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SU0007602_SSNL
EnvironmentalHealth
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2600 - Land Use Program
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PA-0900033
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SU0007602_SSNL
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Last modified
11/20/2024 9:22:01 AM
Creation date
9/4/2019 6:17:42 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0007602
PE
2666
FACILITY_NAME
PA-0900033
STREET_NUMBER
17436
Direction
N
STREET_NAME
STATE ROUTE 88
City
LOCKEFORD
APN
05125012 13
ENTERED_DATE
2/24/2009 12:00:00 AM
SITE_LOCATION
17436 N HWY 88
RECEIVED_DATE
2/23/2009 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\E\HWY 88\17436\PA-0900033\SU0007602\SS STDY.PDF \MIGRATIONS\E\HWY 88\17436\PA-0900033\SU0007602\NL STDY.PDF
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EHD - Public
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+ Page 2 <br /> Spanos Property <br /> Our Project Number: LGS090501 <br /> January 30, 2009 <br /> /hese processes would generally contribute to additional reduction of nitrate-nitrogen <br /> concentrations in ground water to the extent that the nitrate-nitrogen concentration of ground- <br /> water flow from up-gradient areas is lower." <br /> f <br /> -The Hantxsche 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 /> t of seasonal changes" (Hantzsche and Finnemore, 1992). <br /> The method takes into account the development area, soil denitrification 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 /> /1.0 CHEMICAL AND PHYSICAL PROPERTIES OF SOIL <br /> /1.1 Chemical and Physical Soil Properties <br /> s <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 moderately.slow infiltration of water through the <br /> surface soils. Finer grain soils tend to slow the downward movement of percolating effluent <br /> from a septic system disposal field when compared to sandy soils. Due to the lack of sandy <br /> soils below the site, the potential impact to deep ground water is reduced when compared to <br /> 'other sites with thicker sections of sandy soil. The longer the effluent remains near the surface, <br /> the more treatment occurs due to natural processes within the 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 /> 2.2 Potential Ground Water Contamination Issues <br /> 6 <br /> A discussion of issues related to potential ground water contamination is included in Section 4.2 <br /> of the SSS completed by Dillon.& Murphy. <br /> 902 Industrial Way•Lodi,CA 95240•209.367.3701 •Fax 209.369.4228 ©1007 Nei!0.Anderson&Associates,Inc <br />
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