OFFICE OF WATER PROGRAMS
Subsurface Water Pollution
A Selective Annotated Bibliography
Part
Percolation from Surface Sources
U.S. ENVIRONMENTAL PROTECTION AGENCY
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SUBSURFACE WATER POLLUTION
A Selective
Annotated Bibliography
PART I I I
PERCOLATION FROM SURFACE SOURCES
Produced in cooperation with
Water Resources Scientific Information Center
Office of Water Resources Research
U.S. DEPARTMENT OF THE INTERIOR
U.S. ENVIRONMENTAL PROTECTION AGENCY
Office of Water Programs
Division of Applied Technology
Water Quality Protection Branch
Fresh Water Pollution Section
Washington, D.C. 20U60
March 1972
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3P.lti,
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FOREWORD
Subsurface Water Pollution is a selective bibliography
produced by the Fresh Water Pollution Section, Office of
Water Programs, Environmental Protection Agency from the
computerized data base of the Water Resources Scientific
Information Center, Office of Water Resources Research, U.S.
Department of the Interior. This bibliography represents
published research in water resources as abstracted and
indexed in the semimonthly journal, Selected Water Resources
Abstracts (SWRA). This bibliography represents a search of
a 33,980-item data base, covering SWRA from October 1968
through December 1971, and is published in three parts.
Part I covers pollution associated with subsurface waste
injection, Part II covers pollution associated with saline
water intrusion, and Part III covers pollution associated
with percolation from surface sources.
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SUBSURFACE WATER POLLUTION
A Selective Annotated Bibliography
INTRODUCTION
Ground water in the United States has historically been a
quantitatively minor water source whose chief role was in
individual homes or small communities. Today, ground water
accounts for nearly 20 percent of the Nation's requirements
for water/ and has been viewed by some as the answer to the
Nation's water supply problems. The problems associated
with ground water management and its use in satisfying the
future's enormous needs for water storage and supply are
extremely complex. Other than basic relationships
describing flow due to differences in gravity head;
predictive relationships for mixing, flow times, dispersion,
and stratification are only poorly developed. The concept
of irreversibi1ity in ground water pollution is widely
accepted. Once an aquifer has been contaminated, it is
difficult or infeasible to flush or pump out the
contaminants and restore the aquifer to its original
quality. To assure the continuing availability of large
volumes of water of acceptable quality, research and
technology must combine efforts to fill the basic knowledge
gaps in the earth sciences that allow understanding and
prediction of the causes and effects of subsurface water
pol1ut i on.
Sources of ground water pollution generally fall into one of
three distinct categories: 1) subsurface waste injection,
2) intrusion of saline water into fresh water aquifers, and
3) percolation from surface sources. Accordingly, this
bibliography is divided into the same three basic
categories. Within each category, the bibliography
references articles pertaining to technology for prevention
and control of pollution, documented cases of pollution,
litigation, and laws and regulations affecting subsurface
disposal of wastes.
Because the various aspects of the problems of ground water
pollution cover a wide spectrum of science and engineering,
articles bearing on the subject are widely dispersed in the
scientific and technical literature. It is hoped that this
bibliography will serve as a handy reference for scientists,
engineers, and managers concerned with protection of the
subsurface environment.
Selections in this bibliography were made by Clinton W.
Hall, Geologist, Fresh Water Pollution Section, Office of
Water Programs, Environmental Protection Agency.
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ARRANGEMENT
Significant Descriptor Index
This index (blue pages) is made up of a fraction of the
descriptors and identifiers by which each paper in this
bibliography has been indexed, and represents weighted terms
(indicated by asterisks) that best describe the information
content.
Bibliography
Subsurface Water Pollution is divided into three sections:
1) pollution associated with the deliberate injection of
wastes below the water table, 2) pollution associated with
the intrusion of saline waters into fresh water aquifers,
and 3) pollution associated with the percolation of wastes
from surface sources. In each section, the bibliography
contains references to technology dealing with the
prevention or abatement of pollution, litigation pertaining
to incidences of pollution, and laws and regulations
pertaining to the construction and operation of subsurface
waste disposal facilities. Abstracts in each section are
listed in ascending order according to accession number.
Comprehensive Index
This index (yellow pages) is subdivided into three sections,
corresponding to the subdivisions of the bibliography, and
represents all of the descriptors and identifiers by which
each paper has been indexed. Through permutation, each word
in a multiple-word descriptor or identifier is made to file
in its normal alphabetic order, thus affording a multiple
access to each abstract.
USING THE INDEXES
Having thought of a few key words describing your subject
matter of interest, scan the indexes for their presence.
The number in the right margin locates the full record in
the bibliography section, which is arranged in ascending
accession number sequence.
i v
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AVAILABILITY OF COPIES
Neither the Environmental Protection Agency nor the Water
Resources Scientific Information Center supplies copies of
documents listed in this bibliography. Some of the
documents are shown to be available from the National
Technical Information Service, Springfield, Virginia 22151.
PB numbers should be included with all orders. Other
reports may be obtained from publishers or from local
libraries on loan or in reproduction.
Copies of this bibliography can be purchased from the
National Technical Information Service, Springfield,
Virginia 22151 at $3.00 each in paper copy or 95£ in
mi crof i che.
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CONTENTS
Page
FOREWORD i
INTRODUCTION iff
ARRANGEMENT iv
SIGNIFICANT DESCRIPTOR INDEX 1
(blue pages)
BIBLIOGRAPHY 9
COMPREHENSIVE INDEX 117
(yel1ow pages)
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SIGNIFICANT DESCRIPTOR INDEX
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BOLISM, MOBILITY, PARTICIPATE F/
POLLUTION SOURCES, '"GROUNDWATER,
ACE DRAINAGE, '"DRAINAGE, '"EUTRO/
NUTRIENTS, WATER MIXING, RUSSI/
ABORATORY / '"PATH OF POLLUTANTS,
NTS, '"GROUNDWATER/ '"SURFACTANTS,
T/ '"INFILTRATION, '"POROUS MEDIA,
S, *CORES, FIELDS, P/ "'-NITRATES,
--NUTRIENTS, '"SOILS, BLEACHING,
N, WASTE DISPOS/ '"CONTAMINATION,
E, -"CALIFORNIA, WATER YIELD, IN/
ADING, '"WATER REUSE, --TERTIARY /
LAIMED WATER, '"MUNICIPAL WASTES,
FILTRATION, '"PIT RECHARGE, *WAT/
ND-WATER, WATER POLLUX '"VIRUSES,
'"WATER POLLUTION, '"WOOD WASTES,
, '"WOOD WASTES, *BARK, '"LIGNINS,
EWAGE DISPOSAL, ORGANIC LOADING,
TIFICIAL RECHARGE, *WATER REUSE,
C BACTERIA, NITRATES, CHLORIDES,
ION SOURCES, PATH/ *FARM WASTES,
AQUIFER, DISCHARG/ '"FARM WASTES,
*GROUNDWATER POLLUTION,
STE WATER DISPOSAL, '-IRRIGATION,
WATER CHEMISTRY, '"WATER QUALITY,
NT, PERCOLATION, '"MODEL STUDIES,
NDU/ '"WATER MANAGEMENT(A PPL IED ),
SEEPAGE, '"POLLUTION, JUDICIAL D/
SURFACE WATERS, SURFA/ ^FLORIDA,
TION, --DISPERSION, WASTE DISPOS/
D FLOW, '-DIFFUSION, -DISPERSION,
*TRITIUM, '"TRACERS, '-LEACHING,
MONIA, --"WATER POLLUTION SOURCES,
WATER POLLUTION/ *WATER DUALITY,
BON POLLUTION.:
MGTON, *WATER POLLUTION SOURCES,
CTANTS, '"ALKYBENZENE SULFONATES,
-WATER ENVIRONMENT, ANIONIC SUR/
, '"RETURN FLOW, '"DRAINAGE WATER,
ON SOURCES, '"PATH OF POLLUTANTS,
UNDWATER, WASTES, '"UNIFORM FLOW,
LLUTANTS, '"GROUNDWATER MOVEMENT,
ION, '"GROUNDWA/ '"SATURATED FLOW,
DWATER MOVEMENT, *PATH OF POLLU/
DWATER MOVEMENT, */ ^DISPERSION,
COMPUTER PROGRAMS, DIFFUSION, /
ISOTOPES, '"GROUNDWATER MOVEMENT,
T, #NUMER/ '-SIMULATION ANALYSIS,
WA/ *SATURATED FLOW, '-DIFFUSION,
MEDIA, *GROUNDWATER MOVEMENT, #/
ROUNDWATER MOVEMENT, '-DIFFUSION,
GROUNDWATER, WASTES, '-UNIFORM F/
MINATION, '-AQUIFERS, CONVECTION,
^IRRIGATION WATER, '-RETURN FLOW,
WATERSHED, ^SUBSURFACE DRAINAGE,
W, '"DIFFUSION, POROUS MATERIALS,
'-SUBSURFACE DRAINAGE, --DRAINAGE,
PHORUS, NUTRIENTS, ALGAE, NITRA/
'-ARTIFICIAL
'"ARTIFICIAL
'-ARTIFICIAL
'-AGRICULTURAL DRAINAGE, LAKE META
'-AGRICULTURAL POLLUTANTS.:
'"AGRICULTURAL CHEMICALS, FERTILIZ
'"AGRICULTURAL WATERSHED, '"SUBSURF
'"AGRICULTURAL DRAINAGE, DISSOLVED
*ALDRIN, '"GROUNDWATER MOVEMENT, L
'"ALKYBENZENE SULFONATES, '"DETERGE
'"ALLUVIUM, '"LYSIMFTERS, '"RADIOISO
'"AMMONIA, *WATER POLLUTION SOURCE
'"AQUIFER CHARACTERISTICS, SOIL AN
'"AQUIFERS, CONVECTION, '"DISPERSIO
'"ARTIFICIAL RECHARGE, '"WATER REUS
RECHARGE, --"WATER SPRE
RECHARGE, LEGAL ASPEC
RECHARGE, '"INDUCED IN
'"BACTERIOPHAGE, PERCOLATION, GROU
'"BARK, *LIGNINS, '"BIOCHEMICAL OXY
'"BIOCHEMICAL OXYGEN DEMAND, LEACH
'"BIODEGRADATION, SOIL DISPOSAL FI
'"CALIFORNIA, WATER YIELD, INFILTR
'"CAPILLARY CONDUCTIVITY, SOIL MOI
'"CATTLE, '"LEACHING, '"WATER POLLUT
'"CATTLE, '"GROUNDWATER, '"NITRATE,
'"CENTRAL VALLEY(CALIF) . :
'"CHEMICAL WASTES, SPRINKLER IRRIG
'"CLIMATES, '"LAND USE, '"OKLAHOMA,
'"COMPUTER PROGRAMS.: /G, MANAGEME
'"CONJUNCTIVE USE, '"STREAMFLOW, '"I
'"CONNECTICUT, *OILY WATER, '"UNDER
'"CONSUMPTIVE USE, '"GROUNDWATER, '"
'"CONTAMINATION, '"AQUIFERS, CONVEC
'"CONVECTION, '"GROUNDWATER MOVEMEN
'"COPPER, '"WASTE DUMPS, MINE WASTE
'"CORES, FIELDS, PLANTS, ALFALFA,
'"CROP PRODUCTION, --"FERTILIZERS, *
'"DAMAGES! LEGAL ASPECTS), HYDROCAR
'"DAMAGES, '"WATER WELL, IMPAIRED W
'"DETERGENTS, '"GROUNDWATER MOVEMEN
'"DETERGENT BEHAV I OR ( WATER ) , '"SOIL
'"DETERIORATION, *WATER POLLUTION
'"DIFFUSION, '"SOIL WATER MOVEMENT,
'"DIFFUSION, POROUS MATERIALS, ="EN
'"DISPERSION, '"MATHEMA
'"DISPERSION, '"CONVECT
'"POROUS MEDIA, '"GROUN
*POROUS MEDIA, *GROUN
*NUMERICAL ANALYSIS,
'"ION EXCHANGE, DIFFU
'"GROUNDWATER MOVEMEN
^CONVECTION, '"GROUND
'"DIFFUSION, '"POROUS
^MATHEMATICAL MODELS
FLOW, POROUS MEDIA,
WASTE DISPOSAL, THER
WATER, '"DETERIORATION,
*EUTROPHICATION, NITRO
--DIFFUSION,
'"DIFFUSION,
'"DIFFUSION,
'"DIFFUSION, =
'"DISPERISON,
'"DISPERSION,
'"DISPERSION,
^DISPERSION,
'"DISPERSION,
'"DISPERSION,
'"DISPERSION,
^DISPERSION,
'"DRAINAGE
'"DRAINAGE,
'"ENGINEERING MECHANICS.: /ORM FLO
-"EUTROPHICATION, NITROGEN, PHOSPH
'"EUTROPHICATION, *NITROGEN, '"PHOS
W "/1
W "(1
W71-
WTO-
WTO-
W70-
W70-
W69-
WTO-
W71-
W69-
W70-
WTO'
W69-
W71-
W69-
W68-
W68'
W68-
WTO-
W69-
WTO-
WT1-
W71-
W69-
WTO-
W71-
WTO-
WTO-
WTO-
W69-
W69-
W71-
WTO-
W71-
W68-
W'/l-
WTO-
WTO-
WT1-
WTO-
W69-
W69-
W69-
W69-
W69-
W71-
WT1-
W71-
W69-
W69-
W69-
W69-
W69-
W71-
W70-
W69-
WTO-
W71-
-06443
-04121
-04121
-04504
-04504
-01904
-01291
-02681
-04488
-07887
-00651
-05466
-04712
-08620
-12410
-00225
-01269
-01269
-01010
-05466
-01076
-00665
-03543
-04548
-07114
-06102
-09936
-03102
-07631
-00532
-00651
-08921
-11255
-04488
-12084
-00627
-13645
-01291
-01291
-06063
-10058
-01238
-07554
-08921
-03212
-03237
-09611
-11356
-04559
-08921
-03237
-OT554
-01238
-00651
-06063
-04504
-01238
-04504
-06443
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M WASTES, NUTRIENTS, DENITRIFIC/
LUTANTS, '-MUCLEA/ =-RADIOECOLOGY,
ER, '-NITRATE, AQUIFER, DISCHARG/
URGES, "'GR/ -PATH OF POLLUTANTS,
DUATER, PRECIPITATION, / "'SOILS,
, --FERTILIZERS, "'NITRATES, WATE/
'-WATER POLLUTION SOURCES, PATH/
EfJ FLOORS, AERATOR, SPREADING, /
LEY. :
ARK WASTES, -SOIL CONTAMINATION,
ITATION, / "'SOILS, "'FARM WASTES,
WATER QUALITY, '-CROP PRODUCTION,
*PIT RECHARGE, '-WATER TREATMENT,
NTROL, *WATER POLLUTION SOURCES,
NDWATER, "'SURFACE WATERS, SURF A/
HF POLLUTANTS/ "'WASTE DISPOSAL,
LLUTANTS, *LEACHING, "'LANDFILLS,
ELLS, GROUNDWATE/ '-RHODE ISLAND,
ES, JU/ '-NEW YORK, "'WATER WELLS,
TIGATIONS, "'SOIL INVESTIGATIONS,
HELATE EXTRACTION, ATOMIC ABSOR/
CLAMATION, INDUCED INFILTRATION,
CLAMATION, INDUCED INFILTRATION,
, POROSITY, CLOSED CONDUIT FLOW,
R, *SEEPAGE, / *WATER POLLUTION,
US I ON, "'DISPERSION, "'CONVECTION,
, "'DISPERS/ '-PATH OF POLLUTANTS,
NDFILL, SANITA/ "'WASTE DISPOSAL,
OLLU/ "'DIFFUSION, "'POROUS MEDIA,
--PATHOGENIC BACTERIA, "'VIRUSES,
SIGN, "'DIFFUSION, '-POROUS MEDIA,
TABLE, #SURFACE-GROUNDWATER RE/
RFA/ *FLORIDA, "'CONSUMPTIVE USE,
S, "'SOLID WAS/ "'WATER POLLUTION,
/ "'PATH OF POLLUTANTS, '-ALDRIN,
BENZENE SULFONATES, *DETERGENTS,
AT ION TECHNIQ/ '-WATER POLLUTION,
ING, "'LANDFILLS, ^GARBAGE DUMPS,
LEACHING, *SALINE WATER SYSTEMS,
CHING, "'LANDFILLS, '-PERCOLATION,
ION SOURCES, '-INDUSTRIAL WASTES,
H OF POLLUTANTS, *RAD10 ISOTOPES,
HASTIC PROCESSES, *POROUS MEDIA,
OIL WATER MOVEMENT, "'OILY WATER,
WATER POLLUTION CONTR/ '-WYOMING,
ON, "'WATER QUALITY, "'MONITORING,
DISCHARG/ *FARM WASTES, *CATTLE,
I/ *WATER QUALITY, "'RETURN FLOW,
ASTES, *WATER POLLUTION SOURCES,
VALLEY(CALIF) .:
IMULATION ANALYSIS, "'DISPERSION,
POLLUTION EFFECTS.:
DUMPS, "'SOLID WASTES, BLEACHING,
ES, OILY/ "'KENTUCKY, *OIL WELLS,
N FLOW, "'SALINE WATER INTRUSION,
ATER / "'WATER POLLUTION SOURCES,
UTION EFFECTS, "'SODIUM CHLORIDE,
AVAfCZECHOSLOVAKIA ). :
"'EUTROPHICATION, FERTILIZERS, FAR
'-FALLOUT, BLEACHING, "'PATH OF POL
"'FARM WASTES, *CATTLE, *GROUNDWAT
*FARM WASTES, *WATER POLLUTION SO
'-FARM WASTES, '-FERTILIZERS, GROUN
*FARM WASTES, *SOIL CONTAMINATION
'-FARM WASTES, '-CATTLE, '-LEACHING,
'-FEEDLOT, PLATTE RIVER VALLEY.:
'-FEEDLOTS, OXIDATION DITCH, SLOTT
'-FEEDLOTS, SOUTH PLATTE RIVER VAL
'-FERTILIZERS, *NITRATES, WATER PO
'-FERTILIZERS, GROUNDHATER, PRECIP
"'FERTILIZERS, *WATER POLLUTION SO
^FILIATION, ALLUVIA CHANNELS, SUR
'-FINITE DIFFERENCE METHOD.:
'-FISHKILL, STORM RUNOFF, ODOR, SU
'-FLORIDA, '-CONSUMPTIVE USE, '-GROU
'-GARBAGE DUMPS, *LA NDFI LLS , *PATH
'-GARBAGE DUMPS, *GROUNDWATER MOVE
'-GASOLINE, '-PERCOLATING WATER, *W
'-GASOLINE, '-WATER POLLUTION SOURC
*GEOLOGIC INVESTIGATIONS, '-ILLINO
'-GROUND WATER, *TRACE ELEMENTS, C
AGROUND WATER RECHARGE, IRRIGATIO
'-GROUND WATER RECHARGE, IRRIGATIO
'-GROUND WATER MOVEMENT, CAPILLARY
--GROUNDWATER RECHARGE, GROUNDWATE
'-GROUNDWATER MOVEMENT, SOLUTES, W
'-GROUNDWATER MOVEMENT, '^DIFFUSION
'-GROUNDWATER, *WATER QUALITY, '-LA
'-GROUNDWATER MOVEMENT, '-PATH OF P
'-GROUNDWATER MOVEMENT, MUNICIPAL
'-GROUNDWATER MOVEMENT, '-WATER POL
'-GROUNDWATER, *P IEZOMETRY, 'i=WATER
'-GROUNDWATER, '-SURFACE WATERS, SU
'-GROUNDWATER, "-SEEPAGE, *LANDFILL
*GROUNDWATER MOVEMENT, LABORATORY
'-GROUNDWATER MOVEMENT, *WATER POL
'-GROUNDWATER, '-OIL WASTES, *SEPAR
'-GROUNDWATER MOVEMENT, KARST, INF
'-GROUNDWATER MOVEMENT, DRAINAGE S
MOVEMENT,
MOVEMENT,
MOVEMENT,
MOVEMENT,
RECHARGE,
'-GROUNDWATER
'-GROUNDWATER
'-GROUNDWATER
'-GROUNDWATER
'-GROUNDWATER
'-GROUNOWATER,
-GROUNDWATER,
*GROUNDWATER,
'-GROUNDWATER,
^GROUNDWATER,
'-GROUNDWATER
'-GROUNDWATER
--GROUNDWATER
'-GROUNDWATER,
'-GROUNDWATER,
MODEL STUD
'"RECHARGE,
*DISPERSIO
"'STATISTIC
MODEL STUD
*WATER POLLUTION, *
NITRATE, NITRITES,
SNITRATE, AQUIFER,
"'SATURATED SOILS, *
"-AGRICULTURAL CHEMI
POLLUTION, "'CENTRAL
MOVEMENT, "'NUMERICAL
POLLUTION, LANDFILL
HYDROGEOLOGY, WATER
"'SEEPAGE, DRILL HOL
'-HAWAII, IRRIGATION WATER, WATER
"'HERBICIDES, "'NEW MEXICO, "=SOIL W
"'HIGHWAY ICING, "'SNOW REMOVAL, "'M
"'HYDRAULICS LABORATORY OF BRATISL
W71-
W71-
W71-
W71-
W71-
W71-
W70-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W70-
W70-
W71-
W70-
W69-
W70-
W69-
W69-
W69-
W69-
W68-
W69-
W69-
W69-
W69-
W69-
W69-
W70-
W70'
W7O
W70'
W70'
W71'
W71-
W71
W70-
W71'
W71-
W71
W71'
W71
W71
W71
W71
W71
W71
W71
W71
W71
W71
W71
W71
W70
W71
-10372
04882
-03543
04121
03542
02036
-00665
-03543
-03542
-02036
-02036
03542
12084
12410
-09611
-09154
-00532
-06572
-01204
-08025
-06117
-06322
-03197
-05328
-05327
-00979
-00058
-08921
-07554
-03178
-03212
-08621
-03237
-07766
-00532
-06011
-01904
-01291
-01930
-01204
-01932
-09548
-00194
-11356
-11776
-10325
-10446
-12122
-03543
-08073
-04121
-04548
-04559
-07194
-07194
-08055
-08044
-06514
-09844
-01930
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NDFILL, "'INFILTRATION, "'WATER Q/
"'LANDFILLS, *PATH OF POLLUTANTS,
NT/ "'LANDFILLS, "'WASTF DISPOSAL,
TIONS, "'GEOLOGIC INVESTIGATIONS,
TH OF POLLUTANTS, =-H YDROGEOL OGY,
ER POLLUTION CONTROL, "'POLLUTIO/
JUDICIAL DECISIONS, OIL WASTES/
ALLUVIAL / "'PATH OF POLLUTANTS,
RGE, *WAT/ "'ARTIFICIAL RECHARGE,
, "'CONJUNCTIVE USE, "'STRE AKFLOW,
MOVEM/ *WATER POLLUTION SOURCES,
OLOGY, *SOLID WASTES, "'LANDFILL,
"'MONITORING, / "'SEWAGE DISPOSAL,
"'MONITORING, WATER POLLUTION SO/
UNDWATER BASINS, WATER SUPPLY, /
LUVIUM, '-LYSIMETERS, *RADIOISOT/
BACT/ "'POLLUTANTS, GROUNDWATER,
RRIGAT/ WATER POLLUTION SOURCES,
OUNDWATER MOVEMENT, "'DISPERSION,
, '-ION EXCHANGE, "'WATER QUALITY,
IC-OUALITY MODEL.:
"'DRAINAGE WATER, "'DETERIORATION/
*GROUNDWATER, "'SATURATED SOILS,
RELATIONSHIPS, D/ "'RETURN FLOW,
N, HYDRO/ "'WASTE WATER DISPOSAL,
RINKLER / "'WASTE WATER DISPOSAL,
'-OIL WASTES, "'REMEDIES, WATER /
ER, "'SEEPAGE, DRILL HOLES, OILY/
NNETONKA(MINN), SOIL MINERALS, /
HORUS, ALFALFA-BROMEGRASS, SPRI/
YSTEMS, EUTROPHICATION, OLIGOTR/
STRY, *WATER QUALITY, "'CLIMATES,
Q/ "'HYDROGEOLOGY, "'SOLID WASTES,
L, "'GROUNDWATER, "'WATER QUALITY,
ROGEOLOGY, WATER POLLUTION CONT/
LLUTION, "'GROUNDWATER, ^SEEPAGE,
"'WASTE DISPOSAL, "'GARBAGE DUMPS,
IL MOISTURE, EVAPOTRANSPIRATION,
WATER MOVEMENT, MODE/ "'LEACHING,
"'PATH OF POLLUTANTS, "'LEACHING,
STE DUMPS, "'SOLID WASTES, "'LEAC/
WATER MOVEMENT, CAPILLARY FLOW,
DRAINAGE, SANITARY ENGINEERING,
ER, WATER POLLUTION, ABSORPTION,
ES, PATH/ "'FARM WASTES, *CATTLE,
ON, "'WASTE DUMPS, "'SOLID WASTES,
NUCLEA/ "'RADIOECOLOGY, "'FALLOUT,
CS, SOIL AN/ "'NUTRIENTS, "'SOILS,
ON, "'GROUNDWATER MOVEMENT, MODE/
NE WATER-FRESH-WATER INTERFACES,
UMPS, *GRO/ "'PATH OF POLLUTANTS,
"'OILY WATE/ *PATH OF POLLUTANTS,
MIME WASTE/ "'TRITIUM, ^TRACERS,
LVANIA, "'OILY WATER, "'PIPELINES,
"'WELL REGULATIONS, "'WATER WELLS,
POLLUTION, *WOOD WASTES, "'RARK,
*SHALLOW WELLS, WATER WELLS, WA/
"'HYDRAULIC POTENTIAL, CANADA.:
"'HYDROGEOLOGY, "'SOLID WASTES, '-LA
"'HYDROGEOLOGY, "'ILLINOIS, MUNICIP
'-HYDROGEOLOGY, WATER POLLUTION CO
'-ILLINOIS, HYDROLOGIC DATA, GEOLO
"'ILLINOIS, MUNICIPAL WASTES, LEAC
-'ILLINOIS, "-WATER POLLUTION, *WAT
"'ILLINOIS, *SALINE WATER, "'WELLS,
* INDIA.:
-'INDUCED INFILTRATION, COLIFCRMS,
"'INDUCED INFILTRATION, *PIT RECHA
'-INDUCED INFILTRATION, *NEW YORK,
'-INDUSTRIAL WASTES, "'GRQUNDWATER
'-INFILTRATION, *WATER QUALITY POL
'-INFILTRATION, *WATER SPREADING,
'-INFILTRATION, --WATER SPREADING,
"'INFILTRATION, '-PONDS, "'SOIL, GRO
'-INFILTRATION, "'POROUS MEDIA, *AL
'-INFILTRATION, COLIFORKS, ENTERIC
'-ION EXCHANGE, "'WATER QUALITY, *I
"'ION EXCHANGE, DIFFUSION, MIXING,
'-IRRIGATION EFFICIENCY, SIMULATIO
'-IRRIGATION RETURN FLOW, HYDROLOG
"'IRRIGATION WATER, "'RETURN FLOW,
'-IRRIGATION EFFECTS, LEACHING, WA
'-IRRIGATION, * SURFACE- GROUND WATER
'-IRRIGATION, "'SPRINKLER IRRIGATIO
'-IRRIGATION, ^CHEMICAL WASTES, SP
"'KANSAS, "'SALINE WATER INTRUSION,
'-KENTUCKY, #0 1 L WELLS,' "'GROUNDWAT
"'KILLING, ANIMAL MANURES, LAKE MI
*LAKE EUTROPHICATION, "'SOIL PHOSP
'-LAKES, STREAMS, FISH, LAND, ECOS
*LAND USE, '-OKLAHOMA, SALINITY, S
'-LANDFILL HYDROLOGY.:
'-LANDFILL, '.''INFILTRATION, "'WATER
'-LANDFILL, SANITARY FILL, WASTE D
'-LANDFILLS, =:=WASTE DISPOSAL, =-HYD
'-LANDFILLS, *SOLID WASTES, WATER
'-LANDFILLS, "'PATH OF POLLUTANTS,
'-LANDFILLS, DRAINAGE, SANITARY EN
"'LANDFILLS, "'PERCOLATION, "'GROUND
'-LANDFILLS, "'GARBAGE DUMPS, *GROU
'-LANDFILLS, "'WATER POLLUTION, "=WA
"'LAVA, BASALTS, WATER POLLUTION S
"'LEACHING, WATER POLLUTION SOURCE
"REACHING, "'PERCOLATION.: /UNDWAT
"'LEACHING, "'WATER POLLUTION SOURC
"'LEACHING, "'GROUNDWATER, HYDROGEO
"'LEACHING, "'PATH OF POLLUTANTS, *
"'LEACHING, "'AQUIFER CHARACTER 1ST I
"'LEACHING, ^LANDFILLS, *PERCOLATI
'-LEACHING, "'SALINE WATER SYSTEMS,
"'LEACHING, ^LANDFILLS, "'GARBAGE D
"'LEACHING, "-SOIL WATER MOVEMENT,
BLEACHING, 'fCOPPER, *WASTE DUMPS,
"'LEAKAGE, JUDICIAL DECISIONS, OIL
"'LEGISLATION, CONSTRUCTION, PUMPS
"'LIGNINS, "'BIOCHEMICAL OXYGEN DEM
'"LOUISIANA, ''-PERCOLATING WATERS,
W70-07766
W70-09637
W70-06572
W70-07193
W70-06322
W70-06572
W70-02896
V'69-06118
W71-08073
W71-02909
W71-12410
W70-03102
W7 1-00 194
W70-09637
W7 1-0 120 5
W71-01324
W69-07838
W69-02681
W69-01076
W7 1-09936
W7 1-1 135 6
W71-09936
W71-09936
W7 1-0 6063
W7 1-08073
W69-00248
W69-07375
W69-07114
W71-13521
W71-08055
W70-04193
W69-09721
W70-04193
W70-06102
W71-08907
W70-09637
W69-03178
W70-07193
W 7 0-0 60 11
W70-06572
W68-00058
W70-09548
W7 1-0 1204
W7 1-0 7 194
W69-00979
W68-00058
W70-04688
W70-00665
W71-07194
W71-04882
W71-07887
W70-09548
W71-01932
W71-01204
W71-10325
W71-11255
W70-07632
W71-04742
W68-01269
W68-00627
-------
ATION, *POROUS MEDIA, '"ALLUVIUM,
STES, *OIL, LEGISLATION, STATE /
, *HIGHWAY ICING, '"SNOW REMOVAL,
VEMENT, '"DIFFUSION '"DISPERSION,
ILTRATION, RECH/ *WATFR QUALITY,
FEEDLOTS, RESIDUAL ACCUMULAT IO/
POLLUTANTS, -'-SALINE WATER INTRU/
WATERS, '"WATER POLLUTION CON'TRO/
ANN ING, MANAGEMENT, PERCOLATION,
rMEK'T, LEACH/ ="UNS ATURATED FLOW,
IDENTIFICATION, '"WATER QUALITY,
'"INFILTRATION, '"WATER SPREADING,
--INFILTRATION, '"WATER SPREADING,
S, '"WATER WELLS, '"REMEDIES, IMD/
NT, '"UNITED ST/ ="WASTE DISPOSAL,
*WATER REUSE, '-RECLAIMED WATER,
POLLUTION SOURCES, '"HERBICIDES,
E, *'»IATER POLLUTION SOURCES, JU/
REAMFLOW, '"INDUCED INFILTRATION,
M WASTES, '"CATTLE, '"GROUNDWATER,
PRECIPITATION, SEDIM/ '"NITROGEN,
ES, LEACHING, FARM WASTES, GROU/
ATH OF POLLUTANTS, *RETURN FLOW,
, '"SUBSURFACE DRAINAGE, DRAIMAG/
OIL CONTAMINATION, *FERT ILIZERS,
TIOM SOURCES, '"CORES, FIELDS, P/
PUBLIC HEALTH, *SOIL LEACHING, /
DENTIFICATIOM, '"WATER DUALITY, /
CE DRAINAGE, DRAINAG/ *NITRATES,
, ALGAE, MITRA/ '"EUTROPH ICATION,
, AMMONIA, PRECIPITATION, SEDIM/
-'-VENEZUELA,
--LEACHING, ''-PATH OF POLLUTANTS,
SPERSION, '"GROUNDWATER MOVEMENT,
GRAMS, DIFFUSION, / ="D IS PER ISDN ,
OUIFER CHARACTERISTICS, SOIL AN/
XAS), PARMER COUNTY(TEXAS), HOL/
KANSAS, *SALINE WATER INTRUSION,
AHOMA, *HATER POLLUTION SOURCES,
*SALINE WATER INTRU/ '"MICHIGAN,
*WATER POLLUTION, '"GROUNOWATER,
TATE / -MAINE, --WATER POLLUTION,
LVAMIA, *SALINE WATER INTRUSION,
E, DRILL HOLES, OILY/ --KENTUCKY,
, *WATER POLLUTION, *OIL WASTES,
UTION, JUDICIAL D/ CONNECTICUT,
, JUDICIAL DECIS/ *PENNSYLVAN I A,
BLEACHING, *SOIL WATER MOVEMENT,
ES, *OIL WASTES, '"REMEDIES, WAT/
R QUALITY, '--CLIMATES, *LAND USE,
VESTI/ *WATER POLLUTION EFFECTS,
ATMENT, *SLUDGE DIGESTION, AMAE/
, *NITRAT/ '-SIMULATION ANALYSIS,
DIOECOLOGY, ^FALLOUT, *LEACHING,
, *WATER POLLUTION SOURCES, *GR/
R MOVEMENT, '"STATISTICAL MODELS,
SOIL WATER MOVEMENT, *OILY MATE/
*LYSIMETERS, *RADI 01SOTOPES, RADI
'"MAINE, '"WATER POLLUTION, *OIL WA
'-MAINE, DEICERS, ROADS, CHEMCONTR
'"MATHEMATICAL MODELS, MODEL STUDI
'^MATHEMATICAL MODELS, INDUCED IMF
*HETHEMQGLOBIN, NITRATE MOVEMENT,
'-MICHIGAN, --OIL WASTF.S, --PATH OF
'-MISSOURI, ^PERMITS, '-SUBSURFACE
'-MODEL STUDIES, *COMPUTER PROGRAM
'-MOISTURE ROUTING, LANDFILL MANAG
^MONITORING, *GROUNDWATER, NITRAT
^MONITORING, WATER POLLUTION SOUR
'-MONITORING, WATER POLLUTION SOUR
'-MONTANA, '-WATER POLLUTION SOURCE
-'MULTIPHASE FLOW.:
'-MUNICIPAL WASTES, *WASTE TREATME
'"MUNICIPAL WASTES, '^ARTIFICIAL RE
*NEW MEXICO, *SOIL WATER MOVEMENT
*NEW YORK, *WATER WELLS, =:-GASOLIN
'-NEW YORK, HYDROGRAPHS, HYDROGRAP
*NITRATE, AQUIFER, DISCHARGE, AOU
^NITRATES, GROUNDWATER, AMMONIA,
*NITRATES, *WATER POLLUTION SOURC
^NITRATES, MATHEMATICAL MODELS, C
'-NITRATES, '-NITROGEN, *RIO GRANDE
*NITRATES, WATER POLLUTION, NITRO
'-NITRATES, *AMMONIA, *WATER POLLU
'-NITRIFICATION, *SOIL NITROGEN, *
'-NITROGEN COMPOUNDS, '^POLLUTION I
*NITROGEN, *RIO GRANDE, *SUBSURFA
'-NITROGEN, '-PHOSPHORUS, NUTRIENTS
'-NITROGEN, *NITRATES, GROUNDWATER
'-NUCLEAR CANAL EXCAVATION.:
--NUCLEAR ENGINEERING, NUCLEAR EXP
^NUISANCE.:
-''NUMERICAL ANALYSIS, MIXING, COMP
^NUMERICAL ANALYSIS, COMPUTER PRO
'-NUTRIENTS, *SOILS, BLEACHING, *A
*OGALLALA AQUIFER, HIGH PLAINS(TE
'-OIL SPILLS.:
'^REMEDIES, WATER POL
^REMEDIES, WATER POL
*PATH OF POLLUTANTS,
'"SEPARATION TECHNIQU
'--OIL, LEGISLATION, S
"WATER WELLS, GROUNDW
WASTES,
WASTES,
WASTES,
WASTES,
WASTES,
WELLS, :
'"OIL
'"OIL
*OIL
*OIL
*OIL
'"OIL
*OIL WELLS, *GROUNDWATER, '"SEEPAG
'"OIL, LEGISLATION, STATE GOVERNME
'"OILY WATER, *UNDERSEE PAGE, '"POLL
'"OILY WATER, '"PIPELINES, '"LEAKAGE
*OILY WATER, '"GROUNDWATER RECHARG
'"OKLAHOMA, *WATER POLLUTION SOURC
'"OKLAHOMA, SALINITY, STREAMFLOW,
*ON-SITE INVESTIGATIONS, '"SOIL IN
'"OXIDATION LAGOONS, ="TERTIARY TRE
*PATH OF POLLUTANTS, ^RETURN FLOW
*PATH OF POLLUTANTS,
'"PATH OF POLLUTANTS,
*PATH OF POLLUTANTS,
*PATH OF POLLUTANTS,
'"NUCLEAR ENG
'"FARM WASTES
MATHEMATICAL
'"LEACHING, *
W69-
V69-
W70-
W69-
W69-
W71-
W70-
W71-
W71-
W68-
W71-
W71-
V'l I-
W71-
W71-
K' 11
W69-
W71-
W69-
W70-
W71-
W71-
W71-
W71-
W70-
W71-
W70-
W69-
W71-
W70-
W71-
W71-
W71-
W71-
W7O
W71-
W71-
W71'
W71'
W71-
W71
W71'
W70
W71
W69
W71
W71
W69
W70
W70
W71
W71
W70
W70
W71
W71
W71
W71
W71
W71
02681
05370
09844
07554
02611
10372
08026
10157
09936
00058
12122
01205
01324
11692
11776
-08907
08620
-06514
06117
-03102
-03543
-06435
-08218
-04548
-08662
-02036
-04488
-09721
-12122
-08662
-06443
-06435
-04882
-04882
-08025
-04559
-09611
-07887
-12122
-10325
-13521
-11724
-08026
-01930
-05370
-03230
-08055
-05370
-07631
-07632
-10325
-11724
-06102
-06322
-07118
-04548
-04882
-04121
-11776
-10325
-------
ES, *GROUNDWATER MOVEMENT, *DIS/
LANDFILLS, ^GARBAGE DUMPS, -"-GRO/
R INTRU/ ^MICHIGAN, '-OIL WASTES,
ILTRATION, COLIFORMS, ALLUVIAL /
*SOIL/ -'WATER POLLUTION SOURCES,
OUNDWATER MOVEMENT, LABORATORY /
SAL, '''GARBAGE DUMPS, -'LANDFILLS,
US MEDIA, ^GROUNDWATER MOVEMENT,
MOVEMENT, -'DIFFUSION, *DISPERS/
GROUNDWATER MOVEM/ -'-WATER REUSE,
LINES, ^LEAKAGE, JUDICIAL DECIS/
USION, -''OIL WELLS, *WATER WELLS/
--SALINE WATER INTRUSION, '-WATER/
NT, MODE/ -'LEACHING, *LANDFILLS,
DWATE/ -'RHODE ISLAND, -'GASOLINE,
AND, -'SEEPAGE, *WATER POLLUTION,
ION, ^SEEPAGE, '''SUBSURFACE WATE/
ION, "'SEEPAGE, ^SUBSURFACE WATE/
OLLUTION, ABSORPTION, BLEACHING,
HT/ '"REMEDIES, '"WATER POLLUTION,
LS, WATER WELLS, WA/ '"LOUISIANA,
ONDU/ PERCOLATION, GROUND WATER,
TER POLLUTION CONTRO/ '"MISSOURI,
TRA/ -'EUTROPHICATION, '"NITROGEN,
CE-GROUNDWATER RE/ '"GROUNDWATER,
CIS/ '"PENNSYLVANIA, '"OILY WATER,
RECHARGE, '"INDUCED INFILTRATION,
RATION, COLIFORMS, ENTERIC BACT/
CUT, '"OILY WATER, '"UNDERSEE PAGE ,
UTIOM, '"WATER POLLUTION CONTROL,
QUALITY, / '"NITROGEN COMPOUNDS,
, WATER SUPPLY, / -'INFILTRATION,
ENT, -'/ '"DISPERSION, '"DIFFUSION,
EMT, '"PATH OF POLLU/ '"DIFFUSION,
TERS, '"RADIOISOT/ '"INFILTRATION,
EMT, ="ST/ '"STOCHASTIC PROCESSES,
, '"WATER WELLS, '"LEGISLATION, C/
'"NITRIFICATION, '"SOIL NITROGEN,
DIFFUSION, '"SOIL WATER MOVEMENT,
G, *PATH OF POLLUTANTS, *NUCLEA/
MENT, '"DIS/ I'PATH OF POLLUTANTS,
S MEDIA, '"ALLUVIUM, ="L YS I MET ERS ,
L WASTES, -'GROUNDWATER MOVEMENT,
ES, '"ARTIFICIAL R/ -'WATER RFUSE,
R POLLUTION, '"PERCOLATING WATER,
COLATING WATER, '"RELATIVE RIGHT/
POLLUTION SOURCES, '"WATER WELLS,
POLLUTION SOURCES, -'OIL WASTES,
NE WATER INTRUSION, '"OIL WASTES,
URGES, *WATER POLLUTION EFFECTS,
ETERIORATION/ '"IRRIGATION WATER,
N ANALYSIS, *PATH OF POLLUTANTS,
RATED SOILS, '"I/ '"WATER QUALITY,
CE-GROUNDWATER RELATIONSHIPS, D/
WASTE TREATMENT, '"UNITED STATES,
OLLUTION, '"PERCOLATING WATER, R/
ATING WATER, '"WELLS, GROUNDWATE/
, DRAINAG/ -'NITRATES, '"NITROGEN,
STRY, DARCY'S LAW, PERMEABILITY,
*PATH
*PATH
'"PATH
'"PATH
'"PATH
'"PATH
'"PATH
*PATH
'"PATH
OF
OF
OF
OF
OF
OF
OF
OF
OF
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
'"RADIOISOTDP
* LEACHING, *
*SALINE WATE
'"INDUCED IMF
--DIFFUSION,
*ALDRIN, ="GR
I'HYDROGEOLOG
INJECTION WE
*GROUNDWATER
'"PATHOGENIC BACTERIA, *VIRUSES, *
'"PENNSYLVANIA, '"OILY WATER, '"PIPE
--PENNSYLVANIA, -SALINE WATER INTR
'"PENNSYLVANIA, '"WATER POLLUTION,
'"PERCOLATION, '"GROUNDWATER MOVEME
'"PERCOLATING WATER, DWELLS, GROUN
WATER, RIPARIAN RIGH
WATER, '"WATER POLLUT
WATER, '"WATER POLLUT
.: /UNDWATER, WATER P
WATER, '.'-RELATIVE RIG
WATERS, -'SHALLOW WEL
'"PERMEABILITY, POROSITY, CLOSED C
--PERMITS, '"SUBSURFACE WATERS, ="WA
'"PHOSPHORUS, NUTRIENTS, ALGAE, MI
'"PIEZOMETRY, '"WATER TABLE, '"SURFA
'"PIPELINES, '"LEAKAGE, JUDICIAL DF
'"PIT RECHARGE, '"WATER TREATMENT,
'"POLLUTANTS, GROUNDWATER, '"INFILT
'"POLLUTION, JUDICIAL DECISIONS, 0
'-POLLUTION ABATEMENT, STATE GOVER
--POLLUTION IDENTIFICATION, '"WATER
*PONDS, -'SOIL, GROUNDWATER BASINS
'"POROUS MEDIA, '"GROUNDWATER MOVEM
MEDIA, ^GROUNDWATER MOVEM
MEDIA, *ALLUVIUM, '"LYSIME
MEDIA, '"GROUNDWATER MOVEM
HEALTH, '"WELL REGULATIONS
'"PERCOLATING
'"PERCOLATING
'"PERCOLATING
'"PERCOLATION,
--PERCOLATING
'"PERCOLATING
* POROUS
*POROUS
-POROUS
'"PUBLIC
*PUBLIC
HEALTH, *SOIL LEACHING,
G
'"RADIOACTIVE WASTES, EQUATIONS, G
-'RADIQECOLOGY, '"FALLOUT, '"LEACHTN
'"RADIOISOTOPES, '"GROUNDWATER MOVE
-'RADIOISOTOPES, RADIOACTIVE WASTE
'"RECHARGE, --SURF ACE-GROUNDWATER R
-'RECLAIMED WATER, '"MUNICIPAL WAST
'"RELATIVE RIGHTS, WATER LAW, GROU
'"REMEDIES, *WATER POLLUTION, *PER
-''REMEDIES, INDUSTRIAL WASTES, WAT
-'REMEDIES, WATER POLLUTION, WATER
'-REMEDIES, WATER POLLUTION, JUDIC
'-RETURN FLOW, '-SALINE WATER INTRU
--'DRAINAGE WATER, *D
'^NITRATES, MATHEMAT
*GROUNDWATER, *SATU
'-IRRIGATION, -'SURFA
'-REVIEWS, METHODOLOGY, SANITARY E
-'RHODE ISLAND, ^SEEPAGE, =l=WATER P
*RHODE ISLAND, *GASOLINE, *PERCOL
'i'RIO GRANDE, *SUBSURFACE DRAINAGE
'-RIVER FLOW.: /PTION, WATER CHEMI
*RUHR VALLEY.:
-'RETURN
*RETURN
*RETURM
^RETURN
FLOW,
FLOW,
FLOW,
FLOW,
W71-
W71-
W7O
W71-
W70'
W70-
W70-
W69-
W69-
K'69'
W70-
W71'
W71'
W70'
W70-
W71-
W70-
W70-
W70-
W7Q.
W68-
W69-
W?l'
W71-
W70-
W70'
W71-
W69-
W70-
W70'
W71-
V;69'
W69'
W69-
W69-
W71-
W7L
W69'
W70'
W71'
W71-
W69'
W71-
W69-
W70'
W70'
W71-
W 71
W71'
W71-
W71-
W71-
W71'
W69-
W71-
W71-
W70-
W70-
W69-
W71-
-11356
-01204
-08026
-02909
-10058
-01904-
-06572
-03212
-07554
-08621
-07632
-03230
-01028
-09548
-08025
-01043
-08050
-08049
-04688
-00521
-00627
-00979
-10157
-06443
-07766
-07632
-12410
-01076
-07631
-02896
-12122
-07838
-03237
-03212
-02681
-11776
-04742
-09721
-10058
-0.4882
-11356
-02681
-00194
-08620
-00521
-00521
-11692
-11724
-13521
-08044
-06063
-04548
-08073
-00248
-08907
-01043
-08025
-08662
-02611
-12410
-------
TESt '-REMEDIES, HATER / -'KANSAS,
ESH-WATER INTERFACES, '-LEACHING,
OIL WASTES, '-PATH OF POLLUTANTS,
LS, '-WATER WELLS/ =-DEMNS YL VAN I A,
CES, BLEACHING, #SALI\'E WATER S/
'"PENNSYLVANIA, #WATFR POLLUTION,
POLLUTION EFFECTS, #RETURN FLOW,
ECISIONS, OIL WASTES/ -'ILLINOIS,
SPORT.:
ITY, *RETURN FLOW, '-GROUNDWATER,
PERSION, -'CONVECTION, -'GROUNDWA/
*WATER POLLUTION, '-GROUNDWATER,
OUNDWATER RECHARGE, GROUNDWATER,
TUCKY, *OIL WELLS, ^GROUNDWATER,
OLATING WATER, R/ *RHODE ISLAND,
OLATING WATER, #WATER POLLUTION,
OLATING WATER, *WATER POLLUTION,
TIOM, #GROUNDWATFR, #OIL WASTES,
-WATER SPREADING, *MONITORIMG, /
-'LOUISIANA, -'-PERCOLATING WATERS,
, *GROUNDWATER MOVEMENT, *NUMER/
LLUTANTS, *RETURN FLOW, '-NITRAT/
ON LAGOONS, --TERTIARY TREATMENT,
SODTUM CHLORIDE, '"HIGHWAY ICING,
-=SNO/ -'WATER POLLUTION EFFECTS,
, -'NITRATES, MATE/ '-FARM WASTES,
FFECTS, *ON-SITE INVESTIGATIONS,
*SOIL NITROGEN, '-PUBLIC HEALTH,
RECHARGE, GROUNDWATER, '-SEEPAGE,
SOIL LEACHING, / *NITRIFICATI ON ,
ASS, SPRI/ -'LAKE EUTROPH ICAT ION,
ATER TREATMENT, WATER POLLUTION,
ATER TREATMENT, WATER POLLUTION,
*PATH OF POLLUTANTS, '-DIFFUSION,
URCES, -HERBICIDES, #NEW MEXICO,
-'PATH OF POLLUTANTS, '"LEACHING,
SUR/ *DETERGENT REHAV IOR(WATER ) ,
SUPPLY, / '"INFILTRATION, '"PONDS,
S, GROUMDWATER, PRECIPITATION, /
CTERISTICS, SOIL AN/ '"NUTRIENTS,
OLLUTION SOURCES, '"URBAN I ZAT ION,
*WATER POLLUTION, '"WASTE DUMPS,
RATION, *WATER Q/ *HYDROGEOLOGY,
OUNDWATER, '"SEEPAGE, *LANDFILLS,
STE WATER DISPOSAL, '"IRRIGATION,
US MEDIA, '"GROUNDWATER MOVEMENT,
DIA, *GROUi\'DWATER MOVEMENT, -=ST/
MENTUPPL IED) , '"CONJUNCTIVE USE,
*EUTRO/ -'^AGRICULTURAL WATERSHED,
ION CONTRO/ -MISSOURI, *PERMITS,
TER, -'-WATER POLLUTION, '-SEEPAGE,
TER, #WATER POLLUTION, -'-SEEPAGE,
ITRATES, '"NITROGEN, *RIO GRANDE,
ES, MINERALIZATION, NITROGEN SO/
*CONSUMPTIVE USE, *GROUNDWATER,
ATER, *PIEZOMETRY, *WATER TABLE,
INDUCED INFILTRATION, RECHARGE,
S, D/ '"RETURN FLOW, ^IRRIGATION,
'"SAL INE
*SALINE
-=SAL INE
-=SAL INE
*SALINE
-SALINE
*SALINE
*SAL INE
WATER INTRUSION, #01L WAS
WATER SYSTEMS, *GROUNDWAT
WATER INTRUSION, WATER PO
WATER INTRUSION, --OIL WEL
WATER-FRFSH-WATER INTERFA
WATER INTRUSION, --WATER W
WATER INTRUSION, #HAWAII,
WATER, DWELLS, JUDICIAL D
*SALT WATER IRRIGATION, SALT TRAM
-'SATURATED SOILS, -'IRRIGATION EFF
^SATURATED FLOW, #OIFFUSION, #01S
^SEEPAGE CONTROL.:
-'SEEPAGE, #LANDFILLS, *SOLIO WAST
*SEEPAGE, *SOIL MOISTURE, EVAPOTR
-'SEEPAGE, DRILL HOLES, OILY WATER
-'SEEPAGE, #WATER POLLUTION, #PERC
^SEEPAGE, ^SUBSURFACE WATERS, PRI
-'SEEPAGE, *SUBSURPACE WATERS, GRO
-'SEPARATION TECHNIQUES, IMFILTR^T
-'SEWAGE DISPOSAL, -'INFILTRATION,
-'SHALLOW WELLS, WATER WELLS, WATF
-'SIMULATION ANALYSIS, -'DISPERSION
-'SIMULATION ANALYSIS, -'PATH OF PO
-'SLUDGE DIGESTION, ANAEROBIC DIGE
-=SNOH REMOVAL, -'MAINE, DEICERS, R
#SODIUM CHLORIDE, --HIGHWAY ICING,
-'SOIL CONTAMINATION, ^FERTILIZERS
#SOIL INVESTIGATIONS, ^GEOLOGIC I
*SOIL LEACHING, GROUNDWATER, SOIL
-'SOIL MOISTURE, E VAPOTRA NS P I RAT 10
-'SOIL NITROGEN, #PI1RLIC HEALTH, #
*SOIL PHOSPHORUS, ALFALFA-BROMEGR
*SOIL WASTE TREATMENT, SOIL PERCO
-'SOIL WASTE TREATMENT, SOIL PERCO
-'SOIL WATER MOVEMENT, -'RADIOACTIV
-'SOIL WATER MOVEMENT, GROUNDWATFR
-'SOIL WATER MOVEMENT, -'OILY WATER
-'SOIL-WATER ENVIRONMENT, ANIONIC
-'SOIL, GROUNDWATER BASINS, WATER
*SOILS, *FARM WASTES, '-FERTILIZER
'-SOILS, '-LEACHING, #AOUIFER CHARA
-'SOLID WASTES, #WASTE DISPOSAL, S
-'SOLID WASTES, BLEACHING, #GROUND
*SOLID WASTES, -'LANDFILL, -''INFILT
#SOLID WASTES, WATER POLLUTION SO
'-SPRINKLER IRRIGATION, HYDROGEOLO
#STATISTICAL MODELS, *PATH OF POL
'-STOCHASTIC PROCESSES, '-POROUS ME
-'STREAMFLOW, *INDUCED INFILTRATIO
^SUBSURFACE DRAINAGE, ^DRAINAGE,
WATERS, #WATER POLLUT
WATERS, GROUNDWATER,
WATERS, PRIOR APPROPR
DRAINAGE, DRAINAGE WA
RE-CYCLE.:
*SUBSURFACE
*SUBSURFACE
*SUBSURFACE
''-SUBSURFACE
'-SUPERNATANT
-'SURFACE WATERS, GEOLOGICAL SOURC
*SURFACE WATERS, SURFACE RUNOFF,
*SURFACE-GROUNDWATER RELATIONSHIP
#SURFACE-GROUNDWATER RELATIONSHIP
*SURFACE-GROUNDWATER RELATIONSHIP
W 7 1 -
W 71 -
W70-
W71-
W71-
W71-
W 71 -
W69-
W71-
W71-
W69-
W70-
W70-
W68-
I'171-
W7 1-
W70-
V'70-
W71-
1-171-
W68-
W71-
W 71-
W71-
W70-
W70-
W71-
W70-
W69-
W68-
W69-
W69-
W69-
W69-
W70-
W71-
W71-
W 7 0 -
W69-
W71-
W71-
W71-
W 71 -
W70-
W70-
W69-
W71-
W71-
W7O
W70-
W71-
W 70-
Wl 0-
W70-
W 71
W71-
W70-
W70-
W69-
W69-
13521
01932
08026
03230
01932
01028
08044
06118
06063
0892]
06011
06011
00058
08055
01043
08049
08050
01930
01205
00627
'04559
04548
07118
09844
09844
02036
06322
09721
00058
09721
09721
05327
05328
10058
06514
1.0325
01291
07838
03542
07887
05094
07194
09637
0601 1
07375
11776
11776
03102
04504
-10157
08050
08049
08662
-07118
-06435
00532
-07766
-02611
-00248
-------
GROUNDWATER MOVEMENT, ^RECHARGE,
ATES, -'DETERGENTS, -'GROUMDWA TER/
(NY)
-'WATER SPREADING, -'WATER RFUSE,
STION, AMAE/ '-OXIDATION LAGOONS,
, LEACH BED, SPOK/ DRAIN FIELDS,
ON, ATOMIC ABSOR/ '-GROUND WATER,
STE DUMPS, MINE WASTE/ -'TRITIUM,
LE'-I, LEYDEN, THE HAGUE, MINERAL/
OPPFR, -'WASTE DUMPS, MINF WASTE/
AL D/ '-CONNECTICUT, -'OILY WATER,
RODS MEDIA, GROUNDWATER, WASTES,
1C I PAL WASTES, *WASTE TREATMENT,
ING, LANDFILL MANAGEMENT, LEACH/
MO), WILSON CREEK (MO), SPRINGFI/
STE D/ #WATER POLLUTION SOURCES,
TION. :
TION, GROUND-WATER, WATER POLLU/
UTION, ABSORPTION, '-LEACHING, '-/
TER REUSE, '^PATHOGENIC BACTERIA,
RCES, '-DAMAGES, *WATER WELL, IM/
S, '^URBANIZATION, '-SOLID WASTES,
S, '-WASTE TREATMENT, '-UNITED ST/
'-LANDFILLS, *PATH OF POLLUTANTS/
ATER POLLUTION CONT/ '-LANDFILLS,
ATER OUALITY, "'LANDFILL, SANITA/
C/ '-LANDFILLS, -'WATER POLLUTION,
M, '-TRACERS, '-LEACHING, -'COPPER,
STE DISPOSAL, '^'MUNICIPAL WASTES,
M, *SPRINKLER IRRIGATION, HYDRO/
STE TREATMENT, SOIL PERCOLATION,
STE TREATMENT, SOIL PERCOLATION,
R TREATMENT, W/ SEWAGE EFFLUENT,
N, ^CHEMICAL WASTES, SPRINKLER /
R TREATMENT, W/ SEWAGE EFFLUENT,
*CLIMATES, =:=LAND USE, *OKLAHOM/
UNCTIVE USE, '-STREAMFl OW, 'MNDU/
RFACE-GRHUNDWATER RELATIONSHIPS ,
IO/ -'ILLINOIS, -"IATFR POL.LUTIOf^1,
SEEPAGE, -'LANDFILLS, =:'SOLID WAS/
FARM WASTES, '-CATTLF, -'LFACHU'G,
FIELDS, P/ '-NITRATES, '-AMMONIA,
N CONTROL, *POLLUTIO/ -'ILLINOIS,
TERGENTS, '-GROUNHWAT ER MOVEMENT,
E INVESTIGATIONS, -'SOIL INVESTI/
TER, -'RELATIVE RIGHT/ -'REMEDIES,
IL, LEGISLATION, STATE / '-MAINE,
US MEDIA, SGROUNm-'ATER MOVEMENT,
W YORK, *WATER WELLS, -'GASOLINE,
CHARGE, GROUNDWATCR, ^SEEPAGE, /
BARK, -''LIGNINS, '^BIOCHEMICAL OX/
FECTS, '-WATER POLLUTION CONTROL,
IDES, '-NEW MEXICO, *SniL WATER /
POLLUTION CONTROL, -'WATER POLLU/
POLLU/ '-WATER POLLUTION EFFECTS,
FLOW/ *WATER POLLUTION SOURCES,
POLLUTION EFFECTS, *RFTURN FLOW/
'"SURFACE-GROUNDWATER RELATIONSHIP W7l-
'"SURFACTANTS, '"ALKYRFNZ F NE SULFON W70-
-'SUSOUEHANNA RIVER BASIN, (M Y).: W70-
'"SUSOUEHANNA RIVER(NY), BINGHAMTO W71
'"TANNINS, SUGARS.: W68
'"TERTIARY TREATMENT, INFILTRATION W70-
'"TERTIARY TREATMENT, '"SLUDGE DIGE V'/l
-'TEST HOLES, ANNUAL PRECIPITATION 1/69-
'"TRACE ELEMENTS, CHELATE EXTRACT I W69-
'"TRACERS, '"LEACHING, '"COPPER, ="WA W71-
'"TRANSFORMATIONS, AMSTERDAM, HAAR W69-
'"TRITIUM, '"TRACERS, '"LEACHING, ='=C W71-
'"UNDERSEEPAGE, '"POLLUTION, JUDICI W70-
'"UNIFORM FLOW, '"DIFFUSION, POROUS H69-
'"UNITED STATES, '"REVIEWS, METHODO W71-
'"UNSATURATED FLOW, '"MOISTURE ROUT K68-
'"URBAN HYDROLOGY.: W71-
-'URBAN STORM RUNOFF, JAMES RIVER( W"il
-'URBANIZATION, '"SOLID WASTES, ="WA W"i 1
'"VENEZUELA, '"NUCLEAR CANAL EXCAVA W71-
-'VIRUSES, '"BACTERIOPHAGE, PERCOLA W69-
'"VIRUSES, GROUNDWATER, WATER POLL W7O-
-'VIRUSES, '"GROUNDWATER MOVEMENT, W69-
-'WASHINGTON, '"WATER POLLUTION SOU W71-
-00194
-01291
-03102
-02909
-01269
-04712
-07118
-01076
-03197
-11255
-07838
-11255
-07631
-01238
-08907
-00058
-05094
-091 54
-05094
-04882
-00225
-04688
-08621
'"WASTE
'"WASTE
-'WASTE
'"WASTE
'"WASTE
'"WASTE
-'WASTE
'"WASTE
'"i-1 A STE
'"WASTE
'"WASTE
'"WASTE
'"WASTE
'"WASTE
'"WATER
'"WATER
'"WATER
'"WATER
'"WATER
'"WATER
'"WATER
'"WATER
'"WATER
'"WATER
'"WATER
'"WATER
'"WATER
-'WATER
'"WATER
'"WATFR
-'WATFR
'"WATER
'"WATER
'"WATER
'"WATER
'"WATER
DISPOSAL, SURFACE WASTERS,
DISPOSAL, '"MUNICIPAL WASTE
DISPOSAL, -'CARRAGE DUMPS,
DISPOSAL, '"HYDROGEOLOGY, W
DISPOSAL, '"GROUNDWATER, '"W
DUMPS, -'SOLID WASTES, -=LEA
DUMPS, MINF WASTES, MIvIf>'G
TREATMENT, '"UNITED STATES,
WATER DISPOSAL, -'IRRIGATIO
WATFR RECLAMATION, INDUCED
WATER RECLAMATION, INDUCED
WATER DISPOSAL, WASTE WATE
WATER DISPOSAL, '"IRRIGATIO
WATER DISPOSAL, WASTE WATE
CHEMISTRY, '"WATER DUALITY,
MANAGEMENT ( APPLIED), '"COMJ
POLLUTION SOURCES, INFILTR
POLLUTION CONTROL, '"POLL'JT
POLLUTION, '"GROUNDWATER, '"
POLLUTION SOURCES, PATH OF
POLLUTION SOURCES, '"CORES,
POLLUTION, '-WATER POLLUTIO
POLLUTION, INFILTRATION, A
POLLUTIO"' EFFECTS, '"ON-SIT
POLLUTION, '"PERCOLATING WA
POLLUTION, '"OIL WASTES, -'0
POLLUTIOV, PATH OF POLLUTA
POLLUTION SOURCES, JUDICIA
POLLUTION, '"GROUWDWATER RE
POLLUTION, '"WOOD WASTES, '"
POLLUTION SOURCES, -'FISHKI
POLLUTION SOURCES, -'HERBIC
POLLUTION EFFECTS, '"WATER
POLLUTION CONTROL, '"WATER
POLLUTION EFFECTS, '"RETURN
POLLUTION SOURCES, '"WATER
W7 1-0 5094
W71 -08907
W7 0-0 65 7 2
W 70-0 71 93
W69-03178
W~ 1-07194
W71-] 1255
K71-08907
W69-07375
W69-05328
W69-05327
Wf 9-05328
W69-07114
W69-05327
W70-06102
W70-03102
W70-07766
W70-02896
W 7 0-0 60 11
W70-00665
W 7 0-0 44 8 8
W70-02896
V'70-01291
W70-06322
W70-00521
V'69-05370
W69-03237
W69-06117
W6 8-00058
W68-01269
W7 1-09] 54
W71-06514
W7 1-091 54
W7I -091 54
W 7 1-0 8044
H7 1-08044
-------
'"DRAINAGE WATER, -'DETERIORATION,
ZATION, '"SOLID WASTES, '"WASTE D/
G, FARM HASTES, GROU/ '"NITRATES,
ATM OF POLLUTANTS, '"FARM WASTES,
SOLID WASTES, '"LEAC/ '"LANDFILLS,
M CONTR/ *WYOMING, '"GROUNDWATER,
STES, '"REMEDIES, WAT/ '"OKLAHOMA,
'"GROUMDWATER, '"WATER POLLUTION,
WELLS, -"REMEDIES, IND/ '"MONTANA,
I, '"PERMITS, '"SUBSURFACE WATERS,
S, *WATER WELL, I TV '"WASHINGTON,
*CROP PRODUCTION, *FERTILIZERS,
F POLLUTANTS, '"DIFFUSION, '"SOIL/
URFACE WATE/ *PERCOLATING WATER,
URFACE WATE/ '"PERCOLATING WATER,
RIAL WASTES, *GRQUNDWATER MOVEM/
OIL WASTES, '-SEPARATION TECHNIO/
CHLORIDE, '"HIGHWAY ICING, *SNO/
TER, R/ '"RHODE ISLAND, '"SEEPAGE,
NTRUSION, *WATER/ '"PENNSYLVANIA,
ASTES, ^LANDFILL, * INF ILTRATI ON ,
UNDS, ^POLLUTION IDENTIFICATION,
--FERTILIZERS, '"WATER POLLUTION/
OLLUTION SOURCES, '"ION EXCHANGE,
OUNDWATER, '"SATURATED SOILS, '"I/
ELS, INDUCED INFILTRATION, RECH/
--WASTE DISPOSAL, '"GROUNDWATER ,
USE, '"OKLAHOM/ *WATER CHEMISTRY,
YIELD, IN/ -'ARTIFICIAL RECHARGE,
CIAL RECHARGE, *WATER SPREADING,
A, *VIRUSES, '"GROUNDWATER MOVE-M/
MUNICIPAL WASTES, '"ARTIFICIAL R/
TERTIARY / '"ARTIFICIAL RECHARGE,
TER POLLUTION SO/ '-INFILTRATION,
'-SEWAGE DISPOSAL, * INF ILTRAT ION ,
R RE/ *GROUNDWATER, *P IEZOMFTRY,
CED INFILTRATION, *PIT RECHARGE,
MTAMA, *WATER POLLUTION SOURCES,
TER POLLUTION SOURCES, '"DAMAGES,
LUTION, '"SALINE WATER INTRUSION,
INE WATER INTRUSION, *OIL WELLS,
UBLIC HEALTH, '-WELL REGULATIONS,
OLLUTION SOURCES, JU/ *NEW YORK,
OBSERVATION WELLS, HATER LEVELS,
^LEGISLATION, C/ *PUBLIC HEALTH,
, '-GASOLINE, '-PERCOLATING WATER,
ASTES/ '-ILLINOIS, *SALINE WATER,
IOCHEMICAL OX/ *WATER POLLUTION,
LLUTION, *WATER POLLUTION CPNTR/
'-WATER POLLUTION EFFECTS, WATER 0
*WATER POLLUTION SOURCES, *URBANI
'-WATER POLLUTION SOURCES, LEACHIN
'-WATFR POLLUTION SOURCES, *GROU^'D
'"WATER POLLUTION, *WASTE DUMPS, *
'"WATER POLLUTION, '"WATER POLLUTIO
'"WATER POLLUTION SOURCES, '"OIL WA
'"WATER POLLUTION CONTROL, POLLUTI
'"WATER POLLUTION SOURCES, '"WATER
'"WATER POLLUTION CONTROL, WATER P
'"WATER POLLUTION SOURCES, '"DAMAGE
'"WATER POLLUTION SOURCES, NITROGE
'"WATER POLLUTION SOURCES, '"PATH 0
'"WATER POLLUTION, '"SEEPAGE, ="SU^S
'"WATER POLLUTION, '"SEEPAGE, '"SUBS
'"WATFR POLLUTION SOURCES, '"INDUST
="W A lER POLLUTION, '"GROUND WATE R , *
'"WATER POLLUTION EFFECTS, '"SODIUM
'"WATER POLLUTION, '"PERCOLATING WA
'"WATER POLLUTION, '"SALINE WATER I
'"WATER QUALITY POLLUTION, RECHARG
'"WATER QUALITY, '"MONITORING, *GRO
'"WATER QUALITY, '"CROP PRODUCTION,
'"WATER QUALITY, '"IRRIGATION EFFIC
'"WATER QUALITY, '"RETURM FLOW, ="GR
*KATER QUALITY, '"MATHEMATICAL MOD
'"WATER QUALITY, '"LANDFILL, SANITA
'"HATER QUALITY, '"CLIMATES, ="LAND
'"WATER REUSE, '"CALIFORNIA, WATER
'"WATER REUSE, '"TERTIARY TREATMENT
'"WATER REUSE, '"PATHOGENIC BACTERI
="WATER REUSE, '"RECLAIMED WATER, '"
'"WATER SPREADING, -WATER REUSE, ="
'"WATER SPREADING, '"MONITORING, WA
'"WATER SPREADING, '"MONITORING, WA
'"WATFR TABLE, *SUR FAC E-GROUNDWAT E
'"WATER TREATMENT, '"FILTATION, ALL
'"WATER WELLS, '"REMEDIES, INDUSTRI
'"WATER WELL, IMPAIRED WATER QUALI
'"WATER WELLS, OIL INDUSTRY, PUBLI
'"WATER WELLS, GROUNDWATER, SALINE
'"WATER WELLS, *L EG I SLA TI ON, CONST
'"WATER WELLS, '"GASOLINE, '"WATER P
'"WATER WELLS, WATER SUPPLY, AQUIF
'"WELL REGULATIONS, '"WATER WELLS,
'"WELLS, GROUNDWATER, OILY WATER,
'"WELLS, JUDICIAL DECISIONS, OIL W
'"WOOD WASTES, *BARK, '"LIGNINS, '"B
'"WYOMING, '"GROUNDWATER, '"WATER PO
W7 1-06063
W71-05094
W7 1-0 82 18
W71-04121
W71-07194
W71-10446
W> 1-1 1724
W71-10446
W71-11692
W71-10157
W7 1-13645
W71-12084
W~(0-10058
W70-08050
W70-08049
W71-00194
W71-01930
W70-09844
W71-01043
W7 1-0 102 8
W70-09637
W71-12122
W7 1-1 2084
W71-09936
W7 1-08073
W69-02611
(-'69-03178
W70-06102
V'70-05466
W70-04712
W6 9-0 8621
W69-08620
W70-04712
W7 1-0 1324
W7 1-0 120 5
W70-07766
W7 1-12410
W71-11692
W7 1-1 3645
W71-01028
W7 1-03230
W71-04742
W69-06117
\-.'e 9-02611
W71-04742
W7 0-0 80 2 5
W69-06118
W68-01269
W71-10446
8
-------
BIBLIOGRAPHY
-------
-------
WATER MOVEMENT IN AN UNSATURATED SANITARY LANDFILL,
OREXEL INST. OF TECHNOLOGY, PHILADELPHIA, CORNELL UNIV., ITHACA, NY.
IRWIN REMSON, A. ALEXANDER FUNGAROLI, AND ALONZO W. LAWRENCE.
ASCE PROC, JOUR SANIT AND ENG, VOL 94, NO SA2, PAPER 5904, PP 307-317, APR
1968. 11 P, 1 FIG, 4 TAB, 14 REF.
DESCRIPTORS:
*WATER POLLUTION, *GROUNDWATER RECHARGE, GROUNDWATER, ^SEEPAGE, *SOIL
MOISTURE, EVAPOTRANSPIRATION, *LANDFILLS, DRAINAGE, SANITARY
ENGINEERING, #LEACHING, WATER POLLUTION SOURCES, SOLID WASTES, WASTES,
GARBAGE DUMPS, WASTE DUMPS, WASTE STORAGE, SOIL PROPERTIES, MOISTURE
CONTENT, POLLUTANTS, SOIL WATER MOVEMENT.
IDENTIFIERS:
*UNSATURATED FLOW, *MOISTURE ROUTING, LANDFILL MANAGEMENT, LEACHATE,
INFILTRATION CAPACITY, GROUNDWATER CONTAMINATION.
ABSTRACT:
CONTAMINATION OF GROUNDWATER FROM LEACHING OF SANITARY LANDFILLS WILL
BECOME MORE COMMON AS USE OF THIS WASTE-DISPOSAL METHOD SPREADS. AN
UNDERSTANDING OF THE MOISTURE REGIMEN OF THE LANDFILL IS BASIC TO A
KNOWLEDGE OF THE CHARACTER AND QUANTITY OF THE WATER-BORNE CONTAMINANTS
IT GENERATES. MOISTURE-ROUTING METHODS ARE EXTENDED TO PROVIDE AN
APPROXIMATE METHOD FOR PREDICTING VERTICAL MOVEMENT OF MOISTURE THROUGH
A HYPOTHETICAL LANDFILL. THE METHOD IS BASED ON CLIMATOLOGICAL
TECHNIQUES OF SOIL-MOISTURE ROUTING AND INCORPORATES THE HYDRAULIC
CHARACTERISTICS OF THE UNSATURATED PERMEABLE MATERIALS MAKING UP THE
FILL AND OVERLYING SOIL COVER. USING THE METHOD, PREDICTIONS WERE MADE
OF THE EFFECT OF EMPLACEMENT SEASON AND INITIAL CONDITIONS ON THE
MOVEMENT OF MOISTURE. RESULTS SHOW THAT THE TIME THAT ELAPSES BEFORE
THE FIRST LEACHATE APPEARS DEPENDS ON THE SEASON OF EMPLACEMENT AND THE
INITIAL MOISTURE CONTENT. VARIOUS OBJECTIVES IN LANDFILL-MANAGEMENT MAY
BE OBTAINED BY VARYING THE TIME OF EMPLACEMENT, INITIAL MOISTURE
CONTENT, SOIL COVER, AND OTHER FACTORS. TABLES SHOW MOISTURE ROUTING
THROUGH THE SOIL AND COMPACTED REFUSE AND COMPUTATION OF MONTHLY
GROUNDWATER RECHARGE.
FIELD 05A
ACCESSION NO. W68-00058
-------
MONROE '66' OIL COMPANY V HIGHTOWER (LEGAL DAMAGE FROM SHALLOW WELL POLLUTION
BY HYDROCARBONS).
180 SO 20 8-11 (CT APP LA 1965).
DESCRIPTORS:
^LOUISIANA, *PERCOLATING WATERS, *SHALLOW WELLS, WATER WELLS, WATER
POLLUTION, DAMAGE, JUDICIAL DECISIONS, GROUND WATER, PATH OF
POLLUTANTS, SUBSURFACE FLOW, GASOLINE, WATER LAW, WELLS, GROUND WATER
MOVEMENT.
IDENTIFIERS:
*DAMAGES(LEGAL ASPECTS), HYDROCARBON POLLUTION.
ABSTRACT:
THIS WAS AN ACTION ON OPEN ACCOUNT FOR GOODS SOLD AND DELIVERED BY
PLAINTIFF TO DEFENDANT. THE CORRECTNESS OF PLAINTIFF'S CLAIM WAS
ADMITTED. DEFENDANT RECONVENED FOR DAMAGES ALLEGEDLY CAUSED BY
PLAINTIFF'S NEGLIGENCE IN INSTALLING UNDERGROUND GASOLINE STORAGE TANKS
AND CONNECTING LINES TO GAS PUMPS. DEFENDANT OWNED A CAFE WHICH WAS
SUPPLIED WITH WATER FROM A SHALLOW WELL 70 FEET AWAY. PLAINTIFF
INSTALLED PUMPS AND STORAGE TANKS IN FRONT OF CAFE. WITHIN A YEAR
DEFENDANT'S WELL BECAME POLLUTED BY HYDROCARBONS, AND IT WAS FOUND THAT
THE TANK CONNECTIONS WERE LEAKING. AS A RESULT OF THIS POLLUTION OF THE
CAFE'S SOLE WATER SUPPLY, THE HEALTH DEPARTMENT ORDERED DEFENDANT TO
CLOSE THE CAFE BUSINESS. THE CASE DEALS PRIMARILY WITH THE PROPER
MEASURE OF DAMAGES DUE THE DEFENDANT. THE COURT HELD THAT DEFENDANT WAS
ENTITLED TO THE COST OF A NEW WELL PLUS $100 FOR THE EXPENSE AND
INCONVENIENCE OF HAULING WATER.
FIELD 05B
ACCESSION NO. W68-00627
10
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INFILTRATION AND PERCOLATION STUDIES OF SULFIDES AND SEWAGE CARBONACEOUS MATTER,
HAWAII UNIV, HONOLULU.
JAMES S. KUMAGAI.
WATER RESOUR RES CENTER, UNIV HAWAII TECHN REP 7, JUNE 1967. 58 P, 14 FIG, 25
TAB, 26 REF, APPEND.
DESCRIPTORS:
SEWAGE DISPOSAL, ORGANIC LOADING, *BIODEGRADATI ON, SOIL DISPOSAL
FIELDS, CESSPOOLS, SEPTIC TANKS, SULFATES, SULFIDES, PERCOLATING WATER,
INFILTRATION, GROUNDWATER MOVEMENT.
ABSTRACT:
THE LABORATORY STUDY OF INFILTRATION AND PERCOLATION OF SULFIDES AND
SEWAGE CARBONACEOUS MATTER WAS CONDUCTED IN 2 PHASES: PHASE 1 UTILIZED
SIMULATED CESSPOOL LYSIMETERS AND PHASE 2 CONSIDERED THE GENERATION OF
SULFIDES AND THE INFILTRATION AND PERCOLATION OF SULFIDES THROUGH SOIL
AND SAND COLUMNS. PHASE 1 RESULTS DICTATED A NEED FOR FURTHER STUDY
OWING TO FREE PERCOLATION OF CERTAIN ODOROUS COMPOUNDS AND EXCELLENT
COD REMOVALS UNDER PRESUMABLY ANAEROBIC CONDITIONS CONTRARY TO FINDING
IN SIMILAR STUDIES. IN PHASE 2 SOIL COLUMN WAS MORE EFFECTIVE FOR
SULFIDE REMOVAL THAN THE SAND COLUMN WHICH ALLOWED CONTINUOUS
BREAKTHROUGH OF AN ODOROUS PERCOLATE. PROGRESSIVE MOVEMENT OF A BLACK
PRECIPITATE THROUGH THE SANDBED INDICATED THAT FILTERING ACTION OF SAND
WAS NOT AS EFFECTIVE AS SOIL COLUMN. UNDER ACID CONDITIONS, SULFIDE
BREAKTHROUGH WAS CLEARLY DEMONSTRATED IN BOTH SAND AND SOIL COLUMNS.
FLOW RATE SIGNIFICANTLY IMPROVED IN BOTH COLUMNS AFTER PERCOLATION OF
ACIDIFIED FLUIDS. ALL COLUMNS EXHIBITED CHARACTERISTIC NONLINEAR
RELATIONSHIP BETWEEN FILTRATION AND PERCOLATION RATES AND THE HYDRAULIC
GRADIENT.
FIELD 02G, 05G
ACCESSION NO. W68-01010
11
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WATER QUALITY DEGRADATION BY WOOD BARK POLLUTANTS,
MAINE UNIV., WATER RESOURCES CENTER, ORONO, MAINE.
OTIS J. SPROUL, AND CLIFFORD A. SHARPE.
MAINE UNIV., WATER RES CENTER PUB NO 5, 53 P, JUNE 1968. 19 FIG, 6 TAB, 10
REF.
DESCRIPTORS:
*WATER POLLUTION, *WOOD WASTES, *BARK, *LIGNINS, ^BIOCHEMICAL OXYGEN
DEMAND, LEACHING, RUNOFF, GROUNDWATER, CELLULOSE, HYDROGEN ION
CONCENTRATION, TOXICITY.
IDENTIFIERS:
*TANNINS, SUGARS.
ABSTRACT:
THE LEACHING OF WOOD BARK WAS STUDIED IN THE LABORATORY TO DETERMINE
ITS EFFECT UPON WATER QUALITY. SIGNIFICANT WATER QUALITY DEGRADATION
RESULTS FROM MATERIALS LEACHED FROM WOODBARK STOCKPILES ON LAND OR IN
WATERCOURSES. THIS DEGRADATION IS FROM ORGANIC AND INORGANIC MATERIALS
WHICH CAUSE BOD, COLOR, ODOR, COD, ALKALINITY, AND ACIDITY AND INCREASE
THE SOLIDS IN THE WATER. SOFTWOOD BARK LEACHINGS FROM SIMULATED "DRY'
LAND STOCKPILES HAD COLOR OF UP TO 1000 UNITS, BOD UP TO 1200 MG/1 AND
A THRESHOLD ODOR NUMBER OF 500 AT THE END OF 55 DAYS. HARDWOOD BARK
LEACHINGS UNDER SIMILAR CONDITIONS WERE DEGRADED TO A LESSER EXTENT
EXCEPT FOR A HIGHER COLOR. STORAGE UNDER HIGHER TEMPERATURES GENERALLY
DECREASED THE EXTENT OF WATER CONTAMINATION. BENTHAL BARK DEPOSITS
CREATED OXYGEN DEMANDS OF ABOUT 0.6 TO 0.8 POUNDS PER DAY PER TON OF
DRY BARK. BOD VALUES WITHIN THE BARK BENTHAL DEPOSIT REACHED 17,700
MG/1. COLOR OF THE OVERLYING WATER REACHED AS HIGH AS 6,000 UNITS FOR
THE SOFTWOOD BARK. HARDWOOD BARKS GAVE COLORS AS HIGH AS 1,000 UNITS.
WHEN STOCKPILED ON LAND WOODBARK SHOULD BE PLACED OVER IMPERVIOUS
MATERIAL AND SURROUNDED BY IMPERVIOUS BERMS SO THAT RAINWATER MOVING
THROUGH THE PILE CANNOT CARRY THE POLLUTIONAL MATERIALS INTO
WATERCOURSES. (KNAPP-USGS)
FIELD 05C
ACCESSION NO. W68-01269
12
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MIGRATION OF BACTERIOPHAGE T4 IN PERCOLATING WATER THROUGH SELECTED OAHU SOILS,
HAWAII UNIV., HONOLULU.
RICHARD M. TANIMOTO, REGINALD H. F. YOUNG, AND NATHAN C. BURBANK, JR.
OWRR PROJECT NO. A-001-HI, WATER RESOURCES RESEARCH CTR, TECH RPT NO 20, JUN
1968. 45 P, 9 FIG, 4 TAB, 64 REF.
DESCRIPTORS:
*VIRUSES, #BACTERIOPHAGE, PERCOLATION, GROUND-WATER, WATER POLLUTION.
ABSTRACT:
TESTS TO DETERMINE THE ABILITY OF THREE OAHU SOILS TO REMOVE THE
COLIPHAGE T4BR11 MUTANT VIRUS FROM WATER PERCOLATING THROUGH LOW HUMIC
LATOSOLS (WAHIAWA AND LAHAINA SOILS) PROVED THE SOILS ABILITY TO RETAIN
THE VIRUS BUT ONLY AT DEPTHS GREATER THAN 21/2 INCHES. ABSORPTION WAS
100% WHEN THE CONCENTRATION APPLIED WAS 2.5 X 10 TO THE 6 POWER VIRUS
PER ML OF FEED SOLUTION. BREAKTHROUGH AT LESSER THICKNESSES OF SOIL
OCCURRED SLOWLY AT FIRST THEN INCREASED RAPIDLY WITH TIME. TANTALUS
TUFF, A CINDERY PUMICE SUBSTRATUM WAS INEFFECTIVE IN RETAINING VIRUSES
EVEN AT SOIL THICKNESSES OF AS GREAT AS 15 INCHES. (BURBACK-HAWA11)
FIELD 05G
ACCESSION NO. W69-00225
13
-------
PREDICTING RETURN FLOWS FROM IRRIGATION,
BUREAU OF RECLAMATION, U S DEPARTMENT OF THE INTERIOR, DENVER, COLORADO,
OFFICE OF ATMOSPHERIC WATER RESOURCES.
PATRICK A. HURLEY.
ASCE PROC, J IRRIG AND DRAINAGE DIV, VOL 94, NO IR1, PAP 5838, PP 41-48, MAR
1968. 8 P, 3 FIG, 3 TAB, 3 REF.
DESCRIPTORS:
*RETURN FLOW, IRRIGATION, *SURFACE-GROUNDWATER RELATIONSHIPS, DRAINAGE
EFFECTS, DRAINS, DEEP PERCOLATION, EVAPOTRANSPIRATION.
IDENTIFIERS:
TRANSIENT STORAGE, GRAPHICAL SOLUTIONS.
