As part of the evaluation of worker exposures <strong>to</strong>CNT <strong>and</strong> CNF, ‘background’ samples for EC determinationshould be collected outdoors (or atair intakes of the facility) <strong>and</strong> at indoor locationswhere exposure <strong>to</strong> CNT or CNF is unlikely. The ECconcentrations (using Method 5040) determinedfrom ‘background’ samples should be subtractedfrom the EC personal sample results <strong>to</strong> determinewhether worker exposures exceeded the REL. Initially,more samples may be required <strong>to</strong> characterizethe workplace thoroughly. This initial assessmentwill help refine the sampling approach <strong>and</strong> determinewhether EC interference is an issue. Carefulconsideration of environmental background is essential.For example, outdoor EC may sometimesbe higher than indoor background depending onthe facility’s air h<strong>and</strong>ling system. If so, the indoorEC background may be more representative of area<strong>and</strong> worker samples.In workplaces where exposure <strong>to</strong> other types of EC(e.g., diesel soot, carbon black) may occur, the initialevaluation of a worker’s exposure should includethe simultaneous collection of a personal respirableEC sample <strong>and</strong> a personal sample for electron microscopyanalysis (e.g., TEM, SEM). Electron microscopyanalysis, in conjunction with energy dispersivex-ray spectroscopy (EDS), can be used forCNT <strong>and</strong> CNF identification. In addition, considerationshould be given <strong>to</strong> the sizing <strong>and</strong> counting ofCNT <strong>and</strong> CNF structures during electron microscopyanalysis should future efforts <strong>to</strong> control occupationalexposures be based on a different exposuremetric (e.g., number concentrations of airborneCNT <strong>and</strong> CNF structures in a given size bin). Whileno specific electron microscopy (e.g., TEM, SEM)method exists for the sizing <strong>and</strong> counting of CNT<strong>and</strong> CNF structures, methods used in the analysisof other ‘fibrous’ materials are available [NIOSH1994a; ISO 1999, 2002] <strong>and</strong> could be adapted in thecharacterization of exposures.NIOSH investiga<strong>to</strong>rs have conducted a numberof surveys at CNT <strong>and</strong> CNF producers <strong>and</strong>/orsecondary users [Evans et al. 2010; Birch 2011a;Birch et al. 2011b; Dahm et al. 2011]. In manycases ‘background’ EC concentrations were
inductively coupled plasma a<strong>to</strong>mic emission spectroscopy(ICP-AES) may not be adequate at lowCNT/CNF concentrations [Birch et al. 2011b]. Inductivelycoupled plasma mass spectrometry (ICP-MS) offers detection limits superior <strong>to</strong> ICP-AES<strong>and</strong> may be useful, depending on the amount ofCNT/CNF collected, metal <strong>and</strong> percent metal content,<strong>and</strong> whether other aerosol sources are presentthat would interfere with analysis. However, if ametal is employed as a surrogate measure of CNT/CNF, minimal background interference <strong>and</strong> correlationwith CNT/CNF mass (or other relevant metric)would be required [Birch et al. 2011b]. Iron wasnot a useful indica<strong>to</strong>r of CNF exposure in a studyreported by Birch et al. [2011b]. There was no correlationbetween the iron <strong>and</strong> CNF concentrationsfound in a CNF manufacturing facility, because themajor iron source was not CNF-derived. In addition,the LOD for ICP-AES was not adequate for itsdetermination at low EC concentrations (e.g., nearthe EC LOQ).6.1.3 Method 5040 Limi<strong>to</strong>f DetectionAs with all analytical methods, the LOD is a varyingnumber. However, the airborne EC LOD originallyreported for NIOSH Method 5040 (i.e., about2 µg/m 3 ), or an LOQ of 7 µg/m 3 was a high estimate[NIOSH 2010]. The LOD was based on analysis ofpre-cleaned media blanks from different filter lots,during a 6-month period, <strong>and</strong> by different analystsat two different labora<strong>to</strong>ries. Further, variability forthe <strong>to</strong>tal carbon (TC) results was used <strong>to</strong> estimatethe LOD rather than EC results. These combinedfac<strong>to</strong>rs gave a conservative (high) estimate of theEC LOD.In practice, a much lower EC LOD is obtained byNIOSH Method 5040 than was originally reported,because the variability for EC results for a set