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Occupational Exposure to Carbon Nanotubes and Nanofibers

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egion of the lung 1 day post exposure, with subpleuralfibrosis occurring at 2 weeks post exposurethat progressed through 6 weeks of follow-up. Nofibrosis was observed in mice exposed <strong>to</strong> 1 mg/m 3 ofMWCNT or in mice exposed <strong>to</strong> 30 mg/m 3 of nanoscalecarbon black.Subchronic inhalation studies with MWCNT havealso been conducted in labora<strong>to</strong>ry studies withrats <strong>to</strong> assess the potential dose-response <strong>and</strong> timecourse for developing pulmonary effects [Arkema2008; Ma-Hock et al. 2009; Pauluhn 2010a]. Ma-Hock et al. [2009] reported on the results of a 90-day inhalation (head-nose) study with rats exposedat concentrations of 0.1, 0.5, or 2.5 mg/m 3 MWCNT(BASF Nanocyl NC 7000) for 6 hr/day, 5 days/weekfor 13 weeks with a resultant lung burden of 47–1170 µg/rat. No systemic <strong>to</strong>xicity was observed,but the exposure caused hyperplastic responsesin the nasal cavity <strong>and</strong> upper airways (larynx <strong>and</strong>trachea), <strong>and</strong> granuloma<strong>to</strong>us inflammation in thelung <strong>and</strong> in lung-associated lymph nodes at all exposureconcentrations. The incidence <strong>and</strong> severityof the effects were concentration-related. No lungfibrosis was observed but pronounced alveolar lipoproteinosisdid occur.Ellinger-Ziegelbauer <strong>and</strong> Pauluhn [2009] conducteda short-term inhalation bioassay (beforethe Pauluhn 2010a subchronic study) <strong>to</strong> investigatethe dependence of pulmonary inflammationresulting from exposure <strong>to</strong> one type of MWCNT(Bayer Baytubes®), which was highly agglomerated<strong>and</strong> contained a small amount of cobalt (residualcatalyst). Groups of rats were exposed <strong>to</strong> 11 mg/m 3MWCNT containing either 0.53% or 0.12% cobalt<strong>to</strong> assess differences in pulmonary <strong>to</strong>xicity becauseof metal contamination. Another group of rats wasexposed <strong>to</strong> 241 mg/m 3 MWCNT (0.53% cobalt)<strong>to</strong> serve the purpose of hazard identification. Allanimals were exposed <strong>to</strong> a single nose-only inhalationexposure of 6 hr followed by a post-exposureperiod of 3 months. Time course of MWCNTrelatedpulmonary <strong>to</strong>xicity was compared with ratsexposed <strong>to</strong> quartz in post-exposure weeks 1, 4, <strong>and</strong>13 <strong>to</strong> distinguish early, possibly surface area/activityrelatedeffects from retention-related poorly solubleparticle effects. Rats exposed <strong>to</strong> either quartz orMWCNT resulted in somewhat similar patternsof concentration-dependent pulmonary inflammationduring the early phase of the study. Thepulmonary inflammation induced by quartz increasedduring the 3 months post-exposure period,whereas that induced by MWCNT regressed ina concentration-dependent manner. The time courseof pulmonary inflammation associated with retainedMWCNT was independent on the concentrationof residual cobalt. Pauluhn [2010a], using the sameMWCNT (0.53% cobalt) used in the study byEllinger-Ziegelbauer <strong>and</strong> Pauluhn [2009] exposedrats (nose-only) at concentrations 0.1, 0.4, 1.5, <strong>and</strong>6 mg/m 3 for 6 hr/day, 5 days/week for 13 weeks. Theaerosolized MWCNT were described as being highlyagglomerated (mean diameter of 3 µm). Lungclearance of MWCNT at the low doses was slow,with a marked inhibition of clearance at 1.5 <strong>and</strong>6 mg/m 3 . His<strong>to</strong>pathology analysis at 6 months postexposure revealed exposure-related lesions in theupper respira<strong>to</strong>ry (e.g., goblet cell hypermetaplasia<strong>and</strong>/or metaplasia) <strong>and</strong> lower respira<strong>to</strong>ry (e.g., inflammationin the bronchiole-alveolar region) tractin animals exposed at concentrations of 0.4, 1.5, <strong>and</strong>6 mg/m 3 , as well as inflamma<strong>to</strong>ry changes in thedistal nasal cavities that were similar <strong>to</strong> those foundby Ma-Hock et al. [2009]. In rats exposed at 6 mg/m 3 , a time-dependent increase of bronchioloalveolarhyperplasia was observed, as well as changes ingranulomas <strong>and</strong> an increase in collagen depositionthat persisted through the 39-week post-exposureobservation period. No treatment-related effectswere reported for rats exposed at 0.1 mg/m 3 .In a report submitted by Arkema [2008] <strong>to</strong> EPA, ratsexposed (nose only) <strong>to</strong> agglomerates of MWCNT(Arkema) at concentrations of 0.1, 0.5, <strong>and</strong> 2.5 mg/m 3 for 6 hr/day for 5 days exhibited his<strong>to</strong>pathologicaleffects that were consistent with those reportedby Ma-Hock et al. [2009], Ellinger-Ziegelbauer <strong>and</strong>Pauluhn [2009] <strong>and</strong> Pauluhn [2010a]. An increase ofvarious cy<strong>to</strong>kines <strong>and</strong> chemokines in the lung, alongwith the development of granulomas were found inthe 0.5 <strong>and</strong> 2.5 mg/m 3 exposure groups, while notreatment-related effects were reported at 0.1 mg/m 3 .18 NIOSH CIB 65 • <strong>Carbon</strong> <strong>Nanotubes</strong> <strong>and</strong> <strong>Nanofibers</strong>

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