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ARCHIVED REPORTS XR0006544
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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DURHAM FERRY
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4491
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3500 - Local Oversight Program
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PR0544625
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ARCHIVED REPORTS XR0006544
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Entry Properties
Last modified
7/3/2019 7:59:57 PM
Creation date
7/3/2019 4:43:02 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006544
RECORD_ID
PR0544625
PE
3528
FACILITY_ID
FA0003113
FACILITY_NAME
ZAPIEN MARKET
STREET_NUMBER
4491
Direction
W
STREET_NAME
DURHAM FERRY
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25504003
CURRENT_STATUS
02
SITE_LOCATION
4491 W DURHAM FERRY RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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LEAkWXTER <br /> c R 0 u r <br /> • Environmental Servrcrs <br /> request and directed monitoring of the groundwater for two additional quarters to complete four <br /> continuous quarters of monitoring following active remediation <br /> Four quarters of verification monitoring were completed with the third quarter 2000 event Based on <br /> those results, Clearwater requested reconsideration of site closure The SJCPHS/EHD concurred with <br /> the closure recommendation and forwarded the case to the Central Valley Regional Water Quality <br /> Control Board (CVRWQCB) for concurrence on December 27, 2000 The CVRWQCB did not concur <br /> with the closure request and forwarded the project back to the SJCPHS/EHD for additional oversight, in <br /> a letter dated January 25, 2001 The primary concern of the CVRWQCB was that residual dissolved- <br /> phase MTBE concentrations in MW-2 were above primary Maximum Contaminant Levels (MCLS) and <br /> the trend at the very end of monitoring appeared to be unstable <br /> Based on these conditions, Clearwater resumed monitoring of groundwater at the project in February <br /> 2001 <br /> Groundwater Monitonng Methods <br /> On April 2, 2001, Clearwater attempted to monitor all project monitoring and remediation wells An <br /> electronic water level indicator was used to gauge depth to water accurate to within ±0 01-feet Wells <br /> ® RW-1 (silted in from soil vapor extraction), VW-1, VW-2, VW-3, and VW-4 were dry, and therefore <br /> removed from the sampling schedule tlus event All wells were also checked for the presence of Light <br /> Non-Aqueous Phase Liquid (LNAPL) gasoline product prior to purging No measurable thicknesses of <br /> LNAPL were observed in any of the wells Monitoring was performed in accordance with Clearwater's <br /> Field Protocols (attached) <br /> The wells with measurable water columns (MW-1 through MW-7, SW-1, SW-2, and Domestic Well) <br /> were purged until sampling parameters (e g temperature, pH and conductivity) stabilized, which <br /> occurred by approximately three wet casing volumes Groundwater monitoring and well purging <br /> information was recorded on Gauge Data/Purge Calculations and Purge Data sheets (attached) <br /> Following recovery of water levels to at least 80% of their static levels, groundwater samples were <br /> collected from the monitoring wells using dedicated polyethylene bailers Samples were transferred to <br /> laboratory supplied containers, labeled, documented on a chain-of-custody form, and placed on ice in a <br /> cooler for transport to the project laboratory <br /> Purging devices were decontaminated between wells in an Alconox® wash followed by double rinse in <br /> clean tap water to prevent cross-contamination Purge water and rinseate was stored on-site in labeled <br /> 55-gallons drums pending future removal and disposal <br /> All groundwater samples were analyzed by Kiff Analytical, a DHS-certified laboratory located in Davis, <br /> California Groundwater samples were analyzed for concentrations of TPHg, BTEX, and MTBE by EPA <br /> Method 8260B <br /> ZB107C GWMR 2Q01 3 April 9 2001 <br />
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