles irriga-
 ted with volumes  of water below that  evapotranspired by the tomato plants, indi-
 cating the importance  of  avoiding under irrigation  when highly saline water is
 used with trickle irrigation.  In addition, higher  soil water potentials and
 higher yields resulted from irrigating with volumes above  the evapotranspiration.

 Irrigation, Investigation, *Soil water, *Saline deposits, Salt,  Water quantity,
 Soil chemistry, Soil contamination, Root zone, Soil profile, Saline water, Ex-
 perimentation

 *Trickle irrigation, Salt accumulation, Tomato plants
                                         751

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 151J

 WHAT'S  NEW IN SLIME AND  DEPOSIT  CONTROL,

 Dyck, A.  W.  J.

 American  Paper Industry,  Vol.  56, No.  6, p  16-17, May,  1974.   1  tab.

 Slimicides are a  part  of the  pulp and  paper mill  process  and  previously were
 mercurial compounds.   Due to  legislation and control by the Food and  Drug Adminis-
 tration and  the Environmental  Protection Agency,  mercurials were investigated.
 These were found  as a  threat  to  fish and other  aquatic  animals as well as being
 dangerous to mill personnel.   Non-mercurials which  replaced these as  slime con-
 trol agents  were  not as  effective.  More efficient  biocides are  being sought;
 described are four companies'  products—Merck's Metasol J-26,  Nalco's products,
 Dow's Slimicide XD-7287L, and  Betz's Slimicide  DE-508.

 *Slime, *Pulp and paper  industry, *Mercury,  Aquiculture,  Fish, Legislation,
 Products

 *Slimicides, Environmental Protection  Agency, Food  and  Drug Administration,
 Slime control agents,  Dow, Merck, Nalco, Betz
15 2 J

PROGRESS IN THE RURAL WATER PROGRAMS OF LATIN AMERICA,

Donaldson, D.

Boletin De La Oficina Sanitaria Panamericana, Vol. 76, No. 4, p 281-299,
April 1974.  2 fig, 6 tab, 18 ref.

Rural water supply problems in Latin America have been focused upon.  In 1971
about 27 percent of Latin American rural dwellers had potable water, about four
times as many as in 1961.  However, new goals for 1980 have been established by
the Ministers of Health of the Americas.  This involves reviewing kinds of rural
water systems to be installed, administrative and financial structure of the
program, and new approach methods.  Past programs have concentrated on the rural
villages, have used "revolving" funds for internal financing, and have tried
mass approach concepts.  Local participation is necessary to any future success.

*Water supply, *Rural areas, *Potable water, Costs, Administration, Financing,
Programs

Public health, Latin America, Ministers of Health of the Americas
                                      752

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15 3 J

EUTROPHICATION AND RECOVERY IN EXPERIMENTAL LAKES:  IM-
PLICATIONS FOR LAKE MANAGEMENT,

Science, Vol. 184, No. 4139, p 897-899, May 24, 1974.  2 fig, 21 ref.

Experimentation on several small lakes in Ontario, Canada tested whether phos-
phorus alone is responsible for eutrophication problems and how quickly the lakes
could recover after phosphorus removal.  By adding phosphate, ammonia, and sucrose,
rapid eutrophication occurred; but when phosphate additions were discontinued
recovery was almost immediate.  When two basins of one lake were fertilized
with equal amounts of nitrate and sucrose, phosphorus was added to only one and
it quickly became highly eutrophic.  The basin with only nitrogen and carbon re-
mained at prefertilization levels.  The high affinity of sediments for phosphorus,
coupled with these results, indicate that abatement of eutrophication can be
expected to follow phosphorus control measures.  Reducing phosphorus input should
cause a proportional abatement in phytoplankton blooms and other forms of eutro-
phication.  About fifty percent of the phosphorus which comes into the St. Law-
rence Great Lakes could be eliminated by banning or greatly reducing detergent
phosphates.

*Phosphates, *Eutrophication, *Lakes, Experimentation, Canada, Nitrogen, Carbon,
Great Lakes, Algae, Water management (applied), Phytoplankton, Lake basins,
Sediments, Water pollution control

Phosphorus removal, Ontario,  Canada, Detergents
 15 4 J

 HIGH-LEVEL COPPER FEEDING OF SWINE AND POULTRY AND THE
 ECOLOGY,

 Davis, G. K.

 Florida University, Gainesville, Florida

 Federation Proceedings, Vol. 33, p 1194-1196, 1974.  2 tab, 25 ref.

 Swine and poultry have been fed high levels of copper to increase  their growth.
 In localized levels their fecal wastes has raised  the environmental level of cop-
 per and created a problem.  For example, in bodies of water, copper adversely^af-
 fects aquatic organisms and on land it may endanger plants and crops.  In addi-
 tion, animals which eat these plants may have toxic reactions.  Sheep, as the
 most  sensitive to copper toxicity, are susceptible to these increased levels
 only  if they have inadequate dietary molybdenum.  Monitoring copper feedings
 and knowledge of appropriate counter-measures  (such as addition of  lime) are
 necessary to control  this problem.

 *Copper, *Toxicity, *Plants, *Animals, Diets, Feeding, Agriculture, Livestock,
 Water pollution, Soil, Animal wastes

 Molybdenum
                                    753

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155J

CONSEQUENCES OF HIGH NITRATE LEVELS IN FEED AND WATER
SUPPLIES,

Emerick, R. J.

South Dakota State University, Brookings, South Dakota,
Experiment Station Biochemistry Department

Federation Proceedings, Vol. 33, No. 5, p 1183-1187, 1974.  77 ref.

Presently available data and lack of data indicate caution with regard to nitrate
and nitrite contents of food and water supplies for humans.  Animal tests, how-
ever, indicate that subacute effects usually have occurred only with levels of
nitrate and/or nitrite approaching those of being potentially acutely toxic.
Feeds containing less than 0.1 percent N03-N and waters containing less than 100
ppm N03-N appear to within a safe range for all classes of livestock.  Maximum
amounts seem to depend upon the species of animal, the type and quantity of
diet, and the time period over which the dose is consumed.

*Water supply, *Potable water, *Nitrates, *Nitrites, Data, Toxicity, Livestock,
Feed, Diets, Water quality control,  Standards, Public health

South Dakota
 15 6 J

 EFFECTS OF LANDFILL DISPOSAL OF CHEMICAL WASTES ON GROUND-
 WATER QUALITY,

 Saint, P. K.

 Minnesota University, Minnesota

 Dissertation Abstracts International, Vol. 34, No. 7, p 3291, 1974.

 Public health and safety are threatened by disposal of toxic and hazardous
 wastes into landfills.  In addition, contamination of soils and groundwater are
 effects.  Predominant constituents are organic solvents like acetone, alcohol and
 ether, and salts of metals, as seen in an inventory of chemical wastes generated
 by teaching and research laboratories at the University of Minnesota.  Pits into
 which chemical wastes are disposed are located in an outwash sand plain, where the
 water table occurs at a depth of 65 ft and bedrock aquifers at a depth of 110
 ft.  Groundwater flow was seen to be towards the Mississippi River, with an aver-
 age velocity of 1.7 ft per day.  The disposal facilities are close to a ground-
 water divide where hydrological connections exist between the water table and
 bedrock aquifers.  Effects of chemical wastes are seen to lower the pH and to
 increase the concentration of organics, B.O.D., and phenols.  The soils act as
 an effective agent for temporary removal of metals but water soluble organics
 move easily through the soil.  Thus, design for pits receiving chemical wastes
 should aim at protecting the groundwater through containment and collection of
 leachates.  Wastes may be treated by increasing pH, providing adsorptive sur-
 faces, and encouraging microbiological growth to aid the decomposition of organic
 substances.

 *Landfills, *Groundwater, *0rganic matters, *Metals, Salts, Laboratory tests,
 Chemical wastes, Bedrock, Aquifers, Flow, Microbiology, Phenols, Biochemical
 oxygen demand, Water table, Toxicity, Soils, Mississippi River, Public health

 pH


                                       754

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15 7 J

OFFSHORE AIRPORTS EASE ENVIRONMENTAL PROBLEMS,

Lord, C. J.

Ralph M. Parsons Company

World Dredging and Marine Construction, Vol. 10, No. 5, p 32-37, May, 1974.  5 fig.

Due to the increased awareness of the environmental situation by the public,
it has grown increasingly difficult to undertake massive new airport con-
struction on land.  As a result, a number of offshore airports have been pro-
posed or are under construction in the coastal areas of the United States.
Some of the reasons that offshore airports minimize environmental impact are
as follows:  closeness to major metropolitan centers; buffering effect of the
water barrier between the disagreeable features of the development and the
general public; the development is screened from view by the water barrier;
there is a ready water supply for cooling and waste dispersion; and, in
some cases reclaimed land is actually cheaper than existing onshore land.
Related types of developments that may find it desirable to locate in an off-
shore setting include power plants, deep draft ports, sewage treatment plants,
desalination plants, extractive industries, meat packing plants, steel mills,
founderies and metal processing industries, refineries, solid waste disposal
plants, and communication systems industries.  The basic methods of reclama-
tion are earth fill, poldering, pile support, and floating structures.  A
discussion of ongoing projects and costs is included.

*Airports, *Facillties, *Construction costs, *Construction materials, *Eng-
ineering, Environmental effects, United States, Land reclamation, Costs

England, Netherlands, Copenhagen
158J

MAKE WATER POLLUTION CONTROL A MEANINGFUL LOCAL RESPONSIBILITY,

Craddock, J. M.

Muncie Sanitary District, Muncie, Indiana,
Division of Water Quality

The American City, Vol. 63, No. 4, p 63-64, May, 1974. .

The Muncie Sanitary District has established a Division of Water Quality
involving laboratory testing procedures, industrial monitoring,  and local
government.  In this way, local pollution can be controlled internally in
order to solve environmental problems.  Tests within the laboratory include
an oil-extraction unit, COD apparatus, a pH meter, vacuum filter for suspended
solids, jar test equipment, field dissolved oxygen meters, and automatic
field samplers.  Over twenty pollution discharges have been stopped as a
result.  Because about 80 industrial and commercial establishments are in the
Muncie area, samplers now monitor BODS, COD, heavy metals, and suspended
solids.  The research from these projects relate to the community's public
health, added recreational value of water resources, added revenue through
equitable waste-industry charges, and regulation by local rather than state
and federal agency control.

*Water quality control, *Monitoring, laboratory testing, *Environmental
effects, Pollution, Chemical oxygen demand, Dissolved solids, Suspended
solids, Jar testing, Vacuum filters, Industrial wastes, Biochemical oxygen
demand, Water resources, Costs, Regulation

pH, Local control, Muncie, Indiana  (Water Quality Division, Sanitary District)
                                         755

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159J

PLASTIC VALVES STAND UP TO CHLORINE,

The American City, Vol. 89, No. 5, p 85-86.  May, 1974.

In a municipal water treatment plant, plastic valves had several advantages
over metal ones.  These include a lower cost; they do not seize or gall; they
are unaffected by sodium hypochloride and do not corrode; and they do not
experience storm leakage.  For water filtration, at the Baldwin Treatment
Plant in Cleveland, Ohio, after two years of using thirty 3/4 inch and two
1/1/2 inch plastic ball values, no leakage or maintenance problems have
occurred.  Hayward Manufacturing Company's polypropylene and PVC Full-Flo
ball valves were seen as best for their system.

*Plastics, *Water treatment, *Costs, *Valves, Chlorine, Municipal water,
Treatment plants, Filtration

*Ball valves, Plastic valves, Cleveland, Ohio, Full-Flo ball valves, Sodium
hydrochlorite
160J

MERCURY ORGANIC MATTER ASSOCIATIONS IN ESTUARINE SEDIMENTS
AND INTERSTITIAL WATER,

Lindberg, S. E., and Harriss, R. C.

Florida State University, Tallahassee,
Florida, Department of Oceanography

Environmental Science and Technology, Vol. 8, No. 5, p 459-462, May, 1974.
1 fig, 2 tab, 22 ref.

Potential ecological effects of anthropogenic additions of mercury to natural
environments are studied in the Florida Everglades and Mobile Bay Estuary.
Significant associations were found between sediment mercury and sediment
organic matter and between dissolved interstitial mercury and dissolved organic
carbon.  Interstitial water and sediments were sampled, both from surface
and subsurface areas.  With limited data, it appears that increasing salinity
has a negative effect on the mercury complexing capacity of the dissolved
organic matter.  Interstitial dissolved mercury is enriched from 2.6 to 36.0
times over, the associated surface water values, and in. sulfide-rich pore
waters far exceeds the thermodynamic solubility of HgS.  This enrichment is
probably due to formation of organic and polysulfide complexes with mercury.


*Mercury, *Ecological effects, *0rganic matter, *Interstitial water, Sediments,
Solubility, Salinity, Environmental control, Estuaries

*Anthropogenie additions, Florida  (Everglades and Mobile Bay Estuary)
                                     756

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 161J

 SOME CURRENT PAPER INDUSTRY ENVIRONMENTAL PROTECTION PROBLEMS,

 Gellman,  I.

 National  Council of  the Paper  Industry for Air
 and Steam Improvement, Incorporated

 Paper Trade Journal, Vol. 158, No. 13, p 28-30, April 1, 1974.

 Reviewed  are problems relating to three aspects of energy and management.
 These are:  the recovery of energy from materials such as bark and spent
 pulping liquors which were once considered as wastes; the efficient use of
 energy in managing waste water, atmospheric emissions, and solid wastes;
 and the harnessing of natural energy for the dispersal of effluents and
 emissions.  Trends towards incineration of various semi-chemical and acid
 spent sulphite liquors have been due to both technology and the comparison
 of heat and chemical recovery costs within the paper industry.  Aspects dis-
 cussed included current kraft process studies, spent sulphite liquor
 studies, bark burning aspects, innovative industry approaches, high energy
 use by precipitators, lime kiln and sludge problems, sludge handling, and
 organic load and decolorization.  In addition, zero pollution discharge,
 color detectability in surface waters, and the need for year round treat-
ment are mentioned.   Future study on reliability of regional dispersion
models, degree of further refinement, and control of operations are
recommended.

*Energy, *Management, *Pulp wastes, *Waste water, *Bark, Effluents,
Technology, Sulphite, Chemicals, Costs, Pulp and paper industry, Lime,
Precipitation,  Models, Reviews

Zero pollution discharge,  Color detectability, Pulping liquors
162J

MAJOR PORT DEVELOPMENTS AT RICHARDS BAY WITH DUE REGARD TO PRE-
SERVING THE NATURAL ENVIRONMENT,

Zwamborn, J. A., and Cawood, C. H.

Hydraulics Research, CWIR, Pretoria, South Africa

The Civil Engineer in South Africa, Vol. 16, No. 2, p 79-85, February, 1974.
6 fig, 6 ref.

South Africa has experienced a considerable industrial growth which resulted in
the need for more and better harbor facilities.  Particularly in view of the
transport of bulk materials, Richards Bay was chosen as the most suitable
site for the establishment of a deep water port to serve the existing and
future industrial areas of the Transvaal, the Northern Free State and Natal.
Richards Bay consists of a large shallow bay connected to the sea by a shallow
estuary channel through which tidal flow and marine organisms can move freely.
The Natal Provincial Administration proposed the idea of preserving the
southern half of the bay as a nature reserve.  This suggestion was made
possible by the inclusion in the harbor scheme of a levee separating the
harbor area from the southern half of the bay, which at the same time would
provide access to the bluff area on the south side of the harbor entrance
channel and reduce situation in the harbor basins.  Time limitations pre-
cluded the model testing of an estuarlne flood relief channel direct to the
sea.  Thus documents provision was made for both tidal exchange between the
nature reserve and the harbor, and for flood discharge, by the inclusion of
a large flood relief structure in the levee.  An alternative, ecologically
much more attractive solution of a new estuary channel excavated through the
dunes directly to the sea became an economically feasible proposition.

industrial production, *Sea water, *Bays, Marine animals, Tidal flow, Ports,
Channels, Flood relief, Environmental effects

South Africa (Transvaal, Northern Free State), Richards Bay, Environmental
protection
                                    757

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 163J

 URBANIZATION AND THE ENVIRONMENT—ENGINEERING IMPLICATIONS,

 Bolitho, V.

 Health Services, Johannesburg, South Africa

 The Civil Engineer in South Africa, Vol. 16, No. 2, p 44-49, February,
 1974.  10 ref.

 Two of the gravest challenges faced by the Republic of South Africa  are the
 need to build cities and industries for approximately 20 million people by
 the end of the century and the solution of the environmental problems which
 this effort will involve.  Pollution, seen as disturbing equilibrium, is a
 serious threat both within the city and to its surroundings.  The engineer
 will be heavily involved in solutions to these problems, but to increase his
 effectiveness a re-examination of the engineer's role in urban planning and
 environmental control is necessary.

 *Industries, *Cltles, *Human population, *Environmental engineering, En-
 vironmental control, Pollution

 South Africa, Urban planning
164J

SANITARY LANDFILL,

Nelson, D. L.

Army Construction Engineering Research Laboratory

Publication No. AD-773-714, January 1974.  5 fig, 5 tab, 9 ref.

A literature review details the operation and design of sanitary landfills.
Operational parameters reviewed include basic methods of operation, com-
paction procedures and expected in-place refuse densities, cover require-
ments, and site improvements.  The engineering design consideration were:
refuse decomposition (including production and control of leachate and gas);
the use of information on hydrology, geology, climatology, and waste charac-
teristics to evaluate and classify sanitary landfill sites; possible uses for
a completed landfill site; and equipment cost data.  Mathematical analyses
defined optimum cell shape and minimum cover conditions in terms of landfill
parameters.

*Reviews, *Landfills, *Sanitation, *Design criteria, Engineering structures,
Hydrology, Geology, Climatology, Costs, Mathematical costs

*Sanitary landfills
                                      758

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 165J

 FEDERAL AND STATE LEGISLATIVE HISTORY AND PROVISIONS FOR
 LAND TREATMENT OF MUNICIPAL WASTEWATER EFFLUENTS AND SLUDGES,

 Sullivan, R. H.

 Environmental Protection Agency, Washington, D. C.
 Municipal Waste Water Division, Office of Water Program
 Operations

 In:  Proceedings of the Joint Conference on Recycling Municipal Sludges and
 Effluents on Land, July 9-13, 1973, Champaign, Illinois, The National Associa-
 tion of State Universities and Land-Grant Colleges, University of Illinois,
 p 1-8.  2 tab.

 Until the 1970's, the Federal government had traditionally left regulations
 and legislation concerning recycling municipal waste water effluents and
 sludges to the state and local governments.  Recently, land treatment of such
 wastes has been discussed as a matter of public health.  The Federal Water
 Pollution Control Act Amendments of 1972 clarify the trends in legislation.
 The Environmental Protection Agency also lists the major requirements for
 grants for sewage treatment projects.  These include:  priority certification
 from the State and conformation to planning requirements; cost effectiveness,
 pretreatment of industrial wastes; and secondary treatment.  State legislation
 surveys have been compiled by Temple University, Philadelphia, and the American
 Public Works Association.

 *History, legislation, *Municipal wastes, *Land treatment, *Public health,
 Water pollution control, Environmental Protection Agency, Sewage treatment,
 Federal Water Pollution Control Act, Federal jurisdiction, State jurisdiction,
 Treatment facilities, Industrial wastes, Costs, Effluents

 *The Federal Water Pollution Control Act Amendments of 1972
166J

LAND APPLICATION OF WASTEWATER WITH A DEMOGRAPHIC EVALUATION,

Seabrook, B. L.

In:  Proceedings of the Joint Conference on Recycling Municipal Sludges and
Effluents on Land, July 9-13, 1973, Champaign, Illinois, The National Associa-
tion of State Universities and Land-Grant Colleges, University of Illinois,
p 9-24.  3 fig.

After on-site field surveys of 100 facilities in all climates by the American
Public Works Association Research Foundation, data were compiled on land appli-
cation of effluents.  Reasons for use on land of such effluents were for supple-
mental irrigation water, to eliminate excessive costs of long outfall lines
to reach suitable points of disposal into large surface bodies of water, and
to give economical alternative solutions for treating wastes and discharging
them into receiving waters, without causing degradation of rivers, lakes, and
coastal waters.  Irrigation type facilities are discussed in the most depth
but ridge and furrow systems and infiltration lagoons and evaporation ponds
were also surveyed.  A separate APWA bibliography and SELECTED ABSTRACTS has
been published discussing potential health hazards and implications.  Recommen-
dations were that:  guidelines for land application of waste waters should be
provided by the Environmental Protection Agency; land application should not
be seen as a universal treatment; a suitable publication for the public should
be sponsored to describe the practice of sewage effluents on land; training
opportunities should be provided in areas for which technical information is
available; and guidelines which result from the implementation of Section 201
of the 1972 Amendments to the Federal Water Pollution Control Law should be
used for clarification of health implications.

*0n-slte testing, *Effluents, *Irrlgation, Costs, Reviews, Surveys, Public
health, Waste water, Infiltration, Lagoons, Environmental Protection Agency,
Treatment, Sewage treatment, Water pollution

*Land application, *American Public Works Association
                                         759

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167J

SOME EXPERIENCES IN LAND ACQUISITION FOR A LAND DISPOSAL
SYSTEM FOR SEWAGE EFFLUENT,

Postlewait, J. C., and Knudsen, H. J.

Muskegon County Department of Public Works, Muskegon,
Michigan

In:  Proceedings of the Joint Conference on Recycling Municipal Sludges and
Effluents on Land, July 9-13, 1973, Champaign, Illinois, The National Associa-
tion of State Universities and Land-Grant Colleges, University of Illinois,
p 25-38.  2 fig.

For the County of Muskegon, Michigan, a metropolitan area composed of seven
cities and seven urbanized townships, planning was essential for the implemen-
tation of a waste water management system in the areas of land acquisition
and relocation.  Well planned multiple usage sites are seen as advantageous.
Public relations and community acceptance of any program proved to be of pri-
mary importance.  Legal and political problems included zonings and public
hearing processes, road closings within the site areas, and the proximity of
schools, churches, and cemetaries.  In addition, oil, gas, and mineral rights
in land acquisition are factors of site selection.  There is a need for coopera-
tion between engineers and planners.  Legal and technical advice was demonstra-
ted as necessary by the Muskegon Project.

*Municipal water, *Municipal wastes, *Michigan, *Water management (applied),
legislation, Urban planning, Planning, Sites

*Land acquisition, *Public relations, Muskegon Project, Muskegon, Michigan
168J

A REGIONAL VIEW ON THE USE OF LAND FOR DISPOSAL OF MUNI-
CIPAL SEWAGE AND SLUDGE,

Schneider, R. J.

Environmental Protection Agency, Region V

In:  Proceedings of the Joint Conference on Recycling Municipal Sludges and
Effluents on Land, July 9-13, 1973, Champaign, Illinois, The National Associa-
tion of State Universities and Land-Grant Colleges, University of Illinois,
p 63-66.

Federal, state, and local cooperative actions are needed to bring municipal
waste treatment projects to completion.  The new 1972 Amendments to the Federal
Water Pollution Control Act set goals for the 1970's, the 1980's, and beyond.
The role of the Environmental Protection Agency with its Regional Offices is
seen as one of controlling cost-effectiveness.  Support by EPA has been given
to projects within Region V.  These include grants to the Fulton County Sludge
Utilization Project and the Muskegon, Michigan Spray Irrigation Project, as well
as major construction grant support to the latter.  The planning processes in
all cases must be accountable for environmental compatibility within their
respective communities.

*Federal jurisdiction, *State jurisdiction, *Federal Water Pollution Control
Act, *Environmental Protection Agency, Costs, Sludge, Irrigation, Municipal
wastes, Munixipal water, Planning, Urban planning

Muskegon Michigan Spray Irrigation Project, 1972 Amendments to the Federal
Water Pollution Control Act, Regional planning, Cost-effectiveness, Community
involvement
                                        760

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 169 J

 PHYSICAL CHANGES TO SOILS USED FOR LAND APPLICATION OF MU-
 NICIPAL WASTE—WHAT DO WE KNOW?  WHAT DO WE NEED TO KNOW?,

 Erickson, A. E.

 Michigan State University

 In:  Proceedings of the Joint Conference on Recycling Municipal Sludges and
 Effluents on Land, July 9-13, 1973, Champaign, Illinois, The National Associa-
 tion of State Universities and Land-Grant Colleges, University of Illinois,
 p 75-77.

 Less is known about effluents than about sludges and their effects on changing
 the physical properties of soil.  Necessary are more field experiments to de-
 termine the maximum amounts of effluents that can be applied to medium tex-
 tured soils and produce good to maximum crop yields.  This also depends upon
 the existing rainfall.  Sodium in effluents and high sodium sludges as a
 limiting factor on particular soil practices need further study.

 *Sludges, *Effluents, *Soil physical properties, *Soil properties, *Municipal
 wastes, *Soil texture, Sodium, Rainfall, Soil-plant-water relationships,
 Sodium compounds, Agriculture, Experiments, Crops

 *Land applications, Crop yields
170J

SOIL MICROBIOLOGICAL ASPECTS OF RECYCLING SEWAGE SLUDGES
AND WASTE EFFLUENTS ON LAND,

Miller, R. H.

Ohio State University and Ohio Agricultural Research
and Development Center

In:  Proceedings of the Joint Conference on Recycling Municipal Sludges and
Effluents on Land, July 9-13, 1973, Champaign, Illinois, The National Associa-
tion of State Universities and Land-Grant Colleges, University of Illinois,
p 79-90.  7 fig, 50 ref.

The biological component of the soil is significant in the successful function-
ing of the soil filter during recycling of sewage sludges and effluents.  The
areas discussed in waste recycling are:  decomposition of organic compounds
contained in sludge and waste effluents; detoxication of some potentially prob-
lematic organic materials such as detergent residues, pesticides, and petro-
leum hydrocarbons; elimination of pathogenic microorganisms; participation in
the cycling of nitrogen, phosphorus, and sulfur; and in the reactions which
influence the solubility and the mobility of inorganic ions.  Present knowledge
of each microbial reaction is reviewed and needed research in areas such as
the structural basis for resistance to microbial decomposition is emphasized.

*Soil microorganisms, *Soil microbiology, *Sewage sludges, *Soil filters,
*Recycling, *Effluents, *Waste treatment, Organic matter, Hydrocarbons,
Pesticides, Nitrogen, Phosphorus, Detergents, Toxicity, Microorganisms, Sul-
fur

Land applications
                                       761

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171J

INORGANIC REACTIONS OF SEWAGE WASTES WITH SOILS,

Lindsay, W. L.

Colorado State University

In:  Proceedings of the Joint Conference on Recycling Municipal Sludges and
Effluents on Land, July 9-13, 1973, Champaign, Illinois, The National Associa-
tion of State Universities and Land-Grant Colleges, University of Illinois,
p 91-96.  1 fig, 13 ref.

Inorganic constituents added to the soils in the form of sewage wastes form
martices with the soil involving chemical reactions.  Each element has par-
ticular chemical characteristics.  Reaction products of such elements in soils
constitute complex solid phases and often obscure solubility relationships,
especially when specific ionic composition of the soil solution is ignored.
Basic studies in soil chemistry, chemical equilibria, mineralogy, and metal
chelation are needed.  Groups of elements most prevalent in sewage waste are
salts such Na, K, Ca, Mg, Cl, S04, N03, and H3B03 and other compounds and
reaction products of intermediate solubility involving Zn, Cd, Pb, Cu, Ni,
Cr. Hg, Mn, Co, P, As, Se, and Mo.  Long term effects of potentially toxic
heavy metals must be determined to interpret the movement of elements and
their availability to plants in the soils.

*Soil chemistry, *Inorganic matter, *Sewage wastes, Solids, Solubility,
Chemical properties, Plants, Toxicity, Heavy metals, Salts, Soils, Soil-
water-plant relationships

Chemical equilibria
172J

LAND RESOURCES,

Flach, K. W.

Soil Conservation Service
United States Department of Agriculture

In:  Proceedings of the Joint Conference on Recycling Municipal Sludges and
Effluents on Land, July 9-13, 1973, Champaign, Illinois, The National Associa-
tion of State Universities and Land-Grant Colleges, University of Illinois,
p 113-119, 2 fig, 2 tab.

The Soil Conservation Service has taken soil surveys that indicate the pre-
sence of suitable soils for land-based waste disposal systems near most metro-
politan centers.  Climatic factors suggest that ecologically safer locations
are in the semiarid and arid regions of the western part of the United States.
Site selection should also be based on runoff, erosion, permeability, infil-
tration capacity, and available water holding capacity.  Availability of pub-
lic land and farm size must also be considered.  Disposal on land is a
feasible substitute for secondary and tertiary treatment of liquid wastes
but the waste must be destroyed or absorbed in the soil and any effluent
must not contribute to degradation of water and air resources.

*Land resources, *Soil conservation, Runoff, Waste disposal, Municipal
wastes, Climate, Ecological effects, Arid regions, Erosion, Infiltration,
Agriculture, Secondary treatment, Tertiary treatment, Liquid wastes, Soil,
Effluents

*Soil Conservation Service, Soil surveys
                                       762

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17 3 J

SOIL-PLANT RELATIONSHIPS (SOME PRACTICAL CONSIDERATIONS
IN WASTE MANAGEMENT) ,

Melsted, S. W.

University of Illinois

In:  Proceedings of the Joint Conference on Recycling Municipal Sludges and
Effluents on Land, July 9-13, 1973, Champaign, Illinois, The National Associa-
tion of State Universities and Land-Grant Colleges, University of Illinois,
p 121-128, 1 tab, 27 ref.

Municipal sludge and effluent applications on land as related to soil-plant
relationships are discussed.  Distinction is made between disposal of wastes
and recycling.  Relationships between soil and plants include nutrient mobili-
ty in the soil, ion absorption by plants, methods of determining plant compo-
sition through soil analysis, the importance of sludge placement to ion absorp-
tion by crops and nutrient absorption through foliar feeding.  Management
factors are evaluated.  Plant analysis is rated to be more practical than moni-
toring processes at this time.  Suggested tolerance levels for toxic heavy
metals are given.  Recommended are:  defining the available form of heavy
metals; correlating soil levels and plant composition; absorbing noxious com-
pounds from foliar spray irrigation; determining residual nutrient levels;
and determining disposal management systems which maximize the beneficial
properties and minimize the hazards of applying municipal sludges and efflu-
ents on land.

*Municipal wastes, *Soil-plant-water relationships, *Waste disposal, *Re-
cycling, Management, Toxicity, Heavy metals, Irrigation, Effluents, Soil
analysis, Nutrients, Sludge

Soil-plant relationships, Ion absorption, Land applications, Plant analysis,
Hazards
17 4 J

CROP AND FOOD CHAIN EFFECTS OF TOXIC ELEMENTS IN SLUDGES
*"£ I- " UENTS,

Chaney, R. L.

United States Department of Agriculture

In:  Proceedings of the Joint Conference on Recycling Municipal Sludges and
Effluents on Land, July 9-13, 1973, Champaign, Illinois, The National Associa-
tion of State Universities and Land-Grant Colleges, University of Illinois,
p 129-141.  15 tab, 45 ref.

Sewage sludge and effluent are applied to soil and toxic heavy metals are re-
tained by the soil.  These elements will accumulate and persist, and are the
long term environmental hazard in land application.  Elements in sludge and
effluent that are potential hazards to plants or food chain are:  B, Cd, Co,
Cr, Cu, Hg, Ni, Pb, and Zn.  The direct toxicities to plants from Zn, Cu,
and Ni are discussed in detail.  Hazard to the food chain from Cd, Cu, Zn,
Pb, and Hg in crops grown on sludge- and effluent-treated soils emphasizes
the controllable hazard from Cd.  Crop differences in injury from, and accumu-
lation of Cd, Cu, Zn, and Ni are discussed in relation to the high phosphate
and organic matter contents of sludge and effluent.  Recommendations are made
for permissible levels of toxic metals .added to agricultural soils.  Research
needs for protection of plants and the food chain are presented.

*Toxicity, *Heavy metals, *Sludges, *Effluents, *Food chains, *Plants, *Soils,
Environmental effects, Agriculture, Phosphates, Organic matter

Effluent-treated soils, Land applications, Environmental hazards
                                          763

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 17 5J

 CROP SELECTION AND MANAGEMENT ALTERNATIVES—PERENNIALS,

 Sopper, W. M.
 Penn State University,
 University Park, Pennsylvania

 In:  Proceedings of  the Joint Conference on Recycling Municipal Sludges and
 Effluents on Land, July 9-13, 1973, Champaign, Illinois, The National Associa-
 tion of State Universities and Land-Grant Colleges, University of Illinois,
 p 143-153.  10 tab,  10 ref.

 An overview is presented about the use of perennials as a vegetative cover on
 sites  to be used for the disposal of treated municipal sewage effluent and
 sludge.  A review of the available literature suggests that more definitive
 research data is needed on all aspects of environmental impacts.  Criteria which
 were considered included:  water requirements and tolerance, nutrient require-
 ments  and tolerance, optimum soil conditions for growth, season of growth and
 dormancy requirements, sensitivity to toxic heavy metals and salts, nutrients
 utilization and efficiency, ecosystem stability, length of harvesting rotation,
 insect and disease problems, natural range, and demand or market for the pro-
 duct.

 *Environment effects, *Crops, *Management, Vegetation, Nutrients, Toxicity,
 Heavy metals, Salts, Insects, Waste disposal, Reviews

 *Perennials, Water requirements, Harvesting rotation
176J

RECYCLING URBAN EFFLUENTS ON LAND USING ANNUAL CROPS,

Day, A. D.

University of Arizona

In:  Proceedings of the Joint Conference on Recycling Municipal Sludges and
Effluents on Land, July 9-13, 1973, Champaign, Illinois, The National Associa-
tion of State Universities and Land-Grant Colleges, University of Illinois,
155-160.  19 refs.

Treated municipal waste water has been used for industrial purposes, for re-
creation, to produce forest products and to grow agricultural crop plants.
This municipal waste water contains more fertilizer elements (nitrogen, phos-
phorus, and potassium) than do most other forms of irrigation water, and
offers a future agricultural potential.  High yields of relatively high
quality food, feed, forage, oil, and fiber plant products have been obtained
from crop plants utilizing municipal waste water as a source of irrigation
water and plant nutrients.  Soil irrigated with waste water had a lower infil-
tration rate, high modulus of rupture, and more soluble salts, nitrates, and p
phosphates than did soil irrigated with well water and fertilized with sug-
gested amounts of nitrogen, phosphorus, and potassium.  Irrigation with waste-
water (sewage effluent) for 14 years did not result in any adverse effects
on soil that could not be corrected with minor changes in field crop culture.

*Municipal wastes, *Waste disposal, *Crops, Industrial wastes, Recreation,
Fertilizer, Nitrogen, Phosphorus, Potassium, Irrigation, Urban land use, Soil,
Crop production, Infiltration

*Municipal waste water, *Land application
                                 764

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 177J

 INSTITUTIONAL OPTIONS FOR RECYCLING URBAN  SLUDGES AND
 EFFLUENTS  ON LAND,

 Barbolini,  R.  R.

 Metropolitan Sanitary District  of  Greater  Chicago

 In:   Proceedings  of  the Joint Conference on  Recycling Municipal  Sludges  and
 Effluents  on Land, July 9-13, 1973,  Champaign,  Illinois, The National Associa-
 tion of  State Universities  and  Land-Grant  Colleges, University of  Illinois,
 p  199-205.

 Analysis of institutional options  for  recycling effluents and sludges from
 urban waste water treatment plants on  land indicates the presence  of numer-
 ous  alternative methods for financing,  operating, and organizing large scale
 programs.   The effects  of technical, social, political and legal constraints
 are  examined and  found  to be significant in  the determination of preferred
 alternatives.  The Metropolitan Sanitary District of Greater Chicago (MSDGC)
 has  been active in land application  of  sludge and is currently engaged in a
 very large  scale  project to apply  sludge to  rural, stripmined land approximate-
 ly 200 miles from the center of its  collection  and treatment activities.
 Methods of  financing  preferred  are bond sales or State and Federal grants for
 capital improvements,  and current  taxation for  normal maintenance  and opera-
 tion activities.  The alternate for  application facilities requires the  pur-
 chase of large rural  tracts.  Land development  must be achieved  through  care-
 ful  planning activities conducted  with  close cooperation between local govern-
 ment agencies  of  rural  receiving area and  the urban producing area.

 *Recycling,  *Effluents,  *Financing,  *Urban planning, Costs, Waste  water  treat-
 ment, Legislation, Federal  jurisdiction, State  jurisdiction, Sludge, Rural
 areas, Land development,  Taxation, Systems analysis, Planning

 *Chicago, Illinois (Metropolitan Sanitary  District), *Land application
17 8J

PUBLIC ACCEPTANCE—EDUCATIONAL AND INFORMATIONAL NEEDS,

Dunbar, J. 0.

Purdue University

In:  Proceedings of the Joint Conference on Recycling Municipal Sludges and
Effluents on Land, July 9-13, 1973, Champaign, Illinois, The National Associa-
tion of State Universities and Land-Grant Colleges, University of Illinois,
p 207-211.  3 ref.

Efficient use of limited resources is requisite, including the recycling of
urban sewage and sludge to the land.  Public acceptance and support is neces-
sary.  Attitudes towards the recycling of urban effluents must be made posi-
tivistic by knowledge and information about consequences of the processes.
These include alternatives for disposing of sludge, how it will work, dollar
costs, agricultural production, and public health.  Communication, in the
form of personal contact and community involvement are needed.

*Municipal wastes, *Recycling, *Education, Information exchange, Effluents,
Sludge, Waste disposal, Public health, Costs, Agriculture, Communication

*Public relations, Community involvement, Land application
                                    765

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 179J

 SOME EXTENSION SERVICE  CAPABILITIES,

 Ellington,  C.  P.

 University  of  Georgia

 In:   Proceedings  of  the Joint  Conference  on Recycling Municipal Sludges and
 Effluents on Land, July 9-13,  1973, Champaign, Illinois, The National Associa-
 tion of  State  Universities  and Land-Grant Colleges, University of Illinois,
 p  213-214.

 The  Cooperative Extension Service, created by Congress  in 1914, has the on-
 going function of providing information from research of the Agricultural
 Experiment  Stations.  The present role of this service  is to work through
 county leadership towards changes at local levels.  Community support is
 necessary for  any modification of water resources use.  Recycling of municipal
 sludges  is  one specific area in which education and information should be
 disseminated to the  public.

 *Research,  *Education,  Information exchange, *Local governments, *Water
 resources use,  *Recycling,  *Municipal wastes, Agriculture

 Community support, County leadership
180J

INFORMAL OPINIONS,

Jelinek, C.

United States Department of Health, Education and
Welfare

In:  Proceedings of the Joint Conference on Recycling Municipal Sludges and
Effluents on Land, July 9-13, 1973, Champaign, Illinois, The National Associa-
tion of State Universities and Land-Grant Colleges, University of Illinois,
p 215-217.

The Bureau of Foods within the Food and Drug Administration asks that caution
be used in the application of sludge or effluents as fertilizers.  Levels of
toxicity are very vague, including contamination by heavy metals such as mercury,
lead, cadmium, arsenic, selenium, and zinc.  Organic chemicals such as pesti-
cides, PCB's, are also included.  Recommended are monitoring operations for
food crops and animal feed crops.  For example, a test might be set up using
both a control and a commercial fertilizer, measuring for pesticides, patho-
genic organism, and heavy metals.

*Foods, *Fertilizers, *Toxicity, *Contamination, *Heavy metals, Pesticides,
Crops, Mercury, Lead, Cadmium, Zinc, Organic chemicals measurement, Poly-
chlorinated biphenyls
                                       766

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181J

PROCEEDINGS OF THE JOINT COMMITTEE ON RECYCLING MUNICIPAL
SLUDGES AND EFFLUENTS ON LAND,

Coordinating Committee on Environmental Quality

Environmental Protection Agency, Washington, D. C., and
The United States Department of Agriculture, and The
National Association of State Universities and Land-
Grant Colleges

Technical Report PB-227 106, Champaign, Illinois, July 9-13, 1973.  244 p.

A collection of 25 articles on land application of municipal sewages is
published from the proceedings of a Joint Conference held July 9-13, 1973.
Topics include properties of various types of effluents and sludges, physi-
cal processes, treatment methods, economic aspects, and public information.

*Irrigation systems, *Design criteria, *Waste water treatment, *Costs, *Ground-
water, *Recharge, *Agriculture, *Public Health, *Environmental effects, *Sew-
age treatment, Industrial wastes, Climatic zones, Reclaimed water, Soil-plant-
water relationships, Management, Monitoring, Waste disposal, Reviews

*Land applications
182J

MERGER OF WASTE PROBLEMS,

Science News, Vol. 105, No. 14, p 225, April 6, 1974.

Coal-based electricity and oil extracted from tar sands generate serious
waste disposal problems.  When tar sands are treated with large quantities
of hot water and steam, oil and sand tailings are released.  Similarly,
the waste product of burning oil for electrical power, fly ash, is
collected by precipitators before it enters the stacks.  It is suggested
that the two byproducts be combined to produce water and an easily dis-
posable filter cake.

*Waste disposal, Oil wastes, Fly ash, Byproducts, Waste treatment, Coal,
Electricity

Filter cakes, Tar sands
                                       767

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183J

EFFLUENT DISPOSAL FROM YEAST MANUFACTURING PLANT,

Chemical Processing, Vol. 20, No. 2, p 13, February, 1974.

So as to discharge effluent resulting from the production of yeast from
molasses a 50 percent reduction in the biochemical oxygen demand was
required by the Jamaican Ministry of Health.  To meet this requirement
a biological process which would produce the least solids and avoid the
mechanical disposal of solids was optimized.  A trickling filtration system
employing ICI Flocor plastics biological filter medium was selected
and performance indicates a 67 percent BOD reduction.

*Effluents, *Biochemical oxygen demand, *Trickling filters, Biological
treatment, Performance, Plastics, Optimization, Regulation, Public health,
Yeasts

Jamaica
184J

PICKLING PROCESS POLLUTION PROBLEM 'ELIMINATED',

The British Steelmaker, Vol. 40, No.  1-2, p 38, January-February, 1974.

A new process which permits the recovery of up to 99 percent of acids and
heavy metals from pickling baths used in metal processing plants has
been developed in Sweden.  The method rests upon fluid extraction which
provides for sulfuric acid to be added to the nitric an/ hydrofluoric
acids in the pickling bath.  The bulk of the latter two are separated
from the solution, returned to the pickling process, and the remaining
aqueous solution of metal sulfates are recovered in the form of dry oxides.
The only remaining material is a residual amount of sodium sulfate.

*Acids, *Heavy metals, *Industrial wastes, Water pollution control,
Sulfates, Waste water treatment

Metal processing, Sweden
                                  768

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 185J

 SYSTEMIC ARTERIAL DISEASE AND  CHRONIC ARSENICISM IN INFANTS,

 Rosenberg, H.  G.

 Catholic University  of  Chile,  Department of Pathology,
 Clinical Hospital, San  Marcoleta, Santiago, Chile

 Archives of Pathology,  Vol.  97, No.  6, p 360-365, June,  1974.
 7  fig,  3 tab,  21 ref.

 The antecedent of chronic arsenic poisoning from drinking water was  found
 in five cases  at the time of autopsy.  In  all  of them  a  peculiar vascular
 lesion  was found, consisting of intimal thickening in  small  and medium-sized
 arteries.  The most  frequently involved organs were the  heart, gastro-
 intestinal tract, liver, skin, and pancreas.  The vascular lesion is
 considered to  be characteristic and  readily recognized.  The great majority
 of the  lesions found at autopsy were considered to be  secondary to the
 vascular damage; others, although related  to arsenic poisoning, were
 dependent on different  pathogenic mechanisms.

 *Human  pathology, *Toxicity, *Potable water, *Arsenic  compounds, Public health

 *Arterial disease, *Chronic  arsenicism
186J

LEGISLATION CONTROLLING WASTE DISPOSAL,

Guiver, K., and Gray, D. A.

Essex River Authority, Great Britain

The Public Health Engineer, No. 8, p 45-50, March, 1974.  16 ref.

Recent concern in England over the increasing toxicity of industrial waste
and the volumes being deposited to landfills has led to recognition of
the need for measures against groundwater pollution.  Increasing interest
by industry in the possibility of waste injection into the subsurface also
requires that the risks inherent in such practices should be recognized
and provision made for their control.  Current legislative action con-
trolling deposits to landfills and deep well injections is considered
herein and the case for Amendment examined.

*Legislation, *Waste disposal, Landfills, Deep wells, Injection, Industrial
wastes,  Groundwater, Water pollution sources, Public health, Toxicity

*Great Britain
                                         769

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187J

2001 - A WATER ODYSSEY,

Surveyor, Vol. 143, No. 4259, p 10-11, January, 1974.

The Water Resources Board of England having recently completed a report
on the water resources of England and Wales Investigated both the short-term
(until 1981) and long-term (until 2001) strategies.  The full list of pro-
jects recommended for implementation and investigation are tabulated and
shown schematically.  Further recommended research and development includes
large-scale artificial recharge, factors determining the quality of water
in rivers constituting a possible source of supply, effluent discharges
to potable waters, environmental and ecological problems associated with
large inland and offshore storage sources, and river-to-river transfers.

*Water resources, *Water resources development, Project planning, Water
quality, Water supply, Rivers, Artificial recharge, Potable water, Effluents,
Environmental effects, Water storage, Ecology

*Great Britain
188J

AN EXAMINATION OF THE SUCCESSFUL APPROACH TO WATER RESOURCES
DEVELOPMENT IN THE SOUTH WEST,

Dixon, D. J.

The Public Health Engineer, No. 8, p 53-55, March, 1974.

The last ten years have been marked by a notable lack of success in the
promotion of certain water resource development schemes in England.
Throughout the country the pursuit of new schemes to meet rapidly rising
demand for water has been frustrated by opposition from preservation groups
and individuals.  In this climate, promoting authorities have faced up
to the public involvement in new schemes and consulted with individuals
and their representative bodies at an early point in the promotion stage.
This paper seeks to examine and explain the current approach in Devon to
water resources development and to illustrate an example of a recent success.

*Water resources development, Regional development, Optimum development
plants, Projections, Comprehensive planning

Great Britain
                                         770

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189J

"RESTORE OR MAINTAIN":  A REVIEW OF WATER QUALITY IN DEVON,

Mugford, D.

The Public Health Engineer, No. 8, p 57-61, March, 1974.  3 tab.

The area administered by the Devon River Authority covers some 625,810
hectares and can be described as predominantly agricultural with an inland
population being well distributed.  In general the rivers of Devon are
clean with most of the effluents being transient in effect and pollution
not often severe.  It is a general characteristic of the Devon rivers
because of their natural reaeration and self-cleansing properties, to deal
effectively and quickly with biodegradable wastes.  There are, however, a
few lengths where the quality of water is unsatisfactory either because of
poor quality discharges from overloaded or inadequate sewage treatment or
trade effluent works, or from natural pollution because of the peculiar
characteristics of the area.  In addition to the routine chemical analysis
that provides the bulk of information on water quality, tests are constantly
being carried out for a wide variety of toxic constituents of industrial
and mine water discharges, and in connection with sporadic incidents of
river pollution.

*Reviews, *Water resources, Rivers, Water pollution control, *Water
quality, Analytical techniques, On-slte tests, Biodegradation, Effluents,
Industrial wastes, Mine wastes

Great Britain, Devon River Authority
190J

INVESTIGATING THE ENVIRONMENTAL IMPACT OF ENGINEERING
PROJECTS,

Noble, R. G.

South African Council for Scientific and Industrial
Research

Die Siviele Ingenieur in Suid-Afrika, Vol. 16, No. 2, p 77-78, February,
1974.

Because environmental consequences follow all urban and agricultural develop-
ment, there exists a need to improve the planning of the scientific in-
vestigations which should precede and accompany major development projects.
Such investigations must be truly multi-disciplinary, bringing the
best available specialists in each of the fields concerned together,
must be an integral part of the planning phase of the project, and must
form the basis for any decision taken.  The theory involved in dam building,
irrigation schemes, and urbanization is described briefly.  Also the
organized method of approach including both the aims of thy project and
the actual investigation is discussed.

*Project planning, *Environmental engineering, Environmental control,
Construction, Urbanization, Irrigation, Feasibility studies

South Africa
                                         771

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191J

THE EFFECT OF POLLUTION ON THE VAAL RIVER BARRAGE AND
THE QUEST FOR WATER QUALITY,

Laburn, R. J.

Rand Water Board, Chief Engineer, South Africa

Die Siviele Ingenieur in Suid-Afrika, Vol. 16, No. 2, p 62-65, February,
1974.  2 fig.

By the year 2000, the water demand for the Pretoria-Witwatersrand-
Vereenigung region in South Africa will be of the order of 5000 Ml/d
serving a population predicted to range between 10 and 12 million.
Virtually all the water required in the region is supplied from the Vaal
River with Barrage reservoir and the Vaal Dam nearby.  So as to assure
raw water supplies of adequate quality for the future, pollution control
measures are being evaluated now.  Hydrobiological and limnological studies of
surrounding tributaries have been initiated and the following measures studied
possible solution:  separation of types of polluted water; industrial,
agricultural, and potable use of sewage effluents; a dual system of
water supply; and, a return flow effect on consumers below the Barrage.

*Water demand, *Water resources development, *Water quality control,
Investigations, Water pollution, Pollution abatement, Water supply

South Africa
19 2 J

WATER QUALITY CONTROL,

Van Duuren, F. A.

Pretoria University, Water Utilization Engineering,
South Africa

Die Siviele Ingenieur in Suid-Afrika, Vol. 16, No. 2 p 66-67, February,
1974.  2 fig.

Water demand, consumption, qualities, and requirements all form part of the
complex utilization pattern.  Water quality may best be controlled by
a juidicious application of these factors with optimization from available
water quantity by matching qualities of water available to qualities required
for particular uses.  Nature's hydrologic cycle and the man-made water cycle
then can be exploited in a rational manner.  Such is the case with Vaal
River supply system.

*Water quality control, Measurement, Water pollution, Water demand,
Water requirements, Water resources, Systems analysis, Application methods,
Hydrologic cycle

South Africa, Water cycle
                                             772

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193J

TECHNOLOGY AND ENVIRONMENTAL CONCERNS,

Department of Energy, Mines and Resources, Canada

Annual Report 1972-1973.  9 p.

A large share of the research carried out by the Department of Energy,
Mines, and Resources is aimed at increasing the level of technological
effectiveness in Canada.  Because of the mandate in the field of non-
renewable resources, such research is concerned chiefly with mine safety,
the concentration and beneficiation of ores, the processing of fuels to
a marketable state, metallurgy, methodology, and instrumentation used in
various geologic, geophysic, and topographic surveys.  This annual review
discusses such topics.

*Reviews, Automation, Surveys, Instrumentation technology, Environmental
control, Metallurgy, Mining, Safety, Analytical techniques, Remote sensing,
Application methods, Pollution abatement, Geologic investigations, Energy,
Waste treatment, Ice, Canada
194J

OPEN DAY CONDUCTED BY CONTROL EQUIPMENT COMPANY,

Australian Chemical Engineering, Vol. 14, No. 12, p 25-28, December, 1973.
1 tab.

The Zellweger company in Australia conducted an open day discussion
meeting with industrial representatives at its facilities which specialize
in control equipment.  The Polymetron modular instrument system was
highlighted as a new method of automating effluent treatment plants.  The
development of the Polymetron Sensotrode makes ion determination a simpler,
faster operation replacing highly complex chemical determinations.  Out-
lined is the procedure for effluent water treatment in the metal industry
by the polymetron method.

industrial plants, *Control systems, *Effluents, Waste water treatment,
Instrumentation, Automation, Ions, Analytical techniques, Industrial water

*Polymetron Method, Australia, Treatment plants
                                         773

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195J

IN-PLANT USAGE WORKS AND WORKS,

Ockershausen, R. W.

Allied Chemical Corporation,
Industrial Chemicals Division,
Morristown, New Jersey

Environmental Science and Technology, Vol. 8, No.5, p 420-432, May,
1974.  5 fig.

The study of waste water nutrients and the methods of upgrading treatment
plant effluents have resulted as consequence of Federal water pollution
control legislation.  It has been found that chemical storage tanks
and feeders can be rapidly and economically installed in existing plants
in the process of modernizing and increasing the capacity of waste water
treatment plants.  Certain concentrations of carbon, nitrogen, phosphorus,
potassium, silicon, and other elements are essential in the support of
microorganisms, fish, and other marine life; yet, an overabundance of
these nutrients results in excessive algae growths and degradation of the
water begins as the microorganisms die.  The reduction of phosphorus,
suspended solids, and the biochemical oxygen demand is discussed with
respect to primary waste water treatment, a trickling filter plant process,
activated sludge treatment, and physical-chemical treatment.  Also dis-
cussed are the capital and operating costs involved in upgrading waste
water treatment.

*Waste water treatment, *Nutrients, *Phosphorus, *Suspended solids,
*Biochemical oxygen demand, Sewage treatment, Trickling filters, Activated
sludge, Tertiary treatment, Capital costs, Operating costs, Treatment
facilities, Primary treatment, Microorganisms

Treatment plants
196J

OTTAWA SETS TIMETABLE FOR CLEANUP,

Canadian Chemical Processing, Vol. 59, No. 3, p 19-21, March, 1974.
4 tab.

Public Control over pollution in Canada is being achieved via a two-level
system.  The Federal government is enacting legislation that sets acceptable
levels of air and water quality while each province sets and enforces
specific pollution control measures covering processing plants within
its borders.  Ottawa gave its first priortiy to control of water pollution
under the Clean Water Act since health and food were so clearly involved.
Air pollution control objectives and standards were then initiated.  Water
quality standards, chemicals limitations, and industrial effluents program
schedules are tabluated.

*Water pollution control, *Water quality standards, *Canada, *Environmental
control, Legislation, Governments, Air pollution, Effluents, Chemicals,
Public health
                                       774

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197J

FOOL'S GOLD POLLUTES,

Aston, W. M.

West Virginia University

Canadian Mining Journal, Vol. 95, No. 3, p 59-61, March, 1974.

One of the most severe water pollution problems facing West Virginia,
Appalachia, and other coal or base metal mining areas is acid mine drainage.
The causes of this pollution source are explained and the scope of the
problem discussed.  Abatement techniques such as neutralization and reverse
osmosis are described.

*Water pollution sources, *Mine drainage, Metals, Mining, Pollution
abatement, Neutralization, Reverse osmosis, West Virginia, Appalachian
Mountain region, Mining wastes
198J

ENVIRONMENTAL POLICIES CALL FOR NEW PROFESSIONALISM IN
ENGINEERING, SCIENCE,

Grundy, R. D.

Professional Engineer, Vol. 44, No. 5, p 16-19, Mah, 1974.

The development of equitable environmental policies in the future will
require a far greater flow of information across the interfaces between the
scientific, engineering, and business communities and public institu-
tions than has traditionally been the practice.  Accompanying this
exchange will be corporate and technical concerns closer to those of
society as a whole.  Today's priorities now extend beyond economic con-
siderations to include adverse public health, environmental, and consumer
product side-effects of both government and corporate actions.

*Future planning (projected), *Economics, *Environmental engineering,
Industries, Governments, Public health
                                        775

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199J

ENVIRONMENTAL CONTROL,

Clifford, K. L.

St. Joe Minerals Corporation

Mining Engineering, Vol. 25, No. 2, p 83-85, February, 1973.

Over the period 1972-1980 pollution control facilities will cost $26 billion
according to economic impact studies performed under the direction of United
States Government agencies.  The top priority problem for 1972 was the con-
trol of sulfur dioxide.  Hydrometallurgical approaches to pollution abate-
ment included chloride leaching with subsequent control of waste water eff-
luents indicating an increased recycling in mining and milling.  Water re-
clamation in the mining industry also has shown promise for future pollution
abatement as well as being the keystone to byproduct marketing.

*Reviews, *Industries, *Water reuse, *Pollution abatement, Recycling, By-
products, Water pollution control, Sulfur compounds, Metals, Mining,
Costs, Federal jurisdiction
 200J

 ENVIRONMENT UPDATE,

 Siehl, G.

 Library Journal, Vol. 99, No. 10, p 1357-1363, May 15, 1974.

 A  review of environmental materials and developments in 1973 is presented
 with  the following trends being of major importance.  As a result of the
 energy situation in the United States, Congress approved the Alaska pipe-
 line, authorized year-round daylight savings time, set maximum highway speed
 limits, approved the reconsolidation and expansion of energy research endan-
 gered species.  Energy also headed the list of environmentally related issues
 with which the executive branch was concerned during 1973.  Books published
 in 1973 did not reflect the issues given most weight by government, the press,
 and the public; energy does not dominate the list of new titles availble for
 review.  Park, recreation, and wilderness books ranked highest in number.
 A  number of books have continued the assessment of the degree to which the
 environment has been damaged and of the steps required to set things right
 again.  Interest in the resources of the oceans has continued to grow while
 efforts to prevent additional pollution of these waters have struggled to
 keep pace.  The energy situation and the desire to become energy sufficient
 have made the expected hydrocarbon resources of the continental shelf more
 attractive and newsworthy.

 *Reviews, *Environment, *Publications, Federal government, Oceans, Energy,
 Parks, Recreation facilities
                                         776

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201J

NATIONAL ENVIRONMENTAL POLICY SHIFTS:  A CASE FOR
ENGINEERING MANPOWER PLANNING,

Snarponis, J. M.

Institute  for the Certification of Engineering
Technicians

Professional Engineer, Vol. 44, No. 5, p 29-31, May 1974.  1 fig.

Industry has recognized the need  for effective manpower planning and has
developed  a number of methodologies and systems to meet specific needs of
its own.   Government agencies, especially the Environmental Protection
Agency, have also contributed to  the programs.  Successful manpower plan-
ning systems relate predictors to manpower requirements as a basis for
projections.  Three types and levels of manpower planning for waste water
national macro-manpower planning  to determine the levels of economic
growth necessary to achieve employment targets or to fill the human
resource needs for meeting national goals; national manpower program
planning for administration of programs designed to remedy the problems
of special groups of persons; and, micro-manpower planning for the
specialized needs of private business firms, employer associations, employee.
associations, and public agencies.

*Manpower, *Employment opportunities, *Engineering personnel, *Human
resources, Occupations, Professional personnel, Resource allocation,
Waste water treatment, Treatment  facilities
202J

THE MOVEMENT OF EFFLUENT FROM THE CITY OF MIAMI SEWAGE
OCEAN OUTFALL,

D'Amato, R.

University of Miami Sea Grant Program,
National Oceanic and Atmospheric Administration Sea
Grant No. 2-34147, Coral Gables, Florida

Sea Grant Technical Bulletin No. 27, August, 1973.  91 p, 23 fig, 7 tab,
38 ref.

Concern about the location for the ocean outfall in Miami, Florida has
existed for some time.  It is maintained that the present discharge loca-
tion is completely unacceptable and that the following recommendations are
made from the evaluation presented.  Until major alterations are made on the
Miami Sewage Treatment Plant, improved practices need be initiated at the
plant itself.  Furthermore, that waste water treatment plant effluents be
discharged between 300 and 400 feet through diffusers and that treatment
procedures should be increased at least to the state law requirments of
90 percent BOD removal for all ocean outfalls.  Finally, serious con-
sideration should be given to advanced waste treatment and water reuse
systems and that present and planned treatment facilities be prepared for
eventual transfer to water reuse.

*Effluents, *0utlets, *Waste water treatment, Waste discharge, Tertiary
treatment, Water reuse, Treatment facilities, Biochemical oxygen demand

*Miami,  Florida, Treatment plants
                                        777

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 203J

 OZONE TREATMENT FOR POTABLE WATER,

 Water Services, Vol. 78, No. 938, p 117-118, April, 1974.

 A Swiss firm, Kerag, recently completed an ozone drinking water treatment plant
 for Nuremberg.  Water from the confluence of the Danube and Lech rivers is
 used for drinking purposes in Nuremberg, and the new ozonation process will
 render this water as fresh and clear as aline spring water.  Kerag's process
 involves the use of a high frequency technique of ozone generation.  The
 treated water is simultaneously enriched in oxygen and freed of excess car-
 bonic acid.  Kerag has also undertaken a project to provide an ozone water treatment
 plant for Rotterdam, a city as large as Nuremberg, with one million residents.
 Kerag is also involved with a large ozone high frequency generation water
 treatment plant at Zurich.

 *Potable water, *Water quality, *Ws.ter quality control, *0zone, *Dissolved
 oxygen, Treatment facilities

 *Kerag, *0zonation, Switzerland, Zurich, Nuremberg, Rotterdam, Rhine, Danube,
 Lech
204J

PLASTIC-MEDIUM TRICKLING FILTERS FOR BIOLOGICAL NITROGEN
CONTROL,

Buddies, G. A., Richardson, S. E., Earth, E. F.

Dew Chemical Company
Environmental Control Systems

Journal of the Water Pollution Control Federation, Vol. 46, No. 5, p 937-
946, May, 1974.  8 fig, 9 tab, 9 ref.

In evaluating the effects of waste water discharged to a receiving body, increas-
ing attention is being paid to Nitrogenous Oxygen Demand.  Many efficient
conventional biological treatment facilities are capable of high removals of
BOD (90 percent and up) yet these same facilities usually remove no more
than 10 to 60 percent of the NOD.  These NOD-rich effluents have been shown
to play a major role in the oxygen balance of receiving waters.  This paper
described the evaluation of controlling parameters, operational characteristics,
basic design criteria, and economics of using plastic media trickling filter
nitrification as a method of NOD reduction.  Results of the testing done show
that the plastic-medium trickling filter is a stable unit process producing
high quality effluent.  Final clarification is not always necessary after this
process and therefore the operation may be economically competitive with
other physico/chemical and biological methods of NOD reduction.

*Trickling filters, *Biochemical treatment, *Nitrification, Waste water treat-
ment, Bacteria, Biochemical oxygen demand, Toxicity, Chlorination, Design
criteria, Chemical treatment

*Plastic-medlum trickling filters, Dow Chemical Corporation
                                            778

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205J

POLYCHLORINATED BIPHENYLS IN TREATMENT PLANT
EFFLUENTS,

Dube, D. J., Veith, G. D., and Lee, G. F.

Department of Natural Resources,
Madison, Wisconsin

Journal of the Water Pollution Control Federation, Vol. 46, No. 5, p 966-"- p2,
May, 1974.  3 fig, 4 tab, 8 ref.

This study was done to determine the amount of contamination by PCB's in
the waste water of 11 southeastern Wisconsin cities.  Samples were taken of
the inflowing waste stream, in the primary settling tank, in the trickling
filter effluent, and in the final effluent of the treatment plant.  Assay
was done by gas-liquid chromatography.  Results showed 6 of the 11 munici-
pal treatment plants had effluent concentrations of 0.1 to 0.5 micrograms/liter
of a compound which appeared to match the Aroclor 1254 chromatogram.  Two
other municipalities had effluent concentrations of 1 microgram/liter of
Aroclor 1254 equivalent.  One city had a maximum of 42 micrograms/liter in
effluent waters and 5.2 rag/liter in the digester sludge of Aroclor 1248
equivalent.  These concentrations were quite variable with time.  From the
results of this study if appears that treatment of domestic waters removes
up to 70 percent or more of the PCB's in the inflowing waters.

*Polychlorinated biphenyls, *Chromatography, *Waste water treatment, Analytical
techniques, Wisconsin, Sampling, Cities, Domestic wastes., Municipal wastes.
   206J

   SURVEY AND EVALUATION OF MARINE SANITATION DEVICES,

   J. J. Henry, Company, Incorporated,
   Moorestown, New Jersey

   National Technical Information Service Report No. AD-770 327, June,  1973.
   43 p, 70 fig, 15 tab, 85 ref.

   A study of available marine sanitation devices  (MSD) and a technical evaluation
   of how these systems will interface with 14 representative vessels was
   conducted.  Its objective was to perform an extensive survey and technical
   description of the various individual sanitation devices currently marketed
   or under development for installation onboard federal, commercial, and/or
   recreational watercraft.  Also evaluation of the applicability and potential
   impact of marine sanitation concepts and individual systems relative to these
   vessels was made.  This evaluation considered the interactions and impact
   of the concepts and systems on the major installation constraints, operating
   characteristics, and capital/operating costs of each representative  vessel.

   *Sanitation, Recreation, Evaluation, Federal jurisdiction, Installation,
   Treatment, Capital costs, Ships, Operating costs, Surveys, Systems analysis

   *Marine devices, *Watercraft, Marine sanitation devices (MSD), Sample
   vessels, Commercial watercraft
                                          779

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 207J

 THE STATUS OF ACTIVE DEEP MINES  IN THE MONONGAHELA RIVER BASIN,

 Environmental Protection Agency,,
 Wheeling, West Virginia

 National Technical  Information Service Report No. PB-227 064, January, 1973.
 129 p, 4 tab.

 The Monongahela Enforcement Conference survey of mines in the Monongahela
 River basin found that forty-eight active mines produced a discharge at  the time
 of a resurvey in 1971 and 1972.  The owners or operators of 14 additional
 active mines reported no discharges.  In Pennsylvania, the 23 active discharg-
 ing deep mines had  45 discharge points, 13 of which had chemical treatment faci-
 lities.  Only the Hutchison Mine, with two discharges, produced any serious
 pollution problems  in the receiving stream.  That mine and the Pennsylvania
 Department of Environmental Resources are presently in litigation.  In West
 Virginia, the 25 active discharging deep mines had 112 discharge points, eight
 of which were receiving chemical treatment.  The ten mines in the Christopher
 and Mountaineer Divisions of Consolidation Coal were responsible for 75  dis-
 charges.  These Consol mines and two Eastern Associated Coal Corporation mines
were investigated in greater detail.  It was found that the mines in the
 Christopher Division of Consol caused most of the stream pollution from  active
 deep mines in the basin.

 *Strip mine wastes, *Mines, *Mine wastes, Pollution, Streams, Coal mines,
 Reviews

 *Monongahela River basin, Mine discharge, West Virginia, Monongahela
Enforcement Conference, Active mines, Receiving stream
208J

SEWAGE SLUDGE DISPOSAL IN A SANITARY LANDFILL, VOL I:  SUMMARY
AND CONSLUSIONS; VOL II:  DESCRIPTION OF STUDY AND TECHNICAL
DATA,

Ralph Stone and Company, Incorporated,
Oceanside, California

National Technical Information Service Reports, No. PB-225 361 and PB-225 362,
1973.  394 p, 56 fig, 83 tab, 57 ref.

A two volume report gives the results of work conducted during the first two
years (January 1971-December 1972) of a three-year demonstration study of the
disposal of liquid sewage sludge .and septic tank pumpings into solid waste
at a sanitary landfill.  Pilot plant lysimeters were used to investigate the
effects of sewage and septic tank sludges on solid waste temperature, decom-
position, leachate settlement, insects, gases, and odors.  Three large field
lysimeters  were monitored for leachate, temperature, gas compaction, settle-
ment, and waste decomposition as determined by core sampling.  The full-scale
disposal of sludge was monitored for runoff, leachate, equipment operating
efficiency (time and motion studies), odors, vectors, blowing litter, and
weather conditions (rainfall, temperature, wind, and evaporation).

*Landfill, *Waste disposal, *Sewage sludge, Liquid wastes, Tanks, Pumps,
Solid wastes, Odors, Settlement, Monitoring, Lysimeters, Leachate, Decomposi-
tion, Pilot plants, Weather, Gases, Septic tanks

Sanitary landfills, Septic tank pumpings
                                        780

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 209J

 MATERIALS  FOR WET  OXIDATION  PROCESSING EQUIPMENT (SHIPBOARD),

 McCreight,  L.  R.

 National Materials Advisory  Board,
 National Research  Council,
 Division of Engineering

 National Technical Information  Service Report  No. AD-771  745,  November,  1973.
 75  p,  5 fig,  7 tab,  12 ref.

 Since  the wet  oxidation  process requires  the contaminant  of corrosive products
 (the material  being  processed can range from very acidic  to slightly basic and
 over a broad spectrum of wastes), at  elevated  temperatures and pressures,
 difficult but  solvable materials-of-construction problems occur.  Based  on
 the current state-of-the-art, wet oxidation systems  can be constructed from
 commercially pure  titanium as well as from titanium  alloyed with palladium
 (.12-.25 percent).   This type of system,  it is felt,  can  be operated safely
 at  approximately 500 F with  reasonable assurance of  moderate life  (approximately
 10  years).   A  tantalum-lined and coated titanium system provides the longest
 life of materials.   For  higher  temperature operation up to 600 F and a pro-
 jected equipment life of 15  years, a  ceramic-lined and coated  carbon steel
 or  titanium system would have to be developed.   Here, an  added advantage to
 ceramic lining is  improved heat insulation, allowing for  a reduction of  ex-
 ternal insulation.   In addition, a penetration monitoring system can be  incor-
 porated in  the ceramic lining.   From  an overall design consideration point of
 view,  it appears that the wet oxidation process can  be operated in a con-
 tinuous manner in  shipboard  installations and  the reaction vessel can consist
 of  a piping array  configuration.

 *0xidation,  *Equipment,  *Processing,  *Ships, Corrosion, Acidity, Wastes,
 Installation,  Temperature, Titanium,  Design criteria, Construction materials,
 Monitoring

 *Wet oxidation, State-of-the-art review,  Tantalum, Palladium,  Carbon steel
210J

MANPOWER REQUIREMENTS FOR WASTE WATER COLLECTION SYSTEMS IN
CITIES AND TOWNS UP TO 150,000 IN POPULATION,

North Caroline A & T State University,
Greensboro, North Carolina

National Technical Information Service Report No. PB-227 039, June, 1973.
Ill p, 11 fig, 1 tab, 10 ref.

The water pollution control field has need for information on manpower, pro-
vided by this manual.  Requirements for effective operation and maintenance
of waste water collection systems in municipalities of under 150,000 people
are developed.  Specific occupations in the form of Occupational Descriptions
include duties, physical demands, and working conditions, as well as behavioral
and psychological traits recommended for various positions,  Manpower planners
and trainers as well as administrators have need of curriculum programs for
training of personnel and development of resources.

*Water pollution control, *Manuals, *Municipal wastes, *Municipal water, Human
populations, Personnel, Occupations, Human resources, Working conditions,
Employment, Labor, Planning, training

Manpower requirements, Occupational description
                                       781

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211J

THE POTENTIAL ROLE OF MODERN DESALINATION TECHNOLOGY IN THE
DEVELOPMENT OF FRESH WATER SUPPLIES IN UNDER-DEVELOPED
TERRITORIES,

Peel, C.