ABSTRACT:
AN ANALYTICAL METHOD FOR COMPUTING RETURN FLOW OR DRAINAGE FROM
IRRIGATION APPLICATIONS IS PRESENTED AND DISCUSSED. COMPUTATIONS
CONSIDER AQUIFER PROPERTIES, DRAIN SPECING, AND DEEP PERCOLATION. A
GRAPH FOR DETERMINING THE FRACTIONAL PART OF PERCOLATION REMAINING IN
TRANSIENT STORAGE IS INCLUDED. BY USING THE GRAPH AND SIMPLE DIGITAL
PROCEDURES, REALISTIC ESTIMATES OF IRRIGATION RETURN FLOW CAN BE
DETERMINED. THE METHOD WAS USED TO DETERMINE MONTHLY QUANTITIES FOR 13
YR OF RETURN FLOWS IN THE MESILLA VALLEY, NEW MEXICO-TEXAS. (AUTHOR)
FIELD 05B, 048
ACCESSION NO. W69-00248
14
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THE EFFECTS OF TEMPERATURE AND DENSITY GRADIENTS UPON THE MOVEMENT OF
CONTAMINANTS IN SATURATED AQUIFERS,
ALABAMA UNIV., UNIVERSITY.
HAROLD R. HENRY.
UNIV ALABAMA RPT, 1967. 14 P, 4- FIG, 26 REF. OWRR PROJECT B-004-ALA.
DESCRIPTORS:
CONTAMINATION, *AOUIFERS» CONVECTION, ^DISPERSION, WASTE DISPOSAL,
THERMAL PROPERTIES, MODEL TESTS, SATURATION ZONES, SEEPAGE, NUMERICAL
METHOD, LABORATORY TESTS, PERMEABILITY, POROSITY, POROUS MATERIALS,
BIBLIOGRAPHIES, DARCYS LAW.
IDENTIFIERS:
TEMPERATURE PROFILES, THERMAL DIFFUSION.
ABSTRACT:
EXPERIMENTAL AND ANALYTICAL STUDIES WERE MADE ON A SIMPLIFIED GEOMETRIC
MODEL. A HORIZONTAL, LATERAL TEMPERATURE GRADIENT WAS IMPOSED UPON A
HORIZONTAL CHANNEL OF SQUARE CROSS SECTION CONTAINING SAND SATURATED
WITH WATER. VELOCITIES WERE MEASURED BY TRACING DYE PATTERNS ALONG THE
GLASS WALLS AND TOP OF THE CHANNEL. TEMPERATURES WERE MEASURED BY
NETWORKS OF COPPER-CONSTANTAN THERMOCOUPLE JUNCTIONS SPACED THROUGHOUT
THE CHANNEL. EXPERIMENTAL TEMPERATURES AND VELOCITIES INDICATED THE
PRESENCE OF A CONVECTION CURRENT WHICH INCREASED IN STRENGTH AS THE
TEMPERATURE GRADIENT INCREASED. BY DEFINING A STREAM FUNCTION PSI AND
BY APPROPRIATE NORMALIZATION OF THE VARIABLES, THE GOVERNING EQUATIONS
WERE REDUCED TO AN EXPRESSION WHICH IS PARAMETER FREE EXCEPT FOR A
VALUE, M, WHICH IS A MODIFICATION OF THE RAYLEIGH NUMBER. FINITE
DIFFERENCE SOLUTIONS ARE OBTAINED FOR SEVERAL VALUES OF M AND FOR
SEVERAL BOUNDARY CONDITIONS. THE EFFECTIVE VALUE OF THERMAL DIFFUSIVITY
IS FOUND TO BE ABOUT 50 TIMES LARGER THAN THE USUAL VALUE BECAUSE OF
THE DISPERSION WHICH OCCURS WHEN FLUID MOVES THROUGH THE TORTUOUS
CHANNELS WITHIN THE POROUS BED.
FIELD 05B
ACCESSION NO. W69-00651
15
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TRAVEL OF ABS AND AMMONIA NITROGEN WITH PERCOLATING WATER THROUGH SATURATED
OAHU SOILS,
HAWAII UNIV., HONOLULU.
REGINALD H. F. YOUNG, L. STEPHEN LAU, AND NATHAN C. BURBANK.
WATER RESOUR RES CENTER, TECHN REP 1, JAN 1967. 54 p, 13 FIG, 7 TAB, 32 REF,
4 APPEND. OWRR PROJECT A-001-HI.
DESCRIPTORS:
PERCOLATING WATER, INFILTRATION, DETERGENTS, POLLUTANTS, NITROGEN
COMPOUNDS, SOIL CONTAMINATION, CESSPOOLS, SEWAGE DISPOSAL, GROUNDWATER
MOVEMENT, ABSORPTION, ADSORPTION.
ABSTRACT:
A LABORATORY STUDY WAS UNDERTAKEN TO DETERMINE THE ABILITY OF 4 OAHU
SOILS, LOLEKAA, LAHAINA, MANANA, AND WAHIAWA, TO REMOVE AMMONIA, ABS,
AND COLIFORMS FROM WATER PERCOLATING CONTINUOUSLY THROUGH SATURATED
SOILS. SOILS UTILIZED WERE CHOSEN ON THE BASIS OF THEIR WIDE OCCURRENCE
ON THE ISLAND AREAS WHERE PERCOLATING WATER MAY ENTER DIRECTLY AND IN
QUANTITY INTO THE GROUND WATER BODY THAT PRINCIPALLY PROVIDES THE
ISLAND'S DOMESTIC WATER SUPPLY. ALL 4 SOILS HAD A HIGH CLAY CONTENT AND
LOW PH. LABORATORY TESTS WERE CONDUCTED WITH 10-ML BURETTES AND SUBJECT
TO CONTINUOUS SATURATED FLOW. EACH CONTAMINANT WAS APPLIED IN SOLUTION
1 AT A TIME TO A FRESH SOIL SAMPLE. TAP WATER WAS USED FOR ABS AND
AMMONIA NITROGEN WHILE SEWAGE WAS USED TO STUDY COLIFORM REMOVAL. THE
RESULTS OF COLIFORM REMOVAL FROM PERCOLATING LIQUIDS WERE NOT
CONCLUSIVE BECAUSE OF SMALL SOIL SAMPLES AND LOADING PROCEDURES.
PRELIMINARY TESTS VERIFIED SOME GENERAL PRINCIPLES DEVELOPED ELSEWHERE
FOR EFFECTIVE COLIFORM REMOVAL BY GROUND DISPOSAL OF SEWAGE. THE FINAL
CLARIFIER EFFLUENT FROM A TRICKLING FILTER WAS PASSED CONTINUOUSLY
THROUGH A 30 IN. COLUMN OF WAHIAWA SOIL AND AN INITIAL COLIFORM
REDUCTION OF ABOUT 90 S WAS EFFECTED.
FIELD 05B
ACCESSION NO. W69-00652
16
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EFFECTS OF SOLUBLE ORGANICS ON FLOW THROUGH THIN CRACKS OF BASALTIC LAVA,
HAWAII UNIV., MANOA.
KENNETH ISHIZAKI, NATHAN C. BURBANK, JR., AND STEPHEN LAU.
TECH REP 16, WATER RESOUR RES CENTER, AUG 1967. 56 P, 38 FIG, 9 TAB, 42 REF,
2 APPEND. OWRR PROJECT A-001-HI.
DESCRIPTORS:
PERCOLATION, GROUND WATER, *PERMEABILITY, POROSITY, CLOSED CONDUIT
FLOW, *GROUND WATER MOVEMENT, CAPILLARY FLOW, *LAVA, BASALTS, WATER
POLLUTION SOURCES, MICROORGANISMS, FERROBACILLUS, FLOW RESISTANCE,
RETENTION, HAWAII.
IDENTIFIERS:
HAGAN-POISEUILLE FLOW, CLOGGING.
ABSTRACT:
MOST OF OAHU'S DOMESTIC WATER SUPPLY IS FROM GROUND WATER OCCURRING IN
PERMEABLE MATERIALS OF VOLCANIC ROCK. MOVEMENT OF GROUND WATER IS
INTRINSICALLY THROUGH THIN CRACKS IN BASALTIC LAVAS. THIS PROJECT
STUDIED PASSAGE OF AN ORGANIC-RICH LIQUID THROUGH CRACKS IN BASALT.
PERMEABILITY OF BLUE ROCK PORTIONS OF A BASALT WAS DETERMINED AS 2.6 BY
10 TO THE MINUS 4- POWER GAL/DAY/SQ FT OF WATER, CLASSING THE ROCK AS
IMPERVIOUS. A RANGE OF 7.7 TO 10.45? IN POROSITY VALUES WAS OBTAINED
FROM THE BLUE ROCK PORTIONS; THE CLINKER PORTION YIELDED A VALUE OF
50%. THE GREATEST RETARDATION IN FLOW OF NONBIODEGRADABLE LIQUIDS
THROUGH THIN CRACKS OCCURRED IN THE INITIAL HOURS FOLLOWED BY A
SYSTEMATIC REDUCTION OF FLOW TO 7/8 TO 1/100 OF THE INITIAL FLOW RATE.
FLOW OF ORGANIC-RICH LIQUIDS THROUGH SUCH CRACKS, SIMILAR TO
NONBIODEGRADABLE LIQUIDS, EXHIBITS A DECREASE IN FLOW INITIALLY AND
CONTINUES THIS TREND FOR AS LONG AS 220 HR. TERMINAL FLOW VELOCITY OF
TAP WATER IS MUCH GREATER THAN THAT OF SEWAGE WHICH APPEARS TO PROCEED
TO A NO-FLOW CONDITION. THE CLOGGING PHENOMENON WAS DEPENDENT UPON
MICROBIAL ACTIVITY AND FOOD SUPPLY IN SEWAGE. THE PRODUCTS ARE
PRIMARILY POLYSACCHARIDES AND SLIMES ALONG WITH FERROUS SULFIDE,
COMMONLY FOUND IN SEPTIC SEWAGE IN CONTACT WITH SOIL OR ROCK.
FIELD 05B, 02F
ACCESSION NO. W69-00979
17
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MIGRATION OF POLLUTANTS IN A GLACIAL OUTWASH ENVIRONMENT,
WASHINGTON STATE UNIV., PULLMAN.
JAMES W. CROSBY, III, DONALD L. JOHNSTONE, CHARLES H. DRAKE, AND ROBERT L.
FENTON.
WATER RESOURCES RESEARCH, VOL 4, NO 5, PP 1095-1114, OCTOBER 1968. 17 FIG, 1
TAB, 17 REF.
DESCRIPTORS:
^POLLUTANTS, GROUNDWATER, *INFILTRATION, COLIFORMS, ENTERIC BACTERIA,
NITRATES, CHLORIDES, *CAP1LLARY CONDUCTIVITY, SOIL MOISTURE.
IDENTIFIERS:
DRAIN FIELDS, *TEST HOLES, ANNUAL PRECIPITATION, LEACH BED, SPOKANE
RIVER VALLEY.
ABSTRACT:
A TEST DRILLING PROGRAM WAS CONDUCTED IN A DRAIN FIELD AREA OF THE
SPOKANE VALLEY, WASHINGTON TO STUDY THE MOVEMENT OF POLLUTANTS IN
GLACIAL OUTWASH DEPOSITS WHEN THEY ARE SUBJECTED TO EXTREME POLLUTANT
LOADS. CONTRARY TO WHAT MIGHT BE EXPECTED, VERY DRY SOILS WERE FOUND AT
DEPTHS BENEATH THE DRAIN FIELD, AND IT IS CONCLUDED THAT MOST OF THE
WATERS ARE BEING DISPERSED LATERALLY BY CAPILLARY MECHANISMS. MUCH OF
THE SYSTEMIC WATER MAY ULTIMATELY BE RETURNED TO THE ATMOSPHERE BY
EVAPOTRANSPIRATION. MOISTURE CONDITIONS IN THE DRAIN FIELD SYSTEM
STRONGLY INDICATE THAT GROUND-WATER RECHARGE THROUGH INCIDENT
PRECIPITATION IN THIS PART OF THE VALLEY WOULD BE HIGHLY IMPROBABLE.
CHEMICAL POLLUTANTS ARE FOUND TO TRAVEL WITH MOISTURE FRONTS, BUT FINE
MATERIALS ARE DETERMINED TO BE VERY EFFECTIVE IN FILTERING BACTERIA
WITHIN A RELATIVELY FEW FEET OF THE LEACH BED. (SENECA-RUTGERS)
FIELD 05B
ACCESSION NO. W69-01076
18
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BAND DIFFUSION WITH VARIABLE PARAMETERS ALONG FLOW,
SYRACUSE UNIVERSITY, NEW YORK.
WEN-HSIUNG LI.
J ENG MECH OIV, AMER SOC CIV ENG, PROC PAP 4106, VOL 90, NO EM5, PP 343-361,
OCT 1964. 19 P, 8 FIG, 14 REF, APPEND.
DESCRIPTORS:
*DISPERSION, FLOW, POROUS MEDIA, GROUNDWATER, WASTES, ^UNIFORM FLOW,
*DIFFUSION, POROUS MATERIALS, *ENGINEERING MECHANICS.
ABSTRACT:
THE DIFFUSION EQUATION WITH VARIABLE PARAMETERS ALONG THE FLOW CAN BE
SOLVED WHEN THE DIFFUSED QUANTITY IS CONFINED TO A NARROW BAND.
SOLUTIONS ARE OBTAINED FOR DIFFUSION FROM A LINE SOURCE AND A POINT
SOURCE IN NONUNIFORM FLOWS. THE DISPERSION OF A CONTAMINANT IN
NONUNIFORM FLOWS THROUGH POROUS MEDIA IS STUDIED. IT IS FOUND THAT THE
DISPERSION ACROSS THE STREAMLINES CAN BE ESTIMATED BY USING THE
SOLUTIONS OF DIFFUSION FROM A LINE SOURCE AND A POINT SOURCE IN A
UNIFORM FLOW. (S. MAYER-FWPCA)
FIELD 02F, 05B
ACCESSION NO. W69-01238
19
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EFFECT OF RIVER WATER QUALITY ON AN ADJACENT AQUIFERf
CINCINNATI UNIV., OHIO.
HERBERT C. PREUL, AND L. V. POPAT.
SYSTEMS APPROACH TO WATER QUALITY IN THE GREAT LAKES, PROC 3RD ANNU SYMP
WATER RESOURCES RES, PP 73-96, OHIO STATE UNIV, SEPT 1967. 24 P, 11 FIG, 5
TAB, 8 REF.
DESCRIPTORS:
*WATER QUALITY, *MATHEMATICAL MODELS, INDUCED INFILTRATION, RECHARGE,
*SURFACE-GRQUNDWATER RELATIONSHIPS, OBSERVATION WELLS, WATER LEVELS,
*WATER WELLS, WATER SUPPLY, AQUIFERS, ION EXCHANGE, POLLUTANTS,
POLLUTANT IDENTIFICATION, ADSORPTION, WATER CHEMISTRY, DARCY'S LAW,
PERMEABILITY, *RIVER FLOW.
IDENTIFIERS:
GREAT MIAMI RIVER, S.W. OHIO WATER COMPANY, NETWORK ANALYSIS.
ABSTRACT:
PREDICTIVE MATHEMATICAL MODELS USED TO DETERMINE THE QUANTITY AND
QUALITY OF RECHARGE FROM THE GREAT MIAMI RIVER TO COLLECTOR WELLS WERE
PRESENTED. THE QUANTITY MODEL, BASED ON A SIMPLIFIED NODE-NETWORK
MODEL, REPRESENTING GROUND BASIN DYNAMICS BASED ON DARCY'S LAW, WAS A
LINEAR DIFFERENCE-DIFFERENTIAL MODEL USING ONE-HALF YEAR AS THE
INCREMENT OF TIME. THE CONCENTRATION OF POLLUTANTS WAS DETERMINED AS
THE SUM OF CONCENTRATIONS INTRODUCED BY THE CONVECTIVE FLUX BETWEEN THE
RIVER AND WELL. CALCULATED POLLUTANT CONCENTRATIONS WERE TABLED, AND
COMPARED WITH MEASURED CONCENTRATIONS. IT WAS CONCLUDED THAT A HIGH
PERCENTAGE OF THE WATER RECHARGING THE TWO COLLECTOR WELLS ORIGINATES
FROM THE RIVER, AND THAT THE POLLUTANT INHIBITORY CAPABILITIES OF THE
AQUIFER, IN THE FORM OF ADSORPTION AND ION EXCHANGE, WERE NEARLY
EXHAUSTED. (GYSI-CORNELL)
FIELD (KB, 05B
ACCESSION NO. W69-02611
20
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MODEL EXPERIMENTS ON FLUID FLOW IN THE TRANSITION ZONE FROM UNSATURATED TO
SATURATED SOIL,
BUNDESANSTALT FUER GEWASSERKUNDE, COBLENZ, (WEST GERMANY).
F. SCHWILLE, W. LIPPOK, AND D. WEISFLOG.
PROC OF SYMP, INT AT ENERGY AGENCY, VIENNA, AND EUROPE NUCL ENERGY AGENCY, PP
151-160, 1967. 10 P, 10 FIG, DISCUSS.
DESCRIPTORS:
*INFILTRATION, *POROUS MEDIA, ^ALLUVIUM, *LYSIMETERS, *RAD101SOTOPES,
RADIOACTIVE WASTE DISPOSAL, GROUNDWATER MOVEMENT, PERCOLATION, SEEPAGE,
UNSATURATED FLOW, MODEL STUDIES, SATURATED SOILS.
IDENTIFIERS:
HOMOGENEOUS MEDIA, UNSATURATED SOIL.
ABSTRACT:
LYSIMETER STUDIES OF THE INFILTRATION OF WATER INTO SOIL WERE MADE IN A
STUDY OF THE SAFETY FACTORS OF RADIONUCLIDE-PRODUCING PLANTS LOCATED ON
RIVER ALLUVIUM IN GERMANY. MORE THAN FOUR-FIFTHS OF THE DRINKING WATER
IN GERMANY IS GROUNDWATER OR BANK-FILTERED RIVER WATER. THE MOST
IMPORTANT AQUIFERS IN THE FEDERAL REPUBLIC OF GERMANY ARE FLUVIATILE
AND FLUVIOGLACIAL PLEISTOCENE SAND AND GRAVEL DEPOSITS, SITUATED IN THE
VALLEYS OF THE LARGE RIVERS. THE GROUND-WATER LEVEL IS GENERALLY FROM 3
TO 15 M BELOW GROUND SURFACE. DEPENDING ON THE PERMEABILITY OF THE
SUBSTRATA, ABOUT 100 TO 300 MM OF PRECIPITATION WATER PROBABLY
INFILTRATES. THESE ALLUVIAL PLAINS ARE POSSIBLE LOCATIONS FOR
RADIONUCLIDE-PRODUCING PLANTS. HOWEVER, IT IS HARD TO FIND ANY LOCALITY
WHERE SUCH PLANTS WOULD NOT HAVE A MARKED EFFECT ON THE WATER SUPPLY
SYSTEM. TO PROTECT GROUNDWATER AGAINST RADIONUCLIDE CONTAMINATION, A
DETAILED KNOWLEDGE IS FIRST NECESSARY OF THE MIGRATION MECHANISMS OF
RADIONUCLIDE-CONTAINING SOLUTIONS BOTH INTO THE UNSATURATED ZONE AND
THE SATURATED ZONE. INFILTRATION IN THE UNSATURATED ZONE AND SPREADING
IN THE SATURATED ZONE WERE ANALYZED WITH SAND MODELS. LARGE GLASS
LYSIMETERS, EXPERIMENTAL TROUGHS WITH GLASS WALLS AND SMALL DIAMETER
COPPER AND GLASS SEGMENT-TUBES WERE USED AS MODELS. THE LIQUID FRONTS
WERE TRACED MAINLY WITH ULTRA-VIOLET LIGHT. THE RESULT SHOWS THAT IT IS
NOT YET POSSIBLE TO TREAT THE FLOW OF LIQUID ANALYTICALLY IN EVERY
CASE, EVEN IN HOMOGENEOUS MEDIA. (KNAPP-USGS)
FIELD 02G, 05B
ACCESSION NO. W69-02681
21
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INVESTIGATION OF THE INFLUENCE OF WASTE DISPOSAL PRACTICES ON GROUNDWATER
QUALITIES,
SOUTH DAKOTA STATE UNIV., BROOKINGS. DEPT. OF CIVIL ENGINEERING.
JOHN R. ANDERSON, AND JAMES N. DORNBUSH.
TECHNICAL COMPLETION REPORT, WATER RESOURCES INSTITUTE, NOVEMBER, 1968,
WASHINGTON, D. C., 41 P, 5 TAB, 11 FIG, 13 REF. OWRR PROJECT A-003-SDAK.
DESCRIPTORS:
*WASTE DISPOSAL, *GROUNDWATER, *WATER QUALITY, *LANDFILL, SANITARY
FILL, WASTE DILUTION, WATER POLLUTION CONTROL, LEACHING, WATER QUALITY
CONTROL, DOMESTIC WASTES, INFILTRATION, AQUIFORS, SANITARY ENGINEERING.
IDENTIFIERS:
BROOKINGS(SOUTH DAKOTA).
ABSTRACT:
AN EVALUATION OF THE EFFECTS OF ITS LANDFILL ON THE GROUNDWATER QUALITY
WAS INITIATED BY THE CITY OF BROOKINGS, S. D. IN 1960, AND INCORPORATED
IN A COMPREHENSIVE STUDY BY THIS PROJECT IN 1964. THE INITIAL PHASE OF
THE PROJECT CONCLUDED THAT THE MOST USEFUL PARAMETERS FOR DETECTING
CONTAMINATION WERE CHLORIDES, SODIUM AND SPECIFIC CONDUCTANCE WITH THE
NEXT PHASE, CONCLUDING THAT SEASONAL RAINFALL INTENSIFIED LEACHING.
INCREASED IONIC CONCENTRATIONS DURING RAINY PERIODS IMPLIED THAT
EFFECTS OF LEACHING OVERRODE THOSE ATTRIBUTED TO DILUTION. IT APPEARED
THAT AS THE WATER MOVED DOWNSTREAM FROM THE LANDFILL THE QUALITY
IMPROVED AND WAS SUITABLE AS A DOMESTIC WATER SUPPLY AND FOR
IRRIGATIONAL PURPOSES BEFORE IT LEFT THE LANDFILL AREA. IN AS MUCH AS
IT WAS FOUND THAT A POND SEEMED TO IMPROVE THE QUALITY OF THE DEGRADED
GROUNDWATER, A TRENCH WAS CONSTRUCTED TO INTERCEPT THE GROUNDWATER AS
IT MOVED FROM THE FILL AREA. IT WAS SHOWN THAT CHEMICAL CONSTITUENTS
THAT WERE LEACHED FROM THE REFUSE WERE MODIFIED BY THE TRENCH AND WATER
QUALITY EXHIBITED AN IMPROVEMENT. THE TRENCH ALSO MODIFIED THE
CONCENTRATIONS OF ORGANIC MATERIALS AND THE THRESHOLD ODOR LEVELS.
GENERAL RECOMMENDED PRACTICES WERE MADE FOR DISPOSING OF REFUSE INTO
ABANDONED GRAVEL PITS LOCATED IN A REGION OF HIGH WATER TABLE.
FIELD 05B
ACCESSION NO. W69-03178
22
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TRACE AND TRACER ELEMENTS IN GROUND WATER,
ARIZONA UNIV., TUCSON. DEPT. OF HYDROLOGY.
GORDON R. DUTT.
ARIZONA WATER RESOURCES RESEARCH CENTER, RESEARCH PROJECT TECHNICAL
COMPLETION REPORT, AUGUST 1968. 11 P, 1 TAB, 2 REF. OWRR PROJECT
B-001-ARIZ, B-002-ARIZ, AND B-004-ARIZ.
DESCRIPTORS:
*GROUND WATER, *TRACE ELEMENTS, CHELATE EXTRACTION, ATOMIC ABSORPTION
ANALYSES, CARBONATE, BICARBONATE, FLUORIDE, NITRATE, SULFATE, SILICATE,
GROUND WATER RECHARGE, HYDROCHEMICAL FACIES, SEWAGE EFFLUENT, C.O.D.,
B.O.D., WASTE WATERS, HYDRAULIC LOADING, INFILTRATION, TUCSON BASIN,
PROCESS-RESPONSE MODEL, INSTRUMENTATION, HYDROCHEMICAL DATA.
ABSTRACT:
OVER 680 WELLS ARE SAMPLED AND ANALYZED FOR CONDUCTIVITY, PH, CA(-n-),
MG(-n-), NA(+), CL(-), S04(=), C03(-), F(-), N03(-), K(+), SR{++), AND
THE TRACE ELEMENTS, FE, MN, CU, ZN, CR(+6), NI, PB, CO, AND CD. A NEW
METHOD WAS DEVELOPED FOR THE SIMULTANEOUS CHELATE EXTRACTION AND ATOMIC
ABSORPTION ANALYSIS OF THE LAST NINE ELEMENTS IN WATER AND SEWAGE
SAMPLES. THE SURFACE AND SUBSURFACE MOVEMENT OF THE NINE TRACE ELEMENTS
WERE STUDIED ON GRASSED PLOTS WITH EFFLUENT FROM A DOMESTIC SEWAGE
EFFLUENT TREATMENT FACILITY. ANALYSIS OF RECHARGED WATER WAS THE SAME
AS ABOVE PLUS C.O.D. AND B.O.D. DETERMINATIONS. A CONCEPTUAL
PROCESS-RESPONSE MODEL OF THE TUCSON BASIN WAS DEVELOPED TO RELATE
GROUND WATER CHEMICAL COMPOSITION TO THE SOIL, SUBSOIL AND GEOLOGIC
FORMATIONS OF THE RECHARGE AND GROUND WATER FLOW PATTERN OF THE BASIN.
A CALCITE-WATER CHEMICAL EQUILIBRIUM MODEL WAS USED TO DETERMINE THE
PRECIPITATION OR DISSOLUTION OF CALCITE IN THE BASIN AQUIFERS.
FIELD 02F, 05A
ACCESSION NO. W69-03197
23
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CONVECTIVE SALT DIFFUSION IN A RADIAL SUBSURFACE STREAM IN RELATION TO THE
PROTECTION OF SUBSURFACE WATERS FROM CONTAMINATED DISCHARGES,
F. M. BOCHEVERt AND A. YE. ORADOVSKAYA.
TRANSL FROM DOKLADY VODGEO, NO. 13, PP 159-180, 1966. SOVIET HYOROL: SELEC
PAP, ISSUE NO 4, PP 416-431, 1967. 16 P, 5 FIG, 1 TAB, 17 REF.
DESCRIPTORS:
^DIFFUSION, *POROUS MEDIA, *GROUNDWATER MOVEMENT, #PATH OF POLLUTANTS,
INJECTION WELLS, WASTE DISPOSAL, SUBSURFACE WATERS.
IDENTIFIERS:
USSR, RADIAL DIFFUSION EQUATIONS.
ABSTRACT:
METHODS ARE GIVEN FOR CALCULATION OF RADIAL SOLUTE DIFFUSION ALLOWING
FOR SORPTION IN POROUS MEDIA. EXAMPLES OF SUCH DIFFUSION ARE FOUND NEAR
SUBSURFACE WASTE INJECTION WELLS. SOLUTIONS ARE DEVELOPED FOR VARYING
AND UNVARYING CONCENTRATIONS OF INJECTED FLUIDS.
-------
NUMERICAL SOLUTIONS FOR DISPERSION IN POROUS MEDIUMS,
MASSACHUSETTS INST. OF TECH., CAMBRIDGE. HYDRODYNAMICS LAB.
URI Y. SHAMIR, AND DONALD R. F. HARLEMAN.
WATER RESOURCES RES, VOL 3, NO 2, PP 557-581, 1967. 25 P, 14 FIG, 2 TAB, 19
REF.
DESCRIPTORS:
*DISPERSION, ^DIFFUSION, '-POROUS MEDIA, #GROUNDWATER MOVEMENT, *WATER
POLLUTION, PATH OF POLLUTANTS, DIGITAL COMPUTERS, COMPUTER PROGRAMS.
IDENTIFIERS:
NUMERICAL METHODS.
ABSTRACT:
A NUMERICAL METHOD IS PRESENTED FOR THE SOLUTION OF PROBLEMS OF
DISPERSION IN STEADY 3-DIMENSIONAL POTENTIAL FLOW FIELDS IN POROUS
MEDIUMS, IN WHICH THE MISCIBLE FLUIDS HAVE THE SAME DENSITY AND
VISCOSITY. THE METHOD IS DEVELOPED AND TESTED FOR 2-DIMENSIONAL
PROBLEMS, AND THE EXTENSION TO 3 DIMENSIONS IS PRESENTED. EMPHASIS IS
PUT ON THE EFFICIENCY OF THE NUMERICAL SCHEME AND ON ITS GENERALITY. IT
IS SHOWN TO BE INDEPENDENT OF THE GEOMETRY OF THE FLOW FIELD. THE
COMPUTER PROGRAM FOR CARRYING OUT THE COMPUTATIONS AS DESCRIBED IS
TESTED WITH SIMPLE PROBLEMS, FOR WHICH EXACT OR APPROXIMATE ANALYTICAL
SOLUTIONS EXIST. IT IS ALSO USED TO OBTAIN SOLUTIONS TO A FEW PROBLEMS
FOR WHICH NO OTHER SOLUTION IS KNOWN. (KNAPP-USGS)
FIELD 05B, 02F
ACCESSION NO. W69-03237
25
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PUTTING WASTE WATER TO BENEFICIAL USE - THE FLUSHING MEADOWS PROJECT,
AGRICULTURAL RESEARCH SERVICEt PHOENIX, ARIZ. WATER CONSERVATION LAB.
HERMAN BOUWER.
PROC 12TH ANNUAL ARIZONA WATERSHED SYMPOSIUM, PHOENIX, ARIZONA, 18 SEPTEMBER
1968, PP 25-30. 6 P, 3 FIG, 1 TAB, 6 REF.
DESCRIPTORS:
SEWAGE EFFLUENT, *WASTE WATER DISPOSAL, WASTE WATER TREATMENT, WATER
POLLUTION, *SOIL WASTE TREATMENT, SOIL PERCOLATION, *WASTE WATER
RECLAMATION, INDUCED INFILTRATION, *GROUND WATER RECHARGE, IRRIGATION,
DENITRIFICATION, ECONOMICS.
IDENTIFIERS:
SURFACE SPREADING, RECHARGE BASINS, EXPERIMENTAL RECHARGE PROJECT,
FLUSHING MEADOWS PROJECT, PHOENIX(ARIZONA).
ABSTRACT:
IN CENTRAL ARIZONA, DECREASING WATER SUPPLIES AND INCREASING POPULATION
MAKE REUSE OF MUNICIPAL WASTE WATER MANDATORY. AN EXPERIMENTAL PROJECT
WEST OF PHOENIX HAS SHOWN THAT THE HYDROGEOLOGY OF THE SALT RIVER BED
IS UNIQUELY SUITED FOR RECLAIMING WATER FROM SEWAGE EFFLUENT BY SURFACE
SPREADING FOR GROUND WATER RECHARGE. THE PROJECT CONTAINS SIX RECHARGE
BASINS 20 X 700 FT EACH. FOUR BASINS ARE IN BERMUDAGRASS, ONE BASIN IS
COVERED WITH A GRAVEL LAYER, AND ANOTHER IS IN BARE SOIL. THE GRASS
BASINS HAD THE HIGHEST INFILTRATION RATES, THE GRAVEL BASIN THE LOWEST.
INCLUDING DRYUP PERIODS, AN ANNUAL RECHARGE RATE OF ABOUT 300 FT SHOULD
BE ATTAINABLE. WITH SHORT INUNDATION PERIODS (2 DAYS) ALL NITROGEN IN
THE SEWAGE EFFLUENT WAS CONVERTED TO NITRATE IN THE RECLAIMED WATER.
WITH LONG INUNDATION PERIODS (10 DAYS) 90? REMOVAL OF THE NITROGEN WAS
OBTAINED, PROBABLY BECAUSE OF DENITRIFICATION. THE USUAL REDUCTIONS IN
BOO, COLIFORMS, AND PHOSPHORUS WERE OBSERVED. HORIZONTAL AND VERTICAL
HYDRAULIC CONDUCTIVITY OF THE AQUIFER WERE EVALUATED BY ELECTRIC
ANALOG, USING WATER LEVEL DATA FROM TWO OBSERVATION WELLS. PLANS FOR A
LARGE-SCALE RECHARGE PROJECT CONSISTING OF STRIPS OF RECHARGE BASINS ON
EACH SIDE OF THE RIVER BED AND WELLS IN THE CENTER OF THE RIVER BED
WERE DEVELOPED.
FIELD 050, 03F, 04B
ACCESSION NO. W69-05327
26
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RETURNING WASTES TO THE LAND, A NEW ROLE FOR AGRICULTURE,
AGRICULTURAL RESEARCH SERVICE, PHOENIX, ARIZ. WATER CONSERVATION LAB.
HERMAN BOUWER.
JOUR SOIL AND WATER CONSERVATION, VOL 23, NO 5, PP 164-169, 1968. 5 P, 2 FIG,
1 TAB, 22 REF.
DESCRIPTORS:
SEWAGE EFFLUENT, *WASTE WATER DISPOSAL, WASTE WATER TREATMENT, WATER
POLLUTION, #SOIL WASTE TREATMENT, SOIL PERCOLATION, *WASTE WATER
RECLAMATION, INDUCED INFILTRATION, AGROUND WATER RECHARGE, IRRIGATION,
DENITRIFICATION, ECONOMICS.
IDENTIFIERS:
SURFACE SPREADING, RECHARGE BASINS, EXPERIMENTAL RECHARGE PROJECT*
FLUSHING MEADOWS PROJECT, PHOENIX(ARIZONA).
ABSTRACT:
LAND DISPOSAL OF TREATED SEWAGE OR OTHER LIQUID WASTE REDUCES POLLUTION
LOADS ON STREAMS AND LAKES. AFTER INFILTRATION AND PERCOLATION THROUGH
THE SOIL, BIODEGRADABLE MATERIAL, MICROORGANISMS, PHOSPHORUS, NITROGEN,
HEAVY METALS, FLUORIDES, AND OTHER SUBSTANCES ARE EFFECTIVELY REMOVED.
THUSt THE WASTE WATER THAT HAS PERCOLATED TO THE WATER TABLE AND THEN
MOVED AS GROUND WATER FOR SOME DISTANCE CAN BE COLLECTED AS RECLAIMED
WATER SUITABLE FOR REUSE. UNDER FAVORABLE HYDROGEOLOGIC CONDITIONS, THE
COST OF WASTE WATER RENOVATION BY SURFACE SPREADING FOR GROUND WATER
RECHARGE IS A FRACTION OF THAT OF COMPARABLE TERTIARY IN-PLANT
TREATMENT. SEVERAL TYPES OF LAND DISPOSAL OF GROUND WATER RECHARGE
SYSTEMS ARE DISCUSSED AND DESIGN AND OPERATING CRITERIA ARE PRESENTED.
FOR THE EXPERIMENTAL RECHARGE PROJECT NEAR PHOENIX, ARIZONA, SEQUENCES
OF LONG INUNDATION PERIODS (10 DAYS) YIELDED MUCH LOWER NITRATE LEVELS
IN THE RECLAIMED WATER THAN SEQUENCES OF SHORT INUNDATION PERIODS (2
DAYS). THIS IS ATTRIBUTED TO DENITRIFICATION. IN VIEW OF THE INCREASING
AMOUNTS OF WASTE WATER AND THE URGENT NEED FOR POLLUTION CONTROL OF
SURFACE WATERS, AGRICULTURE'S ROLE IN THE FUTURE WILL NOT ONLY BE TO
PROVIDE FOOD AND FIBER, BUT ALSO TO SERVE AS A MEDIUM FOR RECEIVING AND
RENOVATING TREATED SEWAGE AND OTHER WASTES.
FIELD 05D, 03F, 04B
ACCESSION NO. W69-05328
27
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DUMPING OF OIL.
ME REV STAT ANN TIT 17, SEC 2794 (1965).
DESCRIPTORS:
*MAINE, *WATER POLLUTION, #OIL WASTES, #01L, LEGISLATION, STATE
GOVERNMENTS, POLLUTION ABATEMENT, CHEMICAL WASTES, WATER POLLUTION
SOURCES, INDUSTRIAL WASTES, RIVERS, STREAMS, LAKES, PONDS, TIDAL
WATERS, WELLS, GROUNDWATER, SURFACE WATERS, SEEPAGE, PERCOLATION.
ABSTRACT:
THE INTENTIONAL PLACEMENT OR DIRECT DEPOSIT OF OIL, PETROLEUM BASE
PRODUCTS OR MATERIALS CONTAINING SIGNIFICANT QUANTITIES OF SUCH OIL
INTO OR ON THE BANKS OF ANY RIVER, STREAM, PERMANENT OR TEMPORARY LAKE,
POND, OR TIDAL WATERS OR ON THE ICE THEREOF WHERE SUCH MATERIALS MAY
FIND ITS WAY INTO SAID WATERCOURSE OF TIDAL WATERS IS PROHIBITED. ALSO
PROHIBITED IS THE DEPOSIT OF SUCH MATERIALS INTO PITS, WELLS OR ON
GROUND SURFACES IN SUCH A MANNER THAT OIL WILL PERCOLATE, SEEP, OR
OTHERWISE FIND ACCESS INTO GROUNDWATERS OR INTO WELLS USED FOR THE
PRODUCTION OF WATER. (LOGAN-FLA)
FIELD 05G, 06E
ACCESSION NO. W69-05370
28
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PHILLIPS V SUN OIL CO (GASOLINE POLLUTION OF WATER WELL).
307 NY 328, 121 NE 20 249-251 (1954).
DESCRIPTORS:
*NEW YORK, *WATER WELLS, *GASOLINE, *WATER POLLUTION SOURCES, JUDICIAL
DECISIONS, FUELS, WELLS, WATER POLLUTION, SEEPAGE, GROUNDWATER,
PERCOLATING WATER, WELL REGULATIONS, PERCOLATION, SUBSURFACE DRAINAGE,
SHALLOW WELLS, SUBSURFACE WATERS, LEGAL ASPECTS.
IDENTIFIERS:
TRESPASS, INJUNCTIONS(PROHIBITORY), NUISANCE.
ABSTRACT:
PLAINTIFF OWNED LAND ADJACENT TO DEFENDANT'S UNDERGROUND GASOLINE
STORAGE TANKS. GASOLINE TRAVELED UNDERGROUND TO PLAINTIFF'S LAND AND
SEEPED INTO HIS WATER WELL, CONTAMINATING HIS WATER SUPPLY. PLAINTIFF
BROUGHT THIS ACTION IN TRESPASS TO RECOVER DAMAGES. THE COURT HELD THAT
TRESPASS IS AN INTENTIONAL HARM. THE TRESPASSER NEED NOT INTEND OR
EXPECT THE CONSEQUENCE OF HIS ACTION IN ORDER TO BE HELD LIABLE
THEREFOR, BUT HE MUST INTEND THE ACT WHICH PRODUCES THE UNLAWFUL
INTRUSION. EVEN THOUGH THE POLLUTANT HAD DELIBERATELY BEEN PUT INTO THE
LAND, DEFENDANT IS NOT LIABLE FOR A NEIGHBOR'S DAMAGE THEREFROM UNLESS
HE HAD GOOD REASON TO KNOW THAT THERE WOULD BE SEEPAGE TO THE
NEIGHBOR'S LAND. SINCE DEFENDANT DID NOT KNOW OF THE LEAKING GASOLINE,
HE WAS NOT LIABLE FOR DAMAGES RESULTING THEREFROM. INJUNCTIVE RELIEF
MAY HAVE BEEN AVAILABLE TO PREVENT FUTURE HARM TO THE WATER SUPPLY.
(HELWIG-FLA)
FIELD 05G, 06E
ACCESSION NO. W69-06117
29
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PHOENIX V GRAHAM (SALT WATER POLLUTION OF WELLS).
349 ILL APP 326, 110 NE 20 669-673 (1953).
DESCRIPTORS:
*ILLINOIS, *SALINE WATER, *WELLS, JUDICIAL DECISIONS, OIL WASTES, WATER
QUALITY, SALINITY, PERCOLATING WATER, WELL SPACING, SHALLOW WELLS,
GROUNDWATER, WATER SOURCES, DRAINAGE, RIPARIAN RIGHTS, ARTESIAN WELLS,
DITCHES, DRAINAGE EFFECTS, SEEPAGE, WASTE STORAGE, LEGAL ASPECTS.
ABSTRACT:
PLAINTIFF WAS LESSOR OF CERTAIN OIL PRODUCING LAND UPON WHICH DEFENDANT
LESSEE HAD WELLS. SALT WATER PUMPED FROM THE WELLS AND NEGLIGENTLY
DISCHARGED BY DEFENDANT POLLUTED PLAINTIFF'S WATER WELLS. DEFENDANT AND
HIS PREDECESSOR HAD DUG PITS TO STORE THE SALT WATER, AND THE WELLS
BECAME UNUSABLE SOON AFTER ENLARGING ONE OF THE STORAGE PITS. WHILE
THERE IS A CONFLICT AMONG THE JURISDICTIONS REGARDING LIABILITY FROM
SALT WATER DAMAGE, THE COURT HELD THAT ADJOINING LANDOWNERS AND OTHER
DOWNSTREAM OWNERS HAVE A RIGHT TO RECEIVE WATER IN ITS NATURAL STATE.
HOWEVER, LESSORS HAVE NO ACTION FOR SALT DAMAGE TO THEIR OWN LAND FROM
SOURCES ON THE LAND UNLESS SUCH DAMAGE IS CAUSED BY LESSEE'S
NEGLIGENCE. THE LESSEE WELL OPERATOR IS REQUIRED TO USE THE CARE OF AN
ORDINARY PRUDENT OPERATOR; HE HAS THE RIGHT TO USE THAT PART OF THE
LEASED LAND FOR SALT WATER DISPOSAL AS IS REASONABLY NECESSARY. THERE
WAS SUFFICIENT EVIDENCE IN THIS CASE TO SHOW NEGLIGENCE ON THE PART OF
THE LESSEE, HOWEVER, THE COURT REMANDED ON THE ISSUE OF DAMAGES.
PLAINTIFF FAILED TO DEMONSTRATE PERMANENT DAMAGE TO HIS WATER SUPPLY OR
TO SHOW LACK OF ANOTHER WATER SOURCE. (HELWIG-FLA)
FIELD 05G, 06E
ACCESSION NO. W69-06118
30
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SPRAY IRRIGATION OF ORGANIC CHEMICAL WASTES,
COMMERCIAL SOLVENTS CORR., TERRE HAUTE, IND.
RICHARD A. WOODLEY.
PROC OF 23RD IND WASTE CONF, MAY 7-9, 1968, PURDUE UNIV, PART 1, PP 251-261,
1969. 11 P, 1 FIG, 3 TAB.
DESCRIPTORS:
*WASTE WATER DISPOSAL, IRRIGATION, *CHEMICAL WASTES, SPRINKLER
IRRIGATION, INFILTRATION, GROUNDWATER, WATER LEVELS, WATER QUALITY,
BIOCHEMICAL OXYGEN DEMAND, SUSPENDED LOAD.
IDENTIFIERS:
ORGANIC CHEMICAL WASTES.
ABSTRACT:
AT THE TERRE HAUTE, INDIANA PLANT OF COMMERCIAL SOLVENTS CORPORATION, A
SPRAY IRRIGATION SYSTEM HAS BEEN SUCCESSFULLY UTILIZED SINCE AUGUST
1965 FOR TREATMENT OF HIGH STRENGTH, LOW VOLUME WASTE FROM AEROBIC
INDUSTRIAL FERMENTATION PROCESSES. WASTES VARYING IN BOD UP TO 64,700
MG/1, SUSPENDED SOLIDS UP TO 99,700 MG/1, AND FLOWS UP TO 160,000 GPD
HAVE BEEN ROUTINELY SPRAYED ON 100 ONE-ACRE PLOTS WITHOUT CAUSING ANY
ENVIRONMENTAL NUISANCES OR ANY COMMUNITY PROBLEMS WHATSOEVER. THE LAND
APPLICATION SYSTEM HAS BEEN MANAGED SO THAT TOTAL TREATMENT OF ALL
APPLIED WASTES HAS BEEN ACHIEVED. LAND AND SYSTEM MANAGEMENT HAS
CONSISTED OF SPRAY PLOT SELECTION, APPLICATION TIME CONTROL,
ELIMINATION OF SURFACE RUNOFF, AND CONTROL OF SURFACE PONDING.
CONTINUOUS WINTERTIME OPERATION HAS BEEN ACHIEVED BY PRE-PLANNING FOR
MINUS ZERO C OPERATIONS AND THE INSTALLATION OF RAPID DRAINING SPRAY
HEADERS AND LATERALS. EQUIPMENT SUBJECT TO 24 HR CONTAMINANT OF LIQUID
IS PROTECTED BY VARIOUS TYPES OF ELECTRICAL HEATERS.
FIELD 050, 03C, 05G
ACCESSION NO. W69-07114
31
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HYOROGEOLOGIC CONSIDERATIONS IN LIQUID WASTE DISPOSAL,
WISCONSIN UNIV., MADISON. DEPT. OF GEOLOGY.
S. M. BORN, AND D. A. STEPHENSON.
J SOIL AND WATER CONSERV, VOL 24, NO 2, PP 52-55, MAR-APR 1969. 4 P, 2 FIG, 7
REF.
DESCRIPTORS:
*WASTE WATER DISPOSAL, *IRRIGATION, ^SPRINKLER IRRIGATION,
HYDROGEOLOGY, SOILS, POROSITY, PERMEABILITY, GROUNDWATER MOVEMENT,
WATER MOVEMENT, INFILTRATION, PERCOLATION, ADSORPTION, FILTRATION.
SOIL
IDENTIFIERS:
SPRAY DISPOSAL.
ABSTRACT:
THE GEOHYDROLOGY OF LIQUID WASTE DISPOSAL BY IRRIGATION IS REVIEWED.
KNOWLEDGE OF GEOLOGIC CONDITIONS IS NECESSARY FOR SPRAY IRRIGATION
DISPOSAL OF WASTES. THE THICKNESS, NATURE, AND DISTRIBUTION OF
UNCONSOLIDATED SURFACE DEPOSITS DETERMINE INFILTRATION, ADSORPTION
STORAGE, AND DOWNWARD MOVEMENT OF WASTE WATER. INF ILTROMETER TESTS MAY
BE USED IN SITU, OR LABORATORY EXAMINATION OF SAMPLES CAN YIELD QUICKER
LESS ACCURATE INFORMATION. THE CONDITION OF BEDROCK DETERMINES RATE OF
WATER MOVEMENT AND EFFECTIVENESS OF FILTRATION. FLOW SYSTEMS MUST BE
STUDIED TO LEARN WHERE WASTES WILL TRAVEL. (KNAPP-USGS)
FIELD 05E, 03F
ACCESSION NO. W69-07375
32
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WASTE WATER RECHARGE AND DISPERSION IN POROUS MEDIA,
MASSACHUSETTS INST. OF TECH., CAMBRIDGE. DEPT. OF CIVIL ENGINEERING,
JOHN AUSTIN HOOPES, AND DONALD R. F. HARLEMAN.
MASS INST TECH HYDRODYNAMICS LAB REP NO 75, JUNE 1965. 166 P, 40 FIG, 3 TAB,
120 REF. PHS GRANT NO WP-347.
DESCRIPTORS:
*PATH OF POLLUTANTS, *GROUNDWATER MOVEMENT, *OIFFUSION, *DISPERSION,
*MATHEMATICAL MODELS, MODEL STUDIES, HYDRAULIC MODELS, TRACERS,
INJECTION WELLS, ARTIFICIAL RECHARGE, CONVECTION, MIXING, FLOW, POROUS
MEDIA.
IDENTIFIERS:
DISPOSAL WELLS.
ABSTRACT:
THE EFFECTS OF DISPERSION AND DIFFUSION OF WASTEWATER SOLUTES IN
AQUIFERS NEAR THE INJECTION WELLS ARE INCORPORATED IN A MASS
CONSERVATION EQUATION. SOLUTIONS ARE DERIVED TO PREDICT THE TRACER
DISTRIBUTIONS RESULTING FROM VARIOUS RECHARGE AND DISPOSAL OPERATIONS.
FOR UNIFORM FLOW, THE LONGITUDINAL AND LATERAL DISPERSION COEFFICIENTS
ARE RELATED TO THE SEEPAGE VELOCITY, PARTICLE SIZE, AND MEDIA
STRUCTURE. THESE COEFFICIENTS ARE DETERMINED FROM EXPERIMENTAL
MEASUREMENTS OF THE DISTRIBUTION OF A DILUTE SALT TRACER IN FLOW
THROUGH A SAND COLUMN. CONVECTION AND DISPERSION DETERMINE THE TRACER
DISTRIBUTION NEAR THE WELL. AT LARGER DISTANCES FROM THE WELL,
MOLECULAR DIFFUSION AND CONVECTION ALONE ARE IMPORTANT. WITH A PAIR OF
WELLS, ONE RECHARGING TRACER FLUID AND THE OTHER PUMPING THE MIXTURE OF
TRACER AND NATIVE GROUNDWATER, THE SOLUTION FOR THE TRACER DISTRIBUTION
INDICATES THAT LATERAL DISPERSION HAS A NEGLIGIBLE INFLUENCE ON THE
TRACER DISTRIBUTION, EXCEPT VERY NEAR THE LINE JOINING THE TWO WELLS.
MOLECULAR DIFFUSION IS ALSO SHOWN TO BE INSIGNIFICANT, EXCEPT FOR SMALL
FLOW RATES AND LARGE WELL-SPACINGS. LONGITUDINAL DISPERSION DETERMINES
THE SHAPE OF THE TRACER DISTRIBUTION WITHIN THE MEDIA, WHEREAS
CONVECTION DOMINATES THE TRACER DISTRIBUTION AT THE PUMPING WELL,
EXCEPT FOR SHORT TIMES. (KNAPP-USGS)
FIELD 05B
ACCESSION NO. W69-07554
33
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TRANSFORMATIONS IN INFILTRATION PONDS AND IN THE SOIL LAYERS IMMEDIATELY
UNDERNEATH,
RESEARCH INSTITUTE FOR PUBLIC HEALTH ENGINEERING TNO, THE HAGUE
(NETHERLANDS). WATER, SOIL, AND AIR DIV.
J. K. BAARS.
PROC RUDOLFS ..
APPLICATIONS
(EDS)
9 REF
DOLFS RES CONF, RUTGERS UNIV, NEW BRUNSWICK, NJ. PRINCIPLES AND
CATIONS IN AQUATIC MICROBIOLOGY, HEUKELEKIAN, H AND DONDERO, NORMAN C
, JOHN WILEY AND SONS, INC, MEW YORK, PP 344-365, 1964. 8 FIG, 2 TAB,
, DISC.
DESCRIPTORS:
INFILTRATION, *PONDS, *SOIL, GROUNDWATER BASINS, WATER SUPPLY, MUD,
BENTHOS, HYDROGEN, BACTERIA, AEROBIC BACTERIA, METABOLISM, CANALS,
SANDS, CHLORINATIOM, MICROORGANISMS, CHEMICAL ANALYSIS, TEMPERATURE,
NITRATES, PLANTS, AMMONIA, HARDNESS(WATER), ACIDITY, OXYGEN, ALGAE,
SELF-PURIFICATION, BACTERIOPHAGE, RESERVOIRS, SPORES, NITRITES, IRON,
ORGANIC MATTER, SUBSOIL, VELOCITY, OXIDATION, DENITRIF ICATION,
SULFATES, REDUCTIONICHEMICAL), FERMENTATION, METHANE, HYDROGENATION,
CHEMICAL OXYGEN DEMAND, BIOCHEMICAL OXYGEN DEMAND, POTASSIUM COMPOUNDS,
CARBON DIOXIDE, PROTOZOA, SEWAGE, SLUDGE, E COLI.
IDENTIFIERS:
^TRANSFORMATIONS, AMSTERDAM, HAARLEM, LEYDEN, THE HAGUE,
MINERALIZATION, CLAY LENSES, RHINE RIVER, AMSTERDAM RHINE, POLDERS,
COMPOSITION, PSEUDOMONAS, MYCOBACTERIUM, BACILLUS SUBTILIS, BACILLUS
MYCOIDES, BACILLUS MESENTERICUS, DIATOMEA, CLADOPHORA, FLAGELLATA,
CILIATES, RANUNCULUS CIRCINATUS, POTAMOGETON PUSILLUS.
ABSTRACT:
WATER FROM STORAGE PONDS, FILTERED THROUGH BOTTOM MUD AND A BODY OF
SAND, WAS MEASURED FOR CHLORIDE, FORMS OF NITROGEN, OXYGEN, ORGANIC
MATTER, ALGAE, AND BACTERIAL CONTENT. TO STUDY BENTHOS, WATER WAS
ANALYZED FROM WELLS CONSTRUCTED AT DISTANCES FROM A POND IN THE
DIRECTION OF FLOW. NOT ONLY DISSOLVED ORGANIC MATTER, AS DETERMINED BY
THE POTASSIUM PERMANGANATE METHOD, IS MINERALIZED, BUT MUCH MORE
OXIDANT (FREE OXYGEN PLUS NITRATE OXYGEN) IS USED, APPARENTLY IN THE
BENTHOS. THE HIGH OXIDANT CONSUMPTION INDICATES THAT THE REDUCTION OF
ORGANIC MATTER IS INTENSE. ORGANIC SUBSTANCES, DETECTABLE BY TASTE, ARE
NOT COMPLETELY ELIMINATED. WHEN THERE IS A CONSTANT SUPPLY OF NEW
OXIDANT, DEAD BIOLOGICAL MATERIALS MAY BE MINERALIZED AEROBICALLY. IF
THIS SUPPLY IS TERMINATED, ANAEROBIC TRANSFORMATIONS MAY DOMINATE.
PROBABLY BACTERIA ARE STRONGLY ADSORBED TO THE SAND GRAINS IN
CONCENTRATIONS RESULTING IN INTENSE STRUGGLE FOR LIFE AND DECREASE
RAPIDLY WITH INCREASING DISTANCE FROM THE POND. SAMPLES FROM THE BOTTOM
OF THE PONDS DOWNWARD SHOWED PRONOUNCED DECREASE IN BACTERIA AT
0.5-METER DEPTH. A SMALL AMOUNT OF SILT IN THE WATER MAY CAUSE CLOGGING
OF THE SOIL. THE INTERMITTENT INFLILTRATION SYSTEM AFFORDS THESAME
PERMEABILITY OF THE SAND EACH YEAR WITH THE CONSEQUENT USE OF AVAILABLE
PURIFYING ACTORS. (JONES-WIS)
FIELD 05D
ACCESSION NO. W69-07838
34
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GROUNDWATER RECHARGE WITH TREATED MUNICIPAL EFFLUENT,
TEXAS TECHNOLOGICAL COLL. LUBBOCK. WATER RESOURCES CENTER; AND TEXAS
TECHNOLOGICAL COLL., LUBBOCK. DEPT. OF ENGINEERING.
DAN M. WELLS.
SYMP ON MUNIC SEWAGE EFFLUENT FOR IRRIG, JULY 30, 1968, LOUISIANA POLYTECH
INST, RUSTON, P 61-73, 1968. 13 P, 1 TAB, 46 REF. OWRR PROJ NO A-009-LA.
DESCRIPTORS:
*WATER REUSE, *RECLAIMED WATER, ^MUNICIPAL WASTES, *ARTIFICIAL
RECHARGE, LEGAL ASPECTS, AESTHETICS, AQUIFERS, SOIL WATER MOVEMENT,
GROUNDWATER MOVEMENT, INFILTRATION, WATER CHEMISTRY, WATER QUALITY,
SOIL CONTAMINATION.
IDENTIFIERS:
WASTE WATER RECHARGE.
ABSTRACT:
MUNICIPAL EFFLUENT HAS ALWAYS BEEN USED FOR GROUNDWATER RECHARGE.
PRACTICALLY ALL OF THE RECHARGE IN THE PAST HAS BEEN UNINTENTIONAL,
RESULTING FROM THE NATURAL OPERATION OF THE HYDROLOGIC CYCLE, AND IT
DOES NOT APPEAR THAT THIS PATTERN WILL BE APPRECIABLY CHANGED IN THE
FUTURE. IT DOES APPEAR, HOWEVER, THAT THE DELIBERATE USE OF TREATED
EFFLUENT FOR GROUNDWATER RECHARGE WILL INCREASE IN THE FUTURE,
PARTICULARLY IN ARID AND SEMI-ARID AREAS OF THE COUNTRY THAT ARE
RAPIDLY DEPLETING THEIR GROUNDWATER RESOURCES. ALTHOUGH THE
TECHNOLOGICAL CAPABILITY FOR TREATING MUNICIPAL EFFLUENT FOR ANY TYPE
OF REUSE INCLUDING THE RECHARGE OF POTABLE QROUNDWATER SUPPLIES HAS
EXISTED FOR MANY YEARS, MANY PSYCHOLOGICAL PROBLEMS REMAIN TO BE SOLVED
TO WIN PUBLIC ACCEPTANCE FOR ITS WIDESPREAD USE. PHYSICAL PROBLEMS
INCLUDE CLOGGING OF SOILS OF AQUIFERS, CHEMICAL PRECIPITATION, AND
ALGAL OR BACTERIAL GROWTH. THE LEGAL PROBLEMS INCLUDE LIABILITY FOR
DAMAGES TO AQUIFERS, OWNERSHIP OF RECHARGED WATER, AND OWNERSHIP OF
EFFLUENT WATER. (KNAPP-USGS)
FIELD 050, 05F
ACCESSION NO. W69-08620
35
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THE MOVEMENT OF DISEASE PRODUCING ORGANISMS THROUGH SOILS,
CALIFORNIA UNIV., DAVIS, DEPT. OF CIVIL ENGINEERING.
R. B. KRONE.
SYMP ON MUNIC SEWAGE EFFLUENT FOR IRRIG, JULY 30, 1968, LOUISIANA POLYTECH
INST, RUSTON, P 75-104, 1968. 30 P, 2 FIG, 55 REF.
DESCRIPTORS:
#WATER REUSE, *PATHOGENIC BACTERIA, #VIRUSES, #GROUNDWATER MOVEMENT,
MUNICIPAL WASTES, IRRIGATION WATER, ARTIFICIAL RECHARGE, FILTRATION,
SORPTION, INFILTRATION, PERCOLATION, SOIL DISPOSAL FIELDS, SOIL
CONTAMINATION, SOIL PHYSICAL PROPERTIES.
IDENTIFIERS:
MUNICIPAL WASTE RECHARGE.
ABSTRACT:
THE MOVEMENT OF PATHOGENIC ORGANISMS THROUGH SOILS RECHARGED WITH
CONTAMINATED WATER IS DISCUSSED. PATHOGENS HAVE A WIDE VARIETY OF
PHYSICAL AND BIOLOGICAL CHARACTERISTICS, INCLUDING WIDE RANGES OF SIZE,
SHAPE, SURFACE PROPERTIES, AND DIE-AWAY RATES. THE PROCESSES OF
FILTRATION BY SOIL INCLUDE STRAINING AT THE SOIL SURFACE, STRAINING AT
INTERGRAIN CONTACTS, SEDIMENTATION, AND SORPTION BY SOIL PARTICLES.
STRAINING OF PATHOGENS AT THE SOIL SURFACE AND SORPTION OF VIRUSES NEAR
THE SOIL SURFACE IS DESIRABLE BECAUSE IT LIMITS TRAVEL OF PATHOGENS
MOST, AND IT IS SUBJECT TO WIDE VARIATIONS IN TEMPERATURE AND MOISTURE,
AND IT WILL ASSURE AEROBIC CONDITIONS. A SOIL CONTAINING CLAY SHOULD
THEREFORE BE USED FOR IRRIGATION WITH TREATED SEWAGE. WIDE EXPERIENCE
IN IRRIGATION WITH TREATED SEWAGE INDICATES THAT IT IS SAFE PROVIDED
THAT AT LEAST PRIMARY TREATMENT IS USED, AND PROVIDED THAT THE CROPS
ARE NOT CONSUMED DIRECTLY BY HUMANS. SECONDARY TREATMENT AND
CHLORINATION IS RECOMMENDED FOR AESTHETIC REASONS. (KNAPP-USGS)
FIELD 050, 03F
ACCESSION NO. W69-08621
36
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THE EFFECTS OF TEMPERATURE AND DENSITY GRADIENTS UPON THE MOVEMENT OF
CONTAMINANTS IN SATURATED AQUIFERS,
ALABAMA UNIV., UNIVERSITY. DEPT. OF ENGINEERING MECHANICS.
HAROLD R. HENRY.
SYMP ON GEOCHEM, PRECIPITATION, EVAPORATION, SOIL-MOISTURE, HYDROM, PROC GEN
ASSEMBLY OF BERN (SEPT-OCT 1967), INT ASS SCI HYDROL, PUB NO 78, P 54-65,
1968. 12 P, 4 FIG, 26 REF.
DESCRIPTORS:
*SATURATED FLOW, ^DIFFUSION, ^DISPERSION, *CONVECTION, *GROUNDWATER
MOVEMENT, SOLUTES, WASTES, PATH OF POLLUTANTS, MATHEMATICAL MODELS,
CURRENTS(WATER), MASS TRANSFER, AQUIFERS.
IDENTIFIERS:
THERMAL GRADIENTS.
ABSTRACT:
THE EFFECTS OF GRADIENTS IN TEMPERATURE AND DENSITY ON THE MOVEMENT OF
CONTAMINANTS IN GROUNDWATER WERE STUDIED BY IMPOSING A HORIZONTAL
LATERAL TEMPERATURE GRADIENT ON A TUBE OF SQUARE CROSS SECTION
CONTAINING WATER-SATURATED SAND. A CONVECTION CURRENT INCREASED IN
STRENGTH AS THE TEMPERATURE GRADIENT INCREASED. THE EFFECTIVE VALUE OF
THERMAL DIFFUSIVITY WAS ABOUT 50 TIMES LARGER THAN THE EXPECTED VALUE
BECAUSE OF DISPERSION CAUSED BY THE MOVEMENT OF WATER THROUGH
TORTUOUSLY INTERCONNECTED INTERSTICES OF THE SAND. (KNAPP-USGS)
FIELD 02F, 05B
ACCESSION NO. W69-08921
37
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EFFECT OF VARIOUS FACTORS ON MOVEMENT OF NITRATE NITROGEN IN SOIL PROFILES AND
ON TRANSFORMATIONS OF SOIL NITROGENt
WISCONSIN UNIV., MADISON.
R. J. OLSEN.
UNIV OF WISCONSIN, WATER RESOURCES CENTER, REPORT 1969. 79 P. OWRR B-004-WIS.
DESCRIPTORS:
*NITRIFICATION, *SOIL NITROGEN, *PUBLIC HEALTH, *SOIL LEACHING,
GROUNDWATER, SOIL PROFILES, WATER TABLE, SURFACE RUNOFF, FARM WASTES,
AEROBIC CONDITIONS, INCUBATION.
IDENTIFIERS:
*LAKE EUTROPHICATION, *SOIL PHOSPHORUS, ALFALFA-BROMEGRASS, SPRING
THAWS, FERTILIZER-NITROGEN.
ABSTRACT:
THERE IS INCREASING EVIDENCE THAT AGRICULTURE IS CONTRIBUTING TO THE
INCREASE IN NITRATE-NITROGEN IN STREAMS, LAKES, AND DOMESTIC WATER
SUPPLIES. HIGH AMOUNTS OF NITRATE-NITROGEN IN WATER ARE A HEALTH HAZARD
AND CONTRIBUTE TO LAKE EUTROPHICATION. METHODS BY WHICH NITROGEN MAY
ENTER THE WATER FROM AGRICULTURAL SOURCES INCLUDE THE LEACHING OF
NITRATE-NITROGEN THROUGH THE SOIL PROFILE TO THE WATER TABLE AND
SURFACE RUNOFF, ESPECIALLY DURING SPRING THAWS FROM MANURE APPLIED TO
FROZEN SOIL DURING THE WINTER. THE DATA OBTAINED FROM FIELD EXPERIMENTS
INDICATE THAT POLLUTION OF GROUNDWATER WITH NITRATE-NITROGEN CAN BE
LIMITED BY AVOIDING EXCESSIVE RATES OF FERTILIZER NITROGEN; PROVIDING A
CROP COVER ON THE SOIL DURING THE GROWING SEASON; USE OF HAY CROPS,
SUCH AS ALFALFA-BROMEGRASS, IN ROTATION WITH CORN OR OTHER CROPS
RECEIVING FERTILIZER NITROGEN; AND NOT PERMITTING UNPROTECTED MANURE TO
ACCUMULATE DURING THE TIME OF YEAR WHEN LEACHING CAN OCCUR. RECOVERY OF
FERTILIZER NITROGEN BY THREE SUCCESSIVE CORN CROPS AND AS SOIL
INORGANIC NITROGEN FOLLOWING THE LAST CROP RANGED FROM 72 TO 88
PERCENT. THE AVERAGE CONCENTRATION OF NITRATE-NITROGEN IN THE SOIL
SOLUTION AT THE LOWEST PROFILE DEPTH SAMPLED RANGED FROM 14 PPM FOR
VIRGIN SOILS TO 21 PPM FOR MANURE CONTAMINATED SOILS AND TO 33 PPM FOR
CULTIVATED SOILS. RATE OF NITRIFICATION WAS DIRECTLY RELATED TO THE
RATE OF MANURE APPLICATION, PRESENCE OF AEROBIC CONDITIONS, PERIOD OF
INCUBATION, AND SOIL PHOSPHORUS. THE AVERAGE RECOVERY OF NITROGEN BY
CHEMICAL ANALYSIS OF THE SOIL RECEIVING THE HIGHER MANURE RATES AFTER
37 WEEKS OF INCUBATION RANGED FROM 2**% FOR ANAEROBIC CONDITIONS TO 73
TO 80 PERCENT FOR THE AEROBIC CONDITIONS. THESE DATA SUGGEST THAT WHERE
ANIMAL MANURE IS NOT TO BE USED AS A FERTILIZER, LAGOONING OF THE
MANURE UNDER ANAEROBIC CONDITIONS MAY BE AN EFFECTIVE METHOD OF
DISPOSAL WITH A MINIMUM RISK OF WATER POLLUTION. (OLSEN-UNIV OF WIS)
FIELD 05B, 05C
ACCESSION NO. W69-09721
38
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LIABILITY OF LANDOWNERS FOR POLLUTION OF PERCOLATING WATERS,
ROBERT E. SHARP.
MARO L REV, VOL 39, NO 2, P 119-134, FALL 1955. 16 P, 97 REF.
DESCRIPTORS:
*REMEDIES, *WATER POLLUTION, *PERCOLATING WATER, *RELATIVE RIGHTS,
WATER LAW, GROUND WATER, SUBSURFACE WATER, PERCOLATION, SUBSURFACE
RUNOFF, SUBSURFACE STREAMS, DEEP PERCOLATION, GROUND WATER MOVEMENT,
INFILTRATION, PATH OF POLLUTANTS, SEEPAGE, PENETRATION, INDUSTRIAL
WASTES, SEWAGE, WASTE WATER(POLLUTION ), LEGAL ASPECTS.
IDENTIFIERS:
TRESPASS, NEGLIGENCE, NUISANCE, STRICT LIABILITY.
ABSTRACT:
THE PROBLEMS ASSOCIATED WITH POLLUTION OF PERCOLATING WATERS HAS
INCREASED WITH THE RAPID EXPANSION OF RESIDENTIAL AND INDUSTRIAL
COMPLEXES INTO AREAS WHICH SEE A HIGH DEGREE OF PERCOLATED WATER USE.
THE REMEDIES AVAILABLE TO THE LANDOWNER WHO FINDS HIS WATER SUPPLY
POLLUTED FALL INTO FOUR BASIC AREAS: TRESPASS, NEGLIGENCE, NUISANCE,
AND STRICT LIABILITY. SOME JURISDICTIONS DO NOT HOLD TO / RIGHT TO
UNDEFILED WATERS, BASING THEIR OPINIONS ON THE CONCEPT Oh DAMNUM ABSOUE
INJURIA WHICH MEANS A LOSS WITHOUT INJURY. OTHER JURISDICTIONS HOLD
THAT THERE IS AN UNLIMITED RIGHT TO USE PERCOLATING WATER, AND
CONTAMINATION OF SUCH WATER SO AS TO RENDER IT UNFIT FOR USE WHEN IT
COMES ONTO A NEIGHBOR'S LAND IS A VIOLATION OF THE NEIGHBOR'S RIGHTS
FOR WHICH AN ACTION CAN BE MAINTAINED. ONCE THE RIGHT TO REASONABLE
PURITY OF PERCOLATING WATERS IS POSTULATED, THE ONLY REMAINING PROBLEM
CONCERNS THE GROUNDS ON WHICH THE SUIT SHOULD BE BROUGHT. TRESPASS IS
DIFFICULT TO RELY ON, AND NEGLIGENCE GIVES RISE TO SUSTAINING THE
BURDEN OF PROOF. NUISANCE HAS CERTAIN ADVANTAGES AS IT IS ONLY
NECESSARY TO SHOW THAT THE WELL HAS BEEN POLLUTED AND THAT DEFENDANT
HAS MAINTAINED A NUISANCE THAT HAS CAUSED POLLUTION. STRICT LIABILITY
MAKES THE PROOF OF A NUISANCE ALMOST A MATTER OF FACT.
(MOULDER-FLORIDA)
FIELD 05G, 06E
ACCESSION NO. W70-00521
39
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WATER LAW AND ADMINISTRATIONTHE FLORIDA EXPERIENCE: CHAPTER 5 CONSUMPTIVE USE
OF WATER: COMMON LAW RULES*
FLORIDA UNIV., GAINESVILLE. WATER RESOURCES RESEARCH CENTER.
F. MALONEY, S. PLAGER, AND F. BALDWIN.
UNIV OF FLORIDA PRESS, GAINESVILLE, CH 5, P 140-171, 1968. 6 FIG, 1 TABLE.
DESCRIPTORS:
:iUKl Y I UKS :
*FLORIDA, *CONSUMPTIVE USE, *GROUNDWATER, *SURFACE WATERS, SURFACE
RUNOFF, RIPARIAN RIGHTS, COMPETING USES, DOMESTIC WATER, LEGAL ASPECTS,
MUNICIPAL WATER, REASONABLE USE, REMEDIES, WATER UTILIZATION,
PERCOLATING WATER, AQUIFERS, HYDROGEOLOGY, GROUNDWATER BASINS,
HYDROLOGIC CYCLE, OVERDRAFT, WELLS, SURFACE-GROUNDWATER RELATIONSHIPS,
DAMAGES, WATER SUPPLY, SALINE WATER INTRUSION, UNDERGROUND STREAMS.
ABSTRACT:
GROUNDWATER FROM LIMESTONE AQUIFERS IS FLORIDA'S PRINCIPAL SOURCE OF
WATER FOR CONSUMPTIVE USE. THE BASIC PROBLEMS OF GROUNDWATER MANAGEMENT
ARE: (A) INTERFERENCE BETWEEN WELLS; (B) OVERDRAFT OF THE WATERBEARING
BED OR AQUIFER; AND (o CONTAMINATION. SALT-WATER INTRUSION is PROBABLY
FLORIDA'S GREATEST GROUNDWATER CONTAMINATION PROBLEM. GROUNDWATER HAS
BEEN TRADITIONALLY CLASSIFIED INTO EITHER UNDERGROUND STREAMS OR
PERCOLATING WATERS. THE SIGNIFICANCE OF THE DISTINCTIONS, HOWEVER, HAS
BEEN REDUCED SINCE MOST JURISDICTIONS, INCLUDING FLORIDA, NOW BEGIN
WITH THE PRESUMPTION THAT GROUNDWATER IS PERCOLATING. HOWEVER, LEGAL
RIGHTS CONTINUE TO HINGE UPON WHETHER THE PROBLEMS OF PROOF AS TO THE
EXISTENCE OF AN UNDERGROUND STREAM CAN BE OVERCOME. GENERALLY, THE
RIGHTS GOVERNING SURFACE WATERCOURSES APPLY TO UNDERGROUND STREAMS,
WHILE THE RIGHTS REGARDING PERCOLATING WATERS VARY ACCORDING TO WHETHER
THE COMMON LAW OR REASONABLE USE RULE IS FOLLOWED. MANY COURTS HOLD
THAT AS LONG AS THE USE IS BENEFICIAL AND REASONABLE, THE LANDOWNER MAY
USE PERCOLATING WATER ON OVERLYING LAND EVEN IF SUCH USE INJURES
ADJOINING OWNERS. FLORIDA, HOWEVER, SEEMINGLY APPLIES SURFACE WATER
RIPARIAN DOCTRINE TO PERCOLATING WATERS. INJUNCTION IS USUALLY THE
PREFERRED REMEDY RESPECTING GROUNDWATER INTERFERENCE. GENERAL RIPARIAN
DOCTRINES ARE APPLICABLE TO SPRINGS AND DEFINED SURFACE WATERBODIES.
WITH THE INCREASING USE OF SURFACE WATERS AS A SOURCE OF SUPPLY, THE
TREND IS TO REFINE THE ABSOLUTE OWNERSHIP APPLICABLE TO SUCH WATERS.
(SEE W70-00527). (WHEELER-FLORIDA)
FIELD 06E, 04B, 05G
ACCESSION NO. W70-00532
40
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NITROGEN CONTAMINATION OF GROUNDWATER BY BARNYARD LEACHATES,
GUELPH UNIV. (ONTARIO). OEPT. OF SOIL SCIENCE.
R. W. GILLHAM, AND L. R. WEBBER.
J WATER POLLUT CONTR FEDERATION, VOL 41, NO 10, P 1752-1762, OCT 1969. 11 P,
10 FIG, 2 TAB, 13 REF.
DESCRIPTORS:
*FARM WASTES, *CATTLE, BLEACHING, *WATER POLLUTION SOURCES, PATH OF
POLLUTANTS, WATER POLLUTION EFFECTS, NUTRIENTS, GROUNDWATER MOVEMENT,
NITROGEN, WASTE WATERfPOLLUTION).
IDENTIFIERS:
CATTLE WASTES, FEEDLOT WASTES.
ABSTRACT:
A ZONE OF NITROGEN-CONTAMINATED GROUNDWATER ASSOCIATED WITH A BARNYARD
WAS STUDIED TO DETERMINE THE QUANTITY OF INORGANIC NITROGEN REACHING
THE GROUNDWATER FROM THE BARNYARD. FROM PIEZOMETR1C POTENTIAL AND
HYDRAULIC CONDUCTIVITY MEASUREMENTS, QUANTITATIVE FLOW NETS WERE DRAWN
PERMITTING GROUNDWATER DISCHARGE CALCULATIONS. AN INCREASE FROM 2 TO 15
MG/L INORGANIC NITROGEN OCCURRED IN THE GROUNDWATER AS IT PASSED
BENEATH THE BARNYARD. THIS RESULTED IN A CONTRIBUTION OF 4.4 LB (2.0
KG) OF INORGANIC NITROGEN MADE BY THE BARNYARD TO THE G JUNDWATER
DURING THE 5-MONTH STUDY PERIOD. THE CONCENTRATION OF NITROGEN WAS
RELATED TO THE DIRECTION OF GROUNDWATER FLOW AND WAS DEPENDENT ON THE
PRESENCE OF CONDITIONS SUITABLE FOR THE LEACHING OF NITROGEN AND THE
DILUTION POTENTIAL OF THE LOCAL GROUNDWATER FLOW SYSTEM. THE SURFACE
TOPOGRAPHY PROVED TO BE A POOR INDICATION OF THE DIRECTION OF
GROUNDWATER FLOW. (KNAPP-USGS)
FIELD 05B, 05C
ACCESSION NO. W70-00665
41
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BEHAVIOR OF SURFACTANTS AND OTHER DETERGENT COMPONENTS IN WATER AND SOIL-WATER
ENVIRONMENTS*
GEOLOGICAL SURVEY, WASHINGTON, D.C. WATER RESOURCES DIV.
COOPER WAYMAN, H. L. PAGE, AND J. B. ROBERTSON.
FED HOUSING ADMIN TECH STUDIES PUBLICATION NO FHA 532, FEB 1965. 136 P, 104
FIG, 22 TAB, 283 REF.
DESCRIPTORS:
^SURFACTANTS, *ALKYBENZENE SULFONATES, *DETERGENTS, SGROUNDWATER
MOVEMENT, *WATER POLLUTION, INFILTRATION, ANALYTICAL TECHNIQUES, SOIL
CONTAMINATION EFFECTS, ORGANIC COMPOUNDS, DISPERSION, SEWAGE EFFLUENTS,
BIODEGRADATION, METHODOLOGY.
IDENTIFIERS:
*DETERGENT BEHAVIOR(WATER), *SOIL-WATER
SURFACTANTS, SYNTHETIC DETERGENTS.
ENVIRONMENT, ANIONIC
ABSTRACT:
THIS REPORT IS PRIMARILY CONCERNED WITH ALKYLBENZENE SULFONATE (ABS),
THE ANIONIC SURFACE-ACTIVE AGENT MOST FREQUENTLY FOUND IN WATER
SUPPLIES. THE MECHANISMS AND PHYSICAL PRINCIPLES OF DETERGENT MOVEMENT
UNDERGROUND ARE DISCUSSED IN A MANNER TO PROVIDE BACKGROUND FOR
ENGINEERING ANALYSIS OF POLLUTION PROBLEMS. UNLIKE OTHER ORGANIC
WASTES, ABS IS NOT EASILY BROKEN DOWN BY MICROORGANISMS, AND IT MOVES
WITH SEWAGE EFFLUENT, OFTEN INTO GROUNDWATER. ABS CAN BE DETECTED IN
LOW CONCENTRATIONS AND THUS USED TO TRACE THE POLLUTION. THE REPORT
PROVIDES A GOOD TECHNICAL BASIS FOR UNDERSTANDING DETERGENT MOVEMENT
UNDERGROUND; IT DOES NOT CONSTITUTE AN FHA STANDARD. (LANG-USGS)
FIELD 05B, 05A
ACCESSION NO. W70-01291
42
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THE INFILTRATION OF ALDRIN THROUGH OTTAWA SAND COLUMNS,
GEOLOGICAL SURVEY, IDAHO FALLS, IDAHO.
JOHN B. ROBERTSON, AND LLOYD KAHN.
IN: GEOL SURV RES 1969, PROF PAP 650-C, P C219-C223, 1969. 5 P, 3 FIG, 1 TAB,
17 REF.
DESCRIPTORS:
*PATH OF POLLUTANTS, *ALDRIN, *GROUNDWATER MOVEMENT, LABORATORY TESTS,
PERMEAMETERS, SANDS, CHLORINATED HYDROCARBON PESTICIDES, INSECTICIDES,
PESTICIDE RESIDUES, INFILTRATION.
IDENTIFIERS:
OTTAWA SAND, ALDRIN INFILTRATION.
ABSTRACT:
THE PENETRABILITY OF CHLORINATED HYDROCARBON INSECTICIDES THROUGH SOILS
IS DEPENDENT UPON THE TYPE OF FORMULATION APPLIED, FREQUENCY OF ITS
APPLICATION, SOIL CONDITIONS, AND THE FREQUENCY AND RATE OF RAINFALL OR
IRRIGATION. ALDRIN, A REPRESENTATIVE MEMBER OF THE CHLORINATED
HYDROCARBON INSECTICIDE GROUP, WAS INFILTRATED THROUGH COLUMNS OF
OTTAWA SAND IN FOUR EXPERIMENTS. MOST OF THE ELUTED ALDRIN IN ORGANIC
SOLVENT SYSTEMS WAS ELUTED DURING THE PASSAGE OF THE FIRST LITER OF
WATER. THE ALDRIN DISTRIBUTED ITSELF IN A CHARACTERISTIC MANNER THROUGH
EACH COLUMN, DEPENDING UPON THE COMPOSITION AND STABILITY OF THE
EMULSION AND RATE OF WATER INFILTRATION. THE CONCENTRATION OF HHDN
(ACTIVE INGREDIENT IN ALDRIN) IN THE EFFLUENT.FROM THE COLUMNS REACHED
A 'STEADY STATE1 CONDITION OF 0.5 TO 2 MICROGRAMS PER LITER OF WATER. A
COMMERCIAL EMULSIBLE CONCENTRATE MIXTURE TRANSMITTED MORE ALDRIN TO THE
EFFLUENT THAN DID A SYNTHETIC SOLUTION CONTAINING NO EMULSIFIER.
(KNAPP-USGS)
FIELD 05B, 02G
ACCESSION NO. W70-01904
43
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STATE ACTIVITIESt
RICHARD S. NELLE.
AM WATER WORKS ASS'N J, VOL 53, NO 6, P 857-861, JULY 1961, 5 P, 7 REF.
DESCRIPTORS:
^ILLINOIS, *WATER POLLUTION, *WATER POLLUTION CONTROL, ^POLLUTION
ABATEMENT, STATE GOVERNMENTS, LOCAL GOVERNMENTS, LEGISLATION, WATER
RIGHTS, RIPARIAN RIGHTS, NATURAL USE, NATURAL FLOW DOCTRINE, REASONABLE
USE, ARTIFICIAL USE, RIPARIAN LANDS, GROUNDWATER, PERCOLATING WATER,
EMINENT DOMAIN, PUBLIC HEALTH, DOMESTIC WATER, INDUSTRIAL WATER,
RECREATION, WATERSHED MANAGEMENT, WASTE DISPOSAL, PLANNING,
INTER-AGENCY COOPERATION, WATER QUALITY CONTROL.
ABSTRACT:
THE COMMON-LAW WATER RIGHTS DOCTRINE HAS BEEN INTERPRETED IN ILLINOIS
BY THE NATURAL FLOW AND REASONABLE USE THEORIES. STREAM POLLUTION
CONTROL LAWS HAVE ADOPTED THE REASONABLE USE THEORY. IN OTHER
CONSIDERATIONS OF WATER RIGHTS, THE NATURAL FLOW THEORY HAS PREVAILED
IN DIVERSION QUESTIONS WHEREAS THE REASONABLE USE IS MORE FREQUENTLY
APPLIED IN CONSUMPTION PROBLEMS. BECAUSE WATER POLLUTION KNOWS NO
POLITICAL BOUNDARIES, DEVELOPMENT IN THIS AREA MUST COME FROM STATE
GOVERNMENTS. WITH AN EXPANDING INDUSTRIAL ECONOMY AND A GREATER
COMPETITION FOR WATER USE, POLLUTION CONTROL CANNOT BE ATTAINED WITHOUT
CONTROL OF USE. ANY USE OF WATER INVOLVES A CHANGE IN WATER QUALITY,
AND THIS QUALITY NEEDS TO BE MANAGED WITH INCREASED PRECISION AS THE
QUANTITY 'OF WATER DIMINISHES. ALTHOUGH THE CONTROL OF POLLUTION IS
ADMINISTERED AT THE STATE LEVEL, LOCAL GOVERNMENTS MUST EXERCISE THE
AUTHORITY GRANTED TO THEM TO PLAN, CONSTRUCT, AND POLICE WATER SOURCES.
CONTROL OF WATERSHED POLLUTION IS A COOPERATIVE VENTURE. COOPERATION
MUST EXIST BETWEEN LOCAL AND STATE GOVERNMENTS AND AMONG STATE
AGENCIES. SPECIFIC INTERESTS ON THE LOCAL LEVEL AND ON THE STATE LEVEL
ARE DISCUSSED. (SCHRAM-FLOR IDA)
FIELD 05G
ACCESSION NO. W70-02896
44
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DISTRIBUTION OF NITRATES AND OTHER WATER POLLUTANTS UNDER FIELDS AND CORRALS IN
THE MIDDLE SOUTH PLATTE VALLEY OF COLORADO,
AGRICULTURAL RESEARCH SERVICE, FORT COLLINS, COLO. NORTHERN PLAINS BRANCH;
AND COLORADO AGRICULTURAL EXPERIMENT STATION, FORT COLLINS.
