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SU0003122
Environmental Health - Public
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EHD Program Facility Records by Street Name
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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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The system's inherent enhanced treatability, in conjunction with a <br /> high level of mixed-liquor suspended solids(MLSS) (4,000-6,000 ppm) NOTES <br /> and quiescent settling, promotes the growth of facultative organisms <br /> that achieve additional breakdown of the waste by utilizing some of <br /> the chemically bound oxygen present in the mined liquor. <br /> The elevated temperature increases the biological metabolism of <br /> these newly generated floc colonies,which also require lower oxygen <br /> concentrations to remain aerobic.Most conventional treatment plants <br /> generate a crude refrigeration cycle during the aeration process,thus <br /> negating this effect and lowering the overall plant efficiency. <br /> In other systems using similar processes, denitrification of the sludge <br /> may occur in the settling tanks, taus ng sludge flotation and possible <br /> transfer to the next stage. Mechanical skimmers are detrimental to <br /> proper processing, as they prevent proper settling and solids will be <br /> discharged to the chlorine contact chamber. <br /> With the ACT system, floating solids which are not weired back <br /> during the aeration-to-clarifier transfer cycle are trapped on the top <br /> three inches of supernatant, which is not passed to the chlorine <br /> contact chamber, but is returned to the aeration tank by the clarifier <br /> sludge return pump which empties the clarifier tank each cycle. <br /> The rate of sludge buildup is minimal, as it is balanced by the rate of <br /> sludge destruction through repeated recycling from the clarifier, chlo- <br /> rine contact chamber, and the final filters back through the aeration <br /> cycle. <br /> A perfect balance between sludge generation and sludge destruction <br /> is possible in theory, but cannot be achieved from a practical stand- <br /> point. As a result, a plant operating at or near maximum capacity, <br /> which is producing a highly polished effluent,will require that excess <br /> sludge be wasted at intervals of from one to three years. The actual <br /> interval for sludge wasting or removal depends upon system opera- <br /> tor's skill,plant maintenance,and influent characteristics. <br /> Chlorination is accomplished by one of the following means: Diluted <br /> liquid chlorine is injected into the clarifier/chlorine contact chamber <br /> transfer line using a demand-type injection system, or, in cases of <br /> larger systems and where proper safety conditions can be met, chlo- <br /> rine gas may be injected into the transfer line. <br /> In both cases, clarified supernatant is chlorinated prior to entering <br /> the chlorine contact chamher; where the 70-minute settling period <br /> allows complete reaction to the chlorine; thus, there is no effluent <br /> bleedthrough as occurs in flowthrough-type systems. <br /> The chlorine contact chamber may be discharged as secondary efflu- <br /> ent, pumped through either a multimedia pressure filter or a con- <br /> tinuous-backwash filter such as the DynaSand by Parkson.Any min- <br /> ute particles backwashed or rejected from the filters are returned to <br /> either the aeration or buffer tank for recycling. <br /> 4 <br />
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