Water Services, Vol. 78, No. 938, p 119-123, April 1974.  3 fig, 1 tab.

Estimates of the future world population growth rate, food supply, and fresh
water needs are discussed briefly.  Statistics on presently installed and
operating desalination plants are given.  The various desalination techniques
presently available or under development are outlined under the following
three headings:  processes involving a change of phase, methods utilizing
some form of membrane, and processes based on a chemical reaction.

*Desalination, *Desalination plants, *Desalination processes, Membrane
processes, Water supply, Chemical reactions
212J

DOUBLE-BOTTOM BARGES PROVIDE GREATER PROTECTION AGAINST
WATER POLLUTION,

Marine Engineering/Log, No. 5, p 42-43, May 1974.

The Dravo Corporation has designed and built double-skin integrated tank
barges used for the transportation of petroleum products.  From a fuel
utilization standpoint, transportation by towboats and barges is considerably
more efficient and economical as compared with river tank shipping, rail
service, and truck transport.  In double-skin barges, all framing is on
the exterior so that tank compartments have smooth, easy-to-clean interior
surfaces assuring purity of cargo.  Also, double-skin construction provides
for greater protection against spillage should the exterior shell of the
barge hull be damaged.  The upward trend toward the use of double-skin
barges for transporting petroleum products is part of the current growth
in overall shipping volume on the 2;>,000 miles of the United States' inland
waterways system.

*Barges, transportation, Water pollution control, Construction materials,
Oil spills, Costs, Inland waterways

Petroleum products
                                        782

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 213J

 HOW TO CURTAIL OR END DISCHARGES OF SEWAGE FROM SHIPS,

 Marine Engineering/Log, No. 5, p 34-37, 119, May 1974.

 Prevention of discharging untreated sewage from vessels in marine waters
 is becoming increasing apparent not only in the United States, but on an
 international level.  Due to existing and proposed regulations, ship operators
 must install marine sanitation devices (MSD's) costing about $25,000 to
 $80,000, in addition to installation and maintenance costs.  Various types
 of MSD's and discharge systems as well as selection factors are discussed
 in relation to United States regulations.

 *Sea water, *Boating, *Regulations, *Water pollution control, Sewage treatment,
 Treatment facilities, Equipment, Capital costs, Boats, United States,
 Discharge, Maintenance costs

 *Marine Sanitation Devices (MSD's)
214J

UPTAKE OF CHLOROBIPHENYLS BY OYSTERS,

Vreeland, V.

Woods Hole Oceanographic Institution,
Woods Hole, Massachusetts

Environmental Pollution, Vol. 6, No. 2, p 135-140, February, 1974.
2 fig, 16 ref.

Accumulation of individual chlorinated biphenyls in small osyters (Crassostrea
vlrginica) was proportional to the degree to chlorination of the isomer and
to its concentration in seawater at environmental levels.  Equilibrium was
reached after one month, with concentration factors of 1200 to 48,000 for
isomers with 2 to 6 chlorine atoms per molecule.  Partioning of PCB between
more hydrophobia lipids and ambient seawater has been rejected as the uptake
mechanism.

*Polychlorinated biphenyls, *0ysters, Chlorination, Sea water, Investigations

*Chlorobiphenyls uptake
                                        783

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 215J

 COLUMBUS REPLACES HISTORIC WATER TREATMENT PLANT,

 Cosens, K. W., and Farr, F. Jr.

 Alden E. Stilson and Associates, Limited,
 Columbus, Ohio

 Public Works, Vol. 105, No. 6, p 60-62, June 1974.  1 fig, 1 tab, 1 ref.

 A 65 mgd new plant supply facility is replacing the Dublin Road Plant in
 Columbus, Ohio.  The new treatment plant is being constructed in two phases:
 the first involving a functional plant of full capacity; and the second
 involving demolition of old chemical buildings, filters, flocculation and
 settling tanks, and wash-water facilities, followed by construction of
 additional clear well capacity, underground piping, a chemical handling
 facility, lighting, roads, fencing, and landscaping.  Treatment consists
 of screening, coagulation with alum, softening with lime and soda ash or
 caustic soda, recarbonation, pre- and post-chlorination, taste and odor
 control, and threshold treatment.  Treatment plant construction costs are
 estimated at $15.5 million.

 *Treatment facilities, *Waste water treatment, Construction materials,
 Construction costs, Design criteria, Sites, Water supply, Water treatment

 *Columbus, Ohio, Treatment plants
216J

ARSENIC-CONTAINING CARBONATED WATERS, OCCURRENCE PECULIARITIES,
CHEMICAL COMPOSITION, OCCURRENCE CONDITIONS (Mysh'yaksoderzhashchiye
uglekislye vody Kavkoza (osobennosti rasprostraneniya, khimicheskiy sostav,
usloviya formirovaniya)),

Krainov, S. R., Volkov, G. A., Petrova, N. K., Baturinskaya, I. V.

All-Union Scientific Research Institute of Hydrogeology
and Geological Engineering, Moscow, U.S.S.R.

Geokhimiia, No. 2, p 212-227, 1974.  5 fig, 2 tab, 27 ref.

The Caucasus is the largest Soviet province of carbonated arsenic-containing
water which is of the youngest structures.  It is characterized by high
chlorinity and high As/Cl, As/B ratios.  The mobility sequence in such water
is Cl greater than or equal to As greater than B.  The enrichment of carbonated
water in arsenic is connected with local thermometamorphic processes of its
extraction from rocks.  These processes are intensified in the presence
cf chloride water.  The process of carbonated water enrichment in arsenic
is a process being superposed upon chloride water and secondary in relation
to it.

*Carbonate rocks, *Boron, *Chlorine

*Carbonated water, *Arsenic, Chemical mobility, Water enrichment, U.S.S.R.
                                         784

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217J

THE JUBILEE OF THE ROYAL COMMISSION STANDARD,

Roberts, F. W.

East Suffolk and Norfolk River Authority, England

Water Pollution Control, Vol. 73, No. 2, p 129-137, 1974.  2 tab, 11 ref.

Factors involved both in setting standards and in assessing river pollution
levels suggested by the Royal Commission on Sewage Disposal are discussed.
Basic topics reviewed include tests for sewage and sewage effluents, dilution
and suspended solids, reaeration capacity, potable water from rivers, and
the administration of standards.

*Sewage disposal, *Standards, Testing, Biochemical oxygen demand, Nitrogen,
Temperature, Water quality standards, Suspended solids, Waste dilution,
Reaeration, Potable water, Administration, Water pollution control, Rivers

Great Britain
218J

EFFECT OF pH ON SURVIVAL OF ESCHERICHIA COLI,

Parhad, N. M., and Rao, N. U.

Central Public Health Engineering Research Institute,
Nagpur, India, Bacteriology Cell

Journal of the Water Pollution Control Federation, Vol. 46, No. 5, p 980-986,
May 1974.  7 fig, 16 ref.

An attempt has been made to delineate the factors affecting bacterial
reduction of effluents in stabilization ponds using E. coll as a representative
of the indicator bacteria.  A 24-hour peptone broth culture of E. coli isolated
from waste water was used in these experiments with evaluation by multitube
dilution technique using lactose broth in the presumptive test at 37°C for
24 to 48 hours.  Results are discussed and the following conclusions drawn.
The growth of different algae in sterilized waste water results in an increase
of pH from 7.5 to 10 or more.  Both E. coli and algae can grow together
when waste water is buffered at pH 7.5 but E. coli could not grow in waste
water when the pH was greater than 9.2.  E. coli, when grown in association
with algae, is eliminated because of the high pH produced as a result of
algal growth.  The decrease in E. coll observed in stabilization ponds is
attributed to the pH levels that are found in those ponds.

*E. coli, *0xidation lagoons, *Bioindicators, Effluents, Hydrogen ion
concentration, Waste water treatment, Algae, Growth rates, Laboratory tests
                                      785

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  219J

  RIVERS  POLLUTION SURVEY  IN SCOTLAND  IN RETROSPECT AND
  PROSPECT,

  Nicoll,  E.  H.

  Assistant Chief  Engineer,  Scottish Development
  Department,  Scotland

  Water Pollution  Control, Vol. 73, No.  2, p 178-181, 1974.

  A brief  review of the legislation and  regulations  formulated by the Scotish
  River Commission is presented.  A survey report published in 1972 recorded
  234  sewerage authorities serving 5.2 million persons with two-thirds of
  this population  being served by drainage systems terminating in tidal reaches
  of rivers, estuaries, and the open sea.  Six percent of all principal rivers
 were of poor quality or grossly polluted.  Expenditures for sewerage, sewage
  treatment, and disposal are given for  1971.

  *Rivers, *Surveys, *Sewage treatment,  *Water pollution, Water quality control,
 Governments, Legislation

 *Scotland
220J

THE AGRICULTURAL USE OF BLACKBURN SEWAGE SLUDGE,

Rawcliffe, E., and Saul, G. W.

Assistant Sewage Works Manager, Blackburn CBC, England

Water Pollution Control, Vol. 73, No. 2, p 168-177, 1974.  4 fig, 3 tab,
25 ref.

Information on the experiences both past and present associated with
agricultural use of Blackburn, England's sewage sludge is presented.  Over
the years, the repeated addition of sewage sludge to the Blackburn estate
has had a physical effect on the surface of the land.  The soil became soft
and waterlogged, and the frequency of application as practiced precluded
any remedial action by means of plowing.  Work has now commenced on a complete
soil survey of the whole of the sewage works estate with special reference
being given to metals.  The present policy regarding the new areas of farmland
now being treated with digested sludge by mobile tankers is to acquire the
use of sufficient land so that over the next thirty years at least the
accumulation of metals conforms to well within the suggested limits of 250 mg
per liter zinc equivalent in the top soil.

*Agricultural engineering, *Soil physics, *Soil conservation, *Sewage sludge,
Surveys, Metals, Topsoil, Soil investigation

Great Britain
                                    786

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221J

STUDIES ON THE EFFECTS OF THE ORAL ADMINISTRATION OF DI-(2-
ETHYLHEXYL)PHTHALATE ON SOME HEPATIC ENZYMES IN THE RAT,

Lake, B. G., Gangolli, S. D. Wright, M. G., Grasso, P.,
and Lloyd, A. G.
                                                                 ,,V
The British Industrial Biological Research Association,
Carshalton, Surrey, England

Biochemical Society Transactions, Vol. 2, No. 2, p 322-325, 1974.
2 tab, 5 ref.

In the context of a toxicological study on the safety evaluation of di-(2,-
ethylhexyl)phthalate, a commonly used phthalate ester, the biochemical and
histochemlcal effects on the liver after the oral administration of this
ester to rats was investigated.  Metabolic studies conducted on young male
Wistar albino rats with the ester at single oral doses of 20 mg/kg and 2000 mg/kg
and seven daily doses of 200 mg/kg, showed that 98-99 percent of the radio-
activity was excreted within four days.  The study of the hepatic effects was
conducted in rats by the daily gastric intubation of the phthalate ester
dissolved in corn oil, at: a dosage of 200 mg/kg for 4, 7, 14, and 21 days
respectively.  The results of the study, showing that the effects of di-C2-
ethylhexyl)phthalate on the rat hepatic mitochondrial and microsomal enzymes
are not wholly reproducible by either phthalic acid of 2-ethylhexan-l-ol,
indicate that other metabolites of di-(2-ethylhexyl)phthalate may contribute
to the biochemical effects.

*Water pollution sources, *Toxicity, Sea water, Laboratory tests, Laboratory
animals, Animal physiology, Animal pathology-, Environmental effects

*Di-(2-ethylhexyl)phthalate
222J

WATER-BORNE TRANSMISSION OF CHLORAMPHENICOL-RESISTANT
SALMONELLA TYPHI IN MEXICO,

Gonzalez-Cortes, A., Bessudo, D., Sanchez-Leyva, R.,
Fragoso, R.,  Hinojosa, M., and Becerril, P.

Secretariat of Health and Assistance of Mexico,
Institute of  Health and Tropical Diseases, Epidemiology
Unit

Bulletin of the Panamerican Health Organization, Vol. 8, No. 1, p 1-5,
1974.  1 fig, 2 tab, 8 ref.

In mid-1972 an outbreak of typhoid fever occurred in a small village in Central
Mexico.  Eighty-three cases were recorded with six deaths.  Most patients
lived in an area of the village with the highest population density and
lowest income levelsclose to an irrigation canal which traverses the village.
Prior to the  epidemic, the municipal water system had not been operational
because of a  defective pump.  Food-specific attack rates implicated the
drinking of water from the canal as the source of the disease with restoration
of the water  system promptly halting the outbreak.

*Human diseases, *Potable water, *Mexico, *Salmonella, Water pollution sources,
Water supply, Irrigation canals, Municipal water

Typhoid fever
                                       787

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 223J

 THE  EFFECT  OF  NITRITES  ON  ISOLATION-INDUCED AGGRESSION
 IN MICE,

 Gruener,  N.

 Hebrew University-Hadassah Medical School
 Jerusalem,  Israel
 Environmental  Health Laboratory

 Pharmacology Biochemistry  and Behavior,  Vol.  2,  No.  2, p 267-269,  March-April,
 1974.   2  tab,  6 ref.

 Chronic administration  of  sodium nitrite,  one gram per liter,  in drinking
 water  of  pregnant mice  and their offspring caused a significant increase in
 the  isolation-induced aggression of the  male  young.   The cessation of
 administration of sodium nitrite reduced the  aggressive behavior of the
 experimental group to the  control level.   Since  nitrates and nitrites are
 frequently  ingested in  human drinking water,  health implications are cited.

 laboratory animals, *Potable water,  *Nitrites,  *Animal behavior,  Laboratory
 tests

 *Sodium nitrite,  *Anlmal isolation, Mice
224J

PROGRESS IN THE RURAL WATER PROGRAMS OF LATIN AMERICA,

Donaldson, D.

Pan American Health Organization

Bulletin of the Panamerican Health Organization, Vol. 8, No. 1, p 37-53,
1974.  2 fig, 6 tab, 18 ref.

The proportion of rural people in Latin America with access to potable water
rose dramatically during the last decade.  A look at the current situation is
detailed exploring a number of existing problems.  Several methods offering
considerable promise for the future are also outlined.

*Potable water, *Water supply, Rural areas, *Future planning (projected),
Water resources development

*Latin America, Pan American Health Organization
                                        788

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225J

ASBESTOS-LIKE FIBERS IN DULUTH. WATER SUPPLY., RELATION TO CANCER
MORTALITY,

Masson, T. J., McKay, F. W., and Miller, R. W.

Journal of the American Medical Association, Vol. 228, No. 8, p 1019-1020,
May 20, 1974.  1 tab, 6 ref.

Asbestos-like fibers in industrial waste first entered the water supply of
Duluth in 1966.  During the next 14 years, no carcinogenic effect was apparent
in the patterns of cancer mortality among persons of all ages, or among
children.  However, ther period of observation is shorter relative to the
latent period of occupationally induced carcinogenesis from asbestos.  A
longer period of follow up than was possible in this study will be necessary
before it can be concluded that there is no cancer hazard related to the
drinking water supplies of Duluth and its neighboring communities.

*Water supply, *Asbestos, *Statistical methods, Industrial wastes, Minnesota

*Cancer, *Carcinogenesis, *Duluth, Minnesota
 226J

 CAN DREDGING BE CONTINUED TO MAINTAIN GREAT LAKES,

 Cable, C.

 North Central Division,
 U. S. Army Corps of Engineers,
 Construction - Operations Division

 World Dredging and Marine Construction, Vol. 10, No. 5, p 24-27, May, 1974.
 5 fig.

 Escalating dredging costs, environmental concerns, inflation, misinformation,
 and moratoriums on dredging have raised the issue of whether dredging operations
 can be continued on the Great Lakes.  The Corps maintains 64 harbors, 157
 miles of improved channel, and the locks of the St. Mary's Falls Canal.  Normal
 dredging workload amounts to around 12 million cubic yards for maintenance
 and 1 million cubic yards for the improvement of these facilities each year.
 For the past six years the dredging level has been restricted to about 50
 percent of normal and will continue to be curtailed until suitable disposal
 sites on land can be found and prepared to take polluted dredge material.
 There are 71 dredging projects which will require land disposal sites.
 The Corps is currently developing plans for 16 of these sites.  Two sites
 are moving into preparation now with the other 14 to start later this year.
 The Corps at its waterways Experiment Station is currently engaged in
 research in seven broad areas:  environmental impacts and aspects of open
 water disposal; environmental impacts and aspects of land disposal; new
 disposal concepts; productive uses of dredged material; disposal area reuse
 and multiple utilization; dredge material treatment techniques and equipment;
 and dredging/disposal equipment and techniques.

 *Dredging, *Solid wastes, *Disposal, *Harbors, *Channels, *Channel improvement,
 Environmental effects, Costs, Great Lakes, Research and development

 *Polluted dredge material, *0n-land disposal
                                      789

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 227J

 WATER LAWS IN USSR,

 Sharma,  S. K.

 Himachal Pradesh State Electricity Board,
 Simla,  India

 Indian Journal of Power and River Valley Development,  Vol.  23,  No.  12,  p 392-
 393,  December, 1973.

 The water laws of the USSR as  embodied in  the  legislation entitled  "Foundation
 of Water Management Legislation  of the Union of  Soviet Socialist  Republics",
 passed by the Supreme Soviet in  December 1970  are  reviewed.   This legislation
 is composed of five main parts:   "General  Regulations",  ownership,  regulation,
 etc.;  "Water Management",  grant  of use to  municipalities,  etc.; "Protection
 of Waters and Prevention of Their Detrimental  Effect", control  of pollution,
 etc.;  "State Control  and Planning of Water Utilization",  resources  inventory
 and resource allocation;  and "Responsibility for Breaking the Water Laws",
 the civil and criminal code as it applies  to this  legislation.

 *Riparian rights,  *Legislatlon,  *Planning,  Law enforcement,  Resource allocation,
 Water  pollution control

 India, U.S.S.R.,  Water laws
228J

ENVIRONMENTAL INFLUENCES ON OFFSHORE FACILITIES,

Hull, A. R., Austin, T. S.

United States Department of Commerce,
National Oceanic and Atmospheric Administration,
Environmental Data Service

Marine Technology Society Journal, Vol. 8, No. 4, p 15-21, April-May, 1974.
6 fig, 6 ref.

Environmental data will play a very important role in the planning, site
selection, design, construction, and operation of offshore facilities
including deep water ports for supertankers.  Because of the increasing
necessity of energy importation, the United States will be developing three
types of offshore facilities:  nuclear powerplants, drilling rigs, and super-
tanker terminals (deep water ports).  The specific types of data needed
during each phase of development of these facilities, especially deep water
ports, are discussed.  Some of the categories reviewed included:  distance
offshore of suitable water depth; storm surge; extreme wave-wind conditions;
and severe storm frequency.  Cost effectiveness versus protection of the
environment is discussed.  The availability of historical environmental data
from national centers and the need for subsequent on-site observations is
examined.  Two recent data guidelines developed for potential supertanker
ports are reviewed, and the need for more detailed studies is cited.

*Environmental Effects, *0n-site data collections, *Harbors, *0ffshore
platforms, *Data collections, Nuclear powerplants

*Deep water ports, *Environmental influences, ^Historical studies.
                                        790

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  229J

  NITRATES IN WATER SUPPLIES (NITRATE DE L'EAU),

  International Standing Committee on Water Quality
  and Treatment

  Aqua,  No.  1, p 5-25,  1974.  25 p,  6 tab,  67 ref.

  An international investigation was made to review the effects of raised
  nitrates in water supplies on health and water  quality.   Elevated nitrate
  concentration in the  diet and large numbers of  nitrate-reducing bacteria
  in the upper digestive tract is a primary cause of infantile methamoglobinaemia.
  Susceptibility varies with external conditions, but a safety factor in public
  health should be taken into account.  It was concluded that the recommended
  limit  of 45-50 rag/liter should not be raised but should  be further investigated.
  Water  resources with  more nitrate than 45-50 mg/liter could be made safe by
  diluting with water of lower nitrate content.  Pilot plants have tested
  processes for removal of nitrate from sewage and water.   Another alternative
  is to  search for the  origin of nitrogen in all  forms from domestic sewage,
  as well as industrial wastes and runoff,  and to control  these sources.

  *Reviews,  *Public health, *Nltrogen, *Nitrates, *Water supply, Reviews,
  Investigation, Domestic wastes, Safety, Bacteria, Pathology, Disease,
  Pilot  plants, Waste removal, Runoff, Industrial wastes

  World  Health Organization, Methamoglobinaemia
 230J

 COUNTY WATER SYSTEM SOLVES DRY AREA PROBLEMS,

 Hilbert, R. B., and Holzworth, R. T.

 Salt Lake County Water Conservancy District,
 Salt Lake City, Utah

 Public Works, Vol. 105, No. 6, p 72-73, June 1974.

 Discussed are the problems and complexities involved in the supply of adequate
water to a large and expanding metropolitan area where average annual rainfall
 is only 16 inches.  Using a mix of facilities including deep wells, springs,
river diversions, runoff impoundment, and groundwater management, Salt Lake
 City has been able to meet its needs to date.  Future growth in the area
appears to depend on the willingness of the state to support the importation
of water from outside the Salt Lake City region as all local resources are
almost fully development.  The need for land-use planning and comprehensive
consideration of a multitude of factors in future water supply is discussed.

*Water resources,  *Municipal wastes,  *Water resources, development, *Planning,
*Water supply,  Water distribution,  Arid climates, Utah, Local governments,
Cities,  Land use

Salt Lake City,  Utah
                                         791

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 231J

 IS THE WATER SAFE TO DRINK?   PART I:   THE PROBLEM,

 Harris, R. H.,  and Brecher,  E.  M.

 Environmental Defense Fund,  Water Resources Program

 Consumer Reports, Vol. 39, No.  6, p 434-443, June 1974.

 The United States is currently  in the process of implementing a mammoth
 Federal-state program to clean  up its waterways.  Even if this program pro-
 ceeds on schedule, it will take more than a decade to achieve its goals.
 This report was written to call for faster action on a program to upgrade
 Che drinking water now being used in over 40,000 community water systems in
 the country.  The reasons given for urging such a program include the fact
 that even if all man-made pollution were eliminated, there would still be
 natural sources of pollution that would necessitate purification operations.
 There will always be some pollution from accidental spills or discharges, and
 agricultural runoff; if water pollution abatement is put off as air pollution
 abatement has been, the United  States will be drinking dirty water for some
 time to come.  The costs of improving our drinking water now are reasonable
 enough in view of the extra health protection which would be gained.  Types
 of pollution discussed in the article include:  asbestos, bacteria, viruses,
 heavy metals, and organic compounds.

 *Domestic water, *Public health, *Water pollution, *Potable water, *Water
 quality, Accidents, Contamination, Costs, Water supply

 Opinions
 232J

 EFFECTS  OF DIETARY MERCURY  ON MINK,

 Aulerich, R. J., Ringer, R. K., and  Iwamoto, S.

 Michigan State University
 East Lansing, Michigan,
 Poultry  Science Department

 Archives of Environmental Contamination and Toxicology, Vol. 2, No. 1  p 43-61
 March, 1974.  6 tab, 25 ref.

 Mercury contamination in Lake Erie and other lakes and rivers in the United
 States and Canada caused mink ranchers to consider the possibility that mink
who ingested mercury-contaminated fish were contacting mercury poisoning.
Mercury in fish tissue is in the methylated form, quite highly toxic to man.
 Tests were conducted where mink were fed dietary methylmercury; 5 ppm were
 lethal within one month to adult mink.  Mercuric chloride, the inorganic
 form, was not toxic at the level of 10 ppm.  Most likely this is because the
 organic form easily penetrates the brain while the inorganic form is excreted
 from the body.

 *Toxicity,  *0rganic matter, *Inroganic matter, *Mink, Fish, Mercury, Great
Lakes region, Food chains, Lake Erie, Lakes, Rivers, Canada, Fish toxins

Methylmercury,  Mercuric chloride
                                          792

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233J

LEGAL CONTROLS OF POLLUTION IN THE GREAT LAKES BASIN,

Landis, H.

Canadian Bar Review, Vol. 48, p 66-202, 1970.

Legal control of pollution of groundwater and surface waters In the Canadian
part of the Great Lakes Basin is discussed, and the constitutional basis of
such controls is considered.  Provincial rather than federal primacy is
recommended.  Provisions of several laws are reported, including those of
the Ontario Water Resources Commission Act; the Municipal, Drainage, Public
Parks, and Planning acts; the Public Health and Pesticides Acts; the
Conservation Authorities Act; the Energy, Gasoline Handling, and Air Pollution
Control Acts; the Mining Act; the Lakes and Rivers Improvement, Public
Lands, and Provincial Parks Acts; the Migratory Birds Convention Act; and
the Canadian Water Act.  Judicial decisions concerned with federal harbors,
and canals, inland fisheries, agriculture, and Indian lands are also reviewed.

*Legal review, *Legislation, *Groundwater, *Surface water, *Pollution, *Law
enforcement, Canada, Great Lakes region, Harbors, Canals, Fisheries, Agriculture,
Indian reservations, Water resources, Municipal water, Planning, Pesticides,
Public health, Air pollution, Mining, Migratory birds
 234J

 CONTROL OF COLIFORM  IN A  SULPHITE MILL AERATED  STABILIZA-
 TION  BASIN,

 Watkins, S. H.

 Crown Zellerbach Corporation

 Paper Trade Journal, Vol. 158, No. 17, p 28-30, April  29, 1974.

 High  concentrations  of coliforms in  the effluents of Lebanon, Oregon were  due
 to their development at early stages rather  than growth during secondary treat-
 ment.  When a high background level  of coliforms is present  from industrial
 wastes, it becomes difficult to detect pollution from  sources of known public
 health significance.  The method here was to kill coliforms  in the incoming
 wastes on a small scale.  A modified chlorination system, employing caustic in-
 jection into the chlorinator's water supply was the most effective treatment
 found.  Bioassays and chemical analyses proved  that no toxic chlorine residuals
 resulted.  Methods for testing were  the Multiple Fermentation Tube and the
 Membrane Filter.  Pre-treatment was  found to be a practical  way to kill
 coliforms and obtain secondary effluents with acceptable levels of the coliforms.
 The modified chlorination processes may have other applications when more  op-
 portunities to optimize the process are discovered.

 *Coliforms, *Secondary treatment, *Sulfites, *Public health, *Chlorination,
 *Industrial wastes,  Water pollution, Water supply, Toxicity, Pre-treatment

 *Multiple Fermentation Tube, *Membrane Filter, Modified chlorination
                                       793

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235J

THE ABC PROCESS FOR IMPROVING THE TREATMENT OF WASTE WATERS
(LE PROCEDE ABC POUR AMELIORER LE TRAITMENT DES EAUX RESIDUAIRES),

Kerl, J. F.

Revue Generale Des Matieres Colorantes-Teintex, No. 2, p 75-77, 1974.  2 ref.

An integrated biological-chemical waste water treatment process is described
with respect to its applications in the textile industry.  Raw waste water
treatment by short detention aeration in a biological reactor in the presence of
activated sludge followed by rapid sedimentation and sludge recycle in a chemi-
cal separator is explained by citing studies utilizing mixed municipal and in-
dustrial sewage.  Advantages of the patented Accelerated Biological-Chemical
(ABC) process include economic considerations of short aeration detention times
and reduced land and equipment requirements, as well as technical advances of
high BOD, suspended solids, and phosphorus removals with superior performance
under shock loading and transient conditions.

*Waste water treatment, *Textiles, *Biological treatment, *Chemical treatment,
Aeration, Recycling, Activated sludge, Municipal wastes, Industrial wastes,
Costs, Equipment, Biochemical oxygen demand, Suspended solids

Integrated (biological-chemical) treatment, Phosphorus removal
236J

FULL-SCALE HARVEST OF AQUATIC PLANTS:  NUTRIENT REMOVAL
FROM A EUTROPHIC LAKE,

Peterson, S. A., Smith, W. L., and Malueg, K. W.

Environmental Protection Agency,
Corvallis, Oregon,
National Eutrophication Research Program

Journal of the Water Pollution Control Federation, Vol. 46, No. 4, p 697-707,
April, 1974.  5 fig, 6 tab, 27 ref.

Eutrophication in aquatic ecosystems is difficult to control once the nutrients
have entered the water body.  It was suggested that large-scale harvesting of
aquatic plants might be a feasible way to reduce nutrients in lakes.  This
method had been done on relatively small areas but not full scale.  The city
of Detroit Lakes, Minnesota had been supplying Lake Sallie with waste water
effluent for over sixty years and this site was selected to try aquatic plant
harvesting for three months.  Phosphorus loading was measured, and corresponded
with nutrient concentrations of the inflow but not with volume of the inflow.
The most significant conclusion was that continuous harvest of aquatic plants
from Lake Sallie during the growing season could not offset the high loading
of nitrogen and phosphorus.  The wet-weight harvest of 944,000 Ib of plants
removed only 1.37 percent of the total phosphorus input to the lake.

*Eutrophication, *Nutrients, *Aquatic plants, *Nitrogen, *Phosphorus, har-
vesting of algae, Lakes, On-site investigations, Waste water, Effluents

Aquatic ecosystems, Phosphorus loading, Minnesota (Lake Sallie)
                                     794

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237J

PHOSPHATE REMOVAL BY ALGAL  SYSTEMS,

Vanderborgh, N.  E., and  Buyers, A. G.

New Mexico University, Albuquerque, New Mexico,
Department of Chemistry

Journal  of the Water Pollution Control Federation, Vol.  46,  No.  4,  p  726-
734, April,  1974.   7 fig, 1 tab,  23 ref.

Growth of algae  in  surface  waters is a visible  type  of pollution.   Currently,
several  cities are  removing phosphates chemically  from their waste  water efflu-
ents, a  costly process.   The question has  been  raised as to  whether phosphorus
is the rate-limiting step in algal growth.  The Rio  Grande Valley of  New
Mexico has both  excessive nutrient concentrations  and excessive  sunlight,  two
conditions which are known  to stimulate algal growth.  The experiment consisted
of examining the rate of 32P removal from  solutions  of filtered, aqueous sodium
pyrophosphate under controlled conditions  of acidity, temperature,  luminant
flux, and nutrients.  Final data  for removal were  taken  by subtracting the
decay curve  from each of the experimental  plots.   Results suggest that two
mechanisms influence the rate of  radioactive phosphorus  (sodium  pyrophosphate)
removal  from chlorella cultures in soil-water and  chemical media.   Also, the
rate-limiting step  for the  removal can be  interchanged by a  variation in pH.
The removal  rate increases  and changes order as acidity  is increased.   The
inference is that orthophosphate  exchanges, not pyrophosphate  or phosphorus,
and the  hydrolysis  rate  are the rate determiners of  the  exchange process at
elevated pH  values.  A very rapid removal  of phosphorus  under  C02 enriched con-
ditions  suggests interesting strategies for removal  of phosphorus from surface
waters.

*Algae,  *Surface waters,  *Water pollution, *Phosphorus,  *Phosphates,  *Chemical
treatment, *Algal blooms, Waste water, Effluents,  Nutrients, Acidity,  Tempera-
ture, Soil water, Nutrient  removal

*Phosphorus  removal, *pH, Pyrophosphate, Orthophosphate,  Rio Grande Valley,
New Mexico
238J

CHRONIC  TOXICITY OF NICKEL  TO THE FATHEAD  MINNOW,

Pickering, Q. H.

Environmental Protection Agency,
Newtown  Fish Toxicology Laboratory,
C inc inna t i,  Oh io

Journal of the Water Pollution Control Federation, Vol.  46,  No.  4,  p  760-765,
April, 1974.  6  tab, 21 ref.

Metallic wastes  are received  by municipal waste water treatment  plants.  Nickel
seems to be  the  least effectively removed metal and was  investigated  concerning
the interaction  of metallic wastes with the biological waste water  treatment pro-
cesses.  Four heavy metals were selected by the Robert A. Taft Sanitary Engin-
eering Center in Cincinnati,  Ohio.  Nickel seems relatively  nontoxic  to man but
tolerance of aquatic life varied  widely, depending on synergism, species,  and
pH.  Laboratory data for water quality criteria for protection of all  life
stages of aquatic organisms can be derived from chronic  toxicity studies.  Ex-
posure data  for one generation is necessary to ascertain  the maximum acceptable
toxicant concentration (MATC), which is the highest mean  continuous-flov con-
centration that has no adverse effect on survival, growth, and reproduction.
The MATC for fathead minnow  (Pimephales promelas Raflnesque) was estimated.
Nickel concentrations of 0.38 mg/liter and lower are safe; however,  a  concen-
tration of 0.73 mg/liter caused a significant reduction of the number  of eggs
and spawning hatchability.  Extrapolation from laboratory data to the  aquatic
ecosystem is more complex than predicting chronic toxicity in laboratory con-
ditions.   This type of application is presently the best  tool for estimating
the upper limit of safe concentration of heavy metals in  the fish community,
and thus in the food chain.

*Toxicity,  *Nickel, *Municipal wastes,  *Biological treatment, *Heavy metals,
Aquatic life, Laboratory data, Minnows, Fish,  Water quality  standards, Food
chain,  Ecosystems

*Pimephales promelas Rafinesque (Fathead minnow),  *Maximum acceptable  toxicant
concentration (MATC)
                                     795

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 239J

 PATHOGENIC ORGANISMS  IN THE MURDERKILL RIVER ESTUARY,

 DeMichele, E.

 Technical Services,
 Water Pollution Control Federation
 Washington,  D.  C.

 Journal  of the  Water  Pollution  Control Federation,  Vol.  46,  No.  4,  p  772-776,
 April, 1974.  4 fig,  6  ref.

 This study's purpose  was to  determine  pathogenic  indicator profiles over  a
 tidally  influenced river.  The  Murderkill River in  Delaware  receives  raw
 waste water  discharge from homes and restaurants; other  treated  and untreated
 waste water  is  added  to the  river  by tributaries  and ponds.   Implementation  of
 specific tests  for pathogens is difficult and these pathogens may not always
 be present in domestic  waste water.  Indicator organisms are fecal  coliforms (FC),
 total coliforms (TC), and fecal streptococcus (FS).  It  was  found that FC and
 FS were  in rivers due to human  or  animal excrement.  The FC:FS ratios found
 to be low in all cases  tested,  indicating animal  wastes  as the principal  source
 of pollution.   Figures  for  FS and  FC are given; the concentrations  decreased
 logarithmically from  Station 4  to  the  river  mouth.  Although industrial waste
 water sources are not present from downstream river areas, marshy areas caused
 an increase  in  indicator counts between the  mouth of the river and  Station 4.

 *Pathogenic bacteria, *Rivers,  *Tidal  waters,  *Domestic  wastes,  Organisms,
 Water pollution, Industrial  wastes, Coliforms, Estuaries, Delaware, Marshes,
 Waste water

 Raw waste water, Fecal  coliforms,  Total coliforms,  Fecal streptococcus, Indi-
 cator organisms
240J

POLLUTION TROUBLE SHOOTING THEIR JOB,

Marsh, J.

South African Chemical Processing, p 20-21, December 1973/January, 1974.

Fundamental and practical application concerning pollution and projects
currently ongoing by the Pollution Research Group of the Chemical Engineering
Department at the University of Natal are described.  Various doctoral candi-
dates have been allotted time and facilities to carry out research.  The most
recent work has to do with the reverse osmosis process for desalination.  Appli-
cations include the use of the reverse osmosis separation process (and the
ultra filtration process) as a technique for the separation and concentration
of fractionation of substances in fluid solutions, particularly industrial
waste water.  Also, basic principles of RO are being studied for suitable
research by physical chemists for future doctoral degrees.

*Reverse osmosis, *Desalination, *Potable water, *Research, Separation, In-
dustrial wastes, Waste water, Treatment facilities, Application methods

*Pollution Research Group, Natal University, South Africa, Ultrafiltration
                                      796

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241J

HELPING HAND WITH POLLUTION PROBLEMS,

Rohm and Haas Reporter, Vol. 32, No. 1, p 21-23, Spring, 1974.

A new service program has been set up by the Rohm and Haas Company in Philadel-
phia called Fluid Process Service.  Chemists, technicians, and design engineers
work on a contractual consulting basis to solve specific problems in the areas
of ion exchange, flocculation, adsorption, and liquid extraction.  The treatment
processes used vary by location, method of reuse of recovered materials, costs,
and local air and water pollution regulations.  An example of the FPS was a
kraft paper mill, but this service has been extended to meet the needs of
municipal water supplies as well as industrial concerns.

*Planning, *Liquid wastes, *Treatment, *Ion exchange, *Flocculation, *Adsorption,
Costs, Municipal water, Industrial wastes, Regulations, Air pollution, Water
pollution, Kraft mill wastes, Contracts

*Consulting, Fluid Process Service (FPS), Rohm and Haas Company, Liquid extrac-
tion, Municipal water supplies
 242J

 ECOLOGY PROBLEMS SPELL PROFITS,

 Roth,  L.

 Associated Construction Publications,
 Elmhurst,  Illinois

 Engineering and Contract Record, Vol.  87,  No.  3,  p 54-56,  March,  1974.

 Although equipment,  materials,  and fuels have  undergone shortages,  small scale
 firms  for ecological protection have managed to be successful.   A treatment sys-
 tem is described whereby a small aerobic plant may be used to service individual
 apartment buildings  and their domestic wastes.  About 240  such systems  have
 been installed in Florida in areas where building had been stopped because of
 inadequate municipal facilities.  Another service described is that of  system
 evaluation, consultants to consultants.  A third service is that  of a profes-
 sional sweeping company for streets, major shopping areas, low gutters, and
 along  fences.   Additionally,  practical uses  of median strips and  sideslopes along
 highways has been proposed, whereby trees  planted can be a source of future pulp-
 wood.   Related to this is research on  the effect of salt and highway chemicals
 on roadside vegetation with the suggestion that salt-resistant grasses  be
 grown, and that erosion-preventing wood chips  be used in areas of clearing
 operations.

 *Equipment, *Domestic wastes, *Waste treatment, Systems analysis, Treatment
 facilities, Highway  use, Salt,  Chemicals,  Erosion, Florida, Ecology

 *Consultation, Street sweeping
                                        797

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 243J

 WATER TREATMENT:   HOW TO  TOP  EVEN  GOVERNMENT  STANDARDS,

 Synott,  T.,  Williams,  J.  C.,  and Escher,  E. D.

 Holley,  Kenney,  Schott, Incorporated,
 Pittsburgh,  Pennsylvania

 Factory,  Vol.  7,  No.  4, p 47-50, April, 1974.   2  fig.

 Water treatment  at the Cummins  Engine  Company plant  in Walesboro,  Indiana was
 recently designed to  consider all  possibilities for  innovation,  saving  consider-
 able amounts of  money.  The quality  of water  effluents at  this diesel compo-
 nents plant  is higher  than both state  and federal standards.  The  main  industrial
 usage is  cooling  water, process, wet scrubbing  and coolant and wash  tank
 water.   Water  consumed by the plant  must  be purchased from the municipal supply
 of  Columbus, Indiana,  and waste waters produced would be discharged  into the
 city's sanitary  sewage system.  By processes  of cooling at higher  cycles,
 water softening,  direct discharge  to sewers of  rinses without toxic  substances,
 and scrubbing  and filtering of  exterior exhausts, quality  was improved  and
 quantity  of  water consumed (by  the plant)  reduced.   Effluent waste treatment
 facilities were  built  for a batch  process.  In  the system  of chemical treat-
 ment, alum was chosen  as  primary coagulant.   The  plant has both  sanitary and
 process  water  sewer systems;  accidental discharge of wastes are  prevented from
 entering the city's sewage plant.  Automation has been built into  the feed  sys-
 tems as  much as  possible. After final design,  the monthly consumption  of muni-
 cipal water  is 16 million gallons, compared with  the original estimate  of 25
 million  gallons  per month, or 40 percent  reduction.

 *Water treatment,  *Municipal  water,  industrial wastes, *Water quality  control,
 *Waste water treatment, Costs,  Industrial water,  Cooling water,  Toxicity, Sewers,
 Chemical  treatment, Mixing, Discharge, Automation, Alum, Coagulation, Water
 softening

 Indiana  (Walesboro),  Sanitoary  sewage  system, Treatment plants,  Batch process
244J

HEXACHLOROBENZENE (HCB) RESIDUES IN FISH,

Johnson, J. L., Stalling, D. L., and Hogan, J. W.

Bureau of Sport Fisheries and Wildlife, Fish-Pesticide
Research Laboratory, Columbia, Missouri

Bulletin of Environmental Contamination and Toxicology, Vol. 11, No. 5, p 393-
398, May, 1974.  1 fig, 2 tab, 16 ref.

Data on gas chromatography-mass spectrometry identification, silicic acid
column separation, and gas-liquid chromatographic analysis of hexachlorobenzene
(HCB) residues found in various species of freshwater and anadromous fish from
widely scattered areas in the United States are presented.  Also disclosed
are HCB residues in fish eggs, fish fry, and fish oil.  In general, the
concentration of HCB found in fish collected in the United States is comparable
with the levels reported for fish collected in Canada and Europe.

*Data collections, Gas chromatography, Mass spectrometry, Fish, Analytical
techniques, United States, Canada, Europe

*Hexachlorobenzene residues, Silicic acid separation, Gas-liquid chromatogra-
phy
                                     798

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245J

SOME NUTRITIONAL CHARACTERISTICS OF SPIRULINA MAXIMA AL-
GAE GROWN IN EFFLUENTS FROM BIOLOGICAL TREATMENT PLANT,

Nguyen, H. T., Kosaric, N., and Bergougnou, M. A.

Western Ontario University, Faculty of Engineering
Science, Chemical Engineering, London, Ontario,
Canada

Canadian Institute of Food Science Technology, Journal, Vol. 7, No. 2, p 114-
116, April,  1974.  1 fig, 2 tab, 10 ref.

Spirulina maxima, a high protein blue-green algae, was grown in effluents
from the municipal waste treatment plant.  The protein content of the algal
biomass tended to decrease at the later phase of batch culture while the fat
and carbohydrate contents increased.  The relative protein amino acid composi-
tion did not change and was comparable to that of the algae grown in synthetic
medium.

*Cyanophyta, Effluents, Municipal wastes, Treatment facilities, Biological
treatment, Lipids, Carbohydrates, Proteins, Amino acids, Nutrient requirements
246J

SEWAGE ELECTROLYSIS,

Wei, N. S., and Heinke, G. W.

Toronto University, Department of Civil Engineering, Canada

Water and Pollution Control, Vol. 115, No. 5, p 31-32, 36, May, 1974.

A state-of-the-art review of sewage electrolysis is presented.  Electrolysis is
a process in which chemical reactions are induced at each electrode-liquid
interface through the application of an external electrical energy source to
a system of electrodes immersed in a liquid.  The review traces the commercial
and scientific development of the process and includes an extensive patent
survey.

*Reviews, *Electrolysis, Sewage treatment, Chemical reactions, Patents, Tech-
nology
                                          799

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247J

POPULATION, RESOURCES, AND POLLUTION, AND THEIR IMPACT
ON THE HUDSON ESTUARY,

Ketchum, B. H.

Woods Hole Oceanographic Institution, Woods Hole, Massa-
chusetts

Hudson River Colloquium, Annals of the New York Academy of Sciences, Vol. 250,
p 144-156, May 24, 1974.  10 fig, 1 tab, 13 ref.

Data is presented on the distribution properties in the lower end of the Hudson
estuary so as to define and delineate some of the problems that should be
further investigated.  Such data indicate that the Hudson River estuary is not
itself capable of accepting and recycling the nutrients that are being added to
it in the sewage from the population of the city of New York.  Adequate control
of the domestic sewage will require the removal of a substantial part of the
nutrients as well as the removal of the organic material that creates the
biochemical oxygen demand.

*Data collections, *Hudson River, *Surveys, Sewage disposal, Nutrients, Water
pollution sources, Water pollution control, Environmental effects, Phosphorus,
Phytoplankton, Chlorophyll
248J

THE ESTUARY AND INDUSTRIAL WASTES:  POWER PLANTS,

Intorre, B., and DeRienzo, P.

Burns and Roe, Incorporated, Oradell, New Jersey

Hudson River Colloquium, Annals of the New York Academy of Sciences, Vol. 250,
p 169-177, May 24, 1974.  3 fig, 1 tab.

The three major components of a power plant are a boiler or reactor, used to
release the chemical or nuclear energy in the fuel by producing steam; a tur-
bine generator, which converts the mechanical energy into electrical energy; and,
a condenser which converts any remaining energy in the steam to the river
water used for cooling.  The operation of these components in an overall power
cycle are discussed, highlighting those operations that generate potential
contaminants.

*Power plants, Boilers, Condensers, Turbines, Generators, Industrial wastes,
Estuaries, Water pollution sources, Cooling water
                                          800

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249J

PUBLIC USE AND EVALUATION OF RECLAIMED WATER,

Bruvold, W. H., Ongerth, H. J.

University of California, School of Public Health, Berke-
ley, California

Journal of the American Water Works Association, Vol. 66, No. 5, p 294-297,
May, 1974.  5 tab, 7 ref.

Insight into what the public currently thinks of various uses of reclaimed
water has been developed through the use of large-scale systematic research.
The aims of the present research are as follows:  to study behavior of indivi-
duals regarding existing recreational facilities using reclaimed water; to
measure attitudes toward various specific uses of reclaimed water; and, to
develop the implications of the findings for innovative reuse prpjects.  A
summary of the methodology of the major field work, followed by general and
attitudinal results are presented.  Results are discussed and recommendations
made.

*Water reuse, Recreation facilities, Research and development, Evaluation,
Surveys, California

*Public opinion
 250J

 UPTAKE OF MERCURIC CHLORIDE AND METHYLMERCURY  CHLORIDE
 FROM LIQUID MEDIA BY ASPERGILLUS NIGER AND PENICILLIUM
 NOTATUM,

 Hardcastle, J. E. and Mavichakana, N.

 Texas Women's University, Chemistry Department, Denton,
 Texas

 Bulletin of Environmental Contamination and Toxicology, Vol.  11, No. 5,  p  456-
 460, May, 1974.  2 fig, 1 tab, 9 ref.

 The uptake of an inorganic and organic form of mercury by  two common soil
 fungi, Aspergillus niger and Penicillium notatum, have been measured with
 quantitative results being tabulated.  Results of this research indicate that
 both A. niger and P. notatum do have a certain tolerance for  mercury and are
 able to grow and reproduce with certain levels of this element in their  tissues.
 Thus it is suggested that because of their abundance and ability to concentrate
 mercury, the fungi's role in the metabolism of mercury in  the eenvironment is im-
 portant and should receive further study.

 *Mercury, *Soil fungi, Investigations, Environmental effects

 *Mercury uptake
                                        801

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 251J

 PROTECTION OF THE PUBLIC HEALTH,

 Sorber, C. A.

 U.  S. Army Medical Environmental Engineering Research
 Unit, Aberdeen Proving Ground, Maryland

 In:  Proceedings of Conference on Land Disposal of Municipal Effluents and
 Sludges, March 12-13, 1973, Rutgers University, New Brunswick, New Jersey,
 p 201-209.  A ref.

 The public health aspects of waste water treatment by land disposal are de-
 pendent upon a number of variables, the most important of which is the ultimate
 use of the waste water.  Another area of importance is the degree of pre-treat-
 ment for the waste water prior to land disposal.  The effects of these prime
 variables are grouped into the areas of physical, biological, and chemical
 considerations.  It is summarized that few public health problems would exist
 as a result of spray irrigation or land disposal of waste water if basic steps
 such as site selection and planning with regard to aforementioned considera-
 tions were taken into account when designing and implementing a land disposal
 field.

 *Public health, *Waste water treatment, *Land management, Waste disposal,
 *Waste water disposal, Pre-treatment (water)
252J

PROCEEDINGS OF CONFERENCE ON LAND DISPOSAL OF MUNICIPAL
EFFLUENTS AND SLUDGES,

Mason, R. W., and Hess, C. E.

Environmental Protection Agency, New York

Technical Report No. PB-227 115.  Conference Held at Rutgers, The State Univer-
sity of New Jersey, March 12-13, 1973.  261 p.

The proceedings of a conference sponsored by the United States Environmental
Protection Agency and the College of Agriculture and Environmental Science of
Rutgers University includes 19 articles.  These deal with both sludge disposal
on land and with the land treatment of municipal effluents.  The mechanics
and problems of land disposal as applied to specific municipalities, as well
as environmental and social effects are discussed.

*Conferences, *Municipal wastes, Effluents, Land treatment, Environmental
effects, Public health, Sludge disposal, Sewage sludge, Waste water treatment,
Municipal sludge

*Land disposal, Environmental Protection Agency, Treatment methods
                                        802

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 253J

 DRINKING WATER AS  A SOURCE OF LEAD POLLUTION,

 Goldberg,  A.

 Stabhill General Hospital,  Glasgow,  Scotland,
 University Department  Materia Medica

 Environmental  Health Perspectives,  Vol.  7,  p 103-105,  May,  1974.   3  fig,  2  ref.

 Lead poisoning was  found  in some  inhabitants of  houses in  rural  Scotland,
 exposed  to soft water  and lead-lined drinking water  tanks.  Further  investi-
 gations  were carried out  on the clinical and metabolic effects of  lead
 acquired by drinking soft domestic water from lead plumbing systems  in  23
 Glasgow  households,  the  lead content of water from  cold taps was  up to 18
 times  the  upper acceptable,  limit  and was proportional  to the amount  of  lead
 in the plumbing system.   The  blood  lead  of  71 inhabitants of these houses showed
 a significant  negative correlation with  water-lead content.  A small number
 of clinical abnormalities were found but could not be  directly attributed
 to lead  toxicity.   The results of the study underline  the possibility danger
 to health  of lead plumbing  systems  in soft water regions.

 *Potable water, *Lead, *Plumbing,  *Toxicity

 *Glasgow,  Scotland,  *Soft water,  *Lead-lined drinking  water tanks, *Lead
 poisoning,  Metabolic effects
254J

ENVIRONMENTAL LEAD:  A SURVEY OF ITS POSSIBLE PHYSIOLOGICAL
SIGNIFICANCE,

Warren, H. V.

British Columbia University, Vancouver, Canada, Depart-
ment of Geological Sciences

Journal of Biosocial Science, Vol. 6, No. 2, p 223-238, 1974.  4 tab, 49 ref.

Although multiple sclerosis, swayback, scrapie, kuru, Minamata disease, lead
lameness (sheep), motor neurone disease, and amyotrophic lateral sclerosis
are different illnesses, all, with the possible exception of scrapie, appear
to have two  common denominators:  deterioration of the nervous system,
which may or may not include demyelination, and a frequently unexplained
association with lead or mercury.  Sources of lead pollution, in drinking
water, in food, and in air are discussed.  While rural dwellers in areas
of high soil-lead content are more apt to absorb the lead through food, city
dwellers are more likely to inhale lead particles.  Other sources of lead
and mercury  are described and evidence linking metallic elements with
neurological diseases is postulated.

*Lead, *Potable water, *Toxicity, *Soil, *Mercury, Metals, Environmental
effects, Pollution, Human diseases, Rural areas

*Neurological diseases, *Demyelination, Soil-lead
                                          803

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255J

CLOUDS IN THE CRYSTAL BALL,

McKee, J. E., and Rice, T. R.

California Institute of Technology, Pasadena, California,
Department of Environmental Engineering

Journal of the American Water Works Association, Vol. 66, No. 5, p 265-269,
May, 1974.  3 fig, 3 tab, 8 ref.

Population forecasting has become increasingly important in recent years.
Various planners, including water-utility planners, need to know what
future populations will be in areas that they serve in order to assure that
people will be provided with needed facilities.  Water supply is one of
many factors that influences the growth of United States communities.
Moreover, social factors such as unemployment, crime, congestion, and
racial problems may prove to be more significant than physical influences.
A case study of the Las Vegas area shows that growth there will not be
curtailed by a shortage of water.  Even with a forecast of one million
people by 2000 A.D., adequate water will be available for municipal use.
Thereafter it may become necessary to reclaim, demineralize, and reutilize
waste water for potable purposes.

*Population, *Forecasting, *Future planning (projected), Water supply,
Water reuse, Water conservation

Las Vegas, Nevada
256J

STATIC LEACHING STUDIES ON PULPWOOD BARK RESIDUES,

Benedict, A. H., McKeown, J. J., and Hart, R. D.

British Columbia University, Vancouver, British Columbia,
Canada, Department of Civil Engineering

Journal of the Environmental Engineering Division, ASCE, Vol. 100, No. EE3,
p 529-540, June, 1974.  8 fig, 3 tab, 2 ref.

A laboratory study to define and evaluate the characteristics of bark leaching
in terms of the types and quantities of materials leached from bark
residues has been undertaken with the impact of these extractives on water
quality being examined.  The quantities of BODS, COB, color, Kjeldahl
nitrogen, and inorganic phosphorus leached from fresh and aged barks under
static leaching conditions were determined.  Results of these studies
show that the quantity of BODS, COD, color, nitrogen, and phosphorus
extracted from bark depends on the field storage age of bark and on the
characteristics of the water in contact with the bark.  The significance
of each of these factors is examined subsequently.  Based on the results
of this study, the following conclusions can be made:  potential of bark
to leach these variables decreases with storage age in bark piles; under
fresh water conditions variable concentrations will increase with increasing
contact time, approaching limiting values; and, salt water retards BODS,
COD, color, and Kjeldahl nitrogen leaching from bark.

*Leaching, laboratory tests, *Bark, *Evaluation, *Water quality, Biochemical
oxygen demand, Chemical oxygen demand, Color, Nitrogen, Phosphorus

Bark residues, Bark leaching
                                        804

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257J

ATMOSPHERIC COOLERS FOR COOLING INDUSTRIAL WATERS,

Vitek, M.

Czechoslovak Heavy Industry, No. 4, p 39-44, 1974.  7 fig, I tab.

Mlcrotowers, atmospheric coolers of the M range, are coolers of industrial
water with fans, manufactured mostly of plastics.  These are easy to
assemble, and alleviate the shortage of fresh water for towns as well as for
industries.  Microtowers are manufactured in four sizes which are chosen so
that all requirements for cooling circuits of smaller capacities can be
met.  The cooling of the larger quanty of water can be arranged by the
connection in parallel of several microtowers in a cooling circuit.  One
advantage of a parallel connection of several cooling towers is easy main-
tenance.  Also, the probability of cutting some unit out of service increases
as the weather gets cooler.  Microtowers are of a simple design, their
erection and attendance are easy, and their operation is economical within a
wide range of operating conditions.

*Industrlal water, *Water cooling, *Cooling towers, Equipment, Municipal
water, Fresh water

*Microtowers
 258J

 EFFECTS OF GAMMA RADIATION ON AQUEOUS  SOLUTIONS OF
 PHENOLS,

 Coffman,  L. M.,  and Woodbrldge,  D.  D.

 Florida Institute of Technology,  Melbourne,  Florida,
 University Center for Pollution  Research

 Bulletin of Environmental Contamination and  Toxicology,  Vol.  11,  No.  5,  p  461-
 466, May,  1974.   1 fig,  13 ref.

 The  beneficial use of radiation  has been investigated  for  many  applications.
 Radiation research and development  applied to waste water  treatment has
 been limited; however, sufficient research has  been done to  indicate  that
 the  use of radiation may be beneficial in the treatment  of urban  and
 industrial waste water.   The irradiation process is explained and the
 experimental procedure involving irradiation of aqueous  solutions of
 phenols outlined.  Results show  that the phenol structure  can be  destroyed
 by gamma radiation.   At  phenol concentrations of 10 mg/liter, almost  complete
 destruction occurred at  a dose rate of one million rads.  Furthermore,
 this work indicates that the destruction of  phenols by gamma  radiation
 from Cobalt-60 is feasible.

 *Irradiation, *Waste water treatment,  *Phenols, Gamma  rays, Laboratory
 tests,  Feasibility studies
                                           805

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259J

ENVIRONMENTAL-IMP ACT ASSESSMENT FOR PLANT DESIGN AND
OPERATION,

Jones, R. L.

Jones and Stokes Associates, Incorporated, Sacramento,
California

Journal of the American Water Works Association, Vol. 66, No. 5, p 286-290,
May, 1974.  2 tab, 10 ref.

Environmental assessments have had a considerable amount of leverage in
minimizing environmental detriments and realizing benefits.  Most government
agencies and many private concerns are trying to deal effectively with
environmental problems and identify the project features.  Environmental
impact statements (EIS) should be well-conceived and cover all impacts,
whether positive or negative, that a planned project will have upon its
area.  A description of EIS preparation is given.

*Design criteria, *Specifications, Environmental control, Environmental
effects, Planning

*Environmental impact statements  (EIS)
   260J

   ARE THE GREAT LAKES THREATENED?,

   Bruce, J.  P., and Gabriel,  G. F.

   Canada Centre for Inland Waters, Department of the Envi-
   ronment,  Burlington, Ontario, Canada

   Journal of the American Water Works Association,  Vol.  66,  No.  5, p 298-301,
   May, 1974.  4 fig, 1 ref.

   Although the main body of water of the Great Lakes is  still of good quality
   from the criterion of drinking water standards, many problems  such as
   eutrophication, pollution from trace metals, organic and bacterial contamina-
   tion, and oil spills, have developed in near shore areas.   The recently
   signed agreement between Canada and the United States  should begin resolving
   these problems by establishing jointly agreed water quality objectives
   and control programs which are designed to reach those objectives in four
   years.

   *Great Lakes, *Shores, *Water quality,  Water quality control,  Eutrophication,
   Trace metals, Organic matter, Bacteria, Oil spills,  Water pollution sources,
   Project planning, Canada, United States, Potable water
                                         806

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261J

VIRUSES - WHAT IS THEIR SIGNIFICANCE IN WATER SUPPLIES?

Taylor, F. B.

Environmental Protection Agency, Region 1, Air and Water
Programs Division, Water  Supply Branch, Boston, Massa-
chusetts

Journal of the American Water Works Association, Vol. 66, No. 5, p 306-311,
May, 1974.  3 tab, 11 ref.

The attitude toward the safety and significance of viruses in water supplies
has changed over the last few years in both public and water treatment
areas.  How to protect and inform the public without producing unnecessary
scares is the subject of this article.  It is concluded that research is
needed in the fields of virus detection methodology and epidemiological
techniques for detecting viral disease in the general population.  Also,
the water utility and public health professions must be careful to avoid
an attitude of either complacency or doom concerning the entire issue of
virus detection.

*Viruses, *Public health, Potable water, Water supply, Safety, Water pollution
control, Water pollution effects

Public relations, Virus detection
  262J

  NEW LEGAL APPROACHES TO ENVIRONMENTAL CONTROL,

  Wallace,  F.  X.

  New York State  Department of Environmental Conservation,
  General Counsel,  Albany, New York

  Hudson River Colloquium, Annals of the New York Academy of Sciences,  Vol.  250,
  p 182-185, May  24,  1974.

  Presently there are about 200 air, water,  and solid waste cases being conducted
  in New York state,  with many more being prepared for legal action in the
  field.  Since orders that are based merely upon agreements on necessary
  steps have not  proved entirely effective,  a new approach calls for financial
  guarantees that will ensure timely compliance.   Dnder this method, indus-
  tries and municipalities that have been found to be polluting are afforded
  the option of consenting to a commissioner's order and posting a financial
  guarantee of their  compliance such as a surety bond or other security.
  If the polluter complies with the terms of the order, the amount is refunded.
  If the violation continues and the polluter does not comply with the terms
  of the order, the bond or security is automatically forfeited and additional
  steps are taken.  This new approach increases the polluter's sensitivity
  to the need for compliance.  It also shifts the burden of monitoring pollu-
  tion abatement  to the polluter, by requiring that periodic reports be sub-
  mitted, documenting the steps taken to comply with the commissioner's
  order to abate  pollution.  Other areas which give leverage to the enforcement
  division are the refusal to allow operation and maintenance grants and the
  issuance of permits for sewer line extensions.

  *Regulation, *Legal aspects, *New York, Legislation, Pollution abatement,
  Law enforcement,  Penalties (legal), Water  pollution control

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263J

POLYCHLORINATED BIPHENYLS AND P,P' DDE IN GREEN TURTLE
EGGS FROM ASCENSION ISLAND, SOUTH ATLANTIC OCEAN,

Thompson, N. P., Rankln, P. W.,  and Johnston, D. W.

Florida University, Gainesville, Florida, Department of
Food Science and Pesticide Research Laboratory

Bulletin of Environmental Contamination and Toxicology, Vol. 11, No. 5,
p 399-406, May, 1974.  3 fig, 1 tab, 14 ref.

Ascension Island, one of the most isolated islands in the South Atlantic
Ocean, is a volcanic island of approximately 35 square miles located some
900 miles southwest of Liberia,  Africa.  Sea birds and turtles, especially
the pelargic Green Turtle, Chelonia mydas, utilize this island for breeding
with feeding in the nearby waters.  Samples of birds and turtle eggs from
Ascension Island were obtained for polychlorinated biphenyl (PCB) and
pesticide analyses.  Results show that the presence of multiple PCB's
is evident and there are peaks at the retention times of p,p'-DDE, -ODD,
and -DDT.  This brief report of PCB and pesticide burdens in the turtle
eggs carries no concrete information of possible effects on the organisms.
In addition to the ten Green Turtle eggs which were analyzed several hundred
more were transported to Florida for laboratory hatching; in these there
was no dramatic decrease in hatching success or occurrence of deformed
hatchlings.

*Turtles, *Polychlorinated biphenyls, *Chlorinated hydrocarbon pesticides,
Sampling, Water pollution effects, Laboratory tests

*Ascension Island, *Green turtles
 264J

 THE HAZARD OF IRON,

 Dart, F. J.

 Ontario Ministry of Environment, Environmental Associa-
 tion and Planning Division, Ontario, Canada, Pollution
 Control Branch, Water Technology Section

 Water and Pollution Control, Vol. 112, No. 5, p 19-23, 33, 38, May, 1974.
 2  tab, 4 ref.

 In Ontario,  Canada, the Ministry of the Environment has a drinking water
 objective of only 0.3 mg/liter or less of iron, a limit recommended not
 on the basis of possible toxicity but rather to avoid the many nuisance
 problems that arise with excess concentration.  Without the proper identifi-
 cation of the sources of the problem iron, remedial measures can become an
 expensive problem.  On the basis of Ministry field investigations, however,
 considerable progress is being made in identifying and remedying certain
 iron problem situations.  Advances in silicate sequestering and the identi-
 fication of  the problem of interrelationships of iron, organic matter,
 and a multiple-aquifer water sources are examples of ongoing work.

 *Iron, *Water treatment, On-site investigations, Analytical techniques,
 Canada, Water pollution control, Water pollution sources, Aquifers,
 Water pollution sources
                                        808

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265J

THE WATER INDUSTRY IN THE DECADE OF ENVIRONMENTAL CON-
CERN,

Gilbert, J. B.

J. B. Gilbert and Associates, Sacramento, California

Journal of the American Water Works Association, Vol. 66, No. 5, p 272-274,
May, 1974.

Many of the larger states have moved to change their organizations and
establish new water management agencies, but few if any have combined in
one organized program all the decisions that affect their water supply.
Because the crisis in the water part of the environment has centered
around such incidents as the Santa Barbara oil spill, the eutrophication
of Lake Erie, and the califaction of fresh water streams, the focus of
public attention has been on state and national pollution control programs.
As a result, national appropriations, enforcement authorities, planning
programs, and related activities are becoming the focal point of the United
States' effort to manage its water resources.  It is suggested that the
water industry should respond to the changes in public awareness and demands
by participating in new organizations, planning programs, and joint efforts
with waste water agencies.

*Industries, *Administration, *Water Management, Water supply, Environmental
effects, Water pollution control, Waste water treatment, Water resources,
Project planning
 266J

 IRON:   A TWO-EDGED SWORD,

 Water  and Pollution Control,  Vol.  112,  No.  5,  p  26-27, May,  1974.

 Iron in water  has  an unpleasant  connotation for  municipal,  industrial  and
 domestic situations, with  the chief  concern of municipalities being  the
 limitation of  iron concentration below  required  guidelines.  However,  in-
 dustry quality control  personnel have the greatest  incentive in  keeping
 iron problems  to a minimum,  due  to unsaleable  commodities  if an  excess
 of ferric ions are present.   Various chemicals and  treatment methods used
 in removing iron and maintaining water  quality control are  outlined.

 *Iron, *Water  quality control, *Industries,  *Waste  water  treatment,  Chlorine,
 Ozone

 *Treatment methods
                                      809

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267J

THE IMPORTANCE OF DRINKING-WATER PROGRAMS TO THE TOTAL
ENVIRONMENTAL GOAL,

Morris, E. E., Jr.

State Government of South Carolina, Columbia, South
Carolina

Journal of the American Water Works Association, Vol. 66, No. 5, p 270-271,
May, 1974.

The United States water quality has declined and environmental concern has
increased during the past few years.  Overall programs are the best answer
to these problems, especially in light of the complexity of chemical and
bacterial contaminants.  Problems and programs illustrating requirements
a.nd control measures are cited.

*Water quality control, *Water quality standards, Project planning, Potable
water, Long-term planning
 26 8J

 METHODS AND  PROBLEMS OF  ESTIMATING WATER-QUALITY BENEFITS,

 Abel,  F. H.,  and Tihansky, D. P.

 Environmental Protection Agency, Office of Research,
 Implementation Research  Division, Economic Analysis Branch,
 Washington,  D. C.

 Journal of the American  Water Works Association, Vol. 66, No. 5, p 276-281,
 May,  1974.   20 ref.

 The demand for water quality improvement programs necessitates the development
 of methods for estimating benefits of such programs against their costs.
 Methods in use that deal with both tangible and intangible benefits are
 discussed.   In some cases these benefits outweigh any cost.  All of these
 procedures are part of a benefit-cost analysis which yield maximum net
 socioeconomic benefits.

 *Water quality control,  *Cost-benefit analysis, Project planning, Feasibility
 studies, Estimating
                                           810

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269J

ENVIRONMENTAL ASSESSMENT OF WATER-SYSTEM IMPROVEMENTS,

Larkin, D. G., and Anton, W. F.

East Bay Municipal Utility District, Oakland, California

Journal of the American Water Works Association, Vol. 66, No. 5, p 282-285,
May, 1974.  4 fig, 5 ref.

The East Bay Municipal Utility District (EBMUD)  in California has adopted a
policy and detailed procedures to provide environmental assessment of its
programs and projects.  The environmental assessment process provides
a further tool for the planning design team considering water system
improvements.  It improves and widens the planning perspective, results in
design that is in harmony with the surroundings, and requires construction
practices most compatible with the environment.   However, more time is
required from project committment or budget approval for project construction,
and to add to the total project costs.  It is estimated that EBMUD spends
over $2000 per month in direct costs for environmental assessment.

*Water resources development, *Environmental control, *Project planning,
Construction, Design criteria, Costs

*Environmental assessment
 270J

 TEMPERATURE-TOXICITY MODEL  FOR OIL  REFINERY  WASTE,

 Reynolds,  J.  H.,  Middlebrooks,  E. J.,  and  Procella,  D.  B.

 Utah State University,  Logan,  Utah,  Utah Water  Research
 Laboratory

 Journal of the Environmental Engineering Division, ASCE,  Vol.  100,  No.  EE3,
 p 557-576, June,  1974.   3 fig,  12  tab,  54  ref.

 Equations  have been developed using chemostat kinetics  and enzyme  inhibition
 kinetics to describe  the effects  of temperature on  toxicity to microorgan-
 isms.   These equations  were tested  by  semi-continuous and continuous  flow
 experiments with  phenol and the alga Selenastrum capricornutum.  The  data
 obtained were fitted  to competitive, uncompetitive,  and noncompetitive
 inhibitor models.  Results  indicate that phenol exerts  a  competitive
 inhibition effect on the growth of  the alga. Comparison  of the competitive
 inhibition constants  for S. capricornutum  exposed to phenol indicates that
 phenol toxicity increases with an increase in temperature according to  the
 Arrhenius function.

 *Mathematical studies,  *Equations,  *Temperature, *Microorganisms,  *Toxicity,
 Testing, Phenols, Algae, Flow,  Model studies, Environmental effects,  Reviews
                                      811

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271J

ENVIRONMENTAL CONTROL EQUIPMENT,

Hitachi Review, Vol. 23, No. 4, p 188-191, 1974.

Major technical achievements in 1973 in the field of atmospheric pollution
control include an electric precipitator for utility boilers burning heavy
fuel oil and crude oil, a large-capacity electric precipitator for industrial
plants, and various dust collectors.  Hitachi's contributions to water
pollution prevention include a total system for waste water treatment, supplied
to a power station, where it is in satisfactory operation.  For general
industrial waste water, facilities were developed for advanced treatment of
machine works waste water by the activated carbon process and for electrolytic
treatment of high-polymer effluents.  In the field of industrial waste
treatment, improvements included a sludge incinerator combining a centrifugal
membrane evaporator and a dewatering device.  In addition, Hitachi developed
a new sludge incineration system in which coal powder is mixed in undigested
sludge, which is directly burned In a fluidized bed of an activated catalyst.
Another invention is the sludge dryer by an infrared ray heater.  Features
of this equipment are detailed.

*Equlpment, Environmental control, Pollution abatement, Waste water treatment,
Tertiary treatment, Treatment facilities
272J

LAND USE CONTROLS IN WATERSHED AND AQUIFER RECHARGE AREAS,

Gerber, R. G.

Environmental Planning and Design Associates, Incorporated

Water and Sewage Works, Vol. 121, No. 4, p 122, 124-126, April 30, 1974.

Regulations and planning for land use in aquifer recharge areas and watersheds
is discussed.  The need for control is evidenced by loss of water quality and
quantity due to pollution and runoff.  Economic and political aspects are mentioned.
A recommended type of land use control plan is that of impact zoning, basing
standards of land capability on type and design of land use.  Factors which
determine such capability are soil, slope, drainage, and vegetation as well as
social values.  Public relations implementing any changes for local land use
is stressed as necessary.

*Land use, *Watersheds, *Water quality control, Water quantity, runoff,
planning, Soil, Drainage

*Aquifer recharge areas
                                         812

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273J

A NATIONAL WATER STRATEGY FOR ENGLAND AND WALES,

Ardlll, J.

