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Occupational Exposure to Carbon Nanotubes and Nanofibers

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<strong>and</strong> density. The following MMAD <strong>and</strong> GSD valueswere reported by airborne exposure concentrations:0.54 mg/m 3 (MMAD 1.9 µm; GSD 3.1);2.5 mg/m 3 (MMAD 3.2 µm; GSD 2.1); <strong>and</strong> 25 mg/m 3 (MMAD 3.3 µm; GSD 2.0). The density assumedfor this CNF is 0.08 g/ml. Density was not reportedin DeLorme et al. [2012] <strong>and</strong> was obtained fromthe manufacturer’s data analysis sheet, which indicatesit is the same material as that reported inDeLorme et al. [2012].The default breathing rates <strong>and</strong> parameters wereassumed, <strong>and</strong> inhalability adjustment was selected.In MPPD 2.90, nonspherical particle shape can betaken in<strong>to</strong> account in the respira<strong>to</strong>ry tract depositionestimates, but some of the required input parameters(GSD of structure diameter <strong>and</strong> length<strong>and</strong> correlation) were not reported in DeLormeet al. [2012]. So, the spherical particle assumption(aspect ratio of 1.0) was assumed, which maynot be unreasonable given that the fiber interceptionmechanism may be less for CNF structures oflength 5.8 µm than for longer fibers. The defaultbreathing parameters (including 0.21 ml tidal volume<strong>and</strong> 102 breaths/min) may be reasonable forthe female Sprague Dawley rats in the DeLorme etal. [2012] study based on similar body weight (300g) associated with the default values [Kuempel <strong>and</strong>Castranova 2011], but may be <strong>to</strong>o low for the maleSprague Dawley rats. The average body weights incontrol rats (air-only exposed) at the end of 13-wkexposure period <strong>and</strong> the 90-d post-exposure period,respectively, were: 252 <strong>and</strong> 329 g (females);520 <strong>and</strong> 684 g (males) [DeLorme et al. 2012]. Theretained lung burden at the end of the 13-wk exposurewas also estimated in MPPD 2.90 using theparticle size data for each exposure concentration(using MMAD <strong>and</strong> GSD values reported above).The lung dose estimates in rats <strong>and</strong> mice were normalizedby the lung weight or alveolar surface area <strong>to</strong>estimate the equivalent dose across species. The averagelung weights of rats were those reported in DeLormeet al. [2012] 1-d post-exposure in the control rats(1.9 g <strong>and</strong> 1.3 g in males <strong>and</strong> females, respectively).The average mouse lung weight was 0.15 g [personalcommunication, A. Shvedova <strong>to</strong> E. Kuempel, Aug.2012]. The average alveolar surface area assumed forthe rat lungs was 0.4 m 2 [S<strong>to</strong>ne et al. 1992], <strong>and</strong> that ofmice was 0.055 m 2 [Mercer et al. 2010].The <strong>to</strong>tal deposited CNF dose in the alveolar regionwas estimated in rats in the DeLorme et al. [2012]study in the following equation:Deposited lung dose (mg) =<strong>Exposure</strong> Concentration (mg/m 3 ) × Duration (hr/d × d/wk × wk)× Minute Ventilation (L/min) × 0.001 m 3 /L × 60 min/hr× Alveolar Deposition Fractionwhere the exposure concentrations are 0.54, 2.5,or 25 mg/m 3 ; the duration of exposure is 6 hr/d, 5d/wk, 13 wk; the minute ventilation is 0.21 L/min;<strong>and</strong> the alveolar deposition fractions are reportedin Section A.7.5.A.7.6 Equivalent Lung DoseEstimation ResultsThe inhalable fraction estimates of CNF in rats were0.79, 0.73, <strong>and</strong> 0.72, respectively, in rats at the reportedparticles sizes for concentrations of 0.54 mg/m 3 (MMAD 1.9 µm; GSD 3.1); 2.5 mg/m 3 (MMAD3.2 µm; GSD 2.1); <strong>and</strong> 25 mg/m 3 (MMAD 3.3 µm;GSD 2.0) in DeLorme et al. [2012] (based on MPPDv. 2.90 [ARA 2009] as described in Section A.7.4).The alveolar deposition fraction estimates were0.0715, 0.0608, <strong>and</strong> 0.054, respectively, for the 0.54,2.5, <strong>and</strong> 25 mg/m 3 exposure concentrations.The normalized dose estimates in mice <strong>and</strong> rats(as CNF mass per alveolar surface area or mass oflungs) <strong>and</strong> associated lung responses are shown inTables A–15 <strong>and</strong> A–16. In mice, these lung dose estimatesare similar <strong>to</strong> or higher than the depositedlung dose estimate in the rat at the LOAEL (2.5 mg/m 3 ), but less than the deposited lung doses estimatedin rats at the highest concentration (25 mg/m 3 )(Tables A–15 <strong>and</strong> A–16). The mouse deposited lungburden estimates are higher than the rat retainedlung burden estimates at all doses, assuming spherical-particlemodel clearance in MPPD 2.90 [ARA2009]. If CNF is cleared in a similar manner as thatreported for MWCNT in Pauluhn [2010b], the actualretained lung dose in rats may be intermediateNIOSH CIB 65 • <strong>Carbon</strong> <strong>Nanotubes</strong> <strong>and</strong> <strong>Nanofibers</strong>141

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