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SU0009706 SSNL
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SU0009706 SSNL
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Last modified
5/7/2020 11:34:10 AM
Creation date
9/9/2019 10:33:48 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0009706
PE
2631
FACILITY_NAME
PA-1300125
STREET_NUMBER
2454
Direction
N
STREET_NAME
TEEPEE
STREET_TYPE
DR
City
STOCKTON
Zip
95205-
APN
13208009
ENTERED_DATE
7/29/2013 12:00:00 AM
SITE_LOCATION
2454 N TEEPEE DR
RECEIVED_DATE
7/29/2013 12:00:00 AM
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\T\TEEPEE\2454\PA-1300125\SU0009706\SS_NL STDY.PDF
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EHD - Public
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y Trans Sohal Logistics—Nitrate Loading Section Page 8 of 13 <br /> Our Project Number: LGS140011 <br /> October 8, 2014 <br /> 2.0 NITRATE LOADING STUDY <br /> Because of concern regarding nitrate leaching into groundwater from septic systems, a nitrate <br /> loading analysis was required by the EHD for the proposed development to measure the <br /> potential concentration of percolating effluent and rain fall over the long term. Where <br /> percolating effluent leaches into the ground, groundwater quality may be impacted to some <br /> degree should the effluent reach groundwater. <br /> The method utilized for the nitrate loading analysis is based on a simple mass balance formula, <br /> discussed in a published article by Hantzsche and Finnemore (1992), which provides a <br /> convenient and simplified method to estimate long-term groundwater nitrate impacts on an <br /> area-wide basis. <br /> Hantzsche and Finnemore found that over a long period of time, water quality in the upper <br /> saturated groundwater zone closely approximates the quality of percolating recharge waters. <br /> They believe that their method is a good planning tool and provides useful information to <br /> planners and local officials but with some real limitations. In their article published in Ground <br /> Water, Hantzsche and Finnemore mention that "...the equation ignores dispersion, lateral flow, <br /> and mixing with groundwater flow from up-gradient areas. These processes would generally <br /> contribute to additional reduction of nitrate-nitrogen concentrations in groundwater to the <br /> extent that the nitrate-nitrogen concentration of groundwater flow from up-gradient areas is <br /> lower." <br /> The Hantzsche and Fennemore approach is "...a conservative (worst case) first approximation <br /> of groundwater 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 groundwater 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 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 7 and 8. <br /> The units of nitrate used in the mass balance equation are nitrate-N, whose maximum drinking <br /> water contaminant level (MCL) is 10 mg/L. <br /> 2.1 Chemical and Physical Properties of Soil <br /> 2.1.1 Chemical and Physical Soil Properties <br /> For a discussion of on-site soil properties, refer to Section 1.5. No chemical properties are <br /> available as the Site is located within the Urban Land soil type. <br /> 2.1.2 Mass Transport Soil Properties <br /> The percolation tests have revealed that the soils from 0 to 3.2 feet are non-permeable, from <br /> 3.2 to 18 feet are permeable, and from 18 to 24 feet the soils are considered very permeable. <br /> These permeable soils will allow for rapid infiltration of water through the surface soils. The (�,Z <br /> 02014 Neil O.Anderson&Associates,Inc. <br /> A Terracon Company <br />
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