Water and Sewage Works, Vol. 121, No. 5, p 58-60, 73, May, 1974.

Water resource management problems in England and Wales result not from an
intrinsic shortage of water but from an uneven distribution of available water
over time and place.  The Water Resources Board, now over ten years old, acts in
conjunction with a more recently established National Water Council and
Regional Water authorities.  These managerial bodies deal with the fields of
river management, water supply, sewerage and sewage disposal, pollution control,
flood protection, land drainage, fisheries, and recreational use of water space.
The creation of the RWAs will integrate financial and administrative problems.
Recommended plans include building of new reservoirs, expanding existing
reservoirs, and constructing new aqueducts between rivers.  The most novel
development in the program is estuary storage, which will involve major civil
engineering works in the Dee, which separates North Wales from northwest
England.  The various water storage plans are to be undertaken one at a time.

*Water resources management, *Water supply, Sewage disposal, Pollution control,
Flood protection, Drainage, Fisheries, Planning, Reservoirs, Estuaries, Water
storage

*Great Britain, *England, *Wales, Regional Water Authorities (RWAs)
  274J

  THE INFLUENCE OF CERTAIN TOXIC  SUBSTANCES,  FOUND  IN MUN-
  ICIPAL WASTE WATER,  ON THE BACTERIA ESCHERICHIA COLI AND
  PSEUDOMONAS FLUORESCENS (L1INFLUENCE DE CERTAINES SUB-
  STANCES TOXIQUES,  CONTENUES DANS  LES EAUX D'EGOUTS
  MUNICIPAUX, SUR LES  BACTERIES ESCHERICHIA COLI  ET
  PSEUDOMONAS FLUORESCENS),

  Spandowska, S., Lubienska, B.,  and Kozaczkowski,  S.

  Swiss  Journal of Hydrology, Vol.  35, No.  2,  p 278-285,
  1973.  2 fig,  4 tab,  18 ref.

  The toxic influence  of phenol,  aniline, pyridine  and chrome,  substances  often
  found  in municipal waste waters,  on the bacteria  Escherichia  coli  and
  Pseudomonas fluorescens was examined.   The non-toxic,  growth  limiting, toxic,
  and lethal doses were  determined  on the basis of  observations made of E.  coli
  and P. fluorescens reproduction and respiration patterns.   Comparative test
  series were set up.  These used various doses in  different  nutrient cultures
  to ascertain which was more sensitive to the chemicals, the bacteria's
  multiplication process, or carbohydrate decomposition.

  *Toxicity,  *Escherichia coli,  *Municipal waste  waters,  Bacteria, Phenols,
  Laboratory tests,  Nutrients, Measurements

  *Pseudomonas fluorescens, Chrome, Dosage
                                     813

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27 5J

OBSERVATIONS OF WATER, AIR AND SOIL POLLUTION IN ISRAEL
AND VICINITY FROM THE ERTS-L IMAGERY,

Otterman, J., Ginzburg, G. 0., and Mekler,  Y.

Tel-Aviv University Ramat Aviv, Israel,
Department of Environmental Sciences

Israel is a participant in the Earth Resources Technology Satellite Program
(ERTS).   The imagery of Israel and its vicinity taken by the Multi Spectral
Scanner of the ERTS-1 Satellite has been the subject of analysis in a multi-
disciplinary research program.  The objectives of the program were to map
agricultural crops, mainly wheat and orange groves, to map natural vegetation,
and to study Israeli hydrology, arid regions research, geology, and oceanography.
Cases of water, air, and soil pollution have been observed in the imagery on
several dates.  These are: oil slicks in the Gulf of Suez and possibly near
Haifa; smoke plumes, extending over some 1QO km in a nearly straight line along
the Gulf of Suez, and soil pollution caused by copper mine effluents in the
Araya Valley in Israel.  The images of these cases of pollution are presented
and 'space signatures', (the radiometric spectral characteristics of these
cases of pollution as seen from space) are also given.

*Research, *Agriculture, *Hydrology, Water pollution, Oil spills, Soil
pollution, Mines, Crops

*Radiometric methods, *Earth Resources Technology Satellite Program (ERTS).
*Israel, Mine effluents, Copper mines, Space Signatures
 276J

 STUDIES ON THE VARIATION OF RIVER WATER WITH TREATMENT
 OF NATURAL POISONOUS ACID WATER,

 Iriye, T.

 Bulletin of Yamagata University, Natural Science, Vol. 8, No. 1, p 69-84,
 January, 1972.   11 fig, 2 tab, 17 ref.

 Many  rivers in Japan are acidified by natural strongly acidic water  (or so-
 called poisonous acid water).  These rivers influence the quality of surrounding
 fisheries and agriculture.  One method of treatment of the acid water is
 permeation through borings.  In Matsu-kawa, which was affected by acid water
 from  Nishiazuma  mine, this method worked for several years, but the  effect
 suddenly decreased and  the water now has a pH of 4.  This method of  treatment
 was also tried in Zaogawa, Kaminoyama City without much improvement.

 *Rivers, *Water  quality control, *Acidity, Mines, Agriculture, Fisheries,
 Permeation

 *Japan, *pH, Treatment methods
                                      814

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277J

ESTABLISHING A QUALITY CONTROL PROGRAM FOR A STATE
ENVIRONMENTAL LABORATORY,

Frazier, R. P., Jr, Miller, J. A., Murray, J. F., Mauzy,
M. P., and Schaeffer, D. J.

Springfield, Illinois

Water and Sewage Works, Vol. 121, No. 5, p 54-57, 75, May, 1974.

In order to assure the quality of the analytical laboratory work performed
the Illinois Environmental Protection Agency continues to improve its quality
control program.  This program was experimental, developing in response to
efforts to solve specific problems.  It is maintained that a quality control
program can serve many functions by measuring the precision and/or accuracy
of a procedure, providing information data used for legal purposes, and
detecting faulty methods.  The most important effect noted as a result of
the programs described is an increased consciousness by the individual
analysts, regardless of: skill level, that they are professionals, doing a
difficult non-routine job using routine techniques.

laboratory tests, *Testing procedures, *Quality control, Performance,
Evaluation, Scientific personnel
278J

A NEW LOOK FOR WATER MANAGEMENT IN SCOTLAND,

Waddington, J. I., and Hammerton, D.

Effluent and Water Treatment Journal, Vol. 14, No. 4, p 211-217, April, 1974.
3 fig, 1 tab.

Beginning in May 1975, water supply and sewerage in Scotland will be managed
by the new regional authorities with only river purification boards remaining
outside local government.  This article examines the historical reasons for
Scotland splitting from Great Britain, describes the new system in the context
of local government reform, and, considers the future prospects for water
management in all its apsects.

*Water supply, *Water management, *Administration, Local governments, Sewerage,
Sewage treatment, Flood control

*Scotland
                                      815

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279J

WATER MANAGEMENT THROUGH IRRIGATION AND DRAINAGE:
PROGRESS, PROBLEMS, AND OPPORTUNITIES,

Journal of the Irrigation and Drainage Division, ASCE, Vol. 100, No. IR2,
p 153-178, June, 1974.  28 ref.

A wide range of problems associated with drainage and irrigation of water
are presented.  The major topics of concern include:   water supply conservation
and management, involving seepage and evaporation from water surfaces, various
methods of recharge, quality, pollution, social, economics, and institutional
aspects, and improving structures.  Also discussed are:  water use efficiency,
with emphasis on various irrigation systems; and, water quality improvement
in the areas of erosion, nutrients, animal wastes, salts, and land disposal of
wastes.

*Water management, *Irrigation, *Drainage, *Water supply, Water conservation,
Seepage, Evaporation, Artificial recharge, Waste disposal, Water utilization,
Efficiencies, Water quality, Erosion, Sedimentation,  Nutrients, Animal wastes,
Salts, Landfills, Reviews
280J

IS THE WATER SAFE TO DRINK?  PART 2:  HOW TO MAKE IT SAFER,

Harris, R. H., and Brecher, E. M.

Consumer Reports, Vol. 39, No. 7, p 538-542, July, 1974.

In recent decades many lakes and rivers from which millions obtain drinking
water have become increasingly polluted.  Uncontrolled dumping of industrial
wastes and municipal sewage combined with the runoff of agricultural chemicals
has created serious contamination in the raw water sources.  Safeguarding
the quality of today's drinking water requires more than protection against
bacterial hazards.  Many systems, however, still ignore the potential dangers
of viruses, heavy metals, and organic chemicals.  Described are steps the
water supply companies can take to achieve improved standards of drinking
water quality.

*Potable water, *Water quality standards, *Water supply, Water quality control,
Pollution abatement, Activated carbon, Chlorination, Ozone, Research and
development
                                      816

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281J

PACKAGED PUMPING STATIONS FOR SUBURBAN WATER DISTRIBUTION,

Rishel, J. B.

Water and Sewage Works, p 131-132, 134, April 30, 1974.  7 fig.

Packaged pumping stations are available in several types and their efficient
application requires an evaluation of these pumping stations as well as the
types of systems that are encountered in water distribution.  The three
specific styles of stations are the constant speed pumps without discharge
pressure control valves, constant speed pumps with discharge pressure control
valves, and the variable speed pumps.  Suburban water systems are of two
general types with storage tanks or without storage tanks closed systems.
One of the most important factors for any distribution system to be evaluated
is the friction loss in the piping of the water distribution system.  A
description of the basic types of distribution systems with typical system
head curves is provided.  It is shown that the packaged pumping station
selected is dependent upon the size of the system, the topography of the
system, and the quality of electrical power available.  Also included
is a description of four different water distribution systems.

*Pumping plants, *Water distribution, Water Works, Evaluation, Equipment,
Pumps, Storage tanks
 282J

 TWO-TUBE METHOD FOR SCREENING WATER ISOLATES FOR
 SALMONELLA,

 Harris, F. L.

 Environmental Protection Agency, Region VII, Water Quality
 Laboratory, Kansas City, Kansas

 Environmental Letters, Vol. 7, No. 1, p 1-13, 1974.  1 fig, 4 tab, 7 ref.

 Polyvalent H Antiserum, Iron, Indole, Malonate (AI1M), a two-tube Salmonella
 screening method, has been devised for the presumptive identification of
 the Salmonella genus.  The identification is made with Salmonella
 polyvalent H antiserum in a motillty medium; Salmonella growth is confined
 to the stab because of motility inhibition due to the antiserum.  Iron,
 indole, and malonate were used to lessen the possibility of various non-
 motile organisms and various antigenically related microorganisms
 being confused with Salmonella.  River and waste water isolates along with
 stock cultures were used to test the method.  AIIM was found to be useful
 for screening water isolates for Salmonella.  All the typical Salmonella
 testes gave appropriate reactions.

 *Salmonella, *Analytical techniques, Testing, Water analysis, Iron

 Two-tube method, Indole, Malonate
                                        317

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283J

SUBACHTE TOXICITY OF METHYLMERCURY IN THE ADULT CAT,

Charbonneau, S. M., Munro, I. C., Nera, E. A., Willies,
R. F., And Kuiper-Goodman, T.

Department of National Health and Welfare,
Ottawa, Ontario, Canada,
Food Research Laboratories

Toxicology and Applied Pharmacology, Vol. 27, No. 3, p 569-58], March, 1974.
6 fig, 3 tab, 22 ref.

Some species of edible fish from Canadian waters contained hazardous levels of
methylmercury.  A guideline for sale of fish was set at 0.5 ppm Hg.  Since
fish represents the major source of dietary methylmercury, studies for
assessing toxicity of fish in polluted waters were conducted.  Cats were used
because their clinical and pathological features are similar to humans who
consumed toxic quantities of food containing methylmercury.  A dose of 0.25
mg Hg/kg/day was administered to two groups of cats for 12-14 weeks, either as
pure methylmercuric chloride or as methylmercury-contaminated fish.  A control
group received a diet containing uncontaminated fish.  Clinical signs of
methylmercury intoxication consisting of ataxia, intention tremor and impaired
righting reflex and convulsions developed between 55 and 96 days in both
treated groups, at which time the total dose received was between 14 and 24
mg Hg/kg.  Tissue mercury content was similar in both groups of treated animals,
as were the pathologic changes.  Lesions were found in the cerebellar vermis and
the cerebral cortex.  The changes consisted of loss of nerve cells with
replacement by reactive and fibrillary gliosis.  Chromosome studies of terminal
bone marrow samples showed no abnormalities.

*Toxicity, *Mercury, *Fish, Canada, Pollution, Fish, Pathology, Animal
pathology, Food chains

*Cats, *Methylmercury, Methylmercuric chloride
 284J

 THE RELATIVE DISTRIBUTION OF NON-AROMATIC HYDROCARBONS
 IN THE BALTIC IN SEPTEMBER 1971,

 Zsolnay, A.

 Marine Chemistry, Vol. 1, No. 2, p 127-136, April, 1972/3.  3 fig, 1 tab,  13 ref.

 Pollution by hydrocarbons may be due to industrialization and mineral oil  or due
 to the origin decomposition of hydrocarbons in marine sediments.  The relative
 districution of the total non-aromatic  (saturated and olefinic) hydrocarbons
 and of the total saturated hydrocarbons, was determined for the central Baltic
 in September, 197.  Only one litre of sample was required.  The hydrocarbons
 were removed with liquid-liquid extraction, purified with liquid  chromatography,
 and then determined by means of a micro-adsorption detector.  Since hydrocarbons
 in nature are a very  complicated mixture, it was impossible to determine
 their absolute concentration.  Results  give the concentrations in respect  to
 a standard, consisting of water extracted from the Kiel Bight.  Hydrocarbons at
 that time of year originated largely in situ at the sediment-water interface,
 presumably synthesized by anaerobic bacteria.  Low hydrocarbon values
 appeared in regions that would favor the presence of aerobic bacteria.  A
 large amount of hydrocarbons was released by what was presumably  a small plankton
 bloom, but may have been relatively labile.  The net result is that the dissolved
 hydrocarbons that enter into the sediment have most likely been produced at
 the sediment-water interface.

 *Hydrocarbons, *Sediment-water interfaces, *Bacteria, Plankton, Sediments, Aerobic
 bacteria, *Water pollution sources

 *Non-aromatic hydrocarbons, *Baltic, Liquid-liquid extraction, Liquid
 chromatography, Micro-adsorption detector
                                       818

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 285J

CHANGE OF THE CYCLE OF INORGANIC MATTER IN NATURE  (DIE
VERANDERUNGEN DER MINERALSTOFFKREISLAUFE IN DER NATUR),

Schmidt, A.

Chemiker-Zeitung, No. 5, p 219-222, May, 1974.  4  fig, 2 tab, 3 ref.

Growth of the plants is made possible by a circulation of the main nutritional
elements - nitrogen, phosphorus and potassium.  Since the beginning of this
century this circulation has been disturbed by deep changes in the economic
and social structure, such as industrialization, urbanization, and popula-
tion growth.  On one hand, large amounts of nutrients have to be supplied
to the soil in  the form of fertilizers; on the other hand, human and animal
wastes are the  main source of pollution of the surface waters.  The extent of
the problem is  shown and its effects are discussed.

*Nutrients, *Water pollution sources, *Phosphorus, *Nitrogen, *Potassium,
Industrial wastes, Fertilizers, Soil, Human wastes, Animal wastes, Environ-
mental effects, Water pollution, Surface waters, Inorganic matter

Economics, Urbanization
286J

EFFECTS OF CHRONIC DIETARY NITRATES ON CANINE THYROID FUNCTION,

Kelley, S. T., Oehme, F. W., and Hoffman, S. B.

Toxicology and Applied Pharmacology, Vol. 27, No. 2, p 200-203, January, 1974
2 tab, 20 ref.

Potentially toxic levels of nitrate in the water of rural areas has been
recognized.  An investigation was conducted to determine the effects of
dietary nitrate on thyroid function in beagle dogs and their offspring.  The
dogs received 0 ppm, 600 ppm or 1000 ppm sodium nitrate in drinking water
under normal management and feeding conditions.  Continuous consumption
of these sublethal levels of nitrate did not produce a syndrqme of chronic
nitrate toxicosis characterized by thyroid dysfunction.

*Nitrates, *Toxicity, *Investigations, Rural areas, Water quality

*Dietary effects, *Canines, *Thyroids, Beagles
                                        319

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 287J

 AMMONIA DETOXIFYING MECHANISMS  OF RAINBOW TROUT ALTERED BY
 DIETARY DIELDRIN,

 Mehrle, P. M.,  and Bloomfield,  R. A.

 Missouri  University,
 Colombia, Missouri,
 Fish-Pesticide  Research  Laboratory

 Toxicology and  Applied Pharmacology,  Vol. 27,  No.  2,  p  355-365,  February,  1974.
 3  fig, 2  tab, 18  ref.

 Ammonia is one  of the  most  common  toxicants  discharged  into  the  aquatic en-
 vironment.   Ammonia  detoxifying mechanisms and brain  amino acid  metabolism
 of rainbow trout  were  altered by dietary dieldrin  dosages of 14,  43,  143,
 and 430 micrograms/kg  body  weight  per day for  240  days.  Whole-body dieldrin
 residues  in  fish  from  the lowest three dosage  groups  were comparable to those
 found in  fish from the aquatic  environment.  The brain  concentrations of
 amino acids  associated with ammonia  detoxifying mechanisms,  asparate, gluta-
 mate  and  alanine,  were significantly altered,  as were the enzymes related  to
 metabolism.  Brain ammonia  concentrations increased in  the groups given the
 two highest  dosages.   Mitochondrial  morphology in  liver  cells was significantly
 altered by dieldrin  treatment as determined  by electron microscopy.  The
 ammonia detoxifying  mechanisms  of  fish seemed  to be very sensitive to diel-
 drin; the "no-effect"  dosage was below 14 micrograms/kg body weight per day.
 Results indicate  that  fish  carrying  body burdens of dieldrin would be less
 tolerant  to  increased  concentrations of ammonia in water.  Subtle biochemical
 effects of dieldrin  influence the  adaptability and survival  of rainbow trout
 in their  aquatic  environment.

 *Ammonia, *Aquatic environment, *Amino acids,  *Rainbow  trout, *Dieldriti,
 Discharge,  Pollution,  Electron  microscopy,  Fish, Enzymes

 *Detoxification,  Dietary effects,  Brain concentrations,  Liver cells

 288J

 COMPARATIVE  TOXICITY,  ANTICHLOINESTERASE ACTION AND META-
 BOLISM OF METHYL  PARATHION  AND  PARATHION IN  SUNFISH AND MICE,

 Benke, G. M., Cheever, K. L., Mirer,  F.  E.,  and Murphy, S. D.

 Harvard University School of  Public Health,  Boston,
 Massachusetts,  Department of  Physiology, Kresge Center
 for Environmental Health

 Toxicology and  Applied Pharmacology,  Vol. 28,  No.  1,  p 97-109, April,  1974.

 Due to the increased use of insecticides, especially  methyl  parathion (which
 is  replacing DDT in many agricultural  applications),  the species  differences  in
 toxicity  of  methyl paration were investigated.  Chosen to test mammals  and
 fish were sunfish and mice.   The centrachids,  including sunfish,  are  particu-
 larly sensitive to organophosphorus insecticides.   Mice and  fish  were chosen
 to  determine the basis for  the  low toxicity  of methyl parathion in  sunfish
 (LD50 is more than 2500 mg/kg).  The LD50 values of parathion and methyl
 parathion in mice were 13.5 and  11 mg/kg, respectively,  and  the times  to
 death were much shorter for both compounds in mice  than in fish.  Low sen-
 sitivity of  fish cholinesterases to paraoxon as compared to mice  accounted
 for the 10-fold lower toxicity of parathion  in fish (LD50,  110 mg/kg).  By
 contrast,  sunfish had similar cholinesterase sensitivities to methyl  para-
 oxon and paraoxon.  Differences  in rates of  oxidative formation of  the  oxygen
 analog or oxidative cleavage  to p-nitrophenol  and  the corresponding dialkyl
 thiophosphate could not account  for the  selective  resistance of sunfish to methyl
 parathion toxicity.  Fish and mouse liver homogenates catalyzed a glutathione
 (GSH)-dependent metabolism of methyl parathion and methyl paraxon but  not of
 parathion or paraoxon.   Apparently, a  longer time  to  death in fish provided
 the opportunity for GSH-dependent and hydrolytic detoxification,  which  favored
methyl parathion and methyl paraoxon relative to parathion and paraoxon.

 *Toxicity, *Sunfishes,  *Insecticides, Metabolism,  Agriculture, Analytical
 tests

*Mice, *Methyl parathion, Parathion,  Organophosphorus, Cholinesterase  sensiti-
vities, Antichloinesterase
                                      820

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 289J

 AEROBIC TREATMENT OF FARM WASTES,

 Hills, D. J.

 Lincoln College, Agricultural Engineering Institute,
 New Zealand

 New Zealand Journal of Agriculture, Vol. 128, No. 4, p 42-44, April, 1974.  3 fig.

 Since the Water and Soil Conservation Amendment Act of 1971, farmers have
 had to consider alternative treatment methods of their wastes, particularly
 livestock wastes.  The most widely used waste disposal systems in New Zealand
 were anaerobic lagoons and spray disposal.  However, in situations where
 these methods cause odors or aggravate poor soil characteristics, aerobic
 treatment must be considered.  Oxidation ditches and mechanically aerated la-
 goons are both modified forms of the municipal activated sludge treatment
 process.  This may be applied to beef cattle and poultry wastes but is es-
 pecially useful in piggeries.  Mechanically aerated lagoons also may be used
 in New Zealand in the future.  Surface aeration is of value as a means for
 odor control of wastes which will be subsequently spread on land.  Various
 agricultural operations are noted, with their specific problems.  These
 include piggeries, dairy sheds, beef cattle feedlots, poultry houses, and
 livestock.

 *Agricultural wastes, *Waste disposal, *Anaerobic treatment, *Aerobic treatment,
 Lagoons, Odors, Oxidation, Activated sludge, Municipal waters, Livestock,
 Aerated lagoons, Legislation, Oxidation lagoons

 *New Zealand, Oxidation ditches, Piggeries
290J

FISHERIES ACT IS KEY TO WATER QUALITY,

Higgins, P. M.

Environmental Protection Service, Environment Canada, Water
Pollution Control Directorate

Modern Power and Engineering, Vol. 68, No. 4, p 44-45, April, 1974.

Containment of pollution and practical technological approaches have been
stressed by the federal government of Canada for water pollution control.
Legislation specifically discussed is the amended Fisheries Act.  These give
the federal government a means of controlling specific industrial effluents by
defining certain substances as being deleterious to fish.  Regulations which
have been produced involve the paper and pulp industry, the chlor-alkali and
the petroleum refining industry.  Phosphate levels in detergents have been also
regulated.  National guidelines are being developed, with participation of
industry.  This Federal/Provincial/Industrial Task Force then reviews environ-
mental effects and pollution control which influences subsequent regulations
and guidelines.

*Federal jurisdiction, *Fisheries, *Water quality control, Industrial wastes,
Canada, Legislation, Phosphates, Fish, Petroleum, Environmental effects,
Pollution control, Regulations, Technology

*Fisheries Act (Canada), Federal/Provincial/Industrial cooperation
                                      821

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 291J

 COST OF THERMAL EFFLUENT STANDARDS FOR POWER PLANTS,

 Ortolano, L., and Smith, F. A.

 Stanford University, Stanford, California, Department of
 Civil Engineering

 Journal of the Power Division, Vol. 100, No. PO-1, p 15-31, July, 1974.
 5 tab, 8 ref.

 The results of a study to explore thermal pollution abatement possibilities for
 proposed steam-electric generating plants and to develop methods for approxi-
 mating estimates for associated costs are summarized.  Functional relations
 between abatement costs and degrees of effluent control were estimated.  Case
 study applications for alternative cooling system designs were presented.
 Conclusions can be explained in terms of:  the cost-estimating procedure it-
 self; the abatement cost results suggested by the case studies; and some policy
 issues in relation to thermal water quality standards.  From the results of
 the case studies it was seen that thermal effluent modification costs generally
 increase at an increasing rate as functions of both decreases in design ef-
 fluent temperature and decreases in design effluent flow rate.  Effective abate-
 ment programs for proposed plants require modifications in both steam cycle and
 cooling system components.  The most important design variable is the condenser
 pressure.  Policy implications involve predictive capabilities including esti-
 mation of economic costs; prediction of receiving water temperature profiles as
 a function of effluent temperature and flow rate; and prediction of ecological
 impacts from changes in receiving water temperature.  Using the model presented,
 one should determine the physical and ecological consequences of alternative
 effluent standards and then evaluate the economic implications.

 *Thermal pollution, *Water quality standards, *Power plants, Costs, Systems
 analysis, Model studies, Design criteria, Flow rate, Effluents, Temperature,
 Water cooling, Ecological effects

 *Thermal pollution abatement, *Steam-electric plants, Cost estimating,
 Condenser pressure
292J

THE RESPONSE OF LAKE SUPERIOR PERIPHYTON TO HEAD ADDITIONS,

Drown, D. B.

Minnesota University

Dissertation Abstracts International, Vol. 34, No. 11, p 5503-5504B, May, 1974.

The effects of a 10 to 12 degree centigrade temperature increase in Lake Su-
perior were measured in terms of the near-shore periphyton assemblage.  A
field station with holding tanks and a hot water source was built on a rock
ledge of the Lake shore near Castle Danger, Minnesota.  Growth patterns were
followed under two sets of conditions, with both periphyton covered rocks and
denuded rocks, one in unheated lake water and the other in water with the
temperature raised above ambient.  Growth data indicated that a change from
diatoms to greens resulted which might have serious repercussions on benthic
grazers as well as on the whole food chain of the area.  Such temperature
changes could, in fact, occur as a result of a thermal-electric generating
station discharge and could effect the local periphyton community.

*Thermal pollution, *Temperature, *Lake Superior, *Periphyton, Field data,
Algae, Food chain, Discharge, Lakes

*Thermal-electric generating stations
                                         822

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293J

EVALUATION OF THE KENTUCKY WATER SUPPLY PROGRAM.  DRINKING
WATER,

Environmental Protection Agency,
Region IV,
May, 1972

N.T.I.S. Report No. PB228 609, 228 p, 3 tab, 11 ref.

The Kentucky Water Supply Program was investigated and found not to be providing
the health evaluation and engineering services necessary to meet its responsi-
bilities to protect the health of Kentucky's citizens.  Areas studied included
water quality, facilities, and surveillance.  It was recommended that the water
supply program be given more funds; new and competent personnel, including a
bacteriologist and a chemist; and that regulations be revised.  New standards
should include establishing a minimum sampling frequency, clarifying the quality
standards for drinking water, providing for orderly development of new supplies,
and requiring that water system plans be prepared by professional engineers.
For the public health, improvements are needed in the areas of legal statutes,
budget, manpower resources, regulations and policies, laboratory support,
surveillance, and operator training.

*Public health, *Water supply, *Potable water, *Water quality standards,
Engineering, Bacteria, Sampling, Regulations, Systems analysis, Water resources
management, Manpower

*Kentucky Water Supply Program, Kentucky, Surveillance, Operator training
 294J

 TEMPERATURE  EFFECT  ON  BRAIN  GLYCOGEN  OF FISH,

 Breer,  H., and Rahmann,  H.

 Stuttgart-Hohenheim University,
 Zoological Institute,
 German  Federal Republic

 Brain Research,  Vol. 74,  No.  2,  p  360-365,  July  12,  1974.   3  fig,  19  ref.

 Investigations were undertaken  to  determine possible seasonal changes  of  the
 concentration  of brain glycogen  and to  study the  influence  of temperature,  one
 of  the  critical  factors  in the  life of  aquatic poikilotherms,  on  the  glycogen
 metabolism of  fish  CNS.   The  experiments were performed  on  Scardinus
 erythrophthalmus and on  Carassius  auratus.   Results  show that there are very
 different responses of both brain  and liver organs under thermal  stress.  In
 the liver, glycogen levels are  constant, whereas  in  the  brain,  glycogen levels
 are influenced by the  water  temperature.  Also,  the  intensified accumulation
 of  glycogen  in cold-acclimatized goldfish brains  is  an adaptation process
 which starts immediately  after  the temperature changes;  it  is particularly
 intensive during the first hours but  can be observed for over several  weeks.
 Contrary to  the  results  of the experimental temperature  test,  under natural
 conditions there was an  accumulation  of glycogen, in brain  as well as  in
 liver,  during  cold  seasons.   It  could not be shown from  these findings
 which subcellular compartments are responsible for the increased  glycogen
 storage in the cold.

 investigations,  *Temperature, *Fish  physiology,  *Thermal stress,  Seasonal

 *Goldfish, Brains,  Livers, Fish  CNS,  Glycogen levels
                                       323

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 295J

 WE'RE RED-TAPED TO A STANDSTILL,

 Storck, W. J.

 Water and Wastes Engineering, Vol. 11, No. 66, p 47-48, June, 1974.

 The Water Pollution Control Federation's annual Government Affairs Seminar had
 as this year's topic "Energy, Money, and Pollution."  Points of interest
 included the following.  One"of the major problems in Federal funding of
 municipal waste water  treatment facilities is that the present level of
 funding is not keeping up with inflation.  The water pollution program has
 been halved by a series of overt executive impoundments; however,
 bureaucratic red-tape  is slowing the program down even further.  Also, the
 energy shortage will affect waste water treatment plants in ways other than
 short supplies of fuel oil, electricity, and natural gas.  There is likely
 to be an increased competition for funds at the Federal level as the energy
 research and development program calls for an expenditure of more than $10
 billion over a five-year period.  Finally, it was the feeling of many of  the
 participants that PL 92-500 must be amended.

 *Conferences, Financing, Government finance, Waste water treatment, Legislation,
 Standards, Federal government, Priorities, Water pollution control

 *PL 92-500,  *Water Pollution Control Federation
296J

INCIDENCE AND SIGNIFICANCE OF POLYNUCLEAR AROMATIC
HYDROCARBONS IN THE WATER ENVIRONMENT,

Andelman, J. B., and Snodgrass, J. E.

Pittsburgh University, Pittsburgh, Pennsylvania,
Graduate School of Public Health

Critical Reviews in Environmental Control, Vol. 4, No. 1, p 69-83, January,
1974.  9 tab, 69 ref.

It has been established that many polynuclear aromatic hydrocarbons (PAH)
are carcinogenic to animals and probably to man.  Most of the studies to
date on the incidence of PAH in the water environment have been carried out
in Europe with the need to establish hygienic standards for carvinogenic
compounds being given more attention in the last few years.  This review
deals with the pertinent physicochemical properties of PAH, their analysis,
origin, source, and transport in the environment, their presence in
environmental waters, their removal or destruction by various treatment
processes, and the possible health consequences to man of PAH in the water
environment.  The emphasis is on 3,4-benzpyrene.

*Aromatic compounds, *Reviews, Water analysis, Environmental effects,
Chemical properties, Physical properties, Public health

*Polynuclear aromatic hydrocarbons, *4-benapyrene
                                        824

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297J

INFLUENCE OF SEVERAL ALGAE ON  2,4-D RESIDUES IN WATER,

Valentine, J. P., and Bingham, S. W.

Virginia Polytechnical Institute and State University,
Department of Plant Pathology  and Physiology,
Blacksburg, Virginia

Weed Science, Vol. 22, No. 4,  p 358-363, July, 1974.  6 fig, 4 tab, 17 ref.

Removal of (2 to the minus 14)C 2,4-D (2,4.-dichlorophenoxyacetic acid) from
water was pronounced with Scenedesmus quadricauda and most effective uptake
occurred at pH 4.7.  Three other algae were relatively ineffective in removal
of 2,4-D.  Increasing Scenedesmus cell density increased 2,4-D removal, but
the amount absorbed was not a  linear function of cell density.  Similarly,
with a range of herbicide concentrations (0.01 to 1.0 ppmw) the amount
removal was greatest at the highest concentration.  However, a higher percentage
of chemical was removed at lower concentrations.  An equilibrium of 14 C
removal from water and 14 C released to the water was reached by 4 hr.  More
herbicide was removed from water by Scenedesmus in darkness than in light
and low temperature (2 C) reduced uptake slightly.  Relatively high 2,4-D
concentrations were required to reduce growth in any of the four algae and
Scenedesmus was most sensitive.  Scenedesmus metabolized (ring-14 C) in
24 hr to several products which were found in suspension fluid and cells.
Quantitatively, 3-OH-2,4-D (3-hydroxy-2,4-dichlorophenoxy acetic acid) was
the major metabolite, comprising 26 percent of the radioactivity extracted
from cells compared to 15 percent from suspension fluid.  A smaller amount of
5-OH-2,4-D (5-hydroxy-2,4-dichlorophenoxy acetic acid) was isolated from
the suspension fluid and none  from the cells.

*Scenedesmus, *Water analysis, Carbon, Algae, Hydrogen ion concentration,
Laboratory tests, Environmental effects

*2,4-D stability, *2,4-dlchlorophenoxy acetic acid
298J

MERCURY BURDEN OF HUMAN AUTOPSY ORGANS AND TISSUES,

Mottet, N. K., and Body, R. L.

Washington University, School of Medicine, Seattle,
Washington, Department: of Pathology

Archives of Enviromental Health, Vol. 29, No. 1, p 18-24, July, 1974.  4 fig,
5 tab, 36 ref.

A method of flameless atomic absorption spectroscopy was used to assay the
total mercury burden in 14 autopsied organs and tissues from 113 persons.
Their ages ranged from 26 weeks of gestation to 88 years.  Over 70 percent
of all assays, irrespective of organs or age, had a burden of less than 0.25
micrograms/gm of wet weight.  Less than 10 percent had more than 0.75 micrograms.
The kidney was the organ with the most variable burden, 29 percent of the
assays being above 0.75 micrograms/gm.  The burden in fetal organs was more
uniform than those in postnatal life.  Multivariate statistical analysis
suggests that the urban population has a somewhat greater mercury burden than
the rural.  The data did not reveal a statistically significant increase with
age, suggesting that past environmental exposure levels exceed the capacity
of the body to eliminate mercury.

*Human pathology, *Spectroscopy, *Mercury, Data collections, Statistical
analysis

Human kidney
                                     825

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299J

MERCURY IN MAN,

Stein, P. C., Campbell, E. E., Moss, W. D., and
Trujlllo, P.

Los Alamos Scientific Laboratory, Los Alamos, New
Mexico, Health Division, Industrial Hygiene Group,
Bio-Analytical and Chemical Section

Archives of Enviromental Health, Vol. 29, No. 1, p 25-27, July, 1974.  1 fig,
7 tab, 12 ref.

Mercury analyses were performed on tissues removed at autopsy from 47 human
subjects from two geographical areas.  Data obtained from lung, liver, and
kidney could not be correlated with age, sex, or place of residence at the
time of death.  The highest concentrations of mercury were found in the
kidney.  Whether wet or dried tissue is analyzed does not affect the result.
Data are presented to establish some base line for levels of mercury in a
general population.

*Mercury, *Human pathology, Data collections, Analytical techniques


Los Alamos, New Mexico, Denver, Colorado, Human kidney
    300J

    THE LONG-RUN ASYMMETRY OF SUBSIDIES AND TAXES AS
    ANTIPOLLUTION POLICIES,

    Porter, R. C.

    University of Michigan, Ann Arbor, Michigan,
    Department of Economics and Center for Research on
    Economic Development

    Water Resources Research, Vol. 10, No. 3, p 415-417, June, 1974.  1 tab,
    11 ref.

    Primers on the discharge of unwanted but unpriced effluents into the air and
    water now treat as commonplace the symmetry between taxes on effluents and
    subsidies for abatement as means of reducing an industry's pollution.  This
    note shows that on the contrary, serious asymmetry results when entry
    and exit occur in response to subsidies or taxes.  Hot only does the
    quantitative symmetry disappear, but even the qualitative impact (the
    directions of the effects) of charges and bribes on the volume of firm and
    industry effluents may differ.  More specifically, the possibility emerges
    than an abatement subsidy offered to an industry may increase the total
    effluents of that industry.

    *Taxes, *Effluents, industrial wastes, Waste disposal, Pollution
    abatement, Mathematical studies, Economics
                                        826

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 301J

THE ROLE OF MICROORGANISMS  IN MARINE FOULING,

Young, L. Y., and Mitchell, R.

Stanford University, Stanford, California,
Department of Civil Engineering

International Biodeterioration Bulletin, Vol. 9, No. 4, p 105-109, 1973.
4  fig, 20 ref.

Differences in  the microbiological film appear  to be detected by oyster
larvae Crassostrea virginica.  In laboratory studies attachements to surfaces
varied depending on the nature of the microbial film.  Field tests appear
to indicate that the number of animals which attach to a surface is
proportional to the number  of bacteria composing the primary film.  Tests
carried out in  two markedly different locations indicate the same trend
occurring but over different periods of time.   The pristine enviroment
required three  times as long for the development of the same degree of
fouling as the nutrient rich environment.  Oyster larvae dislplay three
characteristic patterns toward a variety of organic compounds and
microoorganisms:  positive, neutral-active and  inactive, and negative
chemotaxis.  It was suggested that control of microbial and macrobiological
fouling be considered  from  the aspect of altering the interaction between the
larvae and the microbial population on the surface.

*Microorganisms, *Fouling,  laboratory tests, On-site investigations, Larvae,
Microbiology, Pollution abatement, Water pollution effects, Organic compounds
302J

TULE CREEK DAM,

Ehly, J.

Water and Sewage Works, p 130, April 30, 1974.

A $2.6 million non-federal aid dam on Tule Creek in Texas is nearing completion.
A 35-foot wide core of Tule clay which is impervious to water rising from a
depth of 25 feet below the canyon floor will extend through the center to
the top of the dam across its full length.  A 30-inch pipe encased in concrete
will be the service outlet.  Stabilized soil will provide slope protection
on the upstream side.  The downstream side of the dam will have 14 acres
of Bermuda grass seeding and a sprinker system.

*Dams, Construction materials, Construction costs, Texas, Dam foundations,
Damsites, Dam design, Dam construction
                                      827

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 303J

WATER RESEARCH IN THE SOVIET UNION,

Barabas, S.

Canada Centre for Inland Waters, Burlington, Ontario,
Canada

Chemistry in Canada, Vol. 26, No. 6, p 14-17, June, 1974.

A two-man delegation was sent by the Environment Canada to the Soviet Union
to identify the Soviet institutes and scientists engaged in inland water
research, to inform the Soviets about what Canada is doing in the field, and
to lay the foundation for future exchanges of information among the inland
water scientists of the two countries.  The various institutes visited are
listed; a brief account of the discussions held at the various institutes
is detailed.

*Research and development, *Canada, Institutions, Research priorities,
Political aspects, Information exchange

U.S.S.R.
 304J

 FACTORS AFFECTING RESIDENTIAL WATER CONSUMPTION:  THE
 MANAGERIAL VIEWPOINT,

 Primeaux, W. J., Jr., and Hollman, K. W.

 Mississippi University, School of Business Administration

 Water and Sewage Works, p 138-140, 142-144, April 30, 1974.  3 tab, 4 ref.

 A study was calculated through the use of multiple regression analysis on the
 effect that price and other selected economic and socioeconomic variables have
 on the quality of water demanded in residential households in northern
 Mississippi.  A regression equation using economic, socioeconomic, and
 climatic factors was derived to describe water demand.  Results suggest that
 those communities whose water systems managers and planners are able to
 forecast correctly their future population growth will be in an advantageous
 position with respect to estimating future demands on their water systems.
 A final conclusion indicates that the results of this study are somewhat
 tentative since both the price response and the income response were weaker
 than those found in other studies.

 *Regression analysis, *Water quality, *Economics, Mississippi, Water demand,
 Project planning, Water consumption
                                         828

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 305J

GROUP CONSIDERS PROPER MANAGEMENT OF COASTAL AREAS,

Environmental Science and Technology, Vol. 8, No. 7, p 6Q6-607, July, 1974.

The United States, faced with massive increases in coastal zone develop-
ment, is in a position to lose as much as it could gain, as was stated
at the National Oceanic and Atmospheric Administration-sponsored Conference
on Coastal Zone Management.  In order to assure a balance between the
two, a national coastal zone management program is needed.  Although many
feel more authority is needed at the federal level if the problems of the
nation's coastal  zones are to be adeuqately handled, the thrust of the
1972 Act is toward setting up programs in each of the individual states.
The local view of the national interest in coastal zone planning and
management was discussed.  It was stated that natural science identi-
fication, assembly, and interpretation are beyond local and probably
state capability  and should be a federal responsibility.

*Dnited States, *Coasts, Coastal engineering, Water management  (Applied),
Administration, Federal water pollution control act, Federal jurisdic-
tion, Conferences, Water pollution  control
 306J

ENVIRONMENT AND ECONOMIC GROWTH,

Environmental Science and Technology, Vol. 8, No. 7, p 608-069, July, 1974.

An intensive study by the Committee for Economic Development (CED)
showed the following results:  there will be a steady increase in the
economic recovery of solid waste for fuels and materials; the United
States can afford and achieve a high-quality environment if it adopts
programs that weigh costs against benefits to produce maximum effective-
ness; and, environmental progress will require more economic growth to
carry the cost of pollution control programs.  The CED foresees either
lack of vigorous enforcement or widespread government regulation of
business decisions with regards to the 1972 clean water law amendment.
As an alternative to regulation, the CED calls for the use of effluent
fees in the form of a monetary charge per unit of waste discharged.
Careful regulation of toxic discharges would be retained.

*Economics, "^Investigations, United States, Solid wastes, Environmental
control,  Cost* inefit analysis,  Pollution abatement
                                      829

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307 J

WATER OFFICERS MEET AT PERTH,

Surveyor, No. 4275, p 38-39, May 17, 1974.

The general mood of the 1974 conference of the Association of Water
Officers (AWO) seemed to be that reorganization has added to the
association's standing as a professional body.  In recounting the
historic achievements of the AWO it was noted that from 1965 to 1974
there were ten years of river authorities which had been set up by the
1963 Act.  This period saw the evolution of the multipurpose river
authority, but it was not fully empowered with regard to pollution.
There was ample water in the country in the form of precipitation but
it was badly spaced in time and location.  The board considered that
the correct policy was to have a small number of large resevoirs rather
than a large number of small resevoirs.  Rivers were used to convey
water and tunnels to convey water from one river to another, if nec-
essary.  AWO now covers 1400 sewerage and sewage disposal authorities.

*Conferences, *Administration, Water management (Applied), Sewage
disposal, Tunnels, Rivers, Reservoir operation

Great Britain
 308J

 INHIBITION OF  INTER-MICROBIAL PREDATION BY CHLORINATED
 HYDROCARBONS,

 Walsh, F. and  Mitchell, R.

 Harvard University, Division of Engineering and Applied
 Physics, Laboratory of Applied Microbiology, Cambridge,
 Massachusetts

 Nature, Vol. 249, No. 5448, p 673-674, June 14, 1974.  1 tab, 6 ref.

 The rate of kill of Escherichia coli by marine predators in the presence
 of 2,4-dichlorophenoxyacetate (2,4-D) and o,o-dichlorobiphenyl has been
 examined.  The predators were isolated from seawater by repeated subcul-
 ture in artificial seawater using E. coli as the sole carbon source.  The
 resulting predators displayed positive chemotaxis to E. coli; the observed
 changes in E.  coli kill rates between lower and higher chlorinated hydro-
 carbon concentrations are the result of inhibition or excitation of the
 chemotactic response in the marine predators of E. coli.  Several attempts
 were made to isolate a single predator species from the mixed predator
 culture; in every case a mixed culture resulted when the isolates were
 reinoculated into artificial seawater with E. coli as the sole carbon
*E. coli, *2,4-D, *Chlorinated hydrocarbon pesticides, *Predation

Chemotactic response
                                       830

-------
 309 J

 SOME IMPLICATIONS OF THE PETROCHEMICAL DECOMPOSITION OF
 PESTICIDES,

 Watkins, D. A. M.

 Bristol University, Long Ashton Research Station,
 Bristol

 Chemistry and Industry, Vol. 2, No. 5, p 185-190, March, 1974.
 5 fig, 1 tab, 46 ref.

 The emphasis in the study of light effects on pesticides has changed from
 observing that an effect occurs, through a phase of identifying products
 in an artificial system, to investigating the effect in various environ-
 mental conditions such  as soil, water, and air.  Interest is also being
 shown in the effect of  photosensitizers and in the photonucleophilic
 reactions of pesticides with other compounds present in the environment.
 A discussion of a representative selection of pesticides is given with
 the empasis on the vapor work that has been reported and also on break-
 downs which give volatile or gaseous products.

 *Pesticides, "Photometry, Irradiation, Dieldrin, DDT,  Carbamate
 pesticides, Heptachlor, Acids, Fungicides

 Dichlofuanid, Dinitrophenols, Dithiocarbamates
310J

EUROPEAN WATER CLEANUP IS UNDER WAY,

0'Sullivan, D.

Environmental Science and Technology, Vol. 8, No. 7  p 602-604
July, 1974.

A three-day conference entitled "Industrial Waste Water and Disposal
Within the European Economic Community" centered mainly on the nine-
member EEC countries, Belgium, Denmark, Italy, France, West Germany,
Ireland, The Netherlands, England, and Luxembourg.  Highlights of the
meeting included:  pollution of the Khine, estuaries, and tidal reaches;
taxes on effluent discharges; and, legislation and enforcement.

"Conferences,  "Europe, Industrial wastes, Waste water treatment, Waste
disposal, Discharge (water), Estuaries, Tidal waters, Taxes,  Legislation

Rhine River
                                   831

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311J

LOOKING TO EUROPE FOR A POLLUTION TAX MODEL.  OR HOW
THE CONSUMER WILL PAY,

Surveyor Public Authority Technology, No. 4275 p 10-12, May 17, 1974.

Economic aspects of the conference on industrial waste water treatment
and disposal within the European Economic Community (EEC)  are examined.
Calculation of the pollution tax instituted in the Netherlands according
to the 1970 Surface Water Pollution Control Act, which imposes a pol-
lution tax relating to the polluting load discharged,  is described.
Opposition to the principle of pollution-must-pay is voiced and the theory
of consumer-will-pay advocated.  It is concluded that uniformity is
required and that centralized treatment facilities be developed.

*Economics, Conferences, Europe, Industrial wastes, Waste water treatment,
Taxes, Treatment facilities
   312J

   STUDY ON SUBACUTE TOXICITY OF CARBON n-HEXANE-ACETONE
   EXTRACT RECOVERED FROM DRINKING WATER,

   Maruoka, S., Nishio, T., and Kawai, S.

   Kyoto Municipal Hygienic Laboratory, Higashi-Takada-cho,
   Mibu, Nakagyo-ku, Kyoto, Japan

   Bulletin of Environmental Contamination and Toxicology, Vol. 11,
   No. 6, p 545-550, 1974.  3 tab, 5 ref.

   The subacute toxicity of organic substances present in the tap water of
   Kyoto using a carbon-n-hexane-acetone extraction (CHAE) method has been
   investigated.  A preliminary acute toxicity study showed that the po LD50
   value of CHAE was over 5 g/kg body weight, althoughit was difficult to
   determine the exact value because of its high viscosity.  The body
   weight, food consumption, and organ weights of mice after three months
   of the dietary regimens showed no significant differences between control
   and test groups.  The gross and histological examinations revealed no
   abnormalities attributable to CHAE.  From these results is is presumed
   that the amounts consumed by citizens may cause no adverse effects on
   health.

   *Toxicity, *Potable water, Organic compounds, Analytical techniques,
   Laboratory animals, Animal physiology, Public health

   *Japan, *Carbon n-hexane-acetone extraction
                                        832

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 313J

 CHLORINATED INSECTICIDE RESIDUES IN THE EGGS OF SOME
 FRESHWATER FISH,

 Johnson, L. G., and Morris, R. L.

 Iowa University, State Hygienic Laboratory, Iowa City,
 Iowa

 Bulletin of Environmental  Contamination and Toxicology, Vol.  11,
 No. 6, p 503-510,  1974.  2  fig, 2 tab, 8 ref.

 Because of the significant  aggregation of  dieldrin in the  flesh of catfish
 found in some rivers  and the wide variation between species in pesticide
 content, study of  the pesticide levels in  the eggs of some fish from
 five locations in  Iowa was  undertaken in 1971.  The pesticide concentra-
 tions and extractable fat  contents found are tabulated.  Dieldrin is  the
 major insecticide  residue  detected in the  eggs.  The highest  concentrations
 were determined in fish flesh and water samples.  The levels  of dieldrin
 found in th,e flesh of catfish were much higher than in  the flesh of any
 pan or game fish.  Concentrations of dieldrin versus percent  lipids are
 presented.  The concentrations of polychlorinated biphenyls found are
 listed and the PCB content  versus percent  lipids is graphically presented.

 *Chlorinated hydrocarbon pesticides, *Catfishes, *Bass, *Pikes, *Walleye,
 Dieldrin, DDE, DDT, ODD, Aldrin, Investigations, Monitoring

 Chlordane, Heptachlor epoxide
314J

HOW PURE IS OUR WATER SUPPLY?,

Environmental Science and Technology, Vol. 8, No. 7, p 612, July, 1974.

Water consumption has increased from 40 billion gpd in 1900 to 390 billion
gpd in 1968.  Home usage has been mainly for toilet flushing, bathing,
and laundering; elsewhere, water is used for heating, cooling, cleaning,
and as a solvent.  Over 90 percent of the United States freshwater re-
sources are underground.  Yet only 20 percent is extracted for supply
purposes.  To achieve the national goal of zero discharge of pollutants
to its navigable waters by 1958 will require the recycling of industrial
process waste waters.  In closing the influent/effluent gap, there still
remains the problem of dissolved solids removal on a practical and econo-
mic basis.

*Water supply, Water consumption, Water resources, United States, Indus-
trial water, Water Utilization, Recycling, Discharge (water) , Dissolved
solids
                                     833

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 315J

 WATER QUALITY PROBLEMS ARISING FROM IRRIGATION RETURN FLOW,

 Ghosh, D.  K.

 Bengal Engineering College,
 Howrah, Bengal,
 Civil Engineering Department

 Journal of the Institution of Engineers (India),  Vol. 54,  Part PH2,  p 55-56,
 February,  1974.  5 ref.

 Major water quality problems arise from irrigation return  flows.   Their solutions,
 the control measures required, and necessary research activities  have been indi-
 cated.  Quality of the residual water draining from irrigated areas  as return flow
 may be materially degraded in several ways,  as compared with the  initial water
 supplied.   Irrigated agriculture consumes  the largest quantity of water, and it
 will be of great significance in the overall water management and development in
 a basin.  This is particularly so when water resources are fully  utilized.  Mea-
 sures for controlling water quality degradation by irrigation return flows are
 urgently required.

 *Water quality control, *Water resources management,  *Irrigation, Agriculture,
 Management, Flows, Research
316 J

ACCUMULATION OF DIETARY POLYCHLORINATED BIPHENYLS (AROCLOR 1254)
BY RAINBOW TROUT (SALMO GAIRDNERI) ,

Lieb, A. J., Bills, D. D., and Sinnhuber, R. 0.

Oregon State University,
Corvallis, Oregon,
Department of Food Science and Technology

Journal of Agricultural Food Chemistry, Vol. 22, No. 4, p 638-642, July/August,
1974.  6 fig, 4 tab, 26 ref.

The accumulation of PCB's (Aroclor 1254) by a Mount Shasta strain of rainbow
trout (Salmo gairdneri) from a dietary level of 15 ppm was determined.  Instrumen-
tation included a gas chromatograph equipped with an electron capture detector.
The relative concentration (parts per million) of PCB's in the fish stabilized;
absolute quantities (micrograms of PCB/fish) increased as the fish grew.  The
total retention of PCB's from the diet was 68 percent for a 32-week feeding period.
The distribution of PCB's was fairly constant in the lipid portion of various
tissues.  Even when the fish were starved, PCB's did not appear to be eliminated
from the trout after PCB exposure ceased.  No mortalities were attributed to PCB
toxicity.

*Rainbow trout, *PCB's, *Gas chromatography, *Dietary effects, Aquatic life,
Toxicity
                                         334

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 317J

 EFFLUENT  CHARGES-A PRICE ON POLLUTION.

 Ferrar, T. A.,  and Horst, R. L.

 The Center for  Air Environment  Studies at  the
 Pennsylvania  State University,  University  Park,
 Pennsylvania

 Atmospheric Environment, Vol. 6, No.  6, p  657-667,  June,  1974.   6  ref.

 The concept of  putting  a price  on  pollution has been  proposed as a means  of
 inducing  control of  environmental  deterioration.  The non-economist  reader is
 presented with  theoretical advantages offered by  an effluent charge  strategy by
 reviewing some  of the arguments presented  by economists  for the  adoption  of a
 national  tax  policy.  Effluent  charge is briefly  discussed.  Analysis  focuses  on
 the question  of efficient allocation  of resources in  an  idealized, perfectly
 competitive economy  with subsequent generalization  to imperfect  markets.  Examined
 also  is the least-cost  to society  attribute of an effluent charge  scheme.

 *Effluents, Pollution,  Economics

 *Effluent charge, National tax  policy
318J

WATER QUALITY CONSIDERATIONS IN PLANNING SMALL WATERSHEDS,

Burt, J. P., and Gentry, R. E.

U.S. Department of Agriculture,
Jackson, Mississippi,
Soil Conservation Service

Journal of Soil and Water Conservation, Vol. 39, No. 3, p 133-135, May/June, 1974.
3 tab, 2 ref.

State water quality criteria in Mississippi are summarized for water supply and
water-contact sports.  Factors listed are dissolved oxygen, pH, temperature,
bacteria, chlorides, specific conductance, dissolved solids, threshold odor,
phenolic compounds, and certain chemicals.  Criteria are listed in order to pro-
tect a participant's health in water sports and to provide a safe and appealing
body of water.  Field reconnaissance of a drainage area and water analyses of its
streams were used to estimate the quality of water in the planned lakes.

*Water quality control, *Water quality standards, *Water supply, *Field studies,
Conservation, Temperature, Dissolved oxygen, Dissolved solids, Odors, Chemicals,
Pnhlir hp^lf-h. 5sf-rpflms. Lakes. Drainage areas
Conservation, Temperature, Dissolved oxygen,
Public health, Streams, Lakes, Drainage areas
*Misslssippi
                                        835

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 319J

 LEAD AND CADMIUM CONTENT OF SELECTED OREGON GROUNDFISH,

 Chllds, E. A., and Gaffke,  J. N.

 Oregon State University,
 Astoria, Oregon,
 Seafoods Laboratory

 Journal of Food Science, Vol. 39,  No.  4,  p 853-854,  July/August,  1974.
 1 tab,  12 ref.

 An experimental study was undertaken to  determine the lead and cadmium content of
 selected groundfish in Oregon.   Samples  were obtained from commercial fishing pro-
 cessors.  The amounts of Pb and Cd were  measured by  atomic absorption spectrophoto-
 metry following extraction of the  metals  into 2-pentanone.  The lead content was
 in most cases less than 0.20 ppm;  Cd was  less than 0.10  ppm.   These data were in
 the general range of Pb and Cd for canned fruit and  vegetables and indicate that
 Oregon groundfish would not provide a  large proportion of  lead or cadmium in a
 diet.

 *Dietary effects, *Fish, *Lead,  *Cadmium,  Toxicity,  Spectrophotometry,  Metals,
 Analytical techniques,  Sampling

 *0regon, Groundfish
320J

RESIDUES IN FISH, WILDLIFE, AND ESTUARIES,

P. W. Borthwick, G. H. Cook and J. M. Patrick, Jr.

Gulf Breeze Environmental Research Laboratory,
Gulf Breeze, Florida

Pesticides Monitoring Journal, Vol. 7, No. 3/7, March, 1974.  3 ref.

In June 1972, a collection was taken of estuarine sediments, crabs, shrimps, and
fishes, two years after aerial applications of mirex bait for controlling fire
ants in coastal regions near Charleston, South Carolina.  Previous monitoring
(October 1969 to June 1971) determined levels of mirex in animal samples as:
crabs, 0-0.60 ppm; shrimps, 0-1.3 ppm; and fishes, 0-0.82 ppm.  Mirex was
recently shown present in three species of fish (white catfish, 0.021 ppm; blue-
gill, 0.047 ppm; carp 0.12 ppm) and blue crabs (0.026 ppm) at fresh water stations.
There was no mirex detected in 36 other species examined taken from nine saline
stations in the estuaries after a period of restricted pesticide use.  No mirex
was found at the bottom sediment samples.

*Pesticide residues, Fish, Wildlife, Estuaries, Monitoring

*White catfish, Bluegill, Carp, Blue crabs
                                     836

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321J

POLLUTION OF A STORAGE RESERVOIR BY ROOSTING GULLS,

Fennell, H., James, D. B., and Morris, J.

Public Health Laboratory  Service, Leeds
Lower Clyde Water Board
Wakefield and District Water Board

Water Treatment and Examination, Vol. 23, No. 1, p 5-24,  1974.  4  fig, 2  tab,
25 ref.

A survey to evaluate pollution caused by roosting gulls was made over a thirteen
month period on a storage reservoir.  From the 111 samples taken from the reservoir,
salmonellae were isolated from 52, although the specimens never originated  from
the incoming water from the catchment area.  Treatment of the reservoir water
effectively eliminated the pollution, never isolating the organisms  from  treated
water or distribution.  Roosting gulls are at their maximum in population in
December and their minimum between April and July.  During the winter a noticeable
deterioration occurred in the bacteriological quality of  reservoir water.   It is
suggested that domestic wastes from dumps provides sources of salmonallae,  and
that by feeding on such refuse, the gulls contaminate the reservoir.

*Reservoirs, *Salmonellae, *Gulls, Domestic wastes, Pollution, Water quality control,
Bacteria, Surveys, Pollution effects

Treatment methods
322J

LEVELS OF MIREX AND SOME OTHER ORGANOCHLORINE RESIDUES IN SEA-
FOOD FROM ATLANTIC AND GULF COASTAL STATES,

Markin, G. P., Hawthorne, J. C., Collins, H. L., and Ford,
J. H.

Forestry Sciences Laboratory,
Corvallis, Oregon

Pesticides Monitoring Journal, Vol. 7, No. 3/4, p 139-144, March, 1974.
1 fig, 2 tab, 9 ref.

A monitoring program of seafood was established to detect mirex insecticide in
1971.  Seventy-seven composite samples of oysters, crabs, shrimps, fish, and fish
products were gathered from seven areas within a certain distance from where the
mirex was being used.  The data showed that only 9 out of the 77 samples showed
an occurrence of mirex, in a ppm range of 0.005-0.024, and that those nine origi-
nated around Savannah, Georgia.  DDT was detected in 74 samples (0.002-2.475 ppm
range).  Aroclor 1260 occurred in 46 samples.  This PCB residue might have been
interpreted as mirex were it not for new cleanup methods.

*Pesticide residues, Oysters, Crabs, Shrimps, Fish, DDT, Polychlorinated biphenyls,
Monitoring, Insecticides

*Mirex, Organochlorine residue
                                         837

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323J

MI. SUNAPEE STATE PARK, NEW HAMPSHIRE SPRAY IRRIGATION
PROJECT,

Frost, T. P., Towne, R. E., and Turner, H. J.

State of New Hampshire, Water Supply and Pollution
Control Commission

In:  Conference on Recycling Treated Municipal Wastewater Through Forest
and Cropland, August 21-24, 1972, The Pennsylvania State University,
University Park, p 348-361.  8 tab, 3 ref.

The Sunapee State Park spray irrigation system in Newbury, New Hampshire,
distributes pretreated sewage to mountain slopes forested with mixed
hardwoods and scattered conifers interspersed with an occasional apple
tree indicating orchard or pastureland abandoned a generation ago.
Conifers tend to dominate the lower part of the slope with the numbers
of oaks and birches increased toward the upper levels.  The system was
planned and designed around the Pennsylvania State University project.
Preliminary analyses of the data indicate that spray irrigating with
pretreated sewage stabilization pond effluent has not resulted in any
substantial or discernible alteration in the composition of the groundwater
in the test wells, water from the drinking wells, or downstream surface
waters.  In conclusion, this small, seasonal, atypical sewage spray
irrigation system appears to have worked effectively to date to protect
contiguous groundwater and surface waters.  Based on experience in
New Hampshire and Pennsylvania it is the opinion of the New Hampshire
Water Supply and Pollution Control Commission staff that the Sunapee
system will probably continue to operate effectively for a long and
perhaps indefinite period of time at the present mode of operation.

*Sewage effluents, *Irrigation systems, *Forests, New Hampshire, Design
criteria, Project planning, Data collections, Groundwater, Water quality,
Surface waters

*Spray irrigation
324J

ECOLOGICAL AND PHYSIOLOGICAL IMPLICATIONS OF GREENBELT
IRRIGATION WITH RECLAIMED WATER,

Youngner, V. B., Kesner, W. D., Berg, A. R., and
Green, L. R.

California University, Department of Plant Sciences

In:  Conference on Recycling Treated Municipal Wastewater Through Forest
and Cropland, August 21-24, 1972, The Pennsylvania State University,
University Park, p 375-386.  5 tab, 9 ref.

The feasibility of using waste water from the mountain communities to
irrigate greenbelts strategically placed would reduce the wildfire hazard
while disposing of waste water, recharging groundwater reservoirs with
purified water, and creating new manageable recreation areas.  Although
no conclusive results have been obtained during the short time this
study has been underway, observations to date are sufficiently encouraging
to make continued study highly worthwhile.  Clearly irrigation of
chaparral during the dry season will increase the moisture content of
the wood and leaves.  Conversion of chaparral brush lands to grasses
and other plants presenting a lower fire hazard appears possible through
waste water irrigation.  The most satisfactory species with particular
reference to the use of the irrigated areas for recreation must still be
determined.

*Feasibility studies, *Waste water treatment, Groundwater recharge,
Water reuse, Irrigation systems, Recreation demand
                                       838

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 325J

 MICHIGAN'S EXPERIENCE WITH UTILIZING THE TEN STATES GUIDELINE
 FOR LAND DISPOSAL OF WASTEWATER,

 Pierce, D. M.

 Michigan Department of: Public Health, Division of Wastewater

 In:  Conference on Recycling Treated Municipal Wastewater Through Forest
 and Cropland, August 21-24, 1972, The Pennsylvania State University,
 University Park, p 410-413.  1 ref.

 Nearly fifty communities have designed land disposal systems, yet only
 two of these have been in operation longer than one year.  Even in this
 early stage of operational experience, some critical deficiencies in
 design are evidenced.  Case illustrations indicate unsatisfactory
 performance attributable to tight soils with loading capabilities less
 than assumed in the design of the system, coupled with high groundwater,
 inadequate drainage, and in one case topography conducive to sheet
 runoff.  Also the Sta.te's lack of experience has led to periods of
 uncertainty and apprenhension with regards to land disposal design and
 operation.

 *Design criteria, *Soil disposal fields, Performance, Waste water treatment,
 Land management, Waste disposal, Michigan
326J

FOREST SERVICE POLICY RELATED TO THE USE OF NATIONAL
FOREST LANDS FOR DISPOSAL OF WASTEWATER AND SLUDGE,

Olson, 0. C., and Johnson, E. A.

United States Department of Agriculture, Forest Service,
Division of Watershed

In:  Conference on Recycling Treated Municipal Wastewater Through Forest
and Cropland, August 21-24, 1972, The Pennsylvania State University,
University Park, p 414-419.

With some notable exceptions in the area of land reclamation and rehabilitation,
it is generally true that the primary concern of the Forest Service is more
one of aiding disposal with minimum detrimental impacts than it is one of
looking to onsite benefits.  This is in support of the established policy
that Forest Service programs contribute to community development and to
the improvement of the rural environment in general.  At the present
time there are 26 sites on National Forests in 14 States involved in
planning for land disposal of waste water and/or sludges by sprinkler or
flood irrigation.  Federal department requirements and general objectives
are discussed in relation to the Forest Service policy.

*Waste disposal, Federal Government, Forests,  Soil disposal fields,
Waste water treatment, Sludge treatment, Irrigation systems, Federal project
policy

U. S. Forest Service
                                    839

-------
 327J

 SPRAY  IRRIGATION - THE REGULARTORY AGENCY VIEW,

 Rhindress,  R. C.

 Pennsylvania Department of Environmental Resources,
 Ground Water Quality Management Unit

 In:  Conference on Recycling Treated Municipal Wastewater Through Forest
 and Cropland, August 21-2A, 1972, The Pennsylvania State University,
 University  Park, p 420-434.

 The Bureau  of Water Quality Management of the Pennsylvania Department of
 Environmental Resources is the regulatory agency concerned with the protection
 from pollution of all the waters within the state.  A regulatory agency
 becomes aware of spray irrigation from two separate sources:   as a new
 technique being promoted and as enforcement officials viewing a number of
 existing problems.  An environmental protection agency has an obligation
 to consider all techniques of waste disposal and to assess their
 applicability to various wastes and their impact upon the environment.  The
 experiences of the department with spray irrigation are discussed together
 with the philosophy concerning the use of land disposal techniques, and
 some important concepts which are included in their Spray Irrigation Manual.

 *Irrigation systems, *Regulations, Environmental control, Waste disposal,
 Soil disposal fields, Pennsylvania

 *Spray irrigation
328J

THE ECONOMIC VALUE OF WATER FOR WASTE DILUTION:
REGIONAL FORECASTS TO 1980,

Gray, S. L., and Young, R. A.

Colorado State University,
Fort Collins, Colorado,
Department of Economics

Journal of the Water Pollution Control Federation, Vol. 46, No. 7,
p 1653-1663, July, 1974.  5 tab, 12 ref.

The procedures and findings of a recent study that developed forecasts of the
value of water for diluting wastes in each of several major regions of the
United States are presented.  The discussion is limited to wastes in terms
of biochemical oxygen demand loadings only.  The conceptual issues in re-
source allocation, methods for estimating economic value and the chosen con-
ceptual framework, sources of data, and forecasts of the regional values of
dilution water for 1980 are examined.  Finally, the conclusions emerging from
the analysis are discussed.

*Forecasting, *Waste dilution, Water utilization, United States, Biochemical
oxygen demand, Economics, Estimating equations, Water resources, Optimization
                                    840

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329J

WATER ACT 1973 RIVERS (PREVENTION OF POLLUTION) ACT
1951 ATTORNEY GENERAL V, WELLINGBOROUGH UDC,

Water Services, Vol. 78, No. 939, p 167, May, 1974.

The Court of Appeal recently has heard the first appeal arising out of
the transfer of sewage disposal functions under the Water Act 1973.  It was
an appeal against an injunction granted against the former Wellingborough
U.D.C.  So as not to lose control of its new facilities, the local authority
stepped up on-line construction and service of the facility, a measure which
breached section 7 of the Rivers Act 1951 since the effluent wcxLd not comply
with the consent which had previously been given.  Thus the Attorney General
requested an injunction against using the new sewage disposal works until
such time as it had been completed effectively.  The Court of Appeal dismissed
the appeal by the Wellingborough U.D.C. against this injunction and also
decided that it was not excusable for the local council to pour effluent from
its uncompleted works Into the river.

legislation, *Regulations, *Local governments, *Judicial decisions,
Jurisdiction, Treatment facilities, Sewage disposal

England
330J

PROGRAM WILL CONTROL POLLUTION FROM WATERCRAFT,

Beszedits, S., and Netzer, A.

Canada Centre for Inland Waters, Water and Wastewater
Treatment Research Subdivision, Burlington, Canada

Water and Pollution Control, Vol. 112, No. 6, p 33-34, 36, June, 1974.

Pollution from watercraft is particularly acute and noticeable in Canadian
inland waters around busy harbors, and in crowded marinas.  Although con-
siderable efforts have been directed towards curbing such discharges, most
vessels still continue to dump their wastes overboard without treatment.
Lack of vigorous legislation and lax enforcement of existing regulations are
primarily to blame for such conditions.  On-board techniques for controlling
pollutant discharges are discussed and manufacturers of marine pollution con-
trol equipment given.

*Boats, *Water pollution sources, Waste discharge, Water pollution control,
Treatment facilities, Equipment, Regulation, Canada
                                       341

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  331J

WATER POLLUTION ASPECTS OF STREET CONTAMINANTS,

Jacobson, A. R.

Illinois State University, College of Applied Science
and Technology

Public Works, Vol. 105, No. 7, p 84, July, 1974.

Pollutant characteristics of street surface contaminants have been investi-
gated with the following recommendations being made based on the findings.
Equipment operators should be trained in how to operate their equipment most
efficiently and in knowing what material needs to be removed and where it is
most commonly located.  Increased effort should be expended on street clean-
ing operations, in maintaining records, in maintaining pavements, and in the
selection of material for paving purposes.  Other guidelines for the opera-
tion and maintenance of streets are indicated and research areas for future
investigation are presented.

*Roads, *Paving, *Cleaning, Water pollution sources, Operation and
maintenance, Investigations, Personnel, Training
332J

THE KINETICS OF INORGANIC CARBON-LIMITED ALGAL GROWTH,

King, D.  L., and Novak,  J.  T.

Missouri University, Columbia, Missouri

Journal of the Water Pollution Control Federation, Vol. 46, No. 7,
p 1812-1816, July, 1974.  5 fig, 5 ref.

In a discussion of a previously presented paper, it is indicated through
recalculation and recasting of the presented data that Selenastrum capri-
cornutum and Scenedesmus quadricauda, two green algae, both respond in a
kinetic fashion to the free carbon dioxide concentration of a water for
their photosynthetic carbon source.  Also their specific growth rate is not
related directly to the total inorganic carbon content of the water as was
suggested by the author.

*Chlorophyta, Carbon dioxide,  Photosynthesis, Carbon cycle, Growth rates,
Water analysis, Data collections
                                         842

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 333J

 THE INSTITUTE AND  EUROPE,

 Simpson,  J. R.

 D. Balfour and  Sons

 Water  Pollution Control, Vol.  73, No.  3, p  295-306,  1974.

 Objectives of the  Institute  of the Water Pollution Control  of  the  United
 Kingdom are presented  in relation to  its influence on national and inter-
 national  attitudes and policies.  The  Institute's position  in  the
 European  Economic  Community  also is discussed.

 *Europe,  *Water pollution control, International commissions,  Project
 planning

 Great  Britain,  European Economic Community
334J

THE EUROPEAN SCENE,

Malz, F.

Emschergenossenschaft and Lippeverband, Department
of Chemistry, Essen, Germany

Water Pollution Control, Vol. 73, No. 3, p 289-294, 1974.  2 tab.

