CNT-protocol-cross-sectional-to-HSRB-final_mod1_02052013

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Exposure Assessment and Epidemiological Study of U.S. Workers Exposed to Carbon Nanotubes and Nanofibers

CNT-protocol-cross-sectional-to-HSRB-final_mod1_02052013

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Industrywide Exposure Assessment and Cross-Sectional Epidemiologic Studies of Workers
at Facilities Manufacturing, Distributing, or Using Carbon Nanotubes or Carbon
Nanofibers in the United States.

Protocol

Project Officers: Mary K. Schubauer-Berigan and Matthew M. Dahm, National Institute for
Occupational Safety and Health; Division of Surveillance, Hazard Evaluations and Field Studies;
Industrywide Studies Branch

November 5, 2012, revised February 5, 2013

Co-Investigators: James A. Deddens*, M. Eileen Birch**, Douglas E. Evans**, Aaron Erdely§
National Institute for Occupational Safety and Health
*Division of Surveillance, Hazard Evaluations and Field Studies; Industrywide Studies Branch
**Division of Applied Research and Technology; Chemical Exposure & Monitoring Branch
Cincinnati, OH
§Health Effects Laboratory Division;
Mention of trade names does not imply endorsement by the United States government or the
National Institute for Occupational Safety and Health

Protocol for an Exposure Assessment and Epidemiologic Study of U.S. CNT & CNF Workers

TABLE OF CONTENTS
List of Tables ................................................................................................................................ iv 
List of Figures............................................................................................................................... iv 
Glossary of Abbreviations .............................................................................................................. v 
ABSTRACT ................................................................................................................................... 1 
INTRODUCTION......................................................................................................................... 2 
Potential health effects of carbon nanotubes and nanofibers ...................................................... 2 
Potential workplace exposures to carbon nanotubes and nanofibers .......................................... 4 
BACKGROUND ON CARBON NANOTUBE AND NANOFIBER PRODUCTION AND USE
IN THE UNITED STATES ....................................................................................................... 5 
CNT/CNF primary manufacturing ......................................................................................... 5 
CNT/CNF secondary manufacturing ...................................................................................... 6 
CNT/CNF distribution.............................................................................................................. 7 
RESULTS OF FEASIBILITY STUDY .................................................................................. 7 
Phase I .................................................................................................................................... 8 
Phase II ................................................................................................................................. 11 
STUDY RATIONALE ................................................................................................................. 13 
STUDY OBJECTIVES ................................................................................................................. 13 
METHODS and MATERIALS ................................................................................................. 14 
I. Industrywide exposure assessment study .............................................................................. 15 
Measurement	Methods	Development ................................................................................... 15 
Exposure	Assessment	Sampling	Strategy ......................................................................... 19 
Sampling	Methods ............................................................................................................... 20 
Information	on	exposure	factors	to	be	collected .............................................................. 24 
Data	analysis	methods	and	assignment	of	exposures	to	workers .................................. 25 
II. Cross-sectional biomarker study .......................................................................................... 28 
Rationale .............................................................................................................................. 28 
Approach .............................................................................................................................. 29 
Biomarkers .......................................................................................................................... 30 
Recruitment	of	Participants	for	Exposure	Assessment	and	Epidemiologic	Study ........ 36 
Biomarkers	to	be	analyzed ................................................................................................. 38 
Sample	Collection	and	Preparation ................................................................................... 39 
Medical	examination	methods ........................................................................................... 45 
Spirometry	methods ........................................................................................................... 45 
Biospecimen	collection	methods ....................................................................................... 50 
Questionnaire	administration ............................................................................................ 54 
EPIDEMIOLOGIC ANALYSIS .................................................................................................. 54 
POWER ANALYSIS .................................................................................................................. 56 
HUMAN SUBJECTS PROTECTIONS.................................................................................... 62 
Confidentiality .......................................................................................................................... 62 
Worker Notification .................................................................................................................. 63 
Study Risks and Benefits .......................................................................................................... 63 
Assessment of Potential Benefits .............................................................................................. 63 
Assessment of Potential Risks .................................................................................................. 64 
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Protocol for an Exposure Assessment and Epidemiologic Study of U.S. CNT & CNF Workers

Description of Measures Taken to Minimize Potential Risks .................................................. 66 
Vulnerable populations ............................................................................................................. 67 
Risk versus Benefit Evaluation ................................................................................................. 67 
STUDY STRENGTHS AND LIMITATIONS ......................................................................... 68 
REFERENCES ............................................................................................................................ 70 
APPENDICES: DOCUMENTS PERTAINING TO CROSS-SECTIONAL BIOMARKER
STUDY ..................................................................................................................................... 86 
Appendix I. Fact sheet and informed consent documents ........................................................ 87 
Appendix II. Questionnaire for participants in study of lung and cardiovascular function, and
biomarkers of early health effects among CNT and CNF workers ........................................ 100 
Appendix III: Exposure factors related to company and employee (to be completed by NIOSH
investigator) ............................................................................................................................ 116 
Appendix IV. Emergency plan while conducting medical examinations and collecting
biospecimens ........................................................................................................................... 121 
Addendum 1: Notification letter #1: immediately available medical results (approved by NIOSH
IRB on 11/29/2012) ................................................................................................................ 122  
Addendum 2: Notification letter #2: clinically significant medical findings ............................. 123 
Addendum 3: Notification letter #3: Exposure assessment results ............................................. 128 
 

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List of Tables
Table 1. Sampling plan to be used for exposure assessment site visits. ....................................... 24 
Table 2. Description of circulating biomarkers to be measured for early effect of exposure....... 42 
Table 3. Panel for blood stimulation study, to be analyzed by NIOSH contractor....................... 43 
Table 4. IARC Group 1 carcinogens shown to cause lung cancer, non-Hodgkin lymphoma
(NHL), chronic lymphocytic leukemia (CLL), mesothelioma, or nervous system cancer.
......................................................................................................................................... 44 
Table 5. Spirometry safety exclusion or precaution items for adults (age 16-79) (adapted from
NHANES 2008). ............................................................................................................. 46 

List of Figures
Figure 1. Universal flow diagram for interpretation of spirometry (adapted by R. McKay from
McKay and Horvath 1994). ........................................................................................... 50 
Figure 2. Simulated forced vital capacity (FVC), as percent predicted, resulting from a decrement
of 1% per unit of background-corrected elemental carbon exposure, assuming a
standard deviation of 10% in FVC among the unexposed. ............................................ 59 
Figure 3. Effect measure [R2(T)] detectable for forced vital capacity (as a percent of age-, race-,
gender- and height-predicted) related to background-corrected elemental carbon at a
power of 0.8 and an alpha of 0.05. ................................................................................. 60 
Figure 4. Effect measure [R2(T)] detectable for a set of five biomarkers (adjusted for six
confounding variables) related to background-corrected elemental carbon at a power of
0.8 and an alpha of 0.05. ................................................................................................ 61 

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Glossary	of	Abbreviations	
8-OHdG

8-hydroxy-2’-deoxyguanosine

ATS

American Thoracic Society

BEV

back-extrapolated volume

CBC

complete blood count

CLL

chronic lymphocytic leukemia

CNF

carbon nanofiber

CNT

carbon nanotube

CPC

condensation particle counter

CRP

C-reactive protein

DART

Division of Applied Research and Technology

DC

diffusion charger

DNA

deoxyribonucleic acid

DSHEFS

Division of Surveillance, Hazard Evaluations, and Field Studies

DRI

direct-reading instruments

DTT

dithiothreitol

EC

elemental carbon

ECN

engineered carbonaceous nanomaterials

EDXA

energy dispersive X-ray analysis

ELISA

enzyme-linked immunosorbent assay

EPA

Environmental Protection Agency

ERS

European Respiratory Society

FEF25-75

forced expiratory flow during the middle two quarters of the FVC

FEV1

forced expiratory volume in 1 second

FERV

Field Evaluations and Response Vehicle

FVC

forced vital capacity

GC/MS

gas chromatography with mass spectrometry

GM-CSF

granulocyte macrophage colony-stimulating factor

GPx

glutathione peroxidase

hCAEC

human coronary artery endothelial cells

HELD

Health Effects Laboratory Division

IARC

International Agency for Research on Cancer
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Protocol for an Exposure Assessment and Epidemiologic Study of U.S. CNT & CNF Workers

ICAM

intercellular adhesion molecule-1

IL

interleukin

ICD

International Classification of Diseases

ICP-AES

inductively coupled plasma with atomic emission spectroscopy

IRB

Institutional Review Board

IH

industrial hygiene

KL

Krebs von den Lungen

LC/MS

liquid chromatography with mass spectrometry

LOD

limit of detection

LPM

liters per minute

LLN

lower limit of normal

MCE

mixed cellulose ester

MDC

macrophage derived chemokine

M-FISH

multiplex fluorescence in situ hybridization

MMP

matrix metalloprotease

MW

multi-walled

NHL

non-Hodgkin lymphoma

NHANES

National Health and Nutrition Examination Survey

NIOSH

National Institute for Occupational Safety and Health

NMAM

NIOSH manual of analytic methods

PAH

polycyclic aromatic hydrocarbon

PAI

plasminogen activator inhibitor

PBZ

personal breathing zone

PM

particulate matter

QFF

quartz fiber filters

R&D

research and development

SCGE

single-cell gel electrophoresis

SEM

scanning electron microscopy

SKY

spectral karyotyping

SOD

superoxide dismutase

SW

single-walled

t-PA

tissue plasminogen activator
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Protocol for an Exposure Assessment and Epidemiologic Study of U.S. CNT & CNF Workers

TEM

transmission electron microscopy

TNF

tumor necrosis factor

VCAM

vascular cell adhesion molecule

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ABSTRACT
Health effects from exposure to nanomaterials are uncertain, but may be more severe than from
larger-sized particles of the same material. This is due to the small size, high surface area per
unit mass (i.e., specific surface area) or (in some cases) high aspect ratio of nanomaterials.
Carbon nanotubes and nanofibers (CNT and CNF) are among the nanomaterials of greatest
interest from a public health perspective because of their potentially asbestiform properties (e.g.,
high aspect ratio) and toxicological evidence of possible fibrogenic, inflammatory, and
clastogenic damage resulting from exposures at occupationally relevant levels. In addition, the
useful properties of CNT and CNF have rendered them among the first nanomaterials to be
commercially exploited in manufacturing settings. Thus, an epidemiologic study to determine
whether early or late health effects occur from occupational exposure to CNT and CNF seems
warranted. This protocol describes a cross-sectional study of the small current workforce
involved with CNT and CNF in manufacturing and distribution, to be conducted in the following
phases: 1) industrywide exposure assessment study to evaluate worker exposure and further
development and refinement of measurement methods for CNT and CNF; and 2) a crosssectional study relating the best metrics of CNT and CNF exposure to markers of early
pulmonary or cardiovascular health effects. Future phases described in a forthcoming protocol
include the development of an exposure registry that will collect demographic, identifying, work
history and (where available) exposure information on workers at companies manufacturing or
using CNT or CNF; and a long-term prospective cohort study developed from the registry.

