<strong>and</strong> oxidative degradation of the tubes occurred[Liu et al. 2010]. Kagan et al. [2010] reported thatin vitro myeloperoxidase, which is found in highconcentrations in polymorphonuclear neutrophils(PMN), degraded SWCNT. However, it is uncertainas <strong>to</strong> whether PMN-derived myeloperoxidasewould degrade SWCNT in vivo (e.g., in the lung)because of the following: (1) PMN recruitment afterSWCNT exposure is a transient rather than persistentresponse, (2) there is no strong evidence forSWCNT phagocy<strong>to</strong>sis by PMN, <strong>and</strong> (3) SWCNT<strong>and</strong> MWCNT are found in the lungs of micemonths after pharyngeal aspiration [Shvedova etal. 2005; Mercer et al. 2008; Porter et al. 2010].Several animal studies have shown that the size(e.g., length) of MWCNT <strong>and</strong> SWCNT may have aneffect on their biological activity [Takagi et al. 2008;Pol<strong>and</strong> et al. 2008; Muller et al. 2009]. Intraperi<strong>to</strong>nealinjection of mice with long MWCNT (20 µm length),but not short MWCNT (< 5 µm length), caused granuloma<strong>to</strong>uslesions on the diaphragm in a 2-weekpost-exposure study [Pol<strong>and</strong> et al. 2008]. Fibroticperi<strong>to</strong>neal adhesions <strong>and</strong> mesothelioma were alsoobserved after exposure <strong>to</strong> MWCNT in which approximately28% of the tubes were > 5 µm in length[Takagi et al. 2008]. However, when rats were exposed<strong>to</strong> short MWCNT (< 1 µm length) by intraperi<strong>to</strong>nealinjection, only acute inflammation wasobserved, with no evidence of mesothelioma overthe 2 year post-exposure period [Muller et al. 2009].Nagai et al. [2011] provided evidence that the carcinogenicpotential of MWCNT may be related <strong>to</strong>the fiber-like properties <strong>and</strong> dimensions. Fischer344/Brown Norway (male <strong>and</strong> female, 6 wk old)were injected with doses of 1 or 10 mg of one offive types of MWCNT with different dimensions<strong>and</strong> rigidity. The thin diameter MWCNT (~50nm) with high crystallinity caused inflammation<strong>and</strong> mesothelioma, whereas thick (~150 nm) ortangled structures (~2–20 nm) were less cy<strong>to</strong><strong>to</strong>xic,inflammogenic, or carcinogenic. A specific mutation<strong>to</strong> tumor suppressor genes (Cdkn2a/2b) wasobserved in the mesotheliomas, which is similar<strong>to</strong> that observed in asbes<strong>to</strong>s-associated mesotheliomasinduced by asbes<strong>to</strong>s. In vitro studies withmesothelial cells showed that the thin MWCNTpierced cell membranes <strong>and</strong> caused cy<strong>to</strong><strong>to</strong>xicity.Numerous studies have investigated the geno<strong>to</strong>xicproperties of CNT with results from in vitro assaysindicating that exposure <strong>to</strong> SWCNT <strong>and</strong> MWCNTcan induce DNA damage, micronuclei formation,disruption of the mi<strong>to</strong>tic spindle, <strong>and</strong> induction ofpolyploidy [Li et al. 2005; Kisin et al. 2007; Muller etal. 2008a; Pacurari et al. 2008; Lindberg et al. 2009;Sargent et al. 2009; Asakura et al. 2010]. Other invitro studies of some MWCNT did not show evidenceof geno<strong>to</strong>xicity [Wirnitzer et al. 2009; Kim etal. 2011]. The presence of residual metal catalystswas also found <strong>to</strong> promote the generation of reactiveoxygen species (ROS), thereby enhancing thepotential for DNA damage [Pulskamp et al. 2007;Barillet et al. 2010]. The results from in vitro studieswith CNF have also shown that exposure can causegeno<strong>to</strong>xicity [Magrez et al. 2006; Lindberg et al.2009; Kisin et al. 2011] including aneugenic as wellas clas<strong>to</strong>genic events. In addition, low-dose, longtermexposure of bronchial epithelial cells <strong>to</strong> SW-CNT or MWCNT has been reported <strong>to</strong> transformthese cells <strong>to</strong> exhibit unregulated proliferation, lossof contact inhibition of division, enhanced migration<strong>and</strong> invasion, <strong>and</strong> growth in solf agar [Stueckleet al. 20011]. When SWCNT-transformed epithelialcells were subcutaneously injected in<strong>to</strong> thehind flanks of immunodeficient nude mice, smalltumors were observed at one week post-injection.His<strong>to</strong>logical evaluation of tumors showed classiccancer cell morphology, including the presence ofmultinucleated cells, an indica<strong>to</strong>r of mi<strong>to</strong>tic dysfunction[Wang et al. 2011].When CNT <strong>and</strong> CNF are suspended in test media,agglomerates of various sizes frequently occur. Thisis particularly evident in test media used in recentstudies where animals have been exposed <strong>to</strong> CNTsuspensions by intratracheal instillation, intraperi<strong>to</strong>nealinjection, or by pharyngeal aspiration (a techniquewhere particle deposition closely resemblesinhalation). The agglomerate size for CNT <strong>and</strong> CNFis normally smaller in a dry aerosol than when suspendedin physiological media. Evidence from <strong>to</strong>xicitystudies in labora<strong>to</strong>ry animals indicates that14 NIOSH CIB 65 • <strong>Carbon</strong> <strong>Nanotubes</strong> <strong>and</strong> <strong>Nanofibers</strong>
