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ARCHIVED REPORTS XR0001492
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0544206
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ARCHIVED REPORTS XR0001492
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Entry Properties
Last modified
3/1/2019 1:55:52 PM
Creation date
3/1/2019 1:41:47 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001492
RECORD_ID
PR0544206
PE
3528
FACILITY_ID
FA0005239
FACILITY_NAME
GOTELLI TRUCKING
STREET_NUMBER
1634
Direction
E
STREET_NAME
CHANNEL
STREET_TYPE
ST
City
STOCKTON
Zip
95205
APN
15304021
CURRENT_STATUS
02
SITE_LOCATION
1634 E CHANNEL ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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WNg
Tags
EHD - Public
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14 August 1991 <br /> GeoAudit CV 43C5-1. 3 <br /> Page 2 Of 4 <br /> ionization detector (PID) was used to monitor contamination levels <br /> during excavation. The excavated soil was stockpiled adjacent to <br /> the tank cavity and covered with plastic. One soil sample (GOTI-9) <br /> from d depth of approximately 9 feet was preserved in a brass <br /> sleeve and relinquished to a state-certified laboratory for <br /> analysis of aquatic toxicity. <br /> An excavator was used to deepen the excavation to 21 feet on 27 <br /> June and a backhoe was used to enlarge it slightly on 16 July. Snll <br /> samples were coll-cted on both days. Sample MCT-1 was collected <br /> from the bottom of the excavation. SYdewall samples MCSW-1, MCSW--2, <br /> MCSW-3, and MCSW-4 were collected from the excavation walls at a <br /> depth of approximately 15 ft below grade (Figure 2) . The backhoe <br /> was used to excavate soil from the sidewalls, and a slide hammer <br /> loaded with two 2-inch brass tubes was used to collect samples from <br /> the backhoe bucket. Stockp?le samples MCSP--_A and B and MCSP-2A, B, <br /> C, and D were collected by slide hammer from the soil piles. <br /> Samples were covered with aluminum foil, <br /> tape, and capped, sealed With duct <br /> placed on .ice until transport to WEST, Inc. for <br /> laboratory analysis. Samples were analyzed for gasoline, diesel, <br /> motor 011, and BTE&X (EPA methods 8015 and 8020) <br /> ,., hydrocarbons (EPA method 8010) , PCB's ,EPA method 8270) , and five <br /> metals (Cr, Cd, Pb, Zn, and Ni) . and five <br /> t <br /> The northwest corner of the ex^avation was enlarged on 2 August <br /> 1991 because residual contamination was detected in sample MCSW-1 <br /> from that portion of the cavity. After reexcavation, sample McsW-5 <br /> was taken by excavator from a depth of approximately 22 feet <br /> (Figure 2) . <br /> FXNDINGS <br /> Copies of laboratory results and chains of custody for all samples <br /> are attached. The results are discussed briefly below. <br /> x� <br /> A dark gray gravelly clay layer, containing bits of pipe and other <br /> man-made material, was present in the upper three feet of the <br /> �. excavation. This layer is backfill material. A layer of yellow <br /> silty fine--to-very-fine-grained sand extends from 3 feet to 13 . 5 <br /> feet. PID readings of SO11 samples betweeen 8 ft and 14 f below <br /> �W grade ranged between 250 and 500 ppm. <br /> The top of a relatively dense, hard clay bed was encountered at <br /> OL 13 . 5 feet. The base of this layer was difficult to identify, but <br /> appeared to be approximately 20 feet. <br /> Laboratory analyses confirm the field observations that <br /> contamination was present in the tank cavity. Szdewall samples <br />
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