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PR0537923
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Last modified
2/13/2020 1:51:25 PM
Creation date
2/13/2020 11:19:48 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0537923
PE
2950
FACILITY_ID
FA0021891
FACILITY_NAME
DUFFY PROPERTY
STREET_NUMBER
375
Direction
W
STREET_NAME
LARCH
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
21220010
CURRENT_STATUS
01
SITE_LOCATION
375 W LARCH RD
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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i • <br /> 375 West Larch Road,Tracy <br /> August 28, 2013 <br /> Page 4 <br /> ANALYTICAL RESULTS <br /> The groundwater samples were transported under chain-of-custody procedures to McCampbell <br /> Analytical,a state-certified laboratory in Pittsburg, California. One soil sample from each boring was <br /> selected for analysis. The laboratory report and chain of custody form are included as Attachment <br /> F. <br /> The samples were analyzed for the presence of total petroleum hydrocarbons quantified as gasoline <br /> range organics (TPH-grog) and total petroleum hydrocarbons quantified as diesel range organics <br /> (TPH-dro) by EPA Method 8015C, benzene,toluene, ethylbenzene,and xylenes(BTEX), methyl tert <br /> butyl ether(MTBE), naphthalene, fuel oxygenates, and lead scavengers by EPA method 8060, and <br /> total lead by E200.8. <br /> No concentrations of TPH-gro, TPH-dro, benzene, toluene, MTBE, naphthalene, fuel oxygenates, <br /> lead scavengers, or total lead were detected above the laboratory detection limits. <br /> Ethylbenzene and toluene were detected in the groundwater samples collected from B-1 only at <br /> concentrations of 2.3 micrograms per liter(Ng/L)and 16 pg/L respectively. Both concentrations are <br /> well below the Maximum Concentration Levels (MCL's) set forth by the California Department of <br /> Public Health (CDPH). The MCL for toluene is 300 pg/L and for xylenes is 1,750 p/L. <br /> CONCLUSIONS AND RECOMMENDATIONS <br /> In 1970 two maps indicated a plan to install a 8,000-10,000 gallon fuel tank(unspecified above or <br /> below ground)and two fuel dispensers. In 1973 an inspection record indicated that a 1,000 gallon <br /> diesel AST was present on the Property illegally and was required to be replaced with a UST. No <br /> further information regarding UST's or AST's was found. <br /> ERAS scanned the area for the presence of any remaining UST's and none were found. <br /> Following approval from the S]CEHD, ERAS advanced three soil borings(B-1 through B-3)on August <br /> 15t', 2013 for the collection of groundwater samples in the location of a former fuel tank and <br /> dispenser. The samples were analyzed for the presence of TPH-gro, TPH-dro, BTEX, MTBE, <br /> oxygenates, naphthalene, lead scavengers, and total lead. <br /> The only contaminants detected were ethylbenzene and toluene in the groundwater samples <br /> collected from B-1 at concentrations of 2.3 pg/L and 16pg/L respectively, below the MCUs set forth <br /> by the CDPH. <br /> TPH-gro,TPH-dro,and TPH-oro are methods that compare analytical results to standards for gasoline,diesel and motor oil,respectively. <br /> Therefore analytical results are estimates of quantities based on what would be expected for the range of hydrocarbon results for the standard. <br /> Gasoline range organics(giro)are those hydrocarbon compounds that are in the range of C6 to CIO,diesel range organics(dro)are those <br /> hydrocarbon compounds that are in the range of CIO to C23,and oil range organics(oro)are those hydrocarbon compounds that are in the range of <br /> CI8 to C36. There can be overlap in reporting methods as well as identification of compounds that fall within the standard that may not necessarily <br /> be derived from gasoline,diesel,or oil. <br />
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