B. A. STEWART, F. G. VIETS, JR., G. L. HUTCHINSON, W. D. KEMPER, AND F. E.
CLARK.
U S DEPARTMENT OF AGRICULTURE, AGRICULTURAL RESEARCH SERVICE, ARS 41-134,
DECEMBER 1967, 206 P. 31 FIG, 25 TAB, 13 REF.>
DESCRIPTORS:
^NITRATES, -AMMONIA, *WATER POLLUTION SOURCES, #CORES, FIELDS, PLANTS,
ALFALFA, CEREAL CROPS, IRRIGATED LAND, COLORADO, GROUNDWATER,
PERCOLATION.
IDENTIFIERS:
NATIVE GRASSES, FEEDLOTS, CORRALS, SOUTH PLATTE VALLEY(COLO).
ABSTRACT:
CORES REPRESENTING NONIRRIGATED FIELDS IN NATIVE GRASS, CULTIVATED
NONIRRIGATED FIELDS, IRRIGATED FIELDS IN ALFALFA, IRRIGATED FIELDS IN
CROPS OTHER THAN ALFALFA, AND CORRALS WERE OBTAINED FROM NORTHEASTERN
COLORADO DURING 1966. CULTIVATED NONIRRIGATED FIELDS USUALLY CONTAINED
SMALL ACCUMULATIONS OF NITRATE BELOW THE ROOT ZONE. NATIVE GRASS
FIELDS, ORDINARILY, DID NOT SHOW NITRATE ACCUMULATION IN CORE PROFILES.
SIGNIFICANT QUANTITIES OF NITRATE WERE FOUND IN MOST CORES FROM
IRRIGATED FIELDS WITH ROW CROPS OR CEREAL GRAINS. ALTERNATELY, CORES
FROM IRRIGATED ALFALFA FIELDS GENERALLY CONTAINED INSIGNIFICANT AMOUNTS
OF NITRATE. AMOUNTS OF NITROGEN AS NITRATE FOUND UNDER CORRALS WERE
EXTREMELY VARIED, RANGING FROM ALMOST NONE TO MORE THAN 5000
POUNDS/ACRE IN A 20-FOOT PROFILE. EVIDENCE DISCLOSED THAT
DENITRIFICATION WAS OCCURRING UNDER FEEOLOTS, EVEN AT SEVERAL FEET
BELOW THE SURFACE, CONSEQUENTLY, MUCH OF NITRATE UNDER FEEDLOTS WILL
PROBABLY NEVER REACH THE WATER TABLE. WATER SAMPLES BENEATH SEVERAL
CORRALS CONTAINED LARGE AMOUNTS OF ORGANIC CARBON AND AMMONIA AND
POSSESSED OFFENSIVE ODOR. BACTERIAL COUNTS UNDER CORRALS WERE
CONSIDERABLY HIGHER THAN UNDER OTHER AREAS, ESPECIALLY AT LOWER DEPTHS.
THESE FINDINGS INDICATE SOME POLLUTION OF GROUNDWATER BY DEEP
PERCOLATION IS OCCURRING FROM CORRALS, BUT MORE STUDIES ARE REQUIRED
BEFORE SIGNIFICANCE AND MAGNITUDE OF THIS POLLUTION CAN BE ASSESSED.
(KEENEY-WISCONSIN)
FIELD 05B
ACCESSION MO. W70-04488
47
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AGRICULTURAL DRAINAGE AND EUTROPHICATION,
WISCONSIN UNIV., MADISON.
J. W. BIGGAR, AND R. B. COREY.
EUTROPHICATION: CAUSES, CONSEQUENCES, CORRECTIVES, PRINTING AND PUBLISHING
OFFICE, NATIONAL ACADEMY OF SCIENCES, WASHINGTON, D C, 1969. P 404-445, 8
FIG, 14 TAB, 69 REF.
DESCRIPTORS:
*AGRICULTURAL WATERSHED, ^SUBSURFACE DRAINAGE, ^DRAINAGE,
*EUTROPHICATION, NITROGEN, PHOSPHORUS, SURFACE WATERS, PERCOLATION,
SUSPENDED LOAD, GROUNDWATER, AQUIFER CHARACTERISTICS.
IDENTIFIERS:
*AGRICULTURAL DRAINAGE, DISSOLVED NUTRIENTS, WATER MIXING, RUSSIAN
RIVER(CALIF), YAKIMA BASIN(PACIF1C NORTHWEST), LAKE MENDOTA(WIS).
ABSTRACT:
A COMPREHENSIVE REVIEW OF NUMEROUS ASPECTS INVOLVED IN THE RELATIONSHIP
OF AGRICULTURAL DRAINAGE AND WATER EUTROPHICATION IS PRESENTED.
PARTICULAR ATTENTION IS GIVEN TO CHEMICAL REACTIONS THAT NITROGEN AND
PHOSPHORUS UNDERGO IN SOIL-WATER SYSTEM. THE FATE OF NUTRIENTS
TRANSPORTED BY SURFACE RUNOFF, INTERFLOW, AND DEEP PERCOLATING WATER IS
DETERMINED BY COMPLEX COINFLUENCING FACTORS, SUCH AS NATURE OF
SUSPENDED MATERIAL, HETEROGENY OF SOIL PROFILE, AND DEGREE OF WATER
MIXING. STRESS IS PLACED ON THE INAPPLICABILITY OF MACRO-PARAMETERS,
SUCH AS AVERAGE HYDRAULIC CONDUCTIVITY, TO PROCESSES OCCURRING ON A
MICROSCOPIC SCALE. THE REPORT INCLUDES ILLUSTRATIONS OF PLANT NUTRIENT
LOSS FROM HARVESTED AREAS AND CONTRIBUTIONS OF FERTILIZING ELEMENTS
FROM AGRICULTURAL LANDS. AN APPRAISAL OF AGRICULTURAL DRAINAGE
INFLUENCE ON EUTROPHICATION REQUIRES INVESTIGATIONS OF CHEMICAL AND
MINERALOGICAL CONTENTS OF RUNOFF WATERS IN DIFFERENT SEASONS, DYNAMICS
OF GROUNDWATER, AND WATER IN THE UNSATURATED ZONE BELOW ROOT SYSTEMS.
(SEE VOL. 3, NO. 10, FIELD 5C, W70-03975). (WILDE-WISCONSIN)
FIELD 05C, 05B
ACCESSION NO. W70-04504
48
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MIGRATION OF POLIOVIRUS TYPE 2 IN PERCOLATING WATER THROUGH SELECTED OAHU SOILS,
HAWAII UNIV., HONOLULU. WATER RESOURCES RESEARCH CENTER.
DANIEL H. HORI, NATHAN C. BURBANK, JR., REGINALD H. F. YOUNG, L. STEPHEN LAU,
AND HOWARD W. KLEMMER.
AVAILABLE FROM THE CLEARINGHOUSE AS PB-190 271, $3.00 IN PAPER COPY, $0.65 IN
MICROFICHE. TECHNICAL REPORT NO 36, HAWAII WATER RESOURCES RESEARCH CENTER,
JANUARY 1970. 40 P. OWRR PROJECT A-001-HI.
DESCRIPTORS:
^VIRUSES, GROUNDWATER, WATER POLLUTION, ABSORPTION, BLEACHING,
^PERCOLATION.
ABSTRACT:
A LABORATORY STUDY WAS MADE TO DETERMINE THE ABILITY OF THREE OAHU
SOILS, WAHIAWA, LAHAINA, (BOTH LOW HUMIC LATOSOLS), AND TANTALUS CINDER
TO PREVENT POSSIBLE CONTAMINATION OF THE BASAL-WATER LENS BY THE
PASSAGE OF VIRUS. THE STUDY WAS PERFORMED UTILIZING COLUMNS CONTAINING
THE SELECTED SOILS AND SUBJECT TO INTERMITTENT PERCOLATING WATER
CONTAINING A KNOWN CONCENTRATION OF POLIOVIRUS TYPE 2, SIMULATING THE
ACTION OF A CESSPOOL LEACHING INTO THE GROUND. THE EFFLUENT FROM THE
SOIL COLUMN WAS COLLECTED AND ANALYZED FOR VIRAL CONTENT BY THE PLAQUE
FORMING TECHNIQUES. BREAKTHROUGH OF THE VIRUS OCCURRED IN BOTH WAHIAWA
AND LAHAINA SOILS AT SOIL THICKNESSES OF 6-INCH, 2 1/2 INCH, AND 1 1/2
INCH AT APPLIED CONCENTRATION OF 150,000 PFU/ML OF FEED SOLUTION. THE
VIRUS REMOVAL WAS OVER 97 PERCENT OF THE APPLIED TITER. THE TANTALUS
CINDER PROVED INEFFECTIVE IN WITHHOLDING THE VIRUS AT THE APPLIED
CONCENTRATION OF 150,000 PFU/ML OF FEED SOLUTION. THE VIRUS
BREAKTHROUGH VARIES BETWEEN 39 PERCENT TO 78 PERCENT OF THE APPLIED
TITER.
FIELD 05G, 02G
ACCESSION NO. W70-04688
49
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GROUNDWATER RECHARGE DESIGN FOR RENOVATING WASTE WATER,
AGRICULTURAL RESEARCH SERVICE, PHOENIX, ARIZ. WATER CONSERVATION LAB.
HERMAN BOUWER.
ASCE PROCEEDINGS, JOURNAL SANITARY ENGINEERING DIVISION, VOL 95, NO SA1,
PAPER 7096, P 59-74, FEBRUARY 1970. 16 P, 10 FIG, 1 TAB, 20 REF.
DESCRIPTORS:
^ARTIFICIAL RECHARGE, *WATER SPREADING, *WATER REUSE, ^TERTIARY
TREATMENT, INFILTRATION, FILTRATION, SEWAGE TREATMENT, SEWAGE DISPOSAL*
HYDROGEOLOGY, GROUNOWATER MOVEMENT, WATER RESOURCES DEVELOPMENT,
RECLAIMED WATER.
IDENTIFIERS:
PHOENIX(ARIZ), SALT RIVER(ARIZ).
ABSTRACT:
SOIL AND HYDROGEOLOGIC CONDITIONS PERMITTING, GROUNDWATER RECHARGE BY
SURFACE SPREADING IS AN ECONOMIC AND ESTHETIC WAY FOR FURTHER TREATMENT
OR RENOVATION OF SECONDARY SEWAGE EFFLUENT, CANNERY WASTES, OR SIMILAR
LOW-QUALITY WATER. THE DESIGN OF A SYSTEM OF SPREADING AREAS KITH WELLS
OR DRAINS FOR COLLECTING THE RECLAIMED WATER SHOULD GENERALLY BE BASED
ON: (1) A MAXIMUM LIMIT FOR THE ELEVATION OF THE WATER TABLE MOUND
BENEATH THE SPREADING AREAS; (2) A MINIMUM LIMIT FOR THE UNDERGROUND
DETENTION TIME AND TRAVEL DISTANCE AS THE WATER MOVES TO THE WELLS OR
DRAINS; AND <3> MINIMUM CONTAMINATION OF THE GROUNDWATER IN THE AQUIFER
OUTSIDE THE RECHARGE SYSTEM. HYDRAULIC PROPERTIES OF AQUIFERS,
INCLUDING ANISOTROPY, CAN BE DETERMINED BY ANALOG AND BY FIELD
MEASUREMENTS. THESE DATA ARE USED TO EVALUATE THE EFFECTIVE
TRANSMISSIBILITY FOR RECHARGE, AND TO CALCULATE WATER-TABLE POSITIONS
AND UNDERGROUND DETENTION TIMES FOR A SYSTEM OF LONG, PARALLEL
SPREADING STRIPS WITH WELLS MIDWAY BETWEEN THE STRIPS. (KNAPP-USGS)
FIELD 05D, 04B
ACCESSION NO. W70-04712
50
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REUTILIZATION OF WASTEWATER RECYCLED THROUGH GROUNDWATER, VOLUME 1 AND 2.
EASTERN MUNICIPAL WATER DISTRICT, HEMET, CALIF.
AVAILABLE FROM THE CLEARINGHOUSE AS PB-190 790 (VOL. I), AND PB-190 791 (VOL.
II), $3.00 EACH IN PAPER COPY, $0.65 EACH IN MICROFICHE. PROGRESS REPORT TO
FEDERAL WATER POLLUTION CONTROL ADMINISTRATION FOR PROJECT 16060, DECEMBER
1968. VOLUME 1 - 125 P, 45 FIG, 20 TAB, 13 REF, VOLUME 2 - 87 P, 61 REF, 3
APPEND. GRANT FWPCA 16060 DDZ 12/69.
DESCRIPTORS:
^ARTIFICIAL RECHARGE, #WATER REUSE, ^CALIFORNIA, WATER YIELD,
INFILTRATION, WATER SPREADING, PIT RECHARGE, SAFE YIELD, WATER BALANCE,
HYDROGEOLOGY, DATA COLLECTIONS, HYDROLOGIC DATA, GROUNDWATER MOVEMENT,
WATER QUALITY, WATER LEVELS, WATER SUPPLY, WATER UTILIZATION, SURVEYS,
GEOPHYSICS.
IDENTIFIERS:
SAN JACINTO VALLEY(CALIF).
ABSTRACT:
THE WATER QUALITY FACTORS INVOLVED IN THE RECHARGING OF THE SAN JACINTO
BASIN, CALIFORNIA ARE EVALUATED SO THAT THE OVERALL OPERATION MAY BE
CONDUCTED IN A MANNER TO PROVIDE ADEQUATE PROTECTION OF GROUNDWATER
QUALITY WHILE PERMITTING RECLAMATION OF WASTES FOR REGIONAL WATER
CONSERVATION. ANOTHER OBJECTIVE IS TO STUDY THE BENEFITS TO THE SALT
BALANCE PROBLEM CAUSED BY RECHARGING. IN THE PREVIOUS SITUATION, SOME
EFFLUENTS WERE DISCHARGED TO THE SAN JACINTO R,IVER AREA AND SOME WERE
USED AS IRRIGATION WATER. WITH RECHARGE THERE IS A SIGNIFICANT
REDUCTION IN EVAPOTRANSPIRATION LOSSES, THUS IMPROVING GROUNDWATER
QUALITY BY DILUTING THE DISSOLVED SALTS. THE SAFE GROUNDWATER YIELD IS
LIMITED TO APPROXIMATELY 11, 205 ACRE-FEET/YEAR. THE VOLUMES OF WATER
RECLAIMED AND PUT UNDERGROUND TO REPLENISH THE OVERDRAFT NOW AVERAGE
APPROXIMATELY 1430 ACRE-FEET/YEAR. WITHDRAWALS NOW APPROXIMATE 12,000
ACRE-FEET/YEAR, AND IMPORTATION OF COLORADO RIVER WATER APPROXIMATES
1900 ACRE-FEET/YEAR. INFLOW OF SALT INTO THE BASIN IS NOW ESTIMATED AT
5800 TON/YEAR; 3900 TON/YEAR FROM INFLOWING GROUNDWATER AND 1900
TON/YEAR FROM IMPORTED COLORADO RIVER WATER. (KNAPP-USGS)
FIELD 05D, 04B
ACCESSION NO. W70-05466
51
-------
SEEPAGE AND SEEPAGE CONTROL PROBLEMS IN SANITARY LANDFILLS,
LOS ANGELES COUNTY SANITATION DISTRICT, LOS ANGELES, CALIF.
FRANK R. DAIR,
PROCEEDINGS, SEEPAGE SYMPOSIUM, SECOND, MARCH 25-27, 1968, PHOENIX, ARIZONA,
U.S. DEPT. OF AGRICULTURE, AGRICULTURAL RESEARCH SERVICE ARS 41-147, APRIL
1969, P 14-16.
DESCRIPTORS:
#WATER POLLUTION, *GROUNDWATER, ^SEEPAGE, ^LANDFILLS, *SOLID WASTES,
WATER POLLUTION SOURCES, WATER POLLUTION CONTROL, PUBLIC HEALTH,
ENVIRONMENTAL SANITATION, WASTE DISPOSAL, DISPOSAL, WASTES, CALIFORNIA,
PERCOLATING WATER, PERCOLATION, LEACHING, AQUIFERS, WATER TABLE, WATER
SUPPLY, GASES, CARBON DIOXIDE, METHANE, BARRIERS, INFILTRATION.
IDENTIFIERS:
^SEEPAGE CONTROL.
ABSTRACT:
GROUNDWATER POLLUTION RESULTING FROM SOLID WASTE LANDFILLS HAS BEEN THE
SUBJECT OF INTENSIVE INVESTIGATION IN SOUTHERN CALIFORNIA. ALTHOUGH
THESE STUDIES HAVE PRODUCED AN ENORMOUS QUANTITY OF DATA, THE MAJOR
PROBLEMS OF GROUNDWATER POLLUTION FROM LANDFILLS GO UNSOLVED. RESEARCH
IS NEEDED TO DISCOVER FEASIBLE YET SANITARY METHODS OF DEPOSITING
REFUSE IN. DIRECT CONTACT WITH GROUNDWATER. FURTHER STUDY IS ALSO
REQUIRED TO DETERMINE WHETHER WATER DOES IN FACT LEACH THROUGH
LANDFILLS IN APPRECIABLE AMOUNTS AND PERCOLATE DOWN TO THE WATER TABLE.
EXPERIMENTATION SHOULD ALSO PROCEED IN AN ATTEMPT TO DEVELOP BARRIERS
TO PREVENT THE ESCAPE OF REFUSE-PRODUCED GASES INTO THE GROUNDWATER.
(SEE W70-06012). (CARR-ARIZONA)
FIELD 04A, 05E
ACCESSION NO. W70-06011
52
-------
EFFECT OF CLIMATE, IMPOUNDMENTS, AND LAND USE ON STREAM SALINITY,
AGRICULTURAL RESEARCH SERVICE, CHICKASHA, OKLA. SOUTHERN PLAINS BRANCH.
HARRY B. PIONKE.
JOURNAL OF SOIL AND WATER CONSERVATION, VOL 25, NO 2, P 62-64, MARCH-APRIL
1970, 3 P, 4 FIG, 7 REF.
DESCRIPTORS:
*WATER CHEMISTRY, #WATER QUALITY, ^CLIMATES, #LAND USE, ^OKLAHOMA,
SALINITY, STREAMFLOW, SURFACE-GROUNDWATER RELATIONSHIPS, INFILTRATION,
EVAPOTRANSPIRATION, PERCOLATION, FLOOD CONTROL, RESERVOIRS,
PRECIPITATION(ATMOSPHERIC).
IDENTIFIERS:
CLIMATIC CHANGE.
ABSTRACT:
AVERAGE SALINITY OF THE WASHITA RIVER IN OKLAHOMA INCREASED
SUBSTANTIALLY BETWEEN 1954 AND 1967. AMONG ALL VARIABLES STUDIED,
CLIMATIC CHANGES APPEARED TO EXERT THE GREATEST INFLUENCE ON STREAM
SALINITY LEVELS. AFTER CORRECTING FOR THE EFFECT OF CLIMATIC CHANGE,
THE SAME TREND OF SALINITY INCREASE REMAINED AND APPEARED TO BE MORE
CLOSELY RELATED TO CHANGING LAND USE THAN TO THE RECENT INTRODUCTION OF
NUMEROUS IMPOUNDMENTS AT UPSTREAM LOCATIONS. (KNAPP-USGS)
FIELD 04C, 05B
ACCESSION NO. W70-06102
53
-------
GEOLOGIC INVESTIGATION OF THE SITE FOR AN ENVIRONMENTAL POLLUTION STUDY,
ILLINOIS STATE GEOLOGICAL SURVEY, URBANA.
PAUL B. DUMONTELLE.
ILLINOIS STATE GEOLOGICAL SURVEY ENVIRONMENTAL GEOLOGY NOTE NO 31, MARCH
1970. 19 P, 4 FIG, 1 TAB, 4 REF, APPEND.
DESCRIPTORS:
#WATER POLLUTION EFFECTS, *ON-SITE INVESTIGATIONS, #SOIL
INVESTIGATIONS, ^GEOLOGIC INVESTIGATIONS, ^ILLINOIS, HYDROLOGIC DATA,
GEOLOGY, HYDROLOGY, HYDROGEOLOGY, INFILTRATION, PERMEABILITY, SAMPLING,
GROUNDWATER MOVEMENT, PATH OF POLLUTANTS, ENVIRONMENT.
IDENTIFIERS:
TEST HOLES, UNIVERSITY OF ILLINOIS, ENVIRONMENTAL POLLUTION.
ABSTRACT:
TO STUDY THE EFFECTS OF POLLUTANTS UNDER SIMULATED NATURAL-FLOW
CONDITIONS, THE ILLINOIS NATURAL HISTORY SURVEY IS PLANNING A STUDY
AREA CONTAINING 16 LARGE PONDS AND 6 SMALLER PONDS, INTERCONNECTED BY A
CENTRAL DRAIN AND A CATCHMENT BASIN. THE LARGER PONDS WILL MEASURE 190
BY 50 FT AND THE SMALLER ONES 85 BY 36 FT. THEY WILL BE FROM 4 TO 8 FT
DEEP. THE CHAMPAIGN GLACIAL MORAINE FORMS A PROMINENT RIDGE TRENDING
NORTHWEST-SOUTHEAST THROUGH THE SOUTH PART OF CHAMPAIGN AND URBANA. THE
SOUTH SIDE OF THE MORAINE HAS A VERY GENTLE SLOPE OF ABOUT 50 FT PER
MILE, WHICH EXHIBITS THE POORLY DEFINED DRAINAGE SYSTEM TYPICAL OF
TOPOGRAPHY RELATED TO GLACIATION. THESE UPLANDS ARE UNDISSECTED, BUT
ARE A PART OF THE EMBARRAS RIVER WATERSHED TO THE SOUTH. THE PROPOSED
SITE FOR THE ENVIRONMENTAL POLLUTION STUDY IS LOCATED IN THE MID-PART
OF THE SOUTH SLOPE OF THE CHAMPAIGN MORAINE. THE SITE CHOSEN FOR THE
ENVIRONMENTAL POLLUTION PROJECT IS GEOLOGICALLY FEASIBLE. THE
RECTANGULAR-SHAPED PONDS MAY BE SATISFACTORILY CONSTRUCTED OF IN SITU
MATERIALS IF SOME PRECAUTIONS ARE TAKEN. (KNAPP-USGS)
FIELD 05C, 06G
ACCESSION NO. W70-06322
54
-------
SELECTION OF REFUSE DISPOSAL SITES IN NORTHEASTERN ILLINOIS,
ILLINOIS STATE GEOLOGICAL SURVEY, URBANA.
GEORGE M. HUGHES.
ILLINOIS STATE GEOLOGICAL SURVEY ENVIRONMENTAL GEOLOGY NOTE NO 17, SEPTEMBER
1967. 18 P, 2 FIG, 1 TAB, 41 REF.
DESCRIPTORS *
#WASTE DISPOSAL, ^GARBAGE DUMPS, *LANDFILLS, *PATH OF POLLUTANTS,
*HYDRQGEOLOGY, ^ILLINOIS, MUNICIPAL WASTES, LEACHING, GROUNOWATER
MOVEMENT, ENVIRONMENTAL SANITATION, ENVIRONMENTAL ENGINEERING, WATER
POLLUTION SOURCES.
IDENTIFIERS:
ENVIRONMENTAL GEOLOGY.
ABSTRACT:
GEOLOGIC ENVIRONMENTS IN NORTHEASTERN ILLINOIS WERE EVALUATED IN TERMS
OF RESULTS OF STUDIES ON REFUSE DISPOSAL AND GROUNDWATER CONTAMINATION
THAT HAVE BEEN MADE ELSEWHERE. THE GEOLOGIC ENVIRONMENTS COMMONLY
CONSIDERED AS SAFE FOR REFUSE DISPOSAL IN THIS AREA ARE THOSE WITH
MATERIALS OF LOW PERMEABILITY AND THOSE THAT ARE RELATIVELY DRY. A
THIRD TYPE OF ENVIRONMENT, ONE WHICH IS HYDROLOGI CALLY PROTECTIVE, ALSO
SHOULD BE CONSIDERED FOR DISPOSAL PURPOSES. (KNAPP-USGS)
FIELD 05B, 05E
ACCESSION NO. W70-06572
55
-------
SANITARY LANDFILL LOCATION STUDY.
STARK COUNTY REGIONAL PLANNING COMMISSION, CANTON, OHIO.
REPORT AVAILABLE FROM CLEARINGHOUSE AS PB-187 807, $3.00 IN PAPER COPY, $0.65
IN MICROFICHE. STARK COUNTY REGIONAL PLANNING COMMISSION, CANTON, OHIO,
SEPT 1969. 84 P, 5 FIG, 18 REF. PROJECT NO OHIO P-238 HUD.
DESCRIPTORS:
^LANDFILLS, #WASTE DISPOSAL, #HYDROGEQLOGY, WATER POLLUTION CONTROL,
SURVEYS, LEACHING, GEOLOGY, GROUNDWATER MOVEMENT,
IDENTIFIERS:
STARK COUNTY(OHIO).
ABSTRACT:
TWENTY-SEVEN STRIP MINE SITES IN STARK COUNTY, OHIO WERE ANALYZED AS TO
THEIR SUITABILITY FOR A SANITARY LANDFILL. TWELVE OF THE 27 SITES ARE
RECOMMENDED. THE 12 SITES RECOMMENDED FOR A SANITARY LANDFILL ARE
ANALYZED ACCORDING TO A LIST OF GEOHYDROLOGICAL CRITERIA. EACH OF THE
12 SITES IS CLASSIFIED ACCORDING TO ITS MAJOR GEOHYDROLOGICAL
CHARACTERISTICS AND THE TYPES OF WASTE MATERIALS ACCEPTABLE TO EACH
CLASS. EACH SITE IS DESCRIBED AND ANALYZED ON AN INDIVIDUAL BASIS
ACCORDING TO: (A) LOCATION, LAND USE AND ZONING, (B) SIZE AND
OWNERSHIP, (C) CLASSIFICATION, SUITABILITY, AND LIFE EXPECTANCY, (D)
POTENTIAL REUSE OF THE COMPLETED LANDFILL, AND (E) GENERALIZED ANALYSIS
OF GEOLOGIC MATERIALS. (KNAPP-USGS)
»
FIELD 05E, 05G
ACCESSION NO. W70-07193
56
-------
SWIFT AND CO V PEOPLES COAL AND OIL CO (LIABILITY FOR UNDERGROUND OIL SEEPAGE).
186 A 629-635 (CONN 1936).
DESCRIPTORS:
^CONNECTICUT, *OILY WATER, *UNDERSEEPAGE, ^POLLUTION, JUDICIAL
DECISIONS, OIL, SEEPAGE, DAMAGES, OIL INDUSTRY, STORAGE TANKS,
SUBSURFACE DRAINAGE, UNDERFLOW, UNDERGROUND STREAMS, PERCOLATING WATER,
SUBSURFACE WATERS, UNDERGROUND, LEAKAGE, PERCOLATION, WATER RIGHTS,
WATER POLLUTION SOURCES, GROUNDWATER, GROUNDWATER MOVEMENT,
PERMEABILITY, LEGAL ASPECTS.
ABSTRACT:
PLAINTIFF SUED DEFENDANT OIL COMPANY FOR DAMAGES RESULTING FROM OIL
SEEPAGE INTO PLAINTIFF'S CELLAR. DYE TESTS SHOWED THAT WATER PERCOLATED
FROM DEFENDANT'S PROPERTY INTO PLAINTIFF'S CELLAR, AND SINCE THERE WAS
A CONSIDERABLE AMOUNT OF FREE OIL ON DEFENDANT'S PROPERTY THE COURT
FOUND THAT TO BE THE SOURCE OF OIL ON PLAINTIFF'S PREMISES. THE COURT
HELD THAT THE ABSOLUTE RIGHT A LANDOWNER HAS TO USE UNDERGROUND WATERS
DOES NOT CARRY WITH IT A RIGHT TO MAKE THAT WATER UNUSEABLE FOR OTHERS.
A LANDOWNER'S RIGHTS ARE RESTRICTED WHEN HE KNOWS OR SHOULD KNOW THAT
HIS USE OF HIS LAND WILL CAUSE INJURY TO ANOTHER, THE POLLUTION OF
SUBTERRANEAN WATERS WAS HELD TO BE A NUISANCE WITHOUT A SHOWING OF
NEGLIGENCE. THE RULE THAT REMOVED LIABILITY FOR POLLUTION BROUGHT TO
ANOTHER'S LANDS BY SUBTERRANEAN CURRENTS WAS OVERRULED. ALTHOUGH HE
LEASED THE PROPERTY TO THE OIL COMPANY, DEFENDANT LANDOWNER WAS ALSO
HELD LIABLE BECAUSE HE RENEWED THE LEASE TO DEFENDANT OIL COMPANY
WITHOUT ABATING THE KNOWN NUISANCE.
-------
JACKSON V UNITED STATES PIPE LINE CO (LIABILITY FOR UNDERGROUND OIL SEEPAGE)*
325 PA 436, 191 A 165-166 (1937).
DESCRIPTORS:
*PENNSYLVANIA, *OILY WATER? *PIPELINES, ^LEAKAGE, JUDICIAL DECISIONS*
OlLt OIL INDUSTRY, SUBSURFACE DRAINAGE, WATER POLLUTION SOURCES, PIPES,
CLOSED CONDUITS, METAL PIPES, WELLS, ARTESIAN WELLS, WATER WELLS,
INFLOW, UNDERGROUND, GROUNDWATER, WATER SUPPLY, SEEPAGE, INFILTRATION,
WATER POLLUTION, POLLUTANTS, LEGAL ASPECTS.
ABSTRACT:
DEFENDANT OPERATED A PIPE CARRYING OIL ACROSS PLAINTIFF'S PROPERTY AT A
HIGHER ELEVATION THAN PLAINTIFF'S WATER WELL. UPON DISCOVERING
SUBSTANTIAL AMOUNTS OF OIL IN HIS WELL, PLAINTIFF SUED FOR DAMAGES. THE
COURT FOUND THAT THE EVIDENCE WAS SUFFICIENT TO JUSTIFY A VERDICT IN
FAVOR OF PLAINTIFF, EVEN IN THE ABSENCE OF DIRECT PROOF OF LEAKAGE FROM
DEFENDANT'S PIPE. A SECTION OF THE PIPE THAT WAS REPLACED WAS FOUND TO
HAVE HOLES IN IT, AND SUBSEQUENT TO THE REPLACEMENT THE OIL CONTENT IN
THE WELL WAS SUBSTANTIALLY REDUCED. THE GROUND SLOPED DOWNWARD FROM THE
PIPE TO PLAINTIFF'S WELL, AND THERE WERE NO OTHER POSSIBLE SOURCES FOR
THE OIL IN THE VICINITY. AN EXPERIENCED WELL DRILLER TESTIFIED THAT THE
OIL CAME FROM THE DEFECTIVE PIPE LINE. UNDER THE APPLICABLE STATUTE THE
DEFENDANT WAS HELD TO BE LIABLE WITHOUT A SHOWING OF NEGLIGENCE SINCE
OIL FROM ITS PIPE WAS FOUND TO HAVE POLLUTED THE WELL.
(DOUBERLEY-FLORIDA)
FIELD 05G
ACCESSION NO. W70-07632
58
-------
GROUNDWATER CONTAMINATION,
GUELPH UNIV. (ONTARIO). DEPT. OF SOIL SCIENCE.
ROBERT W. GILLHAM, AND L. R. WEBBER.
WATER AND POLLUTION CONTROL, VOL 106, NO 5, P 54-57, MAY 1968. 5 FIG, 1 TAB,
11 REF.
DESCRIPTORS:
*GROUNDWATER, *PIEZOMETRY, *WATER TABLE, #SURFACE-GROUNDWATER
RELATIONSHIPS, #WATER POLLUTION SOURCES, INFILTRATION, WASTES,
HYDRAULIC CONDUCTIVITY, SUBSURFACE DRAINAGE, TRANSMISSIVITY, HEAD LOSS,
DARCYS LAW, TIME LAG, NITROGEN COMPOUNDS, NITRATES, DISCHARGE
MEASUREMENT, DISCHARGE(WATER), ON-SITE DATA COLLECTIONS, UNDERFLOW.
IDENTIFIERS:
SHYDRAULIC POTENTIAL, CANADA.
ABSTRACT:
ALL INORGANIC SALTS OF N ARE VERY SOLUBLE IN WATER AND N IN THE NITRATE
FORM IS PARTICULARLY HAZARDOUS FOR BOTH HUMANS AND LIVESTOCK. BARNYARDS
AND FEEDLOTS MAY BE PRIME SOURCES OF INORGANIC N IN GROUNDWATER. A
PIEZOMETRIC NETWORK WAS INSTALLED RADIALLY THROUGHOUT A BARNYARD FOR
DETERMINATION OF GROUNDWATER DISCHARGE OUT OF THE BARNYARD SO THAT IT
COULD BE CORRELATED WITH THE CHANGES IN THE N CONCENTRATION OF THE
WATER AS IT PASSED BENEATH THE BARNYARD. THE ACTIVE HEAD OF WATER IN A
GIVEN PIEZOMETER WAS MEASURED AT DIFFERENT TIMES. ITS BASIC TIME LAG,
TOGETHER WITH THE GEOMETRY OF THE PIEZOMETER, COULD BE USED TO
CALCULATE HYDRAULIC CONDUCTIVITIES FROM A LARGE NUMBER OF SITES. THESE
WERE THEN USED TO CONSTRUCT A MAP OF ISOPDTENTIAL LINES INDICATING
CHANGES IN HYDRAULIC POTENTIAL WITH DISTANCE. A SIMPLIFYING ASSUMPTION
WAS THAT HYDRAULIC POTENTIAL DID NOT VARY VERTICALLY IN THE WATER TABLE
TO BEDROCK. TOGETHER WITH N MEASUREMENTS AT VARIOUS DEPTHS TO BEDROCK,
THE RESULTS SHOWED THAT THE BARNYARD CONTRIBUTED 0.00189 LB N/HR TO THE
GROUNDWATER, OR ABOUT 17.5 LB N/YR. THIS WAS CONSIDERED SURPRISINGLY
LOW, SINCE THE MANURE OF A SINGLE COW COULD PRODUCE 74 LB N/YR.
(CASEY-ARIZONA)
FIELD 05B, 04-B
ACCESSION NO. W70-07766
59
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ROSE V SOCONY-VACUUM CORP (NEGLIGENT POLLUTION OF GROUNDWATER).
24 A2D 422-428 (R I 1942).
DESCRIPTORS:
*RHODE ISLAND, ^GASOLINE, ^PERCOLATING WATER, DWELLS, GROUNDWATER, OILY
WATER, OIL INDUSTRY, WATER POLLUTION SOURCES, GROUNDWATER MOVEMENT,
UNDERFLOW, ARTESIAN WELLS, STREAMS, JUDICIAL DECISIONS, POLLUTION
ABATEMENT, POTABLE WATER, STANDARDS, WATER POLLUTION EFFECTS, IMPAIRED
WATER QUALITY, PERCOLATION, PENETRATION, DIFFUSION, SEEPAGE, HOGS,
STORAGE TANKS, WATER SUPPLY.
IDENTIFIERS:
^NUISANCE.
ABSTRACT:
PLAINTIFF OWNED FARMLAND ON WHICH HE RAISED CROPS AND PIGS. DEFENDANT
OWNED A GAS STATION ON ADJOINING LAND. A BREAK OCCURRED IN A PIPELINE
TO A TANK ON DEFENDANT'S PROPERTY AND OVER 800,000 GALLONS OF GAS
ESCAPED INTO THE GROUND. A YEAR AND A HALF LATER PLAINTIFF CLAIMED
GASOLINE APPEARED IN THE WELL ON HIS LAND. IN AN ACTION FOR NUISANCE,
PLAINTIFF ALLEGED THAT THE GASOLINE HAD PERCOLATED IN GROUNDWATERS TO
PLAINTIFF'S PREMISES, POLLUTING HIS WATER SUPPLY AND CAUSING THE DEATHS
OF HIS PIGS. THE COURT FOUND THAT THE DEFENDANT WAS NEGLIGENT IN
HANDLING THE GASOLINE. HOWEVER, IN HOLDING FOR THE DEFENDANT, THE COURT
HELD THE EVIDENCE INSUFFICIENT TO ESTABLISH THAT GASOLINE HAD ENTERED
PLAINTIFF'S WELL AND STREAM OR WAS THE CAUSE OF DEATH OF THE HOGS.
TESTIMONY THAT THE WATER HAD THE TASTE OF GAS, OR AN OILY APPEARANCE,
WAS NOT SUFFICIENT TO PROVE THAT THE GASOLINE SPILLED ON DEFENDANT'S
GROUND HAD INVADED PLAINTIFF'S WATER SUPPLY. MOREOVER, THE EVIDENCE
TENDED TO SHOW THAT THE GROUNDWATER SLOPE FROM DEFENDANT'S PREMISES DID
NOT LEAD IN THE DIRECTION OF PLAINTIFF'S WELL. (HUBENER-FLORI DA)
FIELD 05G
ACCESSION NO. W70-08025
60
-------
JOLOERSMA V MUSKEGON DEVELOPMENT CO (POLLUTION OF WATER SUPPLY BY OIL WELL ON
ADJOINING LAND).
286 MICH 520, 282 NW 229-231 (1938).
DESCRIPTORS:
^MICHIGAN, #OIL WASTES, #PATH OF POLLUTANTS, #SALINE WATER INTRUSION,
WATER POLLUTION, IMPAIRED WATER QUALITY, POLLUTANTS, INDUSTRIAL WASTESt
GROUNDWATER, WATER POLLUTION EFFECTS, LEGAL ASPECTS, JUDICIAL
DECISIONS, GROUNDWATER MOVEMENT, PERCOLATING WATER, SUBSURFACE WATERS,
DIFFUSION, GRAVITATIONAL WATER, SALTS, SALINE SOILS, WASTE STORAGE, OIL
INDUSTRY, OIL FIELDS, OIL.
ABSTRACT:
PLAINTIFFS OWNED A 10 ACRE TRACT OF FARMLAND ON WHICH THEY RAISED
CELERY. DEFENDANTS OPERATED AN OIL WELL ON ADJOINING LAND AND DISPOSED
OF SALT WATER AND OTHER DRILLING REFUSE BY DEPOSITING IT INTO A PIT.
PLAINTIFFS BROUGHT ACTION FOR DAMAGES ALLEGING THAT SALT DEPOSITS WHICH
APPEARED IN THEIR LAND AND WATER SUPPLY, AND WHICH RENDERED PLAINTIFFS1
FARM USELESS FOR RAISING CROPS, CAME FROM DEFENDANTS' PIT. THE COURT
FOUND FOR DEFENDANT, HOLDING INSUFFICIENT PLAINTIFFS' EVIDENCE THAT THE
SALT DEPOSITED ON THEIR LAND WAS DUE TO A SUBTERRANEAN FLOW OF
PERCOLATING WATERS CONTAINING SALT FROM DEFENDANTS' PIT. THE COURT
NOTED THE EXISTENCE OF OTHER WELLS IN THE VICINITY AND CONCLUDED THAT
IT WAS IMPOSSIBLE TO DETERMINE THAT THE DIRECTION OF UNDERGROUND FLOW
LED FROM THE AREA OF THE DEFENDANTS' PIT TO PLAINTIFFS' LAND.
(HUBENER-FLORIDA)
FIELD 05G
ACCESSION NO. W70-08026
61
-------
LIABILITY FOR POLLUTION OF SUBTERRANEAN WATERS.
38 ALR20 1265-1306 (1954).
DESCRIPTORS:
^PERCOLATING WATER, #WATER POLLUTION, ^SEEPAGE, ^SUBSURFACE WATERS,
PRIOR APPROPRIATION, GROUNDWATER, UNDERGROUND STREAMS, SUBSURFACE
RUNOFF, REASONABLE USE, DAMAGES, SURFACE RUNOFF, GASOLINE, WATER
POLLUTION SOURCES, MINE WATER, OIL WASTES, CESSPOOLS, SEWAGE DISPOSAL,
DOMESTIC WASTES, FARM WASTES, MUNICIPAL WASTES, NATURAL GAS, SALINE
WATER INTRUSION, JUDICIAL DECISIONS, LEGAL ASPECTS, MINE ACIDS, DEEP
PERCOLATION, WATER POLLUTION CONTROL.
IDENTIFIERS:
CEMETERIES.
ABSTRACT:
CONSIDERED HEREIN IS THE LIABILITY IN DAMAGES FOR, OR THE ENJOINING OF,
THE POLLUTION OF SUBTERRANEAN WATERS. A DEFINITIONAL SECTION EXPLAINS
THE TERMS USED IN THE ANNOTATION. VARIOUS ASPECTS OF THE RIGHTS AND
LIABILITIES OF PARTIES WHO POLLUTE SUBTERRANEAN OR PERCOLATING WATERS
FORM THE BULK OF THIS WORK. MAJOR CASES IN VARIOUS JURISDICTIONS ARE
CITED AS AUTHORITY FOR THE PROPOSITIONS PRESENTED IN THE BODY OF THE
TEXT. GENERALLY, THE AREAS CONSIDERED ARE: (1) LIABILITY FOR THE
POLLUTION OF WATERS WHETHER PERCOLATING OR IN SUBTERRANEAN STREAMS; (2)
THE RIGHT TO ENJOIN THE CONTINUANCE OF AN EXISTING OR A POSSIBLE FUTURE
POLLUTION; (3) WHETHER LIABILITY EXISTS UNDER A CHARGE OF NEGLIGENCE OR
NUISANCE; K) THE SOURCES OF POLLUTION OF SUBTERRANEAN WATERS INCLUDING
REFINERIES, CESSPOOLS, PRIVIES, OIL AND GAS WORKS, SALINE INTRUSION,
MUNICIPAL WASTES, MANURE, DEAD ANIMALS AND THE LIKE; AND (5)
INJUNCTIONS AGAINST THE ESTABLISHMENT OF CEMETERIES IF POLLUTION IS
LIKELY TO RESULT. A DISTINCTION IS MADE BETWEEN THE AMERICAN RULE OF
REASONABLE USE AND THE ENGLISH RULE OF ABSOLUTE OWNERSHIP. (SEE ALSO
W70-08050 AND WTO-08051). (BARNETT-FLQRIDA)
FIELD 05G
ACCESSION NO. W70-08049
62
-------
LIABILITY FOR POLLUTION OF SUBTERRANEAN WATERS (THE DISTINCTION BETWEEN
SUBTERRANEAN STREAMS AND PERCOLATING WATERS).
38 ALR2D P 1269-1272 (1954)
DESCRIPTORS:
^PERCOLATING WATER, *WATER POLLUTION, ^SEEPAGE, ^SUBSURFACE WATERS,
GROUNDWATER, UNDERGROUND STREAMS, SUBSURFACE RUNOFF, REASONABLE USE,
PRIOR APPROPRIATION, WATER POLLUTION SOURCES, JUDICIAL DECISIONS, LEGAL
ASPECTS, DEEP PERCOLATION.
ABSTRACT:
WITH REGARD TO LIABILITY FOR THEIR POLLUTION, A CLEAR DISTINCTION IS
MADE BETWEEN WELL-DEFINED SUBTERRANEAN STREAMS AND PERCOLATING WATERS.
THE GENERAL RULE IS THAT THE OWNER OF LAND ABUTTING ON A SURFACE STREAM
MAY NOT POLLUTE IT TO THE INJURY OF OTHER RIPPARIAN OWNERS. THIS SAME
RULE WAS FOUND APPLICABLE IN RHODE ISLAND TO SUBTERRANEAN STREAMS
FOLLOWING A WELL-DEFINED COURSE, BUT NOT SO FOR WATERS PASSING BY
PERCOLATION OR SEEPAGE. IN MICHIGAN, AN INADVERTENT AND NON-NEGLIGENT
POLLUTION OF SUBTERRANEAN WATERS WAS HELD TO BE NOT ACTIONABLE. THE
PROBLEM OF DIFFERENTIATION BETWEEN 'FLOW AND SEEPAGE' IS DISCUSSED WITH
REGARD TO LIABILITY FOR POLLUTION OF A WELL BY SEEPAGE WHERE A CONTRAST
WAS DRAWN ONLY TO IMPOSE LIABILITY FOR THE FLOW OF CERTAIN WATERS. (SEE
ALSO W70-08049 AND W70-08051). (BARNETT-FLORIDA)
FIELD 05G
ACCESSION NO. W70-08050
63
-------
NITRATE CONTENT OF THE UPPER RIO GRANDE AS INFLUENCED BY NITROGEN FERTILIZATION
OF ADJACENT IRRIGATED LANDS,
AGRICULTURAL RESEARCH SERVICE, RIVERSIDE, CALIF. SALINITY LAB.; BUREAU OF
RECLAMATION, EL PASO, TEX.; AND INTERNATIONAL BOUNDARY AND WATER
COMMISSION, EL PASO, TEX.
C. A. BOWER, AND L. V. WILCOX.
SOIL SCIENCE SOCIETY OF AMERICA PROCEEDINGS, VOL 33, NO 6, 1969. 1 FIG, 3
TAB, 11 REF.
DESCRIPTORS:
^NITRATES, ^NITROGEN, *RIO GRANDE, ^SUBSURFACE DRAINAGE, DRAINAGE
WATER, SALINITY, FERTILIZERS, GROUNDWATER, IRRIGATION EFFECTS,
LEACHING, DENITRIFICATION, RIVER FLOW, WATER POLLUTION SOURCES.
IDENTIFIERS:
UPPER RIO GRANDE, SALT BALANCE.
ABSTRACT:
AN ANALYSIS OF SALT BALANCE CONDITIONS ON THREE IRRIGATED AREAS ALONG
UPPER RIO GRANDE BETWEEN 1934-1963 IS SUMMARIZED. NITRATE CONTENT OF
WATER BEFORE IRRIGATION AND OF DRAINAGE WATER WAS OF SPECIFIC INTEREST.
DURING 30-YEAR PERIOD AMOUNT OF NITROGEN FERTILIZER APPLIED INCREASED
BY 35- TO 100-FOLD. DECREASING ANNUAL RIVER FLOWS WERE MAJOR CAUSE OF
SIGNIFICANT INCREASE OF AVERAGE ANNUAL NITRATE LOAD OF RIVER BETWEEN
1954-1963 PERIOD. INCREASED USE OF NITROGEN FERTILIZER IN THREE AREAS
HAS NOT INCREASED OVERALL NITRATE NITROGEN IN UPPER RIO GRANDE. EL PASO
VALLEY HAS SLIGHTLY INCREASED RIVER NITRATE NITROGEN DUE TO VERY LOW
FLOWS AND SEWAGE EFFLUENT. INSIGNIFICANT CONTRIBUTION OF NITRATE
NITROGEN LOAD TO RIVER FROM RINCON AND MESILLA VALLEYS WAS RESULT OF
DENITRIFICATION OF LEACHED NITRATE NITROGEN UNDER ANAEROBIC CONDITIONS
IN WATER SATURATED SOIL. (BANNERMAN-WI SCONS IN)
FIELD 05B
ACCESSION NO. W70-08662
64
-------
LEACHING FROM SIMULATED LANDFILLS,
BATTELLE MEMORIAL INST., COLUMBUS, OHIO; AND WEST VIRGINIA UNIV., MORGANTOWN.
DEPT. OF CIVIL ENGINEERING.
SYED R. OASIM, AND JERRY C. BURCHINAL.
JOURNAL WATER POLLUTION CONTROL FEDERATION, VOL 42, NO 3, PART 1, P 371-379,
MARCH 1970. 9 P, 10 FIG, 4 TAB, 8 REF. USPHS GRANT EF-40(R1).
DESCRIPTORS:
BLEACHING, ^LANDFILLS, #PERCOLATION, *GROUNDWATER MOVEMENT, MODEL
STUDIES, LABORATORY TESTS, PATH OF POLLUTANTS, WATER POLLUTION SOURCES,
SELF-PURIFICATION, B IODEGRADATION.
IDENTIFIERS:
SIMULATED LANDFILL.
ABSTRACT:
SIMULATED LANDFILLS 3 FT IN DIAM AND 4 TO 16 FT IN HEIGHT WERE FILLED
WITH MIXED MUNICIPAL REFUSE. THE CYLINDERS WERE SATURATED WITH WATER
AND ADDITIONAL WATER ADDED AT TWO-WEEK INTERVALS. PERCOLATED WATER WAS
DRAINED AND ANALYZED ON A REGULAR SCHEDULE FOR CHEMICAL AND BACTERIAL
QUALITY. THE STUDY COVERED A MAXIMUM OF 163 DAYS. CONCENTRATION OF
EXTRACTED MATERIAL INCREASED INITIALLY BUT BEGAN TO DECREASE AFTER
ABOUT FOUR WEEKS. ANOTHER INCREASE AFTER EIGHT WEEKS WAS EVIDENT. THE
CONCENTRATION IN THE LEACHATE OF 18 ORGANIC AND INORGANIC COMPOUNDS
OVER THE PERIOD OF THE STUDY IS REPORTED. PH SHOWED A SLIGHT INCREASE
FOLLOWED BY A RAPID DECREASE. LEACH SAMPLES TEND TO UNDERGO
BACTERIOLOGICAL AND CHEMICAL SELF-PURIFICATION. DEEPER FILLS CONSUME
MORE WATER, BEFORE LEACHING OCCURS, TAKE A LONGER TIME TO DECOMPOSE,
AND THE BULK OF THE EXTRACTED MATERIAL IS DISTRIBUTED OVER A LONGER
PERIOD. (KNAPP-USGS)
FIELD 05B
ACCESSION NO. W70-09548
65
-------
HYDROGEOLOGY OF SOLID WASTE DISPOSAL SITES IN NORTHEASTERN ILLINOIS,
ILLINOIS STATE GEOLOGICAL SURVEY, URBANA.
G. M. HUGHES, R. A. LANDON, AND R. N. FARVOLDEN.
AVAILABLE FROM BUREAU OF SOLID WASTE MANAGEMENT, 5555 RIDGE AVE, CINCINNATI,
OHIO, 45213. U. S. DEPARTMENT OF HEALTH, EDUCATION, AND WELFARE, BUREAU OF
SOLID WASTE MANAGEMENT, 1969. 137 P, 24 ILLUS, 9 TABS, 3 REF. NO. DO 1 - UI
- 00006.
DESCRIPTORS:
^'HYDROGEOLOGY, *SOLID WASTES, ^LANDFILL, #1NFILTRAT ION, #WATER QUALITY
POLLUTION, RECHARGE, DISCHARGE, GROUNDWATER, SURFACE WATERS, AQUIFERS^
FLOW RATES, LEACHING.
IDENTIFIERS:
NORTHEASTERN ILLINOIS.
ABSTRACT:
THIS PROJECT DESCRIBES THE HYDROGEOLOGIC ENVIRONMENTS IN THE VICINITY
OF FOUR EXISTING LANDFILL SITES IN THE CHICAGO METROPOLITAN AREA, IN
ORDER TO DETERMINE THE CONTROLS ON THE MOVEMENT OF THE GROUND WATER AND
THE SOLIDS DISSOLVED IN GROUND WATER. GROUNDWATER RECHARGE AND
DISCHARGE AREAS ARE DEFINED AND THE QUANTITIES OF WATER MOVED AND RATES
OF MOVEMENT THROUGH VARIOUS MATERIALS AND IN VARIOUS ENVIRONMENTS HAVE
BEEN ESTIMATED. INFORMATION FROM THIS PRELIMINARY STUDY CAN BE USED BY
REGULATORY AGENCIES TO HELP DETERMINE ENVIRONMENTS MOST SUITABLE FOR
NEAR-SURFACE DISPOSAL OF WASTE INSOFAR AS CONTAMINATION OF GROUNDWATER
AND SURFACE WATER IS CONCERNED. THE PROBLEM OF GROUNDWATER
CONTAMINATION BY NEAR-SURFACE SOLID WASTE DISPOSAL IS APPROACHED IN
TERMS OF THE HYDROGEOLOGIC ENVIRONMENT. IN SOME SITES, WATER THAT
INFILTRATES THE GROUND BECOMES PART OF A LOCAL FLOW SYSTEM AND IS
DISCHARGED INTO A NEARBY STREAM OR SWAMP WITH LITTLE RISK OF
CONTAMINATING AN AQUIFER. IN OTHER SITES THIS WATER BECOMES PART OF A
REGIONAL FLOW SYSTEM AND MAY ENTER PRODUCTIVE AQUIFERS WITH DEFINITE
RISK OF CONTAMINATION. THE DEFINITION OF FLOW SYSTEMS IN HOMOGENEOUS
MATERIALS IS RELATIVELY SIMPLE; HOWEVER, THE EFFECTS ON THIS FLOW
SYSTEM OF CHANGES FROM ONE GEOLOGIC MATERIAL TO ANOTHER ARE MORE
DIFFICULT TO EVALUATE. THIS INFORMATION IS NECESSARY IF MOVEMENT OF
REFUSE LEACHATE FROM PROPOSED DISPOSAL SITES IS TO BE PREDICTED.
(MARRIOTT-CHICAGO)
FIELD 05B, 04C
ACCESSION NO. W70-09637
66
-------
ENVIRONMENTAL POLLUTION FROM HIGHWAY DEICING COMPOUNDS,
MAINE UNIV., QRONO. DEPT. OF PLANT AND SOIL SCIENCES.
F. E. HUTCHINSON.
JOURNAL OF SOIL AND WATER CONSERVATION, VOL 25, NO 4, P 144-146, JULY-AUGUST
1970. 3 P, 1 FIG, 3 TAB, 7 REF. OWRR PROJECT A-007-ME.
DESCRIPTORS:
#WATER POLLUTION EFFECTS, #SODIUM CHLORIDE, ^HIGHWAY ICING, *SNOW
REMOVAL, *MAINE, DEICERS, ROADS, CHEMCONTROL, SALTS, GROUNDWATER,
LEACHING, SALINE SOILS, SALINE WATER.
IDENTIFIERS:
HIGHWAY ICE REMOVAL.
ABSTRACT:
DURING THE PERIOD 1965-1969, A STUDY WAS MADE TO DETERMINE WHAT
ENVIRONMENTAL POLLUTION, IF ANY, RESULTED FROM THE AVERAGE ANNUAL
APPLICATION OF 25 TONS OF SODIUM CHLORIDE TO EACH MILE OF PAVED HIGHWAY
IN MAINE. ANALYSES OF WATER SAMPLES INDICATED THAT WELLS AND FARM PONDS
WERE SERIOUSLY CONTAMINATED WITH CHLORIDE IONS. SOIL SAMPLE ANALYSES
REVEALED THAT SOILS CONTIGUOUS TO HIGHWAYS CONTAINED SODIUM LEVELS THAT
THREATEN VEGETATION AND SOIL DRAINAGE. CONCENTRATIONS OF THESE IONS IN
RIVERS APPARENTLY WERE NOT INFLUENCED BY THIS PRACTICE. (KNAPP-USGS)
FIELD 05C
ACCESSION NO. W70-09844
67
-------
FLOW FROM A SPHERICAL SOURCE WITH WATER CONTENT DEPENDENT DIFFUSIVITY,
SAN JOSE STATE COLL., CALIF.
RAMESHWAR SINGH.
WATER RESOURCES RESEARCH, VOL 6,
1 TAB, 8 REF.
NO 4, P 1140-1147, AUGUST 1970. 8 P, 3 FIG,
DESCRIPTORS:
*WATER POLLUTION SOURCES, *PATH OF POLLUTANTS, ^DIFFUSION, #SOIL WATER
MOVEMENT, ^RADIOACTIVE WASTES, EQUATIONS, GROUNDWATER MOVEMENT,
LEACHING, MATHEMATICAL MODELS, MIXING, RADIOACTIVE WASTE DISPOSAL,
UNSATURATED FLOW, SATURATED FLOW, ADSORPTION, ADSORPTION, ION TRANSPORT
IDENTIFIERS:
SPHERICAL DIFFUSIVITY.
ABSTRACT:
LEAKAGE OF MOISTURE FROM UNDERGROUND BURIED SOURCES CAN OCCUR BECAUSE
OF CRACKING OR DETERIORATION OF CONTAINERS. LEAKING MOISTURE CAN BE
RADIOACTIVE OR CONTAMINATED AND MAY ENDANGER PUBLIC HEALTH. IN DISPOSAL
OF SUCH SUBSTANCES UNDERGROUND, CONSIDERATION MUST BE GIVEN TO THE
EXTENT OF DISPERSAL OF MOISTURE FROM WET CONTAINERS IN CASE OF
ACCIDENTS. THE MOVEMENT OF MOISTURE FROM A SPHERICAL BURIED SOURCE INTO
PARTIALLY SATURATED SURROUNDINGS IS DESCRIBED BY A NONLINEAR PARTIAL
DIFFERENTIAL EQUATION. COMPLEXITY OF THE EQUATION PREVENTS OBTAINING AN
EXPLICIT SOLUTION OF THE PROBLEM; HOWEVER, AN APPROXIMATE SOLUTION MAY
BE EXTRACTED BY THE METHOD OF WEIGHTED RESIDUALS. THE TECHNIQUE CALLS
FOR REPRESENTING THE SOLUTION WITH A POLYNOMIAL IN SPACE VARIABLE THAT
HAS ITS COEFFICIENTS AS UNKNOWN FUNCTIONS OF TIME, TO BE DETERMINED
FROM THE CONDITIONS AND BY SATISFYING THE EQUATION BY AVERAGING OVER
THE RANGE OF SPACE-VARIABLE. THIS PROCEDURE ACCEPTS ANY KIND OF
DIFFUSIVITY FUNCTION INCLUDING NUMERICAL VALUES OBTAINED FROM
EXPERIMENTS. THE METHOD IS SIMPLE IN ITS APPLICATION AND PRODUCES
RESULTS THAT COMPARE WELL WITH THE KNOWN SOLUTION. (KNAPP-USGS)
FIELD 05B, 02G
ACCESSION NO. W7Q-10058
68
-------
EFFECTS OF A CONCENTRATED ACID ON WATER CHEMISTRY AND WATER USE IN A
PLEISTOCENE OUTWASH AQUIFER*
GEOLOGICAL SURVEY* LOUISVILLE, KY. WATER RESOURCES DIV.
HAYES F. GRUBB.
GROUNDWATER, VOL 8, NO 5* P 4-7, SEPTEMBER-OCTOBfcK 1970. 4 P, 9 FIG, 2 TAB, 3
REF.
DESCRIPTORS:
#WATER POLLUTION SOURCES, ^INDUSTRIAL WASTES, *GROUNDWATER MOVEMENT,
^RECHARGE, *SURFACE-GROUNDWATER RELATIONSHIPS, MALENCLAVES, PATH OF
POLLUTANTS, ACIDS, LEACHING, CHLORIDES, GLACIAL DRIFT, AQUIFERS, OHIO
RIVER, KENTUCKY.
IDENTIFIERS:
HYDROCHLORIC ACID.
ABSTRACT:
A BREAK IN A WASTE-DISCHARGE LINE AT THE SAME TIME AS A 49-FOOT RISE IN
STAGE OF THE OHIO RIVER IN MARCH 1967 ALLOWED HYDROCHLORIC ACID TO
ENTER THE PLEISTOCENE OUTWASH AQUIFER USED BY A KENTUCKY INDUSTRY.
CHLORIDE CONCENTRATIONS IN EXCESS OF 30,000 MG/LITER WERE OBSERVED IN
THE WATER DISCHARGED FROM THE INDUSTRIAL WELL NEAREST THE BREAK IN THE
WASTE-DISCHARGE LINE. BY MARCH 1968, THE WELL NEAREST THE ACID SOURCE
WAS ABANDONED, THE REMAINING TWO WELLS NEAR THE RIVER WERE USED IN A
SUPPLEMENTAL CAPACITY AND A FOURTH WELL 1,500 FEET FROM THE RIVER PLUS
A NEW WELL WERE THE PRIMARY WATER SOURCES. FLUCTUATIONS OF CHLORIDES IN
AN INDUSTRIAL WELL NEAR THE RIVER FOR A 16-MONTH PERIOD INDICATE A
PERSISTENT BODY OF HIGHLY MINERALIZED WATER NEAR THE ACID. SOURCE.
MOVEMENT OF THIS WATER BODY APPEARS TO BE REGULATED AT Lo'w RIVER STAGES
BY THE INCLINED SURFACE OF THE NEW ALBANY SHALE BEDROCK. (KNAPP-USGS)
FIELD 05B* 05C
ACCESSION NO. W71-00194
69
-------
SCHLICHTKRULL V MELLON-POLLOCK OIL CO (ILLNESS CAUSED BY POLLUTION OF WELL).
301 PA 560, 152 A 832-834 (1930).
DESCRIPTORS:
^PENNSYLVANIA, *WATER POLLUTION, *SALINE WATER INTRUSION, *WATER WELLS,
OIL INDUSTRY, PUBLIC HEALTH, OIL WELLS, DRILLING, OIL FIELDS, SALINE
WATER, SALINE WATER-FRESHWATER INTERFACES, WELLS, WELL CASINGS,
GROUNDWATER, WATER SUPPLY, PERCOLATING WATER, SUBSURFACE WATERS,
JUDICIAL DECISIONS, LEGAL ASPECTS, ADJUDICATION PROCEDURE.
ABSTRACT:
PLAINTIFF LANDOWNER BROUGHT SUIT FOR DAMAGES AGAINST DEFENDANT OIL
COMPANY. DEFENDANT HAD DRILLED AN OIL WELL AND THEREBY CAUSED SALT TO
ACCUMULATE IN PLAINTIFF'S WATER WELL. PLAINTIFF'S WIFE BECAME ILL AND
PLAINTIFF CLAIMED THE ILLNESS WAS CAUSED BY THE SALT IN THE WATER. THE
SUPREME COURT OF PENNSYLVANIA, REVERSING THE TRIAL COURT'S DECISION FOR
PLAINTIFF, RULED THAT BEFORE AN ACTION FOR NEGLIGENCE IN DRILLING AN
OIL WELL WOULD LIE, DANGER TO PUBLIC HEALTH MUST HAVE BEEN FORESEEABLE.
PLAINTIFF HAD NOT MET THE BURDEN OF PROOF REQUISITE TO SUCH AN ACTION.
(BARKER-FLORIDA)
FIELD 06E, 05C
ACCESSION NO. W71-01028
70
-------
ROSE V SOCONY-VACCUUM CORP (POLLUTION OF STREAMS BY SUBSTANCES IN GROUNDWATER).
173 A 627-632 (RI 1934).
DESCRIPTORS:
#RHODE ISLAND, ^SEEPAGE, *WATER POLLUTION, ^PERCOLATING WATER, RIPARIAN
RIGHTS, RELATIVE RIGHTS, WATER POLLUTION EFFECTS, STREAMS, GROUNDWATER,
JUDICIAL DECISIONS, LEGAL ASPECTS, RIPARIAN LAND, PERCOLATION,
SUBSURFACE WATERS, UNDERGROUND STREAMS, GROUNDWATER MOVEMENT, PATH OF
POLLUTANTS, SOIL WATER MOVEMENT, OILY WATER, OIL WASTES, WATER
POLLUTION SOURCES.
ABSTRACT:
DEFENDANT OPERATED A REFINERY ON PROPERTY ADJACENT TO THAT OF
PLAINTIFF. ON PLAINTIFF'S PROPERTY WERE A WELL A' D A STREAM USED BY
PLAINTIFF TO WATER HIS PIGS AND HENS. COLLECTION OF PETROLEUM PRODUCTS
ON DEFENDANT'S LAND ENTERED PERCOLATING WATERS BENEATH THE LAND AND
THEREBY PASSED TO THE WATER SOURCES ON PLAINTIFF'S LAND. THIS RENDERED
THE WATER UNFIT FOR ANIMAL CONSUMPTION AND CAUSED THE DEATH OF NUMBERS
OF PLAINTIFF'S POULTRY AND LIVESTOCK. PLAINTIFF SOUGHT DAMAGES AND AN
INJUNCTION, ALLEGING THAT DEFENDANT WAS PERPETUATING A NUISANCE ON HIS
PROPERTY. NO NEGLIGENCE WAS ALLEGED. DEFENDANT'S DEMURRER WAS
SUSTAINED, AND THE APPELLATE COURT AFFIRMED, REJECTING THE DOCTRINE OF
RYLANDS V FLETCHER AND STATING THAT NEGLIGENCE MUST BE SHOWN FOR
RECOVERY WHERE POLLUTION IS SPREAD BY PERCOLATING WATERS. THE RULE THAT
ONE RIPARIAN OWNER MAY NOT INJURE ANOTHER'S USE OF THE WATER WAS HELD
TO APPLY TO SURFACE STREAMS AND NOT TO PERCOLATING WATERS, WHERE THE
LOCATION AND COURSE OF THE WATER IS GENERALLY UNKNOWN. (DYE-FLORIDA)
FIELD 06E, 05B
ACCESSION NO. W71-01043
71
-------
LEACHATE MOVEMENT IN THE SUB-SOIL BENEATH A SANITARY LANDFILL TRENCH TRACED BY
MEANS OF SUCTION LYSIMETERS,
PENNSYLVANIA STATE UNIV., UNIVERSITY PARK. DEPT. OF GEOLOGY AND GEOPHYSICS.
BURKE E. LANE, AND RICHARD R. PARIZEK.
PROCEEDINGS OF THE 2ND MID-ATLANTIC INDUSTRIAL WASTE CONFERENCE, NOVEMBER
18-20, 1968, DREXEL INSTITUTE OF TECHNOLOGY, P 261-277, 1968. 17 P, 11 FIG,
1 REF.
DESCRIPTORS:
*PATH OF POLLUTANTS, BLEACHING, ^LANDFILLS, ^GARBAGE DUMPS,
*GROUNDWATER MOVEMENT, KARST, INFILTRATION, ION TRANSPORT,
PENNSYLVANIA, SUBSURFACE DRAINAGE, WATER QUALITY, WATER POLLUTION
SOURCES, LYSIMETERS.
IDENTIFIERS:
STATE COLLEGE(PENN), SANITARY LANDFILL DRAINAGE.
ABSTRACT:
THE LANDFILL SITE LIES ABOUT 2 MILES NORTHWEST OF STATE COLLEGE. THE
LANDFILLING OPERATION IS ON STEEP HILLSIDES. THE TOPS OF THE VALLEY
WALLS ARE ABOUT 100 FEET HIGH AND THE SLOPES APPROACH 40 DEGREES NEAR
THE VALLEY BOTTOM. THE VALLEY BOTTOM IS A DRY, UNDERDRAINED KARST
STREAM BED. GROUNDWATER EXISTS UNDER WATER TABLE CONDITIONS AT A DEPTH
OF ABOUT 250 FEET. THE WATER QUALITY MONITORING SYSTEM CONSISTED OF A
900 SQUARE-FOOT SHEET OF PLASTIC TO LINE THE BOTTOM OF A LANDFILL
TRENCH, A SPREADER PIPE IN AN INFILTRATION TRENCH, AND A PROTECTIVE
HOUSING. THE SOIL WATER SAMPLING DEVICES CONSISTED OF 17 SUCTION
LYSIMETERS INSTALLED AT VARIOUS DEPTHS IN THE SOIL BENEATH THE LANDFILL
TRENCH. MOVEMENT OF A WAVE FRONT OF LEACHATE-POLLUTED SOIL WATER COULD
BE TRACED IN THE SOIL BENEATH THE LANDFILL TRENCH. SEVERE POLLUTION OF
THE SOIL WATER IN THE IMMEDIATE VICINITY OF A LANDFILL CAN RESULT EVEN
THOUGH THE LANDFILL IS NOT IN DIRECT CONTACT WITH A WATER TABLE AND
EVEN BEFORE THE REFUSE HAS BECOME SATURATED TO FIELD CAPACITY.
(KNAPP-USGS)
FIELD 05B, 02G
ACCESSION NO. W71-01204
72
-------
FURTHER CONSIDERATIONS ON INLAND SEWAGE DISPOSAL IN FALMOUTH, MASSACHUSETTS,
GEOLOGICAL SURVEY, WOODS HOLE, MASS.
ROBERT H. MEADE.
WOODS HOLE OCEANOGRAPHIC INSTITUTION TECHNICAL REPORT, REFERENCE NO 70-42,
SEPTEMBER 1970. 24 P, 5 FIG, 2 TAB, 6 REF. 3 APPEND. (UNPUBLISHED
MANUSCRIPT).
DESCRIPTORS:
#SEWAGE DISPOSAL, -^INFILTRATION, #WATER SPREADING, ^MONITORING, WATER
POLLUTION SOURCES, SEWAGE TREATMENT, WASTE WATER DISPOSAL, NITRATES,
EUTROPHICATION, AQUIFERS, GROUNDWATER MOVEMENT, MASSACHUSETTS.
IDENTIFIERS:
INFILTRATION PONDS, CAPE COD(MASS), FALMOUTH(MASS>.
ABSTRACT:
IF THE TOWN OF FALMOUTH, MASS., DECIDES TO DISPOSE OF SECONDARY-TREATED
SEWAGE EFFLUENT AT AN INLAND SITE, THE GROUNDWATERS DOWNSTREAM OF THE
DISPOSAL SITE SHOULD BE MONITORED CAREFULLY, AND ADEQUATE SPACE AND
ACCESS FOR MORE ADVANCED WASTE-TREATMENT FACILITIES SHOULD BE INCLUDED
IN THE PLANT IN CASE THE MONITORING SHOWS THAT DELETERIOUS SUBSTANCES
ARE BEGINNING TO CONTAMINATE THE GROUNDWATER. THE PRESENT INLAND SEWAGE
DISPOSAL PLANT AT OTIS AIR FORCE BASE HAS NO SIGNIFICANT EFFECT ON
GROUNDWATER QUALITY AT ITS PRESENT LOW LEVEL OF OPERATIONS. EFFLUENT
FROM A PROPOSED INLAND SITE COULD CONTAMINATE NEARLY GROUNDWATER AND
CONTRIBUTE TO THE OVERFERTILIZATION OF ESTUARIES IN SOUTHERN FALMOUTH.
DISPOSAL OF 3.7 MGD OF EFFLUENT THROUGH A SEA OUTFALL COULD RESULT IN A
GENERAL DECLINE IN GROUNDWATER LEVELS OF 3 TO 5 INCHES; THEREFORE,
CAREFUL DISPOSAL BY RECHARGE IS RECOMMENDED TO CONSERVE GROUNDWATER.
(KNAPP-USGS)
FIELD 05E, 05B
ACCESSION NO. W71-01205
73
-------
CONSIDERATIONS ON INLAND SEWAGE DISPOSAL IN FALMOUTH, MASSACHUSETTSf
WOODS HOLE OCEANOGRAPHIC INSTITUTION, MASS.
ROBERT H. MEADE, AND RALPH F. VACCARO.
TECHNICAL REPORT, REFERENCE NO 70-3, FEBRUARY 1970. 22 P, 4 FIG, 1 TAB, 9
REF, 2 APPEND. (UNPUBLISHED MANUSCRIPT).
DESCRIPTORS:
^INFILTRATION, *WATER SPREADING, ^MONITORING, WATER POLLUTION SOURCES,
SEWAGE TREATMENT, WASTE WATER DISPOSAL, NITRATES, EUTROPHICAT ION,
AQUIFERS, GROUNDWATER MOVEMENT, MASSACHUSETTSr
IDENTIFIERS:
INFILTRATION PONDS, CAPE COD(MASS), FALMOUTH(MASS).
ABSTRACT:
THE CONSEQUENCES ARE CONSIDERED OF DISPOSING OF SECONDARY TREATED
EFFLUENT FROM THE TOWN OF FALMOUTH, MASS., BY INFILTRATION INLAND SITES
RATHER THAN BY MARINE OUTFALLS. FOR THE TERMINAL DISPOSAL OF TREATED
SEWAGE cFFLUENTS, TRANSFER INTO THE GROUND CAN BE AN ACCEPTABLE AND
EFFECTIVE METHOD. VERY MANY SEWAGE TREATMENT PLANTS OPERATE IN THIS
MANNER. IN MANY INSTANCES, SUCH PRACTICE ENHANCES WATER CONSERVATION BY
HELPING MAINTAIN GROUNDWATER RESERVES. HOWEVER, IN TOWNS SUCH AS
FALMOUTH, WHICH DEPEND UPON GROUNDWATER FOR POTABLE WATER, GREAT CARE
MUST BE TAKEN TO ASSURE THAT RECHARGING DOES NOT CAUSE ANY UNDUE
CONTAMINATION OF THE LOCAL GROUNDWATER SYSTEM. NITRATE IS ONE OF THE
MORE UNPREDICTABLE BY-PRODUCTS OF SEWAGE TREATMENT AND ITS ULTIMATE
APPEARANCE IN NATURAL WATERS CAN HAVE AN ADVERSE EFFECT ON WATER
QUALITY. EXCESSIVE AMOUNTS OF NITRATE, IN CONJUNCTION WITH OTHER PLANT
NUTRIENTS, CAN LEAD TO UNSIGHTLY BLOOMS OF NUISANCE AQUATIC PLANTS ONCE
EXPOSURE TO SUNLIGHT IS PROVIDED. ADEQUATE ALLOWANCE FOR THIS
UNCERTAINTY SHOULD BE PROVIDED AT THE PLANNING STAGES OF ANY INLAND
SEWAGE DISPOSAL PLANT WHICH DEPENDS UPON TERMINAL DISPOSAL INTO THE
GROUND. AN EARLY-WARNING MONITORING SYSTEM OF OBSERVATION WELLS NEAR
THE DISPOSAL SITE IS RECOMMENDED TO DETECT ANY INCIPIENT CONTAMINATION
PROBLEM BEFORE IT BECOMES SERIOUS. (KNAPP-USGS)
FIELD 05E, 05B
ACCESSION NO. W71-01324
74
-------
SEPARATION OF OIL AND WATER WITH GRAVITY SEPARATOR (FRENCH),
LAVAL UNIV., QUEBEC; AND HYDRAULIC RESEARCH INST., BRATISLAVA
(CZECHOSLOVAKIA).
K. ROHAN, AND M. ZAJDLIK.
ENGLISH SYNOPSIS. IN: PROCEEDINGS 13TH CONGRESS OF THE INTERNATIONAL
ASSOCIATION FOR HYDRAULIC RESEARCH, KYOTO, JAPAN, AUGUST 31-SEPTEMBER 5,
1969, VOL 2 (SUBJECT B), SCIENCE COUNCIL OF JAPAN, KYOTO, P 177-189, 1969.
13 P, 6 FIG, 2 TAB, 5 REF.
DESCRIPTORS:
*WATER POLLUTION, *GROUNDWATER, #01L WASTES, ^SEPARATION TECHNIQUES,
INFILTRATION, MODEL STUDIES, MATHEMATICS, EQUATIONS, PATH OF
POLLUTANTS, FOREIGN PROJECTS.
IDENTIFIERS:
^HYDRAULICS LABORATORY OF BRATISLAVA^CZECHOSLOVAK!A).
ABSTRACT:
THIS PAPER GIVES THE TEST RESULTS AND COMPUTATION METHODS USED IN THE
HYDRAULICS LABORATORY OF BRATISLAVA, CZECHOSLOVAKIA, CONCERNING OIL AND
WATER MIXTURES WITH EMPHASIS ON PROTECTION OF GROUNDWATER SUPPLIES
AGAINST POLLUTION FROM OIL PENTRATION. RELATED EQUATIONS AND GRAPHS ARE
INCLUDED. IT IS POSSIBLE TO UTILIZE GRAVITY SEPARATORS BECAUSE WATER
AND OIL USUALLY DO NOT CREATE EMULSIONS. (WOQDARD-USGS)
FIELD 05G, 05B, OAB
ACCESSION NO. W71-01930
75
-------
REMOVAL OF SALINE WATER FROM AQUIFERSt
BUREAU OF RECLAMATION, DENVER, COLO. OFFICE OF CHIEF ENGINEER.
E. J. CARLSON, AND P. F. ENGER.
FRENCH RESUME. IN: PROCEEDINGS 13TH CONGRESS OF THE INTERNATIONAL ASSOCIATION
FOR HYDRAULIC RESEARCH, KYOTO, JAPAN, AUGUST 31-SEPTEMBER 5, 1969, VOL 4
(SUBJECT 0), SCIENCE COUNCIL OF JAPAN, KYOTO, P 121-134, 1969. 14 P, 4 FIG,
1 TAB, 16 REF.
DESCRIPTORS:
*SALINE WATER-FRESH-WATER INTERFACES, BLEACHING, *SALINE WATER SYSTEMS,
*GROUNDWATER MOVEMENT, DRAINAGE SYSTEMS, HYDRAULIC MODELS, MATHEMATICAL
MODELS, AQUIFERS, MODEL STUDIES, DRAINAGE PROGRAMS, SUBSURFACE
DRAINAGE, WATER MANAGEMENT(APPLIED).
IDENTIFIERS:
AQUIFER SWEETENING, AQUIFER DESALINATION.
ABSTRACT:
AQUIFER DESALTING WAS STUDIED IN A RECTANGULAR, GLASS-WALLED,
SAND-FILLED TANK AND IN A MATHEMATICAL MODEL. TWO TYPES OF AQUIFERS
WERE STUDIED: (1) A 1:40 SCALE, TWO-PART AQUIFER (COURSE AND FINE SAND)
REPRESENTING A VERTICAL CROSS SECTION THROUGH AN IDEALIZED PORTION OF
AN IRRIGATED VALLEY; AND (2) A FINE SAND, SINGLE-PART AQUIFER USED TO
EVALUATE A FORMULA DERIVED FROM THE GHYBEN-HERZBERG PRINCIPLE FOR
COMPUTING DEPTH TO A SALINE-FRESH WATER INTERFACE. SALT WATER WAS
FLUSHED FROM THE AQUIFERS INTO SUBSURFACE DRAINS BY APPLYING FRESH
WATER TO THE SURFACE. TEST RESULTS FOR BOTH AQUIFER TYPES SHOWED THAT
TILE DRAINS PLACED NEAR THE GROUND SURFACE WILL NOT INTERCEPT AND
DISCHARGE SURFACE-APPLIED FRESH WATER IF ALL OR PART OF THE AQUIFER
CONTAINS SALT WATER. THE FRESH WATER DISPLACES THE SALT WATER WITHOUT
APPRECIABLE MIXING AND MOVES IT INTO THE DRAINS. A STABLE FRESH-SALT
WATER INTERFACE IS THEREBY FORMED IN THE AQUIFER. REDUCED SPACING OF
DRAINS REDUCED THE AMOUNT OF SALT WATER THAT WILL BE REMOVED FROM THE
AQUIFER. PROGRESS OF THE TESTS WAS RECORDED IN STILL AND TIMED-SEQUENCE
MOTION PICTURES. (KNAPP-USGSJ
FIELD 05G, 02F, 04B
ACCESSION NO. W71-01932
76
-------
FERTILIZERS AND FEEDLOTS WHAT ROLE IN GRQUNDWATER POLLUTION.
AGRICULTURAL RESEARCH, VOL 18, NO 6, DECEMBER 1969, P 14-15.
DESCRIPTORS:
*FARM WASTES, #SOIL CONTAMINATION, #FERTILIZERS, ^NITRATES, WATER
POLLUTION, NITROGEN, NITRITES, AQUIFERS, COLORADO, DENITRIFICATION,
WATER TABLE, PERCOLATION.
IDENTIFIERS:
^FEEDLOTS, SOUTH PLATTE RIVER VALLEY.
ABSTRACT:
NO SIGNIFICANT CONTAMINATION OF THE WATER TABLE WITH NITRATE FROM FARM
FERTILIZERS OR EXTENSIVE CATTLE FEEDING OPERATIONS WAS FOUND IN
PRELIMINARY ARS STUDIES IN NORTHEASTERN COLORADO. BUT STUDIES INDICATED
THAT SUBSTANTIAL AMOUNTS OF NITRATE COULD EVENTUALLY REACH THE WATER
TABLE UNDER HEAVILY FERTILIZED IRRIGATED FIELDS AND UNDER FEEDLOTS, ARS
SOIL SCIENTISTS MEASURED NITRATES IN 129 SOIL CORES DRILLED TO BEDROCK
OR THE WATER TABLE AND IN 75 SAMPLES OF GROUNDWATER TAKEN WITH THE
CORES IN COLORADO'S SOUTH PLATTE RIVER VALLEY. THE INVESTIGATORS FOUND
THAT, ON THE AVERAGED THE KIND OF LAND USE DID NOT EFFECT THE NITRATE
CONCENTRATION OF WATER ENTERING THE BOTTOM OF THE HOLES WHERE THE CORES
WERE TAKEN. THE SURFACE MAY CONTAIN MORE POLLUTANTS THAN WATER DEEPER
IN THE AQUIFER. (WHITE-IOWA STATE)
FIELD 05B
ACCESSION NO. W71-02036
77
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MOVEMENT OF BACTERIA FROM A RIVER TO A MUNICIPAL WELL A CASE HISTORY,
GEOLOGICAL SURVEY, ALBANY, N.Y.
ALLAN D. RANDALL.
JOURNAL AMERICAN WATER WORKS ASSOCIATION, VOL 62, NO 11, PART 1, P 716-720,
NOVEMBER 1970. 5 P, 5 FIG, 4 REF.
DESCRIPTORS:
#PATH OF POLLUTANTS, ^INDUCED INFILTRATION, COLIFORMS, ALLUVIAL
CHANNELS, DREDGING, EXCAVATION, AQUIFERS, GRAVELS, AQUITARDS, PUMPING,
WATER WELLS, MUNICIPAL WATER, SURF ACE-GROUNDWATER RELATIONSHIPS,
GROUNDWATER MOVEMENT.
IDENTIFIERS:
*SUSQUEHANNA RIVER(NY), B INGHAMTONfNY ) .
ABSTRACT:
COLIFORM BACTERIA REGULARLY TRAVEL AT LEAST 180 FT TO MUNICIPAL WELL
FROM A REACH OF THE SUSQUEHANNA RIVER (NY) POLLUTED BY SEWAGE.
EXCAVATION OF THE RIVERBED, IN AN AREA ALREADY GEOLOGICALLY FAVORABLE
FOR INDUCED INFILTRATION, SEEMS RESPONSIBLE FOR BACTERIA REACHING THE
WELL, AFTER 19 YR OF TROUBLE-FREE OPERATION. THE WELL PRODUCES FROM
BEDS OF COARSE SAND AND GRAVEL AND 10 TO 80 FT BELOW LAND SURFACE. FROM
1945 THROUGH 1964 IT WAS IN DAILY USE, WITH ONLY OCCASIONAL
INTERRUPTIONS DUE TO EQUIPMENT FAILURE, SUPPLYING 1.0 TO 1.6 MGD OF
COOD WATER. (KNAPP-USGS)
FIELD 05B, 02G
ACCESSION NO. W71-02909
78
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SCHLICHTRULL V MELLON-POLLOCK OIL CO (NEGLIGENT DRILLING OF OIL WELL ALLEGED TO
HAVE CAUSED SALINE WATER INTRUSION).
301 PA 553, 152 A 829-831 (1930).
DESCRIPTORS:
^PENNSYLVANIA, *SALINE WATER INTRUSION, *OIL WELLS, *WATER WELLS,
GROUNDWATER, SALINE WATER-FRESH WATER INTERFACES, MIXING, PENETRATION,
DRILL HOLES, GROUNDWATER MOVEMENT, DAMAGES, LEGAL ASPECTS,
COMPENSATION, BRINES, WATER SUPPLY, BOUNDARIES(SURFACES), WELL CASINGS,
SALINE WATER, WELLS, SEEPAGE, DAMAGES, REMEDIES.
