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SU0004984 SSNL
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SU0004984 SSNL
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Last modified
5/7/2020 11:31:22 AM
Creation date
9/4/2019 9:52:27 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SU0004984
PE
2622
FACILITY_NAME
PA-0500194
STREET_NUMBER
767
Direction
N
STREET_NAME
ALPINE
STREET_TYPE
RD
City
STOCKTON
APN
10126007
ENTERED_DATE
4/13/2005 12:00:00 AM
SITE_LOCATION
767 N ALPINE RD
RECEIVED_DATE
4/12/2005 12:00:00 AM
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\A\ALPINE\767\PA-0500194\SU0004984\NL STDY.PDF
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EHD - Public
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F <br /> e <br /> Fi, <br /> FFAwater ample was obtained from the domestic well that serves the residente on the sub1ect property. <br /> actual well is inside the detached garage, the water sample was taken from an outdoor <br /> snaucet. Two separate containers were used for the analyses. For nitrate and total alkalinity, a <br /> plastic bottle was used for the sample and for the DBCP/EDB analysis a VOC bottle containing <br /> preservative was used. The samples were drawn after the well pump had run for ten minutes to <br /> ensure aquifer formation water was sampled. The samples were placed in a cooled ice chest and <br /> F transported to A&L Labs of Modesto, under the attached Chain of Custody. <br /> F. <br /> Testing of the well water sample reveals a nitrate concentration of 52 ppm (12.4 ppm NO3-N). The <br /> Maximum Contaminant Level (MCL) for nitrate (as NO3) is 45 ppm. Dibromochloropropane <br /> (DBCP)was detected at 0.15 pg/L or 0.15 ppb. The MCL for DBCP is 0.0002 ppm or 0.2 pg/L. <br /> Therefore, the shallower aquifers are near the MCL for DBCP. Ethylene dibromide (EDB) was found <br /> to be non-detect. <br /> The nitrate-nitrogen loading calculations below are contingent upon the environmental factors <br /> required for nitrification to occur. As discussed, these conditions include soil pore-space oxygen <br /> content, soil temperature, pH, electrical conductivity, organic matter, cation exchange capacity, and <br /> alkalinity. Alkalinity in wastewater effluent is derived from the domestic water supply and the <br /> introduction of wastes to the wastewater. Nitrification consumes approximately 7.1 mg of alkalinity <br /> ' for every milligram of ammonia-nitrogen (NH4-N) oxidized. Water chemistry results for the on-site <br /> domestic well indicate a Total Alkalinity of 232 mg/L. <br /> Assuming complete nitrification of a Total Nitrogen (TN) concentration of 53 mg/L, as determined in <br /> Section III D below, and considering that ammonium typically composes 70-90% of the total nitrogen <br /> in septic tank effluent, we find that: 53 mg N/L x 80% =42 mg NH4-N/L x 7.1 mg CaCO3 = 301 <br /> mg/L alkalinity required. However, only 232 mg/L of alkalinity exists in the upper groundwater. <br /> Therefore the alkalinity in the domestic water supply may be deficient if the TN will be <br /> approximately 53 mg/L, and nitrification may be inhibited to a slight extent. <br /> Fk <br /> e <br /> F B. SURFACE WATER INFORMATION <br /> Surface water consists of all other water sources originating on the surface of the project, other than <br /> Fj 4 septic system effluent. These sources include rainfall, surface runoff, domestic irrigation and on-site <br /> stormY Map retention. The attached San Joaquin County of Public Works - Isoh etal Ma indicates <br /> 13.5 inches of rainfall to be the Mean Annual Precipitation in the area of the project. There should be <br /> no impact to surface waters from septic effluent provided applicable distance requirements as <br /> F, promulgated in the San Joaquin County Sewage Standards, are followed. <br /> r# <br /> 7 <br /> Chc sney Consulting <br />
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