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SU0009809_SSNL
EnvironmentalHealth
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SU0009809_SSNL
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Last modified
11/19/2024 3:46:26 PM
Creation date
9/9/2019 10:26:16 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0009809
PE
2625
FACILITY_NAME
PA-1300168
STREET_NUMBER
5400
Direction
W
STREET_NAME
STATE ROUTE 12
City
LODI
Zip
95240-
APN
05516072
ENTERED_DATE
10/28/2013 12:00:00 AM
SITE_LOCATION
5400 W HWY 12
RECEIVED_DATE
10/25/2013 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
Scanner
SJGOV\rtan
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FilePath
\MIGRATIONS\T\HWY 12\5400\PA-1300168\SU0009809\NL STDY.PDF
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EHD - Public
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Odyssey Landscape—Nitrate Loading Section Page 9 of 13 <br /> Our Project Number: NA157000 <br /> March 17, 2015 <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 Finnemore approach is "...a conservative (worst case) first approximation of <br /> 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. <br /> .� 2.1.2 Mass Transport Soil Properties / <br /> The percolation test has revealed that the soils from 0 to 3.25 feet are permeable. These <br /> permeable soils will allow for moderate to rapid infiltration of water through the surface soils. <br /> The longer the effluent remains near the surface, the more treatment is enhanced due to C J <br /> ©2015 Neil O.Anderson&Associates,Inc. <br /> A Terracon Company <br />
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