ABSTRACT:
PLAINTIFF FARMOWNER SUED DEFENDANT OIL WELL LESSEE FOR DAMAGES CAUSED
BY POLLUTION OF PLAINTIFF'S WELL. DEFENDANT HAD ENCOUNTERED SALT WATER
IN DRILLING, AND BECAUSE DEFENDANT HAD FAILED TO DRIVE CASINGS TO
PREVENT INTRUSION OF THE SALT WATER INTO THE FRESH WATER STRATA LYING
ABOVE, THE SALT WATER SEEPED INTO PLAINTIFF'S WELL. THE COURT NOTED
THAT WITHOUT NEGLIGENCE NO LIABILITY INURES FOR INTERFERENCE WITH
SUBTERRANEAN WATERS. HOWEVER, DEFENDANT WAS LIABLE BECAUSE IT HAD
FAILED TO EXERCISE DUE CARE. DEFENDANT ASSERTED THAT THE OIL WELL WAS
TO BE ABANDONED IN SIX MONTHS AND THAT, THEREFORE, THE INJURY WAS
TEMPORARY. PLAINTIFF ASSERTED THAT THE INJURY WAS PERMANENT, SINCE
DEFENDANT HAD NOT PROVEN THAT PLUGGING THE WELL WOULD PREVENT SALT
WATER INTRUSION OR RESTORE THE PROPERTY TO ITS ORIGINAL CONDITION.
HOLDING THAT THE INJURY WAS PERMANENT, THE COURT AFFIRMED THE TRIAL
COURT'S MEASURE OF DAMAGES BASED UPON THE DIMINUTION IN MARKET VALUE OF
PLAINTIFF'S TRACT. (HART-FLORIDA)
FIELD 06E, 05B
ACCESSION NO. W71-03230
79
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RELATIONSHIP OF AGRICULTURE TO SOIL AND WATER POLLUTION.
CORNELL UNIV., ITHACA, N.Y.
PROCEEDINGS, CORNELL UNIVERSITY CONFERENCE ON AGRICULTURAL WASTE MANAGEMENT,
JANUARY 19-21, 1970. ITHACA, 1970. 270 P.
DESCRIPTORS:
*SOILS, #FARM WASTES, #FERTILIZERS, GROUNDWATER, PRECIPITATION,
POTASSIUM, POULTRY, CATTLE, HOGS, NITROGEN, NITRATE, PHOSPHORUS,
PHOSPHATES, RATES OF APPLICATION, NUTRIENTS, EFFLUENT, AQUIFER,
AMMONIA, SOIL CONTAMINATION, WATER POLLUTION, WATER TABLE, OXIDATION
LAGOON, IRRIGATION, AERATION, BIOCHEMICAL OXYGEN DEMAND, CHEMICAL
OXYGEN DEMAND, ODOR, BIOLOGICAL TREATMENT, COSTS, DENITRIFICATION,
NITRIFICATION, SLUDGE, STORAGE, NUTRIENT REQUIREMENTS, FLORIDA,
NEBRASKA, SURFACE RUNOFF, INFILTRATION.
IDENTIFIERS:
#FEEDLOTS, OXIDATION DITCH, SLOTTED FLOORS, AERATOR, SPREADING, LAND
DISPOSAL.
ABSTRACT:
THE 1970 CONFERENCE ATTEMPTED TO BRING KNOWLEDGEABLE INDIVIDUALS FROM
MANY DISCIPLINES TOGETHER TO DISCUSS VARIOUS ASPECTS OF THE PROBLEM. IT
WAS DESIGNED TO SERVE AS A MECHANISM FOR TRANSMITTING NEW RESEARCH
FINDINGS TO THOSE INTERESTED IN THIS AREA AND TO DEMONSTRATE THAT
AGRICULTURE IS AWARE OF ITS POTENTIAL CONTRIBUTIONS TO ENVIRONMENTAL
POLLUTION AS WELL AS ITS RESPONSIBILITY TO SOCIETY TO FIND METHODS OF
ALLEVIATING SUCH POLLUTION WHILE INCREASING THE EFFICIENCY OF
PRODUCTION. THE CONFERENCE PLAYED A USEFUL ROLE IN PROVIDING
COMMUNICATION ACROSS DISCIPLINES. THIRTY-TWO PAPERS ARE PUBLISHED IN
THE PROCEEDINGS DEALING WITH ALL AREAS OF AGRICULTURAL POLLUTION. (SEE
ALSO W71-03543 THRU W71-03554) (WHITE-IOWA STATE)
FIELD 05B, 05D, 05C, 05G
ACCESSION NO. W71-03542
80
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GROUNDWATER QUALITY AND FLUCTUATIONS IN A SHALLOW UNCONFINED AQUIFER UNDER A
LEVEL FEEDLOT,
DEPARTMENT OF AGRICULTURE, LINCOLN, NEBR.
L. N. MIELKEf J. R. ELLIS, N. P. SWANSON, J. C. LORIMOR, AND
IN: RELATIONSHIP OF AGRICULTURE TO SOIL AND WATER POLLUTION; PROCEEDINGS*
CORNELL UNIVERSITY CONFERENCE ON AGRICULTURAL WASTE MANAGEMENT, ROCHESTER,
JANUARY 19-21, 1970, ITHACA, 1970, P 31-40. 2 TAB, 4 FIG, 13 REF.
DESCRIPTORS:
#FARM WASTES, ^CATTLE, ^GROUNDWATER, *NITRATE, AQUIFER, DISCHARGE,
AQUIFER CHARACTERISTICS, EFFLUENT STREAM, GROUNDWATER RECHARGE,
TRANSMISSIVITY, WATER LEVEL FLUCTUATIONS, AMMONIA, NEBRASKA, SOIL
CONTAMINATION, OBSERVATION WELLS, WATER TABLE, INFILTRATION.
IDENTIFIERS:
*FEEDLOT, PLATTE RIVER VALLEY.
ABSTRACT:
THE QUALITY WAS INVESTIGATED OF THE GROUNDWATER IN THE PROXIMITY OF A
LEVEL FEEDLOT ON A PERMEABLE SOIL WITH FLUCTUATING HIGH WATER TABLE. AT
THE FEEDLOT SITE, THE AQUIFER CONSISTS OF 30-35 FEET OF HIGH QUALITY
GRAVEL HAVING A COEFFICIENT OF TRANSMISSIBILITY IN THE RANGE OF
90,000-120,000 GALLONS PER DAY PER FOOT. AQUIFER RECHARGE OCCURS AS A
RESULT OF DIRECT PRECIPITATION AND INTERFLOW FROM THE VALLEY UPLANDS.
SIX OBSERVATION WELLS WERE INSTALLED IN THE VICINITY OF THE FEEDLOT AS
WELL AS SIX WATER LEVEL MEASURING WELLS. TWO RECORDING WELLS,
CONSTRUCTED OF 4-INCH DIAMETER ALUMINUM IRRIGATION PIPE, WERE JETTED
INTO THE GRAVEL AQUIFER. THE WATER TABLE DEPTH AT THE FEEDLOT VARIES
WITH THE SEASON. GROUNDWATER LEVEL CHANGES REFLECT MAJOR RAINSTORMS
WITHIN HOURS AFTER THE EVENT. THE MAXIMUM GROUNDWATER ELEVATION UNDER
THE FFEDLOT WAS APPROXIMATELY 2 FEET BELOW THE SOIL SURFACE. SOIL CORES
WERE TAKEN TO DETERMINE THE QUANTITY OF NITRATE WHICH COULD MOVE INTO
THE WATER TABLE. LOW LEVELS OF NITRATE WERE FOUND BELOW THE FIRST FOOT.
AMMONIA WAS PRESENT IN ONLY MODERATE AMOUNTS BELOW 3 FEET ( 30PPM) AND
RAPIDLY DECREASED IN CONCENTRATION WITH INCREASED DEPTH TO THE WATER
TABLE. ANALYSIS OF THE CORE SAMPLES INDICATED THAT DOWNWARD MOVEMENT OF
NITRATES AND OTHER FORMS OF NITROGEN IN THE SOIL WAS MINOR. THE 12-15
INCHES OF MANURE PACK DECREASED THE ACTUAL PENETRATION DEPTH OF THE
NITROGEN INTO THE PROFILE. SOME SAMPLES EXHIBITED LEVELS OF NITRATE
THAT EXCEEDED PUBLIC HEALTH STANDARDS (10PPM). THIS MAY HAVE BEEN DUE
TO THE APPLICATION OF ANHYDROUS AMMONIA PRIOR TO THE FIRST IRRIGATION.
GENERALLY, THE NITRATE ANALYSIS SHOWED RELATIVELY LOW NITRATE LEVEL IN
THE PROFILE. (SEE ALSO W71-03542) (WHITE-IOWA STATE)
FIELD 05B
ACCESSION NO. W71-03543
81
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MOVEMENT OF AGRICULTURAL POLLUTANTS WITH GROUNDWATER,
GEOLOGICAL SURVEY, RALEIGH, N.C.
HARRY E. LEGRAND.
IN: AGRICULTURAL PRACTICES AND WATER QUALITY, IOWA STATE UNIVERSITY PRESS,
AMES, 1970, P 303-313. 2 FIG, 18 REF.
DESCRIPTORS:
*PATH OF POLLUTANTS, #FARM WASTES, *WATER POLLUTION SOURCES,
^GROUNDWATER, *AGRICULTURAL CHEMICALS, FERTILIZERS, PESTICIDES,
NUTRIENTS, SOIL WATER, SOILS, SEEPAGE, SOIL CHEMISTRY, ABSORPTION, SOIL
MECHANICS, WATER QUALITY, SOIL PROPERTIES, WATER WELLS, WATER TABLE,
ENVIRONMENTAL EFFECTS, WATER CHEMISTRY, INFILTRATION.
IDENTIFIERS:
^AGRICULTURAL POLLUTANTS.
ABSTRACT:
THE VOLUME OF GROUNDWATER POLLUTED BY PLANT NUTRIENTS, ANIMAL WASTES,
AND PESTICIDES APPEARS TO BE SMALL. NUMEROUS SMALL POLLUTED ZONES OF
WATER OCCUR IN THE UPPER PART OF THE ZONE OF SATURATION. SUFFICIENT
SAFEGUARDS ARE AVAILABLE TO MINIMIZE GROUNDWATER POLLUTION TO THE
EXTENT THAT GOOD AGRICULTURAL PRACTICES SHOULD NOT BE DETERRED. THE
UNSATURATED ZONE ABOVE THE WATER TABLE ATTENUATES ALMOST ALL OF THE
FOREIGN BODIES THAT ARE POTENTIAL POLLUTANTS OF THE UNDERLYING
GROUNDWATER. CHEMICAL FERTILIZERS, ANIMAL WASTES, AND PESTICIDES VARY
GREATLY IN THEIR TENDENCY TO DEGRADE IN GROUND ENVIRONMENTS. THE
FOLLOWING FAVORABLE ENVIRONMENTAL FACTORS TEND TO REDUCE THE CHANGES OF
POLLUTION OF WATER FROM WELLS AND SPRINGS: (1) A DEEP WATER TABLE,
WHICH (A) ALLOWS FOR SORPTION OF POLLUTANTS ON EARTH MATERIALS, (B)
SLOWS SUBSURFACE MOVEMENT OF POLLUTANTS, AND
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PREDICTING CHANGES IN NITROGENOUS COMPOUNDS IN SOIL-WATER SYSTEMS,
ARIZONA UNIV., TUCSON.
MARVIN J. SHAFFER, GORDON R. DUTT, AND WILLIAM J. MOORE.
IN: COLLECTED PAPERS REGARDING NITRATES IN AGRICULTURAL WASTE WATERS, FEDERAL
WATER QUALITY ADMINISTRATION WATER POLLUTION CONTROL RESEARCH SERIES
13030ELY 12/69, P 15-28, DECEMBER 1969. 14 P, 7 FIG, 4 TAB, 9 REF. FWQA
PROJECT NO 13030ELY; BUR RECLAM. CONTRACT NO 10-06-D-6464.
DESCRIPTORS:
^SIMULATION ANALYSIS, *PATH OF POLLUTANTS, ^RETURN FLOW, *NITRATES,
MATHEMATICAL MODELS, COMPUTER PROGRAMS, CALIFORNIA, WATER POLLUTION
SOURCES, LEACHING, DRAINAGE WATER, AMMONIA, DRAINAGE EFFECTS,
GROUNDWATER, WATER QUALITY, SOIL WATER.
IDENTIFIERS:
*GROUNDWATER POLLUTION, ^CENTRAL VALLEY(CALIF).
ABSTRACT:
A DIGITAL COMPUTER PROGRAM WAS DEVELOPED TO MODEL SOIL-WATER SYSTEMS
WITH RESPECT TO NITROGEN TRANSFORMATIONS, INCLUDING HYDROLYSIS OF UREA,
IMMOBILIZATION-MINERALIZATION OF AMMONIA AND ORGANIC NITROGEN, AND
IMMOBILIZATION OF NITRATE NITROGEN. COMPARISONS WERE MADE OF PREDICTED
AND OBSERVED DATA FOR SEVERAL SOILS HAVING DIFFERENT TEXTURES AND
VARIOUS MOISTURE CONTENTS, TEMPERATURES, AND FERTILIZER APPLICATIONS.
THIS PROCEDURE YIELDED SIMPLE CORRELATION COEFFICIENTS OF 0.99, 0.97,
AND 0.97 FOR THE UREA, ORGANIC, AND AMMONIA NITROGENOUS TYPES. A MODEL
PREDICTING THE CONCENTRATIONS OF NITROGENOUS SPECIES OCCURRING IN
SOIL-WATER SYSTEMS AIDS IN PLANNING MANAGEMENT CRITERIA FOR POLLUTION
CONTROL AND FERTILIZER PROGRAMS. (SEE ALSO W71-04546) (KNAPP-USGS)
FIELD 05G, 05B
ACCESSION NO. W71-04548
83
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NUMERICAL SIMULATION OF DISPERSION IN GROUNDWATER AQUIFERS,
COLORADO STATE UNIV., FORT COLLINS. DEPT. OF AGRICULTURAL ENGINEERING; AND
COLORADO STATE UNIV., FORT COLLINS. DEPT. OF CIVIL ENGINEERING.
DONALD LEE REDDELL, AND DANIEL K. SUNADA.
COLORADO STATE UNIVERSITY HYDROLOGY PAPER NO 41, JUNE 1970. 79 P, 35 FIG, 1
TAB, 96 REF, 8 APPEND. OWRR PROJECT A-001-COLO(8).
DESCRIPTORS:
^SIMULATION ANALYSIS, ^DISPERSION, ^GROUNDWATER MOVEMENT, ^NUMERICAL
ANALYSIS, MIXING, COMPUTER PROGRAMS, COMPUTER MODELS, MATHEMATICAL
MODELS, SALINE WATER INTRUSION, AQUIFERS, POROUS MEDIA, DIFFUSION,
CONVECTION, DIFFUSIVITY.
IDENTIFIERS:
LONGITUDINAL DISPERSION.
ABSTRACT:
A FLOW EQUATION FOR A MIXTURE OF MISCIBLE FLUIDS WAS DERIVED BY
COMBINING THE LAW OF CONSERVATION OF MASS, DARCY'S LAW, AND AN EQUATION
OF STATE DESCRIBING THE PRESSURE-VOLUME-TEMPERATURE-CONCENTRATION
RELATIONSHIP. THE RESULT IS AN EQUATION INVOLVING TWO DEPENDENT
VARIABLES, PRESSURE AND CONCENTRATION. A RELATIONSHIP FOR DETERMINING
CONCENTRATION WAS DERIVED BY EXPRESSING A CONTINUITY EQUATION FOP THE
DISPERSED TRACER. AN IMPLICIT NUMERICAL TECHNIQUE WAS USED TO SOLVE THE
FLOW EQUATION FOR PRESSURE* AND THE METHOD OF CHARACTERISTICS WITH A
TENSOR TRANSFORMATION WAS USED TO SOLVE THE CONVECTIVE-DISPER5I ON
EQUATION. THE RESULTS FROM THE FLOW EQUATION WERE USED IN SOLVING THE
COMVECTIVE-DISPERSION EQUATION AND THE RESULTS FROM THE
CONVECTIVE-DISPERSION EQUATION WERE THEN USED TO RESOLVE THE FLOW
EQUATION. THE COMPUTER SIMULATOR SUCCESSFULLY SOLVED THE LONGITUDINAL
DISPERSION PROBLEM AND THE LONGITUDINAL AND LATERAL DISPERSION PROBLEM.
USING THE TENSOR TRANSFORMATION, PROBLEMS OF LONGITUDINAL AND LATERAL
DISPERSION WERE SUCCESSFULLY SOLVED IN A ROTATED COORDINATE SYSTEM. THE
COMPUTER SIMULATOR WAS USED TO SOLVE THE SALT-WATER INTRUSION PROBLEM.
THE NUMERICAL RESULTS FOR THE FRESH WATER HEAD IN THE AQUIFER CLOSELY
MATCHED THOSE OBTAINED ANALYTICALLY. (SEE W70-04051) (KNAPP-USGS)
o
FIELD 06A, 05B, 02F
ACCESSION NO. W71-04559
84
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THE 'FINAL1 WATER WELL LAW AND REGULATIONS (STANDARDS FOR WATER WELL
CONSTRUCTION AND PUMP INSTALLATION),
GROUND WATER RESOURCES INST.
DURWARD HUMES.
WATER WELL JOURNAL* VOL 20, P 3-11, JAN 1966. 1 TAB, 9 REF.
DESCRIPTORS:
^PUBLIC HEALTH, #WELL REGULATIONS, *WATER WELLS, #LEG ISLATION,
CONSTRUCTION, PUMPS, PUMPING, STANDARDS, REGULATION, WELL PERMITS,
DRILLING, ADMINISTRATIVE AGENCIES, ADMINISTRATION, GROUNDWATER, WATER
QUALITY, INSPECTION, INSTALLATION, WELL CASINGS, ARTESIAN WELLS, WELL
SCREENS, EXCAVATION, WATER POLICY, AQUIFERS, PERCOLATING WATER, LEGAL
ASPECTS.
ABSTRACT:
REFLECTING THE DESIRE OF THE WELL-MANUFACTURING INDUSTRY TO PROTECT
PUBLIC HEALTH AND TO UPGRADE CONSTRUCTION STANDARDS IN THE INDUSTRY,
THE MODEL WATER WELL CONSTRUCTION AND PUMP INSTALLATION ACT PRESCRIBES
STATE REGULATION OF THE WELL-CONSTRUCTION INDUSTRY. THIS REPORT
CONTAINS THE PROPOSED LAW, EXPLANATORY COMMENTS ACCOMPANYING IMPORTANT
SECTIONS, AND PROPOSED MODEL ADMINISTRATIVE REGULATIONS. ALSO INCLUDED
IS A TABLE OUTLINING STANDARDS FOR THE CONSTRUCTION OF WELLS. THE
GENERAL SCOPE OF THE ACT IS TO PROHIBIT CONSTRUCTION OF WELLS IN
VIOLATION OF ITS APPLICABLE RULES AND REGULATIONS. THE STATE DEPARTMENT
OF HEALTH OR SOME OTHER APPROPRIATE AGENCY WOULD ADMINISTER AND ENFORCE
THE ACT, AND THE DEPARTMENT WOULD HAVE THE POWERS NECESSARY TO: (1)
REQUIRE PERMISSION AND NOTIFICATION IN DESIGNATED AREAS BEFORE
CONSTRUCTION OF WATER WELLS, ABANDONMENT OF WATER WELLS, OR
INSTALLATION OF PUMPING EQUIPMENT IN ANY WELLS; (2) INSPECT WATER
WELLS, ABANDONED WATER WELLS OR PUMP INSTALLATIONS; (3) LICENSE WATER
WELL CONTRACTORS; AND (4) GRANT EXEMPTIONS FROM THE OPERATION OF THE
ACT. SECTIONS COVER FEES, PROCEDURES FOR ENFORCEMENT, ADMINISTRATIVE
HEARINGS, JUDICIAL REVIEW AND PENALTIES FOR VIOLATIONS. THE
ADMINISTRATIVE REGULATIONS DEFINE MORE SPECIFICALLY STANDARDS AND
PROCEDURES UNDER THE ACT. (DUSS-FLORIDA)
FIELD 06E, 05G
ACCESSION NO. W71-0474-2
85
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MODEL OF HYDROLOGIC REDISTRIBUTION OF RADIONUCLIDES AROUND NUCLEAR-EXCAVATED
SEA-LEVEL CANALS,
ISOTOPES, INC., PALO ALTO, CALIF. PALO ALTO LABS.
R. L. CHARNELL, D. E. HOLLY, AND P. R. FENSKE.
IN: ISOTOPE HYDROLOGY, 1970, PROCEEDINGS SYMPOSIUM OF INTERNATIONAL ATOMIC
ENERGY AGENCY AND UNESCO, VIENNA, MARCH 9-13, 1970? VIENNA, INTERNATIONAL
ATOMIC ENERGY AGENCY STI/PUB/255, PAPER NO SM-129/51, P 801-814, 1970. 14
P, 5 FIG, 14 REF. USAEC CONTRACT AT(26-1)-171.
DESCRIPTORS:
#RADIOECOLOGY, *FALLOUT, BLEACHING, *PATH OF POLLUTANTS, ^NUCLEAR
ENGINEERING, NUCLEAR EXPLOSIONS, CANALS, CANAL CONSTRUCTION,
GROUNDWATER MOVEMENT, INFILTRATION, NAVIGATION, SEEPAGE.
IDENTIFIERS:
^VENEZUELA, ^NUCLEAR CANAL EXCAVATION.
ABSTRACT:
AS PART OF THE BIOENVIRONMENTAL AND RADIOLOGICAL-SAFETY FEASIBILITY
STUDIES FOR NUCLEAR EXCAVATION OF A SEA-LEVEL CANAL IN CENTRAL AMERICA,
A MODEL WAS DEVELOPED TO ESTIMATE THE RATE AT WHICH EXCAVATION-PRODUCED
RADIONUCLIDES ARE REDISTRIBUTED BY NATURAL HYDROLOGIC PROCESSES. THE
MODEL CAN BE USED TO ESTIMATE THE AMOUNT OF A SPECIFIC RADIONUCLIDE
AVAILABLE FOR INTERACTION WITH PLANT, ANIMAL, OR MAN. THE MODEL WAS
FORMULATED FOR TWO DISTINCT REGIONS: IN THE CANAL CHANNEL ITSELF AND
THE REGION AWAY FROM THE CANAL WHERE DUST AND FINE PARTICLES ARE
DEPOSITED AS WIND-DISTRIBUTED FALLOUT. FOR THE FALLOUT ZONE PORTION OF
THE MODEL, REDISTRIBUTION IS CONTROLLED BY THE INITIAL REMOVAL BY
RAINWATER LEACHING. THE AMOUNT OF RADIONUCLIDE WHICH IS REMOVED WITH
RAINFALL IS REPRESENTED BY THE SIMPLE DISTRIBUTION COEFFICIENT KDJ.
ONCE THE NUCLIDE IS DISSOLVED, ITS RATE OF ENTRY INTO THE GROUNDWATER
RESERVOIR AND INTO THE STREAM CAN BE DETERMINED FROM SOIL DENSITY AND
POROSITY, LONG-TERM INFILTRATION RATES, AND SOME PRE-EXCAVAT ION
HYDROLOGIC DATA. THIS MODEL WAS APPLIED TO TWO OF THE PROPOSED CANAL
SITES IN PANAMA AND COLOMBIA. FOR RADIONUCLIDES WITH DISTRIBUTION
COEFFICIENTS HIGHER THAN 100, CONCENTRATION OF THE RADIONUCLIDE IN
RIVER WATER CONTINUES AT A NEAR CONSTANT LEVEL DECREASED ONLY BY
RADIOACTIVE DECAY. REMOVAL FROM THE LAND SURFACE BY LEACHING IS NOT
SIGNIFICANT DURING THE FIRST YEAR FOLLOWING EXCAVATION. ON THE OTHER
HAND, FOR NUCLIDES WITH DISTRIBUTION COEFFICIENTS LESS THAN 100,
LEACHING REMOVAL FROM THE LAND SURFACE IS SIGNIFICANT IN ONE YEAR AND
THE CONCENTRATION IN STREAMS DROPS RAPIDLY. (KNAPP-USGS)
FIELD 05B, 07B, 08H
ACCESSION NO. W71-04882
86
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HYDROLQGIC IMPLICATIONS OF SOLID-WASTE DISPOSAL,
GEOLOGICAL SURVEY, WASHINGTON, D.C.
WILLIAM J. SCHNEIDER.
FREE ON APPLICATION TO THE US GEOLOGICAL SURVEY, WASH, DC 20242. GEOLOGICAL
SURVEY CIRCULAR 601-F, 1970. 10 P, 2 FIG, 2 TAB, 7 REF.
DESCRIPTORS:
#WATER POLLUTION SOURCES, ^URBANIZATION, *SOLID WASTES, *WASTE
DISPOSAL, SURFACE WASTERS, GROUNDWATER, GARBAGE DUMPS, LANDFILLS, WASTE
DUMPS, WATER POLLUTION, PRECIPI TAT I ON(ATMOSPHER1C), SEEPAGE,
INFILTRATION, GROUNDWATER MOVEMENT, HYDRAULICS, SURFACE RUNOFF,
STREAMS, SOIL TYPES, PERMEABILITY, FLOODS, EVALUATION, PLANNING.
IDENTIFIERS:
DURBAN HYDROLOGY.
ABSTRACT:
THE DISPOSAL OF MORE THAN 1,400 MILLION POUNDS OF SOLID WASTES IN THE
UNITED STATES EACH DAY IS A MAJOR PROBLEM. FOUR DISPOSAL METHODS-OPEN
DUMPS, SANITARY LANDFILL, INCINERATION, AND ONSITE DISPOSAL-CARRY AN
INHERENT POTENTIAL FOR POLLUTION OF WATER RESOURCES. SEEPAGE OF
RAINWATER THROUGH THE WASTES LEACHES UNDESIRABLE CONSTITUENTS WHICH
REACH THE GROUNDWATER IN THE AREA. THIS LEACHATE IS GENERALLY BOTH
BIOLOGICALLY AND CHEMICALLY CONTAMINATED. POLLUTION POTENTIAL IS
HIGHEST IN PERMEABLE AREAS WITH A SHALLOW WATER TABLE WHERE THE WASTES
ARE IN DIRECT CONTACT WITH THE GROUNDWATER. SITE SELECTION FOR DISPOSAL
OF SOLID WASTES MUST BE BASED ON ADEQUATE WATER-RESOURCES INFORMATION
IF POLLUTIONAL POTENTIAL IS TO BE MINIMIZED. THIS WILL REQUIRE REGIONAL
AS WELL AS LOCALIZED DATA ON THE WATER RESOURCES OF THE AREA. ONLY
THROUGH SUCH AN APPROACH CAN ADEQUATE PROTECTION BE AFFORDED TO THE
ENVIRONMENT IN GENERAL AND THE WATER RESOURCES IN PARTICULAR.
(WQQDARD-USGS)
FIELD 05B, 05E, 04B
ACCESSION NO. W71-05094
87
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DEGRADATION OF WATER QUALITY IN IRRIGATION RETURN FLOWS,
ROBERT S. KERR WATER RESEARCH CENTER, ADA, QKLA.; AND OKLAHOMA STATE UNIV.,
STILLWATER. DEPT. OF AGRONOMY*
JAMES P. LAW, JR., J. M. DAVIDSON, AMD LESTER W. REED.
OKLAHOMA AGRICULTURAL EXPERIMENT STATION, BULLETIN B-684, OCTOBER 1970. 26 P,
9 TAB, 7 FIG, 27 REF.
DESCRIPTORS:
^IRRIGATION WATER, *RETURN FLOW, ^DRAINAGE WATER, -^DETERIORATION,
*WATER POLLUTION EFFECTS, WATER QUALITY, SALINITY, GROUNDWATER,
DISSOLVED SOLIDS, LEACHING, SALT BALANCE, PERCOLATING WATER, POLLUTION
IDENTIFICATION, SOIL WATER, SALINE WATER, WATER CONSERVATION,
IRRIGATION PRACTICES.
IDENTIFIERS:
*SALT WATER IRRIGATION, SALT TRANSPORT.
ABSTRACT:
THE OBJECT WAS TO DETERMINE WATER-QUALITY DEGRADATION IN IRRIGATION
RETURN FLOWS, TO DETERMINE SALINITY STATUS OF A SALT-WATER-IRRIGATED
CLAY LOAM SOIL, AND TO RELATE THESE RESULTS TO IRRIGATION RETURNS ON
SURFACE AND GROUNDWATER QUALITY. TOTAL DISSOLVED SOLIDS (TDS) INCREASED
20% IN THE SURFACE RETURN FLOW, WHILE PERCOLATING SOIL WATER INCREASED
5 TO 8 FOLD IN TDS. THE CLAY LOAM SOIL SHOWED AN INCREASE IN SOLUBLE
SALT AFTER 15 YEARS OF HIGH-SALT-WATER IRRIGATION (TDS OF 1,430 PPM),
THOUGH LEACHING BY RAIN CONTRIBUTED A FAVORABLE SALT BALANCE.
PERCOLATING IRRIGATION WATER TRANSPORTS ABOUT 10 TONS OF SALT PER
ACRE-FOOT. DRAINING AND PERCOLATING WATERS ADVERSELY AFFECT SURFACE AND
GROUNDWATER. FUTURE STUDIES WILL CONSIDER SEASONAL FLUCTUATIONS AND
DYNAMICS OF SOIL WATER QUALITY AND QUANTITY. TABLES SHOW WATER-TABLE
DEPTHS, WATER-SAMPLING LOCATIONS, SCHEDULE OF OPERATIONS, QUALITY DATA
OF IRRIGATION, DRAINAGE AND GROUNDWATER, AND ESTIMATED NUTRIENT LOSSES.
FIGURES SHOW SALT CONTENT AT TIME AND DEPTH OF WATER. (POPKIN - ARIZONA)
FIELD 03F, 05C, 02G
ACCESSION NO. W71-06063
88
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SOURCES OF NITROGEN IN WATER SUPPLIES*
GEOLOGICAL SURVEY, DENVER* COLO.
MARVIN C. GOLDBERG.
AGRICULTURAL PRACTICES AMD WATER QUALITY* IOWA STATE UNIVERSITY PRESS, AMES,
IOWA, 1970* CHAPTER 7* P 94-124. 4- FIG, 8 TAB, 72 REF.
DESCRIPTORS:
#NITROGEN, ^NITRATES* GROUNDWATER* AMMONIA, PRECIPITATION, SEDIMENTS,
DENITRIFICATION, RUNOFF, UREAS* FERTILIZERS* DRAINAGE WATER,
IRRIGATION, RETURN FLOW* WATER SUPPLY, LIVESTOCK, SEWAGE, INFILTRATION,
INDUSTRIAL WASTES, ALGAE, PONDS* FARM WASTES.
IDENTIFIERS:
^SURFACE WATERS* GEOLOGICAL SOURCES* MINERALIZATION, NITROGEN SOURCES,
WELL WATER* FEEDLOTS.
ABSTRACT:
WATER SUPPLIES CAN BE CATEGORIZED AS SURFACE WATERS OR GROUNDWATERS.
THIS PAPER EXAMINES REPRESENTATIVE STUDIES OF NITRATE ENTRANCE TO BOTH
TYPES OF WATER SUPPLIES* WITH SUMMARIES OF SOME OF THE MANY LABORATORY
AND FIELD STUDIES DESCRIBED IN THE CURRENT LITERATURE. SOME OF THE
SOURCES OF NITROGEN ENTRANCE TO WATER SUPPLIES INCLUDE ATMOSPHERIC,
GEOLOGIC, RURAL AND URBAN RUNOFF* SEWAGE, IRRIGATION, ANIMAL WASTES*
AND INDUSTRIAL WASTES AMONG MANY OTHERS. SOURCES OF MA !OR IMPORTANCE TO
BOTH SURFACE AND GROUNDWATER SUPPLIES ARE POINTED OUT AND FIELD OR
LABORATORY STUDIES ARE REPORTED. (SEE ALSO W71-05437) (WHITE-JOWA STATE)
FIELD 05B
ACCESSION NO. W71-06435
89
-------
EFFECTS OF AGRICULTURAL POLLUTION ON EUTROPHICATION,
WISCONSIN UNIV., MADISON. DEPT. OF SANITARY ENGINEERING, AND WISCONSIN UNIV.*
MADISON. DEPT. OF WATER CHEMISTRY.
D* E. ARMSTRONG, AND G. A. ROHLICH,
AGRICULTURAL PRACTICES AND WATER QUALITY, IOWA STATE UNIVERSITY PRESS, AMES,
IOWA, 1970, CHAPTER 23, P 314-330. 14 TAB, 2 FIG, 26 REF.
DESCRIPTORS:
*EUTROPHICATION, *MITROGEN, ^PHOSPHORUS, NUTRIENTS, ALGAE, NITRATES,
SURFACE RUNOFF, BASE FLOW, PERCOLATION, LEACHING, DRAINAGE, FARM
WASTES, SOIL MANAGEMENT, GROUNDWATER, WISCONSIN, WATER SUPPLY.
IDENTIFIERS:
*AGRICULTURAL DRAINAGE, LAKE METABOLISM, MOBILITY, PARTICULATE FORM,
FEEDLOTS, NUTRIENT SOURCES.
ABSTRACT:
THE PAPER DISCUSSES NITROGEN AND PHOSPHORUS TRANSPORT IN AGRICULTURAL
DRAINAGE SINCE THESE ARE THE MOST IMPORTANT NTURIENTS INVOLVED IN
EUTROPHICATION. IT IS GENERALLY EXPECTED THAT INORGANIC NITROGEN IS
TRANSPORTED MAINLY AS NITRATE BY PERCOLATING WATER, ALTHOUGH THE
AMOUNTS OF AMMONIUM AND NITRATE CARRIED IN RUNOFF WATERS MAY BE HIGHLY
SIGNIFICANT IN TERMS OF THE RECEIVING WATER. SIMILARLY, THE LARGEST
AMOUNT OF PHOSPHORUS IS LIKELY TRANSPORTED IN PARTICULATE FORM IN
RUNOFF WATERS, BUT THE AMOUNT OF DISSOLVED PHOSPHORUS IN RUNOFF WATER
MAY BE OF EQUAL OR GREATER IMPORTANCE EVEN THOUGH LOWER IN QUANTITY.
THE CONTRIBUTION OF AGRICULTURAL DRAINAGE TO THE NITROGEN AND
PHOSPHORUS STATUS OF WATERS is NEXT EXAMINED. THE DATA PRESENTED
SUGGEST THAT AGRICULTURAL LAND IS AN IMPORTANT CONTRIBUTOR OF NITROGEN
AND PHOSPHORUS TO WATER. ABOUT 60% OF THE NITROGEN AND 422? OF THE
PHOSPHORUS WERE ESTIMATED TO COME FROM AGRICULTURAL LAND. NUTRIENT
BUDGET ESTIMATIONS WERE BASED ON DATA OBTAINED ON A SMALL SCALE AND
EXTRAPOLATED AND THUS HAVE A LOW RELIABILITY. NUTRIENT SOURCES ARE
NUMEROUS AND GENERALIZATIONS AS TO WHICH SOURCE IS THE MOST IMPORTANT
CANNOT BE MADE. THE CONTRIBUTION OF AGRICULTURE SHOULD BE REDUCED BY
IMPROVED AND MORE EFFICIENT AGRICULTURAL MANAGEMENT PRACTICES. (SEE
ALSO W71-05437) (WHITE-IOWA STATE)
FIELD 05C, 02H
ACCESSION NO. W71-06443
90
-------
MOVEMENT OF 2,4-D IN SOILS,
NEW MEXICO AGRICULTURAL EXPERIMENT STATION, UNIVERSITY PARK.
H. E. DREGNE, S. GOMEZ, AND W. HARRIS.
NEW MEXICO AGRICULTURAL EXPERIMENT STATION WESTERN REGIONAL RESEARCH PROJECT
PROGRESS REPORT, NOVEMBER 1969. 35 P, 21 FIG, 8 TAB, 41 REF.
DESCRIPTORS:
#WATER POLLUTION SOURCES, ^HERBICIDES, *NEW MEXICO, *SOIL WATER
MOVEMENT, GRQUNDWATER, SURFACE WATERS, TESTING, TEST PROCEDURES,
METHODOLOGY, WATER QUALITY, SOILS, PESTICIDES, CHROMATOGRAPHY,
ADSORPTION, CHEMICAL ANALYSIS, ANALYTICAL TECHNIQUES, BIOASSAY, SOIL
STRUCTURE, INFILTRATION, SOIL PROPERTIES, LEACHING, PATH OF PCLLUTANTS.
ABSTRACT:
MOVEMENT OF 2,4-DICHLOROPHENOXYACET1C ACID (2,4-D) IN THREE SOILS WAS
STUDIED TO DETERMINE THE EXTENT TO WHICH HERBICIDES APPLIED IN THE
FIELD ENTER THE SURFACE AND GROUNDWATER SYSTEMS* ANALYTICAL TECHNIQUES
USED INCLUDED GAS CHROMATOGRAPHY, THIN LAYER CHROMATOGRAPHY, SOIL THIN
LAYER CHROMATOGRAPHY, RESIN THIN LAYER CHROMATOGRAPHY, BIQASSAYS, AND
AUTORADIOGRAPHY. PRIMARY EMPHASIS WAS PLACED UPON THE EFFECT OF
EXCHANGEABLE CATIONS ON 2,4-D MOVEMENT. ADSORPTION ISOTHERMS,
BREAKTHROUGH CURVES, LEACHING STUDIES, AND BIOASSAYS INDICATE THAT
2,4-D IN THE ACID OR SALT FORM, IS ONLY SLIGHTLY ADSORBED BY SOIL
PARTICLES. IT IS EASILY LEACHED IF THE SOILS ARE PERMEABLE. VIRTUALLY
100% OF APPLIED 2,4-D WAS RECOVERED FROM A SANDY LOAM IN SIX AND
ONE-HALF HOURS OF LEACHING. ONLY 382 WAS RECOVERED FROM A SLOWLY
PERMEABLE SILTY CLAY LOAM OVER A PERIOD OF TEN MONTHS. DEGRADATION
PRODUCTS OF 2,4-D WERE LEACHED AS EASILY AS 2,4-D ITSELF.
(WOODARD-USGS)
FIELD 05B, 02G
ACCESSION NO. W71-06514
91
-------
DIGESTED SLUDGE LAGOONS*
DAYTON, OHIO.
DEFRO TOSSEY.
2ND INTERNATIONAL SYMPOSIUM FOR WASTE TREATMENT LAGOONS, JUNE 23-25, 1970,
KANSAS CITY, MISSOURI, P 333-334.
DESCRIPTORS:
^OXIDATION LAGOONS, ^TERTIARY TREATMENT, *SLUDGE DIGESTION, ANAEROBIC
DIGESTION, ODORS, GROUNDWATER, EVAPORATION, INFILTRATION, CLIMATIC
CONDITIONS, INCINERATION, AIR POLLUTION, TEMPERATURE, WASTE WATER
TREATMENT, OHIO.
IDENTIFIERS:
^SUPERNATANT RE-CYCLE.
ABSTRACT:
DISPOSAL OF DIGESTED SLUDGES IN SLUDGE LAGOONS HAS BEEN ACCEPTED
PRACTICE FOR THE CITY OF DAYTON FOR 35 YEARS. THE CURRENT LAND DISPOSAL
FACILITIES OCCUPY 15 ACRES AND INCLUDE BOTH THE LAGOONS AND
INFILTRATION BEDS WHERE THE SUPERNATANT IS USED TO IRRIGATE THE LAND.
SUCCESS OF SLUDGE LAGOONING HAS BEEN FOUND TO BE DEPENDENT UPON THE
QUALITY OF SLUDGE ENTERING THE LAGOON. INADEQUATE PRIMARY AND SECONDARY
DIGESTION PRODUCES TROUBLESOME CONDITIONS IN A SLUGE LAGOON SYSTEM.
SOLIDS DESTRUCTION CONTINUES WITHIN THE BOTTOM SLUDGES, WHICH ARE
ESTIMATED TO BE 20 TO 25% SOLIDS, HELPING TO ALLEVIATE PROBLEMS
ASSOCIATED WITH POORLY DIGESTED SLUDGES. THE SOIL THROUGH WHICH THE
SUPERNATANT INFILTRATES HAS SHOWN NO SIGNS OF BLINDING AND HAS BECOME
QUITE ENRICHED THROUGH DEPOSITION OF ORGANIC MATTER. NO DOCUMENTED
EVIDENCE OF GROUNDWATER DETERIORATION HAS BEEN FOUND BUT A SYSTEM OF
TESTING IS CURRENTLY BEING ORGANIZED TO DETERMINE WHETHER ANY
DETERIORATION IS TAKING PLACE. LAGOONING HAS BEEN ECONOMICAL, AND LAND
DISPOSAL HAS AVOIDED BOTH SUPERNATANT RECYCLE AND SLUDGE INCINERATION
WITH ITS ASSOCIATED AIR POLLUTIONAL PROBLEMS. BOTH PRACTICES WILL
THEREFORE CONTINUE TO BE USED BY THE CITY OF DAYTON. (SEE ALSO
W71-07079) (LOWRY-TEXAS)
FIELD 05D
ACCESSION NO. W71-07118
92
-------
GROUNDWATER POLLUTION FROM SANITARY LANDFILLS AND REFUSE DUMP GROUNDS, A
CRITICAL REVIEW,
MARQUETTE UNIV., MILWAUKEE, WIS. DEPT. OF CIVIL ENGINEERING,
A. E. ZANONI.
WISCONSIN DEPARTMENT OF NATURAL RESOURCES, RESEARCH REPORT 69, 1971. 43 P, 8
TAB, 62 REF.
DESCRIPTORS:
^LANDFILLS, *WATER POLLUTION, *WASTE DUMPS, *SOLID WASTES, BLEACHING,
^GROUNDWATER, HYDROGEOLOGY, WATER POLLUTION SOURCES, GROUNDWATER
MOVEMENT, PERCOLATION, WATER MANAGEMENT, IMPAIRED WATER QUALITY, WASTE
DISPOSAL, GARBAGE DUMPS.
IDENTIFIERS:
^GROUNDWATER POLLUTION, LANDFILL POLLUTION EFFECTS.
ABSTRACT:
A CRITICAL REVIEW IS PRESENTED OF THE IMPORTANT LITERATURE COVERING THE
AREA OF THE GROUNDWATER POLLUTION POTENTIAL FROM SANITARY LANDFILLS AND
DUMP GROUNDS. THIS IS FOLLOWED BY A REVIEW OF THE PRACTICES IN
TWENTY-ONE STATES IN THE U.S. RELATED TO THIS SAME TOPIC. BASED ON THE
INFORMATION DERIVED FROM THESE TWO SOURCES, A SERIES OF RECOMMENDATIONS
ARE SUGGESTED TO REGULATORY AGENCIES CONCERNED WITH THE TASK OF
APPROVING AND LICENSING SOLID WASTE DISPOSAL SITES. IT IS EMPHASIZED
THAT A REGULATORY AGENCY SHOULD HAVE AVAILABLE A GEOLOGIST, IDEALLY ONE
TRAINED IN HYDROGEOLOGY, TO ASSIST IN SANITARY LANDFILL SITE SELECTION
PROCESSES. HE SHOULD ACCUMULATE GEOLOGICAL DATA AND BROADLY OUTLINE
AREAS CONSIDERED AS EITHER GOOD OR POOR POTENTIAL LANDFILL SITES.
EXTREME CAUTION SHOULD BE EXERCISED BEFORE APPROVING GROUND DISPOSAL OF
INDUSTRIAL WASTES. MONITORING WELLS SHOULD RE USED IN CASES WHERE DOUBT
EXISTS AS TO THE FUTURE EFFECTS OF A PARTICULAR LANDFILL ONrGROUNDWATER
SUPPLIES. THE REGULATORY AGENCY SHOULD FOLLOW A POLICY OF SLOPING DOWN
THE REFUSE DEGRADATION PROCESS BY MINIMIZING WATER PERCOLATION THROUGH
REFUSE MASSES TO PROVIDE FOR LEACHATE ATTENUATION. THE REGULATORY
AGENCY SHOULD ENCOURAGE REGIONAL OR DISTRICT APPROACHES TO SOLID WASTES
COLLECTION AND DISPOSAL. AS A RULE, IT SHOULD PROHIBIT TH£ USE OF
ABANDONED ROCK, GRAVEL OR SAND QUARRIES AS SITES FOR REFUSE DISPOSAL.
REGULATORY AGENCIES SHOULD SUPPORT RESEARCH IN THE AREA OF GROUND WATER
POLLUTION. (POERTNER)
FIELD 05E, 02F, 10
ACCESSION NO. W71-07194
93
-------
LEACHING OF NUTRIENTS BY DRAINAGE WATERS,
LITOVSKAYA SELSKOKHOZYAISTVENNAYA AKADEMIYA SSR, KAUNAS.
Z. B. KINDERIS.
TRANS. FROM POCHVOVEDENI YE, NO 2, 1970. SOVIET SOIL SCIENCE, NO 1, P 99-108,
1970. 1 FIG, 4 TAB, 19 REF.
DESCRIPTORS:
^NUTRIENTS, *SOILS, BLEACHING, ^AQUIFER CHARACTERISTICS, SOIL ANALYSIS,
TEST PROCEDURES, CHEMICAL PROPERTIES, GROUNDWATER, SOIL WATER,
SOLUBILITY, SOIL WATER TRANSMISSIV ITY .
IDENTIFIERS:
LITHUANIAtUSSR).
ABSTRACT:
SAMPLES OF WATER WERE PERIODICALLY COLLECTED FROM TILE DRAINAGE SYSTEM
ESTABLISHED IN A WEAKLY PODZOLIZED DIORN-GLEY SOIL. ANALYSES INCLUDED
DETERMINATION OF POTASSIUM, SODIUM, CALCIUM, MAGNESIUM, AND CARBONATE,
NITRATE, SULFATE, AND CHLORIDE RADICALS. THE REMOVAL OF CHEMICAL
CONSTITUENTS VARIED DEPENDING UPON THE SEASON AND METEOROLOGICAL
CONDITIONS, RATE OF WATER DISCHARGE, NATURE OF CROPS, AND FERTILIZER
TREATMENTS. (WILDE-WISCONSIN)
FIELD 05B, 02F
ACCESSION NO. W71-07887
94
-------
THE EFFECTS OF RETURN IRRIGATION WATER ON THE BASAL LENS IN KAHUKU PLANTATION,
OAHU AND PIONEER MILL AND HAWAIIAN COMMERCIAL AND SUGAR COMPANY PLANTATIONS
ON MAUIt
HAWAII UNIV., HONOLULU.
PEDRO A. TENORIO.
M. S. THESIS, HAWAII UNIVERSITY, AUG 1970. 176 P, 66 FIG, 7 TAB, 54 REF,
APPEND. PROJECT B-012-HI (2).
DESCRIPTORS:
*WATER POLLUTION SOURCES, *WATER POLLUTION EFFECTS, ^RETURN FLOW,
*SALINE WATER INTRUSION, ^HAWAII, IRRIGATION WATER, WATER CHEMISTRY,
SOLUTES, NITRATES, SALINITY, WITHDRAWAL, GROUNDWATER, GROUNDWATER
MOVEMENT, LEACHING, INFILTRATION, WATER QUALITY.
IDENTIFIERS:
OAHU(HAWAII), MAUKHAWAII ).
ABSTRACT:
THE EFFECTS OF IRRIGATION RETURN WATER ON THE QUALITY OF THE BASAL
GROUNDWATER BODIES WERE IDENTIFIED AND DESCRIBED IN 3 AREAS ON THE
ISLANDS OF OAHU AND MAUI. PRESENTLY, ALL THREE AREAS ARE PLANTED WITH
SUGARCANE. LEACHING OF FERTILIZER COMPONENTS, PRINCIPALLY NITRATE AND
SULFATE, INTO THE BASAL AQUIFER OCCURS AS A RESULT OF IRRIGATION WATER
APPLICATION OVER THE FIELDS. EXCESSIVE WITHDRAWALS OF THE BASAL WATER
IN SIMPLE GHYBEN-HERZBERG LENS ACCELERATES SALINE WATER INTRUSION. ALL
OF THE IRRIGATION WATER SOURCES FROM THE THREE AREAS ARE SUITABLE FOR
THE IRRIGATION OF SUGARCANE CROP. (KNAPP-USGS)
FIELD 05C, 05B
ACCESSION NO. W71-08044-
95
-------
PALMER CORPORATION V COLLINS (CONTAMINATION OF OIL BY WATER SEEPAGE FROM
NEGLIGENTLY ABANDONED OIL WELL).
214 KY 838, 284 SW 95-98 (1926).
DESCRIPTORS:
^KENTUCKY, *OIL WELLS, *GROUNDWATER, ^SEEPAGE, DRILL HOLES, OILY WATER,
GROUNDWATER MOVEMENT, OIL-WATER INTERFACES, IMPERVIOUS SOILS,
GROUNDWATER BARRIERS, INFILTRATION, OIL, OIL RESERVOIRS, DRILLING
EQUIPMENT, LEASES, DAMAGES, LAND TENURE, JUDICIAL DECISIONS,
LEGISLATION, LEGAL ASPECTS.
ABSTRACT:
PLAINTIFF LEASEHOLDER SUED DEFENDANT CORPORATION FOR DAMAGES CAUSED BY
DEFENDANT'S FAILURE TO ADEQUATELY PLUG UP ABANDONED OIL WELLS.
PLAINTIFF CONTENDED THAT THE ABANDONED WELLS ALLOWED WATER TO SEEP INTO
THE OIL-BEARING STRATUM, THUS CONTAMINATING PLAINTIFF'S OIL WITH WATER.
DEFENDANT CONTENDED THAT PLAINTIFF HAD NOT SUFFICIENTLY PROVEN THAT THE
WATER CAME FROM DEFENDANT'S ABANDONED WELLS. DEFENDANT ALSO CONTENDED
THAT A STATUTE AUTHORIZING PLAINTIFF TO GO ON DEFENDANT'S LAND AND PLUG
UP THE WELLS AND THEN MAINTAIN AN ACTION AGAINST DEFENDANT TO RECOVER
THE COST PRECLUDED THE PLAINTIFF FROM ADDITIONALLY SEEKING DAMAGES TO
HIS OIL. THE COURT OF APPEALS OF KENTUCKY, IN AFFIRMING THE LOWER COURT
JUDGMENT FOR PLAINTIFF, NOTED THAT WATER HAD NOT APPEARED IN
PLAINTIFF'S OIL UNTIL DEFENDANT'S WELLS WERE ABANDONED AND SUBSEQUENTLY
FOUND TO CONTAIN WATER. THE STATUTE AUTHORIZING PLAINTIFF TO PREVENT
FUTURE DAMAGES DID NOT PRECLUDE HIS RIGHT TO RECOVER FOR THE PAST
INJURY INCURRED BY THE WATER. TO DESTROY THE PRODUCTION OF OIL IS TO
DESTROY PROPERTY, ALLOWING THE OWNER TO RECOVER DAMAGES THEREBY
SUSTAINED. (SMILJANICH-FLORIDA)
FIELD 06E, 05G
ACCESSION NO. W71-08055
96
-------
A STUDY ON CHANGES IN QUALITY OF UNDERGROUND WATER,
TABELA HOUSE, KOTA (INDIA). AGRICULTURAL CHEMISTRY SECTION.
B. L. DARRA, HARVINDER SINGH, AND R. S. MENDIRATTA.
JOURNAL OF SOIL AND WATER CONSERVATION IN INDIA, VOL 18, NOS 1 AND 2, P
JAN-JUNE 1970. 3 P, 3 TAB, 6 REF.
DESCRIPTORS:
#WATER QUALITY, ^RETURN FLOW, *GROUNDWATER, ^SATURATED SOILS,
^IRRIGATION EFFECTS, LEACHING, WATER LEVEL FLUCTUATIONS, SALINE SOILS,
LAND RECLAMATION, PATH OF POLLUTANTS.
IDENTIFIERS:
#INDIA.
ABSTRACT:
UNDERGROUND WELL WATERS WERE COLLECTED IN PRE AND POST SEASONS TO
ASSESS THE CHANGES BROUGHT ABOUT IN QUALITY OF WATERS IN THE TWO
IRRIGATION SEASONS UNDER SALINE AND SALINE-ALKALI WATER LOGGED AREAS OF
BUNDI DISTRICT OF CHAMBAL COMMAND, INDIA. THE QUALITY OF WATER SLIGHTLY
IMPROVED AFTER RAINS, WHILE IN ANOTHER PART IT WAS SLIGHTLY IMPAIRED.
THE CANAL WATER IS OF GOOD QUALITY. EFFORTS ARE IN PROGRESS TC DECREASE
THE SALT CONTENTS OF THE SURFACE BY LEACHING AND FLUSHING AIDED BY
LOWERING THE WATER TABLE USING SURFACE DRAINAGE FACILITIES.
SIMULTANEOUSLY OTHER SOIL RECLAMATION MEASURES HAVE ALSO BEEN
UNDERTAKEN TO BOOST CROP PRODUCTION. (KNAPP-USGS)
FIELD 05B, 03C, 04B
ACCESSION NO. W71-08073
97
-------
NITRATE AND OTHER WATER POLLUTANTS UNDER FIELDS AND FEEDLOTS,
AGRICULTURAL RESEARCH SERVICE, FORT COLLINS, COLO. SOIL AND WATER
CONSERVATION RESEARCH DIV.
B. A. STEWART, F. G. VIETS, JR., G. L. HUTCHINSON, AND W. D. KEMPER.
ENVIRONMENTAL SCIENCE AND TECHNOLOGY, VOL 1, NO 9, P 736-739, 1967. 2 FIG, 1
TAB, 1 REF.
DESCRIPTORS:
^NITRATES, #WATER POLLUTION SOURCES, LEACHING, FARM WASTES,
GROUNDWATER, HYDRAULIC CONDUCTIVITY.
IDENTIFIERS:
ORGANIC CARBON, FEEDLOTS.
ABSTRACT:
AGRICULTURE'S EFFECT ON NITRATE POLLUTION OF GROUNDWATER WAS
INVESTIGATED IN THE SOUTH PLATTE VALLEY OF COLORADO. THE VALLEY IS
INTENSIVELY FARMED AND CONTAINS MANY CONCENTRATED LIVESTOCK FEEDING
OPERATIONS. A WATER TABLE, GENERALLY BETWEEN 3 AND 20 METERS BELOW THE
SURFACE, UNDERLIES MUCH OF THE AREA. THE AVERAGE TOTAL NITRATE-NITROGEN
TO A DEPTH OF 6.7 METERS IN THE PROFILES FOR THE VARIOUS KINDS OF LAND
USE WAS: ALFALFA (MEDICAGO SATIVA) (13 CORES), 70; NATIVE GRASSLAND (17
CORES), 815 CULTIVATED DRYLAND (21 CORES), 233; IRRIGATED FIELDS NOT IN
ALFALFA (28 CORES), 452; AND FEEDLOTS (47 CORES), 1282 KG. PER HECTARE.
GROUNDWATER SAMPLES OFTEN CONTAINED HIGH CONCENTRATIONS OF NITRATE, AND
THOSE OBTAINED BENEATH FEEDLOTS CONTAINED AMMONIUM-NITROGEN AND ORGANIC
CARBON. DATA PRESENTED SHOW THAT NITRATE IS MOVING THROUGH THE SOIL AND
INTO THE GROUNDWATER SUPPLY UNDER BOTH FEEDLOTS AND IRRIGATED FIELDS IN
CROPS, EXCLUDING ALFALFA. (PARKER-IOWA STATE)
FIELD 05B
ACCESSION NO. W71-08218
98
-------
CASE STUDIES OF MUNICIPAL WASTE DISPOSAL SYSTEMS,
BUREAU OF MINES, PITTSBURGH, PA. EASTERN FIELD OPERATION CENTER.
H. W. SHEFFER, E. C. RAKER, AND G. C. EVANS.
BUREAU OF MINES INFORMATION CIRCULAR 8498, 1971. 36 P, 14 FIG, 19 REF.
DESCRIPTORS:
*WASTE DISPOSAL, ^MUNICIPAL WASTES, *WASTE TREATMENT, ^UNITED STATES,
^REVIEWS, METHODOLOGY, SANITARY ENGINEERING, LANDFILLS, HYDROLOGY,
WATER POLLUTION, PATH OF POLLUTANTS, MINE WASTES, GEOLOGY, GROUNDWATER,
WATER QUALITY, COMPACTION, COMPRESSIBILITY, SOLID WASTES, INCINERATION,
PERCOLATION, SEEPAGE.
IDENTIFIERS:
-LANDFILL HYDROLOGY.
ABSTRACT:
TECHNICAL AND ECONOMIC ASPECTS OF COMMUNITY REFUSE DISPOSAL SYSTEMS AND
THEIR EFFECTS ON THE ENVIRONMENT ARE IDENTIFIED AND DESCRIBED. SEVEN
LANDFILLS AND TWO INCINERATION SYSTEMS, LOCATED THROUGHOUT THE UNITED
STATES, ARE REVIEWED. FOR EXAMPLE, A SOLID WASTES LANDFILL
STABILIZATION PROJECT CONDUCTED FOR THE CITY OF SANTA CLARA, CALIF.,
PROVED THAT AERATION OF SANITARY LANDFILLS PROVIDES MORE RAPID
STABILIZATION, GREATER REFUSE DENSITY FOLLOWING COMPACTION, THE
CONSERVATION OF LANDFILL SPACE, AND ELIMINATION OF VERMIN AND BACTERIA
BY HIGH-TEMPERATURE OXIDATION.
FIELD 05E, 05D
ACCESSION NO. W71-08907
99
-------
JAMES RIVER-WILSON CREEK STUDY, SPRINGFIELD, MISSOURI.
FEDERAL WATER POLLUTION CONTROL AOMIN., ROBERT S. KERR WATER RESEARCH CENTER,
ADA, OKLA.
VOL 1, JUNE 1969. 60 P, 14 FIG, 2 TAB, 23 REF.
DESCRIPTORS:
#WATER POLLUTION EFFECTS, *WATER POLLUTION CONTROL, #WATER POLLUTION
SOURCES, #FISHKILL, STORM RUNOFF, ODOR, SUBSURFACE RUNOFF, GROUNDWATER
MOVEMENT, LIMESTONES, INFILTRATION, DOMESTIC WASTES, BENTHIC FAUNA,
INDUSTRIAL WASTES, DRAINAGE, AQUIFERS, SINKS, CITIES, SEWAGE TREATMENT,
SEWERS, AERATION, MONITORING, LANDFILLS, BIOCHEMICAL OXYGEN DEMAND,
CHEMICAL OXYGEN DEMAND.
IDENTIFIERS:
DURBAN STORM RUNOFF, JAMES RIVER(MO), WILSON CREEK(MO),
SPRINGFIELD(MO), SEWAGE PLANT BYPASSES.
ABSTRACT:
FISH KILLS, ASSOCIATED WITH STORM RUNOFF, AND ODOROUS AND UNSIGHTLY
CONDITIONS IN WILSON CREEK WHICH FLOWS PAST SPRINGFIELD (MO) AND THE
WILSON'S CREEK BATTLEFIELD NATIONAL PARK PROMPTED INVESTIGATION.
THUNDERSTORMS CAUSED WILSON CREEK TO DOMINATE FLOW AT POINT OF
CONFLUENCE WITH THE JAMES RIVER. SINCE THE AREA IS UNDERLAIN WITH
LIMESTONE, SIGNIFICANT VOLUMES OF SURFACE AND WASTE WATER ENTER THE
UPPER GROUNDWATER AQUIFERS THROUGH NUMEROUS SINKHOLES AND CREVICES,
SOME OF WHICH ARE IN THE WILSON CREEK BED. THIS WATER, PASSING THROUGH
A MAZE OF, FRACTURES AND SOLUTION CHANNELS IN THE LIMESTONE, OFTEN
REAPPEARS IN DEGRADED CONDITION. POSSIBLE POLLUTION CAUSES WERE SEWAGE
TREATMENT PLANT BYPASSES (ESPECIALLY FOLLOWING RAINS), SCOURING OF
SLUDGE DEPOSITS, INDUSTRIAL WASTE DISCHARGES, STORM RUNOFF FROM
SPRINGFIELD, AND SLUGS OF POOR QUALITY SUBSURFACE WATER FROM RADER
SPRING ENTERING SURFACE WATERS. RECOMMENDATIONS ARE STORM RUNOFF
CONTROL, SEWAGE TREATMENT PLANT IMPROVEMENT, IMPROVEMENT OF INDUSTRIAL
WASTE TREATMENT FACILITIES, EFFORT TO RESTORE RADER SPRING TO HIGH
QUALITY, ATTEMPT TO PRECLUDE POLLUTION OF GROUNDWATER AQUIFERS,
CONSTRUCTION OF A RESERVOIR ON THE JAMES RIVER FOR FLOW AUGMENTATION,
AND ESTABLISHMENT OF A MONITORING SYSTEM. HISTORY, DESCRIPTION OF
PROBLEMS AND DISCUSSION ARE INCLUDED. (JONES-WISCONSIN)
FIELD 05C
ACCESSION NO. W71-09154
100
-------
IMPROVEMENTS IN THE FINITE DIFFERENCE SOLUTION OF TWO-DIMENSIONAL DISPERSION
PROBLEMS,
GUELPH UNIV. (ONTARIO).
D. W. LAWSON.
SUPPORTED BY NATIONAL RESEARCH COUNCIL OF CANADA. WATER RESOURCES RESEARCH,
VOL 7, NO 3, P 721-725, JUN 1971. 5 P, 1 FIG, 2 TAB, 6 REF.
DESCRIPTORS:
#DISPERISQN, ^NUMERICAL ANALYSIS, COMPUTER PROGRAMS, DIFFUSION, MIXING,
GROUNDWATER MOVEMENT, SEEPAGE, POROUS MEDIA, EQUATIONS, MATHEMATICAL
MODELS.
IDENTIFIERS:
^FINITE DIFFERENCE METHOD.
ABSTRACT:
TWO MODIFICATIONS OF SHAMIR AND HARLEMAN'S TWO-EQUATION SCHEME FOR THE
FINITE DIFFERENCE SOLUTION OF TWO-DIMENSIONAL DISPERSION PROBLEMS ARE
PRESENTED. THESE MODIFICATIONS IMPROVE BOTH THE ACCURACY AND THE
EFFICIENCY OF THE SOLUTION. SHAMIR AND HARLEMAN«S ONE-EQUATION SCHEME
IS MORE EFFICIENT THAN THE IMPROVED TWO-EQUATION SCHEMES, BUT IT IS NOT
AS ACCURATE. (KNAPP-USGS)
FIELD 05B, 02F, 06A
ACCESSION NO. W71-09611
101
-------
QUANTITY AND CHEMICAL QUALITY OF RETURN FLOW,
UTAH WATER RESEARCH LAB., LOGAN.
JIMMIE L. THOMAS, J. PAUL, AND EUGENE K. ISRAELSEN.
AVAILABLE FROM THE NATIONAL TECHNICAL INFORMATION SERVICE AS PB-201 004,
$3.00 IN PAPER COPY, $0.95 MICROFICHE. REPORT PRWG 77-1, JUNE, 1971, 94 P,
28 FIG, 6 TAB, 92 REF, 4 APPEND. OWRR PROJECT B-038-UTAH{1>.
DESCRIPTORS:
WATER POLLUTION SOURCES, #IQN EXCHANGE, *WATER QUALITY, ^IRRIGATION
EFFICIENCY, SIMULATION, GROUNDWATER, PLANNING, MANAGEMENT, PERCOLATION,
*MODEL STUDIES, ^COMPUTER PROGRAMS.
IDENTIFIERS:
^IRRIGATION RETURN FLOW, HYDROLOGIC-QUALITY MODEL.
ABSTRACT:
A HYBRID COMPUTER PROGRAM IS DEVELOPED TO PREDICT THE WATER AND SALT
OUTFLOW FROM A RIVER BASIN IN WHICH IRRIGATION IS THE MAJOR WATER USER.
A CHEMICAL MODEL WHICH PREDICTS THE QUALITY OF WATER PERCOLATED THROUGH
A SOIL PROFILE IS COMBINED WITH A GENERAL HYOROLOGIC MODEL TO FORM THE
SYSTEM SIMULATION MODEL. THE CHEMICAL MODEL CONSIDERS THE REACTIONS
THAT OCCUR IN THE SOIL, INCLUDING THE EXCHANGE OF CALCUIM, MAGNESIUM,
AND SODIUM CATIONS ON THE SOIL COMPLEX, AND THE DISSOLUTION AND
PRECIPITATION OF GYPSUM AND LIME. THE CHEMICAL COMPOSITION OF THE
OUTFLOW IS A FUNCTION OF THESE CHEMICAL PROCESSES WITHIN THE SOIL, PLUS
THE BLENDING OF UNDIVERTED INFLOWS, EVAPORATION, TRANSPIRATION, AND THE
MIXING OF SUBSURFACE RETURN FLOWS WITH GROUNDWATER. THE SIX COMMON IONS
OF WESTERN WATERS, NAMELY CALCIUM (CA(++)), MAGNESIUM (MG(++M, SODIUM
(NA(+)), SULFATE (S04(=)), CHLORIDE (CL(-)), AND BICARBONATE (HCQ3(->)
ARE CONSIDERED IN THE STUDY. TOTAL DISSOLVED SOLIDS (TOS) OUTFLOW IS
OBTAINED BY ADDING THE INDIVIDUAL IONS. THE OVERALL MODEL OPERATES ON
MONTHLY TIME INCREMENTS. THE MODEL IS TESTED ON A PORTION OF THE LITTLE
BEAR RIVER BASIN IN NORTHERN UTAH. THE MODEL SUCCESSFULLY SIMULATES
MEASURED OUTFLOWS OF WATER AND EACH OF THE SIX IONS FOR 24-MONTH
PERIOD. ONLY SODIUM IONS, WHICH OCCURRED IN SMALL CONCENTRATIONS
COMPRISING APPROXIMATELY 2 PERCENT OF THE TOTAL SALT OUTFLOW, EXHIBIT
SIGNIFICANT DISCREPANCIES BETWEEN PREDICTED AND OBSERVED VALUES. ALL
OTHER IONS AGREE WITHIN 10 PERCENT ON A WEIGHT BASIS FOR THE TWO-YEAR
MODEL PERIOD, WITH CORRELATION COEFFICIENTS RANGING FROM .87 TO .97.
THE USEFULNESS OF THE MODEL IS DEMONSTRATED BY A MANAGEMENT STUDY OF
THE PROTOTYPE SYSTEM. FOR EXAMPLE, PRELIMINARY RESULTS INDICATED THAT
THE AVAILABLE WATER SUPPLY COULD BE USED TO IRRIGATE ADDITIONAL LAND
WITHOUT UNDULY INCREASING THE SALT OUTFLOW FROM THE BASIN. WITH MINOR
ADJUSTMENTS THE MODEL CAN BE APPLIED TO OTHER AREAS.
FIELD 05B, 02A, 02G, 03F, 02K
ACCESSION NO. W71-09936
102
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REGULATIONS FOR PREVENTION OF POLLUTION OF SUBSURFACE WATERS OF THE STATEt
MISSOURI WATER POLLUTION BOARD, JEFFERSON CITY, MO.
1967, 3 P.
DESCRIPTORS
^MISSOURI, ^PERMITS, ^SUBSURFACE WATERS, *WATER POLLUTION CONTROL,
WATER POLLUTION TREATMENT, WELL PERMITS, ADMINISTRATIVE AGENCIES,
CONTROL, REGULATION, AQUIFERS, WELL REGULATIONS, SUBSURFACE DRAINAGE,
WASTE TREATMENT, WASTE WATER TREATMENT, WATER POLLUTION, PERCOLATING
WATER, WATER CONSERVATION, ADMINISTRATION.
ABSTRACT:
THE PURPOSE OF THIS REGULATION IS TO PROTECT SUBSURFACE WATERS FROM
POLLUTION. A PERMIT MUST BE OBTAINED FROM THE STATE WATER POLLUTION
BOARD BY ANY PERSON DESIRING TO ERECT, MODIFY, COMMENCE, OR OPERATE ANY
SYSTEM FOR THE DISPOSAL OF SEWAGE OR OTHER WASTE INTO THE SUBSURFACE
WATERS OF THE STATE. OPERATING PERMITS SHALL SPECIFY THE CO^MTIONS
UPON WHICH THEY ARE ISSUED AND SHALL BE DESIGNED TO CARRY CUT THE
PURPOSES OF THE STATE WATER POLLUTION ACT. THE BOARD SHALL ISSUE
CONSTRUCTION PERMITS AFTER APPROVING PRELIMINARY ENGINEERING REPORTS
AND DETAILED FINAL PLANS SUBMITTED BY A REGISTERED ENGINEER. THE
OPERATING PERMIT SHALL BE ISSUED UPON THE BOARD'S DETERMINATION THAT
THE COMPLETED WORK SUBSTANTIALLY ADHERES TO THE APPROVED PLANS.
REPRESENTATIVES OF THE BOARD SHALL CONDUCT PERIODIC INSPECTION OF ALL
OPERATING PLANTS. THE PERMIT OF ANY PLANT OPERATING IN A FASHION NOT IN
ACCORD WITH APPROVED PLANS SHALL BE REVOKED AFTER ALLOWING A REASONABLE
TIME FOR CORRECTION. THE BOARD MUST BE NOTIFIED WHEN ANY WELL IS
ABANDONED, AND SUCH WELL MUST BE PLUGGED OR SEALED TO PREVENT
POLLUTION. NO WASTE THAT CAUSES POLLUTION IS TO BE PLACED IN SINKHOLES
WHICH CONNECT WITH AQUIFERS. (HORWITZ-FLORIDA)
FIELD 05G, 06E
ACCESSION NO. W71-10157
103
-------
TRANSPORT OF MINERAL OIL COMPONENTS TO GROUNDWATER1. MODEL EXPERIMENTS ON THE
TRANSFER OF HYDROCARBONS FROM A RESIDUAL OIL ZONE TO TRICKLING WATER,
KONINKLIYKE/SHFLL-LABORATORIUM, AMSTERDAM (NETHERLANDS)*
M. VAN DER WAARDEN, A. L. A. M. BRIDIE, AMD W. M. GROENEWOUD.
WATER RESEARCH, VOL 5, NO 5, P 213-226, MAY 1971. 14 P, 7 FIG, 3 TAB, 12 REF.
WATER,
WASTES,
DESCRIPTORS:
*PATH OF POLLUTANTS, *LEACHING, #SOIL WATER MOVEMENT, *OILY
#GROUNDWATER RECHARGE, MODEL STUDIES, HYDRAULIC MODELS, OIL
WATER POLLUTION SOURCES.
IDENTIFIERS:
*OIL SPILLS.
ABSTRACT:
OIL SPILLS IN SOILS BECOME IMMOBILE AFTER SOME TIME. SUBSEQUENT
RAINFALL MAY THEN LEACH OUT WATER-SOLUBLE COMPONENTS, WHICH ARE CARRIED
DOWNWARD. IN LABORATORY EXPERIMENTS A PACK OF NON-ADSORBING GLASS
PARTICLES WAS USED AS A SOIL MODEL TO STUDY THE TRANSFER OF OIL
COMPONENTS TO GROUNDWATER. OIL WAS INJECTED INTO A ZONE WITH RESIDUAL
WATER SATURATION OF THIS MODEL AND ALLOWED TO DISPERSE FREELY.
SUBSEQUENTLY WATER WAS ALLOWED TO TRICKLE THROUGH THE PACK AND THE
DRAIN WATER, WHICH DID NOT CONTAIN ANY FREE OIL, WAS ANALYZED FOR
CONTAMINANTS. EXPERIMENTS WERE CARRIED OUT WITH A GAS OIL RAFFINATE
CONTAINING VERY SMALL AMOUNTS OF 2-1SOPROPYLPHENOL AS A MODEL FOR
ACTUAL MINERAL OIL PRODUCTS: GASOLINE,
EXPERIMENTS WATER-EXTRACTARLE
AN OIL ZONE BY TRICKLING WATER AT A
RATE DETERMINED BY THE PARTITION COEFFICIENT OF THE COMPONENTS AND BY
THE WATER/OIL RATIO. WHEN THE GLASS PARTICLES WERE REPLACED BY NATURAL
DUNE SAND THE TRANSFER OF OIL COMPONENTS WAS DELAYED BY ADSORPTION AND
THEIR CONCENTRATION IN THE DRAIN WATER DECREASED CORRESPONDINGLY. UNDER
FIELD CONDITIONS THESE EFFECTS OF ADSORPTION MIGHT BE MUCH STRONGER; IN
ADDITION, CHEMICAL OR BIOLOGICAL OXIDATION AND EVAPORATION MAY ALSO TO
SOME EXTENT DETERMINE THE FATE OF OIL IN SOIL. (KNAPP-USGS)
FIELD 05B, 02G, 02F
ACCESSION NO. W71-10325
TRANSFERABLE COMPONENTS AND WITH
KEROSENE AND GAS OIL. IN ALL THE
COMPONENTS WERE LEACHED OUT FROM
104
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CONTRIBUTION OF FERTILIZERS TO WATER POLLUTION,
MISSOURI UNIV., COLUMBIA. WATER RESOURCES RESEARCH CENTER.
G. E. SMITH.
IN: 2ND COMPENDIUM OF ANIMAL WASTE MANAGEMENT, JUNE 1969, PAPER NO. 7, 16 P,
7 TAB, 5 FIG, 24 REF. PHS-FWPCA-USDI - WP00533.
DESCRIPTORS:
#EUTROPHICATION» FERTILIZERS, FARM WASTES, NUTRIENTS, DENITRIFICATION,
NITRIFICATION, AMMONIFICATION, LEACHING, EROSION, NITROGEN, RUNOFF,
WATER POLLUTION CONTROL, GROUNDWATER, SEPTIC TANKS, MANAGEMENT.
IDENTIFIERS:
*METHEMOGLOBIN, NITRATE MOVEMENT, FEEDLOTS, RESIDUAL ACCUMULATION, SOIL
CORES.
ABSTRACT:
WITHOUT CHEMICAL SOIL AMENDMENTS THE UNITED STATES WOULD BE A FOOD
IMPORTING NATION. DESPITE LIBERAL FERTILIZER USE, CROPS ARE REMOVING
MORE NITROGEN AND MINERALS THAN ARE BEING ADDED IN SOIL AMENDMENTS.
MANY SHALLOW WELLS IN MISSOURI ARE CONTAMINATED WITH M TRATES AS A
RESULT OF LEACHING FROM LIVESTOCK FEEDING OPERATIONS. THE NITOATE IS
NOT ASSOCIATED WITH LOSSES FROM FERTILIZED FARM FIELDS IN MOST CASES.
THERE IS LITTLE QUESTION THAT SOME OF THE NUTRIENTS APPLIED IN CHEMICAL
FERTILIZERS ARE MOVING INTO BOTH SURFACE AND GROUND WATER; THE
PERCENTAGE IS THOUGHT TO BE RELATIVELY SMALL. IT IS POSSIBLE THAT
NUTRIENT LOSSES MAY BE LESS WHERE GOOD FERTILIZATION PRACTICES ARE
FOLLOWED THAN ON UNFERTILIZED SOILS. (SEE ALSO W71-10366) (IOKA STATE)
FIELD 05G, 05B
*
ACCESSION NO. W71-10372
105
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POLLUTION OF UNDERGROUND WATER.
WYOMING STATUTES SECS 41-121* 41-126 (1959).
DESCRIPTORS:
^WYOMING, *GROUNDWATER, #WATER POLLUTION, *WATER POLLUTION CONTROL,
POLLUTION ABATEMENT, SUBSURFACE WATERS, PERCOLATING WATER, UNDERGROUND,
WELLS, SALINE WATER INTRUSION, WATER POLLUTION SOURCES, MINERALOGY,
INDUSTRIAL WASTES, MUNICIPAL WASTES, SEWAGE, WATER QUALITY CONTROL,
WATER POLLUTION TREATMENT, ADMINISTRATIVE AGENCIES, LEGISLATION, PUBLIC
HEALTH, REGULATION, LEGAL ASPECTS, ADMINISTRATION.
ABSTRACT:
AN ACT RELATING TO UNDERGROUND WATER PROVIDES THAT POLLUTION CF
UNDERGROUND WATER MEANS ANY IMPAIRMENT OF THE NATURAL QUALITY OF SUCH
WATER, HOWEVER CAUSED, INCLUDING IMPAIRMENT BY SALINES, MINERALS,
INDUSTRIAL WASTES, DOMESTIC WASTES* OR SEWAGE. UNDERGROUND WATER REFERS
TO ANY WATER BENEATH THE SURFACE OF THE LAND OR THE BED OF ANY STREAM,
LAKE, OR OTHER BODY OF SURFACE WATER. IN THE ADMINISTRATION AND
ENFORCEMENT OF THIS ACT THE STATE ENGINEER IS AUTHORIZED TO REQUIRE THE
ABATEMENT OF ANY CONDITION, OR THE SEALING OF ANY WELL, RESPONSIBLE FOR
ADMITTING POLLUTING MATERIALS INTO AN UNDERGROUND WATER SUPPLY, AND IS
FURTHER AUTHORIZED TO PERFORM NECESSARY DUTIES RELATING TO
INVESTIGATION, REGULATION, AND CONSTRUCTION OF WELLS IN ORDER TO
CONSERVE THE STATE'S UNDERGROUND WATER RESOURCES. (SMILJANICH-FLORIDA)
FIELD 06E, 05G
ACCESSION NO. W71-10446
106
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TRITIATEO WATER AS A TRACER IN THE DUMP LEACHING OF COPPER,
BUREAU OF MINES* BARTLESVILLE, OKLA. BARTLESVILLE PETROLEUM RESEARCH CENTER.,
AND INSTITUTE OF MINING AND TECHNOLOGY, SOCORRO, N. MEX. DEPT. OF
GROUND-WATER HYDROLOGY.
F. E. ARMSTRONG, G. C. EVANS, AND G. E. FLETCHER.
BUREAU OF MINES REPORT OF INVESTIGATIONS RI 7510, MAY 1971. 39 P, 12 FIG, 5
TAB, 10 REF, 5 APPEND.
DESCRIPTORS:
#TRITIUM, #TRACERS, BLEACHING, #COPPER» #WASTE DUMPS, MINE WASTES?
MINING, GROUNDWATER MOVEMENT, FLOW PROFILES, SAMPLING, DATA COLLECTION,
WELLS, METHODOLOGY, CHEMICAL ANALYSIS.
IDENTIFIERS:
TRITIATED WATER(TRACER), MINE DUMP LEACHING.
ABSTRACT:
TRITIATED WATER WAS USED AS A TRACER TO FOLLOW THE PATH OF LEACH
LIQUIDS AS THEY FLOW THROUGH A COPPER-MINE DUMP. SEMI PERMEABLE LAYERS,
PRODUCED WITHIN THE DUMP BY COMPACTION AND 'STRATIFICATION1 OF
DEPOSITED DUMP MATERIAL, RESTRICT THE VERTICAL MOVEMENT OF WATER.
KNOWLEDGE OF THIS RESTRICTION AIDS IN THE OPTIMIZATION OF THE LEACHING
PROCESS. THE PORTION OF THE DUMP STUDIED WAS APPROXIMATELY 2,000 FEET
LONG, 800 FEET WIDE, AND 200 FEET HIGH. A TOTAL OF 94 CURIES OF
TRITIATED WATER WAS INJECTED INTO THE DUMP AT THE RATE OF 650 GPM OVER
A PERIOD OF 39 HOURS. THE LEACH LIQUID WAS SAMPLED AT NATURAL SURFACE
OUTFLOWS AND THROUGH A SERIES OF WELLS, SOME DRILLED TO THE BOTTOM OF
THE DUMP AND OTHERS TO INTERMEDIATE LEVELS. MORE THAN 3,300 SAMPLES
WERE ANALYZED EITHER BY LIQUID SCINTILLATION COUNTING OR BY GAS
COUNTING. DATA OBTAINED PERMITTED CALCULATION OF FLOW PATHS, RECYCLE
TIMES, TOTAL FLUID VOLUME, AND ESTIMATES OF RETENTION TIMES IN VARIOUS
PORTIONS OF THE DUMP. LEACHING WITH SUBSEQUENT RECOVERY FROM THE
PREGNANT LEACH LIQUID IS AN IMPORTANT SOURCE OF COPPER. (WOODARD-USGS)
FIELD 05B, 02F
ACCESSION NO. W71-11255
107
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A METHOD TO DESCRIBE THE FLOW OF RADIOACTIVE IONS IN GROUND WATER,
GEOLOGICAL SURVEY, DENVER, COLO.
DAVID B. GROVE.
AVAILABLE FROM NAT. TECH. INF. SERVICE, SPRINGFIELD, VA. 22151 PRICE $3.00
PRINTED COPY, 95 CENTS MICROFICHE. SANDIA LABORATORIES CONTRACT REPORT
SC-CR-70-6139, DEC 1970. 38 P, 4 FIG, 1 TAB, 17 REF.
DESCRIPTORS:
#PATH OF POLLUTANTS, #RAD10 I SOTOPES, #GRQUNDWATER MOVEMENT,
^DISPERSION, *ION EXCHANGE, DIFFUSION, MIXING, RADIOACTIVITY,
RADIATION, RADIOACTIVE WASTES, IONS, EQUATIONS, MATHEMATICAL MODELS,
CONVECTION, NUCLEAR POWERPLANTS.
ABSTRACT:
AN EQUATION BASED ON INSTANTANEOUS ION EXCHANGE AND ON A LINEAR
ADSORPTION ISOTHERM PREDICTS RADIOACTIVE IONIC CONCENTRATIONS IN
GROUNDWATER SYSTEMS AS A FUNCTION OF TIME AND POSITION. THIS EQUATION
ACCOUNTS FOR RADIOACTIVE DECAY, ION EXCHANGE, AND LONGITUDINAL
HYDRAULIC DISPERSION. DATA NECESSARY FOR SOLUTION INCLUDE GROUNDWATER
VELOCITY, ION-EXCHANGE DISTRIBUTION COEFFICIENT, EXCHANGE RATIO, AND
DISPERSION COEFFICIENT. THE NEED FOR SIMPLICITY DICTATES THE USE OF AN
EQUILIBRIUM CONCEPT RATHER THAN A RATE PROCESS TO DESCRIBE THE
ION-EXCHANGE REACTION. (KNAPP-USGS)
FIELD 07B, 05B, 02F
ACCESSION NO. W71-11356
108
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NELSON V C AND C PLYWOOD CORP (STATUTE OF LIMITATIONS AND THEORIES OF LIABILITY
FOR POLLUTING UNDERGROUND WATER).
465 P2D 314-326 (MONT 1970).
DESCRIPTORS:
^MONTANA, *WATER POLLUTION SOURCES, *WATER WELLS, ^REMEDIES, INDUSTRIAL
WASTES, WATER POLLUTION, POLLUTION ABATEMENT, WATER POLLUTION EFFECTS,
POLLUTANTS, WASTE DISPOSAL, GROUNDWATER, PERCOLATING WATER,
PERCOLATION, PATH OF POLLUTANTS, WOOD WASTES, PULP AND PAPER INDUSTRY,
DAMAGES, HYDROLOGIC DATA, LEGISLATION, LAND TENURE, LEGAL ASPECTS,
JUDICIAL DECISIONS, WELLS.
ABSTRACT:
PLAINTIFF LANDOWNER SUED DEFENDANT CORPORATION FOR DAMAGES FOR THE
POLLUTION OF HIS WELL BY DEFENDANT'S PLYWOOD OPERATION. PLAINTIFF
CONTENDED THAT THE DEFENDANT'S DUMPING OF GLUE WASTES INTO THE GROUND
POLLUTED HIS WELL AND RENDERED IT UNFIT FOR USE. DEFENDANT CONTENDED
THAT THE TRIAL JUDGE INCORRECTLY INSTRUCTED THE JURY ON BOTH NEGLIGENCE
AND PRIVATE NUISANCE, AN ADJOINING LAND-OWNER IS NOT RESPONSIBLE FOR
DAMAGE TO THE PERCOLATING WATER OF A NEIGHBOR, AND THE STATUTE OF
LIMITATIONS HAD RUN ON A PERMANENT NUISANCE. IN AFFIRMING A VERDICT FOR
PLAINTIFF, THE SUPREME COURT OF MONTANA HELD THAT THEORIES OF
NEGLIGENCE AND PRIVATE NUISANCE ARE BOTH APPLICABLE TO UNDERGROUND
WATER POLLUTION, AND THAT DUE TO ADVANCES IN HYDROLOGICAL SCIENCE,
UNDERGROUND WATER POLLUTION CAN BE PROVEN AND IS THUS ACTIONABLE. THE
COURT ALSO RULED THAT WHERE A PRIVATE NUISANCE IS TEMPORARY AND
CONTINUOUS IN CHARACTER, ACTUAL DAMAGES CREATE SEPARATE CAUSES OF
ACTION. THUS, A RECOVERY MAY BE HAD FOR DAMAGES ACCRUING WITHIN THE
STATUTORY PERIOD NEXT PRECEDING THE COMMENCEMENT OF THE ACTION. THE
POLLUTION OF GROUNDWATER BY THE DUMPING OF GLUE WASTES IS SUCH A
CONTINUING, TEMPORARY NUISANCE. (SMILJANICH-FLORI DA)
FIELD 06E, 5G
ACCESSION NO. W71-11692
109
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NORMAN V GREENLAND DRILLING CO (INFERRED LIABILITY FOR WATER POLLUTION FROM OIL
PRODUCTION OPERATIONS).
