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ARCHIVED REPORTS_XR0012626
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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2900 - Site Mitigation Program
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PR0543041
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ARCHIVED REPORTS_XR0012626
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Last modified
5/18/2020 3:03:14 PM
Creation date
5/18/2020 2:45:25 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012626
RECORD_ID
PR0543041
PE
2960
FACILITY_ID
FA0024604
FACILITY_NAME
HUMAN SERVICES AGENCY
STREET_NUMBER
145
Direction
S
STREET_NAME
SUTTER
STREET_TYPE
ST
City
STOCKTON
Zip
95202
APN
14912016
CURRENT_STATUS
01
SITE_LOCATION
145 S SUTTER ST
P_LOCATION
01
QC Status
Approved
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EHD - Public
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I <br /> W. <br /> Table 4 presents a summary of pertinent construction information <br /> for each of the wells installed. <br /> Table 4 - Monitor Well Construction Information <br /> !-• Total Borehole Depth to Screened Top of Top of <br /> uel( Ileal Depth (BGS) De (h BGS) Water (BCS) Interval (BGS) sand Ag GS) BMt2t11t4 (BGS) <br /> r^ <br /> hV1 30.5' 30.5' 25.97' 151 30' 12.83' 11.58, <br /> HIl2 48.8' 45.5' 37.89' 30- - 45' 27.67' 26.41' <br /> W3 30.4' 30.5' 28.78' 15, 30' 13.00, 11.75' <br /> 3.1 Well Development <br /> On June 17, 1988, the monitor wells were developed by a combina- <br /> tion of swabbing and bailing for a period greater than 20 minutes <br /> using a Acher-AD2 drill rig equipped with a surgeblock. Each well <br /> was first swabbed repeatedly, then bailed. Approximately 30 <br /> gallons of water was bailed from MW1, 60 gallons of water was <br /> bailed from MW2 and approximately 20 gallons of water was bailed <br /> € from MW3. This bailing removed the heavier materials from inside <br /> of the wells. For each well, the effluent was relatively sedi- <br /> ment free at the end of the development process. The swab and <br /> bailer were steam cleaned prior to first use and between each <br /> subsequent use. <br /> r- <br /> 3.2 Well Surveying <br /> 4 <br /> on December 30, 1988, the monitor wells were surveyed by WESTON <br /> personnel using a level and rod. The survey established eleva- <br /> tions to the top of the PVC casing at each well relative to an <br /> arbitrary bench mark (ABM) located on the southeast corner of the <br /> excavation on the sidewalk (see Figure 2) . The ASM was set at <br /> 100.00 feet. The relative top of casing elevations are MW1 at <br /> 91.85 feet; MW2 at 103.35 feet and MW3 at 94.06 feet. <br /> 3.3 Groundwater Sam lin <br /> Groundwater sampling was conducted on December 30, 1988. All <br /> wells were first checked for the existence of floating product by ' <br /> the use of a clear teflon bailer. Depth to water and total well <br /> depth measurements were also taken. No product layer was ob- <br /> served within any of the wells. The total petroleum hydrocarbons <br /> and organic lead samples were obtained using a clean, transparent <br /> teflon bailer lowered into each well using, clean monofillament <br /> line until the bailer was partially submerged. The bailer was <br /> retrieved and inspected visually and its contents were poured <br /> into a clean, kiln dried 1 liter, unpreserved, amber glass <br /> container and two 40 ml unpreserved airy-)er glass VOA vials. All <br /> containers were capped with teflon lined screw caps. It was <br /> necessary to lower the bailer more than once in order to obtain <br /> sufficient water samples. The wells were then bailed to purge <br /> i <br /> the well of 3 volumes of water. Each of the wells purge <br />
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