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SU0006108 SSCRPT
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SU0006108 SSCRPT
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Last modified
5/7/2020 11:32:08 AM
Creation date
9/9/2019 11:03:38 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSCRPT
RECORD_ID
SU0006108
PE
2611
FACILITY_NAME
PA-0600353
STREET_NUMBER
34701
Direction
S
STREET_NAME
WELTY
STREET_TYPE
RD
City
TRACY
APN
25518015
ENTERED_DATE
7/5/2006 12:00:00 AM
SITE_LOCATION
34701 S WELTY RD
RECEIVED_DATE
7/3/2006 12:00:00 AM
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\W\WELTY\34701\PA-0600353\SU0006108\SSC RPT.PDF
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Soil and Groundwater Investigation Report and October 2005 <br /> Second Quarter 2005 Monitoring and Sampling, US Can-Welty Road <br /> 10.4 QUALITY ASSURANCE/QUALITY CONTROL <br /> ` All field procedures were conducted in accordance with SAIC's Quality Assurance and Qualiry Control <br /> Sample Collection, Handling, and Analysis procedures. No sample was received by the laboratory <br /> outside of acceptable temperature or pH limits. In addition to routine laboratory quality control (QC) <br /> analyses, a trip blank(QA-T)and equipment rinsate(QA-RB) were submitted to the laboratory with <br /> samples WFSMW-1 and MW-5. In accordance with SAIC's standard procedures,the trip blank was <br /> analyzed. No BTEX were detected in the trip blank. <br /> ` The laboratory control sample (LCS)and laboratory control sample duplicate(LCSD)appear to be within <br /> the LCS/LCSD limits. The matrix spike (MS) and matrix spike duplicate (MSD)also are within the <br /> L MS/MSD limits and the relative percent difference criteria was within the acceptable range for either the <br /> LCS/LCSD or MS/MSD samples except for PAH compound (benzo[a]pyrene). The laboratory analytical <br /> report noted this PAH compound as"outside of specification." While not all of the laboratory QC <br /> parameters were within specification range, the information provided by these analytical results is <br /> considered useable. Laboratory QA/QC data from this sampling event are considered acceptable and the <br /> sample analytical data are considered valid. <br /> 11. DISCUSSION <br /> Based on the analytical results,the lateral extent of petroleum-affected soil at US Can—Welty Road <br /> appears to be delineated northwest to northeast of borings GMX-10 through GMX 12 by soil borings <br /> SB-13, SB-14, SB-15 and former borings GMX-6 and GMX-7. However, petroleum-affected soil does <br /> not appear to be delineated southeast of GMX-11, adjacent to the former OVP pipeline ROW. Affected <br /> soil in this area was encountered in boring SB-17, but not unexpected since it is adjacent to the former <br /> ` pipeline ROW and borders the former Vernalis Pump Station. <br /> Affected groundwater has been delineated by groundwater samples collected from wells WFSMW-1 and <br /> MW-5. Well MW-5 did not contain detectable concentrations of petroleum hydrocarbons and the <br /> groundwater sample from well WFSMW-1 did not contain detectable TPHg, BTEX, or MTBE. <br /> However,the groundwater sample collected from well WFSMW-1 contained TPHd at a concentration of <br /> 71 µg/L, below the water quality objective (WQO)of 100 pg/L. Although grab groundwater samples <br /> ` collected from soil borings SB-13 and SB-14 contained detectable TPHd at concentrations of 450 and 200 <br /> pg/L, respectively,these samples should be considered lesser quality and expected to be an order of <br /> magnitude higher in concentration than detected in the groundwater monitoring wells. Detectable <br /> r. <br /> concentrations of TPHg, BTEX, or MTBE were not detected in these grab groundwater samples. <br /> The grab groundwater sample collected from SB-17 contained 480 µg/L of TPHg, 150,000 µg/L of TPHd <br /> and 0.6 pg/L of benzene. The detection of dissolved-phase TPHg is likely an overlap of the diesel range <br /> organics based on the elevated concentration of dissolved TPHd detected. However, the presence of <br /> benzene in the grab groundwater sample from SB-17 could indicate a refined fuel plume is emanating <br /> from the former Union Oil Service Station, located north (cross gradient)of boring location SB-17. <br /> 12. SUMMARY/CONCLUSIONS <br /> The data collected during this and former subsurface investigations indicate that residual petroleum has <br /> ` mainly affected soil between 5 and 42 feet bgs in the vicinity of SB-17, MW-1, SB-1, SB-2, SB-3, B-I, <br /> B4 through B-7 (MW-2), GMX-3,GMX-8, GMX-I B, and GMX-12. In SB-17 lean clay and sandy <br /> layers below 37 feet bgs appear to be the most affected soil areas. In general,the depth of affected areas <br /> r varies through the site. The lateral extent of petroleum-affected soil appears to be delineated towards the <br /> south,west, north, northeast, and east. However, the lateral extent of petroleum-affected soil southeast of <br /> the subject site has not been fully characterized adjacent to the former OVP ROW, which borders the <br /> ` 9 From Science to Solutions° <br />
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