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

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1 important determinant in the particle overload phenomenon. The contribution of extractable<br />

2 organics has been shown to be inconsequential in this response (this subject is discussed in more<br />

3 detail in Chapter 1 0). It is, however, important to note that dose determination <strong>for</strong> inhaled<br />

4 compounds remains problematic among toxicologists (Dahl et al., 1991).<br />

5 The dosimetric aspects considered will include deposition in the conducting airways and<br />

6 alveolar regions, normal particle clearance mechanisms and rates in both regions, clearance rates<br />

7 during lung overload, elution of organics from the particles, particle transport to extraalveolar<br />

8 sites, and the interrelationships of these factors in determining the target organ dose.<br />

9<br />

10 4.2. REGIONAL DEPOSITION OF INHALED PARTICLES<br />

11 The regional deposition of particulate matter in the respiratory tract is dependent on the<br />

12 interaction of a number of factors, including respiratory tract anatomy (airway dimensions and<br />

13 branching configurations), ventilatory characteristics (breathing mode and rate, ventilatory<br />

14 volumes and capacities), physical processes (diffusion, sedimentation, impaction, and<br />

15 interception), and the physicochemical characteristics (particle size, shape, and density) of the<br />

16 inhaled particles. Regional deposition of particulate material is usually expressed as deposition<br />

17 fraction of the total particles or mass inhaled and may be represented by the ratio of the particles<br />

18 or mass deposited in a specific region to the number or mass ofparticles inspired. The factors<br />

19 affecting deposition in these various regions and their importance in understanding the fate of<br />

' .<br />

20 inhaled diesel exhaust particulate matter are discussed in the following sections. It is beyond the<br />

21 scope of this document to present a comprehensive account of the complexities of respiratory<br />

22 mechanics, physiology, and toxicology. Where appropriate, the reader is referred to publications<br />

23 that provide a more in-depth treatment of these topics (Weibel, 1963; Brain and Mensah, 1983;<br />

24 Raabe et al., 1988; StOber et al., 1993).<br />

25<br />

26 4.2.1. Physical Processes, Physiological/Anatomical Considerations, and Particle<br />

27 Characteristics<br />

28 Oeposition of particles may occur through several processes or combinations thereof,<br />

29 including diffusion, sedimentation (gravitational settling), interception, electrostatic<br />

30 precipitation, and impaction. It is important to appreciate that these processes are not necessarily<br />

31 independent but may, in some instances, interact with one another. such that total deposition in<br />

32 the respiratory tract resulting from these processes may be less than the calculated probabilities<br />

33 <strong>for</strong> deposition by the individual processes (Raabe, 1982). Depending on the particle size and<br />

34 mass, varying degrees f deposition may occur in the nasopharyngeal, tracheobronchial, and<br />

35 alveolar regions of the respiratory tract.<br />

2/1/98 4-2 DRAFT--DO NOT CITE OR QUOTE

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