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ARCHIVED REPORTS_XR0010254
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3500 - Local Oversight Program
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PR0545679
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ARCHIVED REPORTS_XR0010254
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Last modified
5/20/2020 12:18:13 PM
Creation date
5/20/2020 11:55:19 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0010254
RECORD_ID
PR0545679
PE
3528
FACILITY_ID
FA0005644
FACILITY_NAME
ATCHISON TOPEKA & SANTA FE RR*
STREET_NUMBER
1033
Direction
E
STREET_NAME
SCOTTS
STREET_TYPE
AVE
City
STOCKTON
Zip
95205
CURRENT_STATUS
02
SITE_LOCATION
1033 E SCOTTS AVE
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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A.7TORNEY-CLIENT PRIVILEGE <br /> 2.0 SUMMARY OF PREVIOUS INVESTIGATIONS <br /> 2.1 RISK ASSESSMENT SUMMARY <br /> In May, 1993, ChemRisk® submitted to S3CPHS a baseline risk assessment for the Site <br /> which assessed (1) the potential for chemical migration through soil to groundwater and (2) <br /> the magnitude of any potential Site-related exposures and potential health risks associated <br /> with current Site conditions Using environmental fate and transport modeling, it was <br /> demonstrated that the petroleum hydrocarbons had only limited migration potential in Site <br /> soil Over a 99-year period, tetradecane, used as a conservative surrogate chemical, <br /> migrated less than one foot ChemRisO concluded that the petroleum hydrocarbons will not <br /> impact the groundwater beneath the Site There were therefore no complete exposure <br /> pathways at the Site It was recommended that the petroleum hydrocarbons present in soil <br /> beneath the Santa Fe Railway Company Site can safely remain in place because they do not <br /> pose a threat to either groundwater resources or human populations No further <br /> investigations are necessary and additional groundwater monitoring at the Site is unnecessary, <br /> 2.2 SOIL SAMPLING AND ANALYSIS <br /> Six rounds of soil sampling have been completed Soil from beneath the Site was sampled <br /> and analyzed in January 1988, August 1989, January 1991, May 1991, December 1992, and <br /> April 1993 The first round of sampling included analyses for (1) total petroleum <br /> hydrocarbons (as diesel) (2) benzene, (3) toluene, (4) ethylbenzene, (5) xylenes, (6) <br /> halogenated volatile organics, and (7) polychlonnated biphenyls (PCBs) As halogenated <br /> volatile organics PCBs, and BTEX were not detected in the preliminary samples, subsequent <br /> samples were analyzed only for TPHd, gasoline and in some instances, BTEX. The results <br /> of the soil sampling are presented in Tables IA and 1B Figure 2-1 presents the sampling <br /> locations and summarizes the results Figures 2-2 to 2-4 illustrate the vertical and lateral <br /> extent of contamination as characterized during the soil sampling investigation of May 1991 <br /> TPHd as high as 6,900 ppm was detected during the initial sampling round Subsequent <br /> investigations reported TPH,, concentrations as high as 7,400 ppm in a sample taken at a <br /> depth of I1 0-I2 0 feet (B-5) In the third round of sampling which included samples taken <br /> during monitoring well installation, TPH, was less than 1 0 ppm (the reporting limit) In the <br /> May 1991 sampling event, a concentration of 4,300 ppm of TPHd was identified in a sample <br /> taken at a depth of 15 5 to 16 0 feet The primary purpose of the final two rounds of soil <br /> sampling was for partitioning studies to simulate the movement of TPHd These <br /> investigations are discussed below in Section 3 0 <br /> 1 <br /> G�iymLMONTEICLOSURE SMMiOeM7t 7 002 2 <br />
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