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INTRODUCTION
Potential	health	effects	of	carbon	nanotubes	and	nanofibers	
Human health effects from workplace exposures to engineered nanomaterials are
uncertain, as no epidemiological studies have been conducted (Schulte et al. 2009; Laney et al.
2011). However, toxicological studies suggest that certain physical properties of engineered
nanomaterials, such as particle number, size, surface area, and shape, may be of greater
importance than particle mass (a traditional metric for larger-scale materials) in determining
exposure and toxicity. For example, nano-sized carbon particles may be more likely to reach the
alveolar region than larger particles and thus may present a greater health hazard. The long, thin
shape of carbon nanotubes (CNT) and nanofibers (CNF) may confer asbestiform properties upon
elemental carbon (EC) (Seaton and Donaldson 2005; Murphy et al. 2011).
Recent toxicological evidence suggests wide-ranging health effects from exposure to
CNT or CNF. These likely include injury at the site of initial exposure [e.g., pulmonary
inflammation and subsequent fibrosis, or malignant transformation (Sargent et al. 2009, 2010)]
but may also include effects at remote sites (e.g., immunological and cardiovascular effects) due
to either translocation of the particles or response to an inflammatory cascade (Seaton and
Donaldson 2005, Simeonova and Erdely 2009). In vitro studies have found that CNT and CNF
show potentially genotoxic effects, such as mitotic spindle disruption, development of
aneuploidy or polyploidy, and formation of micronuclei (Sargent et al. 2009, 2010; Kisin et al.
2011). The toxicity of CNF is not as well studied as that of CNT; however, a recent evaluation of
the genotoxicity of CNF (Kisin et al. 2011) found them to be more potent clastogens in the comet

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assay and micronuclei test than single-walled (SW) CNT (but slightly less than crocidolite
asbestos).
There may be differences in biopersistence, toxicity or potential carcinogenicity by CNT
or CNF shape, size, or tendency to agglomerate (Osmond-McLeod et al. 2011). A recent
mesothelial instillation study in mice observed that long multi-walled (MW) CNT fibers (~5-50
µm) were retained in the pleura to a greater degree than shorter fibers (Murphy et al. 2011). Our
initial feasibility investigations (Dahm et al. 2011; Dahm et al. 2012) suggest that most of the
CNT fibers being produced in the U.S. are long, with a mean length of 58.4 μm for CNF, 187.9
μm for single-walled (SW) CNT, and 773.3 μm for multi-walled (MW) CNT (Dahm et al. 2011).
These particles also have very high aspect ratios with a strong tendency to agglomerate.
However, the agglomerate dimensions (e.g., 1 µm x 3 µm) suggest that they are of inhalable, and
most of respirable, size. Furthermore, the extent of de-agglomeration in the lung or bronchial
tract is unknown. Questions remain about whether such long fibers are able to penetrate the lung
and visceral pleura to reach the parietal pleura and mesothelium. Recent in vitro studies suggest
it is the high aspect ratio, not surface area or iron content (a contaminant from the production
method employed), of CNT that conveys their highest fibrogenic properties (Sanchez et al. 2011)
and likely retention in the pleura (Murphy et al. 2011).
Several national and international organizations such as the National Institute for
Occupational Safety and Health (NIOSH), the U.K.’s Health and Safety Executive, the National
Cancer Institute, the National Toxicology Program, and the International Agency for Research
on Cancer (IARC) have emphasized the need for basic knowledge about the human health effects
of exposures to engineered nanomaterials (e.g., IARC 2008). Limitations to the ability to study
health effects of CNT exposures in human populations include finding and accessing a large
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

enough exposed population to study, measuring biologically relevant exposure, the lack of
sufficient latency to observe chronic health effects, and understanding which pathways of
exposure and effect are most relevant (Schulte et al. 2009; Schubauer-Berigan et al. 2011;
Schulte and Trout 2011; Schulte et al. 2011). A recommended approach is to develop an
exposure registry that may serve as the sampling frame for a series of biomarker studies, panel
studies, or cohorts for long-term epidemiologic follow-up (Laney et al. 2011; Peters et al. 2011;
Schulte and Trout 2011).

Potential	workplace	exposures	to	carbon	nanotubes	and	nanofibers	
At present, because of the newness of the technology, much of the occupational exposure
to engineered nanomaterials occurs at the research and development (R&D) scale. There have
been few reliable surveys of the size of the workforce exposed to nanomaterials. More than 30%
of nano-manufacturers worldwide participating in a voluntary survey indicated that they create
and handle carbonaceous nanomaterials (e.g., CNT, fullerenes, and carbon black) (Gerritzen et
al. 2007). A recent NIOSH feasibility study of companies manufacturing or using engineered
carbonaceous nanomaterials in the US (above R&D scale) found that 50 (82%) of 61 were
handling CNT or CNF (Schubauer-Berigan et al. 2011). Most of these companies were small,
with an average of about 10 workers per company. This workforce (estimated at 500 in 2008)
was projected to grow about 16% annually, with CNT use growing more than 20% annually
(Schubauer-Berigan et al. 2011). About half the companies identified in the NIOSH study
provided information about the size, shape, and other properties of the CNT and CNF produced
or used, and about the use of exposure controls and protective equipment for workers (Dahm et
al. 2011).
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Based on the findings from this feasibility study, in FY10-FY11 NIOSH funded a study
to evaluate worker exposures at ten of these 50 CNT and CNF producers and users. As a result of
this work (described further below), this protocol describes the development of an exposure
registry for workers exposed to CNT and CNF and the conduct of epidemiologic studies
designed to evaluate workplace exposures to CNT and CNF. The goal of these studies will be to
determine whether exposures to CNT or CNF are related to biomarkers of early health effects or,
in the long term, to persistent health effects such as pulmonary fibrosis, cardiovascular disease or
cancer.

BACKGROUND ON CARBON NANOTUBE AND NANOFIBER
PRODUCTION AND USE IN THE UNITED STATES
Basic information about CNT and CNF manufacturing and use in the U.S. is provided in
the following paragraphs. The results of a feasibility investigation regarding exposure assessment
and epidemiologic industrywide studies of engineered carbonaceous nanomaterials (ECN) are
also described below. Phase I of this investigation describes the enumeration and
characterization of ECN manufacturers and users. Phase II considers the exposure characteristics
of a group of 10 CNT and CNF manufacturers and users from among the companies
participating in Phase I.
CNT/CNF primary manufacturing
Anecdotally, it is apparent that there are a large number of university-based or corporate
start-up manufacturers of CNT and CNF, but the size of this workforce is unknown. Beyond pure
research-and-development scale, a recent NIOSH feasibility study attempted to identify all U.S.
primary manufacturers of these materials (Schubauer-Berigan et al. 2011; Dahm et al. 2011). Of
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

the 50 CNT or CNF manufacturers and users, 28 were primary manufacturers. Among these,
65% reported using chemical vapor deposition as a synthesis method, 18% used arc discharge,
12% used flame combustion, and 6% used laser ablation. Synthesis methods are associated with
different co-exposures (see next paragraph) as well as potential contact with the CNT and CNF
during primary manufacturing. We estimated in our feasibility study that at least 251 workers
were involved in primary manufacturing in 2008, some of whom were also involved in
secondary manufacturing. Most occurs in the northeastern, Midwestern and western U.S. states,
with Massachusetts, California, Ohio and Texas leading the manufacturing efforts.
The primary manufacture of CNT and CNF involves exposure to other potentially
hazardous materials, including polycyclic aromatic hydrocarbon (PAHs) formed during synthesis
of CNT and CNF, heavy metals used as catalysts, or solvents used in product processing (Birch
et al. 2011; Birch 2011).
CNT/CNF secondary manufacturing
The recent NIOSH feasibility study (Schubauer-Berigan et al. 2011) found that 32 of the
50 CNT/CNF companies were involved in secondary manufacturing (11 of these were also
primary manufacturers). The total workforce size at these companies was estimated at 181, and
the companies were located primarily in California, Massachusetts, Ohio and Texas, in
descending order. Some companies that are involved in both primary and secondary
manufacturing maintain separate facilities (often in different states) for these activities. The most
common type of secondary manufacturing includes the production or use of polymers or polymer
composite (Khare and Bose 2005), with generally small percentages of CNT and CNF in the
mixtures. Other uses include creation and use of CNT or CNF-containing inks for flexible

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

printing and dispersing or otherwise enhancing the properties of the CNT or CNF materials for
other downstream users.
Possible hazards associated with secondary manufacture vary by the type of process, but
could include: free CNT and CNF, especially if used in powder form; polymers, carbon fibers or
other substances used in polymer or composite production; solvents used in ink generation;
adhesives used in fabrication; and dusts generated in the drilling, sanding or machining of parts
(Dahm et al. 2012).
CNT/CNF distribution
In designing the NIOSH feasibility study, distributors were initially excluded from
participation because the focus of the study was on manufacturers (Schubauer-Berigan et al.
2011). However, given the potential for worker exposure in the handling of powder-form CNT
and CNF, distributors are considered eligible for the current study. Seven companies (three in
California) were identified as distributors in the original database for the feasibility study; since
then, several others have been identified as importers and possible distributors. Because the
distributors were not included in the original feasibility study, it is unknown how many workers
are employed by CNT or CNF distributors.

RESULTS OF FEASIBILITY STUDY
As mentioned above, in 2008, NIOSH researchers began an assessment of the feasibility
of industrywide exposure and epidemiology studies of workers exposed to ECN (Dahm et al.
2011; Schubauer-Berigan et al. 2011). The purpose was to determine whether industrywide
studies are feasible among U.S. workers exposed to ECN, based on workforce size and
distribution, exposure levels, sufficient (likely) latency between exposures and possible health
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

outcomes, and willingness to participate. The feasibility study was conducted in two phases,
described further below.

Phase I
The goal of Phase I of the feasibility study was to identify the most promising population
and ECN type for study, and to consider the most appropriate exposure assessment methods and
epidemiologic study design. This phase of the feasibility study identified types of carbon
nanomaterials produced; size, shape and quantities manufactured; and facility locations as well
as the workforce size (Yencken and Tucker 2009; Dahm et al. 2011; Schubauer-Berigan et al.
2011).
In Phase I, employing industry profiles, internet searches, and personal contacts, we
identified 139 potentially eligible companies. To be eligible, companies must be manufacturing
(or using in other manufacturing processes) ECN in the U.S. above the research and development
scale, or at research and development scale with plans to scale-up within five years. Of these, 61
companies were found to be eligible, and the most common substance manufactured was CNT
(by 43 companies). We also found 9 ECN distributors. We enumerated a total of at least 620
workers at the eligible companies, 375 of whom work with CNT. Workforce growth was
projected at 15-17% annually across all ECN and was highest for CNT at 22%. Most pilot-scale
growth was due to CNT manufacturing. A total of 18,000 kg ECN was estimated to be produced
annually in the U.S. at the eligible companies. Many of the companies appeared to be spin-offs
using technologies developed at university laboratories. These results are described in
Schubauer-Berigan et al. (2011).

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Half the manufacturers agreed to complete a questionnaire about their workforce size,
materials produced, and the use of controls to prevent occupational exposure (Dahm et al. 2011).
Most companies reported using some form of administrative controls, engineering controls, or
personal protective equipment to control worker exposure.
From the Phase I feasibility study, the following observations were made that may affect
feasibility: 1) Most ECN manufacturers are small companies, often near major universities (i.e.,
spinoffs of research projects); 2) the largest workforce with greatest scale-up potential at the
present time is involved in CNT production, use and distribution; 3) operations involved in
handling powdered material are most likely to pose a hazard in the workplace, suggesting that
primary and secondary manufacturers and raw material distribution are key for study. As a result,
we determined that CNT and CNF manufacturers, powder users, and distributors were most
promising for industrywide exposure assessment and epidemiology studies.
At this time, it appears that the potential for CNT and CNF exposure is highest among
workers handling forms of nanomaterials that have been shown to cause adverse effects in
toxicology studies (e.g., airborne particles or liquid formulations with the potential for dermal
exposure). This group includes primary manufacturers, secondary manufacturers (users), and
distributors. We recognize that the hazard may extend to workers who use the final products
containing CNT and CNF materials. However, there are three main limitations to adding such
workers: (1) most primary and secondary manufacturers are currently still in pilot or
demonstration scale production and there is not a large enough workforce using or recycling the
final products; (2) companies are often reluctant to identify their customers to research
investigators; and (3) the forms of the CNT or CNF are often encapsulated into hardened
polymers or fixed films and the potential for exposure is likely minimal unless airborne dust is
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

generated by a work process (e.g. sanding, grinding a composite). And in these cases, the CNT
and CNF in the dust is embedded in a polymeric matrix, usually at low mass fraction, which
differs from the bulk materials under study.
The efforts recommended as feasible at the end of Phase I were:
1. Conduct an industrywide exposure assessment, developing and deploying the
most specific and health-relevant exposure metrics for CNT and CNF.
2. Conduct concomitantly cross-sectional studies using workplace exposure
measurements, biomarkers of exposure and of early effects for pulmonary
fibrosis, inflammation, cancer or genetic damage, and cardiovascular disease.
3. Begin rostering the U.S. CNT and CNF manufacturing and commercial
distribution workforce for development of a cohort.
4. Consider adding the large research and development enterprises involved in CNT
and CNF production.
As mentioned above, based on the Phase I findings and supplemented by Phase II
observations while visiting several CNT primary and secondary manufacturers (described further
below), we concluded that it was appropriate to add CNT distributors and CNF manufacturers as
well. Including CNT and CNF primary and secondary manufacturers as well as distributors, we
identified 59 eligible companies with a total of at least 500 workers, for an average of about 10
workers handling or otherwise exposed to CNT or CNF per company. This number differs from
the 61 companies mentioned above because the 61 refers to all ECN companies, whereas the 59
companies refers just to those manufacturing, distributing or using CNT or CNF.

