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ARCHIVED REPORTS_XR0002650
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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H
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HARDING
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3500 - Local Oversight Program
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PR0545260
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ARCHIVED REPORTS_XR0002650
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Entry Properties
Last modified
1/30/2020 2:09:02 PM
Creation date
1/30/2020 1:15:01 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002650
RECORD_ID
PR0545260
PE
3528
FACILITY_ID
FA0005325
FACILITY_NAME
INLAND PAINT COMPANY
STREET_NUMBER
117
Direction
W
STREET_NAME
HARDING
STREET_TYPE
WAY
City
STOCKTON
Zip
95204
APN
12707031
CURRENT_STATUS
02
SITE_LOCATION
117 W HARDING WAY
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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C. V <br /> • ASSOCIATES I N C . <br /> accordance with ATC Associates' Workplan for Subsurface Investigation at Inland Paint <br /> Company, 117 West Harding Way, Stockton, California, dated September 4, 1997. The <br /> workplan was verbally approved by San Joaquin County Public Health Services Environmental <br /> Health Division (PHS/EHD). <br /> Soil Sample Collection <br /> On January 8, 1998, an ATC Associates geologist supervised the advancement of one soil boring <br /> to 41.5 feet bgs. A site plan showing the soil boring location is included as Figure 2. Drilling was <br /> conducted by V&W Drilling (State C57 license no. 710678) utilizing a hollow stem auger drill rig. <br /> A field geologist logged all drill cuttings and cored soil samples utilizing the Unified Soil <br /> Classification System. Cored soil samples were collected at five-foot intervals using a 2-inch <br /> diameter split-spoon sampler containing three brass tubes. The cored samples and drill cuttings <br /> were characterized for soil type, moisture content, and visual evidence of petroleum <br /> contamination. Descriptions of soil types encountered and sample collection intervals are <br /> presented on the boring log contained in Attachment 1. <br /> Each soil sample was field screened with a Photoionization Detector (PID) for the presence of <br /> volatile organic compounds. The measured PID readings ranged from 667 parts per million <br /> • (ppm) at 5.5 feet bgs to 7 ppm at 41.5 bgs, the maximum depth explored. Soil sample tubes were <br /> then sealed at each end using Teflon tape and plastic end caps, labeled, and placed on ice. <br /> Selected soil samples were kept on ice and delivered under chain-of-custody documentation to <br /> State-certified American Environmental Network (AEN) laboratory (DOHS Cert. No. 1172) for <br /> chemical analysis. PID readings are contained on boring log in Attachment 1 and field notes are <br /> contained in Attachment 2. <br /> Groundwater S_ample Collection <br /> A Hydropunch groundwater sampling probe was advanced by V & W Drilling in soil boring SB 1. <br /> The probe was hydraulically driven into the ground to a depth of 1 to 2 feet beneath the <br /> groundwater piezometric surface. A field geologist was present to supervise the investigation and <br /> collect a groundwater sample. Descriptions of field conditions encountered and sample collection <br /> details were recorded and are contained in Attachments 1 and 2. Subsequent to the sample <br /> collection, the open sampling hole was tremie grouted to the surface with neat cement. <br /> Soil and Groundwater Sample Analis <br /> Selected soil samples and groundwater samples from boring SB 1 were placed on ice and delivered <br /> to AEN laboratory. Soil samples were analyzed for total petroleum hydrocarbons as gasoline and <br /> diesel (TPHg and TPHd) by EPA Methods 8015; and volatile organic compounds (VOCs) by <br /> EPA Method 8260. Groundwater samples were analyzed for TPHg, TPHd, VOCs, and <br /> halogenated volatile organic compounds (HVOCs) by EPA Method 8010/8020. <br /> w:1172951repoM\sum.doc 2 <br />
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