Laserfiche WebLink
DATA GAP ASSESSMENT WORK PLAN AND PATH TO CLOSURE REVIEW <br />Chase Chevrolet, 424 N. Van Buren Street <br />LTCP Closure Evaluation <br />January 2, 2018 <br />during SVE operation was not available on GeoTracker, or in the SCJEHD and City <br />files. <br />An ozone sparging system with 17 wells was operated at the site between June <br />2003 and sometime before the destruction of all site wells in March 2004 (T&R, <br />2004). A report detailing the calculated petroleum hydrocarbon mass removed <br />during SVE operation was not available on GeoTracker, or in the SCJEHD and City <br />files. <br />Between April and May 2004, approximately 1,180 tons of impacted soil was <br />excavated from a 28-foot by 30-foot by 22-foot-deep area that included the <br />former UST pit and well MW-3. During the excavation, approximately 40,000 <br />gallons of petroleum hydrocarbon-impacted groundwater was pumped from the <br />pit and discharged to the sanitary sewer after carbon filter treatment. Prior to <br />backfilling the excavation with clean imported fill material, approximately 500 <br />pounds of oxygen release compound (ORC) was placed in the bottom of the <br />excavation pit (T&R 2004). <br />Soil and groundwater has been tested for MTBE and results reported in accordance with <br />Health and Safety Code section 25296.15? <br />Yes. <br />Nuisance as defined by Water Code section 13050 does not exist at the site? <br />Yes. There are no known nuisance conditions at the site. <br />3.2 MEDIA-SPECIFIC CRITERIA <br />3.2.1 Groundwater-Specific Criteria <br />A groundwater monitoring and sampling program was performed at the site between <br />September 1990 and October 2003 before all site wells were destroyed in March 2004 prior to site <br />redevelopment. An analysis of the characteristics that define if the site meets the requirements <br />for case closure under the groundwater-specific criteria of the LTCP is as follows: <br />Plume Length: During the last groundwater monitoring and sampling event, the length of <br />dissolved phase plume was estimated to be approximately 350 feet (October 2003 dissolved <br />-phase isoconcentration map, Appendix D). It should be noted the dissolved gasoline range <br />organics (GRO) and benzene plume length is controlled by the presence of 69 ug/L GRO <br />and 0.87 ug/L benzene reported in the downgradient well MW-15. Referring to groundwater <br />data for MW-15 included in Appendix C, the well was sampled 30 times and 26 of the water <br />samples collected from well did not contain GRO or benzene at concentrations above the <br />laboratory reporting limits. The plume was stable to shrinking in aerial extent based on the <br />decreasing concentrations of petroleum hydrocarbon constituents in site wells over time <br />(historical groundwater analytical tables, Appendix C). A very conservative estimate of the <br />plume current plume length is >250 feet and <1,000 feet; however, the actual length of the <br />dissolved phase plume is likely <250 feet given the historical groundwater data collected <br />Stantec <br />bm \ \ us1312- <br />f02 \ workgroup \ 1857 \ active\ 185703766 \ 05_report_deliv \ deliverable \ work_plan \ 185703766_20180102_424_van_buren_work_plan_final.docx 3.2