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(VCCEP) Tier 1 Pilot Submission for BENZENE - Tera

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7.2 Sources of Benzene Exposure<br />

Childrens’ exposures to benzene were quantified based on in<strong>for</strong>mation provided in the scientific<br />

peer-reviewed literature or through exposure modeling using various EPA exposure models.<br />

The sources of benzene have been defined in terms of two general source categories: ambient<br />

sources of exposures and exposures resulting from specific sources.<br />

7.2.1 Ambient Environmental Exposures<br />

Ambient childhood exposures to benzene could occur from four general sources: 1) ambient air,<br />

2) food, 3) drinking water, and 4) human milk. Potential exposures to each source are described<br />

further below.<br />

7.2.1.1 Ambient Air<br />

During the 1980s and early 1990s the EPA funded and provided oversight <strong>for</strong> human exposure<br />

research with the objective of directly measuring exposure to VOCs using personal air<br />

samplers. The conclusion of this extensive research project, known as the EPA Total Exposure<br />

Assessment Methodology (TEAM) Studies, was that the most important sources of exposure<br />

are small and originate close to the person (Wallace, 2001). The presence of major point<br />

sources, such as refineries and chemical facilities, was not correlated with increased personal<br />

exposure to organic chemicals. For many chemicals, including benzene, distant sources of air<br />

releases play a smaller part in the determination of total exposure than localized sources such<br />

as use of petroleum products, time spent in vehicles, and use of tobacco products.<br />

The Clean Air Act Amendments of 1990 provided <strong>for</strong> creation of the National Urban Air Toxics<br />

Research Center (NUATRC). The goal of this organization is to promote, develop and support<br />

research related to human health risks from air toxics. As part of the NUATRC mission, several<br />

studies were conducted where VOC exposures to children were evaluated. The Health Effects<br />

Institute (HEI) and the Mickey Leland National Urban Air Toxics Research Center (NUATRC)<br />

jointly funded a project called the Relationship between Indoor, Outdoor and Personal Air<br />

(RIOPA); a large urban air toxics project that was comprised of three studies. The RIOPA<br />

project tested the hypothesis that personal exposure to air toxics is influenced by outdoor<br />

sources of these air toxics. It involved 3 cities with different air pollution source profiles: Los<br />

Angeles, Cali<strong>for</strong>nia is dominated by mobile sources; Houston, Texas is dominated by industrial<br />

point sources; and Elizabeth, New Jersey includes a mixture of mobile and point sources. In<br />

each city, 100 homes were monitored <strong>for</strong> 48 hours in each of 2 seasons. The homes were<br />

monitored indoors and outdoors <strong>for</strong> particulate matter smaller than 2.5 microns (PM2.5), VOCs,<br />

and aldehydes. In addition, personal exposure to PM2.5, VOCs, and aldehydes, and in-vehicle<br />

exposure to aldehydes were measured <strong>for</strong> residents of these homes. In general it was found<br />

that indoor air benzene concentrations were higher than outdoor air, but lower than the personal<br />

benzene concentrations.<br />

A community based study conducted by Buckley et al., (2005) in Baltimore also evaluated the<br />

impact of industry on community air quality and individual resident exposure to15 VOCs. The<br />

study was designed to examine the potential industry effect by comparing indoor, outdoor, and<br />

personal air concentrations in South Baltimore to those in Hampden, an urban Baltimore<br />

community with a less intense industrial presence. Buckley et al. concluded that except <strong>for</strong><br />

ethylbenzene and m,p-xylene, the VOC concentrations at all three levels of monitoring (outdoor,<br />

indoor, and personal) were comparable in the two communities, suggesting no industrial impact<br />

or an impact smaller than that detectable with the sample size of the study. For the two<br />

Benzene <strong>VCCEP</strong> <strong>Submission</strong><br />

March 2006<br />

100

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