A description of sewage treatment facilities in Switzerland, Holland, Sweden,
and Western Germany is presented.  The trend of improvement of their technical
activities in the control of water pollution is examined.  Various water asso-
ciations are mentioned as well as treatment practices for industrial wastes
and water quality monitoring.

*Europe, *Sewage treatment, *Treatment facilities, Industrial wastes,
Monitoring, Water quality control, Organizations
                                         843

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 335J

 RESEARCH AND DEVELOPMENT,

 Downing,  A.  L.,  and  Price,  D.  H.  A.

 Water Pollution  Research Laboratory

 Water Pollution  Control, Vol.  73,  No.  3,  p  277-288,  1974.   3 ref.

 The  types of research and  development  activity in the  environmental field
 that are likely  to develop  under  the European Economic Community  auspices
 are  indicated.   A background of information about the  role of relevant
 community Institutions,  their  policy in regard to environmental problems,
 and  their interactions with other international bodies sponsoring research
 in this  sphere are presented.

 *Research and development,  Europe, Project  planning, Water pollution control,
 International commissions

 European Economic Community
336J

MCA ENDORSES WASTE DISPOSAL PROVISIONS,

Chemical and Engineering, Vol. 52, No. 30, p 5, July 29, 1974.

Legislation dealing with the safe disposal of solid wastes has received
endorsement by the Manufacturing Chemists Association (MCA).  Next to toxic
substances control legislation, legislative proposals for extending the
solid waste act and strict management of hazardous solid wastes rank
highest of environmental legislative concerns.  Defining product compositions
based upon either wastes produced in their manufacture or resource recovery
potential is of great importance to the MCA.

legislation, *Solid wastes, *Waste disposal, Industrial wastes

*Manufacturing Chemists Association
                                           844

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337J

ADVANCED SEWAGE TREATMENT PILOT PLANT FOR
DAVYHULME,

Sane, M.

W. S. Atkins and Partners, Process and Production
Engineering Department

Water and Waste Treatment, Vol. 17, No. 5, p 18-20, May, 1974.  1 fig,
2 tab, 1 ref.

The aims of the Davyhulme, England, pilot plant; the equipment to be installed;
and the various treatment processes available for investigation using the
equipment provided are outlined.  The pilot plant, designed primarily for
manual control, should abstract up to 96,000 gpd of raw screened and mace-
rated sewage from below the intake works, abstracting at either fixed rates
of flow from 500 to 4000 gph or in accordance with a prearranged program
representing a diurnal variation of flow.  All process vessels incorporated
in the plant will be fabricated in steel, suitably protected, to facilitate
dismantling and re-erection on alternative sites.

*Pilot plants, *Equipment, treatment facilities, Construction materials,
Investigations, Sewage treatment, Flow rates, Instrumentation, Monitoring,
Sludge treatment

England
 338J

 LITIGATION UNDER PL 92-500:  A STATUS REPORT,

 Rawls, W. L.

 Journal of the Water Pollution Control Federation, Vol. 46, No.  7,
 p 1646-1648, July, 1974.

 A corresponding surge in litigation has been witnessed in the second year
 following the 1972 amendments to the Federal Water Pollution Control Act.
 Grievances of the plaintiffs, including states, municipalities,  environmental-
 ists, and industries, have all centered on the issue of administrative
 flexibility and discretion under the law.  States have confined  their liti-
 gation to funding and permits for federal facilities.  Setbacks  and victories
 of the environmentalists with regards to the 1972 amendment are  mentioned
 stressing the importance of the legality of EPA's variance clause for
 its Section 304 guidelines and its permit regulation exempting certain classes
 of agricultural point sources and silvacultureal and storm sewer point
 sources.  There have been isolated challenges to individual industrial per-
 mits but the consent decrees negotiated have added nothing in the way of
 importance to case law.  Although no legal briefs have been filed concerning
 effluent guidelines, preliminary motions broadly outline the position indus-
 try will assume.

 *Legal aspects, *Federal Water Pollution Control Act, Administration,
 Environmental control, Municipalities, Industries, State governments

 Environmental Protection Agency
                                         845

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 339J

 MEETING THE NPDES PERMIT DEADLINE:  DOES CLOSE ONLY
 COUNT  IN HORSESHOES?,

 Sliter, J. T.

 Journal of the Water Pollution Control Federation, Vol. 46, No. 7,
 p  1649-1650, July, 1974.

 With nearly 45,000 applications now on file, it will be impossible  for the
 Environmental Protection Agency and/or the  15 states administering  their own
 programs to issue the National Pollution Discharge Elimination System (NPDES)
 permits to all discharges by the required congressionally-imposed deadline
 date of December 31, 1974.  EPA announced that the agency hopes to  issue
 permits to all major dischargers and to a substantial number of minor ones
 by the end of the calender year.  EPA has called for legislative relief from
 this and other impending deadlines with a change in the permit deadline to
 July 1, 1974.  It is thought that the focus of attention regarding  permits
 may shift from attempts to obtain them to the issue of enforcing them by
 January 1975.  Methods of enforcement for noncompliance include jail sen-
 tences for company officials as well as enforcement orders and civil actions
 in district courts.

 legislation, *Discharge (Water), *Permits, Legal aspects, Federal
 government

 *Environmental Protection Agency, Enforcement
340J

ESTIMATION OF WASHLOAD PRODUCED ON CERTAIN
SMALL WATERSHEDS,

Rendon-Herrero, 0.

K'ew York State University, Department of Civil Engineering,
Buffalo, New York

Journal of the Hydraulics Division, ASCE, Vol. 100, No. HY 7,
p 835-848, July, 1974.  10 fig, 1 tab, 9 ref.

A series graph method, applicable to certain small watersheds is pre-
sented which can enable the estimation of sediment discharge on a storm
basis, depending on the amount of effective precipitation.  The method
has been applied to the Bixler Run Watershed near Loysville, Pennsylvania
which has a sediment transport of predominantly washload.  Such a method
is used where the quantitative analysis washload is necessary for the esti-
mation of total sediment discharge from a storm or its variation with time,
or both, a particularly important consideration when allocating storage
volumes in new resevoirs.  Two important findings disclosed from this study
are that: a relationship exists between excess runoff and the washload that
is mobilized by it over the watershed area; and, the series graph method can
be used as a method to predict washload and its variations with time.

*Sediment discharge, ^Suspended load, *Watersheds(Basins), Precipitation,
Storm runoff, Estimating equations, Pennsylvania, Time, Sediment transport
                                        846

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341J

EXPANSION SPARKS NEW DESIGN,

Malcolm Pirnie, Inc., White Plains, New York

Water and Wastes Engineering, Vol. 11, No. 7, p 38-42, July, 1974.  7 fig, 5 tab.

The operation and tests necessary in designing the Sturgeon Point Water
Treatment Plant in Erie County, New York are described.  The data ob-
tained from the six-month study program were analyzed and evaluated to
determine the performance of the proposed basin/filter system compared
to the control system.  The performance evaluation of the two systems was
based on removals of turbidity and total microscopic count and on the in-
crease or decrease in aluminum ion concentration in settled and filtered
water through each system.  Investigative results and subsequent conclusions
are presented.

*Performance, *0perations, *Treatment facilities, Evaluation, Testing,
New York, Water treatment, Turbidity, Filters, Head loss, Design criteria

Aluminum ion concentration, Total microscopic count
342J

COMPOSITION OF FREE LIPIDS IN SEDIMENTS OF THE TROPICAL WEST
PACIFIC AND SOUTH ATLANTIC (sostav svobodkykh
lipidov donnykh osadkov zapadnoy tropicheskoy chasti tik-
hogo i yuznoy chasti atlanticheskoy okeanov),

Belyayeva, A. N.

Okeanologiya, Vol. 14, No. 1, p 77-81, 1974.  1 tab, 10 ref.

The composition of free lipids in the upper layers of low-siliceous
diatomaceous ooze of the South Atlantic and calcarous foramlniferal,
coral sediments and red clay of the tropical West Pacific was studied
by a thin-layer chromatographic method, using methanol and a 2 : 1
ratio of chloroform methanol for extraction, and mixtures of hexane,
ether and methanol for elution.  The total free lipid content of these
sediments was determined to range from 0.014 to 0.057 percent of dry
sediment, the concentration being inversely related to the total amount
of organic carbon content.  Lipids of low polarity made up of 44.28-85.95
percent of the total lipid content, and they were dominated by hydro-
carbons and fatty acids with contents of 8,57-29.97 percent and 2.12-
9.15 percent, while tropical deepwater sediments contained no triglycer-
ides.  The concentration of sterols, more resistant to microbial degrada-
tion than fatty acids and triglycerides, was in a range of 3.57-9.90 per-
cent in the lipids.  The relative contents in the total lipids of com-
pounds of low polarity, and especially of hydrocarbons, fatty acids and
sterols can be indicative to the degree of transformation of organic
matter of the sediment since these compounds posses different stability
against microbial and hydrolytic decomposition in redox processes.

*Analytical techniques, *Chromatography, Lipids, Hydrocarbons,
Organic matter, Decomposition, Sediments

South Atlantic, Free lipids
                                   847

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34 3 J

MICROBIOLOGY: DETECTION, OCCURENCE, AND REMOVAL OF
VIRUSES,

Berg, G.

National Environmental Research Center,
Cincinnati, Ohio

Journal of the Water Pollution Control Federation, Vol.  46,  No.  6,
p 1408-1413, June, 1974.  35 ref.

The virus concentrator lends itself to monitoring water reclamation plants
for the determination of their efficiency in the inactivation and removal
of viruses.  Acidification of clean water which passes through the con-
centrator permits efficient adsorption of viruses onto epoxy-fiberglass
and nitrocelulose filters.  HC1 acidifies the water before passing through
a virus adsorber.  Adsorbed viruses are eluted with one liter of pH 11.5
elutant,  then reconcentrated by adsorption to and elution from an epoxy-
fiberglass filter.  Small amounts of poliovlrus I in 100 gallons of tap
water were concentrated almost 40,000 fold.  A 77 percent virus recovery
efficiency was reached.  Filtration of virus-seeded water through asbestos
filters filled with sodium alginate and subsequent concentration of the
virus onto La-Al-alginate soluble ultra-filters achieved a total recovery
of the virus.  Well water, waste water, and rivers and lakes, as well as
vegetables grown on virus-laden soil were the sites of recovery.  Virus may
also be removed from waste water by biological and chemico-physical treat-
ment methods.

*Microbiology, *Viruses, *Water pollution, Waste water treatment, Adsorption,
Biological treatment

Epoxy-fiberglass filters, Nitrocelulose filters, Physico-chemical treatment
   344J

   THE LAW AND  THE  DESIGNER,

   Gegauff,  R.

   The Occupational Safety  and Health Administration
   and the Environmental Protection Agency

   Design  News, Vol.  28, No.  22, p 45-54, November, 1973.

   The regulations  established by the EPA and OSHA are inspired by the voters '
   demands for  reduced  costs, the salvaging of materials by reuse or careful
   layout, and  the  consumer demands.  Old products are being adapted to meet
   the new standards, with new products filling newer needs.  The OSHA gathered
   its original standards from the American National Standards Institute, and
   a  problem of interpretation ensued.  Standards were revised in more defini-
   tive  terms,  and  the  Compressed Gas Association was also consulted-for further
   standard gathering.  Also  adopted were the National Fire Protection Associ-
   ation standards.  Now, however, the OSHA and EPA determine their own priori-
   ties, employ independent labs, and contract industries to perform studies.
   With  the collapse of the National Industrial Pollution Control Council, the
   OSHA  and EPA are the remaining mediators between industry and government.
   The concerns of  these agencies include plant safety, air pollution, auto-
   mobiles in terms of their  contribution to the pollution of the environment,
  water pollution, laundry waste, water reuse, recycling and consumer safety.

   *Water  pollution, *Air pollution, *Recycling, Industrial pollution

   *Environmental Protection  Agency, *The Occupational Safety and Health
  Administration
                                      848

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345J

MARINE AND ESTUARINE POLLUTION,

Reish, D. J., and Kauwling, I. J.

Department of Biology, California State
University, Long Beach, California

Journal of the Water Pollution Control Federation, Vol. 46, No. 6,
p 1437-1451, June, 1974.  151 ref.

A study of marine pollution was made by Aubert and Aubert, emphasizing
the sources of contamination, the techniques for measuring the extent
of pollution, and its prevention.  Waste disposal, oil spills, radio-
activity, heat and pesticides were considered in terms of their effect
on marine organisms.  Possible solutions to these problems were pre-
sented, being summaries of previous experiments dealing with the Col-
umbia River Estuary, Southern California Bight, Chesapeake Bay, and Port
Philip Bay, Australia.  Chemical and physical characteristics of water
and sediment and the planktonic and benthic biota are included.

*Water pollution, *Estuaries, *Aquatic environments, Waste disposal,
Oil spills, Radioactivity, Pesticides, Plankton, Benthos

*Marine organisms
   346J

   AQUATIC SEDIMENTS,

   Ku, W. C., and Foess, G. W.

   University of Massachusetts, Anherst,
   Massachusetts.

   Journal of the Water Pollution Control Federation, Vol. 46, No. 6,
   p 1420-1437, June, 1974.  66 ref.

   Various chemical transformations occurring in sediments, and their effects
   on the quality of overlying water was the basis of most of the literature
   of 1973.   Examples from the United States were studied to determine the ef-
   fect of sediment on water quality.  Also discussed were sediment-water rela-
   tionships and their influence of water usage, fish and wildlife habitat,
   public water supply,  agricultural and industrial use and the disposal of
   waste water.   Other investigators examined the release of heavy metals and
   inorganic constituents from sediments.  It was determined that nitrilori-
   acetic acids could release heavy metal ions from their complexes with humic
   compounds in sediments.   Further data obtained that the amount of copper re-
   leased from sediments decreased with the increase of the NTA.   Further
   studies on the interaction of sediment and water are mentioned.

   *Sediment, *Water quality, *Water pollution,  Fish, Wildlife, Water supply,
   Agriculture,  Industry,  Waste water disposal,  Copper, Heavy metals
                                       849

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34 7 J

MOLYBDENUM AND FISH,

Industrial Water Engineering, Vol. 11, No. 3, p 6, May/June, 1974.

Results of extensive tests to determine the effects of water-soluble
molybdenum on several varieties of fish have been announced.  The fish
species tested were bluegill, rainbow trout, fathead minnows, and chan-
nel catfish.  The amount of active ingredient toxic to 50 percent of
the specimens for all species ranged from 6500 to greater than 10,000
ppm,  the highest concentration tested.  The level at which no adverse
symptons were observed varied from 2400 ppm for bluegill to 7500 ppm for
channel catfish.

*Molybdenum, ^Laboratory tests, *Sunfishes, *Rainbow trout, *Channel
catfish, *Toxicity

*Fathead minnows
 348J

 BRITAIN'S PROMPT ACTION AGAINST MARINE POLLUTION,

 Shipbuilding  and Marine Engineering  International, Vol. 97, No.  1177,
 p  255,  257, May, 1974

 The British House  of Commons  gave  an unopposed  Second Reading  to the
 Government's  Dumping at Sea Bill which prohibits  the dumping in  tidal
 waters  and the  sea of  any substances loaded in  a  British port  or within
 British waters  on  to a ship,  aircraft, or marine  station.  Controlled
 dumping will  be subject to a  licensing procedure  and an inspectorate is
 to be set up  with  powers  to examine  all ships and marine installations
 and to  take samples and documents.   The Convention for control will come
 into force 12 months after the date  on which not  less than 15  nations
 have become signatories.  A survey of available equipment which  can be
 carried on board and is suitable for complying with the spirit of  the
 Convention on Marine Pollution has been appended  to include the  manu-
 facturers of  specific  shipbome equipment.

 *Water  pollution control, *Ships,  Waste disposal, Waste treatment,
 Sea water, International waters, International  commisions

 United  Kingdom
                                       850

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   349J

   SHALL WE DEVELOP MOM: WATER?,

   Bacon, V. W.

   Wisconsin University, Department of Civil
   Engineering, Milwaukee, Wisconsin

   Water and Sewage Works, Vol. 121, No. 6, p 46-47, June, 1974.  1 tab.

   Guidelines for effective water philosophy to aid water development
   and management are presented.  Water quantity, water conservation
   through quality control and the economics of waste water treatment
   are stressed.

   *Water resources development, *Water management(applied), Water
   quality control, Waste water treatment, Economics, Water conservation
350J

MICROBIAL FOULING OF THE PIPES OF WATER COOLERS UPON
THE APPLICATION OF POLLUTED CANAL WATER,

Voets, J. P., Vansteeri, H., and Verstraete, W.

Faculteit van de Landbouwwetenschappen, Department of
General and Industrial Microbiology, Rijksuniversiteit
Gent, Belgium

Materials and Organisms, Vol. 9, No. 1, p 1-12, 1974.  6 fig, 1 tab, 12 ref.

The microbial phenomena governing the fouling of industrial once-through
water coolers has been studied.  The fouling processes were initiated by
the attachment to the walls of the cooler pipes of a film of zoogloeal and
filamentous organisms.  Upon this initial colonization phase follows a
logarithmic secondary colonization phase characterized by the accumula-
tion of a wide variety of Chlorophyta, Cyanophyta, Bacillarlophyta, and
Protozoa.  Practical methods which inhibit on a long term basis these
fouling processes are not available, but alternative shock treatment of
the cooling water with biocides retard these processes considerably.

*Fouling, Microbiology, Industrial plants, Aquatic microorganisms,
Chlorophyta, Cyanophyta, Aerobic bacteria, Protozoa, Investigations,
Cooling water

*Water coolers, Colonization, Biocides
                                       351

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351J

LEGAL ASPECTS OF THERMAL DISCHARGES,

Martin, A. J.

Power Authority of State of New York,
New York City, New York

Journal of the Hydraulics Division, Vol. 100, No. HY 7, p 1059-1072,
July, 1974.  34 ref.

An overview of those legal areas which directly affect technical and
planning decisions is presented in the form of two legal approaches
which constrain the indiscriminate release of thermal discharges to
receiving waters.  One takes the form of private remedies which have
traditionally been available to aggrieved parties who are in some way
damaged by the harmful discharge.  The second approach utilizes
the various statutory constraints leading to direct governmental ac-
tion.  It appears that statutory law is playing the prominent role in
restricting the temperature to which receiving waters may be raised as
a result of such discharges by using effluent limitations and water
quality standards.

*Legal aspects, *Reviews, Design criteria, Thermal pollution, Federal
government, Legislation

*Thermal discharges
 352J

 1971  ANNUAL REVIEW OF LITERATURE.  WASTE WATER TREATMENT
 PHYSICAL AND CHEMICAL METHODS,

 Cohen,  J.  M.,  and Kugelman,  I.  J.

 National Environmental Research Center, Environmental
 Protection Agency,  Cincinnati,  Ohio,  Physical-Chemical
 Treatment Research Program

 National Technical Information  Service Report  PB-213 826,  1972.
 22  p,  90 ref.

 A review of the  literature of 1971 shows an  increasing  interest  in  using
 physical-chemical methods  as practical alternatives in  conventional bio-
 logical methods.   New views  on  the topics  of water reclamation,  phosphorus
 removal, nitrogen removal, adsorption, coagulation-flocculation-sedimenta-
 tion,  filtration,  and demineralization, are  discussed with specific reference
 to  articles dealing with these  subjects.

 *Waste  water treatment, *Reviews, Water clarification,  Filtration,  Phosphorus,
 Nirtogen,  Flocculation, Sedimentation, Coagulation, Adsorption,  Deminerali-
 zation, Chemical control,  Physical control,  Water reclamation

 Physical-Chemical treatment, Phosphorus removal, Nitrogen removal
                                         852

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353J

SCI AMSTERDAM CONFERENCE,

Effluent and Water Treatment Journal, Vol. 14, No. 6, p 337-339, June, 1974.

The Society of Chemical Industry arranged a three day International Conference
on Industrial Waste Water Treatment and Disposal in July, 1974.  Twenty-one
papers were delivered concerning the legislation, economics and practical as-
pects of pollution.  The following points were raised:  proper monitoring
of the environment must be shared by the international organizations and in-
dustry; one method of pollution control is to levy charges on discharges;
a tax on discharges should be based on the oxygen consumption of the dis-
charge; the discharger should be charged for additional treatment neces-
sary so that the discharges will be fit for use in the public supply; an
indirect method of pollution control is to levy duties and then distribute the
collected money to producers of waste waters who want to build their own treat-
ment facilities; it is not the polluter who pays for the treatment but
rather the customers of the polluter; the true (avoidable) costs of con-
trolling pollution are lower than the apparent costs of pollution control; and
there is a need for more and better data on the economics of pollution control.
The most significant points were for the use of the ability of a natural water
course to recover from pollution, closer cooperation with the people respon-
sible for the quality of the water and a better appreciation of the recovery
of raw materials.  The conference concluded with the suggested principle that
"The Polluter must save Water, Materials and Money".

*Water pollution, *Waste water treatment, *Water pollution control, Legisla-
tion, Industries, Law, Law enforcement, Pollution charges, Economics, Costs,
Social aspects, Organic wastes, Industrial wastes

International Conference on Industrial Waste Water Treatment and Disposal
354J

INTERRELATIONS BETWEEN SULFATE-REDUCING AND METHANE-
PRODUCING BACTERIA IN BOTTOM DEPOSITS OF A FRESH-WATER
LAKE.  II.  INHIBITION EXPERIMENTS,

Cappenberg, T.

Limnological Institute "Vijverhof",
Nieuwersluis, the Netherlands

Antonie van Leeuwenhoek, Vol. 40, No. 2, p 297-306, 1974.  3 fig, 1 tab,
21 ref.

A possible substrate interrelationship between methane-producing and sulfate-
reducing bacteria has been studied in bottom deposits of Lake Vechten.  The
inhibition of methanogenesis in mud samples by chlorine-containing analogues
of methane resulted in an accumulation of acetate.  Fluoroacetate reduced the
concentration of methane by about 75 percent.  If carbon tetrachloride was
used, an accumulation of hydrogen gas was observed.  These results indicate
that acetate is the main precursor of methanogenesis in mud.  After addition
of beta-fluorolactate, lactate accumulated and H2S was no longer produced, which
indicates that lactate is the main source of energy for sulfate reduction in
mud.  Simultaneously, the concentration of methane increased.  This may be due
to the lower concentration of H2S, which has a toxic effect on methanogenesis.
Experiments with intact mud cores have provided evidence that the described
phenomena occur also in nature.

*Bacteria, *Methane bacteria, *Sulfate-reducing bacteria, Freshwater bacteria,
Aquatic bacteria, Inhibition, Methane, Water pollution sources, Water pollution

*Acetate, inhibition experiments, Lake Vechten, the. Netherlands, MeXhano genes Is,
Lactate
                                    853

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355J

INTERRELATIONS BETWEEN SULFATE-REDUCING AND METHANE-
PRODUCING BACTERIA IN BOTTOM DEPOSITS OF A FRESH-WATER
LAKE. I.  FIELD OBSERVATIONS,

Cappeuberg, T.

Llmnological Institute "Vijverhof", Nleuwersluis,
the Netherlands

Antonie van Leeuwenhoek, Vol. 40, No. 2, p 285-295, 1974.  3 fig, 2 tab, 28 ref.

Observations on the seasonal periodicity in the bottom deposits of Lake Vechten
indicate than an ecological relationship exists between the methane-producing
and the sulfate-reducing bacteria.  The sulfate-reducing bacteria are most
abundant at depths of 0 to 2 cm in the mud at hydrogen sulflde potential values
around 11 and redox potential values between 100 and 150 mV.  The methane-pro-
ducing bacteria are most abundant at depths of 3 to 6 cm and at hydrogen sulfide
potential values around 14 and redox potential values between 250 and 300 mV.
It was observed that during the summer stratification, the numbers of both
groups of bacteria rose but that the methane-producers increased much more than
the sulfate-reducers.  The abundance of the sulfate-reducers is. limited by the
sulfate concentration in the interstitial water of the mud.  Methane-producers
are at greater depths in the mud than the sulfate-reducers and the concentra-
tion of hydrogen sulphide is less.  It is concluded that the different locations
of the bacterial groups may be due to sensitivity of the. methane-producers to
hydrogen sulphide.

*Bacteria, *Methane bacteria, *Sulfate-reducing bacteria, Freshwater bacteria,
Aquatic bacteria, Water pollution sources, Water pollution, Sand pits, Methane,
Redox potential

*Acetate, *Seepage, Lake Vechten, the Netherlands
356J

TORULOPSIS AUSTROMATINA SP. NOV. A YEAST ISOLATED FROM
THE ANTARTIC OCEAN,

Fell, J., and Hunter, I.

Miami University, Miami, Florida, Rosenstiel
School of Marine and Atmospheric Science

Antonie van Leeuwenhoek, Vol. 40, No. 2, p 307-310, 1974.  8 ref.

A new species of yeast, Torulopsis austromarina, has been found in the
oceanic waters of the Indo-Pacific and Indian Ocean parts of the Antartic.
T. austromarina is related to T. inconspicua but T. inconspicua can not
assimilate galactose, trehalose, inulin or soluble starch and has a higher
maximum temperature.

*Yeasts, *Antarctic, Water pollution sources, Water pollution, Pollutants,
Water quality

*Troulopsis austromarina, New species
                                     854

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357J

 GROWTH STIMULATION AND BIOCHEMICAL CHANGES IN
JUVENILE COHO SALMON  (ONCORHYNCHUS KISUTCH) EXPOSED TO
BLEACHED KRAFT PULPMILL EFFLUENT FOR 200 DAYS,

McLeay, D., and Brown, D.

British Columbia Research, Vancouver, British
Columbia, Division of Applied Biology

Journal of the Fisheries Research Board of Canada, Vol. 31, No. 6, p 1043-
1047, June, 1974.  1  fig, 3 tab, 36 ref.

Large quantities of kraft pulpmill wastes are discharged in the estuarine and
fresh waters of Canada.  This article deals with what effects long-term ex-
posure to sub-lethal  concentrations of this waste may have on juvenile coho
salmon.  The fish were exposed to for 200 days to neutralized, filtered bleached
kraft mill effluent (BKME) at concentrations that were 0.1 and 0.25 of the.
samples' 96-h LC50 values.  There was growth- stimulation: the length, weight,
and condition factor of the fish, in the 0.25 concentration of the 96-h. LC5Q
were significantly greater than that of the controls; the growth of the fish.
in the 0.1 concentration of the 96-h LC50 was consistently not significantly
greater than that of  the controls.  The mechanism of growth stimulation was
not determined.  Biochemical changes also resulted from the exposure to bleached
kraft mill effluent: lactate acid levels were elevated in the blood and muscle
of the fish in the .25 LC50 concentration; serum pyruvate levels were decreased
in both experimental groups; plasma glucose levels were elevated in both experi-
mental groups; the liver: muscle ratio was increased in fish in both concentra-
tions; body protein content decreased in fish in the higher concentration; num-
bers of circulating neutrophiles were higher in the fish in the 0.25 LC50 con-
centration.  The salmon displayed a chronic stress response pattern similar to
a previously proposed stage of resistance to stress for mammals.

*Salmon, *Lethal limit, *Water pollution effects, *Kraft mill wastes, Water
pollution sources, Industrial wastes, Canada,  Water pollution., Pulp and paper
Industry, Pulp wastes, Animal growth, Fish, Fish physiology

*Coho salmon,  *Junenile coho salmon, LC5Q, Growth, stimulation, Biochemical
changes
 358J

 OLFACTORY RESPONSE AND FENITROTHION TOXICITY IN AMERICAN
 LOBSTERS  (HOMARUS AMERICANUS),

 McLeese,  D.

 Department of the Environment,  Fisheries and Marine
 Service,  Biological Station,  Saint Andrews,  New Bruns-
 wick,  Canada

 Journal of the Fisheries  Research Board of Canada,  Vol.  31,  No.  6,  p 1127-1131,
 1974.  2  fig,  3 tab,  13 ref.

 Fenitrothion,  an organic  pesticide,  has been used in New Brunswick  for spruce
 budworm control.   The authors determined that at low concentrations of feni-
 trothion  the olfactory response of American lobsters to  cod  muscle  extract is
 not  hampered.   In test runways  the olfactory response to cod muscle extract is
 not  affected by simultaneous  presentation of fenitrothoin at measured concentra-
 tions  ranging from 0.05 to  25.4 ppb.   For both adult and larval  lobsters the
 96-hr  LC50 is  about 1 ppb.  The lethal threshold for larvae  is about 0.015 ppb
 and  the lethal threshold  for  adults  is about 0.3 ppb or  lower.

 *Water pollution,  *Pesticide  toxicity,  *0rganic pesticides,  *Lobsters,
 Pesticides,  Environmental effects, Animal behavior,  Animal physiology,
 Physiological  ecology,  Canada

 *Hommarus  americanus,  *American lobster,  *LC50,  *Fenitrothion, Organophosphate
 insecticides,  New Brunswick
                                         855

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 359J

 THE EFFECTS OF MERCURIC CHLORIDE UPON RESPIRATION IN
 CONGERIA LEUCOPHAETA,

 Dorn, P.

 Texas A and M University, College Station,
 Texas, Biology Department

 Bulletin of Environmental Contamination and Toxicology, Vol. 12, No. 1,
 p 86-91, July, 1974.  2 fig, 2 tab, 10 ref.

 Mercury in the marine environment can alter the normal life functions of
 the aquatic fauna.  Respiration is one function that can be affected by
 mercury.  The respiration rates of the bivalve, Congeria leicophaeata were
 measured in sublethal concentrations of mercuric chloride.  It was determined
 that solutions containing 1.0, 0.1, 0.01, and 0.001 ppm mercury as mercuric
 chloride were sublethal for 48 hours of exposure.  The respiration rate of C.
 leucophaeata rose with increasing mercury concentration.  The results were
 statistically significant above 0.01 ppm.

 *Mercury, *Respiration, Water pollution, Water pollution sources,
 Statistical methods

 *Congeria leucophaeta, *Mercury pollution, *Respiration rates,
 Calves ton, Texas
360J

WATER POLLUTION PROBLEMS IN THE REPUBLIC OF SINGAPORE,

Kershaw, M.

Effluent and Water Treatment Journal, Vol. 14, No. 6, p 301-308,
June, 1974.  2 fig, 1 tab, 6 ref.

A booming economy, growing population, large scale housing and commercial
development, and rapid industrial growth have all contributed to Singapore's
problems with water supply, main drainage, sewage treatment, industrial
growth, and water pollution problems in general.  The government of Singa-
pore has formulated regulations concerning domestic sewage and trade effluents.
In 1972, a Ministry of the Environment was created to deal with pollution con-
trol and environmental health.  The measures adopted to control pollution
(water, air, noise, or solid waste) are enforcement, education, and equipment
(provision of essential services).  A division of the Singapore Institute of
Standards and Industrial Research provides the expert advice to manufacturers
as to how to treat trade effluents.

*Water supply, *Drainage, *Water policy, *Water pollution, *Governments,
Reservoirs, Surface runoff, Surface water availability, Water supply develop-
ment, Drainage area, Drainage systems, Sewerage, Sewage treatment, Industrial
wastes, Industrial water, Water pollution control, Foreign countries, Insti-
tutions, Legislation, Regulation

*Water control regulations, *Republic of Singapore, Catchment areas, Open
"monsoon" drains, Open canals
                                         856

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361J

FLUORIDE CONCENTRATIONS IN TWO PACIFIC COAST INLETS-
AN INDICATION OF INDUSTRIAL CONTAMINATION,

Harbo, R., McComas, F., and Thompson, J.

Department of the Environment, Fisheries and Marine
Service Pacific Environment Institute, West Vancouver,
British Columbia, Canada

Journal of the Fisheries Research Board of Canada, Vol. 31, No. 6, p 1151-
1154, 1974.  2 fig, 2 tab, 9 ref.

This study was undertaken to better understand the effects of anthropogenic
fluoride upon estuaine and marine ecosystems.  A comparison of Kitimat Arm,
where fluoride wastes have been discharged for nearly twenty years, and of
Howe Sound, British Columbia, where there is not known to be any input of
non-natural fluoride, indicated that there is some contamination.  A statis-
tical treatment of the data further serves to demonstrate this conclusion.

*Water pollution, *Fluorides, Analytical techniques, Chemical analysis,
Water sampling, Sampling, Statistical methods,  Statistics, Water analysis,
Connate water, Industrial wastes, Chemical wastes, Water pollution sources

*Anthropogenic fluoride, *Aluminum smelting wastes, Kitimat River estuary,
Canada, Howe Sound, British Columbia
362J

EUTROPHICATION,

Foehrenbach, J.

New York State Department of Environmental
Conservation, Stony Brook, New York

Journal of the Water Pollution Control Federation, Vol. 46, No. 6, p 1350-
1355, June, 1974.  38 ref.

Inorganic compounds of nitrogen and phosphorus are generally the factors
measured when determining the causes of excessive algae growths.  It is
suggested that caution be used when interpreting enrichment experiments.
While N03 and P043 stimulate the growth, alone or along with another agent,
ionic Si causes increased diatom growth, as well as Na+.  The productivity
of 43 lakes and 12 reservoirs from tropical latitudes to the Arctic Circle
were studied.  The amount of sunlight was discovered to be the governing
factor.  The bottom sediments of deep lakes were analyzed by Emery, who
determined that the sediments from depths greater than 10 m were structured,
and that those above 10 m exhibited mixing.  Nutrients, then, can be recycled
from shallow areas.  Austin and Lee measured the release of inorganic N from
sediments in Trout Lake and Lake Mendota, in Wisconsin.  In aerobic conditions,
0.09 and 0.04 mg/liter day were released from these, lakes, while under anae-
robic conditions, the values were under 0.01 mg/ltter day.

*Eutrophication, *Algae., *Sedimentation, *Lakes, Reservoirs., Nutrients,
Lake morphology,

Microcystis aeruginosa, Cladophora glomerata, Anabeana, Anacytis.,
Chlorella vulgaria, Ocytis marsonii, Prymnesium provum, Aphanizonenon,
Wolffa columbiana, Salvinia rotundefolia, Lemna minor
                                       857

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 363J

 ECONOMICS,

 James, L. D.

 Environmental Resources Center, Georgia Institute
 of Technology, Atlanta, Georgia

 Journal of the Water Pollution Control Federation, Vol. 46, No. 6, p 1611-
 1618, June, 1974.  77 ref.

 Two important government documents on water resources planning procedure
 were published in 1973.  New standards for federal water planning in the
 U. S. were released by the U. S. Water Resources Council.  The new approach
 is that enhancement of environmental quality is included with economic ef-
 ficiency as planning objectives, and measurement is made of both environ-
 mental and economic effects.  An increase in planning discount rate to 6.875
 percent and a new emphasis that benefits be paid for by the beneficiaries are
 radical changes from past practice.  A five year study by the National Water
 Commission was completed dealing with water management.  "Zero discharge"
 was rejected as a goal by the Commission, recommending that the cost of pol-
 lution be paid by those who produce it.  The evaluation of the causes of
 conflict between environmental quality and water resources for economic gain
 was discussed in an assemblage of 28 papers by Goldman for the National Water
 Commission.

 *Costs, *Water resources, *Water resource management, Water pollution,
 Reviews, Legislation, Planning

 The U. S. Water Resources Council, The National Water Commission
 364J

 EFFECTS OF POLLUTION ON FRESHWATER FISH,

 McKim, J. M., Christensen, G. M., Tucker, J. H.,
 Benoit, D. A., and Lewis, M. J.

 National Water Quality Laboratory,
 Duluth, Minnesota

 Journal of the Water Pollution Control Federation, Vol. 46, No. 6, p 1540-
 1590, June, 1974.  399 ref.

 Many books dealing with biological indicators, biochemical ecology, water
 quality, and management were published between 1972 and 1973.  One treatise
 contained articles on thermal pollution, monitoring, and enforcement.  Papers
 on various bioassay methods and water chemistry problems were compiled by
 Glass.  The American Society for Testing and Materials listed 140 new biolo-
 gical and chemical methods.  Instrumental analysis, automated chemical analy-
 sis, and data analysis was investigated.  Mercury contamination of the en-
 vironment dealing with occurrence, methods of analysis, environmental dyna-
 mics, and biological effects was studied by Hartung, Friberg and Vostal.  Oc-
 currence, dynamics, methods of minimizing persistent pesticides, and inter-
 national control of such pesticides was researched by Edwards.  The biolo-
 gical and environmental aspects of chlorinated insecticides, dealing with
 biochemistry and toxicity to nontarget organisms was explored by Brooks.  The
 effects of pesticides on aquatic environments was the subject of several re-
 views, including those of McCaull, Pimentel, Mawdesley-Thomas and Fraser.

 *Biochemistry, *Water pollution, *Fish, Thermal pollution, Monitoring,
 Bioassay, Mercury, Tritium, Aquatic environments, Pesticides, Water quality,
Methodology, Salinity, Herbicides, Industrial pollution, Piscicides, Pulp
wastes, Domestic pollution

 Enforcement, Organochloride pesticides, Organophosphates, Cholinesterase,
Alpha-Beta endosulfan
                                      358

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 365J

 MICROBIOLOGY-WATERBORNE OUTBREAKS,

 Craun, G. F.

 National Environmental Research  Center,  EPA,
 Cincinnati, Ohio

 Journal of  the Water Pollution Control Federation, Vol. 46, No.  6, p  1384-
 1395, June, 1974.   89 ref.

 A review was made by Craun and McCabe of  the  causes of waterborne-diseases
 occurring in the United States during the period of 1946  to 1970.  There
 were a recorded 358 outbreaks of diseases or  poisoning from contaminated
 drinking water.  Illnesses were  of  five  major categories:  gastroenteritis
 of  unknown  etiology (178 outbreaks), typhoid  (53 outbreaks), infectious
 (13 outbreaks).  Seventy-one percent of  the outbreaks resulted  from the con-
 tamination  of private, individual water  systems, while 83 percent of  the
 illness was a result of polluted community water systems.  The  distribution
 system of the community facilities  was found  to be the major cause through
 cross-connections and back siphonage.  Data indicates that waterhorne dis-
 eases are on the increase during the last three decades.   A slight increase
 in  mortalities has  occurred for  gastritis, duodenitis:, enteritis, and colitis
 in  persons  over 65, however, it  is  still  significantly lower than was ob-
 served in the 1920's.

 *Microbiology, *Water pollution, *Diseases, Chemical pollution

 Gastroenteritis, Typhoid, Hepatitis, Shigellosis, Salmonellosis, Amoebic
 meningoencephalitis, Naegleria fowleri,  Cholera, Dracontiasis,  Leptos.pl-
 rosis, Schistosomiasis, Shellfish poisoning
366J

CHEMICALS AND ALLIED PRODUCTS,

Macauley, Dennis C.

Union Carbide Corporation, South Charleston,
West Virginia

Journal of the Water Pollution Control Federation, Vol. 46, No. 6, p 1337-
1341, June, 1974.  36 ref.

The organic chemical industry has set up guidelines for the implementation
of the 1972 Federal Water Pollution Control Act, along with the synthetic
resins segment of the plastics and synthetics industry.  The degree to which
water can be made pollution-free by the best technology available which is
economically feasible was determined, with consideration to the estimated
cost.  Farrell examined water pollution in the nitrogen industry, including
nitrogenous chemicals used for chemical processing and nitrogenous fertilizer.

*Chemical industry, *Nitrogen, *Water pollution, Plastics, Adsorption,
Waste water treatment, Biological treatment, Recycling, Federal Water
Pollution Act

In-unit Control, Synthetic resins, Nitrogenous fertilizer
                                        859

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367J

MICROBIOLOGY-DETECTION OF BACTERIAL PATHOGENS AND
THEIR OCCURRENCE,

Reasoner, D. J.

National Environmental Research Center,
EPA, Cincinnati, Ohio

Journal of the Water Pollution Control Federation, Vol. 46, No. 6,
p 1395-1408, June, 1974.  19 ref.

Enteropathogenic Escherichia coli, which are the cause of gastrointestinal
illnesses, have been attributed to such bacteria as Salmonella.  EEC is
most serious in young animals and children.  Chlorination of water pre-
vented contamination of water that had led to the poisoning of laboratory
animals.  Ewin developed the three species concept to avoid confusion in
the study of Salmonella.  All Salmonella, excepting the S. cholera-suis
and S. typhi, are considered serotypes or biserotypes of S. enteritidis,
numbering 1,500 or more.  According to the U. S. Department of Agriculture,
the frequency of salmonellae isolations from different nonhuman source cate-
gories were: animal feeds (32.6 percent), domestic animals and their en-
vironment (26.7 percent), human food products; eggs, poultry, red meat, etc.
(14.5 percent), fish, reptiles and environment (10.1 percent), and wild ani-
mals and birds (4.4 percent).  It was determined that the salmonellae in
feed were not the salmonellae which produced salmonellosis in animals.

*Microbiology, *Salmonella, *Water pollution, *Disease

*Gastrointestinal disturbances, Enteropathogenic Escherichia coli
368J

POLLUTION EFFECTS ON SURFACE AND GROUND WATERS,

Young, R. H. F.

Hawaii University, Honolulu, Hawaii, Department
of Civil Engineering

Journal of the Water Pollution Control Federation, Vol. 46, No. 6,
p 1419-1429, June, 1974.  103 ref.

The causes of eutrophication were discussed.  Examined were the changes in
the Indian Creek Reservoir, receiving effluent discharge from the South
Lake Tahoe Public Utility District tertiary.  The reservoir appears to be
changing from a low diversity and high-production ecosystem to one of higher
diversity and lower productivity.  The effects of phosphorus discharge from
farming arid livestock on surface water in Britain are explored.  Also
studied were the discharges of septic tanks and cesspools which percolate
to groundwater.  A study of surface irrigation with dairy manure slurries
was made, noting the application of 100-tons dry matter/acre over a 24 month
period resulted in higher levels of fecal coliform, BOD, chloride, and TDS
in surface runoff from conventional pasture areas.  FWPCA standards were met
by percolate from slurry in infiltration downslope from the test pasture,
for raw surface water used for public consumption.  The use of livestock
manure as fertilizer for sorghum-sudan forage was investigated.  Nitrogen
and sodium were shown not to pollute surface runoff, while potassium levels
inhibited the use of runoff to irrigation only, and groundwater from the
field kept its potability.

*Potable water, *Surface water, *Groundwater, Runoff, Nutrients,
Eutrophication, Agriculture, Reservoirs, Waste water treatment, Effluent,
Fish, Livestock, Industrial pollution, Sludge treatment, Heavy metals,
Chemical pollution, Soil pollution, Biological pollution

*Radionuclide pollution

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   369J

   OXYGEN SAG AND STREAM PURIFICATION,

   Neal, L. A.

   Environmental Protection Division, Georgia
   Department of Natural Resources, Atlanta, Georgia

   Journal of the Water Pollution Control Federation, Vol. 46, No. 6,
   p 1413-1418, June, 1974.  56 ref.

   An extensive bibliography of U. S. and foreign literature on the aeration of
   natural waters was compiled.  A generalized model including the effects of
   photosynthesis and nitrification was developed.  Sornberger and Keshaven
   produced a stochastic DO simulation under constant and variable temperature
   conditions, comparing the range of probable DO concentrations against mean
   values from a determinitic model.  A stochastic DO model for streams and
   estuaries was developed fay Schofield and Krutchkoff and compared predicted
   values against data from the Ohio River and the Potomac estuary.  The method
   of moments, Reed-Theriault, Thomas slope, and log differences were estimating
   time series BOD data.  Bochinski investigated the merits of the TOD test in
   using non-biological techniques for estimating BOD, and presented correla-
   tions of TOD to COD and TOD to BOD.  The results of direct reaeration capa-
   city measurements, employing a radioactive tracer gas for oxygen, and associ-
   ated hydraulic properties in five rivers were presented by Wallace and Tsiva-
   glou.

   *Aeration, *0xygen sag, *Stream purification, Photosynthesis, Nitrifi-
   cation, Stochastic processes, Estuaries, Runoff, Reaeration, Biochemical
   oxygen demand

   Benthic deposits, Dissolved oxygen models
370J

CONCEPT DEVELOPMENT OF A FREE VORTEX OIL RECOVERY SYSTEM,

Nebeker, E. B. and Rodriguez, S. E.

Scientific Associates, Incorporated, Santa Monica,
California

National Technical Information Service Report AD-777-024, May, 1973.
180 p, 38 fig, 7 tab, 24 ref, 6 append.

A Free Vortex has been developed for use in recovering oil spilled under
high sea conditions.  Free Vortex skimming is applicable under these
conditions:  oil films one inch thick or less, operation while stationary
and in currents up to 0.75 knots, and severe Sea State 7 waves.  The
principal involves the production of two flows on and near the surface
of the water, surface oil is brought inwards to the vortex and then
concentrated as an oil packet, and a recovery pump intake can then remove
the oil with little water.  Efficiency of the model varied between 10 and
46 percent over the range of the thickness of the oil tested, 1/16 to
one inch.  A recovery rate of 110 gpm was achieved.  Higher rates of recovery
are possible if the pump size is changed.

*0il spills, *Pollution abatement, Research and development, Model studies,
Water pollution,  Pollutants, Technology, Equipment

*Free Vortex, *0il spill recovery, Oil spill clean-up, New equipment
                                          861

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 371J

 SURVEY OF NEEDS FOR MUNICIPAL WASTE TREATMENT FACILITIES,

 Environmental Protection Agency, Washington, D. C., Office
 of Water Programs, Division of Municipal Waste Water
 Programs

 Rational Technical Information Service Report PB-230 084, February, 1972.
 39 p, 1 fig, 14 tab.

 This survey was conducted to obtain current estimates of the scope and cost
 of construction of municipal waste treatment facilities that are needed to
 meet existing water quality standards implementation schedules or other
 standards or enforcement requirements.  The precedures and findings are
 explained.  Figures obtained from this survey are considered as a useful
 and practical measure of the cost and scope of the construction needs
 for sewage treatment facilities.

 *Waste water treatment, *Municipal wastes, *Treatment facilities, Sewage
 treatment, Costs, Water quality control, Water pollution treatment, Surveys

 *Environmental Protection Agency, Municipal waste treatment facilities
372J

WASTE OIL RECOVERY PRACTICES—STATE OF THE ART,

Environmental Quality Systems, Incorporated, Washington,
D. C.

National Technical Information Service Report PB-229 801, December, 1972.
250 p, 39 fig, 46 tab, 128 ref, 3 append.

A study of waste oil production, collection, reprocessing, re-refining
and disposal was performed primarily on the state of Maryland.  Data is
presented on the origin and amounts of waste automotive, industrial and
other waste oils.  The effect of changing gasoline lead concentration on
waste crankcase oils is found to be significant with respect to future
uses of such waste oils.  The exact fate of waste oils within Maryland
is being investigated.  Methods for purifying, re-refining, reprocessing
or disposing of waste oils of several types are given.  The predominant
precess for re-refining waste crankcase oils is the acid/clay method
using sulfuric acid and adsorbent clays.  Newer processes reducing or
eliminating the need for acids or clay are being tried.  When the burning
of waste oils for heat recovery or incineration is practiced, metallic
compounds in the oil may pose a health hazard if released to the atmosphere.
Waste oil reprocessing is generally not economically feasible because of high
collection costs, low process yields, small plant operations and unfavorable
legislation.

*0il wastes, *0il pollution, Fuels, Industrial wastes, Gasoline, Waste
disposal, Maryland, Water pollution sources, Economics, Legislation

*Waste oil production, *Waste oil re-refining, Acid/clay re-refining
                                          862

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373J

A LOOK AT THE NATIONAL PERMIT PROGRAM,

Ziemba, J.

Industrial Wastes, Vol. 22, No. 3, p 44-45, May-June 1974.

The Water Pollution Control Act of 1972 (P.L.92-500) is cited as a
significant basis for future water pollution legislation, providing a
workable framework for effective safeguards, by means of which a situation
of "zero discharge" may be attained.  A focal point of P.L.92-500, the
National Pollutant Discharge Elimination System, would require a permit
in order to discharge any type of pollutant.  The permit program encourages
citizen involvement through public hearings.  The program is implemented
by the state, with the Federal Agency safeguarding proper enforcement.
States without their own program leave permit procedures including application,
review, public hearing, approval and the duration of the permit to the
Federal agency.  The permit program would provide specific guidelines
for water pollution control under the Water Pollution Control Act.

*Water pollution control, legislation, Water discharge, Permits, Federal
Water Pollution Control Act

The Water Pollution Control Act of 1972, PL 92-500, Zero discharge
 374J

 ANTICHOLINESTERASE ACTION OF METHYL PARATHION, PARATHION
 AND AZINPHOSMETHYL IN MICE AND FISH:  ONSET AND RECOVERY
 OF INHIBITION,

 Benke, G. M. and Murphy, S. D.

 Harvard University, Boston, Massachusetts, School of
 Public Health, Kreage Center for Environmental Health,
 Department of Physiology

 Bulletin of Environmental Contamination and Toxicology, Vol. 12, No. 1,
 p 117-122, July, 1974.  2 fig, 1 tab, 16 ref.

 It has been found that the lethal dose ranges for single intraperltoneal
 injections of parathion, methyl parathion and azinphosmethyl in mice
 were 13-15, 10-12 and 304.5 mg/kg respectively and in sunfish the respective
 dose ranges were 10-200, greater than 2500 and 1-10 mg/kg.  This experiment
 was performed to ascertain if determinations of the rate of onset and recovery
 of acetylchollnesterase (AChE) inhibition in sunfish and mice could
 partially explain the large differences in acute toxicity of these three
 organophosphorus insecticides.  The rates of onset of AChE inhibition do
 not explain the greater toxicity of paration and azinphosmethyl relative
 to methyl paration in sunfish.  Onset and recovery rate of AChE inhibition
by all three pesticides in fish brain and muscle is. considerably slower
 than the rate in mice.  The slow recovery of AChE in fish may make them
more susceptible to cumulative damage by these compounds.

 *0rganophosphorus pesticides,  *Pesticides, Water pollution effects, Fish
physiology,  Fish toxins, Pesticide toxicity,  Fish, Inhibitors,  Bioindicators

Acetylcholinesterase,  Parathion, Methyl parathion, Azinphosmethyl, Mice
                                         363

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375J

CONDUCTION VELOCITIES IN METHYLMERCURY POISONED PATIENTS,

Von Burg, R. and Rustam, H.

Rochester University, Rochester, New York, Department
of Pharmacology and Toxicology

Bulletin of Environmental Contamination and Toxicology, Vol. 12, No. 1,
p 81-85, July, 1974.  2 tab, 12 ref.

This paper investigated the claims that the early symptoms of methylmercury
intoxication are similar to peripheral polyneuropathy.   The peripheral
nervous system was examined by electrophysiological techniques because these
techniques are useful in diagnosing peripheral polyneuropathy.  A control
group and a group composed of methylmercury poisoning patients showed
no statistical difference when tested.  This indicates  that, in humans,
clinical electrophysical testing does not support the idea that methylmercury
intoxication resembles peripheral polyneuropathy.

*Mercury, *Toxicity, Analytical techniques, Public health, Poisons, Water
pollution effects, Water pollution, Heavy metals

*Methylmercury poisoning, *Peripheral polyneuropathy, Electrophysiological
techniques
376J

NITRATE AND CHLORIDE MOVEMENT IN THE PLAINFIELD LOAMY
SAND UNDER INTENSIVE IRRIGATION,

Endelman, F. J., Keeney, D. R., Gilmour, J. T., and
Saffigna, P. G.

Wisconsin University, Madison, Wisconsin, Department
of Soil Science

Journal of Environmental Quality, Vol. 3, No. 3, p 295-298, July-September,
1974.  5 fig, 2 tab, 11 ref.

The results of a field experiment show that N02-N can move rapidly beyond
the rooting zone of Plainfield loamy sand due to rainfall and/or irrigation.
Leaching was evaluated under intensive irrigation over an 11-day period.  KN03
and KC1 were used as fertilizers.  The N03 and Cl concentration was
determined in soil profile and lysimeter leachate samples collected daily.
Water in the amount of 2.5 cm moved 19 cm in the surface and 28 cm in
subsurface soil.  Chloride concentrations were similar to those of N03-N.

*Groundwater pollution, *Leaching, *Fertilizers

Plainfield loamy sand, Wisconsin University Experimental Farm, Hancock,
Wisconsin, College of Agricultural and Life Sciences, Wisconsin University
Institute for Environmental Studies
                                    864

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377J

PHOSPHOROUS ASSOCIATED WITH SEDIMENTS IN IRRIGATION AND
DRAINAGE WATERS FOR TWO LARGE TRACTS IN SOUTHERN IDAHO,

Carter, D. L., Brown, M. J., Robbins, C. W. and Bondurant,
J. A.

Snake River Conservation Research Center, Kimberly, Idaho

Journal of Environmental Quality, Vol. 3, No. 3, p 287-291, July-September,
1974.  5 tab, 18 ref.

Phosphorus was measured in irrigation and surface drainage.  Present
practices remove more phosphorus from the Snake River in irrigation than
is returned in drainage; new practices could be implemented for phosphorus
conservation.  Due to particle size separation in drainage streams, finer
sediments return to the river containing higher phosphorus concentrations
than the soils from which they were eroded.  The importance of defining
sampling methods and procedures is illustrated by comparative data on
irrigation and drainage waters.

*Phosphorus, *Quality control, Irrigation, Drainage

Snake River, Kimberly, Idaho
378J

WATER QUALITY AFTER CLEARCUTTING A SMALL WATERSHED IN
WEST VIRGINIA,

Auberton, G. M. and Patric, J. H.

USDA Forest Service Timber and Watershed Laboratory,
Parsons, West Virginia

Journal of Environmental Quality, Vol. 3, No. 3, p 243-249, July-September,
1974.  2 fig, 3 tab, 13 ref.

In 1969, an 85-acre watershed was clearcut on the Fernow Experimental
Forest, Parsons, West Virginia.  As a result of the clearcutting, streamflow
increased; this increase was reduced during the second year by rapid
vegetation.  Clearcutting had a negligible effect on the temperature, pH,
nonstorm turbidity, and concentrations of dissolved solids.  Storm
turbidity, nitrate-nitrogen and phosphate concentrations showed slight
increase.  Water quality remained high due to careful road management,
retention of forest along the stream, and lush vegetation after cutting.

*Age, *Turbidity, *Forestry, *Streamflow, *Nutrients, Temperature,
Agriculture, Watersheds, Water resource management (applied)

Fernow Experimental Forest, Parsons,  West Virginia, Northeastern Forest
Experimental Station,  pH
                                         365

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 379J

 NITRATE AND CHLORIDE ACCUMULATION AND DISTRIBUTION IN
 FERTILIZED TILE-DRAINED SOILS,

 Cast, R. G., Nelson, W. W.,  and MacGregor, J. M.

 Minnesota University, St. Paul, Minnesota,
 Departmen  of Soil Science

 Journal of Environmental Quality, Vol. 3, No. 3, p 209-213, July-September,
 1974.  5 fig, 3 tab, 9 ref.

 Corn studies on tile drained Webster loam in Minnesota determined that
 annual N application up to 70 percent greater than N removed in grain is
 necessary for maximum yields.  The purpose of the study was to establish
 the relative role of N incorporation into the soil organic matter and/or
 loss through denitrification, downward leaching, or tile drainage in the
 determination of the fate of this fertilizer-N added above that removed
 in corn grain.  Accumulation of nitrate and chloride and their distribution
 were determined in Webster loam and Waldorf silty clay loam profiles after
 long term fertilization for  continuous corn crops.  Concentrations in the.
 profiles were determined at  0.3 m depth Intervals and lacreasing distances
 from the tile lines.

 *Nitrate, *Chlorlde, *Soil pollution, *Tile drains, Loam, Fertilization,
 Soil treatment, Denitrification, Soil leaching,  Corn grains

 Webster loam, Waldorf silty  clay, Nitrate loss
380J

STANDARDS, ADMINISTRATION, AND SURVEYS,

Forges, R. and Gross, S. P.

Delaware River Basin Commission

Journal of the Water Pollution Control Federation, Vol. 46, No. 6, p 1625-1643,
June, 1974.  216 ref.

Water quality standard guidelines for revision and general development under
the Federal Water Pollution Act Amendments of 1972, as applied to interstate
and intrastate waters were published by EPA.  Objectives, goals, policy guide-
lines, legislative requirements and other salient issues were examined.  Re-
vised water quality standards were proposed for the navigable waters of Illinois,
West Virginia, Puerto Rico, New Jersey, and New York.  The National Academy
of Sciences-National Academy of Engineering's Environmental Studies Board has
completed a revision of "Water Quality Criteria" issued in 1968.  Criteria for
six classes of water uses, such as recreation and aesthetics, public water
supplies, both fresh and marine water aquatic life and wildlife, agricultural
use and industrial supplies, were established.  A presentation of criteria In
numerical and verbal form for the physical, chemical, biological and esthetic
determinants of water quality for the six uses was made.  The Federal Act makes
the EPA required to publish criteria for water quality and information for
restoration and maintenance of aquatic integrity, and water measurement and
classification.  The development of effluent limitation guidelines contracted
for by EPA is examined by Longfield.  Level I technology was based on the
average of the best performance by plants of different sizes, ages, and unit
processes in each industrial category.

*Water pollution control, *Federal Water Pollution Control Act of 1972,
Standards, Administration, Surveys, Water quality standards, Aquatic biota,
Aquatic wildlife

EPA, National Academy of Sciences-National Academy of Engineering's
Environmental Studies Board, National Technical Advisory Committee
                                    866

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381J

A SUMMARY AND COMPARISON OF NUTRIENTS AND RELATED WATER
QUALITY IN LAKES ERIE, ONTARIO, HURON, AND SUPERIOR,

Dobson, H. F. H., Gilbertson, M., and Sly, P. G.

Canada Centre for Inland Waters,
Department of the Environment, Fisheries and Marine
Service, Burlington, Ontario, Canada

Journal of the Fisheries Research Board of Canada, Vol. 31, No. 5, p 731-738,
May, 1974.  13 fig, 7 ref.

This paper uses the presence of dissolved nutrient elements, nitrogen as
nitrate and ammonia, phosphorus as inorganic phosphate or soluble reactive
phosphate, silicon as reactive silicate, carbon as inorganic carbon, dissolved
organic matter, the Secchi depth, chlorophyll a, particulate phosphate, and
dissolved oxygen to summarize and compare the nutrients and water quality of
the Great Lakes.  Related water quality is described by a simple indexing
system, based on some of these parameters.

*Nitrogen, *Phosphorus, *Carbon, *Nutrients, Organic matter, Dissolved
oxygen, Chlorophyll, Great lakes

*Secchi depth, Chlorophyll a, Silicon
382J

LAW,

Smith, J. 0.

Georgia University, Athens, Georgia, Extension Service
and Institute of Government

Journal of the Water Pollution Control Federation, Vol. 46, No. 6,
p 1618-1625, June, 1974.  70 ref.

The amendments of 1972 to the Federal Water Pollution Control Act was the
most popular consideration in literature concerning federal efforts in water
quality control.  The inadequacies of past federal efforts in this area and
the important parts of the new amendments were discussed by McMahon.
Rasmussen and Kuchenbacker concluded that the improved enforcement procedures,
including citizen suits, the right to enter and monitor effluent discharge,
and the new permit program, should have a significantly positive effect on
the curbing of water pollution.  Coleman, on the other hand, criticized the
new amendments, considering the possibility of the development of problems
like those inputed to the Clean Air Act; such as alleged blackmailing of
the states by the EPA.  The amendments use of technologically-based standards
was criticized by Rauch, who then concluded that this policy, and its cost
factors, would perpetuate a negative incentive for technological development
necessary to meet the final goal.  In the role of state governments provided
by the Act, Finnell examined the Florida Environmental Land and Management
Act of 1972.  The trust doctrine of Virginia's new constitution dealing with,
natural resources was examined by Brion.

*Law enforcement, *Federal Water Pollution Control Act, Water pollution,
Water quality control, Waste water treatment, Effluent control, Groundwater
management

Citizen suits, Federal water quality legislation (pre-1972)
                                         867

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383J

NUTRIENT LOSSES FROM FERTILIZED GRASSED WATERSHEDS IN
WESTERN NORTH CAROLINA,

Kilmer, V. J., Gilliam, J. W., Lutz, J. F., Joyce,
R. T., and Eklund, C. D.

Tennessee Valley Authority and North Carolina State
University Agricultural Experimental Station,
Office of Water Resources Research, Department of
Interior

Journal for Environmental Quality, Vol. 3, No. 3, p 214-219, July-September,
1974.  1 fig, 7 tab, 29 ref.

Plant nutrient transport in drainage waters from two steeply sloping, differ-
entially fertilized, grassed watersheds in western North Carolina was ascer-
tained over a period of 4 years.  The dominant slopes on both watersheds are
35 to 40 percent.  During this time period, watershed No. 1 received
112-48-24 kg N-P-K/ha, with watershed No. 2 receiving 448-192-24 kg N-P-K/ha.
Average annual N loss was measured at 3.28 and 12.08 kg/ha for No. 1 and
No. 2, respectively; N03-N comprised 70 percent and 85 percent of the total
N lost in discharge waters from Both, watersheds.  Over the 4 years the total
N lost from each watershed was 6 to 10 percent of the fertilizer N applied.
Losses of nutrients usually occurred because of deep seepage..  Losses were
highest during the winter and spring months.  Watershed No. 2 had consistently
higher concentrations of nutrients in discharge water.  N03-N concentrations
were higher than 10 ppm on watershed No. 2 only once in the period of obser-
vation.  Steeply sloping pastures, judiciously fertilized, are not important
sources of nutrients occurring in surface and groundwaters, according to
this study.

*Nutrlents, *Drainage waters, *Runoff, Watersheds, Slopes, Fertilizers,
Surface waters, Groundwater

*Fertilized grassed watersheds, *Nutrient loss, *Steeply sloping pastures
384J

SETTING UP A SPECIAL COLLECTION ON WATER POLLUTION
IN A UNIVERSITY LIBRARY,

Friedlander, J.

Case Western Reserve University, Lake Erie Study
Collection, Sears Library, Cleveland, Ohio

Special Libraries, Vol. 65, No. 7, p 291-296, July, 1974.  12 ref.

The Cleveland area has three interdisciplinary research teams which are studying
the pollution of Lake Erie.  Water pollution materials are distributed in
various locations and with varying subject classification.  A special library
collection was established in the university library, and the complexity of
identifying and collecting reports in the field of environment, along with
locating other water pollution agencies and recording locations of other local
collections of data are elucidated.  The functions of the Lake Erie Study
Collection as a special library are considered by its librarian, in relation
to the project members' research.

*Water pollution, *Lake Erie, *Data collections, Environmental control

*Case Western Reserve University, *Lake Erie Study Collection

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385J

IS THE WATER SAFE TO DRINK?  PART 3:  WHAT YOU CAN DO,

Harris, R. H. and Brecher, E. M.

Consumer Reports, Vol. 39, No. 8, p 623-627, August, 1974.

There is a great need for assuring the purity of drinking water being piped
into homes and businesses by some 40,000 community water systems in the
United States.  Methods for achieving a higher standard of water quality
was discussed in two previous articles.  The role of the individual citizen
is now in focus.  Recommendations for reducing one's heavy metal contamination
intake are as follows:  water should be let running for a minute or so after
several hours of nonuse, avoid using hot water for preparing infant's formula
or cooking since hot water tends to be higher in heavy metal content, although
boiling is essential for water which is frequently contaminated by bacteria,
and most importantly, organizing citizens groups to demand the upgrading of
water quality from the community supplies, and Being prepared to pay the
price of purification.

*Water pollution, *Environmental control, *Potable water, Public healtK

*Citizen action
386J

PROGRESS IN SATISFYING ENVIRONMENTAL REQUIREMENTS,

Patterson, W. D.

Public Utilities Fortnightly, Vol. 94, No. 3, p 13-27, August 1, 1974.
9 fig, 4 tab.

Legislative and regulatory developments at the federal level concerning
environmental control are reviewed.  The Clean Air Act Amendments of 1970
gave the EPA authority to establish safe ground level concentrations of air
pollutants, and to enforce achievement of such levels through the application
of controls.  EPA has promulgated two sets of ambient air quality standards,
specifying maximum acceptable ground level concentrations of pollutants.
Primary standards are those strict enough to protect public health.  These
standards are to be reached nationally by 1975, regardless of expense.
Secondary standards represent the protection of the public welfare.  These
standards specify levels necessary to protect vegetation, animals, and
materials from hazardous contamination, being expected for national attain-
ment sometime between 1978 and 1980.  State ambient air quality standards
will also have to be met, and in some cases, with greater rigidity.  Since
the enactment of NEPA, significant progress has been made.  Legislation now
pending should provide a basis for effective land-use control.  New equipment
and technology has had a significant impact on industrial waste quality,
evidenced in increased expenditures since 1970.  The power facility siting
process has also been an indication of progress in the. environmental area.
Development of a national land-use policy and the specification of existing
regulations would enhance environmental protection.

*Environmental control, legislation, Clean Air Act, Federal Water Pollution
Control Act, Industrial wastes, Chemical pollution, Waste water treatment,
Water quality control

*National Environmental Policy Act, *Environmental Protection Agency
                                    869

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387J

EPA'S POLLUTION CONTROL COALS TAKE BROADSIDE IN SEATTLE,

Engineering News Record, Vol. 193, No. 5, p 15, July 25, 1974.

The federal water pollution control program came under fire in Seattle from
public officials.  John D. Parkhurst of the Water Pollution Control Federation
attacked what he claimed was the "economic madness" of the EPA's standard for
secondary treatment.  Parkhurst said that "American taxpayers will be reluctant
to share in without assurances, that water quality will be enhanced on a
commensurate basis."  The general manager of the Los Angeles County Sanitation
District also predicted the secondary treatment would cost more than $100
billion.  Richard S. Page, executive director of the Municipality of Metropolitan
Seattle, claimed that the 85% removal of BOD required by the EPA would produce
no significant benefit to the quality of water on the Pacific Coast.  The
director asserted that $650 million would be needed to meet this requirement
on the Pacific Coast alone.

*Water quality control, *Water pollution, *Secondary waste water treatment,
Economics, Pacific Coast, BOD, Governmental water policy

*Environmental Protection Agency
388J

ON POLLUTION CONTROL,

New Civil Engineer Special Review, Vol. 95, p 53, May, 1974.

California waters suffered from an excess of pollution in 1969.  In the Santa
Barbara channel 100,000 barrels of crude oil were spilled due to a blowout.
Further eruptions necessitated the sealing of the fissure in March, with continued
seepage following for longer than a year.  In December, a 120 sq km oil slick
developed from a Union Oil pipeline break.  A ban on oil drilling was then
instituted by the state of California.  Because of environmental protest, not
much more than seismic surveys have been done in the U.S. Atlantic or Pacific
continental shelves.  Legislation covering pollution control in the UK sector
of the North Sea is the Continental Shelf Act of 1964, which makes the discharge
of oil from drilling and production operations in that area an offense, with
a license dependent upon the operator's liability for control of any such
discharge.  The Petroleum Regulations of 1966 recommend that oil escape into
licensed waters be avoided by all necessary preventive measures.  Relevant
legislation was later added in the form of the Prevention of Oil Pollution Act
of 1971.  The "UK offshore operators' emergency action group", established by
the oil companies, has agreed to cooperate with the marine division of the DTI
in case of serious leakage from a pipeline or oil rig.  However, experts doubt
that such a minor scale of approach to such an enormous problem can he of any
great use at all.

*Water pollution, *0il spills, *0il pollution, Legislation, Water quality
control

Santa Barbara channel, US Atlantic and Pacific continental shelves., North. Sea,
Continental Shelf Act of 1964, Petroleum Regulations of 19.66, Prevention of
Oil Pollution Act of 1971
                                      870

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   389J

   SOLID WASTE  AND WATER QUALITY,

   Heidman,  J.  A.  and Brunner,  D.  R.

   Advanced  Waste  Treatment:  Laboratory,
   U.S.  Environmental Protection Agency, Washington,  D.C.

   Journal of the  Water  Pollution  Control  Federation,  Vol.  46, No.  6,  p  1315-1317,
   June,  1974.   20 ref.

   The potential for groundwater pollution resulting  from the  land  disposal  of
   solid wastes has been reviewed.  Leachate  characteristics,  leachate attenuation
   in soil,  leachate pollution  problems, site evacuation methodology,  and new
   refuse processing and disposal  methods  which have  a potential  effect  on ground-
   water quality were examined.  Solid waste  disposal  as related  to leachate
   production and  groundwater pollution  and consideration to design of landfills
   for leachate control  were discussed.  Toxicity  and  solubility  of hazardous
   solid and liquid wastes were considered.   Reduction, neutralization,  recovery
   and disposal techniques recommended for waste streams containing pesticides,
   CN, Hg, As,  Cr,  Cd and miscellaneous  organic and inorganic  materials  and  nuclear
   materials were  examined also.   The  hydrogeologic factors in consideration of the
   situating and design  of landfills under climatic conditions in northeastern
   Illinois  have been discussed.   Engineering techniques effective  in  control of
   production and  migration  of  leachate, are  also  examined with conceptual designs
   for landfills in four different hydrogeologic environments.  An  evaluation of
   sanitary  landfills and factors  influencing leachate production was  made.  In
   one chase, soil types, groundwater  flow patterns,  and leachate characteristics
   at a  landfill site in use for 5 years were examined in detail.

   *Water quality  control, *Soil leaching,  *Solid  wastes, Hydrogeology,  Groundwater,
   Landfills, Attenuation, Waste disposal,  Pesticides,  Alkalinity,  COD,  Nitrogen,
   Mercury,  Cadmium, Chromium

   Leachate  attenuation,  CN,  As
390J

POLLUTION CONTROL IN JAPAN-A SURVEY,

Process Biochemistry, Vol. 9, No. 5, p 15, 34, June, 1974.  1 tab.

The overall picture of water pollution in Japan is very serious, not only in
the primary effects but also in a chain of secondary effects, in both Japan's
fresh and marine waters.  The Anti-pollution Act of 1970 is one of the most
comprehensive environmental protection laws in the world.  It is a framework
of definitions and plans of action.  The two series of effluent standards set
for water quality are for the protection of health and for environmental
preservation.  The pollution control market is one of the fastest growing areas
in the Japanese economy.  The market has been mainly concerned with solving
existing problems, developing, purchasing and marketing the existing technology.
However, the development of preventive measures is becoming more important.
The developments are in three areas:  the development of new recovery techniques;
the detailed application of these and existing technology to specific industrial
problems; and the redesign of processes to avoid initial pollution.

