nificant only in the rats exposed <strong>to</strong> 25 mg/m 3 CNF.However, the percent PMNs increased in a doseresponsivemanner: 1.2 (± 0.81), 1.4 (± 0.79), 2.7 (±0.67), <strong>and</strong> 11 (± 2.0), respectively, in the 0, 0.54, 2.5,<strong>and</strong> 25 mg/m 3 exposure groups. LDH <strong>and</strong> otherBALF markers were elevated at the end of the 13-wk exposure only in the 25 mg/m 3 exposure group,<strong>and</strong> LDH remained elevated at 3-mo. post-exposurein that group. The observed no adverse effect level(NOAEL) in rats was reported <strong>to</strong> be 0.54 mg/m 3 . Thelowest observed adverse effect level (LOAEL) wasreported <strong>to</strong> be 2.5 mg/m 3 “…based on the minimalinflammation observed in terminal bronchioles<strong>and</strong> alveolar ducts of male <strong>and</strong> female rats…” [De-Lorme et al. 2012].The sample size <strong>and</strong> sensitivity of the markers orassays are fac<strong>to</strong>rs that could influence the statisticalpower <strong>and</strong> likelihood of observing exposurerelatedeffects in these animal studies. In Murrayet al. [2012], six animals per group were used forthe BAL analysis, his<strong>to</strong>pathology evaluation, oxidativestress markers, <strong>and</strong> lung collagen measurements.Five animals per group were used for theBAL <strong>and</strong> cell proliferation assays in the DeLormeet al. [2012] study (male <strong>and</strong> female data were analyzedseparately). The Murray et al. [2012] studyused a more sensitive marker of interstitial fibrosisin measuring the average thickness of the alveolarconnective tissue, while the DeLorme et al. [2012]study did not report using that assay.A.7.4 Effects in Other TissuesIn rats, CNF were observed in the nasal turbinatesof the high-dose group (25 mg/m 3 ) at 1 daypost-exposure, which was accompanied by hyalinedroplet formation in the epithelium; CNF persistedin the nasal turbinates at 3-mo. post-exposurein the high dose group [DeLorme et al. 2012]. Inall exposure groups, CNF translocated <strong>to</strong> the tracheobronchiallymph nodes <strong>and</strong> CNF fibers wereseen in brain, heart, liver, kidney, spleen, intestinaltract, kidneys, <strong>and</strong> mediastinal lymph nodes, butno associated his<strong>to</strong>pathologic abnormalities weredetected [DeLorme et al. 2012]. In CNF-exposedmice, T cell mi<strong>to</strong>gen (concavalin A) responsivenessindicated decrease T cell responses in the spleen at28 days post-exposure [Murray et al. 2012].A.7.5 Equivalent Lung DoseEstimation MethodsIn order <strong>to</strong> quantitatively compare the results of thetwo CNF studies in mice <strong>and</strong> rats, equivalent lungdoses were estimated by accounting for differencesin route of exposure <strong>and</strong> particle size characteristics<strong>and</strong> by normalizing <strong>to</strong> either the mass or alveolarsurface area of the lungs in each species. Therespira<strong>to</strong>ry tract region where the adverse effectswere observed is the pulmonary (a.k.a. alveolar) region,which is where gas exchange occurs betweenthe lungs <strong>and</strong> blood circula<strong>to</strong>ry system across thealveolar septal walls. In mice, the lung dose estimateis simply the proportion of the administereddose (by pharyngeal aspiration) [Murray et al.2012] that is estimated <strong>to</strong> deposit in the alveolar region.Mercer et al. [2010] reported that 81% of theaspirated MWCNT by pharyngeal aspiration depositedin the alveolar region of the mouse. If thisfigure applies <strong>to</strong> the CNF reported in Murray et al.[2012], then approximately 97 µg of the 120 µg administereddose would be deposited in the alveolarregion. In the absence of CNF-specific data, 100%alveolar deposition of the administered dose wasalso assumed.In rats, the airborne particle size data are used <strong>to</strong>estimate the inhalable, deposited, <strong>and</strong> retainedlung doses of CNT, based on the exposure concentrations<strong>and</strong> particle size characteristics reported[DeLorme et al. 2012]. The multipath particle depositionmodel (MPPD), version 2.90 [ARA 2009],was used <strong>to</strong> estimate these lung doses. MPPD version2.11 was originally used <strong>to</strong> obtain some particledeposition estimates, but some output indicatederrors in estimating the tracheobronchial regionaldeposited dose, which appeared <strong>to</strong> lower the alveolardeposition estimates. This issue was apparentlyresolved in the updated version (2.90).Particle characteristic input values used in MPPDinclude the mass median aerodynamic diameter(MMAD), geometric st<strong>and</strong>ard deviation (GSD),140 NIOSH CIB 65 • <strong>Carbon</strong> <strong>Nanotubes</strong> <strong>and</strong> <strong>Nanofibers</strong>
<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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CURRENT INTELLIGENCE BULLETIN 65Occ
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Current Intelligence Bulletin 65Occ
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ForewordThe Occupational Safety and
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Executive SummaryOverviewCarbon nan
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2009; Pauluhn 2010a; Porter et al.
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neurogenic sig nals from sensory ir
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possible. Until the results from an
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••Follow exposure and hazard as
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Periodic Evaluations••Evaluatio
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ContentsForeword ..................
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A.3.2 Comparison of Short-term and
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ESPFeFMPSFPSSgGMGSDHCLHECHEPAhrISOI
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AcknowledgementsThis Current Intell
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1 IntroductionMany nanomaterial-bas
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2 Potential for ExposureThe novel a
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CNMs, with MWCNT agglomerates obser
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composite materials with local exha
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information on air contaminants. Sa
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3 Evidence for Potential Adverse He
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decreasing agglomerate size increas
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examined up to 60 days post-exposur
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3.3 SWCNT and MWCNTIntraperitoneal
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The same potency sequence was obser
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Table 3-3. Findings from published
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Table 3-5. Findings from published
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Table 3-6. Findings from published
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Table 3-7 (Continued). Findings fro
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Table 3-8. Findings from published
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length, respectively) [Muller et al
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5 CNT Risk Assessment and Recommend
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A-6). Risk estimates derived from o
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Table 5-4. Factors, assumptions, an
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and analytical methods. NIOSH is re
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Table 5-5. Recommended occupational
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deficits in animals or clinically s
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(3) Rat lung dose estimationIn the
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tasks where worker exposures exceed
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As part of the evaluation of worker
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Table 6-1. EC LODs and LOQs for 25-
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6.2 Engineering ControlsOne of the
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Table 6-6 (Continued). Examples of
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Table 6-7 (Continued). Engineering
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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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- Page 149 and 150: cell surface area). However, the wo
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