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SU0003122
Environmental Health - Public
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THORNTON
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2600 - Land Use Program
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SA-93-26
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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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Design and Specifications <br /> Complete installation drawings and operating instructions shall be provided for all equipment <br /> +. furnished. <br /> OPERATING CONDITIONS <br /> ODORS. The treatment plant shall produce no objectionable odors. <br /> PLANT STARTUP. During the plant startup phase, the influent will enter the buffer-tank pumpwell <br /> for transfer directly to the aeration chamber. Generally, a 10-day period at near-maximum design <br /> flows is sufficient to achieve system stabilization. A longer period may be required under reduced <br /> flow conditions. <br /> PLANT BIOLOGIC LOADING. The calculated per capita biologic loading for this project follows <br /> EPA guidelines and is 9.5 lbs of BOD. The plant is capable of a maximum biologic loading of <br /> 10.8 lbs of BOD. <br /> TERTIARY DISCHARGE. This plant shall be capable of removing, as a minimum, 90% of the <br /> biochemical oxygen demand (BOD) and suspended solids (SS) from 5,000 gpd of raw domestic <br /> 4- sanitary sewage or waste with a maximum organic loading of 10.8 pounds of BOD per 24-hour <br /> day. <br /> The tertiary filter is an Everfilt Model SMH24-2A in dual configuration. The filters are so de- <br /> signed that they use the filtrate of one filter to backwash the other, automatically reversing this <br /> cycle to backwash the first filter. The filters are capable of reducing suspended solids peak <br /> ,+ loadings of 50 mg/L or less and average loadings of 30 mg/1, or less to 10 mg/L or less. <br /> " SLUDGE GENERATION AND WASTING <br /> �- The batch reactor shall achieve long periods of efficient operation without wasting sludge due to <br /> the holding/digestion aeration batch concept. Influent shall be reseeded by 100% of RAS 14.7 <br /> times in every 24-hour period. Mixed liquor shall be held without runoff, thus allowing digestion <br /> without dilution with a stabilized background. As long as bulking does not occur within the <br /> settling cycle (common to old sludge), and the SSV-60 test maintains less than 500 ml, wasting <br /> shall not be required. <br /> Sludge wasting, when SSV-60 tests indicate the need, shall be performed from the clarifier. The <br /> amount of sludge generated within the aeration chamber (MISS) is controlled by the operator's <br /> +r proper use of the clarifier. <br /> Plant design is based on concentrated wastes received, which average between 90 and 300 mg/L. <br /> Poor collection system integrity, while hydraulically loading the plant to maximum flows, will <br /> generate less sludge over the same retention time and produce lesser volatility (MLVSS) in the <br /> mixed liquor/suspended solids (MLSS). <br /> The F:M ratio is important in determining plant fine-tuning procedures to maintain good effluent <br /> quality. Sludge age is also an important factor, especially if sludge concentrations are minimal. <br /> 9 <br />
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