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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
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 />from the bacteria that utilize the organic matter and thus assist greatly in the settling stage in the <br />clarifier. <br />TECHNICAL DESCRIPTION <br />With the advent of complete oxidation-type, activated-sludge systems, such as the Bio-Pure sys- <br />tem, the rotifers have been the predominant animal form and can utilize larger fragments of acti- <br />vated sludge floc than can the protozoa. They can survive after all the free-swimming bacteria <br />have been consumed by the protozoa. The dominance of rotifers indicates an extremely stable bio- <br />logical system. <br />Activated sludge can be formed from wastes high in colloidal solids, such as domestic sewage, or <br />from a completely soluble waste, such as industrial waste from the manufacture of synthetic <br />chemicals. The formation of activated sludge is the same in both extremes as long as the wastes <br />are considered nutritionally stable, thereby containing all the elements necessary for normal bacte- <br />ria growth. <br />Most domestic sewage contains sufficient microorganisms and nutrients to produce a activated <br />sludge without seeding. The exception would be a treatment plant receiving high degrees of rain- <br />water or other nonsewage-bearing waters. <br />As fresh waste enters, the food-to-microorganism (F:M) ratio is very low. Microorganisms are in <br />excess of food supply and are thus competitive for the food. As the bacteria begin to grow and <br />multiply, the protozoa begin to grow. During this log growth rate, organic matter in the waste is <br />removed at its maximum rate with optimum conversion of organic matter into new cells. The en- <br />ergy level is sufficiently high to keep microorganisms dispersed. <br />It is impossible to get activated sludge to form as long as the microorganisms remain in the log <br />phase. The high metabolic rate of the bacteria creates a constant need for additional oxygen. <br />If aerobic conditions are not maintained by proper oxygen transfer, the rate of metabolism will not <br />follow a log rate, but rather an arithmetical rate until oxygen is no longer the limiting factor and <br />the protozoa would then be adversely affected. <br />The F:M ratio drops rapidly as the food is consumed and new cells are produced, consuming <br />more of the nitrogen and phosphorous which is present in the wastewater. <br />A point is reached where the food becomes the limiting factor in further growth. The bacteria and <br />protozoa begin to decline. The cells begin to die and floc begins to form. In the turbulent aeration <br />tank, the bacteria are constantly being brought into contact with each other; as long as they have <br />sufficient energy, they split apart and continue their normal metabolic function. <br />As their energy content decreases, more and more bacteria lack the energy to overcome the forces <br />of attraction between two colliding cells. The two cells then move as a unit and soon become <br />three, then four, and so on, until a large floc colony has formed. <br />The food concentration continues to drop and microorganisms continue to increase, but at an <br />ever-slowing rate. The minimum F:M ratio is reached at the end of the declining growth phase <br />and nitrogenous substances begin to form. <br />When the bacteria are unable to obtain sufficient energy from the little remaining food, they begin <br />to metabolize food reserves within their own cells. Excess fats and carbohydrates are consumed <br />3 <br />1'
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