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Phase II
The goal of Phase II of the feasibility investigation was to estimate occupational exposure
levels for workers exposed to the most promising ECNs (on the basis of workforce size and
toxicological hazard) identified in Phase I, and to gauge initial interest in participating in an
epidemiologic study. In fiscal years 2010 and 2011, walk-through surveys, including taskspecific and full-shift personal breathing zone (PBZ) sampling, were conducted at ten CNT and
CNF sites, including producers (primary manufacturers) and users (secondary manufacturers).
No distributors have as yet agreed to participate. Exposures to MWCNT and SWCNT were
evaluated among workers based on EC (Birch et al. 2011) and EC plus transmission electron
microscopy (TEM)-based particle counts for air samples (Dahm et al. 2012). Results of the Phase
II study (Dahm et al. 2012; Dahm et al., in press) suggest that exposure assessment methodology
development should continue concurrently with the industry-wide exposure assessment and
epidemiology study to ensure that different metrics of exposure (e.g., mass concentration,
particle size distribution, fiber size, shape and agglomeration) can be adequately measured at the
low levels at which health effects may occur (Kuempel 2011).
In 2012, a continuation of Phase II is being carried out. Sampling is being conducted at
several additional facilities that have agreed to participate in the exposure assessment study. The
sampling plan is focused on collecting full-shift PBZ samples for the mass concentration of EC
and for analysis by transmission electron microscopy, along with direct-reading instruments
(DRI) to collect additional metrics of exposure and to determine how exposures may be
occurring (i.e., the emissions source). This information will help establish a worker’s daily
exposure compared to the mostly task-based, area samples reported to date.

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

The Phase II continuation is applying methods used previously to assess exposures as
well as field test the suitability of emerging methods for assessing worker exposures to CNTs
and CNFs (Evans et al. 2010, Birch et al. 2011, Dahm et al. 2012). Exposure measurement
methods work is currently underway to support this and other field studies. Its main objectives
include lowering the detection limit for EC (NMAM 5040), a key indicator of exposure to CNTs
and CNFs. A higher-flow, PBZ respirable cyclone sampler to assess health-relevant exposures is
being evaluated. Other new equipment (such as a personal sampler that measures particle size
distribution), which is being designed by NIOSH researchers, will be field tested, if available.
Additional work is also underway to determine the best way to conduct microscopy-based, sizespecific CNT and CNF structure counts for air samples.
During field investigations, we have observed very high acceptance (and reporting) of
use of personal protective equipment (e.g., gloves and laboratory coats) to prevent dermal
exposure to CNT and CNF (Dahm et al. 2011, 2012). Despite this, it is uncertain to what extent
these measures protect the entire skin surface in regular contact with the nanomaterials: we have
frequently observed that wrists are uncovered and may receive exposure to the CNT- or CNFcontaining materials. Thus, we will also include an evaluation of exposures to skin surfaces in
contact with these materials.
Discussions with plant management and workers in Phase I and II indicate there is an
interest from many of the participating companies in also taking part in the epidemiologic
component of the study, including a biomarker and prospective cohort study.

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

STUDY RATIONALE
As described above, numerous in vitro and in vivo toxicology studies have demonstrated
the fibrogenic, inflammatory, and possibly mutagenic properties of some CNT and CNF. The
feasibility study conducted by NIOSH researchers indicates that there is a growing workforce,
currently at least 500 in the U.S., involved in the manufacture, use, and distribution of CNT or
CNF. There have been to date no epidemiologic studies published within the workforce exposed
to CNT or CNF; however, there is interest in evaluating the potential human health effects of
exposure to CNT and CNF. Carbon nanoparticles, primarily SWCNT and MWCNT were
identified as a high priority for the evaluation of carcinogenicity by IARC, based on the findings
from animal toxicology studies (IARC 2008). As described above, sufficient feasibility now
exists to begin conducting industrywide exposure assessment and biomarker studies, and to
develop an exposure registry to serve as the framework for a prospective cohort study, which
may require international pooling for optimal statistical power.

STUDY OBJECTIVES
The overall study protocol has two major components, summarized below and detailed
more extensively in the methods and materials section.
I. Industrywide exposure assessment study: This component will establish sampling and
analysis protocols for the detection and quantification of CNT and CNF in US workplaces. Taskbased and full-shift exposure assessments, focused on the collection of PBZ samples, will be
conducted at facilities participating in the cross-sectional biomarker study and at some other
facilities not included in that study. These PBZ samples will be collected for the metrics that are
the most current and feasible to assess exposures to CNT or CNF, which are the mass
13

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

concentration of EC (a marker for CNT and CNF exposure) as well as size-specific CNT and
CNF structure count estimates (Dahm et al. 2012).
II. Cross-sectional biomarker study: After the sampling and analysis protocols have been
established to measure CNT and CNF, concurrent with the industrywide exposure assessment
study, several biomarkers of early effect (for pulmonary fibrosis, cardiovascular disease, and
genetic damage) will be measured for workers exposed to a range of CNT and CNF levels. This
will be accompanied by a questionnaire to assist in interpretation of the biomarker results and
medical examinations to evaluate pulmonary function and cardiovascular health. Statistical
analyses will be conducted to determine the nature of the relation between exposure to CNT and
CNF and these biomarkers of early effect, considering potential confounding factors such as
smoking, age, gender, and workplace co-exposures, including non-engineered particulate matter.
Additional components that are planned for the future include the development of an
industrywide exposure registry of CNT and CNF workers, the identification of a cohort of these
workers to be followed on a prospective basis for a variety of health outcomes, including
incidence and mortality from pulmonary disease (e.g., fibrosis), cardiovascular disease, and
cancer. This information will be collected via periodic questionnaires administered to the cohort,
and through linkage of the cohort with disease and mortality registries, and consideration of
international pooling of cohorts for larger studies to increase statistical power. These additional
components are described in a separate protocol that is under development.

METHODS and MATERIALS
Methods for the two components of the study are described here.

14

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

I. Industrywide exposure assessment study
In this component, we will: 1) refine measurement methods for CNT and CNF, and the
metals and polycyclic aromatic hydrocarbons (PAHs) associated with their production (i.e., seen
in primary production facilities); 2) conduct task-based and full-shift exposure assessments,
focusing on the collection of PBZ air samples; and 3) evaluate dermal exposures on wrists and
hands for workers exposed to CNT or CNF . These exposure assessments will primarily consist
of samples collected for the mass concentration of EC, a marker for CNT and CNF exposure, and
size-specific CNT/CNF structure count estimates from breathing-zone air samples, in a
representative group of CNT and CNF manufacturers and users, as well as an assessment of postshift dermal exposures among these workers.
At least ten companies that have taken part in the Phase I and/or Phase II feasibility study
will be invited to participate in this study and the biomarker study, which will be carried out
concurrently. The goal is to enroll at least 100 workers, with a range of exposures, in the joint
studies. We estimate that 10 employees per company will participate. All facilities included in
the study will have been evaluated in Phase II by the field teams in three NIOSH Divisions [the
Division of Surveillance, Hazard Evaluations, and Field Studies (DSHEFS), the Division of
Applied Research and Technology (DART), or the Education and Information Division (EID)].
Measurement	Methods	Development	
Results of the Phase II feasibility study site visits suggest that exposure assessment
methodology development should continue concurrently with the industry-wide exposure
assessment study to ensure that different aspects of exposure (e.g., mass concentration, particle

15

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

size distribution, fiber size, shape and agglomeration) can be adequately measured at the low
levels at which health effects may occur (Kuempel 2011).
This project will apply methods used previously as well as field-test the suitability of
emerging methods for assessing worker exposures to CNTs and CNFs (Evans et al. 2010; Birch
et al. 2011). As mentioned in the Phase II summary above, the objective for this continued work
is to lower the detection limit for EC (NMAM 5040), which includes evaluating higher-flow,
PBZ respirable cyclones to assess health relevant exposures. Other new equipment (such as a
personal sampler that measures particle size distribution), which is currently being designed by
NIOSH researchers, will be field tested if available and preliminary assessments indicate
suitability for CNT and CNF monitoring.
Modified methods for TEM analysis also will be applied to determine a CNT/CNF
structure count. Specifically, a modified NIOSH Method 7402 will be employed to analyze air
and bulk samples on a JEOL2100F TEM. Modifications mostly entail eliminating steps required
for asbestos identification and classifying and counting CNT/CNF ‘structures’. As with NIOSH
7402, a pump is used to draw a measured volume of air through a polycarbonate or mixed
cellulose ester (MCE) membrane filter. After sample collection, a thin film of carbon is applied
to the filter surface by vacuum evaporation (MCE filters must first be chemically treated to
collapse their pore structure). Three small sections are cut from the carbon-coated filter, placed
on TEM grids, and the filter medium is dissolved by a solvent. This procedure deposits the
carbon film on the grid such that it bridges grid openings and supports the particles in their
original positions on the filter.
After preparation, each grid is examined at low magnification to ensure that the loading
16

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

and preparation quality are acceptable for a structure count. Randomly selected grid openings are
viewed, the total number of structures and grid openings examined are reported, and
representative photomicrographs for each grid are taken. The elemental composition of a
nanotube structure is determined by energy dispersive X-ray analysis (EDXA). The structure
classification is based on morphology and qualitative EDXA. Ambient outdoor and indoor
workplace air samples may contain complex nanotube aggregates (and other particle types).
Individual CNT and CNF and more complex particles containing CNT/CNF are counted as
‘structures’, classified as either individual tubes/fibers, clusters or matrices. Along with the air
volume, the count may be used to estimate the airborne concentration of CNT/CNF structures.
The method for categorizing structures and determining the accuracy of the count is currently
under investigation. Improvements to be evaluated include adding a measurement component to
permit size-specific structure counts to be conducted. At present, we are evaluating the
classification of CNT structures into five different size-specific ‘bins’ based on the longest
dimension. The second dimension is annotated if it is less than half the first dimension. For
single nanotubes or nanofibers, mean diameters and lengths are estimated, in addition to counts.
Representative photomicrographs are captured and retained in an image library. The MCE filters
from each collected sample will be retained to permit the re-evaluation of previously collected
samples using the methods determined to be most efficient and accurate at capturing the healthrelevant aspects of exposure.
Previous work at a primary CNF manufacturer indicated that workplace exposures also
occurred to a complex mixture of CNFs (EC used as a marker for exposure) and production
byproducts, which included fine/ultrafine, iron-rich soot (Birch et al. 2011), CO (Evans et al.
2010), and PAHs (Birch 2011). Naphthalene and acenaphthylene were the dominant PAHs in air
17

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

samples. In the raw CNF products, the top three PAHs were pyrene, benzo(g,h,i)perylene, and
fluoranthene. Other toxic PAHs also were identified, including the carcinogen benzo(a)pyrene.
As a result of this previous work, screening analyses of bulk samples for PAHs will be
conducted as part of this study. We anticipate that PAH and metals samples will be more
relevant for primary manufacturers producing CNTs and CNFs as compared to downstream
secondary manufacturers using the purified products. The presence of PAH in air and raw
(unpurified) CNF samples will be assessed for primary manufacturers, based on professional
judgment related to reactor design as well as precursors and catalysts employed. The metal
content of CNTs and CNFs also may be a factor in the potential toxicity of these materials. Thus,
bulk samples also will be analyzed for residual metals. Contaminants (PAH and metals) in final
products of primary manufacturers are expected to be much lower than those in raw products
because final products are purified to remove organic and metal impurities.
For PAH analyses, target and non-target analytes will be identified by gas
chromatography with mass spectrometry (GC/MS); liquid chromatography with mass
spectrometry (LC/MS) may also be applied. Target analytes will be quantified, while non-target
analytes will be identified based on a library (MS) search and their reported concentrations will
be estimated. Metals will be determined by inductively coupled plasma with atomic emission
spectroscopy (ICP-AES) according to NIOSH Method 7300 (with modified sample digestion
procedure). Method 7300 includes the following metals: Ag, Al, As, Ba, Be, Ca, Cd, Co, Cr, Cu,
Fe, K, La, Li, Mg, Mn, Mo, Na, Ni, P, Pb, Sb, Se, Sr, Te, Ti, Tl, V, Y, Zn, and Zr. Other
techniques (e.g., ICP/MS) also are available for trace metals analyses.

18

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Potential dermal exposures will be assessed in a qualitative fashion. Dermal samples will
be collected post-shift for each individual participating in the CNT/CNF exposure assessment
sampling. Samples will be collected by using a tape stripping method for the outermost skin
layer, the stratum corneum (Rougier et al. 1987; Schneider et al. 2000; Lundgren et al. 2006).
Any removed CNTs/CNFs will then be visually identified by scanning electron microscopy
(SEM). Specifically, double-sided, adhesive-coated substrate will be used as the sampling
medium, which will be analyzed directly by SEM. The tape will be placed with a sticky surface
on the skin, with slight pressure being applied. This will provide a qualitative (yes/no) answer to
whether CNT/CNF material is present or absent on the sampled area, and possibly a relative
loading level (high, medium, low). Two samples will be collected from each worker on their
dominant hand. One sample will be collected on the hand, which will include the palm and
fingers, and will indicate the effectiveness of gloves and potential hand-to-mouth exposures
(ingestion). The other sample will be collected on the wrist and forearm. This sample is
representative of the most typical dermal exposure seen in workplaces, between the end of the
glove near the wrist and the beginning of the lab coat or Tyvek suit.
Exposure	Assessment	Sampling	Strategy	
Upon arriving at the facility, NIOSH researchers will hold an initial meeting with
company personnel to explain the intentions and needs of the exposure assessment and
biomarker study and the site visit as well as preparing the equipment for sampling. A
walkthrough of the facility will be conducted to understand possible exposure points and
potentially exposed personnel to CNT or CNF.

