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SITE INFORMATION AND CORRESPONDENCE_1987-1992
Environmental Health - Public
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SITE INFORMATION AND CORRESPONDENCE_1987-1992
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Last modified
3/31/2020 3:01:00 PM
Creation date
3/31/2020 2:27:26 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
1987-1992
RECORD_ID
PR0506203
PE
2960
FACILITY_ID
FA0007271
FACILITY_NAME
LINCOLN CNTR ENV REMEDIATION TRUST
STREET_NUMBER
0
STREET_NAME
PACIFIC
STREET_TYPE
AVE
City
STOCKTON
Zip
95207
CURRENT_STATUS
01
SITE_LOCATION
PACIFIC AVE
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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LEEDSHILL•HERKENHOFF. INC. <br /> CHAPTER 4 <br /> ' RESULTS <br /> ' 4. 1 Groundwater Gradient and Direction <br /> ' Three municipal wells and three of the four monitoring wells are located <br /> along the western edge of LVC, along Gettysburg Place. LVMD well #1 and <br /> monitoring well #4 are approximately fifty feet apart; however, static water <br /> ' levels in the municipal wells are roughly twelve to fourteen feet lower than <br /> static water levels in the monitoring wells. The municipal wells are over <br /> 150 feet deeper than the monitoring wells and are perforated in a water <br /> ' bearing sand layer located at a depth of approximately 175 to 200 feet below <br /> the ground surface. This hydrogeologic data supports the theory that the <br /> municipal and monitoring wells are constructed in different zones, with the <br /> municipal wells tapping into a semi-confined aquifer; while the monitoring <br /> ' wells tap into an, upper water bearing zone. <br /> The groundwater direction and gradient of the upper water bearing zone is <br /> ' generally easterly to northeasterly with little slope (the fall is approxi- <br /> mately 1'/500' , or 0.2%) . Figure 4.1 shows June 1988 groundwater elevation <br /> contours for the upper water bearing zone beneath Lincoln Village Center. <br /> Based on limited data, the localized direction of groundwater flow in the <br /> ' semi-confined layer was found to be toward the cone of depression created by <br /> the active pumpage of LVMD wells #1 and #2. <br /> ' 4.2 Groundwater Sampling Results <br /> Analysis of the monitoring well water samples and confirmation sample col- <br /> lected from MW#4 revealed PCE and TCE contamination in monitoring well #4, <br /> but not in monitoring wells #1, #2, or #3. The initial sampling at monitor- <br /> ing well #4 contained 1900 ppb of PCE and 110 ppb of TCE; the confirmation <br /> sample contained 2500 ppb of PCE and 190 ppb of TCE. All other samples were <br /> ' non-detect for purgeable halocarbons. (See Appendix C for individual <br /> laboratory data sheets. ) <br /> ' Given the direction of groundwater flow in the upper water bearing zone (as <br /> measured at the time of this investigation), there are no downgradient <br /> domestic wells within a 1-mile radius of the site. In fact, there are only <br /> two down gradient wells within one-half mile of the site. One of these <br /> ' wells is a deep municipal supply well whose highest perforation is located <br /> at a depth of 237 feet and is therefore drawing water only from the lower <br /> aquifer. The other well is the Chevron monitoring well located in the <br /> ' upper water bearing unit, which is approximately 900 feet down gradient from <br /> LVMD #1. This well , which was sampled by RWQCB staff in January 1987, <br /> showed non-detectable levels of PCE and TCE. <br /> 4-1 <br />
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