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ARCHIVED REPORTS XR0009207
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2900 - Site Mitigation Program
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PR0544690
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ARCHIVED REPORTS XR0009207
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Last modified
7/24/2019 1:05:35 PM
Creation date
7/24/2019 11:45:01 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0009207
RECORD_ID
PR0544690
PE
3528
FACILITY_ID
FA0005839
FACILITY_NAME
CASTLE AUTOMOTIVE REPAIR INC.
STREET_NUMBER
2315
Direction
N
STREET_NAME
EL DORADO
STREET_TYPE
ST
City
STOCKTON
Zip
95204
APN
12510017
CURRENT_STATUS
02
SITE_LOCATION
2315 N EL DORADO ST
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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GeofogicafTechnws Inc Page 2 <br /> Groundwater Monitoring Report <br /> Project No 723 2 <br /> June 29,2000 <br /> 1.0 GROUNDWATER MONITORING <br /> 1.1 Hydrogeology of Site <br /> A site-specific groundwater gradient and bearing was calculated from the depth to water <br /> measurements taken during the groundwater monitoring The gradient was 0 0033 Rift <br /> flowing N70°E This is the fourth event where a site specific groundwater gradient was <br /> calculated The groundwater gradient was calculated by resolving a three-point problem <br /> using MW-4, MW-5 and MW-6 These wells were selected because they are constructed <br /> relatively similar in regards to depth of screen interval The average elevation of <br /> groundwater under the site was 15 18 feet below mean sea level Depths to water ranged <br /> from 25 21 to 26 02 feet bgs <br /> Figure 2 is a groundwater gradient map for the May 4, 2000 event <br /> This is the third event where the deep discretely screened well, MW-101, was monitored A <br /> shallow well was not installed next to MW-101 so a vertical gradient cannot easily be <br /> calculated The groundwater head in MW-101 is nearly equal (+0 01 feet) to the head in <br /> nearby MW-3 so it appears there was not a significant vertical gradient on May 4, 2000 <br /> Table 1 in Appendix A contains the groundwater elevations and gradients for the site <br /> 1.2 Groundwater Sampling Procedure <br /> On May 4, 2000, Del-Tech Geotechnical Support personnel arrived on-site, opened the wells, <br /> and measured the depth to water with an electrically actuated sounding tape The water level <br /> reading was recorded to an accuracy of 0 01 foot In wells where free floating product was <br /> suspected, a clear disposable bailer is used to gauge the interface During tlus monitoring no <br /> rfree product was noted <br /> Stagnant water in the well casing was purged using a Waterra pump as recorded in the field <br /> logs (Appendix C) The rate of well purging was monitored The wells were purged of <br /> approximately three casing volumes and until the groundwater parameters (temperature, <br />' conductivity, and pH) had stabilized (Appendix C) indicating that water, representative of <br /> actual aquifer conditions, was entering the well Groundwater parameter stabilization was <br /> characterized by three successive readings within 10% <br /> Before a sample was collected, the well's water level was allowed to recharge to at least 80% <br /> of the initial level All water removed from the monitoring well and not used as a sample, <br />' was placed in a 55 gallon DOT (Department of Transportation 17-H) approved container that <br /> is properly labeled and temporally stored on-site <br />
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