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SU0002309 SSNL
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UP-93-01
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SU0002309 SSNL
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Entry Properties
Last modified
5/7/2020 11:29:10 AM
Creation date
9/6/2019 10:11:00 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0002309
PE
2626
FACILITY_NAME
UP-93-01
STREET_NUMBER
11011
STREET_NAME
MICKE GROVE
STREET_TYPE
RD
City
LODI
Zip
95240
APN
05921028
ENTERED_DATE
10/26/2001 12:00:00 AM
SITE_LOCATION
11011 MICKE GROVE RD
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\M\MICKE GROVE\11011\UP-93-01\SU0002309\NL STDY.PDF
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EHD - Public
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w <br /> The three existing seepage pits accommodate the excess septic effluent produced <br /> during peak water-use periods. Two 36 inch diameter seepage pits completed to 25 feet <br /> bgs and backfilled with rock each provide an additional 400 gallon capacity for septic <br /> effluent during peak-use periods. A third rock filled seepage pit that is 42 inches in <br /> diameter and 25 feet deep provides an additional 540 gallon capacity. The estimated <br /> total infiltration capacity of the three seepage pits is approximately 1 ,300 gallons. <br /> Assuming that no infiltration were to occur for one week, the three seepage pits provide <br /> assimilative capacity for the wastewater produced by four people for an entire week (for <br /> calculations, see Appendix F). <br /> The additional water storage capacity supplied by the seepage pits compensates <br /> for the slow water infiltration of the soils where the leach lines are located. As discussed <br /> in Section 4, a sandy soil layer is encountered at approximately 10 to 15 feet bgs. <br /> Although the infiltration rate in this sand layer was not measured, it is expected to be <br /> significantly higher than in the overlying clay soils. The additional storage capacity of the <br /> seepage pits combined with the rapid infiltration rate of the sandy subsoil layer provides <br /> excess capacity for a four bedroom residence. <br /> 6.1 .2 Nitrogen Loading <br /> The actual nitrogen loading from the existing residence was not measured for this <br /> septic system evaluation. Therefore, nitrogen loading estimates are based on information <br /> published in established references including "Design Manual for Onsite Wastewater <br /> Treatment and Disposal Systems (EPA, 1980). <br /> Nitrogen loading from the existing septic system will be evaluated in two ways. <br /> First, average values for nitrogen concentrations in septic tank influent and effluent will <br /> be considered relative to site characteristics (cation exchange capacity, soil type, depth <br /> to groundwater, etc.) and expected attenuation factors for nitrogen in soil. The factors <br /> affecting nitrogen movement through soils include ammonia volatilization, adsorption of <br /> ammonium to soils, mineralization of organic nitrogen, and nitrification and denitrification <br /> rates. For a general discussion of these processes, see Appendix G. <br /> For this property, Figure 3 summarizes the nitrogen transformations from a typical <br /> household and indicates approximate concentrations for various nitrogen species (e.g. <br /> organic nitrogen, nitrate, ammonia, etc.) in the unsaturated zone. Figure 3 suggests that <br /> the typical household located on clayey soils similar to those at the property will produce <br /> wastewater containing some nitrate. However, with the clayey soils present at the <br /> SAC 125.12 8 <br /> DAMES & MOORE <br />
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