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ARCHIVED REPORTS BIOTREATMENT BEDS POST REMEDIATION INVESTIGATION REPORT
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ARCHIVED REPORTS BIOTREATMENT BEDS POST REMEDIATION INVESTIGATION REPORT
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Last modified
12/14/2018 4:39:42 PM
Creation date
11/6/2018 1:40:20 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
BIOTREATMENT BEDS POST REMEDIATION INVESTIGATION REPORT
RECORD_ID
PR0009049
PE
2960
FACILITY_ID
FA0004041
FACILITY_NAME
UP TRACY RAIL YARD
STREET_NUMBER
720
Direction
E
STREET_NAME
SIXTH
STREET_TYPE
ST
City
TRACY
Zip
95376
APN
25001014
CURRENT_STATUS
01
SITE_LOCATION
720 E SIXTH ST
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
Scanner
WNg
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FilePath
\MIGRATIONS\S\SIXTH\720\PR0009049\BIOTREATMENT BEDS POST REMEDIATION INVESTIGATION REPORT.PDF
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EHD - Public
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ARCADIS Ms. Kathryn Dominic , <br /> August 24, 2010 <br /> 1 <br /> biotreatment bed in native soil (3 ft bgs). However, it is apparent that the , <br /> biotreatment bed thickness varied across the site and in some places is likely thicker <br /> than 3 feet. , <br /> Soil samples were collected using a hand auger and slide-hammer sampler. The soil <br /> cuttings were classified in accordance with the Unified Soil Classification System ' <br /> (USCS). The boring logs are provided in Appendix B. Samples were placed in <br /> appropriate containers, labeled, sealed, packed on ice, and submitted under <br /> standard chain-of-custody to TestAmerica, Inc., a state-certified laboratory. The ' <br /> samples were analyzed for TPH-d using United States Environmental Protection <br /> Agency(US EPA) Method 8015B (with and without silica gel preparation [US EPA <br /> Method 3630C]) ' <br /> Conestoga-Rovers Associates (CRA)was contracted by UPRR to conduct a data <br /> validation and prepare a report to document the accuracy and quality control for the ' <br /> analytical results. <br /> Post-Remediation Soil Sampling Results ' <br /> The analytical results are summarized in Table 1 and the laboratory reports are <br /> included in Appendix C. The data validation report prepared by CRA is included in ' <br /> Appendix D. <br /> TPH-mo concentrations in samples collected during March 2010 ranged from "non- ' <br /> detect' (not detected above the reporting limit) in three of the six three-foot deep <br /> samples to 970 milligrams per kilogram (mg/kg; HA-6, 1 ft bgs). Although TPH-mo <br /> has no corresponding CAO cleanup concentration, the data are summarized for ' <br /> reference in Table 1. <br /> As shown in Table 1, TPH-d concentrations in samples collected during March 2010 ' <br /> ranged from "non-detect' (not detected above the reporting limit; HA-5, 3 ft bgs)to <br /> 620 milligrams per kilogram (mg/kg; HA-6, 1 ft bgs). Although the TPH-d <br /> concentrations exceed the CAO cleanup concentration of 50 mg/kg in eight of the ' <br /> twelve samples collected, the corresponding soil samples collected from 3 ft bgs are <br /> generally lower that the sample collected from 1 ft bgs depth interval at each <br /> location. Considering only the soil samples collected from 3 ft bgs, only two of the six ' <br /> samples slightly exceed the CAO cleanup concentration (HA-1 [98 mg/kg] and HA-3 <br /> [74 mg/kg]). ' <br /> 1 <br /> Page: <br /> 8/12 ' <br />
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