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SR0078905 SSNL
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Entry Properties
Last modified
12/14/2022 3:21:13 PM
Creation date
4/24/2020 1:39:24 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0078905
PE
2602
STREET_NUMBER
26783
Direction
N
STREET_NAME
CHEROKEE
STREET_TYPE
LN
City
LODI
Zip
95632
APN
00511013
ENTERED_DATE
3/22/2018 12:00:00 AM
SITE_LOCATION
26783 N CHEROKEE LN
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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NLS§ 2.2, 3.1, SSS§ 2.1, 4.2. Since the surrounding properties have been farmed for a number of <br />decades, the potential for nitrate contamination to the underlying groundwater aquifers can be <br />considered significant. However, this was not observed. <br />NLS§ 2.3, SSS§ 4.3, 4.4, 4.5, 4.6. Mr. Bowen's existing domestic well was sampled for analysis. <br />The pump was run for 20 minutes before sampling, with the sample obtained from a hose bibb on <br />the south side of Mr. Bowen's house. The Table below summarizes the test results obtained. <br />TABLE 3 <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 content, <br />soil temperature, pH, electrical conductivity, organic matter, cation exchange capacity, and <br />alkalinity. Alkalinity in wastewater effluent is derived from the well water, in addition to the <br />introduction of wastes. Nitrification consumes approximately 7.1 mg of alkalinity for every mg of <br />ammonia -nitrogen (NH4-N) oxidized. Nitrification of the average Total Nitrogen (TN) <br />concentration of 62 mg/L, as determined on Page 7, would require: 62 mg/L NH4-N x 7.1 mg <br />CaCO3 = 440 mg/L alkalinity. The alkalinity concentration in the Parcel 1 well water was <br />determined to be 195 ppm. Therefore, there is an insufficient alkalinity in the well water for <br />complete nitrification to readily proceed without the introduction of wastes and the alkalinity within <br />the soil environment. <br />E. SURFACE WATER INFORMATION <br />Storm water management will be by on-site retention. Percolating rainwater will theoretically <br />provide an indeterminable water table dilution effect to percolating wastewater effluent. However, <br />as referenced in the next Section, rainfall in comparison to evapotranspiration is minimal. <br />Climatic Data: Rainfall versus Evapotranspiration <br />NLS§ 3.2. It is generally and scientifically accepted that when precipitation exceeds <br />evapotranspiration (Eto), deep percolation of surface rainwater may occur. Evapotranspiration <br />refers to water evaporation that takes place both at the soil surface and transpiration by plants. <br />Page -5- <br />Chesney Consulting <br />WELLI <br />ANALYTE <br />CONCENTRATION <br />I FOUND <br />MAXIMUM CONTAMINANT <br />LEVEL (MCL) <br />Proposed <br />Nitrate (As Nitrate) <br />15 ppm <br />45 ppm <br />Parcel 1 <br />Domestic Well <br />Sampled from <br />Total Alkalinity <br />195 ppm <br />N/A <br />Sampling Port <br />on south wellLromochloropropane <br />Below Detectable Limits <br />I <br />0.010 µ/L (ppb) <br />discharge pipe. <br />DBCP <br />(BDL) <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 content, <br />soil temperature, pH, electrical conductivity, organic matter, cation exchange capacity, and <br />alkalinity. Alkalinity in wastewater effluent is derived from the well water, in addition to the <br />introduction of wastes. Nitrification consumes approximately 7.1 mg of alkalinity for every mg of <br />ammonia -nitrogen (NH4-N) oxidized. Nitrification of the average Total Nitrogen (TN) <br />concentration of 62 mg/L, as determined on Page 7, would require: 62 mg/L NH4-N x 7.1 mg <br />CaCO3 = 440 mg/L alkalinity. The alkalinity concentration in the Parcel 1 well water was <br />determined to be 195 ppm. Therefore, there is an insufficient alkalinity in the well water for <br />complete nitrification to readily proceed without the introduction of wastes and the alkalinity within <br />the soil environment. <br />E. SURFACE WATER INFORMATION <br />Storm water management will be by on-site retention. Percolating rainwater will theoretically <br />provide an indeterminable water table dilution effect to percolating wastewater effluent. However, <br />as referenced in the next Section, rainfall in comparison to evapotranspiration is minimal. <br />Climatic Data: Rainfall versus Evapotranspiration <br />NLS§ 3.2. It is generally and scientifically accepted that when precipitation exceeds <br />evapotranspiration (Eto), deep percolation of surface rainwater may occur. Evapotranspiration <br />refers to water evaporation that takes place both at the soil surface and transpiration by plants. <br />Page -5- <br />Chesney Consulting <br />
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