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SR0080751 SSNL
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SR0080751 SSNL
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Last modified
12/3/2019 4:01:11 PM
Creation date
12/3/2019 3:38:55 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0080751
PE
4301
STREET_NUMBER
20500
Direction
S
STREET_NAME
HOLLY
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
21216020
ENTERED_DATE
6/14/2019 12:00:00 AM
SITE_LOCATION
20500 S HOLLY DR
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
Scanner
TSok
Tags
EHD - Public
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The CEC measures the ability of the soil to theoretically trap and hold ammonium molecules. All four <br /> sample sites possess very high CEC and illustrates a high potential for the clay soil to retain <br /> ammonium molecules that remain as ammonium and do not nitrify. Nitrification is also hindered due <br /> to the alkaline pH and from the anaerobic 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 from the four test locations: <br /> TABLE 1 <br /> SOIL PROFILE CHARACTERISTICS AND <br /> ANALYTICAL TEST RESULTS <br /> SAMPLE NUMBER ON SOIL SAMPLE DEPTH NITRATE- pH AND <br /> TEST RESULT FORM CLASSIFICATION NITROGEN CONTENT AND CATION EXCHANGE <br /> (SAMPLE DEPTH=36") AND CLAY"% DECREASE%FROM SURFACE CAPACITY <br /> CONCENTRATION (CEC) <br /> (Surface Soil=14 ppm) <br /> BD-AS(Bldg A-South) Clay- 50% 10 ppm NO3-N 29%Decrease 8.1 34.3 meq/100g <br /> BD-BS(Bldg B-South) Clay Loam-35% 14 ppm NO,-N Same 8.3 25.3 meq/100g <br /> t <br /> AN(Bldg A-North) Clay Loam-38% 10 ppm NO,-N 29%Decrease 8.4 27.8 meq/100g <br /> BN(Bld B-North) Clay Loam- 36% 5 ppm NO;-N 64%Decrease 7.8 34.9 meg/I OO <br /> C. PERCOLATION TEST RESULTS <br /> SSS§ 6.2. To assess the permeability in the four test borings, the aforementioned percolation test <br /> borings were completed in the 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 March 19, 2019, percolation testing commenced for the South disposal areas, <br /> and on April 1, 2019 for the North disposal areas for Buildings A&B. No standing water was <br /> observed after the 24-hr soak period. Consequently, EHD Perc Test Procedure #2 was conducted. <br /> Testing was done over a four-hour period to induce maximum soil saturation, which was easily <br /> achieved since this rainy season was one of the heaviest on record. <br /> The test results indicate a perc rate after complete soil saturation of 41.7 min/in and 125 min/in for the <br /> South tests and 35.7 min/in for both North tests. A perc rate of 60 min/inch or faster is considered <br /> passing and rates slower than this require an engineered system. The 125 min/in rate in the SWC or <br /> the property can be considered an anomaly. A summary of the perc test results with corresponding <br /> application rates in gallons of effluent accepted per square foot of soil per day are illustrated in Table <br /> 2 below: <br /> I <br /> Page-3- <br /> Chesney Consulting <br />
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