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ARCHIVED REPORTS_XR0008762
Environmental Health - Public
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EHD Program Facility Records by Street Name
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WASHINGTON
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4325
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3500 - Local Oversight Program
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PR0545834
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ARCHIVED REPORTS_XR0008762
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Last modified
7/15/2020 2:59:11 PM
Creation date
7/15/2020 1:51:54 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008762
RECORD_ID
PR0545834
PE
3528
FACILITY_ID
FA0005104
FACILITY_NAME
ECONO GAS
STREET_NUMBER
4325
Direction
E
STREET_NAME
WASHINGTON
STREET_TYPE
ST
City
STOCKTON
Zip
95205
APN
15733708
CURRENT_STATUS
02
SITE_LOCATION
4325 E WASHINGTON ST
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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GROUNDWATER MONITORING AND SAMPLING PROCEDURES <br /> Introduction <br /> The groundwater monitoring and sampling event was conducted In accordance with , <br /> procedures detailed in the State of California LUIT Manual The objectives of the <br /> monitoring and sampling procedures were to determine the groundwater gradient at the site <br /> and to collect and preserve representative samples of the groundwater at the site for , <br /> delivery to a State of California-certified laboratory Samples were collected from four <br /> groundwater monitoring wells during this event Samples were analyzed by Trace Analysis <br /> Laboratory, Hayward, California, for concentrations of Benzene, Ethylbenzene, Toluene, and , <br /> Xylenes (BETX) using the Modified EPA Method 8020, and Total Petroleum Hydrocarbons <br /> as gasoline (TPHg) using the DHS Method ' <br /> Sample and Data Collection <br /> All field parameter meters were calibrated according to the manufacturers Instructions prior <br /> to use Static depths to water and total depths of all wells were measured using a scaled , <br /> electronic water level meter Water level measurements were recorded In the field log to <br /> the nearest 0 01 foot If free product was present, the depth to free product and the depth <br /> to water were measured using an electronic oil/water interface probe and an observation <br /> sample was collected with a clear acrylic bailer for confirmation No analytical samples <br /> were collected from monitoring wells containing more than 0 25 inch of free product Prior ' <br /> to collecting a sample, standing water was purged from the well using a clean Teflon bailer <br /> Care was taken during purging and sample collection to minimize the loss of volatile <br /> constituents from the sample Purged water was periodically monitored for temperature, ' <br /> pH, and specific conductance, and the values were recorded in the field fog Physical <br /> characteristics such as color, turbidity, odor, or the presence of a sheen were noted during ' <br /> purging and recorded in the field log Samples were collected after stabilization of the <br /> measured parameters and recovery of the water level to at least 80 percent of its initial <br /> level Wells dewatered during purging were sampled after 80 percent recovery, or, when ' <br /> recovery to 80 percent exceeded two hours, a sample was collected when sufficient <br /> volume was available Samples to be analyzed for TPHg and BETX were decanted from the ' <br /> top of the bailer into two EPA-approved 40-m1 volatile organic analysis (VOA) bottles <br /> preserved with hydrochloric acid Sample bottles were completely filled with no observable <br /> headspace Sample bottles were labeled with the project name and number, well ' <br /> identification number, date, name of sampler, preservation method, and analysis requested <br /> Samples were immediately placed In an ice chest and maintained at 4°C for delivery to a <br /> State of California-certified laboratory Water generated during the purging process was <br /> stored on-site in properly labeled (Title 22 CCR §66508) DOT-approved 55-gallon drum$ <br /> pending disposal <br /> Du Pont Environmental Remediation Services A-1 <br /> 0511 14 Rev 0 Printed on Recycled Paper ' <br />
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