*Water pollution, Water pollution sources, Pollution abatement, Water pollution
control, Equipment, Foreign countries, Foreign technology, Legislation, Planning,
Water resources development

Japan
                                        871

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 391J

 THE TOXICITY OF 2,3,7,8-TETRACHLORODIBENZO-P-DIOXIN  (TCDD)
 IN GUPPIES  (POECILIA RETICULATUS PETERS),

 Norris, L. A. and Miller, R. A.

 United States Department of Agriculture, Corvallis, Oregon,
 Pacific Northwest Forest and Range Experimental Station
 Forest Service

 Bulletin of Environmental Contamination and Toxicology, Vol. 12, No. 1,
 p 76-80, July, 1974.  1 fig, 2 tab, 18 ref.

 The compound 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) is a contaminant of the
 herbicide 2,4,5,-trichlorophenoxyacetic acid.  TCDD is immobile, slowly degraded
 in soils, not taken up readily by plants, subject to photodecomposition, low
 in water solubility, and highly toxic and teratogenic in mammals.  This experiment
 determined the characteristics of TCDD in guppies.  Exposure of the guppies to
 0.1, 1.0 and 10.0 ppb TCDD for 120 hours caused complete mortality in the
 following 32, 21, and 30 days, respectively.  The suggested reason for the
 apparent decrease in toxicity between 1.0 and 10.0 ppb TCDD is that fish in
 the 1.0 ppb TCDD concentration may have been exposed to supersaturated levels
 of TCDD.  There was a significant positive correlation of duration of survival
 with the body length.

 *Fish, *Herbicides, *Pollutants, Toxicity, Chemicals., 2,4,5-T, Brush, control,
 Analytical techniques

 *Guppies, *Poecilia reticulatus, TCDD
392J

WHITHER WATER?,

Gribbin, J.

Nature, Vol. 250, No. 5464, p 276-277, June, 1974.  1 fig, 2 tab.

The future plans for water resources in Britain are discussed.  River management,
water supply, and sewage disposal are under the control of new regional water
authorities.  A Central Water Planning Unit assists with the issues on a
national basis, at the government level and at the regional level.  The
possibility that a new weather pattern is developing is also discussed.
Proposals for climatic research are under consideration.  The CWPU would like
to develop a "national water grid" involving transfers from region to region
and the extension of the present system of river regulation.  There are plans
to develop groundwater abstraction.  Desalination is also being considered but
does not appear to be feasible.

*Water resources development, *Water supply development, *Comprehensive planning,
Groundwater resources, Legislation, Potential water supply, Projections, Great
Britain, Water resources, Desalination

Central Water Planning Unit
                                     872

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39 3 J

NOTE ON THE FERTILITY VALUE OF OXIDATION POND EFFLUENT
FOR GROUNDNUT (ARACHIS HYPOGAEA L.),

Kale, C. K.

Central Public Health Engineering Research Institute,
Nagpur, India

Indian Journal of Agricultural Science, Vol. 43, No. 5, p 523-525, May, 1973.
2 tab, 4 ref.

The value of domestic sewage as a fertilizer was tested at an oxidation pond,
using groundnut as the test plant.  Seven treatments were used, including
tap-water control.  Concentrations of the fertilizers N,P, and K are given.
The effect of different treatments on root growth was significant at 5 percent
level.  Synthetic sewage and control gave similar results.  The effect of
irrigation treatments on the vegetative growth of the groundnut was significant
at the 1 percent level.  Although the addition of phosphorus to this effluent
gave a better yield, the increase over the effluent alone was: not significant.
It is believed that the shortage of phosphorus in comparison to nitrogen and
potassium in the raw sewage and effluent was. compensated for by other nutrient
elements, including microelements.

*Legumes, *Phosphorus, *Effluents, Oxidation Lagoons, Nutrients, Sewage treatment,
Fertilizers

Central Public Health Engineering Research Institute, Nagpur, India,
Groundnut (Arachis hypogaea L)
 394J

 BENTHOS AND  ALLOCHTHONOUS  ORGANIC  MATTER IN STREAMS,

 Hynes, H.  B.,  Kaushik,  N.  K.,  Lock,  M.  A.,  Lush,  D. L.,
 and Stocker, Z.  S.  J.

 Waterloo University, Waterloo,  Ontario,  Department of Biology

 Journal of the Fisheries Research  Board of  Canada, Vol.  31,  No.  5,  p  545-553,
 May,  1974.   10 fig, 13  ref.

 The findings are in relation to general stream  ecology.  A  coring technique
 showed that  stream  animals are  vertically distributed many  centimeters down
 into  the gravel,  with 17 percent in  the top 5 cm.  Arctic stream sampling
 chironomid larvae comprised 70-80  percent of numbers in  the  benthos;  their
 rate  of drift  did not vary with the  time of day.  The effect of  nutrients
 and temperature  on  the  decomposition of autumn  leaves shed  in water was
 studied.   The  addition  of nutrients  N and P increased the amount of nitrogen
 after incubation, but temperature  affected  only the decomposition rate.
 The importance of bacteria and  fungi in decomposition were noted.   Food
 preference for several  leaf species  were shown  by Gammarus.  Up  to  40 percent
 of autumn-shed leaf is  water-soluble.   One  process by which  it is made available
 to stream  animals is conversion to particles and  involves mechanisms  similar
 to those found in soils.  Field investigations  showed large-scale fluctuations,
 in a  short time  period, of dissolved and particulate matter  in the  water.

 *Benthos,  *Animal groupings, Autumn, Leaves, Streams, Nutrients

 Gammarus, Chironomidae, Blackfly larvicide
                                          873

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 39 5 J

 PP'-DDT ADSORPTION TO SUSPENDED PARTICULATE MATTER IN SEA
 WATER,

 Pierce, R. H., Olney, C. E., and Felbeck, G. T.

 Rhode Island University, Kingston, Rhode Island,
 Department of Plant Pathology-Entomology

 Geochemical et Cosmochimica Acta, Vol. 38, No. 7, p 1061-1073, July, 1974.  5 fig
 5 tab, 35 ref.

 Contamination of the ecostem by chlorinated hydrocarbons has occurred by transporta-
 tion from areas of application and dumping via the air, rivers and land drainage
 and also by being directly introduced in municipal and industrial wastes.  It has
 been suggested that the chlorinated hydrocarbons are transported through water by
 adsorption to suspended particulate matter.  This investigation determined what
 fraction of the suspended particulate matter is responsible for adsorbing chlorinated
 hydrocarbons from sea water and what are the mechanisms: of adsorption.  A procedure
 was developed to study pp'-DDT adsorption and desorption to suspended particles in
 aqueous solutions.  It was observed that humic acid had the highest adsorbing capacity,
 sediment was intermediate and clay adsorbed the least.  Removal of organic matter
 from the sediment greatly reduced its adsortive capacity.  The suggested mechanism of
 DDT adsorption to clay particles is an electrostatic attraction between hydrogen
 atoms on the aromatic rings and negatively charged sates, on the clay s.urf aces.  The
 adsorption of DDT to humic acid is attributed to hydrophobic bonding to portions of
 the humic polymer.  Since many sources of pesticides such, as soil erosion and
 sewage effluent contain large amounts of humic substances, the pollutants could be
 adsorbed before they reach the aquatic environment.

 *Pestlcides, *Water pollution sources, *Chlorinated hydrocarbon pesticides, *DDT,
Adsorption, Agricultural chemicals, Pesticide drift,  Waste treatment,
 Environmental effects
  39 6J

  PHYTOPLANKTON PRODUCTION IN CHAR LAKE,  A NATURAL POLAR LAKE,
  AND IN MERETTA LAKE,  A POLLUTED POLAR LAKE,  COBNWALLIS ISLAND
  NORTHWEST TERRITORIES,

  Kalff, J. and Welch,  H.  E.

  McGill University,
  Montreal, Quebec, Canada
  Department of Biology

  Journal of the Fisheries, Research Board of  Canada,  Vol.  31,  No.  5,  p 621-636, May,
  1974.   16 fig, 5 tab, 18 ref.

  Between 1969 and 1972,  the phytoplankton production  of ultraoligotrophlc Char Lake
  and polluted Meretta Lake was  studied,  and findings  of the study are presented.  In
  Char Lake, the most oligotrophic lake existing,  photosynthesis occurs during the
  entire nine months  that  the sun is above the horizon.   The production rate is much
  more constant than would be suggested by the light input (on which snow cover has a
  considerable effect)  because of changes in depth of  maximum photosynthesis, in
  efficiency of low light  utilization, and in optimal  light flux.   Meretta Lake has a
  greater phytoplankton production and chlorophyll concentration twenty times greater
  than Char Lake.  Nutrient deficiencies  are most likely responsible for low production
  in Char Lake.  In both lakes benthic production is of major significance.

   *Phtoplankton, *Photosynthesis, *Chlorophyll, Sewage, Snow cover, *Productivity,
  Comparative productivity, Ecology, Oligotrophy

  Ultraoligotrophic,  Polluted, Nutrient Deficiencies,  Benthic production
                                         874

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  39 7J

  DYE AND DROGUE STUDIES OF SPOIL DISPOSAL AND OIL
  DISPERSION,

  Klemas, V.,  Maurer,  D., Leatham, W.,  Kinner P.,  and Treasure,
  W.

  Delaware University, Newark,  Delaware,  College of Marine
  Sciences

  Journal of the Water Pollution Control  Federation, Vol.  46,
  No. 8, p 2026-2034,  August,  1974.  18 fig,  12 ref.

  As part of a study to determine short-term consequences  of dredging and dumping
  on benthic invertebrate colonies near the mouth of the Delaware Bay,  a sampling
  grid for geological  and biological stations was designed before dredging commenced.
  Dye and drogue studies were  made to map the general hydrographic circulation in
  order to establish these stations, and  a dye study was also made of surface water
  movement at  a suggested off-shore oil terminal location.  The procedures used and
  results obtained from these  studies,  which utilized aircraftboat,  radio-coordinated
  teams, are presented.

  *Dredging, *Dye, *Currents,  Sediments,  Estuaries, Circulation

  *Hydrographic circulation, Drogue, Surface water movement, Aquatic frontal system,
  Tidal flow
39 8 J

EXPERIMENTAL OIL SKIMMER,

Mechanical Engineering, Vol. 96, No. 8, p 48, August, 1974.  1 fig,

A test was run on an oil skimmer which could be used for emergency oil spills at
high seas.  This system, built by Lockheed Missiles and Space Company, was tested
by riding it (with Coast Guard escorts) through a storm off the northern California
coast.  The oil-recovery capacities are up to 1000 gallons of oil per minute.  A
disc-drum revolves in an oil-water mix, oil adheres to the discs and free water runs
off, and the oil is carried past wipers that direct it to a hollow axle.  Oil then
is pumped from the machine to storage containers.  The machine is designed to be
carried to an airport near an oil-spill site, to be assembled in an hour, and to be
towed or carried on a buoy tender to the work area.

*0ils spills, *0ceans, *0il skimmers, Recovery, Equipment, California

Lockheed Missiles and Space Company, Oil-recovery capacities, Survival test
(equipment)
                                       875

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39 9J

CONVERSION OF MANURE TO OIL BY CATALYTIC HYDROTREATING,

Fu, Y. C., Illig, E. G., and Metlin, S. J.

United States Department of the Interior, Bureau of Mines,
Pittsburgh Energy Research Center, Pittsburgh, Pennsylvania

Environmental Science and Technology, Vol. 8, No. 8, p 737-740, August, 1974.  3
fig, 6 tab, 3 ref.

Agricultural wastes from animals are a pollution, odor, and health problem.  As
an effort to reduce pollution and at the same time to utilize a potential energy
source, the Bureau of Mines experimentally has been converting organic wastes to oil.
As example, bovine manure is hydrogenated and liquefied by hydrogen or synthesis gas
(equal amounts of hydrogen and carbon monoxide) at temperatures of 330-425 degrees C
and operating pressures of 1500-3000 psi in the presence of a recycle manure oil
and a cobalt molybdate catalyst.  With an increase in temperature, oxygen content
and viscosity of oil produce decrease, but hydrogen consumption increases.  A
significant improvement on this process when using synthesis gas:, is achieved Ey
adding sodium carbonate to the reaction mixture; hydrogen consumption is reduced
markedly, oil yield improved, and oil viscosity reduced.

*0il, *Agricultural wastes, Liquification, Hydrogen, Oxygen, Animal wastes-,
Temperature, Pollution

*Bovine manure, Hydrogenation, Oil viscosity
400J

SOIL LIQUEFACTION BY TORSIONAL SIMPLE SHEAR DEVICE,

Ishibashi, I., and Sherif, M. A.

Washington University, Seattle, Washington, Department of
Civil Engineering

Proceedings of the American Society of Civil Engineering, Vol. 100, No. GT8, p 871-
888, August, 1974.  19 fig, 4 tab, 4 ref.

As a result of severe earthquakes, structural damage due to soil liquefaction has
become an area of study in many research laboratories.  A simple shear device, the
conventional equipment for liquefaction laboratory study, has several difficulties.
A new instrument eliminates effects such as wall friction without sacrificing
requirements of duplicating in situ stress and strain conditions.  The new instrument
called the Torsional Simple Shear Device, was compared with the simple shear test
equipment.  It was found that with the Torsional Simple Shear Device one can check
and verify the adequacy of the amount of soil saturation prior to cyclic testing
and one can study the effects of lateral soil confinement on the liquefaction
potential of the test sample.  In addition, the Torsional Simple Shear Device tests
the soil with a unique cross sectional area and Imposes uniform shear strains and
stresses, thus providing more reliable experimental results.

*Soil liquefication, *Shear, *Measurement, Stress, Earthquakes, Shear device,
Laboratory tests, Equipment

*Torsional simple shear device
                                       876

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401J

TISSUE DISTRIBUTION OF (lAC)DDT IN THE LOBSTER AFTER ADMINI-
STRATION VIA INTRAVASCUIAR OR ORAL ROUTES OR AFTER EXPOSURE
FROM AMBIENT SEA WATER,

Guarino, A. M., Pritchard, J. B., Anderson, J. B., and Rail,
D. P.

Laboratory of Toxciology, National Cancer Institute,
National Institutes of Health, Bethesda, Maryland

Toxicology and Applied Pharmacology, Vol. 29, p 277-288, 1974.  1 fig, 5 tab, 11 ref.

A pharmocokinetic approach to studying the fate and distribution of carbon 14
labeled DDT was employed using the lobster.  The radioactive pesticide was administered
intravascularly, orally and by exposure from the ambient water.  After injection,
there was rapid removal of (14C)DDT from the plasma and a persistent increase in
the amount of radioactivity in the hepatopancreas.  Seven days after injection
about 90 percent of the administered radioactivity was found in the hepatopancreas.
When the DDT was administered to the lobster from the ambient water or from food,
again more than 90 percent of the radioactivity was found in the hepatopancreas
seven days after treatment.  Studies concerning the levels of DDT metabolites in
the organs of untreated lobsters indicated that the egg masses: contained the largest
amount followed by the hepatopancreas and then By the carcass (muscle).  These
studies suggest that the lobster may protect itself from DDT toxicity by sequestering
DDT in the hepataopancreas and in egg masses hut that the bioconcentration in
these tissues could be harmful to organisms which, eat thes.e parts, of the lobster.

*DDT, *Lobsters, *Pesticides, Water pollution effects, Insectisides, Pollutants,
Chlorinated hydrocarbon pesticides, Bioassay, Carbon Radioisotopes, Radioactivity,
Aquatic life

(14C)Carbon
402J

OSMOREGULATORY RESPONSES TO DDT AND VARYING SALINITIES IN
SALMO GAIRDNERI-I.  GILL NA-K-ATPASE,

Leadem, I. P., Campbell, R. D., and Johnson, D. W.

Idaho State University,
Pocatello, Idaho
Biology Department,

Comparative Biochemistry and Physiology, Vol. 49A, No. 1, p 197-205, September 1,
1974.  4 fig, 29 ref.

Results from laboratory investigations show that DDT inhibited activity of Na-K-
ATPase and Mg-ATPase in gills of rainbow trout adapted to freshwater, one-third sea
water, and sea water.  A negative correlation was found between gill Na-K-ATPase and
serum sodium in treated fish in sea water.  Enzyme activity was inhibited in fresh
water fish but no osmoregulatory impairment was found, indicating a minor or non-
existent role for gill Na-K-ATPase in fresh water osmoregulation.  Enzyme activity
was inhibited in trout acclimated to sea water

*Laboratory tests, *DDT, *Rainbow trout, Freshwater, Sea water, Enzymes, Salt
tolerance

*0smoregulatory response
                                     877

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  40 3 J

  DAMAGE ASSESSMENT  OF HOUSEHOLD WATER QUALITY,

  Tihansky, D. P.

  U.S. Environmental Protection Agency, Office of Research
  and Development, Washington, D.  C.

  Journal  of  the Environmental Engineering Division, ASCE, Vol.  100, No. EE  4, p  905-
  918, August, 1974.  7  fig,  1 tab,  32 ref.

  This articles reviews  literature  on aspects of mineralized water supply damages,
  compiles economic  data on damages,  and derives functions relating these impacts
  in a typical household to various  levels of water quality.  Total household  damages
  can be calculated  from graphs as  illustrated in later sections.  These relations
  are applied to state-by-state data on water quality and household statistics to
  yield regional estimates of damages from water supply use.  The problem of
  resolving man-made versus natural  causes of these damages is also examined.

  *Reviews, *Water supply, *Domestic water,  *Water quality, Estimating, Regional
  analysis, Damages
404J

LINKS WITH WATER RESOURCES AND LAND USE PLANNING STRESSED
AT CORNELL CONFERENCE,

Civil Engineering-ASCE, Vol. 44, No. 8, p 92-94, August, 1974.

Highlights of the first water quality planning conference held at Cornell University
are outlined.  Points discussed include the implementing of plans, better planning
of river basins, water quality linked with land use, sewers as a dominant factor
in controlling urban growth, Pennsylvania's systematic approach to planning, and
the significance of non-point source pollution.

*Conferences, *Water quality, *Planning, *Alternative Planning, Future planning
(Projected), Project planning, Sewers, Water pollution sources
                                       878

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  405J

  NINE  MILLION  GALLONS  PER MINUTE  DOWN THE  DRAIN,

  Canadian  Petroleum, Vol.  15,  No.  7,  p 40-42,  July,  1974.

  With  their  introduction  of water quality  guidelines  in  1973,  Environment  Canada has
  emphasized  the reduction of  effluent BOD  and  the  elimination  of  such  contaminants
  as  cyanides.   The federal standards  are not nearly  as precise on the  tolerable
  levels  of heavy metals since not enough is known  about  the interaction  of various
  metals.   A  description of various industrial  pollutants,  their effects,  industrial
  problems, and treatment  methods  and  materials is  provided.

  Water quality control, *Industrial water, *Canada,  ^Industries,  Industrial wastes,
  Environmental control, Waste water treatment, Water quality standards,  Effluents,
  Heavy metals
406J

METHYLMERCURY UPTAKE BY FISH AND REACTION MECHANISMS OF
MERCURY BIOMETHYLATION UNDER CONTROLLED LABORATORY
CONDITIONS,

Shin, E-B.

Vanderbilt University,
Nashville, Tennessee

Dissertation Abstracts International B, Vol. 35, No. 1, p 285-286, July, 1974.

A dissertation was written with the following objectives:  to determine uptake rates
of methylmercury biosynthesized in sediment by fish under controlled laboratory
conditions; to determine the effects on the uptake rate of changing environmental
conditions; and to observe the effects of changing environmental conditions on the
overall methylation activities of microorganisms.  The dissertation includes a
general description of the problem, a review of the literature concerning
biomethylation of mercury and its uptake by fish, a review of the physical and
chemical properties of mercury, and discussion of the experimental results with
emphasis on the effects of external environmental parameters.

*Mercury, *Fish, Water pollution effects, Water pollution sources, Toxicity,
Sediments

Dissertation, Biomethylation of mercury
                                       879

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407J

LAND DISPOSAL OF WASTEWATER,

Tofflemire, T. J., and Van Alstyne, F. E.

New York Department of Environmental Conservation, Albany,
New York

Journal of the Water Pollution Control Federation, Vol. 46, No. 6, p 1201-1208,
June, 1974.  96 ref.

Conferences, surveys and general principles on land disposal of waste water are
reviewed.  Several individual systems, technical aspects,, nutrient travel, and deep
well injection are discussed.  Land application is practiced at many sites without
nuisance conditions or health problems.  The spray irrigation system of land
disposal was considered the most reliable.  Technical aspects include laboratory
observation and calculation of the influence of waste water on cation and anion
movement in soil, geocriteria for location, design, and maintenance of land disposal
sites, criteria for operation and maintenance of irrigation and drainage systems
and formulae for calculating pollutant dispersion and travel.  Phosphate adsorption,
phosphate removal, carbon-nitrogen ratios, nitrate, calcium, and sodium concentrations,
nitrogen transformations, and nitrogen removal are discussed with respect to various
methods.

*Waste water disposal, *Injection wells, Irrigation water, Spraying, Operation and
maintenance, Phosphorus, Nitrogen, Carbon, Drainage, systems., Reviews

Land disposal
 408J

 SET PROBE  OF  POLLUTION  CONTROL  AMENDMENTS,

 Engineering News  and  Record,  Vol.  193, No.  7,  p  24, August  8,  1974.

 Five contracts  have been  awarded by  the National Commission on Water  Quality for
 studies  of the  impact of  the  Federal Water  Pollution  Control Act Amendments  of
 1972.  The studies;are  on the cost to municipalities  and  industries of  meeting
 the effluent  limitations  of the law  and possible sources  of local  funding  for
 municipalities  building waste treatment plants;  and studies on petroleum refining,
 iron and steel, pulp  and  paper, and  organic chemicals industries which  include
 examinations  of alternative methods  of waste treatment and  associated costs,
 quality  of effluent with  various methods and materials and  energy  requirements.

 *Waste treatment,  *Costs,  *Industrial wastes,  *Municipal  wastes, Pulp and  paper
 industry,  Chemical industry,  Administrative agencies,  Economic impact,  Federal
 Water Pollution Control Act

 1972 Amendments
                                     5(30

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  409J

  DISTRIBUTION AND METABOLISM OF DDT IN THE CATFISH
  HETEROPNEUSTES FOSSILIS IN RELATION TO THE SIGNS OF POISONING,

  Agarwal, H. C., and Gupta, B.

  Delhi University, Delhi, India
  Department of Zoology

  Toxicology and Applied Pharmacology, Vol. 29, p 204-209, 1974.  2 tab, 22 ref.

  The extensive use of DDT has resulted in its widespread occurrence in the
  environment.  DDT is known to be concentrated as it moves up  the food chain.  Since
  fish are an important part of the food chain, it is necessary to know the form in
  which DDT is accumulated and whether any detojd.cation occurs  in fish.  Adult male
  catfish were given a lethal dose of 800 mg DDT/kg.  The metabolites of DOT in
  different tissues were studied after 24 hours.  DDE was the only metabolite found.
  The major percentage of the DDE was found in the kidney and lesser amounts were
  found in the liver and fat bodies.  The concentration of DDT  increased with time
  and severity of poisoning.  The brain and spinal cord had the lowest DDT content.
  The DDT content in the fat rose steadily and was highest in fish which recovered.
  It was indicated that the signs of poisoning in catfish were  directly related to the
  concentration of DDT in the brain and spinal cord.

  *DDT, *Pesticide toxicity, *Water pollution effects, *Fish, Pesticides, Insecticides,
  DDE, Pollutants, Chlorinated hydrocarbon pesticides, Food chains, Catfishes

  *Heteropneustes  fossilis
410J

EFFECTS OF HYDROELECTRIC DEVELOPMENT  IN WESTERN CANADA OH
AQUATIC ECOSYSTEMS,

Geen, G. H.

Simon Fraser University, Burnaby, British Columbia, Canada,
Department of Biological Sciences

Journal of the Fisheries Research Board of Canada, Vol. 31, No. 5, p 913-927  May
1974.  48 ref.

This paper reviews some of the changes in the aquatic environments which have
resulted from the development of hydroelectric power in Canada.  Developments from
Manitoba west through British Columbia and north to the Northwest Territories and
the Yukon are considered.  The following general predictions are made for the
effects of the creation of a reservoir from a lake or river:  littoral production
is usually low as a reflection of the effects of drawdown; plankton production and
water chemistry are little affected; growth rates of fish feeding on littoral organisms
are frequently reduced; and, the relative abundance of fish and their food organisms
is often altered.  General predictions can not yet be made for the vertical or
horizontal temperature regimes of a reservoir because of a lack of data.  Several
hydroelectric developments have blocked or impeded migrations: of economically
important fish and will probably produce a number of downstream changes in water
temperature or composition.

*Hydroelectric power,  ^Hydroelectric plants,  Reservoira, Aquatic environment,
Canada,  Reviews

*Hydroelectric development
                                        881

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 411J

 MICROBIOLOGY OF WATER,

 Geldreich, E. E.

 Envoronmental Protection Agency, Cincinnati, Ohio
 Water Supply Research Laboratory

 Journal of the Water Pollution Control Federation, Vol. 46, No. 6, p 1355-1372  June
 1974.  123 ref.

 Findings of several studies made regarding microbial pollution indicators are
 presented.  Particular attention is focused on distribution of coliforms, E. coli,
 fecal streptococci, and anaerobic lactobacilli in water sources.  Various methods
 and materials used in determining counts of indicator bacteria and waterborne
 pathogens are considered in detail, including rapid techniques for detection of
 bacterial populations in water sources.  Research done with respect to the
 microbiology of rivers, lakes, ponds, and reservoirs is discussed.  The microbiology
 of potable water and groundwater is also examined.

 *Water pollution, *Microbiology, *Microorganisms, Coliforms, E. coll, Waste water,
 Chlorination, Rivers, Streams, Lakes, Ponds, Reservoirs, Potable water, Groundwater
 Effluents

 Fecal streptococci, Anaerobic lactobacilli, Natural watera, Indicator bacteria,
Waterborne pathogens, Bacterial count, Receiving streams
 412J

 FIELD STUDY OF SOLUTE MOVEMENT IN A HIGHLY AGGREGATED OXISOL
 WITH INTERMITTENT FLOODING:  II.  PICLORAM,

 Roa, P. S. C., Green, R. E., Balasubramanian, V., and
 Kanehiro, Y.

 Hawaii University, Honolulu, Department of Agronomy and
 Soil Science

 Journal of Environmental Quality, Vol. 3, No. 3, p 197-202, July-September,
 1974.  2 fig. 1 tab, 21 ref.

 Previous work on persistence and movement of picloram herbicide is briefly reviewed.
 Materials and methods employed in field studies measuring the nature of picloram
 movement in a highly structured Hawaiian Oxisol, in order to determine whether
 laboratory absorption results could be utilized in the estimation of the
 penetration of the picloram peak for a given amount of applied water, are presented.
 Data from previous work on nitrate movement in the same Molokai soil field plots
 is compared with findings on picloram movement to measure the relative mobility
 of these solutes.  Results of the field studies, which indicated significant
 retardation in leaching of picloram in Molokai soil as compared with less
 aggregated soils, are discussed.

 *Leaching, irrigation, Groundwaters, Herbicides, Pesticides, Water quality

 Picloram herbicides Oxisol Molokai Water Transport, Solute Transport, Aggregated
 soils, Macorpore, Micropore
                                         882

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413J

HOW TO READ A FISH KILL,

Keup, L. E.

Office of water Operations,
Environmental Protection Agency,
Washington, B.C.

Water and Sewage Works, Vol. 121, No. 7, p 48-51, July, 1974.  1 fig.

Teams are more effective than individuals in determining the causes and finding
the solutions to fish kills.  The knowledge of time required for a water mass to
travel to a downstream point is basic to the investigation.  Diffusion rates of
dumped materials will further the investigation, along with observations on the
nature of a pollutant's entry into the river and its mixing with water mass.
Seasons have considerable influence on the magnitude of fish kills.  For example,
less dead fish rise to the surface in cold water.  Synergism and antagonism should
be taken into consideration in a fish kill, as well as habitat considerations.  The
history of water discharges from dams should be investigated in fish kills downstream
from dams.  Finally, human ignorance is often a cause of unexplained fish kills,
while sophisticated poachers may sometimes use fish, toxicants.

*Fishkill, *Water pollution, Toxicity, Water conservation,  Investigation
 414J

 FOULING OF HEAT EXCHANGERS FROM COOLING WATER AND PROCESS
 MATERIALS,

 Capper, C. B.

 Dearborn Chemicals,  Limited,
 Widnes, Lanes, Great Britain

 Effluent and Water Treatment Journal,  Vol. 14, No. 6, p 309-314,  June 1974.

 Fouling is defined as any deposit on heat exchange surfaces which effects
 the flow pattern through the heat exchanger,  the efficiency of the heat transfer
 process or both.  On the waterside,  fouling can be the result of  scale,
 corrosion, participate deposition, microbiological growths or process materials
 having by one way or another entered the waterside.  Fouling on the process  side
 can be caused by deposition of the primary process product itself, materials
 caused by side reactions, impurities present in the feedstock or  other deposits
 caused in a similar way to those from the waterside.

 *Fouling, *Heat Exchangers, Flow patterns, Heat transfer, Corrosion, Scaling,
 Feeds, Cooling water

 Particulate deposition, Waterside fouling, Process: materials
                                    883

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415J

ESTUARIAL AND COASTAL POLLUTION,

Buckley, A. D.
                              •
Mersey and Weaver River Authority

Water Pollution Control, Vol. 73, No. 3, p 307-314, 1974. 3 ref.

The three main sources of pollution in estuaries are domestic sewage, industrial
waste waters and the detrimental quality of the rivers entering the estuaries.
Chemical fertilizers being used in rural areas and run-off from roads and other
non-permeable surfaces also contribute to contamination.  DDT usage is another
problem with a long range effect.  Metalliferous mining waste has effectively
sterilized many streams downstream from industries, where, as in Wales, examples
of such pollution are evident in adjacent coastal waters.  Disinfectants, detergents,
nutrients from human waste, zinc-based ointments and facial creams, and the bacteria
found in biological filters in an activated sludge plant are more sources of
estuarial and coastal pollution.  Diversion of sewage downstream to an outfall into
the sea is one remedy, along with biological treatment aad removal of aolids By
screening.

*Water pollution, *Estuaries, *Coastal waters, Sewage, Bacteria, Detergents,
Industrial wastes, Domestic wastes, Zinc, DDT, Chemical fertilizer

The Royal Commission of 1865, The River Pollution Prevention Act of 1876
416J

PROGRESS OF PROTECTION OF THE ENVIRONMENT AND RESOURCES IN
THE UNITED STATES-A HISTORICAL SURVEY,

Meykar, 0. A.

Naval Sea Systems Command,
Washington D. C.

IEEE Transactions on Aerospace and Electonic Systems, Vol. AES-10, No. 4, p 521-532,
July 4, 1974.  7 ref.

Legislative action on the state and federal levels meant to improve and preserve
environmental quality and conserve natural resources, including water resources, was
developed and implemented in a logical sequence, synchronized with social development
and consciousness of the need for specific legislative, punitive, or constructive
actions.  The needed legislation was developed through a consensus of opinion,
wants, and costs that were to be incurred by those parties affected.  At times,
the Federal Govenment was obliged to increase its budget allocations in areas where-
immediate relief was necessaary and large losses- expected.

legislation, *Environmental control, *Water quality Act, *Water pollution control,
Federal Water Pollution control Act, Water Law, Rivers and Harbor Act, Clean Air
Act

*EPA, Public health service
                                         SS4

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417J

A COUNTER-PERSPECTIVE ON POLLUTION PROBLEMS,

Thomas, J. L.

Ohio University, Athens Ohio, Civil Engineering Department

Civil Engineering-ASCE, Vol. 44, No. 8, p 80-81, August, 1974.

A rebuttal to an article which criticized some environmentalists as prophets of
doom criticizes the following cases:  The Alaskan pipeline, nuclear power, Lake
Erie, pesticides, and economic considerations.  The author advocates a respectful
treatment of the present environmental conditions so as to prevent future ecological
disaster.

*Environmental control, Lake Erie, Pesticides, Economics, Nuclear powerplants

*0pinions, Alaskan pipeline
418J

ENVIRONMENTAL VALUES IN DECISION MAKING:  PORT JEFFERSON
AS A CASE STUDY,

Wells, J., and Hill, D.

Grumman Ecosystems Corporation

Environmental Sciences, Vol. 17, No. 4, p 19-28, July/August, 1974.
1 fig, 7 tab, 4 ref.

The National Environmental Policy Act of 1970 has increased the inclusion of
environmental values in natural resource decision making.  One way of
performing an environmental analysis of a certain course of action is
described.  Port Jefferson Harbor, Long Island, New York, is a delivery
point for petroleum products.  The harbor is not deep enough to accomodate
modern tankers.  The course of action evaluated is whether to dredge the
harbor to allow the large tankers to enter.  The method of analysis contains
the following steps:  establishment of a valid cost-effectiveness framework,
with emphasis on the extent of the geographical area affected; identification
of the environmental parameters that may be affected; preparation of a
qualitative summary of the effects of the alternative plans: on tfie environ-
mental parameters by reviewing the availaBle literature-; evaluation of the
nature of the environmental impacts as Beneficial or detrimental, also
considering countervailing effects and uncertainty; tabulation of tfiese
evaluations by alternative, geographic area, and type- of impact; and,
summarization and analysis of these tables: to determine patterns of environ-
mental impacts.  This analysis summarized in one chart the- complex, contro-
versial subject of the environmental consequence of dredging Port Jefferson
Harbor versus alternatives for delivering oil to the area.

*Planning, *Evaluation, *Decision making, *Environmental effects, Dredging,
Environmental control, New York
                                      885

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419J

STATUS OF CONSTRUCTION FOR ENVIRONMENTAL PROTECTION,

Kollar, K. L.

United States Department of Commerce, Washington, D. C.,
Water Resources and Engineering Program

Public Works, Vol. 105, No. 9, p 85-86, 128, September, 1974.  5 tab.

About $2.1 billion or one-third of the total amount spent on construction
in 1972 was involved in construction of water distribution and waste water
collection systems.  The total construction for public and private water
and waste water systems including treatment plants was about $3.2 billion.
The total spent on water and sewer utilities increased in 1973 to $3.2
billion.  The most significant growth of waste water disposal is a result
of the 1972 amendments to the Water Pollution Control Act.  There is a
steadily increasing market in the waste water field for construction
contractors.  However, no radical or rapid growth is expected for the next
few years.  Projections that have been made on future construction in the
waste water field, based on subjective evaluations of backlog requirements,
obsolescence and depreciation of already existing facilities, the rate
of population growth and the optimum population density that can be served,
are subject to future fundings.   The backlog for water supply systems can
be considered to be only five percent of the population.  Patterns of
housing construction will probably have the greatest effect on the static
water supply construction market.  The certification procedures for waste
water construction have been made more flexible and the local agencies have
been given more responsibility by the EPA.  The construction industry will
be faced with the problems present in our economy, those of shortages and
higher costs.

Construction, *Costs, *Facilities, Water supply, Sewers, Waste water
treatment, Water policy
420J

INTEGRATING WATER QUALITY AND WATER RESOURCES PLANNING,

Kruivak, J. A.

Office of Land Use and Water Planning, Department of the
Interior, Washington, D. C.

Proceedings of the American Society of Civil Engineers, Vol. 100, No. HY9,
p 1257-1262, September, 1974.

The basis for water resources planning and water quality planning are discussed.
Deficiencies in water planning relate to the fact that both water resource and
water quality planners often operate without information about the needs and
intentions of those who are planning for such things as land use, transporta-
tion, housing, and industrial development.  Evidence showing that movement
toward integrated water planning Is beginning includes the joint planning
programs and multiple-purpose water development plans formulated By various
land and water agencies together at the Federal level and the strong state
programs for water planning that have been encouraged by new Federal legis-
lation.  Problems of integrating water planning, in both quantity and
quality, are technical, behavioral, and institutional.  Suggestions for
improving water planning include:  a more coordinated and stabilized system
of intergovernmental relations; a more formal recognition of the positive
contributions available from citizen involvement in the decision-making
process; a formalization of procedures for determining the goals of water
planning; a better syntheses of the highly specialized but separated areas
of knowledge; and, more receptivity demonstrated by the planning profession
toward the desires of the public.

*Water resources development, *Water quality control, *Water policy, *Water
supply, Federal project policy, Project planning, Regulation, Multiple-purpose
projects, Legislation


                                       886

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 421J

 PLANNING METHODOLOGY  FOR THE DESIGN OF REGIONAL WASTE
 WATER TREATMENT SYSTEMS,

 Joeres,  D.  F.,  Dressier,  J.,  Cho,  C-C.,  and Falkner,
 C.  H.

 Wisconsin University,  Madison,  Wisconsin,  Department
 of  Civil and Environmental Engineering

 Water  Resources Research,  Vol.  10,  No. 4,  p 643-649,  August,  1974.   9  fig,
 1 tab,  16 ref.

 A mathematical  programming formulation has been developed to  obtain the
 optimum regional waste water treatment plan considering the trade-off  between
 economies of scale in waste water  treatment plants  and  the costs  of additional
 pipe network collection.   The computer model will select the  optimum plan
 when given  the  definition of all reasonable interceptor routes  connecting
 individual  communities,  local treatment  plant sites,  and associated maximum
 discharge potentials.   The mixed integer programing model relies  on
 piecewise linear approximations of  concave cost curves  and uses capacity
 limits  that are set by the maximum allowable environmental impact at
 potential treatment plant  sites.   The  model is demonstrated by  predicting
 the cost savings possible  for the  central  portion of  Dane County,  Wisconsin.

 *Waste  water treatment,  *Economies  of  scale, *Mathematical models,
 *Computer models,  Costs,  Pipes, Pipelines,  Decision making, Economics,
 Wisconsin
422J

SORTING OUT IRON IN WATER SUPPLIES,

Dart, F. J.

Ontario Ministry of Environment, Environment Association
and Planning Division, Chemistry, Water Technology
Section, Pollution Control Branch

Water and Pollution Control, Vol. 112, No. 8, p 26, 28, August, 1974.

Iron problems in water supplies must be thoroughly diagnosed to determine the
basic causes, or else remedial measures become expensive hit or miss proposi-
tions.  To find the problems of iron in the distribution system a series of
steps is given.  Electrolyte corrosion possibilities should be evaluated,
chemical corrosivity should be evaluated, and then the corrosivity potential
of the water through encouragement of bacterial activity should be determined.
It seems that well chlorinated waters with less than 0.15 mg/liter organic
nitrogen, less than 4-5 mg/liter total organic carbon, and less than
50-70 cu ft of asporator-extractable methane per 100,000 gallons do not
develop nuisance organism problems.  Electrolyte corrosion can usually be
corrected by standard techniques to remove the cause.  Chemical corrosiveness
can sometimes be corrected by increasing the water pK by adding soda ash or
lime; or the addition of lime or limestone contact retention might be an
alternative if the water hardness is low.  After measures to prevent iron
problems have been taken, the mains can be swab.b.ed with compressible foam
sponges to give the mains renewed lease for distributing clean water.

*Water quality control, *Water supply, *Water conveyance, *Iron, Aquifers,
Pipelines, Metal pipes, Corrosion,  Corrosion control, Hydrogen ion
concentration
                                       887

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423J

GROWTH OF SPIRULINA MAXIMA ALGAE IN EFFLUENTS FROM
SECONDARY WASTE-WATER TREATMENT PLANTS,

Kosaric, N., Nguyen, H. T., and Bergougnou, M. A.

Western Ontario University, London, Ontario, Chemical
and Biochemical Engineering Department

Biotechnology and Bioengineering, Vol. 16, No. 7, p 881-896, July, 1974.
10 fig, 2 tab, 12 ref.

The algae Spirulina maxima were grown in effluents from the secondary municipal
waste water treatment plant in London, Ontario, to investigate the factors
influencing the growth of the algae and the value of this treatment with
regard to nutrition (production of a biomass suitable for animal or human
consumption) and tertiary waste water treatment (nitrogen and phosphorus
removal).  There was a high yield of algae when the pH was adjusted to be
between 9 and 10; growth was drastically reduced at pH 11 and inhibited
below pH 8.  Higher light intensity improved growth and constant light also
improved growth.  The optimum temperature for growth was between 25 and 40 C
but the algae began dying at these extremes.  The nutritional quality of the
algae was acceptable.  The removal of nitrogen  was found to be much faster
than the removal of phosphorus.  Nitrogen tends to be the limiting factor in
Spirulina culture.  The removal of nutrients from waste water appears to
depend on the amount of algae in the culture, the initial concentration of
nutrients and the culture conditions.  The preliminary design of an algae
plant for treating sewage is presented.

*Algae, *Waste water treatment, *Tertiary treatment, *Nutrient removal,
Phosphorus, Nitrogen, Domestic wastes, Municipal wastes, Foreign research

Spirulina maxima, London, Ontario
424J

SOLUBILITY STUDIES OF METALLIC MERCURY IN PURE WATER
AT VARIOUS TEMPERATURES,

Onat, E.

Journal of Inorganic Nuclear Chemistry, Vol. 36, No. 9, p 2029-2032,
September, 1974.  3 fig, 2 tab, 24 ref.

A method employing ultraviolet spectrophotometry was developed for a direct
analysis of soluble mercury in aqueous solutions at various temperatures.
Soluble mercury is converted into mercurous form in the presence of mercuric
ions, and the absorbance of mercurous perchlorate measured at a wavelength
of 236.5 nm was utilized for the quantitative determination of mercury in
water.  A determination can be made of mercury in as small an amount as
3 x 10 to the minus seventh power g-atom/liter.   Twenty-three samples at
6 different temperatures were analyzed, with a s-tandard deviation from
compiled data of 0.004.  A solubility curve was  made on the basis of the
results of this experiment.  There was no indication of ionic dissociation
in dimeric mercury or of deviation from Beer's law.

*Mercury, *Solubility, Spectrophotometry, Ions,  Ultraviolet radiation

*Mercurous perchlorate, Ionic dissociation, Dimeric mercury, Beer's Law

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42 5 J

WATER QUANTITY AND QUALITY MANAGEMENT IN THE RUHR
VALLEY,

Imhoff, K. R.

Ruhruerband and Ruhrtalsperrenverein, Essen,
Germany

Journal of the Water Pollution Control Federation, Vol. 46, No. 7,
p 1663-1673, July, 1974.  11 fig, 18 ref.

An industrial zone has developed due to significant coal deposits and good
traffic conditions between the Ruhr, the Rhine and the Emscher Rivers.  About
80 million tons of coal are excavated and some 20 million tons of steel are
smelted in this area.  Water consumption and waste water flow is seven times
the West German areal average, necessitating special measures for water supply
and waste water disposal.  About 6 m of gravel has been laid on a tight layer
of rock by the Ruhr River., and the surface is protected against contamination
by one or two m of clay accumulation.  The filtered river water is purified
by aerobic biochemical processes in the gravel.  The water is potable after
a filter path of 50 m and retention time of one day.  For extra precaution,
0.4 mg/liter of chlorine is added to the water before it is pumped for
supply.  Rapid sand filters and chemical precipitation is sometimes used to
prohibit clogging of the low-rate sand filters.  Invariably, water is
artificially drained underground to equalize temperatures and gain more time
for pollution prevention.  It has become the legal task for the Ruhrtalsperren-
verein to control water quantity, and for the Ruhrverband to insure good quality
in the Ruhr basin.  The Ruhr has an average flow of 75 cu m/sec and a minimal
flow of 4 cu m/sec, being a relatively small river.  To compensate for water
abstraction, a system of reservoirs with a capacity of 470 mil cu m was
constructed.

*Water pollution, *Water quality management, *Industrlal wastes, Water supply,
Rivers, Sludge disposal, Biochemical treatment, Chlorination, Precipitation,
Water loss, Flow rates, Filtration, Groundwater recharge, Reservoirs,
Waste water treatment, Digestion tanks

*Rapid sand filters, Low-rate sand filters, Sulfuric acid regeneration,
Crystal separation
426J

NEW WATER WORKS FOR SUTTON,

Water and Waste Treatment, Vol. 17, No. 8, p 46, August, 1974.  1 tab.

The construction of a new water works at Grander Green Lane, Cheam, Great
Britain, is planned by the Button District Water Company to prevent pollution
and guard against bacterial pollution.  The process of super chlorination
followed by de-chlorination will sterilize the water.  A dose of chlorine
applied to the water at a borehole head as soon as it has been abstracted
from the borehole should prevent any danger of pollution.  As it travels
through a contact tank, the chlorine will have one hour to destroy organisms
present, and the excess chlorine will be removed by a dose of sulphur dioxide.
An addition of ammonia will make the remaining chlorine more persistent in
the distribution system and service reservoirs in corrosion prevention of
plumbing fittings and odor-taste pollution prevention.  Chlorine content will
be monitored, displayed and recorded by a chlorine residual recorder, which
automatically adjusts the residual chlorine being pumped into supply.  The
sterilization system will operate under a "fail-safe" principle, alerting
resident staff to quality control malfunctioning.  A 24-hour service will be
available for consumer problems with domestic plumbing.

*Water pollution, *Water quality control, *Bacterial pollution, *Chlorination,
Reservoirs, Domestic sewage, Boreholes
                                        889

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427J

CONDENSATE TRAPPING ALLEVIATES POLLUTION,

Fischer, J. A.

Electrical World, Vol. 182, No. 3, p 44-46, August 1, 1974.  2 fig, 1 tab.

A trap-drain condensate-reclamation system has been perfected by engineers at
the Public Service Electric and Gas Company, Burlington, New Jersey.  Operating
costs have since been decreased by $20,000, and the system now controls
pollution problems originating in plants where heating-system trap drains are
dumped into local waterways.  A unit was sought that would detect and prevent
contaminants from getting into the condensate-storage system during the
drain recovery.  A cartridge-type replaceable filter was examined for alerting
engineers to high levels of contaminants in the condensate.  The conclusions
reached by experimentation were as follows:  that about one-million gallons
could be filtered between cartridge changes in a unit designed for a
maximum flow of 100 gpm, where a. particle selection size would be one micron
with a cartridge outside diameter of 2.75 in.; that the cartridge filter would
retain fuel oil entrained in the condensate; and, that precoating would be
unnecessary for filtering the installation, although, it could lengthen the
required time between cartridge-element changes.  In the event of condensate—
reclamation system malfunctioning, the filter-differential alarm, conductivity
alarm, oil-detector alarm, power-failure alarm and high:-and-low-level alarms-
were installed as part of the continual operation.

*Water pollution, *Water quality control, *Water reuse, Oil pollution, Sludge
disposal, Drainage systems

*Condensate trapping, *Trap-drain condensate-reclamation system, *Heating-system
trap drains, Cartridge filter, Precoating
428J

CLASSIFYING INDUSTRIAL WASTEWATER EMISSIONS,

Williams, R. T.

Water and Sewage Works, Vol. 121, No. 7, p 86-89, July, 1974.  5 tab.

Fair sewage service charges, source control of users, and completion of
federal discharge permits are requirements which can be achieved by the
categorization of users.  Values given to waste water strengths for different
classes of usage are present in a large metropolitan system.  Results of the
Federal Water Pollution Control Act Amendments of 1972 are the requirement
for the identification of the type of user discharging to their system, the
establishment of limits on toxicants and the enforcement of pre-treatment
standards.  The East Municipal Utility District, treating Almeda County,
California, cities of Almeda, Albany, Berkeley, Emeryville, Oakland, and
Piedmont, consists of daily flows from an individual industry as much, as-
four mg/d.  A sampling program was initiated over a one-year period to develop
waste water strength Information for each Eusiness- classification code category.
A determination was made of the concentration of toxicants and heavy metals
with a goal of setting waste water limitations on customers.  This program
revealed that within a particular business classification code there is little
strength difference between large and small users for various parameters,
when compared to the strength differences between categories of users.  The
regulations developed by Special District #1 considered not only effluent
requirements and the degree of treatment removal, but also the proportionate
mass emission of all users.

*Waste water treatment, *Municipal wastes, *Effluent control, *Water pollution,
Federal Water Pollution Control Act Amendments of 1972, Industrial wastes,
Water quality management

*National Pollutant Discharge Elimination System, Business classification code,
Environmental Protection Agency
                                   890

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 429J

 WASTEWATER ANALYSIS  AND ITS  RELATION  TO  COMPANY
 PROFITS,

 Kern,  J. A.,  and Wilson,  R.

 Harnish and Lookup,  Associates,  Newark,  New York

 Industrial Wastes, Vol.  22,  No.  3,  p  26-28,  52, May/June,  1974.   8  fig,
 2  tab.

 In-plant  sampling and waste  water  analysis  to  estimate  the waste  water
 resulting from increased output  at  the Red  Wing Company of Fredonia,  New York,
 was  initiated  so that individual sources of waste water discharge could  be
 identified for individual control  and/or elimination.   The program  was
 divided into two parts:   an  extensive in-plant analysis of the individual
 process lines;  and,  the unit operation in each line.  The  sampling  included
 grab samples with measured flow, grab samples  with  estimated  flows, samples
 composited by  flow,  and samples  composited  with time.   To  double-check,  the
 total waste water loads  calculated  from  production  records were compared to
 the  results  of a second sampling program on the control plant effluent.
 The  production of jams,  jellies, peanut  butter, tomato  products,  grape juice
 and  grape products were  investigated.  On the  basis of  the individual unit
 process sampling results waste water  discharge was  accurately predicted  for
 a  particular day.  It was also determined which production operations result
 in large  waste loadings  and  which  do  not.   By  knowing the  individual  flows
 that attend  each process, it was possible to determine  when processing
 personnel became careless and discharge  more than necessary for given unit
 operation.

 *Waste water treatment,  *Water pollution, Industrial wastes, *Food processing
 industry, Sampling,  Discharge, Effluent  control

 *Jams, *Jellies, *Peanut butter, *Tomato products,  *Grape  products
430J

A CLOSE LOOK AT LONDON'S WATERS,

Surveyor, Vol. 143, No. 4278, p 39, June 7, 1974.

The Metropolitan Water Board was established as one of the first public bodies
of its type in Great Britain to appraise water quality matters there.  The
MWB itself established a Water Examination Department in 1905 which for years
has produced a reused water supply from water containing increased proportions
of purified sewage and trade effluent, of a safe quality and sufficient supply.
The supply has been derived from the Thame and Lee Valleys, comprising such
industrial areas as Luton, Oxford, Swindon and Stevenage.  MWB originated many
studies and new techniques based on an interest In water bacteriology.  Slow
sand filtration experiments showed how filters might be run at up to 12 m/day
without effluent quality deterioration; being double the rate of previous
practice.  An assessment of the amount of removal of phenols by slow sand
filters was made, resulting in the conclusion that to remove doses of
one mg/liter, a five day acclimatization Is necessary.  Phenol at 0.5 mg/llter
was removed on the first day, and 0.2 mg/liter with Meta Cresol.  In a five
day acclimatization about 7.5 mg/liter of the five phenols was removed.  More
experimentation was initiated in the treatment of water with ozone or chlorine
before filtration, apparently increasing degradability of organic chemical
bacteria.

*Water pollution, *Wat.er quality control, *Filtration techniques, *Effluent
wastes, *lndustrial pollution, Phosphate removal, Bacteriology, Reservoirs,
Chlorophyll, Phenols, Biodegradation

*Slow sand filtration, Meta Cresol, Partlculate carbons, Ammoniacal nitrogen
                                       891

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431J

FUTURE OF DESALTING IS BRIGHT BUT COSTS MUST DROP,

Heckroth, C. W.

Water and Wastes Engineering, Vol. 11, No. 7, p 20-23, 52-54, July, 1974.
15 fig.

Desalting is appearing as a viable means for increasing water and/or raising
water quality.  More than 800 desalting plants of 25,000 gpd capacity or
greater are in operation or under construction in the United States and other
countries.  The technology is expanding at a rate that should double or triple
the total production of fresh water by the end of the 1970's.  Distillation
processes are the most widely used methods for desalting.  Distillation is
used almost exclusively for desalting sea water; membrane processes are used
entirely for desalting brackish water.  The handicap to the increased use of
desalting is the costs associated with, this method.  Information is presented
on the costs of desalting techniques such as electrodialysis, reverse osmosis,
and ion exchange.  The costs of desalting can be reduced through:  improvement
of desalting technology, such as development of longer-lived and more effective
membrane for reverse osmosis; reduction in the cost of energy perhaps by
operating on interruptible power; more efficient use of energy by using the
heat generated from a nuclear or fossil fueled power generating plant;
economies of scale, and, the economic breakpoint beyond which the cost of
additional capacity becomes essentially constant; and, staged construction
utilizing desalting plants that are built in modules and schedules to meet
increases in uses.

*Desalination, *Costs, *Potable water, *Water quality, *Water supply,
Ion exchange, Reverse osmosis, Distillation, Separation techniques,
Economies of scale
432J

LONDON WATERS,

Aqua, No. 2, p 37-39, 1974.

The contents of the fifty-fourth report by Dr. E. W. Taylor on the
bacteriological, chemical and biological examination and treatment of the
London waters and research performed during 1971-1973 are presented.  Section
I of the report pertains to the bacteriological quality of the water supply;
E. coli was not detected in any of the samples of water collected from pumping
out mains at the filtration works and well stations.  Section II is a history
of the Water Examination Department which spans nearly 70 years.  Section III
discusses visits to the laboratories.  Section IV outlines the activities
of the Bacteriology Section which during this time were largely concerned
with the microbiology of slow sand filters.  Section V explains the work of
the Virology Unit.  The detailed and comprehensive analyses of samples from
the Thames and Lea rivers by the Chemistry Unit are detailed in Section VI.
The biological state of the rivers and principal storage reservoirs described
in Section VII indicates that algal growth is being controlled by regular
biological surveys and reservoir management.  The chemical treatment, which
is mainly chlorination, used at the Board's filtration works and well
stations is the topic of Section VIII.  The details of the quality of the
water in the distribution system are given in Section IX.  Section X compares
the current methods for determining color and turbidity with the new method
which uses an absorptiometer; an absorptiometer can measure color and
turbidity simultaneously.  Section XI covers the problems that might occur from
the introduction of new materials that may cause a deterioration of water
quality.

*Water quality, *Potable water, *Bioassays, Chemical analysis, Chemical
treatment, Bacteria, Bioindicators, Filters, Chlorination

London, Great Britain, Thames river, Lea river
                                      392

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 433J

 THE TOXICITIES  OF SEWAGE EFFLUENTS,  INDUSTRIAL DISCHARGES
 AND SOME CHEMICAL SUBSTANCES  TO BROWN TROUT (SALMO TRUTTA)
 IN THE  TRENT RIVER AUTHORITY  AREA,

 Woodiwlss,  F. S., and Fretwell, G.

 Trent River Authority,  Great  Britain, Pollution
 Control and Fisheries Department

 Water Pollution Control, Vol. 73, No. 4,  p 396-405, 1974.  3 fig,  13 tab,
 3 ref.

 An intensive investigation resulted  in the conclusion that  unidentified complex
 organic compounds originating at the chemical manufacturing industry around
 Loughborough were killing the fish population in the lower  part of the Soar
 River,  a tributary of the Trent. A  toxicity test was developed between
 1965-1969 for an examination  of the  effluents in the Trent  River Authority
 area.   A modified version of  the Standard test recommended  by the  Ministry
 of Housing  and  Local  Government involved  the following procedures:  the test
 species was changed from brown trout to rainbow trout because of the availa-
 bility  and  the  standard length of 60 and  150 mm for the tested fish.; the
 temperature used during the tests was Increased from 10 degrees C  to 15 degrees
 C because of easier attainability; and, the dilution water  was standardized,
 with a  choice of either hard  C250 mg/ltter)  or soft (25 mg/llter)  water being
 recommended so  that the one can be chosen which most closely- approximates
 the receiving water.   Several industrial  waste water discharges to sewers-
 were tested on  behalf of sewage works to  trace. tKe. taxietty source in their
 effluents,  or the cause of operational problems such as the inhibition of
 sludge  digestion and  the reduced efficiency of aerobic processes.

 *Water  pollution, *Effluent control, *Fish kills,  industrial wastes,
 *Chemical pollution,  *Trout,  Rivers, Toxicity, Sewage effluents

 *Trent  River Authority, Rainbow trout, Brown trout


 434J

QUALITY CONTROL  IN  RIVER MANAGEMENT  OF  THE BRISTOL
AVON,

Ingham,  G. S. N.

Bristol Avon River  Authority,  Great  Britain

Water Pollution  Control, Vol.  73, No.  4, p 425-432,  1974.

The River Avon and  its  tributaries receive 200 x 1000  cu m  of  sewage effluent,
335 x 1000 cu m  of  industrial waste water, and an unknown volume of effluent
from about 4000  farms roughly estimated as 15  x 1000  cu m daily.   The  river
system carries an estimated effluent  load of 550 x  1000  cu  m/d DWF.  Quality
control is required on  a closely detailed scale, since each section of  the
river receives direct effluent,  influencing  the next  downstream section,
and being itself  Influenced by its adjoining upstream  stretch.  Quality
control necessitates  flow and quality  data at  or near  the source of every
river and tributary;  flow and quality data at strategic points down the  river
or tributary to  its confluence;  flow  and quality data  of all important
effluents discharged  into each river; and, the locations and quantities  of
abstractions.  From such data the following becomes  available:  maximum,
minimum, mean and median for  flow and  quality  parameters, and  the  standard
deviation of all  parameter values; effluent  effects  and  their  location;
recovery rate; pollution load carried;  maximum pollution load  safety
carriable; extent to which overloading  occurs; extent  to which effluent
regulations are  applicable; identification of  lengths where there  are unknown
discharges;  abstraction  effects; extent of abstraction restrictions needed;
and, the extent  to which abstraction  is possible.

*Water quality management, *Water pollution, *Industrial wastes, *Waste water
treatment, Rivers,  Flow  characteristics, Effluent control, Water reuse,
S elf-puri fi cat i on

*Bristol Avon River Authority, Pollution Prevention Acts, Rivers Act (1961)


                                        893

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435J

POLLUTION AND PUBLIC HEALTH:  TACONITE CASE POSES
MAJOR TEST,

Carter, L. J.

Science, Vol. 186, No. 4158, p 31-34, 36, October 4, 1974.  1 fig.

Lake Superior has for the past 18 years been polluted by the wastes of the
Reserve Mining Company.  The Lake, which was once considered of such purity
that Duluth, Minnesota, among other cities, used its water for drinking, is
the largest body of freshwater on earth-350 miles long, 160 miles across at
its widest, and up to 1333 feet deep.  The lake, however, is not large enough
to assimilate the Reserve's discharge of taconite tailings; the discharge
being fivefold greater than the 12,000 tons of solids estimated to enter
naturally each day from the inflow of about 200 rivers and the erosion of
miles of shoreline.  The tailings have despoiled some 200 square miles of the
west end of the lake.  The tailings delta extends 4000 feet offshore from
the discharge point, being nearly a mile wide.  The tailings have settled
at the bottom over large areas, smothering benthic organisms and harming the
ecology of the lake.  The green water phenomenon occurs over many miles of
the lake when large quantities of light-reflective tailings surface.  Last
year it was determined that tailing fibers indistinguishable from amphiobole
asbestos fibers were present in Duluth drinking water.  A high incidence of
cancer occurs among persons exposed to asbestos in their jobs and in the
environment, giving a federal suit against the Reserve new impetus.

*Lake Superior, *Water pollution, *Public health, *Mining, *Mine wastes,
Asbestos, Potability, Benthos

*Taconite tailings, Cancer
436J

PHOSPHORUS DETERGENT BAN-HOW EFFECTIVE?,

Pieczonka, P., and Hopson, N. E.

Water and Sewage Works, Vol. 121, No. 7, p 52-55, July, 1974.  1 tab, 10 ref.

The eutrophication rate of a lake is greatly increased by the addition of
more nutrient, such as phosphorus.  A study in Erie County, New York,
attempted to answer basic questions in phosphorus detergent pollution from
domestic sewage.  What percentage of phosphorus reduction could be expected
in the influent of a sewage treatment plant treating domestic wastes, and
what would an effective ban of phosphate detergents have on sewage treatment
costs were the primary questions explored.  In domestic sewage, the average
phosphorus content is about 10 mg/liter.  The rate limiting concentrations
of phosphorus is about 0.01 mg/liter.  It was determined that the enactment
of a ban on the detergents would not solve the problem of eutrophication.
Phosphorus removal in waste water treatment plants was required.  The
Lackawanna Sewage Treatment Plant was investigated for further solutions.
Composite grab samples were studied for total phosphorus in accordance with
the Standard Methods for the Examination of Water and Wastewater.  A
stannous chloride technique and total phosphate determination were utilized
for all phosphorus analyses.  It was concluded that phosphorus detergent
bans reduced phosphorus loading at a domestic sewage, plant by 55.7 percent,
although the banning is insufficient for fighting this pollution problem
alone.

*Phosphorus, *Detergents, *Water pollution, *Sewage treatment, Domestic
sewage, Effluent control, Eutrophication, Lakes

*Stannous fluoride treatment
                                      894

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437J

CONTROL OF WATER POLLUTION:  MISCELLANEOUS
PROVISIONS,

International Digest: of Health Legislation, Vol. 25, No. 1, p 50-60, 1974.

The Water Resources Management Act of 1972 and the Department of the
Environment Act of 1972 are expected to become laws in Canada simultaneously.
The latter act repeals the Water Resources Commission Act as amended.
Pollution is defined as any change in the temperature, taste, or odor of
Saskatchewan waters; the addition or removal of any liquid, solid, radioactive,
gaseous, or other substance that will be harmful to the public health or that
is unsafe for domestic, municipal, industrial, agricultural, recreational,
or other lawful usage or that is detrimental to wildlife, birds, or aquatic
life, or sewage containing animal, vegetable or mineral matter in suspension
or solution, including rainwater resulting from melted snow or ice which has
entered the sewage works.  The Minister of the Environment is made responsible
for administering the water resources of Saskatchewan and supervising all
pollution matters.  The Minister is also responsible for the g.neral supervi-
sion, control, and regulation of all matters concerning waterworks, sewage,
water quality, and its impairment.  The municipality's medical health officer
is to advise the Minister on matters of public health relating to water and
sewage.

*Water laws, *Public health, *Water pollution, *Water quality management,
Suspended solids, Toxicity, Wildlife, Birds, Aquatic life, Industrial
wastes, Sewage, Discharge, Radioactivity

*Saskatchewan water resources, The Water Resources Management Act,
The Department of the Environment Act, Canada
438J

INVESTIGATION FOR THE MARINE DISPOSAL OF EFFLUENTS,

Staples, K. D.

J. D. and D. M. Watson, Consulting Engineers,
Great Britain

Water Pollution Control, Vol. 73, No. 4, p 417-424, 1974.

Marine disposal should be undertaken as economically as possible consistent
with the proper protection of the public health, as well as the minimum damage
to amenity, recreational and industrial use of the receiving waters and the
minimum waste of natural resources or disruption of the environment.  The
inland disposal of polluting discharges must inevitably mean disposal into
the sea, since waters flowing through almost all lakes, streams and rivers
eventually reach the seas.  The oceans, it can be assumed, have become
progressively polluted with a variety of chemical salts present in the sea;
amounting to some 34,000 ntg/liter total dissolved solids.  In considering the
oxidation capacity of the sea, it should be observed that many of the naturally
derived chemicals occurring in waste discharges are amenable to sea degradation;
acids and alkalis being rapidly dispersed by the sea, while toxics such as
phenols and cyanide compounds are rapidly degraded if prior to discharge they
have been properly diluted.  Buoyant materials are not easily broken down,
and by surface wind action are liable to return to the shoreline, creating
unsightly pollution.  The greatest amount of pollution is. discharged in
solution or colloidal suspension, including the liquid fraction of sewage
and industrial wasstes.  Stable toxins: must not be discharged except as trace
contaminants.

*Water pollution, *Effluents, *Sea water, Phenols, Cyanide, Toxicity, Colloids,
Suspended solids, Discharge, Sewage disposal, Coastal areas, Industrial wastes,
Oxidation, Chemical pollution, Dissolved solids

*Marine disposal systems,  Buoyant materials,  Settleable solids, Intermediate
solids
                                  895

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439J

WATER REUSE... SAFE DRINKING ACT. . .HOW SOON. . .HOW GOOD?,

Heckroth, C.

Water and Wastes Engineering, Vol.  11, No. 8,  p 32, 34, 36-37, August, 1974.

This year's American Water Works Association annual meeting considered the
rising problems in the area of water use, reuse, master planning, dual systems,
and the unpopular Safe Drinking Water Act.  Representative Peter Kyros of
Maine explained that the delay of the Act was  due to the area of chemical
contamination and the need for funds.  Studies and adequate monitoring have
been needed, and these "deficiencies give rise to technical uncertainty, which
in turn impacts on our concern about having the EPA make judgments which will
cause state and local governments to pour out  large sums of money to clean up
water supplies."  Congressmen are unsure as to whether enforcement, monitoring
and reporting should rest with the  states with no power of coercion for the
federal government if the states should fail to take proper measures.  They
are also unsure as to whether standards be set for tap water without providing
operation and maintenance requirements.  There is some question as to the
availability of state funds to meet federal regulations.  The administration's
bill makes no provision to control  underground injection of contaminants.
Water supply administrators were seriously criticized.  It was claimed that the
most difficult metals to remove are arsenic,  lead, cadmium and barium.  Metal
removal appears to function according to the efficiency of the activated sludge
system nitrification.  An increase  in some metals has been attributed to
chemical treatment.

*Water pollution, *Water reuse, *Water laws,  *Federal government, *State
governments, *Potability, Chlorination, Chemical treatment, Water purification,
Toxicity, Heavy metals

*Safe Drinking Water Act, Environmental Protection Agency, American Water Works
Association
440J

ACCOMMODATING TO NEW IMPERATIVES IN WATER-POLLUTION
CONTROL,

Cleary, E. J.

Cincinnati Medical Center University, Cincinnati,
Ohio

American Water Works Association Journal, Vol. 66, No. 7, p 437-440,
July, 1974.  6 ref.

Legislation stemming from hearings and debates during 1970-72 has resulted in
the most comprehensive, complicated, and expensive program for protection of
the environment ever conceived.  A shift in policy was represented by the
rejection of the idea that control of waste water discharges should take into
account the uses and assimilative characteristics of a waterway.  The
application of this strategy depended upon the establishment for each waterway,
quality standards reflecting an appraisal of local social preferences as well
as a balancing of costs and benefits of achieving those standards.  Limitations
were set for individual waste discharges.  An unsatisfactory performance on
the part of both state and federal authorities, along with the legal complica-
tions of enforcing compliance with standards based on ambient-quality condi-
tions, necessitated PL 92-500.  Environmentally, what may be gained from the
elimination of waste residuals from waterways, would be lost in air-and-land
deterioration, as well as increased energy consumption.  Critics of PL 92-500
are skeptical as to how properly the federal bureaucracy will handle the
establishment of national effluent standards.  State regulatory agencies see
themselves as being arbitrarily subjected to the directives, guidelines,
timetables and procedural details of the federal government.  Generally,
PL 92-500 does not appear to promote expedient implementation.

*Water pollution, *Federal Water Pollution Control Act, ^Legislation,
*Discharge, Effluents, Ecology, Federal government

*Environmental Protection Agency
                                  896

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 441J

 THE WORLD'S  LARGEST DESALTING COMPLEX—A REPORT  ON
 TWENTY YEARS EXPERIENCE,

 Reside,  J.,  and Al-Adsani,  A. M.  S.

 Water Resources Development,  Kuwait,  Arabian Gulf

 National Water  Supply  Improvement Association Journal,  Vol.  1, No.  1,
 p 1-14,  July 1974.   1  fig,  3  tab, 4 ref.

 The country  of  Kuwait  is  the  largest  producer of desalted water  in  the
 world.   Kuwait  presently  has  65 mgd of  desalting plant  capacity  and plans
 another  12 mgd  by  1975.   The  first municipal desalting  plant was built
 in 1953.  The original desalting  units  were  the  submerged tube type
 distillation process.  The  first  multistage  flash desalting  plant was
 installed in 1960.   Currently there are three main  plant sites with 24
 individual desalting units  distributed  among them.   The units have
 capabilities ranging from 0.6 to  6.0  mgd.  The design,  operating
 procedures,  and experiences of these  units are described.  The by-product
 recovery and water  distribution systems are  also described.  By-products
 produced include hydrogen,  chlorine,  sodium  hydroxide,  sodium chloride, and
 hydrochloric acid.   Chemical  treatment  used  to reduce the scale  formation
 in the desalting units consists of a  mixture of  tri-polyphosphate,
 lignum sulphonate  and  anti  foam.   The plants are cleaned manually by
 water washing and  by rods and brushes or  they can be cleaned by  acid
 washing.  The advanced use  of desalting technology  in Kuwait has made
 available an inexpensive  supply of electricity and  potable water from
 the sea,

 *Desalinatlon,  *Potable water, *Foreign research, *Desalination  processes,
 Desalination apparatus, Desalination  plants, Descaling, Desalination
 wastes,  Water supply,  Distillation, Flash distillation, Electrodialysis,
 Evaporators

 *Kuwait
442J

SIMULATION AND STATISTICAL QUALITY CONTROL FOR WATER
POLLUTION ABATEMENT,

Phantumvanit, D.

Texas A and M University, College Station, Texas

Dissertation Abstracts International B, Vol. 35, No. 4, p 1682, 1974.

The increases in water pollution problems and in the public demands for
high quality water necessitates the proper management of regional water
quality systems.  To assist in the management of the stochastic nature
of a regional water quality system the following were developed:  a
model of the reliability associated with the system goals; programs
describing the system management strategies; and a sensitivity analysis
to provide planners with alternative solutions subjected to changes
in water quality requirements.  Operating characteristics curves
were formulated for major waste water treatment plants.  These curves
illustrated the relationships between the quality of treated waste
effluent quality and regional water system reliability and also the
impact of each waste water treatment plant on regional water quality.
The overall process efficiency distributions for major waste water
treatment plants were discussed and described by some standard distri-
butions .

*Water pollution abatement, *Water quality control, *Waste water treatment,
*Management, Operation, Planning, Model studies, Theoretical analysis
                                     897

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443J

A PRACTICAL APPROACH TO WATER QUALITY MANAGEMENT
PLANNING,

Peavy, H. S.

