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SITE INFORMATION AND CORRESPONDENCE_1993-1996
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SITE INFORMATION AND CORRESPONDENCE_1993-1996
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Last modified
3/31/2020 3:10:16 PM
Creation date
3/31/2020 2:30:54 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
1993-1996
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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• <br /> Wendy L. Cohen -3- 1 December 1993 <br /> Aquifer testing in Zone C also should be conducted to determine if there is hydraulic <br /> connection between Zones B and C. <br /> 8. Page 18 of the work plan states that because no VOCs are now detected in Zone C, further <br /> characterization is not justified at this time. <br /> Comment: As stated in Item 2, LVMD 2 and 6 have shown contamination in the past. Both <br /> wells (now abandoned) were screened in Zone C which is the largest producer of water and is <br /> the aquifer of most concern. The extent of contamination, ground water flow direction and <br /> gradient in this zone, and hydraulic connection of this zone with Zone B need to be identified. <br /> The work plan must specify the activities to achieve these objectives. <br /> 9. Page 18 of the work plan states that a downgradient Zone C well will be needed to further <br /> verify the absence of VOCs because of the current downgradient use of Zone C wells, e.g., <br /> Well No. 11. <br /> Comment: See Item 4. This statement, albeit accurate, is inconsistent with previous statements <br /> which said that there is no contamination in Zone C. The recognition of the need to monitor <br /> Zone C upgradient of Well 11 presupposes there is contamination in this zone. <br /> 10. Page 18 of the work plan states that pilot testing will be needed to evaluate the remedial <br /> option for the site. <br /> Comment: An evaluation of remedial alternatives should first be performed prior to pilot <br /> testing of the remedial option. This will eliminate consideration of remedial alternatives <br /> which from the outset are not viable. <br /> 11. Page 22 of the work plan states that two of the soil borings with the highest OVA readings, <br /> which are anticipated to be SB-55 and SB-60, will be converted to vapor extraction wells for <br /> VES pilot testing. <br /> Comment: OVA readings are appropriate as a screening tool, but not as a basis for selection of <br /> vapor extraction wells. Soil gas and soil sample results will provide the best data to select soil <br /> vapor extraction well locations. The soil gas survey conducted in August 1989 identified areas <br /> where PCE vapors in the soil gas were significant, i.e., 100 µg/I or greater. These areas <br /> were along the sewer line south of Village Cleaners, near the southern end of the Benjamin <br /> Holt Drive sewer line crossing, along the sewer line serving the former Norge Cleaning <br /> Village parallel to and south of Benjamin Holt Drive, and near MW 4. However, the work <br /> plan does not propose additional investigation and extraction wells in the Village Cleaner <br /> plume. The 1989 soil gas survey report stated that it was not clear whether the source of the <br /> PCE vapor was the sewer, contaminated soil, or contaminated ground water. The uncertainty <br /> in the PCE vapor source provides justification for more investigation in the identified source <br /> areas. Regardless of the source, the contaminated soil is a threat to water quality and must be <br /> remediated. <br />
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