403 P2D 507-511 (OKLA 1965).
DESCRIPTORS:
^OKLAHOMA, #WATER POLLUTION SOURCES, #OIL WASTES* ^REMEDIES, WATER
POLLUTION, WATER POLLUTION EFFECTS, POLLUTION ABATEMENT, PATH OF
POLLUTANTS, OIL INDUSTRY, OIL, GASES, POLLUTANTS, PERCOLATION, WASTES,
WASTE DISPOSAL, LEGISLATION, WELLS, IMPAIRED WATER QUALITY, WATER
POLLUTION CONTROL, DAMAGES, LEGAL ASPECTS, JUDICIAL DECISIONS,
GROUNDWATER.
ABSTRACT:
PLAINTIFF LANDOWNER SUED DEFENDANT OIL DRILLING COMPANY TO RECOVER
DAMAGES FOR THE POLLUTION OF LAND, PONDS, AND A WATER WELL BY GAS, OIL
AND SALT WATER THAT ESCAPED FROM DEFENDANT'S OIL WELL. PLAINTIFF
CONTENDED THAT AN OKLAHOMA STATUTE, RELATING TO THE FLOW OF OIL WASTES
OVER LAND, PRECLUDED THE NECESSITY FOR PROOF OF DEFENDANT'S NEGLIGENCE.
PLAINTIFF ALSO CONTENDED THAT THE DOCTRINE OF RES IPSA LOGQITUR WAS
APPLICABLE AND INFERRED DEFENDANT'S NEGLIGENCE. DEFENDANT DENIED
NEGLIGENCE AND CONTENDED THAT THE STATUTE DID NOT APPLY. REVERSING A
DISMISSAL OF PLAINTIFF'S ACTION, THE SUPREME COURT OF OKLAHOMA HELD
THAT THE OKLAHOMA STATUTE RELATING TO DAMAGES FROM THE FLOW OF OIL
WASTES OVER LAND IS NOT APPLICABLE TO POLLUTION FROM UNDERGROUND
SOURCES. THE COURT HELD, HOWEVER, THAT DEFENDANT'S NEGLIGENCE COULD BE
FAIRLY INFERRED FROM THE FACTS. WHERE AN INJURY-PRODUCING POLLUTION
SOURCE IS SHOWN TO BE UNDER THE MANAGEMENT OF A DEFENDANT, AND THE
ACCIDENT IS SUCH AS DOES NOT ORDINARILY HAPPEN IF PROPER CARE IS USED,
IT AFFORDS A REASONABLE INFERENCE, IN THE ABSENCE OF EXPLANATION, THAT
LACK OF CARE CAUSED THE ACCIDENT. (SMILJANICH-FLORIDA)
FIELD 06E, 05G
ACCESSION NO. W71-11724
110
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STATISTICAL POROUS MEDIA HYDRODYNAMICS,
ILLINOIS UNIV., URBANA. DEPT. OF MINING METALLURGY AND PETROLEUM ENGINEERING.
A. E. SCHEIDEGGER.
ILLINOIS UNIVERSITY WATER RESOURCES CENTER RESEARCH REPORT NO 17, JUL 1968.
70 P, 5 FIG, 1 TAB, 16 REF. OWRR PROJECT B-010-I LL(
DESCRIPTORS:
^STOCHASTIC PROCESSES, *POROUS MEDIA, #GROUNDWATER MOVEMENT,
^STATISTICAL MODELS, *PATH OF POLLUTANTS, MATHEMATICAL MODELS,
PROBABILITY, THERMODYNAMICS, FLOW, MASS TRANSFER, DIFFUSION, MIXING,
DISPERSION.
IDENTIFIERS:
^MULTIPHASE FLOW.
ABSTRACT:
AN INVESTIGATION WAS MADE OF THE STOCHASTIC ASPECTS OF SINGLE AND
MULTIPLE PHASE FLOW THROUGHOUT POROUS MEDIA. THE COMPLETE
CORRESPONDENCE BETWEEN TRANSPORT THEORY AND THERMODYNAMICS WAS
ESTABLISHED, AND THE COROLLARIES OF THE THERMODYNAM I C STABILITY
CONDITIONS IN TRANSPORT THEORY WERE INVESTIGATED. A FURTHER DEVELOPMENT
OF THE CORRESPONDENCE BETWEEN TRANSPORTED QUANTITIES AND THEMODYNAM ICS
WAS OBTAINED BY EXTENDING THE THEORY TO NON-POSITIVE DEFINITE
TRANSPORTED QUANTITIES. THE THEORY WAS THEN APPLIED TO FLOW THROUGH
POROUS MEDIA. A GENERAL INVESTIGATION WAS MADE OF THE POSSIBILITY OF
THE DEVELOPMENT OF A STEADY STATE IN FRONTAL DISPLACEMENT PROCESSES IN
POROUS MEDIA WITH AND WITHOUT 'FINGERS', WITH THE RESULT THAT THIS
STABILIZATION APPEARS TO BE IMPOSSIBLE. A NEW TYPE OF STATISTICAL MODEL
FOR FLOW THROUGH POROUS MEDIA WAS BASED ON A RANDOM ENSEMBLE OF
TOPOLOGICAL GRAPHS. (KNAPP-USGS)
FIELD 02F, 05B
ACCESSION NO. W71-11776
111
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WATER QUALITY IN RELATION TO FARM USE OF FERTILIZER,
AGRICULTURAL RESEARCH SERVICE, FORT COLLINS, COLO. SOIL AND WATER
CONSERVATION DIV.
FRANK G. VIETS, JR.
BIOSCIENCE, VOL 21, NO 10, P 460-467, 1971. 2 TAB, 35 REF.
DESCRIPTORS:
*WATER QUALITY, #CROP PRODUCTION, #FERTILIZERS, #WATER POLLUTION
SOURCES, NITROGEN, NITRATES, NITROGEN CYCLE, PHOSPHORUS, REGULATION,
GROUNDWATER, RUNOFF, PERCOLATION, EUTROPHICATI ON, DRAINAGE EFFECTS,
DETERGENTS, DENITRIFICATION, NITRITES, BIOCHEMICAL OXYGEN DEMAND.
ABSTRACT:
THE EXTENT OF COMMERCIAL FERTILIZER USAGE TO DETERIORATION OF WATER
QUALITY IS DISCUSSED. THE SIGNIFICANCE OF DRAINAGE ENRICHMENT BY
FERTILIZERS MUST BE EVALUATED ON THE BASIS OF COMPOSITION OF AFFECTED
DRAINAGE AND THE EFFECTS OF VARIOUS LAND USES. FERTILIZERS PERMIT
HIGHER PRODUCTION ON FEWER CULTIVATED ACRES, THUS REDUCTION OF
FERTILIZERS WOULD REDUCE FOOD SUPPLIES AND INCREASE FOOD PRICES. THE
ASSEMBLED DATA INDICATE THAT FERTILIZER RESTRICTIONS IMPOSED ON
NATIONAL OR STATE LEVEL WOULD NOT RESULT IN SUFFICIENT IMPROVEMENT IN
WATER QUALITY TO RISK HAZARDS OF A LESS ABUNDANT FOOD SUPPLY.
RESTRICTIONS COULD RESULT IN MORE NITROGEN AND PHOSPHORUS IN SEDIMENT
AND RUNOFF DUE TO CROP EXPANSION OF ACREAGE WITH HIGH EROSION HAZARD
(LARGELY ROW CROPS) TO MEET FOOD AND FIBER REQUIREMENTS. RESTRICTION OF
FERTILIZER USE WITHIN A WATERSHED OR GROUND WATER BASIN IS IN ORDER
WHEN FACTS JUSTIFY IT BUT RESTRICTIONS SHOULD NOT BE IMPOSED UNTIL ALL
SOURCES OF NITROGEN AND PHOSPHORUS INPUTS ARE INVENTORIED AND MOST
EFFECTIVE AND LEAST EXPENSIVE CONTROLS IMPOSED FROM AN ESTABLISHED
FACTUAL PRIORITY LIST. (JONES-WISCONSIN)
FIELD 05C, 05B
ACCESSION NO. W71-12084
112
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THE NITRATE DILEMMA.
HIGH PLAINS UNDERGROUND WATER CONSERVATION DISTRICT NO. 1, LUBROCK, TEX.
CROSS SECTION, VOL 16, NO 6, JUNE 1970, P 1, 3-4. 3 FIG.
DESCRIPTORS:
^NITROGEN COMPOUNDS, ^POLLUTION IDENTIFICATION, #WATER QUALITY,
^MONITORING, #GROUNDWATER, NITRATE, NITRITES, NITROGEN-CYCLE, HISTORY,
SOIL ANALYSIS, WATER TRANSFER, IRRIGATION PRACTICES, LEACHING, TEXAS.
IDENTIFIERS:
*OGALLALA AQUIFER, HIGH PLAINSCTEXAS), PARMER COUNTY(TEXAS), HOLLY
SUGAR STUDIES.
ABSTRACT:
THE HIGH PLAINS UNDERGROUND WATER CONSERVATION DISTRICT AND THE TEXAS
WATER DEVELOPMENT BOARD HAVE A CONTINUING PROGRAM FOR MONITORING WATER
QUALITY IN THE OGALLALA AQUIFER TO: (1) APPRAISE GROUNDWATER FOR THE
LANDOWNER, (2) ESTABLISH REGIONAL WATER QUALITY, AND (3) DEVELOP A
HISTORICAL DATA BASE. SOIL ANALYSIS, WATER IMPORTATION, AND INDUSTRIAL
DEVELOPMENT REQUIRE THE COLLECTION OF SUCH DATA. THERE IS NO EVIDENCE
THAT NITRATE, NITRITE, OR ANY OTHER NITROGEN-CYCLE ELEMENTS ARE
PREVALENT WATER POLLUTERS IN THE HIGH PLAINS AREA. THE AVERAGE NITRATE
CONTENT WAS 7.1 PARTS PER MILLION (PPM) FOR 99 WATER SAMPLES COLLECTED
IN 1965, AND 6.8 PPM FOR 86 SAMPLES COLLECTED IN 1968 IN PARMER COUNTY
CHANGES IN NITRATE CONTENT OF ALL THE COMPARABLE SAMPLES WERE WITHIN
THE RANGE OF ERROR ANALYSIS AND METHODS OF COLLECTION. GROUNDWATER IN
PARMER COUNTY IS LOW IN NITRATES, AND IS NOT AFFECTED BY HIGH DENSITY
FARMING AND FERTILIZATION PRACTICES, ALTHOUGH FARMERS IN THE AREA USE
MORE NITROGEN FERTILIZER AND IRRIGATION THAN IN THE PAST. PLANTS USE
70£ OF THE APPLIED NITROGEN; ANAEROBIC SOIL BACTERIA AND/OR DEEP
SEEPAGE MAY ACCOUNT FOR 30%. THE HOLLY SUGAR STUDIES INDICATE THAT
NITROGEN IS STORED IN SOIL. NITROGEN-MIGRATION RESEARCH IS NEEDED
PARTICULARLY FOR IMPORTED SURFACE WATER TRANSFER, OVER IRRIGATION AND
LEACHING. (POPKIN-ARIZONA)
FIELD 02K, 03F, 04B , 05A
ACCESSION NO. W71-12122
113
-------
FUNDAMENTAL VARIATIONS IN THE WATER QUALITY WITH PERCOLATION IN INFILTRATION
BASINS,
INSTITUTE FOR WATER RESEARCH LTD., DORTMUND (WEST GERMANY).
W. H. FRANK.
PAPER NO 7 OF ARTIFICIAL GROUNDWATER RECHARGES CONFERENCE, UNIVERSITY OF
READING, ENGLAND, SEPTEMBER 21-24, 1970: THE WATER RESEARCH ASSOCIATION,
MARLOW, ENGLAND. 22 P, 25 FIG.
DESCRIPTORS:
^ARTIFICIAL RECHARGE, ^INDUCED INFILTRATION, *PIT RECHARGE, *WATER
TREATMENT, *FILTATION, ALLUVIA CHANNELS, SURFACE-GROUNOWATER
RELATIONSHIPS, PERMEABILITY, ALGAE, DISSOLVED OXYGEN.
IDENTIFIERS:
#RUHR VALLEY.
ABSTRACT:
THE DORTMUNDER STADTWERKE AG SUPPLIES ABOUT 100 MILLION CU M OF
MUNICIAL AND INDUSTRIAL WATER PER YEAR FROM THE GROUNDWATER COLLECTED
IN THE ALLUVIUM OF THE RUHR VALLEY. THE AQUIFER IS 4 TO 5 M DEEP AND IS
COVERED BY A LAYER OF MEADOW LOAM 0.5 TO 2 M THICK. THE PERMEABILITY OF
THE GRAVEL IS IN GENERAL VERY GOOD, ABOUT .001 TO 0.01 M/SEC. MORE THAN
90% OF THE GROUNDWATER CONSISTS OF VARYING PROPORTIONS OF BANK
INFILTRATION AND ARTIFICIALLY RECHARGED GROUNDWATER. IN DRY YEARS WITH
LITTLE WATER FLOW, MORE THAN 75% OF THE REQUIRED WATER MUST BE
ARTIFICIALLY RECHARGED. THE INFILTRATION TAKES PLACE IN BASINS
MEASURING 25 X 200 M. A LAYER OF SAND 50 TO 70 CM THICK IS LAID DOWN AS
A FILTER BED. THIS SAND HAS AN EFFECTIVE PARTICLE DIAMETER (0 10?) OF
0.12 MM, AND AT (D 60%) OF 0.3 MM A COEFFICIENT OF NON-UNIFORMITY OF U
= 2.5. ITS PERMEABILITY IN MOST AREAS IS LESS THAN THAT OF THE SUBSOIL.
BOTH THE BANK INFILTRATION AND THE ARTIFICIALLY RECHARGED GROUNDWATER
ARE RE-COLLECTED AT A DEPTH OF 7 M AFTER A PASSAGE OF AT LEAST 50 M
THROUGH THE SOIL AND PASSED DIRECTLY INTO THE MAINS WITHOUT FURTHER
TREATMENT AFTER A LIGHT PRECAUTIONARY CHLORI NAT I ON. SUSPENDED ORGANIC
AND INORGANIC MATTER IS LARGELY RETAINED ON THE FILTER SURFACE.
TOGETHER WITH THE ALGAE WHICH GROW THERE, THEY CAUSE AN OBSTRUCTION IN
THE FILTER. THE DISSOLVED ORGANIC MATERIAL IN THE WATER IS MINERALIZED
WITH THE HELP OF THE BACTERIA WHICH INHABIT THE FILTER, OXYGEN BEING
CONSUMED AND CARBON DIOXIDE LIBERATED. IN THE WATER ABOVE AN EXPOSED
SAND FILTER, ALGAE CAUSE A DISTINCT DROP IN THE PHOSPHATE ION
CONCENTRATION. IN THE UPPER MOST LAYERS OF SAND MORE PHOSPHATE IONS ARE
LIBERATED BY MICROBIOL DECOMPOSITION THAN THE BACTERIA NEED FOR THEIR
METABOLISM. (KNAPP-USGS)
FIELD 04B, 03A, 05F
ACCESSION NO. W71-12410
114
-------
WENDTLANDT V. NATIONAL CO-OPERATIVE REFINERY ASS'N (SALT WATER INTRUSION
RESULTING FROM OIL DRILLING OPERATIONS).
215 P. 2D 209-215 (KAN. 1950).
DESCRIPTORS:
^KANSAS, *SALINE WATER INTRUSION, #OIL WASTES* ^REMEDIES, WATER
POLLUTION, JUDICIAL DECISIONS, RELATIVE RIGHTS, LEGAL ASPECTS, STATE
GOVERNMENTS, STATE JURISDICTION, OIL INDUSTRY, SALINE WATER, SUBSURFACE
WATERS, GROUNDWATER, PERCOLATING WATERS, DRILLING, OIL WELLS, WATER
SUPPLY, FARMS, WATER POLLUTION EFFECTS, WATER POLLUTION SOURCES,
DAMAGES.
ABSTRACT:
PLAINTIFF LANDOWNER SOUGHT TO RECOVER ACTUAL AND PUNITIVE DAMAGES FOR
PERMANENT INJURY TO HER LAND CAUSED BY SALT WATER FROM DEFENDANT'S OIL
DRILLING OPERATIONS. DEFENDANT OPERATED SEVERAL OIL WELLS ON
PLAINTIFF'S LAND PURSUANT TO A LEASE ARRANGEMENT. THE OIL WELLS
PRODUCED OVER 5000 BARRELS OF SALT WATER PER MONTH. DEFENDANT DISPOSED
OF THIS BY PUMPING IT INTO A LARGE PIT WITH A CAPACITY OF 3,500
BARRELS. DEFENDANT KNEW THE SALT WATER WAS SEEPING INTO THE SOIL, YET
TOOK NO CORRECTIVE ACTION. PORTIONS OF PLAINTIFF'S LAND BECAME POLLUTED
BY SALT WATER AND USELESS FOR AGRICULTURAL PURPOSES. PLAINTIFF ALLEGED
THAT THE VALUE OF HER LAND HAD BEEN PERMANENTLY DECREASED BY $6000.
PLAINTIFF WAS AWARDED $1092 IN PERMANENT DAMAGES AND $5000 IN PUNITIVE
DAMAGES. DEFENDANT APPEALED, CONTENDING THAT THE EVIDENCE WAS
INSUFFICIENT TO WARRANT PUNITIVE DAMAGES. THE SUPREME COURT TO KANSAS
AFFIRMED THE JUDGMENT ON CONDITION THAT THE PUNITIVE DAMAGES RE REDUCED
TO $2500. THE COURT HELD THAT PUNITIVE DAMAGES ARE PERMISSIBLE WHERE A
DEFENDANT INTENTIONALLY EMPTIES SALT WATER ON A PLAINTIFF'S LAND,
KNOWING IT WOULD CAUSE SERIOUS DAMAGE. (HORWITZ-PLORIDA)
FIELD 06E, 05B
ACCESSION NO. W71-13521
115
-------
HAVEMAN V BEULOW (POLLUTION OF WATERWELL).
317 P. 20 313-317 (WASH. 1950).
DESCRIPTORS:
^WASHINGTON, *WATER POLLUTION SOURCES, ^DAMAGES, #WATER WELL, IMPAIRED
WATER QUALITY, UNDER SEEPAGE, WATER POLLUTION, INDUSTRIAL WASTES,
POLLUTANTS, INFILTRATION, GROUNDWATER MOVEMENT, SUBSURFACE MOVEMENT,
CONSUMPTIVE USE, DOMESTIC WATER, POLLUTION ABATEMENT, JUDICIAL
DECISIONS, LEGAL ASPECTS, REMEDIES, WELLS, DIKES, SHALLOW WELLS.
IDENTIFIERS:
INJUNCTION(PROHIBITORY).
ABSTRACT:
PLAINTIFF LANDOWNERS SOUGHT TO RECOVER DAMAGES RESULTING FROM THE
POLLUTION OF HIS WATER WELL BY REFUSE MATTER FROM DEFENDANT'S
DEHYDRATING PLANT OPERATION. PLAINTIFFS ALSO SOUGHT INJUNCTIVE RELIEF.
THE WELL, PUNISHING WATER FOR DOMESTIC PURPOSES, WAS LOCATED ON
PLAINTIFFS' LAND. THE DEFENDANT CONSTRUCTED AN OPEN SUMP, DIKED ON THE
SOUTHERLY AND WESTERLY SIDES. SUCH DIKES ALLOWED REFUSE TO ACCUMULATE
IN THE SUMP. SUBSEQUENTLY, PLAINTIFFS NOTICED A MARKED CHANGE IN THE
QUALITY OF THEIR WELL WATER. DEFENDANT CONTENDED THAT THE REFUSE IN THE
SUMP HAD NOTHING TO DO WITH THE CONTAMINATION OF THE WELL. THE SUPREME
COURT OF WASHINGTON HELD THAT WHERE DAMAGES ARE SOUGHT FOR THE
POLLUTION OF A WATER WELL THROUGH SEEPAGE FROM AN ADJACENT WASTE SUMP,
A PLAINTIFF MUST PROVE THAT THE DEFENDANT'S CONDUCT CAUSED THE
POLLUTION. WHERE INJURY RESULTING FROM THE POLLUTION OF A FARM'S WATER
SUPPLY IS PERMANENT, THE PLAINTIFF CAN RECOVER THE DIFFERENCE IN FAIR
MARKET VALUE BEFORE AND AFTER THE INJURY. FINDING THE MEASURE OF
DAMAGES AMD THE GRANTING OF INJUNCTIVE RELIEF BY THE LOWER COURT TO BE
PROPER, THE COURT AFFIRMED THE JUDGEMENT FOR PLAINTIFFS.
(SHELNUT-FLORIDA)
FIELD 06E, 05B
ACCESSION NO. W71-13645
cv
116
-------
COMPREHENSIVE INDEX
------- OCR error (C:\Conversion\JobRoot\0000070A\tiff\2000Q5P3.tif): Saving image to "C:\Conversion\JobRoot\0000070A\tiff\2000Q5P3.T$F.T$F" failed.
-------
COMPREHENSIVE INDEX
POLLUTION
POLLUTION'
E USE, DOMESTIC WATER, POLLUTION
TER POLLUTION EFFECTS, POLLUTION
STES, WATER POLLUTION,
TER POLLUTION CONTROL ,
ON, STATE GOVERNMENTS, POLLUTION
ER POLLUTION CONTROL, ^POLLUTION
S, JUDICIAL DECISION'S, POLLUTION
S, GROUNDWATER, WATER POLLUTION,
ENTS, CHELATE EXTRACTION, ATOMIC
DISPOSAL, GRQUNDWATER MOVEMENT,
SOILS, SEEPAGE, SOIL CHEMISTRY,
ABATEMENT, JUDICIAL DECISIONS, LE
ABATEMENT, PATH OF POLLUTANTS, 01
WATER POLLUTION EFFECT
SUBSURFACE WATERS, PER
CHEMICAL WASTES, WATER
STATE GOVERNMENTS, LHC
POTABLE WATER, STANDAR
*LEACH ING, fcPERCDLATI
A.VALYSESt CARBONATE, R
ADSORPTION.: / SHWAGE
W71-13645
ABATEMENT,
ABATEMENT,
ABATEMENT,
ABATEMENT,
ABATEMENT,
ABSORPTION
ABSORPTION
ABSORPTION
W71
W71
W69
W70
W 70
1169?
104-46
05370
OP896
0 80 2 5
ABSORPTION, SOIL MECHANICS, WATER
W69-03197
W69-0065?
21
117
-------
ATE MOVEMENT, FEEDLOTS, RESIDUAL
HYDROCHLORIC
LANTSf AMMONIA, HARDNESS(WATER),
MALENCLAVES, PATH OF POLLUTANTS,
DICIAL DECISIONS, LEGAL ASPECTS,
LLUTION TREATMENT, WELL PERMITS,
TRQL, WATER POLLUTION TREATMENT,
ATIMG WATER, WATER CONSERVATION,
ILL ING, ADMINISTRATIVE AGENCIES,
ULATION, WELL PERMITS, DRILL ING,
ILS, PESTICIDES, CHROMATOGRAPHY,
LOW, SATURATED FLOW, ADSORPTION,
MSATURATED FLOW, SATURATED PLOW,
MENT, INFILTRATION, PERCOLATION,
ROUNDWATER MOVEMENT, ABSORPTION,
TANTS, POLLUTANT IDENTIFICATION,
E, OXIDATION LAGOON, IRRIGATION,
ITIES, SEWAGE TREATMENT, SEWERS,
OXIDATION DITCH, SLOTTED FLOORS,
UD, BENTHOS, HYDROGEN, BACTERIA,
LE, SURFACE RUNOFF, FARM WASTES,
IFICIAL RECHARGE, LEGAL ASPECTS,
ERMITS, DRILLING, ADMINISTRATIVE
LOTION TREATMENT, ADMINISTRATIVE
NT, WELL PERMITS, ADMINISTRATIVE
WISCONSIN, MICHIGAN, PHOSPHORUS,
I MAT 1C CONDITIONS, INCINERATION,
OTTAWA SAND,
UTROPHI CATION* -SOIL PHOSPHORUS,
SOURCES, *CORES, FIELDS, PLANTS,
TER RELATIONSHIPS, PERM EARILITY,
ITROGEN, *PHOSPHORUS, NUTRIENTS,
INFILTRATION, INDUSTRIAL WASTES,
OPHICATION, OLIGOTROPHY, SEWAGE,
ARDNESSfWATER), ACIDITY, OXYGEN,
E, #WATER TREATMENT, *FILTATION,
INDUCED INFILTRATION, COL I FORMS,
URGES, LEACHING, DRAINAGE WATER,
, TEMPERATURE, NITRATES, PLANTS,
IVITY, WATER LEVEL FLUCTUATIONS,
ITROGEN, -NITRATES, GROUNDWATER,
N, NUTRIENTS, EFFLUENT, AQUIFER,
DEVITRIFICATION, NITRIFICATION,
ATION, CLAY LENSES, RHINE RIVER,
AGUE, MINERAL/ ^TRANSFORMATIONS,
RY TREATMENT, #SLUDGE DIGESTION,
TE EXTRACTION, ATOMIC ABSORPTION
S.W. OHIO WATER COMPANY, NETWORK
ON, WELLS, METHODOLOGY, CHEMICAL
S, NITROGEN-CYCLE, HISTORY, SOIL
USIQN, / SDISPERISQN, -NUMERICAL
ETURN FLOW, *NITRAT/ ^SIMULATION
, *AOUIFER CHARACTERISTICS, SOIL
MATOGRAPHY, ADSORPTION, CHEMICAL
ER MOVEMENT, #NUMER/ -SIMULATION
GROUNDWATER MOVEMENT, ^NUMERICAL
NATION, MICROORGANISMS, CHEMICAL
EW YORK, HYDROGRAPHS, HYDROGRAPH
*WATER POLLUTION, INFILTRATION,
, ADSORPTION, CHEMICAL ANALYSIS,
ACCUMULATION, SOIL CORES.: / NITR
ACID.:
ACIDITY, OXYGEN, ALGAE, SELF-PUR I
ACIDS, LEACHING, CHLORIDES, GLACI
ADJUDICATION PROCEDURE.: /ERS, JU
ADMINISTRATIVE AGENCIES, CONTROL,
ADMINISTRATIVE AGENCIES, LEGISLAT
ADMINISTRATION.: /LLUTION, PERCOL
ADMINISTRATION, GROUND HATER, HATE
ADMINISTRATIVE AGENCIES, ADM IN 1ST
H71
W 71
W69
W71
W71
ADSORPTION
ADSORPTION
ADSORPTION
ADSORPTION
ADSORPTION
ADSORPTION
CHEMICAL ANALYSIS, AM
ION TRANSPORT.: /ED F
ADSORPTION, ION TRANS
FILTRATION.: /ER MOVE
/ SEWAGE DISPOSAL, G
WATER CHEMISTRY, DARC
AERATION, BIOCHEMICAL OXYGEN DFMA
AERATION, MONITORING, LANDFILLS,
AERATOR, SPREADING, LAND DISPOSAL
AEROP-IC BACTERIA, METABOLISM, CAN
AEROBIC CONDITIONS, INCUBATION.: /
AESTHETICS, AQUIFERS, SOIL WATER
AGENCIES, ADMINISTRATION, GROUNDW
AGEX'CIES, LEGISLATI: /, WATER POL
AGENCIES, CONTROL, REGULATION, 40
AGRICULTURAL WATERSHEDS, ORGANIC
AIR POLLUTION, TEMPERATURE, WASTE
ALDRIN INFILTRATION.:
ALFALFA-BROMEGRASS, SPRING THAWS,
ALFALFA, CEREAL CROPS, IRRIGATED
ALGAE, DISSOLVED OXYGEN.: /OUNDHA
NITRATES, SURFACE RUNOFF,
PONDS, FARM WASTES.: /GE,
SCUM, WEEDS, NUTRIENTS, SE
SELF-PURIFICATION, BACTFRI
ALLUVIA CH ANN1 ELS, SURFACE-GROUNDW
ALLUVIAL CHANNELS, DREDGING, EXCA
DRAINAGE EFFECTS, GROUND
HARDNESSf WATER), ACIDITY
NEBRASKA, SOIL CONTAMINA
PPFCIPITATIPN, SEDIMENTS
AMMONIA, SOIL CONTAMINATION, HATE
AMMONTFICATION, LEACHING, EROS ION
AMSTERDAM RHINE, POLDERS, COMPOSI
HAARLEM, LEYDEN, THE H
DIGESTION, ODORS, GROUN
CARBONATE, BICARBONATE,
GR^AT MIAMI RIVER,
/MPL1NG, DATA COLLECTI
HATER TRANSFER, IRRIGAT
COMPUTER PROGRAMS, DIFF
#PATH OF POLLUTANTS, *R
TEST PROCEDURES, CHEMIC
ANALYTICAL TECHNIQUES,
^DISPERSION, AGROUNDWAT
MIXING, COMPUTER PRPGRA
TEMPERATURE, NITRATES,
ANALYSIS, STATISTICAL MODELS, STA
ANALYTICAL TECHNIQUES, SOIL COMTA
ANALYTICAL TECHNIQUES, RJOASSAY,
ALGAF,
ALGAE,
ALGAF,
ALGAE,
AMMONIA,
AMMONIA,
AMMONIA,
AMMONIA,
AMSTERDAM
ANAEROBIC
ANALYSES,
ANALYSIS.
ANALYSIS.
ANALYSIS,
ANALYSIS,
ANALYSIS,
ANALYSIS,
ANALYSIS,
ANALYSIS,
ANALYSIS,
ANALYSIS,
10372
00194
07838
00194
01028
10157
10446
10157
04742
04742
06514
10058
10058
07375
00652
02611
03542
09154
03542
07838
09721
08620
04742
10446
10157
04193
07118
01904
09721
04488
12410
06443
06435
04193
07338
1 2410
02909
04548
07838
03543
06435
03542
10372
07838
07838
07116
03197
02611
11255
12122
09611
04543
07887
06514
04559
04559
H69-07838
03102
01291
06514
W 7 1 -
W71-
W71-
H71-
W71-
W70-
W70-
W69-
W69-
W69-
W71-
K'71-
W71-
W69-
W69-
W69-
W71-
1-.' 7 1 -
H71-
W70-
W 7 1 -
W 70-
W69-
H 70-
W71-
W 71 -
V 71-
W70-
K'69-
W 7 1 -
U'7l-
W71-
W69-
W 71 -
W71-
W71-
W 69-
W69-
V11.1 -
W69-
W69-
H71-
K 7 1 -
W71-
W71-
71-
'/'7 1
W7 1
W71
H70
W70
W71
118
-------
EFFLUENT,
*NITRATE,
*OGALLALA
INN), SOIL MINERALS, / -KILLING,
WATER), *SOIL-WATER ENVIRONMENT,
SPOK/ DRAIN FIELDS, *TEST HOLES,
PHOSPHORUS* PHOSPHATES, RATFS OF
RFACE DRAINAGE, WATER MANAGEMENT(
AMFLOWt *INDU/ -WATER MANAGEMENTS
EPAGE, ^SUBSURFACE WATERS, PRIOR
CE RUNOFF, REASONABLE USE, PRIOR
R, ^NITRATE, AQUIFER, DISCHARGE,
ON, SUSPENDED LOAD, GROU\DWATER-,
AQUIFER SWEETENING,
INATION.:
PPLICATION, NUTRIENTS,
-CATTLE, #GROUNDWATER,
ER COUNTY(TEXAS), HOL/
CURRENTS(WATER), MASS TRANSFER,
UTILIZATION, PERCOLATING WATER,
ARGF, LEGAL ASPECTS, AESTHETICS,
NG WATER, PERCOLATION, LEACHING,
TISTICAL METHODS, WATER STORAGE,
ELS, *WATER WELLS, WATER SUPPLY,
E AGENCIES, CONTROL, REGULATION,
POSAL, NITRATES, EUTROPHICATION,
CHANNELS, DREDGING, EXCAVATION,
POSAL, NITRATES, EUTROPHICATION,
GE, GROUNDWATER, SURFACE WATERS,
LIC MODELS, MATHEMATICAL MODELS,
R POLLUTION, NITROGEN, NITRITES,
CHIMG, CHLORIDES, GLACIAL DRIFT,
NA, INDUSTRIAL WASTES, DRAINAGE,
REENS, EXCAVATION, WATER POLICY,
MODELS, SAL INE WATER INTRUS ION,
, DOMESTIC WASTES, INFILTRATION,
, EXCAVATION, AQUIFERS, GRAVELS,
PHOENIX(ARIZ), SALT RIVERt
PHOENIXt
LUSHING MEADOWS PROJECT,
LUSHING MEADOWS PROJECT,
RCES, DRAINAGE, RIPARIAN RIGHTS,
ED CONDUITS, METAL PIPES, WFLLS,
GROUNDWATER MOVEMENT, UNDERFLOW,
ION, INSTALLATION, WELL CASINGS,
STORAGE, AQUIFERS, WATER REUSE,
L FLOW DOCTRINE, REASONABLE USE,
ICIDAL HASTES, IRRIGATION WATER,
ODELS, TRACERS, INJECTION WELLS,
LEGISLATION, LAND TENURE, LEGAL
AL DECISIONS, LEGISLATION, LEGAL
WELLS, SUBSURFACE WATERS,
E, HASTE WATER(POLLUTION),
S, SEEPAGE, UASTF STORAGE,
TER POLLUTION, POLLUTANTS, LEGAL
*OAMAGFS(LEGAL
TES, ^ARTIFICIAL RECHARGE, LEGAL
ATFRS, JUDICIAL DECISIONS,
in1-1 A TER MOVEMENT, DAMAGFS,
L1KCFS, JUDICIAL DECISIONS,
t WATER POLLUTION FFFFCTS,
OLLUTION CONTROL, DAMAGES,
PHOENIX!
PHPEMIXt
LEGAL
LEGAL
LEGAL
LEGAL
LEGAL
1 FGAL
LEGAL
LFGAL
AQUIFER
AQUIFER
* *
ANIMAL MANURES, LAKE MINMETONKAtM
ANIOMIC SURFACTANTS, SYNTHETIC DE
ANNUAL PRECIPITATION, LEACH BED,
APPLICATION, NUTRIENTS, EFFLUENT,
APPLIED).: /IMAGE PROGRAMS, SUBSU
APPLIED), ^CONJUNCTIVE USE, *STRE
APPROPRIATION, GROUNDWATER, UNDER
APPROPRIATION, WATER POLLUTION SO
AQUIFER CHARACTERISTICS, EFFLUENT
CHARACTERISTICS.: /COLAT I
DESALINATION!. :
AQUIFER SWEETENING, AQUIFER DESAL
AQUIFER, AMMONIA, SOIL CONTAMINAT
DISCHARGE, AQUIFER CHARA
HIGH PLAINS(TEXAS), PARM
/ MATHEMATICAL MODELS,
HYDROGFOLOGY, GROUNDWAT
SOIL WATER MOVEMENT, GR
WATER TABLE, WATER SUPP
WATER RFUSE, ARTIFICIAL
ION EXCHANGE, POLLUTANT
WFLL REGULATIONS, SUBSU
GROUNDWATFR MOVEMENT, M
GRAVELS, AOUITARDS, PUM
GROUNDHATER MOVEMENT, M
FLOW RATES, LEACHING.: /
MODEL STUDIES, DRAINAGE
COLORADO, DENITRIF 1CAT I
OHIO RIVER, KENTUCKY.: /
SINKS, CITIES, SEWAGE T
PERCOLATING HATER, LEG:
POROUS MEDIA, DIFFUSION
AQUIFORS, SANITARY ENGINEERING.: /
AOUITARDS, PUMPING, WATER WELLS,
ARIZ) .:
ARIZ), SALT RIVERfARIZ).:
ARIZONA).: /L RECHARGE PROJECT, F
ARIZONA).:x /L RECHARGE PROJECT, F
ARTESIAN WELLS, DITCHES, DRAINAGE
WFLLS, WATER WELLS, INFL
WELLS, STREAMS, JUDICIAL
ARTESIAN WELLS, WELL SCREENS, EXC
ARTIFICIAL RECHARGE, LOW-FLOW AUG
ARTIFICIAL USE, RIPARIAN LANDS, G
ARTIFICIAL RECHARGE, FILTRATION,
ARTIFICIAL RECHARGE, CONVECTION,
AS PEC: /DAMAGES, HYDROLOGIC DATA,
/S, LAND TENURE, JUDICI
/FACE DRAINAGE, SHALLOW
/DUSTRIAL WASTES, SEWAG
/TCHES, DRAINAGE EFFECT
/PAGE, TMFILTRATION, HA
HYDROCARBON POLLUTION.:
AESTHETICS, AQUIFERS, SO
ADJUDICATION PROCEDURE.:
CO MP ENSA TION, R RINES, WA
DFEP PERCOLATION.: /N SO
JUDICIA! DECISIONS, GROU
JUDICIAL DECISIONS, GROU
W70
W70
W69
vn i
AQUIFER,
AQUIFER,
AQUIFERS
AQUIFERS,
AQUIFERS,
AQUIFERS,
AQUIFERS,
AQUIFERS,
AQUIFERS,
AQUIFERS,
AQUIFERS,
AQUIFERS,
AQUIFERS,
AQUIFERS,
AQUIFERS,
AQUIFERS,
AQUIFERS,
AQUIFERS,
AQUIFERS,
ARTESIAN
ARTESIAN
* *
ASPECTS
ASPECTS
ASPECTS.:
ASPECTS.:
ASPECTS.:
ASPECTS) ,
ASPECTS,
ASPECTS,
ASPECTS,
ASPECTS,
ASPECTS,
ASPECTS,
W70-
TING USFS, DOMESTIC WATER, LEGAL ASPECTS, MUNICIPAL WATER, REASQNA
VI70-
W71-
W70-
W71-
W71-
W71-
W71-
W71-
\r'69-
W70-
W69-
W70-
W70-
W69-
W71-
W*?l-
VI71-
W71-
W70-
W71-
W71-
W71-
W71-
W71-
W71-
W69-
W71-
I'HO-
W70-
VI 69-
W69-
K'69-
W70-
W70-
H71-
W70-
W70-
W69-
F69-
W71-
W71-
W69-
W70-
W69-
W70-
W6R-
W69-
W71-
W71-
W70-
W70-
\ j 71-
W70-
04193
01791
01076
03547
01932
03102
08049
08050
03543
04504
01932
01932
03542
03543
12122
08971
Q0532
08620
06011
0310 ;
02611
10157
01324
02909
01205
09637
01932
07036
00194
09154
04742
04559
03178
07909
04712
04717
05328
05327
06118
07632
08025
04747
03107
02896
08621
07554
11692
08055
06117
00571
06118
07632
00627
08670
01028
03230
08050
08026
11 724
00532
119
-------
EMENT, JUDICIAL DECISIONS, LEGAL
WATER, JUDICIAL DECISIONS, LEGAL
ECISIONS, RELATIVE RIGHTS, LEGAL
, WATER POLLUTION, PREC I P ITATION(
MTROL, RESERVOIRS, PRECIPI TAT ION(
CE ELEMENTS, CHELATE EXTRACTION,
E, ARTIFICIAL RECHARGE, LOW-FLOW
FACIES, SEWAGE EFFLUENT, C.O.D.,
YCORACTERIUM, BACILLUS SUBTIL IS ,
LUS SUBTIL IS, BACILLUS MYCOIDES,
ION, PSEUnOMONAS, MYCOBACTERIUM ,
SUPPLY, MUD, BENTHOS, HYDROGEN,
HOS, HYDROGEN, BACTERIA, AEROBIC
MOVFM/ *WATER REUSE, ^PATHOGENIC
INFILTRATION, COLIFORMS, ENTERIC
XYGEN, ALGAE, SELF-PURIFICATION,
UPPER RIO GRANDE, SALT
PIT RECHARGE, SAFE YIELD, WATER
DISSOLVED SOLIDS, LEACHING, SALT
S? IMPERVIOUS SOILS, GROUNDWATFR
GASES, CARBON DIOXIDE, METHANE,
MOVEMENT, CAPILLARY FLOW, *LAVA,
ALGAE, NITRATES, SURFACE RUNOFF,
NG, RUSSIAN RIVERICALIF), YAKIMA
*SUSQUEHA.VNA RIVER
1C LOADING, INFILTRATION, TUCSON
JEC/ SURFACE SPREADING, RECHARGE
JEC/ SURFACE SPREADING, RECHARGE
IFERS, HYDROGEOLOGY, GROUNDWATER
TION, ^PONDS, #50 IL, GROUNDWATER
LES, ANNUAL PRECIPITATION, LEACH
RO^MENT, AN ION 1C SUR/ *DETERGFNT
, INFILTRATION, DOMESTIC WASTES,
WATER BASINS, WATER SUPPLY, MUD,
ITY, POROSITY, POROUS MATERIALS,
ABSORPTION ANALYSES, CARBONATE,
*SUSOUEHANNA RIVER(NY),
ANALYSIS, ANALYTICAL TECHNIQUES,
AERATION, MONITORING, LANDFILLS,
ON LAGOON, IRRIGATION, AERATION,
ENTS, DENITRIFICATION, NITRITES,
ER, WATER LEVELS, WATER DUALITY,
S, DISPERSION, SEWAGE EFFLUENTS,
TION SOURCES, SELF-PURIFICATION,
PENSATION, BRINES, WATER SUPPLY,
-HYDRAULICS LABORATORY OF
ES, LEGAL ASPECTS, COMPENSATION,
ATION, *SOIL PHOSPHORUS, ALFALFA-
), SPRINGFIELDfMO
HEMICAL FACIES, S
SAM
WATER POLLUTION,
NTS, WATER MIXING
ASTE DISPOSAL, DI
TICAL MODELS, COM
* HYDRA
INGf NUCLEAR EXPL
*VEME
ENGINEERING, NUCL
), SE
EWAGE
JACI
*CENT
, RUS
SPOSA
PUTER
UL 1C
OS I ON
ZUELA
FAR E
WAGE PLANT
EFFLUENT,
NTO VALLEYf
RAL VALLEY(
SIAN RIVER(
L, WASTES,
PROGRAMS,
POTENTIAL,
S, CANALS,
, #NUCLEAR
XPLOSIONS,
ASPECTS, REMEDIES, WELLS, DIKES,
ASPECTS, RIPARIAN LAND, PERCOLATI
ASPECTS, STATE GnVFRNMENTS, STATE
ATMOSPHERIC), SEEPAGE, TNFILTRATI
ATMOSPHERIC). : /OLATION, FLOOD CO
ATOMIC ABSORPTION ANALYSES, CARRO
AUGMENTATION.: /IFERS, WATER REUS
B.O.D., WASTE WATERS, HYDRAULIC L
BACILLUS MYCOIDES, BACILLUS MESEN
BACILLUS MESENTERICUS, DIATOMEA,
BACILLUS SUBTIL IS, BACILLUS MYCOI
BACTERIA, AEROBIC BACTERIA, METAB
BACTERIA, METABOLISM, CANALS, SAN
BACTERIA, ^VIRUSES, #GROUNDWATER
BACTERIA, NITRATES, CHLORIDES, *C
BACTFRIOPHAGE, RESERVOIRS, SPORES
BALANCE.:
BALANCE, HYDROGEOLOGY, DATA COLLE
BALANCE, PERCOLATING WATER? POLLU
BARRIERS, INFILTRATION, OIL, OIL
BARRIERS, INFILTRATI: /ER SUPPLY,
BASALTS, WATER POLLUTION SOURCES,
BASE FLOW, PERCOLATION, LEACHING,
BASINfPACIFIC NORTHWEST), LAKE ME
BASIN, (N Y).:
BASIN, PRdCESS-RESPONSE MODEL, IN
BASINS, EXPERIMENTAL RECHARGE PRO
BASINS, EXPERIMENTAL RECHARGE PRO
BASINS, HYDROLOGIC CYCLE, OVERDRA
BASINS, WATER SUPPLY, MUD, BENTHO
RED, SPOKANE RIVER VALLEY.: /T HO
BEHAVIOR(WATER), -SOIL-WATER ENVI
BENTHIC FAUNA, INDUSTRIAL WASTES,
BENTHOS, HYDROGEN, BACTERIA, AERO
BIBLIOGRAPHIES, DARCYS LAW.: /RIL
BICARBONATE, FLUORIDE, NITRATE, S
BINGHAMTDN(NY).:
BIOASSAY, SOIL STRUCTURE, INFILTR
BIOCHEMICAL OXYG: /WENT, SEWERS,
BIOCHEMICAL OXYGEN DEMAND, CHEMIC
BIOCHEMICAL OXYGEN DEMAND.: /TERG
BIOCHEMICAL OXYGEN DEMAND, SUSPEN
BIODFGRADATION, METHODOLOGY.: /ND
BIOD^GRADATION.: /TS, WATER POLLU
BDUNPARIES(SURFACES), WELL CASING
BRATISLAVA!CZECHOSLOVAKIA).:
BRINES, WATER SUPPLY, BOUNDARIES!
BROMFGRASS, SPRING THAWS, FERTILI
BROOKlNGSfSOUTH DAKOTA).:
BYPASSES.: /(MO), WILSON CREEMMO
C.O.D., B.O.D., WASTE WATERS, HYD
CALIF).:
CALIF) .: AGROUND
CALIF), YAKIMA BASIN(PACIFIC NORT
CALIFORNIA, PERCOLATING WATER, PE
CALIFORNIA, WATER POLLUTION SOURC
CANADA.:
CANAL CONSTRUCTION, GROUNDWATER M
CANAL EXCAVATION.:
CANALS, CANAL CONSTRUCTION, GROUN
W71
W71
W71
W71
W70
W69
W70
W69
W69
W69
W69
W69
W69
W69
W69
W70
W70
W71
W71
W69-
W71-
W70-
W70-
W69-
W69-
W69-
W70-
W69-
W69-
W70-
W71-
W69-
W69-
W69-
W71-
W71
W71-
H71
W71-
W69-
W70-
W70-
W71-
W71
W 7 1
W69
W69
W 1 1
W69
W70
W71
W70
W70
W 7 1
W 7 0
V'71
W71
W 7 1
13645
01043
13521
05094
0610?
03197
03102
03197
0783B
07838
07838
07838
07838
08621
01076
07838
08662
05466
06063
08055
06011
00979
06443
04504
0310?
03197
05328
05327
00532
07838
01076
01291
09154
07838
00651
03197
02909
06514
09154
03542
12084
07114
01291
09548
03230
01930
03230
09721
03178
09154
03197
05466
04548
04504
06011
-04548
07766
-04882
04882
04882
120
-------
A, AEROBIC BACTF
^AGEMENT, LEACMA
INF
INF
R I A , ME
TE, INF
ILTRATI
ILTRATI
IT FLOW, AGROUND WATER
ATER TABLE, WATER SUPPL
ION, ATOMIC ABSO
r INSPECTION, IN
ESHWATER INTERFA
PPLY, BOUNDARIES
RPTIQN
STALLAT
CES, WE
(SURFAC
TAROLISM,
ILTRATION
ON PONDS,
ON PONDS,
MOVEMENT,
Y, GASES,
ORGANIC
ANALYSES,
ION, WFLL
LLS, V.'ELL
ES) , WELL
ECIPITATION, POTASSIUM, POULTRY,
, LEACHING, RUNOFF, GROUNDWATFR,
-CORES, FIEL
GRADATION, S
N COMPOUNDS,
SOURCES, MIN
NFILTRATION,
R TREATMENT,
ATE, AQUIFER
NTS, -SOILS,
DS, PLANTS, ALFALFA,
OIL DISPOSAL FIELDS,
SOIL CONTAMINATION,
E WATER, OIL WASTES,
CLIMATIC
COLIFORMS, ALLUVIAL
*FILTATION, ALLUVIA
, DISCHARGE, AQUIFER
-LEACHING, *AOt)IFER
ENDED LOAD, GROU
AGROUND WATER,
REMOVAL , -MAINE,
DES, CHROMATOGRA
COLLECTION, WEL
S, CHLORINATIQN,
TION, BIOCHEMICA
SOIL ANALYSIS,
OVFRNMFNTS, POLL
CES, -GROUNDl-'ATF
NDWATER, AQUIFER
*TRACE ELEMENTS,
DEICFRS, ROADS,
PHY, ADSORPTION,
LS, METHODOLOGY,
MICROORGANISMS,
L OXYGEN DEMAND,
TEST PROCEDURES,
UTION ABATEMENT,
ORGANIC
R, -AGRICULTURAL
LE, ENVIRONMENTAL EFFECTS, WATER
SOIL WATER, SOILS, SEFPAGF, SOIL
-HAWAII, IRRIGATION WATER, I-' ATER
ER MOVEMENT, INFILTRATION, HATER
DENTIFICATION, ADSORPTION, '-'ATFR
TES, -LAND USE, -OKLAHPM/ #VATER
WATER POLLUTION EFFECTS, ^SODIUM
OF POLLUTANTS, ACIDS, LEACHING,
RMS, ENTERIC BACTERIA, NITRATFS,
TORY TESTS, PERMEAM ETERS , SANDS,
ERIA, METABOL ISM, CANALS, SANDS,
ATER QUALITY, SOILS, PESTICIDES,
IATOMEA, CLADOPHORA, FLAGELLATA,
FLAGELLATA, CILIATES, RANUNCULUS
STES, DRAINAGE, AQUIFERS, SINKS,
BACILLUS MESENTERICUS, DIATOMEA,
YDEN, THE HAGUE, MINERALIZATION,
ATER, EVAPORATION, INFILTRATION,
HAGAN-POISEUILLE FLOW,
WATER, -PERMEABILITY, POROSITY,
WATER POLLUTION SOURCES, PIPES,
INFILTRATION PONDS, CA^E
INFILTRATION PONDS, CAPE
LLUTANTS, * INDUCED INFILTRATION,
NITRATE,
CONCENTRA
CANALS, SANDS, 0ML ORTNAT I ON, MICR
CAPACITY, GROUNOWATER CONTAMINAT!
CAPE COD(MASS), FALMOUTH
-------
NTS, GROUNDWATER? -INFILTRATION,
? DISCHARGE!WATER)? ON-STTE DATA
ATER BALANCF, HYDROGEOLOGY? DATA
T, FLOW PROFILES? SAMPLING, DATA
DRAINAGE.: STATE
TS, CORRALS, SOUTH PL.ATTE- VALLEYf
A, CEREAL CROPS, IRRIGATED LAND,
N, NITROGEN, NITRITES? AQUIFERS,
OGY? GROUNDWATER? WATER OUALITY,
EAT MIAMI RIVER, S.W. OHIO WATER
OVFMENT, DAMAGES, LEGAL ASPECTS?
SURFACE RUNOFF? RIPARIAN RIGHTS?
RIVFR? AMSTERDAM RHINE, POLDERS,
L CONTAMINATION EFFECTS? ORGANIC
DETERGENTS? POLLUTANTS, NITROGEN
? DARCYS LAW, TIMF LAG, NITROGEN
ION, *WATER QUALITY, / ^NITROGEN
ATER? HATER QUALITY, COMPACTION,
YSIS, MIXING, COMPUTER PROGRAMS,
D IS PER IS ON? '.''NUMERICAL ANALYSIS?
^NITRATES? MATHEMATICAL MODELS,
NT, ^NUMERICAL ANALYSIS, MIXING,
F POLLUTANTS, DIGITAL COMPUTERS,
ION, PATH OF POLLUTANTS? DIGITAL
NDWATER? CELLULOSE? HYDROGFN ION
ACE RUNOFF? FARM WASTES? AEROBIC
PORATIQN, INFILTRATION, CL P'ATIC
M WASTES, GROUNDWATER, HYDRAULIC
NITRATES, CHLORIDES, ^CAPILLARY
INFILTRATION, WASTES? HYDRAULIC
^PERMEABILITY, POROSITY, CLOSED
POLLUTION SOURCES? PIPES, CLOSED
SOIL WATER, SALINE WATER, WATFR
LUTION, PERCOLATING WATER, WATER
ONS, *WATER WELLS? ^LEGISLATION,
UCLEAR EXPLOSIONS, CANALS, CANAL
R MOVEMENT, SUBSURFACF MOVEMENT,
RATES? HATE/ #FARM WASTES, *SOR
EFFLUENT, AQUIFER, AMMONIA, SOIL
UATIONS, AMMONIA, NEBRASKA, SOIL
UTANTS, NITROGEN COMPOUNDS, SOIL
FILTRATION CAPACITY, GROUKOK'ATER
R CHEMISTRY, WATER QUALITY, SOIL
TION? SOIL DISPOSAL FIELDS, SOIL
ION, ANALYTICAL TECHNIQUES, SOIL
ORAGE, SOIL DROPERTIES, MOISTURE
^SEEPAGE
ATER POLLUTION, *WATER
LUTION EFFECTS? *WATER
D WATER QUALITY, WATER POLLUTION
CONTROL? LEACHING, WATER QUALITY
ITROGEN, RUNOFF, WATER POLLUTION
WASTE DILUTION, WATER POLLUTION
LLUTION SOURCES, WATER POLLUTION
ATER POLLUTION? #WATER POLLUTION'
ERMITS, ADMINISTRATIVE AGENCIES,
RAMSPIRAT I ON? PERCOLATION, FLOOD
, *HYDROGEOLOGY, WATER POLLUTION
SURFACE WATERS, *WATER POLLUTION
AL WASTES? SEWAGE, HATER QUALITY
POLLUTION
POLLUTION
CDLIFORMS, ENTERIC RACTERIA, NITR
COLLECTIONS, UNDERFLOW. : /URFMENT
COLLFCTTOMS, HYOROLOGIC DATA, GRO
COLLECTION, WELLS, METHODOLOGY, C
COLL<=GE(PEW > , SAMTTARY LANDFILL
COLO ) . : NATIVE GRASSES, FEEDLD
COLORADO, GROUNDWATER, PERCOLATIO
COLORADO, DENITRIFICATIOM, WATER
COMPACTIONf? COMPRESSIBILITY, SOLI
COMPANY, NFTWORK ANALYSIS.: GR
COMPENSATION, BRINES, HATER SUPPL
COMPETING USES, DOMESTIC WATER, L
COMPOSITION, PSEljnoMQNAS, MYCORAC
COMPOUNDS, DISPERSION, SEWAGE EFF
COMPOUNDS,
COMPOUNDS,
COMPUTER
COMPUTER
COMPUTER
CALIFORNIA? WA
COMPUTER MODEL
/TION, PATH 0
SOIL CONTAMINATION, CE
NITRATES, DISCHARGE ME
COMPOUNDS, * POL LUTION I Olf NT IF 1C AT
COMPRFSSIBT LITY, SOLID WASTES, IN
COMPUTER MODELS, MATHEMATICAL MOD
PROGRAMS, DIFFUSION? MIX
PROGRAMS,
PROGRAMS?
COMPUTER PROGRAMS.
COMPUTERS, COMPUTER PROGRAMS.: /T
CONCENTRATION, TOXICITY.: /, GROU
CONDITIONS, INC UPA TI ON.: /E , SURF
CONDITIONS, INCINERATION? AIR POL
CONDUCTIVITY.: /ES, LEACHING, FAR
CONDUCTIVITY, SOIL MOISTURE.: /ft,
CONDUCTIVITY, SUBSURFACE DRAINAGE
CONDUIT FLOW, AGROUND WATER MOVFM
CONDUITS, METAL PIPES, WELLS, ART
CONSERVATION, IRRIGATION PRACTICE
CONSERVATION? ADMINISTRATION.: /L
CONSTRUCTION, PU^PS, PUMPING, STA
CONSTRUCTION, GROUNDWATER MOVEM EM
CONSUMPTIVE USE, DOMESTIC HATER,
CONTAMINATION,
CONTAMINATION,
CONTAMINATION?
CONTAMINATION,
CONTAMINATION.
CONTAMINATION.
^FERTILIZERS, #NIT
WATER POLLUTION, W
OBSERVATION WELLS,
CESSPOOLS, SEWAGE
/NT, LEACHATE, IN
/FILTRATION, HATE
CONTAMINATION, SOIL PHYSICAL PROP
CONTAMINATION EFFECTS, ORGANIC CO
CONTENT, POLLUTANTS, SOTL WATER M
CONTROL.:
CONTROL, "'POLLUTION ABATEMENT, ST
CONTROL, *WATER POLLUTION SOURCES
CONTROL? DAMAGES, LEGAL ASPECTS,
DOMESTIC WASTES? INFILTR
GROUNDWATER, SEPTIC TANK
LEACHING? WATER QUALITY
PUBLIC HEALTH? ENVIRONME
POLLUTION ABATEMENT, SUB
REGULATION, AQUIFERS? WE
RESERVOIRS? PRECIPITATIO
SURVEYS? LEACHING, GEOLO
WATER POLLUTION TREATMEN
WATER POLLUTION TREATMEN
CONTROL,
CONTROL,
CONTROL?
CONTROL?
CONTROL,
CONTROL,
CONTROL?
CONTROL?
CONTROL?
CONTROL ,
W69-01076
W70-07766
W70-05466
W71-11255
W 7 1 -
W70-
W70-
W 7 I
W71
W69
W71
W7Q
W69
W70
W69
W70
W 7 1
₯11
W71
W71
W71
W71
W69
W69
W68
W69
W71
W71
W69
W70
W69
W70
W71
VII l
W 7 1
W7J
W71
M 7 1
W71
W71
W69
W68
W69
W69
W70
W68
W70
W70
W 7 1
W71
W69
W7l
W69
W70
W71
W71
W70
W70
W 71
W71
04488
04488
02036
08907
02611
03230
00532
07838
01291
00652
07766
1212?
08907
04559
09611
04548
04559
03237
03237
01269
09721
07118
08218
01076
07766
00979
07632
06063
10157
04742
0488?
13645
02036
03542
03543
00652
00058
08620
08621
01291
00058
06011
02896
09154
11724
03178
10372
-03178
-06011
-10446
-10157
-06102
07193
10157
-10446
122
-------
TER, NITRATE,
, GROUNDWATER
EQUATIONS, MATHEMATICAL MODELS,
UIFERS, POROUS MEDIA, DIFFUSION,
SPOS/ "'CONTAMINATION, *AQUIFERS,
TION WELLS, ARTIFICIAL RECHARGE,
OTS, RESIDUAL ACCUMULATION, SOIL
).: NATIVE GRASSES, FEEDLUTS,
STARK
IFER, HIGH PLAINS(TFXAS) , PARMER
RUNOFF, JAMES RIVER(MO), WILSON
FIELDS, PLANTS, ALFALFA, CEREAL
POLLUTANTS, MATHEMATICAL MODELS,
*SUPERNATAMT RE-
NITRITES, NITROGEN-
BASINS, HYDROLOGIC
ES, NITROGEN, NITRATES, NITROGEN
RAULICS LABORATORY OF BRATISLAVA!
CAL FACIES, SEWAGE EFFLUENT, C.O.
ES, SEWAGE EFFLUENT, C.O.D., R.O.
, INSTRUMENTATION, HYD ROC HEM 1CAL
RFACE-GROUNDWATER RELATIONSHIPS,
BROOKINGS(SOUTH
S, WATER WELLS, WATER POLLUTION,
HASTES, PULP AND PAPER INDUSTRY,
UALITY, WATER POLLUTION CONTROL,
ILL HOLES, GROUNDWATER MOVEMENT,
IRS, DRILLING EQUIPMENT, LEASES,
UDICIAL DECISIONS, OIL, SEEPAGE,
S, SALIME WATER, WELLS, SEE°AGF,
BSURFACE RUNOFF, REASONABLE USE,
ON, ADSORPTION, WATER CHEMISTRY,
OROUS MATERIALS, BIBLIOGRAPHIES,
NAGE, TRANSMISSIVITY, HEAD LOSS,
LD, WATER BALANCE, HYDROGFOLOGY,
EMENT, DISCHARGE(HATER), ON-SITE
VEMENT, FLOW PROFILES, SAM PL ING,
TI GAT IONS, * ILLI MilS, HYD ROL OG1C
GY, DATA COLLECTIONS, HYDROLOGIC
ER INDUSTRY, DAMAGES, HYDROLOGIC
L OXYGEN DEMAND, CHEMICAL OXYGEN
, STREAMS, GROUNDWATER, JUDICIAL
TER, SUBSURFACE WATERS,
ATER POLLUTION SOURCES,
DAMAGES, LEGAL ASPECTS,
R, POLLUTION ABATEMENT,
EDIES, WATER POLLUTION,
, DAMAGES, LAND TENURE,
EFFECTS, LEGAL ASPECTS,
DERSEEPAGE, ^POLLUTION,
RTESIAM WELLS, STREAMS,
, ^PIPELINES, ^LEAKAGE,
ATER POLLUTION, DAMAGE,
*SALIME WATER, DWELLS,
ATER POLLUTION SOURCES,
FACE RUNOFF, SUBSURFACE
SHIPS, DRAINAGE EFFECTS,
DICIAL DECISIONS, LEGAL
AY ICING, -SNOW REMOVAL, *MAINE,
ON, NITRITES, BIOCHEMICAL OXYGEN
ON, AERATION, BIOCHEMICAL OXYGEN
K, *LIGNINS, ^BIOCHEMICAL OXYGEN
JUDICIAL
JUDICIAL
JUDICIAL
JUDICIAL
JUDICIAL
JUDICIAL
JUDICIAL
JUDICIAL
JUDICIAL
JUDICIAL
JUDICIAL
JUDICIAL
JUDICIAL
STREAMS,
DRAINS,
ASPECTS,
DAMAGES,
DAMAGES,
DAMAGES,
DAMAGES,
DAMAGES,
DECISIONS,
DECISIONS,
DECISIONS,
DECISIONS,
DECISIONS,
DECISIONS,
DECISIONS,
DECISIONS,
DECISIONS,
DECISIONS,
DECISIONS,
DECISIONS,
DECISIONS,
LEGAL
LEGAL
GROUN
CONVECTION, NUCLEAR POWFRPLANTS.: W71-
CONVECTION, DIFFUSIVITY.: /ON, AO W71-
CONVECTIOK , #DI SPERSION, WASTE HI W69-
CONVECTION, MIXING, FLOW, POROUS K69-
CORES.: / NITRATE MOVEMENT, FEEOL W71-
CORRALS, SOUTH PLATTE VALLEY!COLO W70-
CGUNTY(OHIP) . : W70-
COUNTYtTEXAS), HOLLY SUGAR STUD IE W71-
CREEK(MO), SPRINGFIELO(MO) , SEWAG W71-
CROPS, IRRIGATED LAND, COLORADO, W70-
CURRENTS{WATER), MASS TRANSFER, A W69-
CYCLE.: W71-
CYCLE, HISTORY, SOIL ANALYSIS, WA W71-
CYCLE, OVERDRAFT, WELLS, SURFACE- W70-
CYCLF, PHOSPHORUS, REGULATION, GR W71-
CZECHOSLOVAKIA) .: *HYD W71-
D., B.O.D., WASTE WATERS, HYDRAUL W69-
0., WASTE WATERS, HYDRAULIC LOADI W69-
D: /BASIN, PROCESS-RESPONSE KOOEL W69-
DA: / CYCLE, OVERDRAFT, WELLS, SU W70-
DAKOTA).: W69-
DAMAGE, JUDICIAL DECISIONS, GROUN V168-
DAMAGFS, HYDROLOGIC DATA, LEGISLA W71-
LEGAL ASPECTS, JUDICIAL M71-
LEGAL ASPECTS, COM PENS AT W71-
LAND TENURE, JUDICIAL DF W71-
OIL INDUSTRY, STORAGE TA W70-
RFMEDIES.: / WELL CASING W71-
DAMAGES, SURFACE RUNOFF, GASOLINE W70-
DARCY'S LAW, PERMEABILITY, DRIVER K69-
DARCYS LAW.: /BILTTY, POROSITY, P i»<69-
HARCYS LAW, TIME LAG, NITROGEN CO W70-
DATA COLLECTIONS, HYDROLOGIC DATA VO 0-
DATA COLLECTIONS, UNDERFLOW.: /UR W70-
DATA COLLECTION, WELLS, METHODOLO W71-
DATA, GEOLOGY, HYDROLOGY, HYDROGE W70-
DATA, GROUNDWATER MOVEMENT, WATER W70-
DATA, LEGISLATION, LAND TENURE, L W71-
DE: /GATION, AERATION, BIOCHEKICA W71-
LEGAL ASPECTS, RIPARIA W71-
ASPECTS, ADJUfJlC W71~
ASPECTS, DEEP PE W70-
/TION CONTROL, W71-
LEGAL ASPECTS, REMEDIE W71-
RELATIVE RIGHTS, LEGAL W71-
LEGISLATION, LEGAL ASP W71-
GROUNDWATER MOVEMENT, W70-
01L, SEEPAGE, DAMAGES, WTO-
POLLUTION ABATEMENT, P W70-
01L, OIL INDUSTRY, SUR WTO-
GROUND WATER, PATH OF W68-
01L WASTES, WATER OUAL W69-
DECISIONS, FUELS, WELLS, WATER PO W69-
OEEP PERCOLATION, GROUND WATER M0 W'O-
DEFP PERCOLATION, EVAPOTRANSPIRAT W69-
DEEP PERCOLATION.: /N SOURCES, v)U W70-
DEICERS, ROADS, CHEMCONTROL, SALT WTO-
DEMAND. : /TERGENTS, DEN ITRIF1CAT I WT1-
DEMAND, CHEMICAL OXYGEN DE: /GATI W71-
DEMAND, LEACHING, RUNOFF, GROUNDW W68-
] 1356
04559
00651
07554
1037?
04488
071 93
17122
09154
04488
08921
07118
121 ?2
0053?
1 2084
01930
03197
03197
03197
00532
03178
00627
11692
11724
03230
08055
07631
03230
08049
0?611
00651
07766
05466
0776A
1 1255
06322
05466
11692
03542
01043
01028
08050
11724
13645
13521
08055
08026
07631
08025
07632
00627
06118
06117
00521
00248
08050
09844
12084
03542
01269
123
-------
ATER QUALITY, BIOCHEMICAL OXYGEN
OUND WATER RECHARGE t IRRIGATION,
QU\'D WATER RECHARGE, IRRIGATION,
M, NITRITES, AQUIFERS, COLORADO,
R, IRRIGATION' EFFECTS, LEACHING,
N, DRAINAGE EFFECTS, DETERGENTS,
ILIZERS, FARM HASTES, NUTRIENTS,
MONIA, PRECIPITATION, SEDIMENTS,
AQUIFER SWEETENING, AQUIFER
UTRDPHICATION, DRAINAGE EFFECTS,
, ANIONIC SURFACTANTS, SYNTHETIC
PERCOLATING MATER, INFILTRATION,
DWATER MOVEMENT, WATER RESOURCES
MYCOIDES, BACILLUS MES ENTE R I CUS ,
^FINITE
USSR, RADIAL
TEMPERATURE PROFILES, THERMAL
ALITY, PERCOLATION, PENETRATION,
LATING WATER, SUBSURFACE WATERS,
TRUSION, AQUIFERS, POROUS MEDIA,
CAL ANALYSIS, COMPUTER PROGRAMS,
f-'ODYMAMICS, FLOW, MASS TRANSFER,
ENT, ^DISPERSION, *ION EXCHANGE,
US MEDIA, DIFFUSION, CONVECTION,
SPHERICAL
MS, ^TERTIARY TREATMENT, -SLUDGE
#SLUOGE DIGESTION, ANAEROBIC
R POLLUTION, PATH OF POLLUTANTS,
LEGAL ASPECTS, REMEDIES, '%'FLLS,
*LAMDFILL, SANITARY FILL, WASTE
BLE, WATER SUPPLY, GASES, CARBON
G, NITROGEN COMPOUNDS, NITRATES,
NITRATES , DISCHARGE MEASUREMENT,
TER QUALITY POLLUTION, RECHARGE,
*GPOUND/.'ATER, -NITRATE,
ASS TRANSFER, DIFFUSION,
TION EFFECTS,
INFILTRATION
LOADING, -R
MIXING,
LONGITUDINAL
ORGANIC COMPOUNDS,
, PERCOLATION, SOIL
ICDEGRADATION, SOIL
SPRAY
FLOORS, AERATOR, SPREADING, LAND
S, SEWAGE TREATMENT, WASTE MATER
P R F A D IM G , #M0 NIT 0 RIM G, / -SF W AGE
00 ELS, MIXING, RAD IP ACTIVE '-'ASTF
S, SE'-.'AG= TREATMENT, WASTE 'MTER
TE TREATMENT, -UNITED ST/ -'WASTF
ANI/ATIOiV, #SOL1D WASTES, *>-'ASTE
T, IMPAIRED WATER QUALITY,
ANTS, PERCOLATION, WASTES,
UTIPN EFFECTS, POLLUTANTS,
l-'ASTES, SPRINKLER / #WASTE
W/ SEWAGE EFFLUENT, *WASTE
IRRIGATION, HYDRO/ -WASTE
W/ SEW4GF EFFLUENT, -'WASTF WATER
a DATIDM, SOIL DISPOSAL/ SEWAGE
ITY, *LAt\jDFILL , SAN IT A/ -WASTE
RAD 10 ISOTOPES, RADIOACTIVE MASTE
LLUTANTS* INJECTION W^LI.S, WASTE
i-'ASTE
WASTE
MASTE
i-'ATFR
ECONOMICS. : /*GR
MATER TARLE, PER
RIVER FLOW, MATE
NITRITES, BIOCHE
NITRIFICATION, A
RUNOFF, UREAS, F
DEMAND, SUSPENDED LOAD.: /VELS, W
DENITRIFICATION, ECONOMICS.: /*GR
DENITRIFICATION,
DENITRIFICATION,
DENITRIFICATION,
DENITRIFICATION,
DENITRIFICATION,
DENITRIFICATION,
DFSALINATION.:
DETERGENTS, DENITRIFICATION, NITR
DETERGENTS.: /L-WATER ENVIRONMENT
DETERGENTS, POLLUTANTS, NITROGEN
DEVELOPMENT, RECLAIMED WATER.: /N
DIATOMEA, CLADOPHORA, FLAGELLATA,
DIFFERENCE METHOD.:
DIFFUSION EQUATIONS.:
DIFFUSION. :
SEEPAGE,: /ED WATER QU
GRAVITATIONAL WATER, S
CONVECTION, DIFFUSIVIT
MIXING, GRPUNDWATER MO
MIXING,
MIXING,
/ON,
W69-07114
W69-05327
DIFFUSION,
DIFFUSION,
DIFFUSION,
DIFFUSION,
DIFFUSION,
DIFFUSION,
DIFFUSIVITY.
DISPERSION.: /
RADIOACTIVITY,
AQUIFERS, PORO
DIFFUSIVITY.:
DIGESTION, ANAEROBIC DIGESTION, 0
DIGESTION, ODORS, GROUNDWATER, FV
DIGITAL COMPUTERS, COMPUTER PROGR
DIKES, SHALLOW WELLS.: /ECISIONS,
DILUTION, WATER POLLUTION CONTROL
DIOXIDE, METHANE, BARRIERS, INFIL
DISCHARGE MEASUREMENT, DISCHARGEf
DISCHARGE(WATER), ON-SITE DATA CO
DISCHARGE, GROUNDIVATER, SURFACE W
DISCHARGE, AQUIFER CHARACTERISTIC
/MODYNAMICS, FLOW,
M
DISPERSION.
DISPERSION. :
DISPERSIONS SEWAGE EFFLUENTS, RIO
DISPOSAL FIELDS, SOIL CONTAMIMATI
DISPOSAL FIELDS, CESSPOOLS, SEPT I
PISPnSAL WELLS.:
DISPOSAL.:
DISPOSAL.
DISPOSAL,
DISPOSAL,
DISPOSAL,
DISPOSAL,
DISPOSAL,
DISPOSAL,
DISPOSAL,
DISPOSAL,
DISPOSAL,
DISPOSAL,
DISPOSAL.
DISPOSAL,
DISPOSAL,
DISPOSAL,
DISPOSAL,
/ATinri DITCH, SLOTTED
NITRATES, EUTROPHICATIO
^INFILTRATION, #WATER S
UNSATURATFD FLOW, SATUR
MITRATFS, EUTROPHICATIO
* MUM I C I DA L l-M ST ES , * WA S
SURFACE WASTERS, GROUND
GARBAGE DUMPS.: /AGEM^N
LEGISLATION, '-'ELLS, IMP
GROUND WATER, PERCCJLATIN
-i;I RRIGATION, ^CHEM ICAL
HASTE WATER TREATMENT,
* IRRIGAT IOM, #S PPINK L E R
WASTE WATER TREATMENT,
ORGANIC LOADING, -BIODE
#GROUNDHATER, *WATER OU
GROUNDWATER MOVEMENT, P
DISPOSAL, SUBSURFACE WATERS.: /PO
W7I-02Q36
W? 0-08662
W71-17084
Wll-10372
W71-06435
W71-01932
W71-12084
H7 0-0 129]
H69-00652
W70-0471?
W69-Q783S
W71-09611
W69-0321?
W69-Q0651
W70-Q8025
W70-08026
W71-04559
W71-09611
W7 1-1 1776
W71-11356
W71-04559
W 70- 100 5 8
VT/ 1-071 18
W71-07118
W69-03237
W7 l-]36^i 5
W69-Q3178
W70-06011
W70-07766
W7Q-07766
W70-09637
W7 1-03543
W71-11776
W7 1-0455 9
W7Q-01291
W69-08621
W68-01010
W69-07554
Wf 9-073 75
W71-03542
W71-01205
W71-Q1205
1-/70-10058
W71-01324
H71-08907
l-.'7 1-05094
W71-07194
W7 1-1 1724
W71-11692
W69-071] 4
H69-05328
W69-07375
W69-Q5327
W6 8-0 10 10
W69-03178
W69-02681
W69-03212
124
-------
CONTAMINATION, CESSPOOLS? SEWAGE
, CONVECTION, ^DISPERSION, WASTE
ENVIRONMENTAL SANITATION, ^'ASTE
R, OIL WASTES, CESSPOOLS, SFWAGE
LLS, -PATH OF POLLUTANTS/ -WASTE
RATION, SEWAGE TREATMENT, SEWAGE
MTAL SANITATION, WASTE DISPOSAL,
LLUTIOM CONT/ *LANDFILLS, *'-'ASTE
, RUSSI/ -AGRICULTURAL DRA IMAGE,
AT IONS HI PS, PERMEABILITY, ALGAE,
DUAL ITY, SAL IN ITY, GROUNDWATER,
PREADING, / SFEEDLOTS, OXIDATION
RIPARIAN RIGHTS, ARTESIAN WELLS,
IGHTS, NATURAL USE, NATURAL FLOW
ATER, PERCOLATING WATER, EMINENT
, EMINENT DOMAIN, PUBLIC HEALTH,
TES« CESSPOOLS, SEWAGE DISPOSAL,
RIPARIAN RIGHTS, COMPETING USES,
LEACHING, WATER QUALITY CONTROL,
EMENT, L IMESTONES, INFILTRATION,
RFACE MOVEMENT, CONSUMPTIVE USE,
PRECI°ITATIO^, LEACH BED, SPGK/
RFACE-GROUNDWATER RELATIONSHIPS,
RIGHTS, ARTESIAN WELLS, DITCHES,
FF, PERCOLATION, EUTROPHI CAT ION,
ACHING, DRAINAGE '-'ATER, AMMONIA,
MODELS, AQUIFERS, MODEL STUDIES,
SYSTEMS, -GRQUMD'-fATER MOVEMENT,
TER POLLUTION SOURCES, LEACHING,
10 GRANDE, ^SUBSURFACE DRAINAGE,
TOM, Rl'MOFF, UREAS, FERTIL IZERS,
, WATER POLLUTION, SNOW, RUMOFP,
COLLEGE(PENM), SANITARY LANDFILL
TROGEN, -RIO GRANDE, *SUBSURFACE
NSPORT, PENNSYLVANIA, SUBSURFACE
S, DRAINAGE PROGRAMS, SUBSURFACE
TY, PARTICULATE c/ ^AGRICULTURAL
ASE FLOW, PERCOLATION, LEACHING,
EMTHIC FAUNA, INDUSTRIAL WASTES,
RS, WELL REGULATIONS, SUBSURFACE
ICULTURAL WATERSHED, ^SUBSURFACE
DRAULIC CONDUCTIVITY, SUBSURFACE
TER MIXING? RUSSI/ ^AGRICULTURAL
S, OIL, OIL INDUSTRY, SUBSURFACE
USTRY, STORAGE TANKS, SUBSURFACE
LLS, GROUNDWATER, WATER SOURCES,
LAT IONS, PERCOLATION, SUBSURFACE
EVAPOTRANS PI RATION', ^LANDFILLS,
RELATIONSHIPS, DRAINAGE EFFECTS,
M, COLIFORMS, ALLUVIAL CHANNELS,
DS, LEACHING, CHLORIDES, GLACIAL
INTERFACES, MIXING, PENETRATION,
L WELLS, ^GROUNDWATER, ^SEEPAGE,
FILTRATION, OIL, OIL RESERVOIRS,
DARDS, REGULATION, WELL PERMITS,
USTRY, PUBLIC HEALTH, OIL W^LLS,
GROUNDWATER, PERCOLATING WATERS ,
TRITIATED WATER(TRACER ), MIMF
DUALITY, WASTE DISPOSAL, GARBAGE
BLEACHING, #LANDFILLS, ^GARBAGE
DISPOSAL,
DISPOSAL,
DISPOSAL,
DISPOSAL,
DISPOSAL,
DISPOSAL,
DISSOLVED
DISSOLVED
DOMESTIC
DOMESTIC
DOMESTIC
DOMESTIC
DRAINAGE
DRAINAGE
DRAINAGE
DRAINAGE
DRAINAGE
DRAINAGE
DRAINAGE
DRAINAGE
DRAINAGE
DRAINAGE
DRAINAGE
DRAINAGE
DRAINAGE
DRAINAGE
DRAINAGE
DRAINAGE
DRAINAGE
DRAINAGE
DRAINAGE
DRAINAGE
DRAINAGE
DRAINAGE
DRAINAGE
DRAINAGE
EFFECTS,
EFFECTS,
DISPOSAL, GROUNDWATER MOVEMENT, A
DISPOSAL, THERMAL PROPERTIES, MOD
DISPOSAL, WASTES, CALIF
DOMESTIC WASTES, FARM W
^GARBAGE DUMPS, #LANDFI
HYDROGEOLOGY, GROUNDWAT
WASTES, CALIFORNIA, PER
^HYDROGEOLOGY, WATER PO
NUTRIENTS, WATER MIXING
OXYGEN.: /OUNDWATER REL
DISSOLVED SOLIDS, LEACHING, SALT
DITCH, SLOTTED FLOORS, AERATOR, S
DITCHES, DRAINAGE EFFECTS, SEEPAG
DOCTRINE, REASONABLE USE, ARTIFIC
DP'IAIN, PUBLIC HEALTH, DOMESTIC W
DOMESTIC WATER, INDUSTRIAL WATE: /
WASTES, FARM WASTES, MUM
WATER, LEGAL ASPECTS, MU
WASTES, INFILTRATION, AO
WASTES, BENTHIC FAUNA, I
DOMESTIC WATER, POLLUTION ABATEME
DRAIN FIELDS, *TEST HOLES, ANNUAL
DRAINAGE EFFECTS, DRAINS, DEEP PE
SEEPAGE, WASTE
DETERGENTS, DEN
EFFECTS, GROUNDWATER, KA
PROGRAMS, SUBSURFACE DRA
SYSTEMS, HYDRAULIC MODEL
W ATER, AM ViON I A , DRAINAGE
SALINITY, FERTILI
IRRIGATION, RETUR
GRASSLANDS, SOILr
STATE
DRAINAGE WATER, SALINIT
i-'ATER DUALITY, WATER PO
MATER MANAGEMENT!APPLIE
LAKE METABOLISM, hORRI
FARM HASTES, SOIL MANAG
AQUIFERS, SINKS, CITIES
WASTE TREATMENT, WASTE
*DRAINAGE>, -EUTROPH 1C AT
TRANSMISSIVITY, HEAD LO
DISSOLVED NUTRIENTS, WA
WATER POLLUTION SOURCES
UNDERFLOW, UNDERGROUND
RIPARIAN RIGHTS, ARTESI
SHALLOW HELLS, SUBSURFA
DRAINAGE, SANITARY ENGINEERING, *
DRAINS, DEEP PERCOLATION, EVA POTR
DREDGING, EXCAVATION, AOUIFERS, G
DRIFT, AOUIFERS, OHIO RIVER, KENT
DRILL HOLES, GROUNDWATER MOVEMENT
DRILL HOLES, OILY WATER, GROUNDWA
DRILLING EOUIPMENT, LEASES, DAMAG
DRILL ING, ADMINISTRATIVE AGENCIES
DRILLING, OIL FIELDS, SALINE MATE
DRILLING, OIL WELLS, WATER SUPPLY
DUMP LEACHING.:
DUMPS.: /AGEMENT, IMPAIRED WATER
DUMPS, ^GROUNDWATER MOVEMENT, KAR
WATER,
WATER,
WATER,
W69-00652
WC9-00651
W70-06011
W70-
W70-
H 70-
W70-
W70-
W70-
W71-
W71-
W71-
W69-
W 70-
W70-
W70-
W70-
W70-
W69-
W 7 1 -
W71-
W69-
W69-
H69-
H71-
W 7 1 -
W 71 -
'71-
W71
W70
W 7 1
W70
W 7 1
W71
W71
W71
W71
W71
'V70
W70
W70
W70
W70
W69
W68
W69
W71
W71
W71
W 7 1
W71
W71
H71
V71
W71
W71
06572
0471?