ofmedia blanks submitted (with the sample set) forthe LOD (LOQ) determination is much lower thanreported for the <strong>to</strong>tal carbon (TC) results. Thus,if EC is of primary interest, as with CNT/CNFmeasurement, <strong>and</strong> the level of organic carbon(OC) contamination is acceptable (with respect <strong>to</strong>the OC <strong>and</strong> TC LOD), EC results for as-receivedfilters should be used <strong>to</strong> determine the EC LOD(Appendix C).Estimates of the EC LODs <strong>and</strong> LOQs (in units µgEC/cm 2 of air) determined with 25-mm <strong>and</strong> 37-mmquartz filter media from a given lot, <strong>and</strong> withmanual splits assigned are reported in Table 6–1.OC-EC splits for the media blanks were assigned atthe point when oxygen is introduced so the baselinesignal is integrated over the region in whichEC is removed (oxidized) from the filter.Because there are many possible OC sources, <strong>and</strong>bulk CNT/CNF contain little OC, EC is a betterindica<strong>to</strong>r of exposure than TC. Nevertheless, highparticulate OC concentrations indicate air contamination,<strong>and</strong> these data can be useful for general industrialhygiene purposes if care is taken <strong>to</strong> correctfor OC media contamination (Appendix C). UnlikeEC, OC contamination (e.g., through contactwith a contaminated surface <strong>and</strong>/or vapor adsorption)of the quartz filter media is common. Consequently,the OC (<strong>and</strong> TC) LOD is higher than forEC, <strong>and</strong> the OC (<strong>and</strong> TC) results may have significantpositive bias. Bias is especially apparent whenthe particulate OC air concentrations <strong>and</strong> sampledair volumes are low. To obtain a more accurateestimate of the particulate OC air concentration,an OC blank correction should be applied. Blankcorrection can be accomplished by subtracting theOC media blank or (preferably) by a t<strong>and</strong>em filtercorrection (organic carbon sampling artifacts sectionin Appendix C), with the latter generally beingmore accurate. Mean OC blanks, LODs, <strong>and</strong> LOQsfor 25-mm <strong>and</strong> 37-mm quartz filter media are reportedin Table 6–2 (units are µg OC/cm 2 ).Two additional sets (n = 10 for each set of fivefilters) of 37-mm filters were analyzed severalmonths apart in 2010. The pooled EC results arecomparable <strong>to</strong> those obtained previously. Results(µg C/cm 2 ), including OC results for both sets <strong>and</strong>TC results for one are given in Table 6–3. The resultsin Table 6–3 represent duplicates on two setsof 5 filters.NIOSH CIB 65 • <strong>Carbon</strong> <strong>Nanotubes</strong> <strong>and</strong> <strong>Nanofibers</strong>55
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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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- Page 45 and 46: 3.3 SWCNT and MWCNTIntraperitoneal
- Page 47 and 48: The same potency sequence was obser
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- Page 53 and 54: Table 3-6. Findings from published
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- Page 60 and 61: length, respectively) [Muller et al
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- 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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- Page 92 and 93: Table 6-8. Respiratory protection f
- Page 94 and 95: ••Workers in areas or in jobs w
- Page 97 and 98: 7 Research NeedsAdditional data and
- Page 99 and 100: ReferencesACGIH [1984]. Particle si
- Page 101 and 102: Bolton RE, Vincent HJ, Jones AD, Ad
- Page 103 and 104: eport issued on July 22, 2011. NEDO
- Page 105 and 106: Kobayashi N, Naya M, Mizuno K, Yama
- Page 107 and 108: Methner M, Hodson L, Geraci C [2010
- Page 109 and 110: Human Services, Centers for Disease
- Page 111 and 112: Piegorsch WW, Bailer AF [2005]. Qua
- Page 113 and 114: AD, Baron PA [2003]. Exposure to ca
- Page 115: Varga C, Szendi K [2010]. Carbon na
- Page 119 and 120: ContentsA.1 Introduction ..........
- Page 121 and 122: A.1 IntroductionThe increasing prod
- Page 123 and 124: provide an informal check on the es
- Page 125 and 126: these same dose groups; this effect
- Page 127 and 128: Table A-1. Rodent study information
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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