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PR0505092
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
2/5/2019 4:57:53 PM
Creation date
2/5/2019 4:48:19 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0505092
PE
2960
FACILITY_ID
FA0006532
FACILITY_NAME
LYOTH LOADING STATION/CHEVRON
STREET_NUMBER
26501
Direction
S
STREET_NAME
BANTA
STREET_TYPE
RD
City
TRACY
Zip
95376
CURRENT_STATUS
01
SITE_LOCATION
26501 S BANTA RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Former Lyoth Loading Station - 3 - 8 October 1998 <br /> Chevron Pipe Line, San Joaquin Co. <br /> Comparison of Site Data with Appendix B of Tri-Regional Board Staff Recommendations for <br /> Preliminary Investigation and Evaluation of Underground Tank Sites (Criteria for Low Risk <br /> Vadose Zone/Low Risk Groundwater Designation) <br /> 1. Criteria for Low Risk Vadose Zone Designation <br /> a. Demonstrate that only the vadose zone has been affected. <br /> The site does not meet this criterion because the soil contamination goes below the water table <br /> and the contamination in the vadose zone has not been remediated. <br /> b. The release or leak has been stopped and sources of hydrocarbons in the vadose zone have <br /> been removed or permanently contained. <br /> The release has been stopped but the sources of contamination in the vadose zone have not been <br /> removed or permanently contained. <br /> c. Petroleum hydrocarbons remaining in the vadose zone do not impact or threaten waters of the <br /> State. <br /> The presence of separate phase product (which is being removed quarterly) in MW-2, <br /> occasional detection of TPHd, and the one-time detection of pyrene in MW-7 show that the <br /> waters of the State are being impacted. TPHd was detected in MW-6 in April 1997, October <br /> 1997, and January 1998 at 140 ppb, 85 ppb, and 60 ppb, respectively. Only 140 ppb exceeds <br /> the Board's water quality objective of 100 ppb for TPHd. However, Chevron uses silica gel <br /> cleanup in the analysis. TPHd testing should follow the same procedure required for PAHs. <br /> The decision as to whether the site meets this Criterion C should be made after confirmation of <br /> the TPHd levels at the site. <br /> d. No significant risk to human health and safety exists or is anticipated following remediation. <br /> This criterion does not apply because no remediation is being proposed. <br /> 2. Criteria for Low Risk Groundwater Designation <br /> a. Contaminants remaining in the vadose zone must not reverse or threaten to reverse the mass <br /> reduction rate of groundwater pollutants. <br /> See comments in Lc above. <br /> b. Separate phase product has been removed to the extent possible. <br /> As stated in Lc above, separate phase product is being removed every quarter, but more should <br /> be done to facilitate separate phase product removal, such as removing contaminated soils. <br /> Contaminated soil removal to levels which do not pose a water quality threat also should <br /> eliminate occasional detections of TPHd in groundwater. <br /> c. No existing water supply wells, deeper aquifers, surface waters or other receptors are <br /> threatened by pollutants remaining in the aquifer. <br /> The vertical extent of groundwater contamination has not been defined. Consequently,the <br /> threat to the next groundwater body has not been determined. <br />
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