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ARCHIVED REPORTS_XR0004063
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0508110
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ARCHIVED REPORTS_XR0004063
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Entry Properties
Last modified
2/13/2020 3:40:18 PM
Creation date
2/13/2020 9:57:54 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004063
RECORD_ID
PR0508110
PE
2950
FACILITY_ID
FA0006134
FACILITY_NAME
POMBO RANCH
STREET_NUMBER
24100
Direction
S
STREET_NAME
LAMMERS
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
24002002
CURRENT_STATUS
01
SITE_LOCATION
24100 S LAMMERS RD
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Po,mbo Ranch Facility April 24,2005 <br /> Remedial Excavation&Source Removal <br /> 16 Y Apparent contamination extended in a north to northeast direction and the lateral limits of <br /> the excavation resulted in an irregular shape 65' to the east of the former underground <br /> tank and 50 to 62 feet north of the 65'south lateral line (see Figure 2). Monitoring well <br /> MW-4, located within the area of excavation was destroyed. The well is scheduled for <br /> replacement on May 4, 2005 just outside the excavated area. <br /> Confirmation samples were collected from each of the four sidewalls of the excavation at <br /> ' about ten feet in depth. Gasoline hydrocarbons were not detected in the samples above <br /> reporting limits. Kerosene range hydrocarbons were present in very low levels in two of <br /> the samples. Volatile aromatic hydrocarbons were detected in low concentrations on the <br /> ' west wall and in moderate concentrations on the east wall. None of the Oxygenated <br /> Compounds, including MTBE, were present in the confirmation samples. Lead levels <br /> were similar to the pre-qualification sample levels. Confirmation Iaboratory sample <br /> ' results are shown in Appendix B. <br /> Table of Anal tical Results 03/01/05 <br /> Sample Gasoline TEPH Benzene Toluene E-Benzene Xylenes Oxys Lead <br /> I.D. m /K m /K /Kg jug/Kg REESm <br /> aN <br /> CW-1-10' <1.0 29 <5.0 <5.0 19 19 ND 5.6 <br /> CS-2-10' <1.0 <1.0 <5.0 <5.0 <5.0 <5.0 ND 5.6 <br /> CN-3-10' <1.0 <1.0 <5.0 <5.0 <5.0 <5.0 ND 5.0 <br /> CE-4-10' <1.0 37 <500 1 <500 670 1290 ND 5.5 <br /> ND=Non Detect <br /> 1,524.71 tons of excavated soils were removed from the site and transported to Forward <br /> Landfill for disposal. Disposal Activity Reports are shown in Appendix C. Due to <br /> ' seasonally late rain the soil had to be transported over a number of weeks. Since the soil <br /> was damp and "sticky", and had a tendency to stay in the trailer, vegetable oil was used <br /> to lubricate the 33 foot long end dump trailer between each load. The excavation was <br /> backfilled with clean soils segregated from the excavation and soil provided by Pombo <br /> from an onsite source. The surface was graded and the base rock or road base replaced. <br /> ' 2.1 Soil Sampling <br /> ' All soil sampling equipment was thoroughly cleaned before and between sampling to <br /> prevent cross contamination. Relatively undisturbed soil samples were with a spoon <br /> sampler on a pole when access was available otherwise the sample was collected with the <br /> backhoe bucket and placed in a brass tube. The laboratory samples did not have head <br /> space and were immediately sealed in their liners using plastic caps. <br /> Soils were collected at 10 foot depths from each sidewall for laboratory analysis. All soil <br /> samples were delivered, under chain of custody, to an analytical laboratory licensed by <br /> the State of California for hazardous materials work. The samples were analyzed for <br />' gasoline and gasoline constituents and TEPH for diesel-kerosene-motor oil range <br /> petroleum hydrocarbons, the Oxygenated Compounds and lead. <br /> 7 <br />
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