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SU0009787 SSNL
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SU0009787 SSNL
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Last modified
5/7/2020 11:34:13 AM
Creation date
9/9/2019 11:05:22 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0009787
PE
2626
FACILITY_NAME
PA-1300173
STREET_NUMBER
13391
Direction
E
STREET_NAME
WEST RIPON
STREET_TYPE
RD
City
RIPON
Zip
95366-
APN
22817038
ENTERED_DATE
10/7/2013 12:00:00 AM
SITE_LOCATION
13391 E WEST RIPON RD
RECEIVED_DATE
10/4/2013 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\rtan
Supplemental fields
FilePath
\MIGRATIONS\W\WEST RIPON\13391\PA-1300173\SU0009787\SS_NL STUDY .PDF
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EHD - Public
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Because septic effluent is composed predominately of ammonium (NH4),the pH, along with the <br /> CEC, have significant influence on ammonium molecules. The pH of the soil is alkaline at 8.1 <br /> which will have a large effect on ammonium formation and stability. An alkaline environment will <br /> promote ammonia to remain in the ammonia form,thus retarding nitrification. The CEC measures <br /> the ability of the soil to theoretically trap and hold ammonium molecules. Cation Exchange <br /> Capacities of the soil sample is comparatively low due to the sand content. Therefore,there is a <br /> smaller potential for the retention of ammonium molecules for microbial uptake and denitrification <br /> potential.l. <br /> NLS§3.3, SSS§ 5.3'� Table 1 below summarizes the chemical and physical surface and subsurface <br /> soil characteristics encountered from the soil sample. <br /> TABLE <br /> SOIL PROFILE CHARACTERISTICS AND <br /> ANALYTICAL TEST RESULTS <br /> SAMPLE LOCATION SAND,SILT.AND SOIL SOIL NITROGEN pH AND <br /> AND SAMPLE DEPTH CLAY CLASSIFICATION CONTENT CATION EXCHANGE <br /> PERCENTAGES CAPACTrV <br /> DISPOSAL FIELD AREA 64%24% 12% Sandy loam I ppmNO,-N 8.1 7.4 meq/tong <br /> 3 FT IN DEPTH <br /> C. PERCOLATION TEST RESULTS <br /> SSS§ 6.2 To assess the permeability capability of the proposed filter bed disposal system area, a <br /> percolation test was completed in the location depicted in the Site Plan. As referenced, the test depth <br /> was 36 inches below existing grade. <br /> SSS§ 6.3. On May 11, 2017, the perc test boring was drilled. The sidewall of the boring was scored <br /> with a pry-bar to open potentially smeared sidewalls. Two inches of pea gravel was placed at the <br /> bottom and three-inch perforated PVC pipe was inserted. The boring was then pre-saturated with 12 <br /> inches of water approximately 24 hrs before the start of testing. <br /> SSS§ 6;6.5. On May 12, 2017, percolation testing commenced. No standing water was observed <br /> after the 24-hr soak period. Consequently, EHD Perc Test Procedure#2 was conducted in which <br /> testing was done over a four-hour period to induce maximum soil saturation. The test results <br /> indicate a rapid perc rate at 8.6 minutes per inch (min/in). <br /> A summary of the perc test results with corresponding application rates in gallons of effluent <br /> accepted per square foot of soil per day are found in Table 2: <br /> 3 <br />
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