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4200/4300 - Liquid Waste/Water Well Permits
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SR0079470
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Last modified
3/27/2019 9:00:55 AM
Creation date
3/27/2019 8:27:29 AM
Metadata
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EHD - Public
ProgramCode
4200/4300 - Liquid Waste/Water Well Permits
RECORD_ID
SR0079470
PE
2602
STREET_NUMBER
3413
Direction
E
STREET_NAME
SECTION
STREET_TYPE
AVE
City
STOCKTON
Zip
95205
APN
17309032
ENTERED_DATE
8/6/2018 12:00:00 AM
SITE_LOCATION
3413 E SECTION AVE
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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Soil Suitability / Nitrate Loading Study Irerracon <br /> Thor Property m Stockton, CA <br /> July 19, 2018 ® Terracon Project No. NA187029 <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 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 site clay soils will allow for slow infiltration at 25 feet bgs. <br /> The longer the effluent remains near the surface, the more treatment is enhanced due to natural <br /> processes within the soil. Based on the slow permeability and high water absorption capacity of <br /> the clay soils, effluent is anticipated to remain within the clay soil column much longer when <br /> compared to more permeable sands, silts, and loamy soils. <br /> 2.2 Groundwater Analysis <br /> 2.2.1 Regional Groundwater <br /> A discussion of regional groundwater, including depth to groundwater and flow gradient is <br /> included in Section 1.4.1. No significant seasonal trends were evident from the sources <br /> consulted. <br /> Responsive ■ Resourceful ■ Reliable 12 <br />
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