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ARCHIVED REPORTS_XR0012626
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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2900 - Site Mitigation Program
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PR0543041
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ARCHIVED REPORTS_XR0012626
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Last modified
5/18/2020 3:03:14 PM
Creation date
5/18/2020 2:45:25 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012626
RECORD_ID
PR0543041
PE
2960
FACILITY_ID
FA0024604
FACILITY_NAME
HUMAN SERVICES AGENCY
STREET_NUMBER
145
Direction
S
STREET_NAME
SUTTER
STREET_TYPE
ST
City
STOCKTON
Zip
95202
APN
14912016
CURRENT_STATUS
01
SITE_LOCATION
145 S SUTTER ST
P_LOCATION
01
QC Status
Approved
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EHD - Public
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t <br /> tg <br /> Collection. Soil from tubes not submitted for chemical anal s <br /> will be used to provide lithologic information. y is <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 b number-depth <br /> i s for example, a soil sample numbered well <br /> 5 woulind cate a soil <br /> f ° sample collected at monitor well ice]-1 from 5 feet below grade. <br /> 5.4 Soil ga_mule Analytical Protocol <br /> f € <br /> The soil samples submitted for chemical analysis will be trans- <br /> ported under chain-of-custody to the WESTON Analyticso Stockton, <br /> CA. laboratory. The analytical suite will include benzene, <br /> toluene, xylene isomers and ethylbenaene by EPA Method $pip <br /> (aromatic volatile organics) , total petroleum hydrocarbons by <br /> modifiedMetho <br /> i + <br /> Analytics, Stockton 15aboratoryEDB <br /> s a Californiaextraction <br /> certified WESTON for these anaylses, ora- <br /> 5.5 Water Sampling <br /> t,.. At the time of water sampling, the wells will first be <br /> for the existence of a floating product layer by the use of checked <br /> an <br /> ".• oil-water interface <br /> probe. If the probe indicates product is <br /> Fpresent, its thickness will be measured using the probe, and the <br /> t depth to product and depth to water will be <br /> k; recorded. Regardless <br /> Of the presence or absence Of visually detectable floating <br /> product, the total <br /> collected, petroleum hydrocarbons sample will then be <br /> The sample will be obtained using a clean, transpar- <br /> ent tef�on bailer lowered into well <br /> ament line until using new, clean monofill- <br /> will be retrieved the bailer is partially submerged. The bailer <br /> and inspected for visual confirmation <br /> oil-water of the <br /> f ` <br /> ( ; probe results and its contents will be poured in <br /> appropriate sample container. to the <br /> It may be necessary to lower the <br /> bailer more than once in order to obtain enough water to satisfy <br /> � j 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 /> i depth to water measurement, the volume of standing water in the <br /> «° well and the required g purge volume will be calculated and record-- <br /> ed on a standardized well sampling log sheet. It is proposed to <br /> i ' purge three standing well casing volumes with a 3 inch submers- <br /> ible <br /> pump prior to collection of the water samples. The pump <br /> use with a high pressure <br /> Will be thoroughly cleaned prior to i <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 /> the pH, temperature, and conductivity of the water will be <br /> measured and recorded. A record of the purging activities, <br /> tet <br />
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