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2900 - Site Mitigation Program
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PR0541818
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Last modified
5/28/2021 11:41:05 AM
Creation date
5/28/2021 11:19:51 AM
Metadata
Fields
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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EHD - Public
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Technical Description <br />first and the proteins last. As the energy level drops, floc colony formation increases rapidly. Free- <br />swimming ciliated protozoa cannot find enough bacteria to stay alive and they too begin to die. <br />As the bacteria die, an enzyme dissolves a portion of the cell wall, allowing the remaining nutrient <br />contents in the cell to escape and thus furnishing the remaining cells with a little more food. This <br />process falls under the spectrum of phagocytosis, or more specifically, lysis, after lysin, a specific <br />antibody that destroys blood cells, tissues, and microorganisms only, and is a natural process that <br />allows living bacteria to obtain nutrients from their dead neighbors. <br />If the aeration period were allowed to continue, the bacterial population would continue to de- <br />crease. The free-swimming ciliates would die out completely and the stalked ciliates would start <br />to decrease, but rotifers would start to increase. Rotifers eat small particles of the floc and do not <br />depend upon individual cells, as do protozoa. <br />Too long an aeration period would result in death of all biological forms; only the inert fraction of <br />the cells would remain. Activated sludge is never allowed to go this far in the aeration cycle of the <br />Bio-Pure system before being moved on to the next step in the process. <br />During the endogenous phase, the floc colonies are separated from the liquid before clarification. <br />This concentrated floc is fed by fresh batches of organic matter entering the treatment system. <br />Since the quantity of microorganisms is higher than the first time around, the initial F:M ratio is <br />lower and the bacteria start at a higher level in the growth cycle. A constant period of aeration <br />allows the system to progress further into the endogenous phase with each cycle. This results in <br />better flocculation and a clearer effluent. Thus, the rate of organic removal is most rapid in the <br />growth phase, while floc formation is best in the endogenous phase. <br />EXTENDED AERATION <br />Sludge production is generally an inherent part of the biological digestion process. In typical mu- <br />nicipal systems, there is so much food that the bacteria multiply exponentially with much of the <br />food going into production of new cells, so sludge, which is made up almost entirely of biomass, <br />production is high. <br />Conversely, when food is scarce, as in the low F:M ratio Bio-Pure system, the bacteria become <br />cannibalistic and cell production is low, so sludge production may actually cease as new cells <br />reach equilibrium with those consumed. In the Bio-Pure process, the rate of sludge buildup is bal- <br />anced by the rate of sludge destruction. Since this balancing is not precise, over extended periods <br />of time the effluent discharge quality may ultimately be degraded as small quantities of sludge <br />concentrate, thus periodic wasting of a small volume of sludge may become necessary. This is es- <br />pecially true where a highly polished effluent is desired. <br />Unlike a municipal flowthrough system, where sludge is continually drawn off, the Bio-Pure sys- <br />tem retains and recycles the sludge until the one-liter settleometer test (SSV-60 test) indicates 500 <br />ml of sludge volume. In each batch, 66% of the mixed liquor, the portion that remains in the <br />clarifier after transfer of the supernatant, is returned to the aeration chamber. After settling, this <br />66% represents 100% of the activated sludge. <br />(NOTE: The SSV-60 test, although somewhat similar, is not to be confused with the more com- <br />monly used SW test, (sludge volume index). The SW is used to determine the volume of sludge <br />compared to its weight, and thus its settleability, whereas the SSV-60 test determines only the <br />settled-sludge-to-supernatant ratio.)
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