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SU0003122
Environmental Health - Public
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2600 - Land Use Program
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SU0003122
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Entry Properties
Last modified
5/7/2020 11:29:41 AM
Creation date
9/9/2019 10:38:07 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
RECORD_ID
SU0003122
PE
2633
FACILITY_NAME
SA-93-26
STREET_NUMBER
26440
Direction
N
STREET_NAME
THORNTON
STREET_TYPE
RD
City
THORNTON
ENTERED_DATE
11/6/2001 12:00:00 AM
SITE_LOCATION
26440 N THORNTON RD
QC Status
Approved
Scanner
SJGOV\rtan
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\MIGRATIONS\T\THORNTON\26440\SA-93-26\SU0003122\APPL.PDF \MIGRATIONS\T\THORNTON\26440\SA-93-26\SU0003122\CDD OK.PDF \MIGRATIONS\T\THORNTON\26440\SA-93-26\SU0003122\EH COND.PDF \MIGRATIONS\T\THORNTON\26440\SA-93-26\SU0003122\CORRESPOND.PDF
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EHD - Public
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Technical Description <br /> liquor volatile suspended solids(ML,VSS), and consists mainly of microorganisms, inert suspended <br /> matter, and nonbiodegradable suspended matter. <br /> After a preset time period, the mixed liquor is transferred to the clarifier tank for separation of <br /> suspended solids from the treated wastewater. The biological solids are then returned to the aeration <br /> tank to maintain a concentrated population of microorganism's to treat new, incoming'waste. <br /> 1 <br /> DETAILED PROCESS DESCRIPTION <br /> Incoming sewage is accepted into the aeration chamber via a mesh receiving basket in which it is <br /> subjected to hydraulic comminution bymeans of the composite flow of mixed liquor and air directed <br /> through the basket. This allows only small particles to enter the main area of the chamber,while also <br /> assuring odorfree operation by underwater breakdown of solids. The reserve solids in the basket also <br /> assist in stabilizing the biologic process during periods of low flow. <br /> The amount of air required for complete digestion of sewage is lower in the Bio-Pure plant than <br /> theoretically required.This is because the operating temperature of the mixed liquor is as much as PC <br /> higher than the temperature of incon ng'wastewater, due to the heat exchange from the submerged <br /> transfer and aeration pumps and the closed tank design. This higher temperature, plus the floc-colony <br /> breakup and reactivation caused by increased agitation, renders the organic material more readily <br /> digestible. This enhanced digestibility, in conjunction with the high level of mixed liquor/suspended <br /> solids (MI..SS of 3,000-6,000 mg/L), increases groups of facultative organisms which are able to <br /> initiate further waste digestion by utilizing some of the chemically bound oxygen present in the mixed <br /> liquor. The elevated operating temperature increases the enzyme and biologic activity, thus consid- <br /> erably less retention (or residence) time in the aeration phase is required. <br /> Aeration chamber residence time for the digestible material is 16 hours and is dependent on the final <br /> system batch timing, which is based on effluent testing. <br /> ., <br /> ,a <br /> As the height of the mixed liquor increases in the aeration chamber, a float switch initiates the system <br /> microprocessor which, in turn, starts the mixed liquor transfer pump (MILT) and transfers a fixed <br /> volume(batch)of mixed liquor to the clarifier. The MLT pump is controlled by time, and the actual <br /> programming allows for two or three minutes' pump overrun to overflow the MLT into the weirs, <br /> which skims off the scum and other floatables. These floatables are returned to the aeration chamber <br /> for reprocessing. <br /> Batch time in the clarifier is determined by the amount of time necessary for the remaining bacteria <br /> and dead cells(which flock together once deprived of food and oxygen)to settle, thereby separating <br /> the supernatant from the sludge. This time period is sufficient to allow flocculation and settling, but <br /> is not long enough to encourage an extended anaerobic condition. Average time is 65 minutes. No <br /> coagulants are needed, nor are they recommended. <br /> Two very common problems in most extended-aeration, small-flow treatment plants are the <br /> denitrification of the sludge that occurs in the settling tanks, which causes sludge flotation and <br /> subsequent loss over the weir, and surface skimming devices which prevent a quiescent environment <br /> which, in turn, prevents efficient settling, thus causing a high amount of suspended solids to be <br /> 6 <br />
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