MONITORING OF THE EFFLUENT STREAM
     FROM WASTEWATER TREATMENT PLANTS
                    by

               Robert Smith
       ENVIRONMENTAL PROTECTION AGENCY
      Office of Research and Monitoring
Advanced Waste Treatment Research Laboratory
              Cincinnati, Ohio

                December 1971

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MONITORING OF THE EFFLUENT STREAM FROM WASTEWATER TREATMENT PLANTS









     To evaluate the quality of the effluent stream from a waste-




water treatment plant the number of measurements required will de-




pend on the degree' of precision required by the regulatory agency.




Both the volume flow and the concentration of contaminants will




vary diurnally and seasonally.  In some instances 24 hour composite




samples will be sufficient, in other cases the diurnal variation




will be measured.  Ideally, all measurements should be made on-line




24" hours per day and 365 days per year.  Automatic instruments to




accomplish this task, however, are not available at this time.  The




following list represents a minimum set of measurements to character-




ize the effluent with respect to its impact on the receiving stream:
 I*




     1.  Volume Flow, mgd




     2.  Water Temperature




     3.  pH




     4.  Suspended Solids Concentration, rag/1




     5.  Total Organic Concentration; COD, TOC, TOD, TC





The stream analyst might wish to substitute a measurement of 5-day




BOD or an oxygen uptake measurement as an alternative or in addition




to the fifth measurement shown in the list.





     The first three measurements listed above can be made contin-




uously, but periodic maintenance will be required.  An instrument




which will measure suspended  soli'ds concentration with good precision




does not exist at this time.  Several instruments are available which

     i


operate on the principle of adsorbed or reflected light similar  to

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                               - 1 -
a turbidometer.  Under ideal conditions, the turbidity measurement

                           •

can be related to suspended solids in the range of 0-100 mg/1.  One



alternative is to write the effluent standards in terms of turbidity



instead of suspended solids.  A typical price for this kind of in-



strument is $1580 for the instrument and about $300 for the recorder.
                                                  -*            - j


In the laboratory, suspended 'solids determination is simple and easy



to perform.  The turbidity type of instrument has the advantage of



continuous on-line performa'nce.




     In the measurement of suspended solids, total organic carbon,



and biodegradable organic carbon, the instruments available either



require significant amounts of maintenance and calibration time or



the measurement made is not truly equivalent to the corresponding



wet chemistry method.  The question, therefore, arises whether the



use of the automatic instruments offers any true advantages over



providing a laboratory and hiring a full time chemist to make the



wet chemistry measurements.  This question will be examined later



in this report, after the cost of the automatic instruments and the



cost of the alternative wet chemistry method are presented.




     The traditional 5-day BOD is time consuming to perform in the



laboratory and has the disadvantage of the 5 day delay which pre-



cludes the use of the .measurement for plant control.  An oxygen up-



take measurement can be made with an instrument marketed by Badger



Meter Manufacturing Company which will measure the oxygen depletion



in the sample over a 15 minute time period.  The cost of this instru-



ment is now quoted as $3800 and the installation cost is estimated at



$100O.  This instrument can be used to measure the concentration of

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                               - 2 -
biodegradable organics, but an operator will be needed essentially
                            •
full time to service and attend the instrument.

     If a measure of total organics species (TOC) is needed, instru-
ments manufactured by Beckman instruments, Inc. and Ionics, Inc.
can be used to measure total organic carbon.  The Beckman instrument
is a laboratory instrument and a chemist is required to prepare the
sample and to service and attend the instrument.  The Ionics in-
strument is partially automatic and can be used on-line with or
without a filter in the sample line.  This instrument will also
require significant attention and service to assure reliable and
accurate measurements.  The cost of the Beckman instrument is $6195
complete.  The Ionics, Inc. total organic carbon analyzer which is
an on-line instrument takes a sample every three minutes.  This in-
strument is fed by an 1/8 inch line and will accept particles less
than 1/16 inch in diameter.  The total cost of the Ionics TOC analyzer
is $9775.

