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ARCHIVED REPORTS XR0001282
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0544173
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ARCHIVED REPORTS XR0001282
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Last modified
2/25/2019 2:02:58 PM
Creation date
2/25/2019 10:44:16 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001282
RECORD_ID
PR0544173
PE
3528
FACILITY_ID
FA0003613
FACILITY_NAME
ARCO STATION #4493*
STREET_NUMBER
205
Direction
N
STREET_NAME
CENTER
STREET_TYPE
ST
City
STOCKTON
Zip
95202
APN
13909003
CURRENT_STATUS
02
SITE_LOCATION
205 N CENTER ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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WNg
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EHD - Public
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, z <br /> Atlantic Richfield Comranr <br /> Former iLRU()4493,205 N Coiter Strccl_Stockton.CA <br /> S� tamper 5.2111)0 <br /> • pumped dry of all gasoline, the piping was evacuated and capped, and a temporary <br /> closure plan was submitted to the SJCEHD. <br /> In July 1997, the SJCEHD sent ARCO a letter stating that the former Shell service <br /> station approximately 300 feet east of the site had reported increasing concentrations of <br /> MtBE in their upgradient wells. These wells are to the east of the ARCO station, which <br /> is the historical groundwater flow direction. <br /> In July 1998, SECOR sampled two UST pit observation wells. Analytical results from <br /> the sampling event indicated that MtBE was present in one observation well at a <br /> concentration of 52.4 ppb. Depth to water during the observation well sampling was <br /> approximately 10 feet bgs. <br /> On February 10, 11, and 12, 1999, four groundwater monitoring wells (MW-1 through <br /> MW-4) were installed at the site. The wells are currently sampled on a quarterly basis. <br /> Groundwater flow at the site has ranged from east to southeast at a gradient of 0.003 to <br /> 0.008 ft/ft. Maximum concentrations of TPHg and MtBE are present in well MW-4 on <br /> the east side of the property. <br /> ASSESSMENT ACTIVITIES AND FINDINGS <br /> On May 8, 2000, one continuous core soil boring (B-1) was completed at the site by <br /> Precision Sampling of San Rafael, California. Soil boring B-l was advanced to 60 feet <br /> below ground surface (bgs) using Precision Sampling's direct push Enviro-Core sampling <br /> system. Soil boring B-1 was continuously cored and groundwater "grab' samples were <br /> collected at depths of 30 feet, 45 feet, and 60 feet bgs. On June 2, 2000, three groundwater <br /> monitoring wells (MW-5 through MW-7) were installed downgradient of the site by V&W <br /> Drilling of Isleton, California. Wells MW-5 through MW-7 were installed to a total depth <br /> of 25 feet bgs and were screened from 5 to 2.5 feet bgs. Boring Logs showing well <br /> completion details are included as Attachment B. Technical information on Precision <br /> Sampling's direct push Enviro-Core sampling system is included as Attachment C. The <br /> findings of this assessment are discussed below: <br /> Subsurface Conditions <br /> In boring B-1, a silty sand to silty and sandy clay was encountered from approximately 5 <br /> to 14 feet bgs. From approximately 14 to 33 feet bgs, a silty sand to sand was <br /> encountered. Groundwater was encountered at approximately 16 feet bgs during drilling <br /> within the silty sand to sand. A moist to wet clayey to sandy silt was encountered from <br /> depths of approximately 33 to 43 feet bgs in boring B-1. Sand and silty sand was <br /> encountered from approximately 43 to 56 feet bgs and was underlain by silty clay to the <br /> bottom of the boring at 61 feet bgs. Soil samples collected continuously fi-om boring B-1 <br /> from depths of 14 to 56 were classified as wet to saturated. At depths of 56 to 61 feet <br /> bgs within the silty clay, the moisture content was classified as damp, suggesting that this <br /> maybe a potential confining layer. <br /> 077.41883.3301well install1doc <br />
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