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ARCHIVED REPORTS_XR0012168
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3500 - Local Oversight Program
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PR0541875
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ARCHIVED REPORTS_XR0012168
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Last modified
3/16/2020 5:52:55 PM
Creation date
3/16/2020 3:49:06 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012168
RECORD_ID
PR0541875
PE
2960
FACILITY_ID
FA0024017
FACILITY_NAME
CHEVRON SITE 306415
STREET_NUMBER
437
Direction
E
STREET_NAME
MINER
STREET_TYPE
AVE
City
STOCKTON
Zip
95202
APN
1392417
CURRENT_STATUS
01
SITE_LOCATION
437 E MINER AVE
P_LOCATION
01
QC Status
Approved
Scanner
SJGOV\sballwahn
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EHD - Public
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GSI Field Methods and Procedures <br /> February 14, 1995 <br /> is monitored for the presence of floating product and the depth-to-water is recorded Wells <br /> are then developed by alternately surging the well with a bailer, then purging the well with <br /> a pump to remove accumulated sediments and draw groundwater into the well Development <br /> continues until the groundwater parameters (temperature, pH, and conductivity) have <br /> stabilized Groundwater removed from the well during development is stored at the site in <br /> approved sealed drums pending disposal Wells are allowed to stand a minimum of 24 hours <br /> after development before being sampled <br /> Prior to sampling, well casing water and interstitial water in the artificial sand pack of each <br /> well are purged using a pump or bailer The type of equipment used to purge the well is <br /> chosen based on well size, depth, location, accessibility, chemical constituents, and client or <br /> regulatory recommendations Generally, three to five casing volumes are typically purged <br /> prior to sample collection Wells that dewater or demonstrate low yield will not be sampled <br /> unless the well recharges to at least 80% of the previously measured water column <br /> Temperature, pH, and specific conductivity of the discharged water are monitored during <br /> purging Purging continues until groundwater parameters have stabilized Purged well water <br /> is stored at the site in approved sealed drums pending disposal <br /> Groundwater samples are collected from the well with either a disposable teflon bailer or a <br /> pneumatic bladder pump The sampling device is chosen based on the well criteria outlined <br /> above Groundwater samples are collected in laboratory-prepared containers After sample <br /> collection, the sample bottles are sealed, labelled, and entered on a chain-of-custody form <br /> The sample bottles are then packed in protective foam or bubble-wrap and placed in a cooler <br /> with blue ice for transport to the analytical laboratory <br /> If previous sampling data is available, the wells at a site are generally sampled from the least <br /> contaminated to the most contaminated Well purging and sampling equipment are <br /> decontaminated between wells and between sites using a high-pressure wash of potable water <br /> and Alconox® soap, followed by a rinse in potable water and then distilled water <br /> Storing and Sampling of Drill Cuttings <br /> Drill cuttings are stockpiled on plastic sheeting or stored in drums depending on site <br /> conditions and regulatory requirements Stockpile samples are collected and analyzed on the <br /> basis of one composite sample per 50 cubic yards of soil Stockpile samples are composed <br /> of four discrete soil samples, each collected from an arbitrary location on the stockpile The <br /> four discrete samples are then composited in the laboratory prior to analysis <br /> Each discrete stockpile sample is collected by removing the upper 3 to 6 inches of soil, and <br /> them driving the stainless steel or brass sample tube into the stockpiled material with a hand, <br /> A-3 <br /> GeoStrategies Inc. <br />
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