decreasing agglomerate size increases the pulmonaryresponse <strong>to</strong> exposure [Shvedova et al. 2007,2008; Mercer et al. 2008]. The extent <strong>to</strong> which agglomeratesof CNT <strong>and</strong> CNF de-agglomerate inbiological systems (e.g., in the lung) is unknown.However, a diluted alveolar lining fluid has beenshown <strong>to</strong> substantially improve dispersion of CNTin physiological saline [Porter et al. 2008; Wang etal. 2010a].3.1 Single-Walled <strong>Carbon</strong><strong>Nanotubes</strong> (SWCNT)Mice or rats exposed <strong>to</strong> SWCNT by IT or pharyngealaspiration have developed granuloma<strong>to</strong>us lesionsat sites in the lung where agglomerates of SWCNTdeposited [Lam et al. 2004; Warheit et al. 2004]. Inaddition, interstitial fibrosis has also been reported[Shvedova et al. 2005; Mangum et al. 2006]. Thisfibrotic response was associated with the migrationof smaller SWCNT structures in<strong>to</strong> the interstitiumof alveolar septa [Mercer et al. 2008].3.1.1 IT StudiesLam et al. [2004] investigated the <strong>to</strong>xicity of SW-CNT obtained from three different sources, eachwith different amounts of residual catalytic metalsbeing present. Mice were exposed by IT <strong>to</strong> threedifferent types of SWCNT (containing either 27%Fe, 2% Fe, or 26% Ni <strong>and</strong> 5% Y) at concentrationsof 0.1 or 0.5 mg <strong>and</strong> <strong>to</strong> carbon black (0.5 mg) or<strong>to</strong> quartz (0.5 mg). The mice were <strong>to</strong>xicologicallyassessed 7 or 90 days post exposure. All types ofSWCNT studied produced persistent epithelioidgranulomas (which were associated with particleagglomerates) <strong>and</strong> interstitial inflammation thatwere dose-related. No granulomas were observedin mice exposed <strong>to</strong> carbon black, <strong>and</strong> only mild <strong>to</strong>moderate inflammation of the lungs was observedin the quartz exposure group. High mortality (5/9mice) occurred within 4 <strong>to</strong> 7 days in mice instilledwith the 0.5 mg dose of SWCNT containing nickel<strong>and</strong> yttrium.Warheit et al. [2004] exposed rats via IT <strong>to</strong> concentrationsof 1 or 5 mg/kg SWCNT, quartz, carbonyliron, or graphite particles, <strong>and</strong> evaluated effectsat 24-hr, 1-week, 1-month, <strong>and</strong> 3-months post exposure.The SWCNT were reported <strong>to</strong> have nominaldiameters of 1.4 nm <strong>and</strong> lengths > 1 µm, whichtended <strong>to</strong> agglomerate in<strong>to</strong> micrometer size structures.In this study, ~15% of the SWCNT-instilledrats died within 24 hours of SWCNT exposure, apparentlydue <strong>to</strong> SWCNT blockage of the upper airways.In the remaining rats, a transient inflamma<strong>to</strong>ryresponse of the lung (observed up <strong>to</strong> 1-monthpost exposure) <strong>and</strong> non-dose dependent multifocalgranulomas that were non-uniform in distributionwere observed. Only rats exposed <strong>to</strong> quartz developeda dose-dependent lung inflamma<strong>to</strong>ry responsethat persisted through 3 months. <strong>Exposure</strong>s<strong>to</strong> carbonyl iron or graphite particles produced nosignificant adverse effects.3.1.2 Pharyngeal Aspiration StudiesProgressive interstitial fibrosis of alveolar wallshas also been reported in mice when exposed viapharyngeal aspiration <strong>to</strong> purified SWCNT at dosesof 10, 20, 40 µg/mouse [Shvedova et al. 2005]. Aswith studies by Lam et al. [2004] <strong>and</strong> Warheit etal. [2004], epithelioid granulomas were associatedwith the deposition of SWCNT agglomerates inthe terminal bronchioles <strong>and</strong> proximal alveoli. Thisgranuloma formation was rapid (within 7 days),dose-dependent, <strong>and</strong> it persisted over the 60-daypost exposure period. A rapid, dose-dependent,<strong>and</strong> progressive development of interstitial fibrosisin pulmonary regions distant from depositionsites of SWCNT agglomerates was observed, <strong>and</strong> itappeared <strong>to</strong> be associated with deposition of moredispersed SWCNT structures. At equivalent masslung burdens, nano-sized carbon black failed <strong>to</strong>cause any significant pulmonary responses. Thesefindings were consistent with those reported byMangum et al. [2006], in which rats exposed <strong>to</strong>2 mg/kg via pharyngeal aspiration developed granulomasat sites of SWCNT agglomerates <strong>and</strong> diffuseinterstitial fibrosis at 21 days post exposure.Also noted was the formation of CNT structuresNIOSH CIB 65 • <strong>Carbon</strong> <strong>Nanotubes</strong> <strong>and</strong> <strong>Nanofibers</strong>15
- Page 1 and 2: CURRENT INTELLIGENCE BULLETIN 65Occ
- Page 3 and 4: Current Intelligence Bulletin 65Occ
- Page 5 and 6: ForewordThe Occupational Safety and
- Page 7 and 8: Executive SummaryOverviewCarbon nan
- Page 9 and 10: 2009; Pauluhn 2010a; Porter et al.
