Occupational Exposure to Carbon Nanotubes and Nanofibers
Occupational Exposure to Carbon Nanotubes and Nanofibers
Occupational Exposure to Carbon Nanotubes and Nanofibers
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the DF estimate, although a larger difference (approximatelya fac<strong>to</strong>r of two) is due <strong>to</strong> differences inthe spherical particle model-based estimates (e.g.,MPPD 2.0 vs. 2.1) (Sections A.2.2; A.6.1.1; <strong>and</strong>A.6.1.2).The values used by NIOSH [2010] <strong>and</strong> Pauluhn[2010b] are similar for the VE <strong>and</strong> DF, i.e., for human<strong>and</strong> rat, respectively:••VE (m3/d): 10 <strong>and</strong> 0.015 [Pauluhn 2010b],9.6 <strong>and</strong> 0.09 [NIOSH 2010]; <strong>and</strong>••DF: 0.118 <strong>and</strong> 0.057 [Pauluhn 2010b],0.086 <strong>and</strong> 0.046 [NIOSH 2010].The other two fac<strong>to</strong>rs—retention half-time (RT)<strong>and</strong> interspecies normalization fac<strong>to</strong>r (NF)—c<strong>and</strong>iffer largely depending on the assumed mode ofaction concerning how the deposited CNT interactswith the lung tissue over time. These fac<strong>to</strong>rsare discussed below.A.6.3.2.1 Interspecies dosenormalization fac<strong>to</strong>rThe interspecies NF adjusts for the size differencein the lung (surface area or volume) in<strong>to</strong> which theCNT dose deposits. Studies of other inhaled particlesor fibers are relevant <strong>to</strong> evaluating mechanismsthat may also apply <strong>to</strong> CNT in the lungs. Possibledose metrics related <strong>to</strong> the modes of action forpulmonary inflammation <strong>and</strong> fibrosis include theCNT mass, surface area, or volume dose per alveolarepithelial cell surface area or alveolar macrophagecell volume in each species. Normalizingthe dose (e.g., NOAEL) across species <strong>to</strong> the <strong>to</strong>talaverage alveolar macrophage cell volume in rat orhuman lungs is based on the experimental observationof overloading of alveolar clearance in rats <strong>and</strong>mice exposed <strong>to</strong> respirable poorly soluble particlesor fibers [Bol<strong>to</strong>n et al. 1983; Morrow 1988; Bellmannet al. 1991; Elder et al. 2005; Pauluhn 2010b].(a) Alveolar macrophage cell volumeAt a sufficiently high particle dose, pulmonaryclearance can become impaired due <strong>to</strong> overloadingof alveolar macrophage-mediated clearance. In rats,the overloading dose has been observed as particlemass (~1 mg/g lung), volume (~1 µl/g lung forunit density particles) [Morrow 1988; Muhle et al.1990], or surface area (200–300 cm2 particles perrat lung) [Tran et al. 2000]. On a volume basis, anoverloading particle dose corresponds <strong>to</strong> approximately6%–60% of <strong>to</strong>tal alveolar cell volume, whenoverloading begins <strong>and</strong> is complete, respectively[Morrow 1988]. The 60% value has been observedexperimentally [Oberdörster et al. 1992], althoughparticle clearance impairment may start at lowerparticle volume lung dose [Bellmann et al. 1991;Kuempel et al. 2001a]. Biological responses <strong>to</strong> overloadinginclude: accumulation of particle-filledmacrophages in the alveoli, increased permeabilityof the epithelial cell barrier, persistent inflammation,increased particle translocation <strong>to</strong> the alveolarinterstitium <strong>and</strong> lung-associated lymph nodes,as well as increasing alveolar septal thickening, lipoproteinosis,impaired lung function, <strong>and</strong> fibrosis[Muhle et al. 1990, 1991].Although the overload mode of action in the rat hasbeen well-studied, the extent <strong>to</strong> which overloadingis involved in human lung responses <strong>to</strong> inhaledparticles is not as clear due <strong>to</strong> observed differencesin both the kinetics <strong>and</strong> the pattern of particle retentionin the lungs of rats <strong>and</strong> humans. Whereasparticle clearance in rats is first-order at doses belowoverloading, studies in workers have shownthat human lung clearance of respirable particles isnot first-order even at relatively low retained particlemass lung low doses [Kuempel 2000; Kuempelet al. 2001; Tran <strong>and</strong> Buchanan 2000; Gregorat<strong>to</strong>et al. 2010, 2011]. That is, some portion of the particledose that deposits in the pulmonary region isretained for a very long time (retention half-timeof several years) [ICRP 1994; Kuempel et al. 2001;Gregarat<strong>to</strong> et al. 2010]. Humans also apparently retaina greater portion of the particles in the alveolarinterstitium, whereas rats retain more particles inthe alveolar space [Nikula et al. 1997, 2001]. Thegreater interstitial particle retention may increasethe dose <strong>to</strong> the target tissue for pulmonary fibrosisin humans relative <strong>to</strong> that for the same depositeddose in rats lungs. Given the differences in theparticle clearance kinetics <strong>and</strong> retention patternsin rats <strong>and</strong> humans, normalizing the dose acrossNIOSH CIB 65 • <strong>Carbon</strong> <strong>Nanotubes</strong> <strong>and</strong> <strong>Nanofibers</strong>133