Oklahama University, Norman, Oklahoma

Dissertation Abstracts International B, Vol. 35, No. 4, p 1706, 1974.

An approach to water quality management planning is presented which
provides for the protection of water quality without placing undue
stress on state agencies planning and monitoring resources.  The
approach is designed to meet the requirement of federal and state
statutes on water pollution control.  A model plan was prepared for a
river basin in Oklahoma using data available through the state pollution
control agencies and local governments.  The plan included:  a description
of the natural characteristics which would aid in understanding the problems
relating to natural quantity and quality of the waters within the particular
basin; an assessment of the current quality of the basin's surface waters
and an analysis of the waste load presently imposed; and, the selection
of two models which appeared to sufficiently represent waste assimilative
characteristics and which required data that could be easily obtained.
The models were calibrated by field studies to more closely approximate
reactions in Oklahoma streams and then were used to estimate the maximum
amounts of waste which each discharger can release into the receiving
stream without violating the water quality standards.

*Water quality control, *Planning, *Water pollution control, *Model studies,
Effluents, Standards, Monitoring, Waste water disposal, Oklahoma
444J

COMPLYING WITH DISCHARGE REGULATIONS,

Schafer, C. J.( and Lailas, N.

Environmental Protection Agency,
Washington, D. C.,
Office of Water Enforcement

Environmental Science and Technology, Vol. 8, No. 10, p 903-906, October
1974.  1 fig, 2 tab.

Under the new national permit system for pollutant discharge, the National
Pollutant Discharge Elimination System, all industries and municipalities
must limit their point source effluent discharges into navigable waters.
The permit to be issued has a compliance schedule and monitoring re-
quirements.  Target dates are July, 1977 for "best practicable control
technology currently available", and July, 1983 for "best available treatment
economically achievable", as part of the Federal Water Pollution Control
Act Amendments (PL 92-500).  The legislation gives Environmental Protection
Agency administrators the responsibility of publishing regulations with
guidelines for effluent limitations.  Compliance schedules contain dates
for the preparation of engineering reports, planning and completion of
construction, and the operation of waste water treatment facilities.
Permits will be issued for fixed terms, the maximum duration being five
years.  The permits must specify self-monitoring requirements for a
facility including sample type, frequency of analysis, and frequency of
reporting to the regulatory agency.  Discharges will be reported by each
municipality of industrial facility on a "Monitoring Discharge Form",
recording minimum, average, and maximum values in terms of quantity and
concentration, representing a 24-hour day, as obtained from the analysis
performed.  It will be the responsibility of the permittee to notify the
EPA regional administrator if he cannot comply with effluent limitations at
any time.

*Discharge (water), *Federal Water Pollution Control Act, *Effluents, legis-
lation, Planning, Analysis, Monitoring

*Permits, Environmental Protection Agency


                                   898

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 445J

 SMOKE TESTS DETECT SOURCES OF ILLEGAL INFLOW,

Welker, F.  S., and Miller, D. J.

Department  of Sewers, Cincinnati, Ohio

Public Works, Vol. 105, No. 9, p 90-91, September, 1974.

The method  that the Metropolitan Sewer District of Greater Cincinnati used
to correct  the problem of  illegal connections to its sanitary sewers is
described.  The method employed by the Department of Sewers was to smoke
test the sewers.  Before the  tests were conducted, the sewers were visually
inspected and residents of the area to be tested were notified of the
test to prevent anyone from becoming alarmed at seeing any smoke.  Fire
departments were also alerted.  The tests were performed by sealing off
a manhole and pumping smoke through the area of the line being tested.
Any groundsmoke observed would indicate a cracked main sewer pipe or
customer service laterals, illegal downspouts, or outside drains connected
to the sanitary line.  Notices were sent to property owners notifying them
of any connections they had in violation of the established rules of the
Sewer Department.  A four-man crew, on a typical day, was able to smoke test
1907 feet of sewer lines at a total cost of $0.063 per foot.

*Sewers, *Sewerage, *Smoke, *Separated sewers, Testing, Sanitary engineering,
Manholes, Domestic water, Pipelines, Pipes

Smoke-testing
446J

NEW ATTITUDES TO WASTE TREATMENT,

Hughes, D. E.

University College, Cardiff, Wales, Department of
Microbiology

Journal of Applied Chemistry and Biotechnology, Vol. 24, No. 6, p 373,
June 1974.

The proposal that all wastes should be considered as raw materials which
can be re-used or recycled is discussed.  Organic wastes can be considered
as stored potential energy derived from sunlight and as a store of
negative entropy.  This negative entropy should be maintained at as high
a level as possible; this can be achieved by maintaining the redox state
of organic wastes (keeping them reduced).  If the idea of converting
domestic wastes to useful products is accepted then the thinking about
sewage treatment systems will have to change.  The efficiency of sewage
treatment systems is now considered as the maximum of BOD oxidised to
carbon dioxide and water with the minimum of sludge production.  If
biomass is to be considered as a viable source of raw material then the
kinetics must be changed to give the maximum of biomass produced per amount
of BOD oxidised.

*Waste treatment, *Foreign research, *Sewage treatment, *Recycling,
Organic wastes, Biochemical oxygen demand, Entropy, Energy
                                        399

-------
447J

LASL WASTE SYSTEM BACKS UP INTO STREET,

Nuclear News, Vol. 17, No. 13, p 106, October, 1974.

Radioactive wastes resulted from the spilling of a sewer line twice at
Los Alamos Scientific Laboratory in July and September, 1974.  Both times
the line carrying waste water with low-level concentrations of plutonium
one and a half miles to a reprocessing plant backed up, ruptured, and spilled
water into nearby streets.  The waste was considered low-level, but might
be high-level as an environmental pollutant.  During the first incident,
waste trickled into the ground near the point of rupture.  The second
time hundreds of gallons of waste were sent up through a manhole, along
a gutter, into a sewer intake, and finally into a dry canyon.  Waste
penetrated the sandy soil of a dry bed, one to two feet wide, to af depth
of a few inches.  Cleanup of the radioactive wastes entailed removing the
contaminated soil to a burial area and asphalting the street.

*Radioactive wastes, *Sewers, Waste water, Pollutants, Environmental
effects, Contamination, Pathways of pollutants

*Spills, *Plutonium
448J

FLOOD HAZARD REPORTS:  TOOLS FOR RESOURCE
PLANNING AND MANAGEMENT,

Ringler, T. A., and Kennaugh, J. H.

Soil Conservation Service, United States Department of
Agriculture, Grand Rapids, Michigan

Journal of Soil and Water Conservation, Vol. 29, No. 4, p 182-185,
July/August, 1974.  2 fig, 8 ref.

The mechanics and advantages of flood hazard reports are discussed.
Flood hazard studies consist of two major technical reports.  The
flood plain areas subject to flooding by select-frequency floods are outlined
on aerial photomosaics and soil survey information that identifies the
different types of soils within the flood-plain and its surroundings are
also shown on the photomosaic maps.  The reports contain soil descriptions
and interpretative data.  Flood hazard reports provide local and state
governments and community residents with a technical basis for carrying
out flood-plain management programs.  Suggested nonstructural measures
for flood-plain management resulting from legislation and flood hazard
reports include flood-plain zoning ordinances, flood-plain development
regulation, flood-plain filling regulation, flood insurance program,
open space acquisition, upstream land treatment, and regional land use
planning.  Structural corrective measures include runoff-retarding dams,
levees or walls, channel improvement, and flood-proofing.  The key to
developing technical data for flood planning programs is cooperation
between city, county, regional, state, and federal agencies.  Successful
metropolitan resource management programs must ignore political boundaries.

*Flood plains, *Flood forecasting, *Flood data, *Flood control, Flood
plain zoning, Flood plain insurance, Flood protection, Legislation,
Regional flood, Planning, Management

Flood plain management, Flood hazard reports
                                   900

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449J

DIFFERENCES BETWEEN PLANNED AND ACTUAL COSTS AND
BENEFITS IN SMALL WATERSHED DEVELOPMENT,

Button, J. D.

Natural Resource Economics Division, Economic Research
Service, United States Department of Agriculture,
East Lansing, Michigan

Soil and Water Conservation, Vol. 29, No. 4, p 165-168, July/August, 1974.
4 tab, 4 ref.

Water resource planners design projects on the basis of future benefits;
the discounted future benefits must exceed the economic costs.  The
difficulty in planning is that many of the costs and benefits do not
become apparent until several years after planning, therefore the variables
that relate to the costs and benefits must be projected.  Evaluations
of projects several years after they have been in operation allows an analysis
of the planning process and supplies a way to perfect future planning.
Four completed small watershed projects that had operated for four to
five years were evaluated by qualitatively comparing current values of
primary costs and benefits with planners' estimates and identifying reasons
for divergences between planned and achieved values.  The results indicated
that planners should encourage local involvement in planning; analyze
socioeconomic trends at the project and river basin levels; and, use
a multiobjective planning approach to reduce the difference between the
planned estimates and the actual values.  The projects were largely
considered to have no effect on the environment.  Beauty of the area
involved was most often considered improved.  In areas where the natural
streams were channeled negative responses were received for the effects
on hunting, fishing, and wildlife cover.

*Water resources development, *Watershed management, *Projects planning,
*Environmental effects, Cost-benefit analysis, Cost-benefit ration, River
basin development
                                     901

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                        RADIOACTIVE WASTES
00 IK

ON THE SELECTION OF A GROUND DISPOSAL SITE BY SENSITIVITY
ANALYSIS,

Morisawa, S., and Inoue, Y.

Kyoto University, Dept. of Sanitary Engineering,
Kyoto City 606, Japan

Health Physics, Vol. 26, No. 3, p 251-261, March, 1974.  4 fig, 6 tab, 21 ref.

Desirable conditions for ground disposal of radioactive wastes and the approx-
imate method for estimating the internal dose are discussed through the use
of sensitivity analysis.  Eighteen out of 26 factors in the three ecological
paths through which leaked radionuclodes migrate are quantitatively examined
by sensitivity analysis with relationships between the internal dose and
studied factors tabulated.  The difference between strict calculation and
approximation of internal dose is also examined.  Said approximation is shown
to be useful for the quick estimation of the safety of a site for the ground
disposal of radioactive wastes.

*Radioactive Wastes, *Radioactive Waste Disposal, *Approximation Method,
*Estimating, Underground Waste Disposal, Radioisotopes, Mathematical
Studies, Analytical Techniques

*Sensitivity Analysis
00 2K

IMPROVED CONTROL OF RADIOACTIVE WASTES,

Stubble-field, F. E. and Jackson, E. G.

U. S. Atomic Energy Commission, Bethesda, Md.

Certification of Engineers, Vol. 70, No. 3, p 87-88, March, 1974.  3 fig.

Improved control methods for solid and liquid radioactive wastes are described
at the Hanford plant of the U. S. Atomic Energy Commission at Richland,
Wash.  Previously, solid wastes were buried as received with no provisions
for retrievability.  The expansion of land use at a rate of 3.7 acres/yr
necessitated the following improved procedure:  segregate transuranic con-
taminated waste from other radioactive waste; segregate combustible and
noncombustible transuranic waste; package the transuranic contaminated waste
in retrieval type packages, and store in soil such that retrieval of con-
tamination free packages can be accomplished for at least 20 yr after ini-
tial storage; implement volume reduction measures at the generation facility;
implement improved land utilization; consolidate sites where practical,
thus releasing land areas from contamination restriction.  Liquid wastes
were previously discharged to ground disposal sites, on surface ponds or
swamps, or to subsurface structures (cribs) depending on the amount of
total radioactivity.  The improved method involves:  process changes in-
cluding the addition of effluent treatment facilities to minimize the
amounts of ardioactivity in stream; diversion facilities; and storage of
plutonium containing streams in tanks.

*Radioactive Waste Disposal; *Radioactive Wastes, *Liquid Wastes, Solid
Wastes, Waste Storage

Plutonium, Uranium
                                             902

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003K

ENVIRONMENTAL EFFECT OF A COMPLEX NUCLEAR FACILITY,

Bebbington, W. P.

E. I. Du Pont de Nemours and Co., Aiken, S. C.

Certification of Engineers, Vol. 70, No. 3, p 85-86,  March, 1974.  1 fig.

The storage and disposal of liquid wastes from the Atomic Energy Commission's
Savannah River Plant are described in a discussion of the environmental
effect of a coraplex nuclear facility.  Most of the solids in the highly
radioactive liquid wastes from the separations processes are nonradioactive
salts containing aluminum and inorganic reagents.  Sodium hydroxide is added
and the volume of the alkaline waste is as much as 100 times that generated
in the power reactor fuel cycle.  This alkaline waste is stored underground
in carbon steel tanks, most of which are enclosed in wholly or partially
steel lined concrete vaults.  Hydrated iron, manganese, and aluminum
oxides occur as a sludge that settles from the waste and contains nearly
all of the strontium-90.  Sludge from several tanks  has been combined
into one tank.  This supernatant liquid contains nearly all of the cesium-137.
This solution is concentrated in evaporators, several tanks are now being
filled with the resultant crystalline salts.

Liquid Wastes, Environmental Effects, Nuclear Wastes, Salts, Waste Storage,
Waste Storage, Sludgy Storage, Storage Tanks
004K

CONTENT OF PLUTONIUM IN RIVER WATER IN JAPAN,

Miyake, Y., Sugimura, Y., and Saruhaski, K.

Meteorological Research Institute, Tokoyo, Japan

Papers in Meterology and Geophysics, Vol. 24, No. 1, p 75-78, March, 1973.
1 fig, 1 tab, 6 ref.

The content of plutonium in the water of eight main rivers in Japan was deter-
mined.  The average value of the total content of plutonium is 0.0014pCi/llter
in which 0.004 pCi/liter is contained in the suspended matter.  The annual
runoff plutonium is only 0.12% of the accumulated plutonium on land.  This
suggests that the fallout plutonium is firmly adsorbed on soil surface and
is difficult to leach out.

*Rivers, *Radioactive Wastes, Fallout, Water Pollution, Investigations

*Japan, *Plutonium
                                       903

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005K

THORIUM ISOTOPE CONTENT IN RIVER WATER IN JAPAN,

Miyake, Y., Sugimur, Y., and Yasujima, T.

Meteorological Research Institute, Tokyo, Japan

Papers in Meteorology and Geophysics, Vol. 24, No. 1, p 67-73, March, 1973.
1 fig, 6 tab, 6 ref.

The concentrations of thorium isotopes Th232, Th230, and Th238 were determined
in the river water collected at 10 main rivers in Japan.  The concentration of
dissolved Th232 in river water was one order of magnitude higher than that
in the Pacific surface waters.  The weighted averages were 2.7 times 10 to
the minus 8th power g/liter for Th232 and 2.8 times 10 to the minus 13th g/liter
for Th230.  The constancy in Th232 and Th230 concentration with time was ob-
served, but the concentration of Th238 in river water was quite variable.
Accordingly, the Th238/Th232 activity ratio showed a wide range of variations
from 37 to 0.65 during the period of study.

*Rivers, *Isotope Studies, Radioisotopes, Radioactive Wastes, Investigations,
Analysis, Analytical Techniques, Water Pollution

Japan, Thorium
006K

PREPARING EFFLUENT RELEASES FROM NUCLEAR AND FOSSIL-
FUELED POWER PLANTS,

Hull, A. P.

Brookhaven National Laboratory, Upton, New York,
Health Physics and Safety Division

Nuclear News, Vol. 17, No. 5, p 51-55, April, 1974.  12 fig, 2 tab, 21 ref.

Airborne effluent releases from nuclear power plants are compared to those
from fossil fueled power plants.  Yearly over all average amounts of gaseous,
halogen, and particulate, liquid fission and corrosion products and tritium
activity from 1967 to 1972 have been calculated and are tabulated.  Data for
similar comparisons of conventional radioactivity and pollutants in liquid
effluents are not available.  However, studied to date in the vicinity of
several nuclear power reactors suggest that their radioactive liquid effluents
have been dosimetrically insignificant.  Comparable studies of the degree
of pollution of streams and groundwater by releases peculiar to fossil
fueled plants have not appeared in the literature, so it also appears to be
minimal.

*Air pollution, *Nuclear powerplants, *Fossil fuels, Gases, Halogens,
Particulates, Corrosion, Radioactive wastes, Water pollution sources,
Water pollution effects

Liquid fission
                                          904

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007K

ENVIRONMENTAL HAZARDS 0? NUCLEAR WASTES,

Mlcklin, P. P.

Science and Public Affairs, Vol. 30, No. 4, p 36-42, April, 1974.  1 fig,
29 ref.

The management and storage of nuclear wastes are discussed.  Krypton-85,
cesium-137, and strontium-90 present the greatest management problems because
of their long physical half-lives.  Because of their highly radioactive
content, reactor wastes must be isolated from the biosphere for centuries
or longer.  The greatest quantity of high level wastes, approximately
85 million gallons, is contained at three federal repositories.  Although  not
presently posing a serious storage problem, these high level radioactive wastes
are expected to reach 93 million gallons by the year 2000.  Commercial wastes
are a more serious problem because they can attain heat and radioactivity
levels six times greater per unit of volume.  Tank storage has been satisfactory
so far, but salt formations are preferred for permanent disposal of commercial
high level radioactive wastes since they are dry and impervious to water.
Other possible modes of earth disposal include burial deep within other
geologic formations, on the seabed and within continental ice sheets.

*Management, *Nuclear wastes, *Radioactive waste disposal, Radioactive wastes,
Waste storage, Liquid wastes, Storage tanks, Underground storage, Dead
storage, Geological formations.
008K

ENVIRONMENTAL RADIATION DOSE CRITERIA AND ASSESSMENT--
PATHWAY MODELING AND SURVEILLANCE,

Hull, A. P.

Brookhaven National Laboratory, Upton, New York,
Health Physics and Safety Division

IEEE Transactions on Nuclear Science, Vol. NS-21, No. 1, p 491-495, February,
1974.  2 fig, 3 tab, 24 ref.

The development of environmental radiation dose criteria and assessment through
both pathway modeling and environmental surveillance are discussed.  Con-
siderable effort has been devoted to this end since the first utilization of
nuclear reactors in the United States in the 1940's and particularly since
the advent of civilian nuclear power reactors.  The Atomic Energy Commission
has issued a Safety Guide calling for considerable refinement in the measuring
and reporting of effluents from nuclear power plants, and has only recently
issued a counterpart dealing with the measuring and reporting of radioactivity
in the environs of nuclear power plants.  The EPA has also recently issued
a guide for the surveillance of environmental radioactivity.  Currently, power
reactor operators are being required by the AEC Regulatory Staff to conduct
detailed, sensitive environmental surveillance at levels consistent with the
proposed concentration limits of Appendix I.

*Radiation, *Nuclear powerplants, *Safety, Nuclear physics, Radioactive
wastes, Measurements, *Radioactivity, Monitoring, Nuclear reactors

*Environmental radiation doses
                                      905

-------
009K

INSTRUMENTATION AND ENVIRONMENTAL RADIATION ASSESSMENT
SYSTEMS,

Peters, C. E.

Environmental Protection Agency,
Washington D.C., Office of Radiation Programs

IEEE Transactions on Nuclear Science, Vol. NS-21, No. 1, p 470-477, February,
1974.  7 fig, 1 tab, 10 ref.

The field of radiation protection monitoring was surveyed and those applica-
tions requiring improved instrumentation or monitoring systems are identified.
The application of most pressing concern are emergency response monitoring
systems and systems to monitor the radiation exposure in the vicinity of
nuclear power facilities.  The increasing need for calculating the doses from
sources of radiation exposure has generated two trends that may be of importance
to the future development of nuclear instrumentation and/or monitoring systems.
One trend is the increasing use of models, such as air and water transport
models, to calculate the movement of radionuclides and subsequently the doses.
The other trend is the increasing demand for specific radionuclide concentra-
tion measurements, which can be used for calculating dose, rather than mea-
surements of gross activity.

*Radiation, *Monitoring, *Instrumentation, Nuclear powerplants, Surveys,
Model studies, Water transfer, Radioisotopes

Environmental radiation doses
C10K

RADIOLOGICAL ENVIRONMENTAL MONITORING—THE EPA APPROACH,

Rowe, W. D.

Environmental Protection Agency,
Washington, D.C., Office of Radiation Programs

IEEE Transactions on Nuclear Science, Vol. NS-21, No. 1, p 416-422, February,
1974.  6 fig, 3 tab, 9 ref.

The approach of the Environmental Protection Agency to monitoring is dis-
cussed, with emphasis on dose computation utilizing source data, environ-
mental models, and minimal monitoring for validation.  This approach, which
requires extensive use of models to predict dose and minimal environmental
measurements, is expected to be more cost effective than the conventional
approach.  The need for monitoring at the state and/or local level is pri-
marily to enforce standards and to obtain timely and effective data upon
which emergency response decisions can be based.  The EPA approach to radio-
logical environmental monitoring will require the development and use of
instrumentation which provides the data to implement this approach in the
most cost effective manner.

*Monitoring, *Radiation, Model studies, Instrumentation, Local governments,
Costs

*Environmental Protection Agency, Environmental radiation doses
                                       906

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011K

THE PRINCIPLES OF SUBSTANTIATING PERMISSIBLE CONCENTRA-
TIONS OF RADIOACTIVE SUBSTANCES IN FRESHWATER BODIES,

Marey, A. N., and Barkhudarov, R. M.

Gigiena i Sautariia, No. 1, p 50-54, 1974.  2 tab, 2 ref.

Permissible irradiation doses for man accepted by the national sanitary law
were assumed as base in the standardization of radioactive isotopes in water
bodies.  The entry of radioactive isotopes into the body of a man with drinking
water, their migration from the water body by the food chains, and the action of
ionizing radiation from the surface of the water body and the flood lands were
considered.

*Radioisotopes, *Freshwater, Potable water, Food chains, Surface waters, In-
vestigations

*Radiation doses, USSR
 012K

 RADIOACTIVE WASTES,

 Straub,  C. P.

 Minnesota University, Minneapolis, Minnesota

 Journal  of the Water Pollution  Control  Federation, Vol.  46, No.  6,
 p  1317-1335, June,  1974.   123 ref.

 A  review of the  literature on the  topic of  radioactive wastes  is
 outlined to include the  following  aspects:  ore processing, preci-
 pitation, solvent extraction, adsorption and  ion  exchange,  fixation,
 ground disposal, flotation,  evaporation,  transmutation,  water  envi-
 ronments, uptake by organisms,  costs, and radiological protection.

 *Reviews, *Radioactive wastes,  Precipitation, Solvent extraction,
 Adsorption, Ion  exchange,  Flotation, Evaporation, Environmental  ef-
 fects, Aquatic environment,  Costs, Underground storage

 Ore  processing,  Fixation,  Transmutation,  Organism uptake, Radio-
 logical  protection
                                       907

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   013K

   EVAPORATION OF ALPHA BEARING AQUEOUS WASTES  ON  A
   LABORATORY SCALE,

   Akatsu,  J., and Ishimori,  T.

   Japan Atomic Energy Research Institute,
   Tokal, Japan

   Radiochemical Radioanalytical Letters, Vol.  18,  No.  2,  p  51-59,
   July 15, 1974.   1  fig,  1  tab,  11  ref.

   Alpha-radioactive  aqueous wastes  can not be  treated  with  the  usual beta-
   and  gamma-radioactive wastes and  they must be converted into  a less mobile
   solid state in order to be stored for an. extended period.  Evaporation  is
   one  of the basic methods  for handling alpha-active wastes.  The problems
   of alpha-radioactive contamination of the air released  to the environment,
   bumping  of a salt,  and  generation of a mist  caused by boiling are minimized
   by the use of an infrared  evaporating system.  Ventilating air of a glove
   box  always passes  through an evaporator, In  which various alkaline aqueous
   wastes are evaporated under electric heaters.   The residue In the evaporator
   is transferred to  waste vessels and solidified with  anhydrous gypsum.

   *Radioactive waste disposal,  *Evaporators, Air  pollution, Ultimate disposal,
   Radioactive wastes,  Nuclear energy

   *Alpha-radioactive wastes,  Japan,  Atomic energy
014K

THE COMPARATIVE MARINE GEOCHEMISTRIES OF LEAD 210 AND
RADIUM 226,

Bruland, K. W., Koide, M.,  and Goldberg, E. D.

Scripps Institution of Oceanography,  University of
California at San Diego, La Jolla, California

Journal of Geophysical Research, Vol. 79, No. 21, p 3083-3086, July 20, 1974.
3 fig, 1 tab, 12 ref.

Concentrations of 226Ra and 210Pb in the Gulf of California and eastern North
Pacific seawaters are apparently governed by the extents of upwelling and the
consequential biological productivities.  In the highly productive Gulf of
California surface water, the residence times of 226Ra and 210Pb are estimated
at a few months and less than one month, respectively, based on the upwelling
rates.

*Geochemlstry, *Lead, *Radium, Sea water, Pacific Ocean, Water pollution,
Biological productivity, Upwelling, Radioisotopes, Oceanography, Surface waters

Gulf of California, Eastern North Pacific, 226Ra, 210Pb
                                        908

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015K

RADIOACTIVE WASTE:  PRESENT PROBLEMS,

Girardi, E., and BertoEZi, G.

Chemical Division, Joint Research Centre of the
Commission of the European Communities, Ispra
Establishment

Euro-Spectra, Vol. 13, No. 1, p 23-29, March, 1974.  4 fig.

Kuclear reactors produce energy by the fission of a uranium isotope,
uranium-235, by neutron capture.  The atom splits into two parts, producing
two light elements called the "fission products" and the energy escapes with
neutrons emitted leading to the fission of other uranium atoms in a continuous
chain reaction which- produces heat and fission products.  The latter are
generally radioactive with activity varying In regard to type, intensity and
life.  The longer-lived suBstances are the most dangerous products, for
example strontium-90 and cesium-137, with radioactivity of these substances
halved about every thirty years.  Many hundreds of years must pass before
these substances can be considered harmless, during which time the products
must be surrounded by proper shielding to absorb radioactive emissions.  Also
produced from reactors are alpha-emitting waste elements.  The uranium atom
and its isotope U238 are able to capture neutrons, producing elements
not existing in nature, for example, neptunium, plutonium, americum and curium,
whose decaying characteristics are totally different from those of fission
products.  They emit alpha particles with biological effects far more
hazardous than those caused by beta or gamma radiations, while they are
more easily shielded off with thin material.  These elements have a greater
longetivity; lasting from several hundreds to tens of thousands of years upon
halving.  Vitrification processes have reduced the volume of radioactive
wastes, painting a more optimistic future for the control of and safe
utilization of nuclear energy.

*Nuclear reactors, *Nuclear wastes, *Radioactive wastes, *Uranium radio-
isotopes, *Radioactivity, Nuclear powerplants, Energy

*Vitrification, *U238, Alpha particles, Beta particles, Gamma particles,
Neptunium, Plutonium, Americum, Curium, Fission products
016K

OPERATING EXPERIENCES:  RELEASES OF RADIOACTIVITY
IN EFFLUENTS AND SOLID WASTE FROM NUCLEAR POWER
PLANTS IN 1972,

Casto, W. R.

Nuclear Safety, Vol. 15, No. 3, p 311-316, May-June 1974.  10 tab, 5 ref.

Radioactive materials are produced during the operation of nuclear power
reactors by fission of the nuclear fuel and by neutron interaction with
metals and materials in reactor sys.tems and impurities in reactor coolant
water.  A tabulation of the radioactivity in effluents and solid waste
from nuclear powerplants for 1972 Is given.  The data have been reported
by the licensed plants as required by the Atomic Energy Commission.  A
comparison of the quantities of radioactive material released In 1972 with
the quantities released for 1971 aad 1970 Is made.  The variations are
caused mainly by changes In fuel performance, reactor power production,
the extent of treatment, and improvement of methods and techniques for
measurements of radioactive effluents.  The radioactivity In effluents
from licensed nuclear power plants has generally been lower than the limits
set by the Atomic Energy Commission.

*Radioactive wastes, *Nuclear powerplants, *Quality control, *Monitoring,
Nuclear reactors, Radioactive waste disposal, Radioactivity, Radioactivity
techniques

Atomic Energy Commission
                                      909

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                              SUBJECT INDEX
Absorption
     093C, 244C, 105E, 156E, 012K

Abstracts (collections)
     139J

Acetate
     354J, 355J

Acidity
     158C, 285D, 053E, 276J

Acid mine water
     379D

Acids
     198C, 184J

Acoustics
     024C

Activated carbon
     014C, 060C, 105C, 168C, 300C,
     019D, 028D, 067D, 147D, 206D,
     216D, 260D, 268D, 422D, 430D,
     495D, 071E, 106E, 164E, 105F,
     032J
Activated sludge
013C,
102C,
171C,
010D,
031D,
074D,
118D ,
185D,
259D,
360D,
404D,
446D,
477D,
501D,
023F,
030J,
027C,
107C,
188C,
014D ,
035D,
081D,
13 ID,
205D,
272D,
381D,
430D,
459D,
483D,
012E,
04 IF,
03 3 J
035C,
108C,
211C,
015D,
036D,
082D,
13 7D,
207D,
287D,
384D,
434D,
465D,
486D,
075E,
065F,

036C,
120C,
290C,
016D,
04 3D,
099D,
140D,
249D,
304D,
390D,
435D,
475D,
490D,
167E,
070F,

041C,
129C,
009D,
018D,
05 2D,
114D,
145D,
254D,
359D,
397D,
436D,
476D,
496D,
015F,
106F,

Active diffuser system
     065D

Administration
     073D, 005J, 059J, 062J, 073J,
     152J, 265J
Adsorption
     051C, 157C, 051D, 066D, 067D,
     206D, 260D, 268D, 274D, 430D,
     448D, 454D, 471D, 071E, 106E,
     105F, 010H, 061H, 032J, 241J,
     395J

Aerated lagoons
     155D, 157D, 160D, 483D
Aeration
002C,
036C,
148C,
189C,
283C,
016D,
119D,
174D,
212D,
483D,
235J,

012C,
037C,
166C,
201C,
285C,
018D,
154D,
185D,
259D,
138E,
369J

020C,
096C,
171C,
202C,
307C,
036D,
156D,
195D,
385D,
030F,


030C,
097C,
173C,
204C,
010D,
053D,
159D,
198D,
389D,
069H,


032C,
146C,
179C,
211C,
015D,
094D,
164D,
207D,
403D,
125J,

Aerial photography
     173E

Aerobic bacteria
     339D, 457D

Aerobic conditions
     059C, 103C, 154D, 155D, 464D

Aerobic treatment
     035B, 007C, 151C, 220C, 272C,
     291C, 043D, 053D, 100D, 283D,
     287D, 380D, 382D, 399D, 483D,
     289J

Aerosols
     406D

Agricultural engineering
     220J

Agricultural runoff
     016A

Agricultural wastes
     033C, 118D, 247D, 086E, 040J,
     083J, 289J, 399J

Agricultural watersheds
     025A
                                  910

-------
Agriculture
     128D, 382D, 028E, 275J, 315J

Air circulation
     022E

Air diffusers
     411D

Air pollution
     043E, 003H, 027J, 344J, 006K,
     013K

Airports
     157J

Alaska
     157D, 163D, 143J, 417J

Alcohols
     095E

Alfalfa
     012J
Algae
     298C, 003D, 416D,
     074F, 017J, 036J,
     362J, 423J
079E, 101E,
237J, 297J,
Algal control
     018J

Algorithms
     069B, 005F, 009F, 035F, 060F

Alkalinity
     012D, 462D, 074F, 040H, 072H,
     039J

Alluvial channels
     031F, 024H

Alluvial deposit
     134E, 158E, 051F

Alum
     220D, 442D, 450D

Aluminum
     149C, 020D, 112D, 139D, 262D,
     282D, 291D, 312D, 161E, 145J

Amino Acids
     287J
Ammonia
     015C, 047C, 251C, 265C, 281C,
     097D, 124D, 176D, 234D, 482D,
     131E, 141E, 101F, 287J

Ammonium
     047C, 153C

Anaerobic conditions
     295C, 364D, 464D, 113E, 054H

Anaerobic digestion
     036D, 100D, 120D, 154D, 172D,
     198D, 237D, 288D, 364D, 407D,
     445D, 113E, 047F, 055F

Anaerobic treatment
     289J

Analytical techniques
     042C, 075C, 274C, 275C, 279C,
     292C, 212D, 297D, 001E to 180E,
     030F, 048F, 098F, 016J, 041J,
     098J, 244J, 264J, 299J, 342J,
     361J, 375J

Analyzers
     160C, 167C, 167E

Animal behavior
     07 8J

Animal pathology
     024J

Animal wastes
     154C, 166C, 382D, 239J, 399J

Anion exchange
     285D

Application methods
     024B, 244D, 250D, 348D, 081E,
     094E, 098F, 099F, 047J, 048J

Aquatic environment
     139E, 046J, 079J, 090J, 287J,
     345J, 410J

Aquatic life
     038E, 112E, 043J, 238J

Aquatic plants
     236J

Aqueous solutions
     139C, 157C, 162C, 190C, 191C,
     281C, 306C, 400D, 456D, 180E
                                 911

-------
Aquiculture
     005D, 461D, 060J, 151J

Aquifer management
     091C, 059D, 029H

Aquifer recharge areas
     272J

Aquifers
     020A, 059D, 342D, 051F, 102F,
     009G, 001H, 009H, 015H, 030H,
     031H, 035H, 059H, 067H, 068H,
     070H, 422J

Argon
     133E

Aromatic compounds
     206D, 296J

Arsenic
     003E, 142E, 155E, 185J, 216J

Artificial recharge
     029H, 054H

Asbestos
     498D, 143E, 225J

Atomic absorption
     007E, 015E, 132E

Australia
     078H

Automatic backwash carbon filter  (ABW)
     235D

Autoiiiatic control
     156C, 216C, 274C, 081D, 115D,
     135D, 205D, 343D, 409D, 172E,
     066F, 019H

Automation
     130C, 182C, 216C, 255C, 070D,
     074D, 114D, 133D, 235D, 238D,
     300D, 018E, 045E, 099E, 144E,
     163E, 165E, 169E, 016F, 007G,
     081J, 112J, 139J, 193J

Autoregressive models
     111F
Bacteria
     055B, 289C, 004D, 057D, 162D,
     223D, 313D, 436D, 454D, 044E,
     056E, 093E, 008H, 056H, 204J,
     274J, 284J, 293J, 354J, 355J,
     426J

Bacteriophage
     061D, 050E, 056E, 098E

Baffles
     202C

Barges
     212J

Bark
     256J

Basalts
     035H

Basins
     248C, 192D, 195D, 059F, 043H
Bays
     001E, 162J
Beaches
     106J

Bed load
     028E

Beds
     130C

Benthos
     369J, 394J

Bioassay
     460D, 080E, 149E, 017J, 018J,
     021J, 114J, 432J
Biochemical
     009A,
     191C,
     035D,
     137D,
     174D,
     297D,
     484D,
     022F,
     096F,
     183 J,
     328J
 oxygen demand (BOD)
035B, 158C, 177C, 190C,
228C, 003D, 011D, 017D,
097D, 103D, 117D, 131D,
144D, 151D, 158D, 169D,
194D, 195D, 225D, 271D,
283D, 413D, 429D, 459D,
057E, 084E, 119E, 159E,
047F, 068F, 079F, 087F,
110F, 020H, 034J, 068J,
195J, 204J, 217J, 256J,
                                 912

-------
Biodegradation
     151C, 259C, 008D, 030D, 053D,
     147D, 163D, 304D, 045E, 095E,
     103E, 023F, 093F, 023J, 070J

Bioindicators
     460D, 050E, 015J
Biological
     048C,
     181C,
     016D,
     189D,
     272D,
     354D,
     433D,
     075E,
     204J,
treatment
059C, 119C,
221C, 295C,
051D, 152D,
194D, 198D,
286D, 309D,
358D, 373D,
434D, 457D,
119E, 126E,
235J, 245J
122C,
014D,
153D,
199D,
311D,
3 SOD,
47 8D,
140E,
163C,
015D,
166D,
205D,
34 OD,
418D,
011E,
183J,
Biomass
     399D, 044E

Bleaching
     276C

Boating
     176E, 213J, 330J

Boilers
     039J, 111J, 248J

Boron
     104J, 216J

Brackish water
     135J

Brines
     200C, 340D, 081H, 082H

Bulk density
     459D, 476D

Buoys
     109C

Burning
     031C, 197C, 294C, 069D

Cadmium
     301D, 372D, 013E, 052E, 046H,
     049J, 054J, 078J, 115J, 128J,
     319J

Calcium sulfate
     135J
California
     026D, 064E, 018H, 019H, 022H,
     023H, 249J

Canada
     009A, 003B, 047C, 041D, 050D,
     134D, 159D, 160D, 261D, 274D,
     088F, 001H, 021H, 004J, 019J,
     038J, 142J, 148J, 153J, 196J,
     264J, 283J, 290J, 303J, 405J

Canals
     005A, 005H, 055H

Cancer
     225J

Capacity loss
     005H

Capital costs
     027B, 073B, 215D, 234D, 279D,
     334D

Carbohydrates
     117J

Carbon
     101C, 147C, 221C, 247C, 147D,
     235D, 397D, 434D, 049E, 074E,
     036J, 082J, 297J, 381J

Carbonates
     285D, 090E, 216J

Carbon dioxide
     105C, 332J

Catalysts
     038D, 415D

Cellulose
     010C, 090C, 116C

Centrifugation
     098B, 257C, 284C, 301C, 213D,
     224D, 438D, 491D, 029F

Channels
     060B, 119C, 135E, 062F, 005H,
     021H, 028H, 039H, 226J

Chelation
     143C, 123E

Chemical analysis
     028E, 051E, 361J, 432J
                                913

-------
Chemical control
     021D, 393D, 400D, 058E

Chemical industry
     300C, 415D, 494D, 365J

Chemical oxygen demand (COD)
     003D, 035D, 144D, 297D, 480D,
     057E, 121E, 159E, 162E, 137J,
     256J

Chemical precipitation
     117C, 039D, 042D, 062D, 103D,
     104D, 105D, 106D, 109D, HID,
     126D, 151D, 356D, 433D, 478D,
     494D, 087J, 012K

Chemical properties
     220D, 254D, 037E, 171J, 296J

Chemical reactions
     128C, 295C, 012D, 355D, 010H,
     211J, 246J, 365J

Chemicals
     048D, 066D, 178D, 303D, 111J

Chemical treatment
     161C, 047D, 107D, 115D, 141D,
     152D, 166D, 171D, 189D, 231D,
     433D, 485D, 495D, 078F, 026H,
     235J, 237J

Chemical wastes
     300C, 073D, 240D, 440D, 003E,
     157E, 001F, 083J

Chlorides
     269C, 112D, 353D, 154E, 216J,
     379J

Chlorinated hydrocarbons
     263J, 395J

Chlorination
     025D, 100D, 167D, 168D, 176D,
     197D, 211D, 234D, 288D, 291D,
     455D, 467D, 063J, 214J, 234J,
     426J

Chlorine
     021A, 141C, 156C, 200C, 262C,
     013D, 025D, 033D, 113D, 214D,
     216D, 067E, 106E, 109E, 180E,
     033H, 025J, 063J, 064J, 134J,
     159J, 266J
Chlorine dioxide
     076D

Chlorophyta
     115J, 332J

Chromates
     250C

Chromatography
     006E, OWE, 096E, HOE, 125E,
     205J, 342J

Chromium
     120E, 175E

Circulation
     173C, 189C, 207D, 297J

Cisterns
     104C

Cities
     002A, 009B, 387D, 005E, 043J,
     163J

Civil engineering
     083J
Clarification
     018C, 121C, 143C,
     193C, 242C, 154D,
     196D, 212D, 485D,

Clays
     017F, 034H

Cleaning
     002B, 058B, 001C,
     133C, 078D, 039J,

Cleveland, Ohio
     010B, 024B

Climate
     095F

Coagulation
     034C, 071C, 081C,
     095D, 107D, 141D,
     273D, 375D, 426D,
     466D, 498D, 074E
146C, 151C,
175D, 179D,
047E, 056F
040C, 121C,
042J, 331J
027D, 079D,
178D, 220D,
448D, 458D,
Coal
     066E, 182J, 207J
                                 914
                                              Coalescence
                                                   050C

-------
Coasts
     051J, 415J

Cobalt (radioisotope)
     197D

Cockroaches
     007B

Cold regions
      156D,  157D,  158D,  160D,  163D,
      164D,  165D,  167D,  124J,  140J,
      141J,  143J,  356J

 Coliforms
      007D,  029D,  460D,  020E,  056E,
      079E,  037J,  069J,  130J,  234J,
      411J

 Colloids
      069C,  280D

 Color
      401D

 Colorado
      002B, 004F

 Colorimetry
      018E, 099E,  109E

  Combined sewers
       002A, 020A, 033A, 010B, 019B,
       025B, 026B, 027B, 028B, 036B,
       038B, 065B, 074B, 082B, 088B,
       223C, 318D

  Compressors
       148C

  Computer models
       006A, 017A, 061E, 177E, 034F,
       038F, 067F, 421J

  Computers
       182C, 045D, 133D, 135D, 292D,
       062E, 088E, 166E, 006F, 016F,
       033F, 039F, 052F, 057F, 060F,
       063F, 069F, 076F, 078F, 052H

   Computer studies
        046F

   Concentrations
        068E
   Concrete
        29 3D
                                    915
Concrete pipes
     001B, 005B, 013B, 042B, 045B,
     052B

Concrete structures
     095J

Conduits
     002B, 005C, 006C, 121C, 257C,
     263C, 299D

Conferences
     278D, 338D, 004J, 252J, 295J,
     404J

Conservation
     108J, 130J

Construction
     039B, 059B, 088B, 089B, 093B,
     218C, 253C, 254C, 143D, 263D,
     427D, 168E, 115F, 085J, 093J,
     190J, 269J, 419J

Construction  costs
     099B, 049D, 204D, 157J, 419J

Construction  equipment
     017B, 011G

 Construction  materials
      027B, 060B,  068B,  070B,  085B,
      092B,  218C,  293D,  389D,  115E,
      013J,  157J,  212J,  215J,  302J,
      337J

 Consultants
      241J,  242J

 Contamination
      143C,  167C,  184D,  313D,  357D,
      070H,  180J,  231J,  447J

 Contour farming
      013A

 Contours
      018H

 Contracts
      089D

 Control  systems
      055D, 212D, 213D, 063E, 088E,
      057F, 063F, 066F, 014J, 194J

 Convection
      402D, 028F

-------
Cooling water
     071B, 275C, 181D,  257J

Copper
     372D, 013E, 052E,  070E,  080E,
     015J, 115J, 154J

Correlation analysis
     080H, 058J, 066J

Corrosion
     HOD, 269D, 209J,  414J

Cost analysis
     064D, 116D, 065F

Cost-benefit analysis
     018F, 268J, 449J

Costs
Dams
062B,
022D,
089D,
146D,
193D,
257D,
046E,
168E,
058F,
039 J,
125J,
152J,
243J,
431J,
063B,
03 6D,
098D,
178D,
208D,
350D,
058E,
003F,
060F,
077J,
139J,
159 J,
291J,
010K
075B,
046D,
102D,
18 3D,
218D,
399D,
078E,
032F,
07 8F,
103J,
143 J,
168J,
363 J,

090B,
075D,
116D,
185D,
232D,
417D,
103E,
034F,
114F,
107J,
144J,
177J,
408J,

016D,
084D,
12 OD,
190D,
234D,
456D,
163E,
057F,
028H,
109J,
148J,
181J,
421J,

Countercurrent washing
078D
Cover crops
013A












Crabs
     106J, 322J

Crop production
     202D, 246D, 251D, 368D, 100F,
     175J, 176J

Crustaceans
     340D, 114J, 358J, 401J

Cyanides
     038D, 245J

Cyanophyta
     245J
     010A, 040F, 388D, 037H, 302J
Darey's law
     108F, 034H

Data collections
     106D, 030E, 069E, 076E,
     114E, 065F, 080F, 091F,
     045J, 058J, 228J, 244J,
     298J, 299J, 384J

Data processing
     006F, 039F, 111F

Data storage and retrieval
     292D, 039F, 012H
082E,
004H,
247J,
DDT
     395J, 401J, 402J, 409J
Decomposition
     053E

Dehydration
     154C, 034D, 224D, 230D,

Deicers
     009A, 022A, 140D

Demineralization
     111C, 130C, 384D

Demography
     019A, 072H, 163J, 255J

Denitrification
     055C, 188C, 221C, 259C,
     027D, 037D, 088D, 124D,
     165D, 326D, 368D, 373D

Densitometry
     145E

Deodorization
     34 7D

Depth-duration-frequency
     109F

Depth flow
     004G

Desalination
     199C, 032D, 285D, 289D,
     502D, 081H, 082H, 211J,
     431J, 441J
                                                                           288D
                                                                           295C,
                                                                           137D,
431D,
240J,
                                 916

-------
Design
     054B, 066B, 083B, 084B, 089B,
     098C, 104C, 128D, 136D, 150D,
     381D, 497D, 041F, 042F, 115F

Design criteria
     031B, 049B, 057B, 074B, 088B,
     225C, 049D, 092D, 145D, 164D,
     182D, 203D, 207D, 219D, 233D,
     259D, 261D, 263D, 270D, 299D,
     300D, 332D, 361D, 386D, 411D,
     413D, 424D, 475D, 479D, 481D,
     100E, 010F, 064F, 081F, 088F,
     106F, 048H, 077H, 004J, 042J,
     085J, 087J, 164J, 181J, 259J,
     269J, 325J, 351J

Detergents
     363D, 365D, 478D, 480D, 436J

Dewatering
     103C, 130C, 153C, 048D, 079D,
     082D, 108D, 190D, 210D, 226D,
     230D, 244D, 262D, 428D

Diamond sawing
     042B

Diatomaceous earth
     061D, 412D

Dieldrin
     287J

Dielectric constant
     056C

Dietary effects
     154J, 316J, 319J

Diffusion
     096C, 157D, 207D, 028F, 048F

Digestion
     226D, 477D, 493D

Digester gas
     237D

Discharge (water)
     043B, 187C, 197C, 211D, 216D,
     098E, 076F, 065J, 440J, 444J

Disinfection
     026B, 021C, 078C, 141C, 007D,
     026D, 033D, 058D, 076D, 077D,
     122D, 167D, 168D, 169D, 170D,
     197D, 452D, 470D, 013F, 025J,
     063J, 064J
Dispersion
     374D, 027F, 048F

Dissolved oxygen
     157D, 004E, 029E, 079F, 096F,
     110F, 203J, 396J

Distillation
     125C

Distribution patterns
     137E, 094F, 011J

Documentation
     020B, 039F

Domestic wastes
     158C, 229C, 288C, 120D, 161D,
     188D, 232D, 390D, 394D, 413D,
     465D, 503D, 074E, 022F, 069J,
     239J, 242J, 321J, 415J

Domestic water
     020D, 180D, 417D, 005E, 177E,
     231J, 403J, 445J

Drainage
     072B, 079B, 083B, 225C, 263C,
     299C, 031H, 033H, 036H, 042H,
     070H, 360J, 377J, 383J

Drainage area
     048C, 048H, 079H

Drainage engineering
     012B, 044C, 045C

Drainage systems
     001A, 012B, 040B, 046B, 067B,
     095B, 039C, 226C, 002F, 004F,
     042F, 020H, 042H, 076J

Drains
     031B, 044C, 263C, 379J

Dredging
     074C, 165C, 028H, 077H, 226J,
     397J

Ecology
     027J, 090J, 106J, 128J, 160J

Economic impact
     103F, 073J, 075J

Economics
     080D, 102D, 241D, 299D, 103F,
     059J, 198J, 304J, 317J, 417J
                                  917

-------
Ecosystems
     222D, 072J, 123J

Eddies
     050F
Elevation
     156D

Emergency treatment
     05 7D
Education
     101J, 178J, 179J

Efficiencies
     108D, 135D, 157D, 170D,  17ID,
     225D, 229D, 104F

Effluent control
     366D, 468D, 140E, 428J,  433J
Effluents
024C,
095C,
136C,
197C,
283C,
081D,
145D,
19 2D,
254D,
370D,
467D,
071E,
044F,
057J,
107J,
144J,
170J,
202J,
317J,

036G,
117C,
142C,
240C,
02 3D,
09 ID,
17 3D,
214D,
272D,
387D,
500D,
083E,
032H,
071J,
109J,
146 J,
174J,
218J,
393J,

053C,
127C,
169C,
242C,
038D,
104D,
183D,
216D,
314D,
425D,
031E,
103E,
00 1J,
073J,
127J,
149J,
177J,
244J,
423J,

064C,
131C,
188C,
259C,
072D,
113D,
187D,
228D,
319D,
434D,
044E,
107E,
002J,
075J,
131J,
166J,
183J,
252J,
438J,

088G,
132C,
196C,
268C,
078D,
118D,
191D,
236D,
34 3D,
444D,
054E,
126E,
007J,
099J,
137J,
169 J,
194 J,
300J,
444J
Effluent streams
     294D, 083E

Electroanalytical techniques
     027E

Electrochemistry
     039D, 348D, 027E, 160E

Electrodes
     348D, 113E, 115E, 157E, 116J

Electrolysis
     065C, 178C, 228C, 246J

Electrolytes
     014C, 022C

Electron capture detector
     067E
Employment opportunities
     201J

Emulsions
     069D, 369D, 072E, 160E, 122J

Energy
     121D, 237D, 081H, 082H, 108J,
     161J

Energy conversion
     293C

Engineering
     075D, 062E, 115F, 085J, 094J,
     157J, 201J

Engineering structures
     008A, 006B, OOSB, 012B, 013B,
     014B, 015B, 018B, 034B, 035B,
     036B, 041B, 042B, 044B, 048B,
     001C, 008C, 017C, 019C, 025C,
     044C, 045C, 046C, 055D, 005F,
     006G, 076J

Engineers
     046F

Enteric bacteria
     050E

Environmental control
     387D, 414D, 415D, 125E, 150E,
     074J, 163J, 190J, 193J, 196J,
     199J, 259J, 269J, 271J, 327J,
     338J, 380J, 386J, 416J, 417J

Environmental effects
     022A, 147C, 257D, 278D, 365D,
     108E, 011J, 027J, 061J, 074J,
     078J, 086J, 108J, 110J, 158J,
     175J, 187J, 228J, 250J, 259J,
     265J, 296J, 418J, 447J, 449J

Environmental engineering
     043B, 044B, 046C, 058J, 101J,
     163J, 190J, 198J

Environmental impact studies
     105J
                                 918

-------
Environmental Protection Agency
     074B, 007J, 080J, 108J, 168J,
     338J, 339J, 344J, 380J, 386J,
     387J, 416J

Environmental sanitation
     167D, 168D

Epoxy resins
     033B

Equations
     031A, 066B, 100E, 135E, 151E,
     013F, 014F, 021F, 028F, 074F,
     079F, 087F, 270J
Estuaries
     107F, 049H, 248J, 320J, 345J,
     415J
Equilibrium
008G
Equipment
025B,
091B,
022C,
065C,
073C,
084C,
115C,
164C,
201C,
217C,
249C,
258C,
279C,
284C,
297C,
303C,
103D,
223D,
265D,
298D,
354D,
420D,
041E,
174E,
07 9J,
242J,

076B,
095B,
024C,
066C,
074C,
085C,
136C,
176C,
204C,
224C,
251C,
261C,
280C,
285C,
298C,
306C,
114D,
230D,
266D,
348D,
361D,
456D,
055E,
179E,
084J,
271J,

079B,
006C,
028C,
068C,
076C,
098C,
137C,
179C,
210C,
229C,
25 3C,
262C,
28 1C,
290C,
299C,
0451),
136D,
233D,
271D,
349D,
385D,
017E,
088E,
008G,
087J,
337J

081B,
018C,
029C,
070C,
080C,
107C,
145C,
192C,
212C,
241C,
254C,
267C,
282C,
292C,
300C,
048D,
199D,
247D,
276D,
352D,
409D,
034E,
100E,
028H,
136J,


090B,
020C,
031C,
072C,
082C,
114C,
152C,
195C,
214C,
248C,
256C,
278C,
283C,
296C,
30 2C,
050D,
210D,
259D,
295D,
353D,
411D,
037E,
149E,
069H,
209J,

Erosion
     013A, 032B, 113J

Escherichia coli
     061D, 460D, 020E, 050E, 092E,
     218J, 274J, 367J

Estimating
     030F, 001K
Eutrophication
     370D, 063E, 078F,
     017J, 068J, 072J,
     236J, 260J, 362J

Evaluation
     024B, 063D, 296D,
     345D, 446D, 447D,
     021J, 028J, 046J,
     206J, 249J, 341J,
008J, 010J,
082J, 153J,
30ID, 330D,
04IF, 015J,
074J, 091J,
418J
                                              Evaporation
                                                   217D,  392D,  085F,  013K

                                              Evapotranspiration
                                                   070H

                                              Expansion joints
                                                   054B

                                              Experimentation
                                                   255C,  153J

                                              Extraction
                                                   157C,  172C,  208C,  269C
                                              Facilities
                                                   063B, 073B, 057C,
                                                   087D, 089D, 094D,
                                                   419D, 499D, 172E,
                                                   157J, 419J
                       084D, 085D,
                       394D, 410D,
                       115F, 149J,
Farm management
     202D, 245D, 324D, 003J, 083J

Faulting
     042H

Feasibility studies
     052D, 301D, 268J, 324J

Fecal coliforms
     029D, 092E

Federal government
     032A, 007J, 074J, 200J, 326J,
     439J

Federal jurisdiction
     168J, 206J, 290J

Federal policy
     251D
                                 919

-------
Federal Water Pollution Control Act
     086B, 203D, 204D, 085E, 028J,
     038J, 067J, 073J, 075J, 127J,
     165J, 168J, 338J, 380J, 382J,
     386J, 408J, 440J, 444J

Fermentation
     053D, 113E

Fertilizers
     033C, 070E, 055J, 056J, 057J,
     138J, 180J, 376J, 383J, 393J

Fiber-glass pipes
     008B

Fibers
     218C, 222C

Field data
     292J, 318J

Filaments
     176C

Filtering
     192C, 195C, 132D, 108F

Filter media
     193C, 207C, 211C

Filter plates
     070D, 238D

Filter press
     070D, 238D
Filters
080B,
067C,
150C,
218C,
270C,
298C,
092D,
210D,
226D,
314D,
426D,
165E,
182J

032C,
082C,
16 8C,
244C,
278C,
301C,
125D,
221D,
233D,
371D,
432D,
045F,


052C,
092C,
207C,
249C,
290C,
004D,
129D,
222D,
235D,
412D,
47 9D,
06 OH,


056C,
099C,
208C,
256C,
296C,
070D,
177D,
223D,
238D,
418D,
042E,
061H,


064C,
118C,
212C,
266C,
297C,
080D,
179D,
224D,
263D,
422D,
106E,
062H,

Filtration
024B,
070C,
175C,
297C,
011D,
06 3D,
086D,
142D,
199D,
317D,
473D,
160E,
352J,

007C
092C
200C
298C
022D
067D
087D
174D
2 SOD
412D
474D
045F
430J

9
9
9
9
»
9
9
9
9
9
9
9


018C,
099C,
218C,
299C,
028D,
078D,
090D,
177D,
290D,
458D,
487D,
026H,


026C,
134C,
278C,
301C,
056D,
080D,
092D,
179D,
295D,
466D,
093E,
077H,


039C,
174C,
296C,
008D,
061D,
085D,
136D,
193D,
313D,
47 ID,
112E,
047 J,

Financing
     004B, 295J

Fish
     100C, 040D, 080E, 102E, 124E,
     151E, 024F, 049J, 050J, 078J,
     114J, 120J, 151J, 232J, 244J,
     283J, 294J, 319J, 320J, 347J,
     364J, 391J, 406J

Fisheries
     058J, 290J

Fishkill
     413J, 433J

Fish management
     058J, 059J

Fish physiology
     051J, 054J, 374J

Flame evaporation
     069D

Flexibility
     054B, 118C, 026H

Floating sludge
     205C, 227D

Flocculation
     012C, 049C, 153C, 189C, 240C,
     242C, 260C, 022D, 056D, 067D,
     079D, 105D, 109D, 173D, 261D,
     350D, 424D, 426D, 463D, 466D,
     494D, 037E, 027F

Floe-suspension
     087C
                                 920

-------
Flood control
     004F, 005G, 013H, 047H, 081J,
     448J

Flood damage
     077J, 133J

Flood forecasting
     078H, 081J, 133J, 448J

Flooding
     192D, 299D, 035J, 133J

Floodplains
     052B, 062E, 021H, 047H, 448J

Floodproofing
     052B, 047H

Flood protection
     010A, 029A

Flood relief
     083D

Floods
     029A, 031A, 011B, 088F

Florida
     032B, 051B, 077F, 098J, 121J

Flotation
     023C, 065C, 068C, 145C, 149C,
     159C, 166C, 126D, 265D, 350D,
     37 2D
                             Flow rates
                                  025A, 023B, 026B, 059B, 223C,
                                  275C, 282D, 299D, 396D, 436D,
                                  032E, 134E, 135E, 165E, 047F,
                                  051H, 053H, 067H

                             Flow smoothing
                                  053B

                             Fluidized bed reactor
                                  164C

                             Fluid movement
                                  160C, 292C, 383D

                             Fluids
                                  133C, 192C, 206C, 210C, 255C

                             Fluorescence
                                  024E

                             Fluoridation
                                  020D, 276D

                             Fluorides
                                  097E, 046H, 361J

                             Fluorometry
                                  094E

                             Flush toilets
                                  18 3D
                             Flux
                                  053F
Flow
     053B, 030C,
     086C, 124C,
     206C, 224C,
     287C, 149D,
     021E, 023E,
     062F, 085F,
     015H, 025H,
     088H, 134J
042C, 062C, 071C,
150C, 176C, 194C,
249C, 270C, 285C,
317D, 437D, 441D,
047E, 152E, 017F,
089F, 112F, 013H,
048H, 073H, 074H,
Flow control
     048B, 069C, 077C, 203C, 212C,
     214C, 396D

Flow data
     049F

Flow measurement
     015A, 062C, 021E, 022E, 023E,
     029E, 032E, 069E, 081E, 085E,
     107E, 115E, 016H
Food chains
     007F, 024F, 050J, 061J, 123J,
     174J, 011K

Food consumption
     069F

Food processing industry
     355D, 429J

Foods
     060J, 180J

Forecasting
     011F, 042F, 049F, 094J, 255J,
     328J

Forestry
     378J
                                921

-------
Forests
     328D, 329D, 323J, 326J

Fo rmaldehyde
     176E

Fossil fuels
     105J

Fossils
     105J, 409J

Fouling
     301J, 350J, 414J

Fragmentography
     016E

Frame modules
     07 ID

France
     035C, 036C, 080C

Freshwater
     043H, 257J, 011K

Freundlich equation
     071E

Frost prevention
     008G

Froth flotation
     147J
Fuels
     174C, 237D, 372J, 397J
Fungi
     289C, 019E, 250J

Furnaces
     031C

Future planning (projected)
     201D, 198J, 224J, 255J, 404J

Gadolinium
     03 9D

Gaging stations
     094F

Gamma rays
     197D, 428D, 033E, 034E, 035E,
     043E, 258J
                                  922
Gas chromatography
     006E, 025E, 068E, 104E, 244J,
     316J

Gases
     078C, 092C, 093C, 096C, 164C,
     258C, 472D, 147J

Gastrointestinal disturbances
     367J

Gauges
     023E

Geochemistry
     031J, 014K

Geohydrology
     041H

Geology
     050B, 051F, 040H, 042H, 043H

Geomorphology
     03 9H

Geothermal studies
     081H, 082H

Germany
     092D, 310D, 022E, 077E, 018F

Granular carbon
     028D, 037D

Gravity filters
     263C, 221D

Gravity sewers
     018B

Great Britain
     039B, 046B, 047B, 082C, 021D,
     064D, 068D, 073D, 078D, 083D,
     084D, 087D, 091D, 004G, 007G,
     008G, 004H, 012H, 005J, 014J,
     052J, 273J

Great Lakes region
     043H, 133J, 260J

Groundwater
     072B, 019C, 039C, 077C, 002D,
     208D, 362D, 076E, 089E, 127E,
     032F, 051F, 075F, 102F, 008G,
     009H, 015H, 017H, 018H, 029H,
     030H, 031H, 035H, 037H, 041H,
     051H, 053H, 057H, 067H, 070H,
     043J, 119J, 156J, 181J, 186J,
     233J, 376J, 412J

-------
Groundwater recharge
     059D, 502D, 016H, 023H, 054H,
     063H, 324J, 368J

Growth rates
     360D, 016J
             Hydrants
                  058B

             Hydraulic engineering
                  074B, 011D, 108F, 013H, 021H,
                  028H, 034H, 065H
Gunite
     006G

Gymnodinium
     016J

Harbors
     226J, 228J

Hawaii
     041H

Head loss
     108F, 114F

Heat
     264C, 227D, 228D, 008G, 414J

Heavy metals
     106C, 137C, 142C, 02ID, 044D,
     051D, 228D, 240D, 245D, 493D,
     009E, 139E, 054J, 128J, 174J,
     180J, 184J, 238J, 405J

Herbicides
     008D, 124E, 145E, 391J, 412J

Highway effects
     083B, 163C, 088F, 002H, 027J,
     032J

History
     100J, 121J

Hospitals
     020J

Hudson River
     049H, 247J

Human pathology
     066E, 185J, 222J, 254J, 298J,
     299J, 365J, 367J

Human resources
     201J

Humus
     112E

Hungary
     014D
             Hydraulics
                  011B, 041B, 043B, 150D, 221D,
                  407D, 037E, 165E, 020F, 033F,
                  112F, 025H, 035H, 074H, 075H,
                  071J, 134J

             Hydrocarbons
                  169C, 184C, 205C, 186D, 102E,
                  046H, 023J, 147J, 284J, 342J

             Hydrolectric power
                  410J

             Hydrogen
                  293C, 020D

             Hydrogenation
                  399J

             Hydrogen ion concentration
                  012D, 082D, 126D, 170D, 182D,
                  119F, 064J, 114J, 158J, 218J

             Hydrogen sulfide
                  106J

             Hydrogeology
                  068H, 389J

             Hydrographs
                  092F, 066H, 073H, 078H, 079H,
                  397J

             Hydrologic aspects
                  014A, 030A, 059E, 108E, 010F,
                  011F, 049F, 001H to 082H

             Hydrologic cycle
                  038F, 192J

             Hydrologic data
                  059F, 275J

             Hydrologic models
                  108E, 054F, 085F

             Hydrolysis
                  138C, 170E

             Hydroponics
                  005D
923

-------
Hyperfiltration
     026C
                                   Infrared radiation
                                        156E
Ice
     199C, 159D, 160D
Illinois
     013D

Incineration
     047B, 028C, 054C, 294C, 050D,
     068D, 100D, 186D, 190D, 481D

Incubation
     092E, 159E

India
     366D, 023E, 001G, 047J, 055J,
     056J, 057J

Industrial plants
     343D, 028J, 162J, 163J, 194J

Industrial streams
     047C
Industrial
     050B,
     158C,
     188D,
     269D,
     344D,
     086E,
     057J,
     146J,
     248J,
     336J,
     429J,
wastes
094B, 137C,
178C, 268C,
200D, 231D,
273D, 315D,
347D, 465D,
099E, 126E,
067J, 084J,
149J, 184J,
285J, 290J,
372J, 408J,
433J, 434J
154C,
05 2D,
232D,
333D,
503D,
001F,
097J,
225J,
300J,
415 J,
155C,
091D,
258D,
341D,
084E,
056J,
144 J,
243J,
334J,
425J,
Industrial water
     267D, 303D, 057E, 257J, 265J,
     266J, 405J

Infiltration
     015A, 024A, 014B, 015B, 020B,
     086B, 024D, 255D, 137E, 014F,
     017F, 092F, 007H, 032H, 044H,
     054H

Infiltration equations
     192D, 014F, 089F

Inflow
     020B, 086B

Information
     148E, 179J, 303J
                                  924
Injection wells
     098B, 500D, 023H, 407J

Inland water
     057H

Inorganic compounds
     069C, 279D, HOE, 163E, 074F

Inorganic matter
     090E, 149J, 171J, 232J

Insecticides
     007B, 067E, 050J, 053J, 288J,
     401J

Installation
     097C, 196D, 206J

Instruction
     075E

Instrumentation
     007A, 022C, 024C, 062C, 094G,
     167C, 274C, 275C, 072D, 074D,
     109D, 292D, 004E, 006E, 010E,
     017E, 021E, 022E, 023E, 029E,
     032E, 039E, 045E, 051E, 073E,
     081E, 085E, 087E, 094E, 104E,
     105E, 115E, 130E, 131E, 146E,
     147E, 162E, 063F, 139J, 193J,
     194J, 009K, 010K

Intake structures
     100C

Interceptor sewers
     358D

Interstitial water
     160J

Investigations
     024A, 022B, 023B, 037B, 086D,
     099D, 107D, 137D, 139D, 140D,
     229D, 254D, 257D, 277D, 333D,
     341D, 450D, 053E, 023F, 005H,
     018H, 020H, 034H, 056H, 008J,
     015J, 032J, 034J, 040J, 060J,
     070J, 089J, 115J, 116J, 117J,
     120J, 122J, 150J, 214J, 250J,
     286J, 294J, 413J

Iodine radioisotopes
     035E

-------
Ion exchange
     010C, 015C, 052C, 075C,  088C,
     098C, HOC, 116C, 130C,  224C,
     176D, 285D, 462D, 123E,  061H,
     071J, 104J, 241J
Ions
     280D, 116J, 424J

Iron
     015B, 101C, 250C, 268C,  001D,
     002D, 023D, 112D, 225D,  240D,
     273D, 282D, 031E, 109E,  150E,
     061J, 103J, 124J, 264J,  366J,
     422J

Irradiation
     305C, 060D, 258J

Irrigation
     024A, 080B, 024D, 187D,  218D,
     251D, 255D, 321D, 322D,  328D,
     330D, 331D, 332D, 421D,  0757,
     089F, 044H, 055H, 104J,  150J,
     166J, 315J, 377J, 407J,  412J

Irrigation effects
     012J

Irrigation systems
     255D, 334D, 335D, 031F,  181J,
     323J, 324J, 327J

Isotopes
     108E
Japan
     044D, 093D, 038E, 024F, 010H,
     032J, 033J, 276J, 004K, 005K
Jets
     031B, 170C, 195D, 198D, 048E,
     006H

Joints
     008B, 087B

Kaczmarek model
     012F

Karst hydrology
     051H, 052H, 059H

Kentucky
     028D

Kinetics
     457D, 011E, 055F, 087F, 105F
Krypton
     133E

Labor
     215D, 238D

Laboratory animals
     221J, 223J

Laboratory analysis
     011E, USE

Laboratory equipment
     011E, 149E, 162E, 167E
Laboratory tests
     061B, 043D, 127D,
     302D, 339D, 350D,
     074E, 092E, 126E,
     160E, 052F, 049J,
     136J, 158J, 221J,
     258J, 301J, 347J,

Lagoons
     142J, 218J, 289J

Lake Erie
     384J
      148D, 264D,
      356D, 031E,
      148E, 159E,
      051J, 118J,
      223J, 256J,
      400J, 402J
Lake Michigan
     040D, 086E,

Lake Ontario
     05 4D, 056D

Lake Superior
     292J, 435J

Lakes
     026A, 049E,
     043H, 011J,
     142J, 153J,

Laminar flow
     136C, 207C,

Land application
     190D, 191D,
     058F, 044H,
     176J, 177J,

Land disposal
     324D, 368D,
     407J
003H, 010J, 120J
063E, 044F, 050F,
036J, 113J, 129J,
361J
402D, 048E
247D, 277D, 368D,
165J, 166J, 169J,
178J, 252J
414D, 065E, 252J,
Landfills
     021D, 194D, 241D, 242D, 113J,
     156J, 164J, 186J, 208J
                                    925

-------
Land management
     050B, 009D, 251D, 252D, 253D,
     255D, 256D, 258D, 277D, 331D,
     332D, 336D, 337D, 251J, 325J

Land reclamation
     225C
Lime
     047D, 082D, 098D, 102D, 112D,
     132D, 152D, 169D, 172D, 229D,
     291D, 379D, 438D, 137J

Linear programming
     101F
Land resources
     172J
Liner-inserting machine
     003C
Land use
     025A, 062E, 007H, 047H, 272J

Larvae
     301J

Laser-beam aligner
     017B

Lasers
     017B, 246C, 024E, 007G

Latin America
     224J

Law enforcement
     227J, 233J, 382J

Leachate
     345D, 380D

Leaching
     030D, 089E, 012J, 040J, 256J,
     376J, 389J, 412J

Lead
     021A, 028A, 301D, 013E, 052E,
     253J, 254J, 319J, 014K

Least squares method
     110F

Legal aspects
     032B, 203D, 262J, 338J, 351J

Legislation
     086B, 453D, 028J, 037J, 049J,
     107J, 109J, 148J, 165J, 167J,
     186J, 196J, 198J, 227J, 233J,
     262J, 295J, 329J, 336J, 339J,
     353J, 360J, 373J, 386J, 388J,
     416J, 439J, 440J, 444J

Lignins
     401D, 025F
Linings
     001B, 006B, 008B, 033B, 003C,
     269D

Lipids
     342J

Liquids
     071C, 072C, 074C, 075C, 078C,
     086C, 092C, 093C, 114C, 118C,
     126C, 136C, 140C, 148C, 164C,
     170C, 172C, 182C, 194C, 195C,
     204C, 205C, 208C, 213C, 245C,
     247C, 261C, 267C, 282C, 286C,
     287C, I960

Liquids ventilation
     201C, 266C
Liquid wastes
     050B, 028C,
     083C, 125C,
     179C, 180C,
     291C, 294C,
     068D, 370D,
     001J, 030J,
     002K, 007K

Lobsters
     358J, 401J

Local governments
     179J, 329J
Lodgepole pine trees
     038H

London, England
     007A

Lysimeters
     012J
054C, 057C, 063C,
146C, 166C, 175C,
220C, 250C, 280C,
304C, 038D, 050D,
472D, 169E, 044H,
128J, 208J, 241J,
Mains
     016B
                                 926

-------
Maintenance
     002B, 056B, 073B, 091B, 092B,
     102C, 190C, 080D, 096D, 215D,
     235D, 005H

