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SU0000030 SSNL
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MS-01-04
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SU0000030 SSNL
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Last modified
5/7/2020 11:27:34 AM
Creation date
9/4/2019 10:18:18 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0000030
PE
2622
FACILITY_NAME
MS-01-04
STREET_NUMBER
7855
Direction
W
STREET_NAME
BATES
STREET_TYPE
RD
ENTERED_DATE
8/8/2001 12:00:00 AM
SITE_LOCATION
7855 W BATES RD
RECEIVED_DATE
2/1/2001 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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SJGOV\rtan
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FilePath
\MIGRATIONS\B\BATES\7855\MS-01-04\SU0000030\NL STDY.PDF
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EHD - Public
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7denitrification <br /> on as possible to take advantage of evaporation and evapotranspiration. Deep rooted <br /> should be planted over the leachfield. The scientific literature suggests that <br /> may be enhanced by placing proposed leachlines higher in elevation toward the <br /> soil surface, particularly since the surface soils contain approximately 27% of the clay soil <br /> fraction. <br /> The north leachfield should be installed also with the leachlines high in elevation. During the <br /> rainy season,November through March, nitrification is suppressed during these colder months of <br /> the year, so it would be beneficial for the leachlines to be placed high in elevation where the <br /> soil/effluent interface is colder. Additionally, the north side of the house will not "dry-out" like <br /> the south side can during the winter months, thus keeping a higher moisture content in the soil, <br /> forcing an anaerobic environment and impeding nitrification. <br /> Blackwater may be piped to the north leachfield and graywater piped to the south leachfield. <br /> Deciduous and evergreen plants should be planted no closer than 15 ft from any leachline to <br /> prevent serious root infiltration into the leachlines. These procedures described above should <br /> theoretically provide a triple nitrate mitigation system of 1.) denitrification/clay absorption, 2.) <br /> nitrification suppression and 3.) evaporation/evapotranspiration. <br /> The two septic tanks for the dual system must have two compartments and be 2000-gallons each:. <br /> •Effluent filters must be installed in the second compartment of each tank. If elevations cannot be <br /> matched with grades, then the effluent will have to be pumped to the leachfield, in which case a <br /> filter bed design may be considered...A filter vault with a pump must be installed if the effluent , <br /> is to be,pumped. > <br /> The percolation test results reveal surprisingly good percolation considering the clay soils at a <br /> depth of 42 inches below grade. Hydraulic conductivity testing indicates an application rate of 3 <br /> gallons/sq ft/day, which can also be considered good. <br /> Seepage pits and sumps will not be allowed by the San Joaquin County Envirohmerital Health <br /> Departments Sumps and pits may be the main culprit for nitrate impact originating from septic <br /> systems in this locale. This assumption is due to the fact that these structures are dug or drilled <br /> into the, underlying gravel strata, which is substantial under the Valpico Section. Consequently, <br /> the favorable soil characteristics of denitrification described above and proven analytically, <br /> cannot act upon the effluent once it enters the sumps or pits. <br /> Depending upon the final design imposed by the Environmental Health Department for effluent <br /> management, the leachfield criteria could be based upon the following: <br /> 1.) The leachfield area based upon the percolation rate obtained as stipulated in Section <br /> 10.3.4 of the San Joaquin County Sewage Standards. Since the perc rate was 10 min/in, <br /> the leachfield area should be 6,000 sq ft. Both the north and south leachfields can be 100 <br /> ft x 30 ft= 3,000 + 3,000 = 6,000 sq ft. <br /> 2.) The leachfield area based on the permeability of the soil eventually reaching a conservative <br /> long term application rate (LTAR) of approximately 0.25 gals/ftz/day due to biomat <br /> Page -9- <br /> valley AB Research <br />
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