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PR0540822
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Last modified
5/17/2019 11:49:00 AM
Creation date
5/17/2019 11:48:10 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0540822
PE
2960
FACILITY_ID
FA0023389
FACILITY_NAME
FORMER HELENA CHEMICAL FACILITY
STREET_NUMBER
2245
Direction
W
STREET_NAME
CHARTER
STREET_TYPE
WAY
City
STOCKTON
Zip
95206
APN
16336017
CURRENT_STATUS
01
SITE_LOCATION
2245 W CHARTER WAY
P_LOCATION
01
QC Status
Approved
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Rcview Comments for Revised Site Investigation Work Plan—June 2015 <br /> Former Helena Chemical Facility <br /> Page 3 <br /> In summary no one laboratory has the "lowest commercially available and achievable reporting <br /> limits" Selection of a laboratory based on broadiv such stated criteria is not possible based on <br /> Condor's review of these reporting limits. Two alternatives were developed. The first alternative <br /> to be considered was to prioritize one or two classes of analytes, and/or matrices, and then select <br /> the best laboratory, However, prioritizing one or two groups of contaminants of concern runs <br /> counter to the intendedupu ose of this investigation. The results of this investigation should lead <br /> to elimination and prioritization of some groups of possible contaminants of concern. <br /> The second alternative to be considered was to send the samples to different laboratories. It was <br /> observed that all of the laboratories easily met the reporting reouirements for nitrogen containing <br /> analytes. The second alternative is marginally feasible for soil samples because the samples are <br /> collected in tubes and need to be sealed, chilled, and minimally disturbed according to <br /> Environmental Protection Agency standards. In addition, manual separation of soil would <br /> introduce the potential for cross-contamination, bias, and error. Simply collecting more samples <br /> would expand the sampling interval and decrease the comparability of the data. However, soil <br /> samples collected through a 12-inch interval could be cut or split into two 6-inch intervals. <br /> Condor consulted with the CVRWOCB to develop the proposed Sampling and Analysis Plan <br /> (SAP). Condor has proposed in this revision of the work plan that soil samples will not be split <br /> and the samples will be sent to BC Laboratories. Condor proposes that groundwater samples will <br /> be sent to BSK Laboratories for fumigant pesticide, organo-phosphate, and organo-chlorine <br /> pesticide analysis,and CalTest Laboratories for LUFT 5 metals,and nitro en compound analysis. <br /> 3. Similarly, the proposed RL for each chemical constituent in soil should be at or below the <br /> California Department of Toxic Substances Control Screening Levels(DTSC-SLs)or the USEPA <br /> Regional Screening Level (RSL), whichever is more stringent. Thus, the selected laboratory <br /> should be able to perform analyses using the lowest commercially available and achievable RLs, <br /> to provide quantification of constituents for evaluation with respect to DTSC-SLs or RSLs. <br /> See discussion above. <br /> SPECIFIC COMMENTS <br /> 1. Section 3.0, Third Paragraph: The Work Plan states that "If contaminants of concern are not <br /> detected above the ESL or RSL, then no filrther action should be required. If constituents of <br /> concern are detected above the ESL or RSL and below the MCL, then no fuurther action should be <br /> required. If COCs are found above the MCL, then recommendations for jtrther action will be <br /> made".Please revise the Work Plan to address the following comments: <br /> a. As stated in General Comment No. 1 above, the Site is outside the jurisdiction of Region <br /> 2. Therefore, Region 2 ESLs are not applicable at the Site. The Work Plan should be <br /> revised to remove reference to ESLs. <br /> References have been removed. <br /> b. As stated in General Comment No. 2,groundwater at the Site is designated as suitable for <br /> municipal and domestic uses. Therefore, if constituents of concern are detected at <br /> concentrations below primary/secondary MCLS,but above other screening levels(such as <br /> PHGs, notification levels, background levels), data should be further evaluated to <br /> determine the degree of impact on groundwater beneficial uses and whether further action <br /> is required. If it is determined that further action (remediation) is required, cleanup to <br /> levels other than background levels should be justified through a Technical and <br /> Economic Feasibility Analysis (TEFA). With the exception of where background levels <br /> n %4 <br /> +i1) CONDO <br />
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