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2900 - Site Mitigation Program
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PR0505722
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Last modified
1/30/2020 11:29:04 AM
Creation date
1/30/2020 9:56:36 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0505722
PE
2951
FACILITY_ID
FA0006961
FACILITY_NAME
KJAX
STREET_NUMBER
5451
Direction
E
STREET_NAME
HARDING
STREET_TYPE
WAY
City
STOCKTON
Zip
95202
APN
10122041
CURRENT_STATUS
02
SITE_LOCATION
5451 E HARDING WAY
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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Woodward-Clyde <br /> V <br /> V <br /> 2.1.2 Phase lI Direct Push Technology Soil Borings and Groundwater Sampling <br /> `r On June 1, 1995, WCFS directed the advancement of two additional soil borings to assess <br /> the lateral extent of soil contamination observed in boring B-5 and to collect one groundwater <br /> sample downgradient from the former UST and soil boring B-3. The Phase II soil sampling <br /> was conducted as described above in Section 2.1.1. Soil borings B-6 and B-7 located <br /> northwest and east of the former UST excavation (Figure 4) respectively, were advanced to <br /> depths of 26 feet and 100 feet bgs respectively. One groundwater sample (MW-7) was <br /> collected from soil boring B-7. <br /> Groundwater samples are collected by DPT methods using an expendable point equipped <br /> `r probe rod driven below the water table and then the open bore of the probe rod is exposed <br /> to the groundwater. The rod is allowed to fill with formation water. Tubing with a bottom <br /> check valve is inserted down the bore of the probe rod. The inner tubing is oscillated up and <br /> down in rapid strokes to produce a momentum pumping action. The groundwater sample <br /> �. is then placed in the appropriate containers provided by the laboratory. The containers are <br /> then labeled with sample number, date, time, project number, and placed on ice in an ice <br /> chest until transported under chain of custody procedures to a California State certified <br /> analytical laboratory. Groundwater samples collected at the KJAX site were analyzed for <br /> TPH as gasoline and TPH as diesel using modified EPA Method 8015, and BTEX using <br /> V <br /> EPA Method 8020. <br /> Soil boring B-6 was advanced to a depth of 26 feet bgs located north-northwest of boring B-5 <br /> and northwest of the former UST excavation (Figure 4). Soil samples were collected at 5, <br /> 10, 15, 17, 20, and 24 feet bgs. Soil samples for chemical analysis were collected from <br /> 16.5 to 17, 18.5 to 19, 21.5 to 22, and 25.5 to 26 feet bgs. No visible contamination, or <br /> elevated headspace readings were observed during the advancement of B-6. <br /> Soil boring B-7 was advanced with the Geoprobe DPT to a depth of 100 feet bgs located east <br /> of the former UST excavation and 14 feet east of boring B-3 (Figure 4). Soil samples were <br /> collected at 5, 10, 15, 17, 20, 24, 29, 34, 39, 44, 49, 54, 59, and 64 feet bgs. Soil <br /> samples for chemical analysis were collected from 16.5 to 17, 18 to 18.5, 21 to 21.5, and <br /> 25 to 25.5 feet bgs. No visible contamination, or elevated headspace readings were observed <br /> V <br /> 8054/PEMAMAXPIER.M/8-24-95 SAC 2-5 <br /> V <br />
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