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CO0020059
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2500 – Emergency Response Program
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CO0020059
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Entry Properties
Last modified
5/14/2019 10:35:10 AM
Creation date
2/22/2019 8:47:41 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2500 – Emergency Response Program
RECORD_ID
CO0020059
PE
2546
STREET_NUMBER
23577
STREET_NAME
MOUNTAIN HOUSE
STREET_TYPE
PKWY
City
TRACY
Zip
95391
ENTERED_DATE
12/5/2003 12:00:00 AM
SITE_LOCATION
23577 MOUNTAIN HOUSE PARKWAY
RECEIVED_DATE
12/4/2003 12:00:00 AM
QC Status
Approved
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ADMIN
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FilePath
\MIGRATIONS4\M\MOUNTAIN HOUSE\23577\CO0020059.PDF
Tags
EHD - Public
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Mr.Bob Gondek <br /> C A M B R I A March 11, 2004 <br /> appeared to be ongoing as evidenced by oil leaching from the test pit sidewalls. Photographs 10 <br /> and 11 show the easternmost pit. All test pits were backfilled with native soils to protect site <br /> personnel from the risks of an open excavation. <br /> Pipeline Easement Assessment: On December 15, 2003,Cambria collected samples PLl through <br /> PL6 along the exposed trench bottom to characterize soils beneath the pipeline. Photographs 4 <br /> and 12 show the exhumed pipeline and open trench. Samples were collected by scraping <br /> approximately 6 inches of soil from the sample location then driving a new brass sleeve into the <br /> exposed soil. Sample locations are shown on Figure 2. Soil samples were analyzed for TPH in the <br /> © gasoline range (CQ- C12) and TPH extended range (C13 - C40) by EPA Method 8015M, and for <br /> BTEX by EPA Method 8021. Soil sample P3-5' collected from the trench bottom immediately <br /> beneath the pipeline rupture point contained 3,900 mg/kg TPH(C4-C12), 21,000 mg/kg TPH(C13 <br /> - Cao),<50 mg/kg benzene, 75 mg/kg toluene, 22 mg/kg ethylbenzene, and 130 mg/kg xylenes. In <br /> the five remaining soil samples no TPH (Ca- C12) or BTEX were detected and TPH (C13 - C40) <br /> ranged from 26 to 54 mg/kg, indicating a relatively limited extent of oil impact along the pipeline. <br /> These results also suggest that no other pipeline leaks had occurred at the Site in the past. Soil <br /> sample results are summarized in Table 1 and the analytical laboratory reports are included as <br /> Attachment D. <br /> Interim Remedial Actions <br /> CPL and Cambria directed the emergency response crews in recovering and/or containing all <br /> free-flowing crude oil that posed a risk of migration, to the degree that soil excavation was <br /> feasible and safe. Within 24 hours of the initial release, oil in the areas characterized by the test <br /> pits had already infiltrated to between depths of 5 and 9 ft bgs. Due to the depth of impact, <br /> excavation of all oil-saturated soil was not feasible without appropriate planning including health <br /> and safety engineering. Instead, Cambria directed excavation and stockpiling of surfrcial soils to <br /> eliminate oil puddles and oil-saturated soils that could contribute to soil pore pressure and drive <br /> vertical migration. <br /> Surface Soils Excavation: On December 6,2003,Cambria directed excavation and stockpiling of <br /> oil-saturated soil and areas with residual standing oil. The affected areas were scraped to between <br /> 0.5 and 2 ft bgs. Figure 3 and Photographs 13 through 15 show the areas scraped to help limit <br /> crude oil migration. Cambria estimates that approximately 600 to 800 cubic yards of soil were <br /> excavated and stockpiled as part of this effort. <br /> Receiving Pit Over-Excavation: The receiving pit had been used to collect oil accumulating near <br /> the rupture point. As a result, the floor and sidewalls of the pit were impacted by oil. On <br /> December 6, 2003, after evacuating all oil, the receiving pit was over-excavated and the oil- <br /> impacted soils were stockpiled onsite. Cambria directed over-excavation to remove all visually <br /> 5 <br />
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