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SR0033856_SSNL
Environmental Health - Public
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SR0033856_SSNL
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Entry Properties
Last modified
11/16/2020 11:14:48 AM
Creation date
9/4/2019 6:10:10 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0033856
PE
2601
STREET_NUMBER
8923
Direction
W
STREET_NAME
ETCHEVERRY
STREET_TYPE
DR
City
TRACY
Zip
95304
APN
24812002
ENTERED_DATE
5/16/2003 12:00:00 AM
SITE_LOCATION
8923 W ETCHEVERRY DR
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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FilePath
\MIGRATIONS\E\ETCHEVERRY\8293\SS STDY\SR0033856.PDF
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EHD - Public
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k, <br /> II. SOIL INVESTIGATION FINDINGS <br /> j' A. SUBJECT PROPERTY AND SURROUNDING STUDY AREA INFORMATION <br />'k The subject property was owned by Mr. Rinauro's father until recently purchased by Larry and <br /> Sharon Rinauro. It is located near the northeast corner of Etcheverry Drive and MacArthur Drive. It <br /> is bound to the north, south, east and west by single family residences, mostly on 1.5 acre parcels, and <br /> to the west by a new housing subdivision that is sewered and with much higher densities. The wide- <br /> range surrounding land use, and in particular upgradient land use, has been primarily in gravel mining <br /> and agricultural production for many decades. This is evidenced by the United States Department of <br /> Agriculture (USDA) Soil Maps for San Joaquin County for this area. <br /> Applications on file with the County Environmental Health Department reveal that there have been no <br /> permits issued for additions to existing systems in the one-half mile radius study area, which primarily <br /> includes Etcheverry Drive to the south and Almendra Way to the north. The apparent non-existent <br /> septic system failures in this area may be attributable to most systems having pits and sumps installed. <br /> However, the Environmental Health Department no longer allows sumps and pits in this area. , <br /> l B. SOIL PHYSICAL AND CHEMICAL CHARACTERISTICS <br /> E <br /> 1. SURFACE AND SUBSURFACE SOILS <br /> The shallow soil profile was determined during the drilling of the percolation test boring. Particle <br /> Size and Chemical Analysis was done on a soil sample from the bottom of the percolation test <br /> boring at 42 inches. The test results are denoted on the attached SOIL ANALYSIS REPORT. The <br /> soil has been classified by the laboratory as a loam, which correlates with the United States <br /> Department of Agriculture -Natural Resources Conservation Service (USDA-NRCS) classification <br /> of the on-site soils as a Stomar clay loam (#252). The Unified Soil Classification System (USCS) <br /> identifies this soil as a clayey silt(CL-ML). The fine soil material (clay and silt sized particles) <br /> promote biological treatment of the effluent. Biological treatment includes the destruction of <br /> bacteria and viruses, as well as promotion of denitrification. Gravel strata encountered at <br /> approximately eight feet below grade are illustrated on the attached logs of boring for water wells <br /> drilled in this area. <br /> Since septic effluent is composed predominately of ammonium (NHg) ions, the pH, along with the <br /> Cation Exchange Capacity, have significant influence on ammonium molecules. The pH of the soil, <br /> which is somewhat alkaline at a pH of 7.6 and may inhibit ammonium formation and stability. <br /> Secondly, the CEC measures the ability of the soil to theoretically trap and hold ammonium <br /> molecules. The clayey subsurface soils have a comparatively high CEC of approximately 21.4, <br /> which should increase the retention of ammonium molecules for microbial uptake and nitrification <br /> suppression(nitrate formation). In cation exchange, a positively charged ion within the clay <br /> complex is replaced and released by another type of ion. Ionic exchange,through its effects on <br /> nutrient availability and acidity, has a tremendous effect on biological and chemical <br /> Page -2- <br /> { <br /> Chesney Consufting <br />
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