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ARCHIVED REPORTS_XR0008757
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0545834
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ARCHIVED REPORTS_XR0008757
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Last modified
7/15/2020 2:56:57 PM
Creation date
7/15/2020 1:50:29 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008757
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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IOctober 11, 1993 <br /> Job No 93036 <br />' Page A - 1 <br /> GROUNDWATER MONITORING AND SAMPLING PROCEDURES <br /> Introduction <br />' The groundwater monitoring and sampling event was conducted in accordance with procedures detailed <br /> in the State of California LUFT Manual. The objectives of the monitoring and sampling procedures <br /> were to determine the groundwater gradient at the site and to collect and preserve representative samples <br />' of the groundwater at the site for delivery to a State of California-cemfied laboratory Samples were <br /> collected from four groundwater monitoring wells during this event Samples were analyzed by Trace <br /> Analysis Laboratory, Hayward, California, for concentrations of Benzene, Ethylbenzene, Toluene, and <br />' Xylenes (BETX) using the Modified EPA Method 8020, and Total Petroleum Hydrocarbons as gasoline <br /> (TPHg) using the DHS Method <br />' Sample and Data Collection <br />' All field parameter meters were calibrated according to the manufacturer's instructions prior to use <br /> Static depths to water and total depths of all wells were measured using a scaled electronic water level <br /> meter Water level measurements were recorded in the field log to the nearest 0 01 foot. If free product <br />' was present, the depth to free product and the depth to water were measured using an electronic <br /> oil/water interface probe and an observation sample was collected with a clear acrylic bailer for <br /> confirmation No analytical samples were collected from monitoring wells containing more than 0 25 <br /> inch of free product Prior to collecting a sample, standing water was purged from the well using a <br /> clean Teflon bailer Care was taken during purging and sample collection to minimize the loss of <br /> volatile constituents from the sample Purged water was periodically monitored for temperature,pH, and <br /> specific conductance, and the values were recorded in the field log Physical characteristics such as <br /> color, turbidity, odor, or the presence of a sheen were noted during purging and recorded in the field log <br /> Samples were collected after stabilization of the measured parameters and recovery of the water to at <br />' least 80 percent of its initial level Wells dewatered during purging were sampled after 80 percent <br /> recovery, or, when 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 top of the <br />' bailer into two EPA-approved 40-m1 volatile organic analysis (VOA) bottles preserved with hydrochloric <br /> acid Samples bottles were completely filled with no observable headspace Sample bottles were <br /> completely filled with no observable headspace Sample bottles were labeled with the project name and <br />' number, well 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 State of <br /> California-certified laboratory Water generated during the purging process was stored on-site in <br />' properly labeled (Title 22 CCR § 66508) DOT-approved 55-gallon drums pending disposal <br /> 1 <br /> CdNOCo�93036�QUAH2O2 REP <br /> Eng�neenn� and Construction, Inc <br />
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