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PR0537485
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Last modified
7/27/2020 3:42:55 PM
Creation date
7/27/2020 2:46:18 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0537485
PE
2957
FACILITY_ID
FA0021568
FACILITY_NAME
FORMER RAINWATER CAR WASH
STREET_NUMBER
420
Direction
W
STREET_NAME
YOSEMITE
STREET_TYPE
AVE
City
MANTECA
Zip
95336
APN
21931206
CURRENT_STATUS
01
SITE_LOCATION
420 W YOSEMITE AVE
P_LOCATION
04
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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' Off-Site Groundwater Investigation Work Plan Page 3 <br /> Rainwater Car Wash, Manteca, California 95336 <br /> May 30,2012 <br /> 1 3.2.3 AGE, Sensitive Receptor Survey, September 8, 2000 <br /> ' AGE conducted a sensitive receptor survey to locate potential vertical conduits within a 2,000-foot radius of the <br /> site. The sensitive receptor survey located four City of Manteca Public Works Department(CMPWD)municipal <br /> water wells and 25 groundwater monitoring wells located within one mile of the site. <br /> ' Sensitive Receptors <br /> Name Distance from the Site Description <br /> CMPWD Well#276- 1,900 feet northwest Non-operational water well located 200 feel north of the Almond <br /> Almond Avenue Avenue and Yosemite Avenue intersection <br /> CMPWD Well#431 - 3,000 feet northeast Non-operationsl water well located 100 feet east of the Pine <br /> Pine Street Street and Garfield Avenue intersection <br /> CMPWD Well#331 - Operational water well located 100 feet east of the Jessie Street <br /> Jessie Street <br /> ' 1,500 feet south and Oregon Street intersection <br /> CMPWD Well#613-EI 3,200 feet southwest Operational water well located 100 feet east of the Tenaya Court <br /> Capitan Avenue and Portal Avenue intersection <br /> 11 Groundwater 1,500 feet east Diamond Lumber,151 South Main Street <br /> ' Monitoring Wells <br /> 14 Groundwater 1,800 feet east Golden Grain,229 Moffat Boulevard <br /> Monitodng Wells <br /> ' 3.2.4 AGE, Cone Penetrometer Testing Site Investigation — Fourth Quarter 2000, <br /> February 7, 2001 <br /> ' AGE advanced four additional soil borings(P-7 through P-10)on-site,using cone-penetrometer testing(CPT) <br /> technology to characterize the geologic/hydrogeologic framework and to assess preferential contaminant <br /> migration pathways. Based on the initial CPT data,AGE informally identified four potential hydrogeologic flow <br /> units(designated as the First, Second,Third and Primary Water Zones),and located at depths between 15 and 47 <br /> ' feet below ground surface(bgs), 58 and 92 feet bgs, 102 and 115 feet bgs,and 128 and 150 feet bgs, respectively. <br /> Significant concentrations of dissolved petroleum hydrocarbons were reported from the First Water Zone,and low <br /> to moderate concentrations of dissolved petroleum hydrocarbons and chlorinated solvents(tetrachloroethene and <br /> trichloromethane)were reported from the Second,Third and Primary Aquifer Zones. <br /> 3.2.5 AGE, Ground Water Aquifer Pumping Test Report— Second Quarter 2001, May 15, <br /> ' 2001 <br /> AGE installed groundwater extraction well EW I and groundwater observation well MW6 at the site for <br /> performance of a groundwater pumping test. Soil borings EW 1 and MW6 were advanced to 45 feet bgs. Boring <br /> EW 1 was single-completed as a 6-inch-diameter groundwater extraction well and MW6 single-completed as a 2- <br /> inch-diameter groundwater observation well with screened intervals between 20 and 45 feet bgs.No soil or <br /> groundwater samples were collected during this investigation. <br /> A groundwater aquifer pumping test was performed at well EW 1 to assess the general groundwater aquifer <br /> characteristics at the site. From the pump test,a transmissivity value was calculated at 955 square feet per day,a <br /> storativity value at 0.032,a hydraulic conductivity value of 0.013 centimeters per second,and a groundwater <br /> radius of influence projected at 140 feet, using a semi-logarithmic plot of drawdown versus distance. <br /> 3.2.6 AGE, Interim Remediation Work Plan- June 2001, 21 June 2001 <br /> Interim groundwater pump-and-treat remediation was initiated at the site by continuous extraction of groundwater <br /> from well EW 1 at a rate of approximately 5 gallons per minute. The extracted groundwater was processed through <br /> ' a groundwater treatment system consisting of 8,000 pounds of granular activated carbon.Following treatment, <br /> Ami Adini <br /> ' �Assoctates.inc. <br />
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