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ARCHIVED REPORTS_XR0002830
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0508461
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ARCHIVED REPORTS_XR0002830
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Last modified
1/29/2020 4:10:55 PM
Creation date
1/29/2020 3:36:15 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002830
RECORD_ID
PR0508461
PE
2950
FACILITY_ID
FA0008092
FACILITY_NAME
CONTINENTAL GRAIN CO
STREET_NUMBER
1805
STREET_NAME
HARBOR
STREET_TYPE
ST
City
STOCKTON
Zip
95203
APN
14502005
CURRENT_STATUS
01
SITE_LOCATION
1805 HARBOR ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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• FIELD INVESTIGATION <br /> To investigate the extent of residual soil and groundwater contamination at the site, a total of <br /> seven soil borings were advanced in the vicinities of the former USTs All field activities were <br /> performed in accordance with Smith Technology's Workplan for Subsurface Investigation at <br /> Continental Grain 1805 Harbor Street, Stockton, California, dated September 10, 1997 This <br /> workplan was approved by PHSlEHD on October 1, 1997 with minor modifications <br /> Soil Sample Collection <br /> On October 7, 1997, a Smith Technology geologist supervised the advancement of one soil boring <br /> to 31 feet bgs, one soil boring to 26 feet bgs, and five soil borings to 20 feet bgs Soil borings <br /> SBI through SB6 were placed in the vicinity of the former 10,000-gallon UST and soil boring <br /> SB7 was placed in the vicinity of the former 750-gallon UST A site plan with soil boring <br /> locations is shown on Figure 2 Fisch Environmental, California License C57 683865, advanced <br /> the borings using a truck mounted Geoprobe® narrow diameter ng employing direct push <br /> technology Soil samples were collected from borings SBI and SB7 at five-foot intervals in <br /> acetate sampling tubes and were described according to the Unified Soil Classification System A <br /> soil sample was also collected from boring SB2 at 15 feet bgs Descriptions of soil types <br /> encountered and sample collection intervals are presented on the boring logs contained in <br /> Attachment 1 <br /> Each soil sample was field screened with a Photoiomzation Detector (PID) for the presence of <br /> volatile organic compounds Sample tubes were then sealed at each end using Teflon tape and <br /> plastic end caps, labeled, and placed on ice Selected soil samples were kept on ice and delivered <br /> under chain-of-custody documentation to a State-certified American Environmental Network <br /> (AEN) laboratories, (DOHS Cert No 1172) for chemical analysis Field notes and PID readings <br /> are contained in Attachment 2 <br /> During the advancement of borings SB2 and SB3, large amounts of free product were present in <br /> the groundwater samples With the approval of Mr Bruce Askanas of PHSIEHD, it was decided <br /> in the field to define the groundwater plume Soil sampling was discontinued to ensure that there <br /> was sufficient time to define the groundwater plume <br /> Groundwater Sample Collection <br /> One groundwater sample was collected from each boring at the depth groundwater was first <br /> encountered, approximately 20 feet bgs A Geoprobe® Screen Point 15 Groundwater Sampler <br /> was threaded onto the leading end of the Geoprobe after groundwater had been encountered <br /> When the sampler was advanced, O-ring seals and an expendable drive point provided a <br /> watertight system to ensure sample integrity <br /> • w 1625001reporlslsum doc 2 <br /> • <br /> SMTN <br />
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