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ARCHIVED REPORTS_XR0007864
Environmental Health - Public
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EHD Program Facility Records by Street Name
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WILSON
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1100
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2900 - Site Mitigation Program
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PR0507217
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ARCHIVED REPORTS_XR0007864
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Last modified
10/8/2020 10:09:08 PM
Creation date
6/23/2020 2:46:22 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0007864
RECORD_ID
PR0507217
PE
2950
FACILITY_ID
FA0007741
FACILITY_NAME
AUTO ZONE INC
STREET_NUMBER
1100
Direction
N
STREET_NAME
WILSON
STREET_TYPE
WAY
City
STOCKTON
Zip
95202
APN
11733035
CURRENT_STATUS
02
SITE_LOCATION
1100 N WILSON WAY
P_LOCATION
01
QC Status
Approved
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EHD - Public
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1 <br /> the formation cannot be entirely eliminated by well development After the wells have been <br /> adequately developed, a sample is collected for laboratory analysis <br /> ' Subjective Anal�of Groundwater SamQles <br /> ' Groundwater samples are collected for subjective analysis from just below the air-fluid <br /> interface in a monitoring well by lowering approximately half the length of a clean bailer <br /> through the interface The bailer is retrieved and the water sample examined for floating <br /> ' product, sheen, or other subjective evidence of hydrocarbons <br /> ' Measurement of the Depth to Groundwater in Monitoring Wells <br /> The depth of the groundwater surface in a monitoring well is measured from the top of the <br /> ' well casing to the nearest 0 01 foot with a Solinst or similar electric water-level indicator The <br /> well is vented to the atmosphere before obtaining depth-to-water measurements. Venting is <br /> conducted to allow the groundwater to equilibrate to barometric pressure These <br /> measurements are combined to evaluate the elevation of the groundwater surface in each well <br /> and the slope of the groundwater surface across the site <br /> Groundwater Sam lin <br /> The static water level in each well is measured to the nearest 0 01 foot with a Solinst or similar <br /> electric water-level indicator cleaned with a laboratory-grade non-phosphate detergent and <br /> clean tap or deionized water before use in each well A clean bailer is used to obtain a sample <br /> from the surface of the water in the well for subjective analysis of hydrocarbons The sample <br /> is retrieved and examined for floating product, sheen, color, and clarity <br /> ' Approximately 3 to 5 well volumes are purged from each well with a pre-washed submersible <br /> pump or bailer to allow sampling of representative formation water All down hole equipment <br /> is cleaned with a laboratory-grade non-phosphate detergent and water before use in each well <br /> The wells are purged until pH, temperature, and electrical conductivity of the water have <br /> stabilized, as measured by portable meters calibrated to a standard buffer and conductivity <br /> standard If the well is pumped or bailed dry during purging, the water level is allowed to <br /> ' recover to at least 80 percent of the initial water level prior to sampling <br /> A sample of the formation water then is retrieved from the surface of the water in each of the <br /> ' wells with a dedicated disposable bailer and slowly transferred to laboratory-cleaned sample <br /> containers The recovered fluids from sampling in each well are directed into 55-gallon liquid <br /> ' waste drums approved for this use by the DOT until suitable disposal options are selected <br /> based on analytical results Disposal of water at an appropriate disposal facility is the <br /> responsibility of the client <br /> SHELLSIFLDMTHDS doc 3 <br />
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