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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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AquaClear recommends the use of DynaSand continuous-backwash NOTES <br /> filters wherever possible. Although their initial cost is higher than a <br /> standard pressure filter, cost of ownership over a period of time is <br /> considerably less, as the DynaSand has no moving parts, is virtually <br /> maintenance-free, and produces somewhat higher quality output. <br /> DynaSand filters are approved for California Title 22 Standards for <br /> Wastewater Reclamation. <br /> In systems where pressure filters are used,the following applies: <br /> An important design consideration in a tertiary suspended-solids <br /> removal filter is the ability of the filter to accumulate sufficient solids <br /> in the media during extended filter runs to eliminate the need for <br /> frequent backwashes. Frequent backwashes not only consume en- <br /> ergy and plant operator's time, but impose additional hydraulic load- <br /> ing requirements on the secondary process. <br /> In order to obtain the desired solids holding capability, the media <br /> must allow penetration into the depth of the bed rather than simply <br /> retaining solids on the media surface. <br /> Conventional filter sands, as used in potable water filtration, provide <br /> only this surface removal and retention effect.This is satisfactory for <br /> the low solids concentrations involved in freshwater filtration. How- <br /> ever, in wastewater filtration, solids concentrations are significantly <br /> higher and tend to rapidly seal the surface of conventional filter <br /> sands. <br /> During backwash of conventional filter sand media, another phe- <br /> nomenon occurs which contributes to this surface straining effect. <br /> When the bed is fluidized, the less dense, smaller grain-size media <br /> tends to accumulate as the top layer in the bed. This provides for <br /> efficient particle removal during filtration, but precludes any pene- <br /> tration beyond the surface layer. <br /> A more efficient media system incorporating varied chemical mate- <br /> rial (media) layers is recommended. <br /> The different materials are conventional filter sands with different <br /> specific gravities plus anthracite coal. The denser filter sands are <br /> placed below the coarser but less dense coal, thus allowing deeper <br /> penetration in the direction of flow and maintaining a coarse surface <br /> layer even after backwash.This filter media design concept is termed <br /> multimedia. <br /> Fifty to seventy percent of the secondary effluent BODS concentra- <br /> tion can be removed in the tertiary filter.The BOD that is entrapped <br /> in the suspended solids is removed. Filtration has no measurable <br /> effect on the removal of soluble BOD (10 microns or less). <br /> The most important consideration in the sizing of tertiary filters, and <br /> one requiring considerable engineering judgment, is selection of the <br /> application rate, which is expressed as influent gallons per minute <br /> applied per square foot of filter bed area. <br /> 19 <br />
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