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SU0005666 SSNL
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SU0005666 SSNL
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Last modified
5/7/2020 11:31:42 AM
Creation date
9/9/2019 10:42:13 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0005666
PE
2690
FACILITY_NAME
PA-0500628
STREET_NUMBER
16501
Direction
S
STREET_NAME
TRACY
STREET_TYPE
BLVD
City
TRACY
Zip
95304
APN
18912013 &
ENTERED_DATE
10/6/2005 12:00:00 AM
SITE_LOCATION
16501 S TRACY BLVD
RECEIVED_DATE
10/5/2005 12:00:00 AM
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\T\TRACY\16501\PA-0500628\SU0005666\SS STDY.PDF
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EHD - Public
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I <br /> (§ 3.4) The subject property is in an area designated as "High Water Table"by EHD's colored <br /> map denoting the various soil types and septic system requirements throughout San Joaquin <br /> County. Consequently, only leachlines or filter beds are allowed to be installed in this area of the <br /> County. <br /> (§ 5.1 and 6.0) SOIL PROFILE AND PERCOLATION TESTING <br /> (§ 5.4) As noted on the USDA Soil Survey map, the on-site soils consist of Grangeville fine sandy <br /> loam, #166. Typically, this soil type is moderately well-drained due to the levee system, with <br /> moderately rapid permeability at depths below 12 inches. As discussed below, the shallow perc test <br /> for Parcel 1 had an excellent percolation rate. <br /> (§ 5.2, 5.3, and 5.4) A Log of Boring using the Unified Soil Classification System (USCS), and the <br /> United States Department of Agriculture (USDA) as observed from the 36-inch deep perc test boring <br /> is found on the EHD PERCOLATION TEST DATA SHEETS. Generally, the soils show a clayey, <br /> silty soil on the surface, then a consistent silty sand soil under the surface layer down to three feet. <br /> Soil characteristics were also determined by a particle size analysis conducted by A & L labs on the <br /> soil from the 36 inch depth. The soil is classified(USDA) as a sandy loam: 63% sand, 26% silt and <br /> 11% clay. <br /> (§ 6.1)Percolation testing was conducted near the end of the existing southernmost leachline, as <br /> illustrated on the Site Schematic and Tentative Lot Line Adjustment Map found in Appendix B. <br /> This test location was decided upon because effluent typically travels the length of the perforated <br /> pipe before depositing out the end. As the biomat develops, or as the soil becomes saturated, the <br /> effluent then trickles from the perforations further up the pipe. <br /> (§ 6.2, 6.3 and 6.5) On January 25, 2006, 1400 hrs, one shallow pere test boring of 36 inches was <br /> hand-drilled. The sidewalls of the boring were scored with a pry-bar and the loose material <br /> removed. Two inches of fine gravel was placed at the bottom and three-inch perforated PVC pipe <br /> was inserted in the test boring. The boring was pre-saturated on January 29, 2006 at 1100 hrs with <br /> 12 inches of water. <br /> (§ 6.4) On January 30, 2006, 0800 hrs,percolation testing commenced. There was no standing <br /> water after the 24-hour soak period in the shallow perc tests boring, as illustrated in Table 1 below. <br /> Consequently, EHD Perc Test Procedure#2 was conducted for this test. The last half hour of the <br /> four-hour test was witnessed by Ted Tasiopoulos, R.E.H.S. of the San Joaquin County <br /> Environmental Health Department. Perc test results reveal a rate of 7.1 minutes/inch (min/in). The <br /> maximum acceptable perc rate is 60 min/in for shallow perc tests. <br /> (§ 5.4 and 6.8) The following Table illustrates the proposed Parcel number, septic system <br /> structure based on depth of the passing perc rate, proposed acreage, soil characteristics,post soak <br /> period status and perc test results for the respective perc test depth: <br /> Page -2 _J/ <br /> - <br /> Chesney Consulting <br />
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