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SU0006676_SSNL
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SU0006676_SSNL
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Last modified
11/19/2024 1:52:18 PM
Creation date
9/8/2019 12:49:36 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0006676
PE
2691
FACILITY_NAME
PA-0700359
STREET_NUMBER
10967
Direction
N
STREET_NAME
STATE ROUTE 99
City
LODI
Zip
95241
APN
05914037
ENTERED_DATE
8/3/2007 12:00:00 AM
SITE_LOCATION
10967 N HWY 99
RECEIVED_DATE
8/2/2007 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\rtan
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FilePath
\MIGRATIONS\N\HWY 99\10967\PA-0700359\SU0006676\NL STDY.PDF
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EHD - Public
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�Becauseptic effluent is composed predominately of ammonium (NH,), the pH, along with the <br /> CEC, are significant influences on ammonium molecules. The pH of the soil is acidic at the surface <br /> but alkaline at the deeper depths which may have an effect on ammonium formation and stability. <br /> The CEC measures the ability of the soil to theoretically trap and hold ammonium molecules. <br /> Cation Exchange Capacities of the soil samples are comparatively low, except at the surface. This <br /> ti> suggests there is a low-to-medium potential for the retention of ammonium molecules for microbial <br /> uptake. <br /> NLS§ 3.3, SSS§ 5.3, 5.4. Table 1 below summarizes the surface and subsurface soil physical and <br /> chemical characteristics from the six soil samples retrieved from the exploratory boring: <br /> TABLE 1 <br /> SOIL PROFILE CHARACTERISTICS AND <br /> ANALYTICAL TEST RESULTS <br /> SAMPLE DEPTH AND SAND,SILT AND SOIL SOH,NITRATE- pH AND <br /> (SAMPLE NUMBER ON CLAY CLASSIFICATION NITROGEN CATION EXCHANGE <br /> TEST RESULT FORM) PERCENTAGES CONTENT CAPACITY <br /> 0 FT DEPTH 37%, 30%, 33% Clay Loam 13 ppm NOS N 6.7 17.9 meq/1008 <br /> 5 FT DEPTH 41%,36%,23% Loam 8 ppm NO;N 7.8 12.8 meq/1009 <br /> 10 FT DEPTH 87%, 6%,7% Loamy Sand 7 ppm NO,N 8.3 4.5 meq/100g <br /> 15 FT DEPTH 31%,36%,33% Clay Loam 11 ppm NO;N 7.7 9.5 meq/100g <br /> 20 FT DEPTH 65%, 16%, 19% Sandy Loam 7 ppm NON 7.8 7.7 meq/1008 <br /> 25 FT DEPTH 45%, 28%,27% Clay Loam 7 ppm NO,-N 7.5 9.7 meq/1009 <br /> C. PERCOLATION TEST RESULTS <br /> SSS§ 6.2. To assess the permeability at prescribed depths of the on-site soils, the aforementioned <br /> four percolation test borings were completed in the locations depicted on the District Viewer Map (le S) <br /> found in Appendix C. <br /> SSS§ 6.3. After drilling the perc test borings, the sidewalls of the shallow boring was scored with a <br /> pry-bar to open potentially smeared sidewalls. The deeper borings could not be scored due to their <br /> depths. Two inches of fine gravel was placed at the bottom and three-inch perforated PVC pipe was 3� <br /> inserted in each test boring. On October 14, 2007, each boring was pre-saturated with 12 inches of <br /> water at 0900 hrs, 24 hrs before the start of testing. <br /> SSS§ 6.4, 6.5. On October 15, 2007, percolation testing commenced. Approximately four inches of <br /> standing water was observed after the 24-hr soak period in the 42-inch deep hole, consequently, u <br /> EHD Perc Test Procedure#I was conducted for this test boring. <br /> 4 <br /> Chesney Consulting <br />
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