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SR0082093 SSNL
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Last modified
6/16/2020 8:37:53 AM
Creation date
6/16/2020 8:31:23 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0082093
PE
2602
STREET_NUMBER
32851
Direction
S
STREET_NAME
CHRISMAN
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
25319010
ENTERED_DATE
5/18/2020 12:00:00 AM
SITE_LOCATION
32851 S CHRISMAN RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Soil Suitability! Nitrate Loading Study Irerracan <br /> Pickens Property■ Tracy, California <br /> May 12, 2020 ■ Terracon Project No. NA207032 <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 F. The units <br /> of nitrate used in the mass balance equation are nitrate-N, whose maximum drinking water <br /> contaminant level (MCL) is 10.0 mg/L. <br /> 2.1 Chemical and Physical Properties of Soil <br /> 2.1.1 Chemical and Physical Soil Properties <br /> Terracon reviewed the USDA NRCS Web Soil Survey and USDA Soil Survey of San Joaquin <br /> County (1992) for information regarding Capay clay soils (Section 1.5). Selected physical and <br /> chemical properties for the soil types are listed in the following table. <br /> Table 7. <br /> Physical and Chemical Properties* <br /> Soil Soil Septic tank <br /> Name/ Depth USDA Unified Soil Clay Permeability Salinity <br /> I(%) reaction absorption <br /> Map (in) Texture Classification (/o) (in/hour) (pH) (mmhos/cm) fields <br /> Symbol <br /> Capay 0-20 Clay CL 40-60 0.06-0.2 6.6-8.4 <2 <br /> clay/ Clay,silty Severe: <br /> lay 20-60 CL,CH 40-60 0.06-0.2 6.6-8.4 <2 peres slowly <br /> clay <br /> `Selected USDA physical and chemical properties <br /> Responsive■ Resourceful ■ Reliable 12 <br />
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