19

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Filter-based, PBZ samples will be collected for the mass concentration of EC and TEM
analysis for each worker in the study (see pp. 36-38 for information concerning worker
recruitment). General area samples will be collected at locations deemed to have the highest
potential for exposure, based on professional judgment or observations made during any
previous NIOSH evaluations of the facility. PBZ samples will be collected throughout the
employees’ work shifts. Several DRI will be used alongside the filter-based area samples to
assess exposure, non-selectively, to any nano-scale materials. These include a condensation
particle counter (CPC 3007; TSI Inc., Shoreview, MN, USA), a photometer (DustTrak DRX
Model 8533; TSI Inc.) and a diffusion charger (DC 2000 CE; EcoChem Analytics, Murrieta, CA,
USA) (Evans et al. 2010). Task-based area samples will be collected, when feasible, along with
concurrent full-shift PBZ samples on the participating employees. These task-based area samples
are collected in order to determine any significant tasks that contribute to the worker’s daily
exposure and will supplement the total cumulative PBZ samples collected throughout the day.
Sampling	Methods	
Personal and area filter samples will be collected on 25-mm diameter quartz fiber filters
(QFF), which will be subsequently analyzed for the airborne mass concentration of EC according
to NIOSH Manual of Analytical Methods (NMAM) Method 5040 (NMAM 2006a). Use of these
filters facilitates lower detection limits for EC (Dahm et al. 2012). Open-faced cassette sampling
will be performed for PBZ and area samples using a Leland LegacyTM (SKC Inc. Eighty Four,
PA) pump operating nominally at 6.5 liters per minute (LPM). Respirable PBZ and area samples
will also be collected on a 25-mm diameter QFF through use of a special adapter attached to a
GK 2.69 BGI cyclone (BGI Inc. Waltham, MA). The cyclone samples will be collected using an
XR 5000 (SKC Inc. Eighty Four, PA) pump operating at a flow rate of 4.2 LPM. For area
20

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

samples, an additional 37-mm QFF cyclone sample may be collected for comparison to the
more-experimental 25-mm QFF cyclone adapter.
During instances of high dust concentrations or heavily contaminated workplaces, all
samples will be collected with the respirable cyclones (which operate at lower flow rates) to
reduce the likelihood of “overloading” the samples. This will be based upon professional
judgment upon arriving at a facility.
Additional personal and area filter samples will be collected on 25-mm mixed cellulose
ester (MCE) filters to be analyzed using a modified NMAM 7402 for TEM (NMAM 2006b). XR
5000 or Leland Legacy TM (SKC Inc. Eighty Four, PA) pumps operating at 5 LPM will be used
to collect the TEM samples. Depending on the dust levels within the facility, as well as the
length of a shift, or the quantities of CNT or CNF used, a 25 mm respirable cyclone may be
attached to the 25-mm MCE filter set at a flow rate of 4.2 LPM and used as a personal breathing
sample in order to provide a more size-discriminating respirable sample. This will reduce the
possibility of filter overloading, which could interfere with the accuracy and quality of TEM
analyses. TEM measurements will be used for two main purposes: 1) to provide qualitative
evidence of the presence of CNT and CNF in samples; and 2) to facilitate the estimation of sizespecific structure counts. These counts, made on a representative number of fields, will be
related to the volume of air collected to provide quantitative air concentrations of CNT structures
(e.g., Dahm et al. 2012). Typical size, shape and degree of agglomeration will also be denoted
using TEM methods. All single fibers or agglomerates containing CNT or CNF, with no size or
shape restrictions being used, will be counted and placed into size classes based on length and
width, as described above. CNT or CNF agglomerates in open-face filter samples, which may
contain non-respirable particles, will also be enumerated with no size restrictions, as described
21

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

on p. 16. The size-specific counts will be listed as CNT- or CNF-containing structures per mm2
and will then be normalized for air volume and reported as size-specific structures/cm3 of air. All
pumps used for EC and TEM measurements will be calibrated before and after each day of
sampling.
Real-time measurements of particle number concentration will be performed with a CPC
(CPC 3007; TSI Inc., Shoreview, MN, USA). The CPC measures particles in the size range of 10
to 1000 nm. The data output is expressed as total number of particles per cubic centimeter
(P/cm3) of sampled air with an upper dynamic range of 100,000 P/cm3.
Real-time respirable mass estimates will be obtained using a photometer (DustTrak
Model 8533; TSI Inc). The operating range of the DustTrak is 0.001 to 150 mg/m3, and it
measures mass of particles with diameters in the 0.1 to 15 µm size range. Active surface area
measurements will be provided by a diffusion charging (DC)-based instrument (DC 2000 CE;
EcoChem Analytics, Murrieta, CA, USA). Units are expressed as μm2/cm3, and the DC has an
operating range of 0-2000 μm2/cm3. All area direct-reading (real-time) instruments and area filter
samples will be placed on a cart approximately 1 m from the ground, to enhance the mobility of
the equipment. The DRIs and filter-based air samples will be arranged on the cart with all
sampling inlets placed as close as possible to each other in order to sample the same air space.
The sampling approaches described have been adapted from Evans et al (2010), Birch et al.
(2011) and Methner et al. (2010).
On-board data-logging capabilities will be utilized for the CPC, DustTrak and DC, and
the shortest logging intervals will be selected for all samples: 1 second for the indoor CPC and
DustTrak and 10 seconds for the DC. Outdoor background samples will be collected using the
22

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

CPC and DustTrak, when available, with the logging intervals set at 1 second. Listed below is
the sampling plan (Table 1) along with the specific pieces of equipment used to collect all
personal and area samples.
Outdoor and indoor background measurements will be collected on each day of sampling
due to the potential for contribution of incidental nanoparticles. Anthropogenic sources of fine
and ultrafine EC mainly relate to fossil fuel combustion (e.g., motor vehicle exhaust). Sources
include diesel engines, emissions from coal-fired and fuel oil-fired power plants, as well as the
seasonal burning of biomass (Magliano et al. 1999; Streets et al. 2001; Christoforou et al. 2000;
Schauer 2003). In general, nanoscale particles occur as byproducts of combustion or hot
processes, such as during operation of motor vehicles, compressors, and industrial dryers and
heating systems. Various cleaning operations and condensation processes also can contribute
nanoscale particles. The multiple sources of these fine and ultrafine aerosols are significant
contributors to the total particle concentration measured by the CPC (Lam et al. 2006, Heitbrink
et al. 2007, Demou et al. 2008, Peters et al. 2009, Evans et al. 2010), often precluding reliable
detection of engineered nanoparticles over this size range, if present. To account for ambient
(environmental and occupational) background, samples will be collected using a CPC (particle
number), a DustTrak (particle mass) and filter-based samples for the analysis of the mass
concentration of EC and TEM for CNT or CNF structures. The background samples will be
collected throughout the full day of sampling. Sample locations for indoor and outdoor
background measurements will be selected based on professional judgment and prior knowledge
of the facility for those visited previously. In general, however, outdoor background sampling
will be used for facilities that are open to outdoor air, and indoor background sampling will be

23

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

used for other facilities, at locations that share a common air handling source as the nanomaterial
production area, but that have no potential exposure to the CNT or CNF.
Table 1. Sampling plan to be used for exposure assessment site visits.
Type of
Sample

Direct-Reading
Instruments

Filter

Cyclone

Nominal Flow
Rate (LPM1)

Analytical
Method

None

25 mm QFF1
25 mm QFF
25 mm MCE1

N
Y
N

6.5
4.2
5

NMAM1 5040
NMAM 5040
NMAM 7402

Area

CPC1, DC1, and DustTrak

25 mm QFF
25 mm QFF
37 mm QFF
25 mm MCE

N
Y
Y
N

6.5
4.2
4.2
5

NMAM 5040
NMAM 5040
NMAM 5040
NMAM 7402

Outdoor
Background

CPC and DustTrak

25 mm QFF
25 mm QFF
25 mm MCE

N
Y
N

6.5
4.2
5

NMAM 5040
NMAM 5040
NMAM 7402

Personal (on each
worker)

1

Abbreviations: CPC, condensation particle counter; DC, diffusion charger; LPM, liters per minute; MCE,
mixed cellulose ester; NMAM, NIOSH Manual of Analytic Methods; QFF, quartz fiber filter

Information	on	exposure	factors	to	be	collected	
While conducting the site visits, information will be collected on aspects of the
workforce, which will permit the evaluation of factors that may affect risk (as confounders or
effect modifiers) in epidemiologic studies of CNT and CNF workers. Such information will
include number of workers directly (through active use) and incidentally exposed to these
materials (in the present and anticipated from near-future scale-up), an evaluation of potentially
confounding exposures for pulmonary and cardiovascular diseases, the use of personal protective
equipment that might attenuate exposure, and any employer-based medical surveillance of the
workforce. A more complete list of the factors to be evaluated includes the following:


Synthesis method, if a primary manufacturer

24

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers



Type and toxicity of raw materials and other potential co-exposures



Nominal aspect ratio of CNT or CNF (as reported by the company and measured
in bulk sample whenever possible)



Type of processes and tasks performed by employees



Form of CNT and CNF used—dry powder or liquid emulsion



Use of personal protective equipment



Length of shift



Time spent per shift working directly with CNT or CNF



Time spent per shift potentially indirectly exposed to CNT or CNF



Cleaning operations and waste disposal



Workplace medical surveillance

This information will be collected by discussing the work shifts and tasks with each worker,
supplemented with direct observations by the study team, evaluation of workplace records, and
discussions with the employer. An example data collection form for the field researchers to use
in collecting the data is given in Appendix III.
Data	analysis	methods	and	assignment	of	exposures	to	workers	
Exposure information will be collected for all workers included in the biomarker study,
and the information for these workers will be used as follows: geometric mean exposure
estimates from full-shift personal sampling will be developed for EC estimates. Currently, most
facilities are only operating for one shift per day but (for facilities with more than one shift), the
25

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

number of shifts to be sampled will be decided on a case-by-case basis depending on the number
of employees participating and number of shifts being worked.
Background EC concentrations will be subtracted from the occupational EC exposure
(but the background exposure will be retained as a potentially confounding exposure). The
proportion of the occupational exposure that is derived from CNT or CNF will be estimated
based on the EC measurements and the TEM-based, size-specific CNT/CNF structure counts,
using methods described in this protocol and in the draft NIOSH Current Intelligence Bulletin for
CNT and CNF (NIOSH 2010). The exposure factors mentioned above will be used to modify the
measured air concentrations, where appropriate. For example, a worker’s correct application of
personal protective equipment may be used to reduce the exposure estimated for the worker for
the epidemiologic components of the study.
For EC mass-based measurement data below the limit of detection (LOD), a value of half
the LOD will be employed in evaluating exposure-response relations with the cross-sectional
study, if the number of non-detectable samples is less than one-third of the total number for all
samples in the field study. If the number of non-detectable samples is one-third or more of the
total number, then only non-parametric (qualitative) analyses will be used to evaluate the EC
exposure metric (e.g., subjects would be classified as “exposed at greater than the detection
limit” or “possible exposure below the detection limit”). For microscopy-based samples, a value
of zero will be used for less-than-detectable levels (Dahm et al. 2012).
Other exposures co-occurring with the CNT or CNF in each workplace will be
summarized using mass concentrations, in the case of PAHs and metals, or as particle counts, for
dusts encountered in polymer production or the cutting or sawing of composite materials. The
26

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

direct-reading instrument data collected for each task and facility will be interpreted as a nonspecific measure of all nano- and ultrafine-sized particles, since particle number and mass
concentrations have not been found to be well correlated with CNT or CNF exposures in recent
NIOSH evaluations (Dahm et al., in press).
Temporal variability in the exposure measurements will be evaluated. The specificity of
each exposure measurement method (DRI, elemental carbon, size-specific structure counts)
affects the temporal variability. For example, temporal variability in elemental carbon and DRI
measurements is expected due to several seasonal and diurnal factors, such as seasonal or daily
peak automobile use and the burning of biomass. These issues will be addressed by collecting
indoor or outdoor background samples for the duration of sampling and subtracting the
background from the measured full-shift concentration for each worker. By contrast, CNT and
CNF structure counts are highly specific, and the potential for detectable background
concentrations is minimal.
To address temporal variability in actual CNT or CNF exposures, we will monitor each
worker (or, for unexposed or incidentally exposed workers, a single worker representative) for
two full shifts during our site visit and will use the average of the CNT structure counts and
background-corrected elemental carbon across the two-shift period. Similarly, for DRI (which
will be considered exposure to potentially confounding ultrafine particulates) the average of
mean exposures from two day-long monitoring periods will be calculated for each worker in the
study.
Given the cross-sectional study design, it is not possible to evaluate time-dependent
exposures or biomarker results. We will, however, assess the consistency of the exposure
27

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

findings for a given set of tasks across two years of monitoring, as each major task at each
facility has been monitored for elemental carbon and structure counts by NIOSH in the past
(Dahm et al. in preparation; Dahm et al. in press; Birch et al. 2011; Evans et al. 2010; Dahm et
al. 2012).
The task-specific area samples will not be used to estimate exposures and link with the
health data in the cross-sectional study. Rather, they will be used in the exposure assessment
study which is evaluating specific processes or tasks to determine which have the highest
potential for exposure. This information is of interest from an exposure assessment and control
perspective; moreover, it is likely that the task-specific estimates would be useful in developing
job-exposure matrices for future prospective or retrospective cohort studies.

