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ARCHIVED REPORTS XR0011334
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3500 - Local Oversight Program
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PR0544624
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ARCHIVED REPORTS XR0011334
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Entry Properties
Last modified
7/3/2019 6:59:40 PM
Creation date
7/3/2019 3:50:33 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011334
RECORD_ID
PR0544624
PE
3526
FACILITY_ID
FA0005206
FACILITY_NAME
GEORGES SERVICE
STREET_NUMBER
1600
Direction
W
STREET_NAME
DURHAM FERRY
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25510004
CURRENT_STATUS
02
SITE_LOCATION
1600 W DURHAM FERRY RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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SJGOV\wng
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EHD - Public
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Geologual Technuslnc Page 3 <br /> George's Service <br /> Soil Excavation Report <br /> Project No 425 3 <br /> January 28,2002 <br /> ' drainpipes were installed at the west and east ends of the excavation site to a depth of 10- <br /> feet bgs Pea gravel was used to fill the excavation pit to 1 5 feet bgs and compacted with a <br /> ' vibrating compactor Class 2 base-rock was used to fill the pit to 4-inches bgs and was <br /> capped with asphalt after compaction <br /> ' Field Observations - <br /> The northern wall of the excavation pit was primarily tight plastic clay The clay contained <br /> a 12 foot long by 2-foot thick lens of soft sugary sand located about 6 feet bgs, which <br /> pinched out at both ends The southern wall was silty clay/clayey silt The western wall <br /> ' was clay and silt but also showed some large rocks In the eastern half of the excavation, <br /> contamination started a few feet below ground surface and extended deeper than 12-feet <br /> bgs In the western half of the excavation, the contamination was below 5-feet bgs and <br /> extended to greater then 12-feet bgs <br /> ' Groundwater was at approximately 11-feet bgs Sidewall samples were collected from six <br /> locations around the excavation pit by driving a clean brass tube into the soil The end's of <br /> ' the tubes were covered with Teflon and plastic caps The tubes were labeled, a chain of <br /> custody was filled out and the samples submitted to Sherwood Laboratories in Hilmar for <br /> analysis Figure 1 is a map showing excavation sample locations <br /> ' Two photographs of the excavation are presented in Appendix D <br /> Monitoring Well Damage and Repair <br /> • The casing on MW-102 was bent during the excavation on July 24" The casing was <br /> repaired by GTI on the 25" by cutting off the bent section at approximately 11-feet bgs <br /> and gluing in a riser <br /> • The well casing of MW-5 was cracked at approximately 2 feet bgs The casing was cut <br /> off at two feet bgs and an extension was glued into place <br /> ' • The top of casing of MW-202 was damaged during the excavation on July 25, 2001 <br /> The casing was trimmed and the cap was replaced on MW-202 <br /> In accordance to A132886, on December 21, 2001, all the monitoring and domestic wells <br /> ' were surveyed <br /> Soil Analyses <br /> ' The average TPH-gasoline for the excavation was 4,114 mg/Kg Samples collected at the <br /> SE Sidewall and SW Sidewall locations had the highest concentrations at 11,800 and 26,200 <br /> mg/Kg respectively These two samples also had the highest concentrations of MTBE at <br /> 38,500 and 4,920 ug/Kg respectively, however the MTBE results were performed by EPA <br /> ' method 8020 <br /> A summary data table of the soil data is included as Table 1 in Appendix A Laboratory <br /> ' Data Sheets are included in Appendix B <br /> Soil Disposal <br /> The contaminated soil was piled on plastic and covered with plastic as required by San <br /> Joaquin Valley Unified Air Pollution Control District (SJVUAPCD) The stockpile <br /> remained covered on site until October 31, 2001 <br />
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