06011
07193
04504
12410
06063
03542
06118
02896
02896
02896
08049
00532
03178
09154
13645
01076
00248
06118
12084
04548
01932
01932
04548
08662
06435
04193
01204
08662
0] 204
01932
06443
06443
09154
10157
04504
07766
04504
07632
07631
06118
06117
00058
00248
02909
00194
03230
08055
08055
04742
01028
13521
11 255
07194
01204
125
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UTION
POLLUTION
, DRAINAGE
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POLLUTION
POLLUTION
IRRIGATION
IRRIGATION
H OF POLLUTANTS, WATER POLLUTION
L TECHNIQUES, SOIL CONTAMINATION
WATER POLLUTION, WATER POLLUTION
UTION ABATEMENT, WATER POLLUTION
RELATIVE RIGHTS, WATER POLLUTION
RTESIAN WELLS, DITCHES? DRAINAGE
ELLS, WATER TABLE? ENVIRONMENTAL
R SUPPLY? FARMS, WATER POLLUTION
-DETERIORATION, *WATFR POLLUTION
NGE, *HATER QUALITY, ^IRRIGATION
CHARGE, AQUIFER CHARACTERISTICS,
RATFS OF APPLICATION, NU1RIFNTS,
WASTE '''ATER TREATMENT? W/ SEWAGE
i-'ASTE WATER TREATMENT ? H/
GE, KYDROCHEM1CAL FACIES,
1C COMPOUNDS, DISPERSION,
'/'EEDS, NUTRIENTS, SEPTIC
f-'IC ABSOR/ -GROUND HATER,
GROUNDWATER, PERCOLATING
M r NTA L S A M IT A T I ON , E M V I
INFILTRATION, AQUIFORS,
, -LANDFILLS, DRAINAGE,
G, *PATH OF POLLUTANTS,
^REVIEWS, METHODOLOGY, SANITARY
WATER, ^INFILTRATION, COLIFORMS,
ER MOVEMENT, PATH OF POLLUTANTS,
LEACHING, GROUNDWATER "
OL LUTI Or' CONTROL, PUBLIC
F, ENVIRON-ENTAL SANITATION,
SEWAGE
SFWAGE
SEWAGE
TANKS,
*TRACE
WATER,
'^NTAL
SANITARY
SANITARY
*NUCLEAR
T HOLES, UNIVERSITY OF ILLINOIS,
ENT BEHAVIOR! WATER ) , SSOIL-^ATER
RTIES, WATER WELLS, WATER TABLE,
USSR, RADIAL DIFFUSION
R MOVEMENT, -RADIOACTIVE WASTES,
ION, MODEL STUDIES, MATHFMATICS,
MOVEMENT, SEEPAGE , POROUS MEDIA,
ATION, RADIOACTIVE WASTES, IONS,
DUMPS,
DUMPS,
DUMPS,
DUMPS, ^LANDFILLS, *PATH OF POLLU
DUMPS, * SOL ID WASTES, BLEACHING,
LANDFILLS, WASTE DUMPS, WA
MI ME WASTES, MINING, GROUN
WASTE STORAGE, SOIL PROPER
WASTE DUMPS, WASTE STORAGE
DUMPS, WATER POLLUTION, PRECIPITA
ECONOMICS.: /^GROUND WATER RECHAR
ECONOMICS.: /-GROUND WATER RECHAR
ECOSYSTEMS, EUTRODHI CAT!ON, OLIGO
EFFECTS.: #GROUNDWAT
EFFECTS, ^RETURN FLOW, *SALINE WA
EFFECTS, *HATER POLLUTION CONTROL
*SODIUM CHLORIDE, #HIGHW
#ON-SITE INVESTIGATION^,
DRAINS, DEEP PERCOLATION
DETERGENTS, DENITRIFICAT
GROUNDWATFR, WATER OUALI
IMPAIRED WATER QUALITY,
LEGAL ASPECTS, JUDICIAL
LEACHING, DENITRIFICAT10
LFACHING, WATER LEVEL FL
NUTRIENTS, GROUNDWATER M
ORGANIC COMPOUNDS, DISPE
POLLUTION ABATEMENT, PAT
POLLUTANTS, HASTE DISPOS
STREAMS, GROUNDWATER, JU
SEEPAGE, WASTE STORAGE,
WATER CHEMISTRY, INFILTR
WATER POLLUTION SOURCES,
EFFECTS, WATER QUALITY, SALINITY,
EFFICIENCY, SIMULATION, GROUND WAT
EFFLUENT STREAM, GROUNDWATER RECH
EFFLUENT, AQUIFER, AMMONIA, SOIL
WASTE HATER DISPOSAL,
#WASTE WATER DISPOSAL,
C.O.D., B.O.D., WASTE W
BIODEGRADATION, METHOD
SWAMPS, FOREST SOILS,
ELEMENTS, CHELATE EXTRACTION, ATO
EMINENT DOMAIN, PURLIC HEALTH, DO
ENGINEERING, WATER POLLUTION SOUR
/ DOMESTIC WASTES,
BLEACHING, WATER POL
NUCLEAR EXPLOSIONS,
ENGINEERING, LANDFILLS, HYDROLOGY
ENTERIC BACTERIA, NITRATES, CHLOR
ENVIRONMENT.: /AM^LIVG, GROUNDWAT
ENVIRONMENTAL SANITATION, ENVIRON
SANITATION, WASTE D
ENGINEERING, WATER
GEOLOGY.:
ENVIRONMENTAL POLLUTION. : TES
ENVIRONMENT, ANIOWIC SURFACTANTS,
ENVIRONMENTAL EFFECTS, |JATER CHEM
EQUATIONS.:
GROUNDWATER MOVEMENT,
PATH OF POLLUTANTS? FO
MATHEMATICAL MODELS.: /
EFFfcCTS,
EFFECTS,
EFFECTS,
EFFECTS,
EFFECTS,
EFFECTS,
EFFECTS,
EFFECTS,
EFFECTS,
EFFECTS,
EFFECTS,
EFFECTS,
EFFECTS,
EFFECTS,
EFFECTS,
EFFECTS,
EFFECTS,
EFFLUENT,
EFFLUENT,
EFFLUENT,
EFFLUENTS,
EFFLUENTS,
ENGINEERING.
ENGINEERING,
ENGINEERING,
ENVIRONMENTAL
ENVIRONMENTAL
ENVIRONMENTAL
W70-
1171-
H71-
W71-
W68-
W68-
W71-
W69-
W69-
W70-
!-' 7 1
W71-
W 71
H70-
H70-
W69-
H 7 1 -
W71-
W70-
W70-
W70-
W7L
W70'
H70-
W71'
W71-
H 7 1
W 6 9
W 7 1
H7]<
W 7 1
W71-
W71
H 71
W69-
W 6 9
H69
W 7 0
W 7 0
W 6 9
H 7 0
W 7 0
H 6 9
06572
07194
05094
EQUATIONS,
EQUATIONS,
EQUATIONS,
W7l
W71
W69
W70
W70
W70
W7 Q-
W70
VI70
W70
W71
W69
W70
-00058
-00058
-05094
-05327
-05328
-04193
-07194
-08044
-09154
-09844
-06322
-00248
-12084
-04548
-08025
-08026
-08662
-08073
-00665
-01291
-11724
-11692
-01043
-06118
-04121
-13521
-06063
-09936
-03543
-03542
-05328
-05327
-03197
-01291
-04193
-03197
-02896
-06572
-03178
-00058
-04882
-08907
-01076
-06322
-06572
-06011
-06572
-06572
-06322
-01291
-04121
-03212
EQUATIONS, MATHEMATICAL MODELS, C
10058
W71-01930
H71-09611
W71-11356
126
-------
N, OIL, OIL RESERVOIRS* DRILLING
ATION, AMMONIFICATION, LEACHING,
DRAINAGE WATER, GRASSLANDS, SOIL
STREAMS, FISH, LAND, ECOSYSTEMS,
ALFALFA-BROKE GRASS, SPRI/ -LAKE
ROUMDWATER, 3UNPFF , PE RCOL AT 1.0 N ,
WASTE WATER DISPOSAL, NITRATES,
WASTE WATER DISPOSAL, NITRATES,
OIL TYPES, PERMEABILITY, FLOODS,
C DIGESTION, ODORS, GROUNDWATER,
TER RELATIONSHIPS, INFILTRATION,
FECTS, DRAINS, DEEP PERCOLATION,
WATER, ^SEEPAGE, #SOIL MOISTURE,
S, ARTESIAN WELLS, WELL SCREENS,
-'VENEZUELA, ^NUCLEAR CANAL
MS, ALLUVIAL CHANNELS, DREDGING,
T/ WATER POLLUTION SOURCES, -ION
ATER MOVEMENT, -DISPERSION, *IOM
LLS, WATER SUPPLY, AQUIFERS, ION
FACE SPREADING, RECHARGE BASINS,
FACE SPREADING, RECHARGE BASINS,
S, --''NUCLEAR ENGINEERING, NUCLEAR
WATER, #TRACE ELEMENTS, CHFLATE
ND WATER RECHARGE, HYDROCHEMICAL
ILTRAT10N PONDS, CAPE COD(MASS),
ILTRATION PONDS, CAPE COD(MASS),
INDUSTRIAL WASTES, ALGAE, PONDS,
PERCOLATION, LEACHING, DRAINAGE,
TER POLLUTION SOURCES, LEACHING,
C/ ^EUTROPHICATION, FERTILIZFRS,
ES, WATER TABLE, SURFACE RUNOFF,
EWAGE DISPOSAL, DOMESTIC
ILL ING, OIL WELLS, WATER
RATION, DOMESTIC HASTES,
CATTLE
ORGANIC CARBON,
N, NITROGEN SOURCES, WELL WATER,
ISM, MOBILITY, PARTICIPATE FORM,
M^THEMOGLOBIN, NITRATE MOVEMENT,
ALLEY(COLO).: NATIVE GRASSES,
LLUTION SOURCES, MICROORGANISMS,
HEDS, ORGANIC MATTER, SEDIMENTS,
LFALFA-BROMEGRASS, SPRING THAWS,
TS, DENITRIFIC/ #FUTROPHI CAT ION,
DENITRIFICATION, RUNOFF, UREAS,
IMAGE, DRAINAGE WATER, SAL IN ITY,
DWATER, -AGRICULTURAL CHFMICALS,
PITATION, LEACH BED, SPOK/ DRAIN
, fcRIODEGRADATION, SOIL DISPOSAL
WATER POLLUTION SOURCES, *CPRES»
HEALTH, OIL WELLS, DRILLING, OIL
TION, PERCOLATION, SOIL DISPOSAL
TER QUALITY, ^LANDFILL, SANITARY
TION WATER, ARTIFICIAL RECHARGE,
RATION, PERCOLATION, ADSORPTION,
ERTIARY TREATMENT, INFILTRATION,
ATIDN, OLIGOTR/ #LAKES, STREAMS,
ENTERICUS, DIATOMEA, CLADOPHORA,
EVAPOTRANSPIRATION, PERCOLATION,
REAMS, SOIL TYPES, PERMEARILITY,
WASTES,
SUPPLY,
BENTHIC
WASTES,
EUTROPHICATION,
EUTROPHICATIDN,
EUTROPHICATION,
EQUIPMENT, LEASES, DAMAGES, LAND
EROSION, NITROGEN, RUNOFF, WATER
EROSION,: /LUTION, SNOW, RUNOFF,
EUTROPHICATION, OLIGOTROPHY, SEV!A
*SOIL PHOSPHORUS,
DRAINAGE EFFECTS,
AQUIFERS, GROUNDS
EUTROPHICATION, AQUIFERS, GROUNDW
EVALUATION, PLANNING.: /TREAMS, S
EVAPORATION, INFILTRATION, CLIMAT
EVAPOTRANSPIRATION, PERCOLATION,
EVAPOTRANSPIRATION.: /DRAINAGE EF
EVAPOTRAMSPIRATION, ^LANDFILLS, D
EXCAVATION, WATER POLICY, AQUIFER
EXCAVATION.:
EXCAVATION, AQUIFERS, GRAVELS, AQ
E XC HANGE, -WAT ER OUALIT Y, * IR RIGA
EXCHANGE, DIFFUSION, MIXING, RAD I
EXCHANGE, POLLUTANTS, POLLUTANT I
EXPERIMENTAL RECHARGE PROJECT, Ft.
EXPERIMENTAL RECHARGE PROJECT, EL
EXPLOSIONS, CANALS, CANAL CONSTRU
EXTRACTION, ATOMIC ABSORPTION ANA
FACIFS, SEWAGE EFFLUENT, C.O.D.,
FALMOUTH(MASS).: INF
FALMOUTH(MASS).: INF
FARM WASTES.: /GE, INFILTRATION,
FARM WASTES, SOIL MANAGEMENT, GRO
GROUNDWATER, HYDRAUL
NUTRIENTS, DENITRIFI
AERORIC CONDITIONS,
MUNICIPAL WASTES, MA
FARMS, WATER POLLUTION EFFECTS, W
FAUNA, INDUSTRIAL WASTES, DRAINAG
FEEDLOT WASTES.:
FEEOLOTS.:
: /OURCES, MINERALIZATIO
NUTRIENT SOURCES.: /BOL
RESIDUAL ACCUMULATION,
FFEDLOTS, CORRALS, SOUTH PLATTE V
FERROBACILLUS, FLOW RESISTANCE, R
FERTILIZERS, WATER POLLUTION, SNO
FERTILIZER-NITROGEN.: /SPHORUS, A
I-ERTILIZERS, FARM HASTES, NUTRIEN
FERTILIZERS, DRAINAGE WATER, IRRI
FERTILIZERS, GROUNDWATER, IRRIGAT
FERTILIZERS, PESTICIDES, NUTRIENT
FIELDS, *TEST HOLES, ANNUAL PRECI
CESSPOOLS, SEPTIC TANKS,
PLANTS, ALFALFA, CEREAL C
SALINE WATER, SALINE WATE
FIELDS, SOIL CONTAMINATION, SOIL
FILL, WASTE DILUTION, WATER POLLU
FILTRATION, SORPTION, INFILTRATIO
FILTRATION.: /ER MOVEMENT, INFILT
FILTRATION, SEWAGE TREATMENT, SEW
FISH, LAND, ECOSYSTEMS, EUTROPHIC
FLAGELLATA, CILIATES, RANUNCULUS
FL30D CONTROL, RESERVOIRS, PR EC IP
FLOODS, EVALUATION, PLANNING.: /T
FARM
FARM
FARM
WASTED,
WASTES,
WASTES,
FARM WASTES,
FEEDLOTS.
FEFDLOTxS,
FEEDLOTS,
FIELDS,
FIELDS,
FIELDS,
W71
W70
WTO
W69
W71
W71
W71
W71
W71
W70
W69
W68
W71
W71
W71
W71
W71
W69
W69
W69
W71
W69
W69
W71
W71
W71
W71
W71
W71
W69
W70
W71
W71
W70
W71
W71
W71
W71
W*/0
W69
W70
W69
W71
W71
WTO
K'7 ]
W69
W68
W70
W71
W69
W69
W69
W69
W70
W70
W69
W70
W71
-08055
-10372
-04193
-04193
-09721
-12084
-01324
-01205
-05094
-07118
-06102
-00248
-00058
-04742
-04882
-02909
-09936
-11356
-02611
-05328
-05327
-04882
-03197
-03197
-01205
-01324
-06435
-06443
-08218
-10372
-09721
-08049
-13521
-09154
-00665
-08218
-06435
-06443
-10372
-04488
-00979
-04193
-09721
-10372
-06435
-08662
-04121
-01076
-01010
-04488
-01028
-08621
-03178
-08621
-07375
-04712
-04193
-07838
-06102
-05094
127
-------
-RETURN
CONDUIT
EDLOTS, OXIDATION DITCH, SLOTTED
REUSE, ART IF 1C IAL RECHARGE, LOW-
JAN RIGHTS, NATURAL USE, NATURAL
S, MINING, GROUNDHATER MOVEMENT,
HATER, SURFACE HATERS, AQUIFERS,
, MICROORGANISMS, FERROBACILL US,
^MULTIPHASE
ARCY'S LAW, PERMEABILITY, -RIVER
A, GROUNDHATER, HASTES, * UN I FORM
OMVECTION, -GROUNOHA/ ^SATURATED
TIQM/ -IRRIGATION HATER, -RETURN
ILS, *!/ *WATER QUALITY,
BILITY, POROSITY, CLOSED
DHATER RELATIONSHIPS, D/ ^RETURN
GROUND HATER MOVEMENT, CAPILLARY
MANAGEMENT, LEACH/ ^UNSATURATED
IS, #PATH OF POLLUTANTS, ^RETURN
HATER POLLUTION EFFECTS, -RETURN
SAL, UNSATURATED FLOW, SATURATED
HAGAN-POISEUILLE
, PATH OF POLLUTAMTS, SUBSURFACE
^IRRIGATION RETURN
LS, PR08ABILITY, THERMODYNAMICS,
FRCOLATIOM, SEEPAGE, UNSATURATED
, NITRATES, SURFACE RUNOFF, BASE
HASTES, -UNIFORM F/ ^DISPERSION,
AL RECHARGE, CONVECTION, MIXING,
TIVE WASTE DISPOSAL, UNSATURATED
LEACHING, DENITRIFICATION, RIVER
AINAGE WATER, IRRIGATION, RETURN
N EFFECTS, LEACHING, WATER LEVEL
RGE, TRANSMISSIVITY, WATFR LEVEL
NALYSES, CARBONATE, BICARBONATE,
, EXPERIMENTAL RECHARGE PROJECT,
, EXPERIMENTAL RECHARGF PROJECT,
, EQUATIONS, PATH OF POLLUTANTS?
SEPTIC TANKS, EFFLUENTS, SHAM PS,
ETABOL ISM, MOBILITY, PART ICULATE
WELLS, GROUNDWATER, SAL INE HATER-
, #SALINE HATER S/ -SALINE HATER-
ELDS, SALINE WATFR, SALINE WATER-
ION SOURCES, JUDICIAL DECISIONS,
N SOURCES, SOLID HASTES, WASTES,
D HATER QUALITY, HASTE DISPOSAL,
L , SURFACE WASTERS, GROUNDHATER,
ASTFS, MUNICIPAL HASTFS, NATURAL
FERS, HATER TABLE, HATER SUPPLY,
F POLLUTANTS, OIL INDUSTRY, OIL,
LE USE, DAMAGES, SURFACE RUNOFF,
OF POLLUTANTS, SUBSURFACF FLOW,
N, NITROGEN SO/ ^SURFACE WATERS,
ENVIRONMENTAL
TIOiV' CONTROL, SURVEYS, LEACHING,
PATH OF POLLUTANTS, MINE HASTES,
ONS, *ILL INOIS, HYDROLOGIC DATA,
PLY, WATER UTILIZATION, SURVEYS,
NTS, ACIDS, LEACHING, CHLORIDES,
IVE RIGHTS, LEGAL ASPECTS, STATE
TEMFNT, STATE GOVERNMENTS, LOCAL
HASTES, --OIL, LEGISLATION, STATE
FLOODS, AERATOR, SPREADING, LAND
FLOW AUGMENTATION.: /IFERS, WATER
FLOW DOCTRINE, REASONABLE USE, AR
PROFILES, SAMPLING, DATA COL
RATES, LEACHING.: /E, GROUND
RESISTANCE, RETENTION, HAHA I
FLOW
FLOW
FLOW
FLOW.
FLOW.
FLOW,
FLOH,
FLOW,
FLOW,
FLOW,
FLOW,
FLOW,
FLOW,
FLOW,
FLOW,
FLOW,
FLOW,
FLOW,
FLOW,
FLOW,
FLOW,
FLOW,
FLOW,
FLOW,
FLOW,
FLOW,
/PTION, WATFR CHEMISTRY, D
#D IF FUSION, POROUS MATERIAL
-DIFFUSION, ^DISPERSION, -C
^DRAINAGE HATER, #DETERIORA
#GROUNDWATER, '"SATURATED SO
AGROUND HATER MOVEMENT, CAP
^IRRIGATION, *SURFACE-GROUN
#LAVA, BASALTS, WATER POLLU
^MOISTURE ROUTING, LANDFILL
^NITRATES, MATHEMATICAL MOD
#SALINE WATER INTRUSION, *H
ADSORPTION, ADSORPTION, ION
CLOGGING.:
GASOLINE, WATER LAW, WELLS,
HYDROLOGIC-OUALITY MODEL.
MASS TRANSFER, DIFFUSION,
MODEL STUDIES, SATURATED SO
PERCOLATION, LEACHING, DRAI
POROUS MEDIA, GROUNDHATER,
POROUS MEDIA.: /S, ARTIFICI
SATURATED FLOW, ADSORPTION,
WATER POLLUTION SOURCES.:
FLOW, WATER SUPPLY, LIVESTOCK, SE
FLUCTUATIONS, SALINE SOILS, LAND
FLUCTUATIONS, AMMONIA, NEBRASKA,
FLUORIDE, NITRATE, SULFATE, SILIC
FLUSHING MEADOWS PROJECT, PHOENIX
FLUSHING MEADOWS PROJECT, PHOENIX
FOREIGN PROJECTS. : /, MATHEMATICS
FOREST SOILS, MINNESOTA, WI SCONS I
FORM, FFEDLOTS, NUTRIENT SOURCES.
FRESH WATER INTERFACES, MIXING, P
FRESH-WATER INTERFACES, BLEACHING
FRESHWATER INTERFACES, HELLS, WEL
FUELS, WELLS, WATER POLLUTION, SE
GARBAGE DUMPS, HASTE DUMPS, WASTE
GARBAGE DUMPS. : /AGEMENT, IMPA IRE
GARBAGE DUMPS, LANDFILLS, WASTE D
GAS, SALINE: /STIC WASTES, FARM
GASES, CARBON DIOXIDE, METHANE,
GASES, POLLUTANTS, PERCOLATION, W
GASOLINE, '-'ATER POLLUTION SOURCES
GASOLINE, WATER LAW, WELLS, GROUN
GEOLOGICAL SOURCES, M I NERA L I ZAT I 0
GEOLOGY. :
GROUNDWATER MOVEMENT.:
GROUNDHATER, WATER OUALI
GEOLOGY, HYDROLOGY, HYDROGEOLOGY ,
GEOPHYSICS.: /R LEVELS, WATER SUP
GLACIAL DRIFT, AQUIFERS, OHIO RIV
GOVERNMENTS, STATE JURISDICTION,
GOVERNMENTS, LEGISLATION, WATER R
GOVERNMENTS, POLLUTION ABATEMENT,
W71-
W70-
W70-
W71-
W70-
W69-
W71-
W69-
W69-
H69-
W71-
W71-
W69-
W69-
W69-
W68-
W71-
W71-
W70-
W69-
W68-
GEOLOGY,
GEOLOGY,
M
0
I
I
t
/
E
C
X
X
S
I
*
P
G
L
E
E
E
D
W
B
W
S
N
0
/
I
,
P
V
R
9
W71
W71-
W69
W71-
W69-
W69-
W70
W70
W71
W 7 1
W71-
W 6 9
W69
W69
W 7 1
W70
W7i
V! 1 1
W 7 1
W71
W69
W68
W71
W 1 1
WTO
W 7 0
W71
H 7 0
H 6 8
W 7 1
W 7 0
W 7 0
W71
W 7 0
W70
W71
VI 71
W 7 0
W69
03542
03102
02896
11255
09637
00979
11776
02611
01238
08921
06063
08073
00979
00243
00979
00058
04548
08044
10058
00979
00627
09936
11776
02681
06443
01238
07554
10058
08662
06435
08073
03543
03197
05327
05328
01930
04193
06443
03230
01932
01028
06117
00058
07194
05094
08049
06011
11724
08049
00627
06435
06572
07193
08907
06322
05466
00194
13521
02896
05370
128
-------
ROL, -POLLUTION ABATEMENT, STATE
THERMAL
IMAG/ SNITRATES, ^ITROGEN, -RIO
UPPER RIO
TRANSIENT STORAGE,
P L A T T E V A L L E Y(C 0 L 0).: NATIVE
N, SNOW, RUNOFF, DRAINAGE WATER,
DREDGING, EXCAVATION, ACUIFFRS,
R, SUBSURFACE WATERS, DIFFUSION,
R COMPANY, NETWORK ANALYSIS.:
GAL ASPECTS, JUDICIAL DECISIONS,
IDF, NITRATE, SULFATE, SILICATE,
ION, DAMAGE, JUDICIAL DECISIONS,
LOW, GASOLINE, UATFR LAW, WELLS,
SITY, CLOSED CONDLJ/ PERCOLATION,
RFACE STREAMS, DEEP PERCOLATION,
ER, ^RELATIVE RIGHTS, WATER LAW,
ES, -BACTERIOPHAGE, PERCOLATION,
TURM FLOU, ^IRRIGATION, ^SURFACE
ION', CESSPOOLS, SEWAGE DISPOSAL,
-DISPERS I0>', FLO1-' , POROUS MFD I A,
OKMS, ENTERIC BACT/ ^POLLUTANTS,
PERCOLATING WATER, INFILTRATION,
OXYGEN DEMAND, LEACHING, RUNOFF,
PES, RADIOACTIVE WASTE DISPOSAL,
INFILTRATION, RECHARGE, ^SURFACE
LEACHATE, IMF ILTRAT ION CAPACITY,
OLLUTIO^', -GROUNDWATER RECHARGE,
, AOUIFERS, SOIL '-'ATER MOVEMENT,
/ * IN FIL T RA TION, -PO M DS, *SOIL,
ARTIFICIAL USE, RIPARIAN LANDS,
CYCLE, OVERDRAFT, WELLS, SURFACE
ER, WELL SPACING, SHALLOW WELLS,
AOUIFERS, HYOROGFOLOGY,
HEALTH, * S 0 IL L F AC HING,
, SOILS, POROSITY, PERMEABILITY,
KES, POMQS, TIDAL WATERS, WFLLS,
INKIER IRRIGATION, INFILTRATION,
ER POLLUTION EFFECTS, NUTRIENTS,
WELLS, MATER POLLUTION, SEEPAGE,
G '"'ATER,
^PUBLIC
ORPTION
LEACHING, #/ -VIRUSES,
, SFWAGF DISPOSAL, HYDROGFOLOGY,
ACE WATERS, PRIOR APPROPRIATION,
A, SAL IN ITY, STREAM FLOW, SURFACE
GE UATER, SALINITY, FERTILIZERS,
RS, PERCOLATION, SUSPFNDFO LOAD,
RIGHTS, WATER POLLUTION SOURCES,
GAL ASPECTS, JUDICIAL DECISIONS,
ATER WELLS, INFLOW, UNDERGROUND,
TA COLLECTIONS, HYDROLOGIC DATA,
EZOMETRY, *HATER TABLF, ^SURFACE
OIS, MUNICIPAL WASTES, LEACHING,
INF, -PE RC OLAT ING WATFR, *WFLL S,
CROPS, IRRIGATED LAND, COLORADO,
POLLUTION SOURCES, GROUNDWATER,
N, ^SEEPAGE, -SUBSURFACE WATERS,
, POLLUTANTS, INDUSTRIAL WASTES,
ROL, SURVEYS, LEACHING, GEOLOGY,
DUSTRY, WATER POLLUTION SOURCES,
TRAT I ON, PERMEABILITY, SAM PL ING,
GOVERNMENTS,
GRADIENTS.:
GRANDE, -SUB
GRANDE, SALT
GRAPHICAL SO
GRASSES, FEE
GRASSLANDS,
GRAVELS, AOU
GRAVITATIONA
GREAT MIAMI
GROUN: /TION
GROUND
GROUND
GROUND
GROUND
GROUND
WATFR
WATER
WATFR
WATER
WATER
GROUND WATFR
GROUND-WATER
GROUMDWATER
GROUNDWATER
GROUNDWATER,
GROUMDWATEP,
GROUMDWATER
GROUMDWATER,
GROUNDWATER
GROUNDWATER
GROUMDWATER
GROUNDWATER,
GROUNDWATER
GROUNDNATER
GROUNDWATER,
GROUNDWATER
GROUNDWATERT
GROUNDWATER
GROUNDWATER,
GROUNDWATER
GROUNDWATER,
GROUNDWATER,
GROUNDWATER
GROUMDWATER,
GROUMDWATFR,
GROUNDWATER
GROUMDWATFR,
GROUNDWATER
GROUNDWATER,
GROUNDWATER,
GROUNDWATER,
GROUNDWATER
GROUNDWATER,
GROUMDWATER
GROUMDWATER
GROUNDWATER
GROU^OWATER,
GROUNDWATER,
GROUNDWATER
GROUMDWATER,
GROUNDWATER,
GROUNDWATER
GROUNDWATER
GROUNDWATER
LOCAL GOVERNMENTS, L
SURFACE DRAINAGE, DRA
BALANCE.:
LUTIONS.:
DLOTS, CORRALS, SOUTH
SOIL EROSION,: /LUTIO
ITARDS, PUMPING, WATE
L WATER, SALTS, SALIN
RIVER, S.W. OHIO WATE
CONTROL, DAMAGES, LE
RECHARGE, HYDROCHEMI
, PATH OF POLLUTANTS,
MOVEMENT.: /URFACE P
, ^PERMEABILITY, PORO
MOVEMENT, IMFILTRATI
, SUBSURFACE WATER, P
, WATER POLLUTION.: /
RELATIONSHIPS, DRAINA
MOVEMENT, ABSORPTION,
WASTES, ^UNIFORM FLO
^INFILTRATION, COLIF
MOVEMENT.: /ULFIDES,
CELLULOSE, HYDROGEN
MOVEMENT, PERCOLATION
RELATIONSHIPS, OBSERV
CONTAMINATION.: /NT,
^SEEPAGE, ;:=SOIL MOIS
MOVEMENT, INFILTRATIO
BASINS, WATER SUPPLY,
PERCOLATING WATER, E
RELATIONSHIPS, DA: /
WATER SOURCES, DRAIN
BASINS, HYDROLOGIC CY
SOIL PROFILES, WATER
MOVEMENT, SOIL WATER
SURFACE WATERS, SEEP
WATER LEVELS, WATER
MOVEMENT, NITROGEN, W
PERCOLATING WATER, W
WATER POLLUTION, ABS
MOVEMENT, WATER RESOU
UNDERGROUND STREAMS,
RELATIONSHIPS, INFILT
IRRIGATION EFFECTS,
AQUIFER CHARACTERIST
GROU^DWATER MOVEMENT
MOVEMENT, PERCOLATING
WATER SUPPLY, SEEPAG
MOVEMENT, WATER QUALI
RELATIONSHIPS, *WATER
MOVEMENT, ENVIRONMENT
OILY WATER, OIL INDU
PERCOLATION.: /REAL
MOVEMENT, PERMEABILIT
UNDERGROUND STREAMS,
WATER POLLUTION EFFE
MOVEMENT. : /TION COM
MOVEMENT, UNDERFLOW,
MOVEMENT, PATH OF POL
W70-
W69-
W70-
W 70-
W69-
W70-
W70-
W71-
W70-
W69-
W71-
W69-
K'68-
W68-
W69-
V.1 70-
W70-
W69-
W69-
U'69-
W69-
H69-
W6B-
W68-
W69-
W69-
W68-
W68-
W69-
V'f 9-
W70-
W70-
W69-
W70-
W69-
W 6 9
W69
W70
U69
W70
W70
W70
W70
W70
W70
W70
W70
W70
W70
W70
W70
W70
W70
W70
'-J70
W70
W70
W70
W70
0?896
08921
08662
08662
00248
04488
04193
02909
08026
02611
11724
03197
00627
00627
00979
0052]
00521
00225
00248
0065?
01238
01076
01010
01269
02681
02611
00058
00058
08620
07838
07896
00532
06118
00532
0972]
07375
05370
07114
00665
06117
04688
04712
08049
06102
08662
04504
07631
08026
0763?
05466
07766
06572
08025
04488
07631
08050
08026
07193
08025
06322
129
-------
ASTE DUMPS? MINE HASTES,
N CYCLE, PHOSPHORUS, REGULATION,
ATION, ALLUVIA CHANNELS, SURFACE-
AS TES, POLLUTANTS, INFILTRATION,
CTSt POLLUTANTS, WASTE DISPOSAL,
SALINE HATER, SUBSURFACE WATERS,
ACE WATERS, UNDERGROUND STREAMS,
ATER POLLUTION EFFECTS, STREAMS,
POLLUTION, RECHARGE, DISCHARGE,
INTERFACES, HELLS, WELL CASINGS,
RFACE-GROUNDWATER RELATIONSHIPS ,
^RADIOACTIVE WASTES, EQUATIONS,
HARACTERISTICS, EFFLUENT STREAM,
ILS, *FARM WASTES, -FERTILIZERS,
CERS, ROADS, CHEMCONTROL, SALTS,
US ION, #OIL WELLS, *WATER WELLS,
RATES, EUTROPHICATION, AQUIFERS,
FR MOVEMENT, ^RECHARGE, -SURFACE-
ATER, AMMONIA, DRAINAGE EFFECTS,
RATES, EUTROPHICATION, AQUIFERS,
WELLS, MUNICIPAL HATER, SURFACE-
RATIVE AGENCIES, ADMINISTRATION,
1XIMG, PENETRATION, DRILL HOLES,
E, FARM WASTES, SOIL MANAGEMENT,
ONS, CANALS, CANAL CONSTRUCTION,
SPHERIC), SEEPAGE, INFILTRATION,
RIGATION EFFICIENCY, SIMULATION,
RUNOFF, WATER POLLUTION CONTROL,
SOURCES, LEACHING, FARM WASTES,
LINITY, WITHDRAWAL, GROUNDWATER,
NITRATES, SALINITY, WITHDRAWAL ,
ER INTERFACES, IMPERVIOUS SOILS,
FFECTS, WATER QUALITY, SAL INITY,
OLLUTANTS, MINE WASTES, GEOLOGY,
ION, ANAEROBIC DIGESTION, ODORS,
PROCEDURES, CHEMICAL PROPERTIES,
EEPAGE, DRILL HOLES, OILY WATER,
TER PROGRAMS, DIFFUSION, MIXING,
RUNOFF, ODOR, SUBSURFACE RUNOFF,
EOLOGY, WATER POLLUTION SOURCES,
WASTE DISPOSAL, SURFACE WASTERS,
EW MEXICO, -SOIL WATER MOVEMENT,
ON, SEDIM/ ^NITROGEN, -NITRATES,
AL/ ^TRANSFORMATIONS, AMSTERDAM,
AMSTERDAM, HAARLEM, LEYDEN, THE
TURE, NITRATES, PLANTS, AMMONIA,
LUS, FLOW RESISTANCE, RETENTION,
OAH!J( HAWAII ) , MAUK
OAHU(
URFACE DRAINAGE, TRANSM ISSIV ITY,
ICATION, -SOIL NITROGEN, #PUBL 1C
WELLS, -LEGISLATION, C/ ^PUBLIC
NG WATER, EMINENT DOMAIN, PUBLIC
WATER POLLUTION CONTROL, PUBLIC
ATER WELLS, OIL INDUSTRY, PUBLIC
(TEXAS), HOL/ *OGALLALA AQUIFER,
TRATE, NITRITES, NITROGEN-CYCLE,
ION, POTASSIUM, POULTRY, CATTLE,
GROUNDWATER,
GROUNDWATER
GROUNDWATER,
GPOUNDWATER,
GROUNDWATER,
GROUNDWATER,
GROUNDWATER
GROUNDHATER,
GROUMDWATER
GROUNDWATER MOVEMENT, FLOW PROFIL
GROUNDWATER? RUMOFF, PERCOLATION,
GROUNDWATER RELATIONS'- I PS , PERMEA
GROUNDWATER MOVEMENT, SUBSURFACE-
GROUNDWATER, PERCOLATING WATER, P
PERCOLATING WATERS,
MOVEMENT, PATH OF POL
JUDICIAL DECISIONS,
SURFACE WATERS, AOUI
WATER SUPPLY, PERCOL
GROUNDWATER MOVEMENT.: /WATER, SU
GROUNDWATER MOVEMENT, LEACHING, M
GROUMDWATER RECHARGE, TRANSMISSIV
GROUMDWATER, PRECIPITATION, POTAS
GROUNDWATER, LEACHING, SALINE SOI
GROUMDWATER, SALINE WATER-FRESH W
GROUNDWATER MOVEMENT, MASSACHUSET
GROUMDWATER RELATIONSHIPS, MALENC
GROUMDWATER, WATFR QUALITY, SOIL
GROUNDWATER MOVEMENT, MASSACHUSET
GROUMDWATER RELATIONSHIPS, GROUND
WATER DUALITY, INSPE
MOVEMENT, DAMAGES, LE
WISCONSIN, WATER SUP
MOVEMENT, INFILTRATIO
GROUNDWATER MOVEMENT, HYDRAULICS,
GROUNDWATER, PLANNING, MANAGEMENT
GROUNDWATER, SEPTIC TANKS, MANAGE
GROUNDWATER, HYDRAULIC CONDUCTIVI
GROUNDWATER MOVEMENT, LEACHING, I
GROUNDWATER, GROUNDWATER MOVEMENT
GROUNDWATER BARRIERS, INFILTRATIO
GROUNDWATER, DISSOLVED SOLIDS, LE
WATER QUALITY, COMPA
EVAPORATION, IMFILTR
SOIL WATER, SOLURILI
MOVEMENT, OIL-WATER I
MOVEMENT, SEEPAGE, PO
MOVEMENT, LIMESTONES,
MOVEMENT, PERCOLATION
GARBAGE DUMPS, LANDF
SURFACE WATERS, TEST
GROUNDWATER, AMMONIA, PRECIPITATI
HAARLEM, LEYDEN, THE HAGUE, MINER
HAGAN-POISEUILLE FLOW, CLOGGING.:
HAGUE, MINERALIZATION, CLAY LENSE
HARDNESS(WATER), ACIDITY, OXYGEN,
HAWAII .: /ROORGANISMS, FERROBACIL
HAWA I I ) . :
HAWAII ), MAUI(HAWAII ).:
HEAD LOSS, DARCYS LAW, TIME LAG,
HEALTH, #SOIL LEACHING, GROUNDWAT
HEALTH, #WELL REGULATIONS, *WATER
DOMESTIC WATER, INDUSTRIA
ENVIRONMENTAL SANITATION,
HEALTH, OIL WELLS, DRILLING, OIL
HIGH PLAINS*TEXAS), PARMER COUNTY
HIGHWAY ICE REMOVAL.:
HISTORY, SOIL ANALYSIS, WATER TRA
HOGS, NITROGEN, NITRATE, PHOSPHOR
GROUNDWATER,
GROUNDWATER,
GROUMDWATER,
GROUNDWATER
GROUMDWATER
GROUMDWATER
GROUMDWATER
GROUNDWATER,
GROUNDWATER,
HEALTH,
HEALTH,
W71-
W71-
W 71 -
W71-
W71-
W71-
W71-
W71-
W70-
W71-
W71-
W70-
W71-
W71-
W70-
W71-
W71-
W71-
VJ11 -
VII l-
W71-
W71-
W71-
W/l-
W71-
W71-
W71-
W7]-
W71-
W71-
W"/1-
W71-
W71-
W71-
W71-
W 71-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W69-
W69-
W69-
W69-
W69-
W71-
W71-
W70-
W69-
W71-
W70-
W70-
W71-
W71-
W70-
W71-
W71-
11255
12084
12410
13645
11692
13521
01043
01043
09637
01028
02909
10058
03543
03542
09844
03230
0] 205
00194
04548
01324
02909
04742
03230
06443
04882
05094
09936
10372
08218
08044
08044
08055
06063
08907
07118
07887
08055
09611
09154
07194
05094
06514
06435
07838
00979
07838
07838
00979
08044
08044
07766
09721
^4742
02896
06011
01028
12122
09844
12122
03542
130
-------
H RED, SPOK/ DRAIN FIELDS, #TEST
ACES, MIXING, PENETRATION, PRILL
S, *GROUNDWATER, ^SEEPAGE, PRILL
VTRHNMENTAL PULLUT ION.: TEST
NS(TEXAS),
IL. :
T, C.O.D.,
N SOURCES,
FARMER COUNTY(TEXAS)
B.O.D. , WASTE HATERS,
INFILTRATION, WASTES,
HEMATICAL MODELS, MODEL STUDIES,
CHING, FARM WASTFS, GROUNDWATER,
NOHATER RECHARGE, MODEL STUDIES,
ATER MOVEMENT, DRAINAGE SYSTEMS,
ILTRATIQN, GROUNDWATER MOVEMENT,
PERINEA METERS, SANDS, CHLORINATED
^DAMAGES (LEGAL ASPECTS ) ,
RESPONSE MODEL , INSTRUMENT/AT I ON ,
SILICATE, GROUND WATER RECHARGE,
RUNOFF, GROUNDWATER, CELLULOSE,
INS, WATER SUPPLY, MUD, BENTHOS,
R I GAT ION, -SPRINKLER IRRIGATION,
ON, PERCOLATING WATER, AQUIFERS,
WAGE TREATMENT, SEWAGE DISPOSAL,
OLOGIC DATA, GEOLOGY, HYDROLOGY,
ARGE, SAFE YIELD, WATER BALANCE,
HASTES, -LEACHING, #G ROUND WATER,
TRATIOM, -NEW YORK, HYDROGRAPHS ,
INDUCED INFILTRATION, #NEW YORK,
YDROGEOLOGY, GROUNDWATER BASINS,
HYDRO GEOLOGY, DATA COLLECTIONS,
LOGIC INVESTIGATIONS, ^ILLINOIS,
'-IRRIGATION RETURN FLOW,
ULP AND PAPER INDUSTRY, DAMAGES,
-LANDFILL
DURBAN
, LANDFILLS,
TA, GEOLOGY,
HIGHWAY
DF, ^HI^HWAY
R, POLLUTION
, *POLLUTIO\
S , POLLUTANT
NORTHEASTERN
NIVERSITY OF
R POLLUTION,
ION EFFECTS,
-WATER WELL,
SANITARY ENGINEERING
INPIS, HYOROLOGIC DA
ECTS, #SODIUM CHLORI
CE, PERCOLATING WATE
*NITROGEN COMPOUNDS
EXCHANGE , POLLUTANT
.
TtrST HOLES, U
ATER INTRUSION, WATE
NDARDS, WATER POLLUT
SOURCES, ^DAMAGES,
TE DISPOSAL, LEGISLATION
, PERCOLATION, WATER MAN
MOVEMENT, OIL-'-'ATFR INT
, COMPRESSIBILITY, SOLID
FILTRATION, CLIMATIC CON
FARM WASTES, AEROBIC CON
R OUALITY, ^MATHEMATICAL
ATION, *WASTE WATER RECL
AT ION, *WASTE WATER RECL
OLLUTANTS, SEEPAGE, PENE
, PUBLIC HEALTH, DOMESTI
WASTES, WATER POLLUTION
AIRED WATER DUALITY, POL
, WELLS,
AGEMENT,
ERFACES,
WASTES,
DITIONS,
DITIONS,
MODELS,
AMATION ,
AMATION,
TRAT I ON,
C WATER,
SOURCES,
LUTANTS,
HYDRAULIC
HYDRAULIC
HYDRAULIC
HYDRAULIC
HYDROGEOLOGY,
HYDROGEOLOGY,
HYDROGEOLOGY,
HYDROGEOLOGY,
HOLES, ANNUAL PRECIPITATION, LEAC
HOLES, GROUNDWATFR MOVEMENT, DAMA
HOLES, OILY WATER, GROUNDWATER MO
MOLES, UNIVERSITY OF ILLINOIS, EN
HOLLY SUGAR STUDIES.: / HIGH PLAI
HOMOGENEOUS MEDIA, UNSATURATED SO
HYDRAULIC LOADING, INFILTRATION,
CONDUCTIVITY, SUBSURFAC
MODELS, TRACERS, INJECT
CONDUCTIVITY.: /ES, LEA
MODELS, OIL WASTES, WAT
HYDRAULIC MODELS, MATHEMATICAL MO
HYDRAULICS, SURFACE RUNOFF, STREA
HYDROCARBON PESTICIDES, INSECT 1C I
HYDROCARBON POLLUTION.:
HYDROCHEMICAL D: /BASIN, PRUCESS-
HYHROCHEMICAL FACIES, SEWAGE EFFL'
HYDROCHLORIC ACID.:
HYDROGEN IOM CONCENTRATION, TOXIC
HYDROGEN, BACTERIA, AEROBIC BACTE
HYDROGEOLOGY, SOILS, POROSITY, PE
GROUNDWATER BASINS,
GROUNDWATER MOVEMEN
INFILTRATION, PERME
DATA COLLECTIONS, H
HYDROGEOLOGY, WATER POLLUTION SOU
HYDROGRAPH ANALYSIS, STATISTICAL
HYDROGRAPHS, HYDROGRAPH ANALYSIS,
HYDROLOGIC CYCLE, OVERDRAFT, WELL
HYDROLOGIC DATA, GROUNDWATER MOVE
HYDROLOGIC DATA, GEOLOGY, HYDROLO
HYDROLOGIC-OJALITY MODEL.:
HYOROLOGIC DATA, LEGISLATION, LAN
HYDROLOGY.:
HYDROLOGY.:
HYDROLOGY, WATER POLLUTION, PATH
HYDROLOGY, HYDROGEOLOGY, IMFILTRA
ICE REMOVAL.:
ICING, #SNOW REMOVAL, *MAINE, DEI
IDENTIFICATION, SOIL WATER, SALIN
IDENTIFICATION, *WATER OUALITY, *
IDENTIFICATION, ADSORPTION, WATER
ILLINOIS.:
ILL INOIS, ENVIRONMENTAL
WATER OUALITY,
OUALITY,
OUALITY,
OUALITY,
IMPAIRED WATER OUALITY, WASTE DIS
IMPERVIOUS SOILS, GROUNDWATER BAR
INCINERATION, PERCOLATION, SEEPAG
INCINERATION, AIR POLLUTION, TEMP
INCUBATION.: /E, SURFACE RUNOFF,
INDUCED INFILTRATION, RECHARGE, *
INDUCED INFILTRATION, #GROUND WAT
INDUCED INFILTRATION, AGROUND WAT
INDUSTRIAL WASTES, SEWAGE, WASTE
INDUSTRIAL WATE: / EMINENT DOMAIN
INDUSTRIAL WASTES, RIVERS, STREAM
INDUSTRIAL WASTES, GROUNDWATER, W
IMPAIRED
IMPAIRED
IMPAIRED
IMPAIRED
WATER
WATER
WATER
POLLUT ION
POLLUTANT
PERCOLATI
UNDER SEE
WATER POL
W69-
W71-
W71-
W70-
W71-
W69-
W69-
W 70-
W69-
W ' 1 -
W71-
W71-
W71-
W70-
W68-
W69-
W69-
W71-
W68-
W69-
W 6 9-
W70-
M70-
W70-
W70-
W71-
W70-
W70-
W70-
W70-
W70-
W71-
W 7 1 -
W 71 -
W71-
W71-
W70-
W70-
W70-
W71-
H 71-
W69-
W70-
W70-
w/o-
W70-
W 7 1 -
H71-
W71-
W71-
W71-
W71-
W69-
W69-
W69-
W69-
H70-
W"/0-
W69-
W70-
01076
03230
08055
06322
12122
02681
03197
07766
07554
08218
10325
01932
05094
01904
00627
03197
03197
00194
01269
07838
07375
00532
04712
06322
05466
07194
03102
03102
00532
05466
06322
09936
11692
08907
05094
08907
06322
09844
09844
06063
12122
02611
09637
06322
08026
08025
13645
11724
07194
08055
08907
07118
09721
02611
05327
05328
00521
02896
05370
08026
131
-------
DOMESTIC WASTES, RENTHIC FAUNA,
LIVESTOCK, SEWAGE, INFILTRATION,
R POLLUTION SOURCES, MINERALOGY,
UNDER SEEPAGE, WATER POLLUTION,
OURCES, #WATER WELLS, '-REMEDIES,
NTS, WOOD WASTES, PULP AND PAPER
RNMENTS, STATE JURISDICTION, OIL
ATFMENT, PATH OF POLLUTANTS, OIL
TER INTRUSION, *HATER WELLS, OIL
LS, GROUMDWATER, OILY WATER, OIL
GE, JUDICIAL DECISIONS, OIL, OIL
IONS, OIL, SEEPAGE, DAMAGES, OIL
SHIPS, *WATER POLLUTION SOURCES,
RFACE-GROUNDWATER RELATIONSHIPS,
RBON DIOXIDE, METHANE, BARRIERS,
REUSE, ^CALIFORNIA, WATER YIELD,
UNDWATER, WATER SUPPLY, SEEPAGE,
EOLOGY, HYDROLOGY, HYDRHGEOLOGY,
ATER REUSE, -TERTIARY TREATMENT,
CTIVE USE, -STREAMFLOW, ^INDUCED
AL HASTES, SPRINKLER IRRIGATION,
OTTAWA SAND, ALDRIN
MOVEMENT, GROUNOWATER MOVEMENT,
R MOVEMENT, SOIL WATER MOVEMENT,
MSECTICIDES, PESTICIDE RESIDUES,
ATER MOVEMENT, *WATER POLLUTION,
COL AT ION, GROUND WATER MOVEMENT,
RECHARGE, FILTRATION, SORPTION,
WASTE WATER RECLAMATION, INDUCED
WASTE HATER RECLAMATION, INDUCED
Y, ^MATHEMATICAL MODELS, INDUCED
, LANDFILL MANAGEMENT, LEACHATE,
UALITY CONTROL, DOMESTIC WASTES,
WASTE WATERS, HYDRAULIC LOADING,
ES, SULFIDES, PERCOLATING WATER,
NTS, NITROGE/ PERCOLATING WATER,
), FALMOUTH(MASS). :
/ *PATH OF POLLUTANTS, -INDUCED
KENTAL EFFECTS, WATER CHEMISTRY,
OBSERVATION WELLS, WATER TABLE,
S, ^GROUNDWATER MOVEMENT, KARST,
WASTES, ^SEPARATION TECHNIQUES,
) , FALMOUTH('MASS) . :
-ARTIFICIAL RECHARGE, ^INDUCED
, INDUSTRIAL WASTES, POLLUTANTS,
ROUNDWATER MOVEMENT, LIMESTONES,
STRUCTION, GROUNDWATER MOVEMENT,
OUS SOILS, GROUNDWATER BARRIERS,
IOUFS, BIOASSAY, SOIL STRUCTURE,
WATER SUPPLY, LIVESTOCK, SEWAGE,
ODORS, GROUNDWATEP, EVAPORATION,
GRHUNOWATER MOVEMENT, LEACHING,
IP I TAT ION(ATMOSPHERIC), SEEPAGE,
LS, ARTESIAN WELLS, WATER WELLS,
R MOVEMENT, #PATH OF POLLUTANTS,
DIES, HYDRAULIC MODELS, TRACERS,
E.: TRESPASS,
ORINATED HYDROCARBON PESTICIDES,
ION, GROUNDWATER, WATER DUALITY,
INDUSTRIAL WASTES, DRAINAGE, AOUI
INDUSTRIAL WASTES, ALGAE, PONDS,
WASTES,
INDUSTRIAL
INDUSTRIAL
MUNICIPAL WAST
POLLUTANTS, IN
WATER POLLUTIO
INDUSTRY,
INDUSTRY,
INDUSTRY,
INDUSTRY,
WASTES,
INDUSTRIAL WASTES,
INDUSTRY, DAMAGES, HYDROLOGIC DAT
INDUSTRY, SALINE WATER, SUBSURFAC
OIL, GASES, POLLUTANTS,
PUBLIC HEALTH, OIL WELL
WATER POLLUTION SOURCES
SUBSURFACE DRAINAGE, WA
INDUSTRY, STORAGE TANKS, SUBSURFA
INFILTRATION, WASTES, HYDRAULIC C
INFILTRATION, EVAPOTRANSPI RAT ION,
INFILTRATi: /ER SUPPLY, GASES, CA
INFILTRATION, WATER SPREADING, PI
WATER POLLUTION, PO
PERMEABILITY, SAMPL
FILTRATION, SEWAGE
*NEW YORK, HYDROGRA
GROUNDWATER, WATER
INFILTRATION,
INFILTRATION,
INFILTRATION,
INFILTRATION,
INFILTRATION,
INFILTRATION.:
INFILTRATION,
INFILTRATION,
INFILTRATION.:
INFILTRATION,
INFILTRATION,
INFILTRATION,
INFILTRATION,
INFILTRATION,
WATER CHEMISTRY, WA
PERCOLATION, ADSORP
/BON PESTICIDES, I
ANALYTICAL TECHNIOU
PATH OF POLLUTANTS,
PERCOLATION, SOIL D
*GROUND WATER RECHA
AGROUND WATER RECHA
INFILTRATION, RECHARGE, ^SURFACE-
INFILTRATION CAPACITY, GROUNDWATE
INFILTRATION, AOUIFORS, SANITARY
INFILTRATION', TUCSON BASIN, PROCE
INFILTRATION, GROUNDWATER MOVEMEN
INFILTRATION, DETERGENTS, POLLUTA
INFILTRATION PONDS, CAPE CODtMASS
INFILTRATION, COLIFORMS, ALLUVIAL
INFILTRATION.: /ER TABLE, ENVIRON
INFILTRATION.: /IL CONTAMINATION,
INFILTRATION, ION TRANSPORT, PENN
INFILTRATION, MODEL STUDIES, MATH
INFILTRATION PONDS, CAPE CODCMASS
INFILTRATION, #PIT RECHARGE, *WAT
GROUNDWATER MOVEMEN
DOMESTIC WASTES, BE
NAVIGATION, SEEPAGE
OIL, OIL RESERVOIRS
SOIL PROPERTIES, LE
INDUSTRIAL WASTES,
CLIMATIC CONDITIONS
WATER QUALITY.: /R,
INFILTRATION, GROUNDWATER MOVEMEN
INFLOW, UNDERGROUND, GROUNDWATER,
INJECTION WELLS, WASTE DISPOSAL,
INJECTION WELLS, ARTIFICIAL RECHA
INJUNCTIONS(PROHIBITORY), NUISANC
INJUNCTION!PROHIBITORY).:
INSECTICIDES, PESTICIDE RESIDUES,
INSPECTION, INSTALLATION, WELL CA
INFILTRATION,
INFILTRATION,
INFILTRATION,
INFILTRATION,
INFILTRATION,
INFILTRATION,
INFILTRATION,
INFILTRATION,
W71
W71
W71
W71
W71
W71
W71
W71
W70-
W70-
W70-
W70-
W70-
W70-
W70-
W70-
W70-
W70-
W70-
W69-
W70-
W69-
W69-
W70-
W70-
W70-
W69-
W69-
W69-
W69-
W68-
W69-
W69-
W68-
W69-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
K< (I -
W71-
W71-
W71-
W71-
W71-
W71-
V! 71-
W70-
W69-
W69-
W69-
W71-
W70-
W71-
09154
06435
10446
13645
11692
11692
13521
11724
01028
08025
07632
07631
07766
06102
06011
05466
07632
06322
04712
03102
07114
01904
08620
07375
01904
01291
00521
08621
05327
05328
02611
00058
03178
03197
01010
00652
01324
02909
04121
03543
01204
01930
01 205
12410
13645
09154
04882
08055
06514
06435
07118
08044
05094
07632
03212
07554
06117
13645
01904
04742
132
-------
#SALINE
#SALINE
-SAL INE
SALINE
*SALINE
'.'ATER
WATER
WATER
VA T E R
WATER
WATER
-SOIL
ATER, WATER QUALITY, INSPECTION,
N BASIN, PROCESS-RESPONSE MODEL,
DWATER, SALINE WATER-FRESH WATER
TER S/ '"SALINE WATTR-FRESH-WATER
E WATER, SALINE WATER-FPESHWATFR
GROUNDWATER MOVEMENT, OIL-WATER
UNDERGROUND, WELLS, SALINE WATER
CTS, '"RETURN FLOW,
'"WATER POLLUTION,
!_S/ '"PENNSYLVANIA,
ATHFMATICAL MODELS,
, WATER / -KANSAS,
ATH OF POLLUTANTS, -SALINE
, '"ON-SITE INVESTIGATIONS,
ATER POLLUTION EFFECTS, -ON-SITE
'"SOIL INVESTIGATIONS, '"GEOLOGIC
&ROUNDWATER, CELLULOSE, HYDROGEN
R WELLS, WATER SUPPLY, AQUIFERS,
R MOVEMENT, KARST, INFILTRATION,
ED FLOW, ADSORPTION, ADSORPT ION,
, RADIATION, RADIOACTIVE WASTES,
, PLANTS, ALFALFA, CEREAL CROPS,
INITY, FERTILIZERS, GROUNDWATER ,
TRATION, AGROUND HATER RECHARGE,
TRATION, -GROUND WATER RECHARGE,
ATER MOVEMENT, MUNICIPAL WASTES,
ISPPSAL , -IRRIGATION, '"SPRINKLER
ION, '"CHEMICAL WASTES, SPRINKLER
, SOIL ANALYSIS, WATER TRANSFER,
, WATER TABLE, OXIDATION LAGOON,
ALINE WATER, WATER CONSERVATION,
#SALT WATER
SALINE WATER INTRUSION, '"HAWAII,
AS, FERTILIZERS, DRAINAGE WATER,
ATER, DWELLS, GROUNDWATE/ '"RHODE
N, '"PERCOLATING WATER, R/ '"RHODE
SAN
, SPRINGE I/ DURBAN STORM RUNOFF,
T, LEASES, DAMAGES, LAND TENURE,
LATING WATER, SUBSURFACE WATERS,
N EFFECTS, STREAMS, GROUNDWATER,
STIC WATER, POLLUTION ABATEMENT,
TES, '"REMEDIES, WATER PHI LUTION,
CONTROL, DAMAGES, LEGAL ASPECTS,
IATION, WATER POLLUTION SOURCES,
ERFLOW, ARTESIAN WELLS, STREAMS,
OLLUTION PFFECTS, LEGAL ASPECTS,
ATER, -UNDERSEEPAGE, '"POLLUTION,
ILY WATER, '"PIPELINES, '"LEAKAGE,
ILLINOIS, '"SALINE W*TFR, DWELLS,
OLINE, DWATER POLLUTION SOURCES,
'/ELLS, WATER POLLUTION, DAMAGE,
SPECTS, STATE GOVERNMENTS, STATE
GE DUMPS, -GROUNDWATER MOVEMENT,
IAL DRIFT, AQUIFERS, OHIO RIVER,
OVAKIA).: -HYDRAULICS
ONES, SEEPAGE, NUMERICAL METHOD,
*ALDRIN, '"GROUNDWATER MOVEMENT,
NDWATER MOVEMENT, MODEL STUDIES,
ITY, HEAD LOSS, DARCYS LAW, TIXF
INSTALLATION
INSTRUMENTAT
INTERFACES,
INTERFACES,
INTERFACES,
INTERFACES,
INTRUSION, W
INTRUSION,
INTRUSION,
INTRUSION,
, WE
ION,
MIXI
LL CA
HYDR
NG, P
-LEACHING
SINGS,
OCH EM I
ENETRA
WELL
IMPE
ATER
H AWA
WATE
OIL
, *SAL
LL CAS
S SOIL
UTION
RRIGAT
R WELLS, OI
WELLS *WAT
S, WE
RVIOU
POLL
IT I
ARTES
CAL D:
TION,
IHE WA
INGS,
S, GRO
SOURCE
ION WA
L INDU
ER WEL
TON
ION
INTRUSION, AQUIFERS, POROUS MEDIA
I NT RU S I ON , '"OIL W A S T E S , -R EM ED I E S
INTRUSION, WATER POLLUTION, IMPAI
INVESTIGATIONS, '"GEOLOGIC INVESTI
INVESTIGATIONS, '"SOIL INVESTIGATI
INVESTIGATIONS, '"ILLINOIS, HYDROL
ION CONCENTRATION, TOXICITY.: /,
EXCHANGE, POLLUTANTS, POLLUTA
TRANSPORT, PENNSYLVANIA, SUPS
ION TRANSPORT.: /ED FLOW, SATURAT
IONS, EQUATIONS, MATHEMATICAL MOD
IRRIGATED LAND, COLORADO, GROUNDW
IRRIGATION EFFECTS, LEACHING, DEN
IRRIGATION, DENITRIFICATION, ECON
IRRIGATION, DENITRIFICATION, EC ON
IRRIGATION WATER, ARTIFICIAL RECH
IRRIGATION, HYDROGEOLOGY, SOILS,
IRRIGATION, INFILTRATION, GROUNDW
IRRIGATION PRACTICES, LEACHING, T
IRRIGATION, AERATION, BIOCHEMICAL
IRRIGATION PRACTICES.: / WATER, S
IRRIGATION, SALT TRANSPORT.:
IRRIGATION WATER, WATER CHEMISTRY
IRRIGATION, RETURN FLOW, WATER SU
ISLAND, '"GASOLINE, '"PERCOLATING W
ISLAND, '"SEEPAGE, '"WATER POLLUTIO
JACINTO VALLEY(CALIF).:
JAMES RIVER(MO), WILSON CREEK(MO)
JUDICIAL DECISIONS, LEGISLATION,
DECISIONS,
DECISIONS,
DECISIONS,
DECISIONS,
DECISIONS,
DECISIONS,
DECISIONS,
DECISIONS,
DECISIONS,
DECISIONS,
DECISIONS,
DECISIONS,
JUDICIAL DECISIONS, GROUND WATER,
JURISDICTION, OTL INDUSTRY, SALIN
KARST, INFILTRATION, ION TRANSPOR
KENTUCKY.: /HING, CHLORIDES, GLAC
LABORATORY OF BRATISLAVA{CZECHOSL
TESTS, PERMEABILITY, P
TESTS, PERMEAMETERS, S
JUDICIAL
JUDICIAL
JUDICIAL
JUDICIAL
JUDICIAL
JUDICIAL
JUDICIAL
JUDICIAL
JUDICIAL
JUDICIAL
JUDICIAL
JUDICIAL
LEGAL ASPECTS
LEGAL ASPECTS
LEGAL ASPECTS
RELATIVE RIGH
GROUN: /TION
LEGAL ASPECTS
POLLUTION ABA
GROUNDWATER K
OIL, SEEPAGE,
OIL, OIL INDU
OIL WASTES, W
FUELS, WELLS,
LABORATORY
LABORATORY
LABORATORY TESTS, PATH OF POLLUTA
LAG, NITROGEN COMPOUNDS, NITRATES
W 71-
W69-03197
W71-03230
W71-01932
W71-01028
W71-08055
W 71
W 7 1
W 7 1
W71
W71
W 7 1
W 7 0
V'70
W70
H70
W68-
W69
W71
W70-
W71
W70
W70
W69
W69
W69
W69
W69
W71
W71-
W 7 1
W71-
W71
W 71
W 7 0
W71
W 7 0
W71
W71
W 7 1
W 7 1
W71
W71
W71
W 7 0
W 7 0
V70
W 7 0
W70
W69
W69
W68
W71
W 71
W 7 1
W71
W69
W70
W 7 0
W70
08044
01028
03230
04559
13521
08026
06322
06322
06322
01269
02611
01204
10058
11356
04488
08662
05327
05328
08621
07375
07114
12122
03542
06063
06063
08044
06435
08025
01043
05466
09154
08055
01028
01043
13645
13521
11724
08050
08025
08026
07631
07632
06118
06117
00627
13521
01204
00194
01930
00651
01904
09548
07766
133
-------
DILUTION, HATER TABLE* OXIDATION
UDGE DIGESTION, ANAE/ ^OXIDATION
YAKIMA BASIN(PACIFIC NORTHWEST),
ULATE F/ ^AGRICULTURAL DRAIVAGF,
ALS, / ^KILLING, ANIMAL MANURES,
USTRIAL WASTES, RIVERS? STREAMS,
TTED FLOORS, AERATOR, SPREADING,
EVEL FLUCTUATIONS, SALINE SOILS,
LING EQUIPMENT, LEASES, DAMAGES,
S, HYDROLOGIC DATA, LEGISLATION,
ALFALFA, CEREAL CROPS, IRRIGATED
OLIGOTR/ -LAKES, STREAMS, FISH,
CISIONS, LEGAL ASPECTS, RIPARIAN
STATE COLLEGE!PENN ), SANITARY
TURATED FLOW, ^MOISTURE ROUTING,
^GROUNDWATER POLLUTION,
SIMULATED
T, SEWERS, AERATION, MONITORING,
ERS, GROUNDWATER, GARBAGE DUMPS,
THTDOLOGY, SANITARY ENGINEERING,
LE USE, ARTIFICIAL USE, RIPARIAN
ATFRIALS, BIBLIOGRAPHIES, DARCYS
G WATER, -RELATIVE RIGHTS, '-'ATER
RPTION, WATER CHEMISTRY, DARCY'S
RANSMISSIVITY, HEAD LHSS, DARCYS
SUBSURFACE FLDH, GASOLINF, HATER
EST HOLES, ANNUAL PRECIPITATION,
RE ROUTING, LANDFILL MANAGEMENT,
CE HATERS, AOUIFERS, FLOW RATES,
ITIATED HATER(TRACER), MINE DUMP
TRANSFER, IRRIGATION PRACTICES,
, NITRIFICATION, A M v. ON I F IC A T I ON ,
RATES, #MATER POLLUTION SOURCES,
RUMOFF, BASF FLOW, PERCOLATION,
ATEO SOILS, -IRRIGATION EFFECTS,
, INFILTRATION, SOIL PRO PERTIES,
OUNDWATER, GROUND'-'A T ER ^nVE^FNT,
, GROUNDWATER, DISSOLVED SOLIDS,
AVES, PATH OF POLLUTANTS, ACIDS,
FORNIA, WATER POLLUTIHN SOURCES,
EQUATIONS, GROUNDWATER MOVEMENT,
ATER POLLUTION CONTROL, SURVEYS,
GROUNQi'iATFK, IRRIGATION EFFFCTS,
CHEMCONTRC1L , SALTS , GROUNDWATER,
PERCOLATING WATER, PERCOLATION,
GY, -ILLINOIS, MUNICIPAL HASTES,
LUTIDN, WATER POLLUTION CONTROL,
INS, ^BIOCHEMICAL OXYGEN DEMAND,
NITROGEN, ^PUBLIC HEALTH, #SDIL
SUBSURFACE WATERS, UNDERGROUND,
RESERVOIRS, DRILL ING EQUIPMENT,
CY, AOUIFEKS, PERCOLATING HATER,
FACE WATERS, JUDICIAL DECISION'S,
, GRPUNDWATER MOVEMENT, DAMAGES,
GROUNDWATER, JUDICIAL DECISIONS,
JUniciAL DECISIONS, LEGISLATION,
ATER POLLUTION CONTROL, DAMAGES,
M ABATEMENT, JUDICIAL DECISIONS,
DATA, LEGISLATION, LAND TENURE,
CIAL DECISIONS, RELATIVE RIGHTS,
LAND
LAND
LAND
LAW,
LAW,
LAGOON, IRRIGATION, AERATION, BIO
LAGOONS, ^TERTIARY TREATMENT, *SL
LAKE MENDOTA(WIS).: /VER(CALIF),
LAKE METABOLISM, MOBILITY, PARTIC
LAKE MINNETONKA(MINN), SOIL MINER
LAKES, PONDS, TIDAL WATERS, WELLS
LAND DISPOSAL.: MTION DITCH, SLO
RECLAMATION, PATH OF POLLUTA
TENURE, JUDICIAL DECISIONS,
TENURE, LEGAL ASPEC: /DAMAGE
LAND, COLORADO, GROUNDWATER, PERC
LA\'D, ECOSYSTEMS, EUTROPHI CAT ION ,
LAND, PERCHLATION, SUBSURFACE WAT
LANDFILL DRAINAGE.:
LANDFILL MANAGEMENT, LEACHATE, IN
LANDFILL POLLUTION EFFECTS,:
LANDFILL. :
LANDFILLS, BIOCHEMICAL OXYG: /MEN
LANDFILLS, WASTE DUMPS, WATER POL
LANDFILLS, HYDROLOGY, WATER POLLU
LANDS, GROUMDWATER, PERCOLATING W
LAW.: /BILITY, POROSITY, POROUS M
LAW, GROUND WATER, SUBSURFACE WAT
PERMEABILITY, DRIVER FLOW.: /
TIME LAG, NITROGEN COMPOUNDS
LAW, WELLS, GROUND WATER MOVEMENT
LEACH BED, SPOKANE RIVER VALLEY.:
INFILTRATION CAPACITY,
/E, GROUNDWATER, SURFA
TR
TEXAS.: /NALYSIS, WATER
PROS ION, NITROGEN, RUNO
FARM WASTES, GROUNDWATE
DRAINAGE, FARM WASTES,
''ATER LEVEL FLUCTUATION
PATH OF POLLUTANTS.: /E
INFILTRATION, WATER QUA
SALT BALANCE, PERCOLATI
CHLORIDES, GLACIAL DRIF
DRAINAGE WATER, AMMONIA
MATHEMATICAL MODELS, MI
GEOLOGY, GROUNDWATER MO
DEMITRIFICATION, RIVER
SALINE SOILS, SALINE HA
AQUIFERS, WATER TABLE,
GROUNDWATER MOVEMENT, E
WATER QUALITY CONTROL,
RUNOFF, GROUNDWATER, CE
LEACHING, GROUNDWATER, SOIL PROFI
LEAKAGE, PERCOLATION, WATER RIGHT
LEASFS, DAMAGES, LAND TENURE, JUD
LEG: /ENS, EXCAVATION, WATER POL I
LEGAL ASPECTS, ADJUDICATION PROCE
COMPENSATION, BRIN
RIPARIAN LAND, PER
/S, LAND TENURE,
JUDICIAL DECISIONS
LEACHATE,
LEACHING.
LEACHING.
LEACHING,
LEACHING,
LEACHING,
LEACHING,
LEACHING,
LEACHING,
LEACHING,
LEACHING,
LEACHING,
LEACHING,
LEACHING,
LEACHING,
LEACHING,
LEACHING,
LEACHING,
LFACHING,
LEACHING,
LEACHING,
W71
W71-
W70-
W71-
W70
W69
W71
W71
W 1 1
W 7 1
W70
W70
VI 7 1
W71
W68
W 7 1
W70-
W71-
W71-
W71-
W70-
W69-
H70-
W69-
V70-
W68-
W69-
W68-
W70-
W71-
W 71-
W71-
V! 71-
W71-
W71-
W71-
W7]-
W71-
W71-
W71-
W70-
H70-
W70-
W70-
W7Q-
W70-
LFGAL
LEGAL
LEGAL
LEGAL
LEGAL
ASPECTS,
ASPECTS,
ASPECTS.
ASPECTS,
ASPECTS, REMEDIES, WELLS, D
LEGAL ASPEC: /DAMAGES, HYDROLOGIC
LEGAL ASPECTS, STATE GOVERNMENTS,
W68
W69
W 70
W71
W 71
W71
W71
W71
W71
W71
W71
W71
W71
Q3542
07118
04504
06443
04193
05370
03542
08073
08055
11692
04488
04193
01043
01204
00058
07194
09548
09154
05094
08907
02896
00651
00521
02611
07766
00627
01076
00058
09637
11255
12122
10372
08218
06443
'08073
06514
08044
06063
00194
04548
10058
07193
08662
09844
06011
06572
03178
01269
Q9721
07631
08055
04742
01028
03230
01043
08055
11724
13645
11692
13521
134
-------
ON, WATER POLLUTI
ION SOURCES, JUDI
DWATER, WATER POL
AL WASTES, -ARTIF
SEWAGE, WASTE MA
COMPETING USES,
HALLOW WELLS, SUB
EFFECTS, SEEPAGE,
TION. :
ATMENT, ADMINISTRATIVE AG
LAND TENURE, JUDICIAL DEC
OLATION, WASTES, WASTE DI
USTRY, DAMAGES, HYDROLOGI
ER POLLUTION, #OIL WASTES
ON, POLL
CIAL DEC
LUTION E
ICIAL RE
TER { POLL
DOMESTIC
SURFACE
WASTE S
UTANTS,
ISIONS,
FFECTS,
CHARGE,
UT ION ),
WATERi
WATERS,
TORAGE,
DAMAGES(
ENCIES,
ISIONS,
SPOSAL,
C DATA,
, -OIL,
GOVERNMENTS, LOCAL GOVE
THE HAGUE, MINERALIZATI
IGATION EFFECTS, LEACHIN
RECHARGE, TRANSM I SS I V I T
NSHIPS, OBSERVATION WELL
INFILTRATION, GROUMDWATE
R MOVEMENT, WATER QUALIT
S FORMAT IONS, AMSTERDAM,
SS, NEGLIGENCE, NUISANCE
CE RUNOFF, GROUNDWATER M
RNMENTS ,
ON, CLAY
G, WATER
WATER
WATER
WATER
Y, WATER
HAARLEM,
, STRICT
OVEMENT,
Y ,
S,
R,
TION, RETURN FLOW, WATER SUPPLY,
HEMICAL OXYGEN DEMAND, SUSPENDED
E WATERS, PERCOLATION, SUSPENDED
SPOSAL/ SEWAGE DISPOSAL, ORGANIC
B.O.D., WASTE WATERS, HYDRAULIC
ON ABATEMENT, STATE GOVERNMENTS,
E DRAINAGE, TRANSM ISS IV ITY , HEAD
ATER REUSE, ARTIFICIAL RECHARGE,
UALITY, WATER POLLUTION SOURCES,
R FACE- GROUNDWATER RELATIONSHIPS,
RAMS, SUBSURFACE DRAINAGE, WATER
TROL, GROUNDWATER* SEPTIC TANKS,
ING, DRAINAGE, FARM WASTES, SOIL
MULATION, GROUND HATER, PL ANN ING,
TER MOVEf-'ENT, PERCOLATION, '-'ATER
USE, ^STREAM FLOW, *INDU/ *'-'ATER
LOW, -MOISTURE ROUTING, LANDFILL
OIL MINERALS? / -KILLING, ANIMAL
MATICAL MODELS, CURRENTS ( WATER ),
OBABIL ITY, THERMODYNAMICS, FLOW,
PONDS, CAPE COD( MASS) , FALMOUTHt
PONDS, CAPE COD(MASS), FALMOUTHC
INFILTRATION PONDS, CAPE CODI
INFILTRATION PONDS, CAPE CODI
AQUIFERS, GROUNDWATER MOVEMENT,
AQUIFERS, GROUNDWATER MOVEMENT,
, PERMEABILITY, POROSITY, POROUS
UN I FORM FLOW, -'D I FFUS ION , POROUS
TES, WASTES, PATH OF POLLUTANTS,
GROUNDWATER MOVEMENT, LEACHING,
INAGE SYSTEMS, HYDRAULIC MODELS,
PUTER PROGRAMS, COMPUTER MODELS,
ES, INFILTRATION, KODEL STUDIES,
UTANTS, ^RETURN FLOW, -NITRATES,
LEGAL ASPECTS.
LFGAL ASPECTS,
ASPECTS,
ASPECTS,
ASPECTS.
ASPECTS,
ASPECTS.
ASPECTS.
LEGAL
LEGAL
LEGAL
LEGAL
LEGAL
LEGAL
LEGISLATION,
LEGISLATION,
LEGISLATION,
/PAGE, INFILTRATI WTO-
DEEP PERCOLATION.: W70-
JUnif.IAL DECISIONS WTO-
AESTHETICS, AOUIFE W69-
/DUSTRIAL WASTES, WTO-
MUNICIPAL WATER, R W70-
/FACE DRAINAGE, S VJ69-
/TCHESt DRAINAGE W69-
LEGAL ASPECTS), HYDROCARBON POLLU W68-
LFGISLATI: /, WATER POLLUTION TRE W71-
LEGISLATION, LEGAL ASPECTS.: /S, U71-
WELLS, IMPAIRED WATE W71-
LAND TENURE, LEGAL A WT1-
STATE GOVERNMENTS, P W69-
LEGISLATIOM, WATER RIGHTS, RIPARI V'TO-
LENSFS, RHINE RIVER, AMSTERDAM RH W69-
LEVEL FLUCTUATIONS, SALINE SOILS, W71-
LFVEL FLUCTUATIONS, AMMONIA, NEBR WTI-
LE VELS, #WATER WELLS, WATER SUPPL W69-
LEVELS, WATER QUALITY, RIOCHEMICA VI69-
LEVELS, WATER SUPPLY, HATER UTlLI W70-
LEYDEN, THE HAGUE, MINERALIZATION W69-
LIABILITY. : TRESPA K'70-
L IMESTONES, INFILTRATION, DOMESTI W71-
LITHUANIA(USSR).: W71-
L I VESTOCK, SEWAGE, INF I LTRATI UN, W71-
LOAD.: /VELS, WATER QUALITY, RIDC W69-
LOAD, GROUNDWATER, AQUIFER CHARAC W/0-
LOADING, #RIODEGRADATION, SOIL DI W68-
LOADING, INFILTRATION, TUCSON BAS W69-
LOCAL GOVERNMENTS, LEGISLATION, W W70-
LOMGITUDINAL DISPERSION.: W71-
LOSS, DARCYS LAW, TIME LAG, NITRQ H7Q-
LOW-FLOW AUGMENTATION.: /IFERS, W WTO-
LYSIMETERS.: /E DRAINAGE, WATER Q W71-
MALENCLAVES, PATH OF POLLUTANTS, W71-
MANAGEMENTt APPLIED).: /INAGE PROG W71-
MANAGEME^T.: /WATER POLLUTION CON W71-
MANAGEMENT, GROUNDWATER, WI SCON SI W71-
MANAGEMENT, PERCOLATION, *MOD EL S W71-
MANAGEMENT, IMPAIRED WATER QUALIT H73-
MANAGEMENKAPPLIED), ^CONJUNCT IVE WTO-
MAM AG EM EN T, LEACHATE, INF ILTRAT10 W68-
MANURES, LAKE MINNETONKA ( MINN) , S k'70-
HASS TRANSFER, AQUIFERS.: / MATHE W69-
MASS TRANSFER, DIFFUSION, MIXING, W71-
MASS).: INFILTRATION W71-
MASS).: INFILTRATION WT1-
MASS), FALMOUTH(MASS).: W71-
MASS)t FALMOUTH(MASS).: WT1-
MASSACHUSETTS.: / EUTROPHICAT I ON, WT1-
MASSACHUSETTS.: / EUTROPHICAT ION, WT1-
MATERIALS, BIBLIOGRAPHIES, DARCYS W69-
MATERIALS, * ENGINEERING MECHANICS W69-
MATHEMATICAL MODELS, CURRENTSfHAT W69-
MODELS, MIXING, RAD I WTO-
MODELS, AQUIFERS, MO W71-
MODELS, SALINE WATER W71-
EQUATIONS, PATH OF P W71-
W71-
MATHEMATICAL
MATHEMATICAL
MATHEMATICAL
MATHEMATICS,
0763?
08050
08026
08620
00521
00532
06117
06118
00627
MATHEMATICAL MODELS, COMPUTER PRO
08055
11724
11692
05370
02896
07838
08073
03543
02611
07114
05466
07838
00521
09154
07887
06435
07114
04504
01010
03197
02896
04559
07766
03102
01204
00194
01932
10372
06443
09936
07194
03102
OQ058
04193
OP921
11776
01205
01324
01205
01324
01324
0] 205
00651
01238
08921
10058
Q1932
04559
01930
04548
135
-------
GAL MODELS ,
DACTIVE WASTE
BE PAGE, POROU
AGRICULTURAL
ENTAL RECHARG
ENTAL RECHARG
N COMPOUNDS,
, POROUS MATERIALS
PATH OF
S, IONS,
S MEDIA,
WATERSHE
OA
E PROJEC
E PROJEC
NITRATES
POLLUTANTS,
EQUATIONS,
EOUATIONS,
DS, ORGANIC
HU{ HAWAII ) ,
T, FLUSHING
T, FLUSHING
, DISCHARGE
ENGINEERING
*POROUS
#POROUS
#POROUS
POROUS
SOIL CHEMISTRY, ABSORPTION, SOIL
CONVECTION, MIXING, FLOW, POROUS
ADIOISOT/ ^INFILTRATION,
TH OF POLLU/ -DIFFUSION,
*D I S P E RS I ON , ^DIFFUSION,
-STOCHASTIC PROCESSES,
ATER INTRUS ION, AOUIFERS
DWATER MOVEMENT, SEEPAGE, POROUS
ORM E/ -DISPERSION, FLOW, POROUS
HOMOGENEOUS
A RASINt PACIFIC NORTHWEST), LAKE
LIS, BACILLUS MYCOIDES, BACILLUS
GEN, BACTERIA, AEROBIC BACTERIA,
F/ -AGRICULTURAL DRAINAGE, LAKE
SOURCES, PIPES, CLOSED CONDUITS,
R SUPPLY, GASES, CARBON DIOXIDE,
^FINITE DIFFERENCE
RATION ZONES, SEEPAGE, NUMERICAL
EWAGE EFFLUENTS, B IODEGRA DAT I ON ,
ATERS, TESTING, TEST PROCEDURES,
AMPLING, DATA COLLECTION, WELLS,
TMENT, ^UNITED STATES, ^REVIEWS,
NUMERICAL
STATISTICAL MODELS, STATISTICAL
UTION SOURCES, ^HERBICIDES, #NEW
ANY, NETWORK ANALYS IS. : GREAT
EST SOILS, MINNESOTA, WISCONSIN,
SM, CANALS , SANDS , CHLOR IMAT ION ,
ASALTS, WATER POLLUTION SOURCES,
TRITIATED WATER { TRACE R ),
R POLLUTION, PATH OF POLLUTANTS,
LEACHING, #COPPER, *WASTE DUMPS,
SOLINE, HATER POLLUTION SOURCES,
DAM, HAARLEM, LEYDEN, THE HAGUE,
FACE WATERS, GEOLOGICAL SOURCFS,
RUSION, WATER POLLUTION SOURCES,
RES, LAKE MINNETONKAfMINN ) , SOIL
PPER, *WASTE DUMPS, MINE WASTES,
ANIMAL MANURES, LAKE MINNETONKA(
MINERALS, PLANT RESIDUES, MORRISt
EFFLUENTS, SWAMPS, FOREST SOILS,
^KILLING, ANIMAL MANURES, LAKE
R MOVEMENT, ^NUMERICAL ANALYSIS,
FLOW, MASS TRANSFER, DIFFUSION,
ARTIFICIAL RECHARGE, CONVECTION,
S, COMPUTER PROGRAMS, DIFFUSION,
ME HATER-FRESH WATER INTERFACES,
, LEACHING, MATHEMATICAL MODELS,
RS I ON , * I ON E XC HAMGE , D I F FUS ION ,
NAGE, DISSOLVED NUTRIENTS, WATER
), WILSON CREEMMO), SPRINGFIELD*
MATHEMATICAL MODELS, PROBABILITY,
MATHEMATICAL MODELS, CONVECTION,
MATHEMATICAL MODELS.: /OVEMENT, S
HATTER, SEDIMENTS, FERTILIZERS, W
-AUI (HAWAII ).:
MEADOWS PROJECT, PHOEMIX(ARIZQNA)
MEADOWS PROJECT, PHOENI X(ARIZOMA)
MEASUREMENT, DISCHARGE(HATER), ON
MECHANICS.: /OKM FLOW, ^DIFFUSION
MECHANICS, WATER QUALITY, SOIL PR
MEDIA.: /S, ARTIFICIAL RECHARGE,
MED I A, *A LL UVIUM, * LYS I METERS, #R
MFDIA, ^GROUNDWAT^R MOVEMENT, #PA
*GROUN DWATER MOVEMENT, *WA
^GROUNDWATER MOVEMENT, *ST
DIFF US I ON, C ONVECTI ON, D I F
EQUATIONS, MATHEMATICAL MO
GROUNDWATER, WASTES, *UNIF
MEDIA, UNSATURATED SOIL.:
MENDOTAfWIS) .: /VER(CALIF), YAKIM
MESENTERICUS, DIATOMEA, CLADOPHOR
METABOLISM, CANALS, SANDS, CHI. OR I
METABOLISM, MOBILITY, PARTICULATE
METAL PIPES, WELLS, ARTESIAN WELL
METHANE, BARRIERS,
METHOD.:
METHOD, LABORATORY
METHODOLOGY.: /NDS, DISPERSION, S
METHODOLOGY, WATER QUALITY, SOILS
CHEMICAL ANALYSIS.: /
SANITARY ENGINEERING
MEDIA,
MEDIA,
MEDIA,
MEDIA,
MEDIA,
METHODOLOGY,
METHODOLOGY,
METHODS.:
METHODS, WATER STORAGE, AOUIFERS,
MEXICO, *SOIL WATER MOVEMENT, GRO
MIAMI RIVER, S.W. OHIO WATER CQMP
MICHIGAN, PHOSPHORUS, AGRICULTURA
MICROORGANISMS, CHEMICAL ANALYSIS
MICROORGANISMS, FERRORAC ILLUS, FL
MINE DUMP LEACHING.:
MINE WASTES, GEOLOGY, GROUNDWATER
MINE WASTES, MIMING, GROUNDWATER
MINE WATER, OIL WASTES, CESSPOOLS
MINERALIZATION, CLAY LENSES, RHIN
MINERALIZATION, NITROGEN SOURCES,
MINERALOGY, INDUSTRIAL WASTES, MU
MINERALS, PLANT RESIDUES, MORRIS(
MINING, GROUNDWATER MOVEMENT, FLO
MINN), SOIL MINERALS, PLANT RESID
MINN), SOIL PERCOLATION.: / SOIL
MINNESOTA, WISCONSIN, MICHIGAN, P
MINNETONKA(MINN), SOIL MINERALS,
MIXING, COMPUTER PROGRAMS, COMPUT
DISPERSION.: /MODYNAMICS,
FLOW, POROUS MEDIA.: /S,
GROUNDWATER MOVEMENT, SEE
PENETRATION, DRILL HOLES,
RADIOACTIVE WASTE DISPOSA
RADIOACTIVITY, RADIATION,
MIXING, RUSSIAN RIVER(CALIF), YAK
MO), SEWAGE PLANT BYPASSES,: /(MO
MIXING,
MIXING,
MIX IMG,
MIXING,
MIXING,
MIXING,
W 7 1 -
W71-
W71-
W70-
'/'71-
W69-
W69-
W 70-
W69-
W71-
W69-
W69-
W69-
W69-
W 71-
INFILTRATI: /E
TESTS, PERMEAB !