II. Cross-sectional biomarker study
Rationale		
The results of the Phase I and Phase II feasibility investigations indicate that a crosssectional biomarker study is feasible for the following reasons:
1. In Phase I, we found there is a sufficient workforce size for CNT and CNF
facilities (estimated at about 500 in 2008-2009 and growing at an annual rate of
22%). During Phase II investigations in 2010 and 2011 at 12 CNT or CNF
facilities, we observed on average about 10 employees per facility who were
directly or indirectly potentially exposed to these materials.
2. Phase II found evidence of exposure (i.e., measureable concentrations of EC and
CNT or CNF structures) at most of the 12 facilities evaluated in the walk-through
survey, and a number were found to be above the draft NIOSH recommended
28

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

occupational exposure limit of 7 µg/m3 (Dahm et al. 2012). This exposure level,
over a 40-year working lifetime, is estimated to confer a lifetime excess absolute
risk of pulmonary fibrosis of 10% (NIOSH 2010; Kuempel 2011).
3. Sufficient exposure variability was observed across the workforce, in either Phase
II of this project (Dahm et al 2012) or in previous NIOSH evaluations of CNT and
CNF exposure (Birch et al. 2011; Methner et al. 2010; Evans et al. 2010).
4. Evidence from occupational studies of metal-exposed workers (Hamaguchi et al.
2008) or environmental studies of ultrafine particles associated with air pollution
(Peters et al. 2011) that pulmonary and cardiovascular effects may be effectively
studied using cross-sectional or short-term follow-up studies of biomarkers in
smaller numbers of participants.
Approach
The cross-sectional study will evaluate pulmonary function and biomarkers related to
exposure among workers at companies producing or using CNT or CNF. The biomarkers to be
evaluated are related to inflammation, oxidative stress, coagulation, cardiovascular disease,
fibrosis, and possibly cancer. We will evaluate each biomarker in whole blood, serum, or plasma,
for evaluation of systemic signatures of exposure or effect. In addition, where possible, we will
evaluate the same suite of biomarkers in a tissue (preferably, sputum) that is closer to the site of
initial exposure (Akpinar-Elci et al. 2005). This will allow us to distinguish localized from
systemic responses, an approach that has been recommended for study of nanomaterials (Li and
Nel 2011).

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

A questionnaire will be administered to the study participants (described further below)
to allow interpretation of the pulmonary function testing and biomarker analyses. Both the
biomarker sampling and questionnaire administration will be conducted concomitantly with the
occupational exposure measurements detailed in the Methods and Materials section I above.
Biomarkers	
Circulating Biomarkers of Inflammation
The 19 analytes in the inflammation category (Table 2) are traditional, well-described
indicators of pulmonary and systemic inflammation following a toxicant exposure. Specifically,
after bolus pulmonary exposure of MWCNT in a murine model, circulating levels of interleukin
(IL)-6, CXCL1 (murine analog of IL-8), eotaxin, IL-5, macrophage derived chemokine
(MDC/CCL22), and C-reactive protein (CRP) were acutely increased (Erdely et al. 2009a, 2011).
These mediators were a direct reflection of the ongoing pulmonary response. Apolipoprotein A-1
and A-II, alpha-2-macroglobulin, and complement C3 were increased in the serum 28 days
following a single exposure to MWCNT (Erdely et al. 2011). Many of these and other mediators,
including IL-1β, IL-6, IL-8, TNFα, CRP, and complement C3, have been implicated in human
and animal models of particulate matter exposure (Brook et al. 2010). Other biomarkers chosen
for inclusion are IL-18, MDC/CCL22 and granulocyte macrophage colony-stimulating factor
(GM-CSF). Similar to IL-1β, IL-18 is a cytokine that is activated by the NALP3 inflammasome.
The NALP3 inflammasome is induced by pulmonary injury, including particulate exposures such
as silica, asbestos, and CNT (Cassel et al. 2008; Dolinay et al. 2012; Dostert et al. 2008;
Hornung et al. 2008; Palomäki et al. 2011; Zhou et al. 2012). Increased IL-18 protein levels
measured systemically and in the lung and peripheral blood transcript expression of IL-18 have
been observed (Dolinay et al. 2012; Sager et al. 2012; Zhou et al. 2012). The markers
30

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

MDC/CCL22 and GM-CSF were elevated in the serum of firefighters soon after the World Trade
Center disaster and levels were associated with increased risk of airway obstruction in
subsequent years. After CNT exposure, both were induced in the lungs with MDC/CCL22 being
detected in the serum (Nolan et al. 2011).
Systemic inflammation can also be assessed by a complete blood count (CBC) with
differentials. Increased neutrophil counts following exposure have been found in welders, who
are exposed to a variety of ultrafine particles (Kim et al. 2005). Also, increased total white blood
cell count and neutrophils were found after a 2 hour exposure to concentrated ambient particles
(Brook et al. 2009).
Circulating Biomarkers of Oxidative Stress
Oxidative stress has been implicated as a mechanism for pulmonary fibrosis, cancer and
cardiovascular disease. Biomarkers that will be evaluated (Table 2) include glutathione
peroxidase (GPx) and superoxide dismutase (SOD) activity (Delfino et al. 2011). GPx was
altered in welders, and more recently both SOD and GPx activities were related to exposure in a
cross-sectional study of nanomaterials workers in Taiwan (Han et al. 2005, Liou 2011). The
marker 8-hydroxy-2’-deoxyguanosine (8-OHdG) has been examined in numerous occupations
and found to be associated with PAH, volatile organic carbon, and particulate exposure (e.g., Ma
et al. 2010, Wang et al. 2011). More recently, 8-OHdG has been evaluated and has been found to
be related to CNT exposure (Liou 2011). Similarly, 8-isoprostane, regarded as the gold standard
for the assessment of free radical-mediated lipid peroxidation (Delfino et al. 2011), is being
evaluated in nanomaterial workers (Liou 2011). Myeloperoxidase is an enzyme that is most
abundantly expressed in neutrophils. Circulating myeloperoxidase levels are associated with the
31

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

risk of coronary artery disease (Zhang et al. 2001) and increased levels in circulating neutrophils
have been shown following pulmonary nanoparticle exposure (Nurkiewicz et al. 2006).
Circulating Cardiovascular and Coagulation Biomarkers
Many of the inflammatory and oxidative stress serum cytokines and proteins described
above are also relevant to cardiovascular disease (e.g. IL-6, CRP). Additional markers include
intercellular adhesion molecule (ICAM)-1, vascular cell adhesion molecule (VCAM)-1,
endothelin-1, tissue plasminogen activator (t-PA), plasminogen activator inhibitor (PAI)-1,
fibrinogen, and von Willebrand factor (Table 2). Changes in PAI-1, t-PA, fibrinogen, and von
Willebrand factor were associated with particulate matter exposure (Panasevich et al. 2009,
Brook et al. 2010). In addition, PAI-1 was elevated following CNT exposure in a mouse model
(Erdely et al. 2009a, 2011). ICAM-1 and VCAM-1 are being utilized in other epidemiological
studies and were found to be associated with nanomaterial exposure (Liou 2011). Endothelin-1, a
vasoactive peptide, is linked to the progression of atherosclerosis. Increased endothelin-1 levels
were found in humans exposed to diesel exhaust (Lund et al. 2009) and in children with chronic
PM exposure (Calderón-Garcidueñas et al. 2007).
Evaluation of heart-rate variability was initially considered, as it has been shown to be a
potential transient effect of exposure in studies of persons exposed to sources of air pollution
[e.g., elevated particulate matter (PM) 2.5] (Davoodi et al. 2010; Link and Dockery 2010;
Weichenthal et al. 2011). Heart-rate variability has also been recently found to be correlated with
PM-2.5 from air pollution (Baccarelli et al. 2008), welding fume exposure (Fang et al. 2008), and
urinary biomarkers of PAH exposure (Lee et al. 2011). However, a recent randomized trial with
transient diesel exposure showed no association with heart-rate variability (Mills et al. 2011).
32

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

The facilities included in the feasibility and exposure assessment study also feature wide
variability in background and process-associated ultrafine particulate exposure (Dahm et al., in
press). Given the substantial uncertainty in interpreting heart-rate variability data for the
relatively low CNT and CNF exposure in the U.S. workforce against a backdrop of highly
variable (and often high) ultrafine particulate exposure (e.g., Evans et al. 2010), this measure will
not be included in the present study at this time. A static measure of heart rate will be collected,
however, as part of the overall basic medical examination.
Circulating Biomarkers of Pulmonary Fibrosis, Genetic Damage, or Cancer
Serum Krebs von den Lungen (KL)-6 glycoprotein has been found to be correlated to
extent of pulmonary fibrosis and inflammation (Yokoyama et al. 1998; Ichiyasu et al. 2012).
This biomarker has also been evaluated in workplaces with potentially hazardous exposures: KL6 has been used as a marker of early pulmonary fibrosis in studies of workers exposed to indium
or cobalt-tungsten carbide (Chonan et al. 2007; Hamaguchi et al. 2008; Kaneko et al. 2010). The
matrix metalloproteinases (MMPs) and their inhibitors, e.g., tissue inhibitor of metalloproteinase
(TIMP), are well documented to be involved in fibrosis with the potential for systemic evaluation
after particle exposure (Erdely et al. 2009a; Rosas et al. 2008, Lund et al. 2009). Osteopontin has
been suggested as a biomarker for asbestos-exposed individuals (Park et al. 2009). MWCNT
exposure was found to significantly increase pulmonary protein expression of osteopontin
(Erdely et al. 2009b). Serum levels of osteopontin were generally increased in those mice
exposed to MWCNT although the results were not always consistent. This may be the result of a
small sample size (Park et al. 2009) and the artificial nature of exposure conditions.

33

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Biomarkers of early potential carcinogenic effect will be evaluated in this study. Several
serum cytokines [e.g., IL-6, IL-8 and C-reactive protein (CRP)] have been shown to be
associated with lung cancer incidence (Brichory et al. 2001; Il’yasova et al. 2005; Kaminska et
al. 2006; Siemes et al. 2006; Heikkila et al. 2007; Allin et al. 2009; Pine et al. 2011). Pine et al.
(2011) found the latter two markers in combination to show the most robust association with
lung cancer several years in advance of diagnosis. Based on findings of interference of CNT and
CNF with mitotic spindle fiber formation and chromosomal aberrations in animal studies
(Sargent et al. 2009; Kisin et al. 2011), we will collect biospecimens (serum, nasal and sputum or
buccal cells) to be banked for future measurement of biomarkers of gross chromosomal
aberrations. The samples will be banked to permit their analyses, pending available future
funding, after all sites are visited and all specimen collection is completed.
The markers of DNA damage and impaired repair mechanisms to be analyzed include
single-cell gel electrophoresis (SCGE; comet assay) and multiplex fluorescence in situ
hybridization (M-FISH). SCGE has been used as a measure of strand break rejoining in
peripheral blood lymphocytes, where it was found to be associated with whole-blood
chromium(VI) in electroplating workers (Zhang et al. 2011). M-FISH has been found to be
associated with low-dose ionizing radiation exposure in studies of radiological technologists
(Sigurdson et al. 2008) and airline pilots (Yong et al. 2009) and has been evaluated in persons
exposed to radiation from the Chernobyl disaster (Hieber et al. 2011).
Additional Studies to determine biological effects of CNT or CNF exposure in workers
Leukocyte profiling is being increasingly used in research related to development of a
diagnostic tool (Dolinay et al. 2012; Scherzer et al. 2007). Following silica exposure in rats, a
34

