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Environmental Health - Public
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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 /> Soil samples were collected during Phase I and II using a "Probe-Drive Sampler" tool <br /> V <br /> developed by Geoprobe. The Probe-Drive Sampler is attached to the leading end of the <br /> probe rod and is driven into the subsurface. The threaded stop-pin in the trailing end of the <br /> sampler assembly prevents the piston tip and piston rod from sliding into the sample <br /> collection tube as the assembly is being driven to depth. At the desired sampling depth, the <br /> �— stop-pin, which is threaded into the drive head of the sampler assembly (lined with four 6- <br /> inch long by 1-inch diameter brass liners), is removed using extension rods inserted down <br /> the inside diameter of the probe rods. After the stop-pin has been removed, the sampler is <br /> again driven forward, soil is collected in the sample chamber as the piston retracts. The <br /> assembly is then brought back to the surface. The sample is prepared for chemical analysis <br /> V <br /> by placing Teflon sheeting and plastic end caps over the brass liner sections, labeling the <br /> sample with sample number, date, time, and project number, placing the sample in a <br /> resealable plastic bag, then placing the sample on ice in an ice chest until the samples were <br /> transported under chain of custody procedures to California Laboratory Services in Rancho <br /> Cordova, California, a California certified analytical laboratory. All samplers and probe <br /> rods were steam cleaned prior to use in each boring location. The samplers were <br /> decontaminated between each sample advancement using Alconox detergent wash, double tap <br /> water rinse, and double deionized water rinse. <br /> V <br /> Soil boring B-1 was advanced to a depth of 31 feet bgs located southeast of the former UST <br /> excavation in the vicinity of the former stockpile (Figure 4). Soil samples were collected <br /> at 3, 5, 10, 15, 19, 25, and 29 feet bgs. Soil samples for chemical analysis were collected <br /> from 4.5 to 5, 6.5 to 7, 11.5 to 12, 16 to 16.5, 19.5 to 20, 20 to 20.5, 25.5 to 26, and 30 <br /> to 30.5 feet bgs. No visible contamination, or elevated headspace readings were observed <br /> during the advancement of B-1. <br /> Soil boring B-2 was advanced to a depth of 31 feet bgs located northwest of the former UST <br /> excavation near an existing propane tank. Soil samples were collected at 5, 10, 15, 18, 20, <br /> 25, and 29 feet bgs. Soil samples for chemical analysis were collected from 16.5 to 17, 18.5 <br /> to 19, 19 to 19.5, 21.5 to 22, and 26 to 26.5 feet bgs. No visible contamination, or elevated <br /> headspace readings were observed during the advancement of B-2. <br /> V <br /> V <br /> 8054/FEMAWAXPIER.RFT/8-24-95 SAC 2-3 <br /> V <br />
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