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SU0003122
Environmental Health - Public
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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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FilePath
\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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r <br /> Technical Description <br /> V <br /> to as the mean-cell-residence-time (MCRT), and is a function of the amount of food provided to <br /> bacteria in the aeration reactor tank (the food-to-microorganism [F:M] ratio). <br /> "^ There are three basic classifications of the activated sludge process which are defined by the process <br /> loading range to the microorganisms:high,conventional,and low.The following shows typical ranges <br /> of the MCRT and F:M for each loading range: <br /> MCRT, F:M <br /> Process day lbs BOD/day/lb MLVSS <br /> High Rate 3-5 0.4-1.5 <br /> Conventional Rate 5-15 0.2-0.4 <br /> Low Rate 15-30 0.5-0.2 <br /> (Note. lbs/day x 0.01157 =g/kg) <br /> In the complete-mix, activated-sludge process, the characteristics of the mixed liquor are similar <br /> throughout the aeration tank. That is, the influent waste is rapidly distributed, and operating <br /> �. characteristics measured in terms of solids, oxygen uptake rate (OUR), MLSS, and soluble BOD <br /> concentration are nearly identical throughout the tank,with a very low level offood available to a large <br /> mass of microorganisms at any given time. This is the principal reason far the Bio-Pure system's <br /> ability to handle surges in the organic loading without producing a change in effluent quality. <br /> Critical design factors are the tank's length-to-width ratio, amount of air introduced, and turbulence <br /> �.. throughout the tank. <br /> The system is operated at Water Pollution Control Federation and federal EPA design standards, <br /> which recommend an MLSS of about 3,000 to 6,000 mg/L. The quantity of sludge returning from the <br /> clarifier is 66% of design batch. This percentage is required in order to maintain the aeration solids. <br /> To ensure that a dissolved oxygen(DO)of 0.05 ppm minimum exists at all points, a minimum oxygen <br /> input of 2.0 mg/L is maintained at the effluent end of the aeration chamber. Therefore, air is supplied <br /> at a rate of 0.8 to 115 cubic feet/gallon of wastewater with an additional mixing factor of 1.5 to 2.0 <br /> cubic feet per gallon. <br /> For sizing the air delivery system, the cubic-feet-of-air requirement is expressed as cubic feet of air <br /> required per pound of BOD removed from the aeration reactor. The minimum air/organic loading <br /> 06. recommended by most state agencies is 1,000 cubic feet per pound of BOD. <br /> The Bio-Pure system expands this to 1,500 cubic feet per pound ofBOD removed,allowing a residual <br /> airbase for compensation ofhigher organic loadings than anticipated and to support further processing <br /> of ammonium nitrogen(NH).Air availability is always maintained at 125%ofmaximum demand with <br /> the 25%residual over the 1,500 CFM injected,bled offbetween the compressor and the aeration tank. <br /> Because the total daily air requirement is dependent upon the pounds of BOD applied, the pounds of <br /> BOD entering the treatment plant must be known and can be calculated as follows: <br /> �' 10 <br />
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