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 ------- 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 ------- - 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 ------- - 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 ------- - 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. ------- COST OF EFFLUENT VOLUME FLOW MEASUREMENT with PARSHALL FLUME =2: • « •p 9©: ni 4444 I I c- m tin o< O" "I 10 8 9 i- 8 K 5 » o S ±m m TIE October, tffl ttt LU -iOO TT 0.1 5 678910 1.0 4 5 678910 10 4 6 6 7 8 9 1C 100 Plant Design Capacity, mgd. Figure 1 ------- - 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 ------- 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 ------- 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 •H t\ a a id u T3 C Oi O> G •H (/) H a n $ 48 5O 861 13 5O $7061 188O 10775 4800 400O $21455 10200 17100 Subtotal No. 3 S $27300 p •H M id a. m U "O Q\ C e Cl •H 0 0) rH Si. $16700 1111 1600 $19411 188O 10775 4800 4000 $21455 10200 17100 $27300 p •rl O cd a (d T3 U O* 6 C C^O •H O U) r-l Q II $58500 1911 2400 $72811 1880 10775 4800 4000 $21455 10200 17100 $27300 ' ------- - 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 ------- |