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2900 - Site Mitigation Program
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PR0515573
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
4/7/2020 3:32:38 PM
Creation date
4/7/2020 3:02:51 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0515573
PE
2950
FACILITY_ID
FA0012224
FACILITY_NAME
RIDGEWAY PROPERTY
STREET_NUMBER
1881
STREET_NAME
RUSTAN
STREET_TYPE
RD
City
TRACY
Zip
95376
CURRENT_STATUS
02
SITE_LOCATION
1881 RUSTAN RD
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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Mr. Philip Isorena GEOMATRIX <br /> California Regional Water Quality Control Board <br /> September 14, 2000 <br /> Page 3 <br /> In this comment, RWQCB has requested that Chevron "refine"the evaluation of alternatives <br /> and develop more "accurate" remediation time frames. To address this comment, Geomatrix <br /> will develop revised remedial time frames based on a number of underlying assumptions. It is <br /> important to recognize that the revised time frames may appear to be more precise than the <br /> order-of-magnitude estimates already developed, however, they should not be considered to <br /> be more accurate. Additionally, the revised time frames are not likely to change the <br /> fundamental conclusion from the analysis already performed: except for complete removal of <br /> affected soil, all remediation alternatives will likely require a relatively long period of time <br /> before concentrations of biodegradation byproducts in groundwater are permanently below <br /> the taste and odor WQOs for diesel. <br /> In this comment, RWQCB also requested that Chevron evaluate chemical oxidation and <br /> thermal desorption/destruction. To address this comment,these alternatives will be evaluated <br /> in the final closure request. <br /> C. Total Petroleum Hydrocarbons as Diesel(TPHd) Testing Protocol <br /> Chevron states that the WQOs for biogenic byproducts measured as TPH have not been <br /> established and assumes the WQOs for those constituents have been exceeded in order to <br /> proceed with the evaluation of the site against Regional Board policies, regulations, and <br /> guidelines. The use ofsilica gel cleanup prior to TPHd analysis results in removal of <br /> byproducts of TPH degradation. It is infeasible to identify all of these byproducts. Using <br /> representative constituents in lieu of all the degradation byproducts will result in not <br /> detecting some byproducts which could pose a threat to water quality. Therefore, TPHd <br /> analysis without silica gel cleanup should be used to determine the threat to water quality. If <br /> the TPH at a site falls within the diesel range, staff will compare the TPH concentrations with <br /> the TPHd WQO of 100,ug/1. <br /> As described in a June 29, 2000 work plan prepared by Geomatrix, we will collect <br /> groundwater samples from the existing site monitoring wells and a grab groundwater sample <br /> from the location of former soil boring GB-613. The groundwater samples will be analyzed <br /> for TPH quantified as diesel both with and without a silica gel preparation procedure. This <br /> work was approved in an August 3, 2000 letter from the RWQCB to CEMC. The results of <br /> this work will be presented in the final closure request. Future groundwater sampling <br /> analyses at other sites will include TPH quantified with and without silica gel preparation <br /> procedure. <br /> D. Conformance to Tri-Regional Board Staff Recommendations for Preliminary <br /> Investigation and Evaluation of Underground Tank Sites <br /> Chevron evaluates the site against the four criteria for low risk groundwater in Appendix B of <br /> the Tri-Regional Board Staff Recommendations for Preliminary Investigation and Evaluation <br /> of Underground Tank Sites and provides justification as to why the site meets each criterion. <br />
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