     Ionics also markets a Total Oxygen Demand instrument which is
similar to 'the TOC instrument in that it will accept some particles.
The TOD measurement represents all organic species which can be com-
bined with oxygen.  The cost of the TOD instrument is $8750.  The
estimated installation cost for each Ionics instrument  is $1000.
                                       •
     The TOC and the TOD measurements are similar  to the COD wet
chemistry method in that they do not measure the biodegradable
fraction of the organics present.  Some instruments also make a
measurement of carbon before the dissolved carbon  dioxide is removed
and  this measurement is commonly called total carbon  (TC.)  Some

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                               - 3 -
minimal savings in cost can be realized if this measurement can be




substituted for the TOC measurement.  The COD measurement requires




laboratory space and some glassware.  Up to 72 COD determinations




can be made by one chemist in an 8 hour period.





     Probably the most reliable way to measure the effluent volume




flow is with a Parshall flume.  The Parshall flume is essentially




a Venturi with the water surface open to the atmosphere.  The flow




is a non-linear function of the pressure drop across the Venturi.




The Parshall flume requires a concrete structure to support the




fiber-glass Parshall flume housing.  The estimated cost of the con-




crete structure, the connecting pipeline and the fiber-glass housing




is shown in Figure 1.  The cost of the electronic transmitter which




also interprets the non-linear pressure differential in terms of




volume flow is approximately  $600.  The recorder which gives in-




stantaneous flow, as well as the daily totalized flow, costs approx-




imately $700.  If  the flow recorder is positioned in the adminis-




tration building,  the length  of electrical cable will be about 7O




ft. for a 1. mgd plant, about  220 ft. for a 1O mgd plant and about




680 ft. for a  100  mgd plant.  The cost of two two-conductor wires



in conduit will be about $150 for a 1 mgd plant, $4OO for a 10 mgd




plant and about $1200 for a 100 mgd plant.





     For an additional $300 the tptalizer can be used to control a




proportional sample of the effluent stream.  This, of course, does




not include the cost of  the sampler.  The cost of the sampler will




be in the range $1000-2000.

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                          COST OF EFFLUENT VOLUME FLOW MEASUREMENT


                                             with


                                       PARSHALL FLUME
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         100
                               Plant Design Capacity,  mgd.
                                                                       Figure 1

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                               - 4 -
     For water temperature measurement,  a resistance type ther-


mometer would be the best choice.  The thermometer will cost about


$80.  One electronic transmitter will cost about $20O with an ad-


ditional $131 for installation.  The recorder will cost about $30O.


Electrical wiring will cost about $150 for a 1 mgd plant, $400 for


a 10 mgd plant and $1200 for a 1OO mgd plant.



     The electrode cell for pH measurement sells for about $300.


The transmitter will cost about $600 with an additional $131 for


installation.  The recorder will cost about $300.  Electrical wiring


will cost about the same as the temperature probe.



     An alternative to automatic instrumentation is ivet chemistry
                                        r

which requires adequate laboratory space, analytical instruments


and glassware.  Laboratory facilities are normally installed in


treatment plants, although in the smaller plants they are often not


adequate.  The mimimum recommended laboratory space is about 20 ft.


by 23 ft. in floor area.  A prefabricated building of this size can'


be constructed for about $21.25 per square foot, or a total of about


$10,200.  A total of about $17,100 will be required to equip such


a laboratory.  An itemized list of recommended equipment is shown


with a floor plan of the laboratory in Figure 2.  For effluent mon-


itoring alone, one chemist should be adequate.  The level of chemist


should be about equivalent to GS-.7 in the government service.  The


yearly salary would be $10,298 plus 15% for payroll extras, making


a total of $11,843 per year.



     A summary of construction cost estimates for effluent monitoring


is shown in Table I.  A 9x12 foot building has been provided at the

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                EQUIPMENT FOR ANALYTICAL LABORATORY

              Approximate Costs of Analytical Hardware
Bench  space
Desks  and other furniture
Glassware
Analytical equipment
   Dissolved Oxygen Probe
   Analytical Balance
   Spectrophotoraeter
   pH  Meter
   Conductivity Meter
   Kjeldahl Digestor and Dist'n App.
   Hot plates, flasks,  condensers and
   titration equipment.
   Drying Oven
   Muffle Furnace
   Water  Still
Wall cabinets, pegboard and miscellaneous
                           SAMPLE  LAB.