VI 7 l-
W69-
W69-
W70-
W69-
V69-
W71-
W70-
W70-
W71-
W69-
W70-
W71-
W71-
W71-
W69-
W70-
W71-
W69-
W70-
W69-
W69-
W71-
W71-
W 7 1 -
W70-
W69-
W71-
W71-
W70-
W71-
W70-
N70-
W70-
W70-
W71-
W71-
W69-
W71-
W71-
W70-
Wll-
W70-
W 71-
11776
11356
09611
04193
08044
05327
05328
07766
01238
04121
07554
02681
03212
03237
11776
04559
09611
01233
02681
04504
07838
07838
06443
07632
06011
09611
00651
01291
06514
11255
08907
03237
03102
06514
02611
04193
07838
00979
11255
0*907
11255
08049
07838
06435
10446
04193
11255
04193
04193
04193
04193
04559
11776
07554
09611
03230
10058
1)356
04504
09154
136
-------
F, JAMES RIVH-MMn), WILSON CREEK(
*URRAN STORM RUNOFF, JAMES ^IVER
TURAL DRAINAGE* LAKE METABOLISM ,
LY !*'ATER, ^GROUNDWATER RFCH4RGF,
, MATHEMATICAL MODELS, AQUIFERS,
RATION TECHNIUUES, INF IL TRAT If.m ,
c ML AT ION, *GROUNH WATER MOVEMENT,
ISPERSIO-'I, -MATHEMATICAL MODELS,
TinN, SEEPAGE, UNSATURATED FLOW,
TE DISPOSAL, THERMAL PROPERTIES,
RETURN FLOW, HYOROL OG I C-nu Al_ ITY
TUCSON BASIN, P HOC ES S-R ES »ONS G
,
S
MEDIA
MATHEMATICAL
^STATISTICAL
MATHEMATICAL
MATHEMATICAL
MATHEMATICAL
MATHEMATICAL
EQUATIONS
* MOVEMENT
, HYDRAULIC MODELS
RN! FLOl- , ^NITRATES
S, IONS, EQUATIONS
PATH OF POLLUTANTS
H/ *WATER DUALITY, -^MATHEMATICAL
ING, COMPUTER PROGRAMS, COMPUTER
ENT, DRAINAGF SYSTEMS, HYDRAULIC
MOVEMENT, L FACHING, M/\ THEM.AT 1C AL
SI ON, -DISPERSION, ^MATHEMATICAL
CHARGE, MODEL STUDIES, HYDRAULIC
PATH OF POLLUTANTS, MATHEMATICAL
S, COMPUTER MODELS, MATHEMATICAL
HYDROGRAPH ANALYSIS, STATISTICAL
MODELS, -MODEL STUDIES, HYDRAULIC
!''ASTE STORAGE, SOIL PROPERTIES,
S, -CAPILLARY CONDUCT I V ITY, SOIL
GE, GROUNDWATER, -SEEPAGE, #SOIL
AGE TREATMENT, SEWERS, AERATW,
, SOIL MINERALS, PLANT RESIDUES,
CONTENT, POLLUTANTS, SOIL UATFR
'WATER, INFILTRATION, GRODNO VAT ER
, MATER LAW, WELLS,
, LEACHING, GEOLOGY
WATER RELATIONSHIPS
L INE WATER SYSTEMS,
RATION, DRILL HOL FS
FPAGE, INFILTRATION
LS, -GARBAGE DUMPS,
CA^'AL CONSTRUCTION
LYSIS, -DISPERSION,
-INDUSTRIAL WASTES , #GROU VD^'AT ER
, PATH OF POLLUTANTS, SOIL WATER
GROUND
GROUND
GROUMD
ATER
ATER
ATER
GROUMDk'ATER
GROUMDWATFR
GROUNDK'ATER
GROUNOMATER
GROUNO'-'ATER
GROUNOWATER
GROUNDWATER
UNDERGROUND STREAMS,
PHICATION', AQUIFERS,
PHICATIO'-1, AQUIFERS,
LLUTANTS, BLEACHING, *SOIL WATER
MULATIO/ *METHEMOGLOBIN, NITRATE
TS, -RADIOISOTOPES, -GROUNDWATER
DRA'-'AL, GROUND WATER, GROUNDWATER
MINE WASTES, MINING,
ICIDES, *NEW MEXICO,
, SUBSURFACE RUNOFF,
R POLLUTION SOURCES,
L HOLES, OILY WATER,
, DIFFUSION, MIXING,
GROUNDWATER
-SOIL WATER
GROUND'-'ATER
GROUNDWATER
GROUNOWATER
GROUNDWATER
MODEL
MOD PL
MODEL
MODEL
MODEL
MODEL
MODEL . :
MHDEL,
MODELS.
MODELS,
MODELS,
MODELS,
MODELS,
MODELS.
MODELS,
MODELS,
MODELS,
MODELS,
MODELS,
MODELS,
MODELS,
MODELS,
IODELS,
STUDIES,
STUDIES,
STUDIES,
STUDIES,
M
MO ) , SPRINGEIELD(MO), SEWAGE PLAN
MO), WILSON CREEK(V0), SPRINGFIEL
MOBILITY, PARTICULATE FORM, EEEOL
MODEL STUDIES, HYDRAULIC MODELS,
DRAINAGE PROGRAMS,
MATHEMATICS, EOUAT
LABORATORY TESTS,
HYDRAULIC MODELS,
STUDIES, SATURATED SOILS.: /
TESTS, SATURATION ZONES, SE
: * IRRIGATION
INSTRUMENTATION, HYDROCHEM
/OVEMbNT, SEEPAGE, POROU
*PATH OF POLLUTANTS, MATH
AQUIFERS, MOOEL STUDIES,
COMPUTER PROGRAMS, CAL IFO
CONVECTION, NUCLEAR POW^R
CURRENTS(WATER), MASS TRA
INDUCED INFILTRATION!, REC
MATHEMATICAL MODELS, SAL I
MATHEMATICAL MODELS, AOUI
M IX I
-------
SES,
GROU
LUTA
POSA
ILLS
OURC
MS,
E WA
#PORQUS MEDIA,
NDWATER MOVEMENT
NTS, -DIFFUSION,
L, HYDROGEOLOGY,
, ^PERCOLATION,
ES , GROUMDWATER,
HYDROLOGIC DATA,
STES, EQUATIONS,
JUDICIAL DECISIONS,
R POLLUTION SOURCES,
AL WASTES, LEACHING,
MEARIL ITY, SAMPLING,
OSED CONDUIT FLOW, *
TIV6 WASTE DISPOSAL,
ION, #PQROUS MEDIA,
LS, SEWAGE DISPOSAL,
ION, ^POROUS MEDIA,
OLLUTANTS, -ALDRTM,
GROUNDWATER MOVEMENT
AESTHETICS, AQUIFERS
NATES, ^DETERGENTS,
BACTERIA, ^VIRUSES,
OSITY, PERMEABILITY,
, DEEP PERCOLATION,
PATH OF POLLUTANTS,
RSION, ^CONVECTION,
SOIL WATER MOVEMENT,
EFFECTS, NUTRIENTS,
ROUNDWATER BASINS, W
, DOMESTIC WATER, LE
-VIRUSES, -GROUNDWAT
, SUBSURFACE
*SOIL WATER
GROUNDWATER
^GROUNDWATER
GROUNDWATER
GROUNDWATER
GROUNDWATER
GROUNDWATER
GROUMDWATER
GROUNDWATER
GROUMDWATER
GROUND WATER
GROUMDWATER
^GROUNDWATER
GROUMDWATER
MOVEMENT,
MOVEMENT,
AGROUND
^GROUND
, SOIL
, SOIL
-GROUND
-GROUND
GROUND
GROUND
-GROUND
*GROU>»D
GROUND
GROUND
ATER SU
GAL ASP
ER MOVE
WATER
WATER
'-'ATER
WATER
'-'AT ER
V5ATER
WATER
WATER
WATER
>«'ATER
WATER
WATER
PPLY,
ECTS,
MENT ,
L, DOMESTIC WASTES, FARM WASTES,
TANTSt -HYDROGEOLOGY, *ILL INOIS,
, MINERALOGY, INDUSTRIAL WASTES,
AQUITARDS, PUMPING, WATER WELLS,
LDERS, COMPOSITION, PSEUDOMONAS,
IUM, BACILLUS SUBTILIS, BACILLUS
^SUSQUEHANNA RIVER BASIN,
, SOUTH PLATTE VALL EY ( COLO ) . :
S, RIPARIAN RIGHTS, NATURAL USE,
, FARM WASTES, MUNICIPAL WASTES,
, WATER RIGHTS, RIPARIAN RIGHTS,
UNO WATER MOVEMENT, INFILTRATION,
TER LEVEL FLUCTUATIONS, AMMONIA,
IL ITY. : TRESPASS,
RIVER, S.W. OHIO WATER COMPANY,
UAL ACCUMULATIO/ -METHEMOGL OR IN ,
LITY, ^MONITORING, ^GROUNDWATER,
POULTRY, CATTLE, HOGS, NITROGEN,
ARBONATE, BICARBONATE, FLUORIDE,
ON, COLIFORMS, ENTERIC BACTERIA,
CHEMICAL ANALYSIS, TEMPERATURE,
W, TIME LAG, NITROGEN COMPOUNDS,
TREATMENT, WASTE WATER DISPOSAL,
TREATMENT, WASTE WATER DISPOSAL,
TER POLLUTION SOURCES, NITROGEN,
, ^PHOSPHORUS, NUTRIENTS, ALGAE,
WATER, WATER CHEMISTRY, SOLUTES,
TES, NUTRIENTS, DEN ITR I F I CAT ION ,
MOVEMENT,
MOVEMENT,
MOVEMENT,
MOVEMENT,
MOVEMENT,
MOVEMENT,
MOVEMENT,
MOVEMENT,
MOVEMENT,
MOVEMENT,
MOVEMENT,
MOVEMENT,
MOVEMENT,
MOVEMENT,
MOVEMENT,
MOVEMENT,
MOVEMENT,
MOVEMENT,
MOVEMENT,
MOVEMENT,
MOVEMENT,
MOVEMENT, ^STATISTICAL MODELS, -P WTl-
MOVEMENT, CONSUMPTIVE USE, DOMEST WTl-
*RADIPACTIVE WASTES, EO WTO-
WATER RESOURCES DEVELHP WTO-
MODEL STUDIES, LABORATO W70-
PFRMEARILIT: /LLUTION S WTO-
WATER QUALITY, WATER LE WTO-
LEACHING, MATHEMATICAL WTO-
PERCOLATTNG WATER, SU«S W70-
UNDERFLHH, MTESIAN WFL W7n-
ENV I ROVMENTAL SAM I TAT!0 WT0-
PATH OF POLLUTANTS, ENV W70-
CAPILLARY FLOW, *LAVA, W69-
PERCOLATIOM, SEEPAGE, U W69-
*WATER POLLUTION, PATH V69-
ABSORPTIDM, ADSORPTION. W69-
*PATH OF POLL U"l ANTS, IN W69-
LABORATORY TESTS, PFRMF W70-
INFILTRATION, PERCOLAT I W69-
GROUNDWATER MOVEMENT, I W69-
*WATER POLLUTION, INFIL WTO-
MUNICIPAL WASTES, IRRIG W69-
SOIL WATER MOVEMENT, IN W69-
INFILTRATION, PATH OF o W70-
*DIFFUSION, ^DISPERSION W69-
SOLUTES, WASTES, PATH o W69-
INFILTRATION, WATER CHE W69-
^OVEMENT, NITROGEN, WASTE NATER(P WTO-
MiJD, BENTHOS, HYDROGEN, BACTERIA, W69-
MUNICIPAL WATER, REASONABLE USE, WTO-
WASTES, IRRIGATION WATE W69-
WASTE RECHARGE.: W69-
WASTES, NATURAL GAS, SA WTO-
HASTES, LEACHING, GROUN WTO-
WASTES, SEWAGE, WATER Q WTl-
MUNICIPAL WATER, SURFACE-GROUNDS W71-
''lYCO^ACTERIUM, BACILLUS SURTILIS, W69-
MYCOIDES, RACILLUS MESENTERICUS, W69-
h' Y).: WTO-
NATIVE GRASSES, FEEDLOTS, CORRALS WTO-
NATURAL FLOW DOCTRINE, REASONABLE WTO-
NATURAL GAS, SALINE: /STIC WASTES WTO-
NATURAL USE, NATURAL FLOW DOCTRIN WTO-
NAVIGATION, SEEPAGE.: /CTION, GRO W7l-
\E8RASKA, SOIL CONTAMINATION, OBS W71-
N'EGLIGENCE, NUISANCE, STRICT L IAB WTO-
METWORK ANALYSIS.: GREAT MIAMI W69-
MITRATE MOVEMENT, FEEDLOTS, RESID W7l-
MTRATE, NITRITES, NITROGEN-CYCLE W71-
NITRATE, PHOSPHORUS, PHOSPHATES, W7l-
MITRATE, SULFATE, SILICATE, GROUN W69-
MITRATES, CHLORIDES, ^CAPILLARY C W69-
PLANTS, AMMONIA, HARDNE W69-
DISCHARGE MEASUREMENT, W70-
EUTROPHICATION, AQUIFER WTl-
EUTROPHICATION, AQUIFER W7l-
NITROGFN CYCLE, PHOSPHO W7l-
SURFACE RUNOFF, BASE FL W7l-
NITRATES, SALINITY, WITHDRAWAL, G WTl-
NITRIFICATION, AMMONIF1CAT I ON, LE WTl-
11776
13645
10058
'1UNICIPAL
MUNICIPAL
MUNICIPAL
MUNICIPAL
MUNICIPAL
NITRATES,
NITRATES,
NITRATES,
NITRATES,
NITRATES,
NITRATES,
09548
0763!
05466
10058
08026
08025
06572
06322
009T9
02681
03?3T
00652
03212
01904
OT3T5
08620
01291
08621
OT3T5
00521
OT554
08921
08620
00665
OT838
00532
08621
08621
08049
065T2
10446
02909
07838
OT838
03102
04488
02896
08049
02896
04882
03543
00521
02611
10372
12122
03542
0319T
01076
OT838
OTT66
01205
01324
12084
06443
08044
10372
138
-------
NITQRING, *GRQUNDWATER, NITRATE,
TS, DETERGENTSt DENITRIFICATION,
ATES, WATER POLLUTION, NITROGEN1,
CTFRIOPHAGE, RESERVOIRS, SPORES,
HEAD LOSS, DARCYS LAW, TIME LAG,
TRATION, DETERGENTS, POLLUTANTS,
ION SOURCES, NITROGEN1, NITRATES,
LOGICAL SOURCES, M INERAL I ZAT ION,
EGRASS, SPRING THAWS, FERTILIZER
^GROUNDWATER, NITRATE, NITRITES,
IZE^S, -WATER POLLUTION SOURCES,
BONIFICATION, LEACHING, EROS ION,
OTASSIUM, POULTRY, CATTLF, HOGS,
ERS, *MITRATES, WATER POLLUTION,
NUTRIENTS, GRQUNDWATER MOVEMENT,
AGE, *DRAINAGE, -EUTROPHICATION,
EACHING, / ^NITRIFICATION, *SOIL
VER(CALIF), YAKIMA PAS IN(PACIF 1C
OLLUTANTS, -NUCLEAR ENGINEERING,
MATHEMATICAL MODELS, CONVECTION,
SPASS, INJUNCTIONS(PROHIBITORY),
TRESPASS, NEGLIGENCE,
ESTS, SATURATION ZONES, SEEPAGE,
ITY, PART
ICATION,
AT ION, FE
HOSPHATES
MICALS, F
UTANTS, '-
AGRICULTU
PHY, SEWA
USOUEHANN
ICUL
* N IT
RTIL
, RA
ERTI
ATER
RAL
GE,
A RI
MICAL FACIES,
CIES, SEWAGE
ATE FORM, FEEDLOTS,
ROGEN, ^PHOSPHORUS,
IZERS, FARM WASTES,
TES OF APPLICATION,
LIZERS, PESTICIDES,
POLLUTION EFFECTS,
DRAINAGE, DISSOLVED
ALGAE, SCUM, WFEDS,
VER(NY), BINGHAMTONi
*SUSQUEHANNA ^IVERt
SEWAGE EFFLUENT, C.
EFFLUFNT, C.O.D., B.
A, NEBRASKA, SOIL COMTA
RFACE-GROUNDWATER RELAT
OURCES, SFISHKILL, STOR
DIGESTION, ANAEROBIC D
ORIPES, GLACIAL DRIFT,
SIS.: GREAT MIAMI RI
PERATURE, WASTE WATER T
STA
LIC HEALTH, OIL WELLS,
E WATER INTRUSION, -WAT
N ABATEMENT, PATH OF PO
GOVERNMENTS, STATE JURI
-WELLS, GROU ND WA T E R, 01
EAKAGE, JUDICIAL DECISI
ECISIONS, OIL, SEEPAGE,
TER BARRIERS, INFILTRAT
MODEL STUDIES, HYDRAULI
SOIL WATER MOVEMENT, 01
R POLLUTION SOURCES, MI
TER, DWELLS, JUDICIAL D
LS, OIL INDUSTRY, PUBLI
R, PERCOLATING WATERS,
MINATIOM,
IONSHIPS,
M RUNOFF,
IGESTIPN,
AQUIFERS,
VER, S.W.
REATMENT,
RK COUNTY{
DRILLING,
ER WELLS,
LLUTANTS,
SDICTION,
LY WATER,
DNS, OIL,
DAMAGES,
ION, OIL,
C MODELS,
LY WATER,
ME WATER,
ECISIONS,
C HEALTH,
DRILL ING,
NITROGEN
NITROGEN
ITROGEN
NITRITES, NITROGEN-CYCLE, HISTORY
NITRITES, BIOCHEMICAL OXYGEN DFMA
NITRITES, AQUIFERS, COLORADO, DEN
NITRITES,: /SELF-PURIFICATION, *A
NITROGEN COMPOUNDS, NITRATES, DIS
COMPOUNDS, SOIL COKTAMIN
CYCLE, PHOSPHORUS, REGUL
SOURCES, WELL WATER, FEE
- NITROGEN.: /SPHORUS, ALFALFA-BROM
NITROGEN-CYCLE, HISTORY, SOIL ANA
NITRATES, NITROGEN CYCL
RUNOFF, WATER POLLUTION
NITRATE, PHOSPHORUS, PH
NITRITES, AQUIFERS, COL
WASTE WATER!POLLUTION).
PHOSPHORUS, SURFACE WAT
-PUBLIC HEALTH, #SOIL L
NORTHEASTERN ILLINOIS.:
NORTHWEST), LAKE MENDOTA{WIS).: /
NUCLEAR EXPLOSIONS, CANALS, CANAL
NUCLEAR POWERPLANTS.: /OUATIONS,
NUISANCE.: TRE
NUISANCE, STRICT LIABILITY.:
NUMERICAL METHOD, LABORATORY TEST
NUMERICAL METHODS.:
NUTRIENT SOURCES.: /BOLISM,
NUTRIENTS, ALGAE, NITRATES,
DENITRIFICATION, NITRI
EFFLUENT, AQUIFER, AMM
SOIL WATER, SOILS, SEE
GROUNDWATER MOVENENT,
WATER MIXING, RUSSIAN
SEPTIC TAMKS,
W7 1-1 2122
12084
NITROGEN,
NITROGEN,
NITROGEN,
NITROGEN,
NITROGEN,
NITROGEN,
NITROGEN,
MOBIL
SURFA
EFFLUENT
#S
NUTRIENTS,
NUTRIENTS,
NUTRIENTS,
NUTRIENTS,
NUTRIENTS,
NUTRIENTS,
NY).:
NY) , BINGHAMTON(NY).:
O.D., B.O.D., WASTE WATERS, HYDRA
O.D., WASTE WATERS, HYDRAULIC LOA
OAHU
-------
ILY WATER
ATH OF PO
S, #LEAKA
UNOWATER
-POLLUTI
TING WATE
UND'-'ATER,
POLLUTANT
AND, ECOS
, GROUNDWA
LLUTANTS,
GE, JUDICI
BARRIERS,
ON, JUDICI
R, DWELLS,
-SEEPAGE,
S, SOIL HA
YSTEMS, EU
TER MOVEMENT ,
OIL INDUSTRY,
AL DECISIONS,
INFILTRATIOM,
AL DECISIONS,
GROUNDWATER,
DRILL HOLES,
TER MOVEMENT,
TROPHICATION,
UES, SOIL CONTAMINATION EFFECTS,
SOIL DISPOSAL/ SEWAGE DISPOSAL,
PHORUS, AGRICULTURAL WATERSHEDS,
DWAT
N, W
AERA
NITQ
CHEM
RRIG
IFIC
VELS
bK BA
ATER
TOR,
RING,
ICAL
ATION
ATION
, WAT
BARK,
SINS, HYDR
POLLUTION,
SPREADING,
LANDFILLS
OXYGEN DEM
, AERATION
, NITRITES
ER QUALITY
OLOGIC
WATER
/ ^FE
, BIOC
AND, C
, BIOC
, BIOC
, BIOC
#L IGN INS , *R lOC
CYCLE,
TABLE,
EDLOTS,
HEMICAL
HEMICAL
HEMICAL
HEMICAL
HEMICAL
HE^ ICAL
, PERMEABILITY, ALGAE, DISSOLVED
MQNIA, HARDNESS (WATER), ACIDITY,
SSIAN RIVER(CALIF), YAKIMA
OLLUTANTS, WOOD WASTES, PUL D
ALA AQUIFER, HIGH PL A INS ( TEXAS ),
NAGF, LAKE METABOLISM, MOBILITY,
TIO^, SOIL PROPERTIES, LEACHING,
SALINE SOILS, LAND RECLAMATION,
LLS, HYDROLOGY, 'MTFR POLLUTION,
PERCOLATING WATER, PERCOLATION,
ON EFFECTS, POLLUTION ABATEMENT,
STUDIES, MATHEMATICS , EQUATIONS,
D STREAMS, GROUNDWATER MOVEMENT,
CHING, -WATER POLLUTION SOURCES,
NO t-'ATER MOVEME^IT, INFILTRATION-
WATER MOVEMENT, SOLUTES, BASTES,
ATER MOVEMENT, *V'ATER POLLUTION,
UDICIAL DECISIONS, GROUND WATER,
ATER RELATIONSHIPS, MAL ENCLAVES,
MODEL STUDIES, LABORATORY TFSTS,
SAMPLING, GROUNDWATER MOVEMENT,
IRED WATER QUALITY, PERCOLATION,
ON, PATH OF POLLUTANTS, SEEPAGE,
-FRESH WATER INTERFACES, MIXING,
. : STATE COLLEGEt
ST, INFILTRATION, ION TRANSPORT,
IMGS, GROUNDWATFR, WATER SUPPLY,
SOLIDS, LEACHING, SALT BALANCE,
AVATION, WATER POLICY, AQUIFERS,
SUBSURFACE WATERS, GROUNDWATER,
OM ABATEMENT, SUBSURFACE WATERS,
ATER TREATMENT, '-'ATER POLLUTION,
TS, WASTE DISPOSAL , GROUNDWATER,
WASTES , HATER OUAL ITY, SAL TM ITY,
SE, RIPARIAN LANDS, GROUNDWATER,
SE, REMEDIES, WATER UTILIZATION,
OIL ,
OIL,
OIL,
OIL,
OILY
OILY
ORGANIC
ORGANIC
ORGANIC
OXYGFN
OXYGEN
OXYGEN
OXYGFN
OXYGFN
INTERFACES, IMPERVIOUS
GASES, POLLUTANTS, PERCOLATI
OIL INDUSTRY, SUBSURFACE DRA
OIL RESERVOIRS, DRILLING EOU
SEEPAGE, DAMAGES, OIL INDUST
WATER, OIL INDUSTRY, WATER P
WATER, GROUNDWATER MOVEMENT,
OILY WATER, OIL WASTES, WAT: /OF
OLIGOTROPHY, SEWAGE, ALGAE, SCUM,
ORGANIC CARBON, FEEDLOTS.:
CHEMICAL WASTES.:
COMPOUNDS, DISPERSION, SE
LOADING, #*I OHEGRADATION,
ORGANIC MATTER, SEDIMENTS, FERTIL
OTTAWA SAND, ALDRTN INFILTRATION.
OVERDRAFT, WELLS, SURFACE-GROUNDW
OXIDATION LAGOON, IRRIGATION, AER
OXIDATION DITCH, SLOTTED FLOORS,
OXYG: /MENT, SEWERS, AERATION,
OXYGFN DE: /GATIDN, AERATION,
DEMAND, CHEMICAL OXYGEN DE
DEMAND.: /T-RGENTS, DENITR
DEMAND, SUSPENDED LOAD. : /
DEMAND, LEACHING, RUNOFF,
: /OUNDWATER RELATIONSHIPS
OXYGEN, ALGAE, SELF-PURIFI CATIOM,
PACIFIC NORTHWEST), LAKE MENOOTAt
PAPER INDUSTRY, DAMAGES, HYDROLOG
PARMFR COUNTY(TEXAS), HOLLY SUGAR
PARTICULATE FORM, FEED LOTS, NUTRI
PATH OF POLLUTANTS.: /E, INFILTRA
PATH OF POLLUTANTS.: /UCTUATIONS,
OF POLLUTANTS, MINE WASTES,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
PATH OF POLLUTANTS, ENVIRONMENT.:
PENETRATION', DIFFUSION, SEEPAGE,:
PENETRATION, INDUSTRIAL WASTES, S
^ENETRATION, DRILL HOLES, GROUNDW
PEMN), SANITARY LANDFILL DRAINAGE
PENNSYLVANIA, SUBSURFACE DRAINAGE
PERCOLATING WATER, SUBSURFACE WAT
WATER,
WATER ,
WATERS,
WATER,
WATER,
WATER,
WATER,
WATER,
PATH
PATH
PATH
PATH
PATH
PATH
PATH
PATH
PATH
PATH
PATH
PATH
OF
OF
OF
OF
OF
OF
OF
OF
OF
OF
OF
MOOD WASTES,
OR INDUSTRY,
FOREIGN PROJE
SOIL WATER MO
WATER POLLUTI
SEEPAGE, PENE
MATHEMATICAL
DIGITAL COMPU
SUBSURFACE FL
AGIOS, LEACHI
WATER POLLUTI
PERCOLATING
PERCOLATING
PERCOLATING
PERCOLATING
PERCOLATING
PERCOLATING
PERCOLATING
PERCOLATING
POLLUTION IDEN
LFG: /ENS, EXC
DRILLING, OIL
UNDERGROUND, W
WATER CONSESVA
PERCOLATION, P
W71-
W71-
W70-
W71-
W70-
W70-
W71-
W71-
K70-
W71-
W69-
W70-
W68-
W70-
W70-
W70-
U71-
W 7 1 -
W 71-
W71-
H71-
W71-
W69-
W68-
IV71-
W69-
W70-
1-,' 7 1 -
W71-
W71-
W71-
W71-
71-
PERCOLATING WATER
WELL SPACING,
EMINENT DOMAIN
AQUIFERS, HYDR
W 71
W71-
W 7 1
W 7 1
W70'
W70
1/69
W69
W 6 8
W 7 1
W 7 0
W 7 0
V 7 0
W 7 0
W 71
W 7 1
W71
W 7 1
W71
W7 1
W71
W 71
W 7 1
W 7 1
W 6 9
W70
W70
08055
11724
0763?
08055
07631
08025
08055
01043
04193
08218
07114
01291
01010
04193
01904
00532
03542
03542
09]54
03542
03542
12084
07114
01269
12410
07838
04504
1169?
12122
06443
06514
08073
08907
11692
11724
01930
01043
00665
00521
08921
03237
00627
00194
09548
06322
08025
00521
03230
01204
01204
01028
06063
-0474?
-13521
-10446
10157
-1169?
-061IS
-02896
-00532
140
-------
UNDERFLOW, UNDERGROUND STREAMS,
DEC IS IONS, GROUNDWATEQ MOVEMENT,
L, DISPOSAL, WASTES, CALI FORM I A,
EPTIC TANKS, SULFATES, SULFTOES,
DETERGENTS, POLLUTANTS, NITROGE/
POLLUTION, SEEPAGE, GROUNDWATER,
, DRAINAGE EFFECTS, DRAINS, DEEP
DISPOSAL, GROUNDWATER MOVEMENT,
POLLUX -VIRUSES, #RACTERIOPHAGE,
OLATING HATER, WELL REGULATIONS,
ION, *SOIL WASTE TREATMENT, SOIL
ION, #SO!L WASTF TREATMENT, SOIL
ABILITY, POROSITY, CLOSED CONDU/
DWATER, SURFACE WATERS, SEFPAGE,
CE WATERS, UNDERGROUND, LEAKAGE,
EFFECTS, IMPAIRED WATER djALITY,
L DFCISIONS, L-GAL ASPECTS, DEEP
NFILTRATION, EVAPOTRANSP I RAT ION,
, CALIFORNIA, PERCOLATING V'ATER,
ANT RESIDUES, NORRIS(^IMN ) , SOIL
IL '-'ATFR MOVEMENT, INFILTRATION,
GROUND HATER, SUBSURFACE WATER,
T RAT I ON, SDRPTION, INFILTRATION',
RUNOFF, SUBSURFACE STREAMS, DEEP
TED LAND, COLORADO, GROUMDWATER,
GEN, PHOSPHORUS, SURFACE WATERS,
GROUNDHATER, PE^COLATIVG WATER,
N! SOURCES, GRQUNOWATER MOVEMENT,
ATES, SURFACE RUNOFF, BASE FLOW,
OU >MD WA T E R , PL A NN I N G , M A N A GEM F NT ,
ITY, SOL ID WASTES, INCINERATION,
REGULATION, GROUND HAT^, RUNOFF,
NDUSTRY, OIL, GASES, POLLUTANTS,
S, LEGAL ASDECTS? RIPARIAM LAND,
0., DEVITRIFICATION, WATER TABLE,
ACE RUNOCF, STRFAF'sS, SOIL TYP^S,
RFACE-GROUNDWATER RELATIONSHIPS,
, HYDROGEOLOGY, SOILS, PORO<= ITY,
QGY, HYDROGEOLOGY, INFILTRATION ,
OUKiDHAT^R , GROUNDHATER VOVF"
N, '-'ATER CHEMISTRY, DAROY'S
ERICAL METHOD, LABORATORY TFSTS,
AT£R MOVEMENT, LABORATORY TESTS,
HATER POLLUTION TREATMENT, HR.L
ING, STAMHARDS , PEGULAT loisj , 'JELL
CARBON PESTICIDES, INSECTICIDES,
f SANDS t CHLORINATED HYDROCARBON
CULTURAL CHEMICALS, FFRTILI7ERS,
THODOLOGY, WATER OUALITY, SOILS,
OJECT, FLUSHING "FADOV'S PROJECT,
QJECT, FLUSHING MEADOWS PROJECT,
, NITROGEN, NITRATE, PHOSPHORUS,
CATTLE, HOGS, NITROGFW, NJTRATF,
ROGEN, NITRATES, ^ITROGFN OYCL<=,
PRI/ #LAKE EUTROPHICATION, #SOIL
N A G E, #EUTROOHICATION, N T T R 0 G E M,
M i VNESOTA, w i SCONS IN, M ICHIGAN.
FIELDS, SOIL CONTAMINATION, SOR
A IMAGE, HATER POLLUTION SOURCES,
PERCOLATING WATER, SUBSURFACE WAT
PERCOLATING
PERCOLATING
PERCOLATING
WATER,
W A T E R ,
HATER,
SIJRSURFACF MAT
DFRCOLATION, L
INFILTRATION,
INFILTRATION,
PERCOLATING HATER,
PERCOLATING WATER, HFLL REGULATIO
PERCOLATION, EVAPOTRANSPI RATION.:
SEEPAGE, UNSATURATED
GROUND-HATER, WATER
PERCOLATIO
PERCOLATION,
PERCOLATION',
PERCOLATION,
PERCOLATION
PERCOLATION1
PERCOLATION
PERCOLATION
PERCOLATION
PERCOLATION
PERCOLATION
PERCOLATION
PERCOLATION
PERCOLATION
PERCOLATION
PERCOLATION
PERCOLATION
PERCOLATION.
PERCOLATION,
PFRCOLATIQM,
PERCOLATION ,
DFRCOLATION,
PERCOLATION ,
PERCOLATION,
PERCOLATION,
SUR SURFACE DRAINAGE,
CHASTE HATER RECLA'lA
#HASTE
GROUND
HATER RECLA^A
HATER, *PER'iE
V'ELLS, GROUN
WATER RIGHTS, WATER
PENETRATION', DIFFUSI
/N SOURCES, JUDICIA
FLOOD CONTROL, RESFR
LEACHING, AOUTFERS,
/ SOIL MINERALS, ^L
ADSORPTION, FILTRATI
SURSUPFACE RUNOFF, S
SOIL DISPOSAL FIELDS
GROUND HATER MOVEM EM
/REAL CROPS, IRRTGA
SUSPENDED LOAD, GROU
PATH OF POLLUTANTS,
WATER MANAGEMENT, in
LEACMTNG, DRAINAGE,
*f^OOFL STUDIES, *COM
SEEPAGE.: /PRESSIRIL
EUTROPHTCATION, DRAI
WASTES, HASTE DISPOS
SUBSURFACE HATERS, U
/ AOUT FERS, COL^RA'D
, EVALUAT TO",
PERCOLATION,
PERCOLATION. :
PFRf--cABI LITY,
PERMEASIL!TY, ALG4-, DISSOLVED
PERf-'FAB! LITY, GROUMDWATER
D-^R^.P ABILITY, SAMPLING, G
PERMPABILTT: /LLUTTpv SOURCES, GR
PFRMFABILITY, ^RTV^R FLOW. : /PTIO
PERMEABILITY, POPOSTTY, POROUS "A
p P Rr F AM F T F R S , S A MD <;, CHLORINATED
PcRi-iTTS, ADMINISTRATIVE AGENC IES,
P c RiM T S , DRILLING, ADM T N I S T R AT I V E
PESTICIDE RESIDUES, TNFILTRATTOM.
°ESTJCIDES? INSECTICIDES, p E ST i c i
PESTICIDES, NUTRIENTS, SOIL HATER
PESTICIDES, CHRO^ATOGRAPHY, ADSnR
PHOENIX(ARIZGNA).: /L RECHARGE °R
P^1OE^iTX( ARIZONA) .: /L RECHARGE PR
PHOEN'IX( ART Z) , SALT R I VER ( AR I 7 ) . :
PHOSPHATES, RATES OF APPLICATION,
PHOSPMATFS, RATES OF
REGUtATION, GROUNDHAT
ALFA L FA-RR OME GRASS, S
SURFACE MATERS, PEROO
PHOSPHORUS, AGRICULTURAL HATERS HE
PHYSICAL PROPERTIES.: / DISPOSAL
PIPES, CLOSED CONDUITS, METAL PIP
PHOSPHORUS,
PHOSPHORUS,
PHOSPHORUS,
PHOSPHORUS.
H70-07631
W70-OB026
W70-06011
W69-00652
H69-06117
W6 9-00248
W69-00225
W69-06117
M6Q-05327
H69-0532R
W69-00979
W69-05370
W70-07631
H70-OB025
W70-08050
H70-06102
H70-06011
H70-04193
W69-07375
W70-00521
W69-08621
W70-00521
W70-04488
1-71-1.1 692
W71 -071 94
K'7 1-06443
H71-09936
W71-08907
W71-1 2084
H71-1 17?4
i-'7] -01043
H7 1-02036
H7 1-0 50 94
W71-1 241.0
'-'70-063??
W70-07631
W A 9- 02 61 1
U69-00651
^ 7 0-01 904
W7 1-10157
'H71-04742
904
H7n~oi 904
H' 1-0 41 21
U"n-06514
V[69-05328
W69-05327
H70-04712
1-171-03542
K71 -03542
H71-1 2084
H69-09721
','-^0-04504
W70-04] 93
M6P-08621
VI70-0763?
141
-------
S, PIPES, CLOSED CONDUITS, METAL
, INFILTRATION, WATER SPREADING,
S), HOL/ *OGALLALA AQUIFFR, HIGH
ERMFABILITY, FLOODS, EVALUATION,
CIENCY, SIMULATION, GROUNDWATER,
EEK(MO), SPRINGFIFLD(MQ) , SEWAGE
MINNETONKA(MINN) , SOIL MINERALS,
LLUTION SOURCES, SCORES, FIFLDS,
ANALYSIS, TEMPERATURE, NITRATES,
*FEEDLOT,
*FFFDLOTSt SOUTH
RASSES, FEEDLOTS, CORRALS, SOUTH
HAGAN-
S, RHINE RIVER, AMSTERDAM RHINE,
WELL SCREENS, EXCAVATION, WATER
IFERS, ION EXCHANGE, POLLUTANTS,
SUPPLY, AQUIFERS, ION EXCHANGE,
EMENT, *WATER POLLUTION, PATH OF
^GROUNDWATER MOVEMENT, #PATH OF
IL PROPERTIES, MOISTURE CONTENT,
DECISIONS, GROUND WATFR, PATH OF
HATER, INFILTRATION, DETFRGFMTS,
, -DIFFUSION, #DISPERS/ -PATH OF
OF
OF
OF
OF
OF
OF
OF
HATER POLLUTION SOURCES, PATH
VEMENT, SOLUTES, WASTES, PATH
MOVEMENT, INFILTRATION, PATH
MOVEMENT, LABORATORY / *PATH
UDIFS, LABORATORY TESTS, PATH
ATER POLLUTION SOURCES, #PATH
G, GROUNDWATER MOVEMENT, PATH
ATIONSHIPS, MALENCLAVES, PATH OF
BAGE DUMPS, -LANDFILLS, *PATH OF
, INFILTRATION, WATER POLLUTION,
LLUTION, IMPAIRED WATER QUALITY,
^MICHIGAN, #OIL BASTES, -PATH OF
^AGRICULTURAL
PATH OF
PATH OF
PATH OF
PATH OF
PATH OF
OF
OF
OF
POLLUTION SOURCES, #GR/
, ^GARBAGE DUMPS, #GRO/
S, GROUNDWATER MOVEMENT,
^SIMULATION ANALYSIS,
MATHEMATICS, EQUATIONS,
, COLIFDRMS, ALLUVIAL / *PATH OF
Y, ^FALLOUT, -LEACHING, *PATH OF
TANTS, OIL INDUSTRY, OIL, GASES,
SOILS, LAND RECLAMATION, PATH OF
ROLOGY, HATER POLLUTION, PATH
TS, POLLUTION ABATEMENT, PATH
NDWATER MOVEMENT, *DIS/ *PATH
R MOVEMENT, *OILY WATE/ *PATH OF
TE^ENT, HATER POLLUTION EFFECTS,
TING WATER, PERCOLATION, PATH OF
IL PROPERTIES, LEACHING,
T, ^STATISTICAL MODELS,
ER POLLUTION, INDUSTRIAL WASTES,
ER WELL, IM/ ^WASHINGTON,
PRODUCTION, -FERTILIZERS, *WATER
, WATER POLLUTION EFFECTS, HATER
ELLS, HATER SUPPLY, FARMS, '-.'ATER
CONSUMPTIVE USE, DOMESTIC WATER,
#RFMEDIES, IND/ -MONTANA, *WATFR
PATH OF
PATH OF
PIPES, WELLS, ARTESIAN HELLS, WAT
PIT RECHARGE, SAFE YIELD, HATER R
PLA INS(TEXAS), PARMER COUNTY(TEXA
PLANNING.: /TREAMS, SOIL TYPES, P
PLANNING, MANAGEMENT, PERCOLATION-
PLANT BYPASSES.: /(MO), WILSON CR
PLANT RESIDUES, MORRIS(MINN}, SOI
PLANTS, ALFALFA, CEREAL CROPS, IR
PLANTS, AMMONIA, HARDNESS(WAT PR ) ,
PLATTE RIVER VALLEY.:
PLATTE RIVER VALLEY.:
PLATTF VALLEY(COLO).: NATIVE G
POISEUILLF FLOW, CLOGGING.:
POLDERS, COMPOSITION, PSEUDOMO^AS
POLICY, AQUIFERS, PERCOLATING HAT
POLLUTANT IDENTIFICATION, ADSORPT
POLLUTANTS, POLLUTANT I DENT IF 1CAT
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS.
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS.
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS,
POLLUTANTS.
POLLUTANTS,
DIGITAL COMPUTERS, CO
INJECTION WELLS, HAST
SOIL WATER MOVEMENT.:
SUBSURFACE FLOW, GASO
NITROGEN COMPOUNDS, S
^GROUNDWATER MOVEMENT
WATER POLLUTION EFFEC
MATHEMATICAL MODELS,
SEEPAGE, PENETRATION,
*ALDRIN, *GROUNDWATER
WATER POLLUTION SOURC
^DIFFUSION, *SOIL HAT
ENVIRONMENT.: /AMPLIN
ACIDS, LEACHING, CHLO
*HYDROGEOLOGY, -ILL IN
LEGAL ASPECTS.: /PAGE
INDUSTRIAL WASTES, GR
SSALINE WATER INTRUSI
*FARM WASTES, *WATER
* LEACH TNG, ^LANDFILLS
SOIL HATER MOVEMENT,
^RETURN FLOW, #NITRAT
FOREIGN PROJECTS.: /,
* INDUCED INFILTRATION
*NUCLEAR ENGINEERING,
PERCOLATION, WASTES,
/UCTUATIONS, SALINE
MINE MASTES, GEOLOGY,
OIL INDUSTRY, OIL, GA
*RADIOISOTQPES, -GROU
BLEACHING, #SOIL WATE
WASTE DISPOSAL, GROUN
WOOD HASTES, PULP AMD
/E, INFILTRATION, SO
MATHEMATICAL MODELS,
POLLUTANTS, INFILTRATION, GROUNDW
POLLUTION SOURCES, #OAMAGES, -HAT
SOURCES, NITROGEN, NITR
SOURCES,: /UPPLY, FARMS
EFFECTS, HATER POLLUTIO
ABATEMENT, JUDICIAL DEC
POLLUTION
POLLUTION
POLLUTION
POLLUTION
H70
W 7 0
W 7 1 -
W71-
H 7 1 -
W71-
W70-
W70-
W69-
W71-
W 7 1 -
W70-
W69-
H69-
W 7 3. -
W69-
W69-
W69-
H69-
H68-
H68-
W69-
W69-
W70-
W69-
W70-
W70-
W70-
W70-
W70-
H 7 1 -
W70-
W70-
W70-
W70-
W 7 1 -
H71-
H71-
W71-
V71-
W71-
W71-
W71-
W71-
H71-
W71-
H71-
H 71 -
W71-
W71-
W 7 1
W 71
W 7 1
W 71
H 71
W 71
W 7 1
H71
07632
05466
05Q94
Q9936
09154
04193
04488
07838
03543
02036
04488
00979
07838
04742
02611
02611
03237
03212
00058
00627
0065?
07554
00665
08921
00521
01904
09548
10058
06322
06572
07632
08026
08026
04121
04121
01204
01043
04548
01930
02909
04882
11724
08073
08907
T 1724
11 356
10325
11692
POLLUTION SOURCES, *WATER HELLS,
71-
-11692
-06514
-11776
-13645
-13645
-] 2084
-13521
-13521
-13645
11692
142
-------
GE, WATER OUALITY CONTROL, WATER
EROSION, NITROGEN, RUNOFF, WATER
GROUNDWATER, HYDROGEOLOGY, WATFR
S, IMPAIRED WATER QUALITY, WATER
^GROUNDWATER POLLUTION, LANDFILL
S, SALINE WATER INTRUSION, WATER
USTRIAL WASTES, WATER POLLUTION,
*WATER POLLUTION EFFECTS, *WATER
NEW MEXICO, -SOIL WATER /
REMEDIES, WATER POLLUTION,
TION, POLLUTION ABATEMENT,
*WATER POLLUTION CONTROL,
REMEDIES
W
AT/ '-OKLAHOMA
* WATER
WATER
WATER
WATER
* WATER
*WATER
* WATER
WATER
#WATER
WASTES, GROUX -NITRATES,
ON FFFECTS, ^RETURN FLOW/
#WATER POLLUTION SOURCES,
ON CONTROL, *WATER POLLUX
*WATER POLLUTION CONTROL,
DWATER, *WATER POLLUTION,
LUTION, WATER POLLUTION EFFECTS-
RAULIC MODELS, OIL WASTFS, WATER
UTIONt *WATER POLLUTION CONTROL,
*WATER OUALITY, #IRRTGATX WATER
MITS, -SUBSURFACE WATERS, WATER
UTER PROGRAMS, CALIFORNIA, WATFR
ER SPREADING, ^MONITORING, WATER
GE WATFR, -DETERIORATION, -WATER
ER SPREADING, ^MONITORING, WATER
SALT BALANCE, PERCOLATING WATER,
POLLUTANTS, *FARM WASTES, -WATER
N RIGHTS, RELATIVE RIGHTS, WATER
E DRAINAGE, WATER QUALITY, WATER
*SOLID WASTES, CHASTE DX WATER
E DISPOSAL, #HYDROGEOLQGY, WATER
TAMTS, -DIFFUSION, #SPIL/ -WATER
USF, PRIOR APPRO
PERCOLATION, WATE
, WATER POLLUTION
OILY WATER, OIL
STRY, SUBSURFACE
TTGATIONS, -SOIL
^LANDFILLS, #SOLI
NITRIFICATION, RI
ENVIRONMENTAL ENG
POTABLE WATER, S
SURFACE RUNOFF,
ROUNDWATER RELATI
STES, SGROUNOWATE
PRIATION
R RIGHTS
SOURCES
INDUSTRY
DRAIMAGE
TNVESTIX
D WASTFS
VER FLOW
INEERING
TANDARDS
GASOLINF
ONSHIPS,
R MOVEMX
o-
'F
TRIAL
LS, S
DE, ^
TESTS
URCES
, PX
WASTES,
TREAMS, J
HIGHWAY I
, PATH OF
, PATH OF
^NITRATES
STES, SCATTLE,
L INOIS, DWATER
*WATER WELLS,
ENT, CHEM
SLAT ION,
FILL, WAS
BATEM
LEGI
TARY
GROUNDWATER,
UDICIAL DECIS
CING, -SNO/ #
POLLUTANTS,
POLLUTANTS,
, ^AMMONIA, #
BLEACHING, *
POLLUTION, *
^GASOLINE, *
ICAL WASTES,
STATE GOVERNM
TE DILUTION,
WATER
WATER
WATER
WATFR
WATER
WATER
WATER
WATER
WATER
WATER
WATFR
WATER
WATER
WATER
IONS,
WATER
WATER
WATER
HATER
WATER
WATER
WATER
WATFR
ENTS,
WATER
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
SnURC F S ,
EFFECTS,
SOURCES,
SOURCES,
EFFECTS,
EFFECTS,
SOURCES,
CONTROL,
SOURCES,
SOURCES,
EFFECTS,
TREATMENT, ADMINISTRATI
CONTROL, AROUNDWATER, S
SOURCES, GROUNDWATER MO
CONTROL, DAMAGES, LEGAL
EFFECTS. :
SOURCES, MINERALOGY, IN
ABATEMENT, WATER POLLUT
CONTROL, *WATER POLLUTI
^HERBICIDES, -
POLLUTION ABAT
FFFECTS, POLLUTANTS, WA
TREATMENT, WELL PERMITS
SOURCES, #OIL WASTES, *
LEACHING, FARM
WATER POLLUT I
^RETURN FLOW,
WATER POLLUT I
*FISHKILL, STO
CONTROL, POLLUTION ARAT
ABATEMENT, PATH OF POLL
SOURCES.: /STUDIES, HYD
ABATEMENT, SUBSURFACE W
SOURCFS, *ION EXCHANGE,
WATER POLLUTIO
LEACHING, DRAI
SEWAGE TREAFME
WATER OUALITY,
SOURCES, SEWAGE TREATME
IDENTIFICATION, SOIL HA
SOURCES, #GROU!MD WATER,
STREAMS, GROWN
LYSIMETERS.: /
^URBANIZATION,
SURVEYS, LEACH
-:=PATH OF POLLU
JUDICIAL DECIS
GROUNDWATER, G
PUBLIC HEALTH,
GROUNDWATFR MD
PIPES, CLOSED
*ON-SITE INVES
WATER POLLUTIO
/LEACHING, DE
/SANITATION,
IMPAIRED WATFR
MINE WATER, 01
INFILTRATION,
^INDUSTRIAL WA
EFFECTS, LEGAL ASPECTS,
ABATEMENT, POTABLE WATE
EFFECTS, *SODIUM CHLORI
SELF-PURIFICAT
NUTRIENTS, GRO
SCORES, FIELDS
PATH OF POLLUT
^POLLUTION ABA
JUDICIAL DECIS
SOURCES, INDUSTRIAL WAS
ABATEMENT, CHEMICAL WAS
COK TROL, L FACH ING, WATE
W71
W71-
W 7 1 -
W71-
FFFECTS,
SOURCES,
SOURCES,
CONTROL,
SOURCES,
SOURCES,
SOURCES,
COMTROt ,
SOURCES,
SOURCES,
SOURCES,
SOURCES.
SOURCES.
FFFECTS,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
EFFECTS,
SOURCES,
SOURCES,
CONTROL,
SOURCES,
W71-
W71-
W71-
W 7 1 -
W 7 I -
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
U70-
W70-
W70-
W70-
W70-
W70-
W70-
W70-
W70-
W70-
W70-
H70-
W70-
W70-
W71-
W70-
W70-
W70-
W70-
W70-
W70-
W70-
W70-
W69-
W69-
W69-
W69-
10446
1037?
07194
11724
07194
10446
11692
09154
06514
11724
11692
10157
11724
08218
08044
08044
09154
09154
10446
] 1 724
10325
10446
09936
10157
04548
01205
06063
01324
06063
04121
01043
01204
05094
07193
1005^
08050
07631
06011
08025
07632
06322
06011
08662
06572
08025
08049
07766
00194
08026
08025
09844
09548
00665
04488
00665
02896
06117
05370
05370
0317R
143
-------
RY ENGINEERING, BLEACHING,
LARY FLOW, #LAVA, BASALTS,
AGESILEGAL ASPECTS), HYDROC
PERCOLATION, GROUND-WATER,
RSITY OF ILLINOIS, ENVIRONM
RIAL WASTES* SEWAGE, WASTE
MOVEMENT, NITROGEN, WASTE
R, SEDIMENTS, FERTILIZERS,
ELATIVE RIGHT/ ^REMEDIES, -
OL, *POLLUTIO/ * ILLINOIS, -
, ^GROUNDWATER MOVEMENT, *
#/ -VIRUSES, GROUNDWATER,
, ^INFILTRATION, #WATER OU
'"ATE/ -PERCOLATING WATER, -
'-'ATE/ ^PERCOLATING WATER, *
L
HATER
HATER
ARROW
WATER
ENTAL
WATER!
WATER(
WATER
MATER
WATER
WATER
WATER
ALITY
WATER
WATER
, ^LANDFILLS, -SOLID WAS/ -WATER
LY, SEEPAGE, INF
N, -WATER/ -PENN
, *SALIME WATER
A, #GRDUNDWATER
HALLOW WELLS, WA
L DECISIONS, FUE
LIGNINS, -BIOCHE
AL, WASTE WATER
ISLATION, STATE
AL, WASTE WATER
ILTRA
SYLVA
INTRU
MOVEM
TER W
LS, W
MICAL
TREAT
TION
NIA,
SION
ENT,
FLLS
ELLS
OX/
MENT
, HATER
*WATER
, l''ATFR
/ -MAINE
, ^FERTILIZERS,
-RHODE ISLAND,
TREATMENT
GROUNDWATER, -SEEPAGF, /
^NITRATES
^SEEPAGE,
MONIA, SOIL CONTAMINATION
TES, -SEPARATION TECHNIC/
.: -GROU
S, LANDFILLS, WASTE DUMPS
ECTS. : #GROU
MEDIES, INDUSTRIAL WASTES
^WYOMING, ^GROUNDWATER,
-WATER
HATER
WATER
*'-'ATER
, WATER
*HATER
, WATER
*HATER
, WATER
*WATER
, WATER
-WATER
MDWATER
, HATER
NDWATER
, WATER
fcUATFR
ING, LANDFILLS, HYDROLOGY, WATER
S, -OIL WASTES, ^REMEDIES, HATER
1C CONDITIONS, INCINERATION, AIR
ASTFS, -LEAC/ ^LANDFILLS, *WATER
NT, WASTE WATER TREATMENT, HATER
ER QUALITY, UNDER SEEPAGE, WATER
N, *OIL WASTES, ^REMEDIES, WATER
ASS).: INFILTRATION
ASS) .: INFILTRATION
ATION, INDUSTRIAL WASTES, ALGAE,
WASTES, RIVERS, STREAMS, LAKES,
LABORATORY TESTS, PERMEABILITY,
ON, GROUND WATER, -PERMEABILITY,
IRRIGATION, HYDROGEOLOGY, SOILS,
STES, ^UNIFORM FLOW, -DIFFUSION,
Y TESTS, PERMEABILITY, POROSITY,
, ^UNIFORM F/ ^DISPERSION, FLOW,
HARGE, CONVECTION, MIXING, FLOW,
ALINE WATER INTRUSION, AOUIFERS,
, GROUNDWATER MOVEMENT, SEEPAGE,
DEC IS I QMS, POLLUTION ABATEMENT,
CIL IATES, RANUNCULUS CIRCINATUS,
ERS, GROUNDWATER, PRECIPITATION,
^HYDRAULIC
POLLUTION SOURCES, SOLID WASTES,
POLLUTION SOURCES, MICROORGANISMS
: *DAM
: /ES, *RACTERIOPHAGE,
: TEST HOLES, UNIVE
POLLUTION
POLLUTION
POLLUTION
POLLUTION), LEGAL ASPECTS.: /DUST
: /RIEMTS, GROUNDWATER
SNOW, RUNOFF, DRAINAGE
^PERCOLATING WATER, #R
*WATER POLLUTION CONTR
INFILTRATION, ANALYTIC
ABSORPTION, BLEACHING,
RECHARGE, DISCHARGE, G
^SEEPAGE, #SURSURFACE
-SEEPAGE, ^SUBSURFACE
^GROUNDWATER, -SEEPAGE
POLLUTANTS, LEGAL ASPE
^SALINE WATER INTRUSIO
IMPAIRED WATER QUALITY
PATH DF POLLUTANTS, 01
DAMAGE, JUDICIAL DECTS
SEEPAGE, GR OUMDWAT £ R,
-WOOD HASTES, *BARK, #
*SOIL WASTE TREATMENT,
*OIL WASTES, #OIL, LEG
*SOIL WASTE TREATMENT,
^GROUNDWATER RECHARGE,
NITROGEN, NITRITES, 40
^PERCOLATING WATER, RI
WATER TABLE, OXIDATION
#GROUNDWATER» -OIL WAS
^CENTRAL VALLEY(CALIF)
PRECIPITATION!ATMOSPHE
LANDFILL POLLUTION EFF
POLLUTION ABATEMENT, W
*WATER POLLUTION CONTR
PATH OF POLLUTANTS, MI
WATER POLLUTION EFFECT
TEMPERATURE, WASTE WAT
#WASTE DUMPS, #SOLID W
PERCOLATING WATER, WAT
INDUSTRIAL HASTES, POL
JUDICIAL DECISIONS, RE
PONDS, CAPE COD(MASS), FALMOUTHfM
PONDS, CAPE COD(MASS), FALMQUTHfM
PONDS, FARM WASTES.: /GE, INFILTR
PONDS, TIDAL WATERS, WELLS, GROUN
POROSITY, POROUS MATERIALS, BIBLI
POROSITY, CLOSED CONDUIT FLOW, *G
POROSITY, PERMEABILITY, GROUND ^'AT
POROUS MATERIALS, ^ENGINEERING ME
MATERIALS, BIBLIOGRAPHIES,
MEDIA, GROUNDWATER, WASTES
/S, ARTIFICIAL RFC
DIFFUSION, CONV6CTI
POLLUTION)
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POLLUTION,
POROUS
POROUS
POROUS
POROUS
MEDIA.
KEDIA,
POROUS MEDIA, EQUATIONS, MATH6MAT
POTARLE WATER, STANDARDS, WATER P
POTAMOGETON PUSILLUS.: /GELLATA,
POTASSIUM, POULTRY, CATTLE, HOGS,
POTENTIAL, CANADA.:
W68-
W69
W68
W69
WTO-
W70
WTO
WTO
WTO-
WTO-
WTO
W70
WTO
WTO
W70
WTO
WTO
WTl
W 7 0
W69
W69-
H68-
W69-
W69-
W69-
W68-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
W71-
WT1-
H 7 1 -
WTl-
W71-
WT1-
H71-
W71-
W71-
W71-
W71-
W71-
W69-
W69-
W69-
9
W6
W69
W69
W69
W71
W71
W7Q
W69
W 7 1
W70
00058
00979
00627
00225
0632?
D0521
00665
04193
00521
07896
01291
04688
09637
08049
08050
06011
07632
01028
08026
03237
00627
06117
01269
05328
05370
05327
00058
02036
01043
03542
01930
04548
05094
07194
1 1692
10446
08907
11724
07118
07194
10157
13645
13521
01324
01205
06435
05370
00651
00979
07375
01238
00651
01238
07554
04559
09611
08025
07838
03542
07766
144
-------
COMPUTER
COMPUTER
DRAINAGE
WATCR, PRECIPITATION, POTASSIUM,
ICAL MODELS, COMVFCTIOM, NUCLEAR
, HATER CONSERVATION, IRRIGATION
YSIS, WATER TRANSFER, IRRIHATJW
S, WASTE DUMPS, MATER POLLUTION,
STES, ^FERTILIZERS, GROUNDWATER,
^NITRATES, GROUNDWATER, AMMONIA,
TI ON, EL OOD CONTROL, RES E RVO I RS,
RAIN FIELDS, -TEST HOLES, ANNUAL
N, ^SEEPAGE, ^SUBSURFACE WATERS,
BSURFACE RUNOFF, REASONABLE USE,
POLLUTANTS, MATHEMATICAL MODELS,
RMS, LEGAL ASPECTS, ADJUDICATION
ACTERISTICS, SOIL ANALYSIS, TEST
R, SURFACE WATERS, TESTING, TEST
ING, INFILTRATION, TUCSON BASIN,
WATER MOVEMENT, *ST/ ^STOCHASTIC
POLLUTION/ *WATER QUALITY, #CROP
NIMG, GROUNDWATER MOVEMENT, FLOW
TEMPERATURE
SOIL LEACHING, GROUNDWATFR, SOIL
VTS, DIGITAL COMPUTERS, COMPUTER
ATION, *f'ODEL STUDIES,
N, ^NUMERICAL ANALYSIS,
S, "ATHE'iATICAL MODELS,
OUIFERS, MODEL STUDIES,
RICAL ANALYSIS, MIXING, COMPUTER
INJUNCTION
TRESPASS, INJUNCTIONS
GE BASINS, EXPERIMENTAL RECHARGE
GE BASINS, EXPERIMENTAL RECHARGE
CHARGE PROJECT, FLUSHING MEADOWS
CHARGE PROJECT, FLUSHING MEADOWS
QMS, PATH OF POLLUTANTS, FOREIGN
L MECHANICS, WATER QUALITY, SOIL
IL STRUCTURE, INFILTRATION, SOIL
LYSIS, TEST PROCEDURES, CHEMICAL
WASTE DUMPS, WASTE STORAGE, SOIL
PERSION, WASTE DISPOSAL, THERMAL
OIL CONTAMINATION, SOIL PHYSICAL
DAM RHINE, POLDERS, COMPOSITION,
RCOLATIMG WATER, EMINENT DOMAIN,
ION, #WATER WELLS, OIL INDUSTRY,
OURCES, WATER POLLUTION CONTROL,
PATH OF POLLUTANTS, WOOD WASTES,
EG I SLAT I ON, CONSTRUCTION, PUMPS,
M, AQUIFERS, GRAVELS, AQUITARDS,
LLS, ^LEGISLATION, CONSTRUCT ION,
S, WATER POLLUTION SOURCES, SELF-
R), ACIDITY, OXYGEN, ALGAF, SELF-
NUNCULUS CIRCINATUS, POTAMOGFTON
LLUTION CONTROL, LEACHING, WATER
MUNICIPAL WASTES, SEWAGE, WATER
RIGATIOM RETURN FLOW, HYDROLOGIC-
*LAMQFILL, -INFILTRATION, *HATF.R
T, LEACHING, INFILTRATION, WATER
LIZERS, *WATER POLLUTION/ *WATER
N SOURCES, #ION EXCHANGE, *WATER
ER, ^SATURATED SOILS, *!/ *WATER
POLLUTION IDENTIFICATION, *WATER
PROFILES,
PROFILES,
PROGRAMS.
PROGRAMS.
PROGRAMS,
PROGRAMS,
PROGRAMS,
POULTRY, CATTLE, HOGS, NITROGEN,
PO'''ERPLANTS.: /QUA T IONS, MA THEM AT
PRACTICES.: / WATER, SALINE WATER
PRAC TICE S, L EA CHING, TEXAS.: /NA L
PRECIPITAT ION(ATMOSPHERIC), SEE DA
PRECIPITATION, POTASSIUM, POULTRY
PRECIPITATION, SEDIMENTS, OENITRI
PRFCIPITAT ION(ATMOSPHERIC).: /OLA
PRECIPITATION, LEACH RED, SPOKAME
PRIOR APPROPRIATION, GROUMDWATER,
PRIOR APPROPRIATION!, WATER POLLUT
PROBABILITY, THERMODYNAMICS, FLO'J
PROCEDURE.: /ERS, JUDICIAL DECISI
PROCEDURES, CHEMICAL PROPERTIES,
PROCEDURES, METHODOLOGY, HATER OU
PROCESS-RESPONSE MODEL, INSTRUMEN
PROCESSES, #PORPUS MEDIA, #GROUND
PRODUCTION, *FERTILIZERS, *WATER
PROFILES, SAMPLING, DATA COLLECT I
THERMAL DIFFUSION.:
WATER TABLE, SURFACE RU
/TION, PATH OF POLLUTA
/G, MANAGEMENT, PERCOL
DIFFUSION, MIXING, GROU
CALIFORNIA, WATER POLLU
SUBSURFACE DRAINAGE, HA
PROGRAMS, COMPUTER MODELS, MATHEM
PROHIBITORY).:
PROHIBITORY), NUISANCE.:
PROJECT, FLUSHING MEADOWS
FLUSHING MEADOWS
PHOENIX(ARIZONA).
PHOENIX(ARIZONA).
: /, MATHEMATICS,
PROPERTIES, WATER WELLS, WATER TA
PROPERTIES, LEACHTNH, PATH OF POL
GROUNDWATER, SOIL WAT
MOISTURE CONTENT, POL
MODEL TESTS, SATURATI
/ DISPOSAL FIELDS, S
PSEUDOMONAS, MYCORACTERIUM, RACIL
PUBLIC HEALTH, DOMESTIC WATER, IN
PUBLIC HEALTH, OIL WELLS, DRILLIM
PUBLIC HEALTH, ENVIRONMENTAL SANI
PULP AND PAPER INDUSTRY, DAMAGES,
PUMPING, STANDARDS, REGULATION, w
PUMPING, WATER WELLS, MUNICIPAL W
PUMPS, PUMPING, STANDARDS, REGULA
PURIFICATION, BIOOEGPADATION.: /T
PURIFICATION, BACTERIOPHAGEE, RESE
PUSILLUS.: /GELLATA, CILIATES, RA
DUALITY CONTROL, DOMESTIC WASTES,
CONTROL, WATER POLLUTION
MODEL.: *!R
PROJECT,
PROJECT,
PROJECT,
PROJECTS
PROJECT
PROJECT
: /L RE
: /L RE
EQUATI
PROPERTIES,
PROPERTIES,
PROPERTIES,
PROPERTIES.
QUALITY
QUAL ITY
QUALITY POLLUTION, RECHARGE, DISC
QUALITY.
QUALITY,
QUALITY,
QUALITY,
/R, GROUNDWATER MOVEMEN
*CROP PRODUCTION, *FERTI
^IRRIGATION EFFICIENCY,
^RETURN FLOW, *GROUNDWAT
W71
W71
W "/ 1
H71
W 7 1
W 7 1
W 1 I
W7Q
W69
035^?
1] 356
06063
QUALITY, -MONITORING, *GROUNDWATE
W70-
W71-
W71-
W71-
1-: 7 1 -
W69-
W71-
K1 7 1 -
W71-
H69-
W69-
H69-
W 7 1 -
W71-
W71-
1:71-
W71-
W71-
W69-
VJ69-
W69-
W69-
W69-
W71-
V71-
H71-
W71-
H68-
W69-
W69-
W69-
W70-
W 7 1 -
W70-
W71-
VI71-
W71-
W71-
W70-
H69-
W69-
W69-
W 7 1 -
W71-
W70-
H71-
W 7 1 -
W71-
W71-
W71-
05094-
03547
06435
06102
01076
08049
08050
11776
0102*
07887
06514
03197
11 776
17084
11755
00651
09721
03237
09936
09611
04548
01932
04559
13645
06117
05328
05327
05327
05328
01930
04121
0651^
07887
00058
00651
08621
07838
02896
01028
06011
11692
04747
02909
04742
09548
07838
07838
03178
10446
09936
09637
08044
12084
09936
08073
12122
145
-------
KLAHOM/ *WATER CHEM ISTRY, *WATER
DUCED INFILTRATION, RECH/ #WATER
F DISPOSAL, -GROUNDWATER, *'-'ATFR
GROUMDWATER, WATER LEVELS, '''ATER
TES, GEOLOGY, GROUNPWATER,
MI MIST RAT I ON, GROUNDWATER,
WATER POLLUTION, IMPAIRED
OLLUTIOM EFFECTS, IMPAIRED
IAL DECISIONS, OIL WASTES,
LTRATION, HATER CHEMISTRY,
MAGE EFFECTS, GROUNDWATER,
-WATER POLLUTION E^FFCTS,
BSORPTION, SOIL MFCHAMICS,
T PROCEDURES, METHODOLOGY,
GES, -WATER WELL, IMPAIRED
GISLATION, HELLS, I^-PMREP
WATER MANAGEMENT, IMPAIRED
ANIA, SUBSURFACE DRAINAGE,
ATA, GROUNDWATER MOVEMENT,
WATER
WATER
WATER
WATER
WATER
WATER
WATER
''ATER
WATER
WATER
WATER
HATER
WATER
WATER
USSR,
IF FUSION, MIXING, RADIOACTIVITY,
1C;.' EXCHANGE, DIFFUSION, MIXING,
IX IMG, RADIOACTIVITY, RADIATION,
UM , *L YS I M E T E RS , * RA D 10 I S QTn PES ,
NG, MATHEMATICAL MODELS, MIXING,
LADOPHOR4, FLAGCLLATA, CILIATFS,
NITRATE, PHOSPHORUS, PHOSPHATES,
, SURFACE HATERS, AOUIFERS, FLOW
*SUPERVATANT
OUN'D STREAMS, SUBSURFACE RUNOFF,
OUND STREAMS, SUBSURFACE RUNOFF,
LEGAL ASPECTS, MUNICIPAL HATER,
URAL USE, NATURAL FLOW DOCTRINE,
HARGE PROJEC/ SURFACE SPREADING,
HARGE PROJEC/ SURFACE SPREADING,
G, RECHARGE BASINS, EXPERIMENTAL
G, RECHARGE BASINS, EXPERIMENTAL
MUNIC IPAL HASTE
WASTE MATER
OUIFERS, WATER REUSE, ARTIFICIAL
ES. IRRIGATION WATER, ARTIFICIAL
FILTRATION, WATER SPREADING, PIT
ERS, INJECTION WELLS, ARTIFICIAL
, *MUN1C I PA L WA S TES, *ART IFICIAL
R REUSE, ^TERTIARY / ^ARTIFICIAL
IA, WATER YIELD, IN/ ^ARTIFICIAL
AL MODELS, INDUCED INFILTRATION,
SULFATE, SILICATF, GROUND WATER
#'-'ATER POLLUTION, -GROUNDWATER
UCEP INFILTRATION, -GROUND WATER
UCED INFILTRATION, AGROUND WATER
AT ION, *HATER DUALITY POLLUTION,
EMENT, *OILY WATER, -GROUNQWATER
CS, EFFLUENT STREAM, GROUMOWATER
RGE, -INDUCED INFILTRATION, *PIT
-PIT RECHARGE, *HAT/ ^ARTIFICIAL
NT, WATER RESOURCES DEVELOPMENT,
, SOIL PERCOLATION, *WASTE WATER
, SOIL PERCOLATION, -WASTE WATER
FLUCTUATIONS, SALINE SOILS, LAND
DUALITY,
DUALITY,
OUALITY,
DUALITY,
OUALITY,
PUALITY,
OUAL ITY,
OUALITY,
QUALITY,
OUALITY,
QUALITY,
OUALITY,
OUALITY,
OUALITY,
OUALITY,
QUALITY,
QUALITY,
QUALITY,
COMPACTION,
INSPECTION,
-CLIMATES, -LAND USE, #0
^MATHEMATICAL MODELS, IN
^LANDFILL, SANITARY FILL
BIOCHEMICAL OXYGEN DEMAM
COMPRESSIBIL
INSTALLATION
POLLUTANTS, INDUSTRIAL w
PERCOLATION, PENETRATION
SALINITY, PERCOLATING WA
SOIL CONTAMINATION.: /FI
SOIL WATER.: /OMIA, DR4I
SALINITv, GROUNDWATER, D
SOIL PROPERTIES, WATER W
SOILS, PESTICIDES, CHROM
UNDER SEEPAGE, WATER POL
POLLUTION CONTROL,
DISPOSAL, GARBAGE
POLLUTION SOURCES,
OUALITY, HATER LEVELS, WATER SUPP
RADIAL DIFFUSION EQUATIONS.:
RADIATION, RADIOACTIVE WASTES, 10
RADIOACTIVITY, RADIATION, RADIOAC
RADIOACTIVE HASTES, IONS, EOUATIO
RADIOACTIVE HASTE "ISPOSAL, GROUM
RADIOACTIVE HASTE DISPOSAL, UNSAT
RANUNCULUS CIRCINATUS, POTAMOGETO
RATES OF APPLICATION, NUTRIENTS,
HATER
HASTE
HATER
RATES, LEACHING
RE-CYCLE. :
REASONABLE USE,
REASONABLE
REASONABLE
/E, GROUNDWATER
DAMAGES, SURFACE
USE, PRIOR APPROPRIATI
USE, REMEDIES, WATER U
REASONABLE USE, ARTIFICIAL USE, R
RECHARGE BASINS, EXPERIMENTAL REC
BASINS,
PROJECT,
PROJECT,
RECHARGE
RECHARGE
RECHARGE
RECHARGE
RECHARGE
RECHARGE
RECHARGE
RECHARGE
RECHARGE
RECHARGE
RECHARGE
RECHARGE
RECHARGE
RECHARGE
RECHARGE
RECHARGE
RECHARGE
RECHARGE
RECHARGE,
RECHARGE
RECHARGE
EXPERIMENTAL REC
FLUSHING MEADOW
FLUSHING MEADOW
LOW-FLOW AUGMENTATION.:
FILTRATION, SORPTION, I
SAFE YIELD, WATER BALAN
CONVECTION, MIXING, FLO
LEGAL ASPECTS, AESTHFTI
*WATER SPREADING, *WATE
#WATER REUSE, *CALIFORN
#SURFACE-GROUNDWATER RE
HYDROCHEMICAL FACIES, S
GROUNDWATER, ^SEEPAGE,
IRRIGATION, DENITRIFICA
IRRIGATION, DENITRIFICA
DISCHARGE, GROUNDWATER,
MODEL STUDIES, HYDRAULI
TRANSMISSIVITY, WATER L
*WATER TREATMENT, *FILT
* INDUCED INFILTRATION,
RECLAIMED WATER.: /NDWATER MOVEME
RECLAMATION, INDUCED INFILTRATION
RECLAMATION, INDUCED INFILTRATION]
RECLAMATION, PATH OF POLLUTANTS.:
RECHARGE,
W70-
W69-
W69-
W69-
W71-
W71-
W70-
W70-
W69-
W69-
V! 71-
W71-
W71-
W7i-
W71-
W71-
W71-
06102
02611
03178
07114
08907
08026
08025
06118
08620
04548
06063
04121
06514
13645
11724
07194
01204
W70-05466
V!69-03212
W 7 1
W71
W71
11356
11356
11356
W69-02681
W70-10058
W6C'-07838
W7 1-03542
W70-09637
W71-07118
W70-08049
V170-08050
W70-00532
W70-02896
W69-05327
K'69-05328
W69-05328
W69-05327
V'69-08621
W69-08620
W70-03102
W69-08621
W70-05466
W69-07554
l-'69-08620
Wf0-04712
W70-05466
W69-02611
W69-03197
W68-00058
H69-05328
W69-05327
W70-09637
W71-10325
W71-03543
W71-12410
K'71-12410
W70-04712
W69-05328
W69-05327
W71-08073
146
-------
IRRIGATION,
, RECHARGE,
RAFT, WELLS,
SRECHARGE,
ATER TABLE,
STREAMFLOW,
CIPAL 'WATER,
IA CHANNELS,
CMINISTRATIVE AGENCIES, CONTROL,
TES, NITROGEN CYCLE, PHOSPHORUS,
TROL, REGULATION, AQUIFERS, WELL
LATIQN, C/ ^PUBLIC HEALTH, #WFLL
TION, PUMPS, PUMPING, STANDARDS,
NDWATER, PERCOLATING WATER, WELL
*SURF ACE-GROUND WATER
*SUR FACE-GROUND WATER
SURF ACE-GROUND WATER
*SUR FACE-GROUND WATER
*SURFACE-GROUNDMATER
SURF ACE-GROUND'-' ATE R
SURFACF-GROUNDWATER
SURFACE-GROUNDHATER
K POLLUTION, JUDICIAL DECISIONS,
COLATING WATER, RIPARIAN RIGHTS,
WATER, WELLS? SEEPAGE, DAMAGES,
DICIAL DECISIONS, LEGAL ASPECTS,
MUNICIPAL WATER, REASONABLE USE,
HIGHWAY ICE
CHLORIDE, ^HIGHWAY ICING, *SNOW
ION, PERCOLATION, FLOOD CONTROL,
ELF- PUR IF 1C AT I ON, BACTERIOPHAGE,
BARRIERS, INFILTRATION, OIL, OIL
BIN, NITRATE MOVEMENT, FFEDLOTS,
TIC IDES, INSECTICIDES, PESTICIDE
ONKA(MINN), SOIL MINERALS, PLANT
ROORGANISMS, FE RROBAC I LLUS , FLOW
OGY, GROUNDK'ATER MOVEMENT, WATER
ILTRATIQN, TUCSON BASIN, PROCESS
FERROBACILLUS, FLOW RESISTANCE,
ODEL
*
IRRIGATION
*WATER
*WATER
*WATER
RIPARIAN
RELATIVE
RIPARIAN
ERS, DRAINAGE WATER, IRRIGATION,
IN/ ^ARTIFICIAL RECHARGE, *^ATER
USES, ^GROUNDWATER MOVEM/
AL WASTES, ^ARTIFICIAL R/
CHARGE, #WATER SPREADING,
, WATER STORAGE, AQUIFERS, WATER
UE, MINERALIZATION, CLAY LENSES,
Y LENSES, RHINE RIVER, AMSTERDAM
ATER SOURCES, DRAINAGE, RIPARIAN
WATERS, SURFACE RUNOFF,
ON, JUDICIAL DECISIONS,
ISLATION, WATER RIGHTS,
ON, ^PERCOLATING WATER, RIPARIAN
GOVERNMENTS, LEGISLATION, WATER
N, ^PERCOLATING WATER, RELATIVE
UNO, LEAKAGE, PERCOLATION, WATER
WATER, RIPARIAN RIGHTS, RELATIVE
UPPER
DICIAL DECISIONS, LEGAL ASPECTS,
REASONABLE USE, ARTIFICIAL USE,
ENTS, LEGISLATION, WATER RIGHTS,
^SURFACE WATERS, SURFACE RUNOFF,
R POLLUTION, ^PERCOLATING WATER,
DWATER, WATER SOURCES, DRAINAGE,
*SUSQUEHANNA
ECTS, LEACHING. DENITRIFICATION,
RECIPITATION, LEACH BED, SPOKANE
*FEFDLOTSt SOUTH PLATTE
REGULATION, AQUIFERS, WELL REGULA
REGULATION, GROUMHWATER, RUNOFF,
REGULATIONS, SUBSURFACE DRAINAGE,
REGULATIONS, #WATE3 WELLS, #LEGIS
REGULATION, WELL PERMITS, DRILLIN
REGULATIONS, PERCOLATION, SUB SURF
RELATIONSHIPS, DRAINAGE EFFECTS,
OBSERVATION WELLS,
DA: / CYCLE, OVERD
MALENCLAVES, PATH
DWATER POLLUTION S
INFILTRATION, EVAP
GROUNDWATER MOVE^E
RELATIONSHIPS, PERMEABILITY, ALGA
RELATIVE RIGHTS, LEGAL ASPECTS, S
RIGHTS, '-'ATER POLLUTION
: / WELL CASINGS, SALINE
WELLS, DIKES, SHALLOW W
WATER UTILIZATION, PERC
RELATIONSHIPS,
RELATIONSHIPS,
RELATIONSHIPS,
RELATIONSHIPS,
RELATIONSHIPS,
RELATIONSHIPS,
RELATIVE
REMEDIES.
REMEDIES,
REMEDIES,
REMOVAL.:
REMOVAL, *MAINE, DEICERS, ROADS,
RESERVOIRS, PR EC IP!TAT I ON{ATMOSPH
RESERVOIRS, SPORES, NITRITES,: /S
RESERVOIRS, DRILLING EQUIPMENT, L
RESIDUAL ACCUMULATION, SOIL CORES
RESIDUES, INFILTRATION.: /BON PES
RESIDUES, MORRIS!MINN), SOIL PERC
RESISTANCE, RETENTION, HAWAI I.: /
RESOURCES DEVELOPMENT, RECLAIMED
RESPONSE MODEL, INSTRUMENTATION,
RETENTION, HAWAII.:, /ROORGANI SMS,
RETURN FLOW, HYDROLOGIC-PUALITY M
FLOW, WATER SUPPLY, LIVEST
^CALIFORNIA, WATER YIELD,
^PATHOGENIC BACTERIA, #VIR
^RECLAIMED WATER, #MUNICIP
^TERTIARY TREATMENT, INFIL
ARTIFICIAL RECHARGE, LOW-F
RIVER, AMSTERDAM RHINE, POL
POLDERS, COMPOSITION, PSEU
RIGHTS, ARTESIAN WELLS, DITCHES,
RIGHTS, COMPETING USES, DOMESTIC
LEGAL ASPECTS, STATE GOVE
NATURAL USE, NATURAL FLOW
RELATIVE RIGHTS, WATER PO
RIPARIAN RIGHTS, NATURAL
WATER LAW, GROUND WATER,
WATER POLLUTION SOURCES,
RIGHTS, WATER POLLUTION EFFECTS,
RIO GRANDE, SALT BALANCE.:
RIPARIAN LAND, PERCOLATION, SUBSU
LANDS, GROUNDWATER, PERC
RIGHTS, NATURAL USE, NAT
RETURN
REUSE,
REUSE,
REUSE,
REUSE,
REUSE,
RHINE
RHINE,
RIGHTS,
RIGHTS,
RIGHTS,
RIGHTS,
RIGHTS,
RIGHTS,
RIPARIAN
RIPARIAN
RIPARIAN
RIGHTS,
RIGHTS,
COMPETING USES,
RELATIVE RIGHTS,
RIPARIAN
RIPARIAN RIGHTS, ARTESIAN WELLS,
RIVER BASIN, (N Y) .:
RIVER FLOW, WATER POLLUTION SOURC
RIVER VALLEY.: /T HOLES, ANNUAL P
RIVER VALLEY.:
W 7 1 -
W71-
W1 I -
W71-
W11 -
W69-
W69-
lr'69-
W70-
W 7 1 -
K'70-
V70-
H71-
W71-
W71-
W 71 -
W71-
W71-
M70-
k'70-
W70-
W70-
W69-
W71-
W71-
W70-
W70-
W69-
W 7 0-
W69-
W69-
V71-
W71-
W70-
W69-
W69-
W70-
W70-
W69-
W69-
W69-
W70-
W71-
W70-
W71-
W70-
W70-
W70-
W71-
W70-
W71-
W70
W70
W70
W71
W69
W70
W70
W69
W71
10157
12084
10157
0474?
0474?
06117
00248
0?611
00532
00194
07766
06102
02909
12410
13521
01043
03230
13645
00532
09844
09844
06102
07838
08055
10372
01904
04193
00979
04712
03197
00979
09936
06435
05466
08621
08620
04712
03102
07838
07838
06118
00532
13521
02896
01043
02896
00521
07631
01043
08662
01043
02896
02896
00532
01043
06118
03102
08662
01076
02036
147
-------
*FEEDLOT, PLATTE
PHOENIX( ARIZ), SALT
NUTRIENTS, UATER MIXING, RUSSIAN
r'GFI/ DURBAN STORM RUNOFF, JAMES
#SUSOUEHANNA
MERAL IZATIOM, CLAY LENSES, RHINE
S, GLACIAL DRIFT, AOUIFERS, OHIO
ETWORK ANALYSIS.: GREAT MIAMI
TIDM SOURCES, INDUSTRIAL WASTES,
#SNOW REMOVAL, -MAINE, DEICERS,
CH/ #UNSATURATED FLOW, #MOISTURE
RIENTS, ALGAE, NITRAT'fS, SURFACE
TILIZERS, WATER POLLUTION, SNOW,
L PROFILES, WATER TABLE, SURFACE
REASONABLE USE, DAMAGES, SURFACE
HEMTCAL OXYGEN DEMAND, LEACHING,
, STORM RUNOFF, ODOR, SUBSURFACE
REEK (MO), SPRINGFI/ DURBAN STORM
LUTION SOURCES, #FISHKILL, STORM
PHORUS, REGULATION, GROUND WATER,
UNDERGROUND STREAMS, SUBSURFACE
UNDERGROUND STREAMS, SUBSURFACE
DWATER, ^SURFACE HATERS, SURFACE
ER MOVEMENT, HYDRAUL ICS, SURFACE
E WATER, PERCOLATION, SUBSURFACE
ION, SEDIMENTS, DEN I T R I F I CAT ION ,
ON, LEACHING, EROSION, NITROGEN,
SSOLVED NUTRIENTS, WATER MIXING,
SDRPTION, WATER CHEr ISTRY, DARCY
ANALYSIS.: GREAT MIAMI RIVFR,
ATER SPREADING, PIT RECHARGE,
, GRAVITATIONAL WATER, SALTS,
L, SALTS, GROUNDWATER, LEACHING,
CHING, WATER LEVEL FLUCTUATIONS,
4TIMG WATER, UNDERGROUND, WELLS,
TER MODELS, MATHEMATICAL MODELS,
ELLS, * I-' A TER WELLS , GROUND WATER,
TION IDENTIFICATION, SOIL WATER,
^'OARI ES ( SURFACES ) , '-'ELL CAS INGS ,
TATE JURISDICTION, OIL INDUSTRY,
NOWATER, LEACHING, SALINE SOILS,
LL IMG, OIL FIELDS, SAL IMF WATER,
OIL WELLS, DRILLING, OIL FIELDS,
, MUNICIPAL WASTES, NATURAL GAS,
URFACE DRAINAGE, DRAINAGE WATER,
-CLIMATES, #LAND USE, ^OKLAHOMA,
IONS, OIL WASTES, WATER DUALITY,
DILUTION EFFECTS, WATER QUALITY,
EH CHEMISTRY, SOLUTES, NITRATES,
TER, DISSOLVED SOLIDS, LEACHING,
UPPER RIO GRANDE,
PHOENIX(ARIZ),
*SALT WATER IRRIGATION,
NE, DEICERS, ROADS, CHEMCONTROL,
DIFFUSION, GRAVITATIONAL WAFER,
OGY, INFILTRATION, PERMEAUIL ITY,
NDWATER MOVEMENT, FLO'-' PROFILES,
OTTAWA
1C BACTERIA, METABOLISM, CAMALS,
RIVER VALLEY.:
RIVERfARIZ) .:
RIVER(CALIF) , YAKIMA BASINfPACIFI
RIVER(MO), WILSON CREEK(MO), SPRI
RIVER(NY), BINGHAMTONf NY).:
RIVER, AMSTERDAM RHINE, POLDERS,
RIVER, KENTUCKY.: /HING, CHLORIDE
RIVER, S.W. OHIO WATER COMPANY, N
RIVERS, STREAMS, LAKES, PONDS, TI
ROADS, CHEMCOIMTROL, SALTS, GROUND
ROUTING, LANDFILL MANAGEMENT, LEA
RUNOFF, BASE FLOW, PERCOLATION, L
DRAINAGE WATER, GRASSLAND
FARM WASTES, AEROBIC COND
GASOLINE, WATER POLLUTION
GROUNDWATER, CELLULOSE, H
GROUNDWATER MOVEMENT, LIM
JAMES RIVER(MO), WILSON C
ODOR, SUBSURFACE RUNOFF,
PERCOLATION, EUTROPHICATI
REASONABLE USE, PRIOR APP
REASOiMARLE USE, DAMAGES,
RIPARIAN RIGHTS, COMPETIN
STREAMS, SOIL TYPES, PERM
SUBSURFACE STREAMS, DEEP
UREAS, FERTILIZERS, DRAIN
WATER POLLUTION CONTROL,
RUSSIAN RIVER(CALIF), YAKIMA RASI
S LAW, PERMEABILITY, DRIVER FLOW.