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

specific blood gene expression pattern was observed that was a surrogate for pulmonary toxicity
(Sellamuthu et al. 2011). Previous work has shown that CNT exposure is able to induce
leukocyte activation as determined by whole blood gene expression changes (Erdely et al.
2009b). Ongoing inhalation studies in animals exposed to MWCNT are exploring the possibility
of a molecular signature that will indicate exposure. Because of the potential applications of
expression profiling in leukocytes, whole blood will be collected and RNA will be isolated and
banked. Further analysis will depend on available funding and results from the animal studies.
In conjunction with the circulating biomarkers measured above, we hypothesize that,
among workers exposed to CNT or CNF, the ability for circulating leukocytes to respond to a
secondary stimulation may be compromised. An animal model testing this hypothesis showed
decreased responsiveness of circulating leukocytes following metal-rich particulate matter
exposure (Hulderman et al. 2012). These results were observed without significant changes in
circulating inflammatory cytokine levels, indicating that some circulating markers lack
sensitivity, or that a secondary challenge may be needed for decreased responsiveness to be
evinced. The human leukocyte response to chronic CNT or CNF exposure may alter cytokine
and chemokine production, suggesting the potential for immune dysfunction and chronic
inflammation. To evaluate this hypothesis, whole blood cells for workers in the study will be
incubated in a null (no stimulant) and stimulant tube for 24 hours, followed by supernatant
collection. The analysis will measure the changes in 46 analytes (Table 3), the contractor’s
specific panel for this technology. Since the analyte measurements are made after ex vivo
manipulation, the changes in analyte values by themselves do not have any clinical relevance for
this study. These analytes are chosen simply as responsive proteins that are likely to change
following stimulation. The change in these proteins (null vs. stimulated) will be compared to
35

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

level of exposure and therefore serve as a potential biomarker of exposure. This approach will
add power to the cross-sectional design of this study in that each individual will serve as their
own baseline (null tube), eliminating a major source of variability among individuals.
Additional biomarker evaluation will be performed using a translational in vitro model
(Channell et al. 2012). The methodological design tests the capacity of the collected plasma (or
serum) from workers enrolled in the study to activate primary human coronary artery endothelial
cells (hCAEC). In a controlled human exposure to diesel, plasma from exposed individuals
resulted in increased cardiovascular disease related markers produced by hCAEC (Channell et al.
2012). The changes in these mediators in the cell line serve as evidence of circulating factors in
the plasma (or serum) of exposed workers capable of inducing endothelial activation. This design
will be useful in determining potential effects, in addition to those described above in the section
on circulating coagulation and cardiovascular biomarkers, on the cardiovascular system of
workers exposed to CNT or CNF.
Recruitment	of	Participants	for	Exposure	Assessment	and	Epidemiologic	Study		
The source population consists of facilities producing, using or distributing CNT or CNF
at above R&D scale in the U.S. The population was enumerated in the Phase I feasibility study
and has been augmented since then during Phase II using several additional sources (e.g.,
registrations with the US Environmental Protection Agency to manufacture or use CNT or CNF).
There are currently at least 66 eligible companies. A sample size of at least 100 workers (based
on the results of power analyses) will be sought. Given the small average company size, at least
10 companies will need to be included in the study to achieve this number. As described in
Methods and Materials Section I above, these will be selected from among the companies
36

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

included in the exposure assessments conducted in FY2010 through FY2012, or previously
visited by the NIOSH EID or DART field teams. The criteria for selection of a facility for an
invitation to join the study will be:
1) Potential for elevated (near or above the current NIOSH draft REL of 7 µg/m3 as EC)
CNT and CNF exposure (based on previous NIOSH site visits);
2) Number of workers routinely exposed, directly and indirectly, to CNT or CNF;
3) Representativeness of site activities across the spectrum of primary and secondary
manufacturing and distribution of CNT and CNF;
4) Lack of substantial exposure potential to other agents (not part of the manufacturing
process) that may cause adverse pulmonary effects, such as cancer (e.g., some of the
substances in Table 4). For example, facilities with very high indoor background
concentrations of total particulates due to proximity to a busy highway may receive
lower priority for inclusion.
Eligible companies will be ranked according to these criteria and will be invited to participate in
the order of highest to lowest priority. NIOSH project staff will travel with the Field Evaluations
and Response Vehicle (FERV) to each location. The FERV provides a clean, private space for
conducting questionnaire administration, medical examinations, spirometry, sputum collection or
induction, and biospecimen collection.
The workforce involved in CNT and CNF production and use is still relatively small.
Power calculations conducted for forced vital capacity (a measure of possible fibrotic lung
changes) and biomarker measurements suggest that 100 study subjects will be required to
observe possible impacts suggested from other studies (see “Power Analysis” section). Because
37

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

statistical power will be maximized through the use of regression techniques (rather than
comparison of an “exposed” to a “control” group), it is necessary to include workers who have
minimal or no exposure as well as workers who have regular exposure to CNT or CNF.
Therefore, within each company, all workers will be invited to participate in the cross-sectional
study, which involves both biomarker and exposure assessments, and will be given a fact sheet
about the study (Appendix I). Workers may decline to participate in any aspect of the study,
without jeopardizing their ability to participate in the remaining aspects of the study. For each
participating facility, workers agreeing to participate will be administered an informed consent
document while NIOSH researchers are on-site to carry out the study (see Appendix I) prior to
measuring exposure, collecting any biospecimens, conducting physical examinations, or
administering the questionnaire. The lead project officers will be available at all times that the
study is being conducted to answer questions from workers or company representatives about the
study.
Biomarkers	to	be	analyzed	

	

The biomarkers of exposure or early effects to be measured, the biomarker target, and the
specimen matrix are detailed in Table 2. The rationale for inclusion of these biomarkers is
described above. Most biomarker analyses will be conducted by a contract laboratory, using
existing contracts at NIOSH-HELD, NIOSH-DSHEFS, or NIOSH-DART. A few of the
biomarker analyses (IL-18, SOD activity, GPx, KL-6, 8-isoprostane, 8-OHdG) will be conducted
by NIOSH-HELD.

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Sample	Collection	and	Preparation	
Given the nature of tests to be done, a specific protocol and order for the blood draw
tubes for biomarker analysis is necessary. A total of 44 mL will be collected. The order of the
tubes for the blood draw will be as follows:
1)

Serum separator tubes (2) – 2 tubes of 5 mL each (for serum to be sent to NIOSHHELD)

2)

Lithium heparin (1) – 4 mL (whole blood collection for ex vivo stimulation.
Collected supernatants will be frozen and sent to NIOSH-HELD. A contract
laboratory will analyze for a specific analyte panel indicated in Table 3)

3)

EDTA (3) –2 tubes of 8.5 mL each (for plasma to be sent to NIOSH-HELD and
contract laboratory), 1 tube of 3 mL (whole blood for CBC at reference lab)

4)

PAXgene (4) – four tubes of 2.5 mL each (whole blood collected into a
stabilization agent, frozen, and sent to NIOSH-HELD for RNA isolation)

Samples will be treated in the following manner. Serum tubes will be inverted 5 times
and allowed 30 min to clot. Plasma tubes will be inverted 10 times and immediately spun down.
The immediate spin is recommended for oxidative stress biomarkers. All serum and plasma
samples to be fractionated will be spun at 1000 g for 10 min at 4ºC then aliquoted and frozen.
The 3 mL EDTA tube of whole blood for the reference lab will be inverted 10 times and stored
at room temperature until sent for analysis at the end of the day. The lithium heparin tubes will
be inverted 10 times and 1 mL of whole blood will be transferred to each TruCulture stimulation
tube (1 null and 1 stimulant tube) immediately after the blood draw. The TruCulture tubes are
inverted to mix and then incubated at 37ºC for 24 hours. At 24 hours, the supernatants will be
39

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

collected, frozen at -20 ºC, and banked at NIOSH-HELD for further analysis. The PAXgene
tubes are drawn last due to the stabilization agent contained within the tubes. The tubes are
inverted 8-10 times after the blood draw and then placed at -20ºC. All frozen samples will be
sent overnight on dry ice to NIOSH-HELD pending further analysis.
Sputum specimens will be treated with a mucolytic agent [Sputolysin® or dithiothreitol
(DTT)] and incubated at 15 minutes in a shaking water bath set at 37ºC, centrifuged at
approximately 500 x g, and separated into an acellular and cellular fraction within one hour of
collection. The acellular fraction will be frozen at -40ºC in the field and shipped on dry ice to the
HELD laboratories, where it will be analyzed along with the associated serum specimens by
either HELD or the contract laboratory (Table 2).
The cellular fraction will be used for future FISH analyses (pending available funding),
and to examine using dark-field microscopy for evidence of CNT or CNF in the cellular matrix.
Sputum quality will be evaluated (at NIOSH or by a contractor) by counting the proportion of
total cells that are squamous epithelial cells, using <80% as an evaluation point. The cellular
pellet will be resuspended in an alcohol-based fixative/cryoprotectant (Saccomanno fluid or
methanol) prior to shipment on ice to a HELD laboratory (at least 50% preservative
concentration). After arrival, a cytospin of the cell pellet is prepared on ultrasonically cleaned,
laser cut slides (Schott North America, Inc, Elmsford, N.Y. 10523) to avoid nanoparticle
contamination from the ground edges of traditional slides. For analysis by FISH and dark-field
microscopy, approximately 3,000 cells per slide will be viewed. As typical sputum samples
contain approximately 1 million cells, only a small fraction of the sample is necessary for the
FISH and CNT/CNF microscopic analysis. A cytospin of the acellular fraction will also be
prepared and examined for potential CNT or CNF in the sputum matrix outside the cells.
40

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

To enhance the contrast of nanomaterials for dark-field microscopy, cytospin slides are
stained with Sirius Red. Sirius Red staining consists of immersion of the slides in 0.1%
Picrosirius solution (100 mg of Sirius Red F3BA in 100 ml of saturated aqueous picric acid, (pH
2) for 1 hour followed by washing for 1 minute in 0.01 N HCl. Sections are then briefly
counterstained in freshly filtered Mayer’s hematoxylin for 2 minutes, dehydrated, and
coverslipped.

41

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Table 2. Description of circulating biomarkers to be measured for early effect of exposure†.
Marker
Inflammation
Interleukin-1β§
Interleukin-2§
Interleukin-4§
Interleukin-5§
Interleukin-6§
Interleukin-8§
Interleukin-10§
Interleukin-12p70§
Interleukin-18*
Interleukin-6 receptor beta§
Alpha-2-Macroglobulin§
Complement C3§
C-Reactive Protein§
TNFα§
GM-CSF§
Macrophage derived chemokine§
Eotaxin-1§
Apolipoprotein A-I§
Apolipoprotein A-II§
CBC with Differential§
Oxidative stress
Myeloperoxidase§
SOD activity*
GPx activity*
8-OHdG*
8-isoprostane*
Cardiovascular / Coagulation
ICAM-1§
VCAM-1§
Endothelin-1§
Fibrinogen§
von Willebrand Factor§
PAI-1§
t-PA§
Cancer / Fibrosis
KL-6*
MMP-1§
MMP-2§
MMP-7§
MMP-9§
TIMP1§
Osteopontin§
Genetic Damage
Comet Assay*¶
M-FISH*¶

Sample Matrix

Rationale

Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Whole Blood

These 19 analytes are markers of inflammation. As a
group, the analytes chosen represent a thorough early
screen of effect for exposure to CNT/CNF. These
markers have been shown to be increased in animal
models of CNT exposure or associated pulmonary
exposure studies.

Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum

These markers will indicate the presence of local and
systemic oxidative stress. These markers have been
indicated following pulmonary toxicant exposures and/or
are being analyzed in other nanomaterial epidemiological
studies

Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum

These markers represent a group of cardiovascular and
coagulation specific markers. The analytes have been
increased following pulmonary inflammatory exposures.

Serum & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum
Plasma & Sputum

These analytes represent markers of fibrosis and/or
cancer. KL-6 and MMPs correlate with pulmonary
fibrosis. Some can be increased in incidences of lung
cancer.

Serum and either sputum,
nasal or buccal cells
Serum and either sputum,
nasal or buccal cells

Marker of DNA strand breaks and misrepairs; found to
be elevated in Taiwanese CNT workers.
Marker of chromosome translocations

Increased neutrophils following concentrated ambient
particles or welding fume exposure.

§Analysis to be conducted by NIOSH contractor
*Analysis to be conducted by NIOSH-HELD ¶Future funding
† All except GPx and SOD expected to increase with CNT or CNF exposure. GPx and SOD expected to decrease.

42

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Table 3. Panel for blood stimulation study, to be analyzed by NIOSH contractor.

