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SU0011022 SSNL
Environmental Health - Public
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SU0011022 SSNL
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Last modified
11/19/2024 10:20:00 AM
Creation date
9/4/2019 6:03:38 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0011022
PE
2632
FACILITY_NAME
PA-1600160
STREET_NUMBER
7777
Direction
W
STREET_NAME
ELEVENTH
STREET_TYPE
ST
City
TRACY
Zip
95304-
APN
25014011
ENTERED_DATE
8/17/2016 12:00:00 AM
SITE_LOCATION
7777 W ELEVENTH ST
RECEIVED_DATE
8/17/2016 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\E\ELEVENTH\7777\PA-1600160\SU0011022\SS_NL STUDY .PDF
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EHD - Public
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At this pH, ammonium will have a propensity to remain in the ammonium form and not as ammonia. <br /> The CEC measures the ability of the soil to theoretically trap and hold ammonium molecules. The / <br /> CEC at 15.7 meq/100g illustrates a medium-high potential for the clay soil to retain ammonium <br /> molecules within thesoilenvironment. <br /> NLS§ 3.3 SSS§ 5.3,5.4/ Table 1 below summarizes the soil physical and chemical <br /> characteristics at the proposed soil-effluent interface: <br /> TABLE 1 <br /> SOIL PROFILE CHARACTERISTICS AND <br /> ANALYTICAL TEST RESULTS <br /> SAMPLEDF.PTII AND SOIL SOIL NTT'R.A'rE- PH AND <br /> (SAMPLE NUMBER ON CLASSIFICATION NITROGEN CONTENT CATION EXCHANGE CAPACITY <br /> TEST RESULT FORM).. . In meq/100g <br /> 3 FT DEPTH 36" Clay Loam I 1 m NO.-N 7.1 15. mec/100< <br /> C. PERCOLATION TEST RESULTS <br /> SSS§ 6.2. To assess the permeability at the test depth which corresponds with the soil-effluent <br /> interface, the percolation test boring was completed in the location depicted on the Septic System <br /> design plans found in Appendix B. <br /> SSS§ 6.3. After drilling, the sidewall of the boring was scored with a pry-bar to open potentially <br /> smeared soil surfaces that may have occurred due to the clay soil. Two inches of pea gravel was <br /> placed at the bottom and a three-inch perforated PVC pipe was inserted in the test boring. After <br /> these procedures,the boring was pre-saturated with 12 inches of water approximately 24 hrs prior <br /> to the start of testing. <br /> l <br /> SSS§ 6.4, 6.5. On May 4, 2017, percolation testing commenced at 0600 hrs. No standing water <br /> 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. <br /> The test results indicate a perc rate of 11.5 mi'n/in after complete soil saturation. A perc rate of 60 <br /> min/inch or faster is considered acceptable. 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 below: <br /> TABLE2 <br /> PERCOLATION TEST RESULTS WITH CORRESPONDING <br /> APPLICATION RATES IN GALLONS/FTS/DAY <br /> 36 INCH DEEP PERC TEST BORING 11.5 min/inch / 0.771 gallons/ft'/day <br /> PERCOLATION RATE/APPLICATION RATE <br /> OFFICIAL PERC TEST <br /> Application Rates adapted from Waste Quality ConlroiforSMw Design,Operetim andM.., ,.of On-site Wastewater Treatment Systems,based on the Pero Rate. <br /> Page -3- <br />
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