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SR0081560_SSNL
Environmental Health - Public
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SR0081560_SSNL
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Last modified
2/10/2022 2:13:34 PM
Creation date
3/19/2021 9:49:49 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0081560
PE
2602
STREET_NUMBER
7707
Direction
S
STREET_NAME
ASH
STREET_TYPE
ST
City
FRENCH CAMP
Zip
95231
APN
19310013
ENTERED_DATE
12/23/2019 12:00:00 AM
SITE_LOCATION
7707 S ASH ST
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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D. OPERATIONAL PARAMETERS AND COMPONENTS <br />SSS§ 3.7. An overview of the system operation to serve the proposed residential structure is as <br />follows: Influent will gravity flow into a P&L Concrete, Inc. standard precast, 1,200 gallon septic <br />tank. The tank must be set perfectly level and as high in elevation as possible. A Polylok® PL-68 <br />effluent filter is to be installed on the sanitary tees of both side outlets of this tank. Clarified <br />effluent will gravity flow equally from both side outlets to 3" perforated pipe running down the <br />centers of both 7 ft wide, 37 ft long filter beds. Perforated pipe is to run level, with capped ends to <br />force as equal effluent distribution as possible. A minimum of 12" of washed drain rock, and <br />preferably 18" of rock, is to be placed under the perforated pipe, and extending 2" above the <br />perforated pipe. Geotechnical filter fabric is to be placed over the drain rock and backfilled to final <br />grade with native soil. Due to the nitrate loading calculations demonstrating a loading theoretically <br />exceeding the Maximum Contaminate Level, nitrate loading mitigation measures are discussed in <br />the Conclusion Section below <br />V. CONCLUSIONS AND RECOMMENDATIONS <br />NLS§ 4.2. The shallow subsurface soils underlying the subject property where the two new filter <br />bed disposal areas are to be installed, reveal a sandy loam soil structure with comparatively rapid <br />permeability and a high degree of natural denitrification potential. This potential is based upon the <br />observed significant decrease in nitrate-nitrogen concentration with increasing soil depth. <br />NLS§ 4.1. As referenced, the nitrate loading calculations show the resultant effluent from the <br />proposed primary residential structure will theoretically possess a concentration of approximately <br />32 ppm as nitrate-nitrogen, which exceeds the MCL for nitrate-nitrogen at 10 ppm. Consequently, <br />nitrate impact mitigation measures must be implemented. <br />The importation of organic material onto the floor of the filter bed must be done to prevent the <br />nitrification process at the soil-effluent interface. A sample of sawdust (referenced as "White <br />Wood Fines") was obtained from Recology Blossom Valley Organics, located at 6133 Hammett <br />Ct., Modesto, CA and submitted for laboratory analysis with the following results: <br />TABLE 2 <br />ANALYTE 1 <br />RESULTS <br />Nitrate Nitrogen <0.003% <br />Ammonia Nitrogen 0.010% <br />Organic Nitrogen 0.27% <br />E.C. 1 7 mmhos/cm <br />pH 6.6 <br />C:N Ratio 165:1 <br />Page -7- f <br />Chesney Consulting
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