Alpha-1-Antitrypsin
Beta-2-Microglobulin
Complement C3
Eotaxin-1
Ferritin
Granulocyte-Macrophage Colony-Stimulating
Factor
Intercellular Adhesion Molecule 1
Interleukin-1 alpha
Interleukin-1 receptor antagonist
Interleukin-12 Subunit p40
Interleukin-15
Interleukin-2
Interleukin-3
Interleukin-5
Interleukin-7
Macrophage Inflammatory Protein-1 alpha
Matrix Metalloproteinase-2
Matrix Metalloproteinase-9
Stem Cell Factor
Tissue Inhibitor of Metalloproteinases 1
Tumor Necrosis Factor beta
Vascular Cell Adhesion Molecule-1
Vitamin D-Binding Protein

Alpha-2-Macroglobulin
Brain-Derived Neurotrophic Factor
C-Reactive Protein
Factor VII
Fibrinogen
Haptoglobin
Interferon gamma
Interleukin-1 beta
Interleukin-10
Interleukin-12 Subunit p70
Interleukin-17
Interleukin-23
Interleukin-4
Interleukin-6
Interleukin-8
Macrophage Inflammatory Protein-1 beta
Matrix Metalloproteinase-3
Monocyte Chemotactic Protein 1
T-Cell-Specific Protein RANTES
Tumor Necrosis Factor alpha
Tumor Necrosis factor receptor 2
Vascular Endothelial Growth Factor
von Willebrand Factor

43

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Table 4. IARC Group 1 carcinogens shown to cause lung cancer, non-Hodgkin lymphoma (NHL), chronic
lymphocytic leukemia (CLL), mesothelioma, or nervous system cancer.

Group 1 IARC carcinogen

Site for which evidence is
sufficient or limited

Likelihood of exposure in
CNT/CNF industry

Alpha particle emitters

Lung

Low

Aluminum production

Lung

Low

Arsenic

Lung

Low

Asbestos

Lung, mesothelioma

Low

Benzene

CLL, NHL

Benzo(a)pyrene

None*

High

Beryllium

Lung

Low

Bis(chloromethyl)ether/
chloromethyl methylether

Lung

Low

1,3-Butadiene

CLL, NHL

Low

Cadmium

Lung

Moderate

Chromium(VI)

Lung

Moderate

Coal gasification, coke
production, coal tar pitches

Lung

Low

Diesel exhaust

Lung

Moderate

Dioxins & furans

Lung, NHL

Low

Erionite

Mesothelioma

Low

Ethylene oxide

CLL, NHL

Low

Formaldehyde

CLL

Low

Iron & steel founding

Lung

Low

Nickel (non-metallic)

Lung

Low

Occupation as a painter

Lung, mesothelioma

Low

Rubber manufacturing industry

CLL, lung, NHL

Low

Silica (crystalline)

Lung

Moderate

Soot

Lung

High

Sulfur mustard

Lung

Low

Strong inorganic acid mists

Lung

Moderate

Talc

Lung, mesothelioma

Low

Tobacco smoking

Lung

High

X- or γ-radiation

Lung, nervous system

Low

*IARC designation is based on mechanistic information alone

44

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Medical	examination	methods		
After obtaining informed consent, the medical examinations to be carried out for each
participant in the cross-sectional study include the following:
1. Administration of health questionnaire (see information below)
2. Measurement of height and weight [to interpret spirometry testing and provide
accurate body mass index (BMI)]
3. Waist circumference (to use as a possible indictor of metabolic syndrome, which
may be useful in interpreting cardiovascular disease biomarkers).
4. Measurement of heart rate and blood pressure (systolic and diastolic individually).
5. Pulmonary function testing via spirometry
6. Collection of biospecimens for biomarker analyses (see information below)
Medical and epidemiological professionals with NIOSH will conduct medical examinations
(physician), administer the questionnaire, carry out the pulmonary function testing using
spirometry and biological specimen sampling (blood, as well as sputum, nasal or buccal cells), as
described below.
Spirometry	methods	
Spirometry will be conducted using procedures outlined by the American Thoracic
Society (ATS)-European Respiratory Society (ERS) (Miller et al. 2005). All spirometry
examinations will be conducted by technicians who have passed a NIOSH-approved spirometry
training course, have had several hundred hours of experience in conducting spirometry testing,
and will be overseen by a Principal Investigator with specialized training in the interpretation of
spirometry data.
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Before beginning spirometry examination, each subject will be asked about medical
conditions that might be contraindications for use of spirometry, taken from the most recent
survey conducted by the National Health and Nutrition Examination Survey (NHANES) (Table
5). Inquiry will also be made of medical conditions that lead to precautions in the use of
spirometry (Table 5). Questions about chest, abdominal, oral and facial pain will be asked by the
spirometry technician just before beginning the procedure to ensure that the proper precautions
may be taken during the test. Age, race, and sex will be asked of each subject, and height will be
measured (with the subject in stocking feet) to the nearest half-centimeter, using a stadiometer.
Questions about cigarette smoking will also be included, to assist in interpretation of spirometry
patterns.

Table 5. Spirometry safety exclusion or precaution items for adults (age 16-79) (adapted from
NHANES 2008).
Screening item

Screening level

Precaution advised

Eye surgery in the last 3 months

Exclusion

Exclusion

Chest or abdominal surgery in last 3 months

Exclusion

Exclusion

Self or household member tuberculosis exposure

Exclusion

Exclusion

History of aneurysm or collapsed lung

Exclusion

Exclusion

History of detached retina

Exclusion

Exclusion

Heart attack or stroke within the past 3 months

Exclusion

Exclusion

Presence of respiratory infection

Precaution

Test at end of day;
decontaminate tubing
and use gloves

Cystic fibrosis

Precaution

Test at beginning of day
to minimize chance of
infection

Chest or abdominal pain of any cause

Precaution

Monitor carefully to
ensure test not too
demanding

Oral or facial pain exacerbated by mouthpiece

Precaution

Use alternative
mouthpiece shapes

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Spirometry methodology will be conducted using the steps outlined in the procedures
document for the NHANES survey (NHANES 2008). In brief summary, a volume-based
spirometer will be used for all spirometry testing (OMI/Sensormedics 1022), in order to
maximize measurement accuracy (expected to be better than 1.5%). Diligent and consistent
coaching will be used by the spirometry technician to ensure maximum inspiration and forced
expiration during each test.
Standard acceptability criteria for satisfactory start and end of spirometry tests will be
used (Miller et al. 2005). More specifically, an acceptable test start must not involve excessive
hesitation (evaluated as a BEV ≥5% of FVC or greater than 150 mL) or cough in the first second.
In addition, a rise time to peak flow of <120 msec and volume at peak flow at <35% of FVC,
will be required. The end-of-test criteria to be used are either a) the subject cannot or should not
continue further exhalation (due to discomfort or the appearance of approaching syncope) or b)
the volume-time curve shows a change-in-volume of less than 0.025 L for at least 1 second and
the subject has tried to exhale for at least 6 seconds (i.e., an acceptable plateau was reached, as
determined by the spirometry software). Tracings that do not meet acceptability criteria but that
do provide useable information will be retained and used in relevant analyses.
At least three (and up to eight) spirometry maneuvers will be conducted per subject,
based on three tests meeting criteria for acceptable start and end of test, and acceptable
repeatability among the FVC and FEV1. The technician will employ the ATS-ERS criteria
(Miller et al. 2005) for repeatability: the two highest usable FVCs, and the two highest usable
FEV1s will each differ by less than 0.15 L. Although not required by ATS-ERS criteria, a peak
flow that differs by no more than 20% between the two highest values will be used as an
additional measure of repeatability.
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Software to be used will comply with recommendations of the ATS-ERS (Miller et al.
2005), and will use sex-, height-, and race-specific predictive values for lung function metrics
such as FEV1 and FVC (Hankinson et al. 1999). Quality control checks to be used to test
accuracy of volume, lack of leaks, volume linearity, time, and other variables will be in
accordance with ATS-ERS recommendations for volume spirometers (Table 3 of Miller et al.
2005).
An anti-contamination plan will be used, consisting of the following:
1. Use of single-use mouthpieces with a high-quality bacterial and viral filter
2. Single-use nose clips
3. Flushing of spirometer with room air between subjects
4. Rotation of spirometer tubing to keep dry
5. Disinfection of tubing between subjects
6. Waiting period of at least one-half hour between subjects
7. Washing hands between subjects
8. Avoiding contact with contaminated surfaces
Spirometry software will be used to calculate relevant parameters, including backextrapolated volume (BEV), forced expiratory volume in the first second (FEV1) and forced vital
capacity (FVC), percent predicted, FEV1/FVC% (using the largest valid FEV1 and FVC, even if
from different tests). All values will be corrected for pressure differences at body compared to
ambient temperature. The interpretation software module developed by McKay will be used to
assist in measuring compliance of the test performance with ATS-ERS standards, and in
providing interpretations of observed spirometry patterns. Values will be compared to the “lower
limit of normal”, based on age-, height-, sex- and (for white, African-American, and Hispanic
subjects) race/ethnicity-specific NHANES population data from Hankinson et al. (1999). For
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

subjects of East Asian descent, an adjustment factor of 0.94 based on white subjects will be used,
in accordance with ATS-ERS recommendations, and for those of South Asian descent, the value
for white subjects will be used unadjusted (Miller et al. 2005; Hankinson et al. 2010; R. McKay,
University of Cincinnati, personal communication).
For the research study, lung function patterns resulting from spirometry will be
interpreted using a universal flow diagram, as developed by McKay and Horvath (1994) (Fig. 1).
Restrictive lung patterns will be identified as a FEV1/FVC above the lower limit of normal
(LLN; the lower one-sided confidence limit on the predicted age, sex, race/ethnicity, and heightadjusted value), but with a LLN for FVC below the LLN. Obstructive lung patterns will be
identified as an FEV1/FVC below the LLN, an FVC above the LLN, and the FEV1<95% of
predicted (the latter accounts for some thin, healthy persons with large FVC but normal FEV1).
The FEF25-75 (obtained from the volume-time tracing of the curve that gives the largest sum of
the FEV1 and FVC) that is below the LLN will be used to as a more sensitive measure of
possible early obstructive lung patterns, among those with otherwise normal FEV1/FVC and
FVC (McKay and Horvath 1994).
In reporting results to the study participant, a slightly more conservative (but more widely
accepted and standardized) clinical interpretation will be utilized (Pellegrino et al. 2005), to
minimize the false positive rate and the chance of unduly alarming subjects about possible
obstructive or restrictive lung disease when it does not exist.

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Figure 1. Universal flow diagram for interpretation of spirometry (adapted by R. McKay from McKay and
Horvath 1994).

FEV1/FVC < LLN?

	
	
	
Yes
	
	
	
	
	
	
	
	 FVC < LLN?
	
	
	
Yes
	
	
	
	
	
	
	
	

No

No

No

FVC < LLN?

FEF25-75 < LLN?

Yes

Yes

A. Normal

B. Possibly
normal, or
small or early
airway obstr.
C. Restrictive

No

FEV1 < 95% pred?

No

Yes

D. Probably
Normal
E. Airway
Obstruction
F. Mixed
Obstructive
Restrictive

Biospecimen	collection	methods	
Universal precautions will be observed through all biospecimen collection, to minimize
the possibility of infectious disease communicability. These precautions will consist of use of
nitrile gloves that are discarded after each study participant is processed, lab coats, the frequent
washing of hands, and the use of medical waste and sharps disposal containers.
All biological specimens (blood, sputum, nasal and buccal cell swabs) will be collected at
the middle or end of the shift for which the PBZ exposure measurements were collected. Two
specimen sample types will be collected: one for analyses to be conducted within a matter of
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

days (e.g., CBC with differential) and one for storage to conduct later analyses (e.g., cytokines
and oxidative stress biomarkers, as well as cytogenetic markers). Biospecimens to be analyzed
immediately will be sent via overnight mail to contract laboratories for analysis. Samples to be
stored for future analyses will be prepared in the field as described in section “Sample Collection
and Preparation”, and will be stored in a -20°C freezer in the FERV. These specimens will then
be sent to NIOSH-HELD and will be stored in an ultra-low temperature (-80°C) freezer,
according to National Cancer Institute’s “Best Practices for Biospecimen Resources”
(http://biospecimens.cancer.gov/bestpractices/to/bcpsrd.asp).
Whole blood will be collected from each volunteer study participant after the spirometry
and sputum collection are completed. There will be a total of 44 mL collected from each
volunteer. This represents no more than about 1% of blood volume. Each study participant
undergoing phlebotomy will be offered water or juice and a snack (e.g., crackers) after the blood
withdrawal.
Induced sputum will be collected for each consenting subject who does not have
contraindications or active respiratory infection, using the procedure outlined in an induced
sputum evaluation among popcorn manufacturing workers (Akpinar-Elci et al. 2005), modified
to use isotonic saline at lower nebulizer output rate, which has been shown to reduce the
occurrence of side effects while producing sputum of acceptable quality (Loh et al. 2004). In
brief summary, participants will first be screened to determine whether they meet the eligibility
criteria for induced sputum. Contraindications for sputum induction include beta-blocker use,
cardiac arrhythmia or angina, recent (within past three months) surgery or pneumothorax,
pregnancy, or baseline FEV1 <60% of predicted. Consenting participants who are eligible will
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

inhale for 12 minutes in total a sterile isotonic saline solution produced by a compressed-air
generated nebulizer. Study participants will breathe in the mouthpiece and then, every two
minutes, will be asked to remove the mouthpiece, spit saliva into a cup, take a deep breath
through the mouthpiece and then cough the full breath along with sputum into a sputum cup.
After six minutes of breathing through the nebulizer, the spirometry technician will measure the
FEV1 of the participant (once if within 80% of baseline and twice if less than 80% of baseline).
If two consecutive measurements of FEV1 indicate a 20% drop (compared to baseline), then the
sputum induction procedure will be halted and the participant administered a bronchodilator.
If sputum cannot be induced, or its induction is contraindicated, or the participant does
not consent to sputum induction, the technician will collect buccal and nasal swipe samples of
material from the inside of the study participant’s nose and cheek, respectively. Two separate
swabs will be used for this procedure. A sterile swab will be used to brush the inside of one
cheek or both nostrils for 10 seconds. The swab specimens will be dissolved in a cell-specific
medium and processed for biomarker analyses.
Samples will be de-identified in the field: the worker will be assigned a dummy
identifying number, based on his or her PBZ sample. This number will be used to identify
biological specimens in all analyses. The key to identify the worker will be retained by the
project’s Principal Investigators and will be protected from disclosure according to NIOSH’s
standard procedures under the Privacy Act.

