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Health Assessment Document for Diesel Emissions - NSCEP | US ...

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H ON0 2<br />

·/HN0 3<br />

N0 2<br />

H<br />

14 Table 2-13 summarizes the nitroarene product data <strong>for</strong> OH radical-initiated and N 2 0 5 gas-<br />

15 phase reactions with several PAHs studied to date in environmental chambers (Arey et al., 1989; ·<br />

16 · Zielinska et aL, 1990). Section 2.5.3 will discuss the fact that, generally, the same nitro-PAH<br />

17 isomers that are <strong>for</strong>med from OH radical and N 20 5 reactions are observed in ambient air samples.<br />

18<br />

19 2.4.2.2. Particulate-Phase Reactions<br />

20 Organic compounds present in diesel exhaust are partitioned into the particulate phase<br />

21 under atmospheric conditions. The following chemical processes are likely to contribute to the<br />

22 degradation of these compounds in the troposphere (Atkinson, 1988):<br />

23 • Photolysis,<br />

24<br />

· 25 • Reaction with 0 3 ,<br />

26<br />

27 • Reaction with N 20 5 during nighttime hours,<br />

28<br />

29 • Reaction with N0 2 during nighttime and daytime hours,<br />

30<br />

31 • Reaction with H 20 2 , and<br />

32<br />

33 • Reaction with HN0 3 , HN0 2 , and H 2S0 4 •<br />

34 However, the atmospheric lifetimes of particle-bound organic compounds are not well<br />

35 known, partly because (1) these chemical processes depend on the nature ofthe substrate (e.g.,<br />

36 Behymer and Hites, 1985, 1988) and (2) many of the laboratory studies have been done using<br />

37 atmospherically unrealistic adsorbents, such as glass-fiber and Teflon-coated glass-fiber filters,<br />

2/1198 2-40 DRAFT--DO NOT CITE OR QUOTE

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