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ARCHIVED REPORTS_XR0008403
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2900 - Site Mitigation Program
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PR0506560
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ARCHIVED REPORTS_XR0008403
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Last modified
6/22/2020 8:34:24 AM
Creation date
6/22/2020 8:18:23 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008403
RECORD_ID
PR0506560
PE
2960
FACILITY_ID
FA0004535
FACILITY_NAME
CAL-FARM SUPPLY
STREET_NUMBER
2040
Direction
W
STREET_NAME
WASHINGTON
City
STOCKTON
Zip
95206
APN
14503004
CURRENT_STATUS
01
SITE_LOCATION
2040 W WASHINGTON
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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Kennedy/Jenks/Chilton <br /> Mr. Charles Whitworth <br /> i Cal-Farm Supply <br /> 14 July 1989 <br /> Page 13 <br /> inside the storage trailers. Recommendations to address these three areas are <br /> provided below. <br /> Underground -Storage Tank <br /> It is our understanding that future use of the Stockton facility by Cal -Farm <br /> Supply will not involve utilization of the underground fuel storage tank. <br /> Therefore, to bring the tank into compliance with California underground tank <br /> regulations, the tank should be removed rather than implement leak protection <br /> or monitoring. During excavation and removal of the tank, soil samples should <br /> be collected and analyzed for TPD and BXTE to assist in determining the extent <br /> of possible leakage from the tank. The presence of benzene in the groundwater <br /> is most likely related to leakage of fuel from this tank However, the <br /> horizontal and vertical distribution of this chemical in soil and groundwater, <br /> specifically in the down gradient direction, was not determined during the <br /> ! current investigation. An additional monitoring well may be necessary to <br /> obtain this information. A meeting should be held with representatives from <br /> the Regional Board (as lead agency) to discuss what additional action is <br /> I warranted to address the benzene concentrations in groundwater, if any. <br /> Surface Soils Containing Pesticides <br /> Surface soil with 4,4`-DDT concentrations above the TTLC of 1,000 ug/Kg should <br /> be further investigated to better characterize DDT concentrations in these <br /> areas. These areas are highlighted on Figure 7. Options for developing site <br /> specific cleanup levels and remediation alternatives are as follows- <br /> 0 The "no-action" alternative would result in no further work being <br /> performed on the property concerning the DDT soils If this <br /> alternative is chosen it is most likely that a deed restriction will <br /> be required for this property. <br /> ,i <br /> J o Rather than using TTLC criteria, cleanup levels could be derived from <br /> health-based criteria. This evaluation would consider the intended <br /> future use of this property which at the present time is assumed to <br /> be industrial . <br /> o Remediation of these soils could include excavation, treatment, and <br /> backfilling of treated material on site. It should be noted that <br /> treatment technologies for DDT are only in the developmental stages <br /> and that the EPA has not approved any treatment technology to date. <br /> o Another option for remediating these soils could entail excavation <br /> and disposal of the soils containing elevated levels of DDT at a <br /> Class I hazardous waste facility. At this time disposal of these <br /> soil is complicated because wastes containing DDT are included in the <br />
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