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SU0006274 SSNL
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SU0006274 SSNL
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Last modified
12/13/2019 2:44:06 PM
Creation date
9/6/2019 10:25:59 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0006274
PE
2666
FACILITY_NAME
PA-0600524
STREET_NUMBER
2850
Direction
S
STREET_NAME
JACK TONE
STREET_TYPE
RD
City
STOCKTON
APN
10324016 17 18
ENTERED_DATE
9/27/2006 12:00:00 AM
SITE_LOCATION
2850 S JACK TONE RD
RECEIVED_DATE
9/26/2006 12:00:00 AM
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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SJGOV\sballwahn
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\MIGRATIONS\J\JACK TONE\2850\PA-0600524\SU0006274\SS STDY.PDF
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EHD - Public
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Farmington Murphy Property N%/ Page 2 <br /> Our Project Number: E07213A <br /> December 24, 2007 <br /> The Hantzsche and Fennemore approach is "...a conservative (worst case) first approximation <br /> of ground-water nitrate-nitrogen concentration resulting from the combined effect of on-site <br /> sewage disposal systems and precipitation. This (the equation and approach) is for estimation <br /> of long-term effect (i.e., over years) on ground-water quality, and is not intended for prediction <br /> of seasonal changes" (Hantzsche and Finnemore, 1992). <br /> The method takes into account the development area, soil denitrifaction factor, rainfall volume, <br /> rainfall nitrate concentration, waste effluent quantity, and waste effluent nitrate concentration. <br /> The formula, assumptions and calculations used for the analysis are shown on Plates 1 and 2. <br /> The units of nitrate used in the mass balance equation are nitrate-N, whose maximum drinking <br /> water contaminant level is 10 mg/L. <br /> The specific property use is undetermined at this time; therefore, our office will perform at <br /> scenario which represents the maximum allowable quantity and concentration of total nitrogen <br /> from the site. When the exact project is determined, a nitrate loading update study could be <br /> performed to determine weather ground water will be impacted from the project. <br /> 1.0 CHEMICAL AND PHYSICAL PROPERTIES OF SOIL <br /> 1.1 Chemical and Physical Soil Properties <br /> For a discussion of on-site soil properties, refer to Section 5 of the SSS completed by Dillon & <br /> Murphy. <br /> 1.2 Mass Transport Soil Properties <br /> The percolation tests have revealed that the soils are permeable to the maximum depth of <br /> exploration of 42-inches. These soils will allow moderate infiltration of water through the <br /> surface soils. The longer the effluent remains near the surface, the more treatment occurs due <br /> to natural processes within the soil. <br /> The San Joaquin County Soil Survey indicates clayey soils exist to a depth of 60 inches. A San <br /> Joaquin County ground water investigation report with maps prepared by the California <br /> Department of Water Resources was checked for the sand thickness. These maps indicate that <br /> no mappable sand exists in the vicinity of Jack Tone Road and Highway 4 to a maximum depth <br /> of 50 feet (DWR, 1967). Finer grain soils tend to slow the downward movement of percolating <br /> effluent from a septic system disposal field when compared to sandy soils. Due to the lack of <br /> sandy soils below the site, the potential impact to deep ground water is reduced when <br /> compared to other sites with thicker sections of sandy soil. <br /> 2.0 GROUND WATER ANALYSIS <br /> 2.1 Regional Ground Water <br /> Regional ground water information, including depth to ground water and directional ground <br /> water gradient, is discussed in Section 4.1 of the SSS completed by Dillon & Murphy. <br /> ,.44 <br /> 902 Industrial Way•Lodi,CA 95240•209.367.3701 •Fax 209.369.4228 ©2007 Neil O.Anderson&Associates.Inc <br />
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