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SITE INFORMATION AND CORRESPONDENCE
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Last modified
2/14/2019 3:46:08 PM
Creation date
2/14/2019 9:40:06 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0517323
PE
2960
FACILITY_ID
FA0013339
FACILITY_NAME
MT HOUSE SITES 1-6
STREET_NUMBER
0
STREET_NAME
BYRON
STREET_TYPE
RD
City
TRACY
Zip
95376
CURRENT_STATUS
01
SITE_LOCATION
BYRON RD
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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- 2- 18 April 2012 <br /> Michael Oliphant <br /> NFAR— Catellus, Tracy <br /> The findings of SAI C's October 2010 human health screening evaluation considered a residential land <br /> use scenario for exposure to chemicals of potential concern in onsite soil. The risk evaluation was <br /> conducted using a methodology and approach described in the Preliminary Endangerment Assessment <br /> (PEA) Guidance Manual, California Environmental Protection Agency, Department of Toxic Substances <br /> Control, 1999 (CaIEPA-DTSC). Given that the most of the project lies within a utility corridor, shallow <br /> groundwater is unlikely to be used at the Site, so the screening evaluation did not consider a <br /> groundwater exposure pathway. <br /> SAIC estimated the cancer risk and non-cancer hazard from exposure to onsite soil using a residential <br /> exposure scenario, following equations and assumptions provided in the CaIEPA-DISC PEA Guidance <br /> Manual. SAIC estimated the exposure routes for incidental soil ingested and dermal contact with soil, <br /> inhalation of windblown dust for non-volatile constituents, and inhalation of chemical vapors from soil. <br /> The aggregate cancer risk for oral, dermal, and inhalation exposure to onsite soil was 4E-06, which is <br /> within the acceptable risk range of 1 E-06 to 1 E-04, and does not present an unacceptable risk for a <br /> residential exposure scenario. Given the current Site development, the future onsite use will likely be <br /> by construction/trench workers. The aggregate non-cancer hazard was 3E-03 which is well below the <br /> acceptable health hazard value of 1. The Report estimated that both the cancer risk and non-cancer <br /> hazard indicate the present Site conditions do not pose a health risk for a hypothetical resident. <br /> SAIC's review of the California Department of Fish and Game 2009 Natural Diversity Database for <br /> wildlife indicates that six threatened or sensitive species in the vicinity. The Swainsons' Hawk reported <br /> in 2004 was about 900 feet from the northern property boundary. As noted in the risk screening <br /> evaluation, based on the planned use of the property, the Site is not considered suitable habitat for <br /> sensitive ecological receptors and that a threat does not appear to exist. <br /> Consistent with State Water Resources Control Board (SWRCB) Resolution No. 92-049, Section ill, A <br /> through C, SAIC evaluated alternative cleanup technologies and determined that any process other <br /> than natural attenuation would be ineffective, infeasible, and disproportionally costly. Residual crude oil <br /> concentrations naturally degrade with time, likely over a period of several years. <br /> Issues: In the early 1990's, a release of non-hazardous crude oil to soil and groundwater from the <br /> historical TAOC and/or OVP pipelines that transected the project, was discovered. Soil and <br /> groundwater impacts consist of TPHc constituents. Fuel fingerprint evaluation confirmed the TPH <br /> present was consistent residual weathered San Joaquin Valley crude oil. <br /> Setting: The Site use, described above and surrounding area currently includes some undeveloped <br /> and agriculture land, but has been designated as Urban Reserve 4 in the City of Tracy's General Plan. <br /> The General Plan notes that nearby areas will be developed for industrial, commercial, and office uses <br /> near Interstate 205. Some low density residential use is noted for areas farther from the Interstate. <br /> Source: Historical leaks from crude oil pipeline(s) installed in the early 1900's, and removed from <br /> service during the late 1960's to early 1970's. <br /> Actions: Field investigations were conducted between 2003 and 2008. <br /> • In 2006, 31 soil borings were advanced to collect soil and groundwater samples for TPH <br /> determination. Depth to groundwater ranged from approximately S to 15 feet bgs. The results <br /> for the soil samples submitted for analysis reported TPHc from ND, to a maximum concentration <br /> of 24,000 mg/kg in a sample from a depth of eight feet bgs. Some separate phase crude oil <br /> was noted at this same approximate interval. The majority of TPH detections were in samples <br /> at depths from 5 to about 13 feet bgs. With one exception of 2,300 mg/kg in a sample from <br /> 21.5 feet bgs, analysis of samples from deeper depths of 15 to 29 feet bgs was ND for TPH <br /> compounds, and/or did not exceed respective environmental screening levels. Some <br /> detection's of benzene, toluene, ethylbenzene, and xylenes (BTEX) and some polynuclear <br /> aromatic hydrocarbons (PAHs) were above screening levels, and/or were ND to low <br /> concentrations, not exceeding screening levels. Higher concentrations of the TPH compounds <br /> coincide with elevated concentrations of TPHc in samples. <br />
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