- Page 11 and 12: neurogenic sig nals from sensory ir
- Page 13 and 14: possible. Until the results from an
- Page 15 and 16: ••Follow exposure and hazard as
- Page 17 and 18: Periodic Evaluations••Evaluatio
- Page 19 and 20: ContentsForeword ..................
- Page 21 and 22: A.3.2 Comparison of Short-term and
- Page 23 and 24: ESPFeFMPSFPSSgGMGSDHCLHECHEPAhrISOI
- Page 25 and 26: AcknowledgementsThis Current Intell
- Page 27 and 28: 1 IntroductionMany nanomaterial-bas
- Page 29: 2 Potential for ExposureThe novel a
- Page 32 and 33: CNMs, with MWCNT agglomerates obser
- Page 34 and 35: composite materials with local exha
- Page 36 and 37: information on air contaminants. Sa
- Page 39: 3 Evidence for Potential Adverse He
- Page 43 and 44: examined up to 60 days post-exposur
- Page 45 and 46: 3.3 SWCNT and MWCNTIntraperitoneal
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- Page 49 and 50: Table 3-3. Findings from published
- Page 51 and 52: Table 3-5. Findings from published
- Page 53 and 54: Table 3-6. Findings from published
- Page 55 and 56: Table 3-7 (Continued). Findings fro
- Page 57: Table 3-8. Findings from published
- Page 60 and 61: length, respectively) [Muller et al
- Page 63 and 64: 5 CNT Risk Assessment and Recommend
- Page 65 and 66: A-6). Risk estimates derived from o
- Page 67 and 68: Table 5-4. Factors, assumptions, an
- Page 69 and 70: and analytical methods. NIOSH is re
- Page 71 and 72: Table 5-5. Recommended occupational
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exposure estimates for SWCNT on ind
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Table 6-8. Respiratory protection f
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••Workers in areas or in jobs w
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7 Research NeedsAdditional data and
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ReferencesACGIH [1984]. Particle si
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Bolton RE, Vincent HJ, Jones AD, Ad
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eport issued on July 22, 2011. NEDO
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Kobayashi N, Naya M, Mizuno K, Yama
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Methner M, Hodson L, Geraci C [2010
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Human Services, Centers for Disease
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Piegorsch WW, Bailer AF [2005]. Qua
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AD, Baron PA [2003]. Exposure to ca
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Varga C, Szendi K [2010]. Carbon na
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ContentsA.1 Introduction ..........
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A.1 IntroductionThe increasing prod
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provide an informal check on the es
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these same dose groups; this effect
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Table A-1. Rodent study information
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the deposited (no clearance) and th
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The other BMDS models failed to con
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Figure A-2. Benchmark dose model (m
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Figure A-3 (continued). Benchmark d
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Table A-3. Benchmark dose estimates
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Table A-5. Benchmark dose estimates
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histopathology grade 2 or higher lu
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Table A-8. Working lifetime percent
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developing early-stage adverse lung
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Figure A-4. Dose-response relations
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cell surface area). However, the wo
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purified or unpurified (with differ
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Table A-9. Comparison of rat or hum
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A.6.1.3 Pulmonary Ventilation RateT
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used as the effect levels in evalua
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the DF estimate, although a larger
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or overloading, of particle clearan
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Table A-13. Human-equivalent retain
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A.7.1 Particle CharacteristicsBoth
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and density. The following MMAD and
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Table A-15. CNT lung dose normalize
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B.1 Key Terms Related toMedical Sur
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APPENDIX CNIOSH Method 5040
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filter. In the method evaluation, d
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Most of the studies on sampling art
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e analyzed to determine the onset o
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Delivering on the Nation’s promis