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SU0011858 SSNL
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SU0011858 SSNL
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Last modified
5/7/2020 11:35:29 AM
Creation date
9/5/2019 11:18:18 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0011858
PE
2691
FACILITY_NAME
PA-1800162
STREET_NUMBER
20500
Direction
S
STREET_NAME
HOLLY
STREET_TYPE
DR
City
TRACY
Zip
95304-
APN
21216020
ENTERED_DATE
7/11/2018 12:00:00 AM
SITE_LOCATION
20500 S HOLLY DR
RECEIVED_DATE
7/11/2018 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\H\HOLLY\20500\PA-1800162\SU0011858\SS_NL STUDY.PDF
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EHD - Public
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"a <br /> r <br /> II. SOIL SUITABILITY STUDY FINDINGS <br /> A. SUBJECT PROPERTY AND SURROUNDING STUDY AREA INFORMATION <br /> SSS§ 1.1. Land use to the immediate west and south is agricultural production land. To the east is <br /> the City of Tracy Wastewater Treatment facility and to the north is a commercial recycling facility. <br /> SSS§ 3.1,3.2,3.3,3.4,3.5,3.6,3.7, 6.8. Applications on EHD microfiche files were not available <br /> for review to determine the number of permits issued for repairs/replacements/additions to existing <br /> systems within the one-half mile radius study area. The septic systems in this locale are extremely <br /> sparse so data is-limited. Given the clay content of the on-site and surrounding soils, septic system <br /> longevity is most likely limited and septic system failures will eventually occur. The project site has <br /> level terrain; consequently,there is no need to incorporate design considerations for slopes within the <br /> effluent disposal area. <br /> B. SOIL PHYSICAL CHARACTERISTICS AND ANALYTICAL TEST RESULTS <br /> SSS§ 5.2. The United States Department of Agriculture-Natural Resource Conservation Service <br /> (USDA-NRCS) indicates the property soils are Capay clay(#118). The surface and subsurface soil <br /> investigation began on June 13,2016 with the drilling of one 36-inch deep perc test boring. <br /> In addition to the perc test boring, an excavator was used to explore the underlying soils and to <br /> remove a concrete structure. An excavation down to 12 ft was conducted with the soils a consistent <br /> clay. No water(water table/groundwater)was encountered. <br /> NLS§ 1.1, 1.2. Auger cuttings were sampled from the bottom of the 3-ft test boring for chemical <br /> analysis. As noted on the A&L Laboratory Soil Report in Appendix C, analyses of the soil sample <br /> quantifies a number of constituents that influence nitrate loading for this project. The important <br /> parameters for nitrate loading assessment are the organic matter,pH, cation exchange capacity <br /> } <br /> (CEC), and the nitrate-nitrogen content of the soil. <br /> As noted,the organic matter is 1%which translates to an Estimated Nitrogen Release(ENR) of 54 <br /> lbs. of N/acre. This is an insignificant concentration of nitrogen over a one acre area. The soil <br /> nitrate-nitrogen concentration is high at 73 ppm. It is unknown why this high concentration exists, <br /> s but this is only a slight concern given the clay soil will promote denitrification. <br /> s <br /> Because septic effluent is composed predominately of ammonium(NH4),the pH, along with the CEC, <br /> qJ are significant influences on the ammonium molecules. The pH of the soil is alkaline at the proposed <br /> soil-effluent interface which has a positive effect in promoting ammonia and not the nitrate substrate <br /> ammonium within the alkaline soil environment. The CEC measures the ability of the soil to <br /> theoretically trap and hold ammonium molecules. The CEC illustrates a high potential for the clay soil <br /> for retention of ammonium molecules that remain as ammonium and are not converted to ammonia in <br /> the soil environment. Nitrification is also hindered due to the alkaline pH and from the anaerobic <br /> micro-sites within the clay soil. <br /> Page-2- <br /> Chesney Consulting <br />
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