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SU0011127 SSNL
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SU0011127 SSNL
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Last modified
5/7/2020 11:34:58 AM
Creation date
9/4/2019 10:34:40 AM
Metadata
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Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0011127
PE
2631
FACILITY_NAME
PA-1600261
STREET_NUMBER
12023
Direction
E
STREET_NAME
BRANDT
STREET_TYPE
RD
City
LOCKEFORD
Zip
95237-
APN
05132008
ENTERED_DATE
11/21/2016 12:00:00 AM
SITE_LOCATION
12023 E BRANDT RD
RECEIVED_DATE
11/18/2016 12:00:00 AM
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\B\BRANDT\12023\PA-1600261\SU0011127\SS STDY.PDF
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Soil Suitability Nitrate Loading Study l�err�con <br /> Recreation Vehicle Service Facility ■ Lockeford, CA <br /> April 12, 2017■ Terraoon Project No. NA177006 <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 area- <br /> 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 planners <br /> and local officials but with some real limitations. In their article published in Ground Water, <br /> Hantzsche and Finnemore mention that "...the equation ignores dispersion, lateral flow, and <br /> 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 extent <br /> that the nitrate-nitrogen concentration of groundwater flow from up-gradient areas is 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 sewage <br /> disposal systems and precipitation. This (the equation and approach) is for estimation of long- <br /> term effect(i.e., over years)on groundwater quality, and is not intended for prediction of seasonal <br /> 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. The <br /> formula, assumptions and calculations used for the analysis are shown in Appendix E. The units <br /> of nitrate used in the mass balance equation are nitrate-N, whose maximum drinking water <br /> 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 soils from 0 to 3.5 feet are impermeable and will not allow <br /> for moderate to rapid infiltration of water. The longer the effluent remains near the surface, the l y� <br /> more treatment is enhanced due to natural processes within the soil. <br /> 2.2 Groundwater Analysis <br /> 2.2.1 Regional Groundwater <br /> Responsive■ Resourceful ■ Reliable 12 <br />
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