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SU0006319_SSNL
EnvironmentalHealth
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120 (STATE ROUTE 120)
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2600 - Land Use Program
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PA-0600607
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SU0006319_SSNL
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Last modified
11/19/2024 3:59:59 PM
Creation date
9/8/2019 12:32:18 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0006319
PE
2631
FACILITY_NAME
PA-0600607
STREET_NUMBER
10954
Direction
E
STREET_NAME
STATE ROUTE 120
City
MANTECA
APN
22803025
ENTERED_DATE
11/15/2006 12:00:00 AM
SITE_LOCATION
10954 E HWY 120
RECEIVED_DATE
11/14/2006 12:00:00 AM
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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SJGOV\rtan
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FilePath
\MIGRATIONS\O\HWY 120\10954\PA-0600607\SU0006319\SS_NL STDY.PDF
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EHD - Public
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rThe well water analytical chemistry resultsrobt ' ed from the on-site domestic well indicate that the <br /> nitrate impact to the underlying aquifers rs high. his impact is probably due to the large agricultural <br /> roductieand area directly upgradient o the oject site. <br /> SSS§ 6.8. /the Average Daily Flow is calculated t 'be gals/day om the Men's and Women's <br /> Restrow2 based on the S.J.C. Sewage Standards. ITh, e Apph a on Rate at the native soil-effluent <br /> interface is 1.2 gals/ft2/day from the obtained perc rate o 3.2 min/in at the 40 inch perc test depth. <br /> However, the imported clay loam material should possess a perc rate of approximately 25 min/in, <br /> which should translate to Application Rate of approximately 0.593 gals/ft2/day. Therefor -r is <br /> 2 ft width x 300 LFLL=600 square feet of infiltrative floor surface, this area should acclTt 356 <br /> gallons per day(600 ft2 x 0.593 gals/ft2/day= 356 gal/day). <br /> NLS§4.1 The nitrate loading potential cat ed on Page 11 indicates the percolating effluent may <br /> have a resultant nitrate concentration of 16 ppm nitrate, which is below the drinking water <br /> Maximum Contaminant Level (MCL)o The underlying groundwater aquifers contain a <br /> nitrate concentration of approximately 41 ppm nitrate. Consequently, the recharge effluent water <br /> should theoretically add a dilution effect to the aquifers that were tested. This is theoretical and based <br /> on the assumption that water table receiving waters eventually percolate into the lower aquifers. <br /> RECOMMENDATIONS AND MAINTENANCE <br /> A maintenance program should be established for the wastewater disposal system. Predicting septic <br /> tank pump-out intervals is impossible due to the number of unknowns. These unknowns lead to <br /> changes in the quantity, quality and operational parameters of the proposed septic system. The <br /> Restrooms should be checked a number of times a day to guard against vandalism, such as forcing the <br /> faucets to run continuously. <br /> It is anticipated to have the tank pumped every three years, or pump-out based upon analyzing the <br /> scum and sludge thicknesses after a year of operation. The second maintenance issue will be the <br /> washing off of the septic tank filter periodically,preferably at tank pump-out. A water line with a <br /> hose bibb is adjacent to the septic tank location for filter maintenance. A clean-out must be installed <br /> on the ABS influent tightline from the Restrooms to the septic tank. <br /> As depicted on the Parcel Viewer aerial photograph, a fresh water pipe connects the well to the <br /> pressure tank,in a direct line. This water pipe is buried six feet deep. The east leachlines will <br /> traverse over this water line. EHD will specify the leachline pipe details as the pipes' cross <br /> above the water line, but typically blank(non-perforated) pipe, or encased pipe must extend <br /> five feet on either side of the fresh water line. <br /> The building designer/engineer/architect, the plumber,the landscaper, and the wastewater disposal <br /> system installer must all coordinate so that proper grades are established and maintained. <br /> 14 <br /> Chesney Consulting <br />
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