Maleic anhydride
     236D

Management
     082B, 497D, 161J, 173J, 175J,
     442J, 007K

Mangarese
     023D, 103J, 124J

Mannings equation
     031B

Manpower
     201J, 210J

Manuals
     276D, 210J

Mapping
     018H

Marine biology
     060E, 101E, 031J, 061J, 162J,
     345J

Markov processes
     012F

Massachusetts
     022D

Mass spectrometry
     016E, 068E, 102E, 104E, 244J

Mathematical models
     018A, 019A, 011B, 041B, 043B,
     044B, 061B, 062E, 009F, 012F,
     013F, 015F, 019F, 020F, 032F,
     035F, 036F, 040F, 044F, 050F,
     054F, 058F, 060F, 061F, 068F,
     069F, 071F, 075F, 091F, 093F,
     095F, 097F, 103F, 104F, 105F,
     106F, 116F, 030H, 421J

Mathematical studies
     030A, 012B, 014B, (BOB, 031B,
     037B, 053B, 066B, 078B, 025D,
     175D, 260D, 032E, 038E, 059E,
     164E, 010F, 014F, 021F, 028F,
     037F, 049F, 064F, 065F, 079F,
     094F, 016H, 025H, 027H, 034J,
     270J
                                  927
Measurement
     054C, 066C, 094C, 156C, 177C,
     228C, 423D, 006E, 010E, 017E,
     018E, 023E, 033E, 034E, 036E,
     039E, 041E, 042E, 055E, 064E,
     072E, 077E, 078E, 084E, 085E,
     087E, 119E, 122E, 132E, 136E,
     144E, 146E, 025F, 062F, 011H,
     012H, 087J, 105J, 192J, 400J,
     008K

Mechanical equipment
     007A, 100E

Membrane processes
     008D, 044D, 071D, 487D, 488D,
     492D, 020E, 093E, 211J

Membranes
     090C, 134C, 175C, 008D, 391D,
     432D, 441D

Mercury
     198C, 200C, 279C, 184D, 454D,
     002E, 015E, 060E, 080E, 111E,
     132E, 152E, 046H, 076H, 024J,
     051J, 054J, 079J, 129J, 151J,
     160J, 232J, 250J, 254J, 283J,
     298J, 299J, 359J, 375J, 406J,
     424J

Metabolism
     162D, 288J

Metal pipes
     006B, 015B, 087B

Metal recovery
     200D

Metals
     070B, 243C, 269C, 019D, 400D,
     OOZE, 064E, 083E, 101E, HOE,
     003H, 156J, 197J

Meteorology
     021E, 040E

Methane
     120D, 121D, 027E, 129J, 354J,
     355J

Methodology
     085C, 213C, 216C, 227C, 105D,
     106D, 127D, 019E, 036E, 053E,
     105E, 161E

Methyl parathion
     288J

-------
Mexico
     222J

Michigan
     004A, 335D, 167J

Microbiology
     120D, 264D, 056E, 301J, 343J,
     350J, 365J, 367J, 411J

Mi c ro o rgani sms
     048C, 265C, 264D, 283D, 404D,
     405D, 459D, 013F, 055F, 008H,
     270J, 301J, 350J, 411J

Microstrainers
     023B, 004D, 017D, 199D

Mineral extraction
     067F

Minerals
     111C, 127D, 242D, 243D, 143E

Mines
     207J, 276J

Mine wastes
     207J, 435J

Mining
     388D, 077F, 108J, 197J, 435J

Minitunnel
     007G
Mink
     232J
Mirex
     264D, 050J, 322J

Mixing
     078C, 126C, 182D, 374D, 407D,
     028F, 069H

Modeling
     094F

Model studies
     006A, 008A, 014A, 018A, 019A,
     029A, 031A, 010B, 012B, 041B,
     044B, 162D, 311D, 360D, 464D,
     001F to 116F, 007H, 010H,
     030H, 071H, 073H, 080H, 134J,
     370J, 443J, 010K
Molybdenum
34 7 J
Monitoring
062C,
279C,
250D,
031E,
065E,
087E,
163E,
063F,
048 J,
016K
Moran model
012F


102C,
00 2D,
36 2D,
042E,
069E,
101E,
168E,
046H,
158J,





156C,
109D,
003E,
043E,
077E,
124E,
176E,
048H,
008K,





182C,
205D,
017E,
049E,
07 8E,
136E,
179E,
055H,
009K,





194C,
211D,
029E,
058E,
080E,
137E,
053F,
046 J,
010K,



            Morphoedaphic index
                 151E
            Mud
                 028C, 112C, 121C
Municipal wastes
012A,
065B,
016C,
014D,
062D,
222D,
256D,
320D,
427D,
073E,
172E,
062H,
169J,
210J,
013B,
075B,
147C,
017D,
187D,
231D,
258D,
323D,
496D,
084E,
006F,
026J,
172J,
245J,
014B,
093B,
158C,
018D,
190D,
241D,
270D,
324D,
5 ODD,
086E,
023F,
099J,
173J,
252J,
047B,
008C,
005D,
05 6D,
191D,
251D,
311D,
328D,
005E,
128E,
058F,
165 J,
176J,
371J,
064B,
009C,
006D,
057D,
204D,
254D,
315D,
338D,
058E,
153E,
029H,
167J,
178J,
428J
Moisture content
     089F, 017H
            Municipal waste water
                  053B,  144D,  274D,  309D,  351D,
                  065E,  247J,  408J

            Municipal water
                  099B,  099C,  002D,  007D,  032D,
                  033D,  087D,  187D,  218D,  219D,
                  310D,  469D,  007E,  143E,  089J,
                  167J,  230J,  243J,  257J

            NASA
                  223D,  073E

            Natural  gas
                  184C,  009G,  074J

            Navigation
                  037J
928

-------
Nephelometric methods
     144E

Netherlands
     037C, 098F

Neutralization
     37 9D

New York
     012A, 009B, 253D, 292D, 296D,
     007E, 037J, 077J, 262J, 418J

Niagara Falls
     003B

Nickel
     240D, 070E, 238J

Nitrates
     037C, 127E, 131E, 100F, 040J,
     110J, 116J, 119J, 155J, 229J,
     286J, 379J

Nitrification
     027D, 031D, 117D, 155D, 326D,
     354D, 373D, 070F, 204J

Nitrites
     037C, 109E, 155J, 223J

Nitrogen
     037C, 038C, 049C, 188C, 221C,
     265C, 295C, 088D, 202D, 245D,
     364D, 376D, 398D, 434D, 449D,
     482D, 490D, 131E, 003J, 110J,
     217J, 229J, 236J, 285J, 366J,
     381J

Nitrogen compounds
     030D, 274D

Nozzle
     108C, 115C

Nuclear powerplants
     032D, 042E, 043E, 228J, 417J,
     006K, 008K, 009K, 016K

Nuclear wastes
     150E, 015K

Numerical analysis
     048E, 018F, 030F, 040F, 079F,
     086F, 004G, 036H

Nutrient removal
     295C, 166D, 367D, 461D, 423J
Nutrients
     026A, 246D, 255D, 476D, 127E,
     010J, 123J, 195J, 236J, 247J,
     285J, 381J, 383J

Oceans
     144C, 186D, 050F, 031J, 162J,
     200J, 398J

Odor
     076C, 123D, 001H, 030J

Off-shore facilities
     228J
Oil
     050C, 051C, 056C, 066C,
     140C, 145C, 161C, 176C,
     180C, 186C, 193C, 173D,
     014E, 122J, 146J, 399J

Oil pollution
     066C, 088J, 372J, 388J

Oil spills
     061C, 144C, 145C, 161C,
     298D, 443D, 072E, 088J,
     275J, 370J, 388J, 398J
073C,
178C,
237D,
241C,
212J,
Oil wastes
     061C, 001E, 024E, 182J, 372J

Oil-water separation
     150C

Oily water
     222C, 069D, 260D, 265D, 266D,
     375D

Oligotrophy
     396J

On-site investigation
     447D, 010E, 020J, 046J, 118J,
     264J, 301J

On-site tests
     016A, 041D, 104D, HID, 248D,
     004E, 026F, 166J

Open channel flow
     022E, 069E, 085E, 004G

Operating costs
     215D, 234D, 279D, 334D, 041F
                                   929

-------
Operation and maintenance
     089B, 098D, 215D, 272D, 281D,
     300D, 359D, 387D, 394D, 475D,
     147E, 172E, 064F, 066F, 004H,
     087J, 331J, 341J, 407J

Optical properties
     03 9E

Organic acids
     129E, 111J

Organic carbons
     071E

Organic compounds
     051C, 059C, 211D, 274D, 045E,
     023J, 066J

Organic loading
     117D, 435D, 459D

Organic matter
     101C, 135C, 138C, 040D, 147D,
     188D, 194D, 242D, 246D, 254D,
     287D, 363D, 145E, 068F, 023J,
     090J, 156J, 160J, 232J, 260J

Organic micropollutants
     068E

Organic wastes
     103C, 101D, 100J, 446J

Organochlorine hydrocarbons
     102E
Oxidation lagoons
     141D, 151D, 392D, 439D, 478D

Oxidation reduction potential
     002D

Oxygen
     177C, 252C, 272C, 293C, 185D,
     195D, 259D, 496D, 045H

Oxygenation
     065D, 185D, 381D, 403D, 501D

Oxygen demand
     054C, 045E

Oxygen sag
     369J

Oysters
     461D, 092E, 051J, 214J, 322J

Ozonation
     174D, 346D, 349D, 401D

Ozone
     007D, 058D, 066D, 067D, 122D,
     123D, 170D, 214D, 275D, 294D,
     346D, 347D, 349D, 401D, 495D,
     124J, 203J, 266J

Pacific Ocean
     060E, 061J

Pakistan
     031F
Organophosphorus pesticides
     171E, 374J
Paramecium
     021J
Orthophosphates
     018E
Parameters
     112F
Outfall sewers
     001B, 005B, 037F

Overflow
     034A, 011B, 019B, 021B, 025B,
     026B, 027B, 038B, 061B, 223C

Oxidation
     014C, 059C, 066C, 089C, 139C,
     147C, 191C, 221C, 252C, 272C,
     217D, 275D, 377D, 405D, 413D,
     035E, 121E, 154E, 170E, 025F,
     045F, 079J, 209J, 218J
Particles
     159C, 256C, 287C

Particulate matter
     286C, 414J

Passive diffuser system
     065D

Pasture management
     025A

Patents
     001C to 308C
                                 930

-------
Pathogenic bacteria
     406D, 455D, 008H, 020J, 239J

Percolation
     024D, 302D, 114E

Performance
     077B, 171D, 446D, 099F, 341J

Periphyton
     292J

Permeability
     091C, 034H

Permits
     339J, 373J

Personnel
     006J, 091J, 201J

Pesticides
     007B, 006E, 019E, 067E, 089E,
     106E, 124E, 149E, 171E, 020H,
     119J, 263J, 320J, 322J, 358J,
     374J, 395J, 401J, 402J, 409J,
     417J

Petroleum
     057B, 309D, 001J, 119J

Phenols
     157C, 289C, 304D, 025E, 095E,
     001F, 023F, 070F, 019J, 258J,
     274J, 438J

Phosphate removal
     042D, 109D, HOD

Phosphates
     013C, 035C, 003D, 039D, 042D,
     079D, 086D, 105D, 139D, 225D,
     273D, 311D, 341D, 356D, 018E,
     130E, 052F, 077F, 078F, 002J,
     011J, 039J, 153J
Phosphorus
04 ID,
109D,
172D,
398D,
086E,
036 J,
236J,
436J
04 3D,
110D,
324D,
44 9D,
127E,
072J,
285J,
066D,
HID,
365D,
47 ID,
170E,
082J,
377J,
100D ,
118D ,
376D,
489D,
078F,
137 J,
381J,
10 3D,
150D,
378D,
063E,
035 J,
195J,
393J,
Phosphorus removal
     041D, 098D, 099D, 101D, 102D,
     103D, 104D, 108D, HID, 112D,
     376D, 378D, 004J, 237J, 352J
Photosynthesis
     332J, 369J, 396J

Physical-chemical treatment
     009D, 150D, 268D, 345D, 430D

Phytoplankton
     091F, 056H, 010J, 396J

Pickling
     184J

Pilot plants
     006D, 022D, 023D, 029D, 030D,
     037D, 047D, 058D, 060D, 107D,
     119D, 140D, 14ID, 145D, 148D,
     150D, 205D, 250D, 056F, 337J

Pipe bridges
     029B

Pipe flow
     037B

Pipe foundations
     034B

Pipelines
     046B, 054B, 057B, 069B, 080B,
     087B, 090B, 097B, 011C, 017C,
     040C, 251C, 253C, 254C, 244D,
     055E, 098F, 114F, 093J
Pipes
     006B, 009B,
     044B, 046B,
     053B, 058B,
     080B, 086B,
     003C, 005C,
     019C, 040C,
     077C, 225C,
     055E, 005F,
013B,
049B,
070B,
087B,
008C,
042C,
246C,
114F,
042B,
051B,
077B,
093B,
011C,
045C,
253C,
001G,
043B,
052B,
079B,
001C,
017C,
046C,
254C,
008G
Plains
     038H

Plankton
     284J

Planning
     033A, 064D, 421D, 427D, 147E,
     06-7F, 069F, 086F, 005J, 038J,
     142J, 188J, 227J, 230J, 241J,
     259J, 392J, 404J, 418J, 443J

Plant design
     072D, 016F
                                      931

-------
Plant pathology
     104J

Plastic pipes
     016B, 022B, 034B, 085B,  092B

Plastics
     020A, 003B, 005C, 044C,  045C,
     310D, 389D, 429D, 159J,  366J

Plating
     042J

Plumbing
     097B, 253J

Plutonium
     125E, 002K, 004K

Polarographic analysis
     027E, 052E, 091E, 153E

Pollutants
     180C, 194D, 282D, 045E,  051E,
     068E, 120E, 143E, 180E,  048F,
     096F, 003H, 128J, 391J

Pollution
     186C, 222D, 064E, 129J,  207J,
     233J, 317J

Pollution abatement
     035A, 046C, 050C, 161C,  241C,
     300C, 093D, 333D, 455D,  084J,
     191J, 197J, 199J, 271J,  273J,
     300J, 370J, 442J

Polychlorinated biphenyls
     016E, 102E, 070J, 205J,  214J,
     263J, 316J

Polyelectrolytes
     049C, 069C, 063D, 180D,  369D,
     056F

Polyethylene
     078B, 442D, 491D

Polyethylene pipes
     016B, 078B

Polyhydric phenol
     440D

Polymers
     153C, 155C, 369D, 448D,  111J

Polyurethane
     058B                         932
Porous media
     015A, 134C, 018F, 036H

Potable water
     094C, 243C, 262C, 273C, 288C,
     293C, 063D, 076D, 092D, 142D,
     209D, 303D, 312D, 384D, 395D,
     420D, 422D, 424D, 431D, 462D,
     498D, 097E, 099E, 142E, 179E,
     054H, 055H, 013J, 089J, 110J,
     155J, 185J, 203J, 222J, 223J,
     224J, 231J, 240J, 253J, 254J,
     261J, 267J, 293J, 368J, 385J,
     431J, 432J, 441J, 011K

Potassium
     057E, 090J

Potomac River
     030E

Power
     178C

Power plants
     275C, 248J, 291J

Prague, Czechoslovakia
     003A

Precasting
     095J

Precipitates
     196C, 097E, 340J

Precipitation (atmospheric)
     043F, 057H

Pressure
     128C, 132C, 194C, 206C, 208C,
     264C, 266C, 290C, 284D, 008G

Pressure conduits
     077B, 025C

Pressure sewers
     018B, 022B, 063B

Pre-treatment
     232D, 286D, 351D, 426D, 251J

Priming water
     006C

Probability
     040F

-------
Processing
     140E, 209J

Profiles
     076E

Project planning
     029B, 054D, 064D, 279D, 296D,
     334D, 336D, 009F, 064H, 052J,
     188J, 190J, 268J, 269J, 304J,
     333J, 335J, 449J

Properties
     099D

Proportional weirs
     055D

Proteins
     088C, HOC, 117C, 268C, 071J

Protozoa
     021J, 034J

Pseudomonas
     023J

Publications
     452D, 453D, 075E, 163E, 052J,
     200J

Public health
     049B, 327D, 139E, 178E, 024J,
     025J, 092J, 185J, 198J, 229J,
     234J, 251J, 261J, 293J, 375J,
     435J, 437J

Public relations
     178J

Public rights
     062J

Public utilities
     089J

Public works
     023A, 219D

Pulp and paper industry
     276C, 158D, 161D, 270D, 289D,
     397D, 465D, 073J, 075J, 148J,
     151J, 357J

Pulp wastes
     276C, 282C, 158D, 161D, 270D,
     032J, 161J
Pumping
     081B, 011C, 174C, 195C, 240C,
     027H

Pumping plants
     045B, 129D, 143D, 201D, 019H

Pumping stations
     084B, 093J

Pumps
     071B, 081B, 084B, 098B, 019C,
     074C, 108C, 112C, 115C, 187C,
     258C, 284D, 069E

Purification
     122C, 124C, 127C, 169C, 247C,
     309D, 350D

Quality control
     148E, 174E, 377J

Radiation
     128D, 042E, 008K, 009K, 010K

Radioactive tracers
     211D, 134E, 051H, 053H, 068H

Radioactive wastes
     079C, 428D, 024F, 048J, 447K,
     001K to 016K

Radioactivity
     060E, 120J

Radioactivity techniques
     026E

Radiocarbon
     041H

Radioisotopes
     033E, 034E, 035E, 036E, 133E,
     134E, 090J, 120J, 005K, 011K

Radium
     014K

Rainbow trout
     287J, 316J, 347J, 402J

Rainfall
     018A, 030A, 036A, 038F, 058H,
     08OH, 053J
Rainfall intensity
     003A, 005A, 002F, 042F,
071F
                                 933

-------
Rainfall-runoff relationships
     003A, 005A, 006A, 017A, 018A,
     026A, 031A, 010B, 058H

Rain gauge
     028E

Rain water
     059B

Random walk model
     051F

Rapid sand filter
     108F, 425 J

Raritan River Basin
     017A
Rational formula
     014A, 078H

Receiving streams
     411J

Recession curves
     030E

Recharge
     091C, 009H, 016H, 181J

Recirculated water
     053C, 057C, 207C, 114D

Reclaimed water
     273C, 280C, 179E

Recording
     088E

Recreation
     001A, 206J, 249J
Recycling
     009B, 001C, 013C,
     146C, 001D, 005D,
     093D, 119D, 180D,
     191D, 236D, 262D,
     053F, 061F, 009H,
     034J, 048J, 170J,
     178J, 199J, 344J,

Red  tide
     008J

Reduction
     021C
015C, 058C,
032D, 075D,
181D, 183D,
278D, 007F,
064H, 033J,
173J, 177J,
446J
                                  934
Regional development
     164E, 188J, 403J

Regression analysis
     109F

Regulation
     203D, 333D, 001J, 059J, 065J,
     086J, 101J, 213J, 262J, 327J,
     329J

Relining project
     001B

Remote sensing
     078E, 082E, 094E

Reovirus
     44 7D

Research and development
     044D, 106D, 253D, 338D, USE,
     027J, 029J, 060J, 131J, 179J,
     240J, 249J, 275J, 303J, 335J,
     370J, 441J

Reservoirs
     002B, 122C, 185C, 186C, 090D,
     395D, 410D, 005E, 012H, 019H,
     026H, 027H, 043J, 093J, 102J,
     105J, 321J, 362J, 410J

Reservoir storage
     001A

Resins
     015C, 052C, HOC, 113C, 071J

Resource allocation
     227J

Respiration
     137D, 304D, 395J

Respiration rates
     359J

Retention
     004A, 030B, 044F

Retention basin
     030B, 059B

Reverse osmosis
     090C, 113C, 185C, 071D, 142D,
     267D, 279D, 281D, 289D, 357D,
     391D, 402D, 420D, 425D, 431D,
     432D, 441D, 473D, 488D, 492D,
     053F, 135J, 197J, 240J

-------
Reviews
     022A, 023A, 034A, 020B, 113D,
     146D, 281D, 325D, 327D, 338D,
     357D, 363D, 364D, 365D, 404D,
     418D, 421D, 445D, 452D, 453D,
     489D, 096E, 136E, 163E, 010F,
     064F, 065F, 011H, 003J, 045J,
     063J, 064J, 164J, 189J, 193J,
     199J, 200J, 229J, 246J, 296J,
     351J, 352J, 403J, 012K

Reynolds number
     037B, 402D, 032E, 048E, 025H

Rhine Valley
     067H
                       Rotary kiln
                            068D

                       Rubber
                            054B

                       Runoff
                            018A,  024A, 031A,  028E, 030E,
                            122E,  035F, 036F,  062F, 057H,
                            112J,  113J, 172J,  368J, 383J

                       Runoff forecasting
                            014A,  029A, 079H

                       Runoff graphs
                            073H
Rhode Island
     010D

Rinsing
     042J

Riparian rights
     227J

River basins
     017A, 027H

River flow
     152E

River forecasting
     020F, 033F

Rivers
     003B, 004B, 001D,
     001E, 004E, 026E,
     049E, 054E, 122E,
     020F, 033F, 046F,
     086F, 113F, 005G,
     013H, 021H, 024H,
     081J, 102J, 110J,
     189J, 219J, 239J,

River training
     014J
086D,
040E,
152E,
068F,
002H,
042H,
118J,
276J,
125D,
046E,
158E,
074F,
012H,
076J,
129J,
004K
                       Rural areas
                            004B,  052B, 096D,  143J, 152J,
                            224J,  286J

                       Saline water
                            085C

                       Salinity
                            154E,  075F, 002H

                       Salmon
                            357J

                       Salmonella
                            020J,  222J, 321J,  367J
                       Salt
                            021A, 150J
Salts
     081C, 131C, 141C, 169C, 042D,
     043D, 127D, 156J, 402J

Sampling
     007A, 109C, 159C, 160C, 177C,
     209C, 257C, 274C, 325D, 008E,
     054E, 059E, 061E, 063E, 066E,
     076E, 079E, 084E, 087E, 090E,
     132E, 161E, 163E, 174E, 010J,
     018J, 086J, 098J, 105J, 205J
Roads
     331J

Roasting
     198C
                       Sand
                            168C, 193C, 177D, 221D
                       Sand aquifers
                            009G
Romania
     095F
                       Sand columns
                            03 7D
                                 935

-------
Sand filtration
     317D

San Francisco Bay area
     026D, 001E

Sanitary engineering
     003B, 377D

Sanitary landfills
     164J

Sanitation
     164J, 206J, 213J

Sclairpipe
     001B

Screening/dissolved air flotation
     025B

Screens
     203C, 215C, 223C, 308C

Scum
     023C

Seabeds
     048E

Sea water
     217C, 093E, 097J, 213J, 214J,
     221J, 438J, 014K

Seaweeds
     101E

Secondary pollution
     019D

Secondary treatment
     192D, 193D, 214D, 234J, 387J

Sedimentation
     260C, 270C, 027D, 385D, 437D,
     026F, 064F, 106F, 362J

Sediments
     174C, 292C, 298C, 055D, 403D,
     008E, 063E, 064E, 090F, 100F,
     104F, 020H, 024H, 049H, 076H,
     098J, 160J, 284J, 340J, 346J

Seepage
     015A, 392D

Selenium
     003E
Self-purification
     093F, 008H

Semipermeable membranes
     080C, 289D

Separated sewers
     026A, 015B, 036B, 002C, 445J
Separation
     061B,
     058C,
     084C,
     118C,
     175C,
     215C,
     271C,
     301C,
     069D,
     303D,
     456D,
     035E,
     029J,
techniques
033C, 035C,
063C, 065C,
086C, 095C,
140C, 150C,
176C, 189C,
216C, 222C,
278C, 290C,
304C, 306C,
086D, I960,
391D, 399D,
463D, 472D,
100E, 171E,
070J
050C,
068C,
114C,
163C,
203C,
227C,
296C,
004D,
227D,
432D,
474D,
029F,
056C,
075C,
115C,
174C,
213C,
245C,
299C,
044D,
240D,
451D,
487D,
019J,
Septic tanks
     127C, 277C, 010D, 030D, 096D,
     37OD, 478D, 002J

Settling
     165C, USD, 227D, 047E

Settling basins
     059B, 084C, 291C, 476D, 026F,
     041F, 104F

Settling tanks
     171C, 148D

Sewage
     045B, 075B, 081B, 084B, 099B,
     007C, 010C, 012C, 013C, 020C,
     041C, 043C, 057C, 077C, 081C,
     083C, 120C, 122C, 123C, 132C,
     154C, 173C, 034D, 089D, 093D,
     134D, 135D, 138D, 149D, 314D,
     319D, 425D, 025E, 053E, 176E,
     069J, 097J, 126J, 131J, 138J

Sewage bacteria
     007D, 020E, 069J

Sewage disposal
     096B, 017C, 125C, 074D, 091D,
     143D, 368D, 451D, 464D, 064H,
     217J, 247J

Sewage districts
     005J
                                  936

-------
Sewage effluents
     070C, 039D, 328D, 329D, 330D,
     128E, 323J

Sewage lagoons
     052F

Sewage sludge
     047B, 076B, 264C, 034D, 060D,
     116D, 184D, 202D, 229D, 246D,
     247D, 248D, 250D, 264D, 283D,
     287D, 288D, 320D, 491D, 014E,
     070E, 045H, 003J, 117J, 170J,
     208J, 220J
Sewage treatment
012A.,
094B,
035C,
089C,
123C,
173C,
229C,
285C,
307C,
029D,
049D,
076D,
09 6D,
123D,
15 ID,
270D,
302D,
380D,
393D,
428D,
497D,
090F,
044J,
246J,
Sewerage
032A,
097C,
13 8D,
497D,
020A,
023C,
038C,
097C,
129C,
188C,
244C,
288C,
006D,
036D,
05 3D,
081D,
105D,
12 9D,
15 2D,
271D,
318D,
385D,
408D,
433D,
009E,
004H,
109J,
334 J,

056B,
303C,
251D,
039F,
040B,
027C,
048C,
105C,
135C,
202C,
259C,
293C,
017D,
037D,
064D,
082D,
109D,
13 OD,
173D,
284D,
352D,
386D,
41 ID,
469D,
081E,
075H,
140 J,
371J,

064B,
134D,
25 3D,
122J,
055B,
029C,
053C,
116C,
148C,
219C,
264C,
294C,
019D,
04 5D,
065D,
085D,
120D,
133D,
198D,
29 3D,
36 9D,
391D,
419D,
484D,
119E,
003 J,
213J,
436J,

095B,
135D,
31 8D,
445J
09 OB,
031C,
058C,
119C,
171C,
220C,
277C,
302C,
025D,
046D,
07 4D,
094D,
12 2D,
134D,
239D,
295D,
377D,
392D,
427D,
486D,
166E,
030 J,
219J,
446J

097B,
136D,
416D,

Sewer overflows
     038B

Sewer systems
     003A,  005A,  032A,  033A,  001B,
     to 099B, 001C,  003C,  005C,
     006C,  011C,  025C,  040C,  132C,
     152C,  226C,  246C,  248C,  303C,
     134D,  204D,  037F,  001G,  011G,
     047H,  075H,  002J,  068J,  133J,
     445J,  447J
Sewer rods
     152C

Shales
     040H

Shellfish
     037J, 123J

Ships
     209J, 348J

Silica
     177D, 472D

Simulation
     024A, 067B, 175D, 302D, 304D,
     061E, 034F, 035F, 038F, 058F,
     060F, 062F, 076F, 077F, 091F,
     092F, 102F, 106F, 110F, 006H,
     025H, 071H

Slime
     289C, 079D, 151J

Sludge
     034C, 043C, 073C, 079C, 087C,
     124C, 165C, 170C, 283C, 302C,
     307C, 001D, 075D, 082D, 088D,
     116D, 117D, 121D, 143D, 175D,
     212D, 213D, 220D, 224D, 230D,
     241D, 367D, 396D, 405D, 438D,
     117J, 126J, 174J

Sludge blanket
     087C, 047E

Sludge disposal
     302C, 132D, 146D, 189D, 210D,
     241D, 242D, 244D, 245D, 247D,
     248D, 249D, 250D, 288D, 383D,
     386D, 397D, 481D, 485D, 493D,
     126J

Sludge treatment
     084C, 108C, 117C, 151C, 181C,
     047D, 048D, 060D, 070D, 100D,
     108D, 128D, 130D, 131D, 132D,
     133D, 139D, 146D, 189D, 226D,
     227D, 228D, 229D, 262D, 323D,
     396D, 419D, 429D, 436D, 440D,
     450D, 458D, 106F, 126J, 138J

Slurries
     067C, 112C, 170C, 181C, 199C,
     215C, 251C, 256C, 284C, 047E,
     045F
                                      937

-------
Smoke testing
     097B

Snow
     021A,  022A,  054F,  002H,  038H

Social values
     032D,  121J

Sodium
     325D,  145J

Sodium compounds
     282C,  089E,  223J

Soil analysis
     321D,  019E,  089E,  125E,  060H

Soil chemistry
     243D,  326D,  061H,  065H,  171J

Soil conservation
     100F,  172J,  220J

Soil contamination
     184D,  053J,  275J,  379J

Soil disposal fields
     322D,  325J,  326J

Soil engineering
     101D

Soil filters
     170J

Soil management
     024D,  243D,  248D,  032H,  053J

Soil mechanics
     066B,  045H,  220J

Soil microbiology
     188D,  243D,  062H,  170J

Soil moisture
     011H,  017H

Soil pressure
     078B,  158E

Soil properties
     056B,  188D,  302D,  114E,  017F,
     033H,  060H,  169J
Soils
     032A, 078B, 326D, 036E, 017H,
     036H, 065H, 035J- 040J
Soil water
     010H, 011H, 032H, 033H, 045H,
     065H, 150J

Soil-water-plant relationships
     045H, 171J, 173J

Solids
     067C, 123C, 172C, 261C, 266C,
     284C, 119D, 146D, 267D, 029J

Solid wastes
     079C, 092C, 100C, 125C, 215C,
     227C, 224D, 029F, 075H, 056J,
     112J, 226J, 336J, 389J, 002K

Solubility
     138C, 153C, 243C, 228D, 117J,
     424J

Solutions
     157C, 097F, 147J

Solvents
     051C, 001E, 083E, 019J, 012K

Sorption
     031D

Sound waves
     058D

Spain
     035J

Specific gravity
     114C, 207C

Spectrometers
     033E, 034E, 036E, 043E, 104E

Spectrophotometry
     028A, 007E, 014E, 083E, 123E,
     142E, 175E, 424J

Spectroscopy
     009E, 013E, 111E, 129E, 156E,
     169E, 298J

Spraying
     407J

Spray irrigation
     321D, 322D, 329D, 332D, 323J,
     327J

Springs
     037H
                                  938

-------
Standards
     057B, 162E, 038J, 080J, 086J,
     144J, 217J

State jurisdiction
     168J

Stations
     129C
                       086J, 225J


                       113F, 298J
                       293D
Statistical methods
     059E, 061E, 085J,

Statistics
     075B, 082E, 109F,

Steam
     105C, 273C

Steel pipes
     029B, 057B, 060B,

Stochastic processes
     038E, 012F, 027F

Storage
     030B, 009G
Storage tanks
     032C, 189C, 298D, 095J, 007K

Storm drains
     004A, 009A, 011A, 013B, 009C,
     222D, 002F

Storm runoff
     001A, 002A, 006A, 008A, 019A,
     023A, 025A, 010B, 019B, 028B,
     030B, 038B, 065B, 067B, 046D,
     318D, 002F, 059F, 073F, 092F,
     005G, 077J

Storm sewers
     095B

Storm water
     004A, 007A, 011A, 012A, 034A,
     019B, 021B, 023B, 028B, 065B,
     009C, 226C, 012D, 125D, 222D,
     036F, 095F, 058H

Storm water runoff
     001A to 036A

Strainers
     245C

Stream flow
     030E, 040F, 043F, 094F, 378J
Stream purification
     369J

Streams
     027A, 093C, 123C, 183C, 209C,
     113D, 374D, 045E, 122E, 096F,
     112F, 001H, 002H, 056H, 072J,
     394J

Street runoff
     023A

Strip mining
     323D, 207J

Structural design
     010F

Subsurface flow
     091C, 054F

Sulfates
     144E, 354J, 355J

Sulfides
     139C, 157E

Sulfite liquors
     145J

Sulfites
     183C, 234J

Sulfur
     183C

Sulfuric acid
     121E

Sulfurization
     051D

Sumps
     120C

Surface runoff
     013A, 014A, 016A, 028A, 008E,
     111F, 116F

Surface water
     040B, 039C, 077E, 032F, 075F,
     083F, 102F, 056H, 233J, 237J,
     368J, 011K

Surfactants
     178C, 280D, 363D, 095E, 135E,
     147J
                                   939

-------
Surveys
     020B,  071D,  204D,  258D,  022F,
     022H,  084J,  193J,  219J,  220J,
     247J,  009K

Suspended load
     004C,  270C,  271C,  292C,  066J,
     340J

Suspended solids
     004B,  023B,  001C,  038C,  055C,
     060C,  063C,  135C,  190C,  191C,
     271C,  292C,  004D,  011D,  017D,
     018D,  097D,  117D,  131D,  144D,
     176D,  193D,  255D,  268D,  271D,
     282D,  468D,  479D,  040E,  082E,
     146E,  022F,  070F,  108F,  024H,
     195J

Suspensions
     187C,  210C,  287C,  292C,  USD

Swamps
     142J
Television
     091B, 286C

Temperature
     156C, 160C, 151D, 152D, 153D,
     154D, 155D, 162D, 163D, 164D,
     165D, 167D, 168D, 169D, 170D,
     171D, 172D, 283D, 029E, 072E,
     107E, 043F, 070F, 040H, 053J,
     066J, 270J, 292J, 294J

Tertiary treatment
     019D, 077D, 206D, 268D, 290D,
     294D, 295D, 352D, 366D, 367D,
     378D, 461D, 475D, 479D, 128E,
     164E, 007F, 063H, 018J, 208J,
     271J, 423J

Testing
     077B, 072C, 112D, 209D, 114E,
     147E, 178E, 017J, 217J
Texas
     295D
Sweden
     062D, 044J

Swimming pools
     076D, 025J

Swirl concentrator
     027B, 061B

Systems analysis
     209D, 138E, 003F, 005F, 242J,
     291J

Tanks
     023C, 124C, 126C, 165C, 202C,
     242C, 258C, 312D, 134J, 208J

Tannery wastes
     107J, 109J
Taste
     001H
Taxes
     032A, 300J

Technology
     073E, 246J

Telemetry
     088E, 166E, 063F
Textiles
     222C, 131J, 235J, 397J

Thermal pollution
     107E, 291J, 292J, 331J, 364J

Thermal stress
     294J

Thorium
     005K

Thunderstorms
     03 OA

Tidal waters
     096F, 066J, 076J, 162J, 239J

Times series analysis
     043F, 080F

Tokyo Bay, Japan
     008J

Topography
     129D

Torsional simple shear device
     400J
                                  940

-------
Toxicity
     113D, 168D,
     012E, 142E,
     024J, 049J,
     149J, 154J,
     185J, 221J,
     254J, 270J,
     288J, 357J,
     413J

Toxins
     041J

Trace elements
     052E

Trace metals
     123E

Tracers
     026E, 098E

Training
     075E, 091J

Transportation
     374D, 212J
       I860,  245D,  002E,
       175E,  001J,  021J,
       055J,  104J,  114J,
       155J,  174J,  180J,
       232J,  238J,  253J,
       274J,  283J,  286J,
       375J,  391J,  406J,
Treatment
     032A,
     029C,
     220C,
     041D,
     052D,
     104D,
     HID,
     130D,
     138D,
     162D,
     203D,
     266D,
     290D,
     299D,
     352D,
     389D,
     065E,
     026H,
     093J,
     138 J,
     341J,
facilities
 025B, 047B,
 032C, 149C,
 277C, 003D,
 046D, 047D,
 060D, 062D,
 106D, 107D,
 115D, 125D,
 132D, 133D,
 139D, 143D,
 164D, 165D,
 221D, 239D,
 269D, 271D,
 291D, 293D,
 300D, 335D,
 358D, 359D,
 390D, 451D,
 001F, 006F,
 013J, 044J,
 094J, 103J,
 213J, 215J,
 371J
068B,
214C,
013D,
048D,
068D,
108D,
12 8D,
134D,
14 9D,
166D,
261D,
276D,
295D,
343D,
36 ID,
009E,
026F,
077J,
126J,
245J,
088B,
219C,
02 6D,
049D,
095D,
HOD,
129D,
135D,
153D,
176D,
26 3D,
286D,
296D,
34 4D,
386D,
041E,
056F,
085 J,
136J,
271J,
Treatment methods
     035B, 010C, 018C, 020C, 021C,
     026C, 027C, 041C, 043C, 061C,
     089C, 204C, 001D to 503D,
     015F
Treatment plants
     082B, 099B, 119C, 181C, 096D,
     114D, 149D, 263D, 316D, 058E,
     073E, 136J, 205J, 215J, 334J,
     337J

Trickle irrigation
     150J

Trickling filters
     015D, 016D, 085D, 272D, 359D,
     378D, 418D, 429D, 480D, 183J,
     204J

Tritium
     026E, 041H, 052H, 053H

Tubes
     113C, 208C, 291C

Tubular modules
     071D

Tuna
     024J

Tunnel construction
     005G, 006G, 011G

Tunnel design
     006G

Tunnelling
     068B, 005G, 006G, 007G, 011G

Tunnel linings
     060B, 068B

Tunnels
     011A, 005B, 033B, 039B, 045B,
     008C, 001G, 008G, 026J

Tunnel technology
     001G to 011G

Turbidimeter
     167, 146E

Turbidity
     115D, 213D, 448D, 031E, 039E,
     041E, 146E, 173E, 378J

Turbine blades
     030C

Turbulence
     004G, 059H
                                   941

-------
Turbulent flow
     037B, 021F, 048F, 050F, 006H
Utah
     006D
Turtles
     263J
Utilities
     089D
Two, four-D (2,4-D)
     124E, 107F

Ultrahigh frequency sound
     077D
Vacuum distilation
     217D

Vacuum drying
     233D
Ultraviolet radiation
     096E

Underground storage
     QUA

Underground structures
     125J

Underground waste disposal
     050B, 001K

Universities
     101J, 384J

Unox system
     381D, 501D

Upflow filtration
     063D, 439D

Uranium
     015K

Urban areas
     286D, 061F

Urban drainage
     036B, 009C, 004F

Urban hydrology
     139E, 081F, 014H, 071H,  073H

Urban planning
     027A, 048H, 170J, 190J

Urban runoff
     016A, 026A, 027A, 028A,  034A,
     035A, 067B, 036F, 071F,  081F,
     099F, 116F, 078H
Vacuum filters
     233D, 239D

Vacuum sewage
     055B, 056B

Valves
     048B, 076B, 082C, 104C, 192C,
     214C, 158J

Vapor filtration
     217D

Vegetation
     184D, 005H, 175J, 393J

Velocity
     022E

Venturi fumes
     030C

Vienna, Austria
     010A

Virginia
     011D

Viruses
     HOC, 061D, 214D, 412D, 447D,
     045J, 092J, 261J, 343J

Vortices
     196D

Washing
     135C

Waste activated sludge
     18 9D
 Ureas
      118J
 U.S.S.R.
      034C,  153D,  424D,  216J
                                   942

-------
Waste disposal
     027A, 055B,
     175C, 196C,
     073D, 097D,
     239D, 252D,
     275D, 277D,
     329D, 336D,
     406D, 414D,
     067F, 062H,
     098J, 112J,
     172J, 173J,
     208J, 226J,
     300J, 325J,
     016K

Waste streams
     139C

Waste treatment
     002A, 012A,
     061C, 172C,
     210C, 211C,
     305C, 018D,
     082D, 10ID,
     161D, 163D,
     273D, 275D,
     394D, 398D,
     445D, 449D,
     496D, 128E,
     048J, 141J,
     446J

Waste water
     071B, 060C,
     149D, 452D,
     145E, 044H, 033J, 411J

Waste water disposal
     021D, 040D, 181D, 256D, 257D,
     337D, 406D, 065J, 125J, 346J,
     407J

Waste water flow
     035D

Waste water (pollution)
     061C, 416D, 018J, 019J, 055J,
     161J
Waste water treatment
063B
214C
101D
253D
278D
370D
500D
057J
122J
176J
251J
326J






064B
179C
227C
038D
118D
200D
334D
405D
457D
003F
24 2 J



088D
482D
9
9
9
9
9
9
9
9
9
9
9
J






9
9
9
9
9
9
9
9
9
9
9



9
9
004 C,
005D,
202D,
256D,
286D,
383D,
022F,
083 J,
140J,
182J,
273J,
336J,






012C,
196C,
250C,
051D,
158D,
231D,
355D,
435D,
458D,
074H,
348J,



094D,
044E,
083C,
050D,
236D,
258D,
327D,
388D,
029F,
084J,
141J,
186J,
289J,
348J,






016C,
197C,
27 1C,
068D,
159D,
236D,
390D,
436D,
486D,
042J,
408 J,



147D,
057E,
020A,
014C,
037C,
089C,
137C,
290C,
305C,
015D,
058D,
075D,
097D,
124D,
1450,
180D,
260D,
287D,
302D,
327D,
351D,
367D,
403D,
433D,
455D,
471D,
484D,
495D,
140E,
037F,
029H,
044J,
140J,
215 J,
34 3J,
429 J,
032A,
016C,
043C,
090C,
138C,
291C,
306C,
04 2D,
059D,
077D,
106D,
138D,
165D,
187D,
26 5D,
289D,
314D,
328D,
35 4D,
393D,
404D,
440D,
456D,
473D,
489D,
503D,
161E,
061F,
063H,
047 J,
143 J,
235J,
352J,
434J,
022B,
029C,
049C,
095C,
149C,
294C,
307C,
05 2D,
06 2D,
080D,
116D,
140D,
166D,
218D,
266D,
292D,
319D,
331D,
357D,
395D,
409D,
444D,
463D,
478D,
490D,
011E,
016F,
101F,
020J,
125J,
146 J,
251J,
353J,
44 2 J
082B,
032C,
070C,
102C,
280C,
296C,
006D,
056D,
06 5D,
082D,
117D,
141D,
173D,
220D,
277D,
294D,
32 OD,
335D,
358D,
398D,
429D,
446D,
467D,
48 ID,
492D,
017E,
019F,
105F,
030J,
136J,
194 J,
295J,
371J,

007C
033C
079C
116C
281C
297C
012D
057D
07 3D
087D
12 3D
144D
174D
252D
279D
297D
322D
336D
361D
400D
430D
44 9D
468D
482D
494D
065E
034F
009H
042J
138J
202J
324J
428J

J
9
9
9
y
9
9
9
9
9
9
9
9
9
9
9
9
9
9
9
9
9
9
9
9
5
9
9
9
9
9
9
9

Water allocation (policy)
     006J

Water analysis
     275C, 130E, 131E, 147E, 161E,
     174E, 092J, 116J, 296J, 297J,
     332J

Water chemistry
     129E, 040H

Water conservation
     055B, 349J, 413J

Water consumption
     304J

Water currents
     006H, 397J
                                  943

-------
Water demand
     055B, 342D, 014J, 191J,  192J,
     304J

Water desalting
     134C

Water discharge
     339J, 373J
Water levels
020F
Water policy
094B,
443D,
101F,
360J,
420J
Water pollution
022A,
440D,
010E,
153E,
173E,
00 3H,
127J,
192J,
345J,
364J,
387J,
415J,
434J,
440J,
085C,
441D,
046E,
154E,
175E,
031 J,
144J,
219J,
346J,
366J,
388J,
425J,
435J,
00 4K
Water pollution
026B,
045D,
298D,
016E,
007J,
082 J,
189 J,
26 2J,
353J,
443J
085B,
084D,
336D,
081E,
044 J,
088J,
196J,
330J,
373J,

144C,
467D,
078E,
156E,
178E,
036 J,
145J,
231J,
353J,
382J,
390J,
429J,
436J,

control
216C,
126D,
388D,
166E,
065J,
091J,
210J,
333J,
380J,

366D,
003E,
139E,
157E,
057F,
089 J,
146J,
343J,
361J,
384J,
411J,
430J,
437J,


252C,
210D,
443D,
065F,
067J,
148J,
212J,
335J,
390J,

375D,
005E,
141E,
171E,
086F,
107 J,
191J,
344 J,
363J,
385J,
413J,
433J,
438J,


276C,
252D,
503D,
06 9F,
068J,
184 J,
213J,
348J,
416J,

Water pollution effects
     123D, 054J, 068J, 096J, 097J,
     261J, 263J, 357J, 374J, 401J,
     406J, 409J, 006K
sources
, 028A,
, 015E,
, 097E,
, 178E,
, 067J,
, 097J,
, 248J,
, 390J,
200D,
024E,
105E,
011J,
068J,
119J,
285 J,
395J,
231D,
025E,
107E,
015J,
080J,
197J,
330J,
406J,
                                 944
Water pollution
     023A, 027A
     362D, 414D
     051E, 067E
     110E, HIE
     055J, 056J
     082J, 096J
     221J, 222J
     356J, 359J
     006K
                                              Water pollution treatment
                                                   095C,  272C, 007F

                                              Water pressure
                                                   058B
                                              Water  purificati
                                                  034C,  038C,
                                                  060C,  073C,
                                                  107C,  120C,
                                                  143C,  144C,
                                                  195C,  199C,
                                                  260C,  261C,
                                                  115D,  122D,
                                                  282D,  284D,
                                                  366D,  415D,
                                                  470D,  499D,
                                                  167E,  090F,
                                                  033J,  088J,

                                              Water  quality
                                                  016A,  019A,
                                                  275C,  028D,
                                                  179D,  181D,
                                                  342D,  417D,
                                                  002E,  041E,
                                                  009F,  044F,
                                                  041J,  073J,
                                                  094J,  130J,
                                                  203J,  231J,
                                                  304J,  346J,
                                                  403J,  404J,
Water quality act
     416J

Water quality control
     035A, 019B, 021B, 304C,
     17ID, 172D, 212D, 213D,
     312D, 316D, 395D, 469D,
     488D, 502D, 004E, 049E,
     168E, 176E, 177E, 046F,
     113F, 022H, 023H, 055H,
     007J, 012J, 046J, 158J,
     192J, 203J, 219J, 243J,
     266J, 267J, 268J, 272J,
     290J, 315J, 318J, 382J,
     389J, 405J, 420J, 422J,
     427J, 430J, 442J, 443J
on
052C,
099C,
122C,
163C,
224C,
263C,
19 9D,
303D,
420D,
011E,
008H,
103 J,
070B,
029D,
193D,
418D,
077E,
080F,
07 5J,
131J,
260J,
349J,
412J,

055C,
100C,
140C,
184C,
243C,
305C,
239D,
346D,
442D,
037E,
077H,
124J,
094C,
085D,
208D,
46 9D,
087E,
107F,
091J,
187 J,
272J,
356J,
431J,

058C,
106C,
141C,
185C,
252C,
077D,
28 ID,
349D,
463D,
165E,
025J,
352J
13 1C,
118D,
319D,
499D,
121E,
116F,
092J,
189J,
286J,
380J,
432J
102D,
290D,
470D,
094E,
110F,
072H,
191J,
260J,
276J,
387J,
426J,

-------
Water quality management
     173E, 425J, 434J, 437J

Water quality standards
     130D, 131D, 275D, 046E, 079E,
     112J, 196J, 267J, 291J, 293J,
     318J

Water reclamation
     242D

Water resources
     103F, 022H, 014J, 026J, 043J,
     052J, 062J, 102J, 187J, 189J,
     230J, 363J

Water resources development
     062B, 054D, 201D, 059E, 071F,
     014H, 052J, 062J, 179J, 187J,
     188J, 191J, 230J, 269J, 273J,
     349J, 392J, 420J, 449J

Water resources management  (applied)
     004B, 051B, 062B, 009D, 054D,
     083D, 177E, 011F, 032F, 081F,
     113F, 014H, 071H, 072H, 005J,
     006J, 038J, 062J, 096J, 167J,
     265J, 315J, 349J, 363J

Water reuse
me,
142D,
217D,
416D,
097E,
099J,
249 J,
168C,
180D,
218D,
417D,
138E,
132J,
255J,
273C,
181D,
236D,
421D,
007F,
145 J,
427J,
072D,
183D,
278D,
428D,
026J,
199J,
439J
09 3D,
209D,
331D,
502D,
096J,
202J,
Water sampling
     042C, 217C, 255C, 257C, 267C,
     447C, 019E, 020E, 054E, 098J

Watershed management
     071F, 064H, 130J, 449J

Watersheds
     003A, 005A, 036A, 038A, 081F,
     007H, 017H, 052H, 066H, 072H,
     065J, 130J, 272J, 340J

Water storage
     001A, 040B, 062B, 201D, 095J
Water supply
     004B, 039B, 062B, 064B, 073B,
     109C, 185C, 293C, 208D, 261D,
     267D, 276D, 310D, 408D, 410D,
     425D, 090E, 143E, 061F, 019H,
     022H, 023H, 054H, 013J, 096J,
     099J, 102J, 140J, 141J, 152J,
     155J, 187J, 211J, 224J, 225J,
     229J, 230J, 255J, 261J, 265J,
     273J, 293J, 318J, 360J, 392J,
     403J, 419J, 420J, 422J, 441J

Water supply development
     410D, 037H, 102J, 392J

Water table
     059D, 016H, 035H, 043J

Water temperature
     156D, 159D, 160D, 161D, 179D

Water treatment
     002A, 076B, 093B, 021C, 022C,
     026C, 081C, 087C, 142C, 162C,
     183C, 206C, 244C, 260C, 262C,
     288C, 298C, 299C, 009D, 010D,
     013D, 024D, 026D, 057D, 072D,
     088D, 090D, 09ID, 094D, 095D,
     177D, 178D, 182D, 197D, 208D,
     209D, 219D, 223D, 262D, 291D,
     300D, 313D, 316D, 371D, 408D,
     474D, 498D, 499D, 003F, 027F,
     047J, 063J, 064J, 111J, 127J,
     159J, 243J, 264J, 353J

Water utilization
     020D, 080J, 328J

Waterwells
     015H

Waterworks
     087D, 201D
Weirs
     008A, 011B, 096B, 104C, 277C,
     055D, 090F
Welding
     046B

Wells
     098B, 186J

Wet-front equation
     036A
                                 945

-------
  Wind
       021E

  Winter
       118J

  Wisconsin
       011A, 249D, 076E, 205J

 Xanthate
       372D

 X-rays
      055E, 066E

 Yeast
      454D, 183J,  356J

 Zeolites
      031D,  124D

 Zero  pollution discharge
      216D,  161J

 Zeta potential
     071C,  280D, 040E

Zinc
     070E, 155E,  158E, 115J
                                946

-------
                             AUTHOR INDEX
Abel, F. H.
     268J

Aberley, R. C.
     207D

Abrahameen, J.
     166D

Abshire, R. L.
     455D

Adams,  J.  A.  S.
     04 3E

Adyaklar,  P.  G.
     035H

Afghan,  B.  K.
     099E

Agardy,  F.  J.
     023A

Agarwal, H. C.
     409J

Agg, A. R.
     037F

Agnew,  R.
     025B

Ahnoff, M.
      016E

Ahuj a,  L.  R.
      036A

Airaksiner, J. U.
      16 ID

 Aitken, A. P.
      078H

 Akatsu, J.
      013K

 Al-Adsani, A. M. S.
      441J

 Albanese,  P.
      095E
                                   947
Albertson, M. L.
     032F

Albright, M. A.
     093C

Aldworth, G. A.
     HOD

Alferova, L.
     153D

Al-Mashidani, G.
     035F

Alter, A. J.
     141J

Althaus, H.
     020J

Altshul, A.  D.
     025H

Alverson, D. L.
     059J

Amar, A. C.
     016H

Amirhor, P.
     412D

Anand, A.
     034F

Andelman,  J. B.
     296J

Anderson,  C. G.
      282C

Anderson,  E. A.
      033F

Anderson,  H. T.
      237C

Anderson,  J. B.
      401J

Anderson,  J. J.
      010B

-------
    Anderson, P.  L.
         257C

    Anderson, W.  C.
         361D

    Andersson, J.
         303C

   Andrade,  P. S. L.
         264D

   Anspaugh, L.  R.
        036E

   Anthony, H.
        076F

   Anton, W.  F.
        269J

   Antonie, R. L.
        117D

  Aoyama,  I.
       038E, 024F

  Apostol, S.
       021J

  Applegate,  M. J.
       254C

  Appleton, B.
       082F

  Appleyard,  C. J.
       132J

 Araki, Y.
      290D

 Araman, V. K.
      013D

 Ardill, J.
      273J

 Armstrong, A.
      168C

Armstrong, E. T.
      078C

Armstrong, R. A.
     358D
    Arrowsmith,  J.  D.
         014J

    Arthur, J. W.
         114J

   Arthur, R. M.
        162E

   Asce, F.
        001A

   Aschun, 0.  K.
        158D

   Ash,  R. H.
        019F

   Ashida,  K.
        278C

  Ashworth, R.  G.
        042F

  Asseed, M.  S.
       015A

  Aston, W. M.
       197J

  Atakan, Y.
       067H

  Atkinson, A.
      127D

 Auberton, G. M.
      378J

 Aue, A. I.
      269C

 Auerback, S.  I.
      090J

 Aulerich, R. J.
      232J

 Austin,  E. P.
      065C

Austin,  T. S.
      228J

Aveni, A.
     288D
                                 948

-------
Averill, D. W.
     056B

Ayoub, G, M.
     006H

Ayres, P. A.
     09 3E

Azad,  H. S.
      490D

Azuma, K.
      347D

 Bacchetti, J. A.
      203D

 Bacon, V.  W.
      349J

 Bagozkij, J. B.
       424D

 Bailey, D.  A.
       425D

 Baird,  R.  B.
       304D

  Balaraman, K.
       416D

  Balasubramanian, V.
       412J

  Baldrock,  E. H.
       139D

  Baldwin, W. F.
        239C

  Balkeslee, P.  A.
        065E

   Ball, J.  E.
        185D

   Bambenek, R.  A.
        223D

   Bandyopadhyay, M.
        014A

   Banerji,  S. K.
         365D
Banks, P. A.
     469D

Barbas, S.
     303J

Barker, R.  C.
      129E

Barkhudarov, R. M.
      011K

Barnes,  D.  A.
      07 8F

 Barrett, K. A.
      386D

 Barth, E. F.
      265C, 204J

 Bartlett, L.
      115J

 Bartolini, R. R.
      177J

 Basev,  P.  D.
       009C

 Basu, N.  K.
       001G

  Bates,  T.  E.
       003J

  Batsche, H.
       051H

  Batten, C. E.
       142D

  Baturinskaya, I. V.
       216J

  Bauer,  D. A.
        220D

   Bauer, W. J.
        190D, 244D,  334D

   Bauermann, H.  D.
        432D

   Baum, H. E.
        030J
                                     949

-------
   Baumann, E. R.
        479D, 157E

   Baumann, F. J.
        154E

   Bayer,  A. G.
        039C

   Beavon,  D.  K.
        193C

   Beckrath, H.
        315D

   Beckroth, C.
        439J

  Beech, G.
       070E

  Beer,  C.
       434D

  Beheer, N. V.  H.
      019C

  Behrens, U.
      011E

  Belaya, V. P.
      282D

  Belfort, G.
      492D

 Beliveau,  J.  G.
      110F

 Bella,  D.  A.
      091F

 Bellack, E.
      276D

 Bellinger,  S. L.
      274C

 Belyayeva,  A. H.
      342J

Benedek, A.
     171D

Benedict,  A. H.
     256J
   Benke, G. M.
        288J, 374J

   Bennett,  M.
        014E

   Benoit, D. A.
        364J

   Berg,  A.  R.
        324J

   Berg,  G.
       343J

  Bergert,  K. H.
       068E

  Bergles, J. L.
       244C

  Bergman, H. L.
       213C

  Bergougnou, M.  A.
       245J, 423J

  Berndt, H.
       474D

  Bernhardt,  H.
       017J

  Bernstein,  L
      012J

 Berry, F. A.
      04 OH

 Bertezzi, G.
      015K

 Berthouex,  P.  M.
      030F,  085J,  094J

 Bertine, K.
      046E

 Besik, F.
      274D

Bessudo, D.
     222J

Best, G. A.
     168E
                                  950

-------
Beszedits, S.
     330J

Bettaque, R.
     054H

Betz, V.
     068E

Betzer,  N.
     050E

Beuscher,  D.  B.
     467D

Bevan,  R.
      069J

 Beverly, W. C.
      156C

 Bewtra, J. K.
      483D

 Bex, J.
      065B

 Bexson, J.
      097B

 Beylin, D.  K.
      066B

 Bhattacharyya,  B.
      108F

  Bhole, A. G.
       317D

  Biahchi, R. A.
       068C

  Bills, D. D.
        316J

  Bingham,  S. W.
        297J

   Bishop,  H.  F.
        004F

   Bisogni,  J.  J.
        178E

   Bitton,  G.
        086D
Black, R. D.
     36 ID

Blackwell, W. A.
     203C

Blanc, F. C.
     113E

Blitz, E.
      014B

Blois, R.  S.
      085E

 Bloomfield, R.  A.
      287J

 Blough,  R. S.
      166C

 Bobalek, E. G.
      045F

 Bodrito, P.
      109E

 Body, R. L.
      298J

 Boeglin,  J.  C.
       463D

  Bogardi,  J.  L.
       024H

  Bogedain, F. 0.
       25 3D

  Bokowski, D. L.
       125E

  Bolitho,  V.
       163J

  Bellinger,  K.  A.
       300D

   Bondurant,  J.  A.
        377J

   Boon,  A.  G.
        486D

   Boor,  U.
        069D
                                     951

-------
Booth, F. M.
     301C
Brade, C. E.
     226D
Borthwick, P. W.
     320J

Boschen, W. 0.
     016C
Bradford, G. R.
     016A

Bradley, E. H.
     214C
Bose, B.
     014A
Brainard, E. C.
     085C
Bosje, J.
     171C
Brandsletter, A.
     010B
Bosley, R.
     233D
Braswell, J. R.
     460D
Bosshard, E.
     060D, 128D

Bouma, J.
     37OD, 464D

Bourdimos, E. F.
     017A
Brater, E. F.
     066H

Brauer, F. P.
     035E

Braun, R. D.
     105E
Bourke, J. B.
     118E
Braunscheidel, D. E.
     077J
Bousfield, S.
     44 5D
Brazel, A. J.
     133J
Bouveng, H. 0.
     062D, 433D

Bouwer, H.
     192D, 193D, 029H, 044H, 063H

Bowling, R.
     02 8D
Brecher, E. M.
     231J, 280J, 385J

Bredehoeft, J. D.
     075F

Breer, H.
     294J
Box, E. 0.
     252C
Brewer, R.
     067J
Boyd, G. B.
     023A
Brezonlk, P. L.
     163E
Boyko, B. I.
     HID
Briltz, R. P.
     240C
Boyle, W. C.
     194D, 345D, 022F, 030F

Boyle, W. H.
     299D
Brill, F. W.
     016F

Bringmann, G.
     311D
                                  952

-------
Brink, R.
     289C

Brisbin, R. L.
     329D
Buchan, S.
     066J

Buckle, K.  A.
     092E
Broadbent, F. E.
     188D, 326D

Brociner, H.
     123C
Buckley, A. D.
     415J

Buddemeier, R. W.
     041H
Brock, R. R.
     016H
Buklai, L.
     040E
Brodeur, T. P.
     220D
Bunch, R. L.
     418D
Brooksbank, H. R.
     094B

Brown, C. A.
     290C
Burchett, M. E.
     066F

Burgess, D.  E.
     029B
Brown, C. H.
     266C

Brown, D.
     357J
Burgess, D. R.
     486D

Burke, G. W. Jr.
     092J
Brown, M. J.
     377J
Burlingame, A. L.
     001E
Brown, T. S.
     061D
Burns, B. C.
     017C, 025C
Brown, W. P.
      136E

Bruce, J. P.
      260J

Bruce, R. A.
      301C

Bruland, K. W.
      064E,  014K

Brunner, D. R.
      389J

Brunner, R. E.
      285D

Bruvold, W. H.
      249J
Burns, D. E.
     006D

Burns, V. T.
     267D

Burt, J. P.
     318J

Burwell, R.  E.
     130J

Butruille, Y.
     080C

Buyers, A. G.
     237J

Buzzell, T.  D.
     164D
                                  953

-------
    Cable,  C.
         226J

    Cairns, V. M.
         140D

   Caldwell, D. H.
        265C, 027D

   Caldwell, J. S.
        003E

   Callahan,  W.  F.
        465D

   Callander, R. A.
        031B

   Gallery, R. L.
        010B

   Galloway, J. A.
       101F

  Camp,  I.C.
       047B

  Camp,  J.  R.
      022D

  Campbell,  E.  E.
      299J

  Campbell, R. D.
      402J

  Canale, R. P.
      034J

 Cao, C.
      109F

 Caperton,  C.  B.
      152C

 Cappenberg, T.
      354J,  355J

 Capper,  C. B.
      414J

Capuano, I. A.
     279C

Capuci,  R.
     095E
    Carcich,  I.
         018B,  022B,  063B

    Carlson,  H.  B.
         230C

    Carlson,  R.  0.
         246D

   Carnahan, R. P.
        105F

   Carry, C.  W.
        03 7D

   Carter,  D. L.
        377J

   Carter,  J. W.
        441D

   Carter, L.
        159C

  Carter, L. J.
       435J

  Casling, R. H.
       074D

  Cassin, J.
       037J

  Cassin,  J.  M.
       010E

 Casto,  W. R.
       016K

 Cawood, C. H.
      162J

 Cearley, J.  E.
      078J

 Cembrowlcz,  R.  G.
      005F

 Cescon,  P.
      HOE

 Cessna,  J. 0. H.
     146C

Chakravarty, S.
     146J
                                 954

-------
Chambers, C. W.
     167D

Chander, S.
     111F

Chandler, C. R.
     502D

Chandler, J. H.
     149E

Chandler, S. S.
     236C

Chandrasekaran,  D.
     055D,  090F

 Chaney,  R.  L.
      17 4 J

 Chang, A. C.
      065H

 Chang, L. W.
      024J

 Chapman, B. T.
      044F

 Chapman, W. A.
       231D

 Chapman, W. H.
       me

 Chappal, P.
       258C

  Chappeil,  G.  M.
       158C

  Charbonneau,  S. M.
       283J

  Chau, A.  S. Y.
       025E, 171E

  Chaudhuri, M.
       412D, 045J

  Chaudry,  M.  T.
        032F

   Chebotaryov, A.  I.
        010F
Cheeseman, P. C.
     036H

Cheever, K. L.
     288J

Chen, E. C.
     072E

Chen, I. B.
     450D

Chen, P.  J.
     356D

Cheng,  F.  Y.
     034J

 Chepurnayo,  G.  S.
      015C

 Chermisinoff, P. N.
      087E

 Cherry, G. B.
      238D

 Chian, E. S. K.
      391D

 Chien, J. S.
      137E,  079H

 Childs,  E.  A.
      319J

 Cho, C.  C.
      421J

  Cho, D.
       271D

  Choun, J. M.
       007C

  Christensen, G. M.
       364J

  Christian, R.  T.
       209D

  Christiansen,  C. D.
        157D

  Chubb,  L.  W.
        131E
                                    955

-------
   Church, M. R.
        074F

   Clark, D.
        038D

   Clark, D. W.
        297D

   Clarke,  A.  B.
        400D

   Clasen,  J.
        017J

   Claus, P.
        025F

  Clayfield, G.  W.
       137D

  Cleary, E. J.
       007J, 440J

  Cleary, J. W.
       081C

  Cleasby,  J.  L.
       480D

  Clements,  M. S.
       026F

  Click, C.  N.
       053B

 Clifford, K. L.
      199J

 Clingenpeel, W.  H.
      270D

 Clinger,  R. C.
      011D

 Coburn,  J. E.
      025E

 Cockburn,  R.  T.
      082B

Cockerham,  P. W.
     027F

Coerdt, W.
     106E
   Coffman, L. M.
        258J

   Cohen, J. M.
        393D, 352J

   Coleman, M. S.
        02 8A

   Coleman, R. J.
        078J

   Collier,  S.  A.
        284C

   Collins,  A.  S.
        047F

   Collins,  H. L.
        322J

  Comerton, L. J.
       009A

  Conrad,  J. R.
       364D

  Conway,  R. A.
       206D

  Cook,  E.
       3 800

  Cook,  G. H.
      320J

 Cook, P. M.
      143E

 Copenhauer, E. D.
      139E

 Corey, J.  C.
      011H

 Cornish, A. H.
      219C,  294C

 Corrill, L. S.
      139E

Corson, F. L.
      247C

Cosens, K. W.
     215J
                                 956

-------
Costello, L. S.
     019A

Cotter, J. E.
     072D

Cotton, B. L.
     304C

Cotton, P.
     045D

Cowlishaw,  W. A.
     336D

Cox, J.  L.
     041J

Cox, M.  F.
     079J

 Craddock, J. M.
      158J

 Craun, G. F.
      365J

 Crawford, N.
      071H

 Crawford, P.
      102D

 Creed, H.  K.
       227D

 Crisp, D.  J.
       066J

 Crites,  R.  W.
       187D, 257D

 Cronshaw,  H.
       065J

  Crossland, J.
       08 2 J

  Crumal, J.
       209C

  Csanady, M.
       014D

  Cullis, J. C.
       082C
Gulp, G. L.
     066D, 176D, 268D

Curl, H. C.
     091F

Cutter, B. E.
     329D

Cuttica, H. C.
     358D

Dainty, S. H.
     007A

Dajani, J. S.
     044B

Daly,  M. P.
     263D, 458D

D'Amato, R.
     202J

Daniels,  S.  L.
     109D

Dannals,  L.  E.
      089E

Dannewitz, R.
      274C

Dart,  F.  J.
      264J, 422J

 Datta, A. K.
      442D

 Davenport, C. V.
      168D

 Davis, A. C.
      118E

 Davis, E. D.
       172D, 140J

 Davis, E. M.
       45 2D

 Davis, G. K.
       154J

 Davis, J. M.
       035F
                                    957

-------
  Davis,  P.  R.
       018H

  Davis,  R.  B.
       294C

  Davister,  A.
       298C

  Dawson, R. N.
       165D

  Day,  A. D.
       176J

  Dean, R. B.
       047D, 189D, 242D

  Deb,  A. K.
       114F

 Dechambenoy,  C.
      107E

 Deering, R. W.
      314D

 Deiveekasundaram,  M.
      416D

 De Keyser,  W.  R.
      057B

 de Klerk, H.
      023J

 Delany,  R.  E.
      219C,  294C

 De Latour,  C.
      08 6D

 Delleur, J. W.
      049F

 Del Pico, J.
      473D

 De Michele, E.
      092J, 239J

 De Rienzo, P.
      248J

Derouane, A.
     144E
  Derzansky, L. J.
       402D

  Deshpande, A. W.
       047J

  de Veer,  S.  M.
       078E

  Derries,  J.
       189C

  Dick, R.  I.
       453D

  Dickie, L. M.
       058J

  Dickman,  M.
      009J

 Diebler,  H. G.
      160C, 274C

 Di Gianne, F. A.
      489D

 Di Giano, F. A.
      078F

 Dillon,  N.
      002F

 Ditmars,  J.
      374D

 Dixon, D.  J.
      188J

 Dmitriev,  A.  S.
      102C

 Dobson, H.  F.  H.
      381J

 Doi,  K.
      347D

 Doig, T.
      016J

Dolan, R.
      106J

Dolinsek, F.
     013E
                                 958

-------
Dolobovskaya, A. S.
     032C

Donaldson, D.
     152J, 224J

Dontsova, M. I.
     034C

Dorcey, A. H. J.
     038J

Dorn,  P.
     359J

Doss,  R.  C.
     081C

Dotson,  G.  K.
      245D

 Dougan,  W.  K.
      161E

 Dougay,  P.  P.
      207D

 Douglas, J. H.
      46 ID

 Downey, R. L.
       018E

 Downing, A. L.
       335J

 Dracup,  J.  A.
       061F

 Drago,  M.
       HOE

  Dressier,  J.
       421J

  Dressier,  R.  L.
       330D

  Drown,  D.  B.
       29 2 J

  Dryden, F. D.
       037D

  Dryman, W. R.
       15 OD
Dube, D. J.
     205J

Dubois, E. M. R.
     205C

Dubouchet, J. L.
     216C

Duchateau, G. F.
     172C

Duddles, G.  A.
     204J

Dudley,  A. W. Jr.
     024J

Dujmovie,  M.
      HIE

Dunbar, J. 0.
      178J

 Durazo, R.
      034B

 Durrum, E. L.
      075C

 Durst, R. E.
      04 5F

 Dutton, C.  S.
      468D

 Duval, L. A.
      074C

 Dyck,  A.  W. J.
       151J

 Dyment,  R.
       054D

 Dyson, J. M.
       094B

  Eak-Hour, C.
       019E

  Echelberger,  W. F.
       407D

  Economy, J.
       300C
                                    959

-------
   Eda,  M.
        423D

   Edgerley,  W.  H.  L.
        090E

   Edwards,  A. B.
        496D

   Edwards, C. A.
        053J

  Edwards, R. A.
       092E

  Egan,  W.  G.
       010E

  Eglinton,  G.
       001E

  Ehly,  J.
      302J

  Ehrlen, L.
      044J

  Eklund, C. D.
      383J

  Elder, L. L.
      057B

 Ellington, C.  P.
      179J

 Ellis,  B.  G.
      061H

 Elphick, A.
      369D

 El-Ramly, N.
      081H

 Elvins, B.  J.
      029E

 Emerick, R. J.
      155J

Emmons, D. R.
     15 6C

Emrath,  E.  E.
     230D
   Endelman, F. J.
        376J

   Engelbrecht, R. S.
        327D,  412D

   English,  J.  N.
        03 7D

   Engman, E. T.
        092F, 058H

   Enke, C.   G.
       017E

  Epstein,  E.
       045H

  Epstein,  J.
       005E

  Erdelysky, Z.
       134E

  Erickson,  A.  E.
       16 9J

  Erickson,  L.  E.
       015D, 016D

  Ermakov, I. S.
       070D

 Ermert, U.
      43 2D

 Ernstrom,  E.  K.
      077J

 Escher, E.  D.
      243J

 Etheridge,  D.  C.
      013B

 Evans,  J. D.
      243D,  338D

 Evans, R. L.
     013D,   025D,  134J

Evans, W. H.
     141E

Evard, W. M.
     100C
                                 960

-------
Everett, J. G.
     227D, 228D

Evers, D.
     366D

Fahlenbock, T.
     087J

Fairweather, V.
     086B

Falcke, F.
     078B

Falkner, C. H.
     421J

Fan, L.-T.
     015D, 016D

Fang, H. H. P.
     391D

Farell, J. H.
     06 8C

Farha,  F.
     252C

Farquhar,  G.  J.
     080F

Farr, F.
     215J

Farrell, B.
     047D

Farrell, R. P.
     063B

Fasoli,  U.
     093F

Faust,  S.  D.
      342D, 356D

Felbeck,  G. T.
      395J

Fell, J.
      356J

Fennell,  H.
      321J
Fenton, T. E.
     070B

Ferguson, B. B.
     301D

Ferm, R. L.
     161C

Ferrar, T. A.
     317J

Fetter, C. W. Jr.
     009H

Field, R.
     022A, 034A, 019B, 061B, 074B

Filip, A.
     031E

Flnan, M.
     127D

Firth, R. L.
     249C

Fischer, J. A.
     427J

Flach, K. W.
     172J

Flanagan, M. J.
     08 ID

Fleischmann, L. W.
     177C

Fleming, R. N.
     069F

Fleming, W. G.
     008E

Fleps, W.
     167E

Fletcher, G. C.
     168C

Flood,  F. J.
     059D

Floodgate,  G.  D.
     066J
                                  961

-------
   Foehrenbach, J.
        362J

   Ford,  J.  H.
        050J,  322J

   Foree,  E.
       380D

   Forester, R.
       069E

   Forge,  C. 0.
       075C

  Fossom, G. 0.
       392D

  Foster, D.  H.
       327D

  Foster,  H.
       049D

  Foster,  J. H.
       04 9D

  Fotiyeva, N.  N.
       008G

  Fournier, C. D.
       019F

 Fournier, E.
      118C

 Fowler,  D. P.
      009G

 Fowlie,  P.  J.  A.
      137J

 Fox,  G.  T.
      371D

 Fox,  I. K.
      03 8 J

 Frache, R.
      HOE

Fragoso,  R.
      222J

Francois, L.  E.
     012J
   Franke, P.
        284D

   Fraser, J. H.
        199C

   Frazier,  R.  P.
        277J

   Freese, R.
        029C

   Freeze, R. A.
        054F

  Frenke, K.
        037J

  Frenzel, H.
       077E

  Fretwell,  G.
       433J

  Friedlander,  J.
       384J

  Fries, H.
       081B

  Froman, C. A. Jr.
       080D

  Frost, T. P.
      323J

 Froulunds,  B.
      269C

 Frye,  F. C.
      05 OB

 Fryer, G. E.
      043E

 Fu, Y.  C.
     399J

 Fuchs,  W.
     204C

 Fuge, R.
     101E

Fuhs, G. W.
     072J
                                 962

-------
Fujii, T.
     03 2 J

Fujinaga, T.
     09 IE

Fuller,  C. E.
      219D

Fullerton, R. W.
      45 ID

Fulton,  G.  P.
      262D

 Funk, W. H.
      115J

 Gabriel, G. F.
      260J

 Gadkari, S. K.
      047J

 Gaffke, J. N.
      319J

 Gahler, A. R.
       063E

  Gammon, A.
       026H

  Ganczarczyk,  J.
       04 3D

  Gangolli,  S.  D.
       221J

  Ganley, R. J.
       012A

  Garber, I.
        048J

  Gardiner, D.  K.
        118J

   Garrison,  R.  L.
        27 5D

   Garry, J. A.
         386D

   Carton, A.
         386D
Gary, H. L.
     038H

Gascoigne, P.
     298D

Gasner, L. L.
     401D

Cast, R. G.
     379J

Gaube,  E.
     078B

Gaudy,  A.  F.
      119D, 360D, 405D

 Gautreau,  J.
      017B

 Gburek, W. J.
      058H

 Geen, G. H.
      410J

 Gegauff, R.
      344J

 Geinopolos,  A.
      397D

 Geisinger,  D.  W.
      036D

  Geldreich,  E.  E.
       411J

  Gellman, I.
       161J

  Genetelli, E.
       241D

  Genon, G.
       09 3F

  Gentry, R.  E.
        318J

  Gerber,  R.  G.
        272J

  Geyh,  M.  A.
        06 8H
                                    963

-------
Ghosh, D. K.
     315J
Girling, R. M.
     155D
Ghosh, M. M.
     136E
Giusti, D. M.
     206D
Ghosh, S.
     364D, 055F

