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SU0010821_SSNL
Environmental Health - Public
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99 (STATE ROUTE 99)
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2600 - Land Use Program
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PA-1600040
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SU0010821_SSNL
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Last modified
11/19/2024 1:52:20 PM
Creation date
9/8/2019 12:58:14 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0010821
PE
2631
FACILITY_NAME
PA-1600040
STREET_NUMBER
3515
Direction
S
STREET_NAME
STATE ROUTE 99
City
STOCKTON
Zip
95215-
APN
17909004
ENTERED_DATE
3/14/2016 12:00:00 AM
SITE_LOCATION
3515 S HWY 99
RECEIVED_DATE
3/14/2016 12:00:00 AM
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
Scanner
SJGOV\sballwahn
Supplemental fields
FilePath
\MIGRATIONS\N\HWY 99\3515\PA-1600040\SU0010821\SS STDY.PDF
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EHD - Public
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B. FILTER BED DESIGN AND EFFLUENT ACCEPTANCE <br /> The configuration of the disposal structure can be two methods: leachline trench to a maximum 24 <br /> inches wide and maximum 42 inches deep, or a filter bed arrangement. The calculations are as <br /> follows for leachlines: <br /> 1,200 gallon Base Tank Capacity(BTC)+Average Daily Flow(ADF)= 1,200+210 gpd= 1,410 gals. <br /> 1,410 gals x 0.225 (SF) =317 lineal ft of leachline (LFLL). The Site Plan indicates two - 85 ft <br /> leachlines for a total of 170 LFLL. Therefore, a filter bed arrangement should be considered: <br /> 317 LFLL x 4 = 1,268 sq ft of calculated filter bed area. <br /> The illustrated primary disposal area consists of: 20 ft x 85 ft= 1,700 sq ft. QQ <br /> The proposed filter bed dimensions can be 10 ft wide x 85 ft long= 850 sq ft, and 1 ft deep. The <br /> entire I ft depth must be installed below the clay layer that exists from 0-2.5 ft. Using a filter bed <br /> depth of 1 ft, we find the entire filter bed has an effluent acceptance area of. 1 + 10 + 1 x 85 = 1,020 <br /> sq ft. The acceptance rate correlated with the observed perc rate as referenced on Page 3 is <br /> determined to be 0.671 gals/sq ft/day. Therefore,the filter bed soils will theoretically accept 1,020 sq <br /> ft x 0.671 gals/sq ft/day=684 gpd. <br /> The septic tank, primary and sufficient 100% replacement areas are denoted on the attached Site Plan <br /> produced by Haggerty Construction. Influent will enter the tank, which will be situated northeast of <br /> the guard house. Effluent gravity flows from the septic tank, into a distribution box (D-box - not <br /> shown),then enters two, 3-inch dia. perforated laterals capped at the ends that run level. This will <br /> allow equal gravity distribution of effluent throughout the filter bed. The laterals should be equal <br /> distance apart within the filter bed area. <br /> V. CONCLUSIONS AND RECOMMENDATIONS <br /> SS <br /> S§ The surface and shallow subsurface soils underlying the subject property where the <br /> prop se filter bed is to be installed, reveals a medium permeability. There is a change in soil <br /> structure at approximately 2.5 ft below grade from a an/heavy clay to a clay loam. <br /> The filter bed soils can theoretically accept 684 gals/day. The ADF was determined to be 210 gpd. <br /> However, advanced biomat formation will impede the permeability of the receiving soils to an <br /> indeterminable extent. A decrease in soil permeability of 50%can be considered plausible. <br /> Consequently,the receiving soils with a mature biomat may manage: 1,020 sq ft x 0.671+2 gals/sq <br /> ft/day= 342 gals/day. <br /> NLS The nitrate loading calculations show the resultant effluentfrome subject property will <br /> theor ally possess a_nitrate-nitrogen concentration of approximately 2.6 ppin which is <br /> approximately one-fourth the Federal nitrate Maximum Contaminant Level (MCL). r <br /> ` l <br /> NLS 4, , SSS§ �7. All decentralized wastewater management systems (septic systems)will <br /> eventy fail. A reasonable lifespan for the primary area system can be expected based on the <br /> proposed components of the septic system, equal distribution of effluent,and the indigenous clay loam <br /> soil structure with an acceptable permeability. This lifespan can be measured in years. <br /> 8 <br />
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