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SU0011765 SSNL
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SU0011765 SSNL
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Last modified
5/7/2020 11:35:24 AM
Creation date
9/4/2019 11:08:21 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0011765
PE
2666
FACILITY_NAME
PA-1800078
STREET_NUMBER
26783
Direction
N
STREET_NAME
CHEROKEE
STREET_TYPE
LN
City
GALT
Zip
95632-
APN
00511013
ENTERED_DATE
4/25/2018 12:00:00 AM
SITE_LOCATION
26783 N CHEROKEE LN
RECEIVED_DATE
4/23/2018 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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SJGOV\rtan
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FilePath
\MIGRATIONS\C\CHEROKEE\26783\PA-1800078\SU0011765\SS_NL STUDY .PDF
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EHD - Public
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r�2 <br /> The pH of the soil is alkaline at the anticipated soil-effluent interface which has a positive effect in <br /> promoting ammonia and not the nitrate substrate ammonium within the alkaline soil environment. The <br /> CEC measures the ability of the soil to theoretically trap and hold ammonium molecules. The CEC <br /> illustrates a medium potential for the clay soil to retain ammonium molecules that remain as <br /> ammonium and are not converted to ammonia in the soil environment. Nitrification is also hindered <br /> due 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 soil physical and chemical characteristics <br /> that influence nitrate loading: <br /> TABLE 1 <br /> SOIL PROFILE CHARACTERISTICS AND <br /> ANALYTICAL TEST RESULTS <br /> SAMPLE DEPTH AND.. SOIL SOIL NITRATE- pH AND <br /> (SAMPLE NUMBER O CLASSIFICATION NITROGEN CONTENT CATION EXCHANGE CAPACITY <br /> TEST RESULT FORM) In meq/1008 <br /> 36 IN DEPTH(P136) Sandy Loam 1 ppm NO3 N 7.8 9.3 meq/100g <br /> Parcel 1,36 in.Depth <br /> 20 FT DEPTH(P420) Clay f 3 ppm NO,-N 7.0 16.8 meq/100g <br /> Parcel 4,20 ft Depth <br /> C. PERCOLATION TEST RESULTS <br /> SSS§ 6.2. To assess the permeability of each proposed Parcel, all perc test borings and the one <br /> exploratory boring, were drilled with a truck mounted drill rig. Shallow perc tests were drilled to 42 <br /> inches in depth which is the maximum leachline depth. The deep perc tests were drilled to depths <br /> where what appeared to be permeable soil. However, from all deep test results and the exploratory <br /> boring,the deeper soil under the property has limited permeability. The test borings were <br /> completed in the locations depicted on the Site Plan found in Appendix D. <br /> SSS§ 6.3. After drilling,the sidewalls of the shallow borings were scored with a pry-bar to open <br /> potentially smeared soil surfaces that may have occurred due to the clay soil. The de rings <br /> could not be scored,which may also explain some of the impermeability observed. Two inch f <br /> fine gravel was placed at the bottom and three-inch perforated PVC pipe was inserted <br /> boring. After these pro duces, the borings were pre-saturated wi 12 inche�f water <br /> approximatel��s <br /> 'or to the start of testing. <br /> SSS§ 6.4,6.5. On March 5, 2018, percolation testing commenced for Parcels 1 and 2, with Parcels <br /> 3 and 4 tested the next day. Table 2 below illustrates the applicable perc test data, along with <br /> corresponding Application Rates in gallons of effluent accepted per square foot of soil per based <br /> upon the perc rate obtained. The test results indicate only one test boring had an acceptable rate after <br /> complete soil saturation. A perc rate of 60 min/inch or faster is considered acceptable for shallow test <br /> borings and 30 min/in for deeper test borings. <br /> Page -3- <br /> Chesney Consulting <br />
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