Gibb, J. P.
     208D
Gjeasing, E. T.
     112E

Gladkov, B. A.
     153D
Gibbs, C. F.
     130E
Glass, G. E.
     USE
Gibbs, J.
     03 4F
Glasson, H. H.
     002B
Gibbs, R. H.
     054J
Gleisberg, D.
     003D
Gilbert, J. B.
     265J
Glessner, W. R.
     082B
Gilbert, P. H.
     227D

Gilbertson, M.
     381J
Glover, G.
     023B,  026B

Gluck, W. R.
     007H
Gill, W. N.
     402D

Gillespie, W. A.
     069J
Goda, T.
     122D, 423D

Goddard, J. E.
     131D
Gilliam, J. W.
     383J
Godfrey, K. A., Jr.
     060B
Gilliland, M. W.
     077F
Goeppner, J.
     121D
Gills, E.
     155E
Goldberg, A.
     253J
Gilmour, J. T.
     376J

Ginaven, M. E.
     215C
Goldberg, E. D.
     064E, 031J, 014K

Goldfield, J.
     092C
Ginzburg, G. 0.
     275J
Goldman, C.
     018J
Girardi, E.
     015K
Goldman, J. C.
     007F
                                  964

-------
Gonzalez-Cortes, A.
     222J

Gordon, C. R.
     16 8D

Gosselin, C.
     007G

Goswami,  S.  R.
     002D

 Gould, B. W.
      047E

 Grabow, W.  0. K.
      029D

 Graham, H.  J.
       112D

 Graham, P.  H.
       019A

 Grajcer, D.
       340D

  Grant. R-  A.
       071J

  Grasso, P.
       221J

  Gratzl, J.  S.
        025F

  Gray, D. A.
        186J

  Gray, S.  L.
        328J

   Greco, V.
        092C

   Green, L. R.
        324J

   Green, R.  E.
        412J

   Greening, E.
         214D

    Grenney,  W.  J.
         091F
Gresko, T. M.
     394D

Gribbin, J.
     392J

Grieshaber,  0. A.
     016C

Grimmett,  E.
     273C

Gritzuk,  M.
      250D

 Gross, A. C.
      17 8D

 Gross, M. G.
      049H

 Gross, S. P.
       380J

 Gruener,  N.
       223J

 Grundy,  R.  D.
       198J

  Grzywienski, A.
       010A

  Guarino, A. M.
       401J

  Guarino, C. F.
       496D

  Gugelmann, A.
        108E, 133E

  Guinn,  V.  P.
        060E

   Guiver, K.
        186J

   Gujer, H.
        103C

   Gumbatov,  R.  P.
        102C

   Gunther,  F. A.
         180E
                                      965

-------
Guo, H. M.
     140D
 Hall,  R.  M.
      042E
Gupta, B.
     409J

Gupta, K.
     17 OE
 Hall,  W.  A.
     032F,  103F

 Haller, G.  L.
     129E
Gupta, M. K.
     025B
Halligan,  B.  J.
      114J
Gusberti, L.
     027H
Halls,  S.
     093E
Guter, K. J.
     406D

Gutknecktz, W. F.
     066E

Guzdar, A. R.
     075H
Ham, R. K.
     194D, 345D

Hamann, C. L.
     066D, 176D

Kamano, T.
     218C
Gyori, S. A.
     160C
Hambley, B.
     108D
Haar, L. W.
     227C
Hammerton, D.
     278J
Hablb, J.
     034H
Hamoda, M.
     043D
Hagihara, K.
     05 9F
Hampton, Q. L.
     307C
Hagiwara, K.
     440D

Hagler, R.
     270C
Handin, L.
     464D

Handley, J.
     064F
Halmes, Y. Y.
     102F, 103F
Haney, B. J.
     063D
Hair, M. E.
     010E

Hall, E. S.
     013F
Hanisch, B.
     004D, 199D

Hanks, R. J.
     150J
Hall, J. A.
     171E

Hall, J. B.
     14 2D
Hansen, E. A.
     076E

Haralson, R. H.
     042J
                                  966

-------
Harbo, R.
     361J

Hardcastle, J. E.
     250J

Marker,  R. P.
      131J

Harlin,  C. C.
      256D

 Harris,  A.
      16 2C

 Harris,  A. R.
      076E

 Harris, F. L.
      282J

 Harris, R. H.
       231J, 280J,  385J

 Harris, R. J.
       255C

  Harriss,  R.  C.
       16 OJ

  Harsanyi, E. G.
       015E

  Hart,  J. S.
       076H

  Hart,  R. D.
        256J

   Hartmatm,  L.
        119E

   Harvey, P.
        024B

   Hasebe, S.
         37 2D

   Hashimoto, S.
         295C

   Hasit,  Y.
         044B

    Hasselmann,  D. E.
         12 ID

    Hasting, A. P. M.
         441D
967
         Hatfield, J.
              497D

         Hathaway, W.
              047D

         Hattersley,  R.
               005J

          Hattori, A.
               008J

          Hattori, R.
               057E

          Hawkins, S.
               014J

          Hawthorne,  J.  C.
                050J,  322J

           Haycock,  D. H.
                150D

           Hayden, B.
                106J

           Hayre, H.  S.
                024C

           Hays,  G. E.
                093C

            Hayward,  D.
                 033B

            Hazel, F.
                 268C

            Hazelwarts, D. E.
                 438D

            Heaney, J. P.
                  028B

            Heaton,  R.  E.
                  027E

             Heckroth, C. W.
                  294D, 431J

             Hedenland, L. D.
                  47 5D

             Heeps, D. P.
                  099F

             Hegedus, J.
                   056H

-------
 Heidman,  J.  A.
      389J
 Hills,  D.  J.
      289J
 Heindl,  L.  A.
      014H
 Himmelblau,  D.  M.
      027F
 Heinke,  G. W.
      056B, 148D,  246 J

 Hendrickson, E. R.
      127J
 Hinesly,  T.  D.
      024D,  128E

 Hinkle, C.
      301D
 Heneghan, W.  F.
      487D
 Hlnrlch,  H.
      122E
Henley, T. D.
      250C
 Hirose,  K.
      037B
Henry, J. G.
     162D
 Hirs, G.
     207C
Henry, K.
     00 2G
Hiser, L. L.
     073E
Herschy, R. W.
     152E
Ho, S.
     345D
Hess, A. F.
     353D
Hoadley, A. W.
     460D
Hess, C. E.
     252J
Hobson, P. N.
     445D
Hettling, L. J.
     063B
Hoche, G.
     357D
Hibberd, R. L.
     041F
Hodgson, K. 0.
     095J
Hickin, E. J.
     021H
Hoeppner, S.
     098B
Hickman, R. E.
     010D
Hoffman, S. B.
     286J
Higgins, P. M.
     29 OJ
Hoffmann, W.
     28 5D
Hilbert, R. B.
     230J
Hofstein, S. R.
     286C
Hill, D.
     418J
Hogan, J. W.
     244J
Hill, R. D.
     379D
Hogg, W. R.
     292C
                                  968

-------
Holley, E. R.
     079F
Hoyland, G.
     441D
Hollman, K. W.
     304J
Hsu, J. S-y.
     164E
Holm, H. W.
     079J
Huang, J. Y. C.
     479D
Holynska, B.
     123E
Huber, W. C.
     028B
Holzworth, R. T.
     230J
Hubly, D. W.
     480D
Honegger, R. L.
     217D
Huck, P. M.
     080F
Hood, J. W.
     151C
Huckabay, G. W.
     036E
Hook, J. E.
     324D
Hudenko, B. M.
     153D
Hopson, N. E.
     436J

Hopwood, A. P.
     291C
Hufen, H. T.
     041H

Huggins, H. D.
     263C
 Hornberger, G. M.
      074F

 Horsefield, D. R.
      181D
Hughes, C. D.
      154D

Hughes, D. E.
      446J
 Horst,  R.  L.
      317J

 Horstkotte,  G.  A.
      027D

 Horvath, R.  J.
      251C

 Hosking, R.  J.
      036H

 Houser, E. A.
      275C
 Hughes, R.  C.
      057B

 Hughes, R.  G.
      100C

 Hulanicki,  A.
      116J

 Hull, A. P.
      006K,  008K

 Hull, A. R.
      228J
 Howard, D.  W.
      088E,  063F

 Howe, R. S.
      009D
 Humenick,  M.  J.
      018D, 185D

 Humiston,  G.  F.
      304C
                                  969

-------
 Hunsinger, R.  B.
      112D
 Ingham,  G.  S.  N.
      434J
Hunter,  I.
      356J
 Ingols,  R.  S.
      025J
Hunter, J. S.
      156D, 003F

Hunter, J. V.
      027A, 254D, 319D, 071E

Hupka, G.
      053D

Hurley, J. T.
      006E

Hurley, T. L.
      223D
 Inoue,  M.
      260D,  160E

 Inoue,  S.
      349D

 Inoue,  Y.
      036E,  024F,  001K

 Insley, M.  G.
      088E,  063F

 Intorre, B.
      248J
Hurst, G. E.
     004C, 131J

Hurtubise, F. G.
     142J

Hutchison, R. M.
     008B

Hutzler, N.
     022F
Ipatova, K. G.
     009C

Irhoff, K. R.
     232D

Iriye, T.
     276J

Ishibashi, I.
     400J
Hwang, C. P.
     097E

Hynes, H. B.
     394J

Ichiki, M.
     235C

Idyll, C.
     060J

Ikeda, H.
     278C
Ishihara, T.
     051D

Ishii, M.
     235C

Ishimori, T.
     013K

Iwamoto, S.
     232J

Iwata, Y.
     017D
Illig, E. G.
     399J
Iwata, S.
     010H
Imamura, T.
     240D

Imhoff, R.
     425J
Izumi, K.
     122J

Jackson, E. B.
     002K
                                  970

-------
Jackson, J.  E.
     17 4C

Jacobson, A. R.
     331J

Jaggi, H.
     071B

James, D. B.
     321J

James,  K. H.
      101E

 James,  L. D.
      363J

 Janicki, V.
      032A

 Jank, B. E.
      140D

 Janson, L-E.
      077B

 Jarosewich, E.
       054J

  Jarvis, C. L.
       040F

  Jassby, A.
       050F

  Jayaraman, R.
       023E

  Jelinek,  C.
        180J

  Jenkins,  C.  E.
        061J

   Jenkins,  R.  D.
        47 8D

   Jeris, J. S.
        059D, 434D

   Jespersen, F.
        055B

   Jobes, H. D.
         091J
Joeres, D. F.
     421J

Johannessen, J. M
     248C

Johanson, E. E.
     068C

Johanson, J. B.
     065H

Johanson, K. J.
      341D

 John,  M. K.
      302D,  158E

 Johnson, D. W.
      402J

 Johnson, E. A.
      326J

 Johnson, H. E.
       007B

 Johnson, J. F.
       337D

  Johnson, J. L.
       244J

  Johnson, J. S.
       134C

  Johnson, L. G.
       313J

  Johnson,  W. E.
        199C

  Johnston, D. W.
        263J

   Jolley, R. L.
        211D

   Jones, G. M.
        081D

   Jones, K.
         425D

   Jones, M. K.
         270D
                                      971

-------
    Jones,  P.  H.
         33 9D

    Jones, R.  L.
         128E, 259J

   Jones, S. B.
        268C

   Jones, T. C.
        268C

   Jones, T. I.
        162C

   Jones,  W. F.
        041F

   Joseph, R.  T.
        105C

  Joshl, N. S.
       316D, 047J

  Joyce, J. M.
       066E

  Joyce, R.  T.
       383J

  Jung,  H.
       092D

  Justice, R.  L.
      289C

 Kabeya, H.
      032J

 Kadooka, K.
      057E

 Kaelin, J.  R.
      053C,  179C,  201C,  272C

 Kaiser,  K.  L.
     070J

 Kaiser,  N.
     156E

Kalan, E. B.
     268C

Kale, C. K.
     393J
    Kalff,  J.
         396J

    Kalinske,  A.  A.
         075D

    Kalitsun,  V.  I.
         03 4D

   Kamata, 0.
        017D

   Kamath,  P.  R.
        046J

   Kandler,  J.
        003D

   Kanehiro, Y.
        412J

   Kanunnikova, L. S.
        309D

  Kao,  S. E.
       067B

  Kaplovsky, A.  J.
       241D

  Kardos, L. T.
       322D, 324D, 325D,  328D

  Kasatiya,  S. S.
       051E

  Kato,  S.
       290D

 Kato, T.
      348D

 Katzer, M.  F.
      112C

 Kaufman, W. J.
      119J

 Kaushik, N. K.
      394J

 Kauwling, T.  J.
      345J

Kawahara, 0.
     122D,  423D
                                  972

-------
Kawahata, M.
     014C

Kawai, S.
     312J

Kawazoe,  S.
      210D

Kawert,  K. G.  K.
      243C

 Kaye, J. H.
      035E

 Kaye, S. V.
      090J

 Kaziyev, B. M.
      072B

 Kearton, W.
       048J

  Reefer, T.  N.
       112F

  Keenan, J-  D.
       03 5D

  Keeney, D. R.
       37OD, 464D, 376J

  Keller, F. R.
       076C

   Keller, H.  F.
        150C

   Keller, J.
        150J

   Keller, 0.
         270C

   Keller, R.  J-
         022E

   Kelley, S.  T.
         286J

    Kelly, G.
         064H

    Kelly, M. G.
          07 4F
Kelton, P.
     07 3H

Kelway, P- S.
     038F

Kern, J. A.
     429J

Kemp,  G.  D.
      065C

 Kenard, R. P.
      056E

 Kennaugh, J. H.
      448J

 Kennedy,  J-  F.
       028F

 Kennedy,  S.  R.
       173C

  Kerfoot, W.  B.
       395D

  Kerl, J. F.
       235J

  Kerr, S. R.
        151E

  Kershaw, M.
        360J

   Kesner, W.  D.
        324J

   Ketchum, B. H.
        247J

   Ketchum, B. T.
        395D

   Ketchum, L. H., Jr.
        012D

   Keup,  L.  E.
         413J

    Keve,  T.  K.
         055H

    Kharaka, Y.  K.
         040H
                                       973

-------
Khomylov, G. S.
     225C
Kiss, G. S.
     165C
Kiezyk, P. R.
     019J
Kitahara, S.
     117E
Kilmer, V. J.
     383J
Kite, G. W.
     088F
Kilney, E.
     073C
Klapwijk, A.
     012E
Kimuro, Y.
     032J
Kleester, S. A.
     173E
Kincannon, D. F.
     272D
Klei, H. E.
     205D
King, A. S.
     206C

King, D. L.
     33 2D
Klein, S. A.
     030D, 478D

Klemas, V.
     397J
King, J. A.
     067C
Kluesener, J. W.
     026A
King, L. D.
     368D
Kluge, D. L.
     116D
Kingsford, M.
     090E
Knight, C. H.
     108D
Kingsley, 7. H.
     006F
Knudsen, H. J.
     167J
Kinman, R. N.
     17 OD
Kobayashi, H.
     454D
Kinner, P.
     397J
Koch, C. M.
     035B
Kinrad, J.
     009E
Koehler, D.
     310D
Kirby, C. F.
     308D
Koepf, H. H.
     040J
Kirby, W.
     06 IE
Koganovskii, A. M.
     015C
Kirkham, D.
     015H
Kohout, R.
     281D
Kishore, R.
     060E
Koide, M.
     064E, 014K
                                   974

-------
Koikawa, S.
     349D

Kollar, K. L.
     067J, 419J

Komarov, V. D.
     011F

Kondon, S.
     170C

Konikow, L. F.
     075F

Kontur, I.
     085F

Kopfler, F. C.
     051J

Kosaric, N.
     245J, 423J

Kose,  M.
     347D

Kothandaraman, V.
     035A, 467D,  134J

Kott,  Y.
     050E

Kountz, R. R.
     477D

Kovacs,  S.
     177E

Kovalenko, V.  P.
     17 5D

Kozaczkowski,  S.
     274J

Kozak, M.
     020F

Kozlorchunas,  E.  F.
     225C

Kozlowski, M.  E.
      096F

 Krainov,  S.  R.
      216J
Kratzer, B. P.
     033C

Kratzl, K.
     025F

Kraus, G.
     156E

Kraus, K. A.
     134C

Kreissel, J. F.
     37 8D

Krenke, G.
     083F

Kreske, W.  L.
     022D

Krishen, P. H.
     033A

Kritikos,  H.
     082E

Kriz,  J.
     005H

Krug,  E.  K.
      217D

Kruivak,  J. A.
      420J

Krylova,  M. G.
      309D

Ku, W. C.
      346J

 Kucharczk, N.
      089E

 Kudo,  A.
      076H

 Kudrna, F.
      064H

 Kuehn, R.
      311D

 Kuehn, W.
      106E
                                   975

-------
Kuentzel, L. E.
     036J

Kugelman, I. J.
     398D, 421D, 352J, 393J

Ruhr, R. J.
     118E

Kuji, Y.
     346D, 348D

Kulperger, R. J.
     501D

Kulskii, L. A.
     034C

Kunkle, S. H.
     323D

Kuo, C. L.
     304D

Kurata, Y.
     124D

Kyushin, S.
     476D

Labadie, J. W.
     032F

LaBarre, N.
     021A

Laburn, R. J.
     191J

Ladd, T. A.
     480D

Ladouceur, E.
     098D

La Fleur,  P. D.
     155E

La Grega,  M. D.
     035D

Lailas, N.
     444J

Laitinen,  H. A.
     027E
 Lake,  B.  G.
     221J

 Lake,  L.  J.
     36 9D

 Lakshmanan,  S.
     042H

 Lamb,  R.
     117J

 Lament, P.
     273C

 Lance, J. C.
     193D

 Landis, H.
     23 3J

 Lang,  M.
     222D

 Langford, J. C.
     061J

 Lantz, P. M.
     135J

 Lanyon, R.
     047H

 Larkin, D. G.
     269J

 Lash, R. W.
     016B

Latall, R. C.
     011C

Lau, L. S.
     041H

Laughlin,  W. C.
     034F

Lauza,  P.
     052E

Lavado, R. S.
     035J

La Valle,  P.
     002J
                                  976

-------
Lawrence, A. W.
     384D, 399D, 178E, 072F

Lawson, C. T.
     20 6D
Lemke, A. E.
     114J

Lemmel, D. E.
     018E
Lawson, P.  D.
     16 OD
Lenster, J.
     097F
Leadem, T. P.
     402J
Leonov, A. V.
     087F
Leatham, W.
     397J
Le Roy, R. F.
     208C
Le Blanc, H. P.
     245C
Leung, R.
     099E
Le Blanc, P. J.
     159E
Leutniler, C.
     269D
Lech, R. F.
     446D
Lewandowski, R.
     116J
Lechner, L. J.
     17 2D
Lewis, M. J.
     364J
Le Clair, B. P.
     098D
Li, W-H
     096F
Leclerc, H.
     019E
Liao, P. B.
     481D
Le Compte, A. R.
     191C
Liberman, S. J.
     160E
Lee, G. F.
     026A, 086E, 205J

Lee, K. N.
     032D
Lichwa, J.
     009E

Licsko, I.
     040E
 Lee, P. L. Y.
     07 5C
Lieb, A. J.
     316J
 Lefur,  J.
      302C
Lieberman, R.
     150E
 Lehrer,  I.  H.
      100E
Light, D. J. N.
     189C
 Lejcher,  T. R.
      323D
Ligman, K.
     022F
 Leland,  H.  V.
      139E
Ligon, J. T.
     017H
                                   977

-------
   Lin, R. Y.
        300C

   Lincoln, R. M.
        276C

   Lindberg,  S.  E.
        160J

   Lindsay,  W. L.
        171J

   Lins, S.
        025D

   Linsley, R.
       071H

  Linton,  K. B.
       069J

  Lippolis, M. T.
       052E

  Lishka,  R.  J.
       003E

  Little,  L.  W.
       03 ID

  Lloyd, A.
       083E

  Lloyd, A. C.
       221J

 Lock, M.  A.
      394J

 Locke, M.
      105J

 Loehr, R. C.
      341D,  482D

 Loftus, K.  H.
      151E

 Loll,  U.
      283D

Long, D. A.
     477D

Long, H. G.
     277C
   Long, V. E.
        277C

   Longman, M. D.
        292C

   Lonnquist,  C.  G.
        094F

   Lonsky,  W.
        025F

   Lopata,  J.  R.
        269D

   Lord, C. J.
        15 7 J

  Loring, B. A.
       037H

  Louboutin, R.
       302C

  Loucks,  D.  P.
       138E

  Lubienska, B.
       274J

  Luck,  E.
       106C

  Ludzack, F. J.
      075E

 Lue-Hing, C.
      320D

 Luehr, H.  P.
      018F

 Luescher,  0.
      060D,  128D

 Lundberg,  E.  A.
      082H

 Lundquist
      163C

Lush, D. L.
     394J

Luttinger, L.  B.
     357D
                                 978

-------
Lutz, J.
     383J

Lyman, B. T.
     246D

Lynch, G. P.
     437D

Maar,  I.
      079E

 Macagno, E.  0.
      028F

 Macauley, D. C.
      366J

 Mac Gregor, J. M.
       379J

 Mackay, D.
       019J

 MacKenzie,  W. N.
       100J

  MacKinnon, K. L.
       075C

  MacNelis, D. N.
       150E

  Maddinson, C.
       081E

  Madern,  J. P.
        052C

   Maeda, M.
        34 8D

   Magdoff, E. R.
        370D,  464D

   Magony, L.
         073B

    Mah,  R.  S.  H.
         069B

    Mahmood,  K.
         031F

    Maier, M.
         156E
Maier, W. J.
     049E

Mainka, E.
     106E

Maj, M.
      116J

Majeron,  F.
      084C

 Majori, L.
      015J

 Maki, H.
      032E

 Malina, J. F., Jr.
      061D

 Mallon,  H. J.
      019A

 Malouf,  J. B.
       116F

  Malpas, J. F.
       076D

  Malueg, K. W.
       236J

  Malz, F.
        334J

  Mani,  V.  V. S.
        035H

  Manke,  A.
        114E

   Manot, M. G.
        190C

   Mansfield, W. W.
        135E

   Maqsood, R.
         17 ID

   Mara,  D. D.
         020E

    Marcikic,  S.
         019F
                                      979

-------
   Marey, A. N.
        011K

   Markalunas, J. j.
        115D

   Markin,  G.  P.
        050J,  322J

   Marks, D. H.
        033A

   Markus,  F.  I.
        113D

   Maroney, W. J.
        297C

  Maroschak, E. J.
       045C

  Marsh, J.
       240J

  Marshall, I.
       065C

  Marshall,  W.  L.
       135J

  Martin, A. J.
       351J

  Martin, C.
       318D

 Martin, D. F.
      098J, 016J

 Martin, D. W.
      314D

 Martin, K. L.
      16 9D

 Martin,  R.  J.
      409D

 Maruoka, S.
      312J

Mason, R. E.
      006G

Mason, R. W.
     252J
   Mason, S. G.
        160E

   Massaro, E. J.
        049J

   Masse,  A. N.
        037D

   Masson,  T.  J.
        225J

   Masters,  H.  E.
        022A

   Mastropietro, M. A.
        03 6D

  Masuyama, K.
        240D

  Matalas, W. C.
       059E

  Matlock,  W. G.
       018H

  Matras,  E.  J.
       307C

  Matsche, D.  E.
       334D

 Matsuda, Y.
       240D

 Matsumoto, T.
      260D

 Matsumura, A.
      240D

 Matsuno,  Y.
      210D

 Matsuoka,  H.
      34 6D

 Mattheas, G.
      067H

 Mattingly, G.
      110F

Mattison, V. R.
     114J
                                 980

-------
Mauk, C. E.
     27 5D

Maurer, D.
     397J

Mauzy, M.  P.
     277J

Mavichakana,  N.
      250J

 Mavinic, D. S.
      48 3D

 Mavrovic, I.
      281C

 Mawer, P. A.
      060F

 Maxam,  D. R.
      067C

 Maxwell,  E.
       086D

  Mayzlik,  D.  L.
       289D

  McCalla, T. M.
       130J

  McCandless, W. J. C.
       160C

  McCaull, J.
        082J

  McCleese, D.
        358J

   McClure, G. W.
        008D

   McComas, F.
        361J

   McConnel, H. L.
         049E

   McCoy,  F.  C.
         157C

   McCreight, L.  R.
         209J
McCullough, C. A.
     022H

McDaniel, H. C.
     007B

McDuff, D. P.
     085D

McFarren,  E.  F.
     003E

 McGhee,  T. J.
      439D

 McKay, F.  W.
      225J

 McKee, J. E.
      255J

 McKeown,  J.  J.
       256J

 McKerchar,  A.  I.
       049F

 McKibbe,  J. W.
       002C

  McKim,  J. M.
       364J

  McKinney, R. E.
       084F

  Mclaughlin, S. J.
       091B

  McLean,  E.  0.
       020H

  McLeay,  D.
        357J

   McMenamin, S.  H.
        021C

   McMichael, F. C.
        001F

   McMichael, W. F.
        215D

   McPherson, M. B.
         081F
                                     931

-------
McQuade, R. E.
     219D
Metcalf, S. M.
     37 ID
McQueen, J. R.
     103J
Metlin, S. J.
     399J
McQuivey, R. S.
     112F
Meyer, J. A.
     276C
McShan, M.
     340D

Meckelborg, E. I.
     15 9D
Meyer, P. A.
     096E

Meykar, 0. A.
     416J
Medbery, H. C.
     062J
Michel, H. L.
     277D
Medlar, S.
     313D

Medvedev, M. I.
     034C
Michener, D. W.
     020H

Middlebrooks, E. J,
     270J
Mehrle, P. M.
     287J

Mehta, S. C.
     44 7D
Middleton, A. C.
     399D

Mielke, J. H.
     117D
Main, R. G.
     099F

Mekler, Y.
     27 5 J

Melsted, S. W.
     173J
Miller, D. J.
     445J

Miller, D. W.
     36 2D

Miller, J. A.
     277J
Menzel, R.
     253C
Miller, R. A.
     391J
Meriaux, S.
     033H
Miller, R. D.
     448D
Merrill, W. H., Jr.
     049B

Mertens, J.
     079C
Miller, R. H.
     062H, 170J

Miller, R. W.
     225J
Mesengisser, M. J.
     070D
Milne, J. B.
     021A
Metcalf, C. C.
     116D
Milotich, F. J.
     231C
                                  932

-------
Mineat, R. A.
     363D

Miner, J. R.
     083J

Minton, G. R.
     082D

Mira, D.
     132E
Mohanty, S. K.
     011B

Mohr, A. W.
     028H

Mohsin, M.
     129J

Moldenhauer, W. C.
     024A
Mirer, F. E.
     288J
Molnar, G.
     057H
Mishra, B.
      316D
Molof, A.
     138C
Mishra, P. N.
     015D, 016D

Mitchell, C.
     425D

Mitchell, R.
     086D, 301J,  308J

Mitra,  S. K.
     056J

Mix, T. W.
     053F

Mixon,  F. 0.
     053B

Miyake, Y.
     004K, 005K

Mizukami, Y.
     346D

Modesto, F. A.
     065C

Moeller, U. J.
     06 9D

Moetsch, H.
     060D,  128D

Moghissi, A.  A.
     150E

Mohanrao,  G.  J.
     055J
Molof, A. H.
     354D, 113E

Mondoux, R. G.
     108D

Monro, J. C.
     033F

Montgomery, H. A. C.
     054E

Monti, R. P.
     097D, 174D,  279D

Moore, B. D.
     06 ID

Moore, J. D.
     452D

Morey, E. F.
     177D

Morgeli, B.
     06 7D

Mori,  K.
     044D

Mori,  M.
     495D

Moriguchi,  Z.
     408D

Morikawa, M.
     346D,  347D
                                   983

-------
   Morisawa, S.
        001K

   Morris, E. E.
        267J

   Morris, G. E.
        083B

   Morris, H.  D.
        368D

   Morris,  J.
        321J

  Morris,  R. L.
        313J

  Morrison, R. D.
       01 ID

  Morrison, S. M.
       16 9D

  Moser, H.
       053H

  Moss,  F.  H.
       082B

  Moss,  W.  D.
      299J

  Mottet, N. K.
      298J

 Moudgil, B. M.
      147J

 Mougenot, G.
      096B

 Mourlan,  J.
      080C, 205C

 Movlar, A.  E.
      139J

 Mrklas, L.
      02 OD

 Mudrack, K.
      225D

Mueller, J. A.
     434D
   Mueller,  W.
        078B

   Muennich, K.
        067H

   Mugford, D.
        189J

   Mukai,  S.
        126D

   Mukerj i, A.  B.
        039H

   Mulbarger, M. C.
        376D

  Mulchandi, H. K.
        146J

  Mullins, L. D.
       239C

  Mulvihill,  M. E.
       061F

  Munemiya,  I.
       122D

  Munkacsy, T.
       055H

  Munro, I. C.
      283J

 Muntz, W.
      005A

 Munz, W.
      038B,  059B

 Murakami, K.
      240D

 Murakami, Y.
      440D

 Muraoka,  K.
      086F

Murata, K.
      278C

Murkes, J.
     071D
                                 984

-------
Murphey, W. K.
     329D

Murphy, D. S.
     234C

Murphy, K. L.
     165D, 197D

Murphy, R. S.
     16 3D

Murphy, S. D.
     288J, 374J

Murray, J. F.
     277J

Murray, R. W.
     394D

Musselwhite,  C. C.
     176E
Nalluri, C.
     004G, 068F

Naryshkina, V. L.
     079B

Nashikkar, J. T.
     317D

Neal, L. A.
     369J

Nebeker, E. B.
     370J

Nedokuchayev, B. N.
     079B

Nefedov, Y. I.
     309D

Neish, D.
     115E
Mustata, L.
      095F

Muzik,  I.
      018A
Nelson, D. L.
     164J

Nelson, M. A.
     244C
 Myers,  E.  A.
      331D

 Mysin,  A.  V.
      225C

 Nagamori,  H.
      122J

 Nagel,  0.
      204C

 Nagy, Z.
      053D

 Naito,  M.
      104F

 Nakahiro,  Y.
      126D

 Nakamura,  K.
      019D

 Nakatsuji, K.
      086F
Nelson, M. D.
      145D, 496D

Nelson, W. W.
      379J

Nemedi, L.
      056H

Nera,  E. A.
      283J

Nesbitt, J.  B.
      332D, 477D

Nester, A. W.
      036B

Netzer, A.
      330J

Neumaier,  F.
      051H

Nevin, T.  A.
      00 5D
                                  985

-------
   Nevzorov, M. I.
        032C

   Newton, C. D.
        028A

   Newton,  S. G.
        036F

   Nguyen,  H.  T.
        245J,  423J

   Nickerson,  G. L.
        011D

   Nicklin, T.
        169C

  Nicoll, E. H.
       219J

  Nielson, D. R.
       011H

  Nijs,  M.
       002H

  Niles,  D.  G.
      02 7D

  Niogret, G.
      175C

  Nishi, K.
      210D

 Nishio, T.
      312J

 Nishikawa,  T.
      099C

 Niskin, S.  J.
      217C

 Nitescu,  S.
      02 3D

 Noble,  R. G.
      190J

Nobunaka, M.
      037B

Noda, S.
     34 9D
   Nogal, M.
        033J

   Noonan, M. E.
        082B

   Norman, J. D.
        103D

   Norris, L. A.
        391J

   Novak,  J.  T.
        332J

   Novak,  J.  T.
        457D

  Novak,  P.
        004G

  Nunez, W. J.
       455D

  Nunn,  G.
       005J

  Obayashi,  A. W.
      405D

  Oberholtzer,  J. V.
      233C

  Ockershausen,  R. W.
      195J

 Oehme, F. W.
      286J

 Oertli, J.  J.
      016A

 Oeschger, H.
      108E,  133E

 Offner, F.  F.
      006A

 0'Flaherty,  C.  A.
      042F

Oglesby,  H.  S.
     127J

Oguntuase, A. M.
     017A
                                  986

-------
Ogura, S.
     427D

Ohata, M.
     057E

Ohta, M.
      178C

Okubo,  K.
      271C

Olah, J.
      287D

 Oliver, B. J.
      021A

 Olives!, J.
      286D

 Olmstead, W. R.
      065H

 Olney,  C.  E.
       395J

 Olson, 0.  C.
       326J

  Omura, A.
       117E

  Onat, E.
       424J

  Ongerth, H. J.
        249J

  Onishi, H.
        100F

  Onstott,  E.
        039D

   Onuska,  F.  I.
        145E

   Or, T.
        061C

   Orie, D. H.
         127E

   Ormerod, K.
         497D
Ortolano, L.
     291J

Orvini, E.
     155E

Osburn, Q. W.
     018E

0'Shaughnessy, J. C.
     477D

0'Sullivan,  D.
      310J

 Otsuka, Y.
      429D

 Ott, D. E.
      180E

 Ott, R.
      05 2D

 Otterman, J.
      275J

 Overland, D.
      069E

 Owen,  S. G. H.
       117J

  Oxenham,  J. P.
       180C

  Oxley, N.  C.
       113F

  Pagoria, P. S.
       363D

  Paily, P.  P.
        028F

   Painter, R.  B.
        036F, 012H

   Pakhani,  C.
        084C

   Palin, A.  T.
        063J, 064J

   Palms, J.  M.
        033E
                                     987

-------
   Palusova,  0.
        067E

   Pantell, R. H.
        069F

   Paramasivam, R.
        04 7 J

   Parhad, N. M.
        218J

  Pariel, J.  M.
       028C

  Parizek,  R. R.
       321D

  Parker, D.  S.
       02 7D

  Parker, E.  E.
       183D

  Parker, H.  W.
       377D

  Parker, W.  H.
       465D

  Parmele, L. H.
       058H

 Partridge, B. F.
      141E

 Patin, P.
      008C

 Patric, J. H.
      378J

 Patrick, J.  M.
      320J

 Patterson, R. J.
      05 OH

 Patterson,  R. K.
      439D

Patterson,  W. D.
      386J

Paul, J. L.
     104J
   Paulik, G. J.
        059J

   Paulson,  W.  L.
        435D

   Pawson, J. M.
        062B

   Peantek,  G.
        003D

   Pearson,  S. C.
        485D

  Peavy, H.  S.
       443J

  Peck, W. H.
       284C

  Peel, C.
       211J

  Perlis,  H.  J.
       057F

  Perry, R.  A.
       198C

  Peters, C. E.
       009K

 Peterson, J. R.
      32 OD

 Peterson, R. E.
      081H

 Peterson,  S.  A.
      236J

 Petronio, F.
      015J

 Petrov, E.  G.
      018C

 Petrova, N. K.
      216J

 Petts, K. W.
      176E

Pew, K. A.
     010B
                                988

-------
Pfeil, K.
     031A

Phantumvanit, D.
     442J

Phelps, P. L.
     036E

Phillips, D. W.
     133J

Phillips, W. J.
     180D

Pick, A. R.
     155D

Pick, P. E.
     47 2D

Pickering, Q. H.
     238J

Pieczonka, P.
     436J

Pierce, D. M.
     325J

Pierce, R. H.
     395J

Pierson, H. G. W.
     078D

Piest, R. F.
     130J

Pinezich, J. R.
     230C

Pingry, D. E.
     009F

Pinnell, S.
     089D
Plura, G.
     098C

Poertner, H. G.
     001A

Pohland, F. G.
     055F

Ponomarev, V. G.
     153D

Pontier, L.
     107E

Popalisky, J. R.
     076B

Popov, E. G.
     01 IF

Porter, R. C.
     300J

Postlewait, J. C.
     167J

Potworowski, H. S.
     124J

Pouget, E.
     107E

Pound, C. E.
     187D, 257D

Powell, G.
     102D

Powell, T.
     050F

Prasad, D.
     339D

Prasad, R.
     175E
Pinter, C.
     055H

Pitkin, J. B.
     037D

Platz, R.
     204C
Pratt, L.
     116D

Prendiville, P. W.
     086D

Prengle, H. W.
     275D
                                  989

-------
  Price,  D.  H.  A.
       335J

  Price,  G.  A.
       026F

  Price,  K.  R.
       014C

  Price,  W.  E., Jr.
       051F

  Primeaux,  W. J., Jr.
       304J

  Pritchard, J. B.
      401J

 Procella, D. B.
      270J

 Proges,  R.
      380J

 Proziesky,  0.  W.
      02 9D

 Pruggmayer, D.
      068E

 Pugh,  K. B.
      130E,  131E

 Pugh,  0.
      431D

 Puri,  B. K.
      091E

 Pustoseleva, Z. I.
      350D

 Qadri, R. B.
     092E

 Quigley,  J.
     040D

 Rabe, F.  W.
     115J

Rachor, D. G.
     198C

Rafael, J.
     144C
  Rahmann, H.
       294J

  Rako, J.
       079E

  Rail, D.  P.
       401J

  Ramanuj am,  S.
       175E

  Ramsay, A.  St.  A.
       291D

  Rananthau, K. R.
       16 3D

  Rangaswami,  G.
       416D

  Ranken, M. B. F.
       097J

  Rankin, P. W.
       263J

 Rao, M. N.
      442D

 Rao, N. S. L.
      055D, 090F

 Rao, N. U.
      218J

 Rao, P. V.
      108F

 Ratray, G. B.
      207D

 Rauschenberger,  J.
      053D

 Rawcliffe, E.
      220J

 Rawls, W.  L.
      338J

 Reasoner, D.   J.
      367J

Rebhun, M.
     144D
                                 990

-------
Reed, C. H.
     247D

Reed, R. R.
     003C

Reeves, R. F.
     250C

Regier, H. A.
     151E

Reid, B.
     252D

Reid, B. H.
     168D, 143J

Reid, L. C.
     124J

Reinhardt, H.
     269C

Reish,  D.
     345J

Remus,  G.  A.
     217D

Rendon-Herrero, D.
     340J

Rensink, J.  H.
     459D

Reside, J.
     441J

Rettmer,  S.
     121E

Reuter, I. J.
     315D

Reynolds,  J. H.
     270J

Rhee,  S.  S.
     07 5H

Rhindress, R.  C.
     327J
Rice, A. H.
     17 9D

Rice, R. C.
     192D

Rice, T. R.
     255J

Richardson, N.
     162C

Richardson, S. E.
     204J

Richmond, M. H.
     069J

Richter, J. D.
     019F

Rickert, D.
     071E

Riesbeck, L. J.
     203C

Riggleman,  B. M.
     113C

Riggs, M. S.
     19 3D

Ringer,  R.  K.
     232J

Ringler, T. A.
     448J

Ripley,  B.  D.
     171E

Rishel,  J.  B.
     281J

Rishel,  R.  C.
     114C

Roa, P.  S.  C.
     412J

Robbins, C. W.
     377J
 Rhodes, H. M.
      176C
 Roberts,  F.  W.
      217J
                                  991

-------
  Robinson, C. N., Jr.
       056F

  Robinson, K.
       38 2D

  Robson, C. M.
       011D

  Rock,  B.  M.
       131J

  Rodriguez, S,  E.
       370J

  Roesler,  J.  F.
      140E, 139J

  Roether,  W.
      067H

  Rogers, M. E.
      292D

 Rogowski, A. S.
      092F

 Roland, F. J.
      336D

 Romkens, J. M.
      036A

 Rood,  0. E.,  Jr.
      079F

 Roodvoets, R. J.
      246C, 254C

 Rooney,  T.  C.
     030F

 Rosenberg,  D.  J.
     212C

 Rosenberg,  H.  G.
     185J

 Rosenwald, R. H.
     047C

Ross, D. I.
     042E

Ross, D. S.
     070C
  Roth, G. W.
       036E

  Roth, L.
       242J

  Rotsides, C.
       227D

  Rousar,  D.  C.
       010J

  Routson, W.  G.
       069C,  112C

  Rowe, D. W.
       049J

  Rowe, W.  D.
       010K

  Rozanova, L. M.
      175D

  Rudling, L.
      023F

 Rueb, F.
      224D

 Runge, G.
      06 9D

 Rupke, J. W.  G.
      107D, HID

 Rush,  R.
      04 ID

 Rustham,  H.
      375J

 Ruttan, D.
     009E

 Ruzicka,  J. A.
     020D

 Ryan, J.   F.
     099E

Rybakov,  K. V.
     175D

Rydberg,  J. H.
     269C
                                 992

-------
Ryder, R. A.
     151E
Sangster, J.
     097F
Ryhage, E. R.
     115C
Sanko, S.
     124D
Saad, A. H.
     011J
Sapio, J. P.
     105E
Sackmauerova, M.
     067E
Sarfert, F.
     077E
Sacks, B. R.
     107J
Sargent, H. F.
     089J
Saffigna, P. G.
     376J
Sartor, J. D.
     023A
Saiga, K. K.
     079H
Sartz, R. S.
     025A
Saint, P. K.
     156J
Saruhaski, K.
     004K
Sakai, A.
     169E
Sasaki, S.
     099C
Sakamoto, I.
     170C
Sato, H.
     372D
Sako, F. F.
     236C
Sato, K.
     146E
Salvo, J. M.
     14 ID
Sato, U.
     278C
 Sama, N.
     195C

 Sambridge, N.  E. W.
     226D

 Sanchez-Leyva, R.
     222J
Saul, G. W.
     220J

Savage, E. S.
     188C, 092D

Savalappan, K. N.
     316D
 Sanders,  H.  0.
      149E
 Savall, V.
      302C
 Sands,  D.  C.
      436D
Sawyer, D. L.
      036E
 Sane,  M.
      337J
 Saxena, G. M.
      057J
 Sangal,  S.
      066H
 Scaramelli, A.  B.
      489D
                                  993

-------
   Schaefer, R.  G.
        102E

   Schaeffer, C. W.
        115F

   Schaeffer, D. J.
        277J

  Schafer, C.  J.
       444J

  Scharen, H.
       053F

  Schaub,  S. A.
       406D

  Schervin,  E.  J.
       353D

  Scherz,  J. P.
       173E

  Schiefner, K.
       079E

  Schleicher, A. R.
       074J

  Schlicht, R.  C.
      157C

 Schmidt,  A.
      285J

 Schmidt,  R. L.
      063E

 Schmieder, A.
      059H

 Schneider, L.
      048B

 Schneider, R. J.
      168J

 Schneider, W.  J.
      081F

Scholzke,  D.
     083E

Schon, E.  A.
     480D
  Schroeder, E. D.
       072F

  Schultz, D. P.
       124E

  Schultz, M.
       009A

  Schultz, S. E.
       136J

  Schuman, G. E.
       130J

  Schumann,  G.
       060D,  128D

  Schutte,  R.
       238C

  Schwab,  G.  0.
       020H

  Schwartz, A. K.
       101F

  Scorer, R.
      110J

 Scott, D.
      042D

 Scott, R. B.
      379D

 Seabrook, B. L.
      333D, 166J

 Searles,  S.  S.
      308D

 Seeburg,  V.
      179C

 Seika, Y.
      170C

 Seisz, R.  N.
      062E

Seitz, W. D.
     058F

Seki, H.
     008J
                                 994

-------
Semenyuk, V.  D.
     015C

Sen, R. N.
     108F

Seo, K. K.
     081H

Serpik, B. I.
     010F

Shane, M. S.
     092J

Shannon, E.
     04 ID
Sherman, R. M.
     355D

Sherrard, J. H.
     2720, 015F, 072F

Sherrill, J. D.
     066H

Sherwood, C. R.
     16 4D

Sherwood, R. J.
     034F

Shiba, S.
     104F
Shannon, E. E.
     103D, 141D, 137J

Shapiro, J. S.
     304D

Sharma, S. K.
     227J
Shibata, K.
     170C

Shimkovich, V. V.
     165E

Shin, E-B.
     406J
Sharon, D.
     080H
Shiramasa, I.
     259D
Shaw, M. G.
     132J

Shea, J. J.
     167C
Shirior, I. S.
     009C

Short, C. S.
     234D
Sheikh, H.
     028B

Shell, G. L.
     006D

Shema, B. F.
     289C

Shepard, C. A. Y.
     186C
Shwer, M.
     073D

Sias, D. R.
     005D

Siehl, G.
     200J

Sifalda, V.
     003A
 Shephard, W. W.
      028A
 Silbermann, P. T.
      097D, 174D, 279D
 Sherenkov, M.  I.
      032C

 Sherif, M. A.
      400J
 Silvey,  J. K.  G.
      455D

 Simoneit, B. R.
      001E
                                  995

-------
Simpson, D. W.
     330D

Simpson, J. R.
     333J

Sims, R. C.
     031D

Singh, G. P.
     064B

Singh, K. P.
     094F

Sinnhuber, R. 0.
     316J

Siren, M. J. 0.
     055C

Sirou, F.
     107E

Sixt, M. E.
     299C

Skarlatos, Y.
     129E

Skibin, D.
     003H

Skirdov, I. V.
     15 3D

Slack, J. R.
     059E

Sleath, J. F. A.
     048E

Slipchenko, V. A.
     282D

Sliter, J. T.
     007D, 237D, 339J

Sloth, E.
     105J

Sly, P. G.
     381J

Smiles, D. E.
     017F
Smirnov, D. N.
     102C

Smith, A. W.
     288C

Smith, B.
     098F

Smith, C. E.
     007B

Smith, D. B.
     026E

Smith, D. H.
     001E

Smith, D. W.
     157D

Smith, E.
     047D

Smith, E. W.
     256C

Smith, F. A.
     291J

Smith, H. S.
     435D

Smith, J. E., Jr.
     189D

Smith, J. 0.
     382J

Smith, K.
     037J

Smith, L. G.
     151C

Smith, L. S.
     02 9D

Smith, R. E.
     030A

Smith, S. F.
     077C

Smith, W. H.
     006B
                                  996

-------
Smith, W. L.
     109J, 236J

Smythe, W. J.
     274C
South, C.
     497D

Sowden, W. H.
     084B
Snape, T. R.
     006J
Spandowska,  S.
     274J
Snarponis, J. M.
     201J
Spaulding, M. L.
     107F
Sneyd, A. D.
     036H
Speece, R. E.
     018D
Snodgrass, J. E.
     296J
Sperber, S.
     050E
Snoeyink, V. L.
     113D, 216D

Sokolov, V. P.
     350D
Spolia, S. K.
     111F

Spomer, R. G.
     130J
Solomon, D.
     027J
Sridharan, N.
     086E
Solomon, R. L.
     197C
Srinath, E. G.
     482D
Soltis, R. G.
     485D
Sriniuasaraghaven, R.
     360D
Solyom, P.
     022F

Somasundaran,  P.
     147J
Stafford, D. A.
     120D, 070F

Stalling, D. L.
     244J
Sona, K.
     476D
Stalnaker, R. M.
     001C
Sone, L. J.
     072H
Stanley, H. I.
     018J
Songa, T.
     288D
Stapert, J.
     246C
Sopper, W. E.
     322D, 324D, 325D, 328D

Sopper, W. M.
     175J
Staples, K. D.
     438J

Statham, M.
     098E
Sorber, C. A.
     406D, 251J
Stedman, D. H.
     096E
                                 997

-------
Steimle, S. E.
     063D

Stein, P. C.
     299J

Steinberg, M.
     009B

Stengelin, V.
     095C

Stephanoff, N. N.
     154C

Stephenson, G. R.
     054F

Sterling, P.
     073F

Stern, A. M.
     401D

Stetefeld, W.
     029A

Stevenson, C. D.
     090E

Stewart, F. I.
     121C

Stiff, M. J.
     118J

St. Jean, R.
     051E

Stobbe, G.
     225D

Stocker, Z. S. J.
     394J

Stokes, H. W.
     475D

St. Onge, H. S.
     092B

Stone, J. S.
     229C

Stoneker, L. L.
     024A
Stones, T.
     053E

Storck, W. J.
     295J

Stoy, R. L.
     021E

Straten, G.
     121E

Straub, C. P.
     012K

Strautin, U. F.
     066B

Streit, S.
     144D

Stribling, J. B.
     031C

Strokach, P. P.
     282D

Strundjalic, P.
     031E

Struzeski, Jr., E. J.
     02 2A

Stubblefield, F. E.
     002K

Stuiber, D. A.
     040D

Subrahmanyam, P. V. R.
     055J

Suess,  A.
     060D

Sugata, K.
     373D

Sugata, Y.
     37 2D

Sugimoto, E.
     260D

Sugimura, Y.
     004K, 005K
                                 998

-------
Suhr, L.  G.
     268D

Sullivan, H.
     021B, 027B

Sullivan, R.
     020B

Sullivan, R- H.
      258D,  165J

 Sumitomo, H.
      048F

 Summers, R.
      445D

 Sunada,  D.  K.
      070H

 Sundstrom, D. W.
      20 5D

 Suriyades, R.
      046D

  Surkan, A. J.
       07 3H

  Suss,  A.
       128D

  Sutherland,  G.
       101C

  Sutton, J. D.
       449J

  Sutton, R. M.
       16 5D

   Suzuki, S.
        346D

   Svanteson,  S. E. A.
        083C

   Swales, D.  A.
         232C

   Swanson, E. R.
         058F, 100F

    Swanson, N.  P.
         028E
Swartzendruber,  S. D.
     015A, 014F

Sweeney, G. E.
     087D

Swered, P.
     289C

Swets, D. H.
     116D

Swicegood,  W. R.
     005H

 Synott,  T.
      243J

 Szakatsits, G.
      008A

 Szeeley, P.  J.
      034A

 Szepkuti,  L.
      040E

 Szidorenko,  G.  1.
       008H

  Szokolay,  A.
       067E

  Tabata, N.
       349D,  495D

  Tabatabai,  M. A.
       070B

  Tackett,  R.
       084J

  Taddia, M.
        052E

   Taft,  W.  H.
        098J

   Tafuri, A.
        022A, 019B

   Tai, N.
        02 5H

   Takahashi, H.
         124D
                                     999

-------
   Takamatsu, T.
        104F

   Takayasu, K.
        280C

   Takeno, K.
        117E

   Takeuchi, T.
        260D

   Talley,  W. J.
        223C

   Talmi, Y.
        116E

  Tarn, K. C.
       142E

  Tamburrino,  A.
       027H

  Tara Singh,  H.  D.
       089B

  Tate,  D.  P.
       153C

  Tate,  J. F.
      196C

 Tatu, G.
      014B

 Taylor, C.
      035F

 Taylor, F.  B.
      261J

 Taylor, J.
      469D

 Tchobanoglous, G.
      359D,  387D, 066F

Tenney, M. W.
     407D

Tenore, K. R.
     018J
    Thayer, P. M.
         097C

    Thiele, K.
         094J

    Thirumurthi,  D.
         413D

    Thomas,  J.  F.
         192C

    Thomas, J. L.
         417J

   Thomas,  R.  E.
        255D,  256D, 060H

   Thompson, J.
        361J

   Thompson, L. B.
        226C

   Thompson, N. P.
       263J

  Thompson, R. G.
       101F

  Thorn,  D.
       060F

  Thornhill, W. F.
       104J

  Tihansky, D. P.
       065F, 268J,  403J

 Toerber, E. D.
      435D

 Tofflemire, T. J.
      407J

 Tomsen,  J.  B.
      296C

Torpey,  W.  N.
     221C

Toups, J. M.
     023H
                                  1000

-------
Towne, R. E.
     323J

Toyokuni, E.
     059F, 062F

Tracy, K. D.
     106F

Train, R. E.
     086J

Trainer, F. W.
     030E

Trax, J. R.
     251D

Treasure, W.
     397J

Tredgett, R. G.
     056D,  499D

Trent, D. S.
      021F

Trieff,  N.  M.
      340D

Troeger, J.
      415D

Trollop,  K.  S.
      005G

Troth,  L.
      270C

Trujillo,  P.
      299J

Tsao,  H. Y.
      456D

Tscheschke, P.
      150J

 Tsuge,  H.
      04 4D

 Tsuji,  T.
      008J

 Tsukamoto, M.
      057E
Tucker, G. E.
     385D

Tucker, J. H.
     143E, 364J

Turner, H. J.
     323J

Tymoszcuk, J.
     211C

Ueda, Y.
     104F

Ueno, A.
     271C

Uhnak, J.
     067E

Ulmgren, L.
     152D

Unz, R.  F.
     404D

Urano, K.
     019D

Uratsuko,  K.
     210D

Urban, P.
     047C

Valentine, J.  P.
      297J

Valentine, R.  S.
      056E

Valimaa, P.
      077B

 Van Alstyne, F. E.
      407J

 Vanderborgh, N. E.
      237J

 van der Linden, A. C.
      02 3 J

 Vanderploeg, H. A.
      090J
                                  1001

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Van der Ploeg, R. R.
     015H

Van der Voorde, H.
     002H

Van Dijc, P. J.
     002H

Van Duuren, F. A.
     192J, 503D

Van Es, D. W.
     15 5D

Van Fleet, G. L.
     106D, 107D

Van Loon, J. C.
     184D, 009E, 138J

Van Natta, W. S.
     075B

Vanstaen, H.
     350J

Varshney, R. S.
     011B

Vasil'ev, A. G.
     080B

Vecchioli, J.
     34 2D

Veith, G. D.
     205J

Verduyn, G.
     144E

Vernoff, F. H.
     407D

Verstraete, W.
     350J

Vesilind, P. A.
     146D, 029F

Vidhyasekaran, P.
     416D

Vigani, F. C.
     00 IF
Viitasaari, M.
     151D

Villiers, R. V.
     100D

Vincent, J. H.
     133C

Visser, P.
     227C

Vitek, M.
     257J

Voelkel, K. G.
     314D

Voets, J. P.
     350J

Volkov, G. A.
     216J

Vollheim, G,
     415D

von Baeckmann, A.
     106E

Von Burg, R.
     375J

Vouve, J.
     107E

Vreeland, V.
     214J

Vuskovic, B.
     031E

Waddington, J. I.
     278J

Wade, S.
     068B

Waldron, A. C.
     020H

Walker, A. J. W.
     308C

Walker, J. D.
     202C
                                 1002

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Walker, J. M.
     248D

Wallace, F. X.
     262J

Wallace,  L.  J.
     306J

 Waller,  R.  M.
      043H

 Wallis,  B.  F.
      113F

 Wallis, I. G.
       118D

 Wallis,  J.  R.
       059E

 Walsh,  D.  F.
       149E

  Walsh,  F.
       308J

  Walter, R. H.
       355D

  Walter, R. L.
       066E

  Walters,  T.  M.
        266C

   Wang,  C.  N.
        354D

   Wang, L. K.
        074E

   Ward,  J.  C.
         156D

   Ward,  P. S.
         237D

    Warren,  H.  V.
         254J

    Warren, W.
         030B

    Warrick, W. W.
          089F
Watanabe, M.
     061C, 062F

Watkins, D. A. M.
     309J

Watkins, F. A., Jr,
     030E

Watkins,  S. H.
      234J

 Watters, G. Z.
      074H

 Watts, J. B.
      006C

 Webb, F. J.
      153C

 Webb, L. J.
       229D

  Weber,  R.  B.
       065D

  Weber,  W.  J.
       012D, 430D

  Webster, L.
       003B

  Webster,  L. F-
       123J

  Weddle, C.  L.
        490D

   Wehry, A.
        012B

   Wei, N. S.
        246J

   Welch, H. E.
         396J

   Welker,  F. S.
         445J

    Wells,  J.
         418J

    Welty, J.  R-
         021F
                                      1003

-------
Wendel, H.
     120E

Wesley, R. B.
     293C

Wessels, G. R.
     267C

West, A. W.
     212D, 213D, 396D

Westerhoff, G. P.
     263D, 296D, 458D, 341J

Wheeler, W. B.
     264D

Whimster, K. W.
     239D

Whlnston, A. B.
     009F

Whipple, W.
     027A

White, G. C.
     026D, 470D

White, N. F.
     070H

White, P. W.
     473D

White, R. K.
     020H

White, W. R.
     037F

Whitehead, L. W.
     452D

Whitney, E. W.
     124E

Whittaker, E. L.
     150E

Wilbur, P. F.
     164D

Wildung, R. E.
     063E
Wilkens, J. R.
      142D

Wilkes, A.
      105D

Williams, J. C.
      243J

Williams, R. T.
      428J

Williams, T. C.
      191D, 335D

Willies, R. F.
      283J

Willis, R. D.
      066E

Wilmoth, R. C.
      379D

Wilson, A. L.
      161E

Wilson, C. G.
      249D

Wilson, C. R.
      057B

Wilson, D. B.
      456D

Wilson, D. J.
      301D

Wilson, R.
      429J

Wilson, R. E.
      132C

Wilson, T. V.
      017H

Winkler, H. A.
      HIE, 132E

Winter, R. L.
      182D, 125J

Wise, R. H.
      140E
                                 1004

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Witherspoon, J. P.
     090J

Witt, E.
     049C

Wittgenstein,  G.  F.
     046C

Wnek, W.
      280D

 Wogman, N. A.
      034E

 Wolcott, D. K.
      128J

 Wold,  P.  B.
      488D

 Wolman, A.
      121J

  Wolman,  M. G.
       046E

  Wong,  T.  S.
        070J

  Wood, G. M.
        101D

  Wood, G.  W.
        330D

  Wood, R. E.
        033E

   Woodbridge,  D. D.
        258J

   Woodhouse, D. A.
        071C

   Woodiwiss,  F.  S.
        433J

   Woods,  M. D.
         305C

    Woolhiser,  P.
         038D

    Wright, C.  G.
         007B
Wright, H. W.
     223C

Wright, M. G.
     221J

Wu, Y. C.
     449D

Yadeta,  B.
      045F

 Yagi,  S.
      349D

 Yakovlev, S. V.
      034D

 Yamada, K.
       17 OC

 Yamaguchi,  S.
       024J

 Yamanouchi, T.
       373D

  Yamashita, G.
       065H

  Yamazaki, Y.
       153E

  Yang,  P.
       119D

  Yanko, W.  A.
        304D

   Yao, K. M.
        041B

   Yasimov, A. A.
         289D

   Yasujima, T.
         005K

   Yeaple, D.  S.
         07 8F

   Yeatts,  L.  B.
         135J

    Yelon, A.
         129E
                                     1005

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 Yershova,  K.  P.
      309D

 Yorinks, L.
      082E

 Yost,  K. J.
      220C

 Young, D.  L.  G.
      210C

 Young, D.  N.
      048H

 Young, J.  C.
      228C

 Young, L.  Y.
      301J

 Young, R.  A.
      328J

 Young, R.  H. F.
      368J

 Young, W.  J.
      329D

 Young, W.  L.
     113C

 Youngner,  V. B.
     324J

 Yrjanainen, G.
     030B

 Yu, S. L.
     027 A.

Yu, W.
     102F

 Zachos, G.  H.
     077J

 Zahn, R.
     103E

Zaloum, R.
     099D

Zandi, I.
     035B
 Zanker, A.
      043B

 Zanoni, A. E.
      170E

 Zenz, D. R.
      320D

 Ziebell, W. A.
      37 OD

 Ziemba, J.
      373J

 Zoetl, J.
      052H

 Zojer, H.
     052H

 Zsolnay, A.
     284J

Zuckerman, M.
     138C

Zwamborn, J.  A.
     162J
                                 1006

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Materials Reclamation Weekly

Measurement and Control

Mechanical Engineering

Meerestecknik

Memoirs of the Faculty of
  Engineering (Kyoto University)

Memoirs of the School of
  Engineering (Okayamo University)

Metal Finishing Journal

Meterorologiya in Gidrologiya

Mining Engineering

Mining Journal

Ministry of Technology Notes
  on Water Pollution

Mitsubishi Denki Giho

Mitsui Zosen Giho

Modern Power and Engineering

National Engineer

National Water Supply
  Improvement Association
  Journal

Nature

Neftepererabotka i Neftekhimiya

New Civil Engineer

New Scientist

New York Academy of Sciences
  (Annals)
New Zealand Engineering

New Zealand Journal of Agriculture

New Zealand Journal of Science

Nuclear News

Nuclear Safety

Oeffentliches Gesundheitswesen

Oesterreichische Ingenieur
  Zeitschrift

Oesterreichische Wasserwirtschaft

Official Gazette of the United
  States Patent Office

Official Journal of Patents,
  Trademarks and Designs

The Oil and Gas Journal

Oil Week

Okeanologiya

Optics Communications

Osaka University (Technology
  Reports of the)

Paper Review of the Year

Papers in Meterology and Geophysics

Paper Trade Journal

Patent Office Record

Pesticides Monitoring Journal

Pharmacology Biochemistry and
  Behavior

Photogrammetric Engineering

Pipes and Pipelines International

Plant Engineering
                             1012

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Pollution Engineering

Power Engineering

PPM

Process and Chemical Engineering

Process Biochemistry

Products Finishing

Professional Engineer

Progress Engineering

Promyshlennos t'

The Public Health Engineer

Public Roads

Public Utilities Fortnightly

Public Works

Pure and Applied Chemistry

Radiochemistry and Radioanalytical
  Letters

Research Society of Japan Sugar
  Refinerie's Technologists
  (Proceedings of the)

Remote Sensing of Environment

Research and Industry

Review of Scientific Instruments

Revue Generale des Matieres
  Colerantes-Teintex

Rohm and Haas Reporter

Schweizerische Bauzeriung

Science
Science and Culture

Science and Public Affairs

Science Editor

Science News

Separation Science

Shipbuilding and Marine Engineering
  Internat ional

Shokuhin Kaihatsu

Soil Science

Soil Science Society of America
  (Proceedings)

Solid State Technology

Solid Waste Management

South African Chemical Processing

Soviet Inventions Illustrated

Staedtehygiene

The Steam and Heating Engineer

Sulzer Technical Review

Sumitomo Denki

Surface Science

Surveyor

Swiss Journal of Hydrology

Technical Association of the Pulp
  and Paper Industry (Papers)

Techniques et Sciences Municipales

Thomson's Process and Chemical
  Engineering
                              1013

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Toxicology and Applied Pharmacology

Tunnels and Tunnelling

Umwelthygiene

U.S. Atomic Energy Commission

VDI Berichte

VGB Kraftwerkstechnik

Vizugyi Kozlemenyek

Vodosnabzheniye a Sanitarnaya
  Tekhnika

Wasser, Luft und Betrieb

Wasser und Boden

Wasser-und Energiewirtschaft

Wasserwirtschaft-Wassertechnik

Water, Air, and Soil Pollution

Water and Pollution Control

Water and Sewage Works

Water and Wastes Engineering

Water and Waste Treatment

Water Pollution Control

Water Pollution Control
  Federation (Proceedings
  of the)

Water Purification and Liquid
  Waste Treatment

Water Research

Water Resources Research

Water Services
Water Treatment and  Examination

Weatherwise

Weed Science

Western Construction

Wood Science and Technology

World Construction

World Dredging and Marine
  Construction

World Oil
                                1014
                                           OU.S. GOVERNMENT PRINTING OFFICE: 1975-629-172/643

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  SELECTED WATER
  RESOURCES ABSTRACTS
  INPUT TRANSACTION FORM
  4. Title
         MUNICIPAL WATER POLLUTION CONTROL ABSTRACTS
         K)R 197U,
                                                                 3. Accession No
  7. Author(s)
Murphy, Jo S
                                                                    Project No.

                                                                 E 1BB033  PEMP 08
  9.  Organization
The  Franklin
             Institute Research Laboratories
20th Street and The Parkway
Philadelphia, Pennsylvania
                                                                 //. Contract!Grant No.
                                                                           -01
  15.  Supplementary Notes

  Environmental Protection Agency report numter, EPA-600/2-75-005, April 1975
  16. Abstract   The  Franklin Institute Research Laboratories, Science Information Services
has prepared  for  the Environmental Protection Agency a monthly current-awareness
abstracting bulletin, the Municipal Technology Bulletin (MTB), Volume 2, 197U,
•which  deals with  methods of municipal waste water treatment, problems of water qual-
ity, and water pollution control*  Under the same grant, the Science Information
Services Department has  provided 360 MTB abstracts, as well as ll&O additional ab-
stracts, to the WRSIC data bank as sole supplier of municipal waste water treatment
input  and center  of competence for Water Resources Scientific Information Center.
Hie Municipal Technology Bulletin informs researchers, consultants, engineers,
and government officials of current developments described in over 1*000 technical
journals, both domestic  and foreign.,  The topics covered in MTB, Volume 2, and in
the WRSIC input include:  stoim water runoff;  tunnel technology and sewer systems;
biological, chemical, and physical methods of waste water treatment;  waste dis-
posal  alternatives;   treatment plant operation and automation;  analytical tech-
niques for water  quality measurement; mathematical, statistical, and simulation
model  studies; and construction and equipment for pollution control.  The 1800
abstracts representing 197U input to the WRSIC data bank have been arranged in
chronological order by accession number within subject areaso  A list of the 360
abstracts which appeared in the Municipal Technology Bulletin is providedo  Included
also are a subject index, author index, and joiimnl Hart. (Pragup>-ETRT.)	
             #Abstracts,  *Publications, *Water quality control, *Waste water treat-
ment, -sMunicipal  wastes,  Storm runoff, Sewers, Patents, Sewage treatment, Analytical
techniques, Mathematical  models, Model studies, Pipelines, Equipment, Construction,
Hydrologic aspects,  Treatment facilities, Design criteria, Waste disposal, Tunnels,
Water resources management

  17b. Identifiers *IndeXeS
  17c. CO WRR Field & Group Q^D,  0£E, 0?D, 10A, 10D
  18. Availability
  Abstractor R« H° Prague
                                                      Send To:

                                                      WATER RESOURCES SCIENTIFIC INFORMATION CENTER
                                                      U.S. DEPARTMENT OF THE INTERIOR
                                                      WASHINGTON. DC 2O24O
                                                anklin Institute Research Laboratories
WRSIC 1O2 (REV. JUNE 1971)

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