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SR0080748 SSNL
Environmental Health - Public
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SR0080748 SSNL
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Last modified
3/19/2020 9:47:17 AM
Creation date
12/6/2019 10:12:16 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0080748
PE
2602
STREET_NUMBER
9375
Direction
W
STREET_NAME
SUGAR
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
21216017
ENTERED_DATE
6/14/2019 12:00:00 AM
SITE_LOCATION
9375 W SUGAR RD
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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The reason for this extremely high soil nitrogen content, is due to the fact that the prior land use was <br />as an agricultural by-product recycler. Mounds of biomass were processed and stored in this area, <br />thus leaching nitrogen into the soil and groundwater. <br />Because septic effluent is composed predominately of ammonium (NH4), the pH, along with the CEC, <br />are significant influences on ammonium molecules. The pH of the soil is slightly alkaline which has a <br />positive effect in promoting ammonia and not the nitrate substrate ammonium within the soil <br />environment. <br />The CEC measures the ability of the soil to theoretically trap and hold ammonium molecules. At 27.3 <br />meq/100g, the CEC illustrates a very high potential for the clay soil to retain ammonium molecules <br />that remain as ammonium. Nitrification is also hindered due to the alkaline pH and from the anaerobic <br />micro -sites within the clay soil. <br />NLS§ 3.3, SSS§ 5.3, 5.4. Table 1 below summarizes the encountered soil physical and chemical <br />characteristics: <br />TABLE I <br />SOIL PROFILE CHARACTERISTICS AND <br />ANALYTICAL TEST RESULTS <br />SAMPLE DEPTH AND <br />SOIL <br />SOIL NITRATE -NITROGEN <br />pH AND <br />(SAMPLE NUMBER ON <br />CLASSIFICATION <br />CONTENT <br />CATION EXCHANGE CAPACITY <br />TEST RESULT FORM) <br />In meq/100g <br />BDG24 <br />Silty Clay Loam <br />189 pprn NO, -N/450 Units <br />7.3 27.3 me /100 <br />C. PERCOLATION TEST RESULTS <br />SSS§ 6.2. To assess the permeability in the 36" boring, which corresponds with the approximate <br />soil -effluent interface elevation, the aforementioned percolation test borings were completed in the <br />locations depicted on the Site Plan found in Appendix C. <br />SSS§ 6.3. After drilling, the sidewalls of the borings were scored with a pry -bar to open potentially <br />smeared soil surfaces that may have occurred due to the clay soil, and the cuttings removed. Two <br />inches of gravel was placed at the bottom and three-inch perforated PVC pipe was inserted in each <br />test boring. After these procedures, the borings were pre -saturated with 12 inches of water <br />approximately 24 hrs prior to the start of testing. <br />SSS§ 6.4, 6.5. On February 25, 2019, percolation testing commenced at 0800 hrs. No standing <br />water was observed after the 24 -hr soak period. Consequently, EHD Perc Test Procedure #2 was <br />conducted. Testing was done over a four-hour period to induce maximum soil saturation, which <br />was easily achieved since this rainy season was one of the heaviest on record. <br />-3- <br />Chesney Consulting <br />
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