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PR0515030
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Last modified
5/8/2020 12:31:23 PM
Creation date
5/8/2020 11:55:16 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0515030
PE
2950
FACILITY_ID
FA0012018
FACILITY_NAME
QUALITY CLEANERS
STREET_NUMBER
3081
Direction
N
STREET_NAME
TRACY
STREET_TYPE
BLVD
City
TRACY
Zip
95376
CURRENT_STATUS
01
SITE_LOCATION
3081 N TRACY BLVD
P_DISTRICT
005
QC Status
Approved
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LSauers
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EHD - Public
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Phase 11 Additional Subsurface Investigation <br /> Tracy Corners Shopping Center <br /> 3225 North Tracy Boulevard <br /> Tracy,California 95376 <br /> Partner Project Number 14-129814.3 <br /> January 27,2015 <br /> Page 12 <br /> Phase 1, Quality Cleaners had a projected tenant term from April 1992 to September 2007 at the subject <br /> property. A dry cleaner checklist completed by A/E indicated that one floor drain was present in a room <br /> adjacent to the dry cleaning machine and was connected to the sewer system. In addition, the dry <br /> cleaning machine was manufactured in 1991. <br /> Partner noted during the Phase I investigation completed in December 2014, that according to an <br /> interview with the property manager,this site has operated as a dry cleaning facility since 1992. Although <br /> the current closed-loop dry cleaning machine (installed in 2007) uses a hydrocarbon-based solvent (DF- <br /> 2000 Aliphatic Hydrocarbon Fluid) for dry cleaning purposes, the prior tenant used a closed-loop dry <br /> cleaning machine (operational from 1992 to 2007) that used chlorinated solvents, particularly PCE, during <br /> the dry cleaning process. Chlorinated solvents (a.k.a. chlorinated volatile organic compounds [CVOCs]) <br /> are highly mobile chemicals that can easily accumulate in soil. These solvents, even when properly stored <br /> and handled, can readily migrate into the subsurface as a result of small releases associated with on-site <br /> operations. <br /> During Partner's Phase I investigation in December 2014, two 55-gallon steel drums (one containing new <br /> DF-2000 Aliphatic Hydrocarbon Fluid and one containing dry cleaning process waste sludge) were <br /> observed adjacent to the dry cleaning machine. Steel secondary containment was noted around the dry <br /> cleaning machine. In addition, no significant staining or cracking was observed in the area around the dry <br /> cleaning unit or around the hazardous waste storage area. According to the most recent waste manifest <br /> on-site, Technichem, a licensed transporter of hazardous waste, collects the waste sludge. According to <br /> the property manager, a prior subsurface investigation performed in 1999 indicated that soil beneath the <br /> dry cleaning tenant space had not been impacted by chlorinated solvents. However, based on the length <br /> of time between the prior subsurface investigation and the change from the PCE-based dry cleaning <br /> machine to the hydrocarbon-based dry cleaning machine (approximately eight years), the former use of <br /> chlorinated solvents represented a recognized environmental condition (REC). <br /> Partner completed a Phase II Report on December 19, 2014 for the Quality Cleaners unit in the Tracy <br /> Corners Shopping Center to investigate the potential impact of PCE and related CVOCs in sub-slab soil <br /> gas as a consequence a potential release or releases from the dry cleaning facility. The scope of the Phase <br /> II Investigation included the installation of four sub-slab soil gas points and the collection and analysis of <br /> four soil gas samples and one duplicate soil gas sample for PCE, trichloroethene (TCE), cis-1,2- <br /> dichloroethene(DCE),trans-1,2-DCE, and vinyl chloride. <br /> PCE was detected in each of the four soil gas samples and the one duplicate soil gas sample collected. <br /> Soil gas concentrations were converted into theoretical indoor air concentrations using the Department of <br /> Toxic Substances Control (DTSC) recommended attenuation factor. Applying the applicable DTSC <br /> foundation attenuation factor of 0.05 resulted in a calculated theoretical indoor air concentration of 165 <br /> micrograms per cubic meter(pg/m3) of PCE and 17.5 pg/m3 of TCE. The conversion resulted in indoor air <br /> concentrations above the DTSC recommended value for PCE of 2.08 pg/m3 at each of the four locations <br /> and above the EPA Regional Screening Level (RSL)for TCE of 3.0 pg/main one location (SG3). <br /> PARTNER <br />
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