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2900 - Site Mitigation Program
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PR0541818
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COMPLIANCE INFO
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Last modified
5/28/2021 11:41:05 AM
Creation date
5/28/2021 11:19:51 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0541818
PE
2965
FACILITY_ID
FA0023982
FACILITY_NAME
SJC PUBLIC WORKS UTILITY MAINTENANCE DIVISION
STREET_NUMBER
0
STREET_NAME
LINNE
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
24809015
CURRENT_STATUS
01
SITE_LOCATION
LINNE RD
P_LOCATION
03
QC Status
Approved
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SJGOV\dsedra
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EHD - Public
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Technical Description <br />MLVSS is a good approximation of microorganism concentrations in the MLSS. Data obtained <br />are calculated using a moving seven-day average. <br />Equation 4 predicts that 2.5 moles of oxygen are required to convert one mole of ammonium into <br />2 moles of nitrate ions for new biomass and water. This is equivalent to 4.2 mg/L of 02 per mg/L <br />of NH4—N converted to new cells and nitrate. Therefore, <br />02 x Q = 0 (502 + 2N114 2NO3 +41120) (5) <br />where <br />02 = 4.2 mg/L <br />Q = NH4 <br />o = N05 + H20 (N-3 + CO2 + NO3 + PO4+3 + SD4-2 +H4) <br />The overall equation predicts that 1.98 moles of H are produced per mole of ammonium con- <br />verted, or 7.14 mg of alkalinity as CA CO3 is destroyed per mg of NH4—N converted. The equa- <br />tion also predicts that 0.17 mg of cells is produced per mg of NH4—N converted. <br />The first two parameters (oxygen requirement and alkalinity destruction) are important in the de- <br />sign detention of any hybrid, heterotrophic/autotrophic treatment system. <br />Oxygen is essential for the growth of nitrifiers, and alkalinity consumption is important because <br />nitrifying organisms are efficient only over a relatively narrow pH range. The third parameter, <br />biomass production, is important to the understanding of microbial population dynamics. <br />The low cell production frequently causes washout of nitrifiers in combined carbon-nitrogen oxi- <br />dation systems without high sludge age. The Bio-Pure batch process assures that washout is less <br />likely to occur than in a conventional flowthrough system or process due to the design of the hy- <br />draulic control. <br />Compared to heterotrophic oxidation of carbonaceous waste material, nitrification generates rela- <br />tively little biomass. Therefore, additional solids capacity for nitrogenous processing beyond those <br />allocations given for the heterotrophic process is not required. <br />(NOTE: By increasing detention time from 14 to 16 hours, the process begins to run out the right <br />side of the growth curve. This additional detention time utilizes 02 demand for further conversion <br />of NH4 to NO3.) <br />Samples of MLSS are pulled from the ML entering the clarifier. <br />Formula: <br />F:M = Influent BOD, lbs/day (6) <br />Solids in aeration lbs/day <br />Example: Calculate the F:M. <br />Assumptions: <br />Q = 0.075 MGD <br />Aeration tank volume, V = 0.050 MGD <br />BOD5 = 125 mg/L <br />MLVSS = <br />= Influent BOD 5 <br />1600 mg/L <br />12 <br />1./ /.
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