                          	20'
              to
              CM
                ID
                              IZZ)
                           $ 6,5OO
                               500
                             1,OOO

                               50O
                             1,000
                             2,OOO
                               50O
                               300
                             1,000

                               450
                               500
                               60O
                               75O
                             1,500

                           $17,100
                i. FUME HOOD .

                2 . BENCH UNIT W/ SINK
                 a PEG BOARD.

                3 . PENINSULA TYPE BENCH
                 W/ CENTER DRAIN,
                 SHELF a SINK .

                4 . CHEMICAL STORAGE .
5. INSTRUMENT TABLE  W/
  REGULATED VOLTAGE .
6 . DESKS .

7 . FILE CABINET .
6 . BALANCE  TABLE.
9. TITRATION TABLE .
                                                         Figure  2

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                       TABLE  I
CONSTRUCTION COST FOR' EFFLUENT  MONITORING FACILITIES













Flow Measurement (Pars ha 11 flume)
Water Temperature Measurement
pH Measurement
Subtotal No. 1
Turbidity - Suspended Solids
•
Total Organic Carbon
Oxygen Uptake
9 ft. x 12 ft. Building
at sampling point «
Subtotal No. 2
2O ft. x 24 ft. Analytical
Chemistry Building
Laboratory Equipment
p
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a
id
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C Oi
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$ 48 5O
861
13 5O
$7061
188O
10775
4800

400O
$21455

10200
17100
Subtotal No. 3 S $27300
p
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id
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Cl
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$16700
1111
1600
$19411
188O
10775
4800

4000
$21455

10200
17100
$27300
p
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O
cd
a
(d T3
U O*
6
C
C^O
•H O
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Q II
$58500
1911
2400
$72811
1880
10775
4800

4000
$21455

10200
17100
$27300


'

























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                                - 5 -

    \
 sampling point to house the automatic sampling equipment to minimize

 the length of the sampling lines.   Notice that subtotals 2 and 3 are

 not significantly different.   If we also consider the  fact that most

 wastewater treatment  plants are normally equipped with laboratory

 facilities,  the cost  advantage appears to be in favor  of using wet

 chemistry for suspended solids,  COD  and oxygen uptake or BOD.   It

 is  estimated that one full time chemist  will be needed to service,

 operate   and calibrate the automatic instruments  and that one  full

 time  chemist can also make sufficient measurements by  the wet  chem-

 istry method.


      Although  the best  strategy will depend  on the number and  kind

 of  measurements  required,  it would  appear reasonable to  measure flow,

 water temperature and pH automatically and rely on the wet chemistry

 laboratory to  perform the  COD,  BOD, and suspended  solids  measurements.

 The construction  cost  involved would be  the  sum of subtotals 1  and 3.

 This  amounts to  $34,361  for the  1 mgd plant,  $46,711 for  the 10 mgd.

 plant  and $100,111  for  the  100 mgd plant.   Since the major  part  of the

 cost  is in the Parshall  flume, we can amortize this cost  over 25

 years  at 6%.   In  terms of  cents/Kgal  the  cost would be 0.7 cents/Kgal

 for 1  mgd, 0.1 cents/Kgal  for 10 mgd  and  0.02 cents/Kgal for 10O mgd.

 The cost of one full time  chemist would be 3.2 cents/Kgal  for the

 1 mgd  plant, O.32 cents/Kgal for the  10 mgd plant and 0.032 cents/Kgal

 for the 100 mgd plant.  The total cost would be the sum of  amortization

and one full time chemist.   This amounts  to 3.9 cents/Kgal for  1 mgd,

0.42 cents/Kgal for 10 mgd and 0.05 cents/Kgal for 1OO mgd

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