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SU0009004 SSNL
Environmental Health - Public
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SU0009004 SSNL
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Last modified
5/7/2020 11:33:48 AM
Creation date
9/9/2019 10:55:03 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0009004
PE
2625
FACILITY_NAME
PA-1100229
STREET_NUMBER
12815
Direction
W
STREET_NAME
VALPICO
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
24008011
ENTERED_DATE
12/19/2011 12:00:00 AM
SITE_LOCATION
12815 W VALPICO RD
RECEIVED_DATE
12/16/2011 12:00:00 AM
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\V\VALPICO\12815\PA-1100229\SU0009004\NL STDY.PDF
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EHD - Public
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S§ 5.2 As detailed in the original Studies completed for the nearby St. Bernard's pro7deepcompleted to determine subsurface soil characteristics and depth to groundwabelow regional grade, exists a silty/clayey gravelly/cobble soil that extends down to grou <br /> Rust mottling was not observed in the percolation test borings which would indicate seasonal soil <br /> saturation. <br /> Zj1A. _2?As <br /> noted on the Denele Laboratory Soil Analysis Reports found in Appendix B, <br /> es of the soil samples from the disposal area quantify the constituents that will <br /> influence nitrate loading from this project. The important parameters for nitrate loading assessment <br /> are the organic matter,pH, cation exchange capacity(CEC), and nitrate-nitrogen content. <br /> The nitrate-nitrogen and organic matter concentrations are very low at the 36-48 inch depth. This <br /> suggests a low potential for future nitrate-nitrogen loading from indigenous nitrogen content within <br /> the soil. Since septic effluent is composed predominately of ammonium (NH4),the pH, along with <br /> the CEC, are significant influences on ammonium molecules. The pH of the soil is alkaline which <br /> may inhibit ammonium formation and stability, and may create a propensity for ammonia(NH3) <br /> formation. The CEC measures the ability of the soil to theoretically trap and hold ammonium <br /> molecules. Cation Exchange Capacities of the soil samples are high at the measured depth. This <br /> suggests there is a high potential for the retention of ammonium molecules for microbial uptake, and <br /> suppressi of nitrification. <br /> _XW5.3 able 2 below summarizes the subsurface soil characteristics encountered from the <br /> sam pth between 36-48 inches below grade: <br /> TABLE 2 <br /> SOIL PROFILE CHARACTERISTICS AND <br /> ANALYTICAL TEST RESULTS. . <br /> SAMPLE DEPTH SOIL NITROGEN CATION EXCHANGE pH AND Ec SOIL <br /> CONTENT CAPACITY CLASSIFICATION <br /> 3-4 FT DEPTH 5.0 ppm NO,-N 35.2 meq/1008 7.6 0.60 Sandy Loam <br /> (3648 inches) <br /> C. PERCOLATION TEST RESULTS <br /> SSS 6.2. o assess the permeability of the on-site soils,two percolation test bor mgs-weR <br /> co lete in the proposed leachfield location as depicted in the Site Plan found ih ApMadix.,�1 T- e <br /> "EH fficial"pert test depth at 36 inches below existing grade gives a comparatively detailed <br /> observation of subsurface permeability from approximately 30 to 36 inches in depth. The second test <br /> depth at 48 inches was conducted to measure any permeability changes at the four ft depth. As noted <br /> in Table 3 below,there is rapid permeability at the 36-inch depth, but permeability decreases by 35% <br /> at the 48-inch depth. <br /> 3 <br /> Chesney Consumg <br />
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