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SR0080316 SSNL
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SR0080316 SSNL
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Last modified
5/12/2020 3:53:06 PM
Creation date
5/12/2020 3:00:01 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0080316
PE
2602
FACILITY_NAME
BLOOM INNOVATIONS
STREET_NUMBER
7979
Direction
S
STREET_NAME
AIRPORT
STREET_TYPE
WAY
City
STOCKTON
Zip
95206
APN
17705008
ENTERED_DATE
3/11/2019 12:00:00 AM
SITE_LOCATION
7979 S AIRPORT WAY
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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TSok
Tags
EHD - Public
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TABLE 2 <br /> PERCOLATION TEST RESULTS WITH CORRESPONDING <br /> APPLICATION RATES IN GALLONS /FT'/DAY <br /> 40 INCH DEEP PERC TEST BORING 83.3 min/inch / 0.123 gallons/ftZ/day <br /> PERCOLATION RATE/APPLICATION RATE <br /> OFFICIAL PERC TEST <br /> Application Rates adapted from Waste Quality Control for Siting,Design,Operation and Maintenance of On-site Wastewater Treatment Systems,based on the Pere Rate <br /> D. GROUNDWATER INFORMATION <br /> . l <br /> NLS§ 2.1, SSS§4.1. Groundwater depths and elevations throughout San Joaquin County are <br /> illustrated on maps published by the County Flood Control and Water Conservation District. The <br /> Fall 2016 Lines of Equal Depth Map indicate the groundwater under the property to be <br /> approximately 40 feet below grade and may fluctuate between 30 ft and 50 ft below grade. The <br /> Fall 2016 Lines of Equal Elevation Map illustrates the groundwater directional flow to be in a <br /> northeasterly direction. <br /> NLS§ 2.2,3.1, SSS§ 2.1, 4.2. Since the surrounding properties have been farmed for a number <br /> of decades, in addition to high density housing within the town of French Camp which are on <br /> septic systems(upgradient to the project),the potential for nitrate contamination to the underlying <br /> groundwater aquifers can be considered significant. <br /> NLS§2.3, SSS§4.3,4.4,4.5, 4.6. There are no domestic or irrigation wells on the subject <br /> Parcel. The City of Stockton water is closely monitored for adverse constituents. <br /> Calculation of Alkalinity Requirement for Nitrification <br /> The nitrate-nitrogen loading to the underlying groundwater is contingent upon the environmental <br /> factors required for nitrification to occur. These conditions include soil pore-space oxygen <br /> content, soil temperature,pH, electrical conductivity, organic matter, cation exchange capacity, <br /> and alkalinity. Alkalinity in wastewater effluent is derived from the City supplied water, in <br /> addition to the introduction of wastes. Nitrification consumes approximately 7.1 mg of alkalinity <br /> for every mg of ammonia-nitrogen(NH4-N) oxidized. Nitrification of the average Total Nitrogen <br /> (TN) concentration of 62 mg/L, as determined on Page 6, would require: 62 mg/L NH4-N x 7.1 <br /> mg CaCO3 =440 mg/L alkalinity. The alkalinity concentration in the City water was tested at an <br /> average of 158 ppm, as reported in the City of Stockton Drinking Water Report dated May 2018. <br /> Therefore,there is an insufficient alkalinity in the domestic water for complete nitrification to <br /> readily proceed without the introduction of wastes along with the alkalinity in the soil <br /> environment. <br /> E. SURFACE WATER INFORMATION <br /> Storm water drainage management will be by on-site retention located a the south end of the <br /> property. Percolating rainwater and water from the adjacent Little o reek and stilling basin <br /> will most probably provide an indeterminable water table dilution effect to percolating wastewater <br /> effluent. (� <br /> Page -4- <br /> Chesney Consulting <br />
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