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(VCCEP) Tier 1 Pilot Submission for BENZENE - Tera

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Table 5.11: Benzene Releases <strong>for</strong> All Industries Reporting TRI data <strong>for</strong> 2003<br />

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

March 2006<br />

Type of Release Release Amount<br />

(million<br />

pounds/year)<br />

34<br />

Percent of Total Release<br />

Total air emissions 6.26 93%<br />

Surface water discharges 0.019 0.3%<br />

Underground injections 0.36 5.3%<br />

Releases to land 0.033 0.5%<br />

Transfer to disposal 0.075 1.1%<br />

Total 6.75 100%<br />

5.10 Contribution of Chain-of-Commerce Sources and Releases to Personal Exposure<br />

“The central principal of measuring human exposure is [to] measure where the people are”<br />

(Wallace, 2001). This was the guiding principle of the EPA Total Exposure Assessment<br />

Methodology (TEAM) Studies, which took place between the 1980’s and 1990’s.<br />

The TEAM studies consistently showed that indoor benzene exposures were greater than<br />

outdoor exposures (Wallace, 2001). They also concluded that “no effect on personal exposure<br />

of living close to major fixed sources of benzene (oil refineries, storage tanks, chemical plants,<br />

etc.) could be detected” in six cities where personal exposures to benzene were investigated<br />

(Wallace, 1996). Rather, most benzene exposure was found to be caused by personal<br />

activities, such as riding in a vehicle or smoking cigarettes (Wallace, 1996, 2001). For smokers,<br />

Wallace concluded that 89% of personal benzene exposure was attributable to mainstream<br />

cigarette smoke. Non-smoker’s exposure to benzene was found to be primarily attributable to<br />

automobile exhaust or gasoline vapor emissions (e.g., vapor emissions during refueling or<br />

indoor exposures occurring as a result of vapor intrusion from an attached garage; Wallace,<br />

1996, 2001).<br />

The TEAM studies have concluded that the “following are not important sources of exposure to<br />

benzene on a nationwide basis” (Wallace, 1989a):<br />

• Chemical plants;<br />

• Petroleum refining operations;<br />

• Oil storage tanks; and<br />

• Drinking water.<br />

The findings of Wallace regarding the contribution of community industrial sources on personal<br />

exposures to benzene have also been observed by more recent studies conducted by Mickey<br />

Leland National Urban Air Toxics Research Center (NUATRC) and other independent<br />

researchers. In contrast to the findings of Wallace however, the recent literature indicates that<br />

in-vehicle exposures and environmental tobacco smoke are not the primary sources of personal<br />

benzene exposure. Rather the personal exposures are driven by in-home indoor air<br />

concentrations and mainstream smoking. This is further discussed in Section 7.

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