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SITE INFORMATION AND CORRESPONDENCE_FILE 1
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0009015
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SITE INFORMATION AND CORRESPONDENCE_FILE 1
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Last modified
5/26/2020 12:27:33 PM
Creation date
5/26/2020 10:13:26 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
FILE 1
RECORD_ID
PR0009015
PE
2960
FACILITY_ID
FA0004094
FACILITY_NAME
J R SIMPLOT (OCCIDENTAL CHEMICAL)
STREET_NUMBER
16777
STREET_NAME
HOWLAND
STREET_TYPE
RD
City
LATHROP
Zip
95330
APN
19818005
CURRENT_STATUS
02
SITE_LOCATION
16777 HOWLAND RD
P_LOCATION
07
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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electrical tape. The tubes will then be labeled, inserted into <br />ziplock baggies and placed on ice in an insulated cooler for <br />delivery to the laboratory within 24 hours of collection. Soil <br />from tubes not submitted for chemical analysis will be used to <br />provide lithologic information. <br />All soil samples submitted for chemical analysis will be labeled <br />in the field with an indelible ink pen as they are collected. <br />For each sample, the date and time of sample collection, the <br />sampler's initials, the project name and the designated analyses <br />will be recorded on the label and in the field log book. Soil <br />samples will be identified by a well number -depth combination; <br />for example, a soil sample numbered MW1-5 would indicate a soil <br />sample collected at monitor well MW -1 from 5 feet BGS. <br />5.4 Soil Sample Analytical Protocol <br />The soil samples submitted for chemical analysis will be trans- <br />ported under chain -of -custody to the WESTON Analytics' Stockton, <br />CA. laboratory. The analytical suite will include benzene, <br />toluene, xylene isomers and ethylbenzene by EPA Method 8020 <br />(aromatic volatile organics) and total petroleum hydrocarbons by <br />Method 8015 modified. WESTON Analytics' Stockton Laboratory is a <br />California certified laboratory. <br />5.5 Water Sampling <br />At the time of water sampling, the wells will first be checked <br />for the existence of a floating product layer by the use of an <br />oil -water interface probe. If the probe indicates product is <br />present, its thickness will be measured using the probe, and the <br />depth to product and depth to water will be recorded. Regardless <br />of the presence or absence of visually detectable floating <br />product, the total petroleum hydrocarbons sample will then be <br />collected. The sample will be obtained using a clean, transpar- <br />ent teflon bailer lowered into well using new, clean monofill- <br />ament line until the bailer is partially submerged. The bailer <br />will be retrieved and inspected for visual confirmation of the <br />oil -water probe results and its contents will be poured into the <br />appropriate sample container. It may be necessary to lower the <br />bailer more than once in order to obtain enough water to satisfy <br />the analytical method requirements. <br />Once the total petroleum hydrocarbons sample has been collected, <br />the total well depth will be verified. In conjunction with the <br />depth to water measurement, the volume of standing water in the <br />well and the required purge volume will be calculated and record- <br />ed on a standardized well sampling log sheet. It is proposed to <br />purge three standing well casing volumes with a 3 inch submers- <br />ible pump prior to collection of the water samples. The pump <br />will be thoroughly cleaned prior to use with a high pressure <br />potable water spray rinse, and will be cleaned after each well is <br />purged in the same fashion. In the last moments of well purging, <br />- 13 - <br />
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