S.W. OHIO WATER COMPANY, NETWORK
SAFF YIELD, WATER BALANCE, HYDROG
SALINE SOILS, WASTE STO: / DIFFUS
SALINE WATER.: /TRO
LAND RECLAMATION, P
INTRUSION, WATER POL
WATER INTRUSION, AOUIFERS,
WATER-FRESH WATER INTERFAC
WATER, WATER CONSERVATION,
WATER, WELLS, SEEPAGE, DAM
WATER, SUBSURFACE WATERS,
WATER.: /TROL, SALTS, GROU
WATFR-FRESHWATER INTERFACE
WATER, SALINE WATER-FRESHW
/STIC WASTES, FARM WASTES
RUNOFF,
RUNOFF,
RUNOFF
RUNOFF
RUNOFF
RUNOFF
RUNOFF
RUNOFF
RUNOFF
RUNOFF
RUNOFF
RUNOFF
RUNOFF
RUNOFF
RUNOFF
SALINE
SAL INF
SALINE
SAL INE
SAL INE
SAL I ME
SALINE
SAL IMF
SALINE
SALINE
SALIME
SAL
SOILS,
SOILS,
WATER
SALU ITY, FERTILIZERS,
SALINITY,
SALIMTY,
SALINITY,
SALT
SALT
GROUND WATE
STREAMFLOW, SURFACE-GRO
PERCOLATING WATER, WELL
GROUNDWATER, DISSOLVED
SALINITY, WITHDRAWAL, GROUNDWATER
SALT BALANCE, PERCOLATING WATER,
BALANCE.:
RIVER( ARIZ). :
SALT TRANSPORT. :
SALTS, GROUNDWATER, LEACHING, SAL
SALTS, SALINE SOILS, WASTE STO: /
SAMPLING, GROUNDWATER MOVEMENT, P
SAMPL ING, DATA COLLECTION, WELLS,
SAN JACINTO VALLEY(CALIF) .:
SAND, ALDRIN INFILTRATION.:
SANDS, CHLORINATION, MICROORGANIS
W71-
W70-
W70-
W71-
W71-
W69-
W71-
W69-
W69-
vnn-
W68-
W71-
W70-
W69-
W70-
W68-
W71-
W71-
W71-
W71-
w*?o-
W70-
W70-
W71-
W70-
W71-
W71-
W70-
W69-
W69-
W70-
!'1 70-
W7D-
W71-
W 7 1 -
W7]-
W71
W 7 1
V.1 7 1
VI71
W70
W71
W71
W70
k'70
W70
W 6 9
W71
W71
H71
W70
W71-
W70-
W70-
W70-
W71-
W 70-
W70-
W69-
03543
04712
04504
09154
02909
07838
00194
02611
05370
09844
00058
06443
04193
09721
08049
01269
09154
09154
0915^
12084
08050
08049
00532
05094
0052]
06435
10372
04504
02611
02611
05466
08026
09844
08073
10446
04559
03230
06063
03230
13521
09844
01028
01028
08049
08662
06102
06118
-06063
08044
06063
08662
04712
06063
09844
08026
06322
11255
05466
01904
07838
148
-------
LABORATORY TESTS? PERMEAMETERS,
WASTES, INFILTRATION, AOUIFORS,
SPIRATION, --LANDFILLS, DRAINAGE,
D STATES, ^REVIEWS, METHODOLOGY,
ATER, *WATER QUALITY, *LANDFILL,
STATE COLLEGE(PENN),
OL, PUBLIC HEALTH, ENVIRONMENTAL
UNOWATER MOVEMENT, ENVIRONMENTAL
ASTF DISPOSAL, UNSATURATED FLOW,
UNSATURATED FLOW, MODEL STUDIES,
THERMAL PROPERTIES, MODEL TESTS,
LL CASINGS, ARTESIAN WELLS, WELL
ION, OLIGOTROPHY, SEWAGE, ALGAE,
URAL WATERSHEDS, ORGANIC MATTER,
NOWATER, AMMONIA, PRECIPITATION,
EMENT, INFILTRATION, NAVIGATION,
STES, INCINERATION, PERCOLATION,
LL CASINGS, SALINE WATERt WELLS,
LUTION, JUDICIAL DECISIONS, OIL,
, FUELS, WELLS, WATER POLLUT ION,
nUNO, GROUNOWATER, WATER SUPPLY,
ION, PRECIPITATION(ATMOSPHERIC),
, MODEL TESTS, SATURATION ZONES,
LS, GROUNDWATER, SURFACE WATERS,
NFILTRATION, PATH OF POLLUTANTS,
N, MIXING, GROUNDWATER MOVEMENT,
S, NUTRIENTS, SOIL WATER, SOILS,
OUMDWATER MOVEMENT, PERCOLATION,
ELLS, DITCHES, DRAINAGE EFFECTS,
L, IMPAIRED WATER DUALITY, UNDER
OLATION, PENETRATION, DIFFUSION,
JTAMTS, WATER POLLUTION SOURCES,
(WATER), ACIDITY, OXYGEN, ALGAE,
, ALGAE, SCUM, WfFFOS, MUTRIFMTS,
SO'IL DISPOSAL FIELDS, CESSPOOLS,
POLLUTION CONTROL, GROUNOWATER,
*BIODEGRADATION, SOIL DISPOSAL/
, SOIL CONTAMINATION, CESSPOOLS,
N', FILTRATION, SEWAGE TREATMENT,
ME WATER, OIL WASTES, CESSPOOLS,
, ORGANIC COMPOUNDS, DISPERSION,
POSAL, WASTE WATER TREATMENT, W/
POSAL, WASTE WATER TREATMENT, W/
RECHARGE, HYDROCHEMICAL FAC I ES,
LSON CREEK(f^O) , S PR INGF I FL D ( MO ) ,
A IMAGE, AOUIFERS, SINKS, CITIFS,
TORJNG, WATER POLLUTION SOURCES,
TORINO, WATER POLLUTION SOURCES,
TMENT, INFILTRATION, FILTRATION ,
MS, EUTROPHICATION, OLIGOTRGPHY,
N FLOW, WATER SUPPLY, LIVESTOCK,
STRIAL 'PASTES, MUNICIPAL h'ASTES,
PENETRATION, INDUSTRIAL WASTES ,
SINKS, CITIES, SF'-'AGE TREATMENT,
ASPFCTS, REMEDIES, WELLS, DIKES,
ERCOLATION, SUBSURFACE DRAINAGE,
PERCOLATING WATER, WELL SPACING,
ATE, FLUORIDE, NITRATE, SULFATE,
QUALITY, ^IRRIGATION EFFICIENCY,
SANITARY
SANITARY
SANITARY
SANDS, CHLORINATED HYDROCARBON PE
SANITARY ENGINEERING.: / DOMESTIC
ENGINEERING, BLEACHING,
ENGINEERING, LANDFILLS,
FILL, WASTE DILUTION, WA
SANITARY LANDFILL DRAINAGE.:
SANITATION, WASTE DISPOSAL, DISPO
SANITATION, ENVIRONMENTAL ENGINEE
SATURATED FLOW, ADSORPTION, ADSOR
SATURATED SOILS.: /ION, SEEPAGE,
SATURATION ZONES, SEEPAGE, NUKERI
SCREENS, EXCAVATION, WATER POLICY
SCUM, WEEDS, NUTRIENTS, SEPTIC TA
SEDIMENTS, FERTILIZERS, WATER POL
SEDIMENTS, DENITRIFI CAT ION, RUNOF
SEEPAGE.: /CTIOM, GROUNDWATER MOV
SEEPAGE,: /PRESSIBI LITY, SOLID WA
SEEPAGE, DAMAGES, REMEDIES.: / WE
DAMAGES, OIL INDUSTRY, S
GROUNDWATER, PERCOLATING
INFILTRATION, WATER POLL
SEEPAGE,
SEEPAGE,
SEEPAGE,
SEEPAGE,
SEEPAGE,
SEEPAGE,
SEEPAGE,
SEEPAGE,
SEEPAGE,
SEEPAGE,
SEEPAGE,
SEEPAGE,
SEEPAGE,
INFILTRATION, GROUNDWATE
DISPOSAL,
DISPOSAL,
DISPOSAL,
NUMERICAL METHOD, LABORA
PERCOLATION.: /TERS, WEL
PFK'ETRATION, INDUSTRIAL
POROUS MEDIA, EQUATIONS,
SOIL CHEMISTRY, ABSORPTI
UNSATURATED FLOW, MODEL
WASTE STORAGE, LEGAL ASP
WATER POLLUTION, INDUSTR
/ED WATER DUALITY, PERC
SELF-PURIFICATION, RJODEGRADATION
SELF-PURIFICATION, RACIER IOPHAGE,
SEPTIC TANKS, EFFLUENTS, SWAMPS,
TANKS, SULFATES, SULFIDES,
TANKS, MANAGEMENT.: /WATER
DISPOSAL, ORGANIC LOADING,
GROUNDWATER MOVE
HYDROGEOLOGY, GR
DOMESTIC WASTES,
EFFLUENTS, BIODEGRADATION,
EFFLUENT, *WASTE WATER DIS
EFFLUENT, *WASTE WATER HIS
EFFLUENT, C.O.D., B.Q.D.,
PLANT BYPASSES.: /(MO), WI
TREATMENT, SEWERS, AERATIO
TREATMENT, UASTE WATER DIS
TREATMENT, WASTE HATER DIS
SEWAGE TREATMENT, SEWAGE DISPOSAL
SE'.'/AGE, ALGAE, SCUM, WEEDS, NUTRI
INFILTRATION, INDUSTRIAL
WATER QUALITY CONTROL, MA
WASTE WATER(POLLUTION), L
AERATION, MONITORING, LAN
WELLS.: /EC I SIONS, L EGAL
WELLS, SUBSURFACE WATERS,
SHALLOW WELLS, GROUNDWATER, WATER
SILICATE, GROUND WATER RECHARGE,
SIMULATED LANDFILL.:
SIMULATION, GROUMDWATER, PLANNING
SEPTIC
SEPTIC
SEWAGE
SEWAGE
SEWAGE
SEWAGE
SEWAGE
SEWAGE
SEWAGE
SEWAGE
SEWAGE
SEWAGE
SEWAGE
SEWAGE
SEWAGE,
SEWAGE,
SEWAGE,
SEWERS,
SHALLOW
SHALLOW
WTO
W69
W68
W 7 1
W69
W " 1
W 7 0
W70
W70
W69
W69
W71
WTO
WTO
VTf 1-
WT1
WT1
W 1 1
WTO
W69-
W 7 0
WT1
W69
K69
VHO
WT1
if/69
W69
W71
WTO
01904
03178
00058
08907
03178
01204
06011
06572
10058
02681
00651
04742
04193
04193
06435
04882
08907
03230
07631
06117
07632
05094
00651
05370
00521
09611
04121
02681
06118
13645
08025
W70-09548
W69-
V70-
W68-
W71-
W68-
W69-
W70-
W70-
W70-
W69-
W69-
W69-
W 7 1 -
W71-
W 7 1 -
W71-
W70-
W70-
W71-
Wll-
W'/O-
W71-
₯11-
W69-
W69-
W69-
W70-
W71-
07838
04193
01010
10372
01010
00652
04712
08049
01291
05327
0532^
03197
09154
09154
01205
01324
04712
04193
06435
10446
00521
09154
13645
06117
06118
03197
0954*
09936
149
-------
RIAL WASTES* DRAINAGE, AQUIFERS,
EASIJREMENT, DISC HARGE(WATER), ON-
I/ SWATER POLLUTION EFFECTS? *ON-
Gt / SFFEDLOTS, OXIDATION DITCH,
St FERTILIZERS, WATER POLLUTION,
CHING, SAOUIFER CHARACTERISTICS,
TKITES, NITROGEN-CYCLE, HISTORY,
NTS, SOIL WATER, SOILS, SEEPAGE,
NTS, EFFLUENT, AQUIFER, AMMONIA,
FLUCTUATIONS, AMMONIA, NEBRASKA,
WATER CHEMISTRY, WATER QUALITY,
RCOLATION, SOIL DISPOSAL FIELDS,
LTRATIQN, ANALYTICAL TECHNIQUES,
POLLUTANTS, NITROGEN COMPOUNDS,
FEEDLOTS, RESIDUAL ACCUMULATION,
RGANIC LOADING, *RIODEGRADATION,
TION, INFILTRATION, PERCOLATION,
OFF, DRAINAGE WATER, GRASSLANDS,
LEACHING, DRAINAGE, FARM WASTES,
AGE, SOIL CHEMISTRY, ABSORPTION,
MANURES, LAKE MINNETONKA(MINN),
ORIOES, -CAPILLARY CONDUCTIVITY,
OLLUTICN, #SOIL WASTE TREATMENT,
OLLUTIONv *SOIL WASTE TREATMENT,
S, PLANT RESIDUES, MORRIS(M INN ) ,
OSAL FIELDS, SOIL CONTAMINATION,
TH, *S(?IL LEACHING, GROUNPWATER,
MPS, WASTE DUMPS, WASTE STORAGE,
Y, SOIL STRUCTURE, INFILTRATION,
, SOIL MECHANICS, WATER QUALITY,
ANALYTICAL TECHNIQUES, BIOASSAY,
AULTCS, SURFACE RUNOFF, STREAMS,
CTS, GROUMDWATER, WATER QUALITY,
WATER, POLLUTION IDENTIFICATION,
TILIZERS, PESTICIDES, NUTRIENTS,
NDWATER, SOIL WATFR, SOLUBILITY,
HEMTCAL PROPERTIES, GROUNDWATER,
S, MOISTURE CONTENT, POLLUTANTS,
MEABILiTY, GROUNDWATER MOVEMENT,
L ASPECTS, AESTHETICS, AQUIFERS,
ER MOVEMENT, PATH OF POLLUTANTS,
HOMOGENEOUS MEDIA, UNSATURATED
D FLOW, MODEL STUDIES, SATURATED
N FLOW, -GROUNDWATER, ^SATURATED
OIL-WATER INTERFACES, IMPERVIOUS
WATFR LFVEL FLUCTUATIONS, SALINE
TANKS, EFFLUENTS, SWAMPS, FOREST
RES, METHODOLOGY, WATER QUALITY,
IMKLEK IRRIGATION, HYDROGEOLOGY,
S, GROUNDWATER, LEACHING, SALINE
STICIDES, NUTRIENTS, SOIL WATER,
AVITATIO'MAL WATER, SALTS, SALINE
ACHING, 'A'ATFR POLLUTION SOURCES,
TY, COMPACTION, COMPRESSIBILITY,
SALINITY, GROUNDWATER, DISSOLVED
rRTIES, GROUNDWATER, SOIL WATER,
RIGATION WATER, WATER CHFMISTRY,
NVECTION, *GROUMDHATER MOVEMENT,
TRANSIENT STORAGE, GRAPHICAL
ARTIFICIAL RECHARGE, FILTRATION,
SINKS, CITIES, SEWAGE TREATMENT,
SITE DATA COLLECTIONS, UNDERFLOW.
SITE INVESTIGATIONS, *SQIL INVEST
SLOTTED FLOORS, AERATOR, SPREADIN
SNOW, RUNOFF, DRAINAGE WATER, GRA
SOIL ANALYSIS, TEST PROCEDURES, C
ANALYSIS, WATER TRANSFER, IR
CHEMISTRY, ABSORPTION, SOIL
CONTAMINATION, WATER PQLLUTI
CONTAMINATION, OBSERVATION W
CONTAMINATION.: /FILTRATION,
CONTAMINATION, SOIL PHYSICAL
CONTAMINATION EFFECTS, ORGAN
CONTAMINATION, CESSPOOLS, SE
CORES.: / NITRATE MOVEMENT,
DISPOSAL FIELDS, CESSPOOLS,
DISPOSAL FIELDS, SOIL CONTAM
EROSION,: /L UTI ON, SNOW, RUN
MANAGEMENT, GROUNDWATER, WIS
MECHANICS, WATER QUALITY, SO
MINERALS, PLANT RESIDUES, MO
MOISTURE.: /A, NITRATES, CHL
PERCOLATION, *WASTE WATER RE
PERCOLATION, *WASTE WATER RE
PERCOLATION.: / SOIL MINERAL
PHYSICAL PROPERTIES.: / DISP
PROFILES, MATER TABLE, SURFA
PROPERTIES, MOISTURE CONTENT
PROPERTIES, LEACHING, PATH 0
PROPERTIES, MATER WELLS, WAT
STRUCTURE, INFILTRATION, SOI
TYPES, PERMEABILITY, FLOODS,
WATER.: /QNJA, DRAINAGE EFFE
SALINE WATER, KATER C
SOILS, SEEPAGE, SOIL
TRANS MI SSI VITY.: /GROU
SOLUBILITY, SOIL WATE
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL
SOIL.:
SOILS.
SOILS,
SOILS,
SOILS,
SOILS,
SOILS,
SOILS,
SOILS,
SOILS,
WATER
WATER
WATER
WATER
WATER
WATER
WATER
WATER
MOVEMENT.
MOVEMENT,
MOVEMENT,
MOVEMENT,
/ PROPERTIE
INFILTRATION
GROUNOWATER
OILY WATER,
/ION, SEEPAGE, UNSATURATE
^IRRIGATION EFFECTS, LEACH
GROUNDWATER BARRIERS, INFI
LAND RECLAMATION, PATH OF
MINNESOTA, WISCONSIN, MICH
PESTICIDES, CHRDMATOCRA PHY
POROSITY, PERMEABILITY, GR
SALINE WATER.: /TROL, SALT
SEEPAGE, SOIL CHEMISTRY, A
SOILS, WASTE STO: / DIFFUSION, P-R
SOL 10 WASTES, WASTES, GARBAGE DUM
SOLID WASTES, INCINERATION, PFRCO
SOLIDS, LEACHING, SALT BALANCE, P
SOLUBILITY, SOIL MATER TRANSMISSI
SOLUTES, NITRATES, SALINITY, WITH
SOLUTES, WASTES, PATH OF POLLUTAN
SOLUTIONS*:
SORPTION, INFILTRATION, PERCOLATI
W71
W70
W70
W71
W70
W71
M71
W71
W71
W69
W69
W7Q
V169
W71
W68
W69
W70
W71
W71
W70
W69
W69
W69
W69
W68
W71
W71
W 7 1
W71
W71
W71
W/l
W71
K( 7 1
W68
W69
W 7 1
K69
1-/69-
H 7 1
W 7 1
W71-
1-! 7 0-
W71-
W69
W70
W 7 1
V70
W68
I-.' 7 1
lr/71
W 7 1
l-.f 7 1
W69
W69
W 6 9
09154
07766
0632?
03542
04193
07887
12122
04121
03542
03543
08620
08621
01291
0065?
10372
01010
08621
04193
06443
04121
04193
01076
05327
05328
04193
08621
09721
00058
06514
04121
'06514
'05094
04548
06063
04121
07887
07887
00058
07375
08620
01043
02681
02681
08073
08055
08073
04193
06514
07375
09844
04121
08026
00058
08907
06063
-07887
08044
-08921
00248
-08621
150
-------
TAL ENGINEERING
ION, RIVER FLOW
ELS, OIL WASTES
ICULATE FORM, F
, #FARM HASTES,
STES, -WASTE D/
, *SOIL WATER /
, ^RETURN FLOW/
LUTION CONTROL,
WAT/ ^OKLAHOMA,
IND/ ^MONTANA,
ALITY, #IRRIGAT
M/ ^WASHINGTON,
UNDWATFR MMVEM/
FFUSION, *SOIL/
ATES, -AMMONIA,
, WATER
, MATER
, WATER
EEDLOTS
#WATER
*WATER
* WATER
-WATER
*WATER
#WATER
*WATER
/ WATER
*WATER
--WATER
*WATER
#WATER
HALLOW WELLS, GROUNDWA
R, OIL INDUSTRY, WATER
N, WATER RIGHTS, WATER
R, HYDROGEOLOGY, WATER
RELATIONSHIPS, -WATER
CHEMICAL WASTES, WATER
L L S , -GA S OL I NE , -WATER
POLLUTION
POLLUTION
POLLUTION
, NUTRIENT
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
TER, WATER
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
GEOLOGICAL
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
POLLUTION
, NITROGEN
POLLUTION
POLLUTION
BROOK INGS
, CORRALS*
*FEEDLOTS,
ATER, HELL
#OIL
ANNUAL PRECIPITATION, LEACH BED,
TION, BACTERIOPHAGE, RESERVOIRS,
R APPROPRIATION,
, WATER QUALITY,
ROU/ #NIT RATES,
AMS, CALIFORNIA,
SO/ *SURFACE WA
HATER INTRUSION,
UMOFF, GASOLINE,
*LAVA, BASALTS,
, ^FERTILIZERS,
URFACE DRAINAGE,
TLE,
H OF
NG,
RING
NG,
OUKC
BLEACHING,
POLLUTANTS,
^MONITORING,
, BLEACHING,
^MONITORING,
ES, MINERALI
OLID WASTES,
LLUTION EFFECTS,
S
WATER
WATER
*WATER
WATER
TERS,
WATER
WATER
WATER
#HATER
HATER
*WATER
HATER
HATER
WATER
WATER
ZATION
WATER
HATER
TIVE GRASSES, FEEDLOTS
ALIMITY, PERCOLATING
W
1MENTAL
IMEMTAL
Y / #ART
WATFR YI
DISPOSA
LUTION S
DITCH,
PHOSPHO
RECHA
RECHA
IFICI
ELD,
L, *I
O/ *I
SLOTT
RUS,
MES RIVEK(MO)
RGE PROJ
RGE PROJ
AL RECHA
INFILTRA
[^ FILTRAT
NFILTRAT
ED FLOOR
ALFALFA-
, WILSON
'.TION, *CHEMI
FC/
RGE,
T I ON
ION,
ION,
S, A
BROM
CRE
CAL
SURFACE
SURFACE
*WATER
9 WATER
*HATFR
*UATER
ERATOR,
EGRASS,
EK(KO) ,
WASTES,
SOURCES.
SOURCES.
SOURCES.
SOURCES.
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
o
/SANITATION, ENVIRONMEN WTO-
./LEACHING, DENITRIFICAT W70-
/STUDIES, HYDRAULIC MOD W71-
/BOLISM, MOBILITY, PART W71-
*GROUNDV!ATER, *AGRICULTU W71-
*URRANIZATION, ;;=SOLID WA W71-
;::HERBICIDES, *MEW MEXICO W71-
#WATER POLLUTION EFFECTS W71-
*FISHKILL, STORM RUNOFF, W71-
*OIL WASTES, ^REMEDIES, W71-
*WATER HELLS, ^REMEDIES, VJ71-
*ION EXCHANGE, =i-WATER OU W71-
*DAMAGES, *WATER WELL, I W71-
*INOUSTRIAL WASTES, *GRO W71-
=::PATH OF POLLUTANTS, *DI W70-
*CORES, FIELDS, PLANTS, WTO-
DRAINAGE, RIPARIAN RIGHT W69-
GROUNDWATER MOVEMENT, UN W70-
GROUNDWATER, GROUNDWATER W70-
GROUNDWATFR MOVEMENT, PE W71-
IMF I LTRAT I ON, WASTES, HY W70-
I NOUS TRIAL WASTES, RIVER W69-
JUDICIAL DECISIONS, FUEL W69-
JUDICIAL DECISIONS, LEGA W70-
LYSIMETERS.: /E DRAINAGE W71-
LEACHING, FARM WASTES, G W71-
LEACHING, DRAINAGE WATER W71-
MINERALIZATION, NITROGEN W71-
MTNERALOGY, INDUSTRIAL W W71-
MIME WATER, OIL WASTES, W70-
MICROORGANISMS, FERROBAC W69-
NITROGEN, NITRATES, NITR W71-
PIPES, CLOSED CONDUITS, W70-
PATH OF POLLUTANTS, WATE W70-
SELF-PURIFICATION, BIODE WTO-
SEWAGE TREATMENT, WASTE W71-
SOLID WASTES, WASTES, GA W68-
SEUAGE TREATMENT, WASTE W71-
WELL WATER, FEEDLOTS.: / H71-
WATER POLLUTION CONTROL, W70-
/UPPLY, FARMS, HATER PO W71-
SOUTH DAKOTA).: W69-
SOUTH PLATTE VALLEY(COLO).: MA WTO-
SOUTH PLATTE RIVER VALLEY.: W71-
SPACING, SHALLOW WELLS, GROUNDWAT W69-
SPHERICAL DIFFUSIVITY.: WTO-
SPILLS.: W71-
SPOKANE RIVER VALLEY.: /T HOLES, W69-
SPORES, NITRITES,: /SELF-PUR IF 1CA W69-
SPRAY DISPOSAL.: W69-
SPREADING, RECHARGE BASINS, EXPER W69-
RECHARGE BASINS, EXPER V.69-
*WATER REUSE, #TERTIAR WTO-
PIT RECHARGE, SAFE YIE WTO-
*MONITORIMG, WATER POL »//?!-
^MONITORING, WATER POL W71-
SPREADING, LAND DISPOSAL.: /ATION WT1-
SPRING THAMS, FERTILIZER-NITROGEN W69-
SPRINGFIELD(MO), SEWAGE PLANT BYP WT1-
SPRINKLER IRRIGATION, INF I LTRAT10 W69-
OURCES,
SOURCES,
SOURCES,
.SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES,
SOURCES",
SOURCES,
SOURCES,
SPREADING,
SPREADING,
SPREADING,
SPREADING,
SPREADING,
06572
08662
10325
06443
04121
05094
06514
08044
09154
11724
1 1692
09936
13645
00194
10058
04488
06118
08025
07631
07194
07766
05370
06117
08050
01204
08218
04548
06435
10446
08049
00979
3 2084
07632
00665
09548
01 205
00058
01324
06435
06011
13521
03178
04488
02036
06118
10058
10325
01076
07838
07375
05328
05327
04712
05466
01205
01324
03542
09721
09154
07114
151
-------
LUTION ABATEMENT, POTABLE HATER,
N, CONSTRUCTION, PUMPS, PUMPING,
DFILL DRAINAGE.:
#OIL WASTES, #OIL, LEGISLATION,
N CONTROL, -POLLUTION ABATEMENT,
RELATIVE RIGHTS, LEGAL ASPECTS,
^GAL ASPECTS, STATE GOVERNMENTS,
ASTFS, *WASTE TREATMENT, "'UNITED
YDROGRAPHS, HYDROGRAPH ANALYSIS,
PH ANALYSIS, STATISTICAL MODELS,
ATER, SALTS, SALINE SOILS, HASTE
SEEPAGE, DAMAGES, OIL INDUSTRY ,
DELS, STATISTICAL METHODS, WATER
TRANSIENT
DRAINAGE EFFECTS, SEEPAGE, WASTE
ARBAGE DUMPS, WASTE DUMPS, '-'ASTE
LSDM CREEK(MO), SPRINGFI/ -URBAN
ER POLLUTION SOURCES, #FISHKILL,
O'JIFER CHARACTERISTICS, EFFLUENT
-LAND USE, ^OKLAHOMA, SALINITY,
N, SUBSURFACE RUNOFF, SUBSURFACE
EUTROPHICATION, OLIGOTR/ *LAKES,
, SUBSURFACE WATERS, UNDERGROUND
RIGHTS, WATER POLLUTION EFFECTS,
MENT, UNDERFLOW, ARTESIAN WELLS,
RCES, INDUSTRIAL WASTES, RIVERS,
DRAINAGE, UNDERFLOW, UNDERGROUND
I AT I ON, GROUNDWATER, UNDERGROUND
WATERS, GROUNDWATER, UNDERGROUND
ENT, HYDRAULICS, SURFACE RUNOFF,
TRESPASS, NEGLIGENCE, NUISANCE,
TICAL TECHNIQUES, RIOASSAY, SOIL
ARMER COUNTY(TEXAS), HOLLY SUGAR
MANAGEMENT, PERCOLATION, *MQDFL
EMATICAL MODELS, AQUIFERS, MODEL
ER, #GROUNUWATER RECHARGE,
ION, ^MATHEMATICAL MODELS,
ON, AGROUNDWATER MOVEMENT,
TECHNIQUES, INFILTRATION,
SEEPAGE, UNSATURATED FLOW, MODEL
, WELL REGULATIONS, PERCOLATION,
SURFACE DRAINAGE, SHALLOW WELLS,
ROUND WATER, PATH OF POLLUTANTS,
INJECTION WELLS, WASTE DISPOSAL,
ES, OIL INDUSTRY, STORAGE TANKS,
ON, ION TRANSPORT , PENNSYLVANIA,
TER MOVEMENT, PERCOLATING WATER,
AL DECISIONS, OIL, OIL INDUSTRY,
ROUNDHATER, UNDERGROUND STREAMS,
ROUNDWATER, UNDERGROUND STREAMS,
OUND STREAMS, PERCOLATING WATER,
WATER SUPPLY, PERCOLATING WATER,
CTS, RIPARIAN LAND, PERCOLATION,
WASTES, HYDRAULIC CONDUCTIVITY,
RIGHTS, WATER LAW, GROUND WATER,
f SUBSURFACE WATER, PERCOLATION,
PERCOLATION, SUBSURFACE RUNOFF,
ODEL STUDIES, DRAINAGE PROGRAMS,
ION, AQUIFERS, WELL REGULATIONS,
STATE
STATE
STATE
STATE
MODEL
MODEL
MODEL
MODEL
STORAGE,
STORAGE,
STORAGE,
STANDARDS, WATER POLLUTION EFFECT
STANDARDS, REGULATION, WELL PERM I
STARK COUNTY(OHIO).:
COLLEGE!PENN), SANITARY LAN
GOVERNMENTS, POLLUTION ABAT
GOVERNMENTS, LOCAL GQVERNHE
GOVERNMENTS, STATE JURISDIC
STATE JURISDICTION, OIL INDUSTRY,
STATES, ^REVIEWS, METHODOLOGY, SA
STATISTICAL MODELS, STATISTICAL M
STATISTICAL METHODS, WATER STORAG
STO: / DIFFUSION, GRAVITATIONAL W
STORAGE TANKS, SUBSURFACE DRAIMAG
STORAGE, AQUIFERS, WATER REUSE, A
GRAPHICAL SOLUTIONS.:
LEGAL ASPECTS.: /TCHES,
SOIL PROPERTIES, MOISTUR
STORM RUNOFF, JAMES RIVER(MO), WI
STORM RUNOFF, ODOR, SUBSURFACE RU
STREAM, GRDUNDWATER RECHARGE, TRA
STREAMFLOW, SURFACE-GROUNDWATER R
STREAMS, DEEP PERCOLATION, GROUND
FISH, LAND, ECOSYSTEMS,
GROUNDWATER MOVEMENT, PA
GROUNDWATER, JUDICIAL DE
JUDICIAL DECISIONS, POLL
LAKES, PONDS, TIDAL V/ATE
PERCOLATING WATER, SUBSU
SUBSURFACE RUNOFF, REASO
SUBSURFACE RUNOFF, REASO
STREAMS, SOIL TYPES, PERMEABILITY
STRICT LIABILITY.:
STRUCTURE, INFILTRATION, SOIL PRO
STUDIES.: / HIGrt PLAINS*TEXAS), P
STUDIES, -COMPUTER PROGRAMS.: /G,
DRAINAGE PROGRAMS, SUBSU
HYDRAULIC MODELS, OIL WA
HYDRAULIC MODELS, TRACER
LABORATORY TESTS, PATH 0
MATHEMATICS, EQUATIONS,
STUDIES, SATURATED SOILS.: /ION,
SUBSURFACE DRAINAGE, SHALLOW WELL
WATERS, LEGAL ASPECTS.
FLOW, GASOLINE, WATER
WATERS.: /POLLUTANTS,
DRAINAGE, U NO ER FL 0W, U
DRAINAGE, WATER QUALIT
WATERS, DIFFUSION, GRA
DRAINAGE, WATER POLLUT
RUNOFF, REASONABLE USE
RUNOFF,
WATERS,
WATERS,
STREAMS,
STREAMS,
STREAMS,
STREAMS,
STREAMS,
STREAMS,
STREAMS,
STREAMS,
STUDIES,
STUDIES,
STUDIES,
STUDIES,
STUDIES,
SUBSURFACE
SUBSURFACE
SUBSURFACE
SUBSURFACE
SUBSURFACE
SUBSURFACE
SUBSURFACE
SUBSURFACE
SUBSURFACE
SUBSURFACE
SUBSURFACE
SUBSURFACE
SUBSURFACE
SUBSURFACE
SUBSURFACE
SUBSURFACE
SUBSURFACE
REASONABLE USE
UNDERGROUND, L
JUDICIAL OECIS
WATERS, UNDERGROUND ST
DRAINAGE, TRANSMISSIVI
WATER, PERCOLATION, SU
RUNOFF, SUBSURFACE STR
STREAMS, DEEP PERCOLAT
DRAINAGE, WATER MANAGE
SUBSURFACE DRAINAGE, WASTE TREATM
W70
W71
w 10
W71
W69-
W70-
W71-
W71-
W71-
W70-
W70-
W70-
W70-
W70-
W69-
W69-
W68-
W71-
W71-
W71-
W70-
W70-
W70-
W71-
W 7 1 -
W70-
W69-
W70-
W70-
W70-
W71-
W70-
W 7 1 -
W71-
W71-
W71-
W71-
W69-
W70-
W71-
W69-
W69-
W69-
W68-
W69-
W70-
W71-
W70-
W70-
W70-
W70-
W70-
W71-
W71-
W70«
W70-
W70-
W70-
W71-
W71-
Q8025
04742
07193
01204
05370
02896
13521
13521
08907
03102
03102
03026
07631
03102
00248
06118
00058
09154
09154
03543
06102
00521
04193
01043
01043
08025
05370
07631
08049
08050
05094
00521
06514
12122
09936
01932
10325
07554
09548
01930
02681
06117
06117
00627
03212
07631
01204
08026
07632
08049
08050
07631
01028
01043
07766
00521
00521
00521
01932
10157
152
-------
ON) CONTROL , POLLUTION
, *FISHKILL, STORM RUNOFF, ODOR,
ILTRATJON, GRfJUwD»''ATER MOVEMENT ,
ION, OIL INDUSTRY, SALINE '-'ATFR,
PCV'ONAS, MYCOBACTERIUM, BACILLUS
AS) , PARMEK COUNTY(TEXAS) , HOLLY
'''ATER
VATER
WATFR
'''ATER
'"'ATER
''ATER
HATER
BICARBONATE, FLUOR IDF, NITRATE,
FIELDS, CESSPOOLS, SEPTIC TANKS,
SSPOOLS, SEPTIC TANKS, SULFATES,
ATE^/ -SURFACTANTS, -ALKYBE^ZENE
T, GROUNOHATER, HISCQ^SI<> , '/'ATER
ATE^ LEVELS, *HATER WELLS,
CTS, COMPENSATIOv, BKINES,
TERS, DRILLING, OIL HELLS,
NG, AQUIFERS, WATFR TABLE
, IRRIGATION, RETURN FLOW
-SOIL, GRQIJMDHATER BASINS
WELL CAS INGS, GROUNDWATER
UNDERGROUND, GROUNDWATER
TER QUALITY, WATER LEVELS, l«iATED
, *GROUNDHATFR, -SURFACE MATERS,
TER, SOIL PROFILES, WATER TABLE,
RUNOFF, REASONABLE USE, DAMAGES,
RUS, NUTRIENTS, *LGAE, NITRATFS,
RQLJMDWATER MOVEMENT, HYDRAUL ICS,
S, EXPERIMENTAL RECHARGE PROJEC/
S, EXPERIMENTAL RECHARGE PR^JEC/
IDAL WATERS, WELLS, GROUMDHATER,
ECHARGE, DISCHARGE, GROUNDHATER,
P HIC A TIQM, NIT RO GE N, P HO S P HO RU S,
-SOLID HASTES, *'-'ASTE DISPOSAL,
OIL HATER MOVEMENT, GROUNDWATER,
G, HATER HELLS, MUNICIPAL HATER,
T, *FILT/\TION, ALLUVIA CHANNELS,
ROLOGIC CYCLE, OVERDRAFT, HELLS,
*OKLAHOMA, SALINITY, STREAK FLOW,
BRINES, HATER SUPPLY, BOUNDARIES(
^SOIL-'-'ATER ENVIRONMENT, AN ION 1C
WATER SUPPLY, WATER UTILIZATION,
EOLOGY, HATER POLLUTION CONTROL,
US, SURFACE HATERS, PERCOLATION,
LITY, BIOCHEMICAL OXYGEN DEMAND,
RIENTS, SEPTIC TAWKS, EFFLUENTS,
: AQUIFER
NVIRON^ENT, AN I ON 1C SURFACTANTS,
RFACES, -LEACHING, -SALINE HATER
*GRCJUNDHATER MOVEMENT, DRAINAGE
GROUNDWATER, #PIEZOMETRY, #i>'ATER
L PROPERTIES, WATER WELLS,
NATION, OBSERVATION WELLS
MIHATION, WATER POLLUTION
COLORADO, DENITRIFICATION,
ROUNDWATER, SOIL PROFILES,
AT I ON, LEACHING, AQUIFERS, WATFR
, SCUM, WEEDS, NUTRIENTS, SEPTIC
ION CONTROL, GROUNDWATER, SEPTIC
, DAMAGES, OIL INDUSTRY, STORAGE
SPOSAL FIELDS, CESSPOOLS, SEPTIC
LUTION, INFILTRATION, ANALYTICAL
WATER
MATER
HATER
HATER
HATER
SUBSURFACE HATERS, PERCOLATING HA
SUBSURFACE RUNOFF, GROUNDHATER MO
SUB-SURFACE MOVEMENT, CONSUMPTIVE
SUBSURFACE HATERS, GROUNDWATER, P
SUBTILIS, BACILLUS MYCOIDES, BACI
SUGAR STUDIES.: / HIGH P!_AINS(TEX
SUGARS.:
SULFATE, SILICATE, GROUND HATER R
SULFATES, SULFIDES, PERCOLATING H
SULFIDES, PERCOLATING MATER, INF I
SULFONATES, -DETERGENTS, AGROUNDW
SUPPLY.: / WASTES, SOIL MA-VAGEMFN
SUPPLY, AQUIFERS, ION EXCHANGE, P
SOUNDARIES(SURFACES), WEL
FARMS, WATER POLLUTION EF
GASES, CARBON DIOXIDE, ME
LIVESTOCK, SEWAGE, INFILT
MUD, BENTHOS, HYDROGEN, R
PERCOLATING WATER, SUBSUR
SEEPAGE, INFILTRATION, HA
HATER UTILIZATION, SURVEY
RUNOFF, RIPARIAN RIGHTS,
F/\PM BASTES, AERO
GASOLINE, HATER P
SUPPLY,
SUPPLY,
SUPPLY,
SUPPLY,
SUPPLY,
SUPPLY,
SUPPLY,
SUPPLY,
SURFACE
SURFACE
SURFACE
SURFACE
SURFACE
SURFACE
SURFACE
SURFACE
SURFACE
SURFACE
SURFACE
RUNOFF,
RUNOFF,
RUNOFF,
BASE FLOW PERCOL
RELATIONSHIPS
RELATIONSHIPS
RUNOFF, STREAMS, SOIL TYP
SPREADING, RECHARGE BASIN
SPREADING, RECHARGE BASIN
WATERS, SEEPAGE, PERCOLAT
WATERS, AQUIFERS, FLOW RA
WATERS, PFRCOLATIO^, SUSP
WASTERS, GROUNDHATER, GAR
SURFACE WATERS, TESTING, TEST PRO
SURF ACE-GROUNDSATER RELATIONSHIPS
SURFACE-GROUNDWATER
SURFACE-GROUNDHATER
SURFACE-GROUNDSATER RELATIONSHIPS
SURFACES), WELL CASINGS, SALINE H
SURFACTANTS, SYNTHETIC. DETERGENTS
SURVFYS, GFOPHYSKS.: /R LEVELS,
SURVEYS, LEACHING, GEOLOGY, GROUN
SUSPENDED LOAD, GROUNDWATER, ACHJI
SUSPENDED LOAD.: /VELS, WATER OUA
SWAMPS, FOREST SOILS, MINNESOTA,
SWEETENING, AQUIFER DESALINATION.
SYNTHETIC DETERGENTS.: /L-WATER E
SYSTEMS, ^GROUNDHATER MOVEMENT, D
SYSTEMS, HYDRAULIC MODELS, MATHEM
TABLE, -SURFACE-GROUNDWATER RELAT
ENVIRONMENTAL EFFECTS, '-'AT
INFILTRATION.: /IL CONTAMI
OXIDATION LAGOON, IRRIGATI
PERCOLATION.: / AQUIFERS,
SURFACE RUNOFF, EARN1 WASTE
WATFR SUPPLY, GASES, CARBO
EFFLUENTS, SWAMPS, FOREST
MANAGEMENT.: /WATER POLLUT
SUBSURFACE DRAINAGE, UNDER
SULFATES, SULFIDES, PERCOL
TABLE,
TABLE,
TABLE,
TABLE,
TABLE,
TABLE,
TANKS,
TANKS,
TANKS,
TANKS,
H71-
W 1 1 -
H71-
W69-
W -/ 1 -
W68-
H69-
H68-
K68-
H71-
H69-
H7J-
!/ 7 1 -
'/,' 70-
H71-
H69-
H 7 ] -
H70-
H70-
09154
13645
13521
0783B
12122
01269
03197
01010
01010
01291
06443
02611
03230
13521
06011
06435
0783*
W69-
H70-
H71-
H 7 1 -
W69-
H69-
W69-
W70-
H70-
H 7 1 -
Nil-
H 7 1 -
VO1-
'.'70-
TECHNIQUES, SOIL CONTAMINATION EF
H71-
W70-
W7Q-
H70-
H70-
H69-
H70-
W71-
W70-
W71-
W71-
W70-
W 'i I -
W71-
H71-
V.' 7 1 -
W69-
W7Q-
H7D-
W 7 1 -
H70-
W68-
H70-
07632
05466
00532
09721
08049
06443
05094
05328
05327
05370
09637
04504
05094
06514
02909
17410
0053?
06102
03230
01291
05466
07193
04504
07114
04] 93
01932
01291
01932
01932
07766
04121
03543
03542
02036
09721
06011
04193
10372
0763]
01010
01291
153
-------
N, CHEMICAL ANALYSIS, ANALYTICAL
DWATER, -OIL WASTES, ^SEPARATION
MS, INCINERATION AIR POLLUTION1,
CROORGANISHS, CHEMICAL ANALYSIS,
FUSION.:
EQUIPMENT, LEASES, DAMAGES, LAND
DROLOGIC DATA, LEGISLATION, LAf'O
S , ENV I P.UNM FMTAL PH|. L UT I OM .:
CHARACTERISTICS, SOIL ANALYSIS,
DWATER, SURFACE HATERS, TESTING,
NT, GROUMDWATER, SURFACE CATERS ,
EMENT, MODEL STUDIES, LABORATORY
GROUNDWATER MOVEMENT, LABORATORY
GE, NUMERICAL METHOD, LABORATORY
POSAL, THERMAL PROPERTIES, MOOEL
IRRIGATION DRACTICES, LEACHING,
IGH PLA I'\'S( TEXAS ), PARMER COUNTYf
*QGALLALA AQUIFER, HIGH PLAINS(
ORUS? ALFALFA-6RDMEGRASS, SPRING
TEMPERATURE PROFILES,
TRANSM ISSIVITY.
TRANSMISSIVITY,
, *DISPERSIOV, UASTP DISPOSAL,
ATHFMATICAL MODELS, PROBABILITY,
, RIVERS, STREAMS, LAKES, PONDS,
ISSIVITY, HEAD LOSS, OARCYS LAW,
OSE, HYDROGEN 1ON CONCENTRATION,
TRITIATED WATER(
MODEL STUDIES, HYDRAULIC MODELS,
AL MODELS, CURRENTS(WATFR)? VASS
LITY, THERMODYNAMICS, FLOW, MASS TRANSFER,
F, HISTORY, SOIL ANALYSIS, WATER TRANSFER,
TIOMS.:
NDUCTIVITY, SUBSURFACE DRAINAGE,
IL WATER, SOLUBILITY, SOIL '-'ATER
NT STREAM, GROUNDWATER RECHARGE,
-SALT HATER J R»IGATIPM, SALT
LOW, ADSORPTION, ADSORPTION, ION
VEMENT, KARST, INF ILTRATION, ION
WATFR POLLUTION SOURCES, SEWAGE
WATER POLLUTION SOURCES, SEWAGE
NT, WATER POLLUTION, *SOIL '-'ASTE
ASTE WATER DISPOSAL,
>VT, WATER POLLUTION,
ASTE WATER DISPOSAL, WASTE WATFR
READING, -WATER REUSE, ^TERTIARY
INFILTRATION, FILTRATION, SEWAGE
E/ ^OXIDATION LAGOONS, -TERTIARY
LUTION, TEMPERATURE, WASTE WATER
LLUTION CONTROL, WATER POLLUTION
QUALITY CONTROL, '-'ATER POLLUTION
GE, WASTE TREATMENT, WASTE WATER
POSAL, ^MUNICIPAL WASTES, -WASTE
ILTRATION, *PIT RFCHARGE,
AOUIFFRS, S INKS , CITIES,
IONS, SUBSURFACE DRAINAGE
TRICT LIABILITY.:
), NUISANCE.:
P LFACHING.:
HYDRAULIC LOADING, INFILTRATION,
S, SURFACE RUNOFF, STREAMS, SOIL
TECHNIQUES, BIOASSAY, SOIL STRUCT
TFCHMIOUES, INFILTRATIONS MODEL S
TEMPFRATURE, WASTE WATER TREATMEN
TEMPFRATURE, NITRATES, PLANTS, AM
TEMPFRATURF PROFILES, THERMAL DIF
TENU*E, JUDICIAL DECISIONS, LEGIS
TENURF, LEPAL ASPFC: /DAMAGES, HY
TEST HOLES, UNIVERSITY OF ILLINOI
TEST PROCEDURES, CHEMICAL ^ROPERT
TEST PROCEDURES, METHODOLOGY, WAT
TF^TIK'G, TEST PROCEDURES, METHODO
TESTS, PATH OF POLLUTANTS, WATER
PER^EAMETERS, SANDS, CHLOR
PERME ABILITY, POROSITY, PO
SATIJRATION ZONES, SEEPAGE,
/NALYSIS, WATER TRANSFER,
HOLLY SUGAR STUDIES.: / H
PARMER COUNTY( TEXAS) , HOL
FERTILIZER-NITROGEN.: /SPH
THERMAL DIFFUSION. :
THERf'AL GRADIENTS.:
THERMAL PROPERTIES, MODEL TESTS,
THER^ODYNAMICS, FLOW, MASS TRAMSF
TIDAL WATERS, WELLS, GROUND WATER,
TIME LAG, NITROGEM COMPOUNDS, NIT
TOXICITY.: /, GROUND WATER, CELLUL
TRACER), MINE DUMP LEACHING.:
TRACERS, IN JECTIOM WELLS, ART IF 1C
TRANSFER, AQUIFERS. : / MATHEMATIC
DIFFUSION, MIXING, DISP
IRRIGATION PRACTICES, L
TRANSIENT STORAGE, GRAPHICAL SOLU
TRANSMISSIVITY, HEAD LOSS, DARCYS
/GROUND WATER , SO
i-'ATER LEVEL FLUCT
W71-
W71-
W69-
W69-
TESTS,
TESTS,
TESTS,
TEXAS.
TEXAS )
TEXAS)
THAWS,
WASTE
#50 IL
MATER
"ASTE
*WATER
SEWAGE
''ASTE
TRANSPORT.
TRANSPORT.
TRANSPORT,
TREATMENT,
TREATMENT,
TREATMENT,
TREATMENT,
TREATMENT,
TREATMENT,
TREATMENT,
TREATMENT,
TREATMENT,
TREATMENT,
TREATMENT,
TREATMENT,
TREATMENT,
TREATMENT,
TREATMENT,
TREATMENT,
/ED FLOW, SATURATED F
PENNSYLVANIA, SUB SURF A
WASTE WATER DISPOSAL,
WASTE WATER DISPOSAL,
SOIL PERCOLATION, *WAS
WATER POLLUTION, ;:;SOIL
SOIL PERCOLATION, *WAS
WATER POLLUTION, *SOIL
INF ILTRAT I ON, F ILTRAT I
SEWAGE DISPOSAL, HYDRO
=;=SLUDGE DIGESTION, ANA
OHIO.: /AT I ON, AIR POL
WELL PERMITS, ADM IN 1ST
ADMINISTRATIVE AGENCIF
i-lATER POLLUT ION, PERCO
^UNITED STATES, *REVIE
*F I LT AT I OM , ALLUV I A CH
S EW ER S , AERATION, M ON I
TREATMENT, WASTE WATER TREATMENT,
TRFS'JASS, NEGLIGENCE, NUISANCE, S
TRESPASS, I NJUNCTTON^t PROHIBITORY
TRITTATED i-'ATER ( TRACER ), MINE DUM
TUCSHN BASJK', PROCESS-RESPONSE MO
TYPC-S, PERMEABILITY, FLOODS, EVAL
W71
W/0
W71
W71
W7 l
W70
W70
W69
W69
H71
W" 1
W71
H69
W69
l-'69
W69
W71
W69
W70
k'68
W71
F69
H69
W71
W71
l-'69
K'70
W71
K'7l
W71-
K'70-
W71-
W7 1-
!>'71-
W69-
W69-
W69-
lr'69-
W70-
W70-
K'71-
W71-
W/l-
W71-
W71-
W71-
W7 1-
W7 1 -
W7 l-
W70-
W69-
W71-
W69-
W71-
06514
01930
07118
07838
00651
08055
11692
06322
07887
06514
06514
09548
01904
00651
00651
12122
1212?
12122
09721
00651
08921
00651
11776
05370
07766
01269
11255
07554
08921
11776
12122
00248
07766
07887
03543
06063
10058
03 204
01324
01205
05327
05328
05328
05327
04712
04712
07118
07118
10157
10446
10157
08907
12410
09154
10157
00521
06117
11255
03197
05094
154
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UNDERFLOW.: /UREMENT, DI SCHARGEf W
UNDERFLOW, ARTEST AM '-'ELLS, STREAM
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UNDERGROUND, LEAKAGE, PERCOLATION
UNDERGROUND STREAMS, GROUNDHATER
UNDERGROUND STREAMS, SUBSURFACE R
UNDERGROUND STREAMS, SURSURFACF R
UNDERGROUND STREAMS, PERCOLATING
UNDERGROUND, GROUND^ATER , HATER S
UNDERGROUND, HELLS, SAL INF WATER
UNIVERSITY OF ILLINOIS, EN V I ROW E
UNSATURATED FLOH, SATURATED R.O'^S
UNSATURATED SOIL.:
IP-SATURATED FLOW, MODFL STUDIES,
UPPER RIO GRANDE, ^ALT BALANCE.:
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USE, *GROUMDW/\TFR, #SURFACF WATER
USE, ^OKLAHOMA, SALINITY, STREA^F
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USE, ARTIFICIAL USE, RIPARIAN LAN
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USE, DOMESTIC HATER, POLLUTION A ^
USE, NATURAL FLOW DOCTRINE, REASO
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USSR, RADIAL DIFFUSION EQUATIONS.
UTILIZATION, SURVEYS, GEOPHYSICS.
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VALLEY.:
VALLEY.:
VALLEY.: /T HOLES, ANNUAL PRECIPI
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VALL:-Y( CALIF) . :
V ALL FY{ COLO) .: NATIVE GRASSES,
''. OHIO WATER COMPANY, NETWORK AN
WASTE DILUTION, MATER POLLUTION C
HASTE DISPOSAL, GROUNDHATER MOVEM
WASTE DISPOSAL, THERMAL PROPERTIE
HASTE DISPOSAL, SUBSURFACE HATERS
WASTE DISPOSAL, DISPOSAL, WASTES,
WASTE DISPOSAL, UNSATURATED FLOH,
HASTF DISPOSAL, GARBAGE DUMPS.: /
WASTE DISPOSAL, GROUNDWATER, PERC
HASTE DISPOSAL, LEGISLATION, WELL
WASTE DUMPS, WATER POLLUTION, PRE
WASTF DUMPS, WASTE STORAGE, SOIL
WASTE RECHARGE.:
WASTF STO: / DIFFUSIONS GRAVITATI
WASTE STORAGE, SOIL PROPERTIES, M
WASTE STORAGE, LEGAL ASPECTS.: /T
HASTE TREATMENT, SOIL PERCOLATION
WASTE TREATMENT, SOIL PERCOLATION
WASTE TREATMENT, HASTE WATER TREA
HASTE WATER TREATMENT, WATER POLL
WASTE WATER TREATMENT, OHIO.: /AT
W 7 1
H 7 0
W 7 0
W 7 n
H 7 0
W71
H7n
W 7 0
W 7 0
H70
W 7 1
H 7 0
H 7 0
1-169
H 6 9
H 7 0
M 7 i
H70
W 7 0
L' 70
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W70
H '/ 1
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H70
H70
H 7 0
W 7 1
W69
W 7 0
V' 7 0
W 7 1
W 7 1
VI 1 1
V69
W 7 0
W 7 1
1-170
W69
W69
H69
W 6 9
W69
1-' 7 0
H 7 0
W 7 1
W 7 1
W 7 1
W71
W68
W 6 9
W 7 0
W68
W69
H69
H 6 9
W71
W 7 1
W 7 1
13645
07766
08025
07631
07631
01043
OH049
0763T
0763?
0632?
-10058
0?681
02681
08662
06435
0053?
0610?
03102
02896
08049
13645
02896
08050
00532
02896
00532
07887
03212
05466
00532
1 2410
02036
03543
01076
05466
04548
04488
02611
03178
02681
00651
03212
06011
10058
07194
11692
11724
05094
00058
08621
08026
00058
06118
05327
05328
10157
10157
07118
155
-------
SE'.-'AGE EFFLUENT, C.O.D., B.O.D.,
EFFLUENT, *WASTE WATER DISPOSAL,
EFFLUENT, #WASTE '-'ATER DISPOSAL,
UTIPN SOURCES, SEWAGE TREATMENT,
UTIPM SOURCES, SEWAGE TREATMENT,
TIOM, INDUSTRIAL HASTESt SEWAGE,
GROUNDWATER MOVEMENT, NITROGEN,
WASTES, -HASTE DISPOSAL, SURFACE
CATTLE HASTFS, FEEOLOT
ORGANIC CHEMICAL
TRIAL PASTES, ALGAE, PONDS, FARM
SE, ^RECLAIMED WATER, #Ml)MICIPAL
ICAL OX/ #WATER POLLUTION, #WOOn
R POLLUTION SOURCES, PATH/ *FARM
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*'"'AT
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WASTFS,
WASTES,
''ASTFS,
WAST-S,
WASTES,
KASTFS,
WASTES,
WASTES,
''ASTES,
W ASTFS,
WASTES,
WASTFS,
HASTES,
WASTFS,
W A S T F S ,
WASTES,
WASTES, MUNICIPAL WASTES, SEHAGF
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WASTES, SEHAGE, '-'ASTE l'ATER( POLLU
WASTFS, SEWAGE, '-'ATER DUALITY CON
W69-03197
W69-05327
W69-05328
W69-08620
W71-01205
W70-00521
P70-00665
W7 1-0 5094
W70-00665
W69-07114
W"/ 1-06435
K'69-08620
W68-01269
W70-00665
W71-03543
W7 1-03542
Iv71-00194
W70-09637
W71-07194
W6 9-05370
W70-08026
H71-] 3521
W71-13 724
W7 1-02036
W"/ 1-0 1930
W") 1-05094
W' 1-04121
W71-08907
W69-09721
!-'" 1-06435
W~ 1-09154
W70-06011
W70-08049
^'71-09154
W 7 0-1 00 5 8
W70-08049
K7 0-0066 5
W68-0005«
W71-08907
W"?1-08?1-Q
W70-07766
W69-03178
W71-08907
'''; 1-11 356
l-.'7 0-0 65 7?
W71-3 1255
W71-10446
W70-08049
W71-10372
W 6 9- OS 921
'"'7 1-13645
W7 1-1 1692
W69-05370
W70-00521
W71-10446
156
-------
HATER,
*"ASTF
*i-'ASTE
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L AT I ON, L EACH IMG, D RAINA GF, FARM
DIS POSAL , - IRRI GAT I ON , *CHEM 1CAL
*HELLS, JUDICIAL PEC IS ION'S, OIL
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L STUDIES, HYDRAULIC MODELS, OIL
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TANT IDENTIFICATION, ADSORPTION,
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GREAT MIAMI RIVER, S .'"'. OHIO
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SOURCES, S EWAGE TREATMENT,
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COMPANY, NETWORK ANALYSIS.:
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R LAW, GROUND WATER, SUBSURFA
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R LEVELS, V.'ATER DUALITY, RIOC
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-06443
W69-07114
W69-06118
W69-05370
W68-00058
W70-06011
W11-01043
V71
W71
V.171-
W70-
W70-
W69-
W69-
V.1" 1 -
W71-
W69-
l-.' 7 1 -
11724
11692
01043
02896
05466
026] 1
08620
08044
04121
02611
06063
10157
W69-05327
W69-07114
W69-05328
|-'69-07375
W71-01324
01205
01291
01932
08055
03230
03230
04559
13521
10446
OS044
0102.°.
08026
06063
00521
00627
02611
071
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W71
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05466
03543
08073
07194
0193?
04504
00521
00979
07375
00058
OK620
00627
W7 1-0 104:
V,17 0
W11
W71
K 7 1
W'l
10058
06514
10325
04742
07194
157
-------
F. DUi-'PS, LANDFILLS, WASTE DUNPS,
, COMPUTER PROGR'V'S, C AL I FO^M 1 1\ ,
NATION, FERTILIZERS, #*' ITKATFS ,
ER,
ANNO. IA, SOIL CfMTA" F :AT I 0- ,
TRUS IUM , #0 JL XASTES , *REMFHIES ,
TES, -REMEDIES, "ATER POLLUTION,
HA. 'GE , *"ATFR UUA L I T Y , #1 RR IGA T/
SOURCES, #OIL HASTES, ^R^EHIES,
S, *REf' ED IES, INDUSTRIAL "A ST ES ,
HI"C, EROSION, NITROGEN, RUNOFF,
G I ME E RING, LANDFILLS, HYD ROL OGY,
, '.'ELLS, SALINF NATER INTRUSION,
, S^'.'AGE, "ATER DUALITY CONTROL,
REATNENT, I'ASTE !,,'*TFR TREATMENT,
FD "ATER QUALITY, UNDER SEEPAGE,
OIL VELLS, ',/ATfcR SUPPLY, FARNS,
ATFRS, -V'ATER POLLUTION CONTROL,
FARNS, "ATER POLLUTION EFFECTS,
s, HYDRAULIC MODELS, OIL "ASTES,
, "ELLS, I'PAIKFD "ATER QUALITY,
POLLUT ION, POLLUTION ABATEMENT,
ATO^Y TESTS, PATH OF POLL UT''1" ITS,
. AGES, SURFACE RUNOFF, GASOLINE,
: POLLUTIO" CO-'TROL, LEACHING,
M priCisir.rs, PIL --^STES,
' IA, SUtiSURFACE ORAT-'AGE,
'..'ATER
"ATER
"'ATER
!-: A T E R
V'ATER
"ATER
1'ATEQ
"ATER
"ATFP
I .' A T E R
'.'ATEFi
1'ATER
"ATER
I;ATER
''ATE*?
l-'ATEP
"ATER
! 'ATE R
"ATER
V'ATER
"ATEP
l.'ATER
\ ' A T E n
"ATEP
1 ! A T E R
'ATEk
"ATEP
\ ATE!1,
"ATER
"ATER
P
''AT-R
i i t, -p i-
, i\ \ c
WATER
"ATER
"AT E R
V'ATER
N A T E R
"ATER
"ATER
"ATER
"ATEP
V'AThR
A T E R
'
1 ATE-;
"ATER
UATEP
H A T E P
V'ATER
US I P. ', "ATER POL L UT I ON , Ir: P A I R \- n " ATE R
FR POLLUTION EFFECTS, IMPAIRED Vi
POLLUTION, PRECIPITATION!AT
POLLUTION SOURCES, LEACHING
POLL UTION, NITROGEM, i J ITR IT
POLLUTION, "ATE^ TAKLE, OX I
POLLUTION, JUDICIAL DEC IS 10
POLLUTION EFFECTS, POLLUTIO
POLLUTION SOURCES, -ION EXC
POLLUTION, "ATER POLLUTION
POLLUT ION, POLLUT IQtl A^ATE'i
POLLUTION CONTROL, GROUNDS
POLLUTION, PATH OF POLLUTAV
POLLUTION SOURCES, fllNERALO
POLLUTION TREATN;E^IT, ADf'.P'I
POLLUTION, PFRCOLATI.MG "ATE
POLLUTION, INDUSTRIAL WASTE
POLLUTION EFFECTS, V.'ATER PO
POLLUTION TREATMENT, UELL P
POLLUTION SOURCES,: /UPPLY,
POLLUTION SOURCES.
POLLUTION CONTROL,
POLLUTION EFFECTS,
POLLUTION SOURCES,
POLLUTION SOURCES,
POLLUTION SOURCES,
POLLUTION SOURCES, S El'AGE T
POLLUTION EFFECTS, STREAMS,
POLLUTION, IMPAIRED HATER O
JOLLUTIOr! SOURCES.: /LEACHI
1-05094
'nl
i. ^ j.
/STu
DAC.AGES,
POLLUTAN
SELF-PUR
Mil-IE "AT
POLLUTION SOURCES, LYSI-ETE
POLLUTION, POLLUTANTS, |_EGA
PULLi'TIUH SOURCES, JUDICIAL
POLLLTlOiN SOURCES, PIPES,
POLLUTIO!
POLLUTION
POLLUTION
EFFECTS,
EFFECTS,
SOURCES,
D
POLLUTION SOURCES,
ir.PAI
LEGAL AS
GROUMD"A
SEUAGE T
POLL'. 'T ION , n /\ r.i AGE, J UP 1C I A L
POLLUTION, SEEPAGE, GKraj; D'-1
POLLUTION CONTROL, LEACH IMG
POLLUTION, *SOIL "ASTh TREA
POLLUTION SOURCES, SOLID '-'A
POLLUTIC^J SOURCES, NICROHRG
POLLUTION SOURCES, INDUST^I
POLLUTION, *sniL V.'ASTE TREA
POLLUTION.: /ES, *RACTERIOP
POLLUTION EFFECTS, \IUTRIEVT
POLLUTION, SNOU, RUNOFF, DR
POLLJTI ON CONTROL, SURVEYS,
POLLUTION, ABSORPTION, *LEA
DDLLUTION CONTROL, PUBLIC H
SOU^C^S, l.'ATER PO
SOURCES. : /SAMITA
ATFR LEVELS, "ATE
IOCHFHTCAL OXYGEN1
DUALITY, SOIL CONTACT NATION
DUALITY CONTROL, DOMESTIC "
'U/-.LITY, SALINITY, PEKCOLAT
DUALITY, "ATEP POLLUTION SO
QUALITY, POLLUTANTS, INDUST
QUALITY, PERCOLATION, PE\'FT
POLLUTION
POLLUTION
QUALITY,
UUALT TY ,
V'71-0354-2
K71-13521
1/71-11724
VI1-09936
!-'7 1-11724
U71-1169?
-10372
-08907
VI1-10446
1-17 1-1044 6
U71-ini57
I-17 1-13645
W71-13521
-10157
.-13521
"71-10325
'r'71-11724
W71-11692
U70-09548
V70-08049
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U70-08026
"70-0^025
158
-------
ASTES, MUNICIPAL "AST^S, SE'.'AGE,
NE HASTES? GEOLOGY, GROUNDHATER,
AL, LEGISLATION, HELLS, IMPAIRED
OVEMENT, LEACHING, INFILTRAT ION,
^DAMAGES, -WATER WELL, IMPAIRED
ES, ADMIN ISTRATIUN, GROUND'.M TER ,
Gt TEST PROCEDURES, METHODOLOGY,
TRY, ABSORPTION, SOIL MECHANICS,
TION, WATER MANAGEMENT, IMPAIRED
ATION, *HATER POLLUTION EFFECTS,
, DRAINAGE EFFECTS, GROUNDHATER,
TRATE, SULFATE, SILICATE, GROUND
V'ASTE
N, INDUCED INFILTRATION, -GROUND
N, INDUCED INFILTRAT ION , -GROUND
ATMEMT, SOIL PERCOLATION, *VASTE
ATMFNT, SOIL PERCOLATION, *WASTE
ROGEOLOGY, GROUNOWATfcR MOVEMENT,
ETHODS, WATER STORAGE, AQUIFERS,
LOCAL GOVERNMENTS, LEGISLATION,
DERGROUND, LEAKAGE, PERCOLATION,
IMG, SHALLOW WELLS, GROUNDHATER,
RNIA, WATER YIELD, INFILTRATION,
CAL MODELS, STATISTICAL METHODS,
LEACHING, AQUIFERS, WATER TABLE,
NT, WATER QUALITY, WATER LEVELS,
LLS, WATER LEVELS, #WATER WELLS,
ONDS, -SOIL, GROUNDWATER BASINS,
NFLOW, UNDERGROUND, GROUNDWATER,
ELLS, WELL CASINGS, GROUNDWATER,
L ASPECTS, COMPENSATION, BRINES,
WATER, IRRIGATION, RETURN FLOW,
AGEMENT, GROUNDWATER, WISCONSIN,
ING WATERS, DRILLING, OIL WELLS,
R INTERFACES, BLEACHING, *SALINE
PERCOLATION, LEACHING, AQUIFERS,
IMG, GROUNDWATER, SOIL PROFILES,
OMTAMIMATION, OBSERVATION WELLS,
Y, SOIL PROPERTIES, WATER WELLS,
FERS, COLORADO, DEN ITRIFICAT I ON,
CONTAMINATION, WATER POLLUTION,
ER, SOIL WATER, SOLUBILITY, SOIL
N-CYCLE, HISTORY, SOIL ANALYSIS,
DRAINAGE, WASTE TREATMENT, HASTE
IR POLLUTION, TEMPERATURE, '-'ASTE
NT, *WASTE WATER DISPOSAL, UASTE
NT, *WASTE WATER DISPOSAL, WASTE
ITY, WATER LEVELS, WATER SUPPLY,
WATFR, REASONABLE USE, REMEDIES,
COLATING WATERS, *SHAILPW WELLS,
AL PIPES, WELLS, ARTESIAN WFLLS,
WATER QUALITY, SOIL PROPERTIES,
RS, GRAVELS, AOUITARDS, PUMP IMG,
ARGF, -'-'WATER REUSE, -CAL IFORNIA,
RESOURCES DEVELOPMENT, RECLAIMED
GROUNDWATER, WATER QUALITY, SOIL
, LEACHING, SALINE SOILS, SALINE
INDUSTRIAL WASTES, SEWAGE, '-.'ASTE
DWATER MOVEMENT, NITROGEN, MASTE
.: TRITIATED
\' A
HATER
W A T E R
WATER
HATER
HATtR
HATER
HATER
WATER
H A T E R
WATER
WATER
HATER
WATER
WATER
HATtR
WATER
WATfcR
HATER
HATER
HATER
WATER
WATER
WATER
HATER
HATER
WATER
HATER
WATER
WATER
WATER
WATER
WATER
HATER
HATER
HATER
HATER
WATER
WATER
WATER
WATER
WATER
HATER
WATER
WATER
WATER
WATER
WATER
WATER
HATER
WATER
HATER
HATER
HATER
WATER.
HATER.
HATER.
HATtR(
WATERt
UATER(
QUALITY CONTROL, HATEK POLL
QUALITY, COMPACTION, COMPRE
WATER POLLUTION CO
/R, GROUNDHATER M
UNDER SEEPAGE, HAT
INSPECTION, INSTAL
SOI!S, PESTICIDES,
SOIL PROPERTIES, W
WASTE DISPOSAL, GA
SALINITY, GROUNDWA
SHU WATER.: /ON IA
HYDROCHEMICAL FAC
QUALITY,
QUALITY.
QUALITY,
QUALITY,
QUALITY,
QUALITY,
QUALITY,
QUALITY,
QUALITY,
RECHARGE.
RECHARGE.:
RECHARGE, IRRIGATION, DEN IT
RECHARGE, IRRIGATION, DEN IT
RECLAMATION, INDUCED INFILT
RECLAMATION, INDUCED INFILT
RESOURCES DEVELOPMENT, RECL
REUSE, ARTIFICIAL RECHARGE,
RIGHTS, RIPARIAN RIGHTS, NA
RIGHTS, WATER POLLUTION SOU
SOURCES, DRAINAGE, RIPARIAN
SPREADING, PIT RECHARGE, SA
STORAGE, AQUIFERS, WATER RE
SUPPLY, GASES, CARBON DIOXI
HATER UTILIZATION,
AQUIFERS, ION EXCHA
MUD, BENTHOS, HYDRO
SEEPAGE, INFILTRAT!
PERCOLATING WATER,
BOUNDARIES*SURFACES
LIVESTOCK, SEU'AGE,
/ HASTES, SOIL MAN
SUPPLY, FARMS, HATER POLLUT
SYSTEMS, ^GROUNDWATER MOVEM
TABLE, WATER SUPPLY, GASES,
TABLE, SURFACE RUNOFF, FARM
TABLE, INFILTRATION.: /IL C
ENVIRONMENTAL EFFECT
PERCOLATION.: / AQUI
TABLE, OXIDATION LAGOON, IR
TRANSMISSIVITY.: /GROUNDHAT
TRANSFER, IRRIGATION PRACTI
HATER POLLUTION,
OHIO.: /AT I ON, A
WATER POLLUTION,
TER POLLUTION,
SURVEYS, GEOPH
PERCOLATING HA
HELLS, HATER POLLUTION, DAM
HELLS, INFLOW, UNDERGROUND,
HATER TABLE, ENVIRON
MUNICIPAL WATER, SUR
YIELD, INFILTRA TI ON, WAT E R
: /NDWATER MOVEMENT, HATER
: /ONIA, DRAINAGE EFFECTS,
: /TROL, SALTS, GROUNDWATER
POLLUTION), LEGAL ASPECTS.:
POLLUTION).: /RJENTS, GROUN
TRACER), MIME PUMP LEACHING
SUPPLY,
SUPPLY,
SUPPLY,
SUPPLY,
SUPPLY,
SUPPLY,
SUPPLY,
SUPPLY.
TABLE,
TABLE,
TREATMENT,
TREATMENT,
TREATMENT,
TREATMENT, h
UTILIZATION,
UTILIZATION,
WELLS,
HELLS,
H 71-
i-r/i-
H71-
W71-
W 7 1 -
W71-
W 7 1 -
H71-
W 71-
W71-
W 7 1 -
W69-
W69-
H69-
W69-
W69-
W69-
W70-
W70-
W70-
W70-
W69-
H70-
H70-
W70-
W 7 0 -
W69-
H69-
W70-
W71-
W71-
W71-
W71-
W71-
H 7 I -
W70-
W69-
H71-
H 71 -
W71-
H71-
H 7 1 -
W71-
W71-
W71-
H69-
W69-
W70-
W7Q-
W63-
H70-
W71-
W7l-
V. 70-
H70-
W71-
W70-
1',' 70-
W7Q-
H 71-
08907
11724
08044
13645
0474?
06514
04121
07194
06063
04548
Q3197
08620
0532ft
05327
05327
05328
0471?
03102
02896
07631
06118
05466
03102
06011
05466
02611
07838
0763?
01028
03230
06435
06443
13521
01932
06011
09723
03543
04].?]
0?036
03542
07887
12122
10157
07118
05327
05328
05466
00532
00627
07632
04121
02909
05466
04712
04548
09844
00521
00665
11255
159
-------
ANIOPIC SUK/ ^DETERGENT BEHAVIOR!
KATES, PLANTS, AMMONIA, HARDNESS I
S, MATHEMATICAL MODELS, CURRENTS(
DISCHARGE MEASUREMENT, OISCHARGE(
OIL FIELDS, SAL IMF WATER, SALINE
ACHING, -SALINE WATER S/ #SAL INE
WATER WELLS, GROUNDWATER, SALINE
N WATER, -RETURN FLOW, ^DRAINAGE
ING, -SOIL WATER r-'OVEMENT, *OILY
CIAL R/ *'MTER REUSE, -RECLAIMED
LUSH) COMOU/ PERCOLATION, GROUND
CIAL DECIS/ ^PENNSYLVANIA, *OILY
, *HATER POLLUTION, -PERCOLATING
T E R, -'DETERIORATION/ * I RRIGA TI ON
XTRACTION, ATOMIC ABSOR/ -GROUND
JUDICIAL D/ '"CONNECTICUT, *OILY
, ^SUBSURFACE HATE/ -PERCOLATING
, ^SUBSURFACE "ATE/ -PERCOLATING
ISLAND, #GASOLINE, -PERCOLATING
, OIL WASTES/ --ILLINOIS, #SALTNF
TIDN SOURCES, LEACHING, DRAINAGE
, WATER UTILIZATION, PERCOLATING
NT, MUNICIPAL WASTES, IRRIGATION1
LANDS, GROUNDWATFR, PERCOLATING
LIZATION, NITROGE^ SOURCES, WFLL
OLLUTION, SNOW, RUNOFF, DRAINAGE
TER, -SEEPAGE, DRILL HOLES, OILY
DOHA IN , PURL 1C HEALTH, DOMESTIC
POLLUTANTS
ITROGE/ PERCOLATING
SULFATES, SULFIDES, PERCOLATING
FF, UREAS, FERTILIZERS, DRAINAGE
ER POLICY, AQUIFERS, PERCOLATING
RIGHTS, COMPETING USES, DOMESTIC
TAiMTS, SOIL WATER MOVEMENT, OILY
WATER, DWELLS, GROUNDWATER, OILY
E, WATER POLLUTION SOURCES, MINE
MAGF, JUDICIAL DECISIONS, GROUND
WASTES, CALIFORNIA, PERCOLATING
ER LAW, GROUND WATER, SUBSURFACE
SPOSAL, GRUUNDHATER* PERCOLATING
EMENT, CONSUMPTIVE USE, DOMESTIC
CHING, SALT BALANCE, PERCOLATING
WATER, LEGAL ASPECTS, MUNICIPAL
, *WATER POLLUTION, ^PERCOLATING
WATERS, DIFFUSION, GRAVITATIONAL
LS, DRILLING, OIL FIEtDS, SALINE
, -SUBSURFACE DRAINAGE, DRAINAGE
, POLLUTION IDENTIFICATION, SOIL
ERS, PESTICIDES, NUTRIENTS, SOIL
AL PROPERTIES, GHOUNDHATER, SOIL
NS, POLLUTION ABATEMENT, POTABLE
ROUMDWATER MOVEMENT, PERCOLATING
WATER, I'ATfcR SUPPLY,
LATIVE RIGHTS, WATER
UNDERGROUND STREAMS,
RisoicTiON, OIL INDUSTRY, SALINE
PUMPING, WATER HELLS, MUNICIPAL
, SUBSURFACE WATERS, PERCOLATING
NT, WAT E R POL L UTI ON, PERCOLATING
EMTIFICATION, SOIL WATER, SALINE
PERCOLATING
LAW, GROUND
PERCOLATING
WATER),
WATER),
'''ATEP ) ,
WATER) ,
WATER-F
lJ/\Tf:R-F
WATER-F
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
HATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
W A T E R ,
WATER,
WATER,
WATER,
UATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
WATER,
#SOIL-WA
ACIDITY,
MASS TRA
OM-SITE
RESHWATER
RESH -WATE
RESH WATE
^DETERIOR
*GROUNDHA
-MUN I C I P A
#PE RMEAB I
-PIPELINE
-RELATIVE
^RETURN F
-TRACE EL
*UNDFR SEE
*HA TE R PO
* W A TE R PO
DWELLS, G
DWELLS, J
TER EHVIRONf-'iE
OXYGEN, ALGA
fMSFEP, AQUIFE
DATA COLLECTI
INTERFACES,
R INTERFACES,
R INTERFACES,
ATION, *WATER
TER RECHARGE,
L PASTES, -AR
LITY, POROSIT
S, ^LEAKAGE,
RIGHTS, MATE
LOW, #DRAIiMAG
FMENTS, CHELA
PAGE, #POLLUT
LLUTIPN, #SEE
LLUTION, *SEE
ROUNDWATER, 0
UDTCIAL DEC IS
NT,
E,
S
RS. :
OMS,
w ELL
#LF
MIX
POL
MOD
TIFI
Y, C
jum
R LA
E WA
TE E
ION,
PAGE
PAGE
ILY
IONS
AMMONIA, DRAINAGE EFFECTS,
AQUIFERS, HYDROGEOLOGY, r,R
ARTIFICIAL RECHARGE, FILTR
EMINENT DOMAIN, PUBLIC HEA
FEEDLOTS.: /OURCES, MINERA
GRASSLANDS, SOIL EROSION,:
GROUNDWATFR MOVEMENT, OIL-
INDUSTRIAL WATE: / FMIiMEM
INFILTRATION, DETERGENTS,
INF I LTRATION, GROUNDWATER
IRRIGATION, RETURN FLOW,
LEG: /ENS, EXCAVATION, WAT
LEGAL ASPECTS, MUNICIPAL H
OIL HASTES, WAT: /OF POLIJJ
OIL INDUSTRY, WATER POLLUT
OIL HASTES, CESSPOOLS, SEW
PATH OF POLLUTANTS, SUBSUR
PERCOLATION, LEACHING, AOU
PERCOLATION, SUBSURFACE RU
PERCOLATION, RATH OF POLLU
POLLUTION ABATEMENT, JUDIC
POLLUTION IDENTIFICATION,
REASONABLE USF, REMEDIES,
RIPARIAN RIGHTS, RELATIVE
SALTS, SALINE SOILS, HASTE
SALINE WATER-FRESHWATER IN
SALINITY, FERTILIZERS, GRO
SALINE HATER, HATER CONSER
SOILS, SEEPAGE, SOIL CHEMI
SOLUBILITY, SOIL WATER TRA
STANDARDS, HATER POLLUTION
HATERS, DIFFUSI
WATERS, JUDICIA
''ATER, PERCOLAT
WATERS, UhlDERGR
SUBSURFACE WATERS, GROUMDW
SURFACc-GROUMDWATER RELATI
UNDERGROUND, HELLS, SALINE
HATER CONSERVATION, ADM IN I
HATER CONSERVATION, IRRIGA
SUBSURFACE
SUBSURFACE
SUBSURFACE
SUBSURFACE
W70-
W69-
W69-
W70-
H71-
W71-
W1 I -
W71-
W71-
H69-
W69-
H70-
w/n-
W71-
W69-
W70-
W70-
W70-
H70-
H69-
W 7 1 -
W70-
H69-
H70-
W 71-
W70-
W 71 -
H70-
H69-
W68-
V! f I
W71-
H70-
H71-
H70-
W70-
W68'
W 7 0
W70'
W71-
W 7 1
H73
H 7 0
W71
W 7 0
H71
W 7 0
W 71
V! 71
W 71
W 7 0
H70
H 7 1
H70
W70
W71
W 7 1
W 71
H 7 1
W71
0]
07838
08921
07766
01028
01932
03230
06063
10325
08620
00979
07632
00521
06063
03197
07631
08050
08049
08025
06118
04548
0053?
08621
02896
06435
04193
OH055
02896
00652
01010
06435
04742
00532
01043
08025
08049
00627
06011
00521
11692
13645
06063
00532
01 043
08026
01028
0866?
06063
0412.1
07887
08025
08026
01028
-00521
07631
13521
-02909
10446
-10157
06063
160
-------
R I MTRUS I Of- , -HAW A II, I RR I GAT I OK'
CTERIOPHAGE, PERCOLATION, GROUND
EEPAGE, GROUNDWATER, °ERCOLAT ING
R QUALITY, SALINITY, PERCOLATING
(SURFACES), WELL CASINGS, SALINE
ELLS, WASTE DISPOSAL, SUBSURFACE
LS, WAX -LOUISIANA, ^PERCOLATING
-'MISSOURI, -PERMITS, *SURSURFACE
DISCHARGE, GROUNDWATER, SURFACE
T, PERCOLATING WATER, SUBSURFACE
WATERS, GROUNDWATER, PERCOLATING
ALIZATIO
M
NITROGEN SO/ -SURFACE
DUSTRY, SALINE WATER, SUBSURFACE
POLLUTION, -SEEPAGE, ^SUBSURFACE
EFFLUENT, C.O.D., B.O.D., WASTE
Y, PERCOLATING WATER, SUBSURFACE
JNAGE, SHALLOW WFLLS, SUBSURFACE
N, NITROGEN, PHOSPHORUS, SURFACE
POLLUTION ABATEMENT, SUBSURFACE
POLLUTION, *SEEPAGF, -SU8SURFACF
ERS, WELLS, GROUNDWATER, SURFACE
TIVF USE, -GROUNDWATER, -SURFACE
R MOVEMENT, GROUNDWATER, SURFACE
S, PERCOLATING WATER, SUBSURFACE
AN LAND, PERCOLATION, SUBSURFACE
RS, STREAMS, LAKES, PONDS, TIDAL
-DRAINAGE, -EUTRO/ ^AGRICULTURAL
CHIGAN, PHOSPHORUS, AGRICULTURAL
LIGOTROPHY, SEWAGE, ALGAE, SCUM,
ER-FRESHWATER INTERFACES, WELLS,
ALITY, INSPECTION, INSTALLATION,
ER SUPPLY, BOUNDARIES(SURFACES),
PUMPING, STANDARDS, REGULATION,
TROL, WATER POLLUTION TREATMENT,
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*SALINE WATER INTRUSION, *WATER
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it U. S. GOVERNMENT PRINTING OFFICE : 1972 O - 466-139
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