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SITE INFORMATION AND CORRESPONDENCE_CASE 1
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SITE INFORMATION AND CORRESPONDENCE_CASE 1
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Last modified
5/19/2021 4:29:38 PM
Creation date
5/19/2021 4:01:54 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
CASE 1
RECORD_ID
PR0508042
PE
2960
FACILITY_ID
FA0005316
FACILITY_NAME
U S CAN COMPANY
STREET_NUMBER
35275
Direction
S
STREET_NAME
WELTY
STREET_TYPE
RD
City
VERNALIS
Zip
95385
APN
25518009
CURRENT_STATUS
01
SITE_LOCATION
35275 S WELTY RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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SJGOV\dsedra
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EHD - Public
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M. Scott Mansholt - 2 - 14 December 2005 <br /> Chevron Environmental <br /> US Can-Welty Road <br /> In a 1997 investigation, TCE was not detected in groundwater, but 2.4 µg/L cis-1-2 dichloroethene (a <br /> TCE degradation by-product) was detected in one sample. Since TCE, benzene, and gasoline <br /> specifically are unrelated to the OVP, after about 1997 analysis for these compounds was not routinely <br /> conducted for the pipeline investigations. <br /> Elevated TPH concentrations in groundwater generally correspond to and downgradient of the on-site <br /> areas having impacted soil and free phase petroleum (sheen) in monitoring wells MW-1 and MW-2. <br /> Depth to groundwater is between 32 and 38 feet and the gradient is east/northeast. <br /> Consequently, it appears that in addition to the impacts as a result of OVP leaks, the elevated TPHg <br /> concentrations and detectable TCE concentrations, suggests that these compounds may be related to the <br /> waste/bum pit. <br /> Current Investigation and Quarterly Groundwater Monitoring <br /> The purpose of the current investigation was to characterize subsurface soils off-site and downgradient <br /> of former boring GMX-12 (north of the UPRR tracks) and to delineate impacted groundwater <br /> downgradient of the site. The current investigation describes the advancement of four soil borings, <br /> installation of MW-5, and collection of soil and groundwater samples for laboratory analysis. <br /> During the third quarterly monitoring event (July 2005) groundwater samples were also obtained from <br /> three of four on-site wells (MW-1 had a sheen and was not sampled) and two off-site wells (MW-5 and <br /> WFSMW-1) as part of the third quarterly monitoring event. Between 1996 and 2003, the onsite wells <br /> were sampled three or less quarterly monitoring events, but beginning with the third quarter 2005, and <br /> until further notice, sampling will be conducted for several consecutive quarters. <br /> A well search, conducted to identify water supply wells within a 2,000 foot radius of the site, noted one <br /> crossgradient and two upgradient domestic wells within the search area. Well records for the domestic <br /> wells indicate that surface seals are a minimum of 20 feet. Two onsite wells described as "public" wells <br /> were observed on-site. Monitoring wells associated with other nearby sites under environmental <br /> investigation were also identified. <br /> Soil <br /> Borings SB-13, 14, and 15 were advanced approximately 100 to 150 feet NE-NW of boring GMX-12 to <br /> characterize/delineate the previously identified impact. TPH as crude oil (TPHc) at 15,000 mg/kg in soil <br /> was reported at 41.5 feet in GMX-12. The borings were advanced to a target depth of 48 feet to coincide <br /> with maximum depths of previous soil borings. According to the results, with the exception of 120 <br /> mg/kg TPHc atone foot in SB-14, there was no evidence of petroleum hydrocarbons. Boring SB-15 <br /> (converted to MW-5), advanced approximately 100 feet north (downgradient) of boring GMX-10, <br /> similarly did not report TPH compounds present in soil. Therefore, it appears borings SB-13 to SB-15 <br /> and former borings GMX-6 and GMX-7 define the lateral extent of impacts in soil downgradient, to the <br /> north-northwest of the site. <br />
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