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

It is unlikely that any medical emergencies will result from the spirometry or medical
examinations, or from the collection of blood, nasal, or buccal cells. Sputum induction with
isotonic saline carries a very small risk of induction of bronchial spasm or reduction of FEV1
[2.7% for hypertonic saline in a recent study of biomarkers of airways disease in a group of
microwave popcorn manufacturing workers (Akpinar-Elci et al. 2005), and 0% in an evaluation
among 16 subjects who underwent sputum induction with isotonic saline (Loh et al. 2004)]. A
metered-dose inhaler of a beta-adrenergic receptor agonist (albuterol, e.g., Proventil)
bronchodilatorwill be available to counteract any bronchospasm that occurs. A NIOSH physician
who is board-certified in Internal Medicine and/or Occupational Medicine and has extensive
experience in carrying out medical procedures in field studies will be present onsite during these
procedures to administer the bronchodilator if necessary and assist in handling any adverse
reactions. One of two NIOSH physicians (either Marie De Perio, MD, or Douglas Trout, MD,
MHS) will accompany the study team on each site visit. Dr. De Perio is a licensed practicing
physician board-certified in Internal Medicine and Infectious Diseases. Dr. Trout is also a
licensed practicing physician and is Board-certified in Internal Medicine and Occupational
Medicine. Drs. De Perio and Trout have each served as lead physician on many field
investigations at NIOSH. If one of these physicians is not available to participate in a site visit,
then a NIOSH physician with similar qualifications will be identified to join the team, and a
request to add the physician will be made to the NIOSH Institutional Review Board (IRB) via
email. In addition, the project officers are trained by the American Red Cross in Community First
Aid and Safety, including CPR. All members of the testing team will be provided with a copy of
the emergency plan (Appendix IV).

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Questionnaire	administration	
In order to determine if the study participant has any contraindications for spirometry or
sputum induction, and to properly interpret the spirometry results as well as biomarkers of
exposure and early effect, a questionnaire (see Appendix II) will be administered by NIOSH
investigators to study participants after informed consent is obtained. The questionnaire will
begin with the American Thoracic Society’s 1978 Adult Questionnaire
(http://www.cdc.gov/niosh/atswww.txt) and will include or be supplemented with the following
information: medical and smoking histories, exposure to passive (secondhand) smoke, exposures
to agents that may cause adverse pulmonary effects (e.g., see Table 4), and history of diseases or
conditions that may interfere with the interpretation of the biomarker results. For example,
questions regarding dyspnea (resting or under exertion) or weight loss (Kaneko et al. 2010) are
necessary for interpreting spirometry or certain biomarkers as possible early indicators of
pulmonary fibrosis; other collagen diseases such as cystic fibrosis, scleroderma, hepatitis C,
which might cause elevations in some of the fibrosis biomarkers. The NIOSH physician on the
field study (Dr. Marie De Perio or Dr. Douglas Trout) will make the determination regarding the
subject’s eligibility for spirometry and sputum induction, based on the questionnaire responses
and the results of the medical examination, evaluated against the contraindications for
spirometry.

EPIDEMIOLOGIC ANALYSIS
All statistical analyses will be conducted using the latest version of SAS (SAS, Inc, Cary,
NC). Statistical analyses such as multiple linear regression models will relate different aspects of
measured CNT and CNF PBZ exposure (e.g., respirable mass concentration, particle
54

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

concentration and surface area) to the outcome measures, which include spirometry
measurements (e.g., FVC as percent of predicted), systolic and diastolic blood pressure, and
potential biomarkers of early effect. These models will be adjusted for covariates such as age,
gender, race, other workplace exposure, relevant exposure factors, and smoking history.
Appropriate methods will be used to ensure the validity of the regression models employed (e.g.,
log-transformations of exposure or outcome data to ensure normality of the model residuals and
good-fitting exposure-response associations). Because of the large number of biomarkers
involved, consideration will be given to appropriate methods for adjusting for multiple
comparisons.
For dermal exposure, the exposure-response analysis approach will be similar to that
described above to evaluate associations between PBZ exposures and health outcomes and
biomarkers, except that analyses will exclude the markers of early pulmonary fibrosis (e.g., KL6) and measures of lung function.
For the leukocyte stimulation study, for each of the 46 evaluated biomarkers (b), a
stimulation effect for the ith individual (StimEffi) will be calculated as follows:
StimEffbi = ([Stimulated_cellsi]b – [Null_cellsi]b)/Total_leukocytesi
Where [Stimulated_cellsi]b is the biomarker b concentration in the supernatant from
stimulated cells for individual i;
[Null_cellsi]b is the biomarker b concentration in the supernatant from null (unstimulated)
cells for individual i;
Total_leukocytesi, the total number of leukocytes for individual i.

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Normalization to total leukocyte count is used for each individual because the stimulation
is based on a consistent volume (1 mL) of whole blood instead of leukocyte number, and
exposure to CNT or CNF may result in an increase in total leukocyte count (e.g., Hulderman et
al. 2012), which is not of interest in this study.
The StimEff variable calculated for each biomarker will be used as a dependent variable
in a multiple linear regression model evaluating the association with each individual’s CNT or
CNF exposure level (based on mass, particle concentration, or surface area), after adjusting for
potential confounders such as age, gender, race, other workplace exposure, relevant exposure
factors, and smoking history. Consideration will be given to grouping the biomarkers into
classes, based on presumed mechanism or type of effect (e.g., inflammatory, oxidative stress,
coagulation, immune), to determine whether similar biomarkers elicit similar response patterns.

POWER ANALYSIS
A power analysis was conducted for the FVC as a percent of predicted (as a measure of
possible restrictive lung disease), and for biomarkers that have been evaluated in studies of other
potentially hazardous exposures. In the design of the present study, multiple linear regression is
proposed (after Cohen 1988) to evaluate the relation between CNT or CNF exposure and the
spirometry or biomarker result, controlling for several potential confounders, including age,
race/ethnicity, gender, smoking and possible exposure to sources of non-engineered
nanomaterials or other potentially hazardous agents.
Power analysis calculations for FVC were based on simulations of effect sizes in SAS,
followed by power calculations of the simulated effect size using Power Analysis and Sample
Size Software (PASS 11; NCSS Statistical Software, Kaysville UT). For the biomarker analyses,
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

just PASS 11 software was used. For all sample size analyses, a Type I error rate (α) of 0.05 and
a power (1-β) of 0.8 were assumed. For simplicity, the exposure metric employed for FVC power
analyses was background-corrected EC concentration (µg/m3) as an eight-hour TWA, measured
in at least one PBZ sample for the participant or his or her group representative. Data from the
Phase II feasibility study (Dahm et al. 2012, supplemented with the related NIOSH research of
Birch et al. 2011 and Evans et al. 2010, as well as more recent information) were used to
estimate exposure distributions. The exposure distribution for the entire workforce group was
assumed to be right-skewed, with 30% having an assigned exposure value of zero, 20% having
exposure values between 0.5 and 2.0 µg/m3 (mean 1.25 µg/m3), 20% having exposure values
between 2.0 and 4.0 µg/m3 (mean 3.0 µg/m3), 20% having exposure values between 4.0 and 8.0
µg/m3 (mean 6.0 µg/m3), and 10% having exposure values of greater than or equal to 8.0 µg/m3
(assumed mean 12 µg/m3).
For the spirometry simulation calculations, a reduction of FVC (as a percent of age-,
race/ethnicity-, gender- and height-predicted) was assumed to be 1% for each increase of 1
µg/m3 of background-corrected EC exposure. Unexposed (non-smoking) subjects were assumed
to have FVCs averaging 100% of predicted, with a standard deviation of 10%. This standard
deviation was also assumed to apply at the higher EC levels. It was assumed that smoking and
exposure to other dusts or non-engineered nanoparticles would be adjusted-for as a confounder
(and would together explain 30% of the variability in FVC), but it was also assumed that there
would be no effect modification by these factors. In simulations using the exposure and effect
scenario given above for the EC distribution in the studied group and its association with FVC
decrement, a mean R2(T) of 0.12 is found (standard deviation=0.053) (Fig. 2).
For a multiple regression model controlling for two confounding variables (smoking and
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

exposure to non-CNT dusts or PM) that together result in a coefficient of multiple determination
from “control variables” [R2(C)] of 0.30, a sample size of 41 would give a power of 0.80 to
detect an increase of 0.12 in the coefficient of multiple determination [from “test variables”,
R2(T)] (Fig. 3). Although power to detect a 1% drop in FVC per 1 unit increase in EC might be
adequate with 41 subjects, the estimate of R2(T) of 0.12 is quite variable as shown above, with a
standard deviation of nearly half the mean. A more conservative estimate of R2(T) would be
0.05, which would have 80% power with 100 study subjects. Thus, with 100 study participants,
power appears more than adequate to detect an FVC decrement of at least 1% per µg/m3 of
background-corrected EC exposure.
For the biomarker analyses, power analyses were conducted assuming that six
confounding variables (age, sex, race/ethnicity, body mass index, smoking and exposure to nonengineered nanomaterial or other agents) are to be controlled in the analyses for five biomarkers
of primary interest as measures of early pulmonary fibrosis (KL-6), inflammation and
cardiovascular disease or coagulation (IL-6, fibrinogen), and oxidative stress (GPx and 8isoprostane), and that these six factors together have an R2(C) of 0.40. The five biomarkers of
interest were selected either because they are good indicators of pre-clinical pulmonary fibrosis
(i.e., KL-6), or because they showed associations with CNT or other nanomaterial exposures in
the only nano-epidemiology study reported publicly to date (Liou 2011). Under this scenario, a
sample size of 100 would give a power of 0.80 to detect an increase of 0.07 in the coefficient of
multiple determination [from “test variables”, R2(T)] (Fig. 4). No published biomarker studies
have been reported on CNT or CNF-exposed populations, so estimates of expected effect are
difficult to make. However, more generally, required sample sizes have been found to be small
for some biomarkers: Wones et al (1995) presented details on sample size estimation in
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

biomarker studies; they concluded that 12 participants per group were needed to show a twofold
increase in hprt frequency at α=0.05 with 80% power. Thus, the calculations performed above
suggest that a sample size of 100 will be sufficient to observe a relatively small increase in
predictive capability of background-corrected values for the biomarker outcome variables.

Figure 2. Simulated forced vital capacity (FVC), as percent predicted, resulting from a decrement of 1%
per unit of background-corrected elemental carbon exposure, assuming a standard deviation of 10% in
FVC among the unexposed.

Forced vital capacity percent of 
predicted

120%
110%
100%
90%
80%
70%
y = ‐0.0104x + 1.0114
R² = 0.1232

60%
50%
0

5

10

15

Elemental carbon exposure (µg/m3)

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Figure 3. Effect measure [R2(T)] detectable for forced vital capacity (as a percent of age-, race-, genderand height-predicted) related to background-corrected elemental carbon at a power of 0.8 and an alpha of
0.05.

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Figure 4. Effect measure [R2(T)] detectable for a set of five biomarkers (adjusted for six
confounding variables) related to background-corrected elemental carbon at a power of 0.8 and
an alpha of 0.05.

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HUMAN SUBJECTS PROTECTIONS
This protocol will be reviewed by the NIOSH IRB at project initiation and yearly
thereafter. The NIOSH IRB review process provides mechanisms for reporting adverse events.
For the cross-sectional study of early health effects and biomarkers, subjects will be informed of
study objectives, procedures, the voluntary nature of their participation, and the risks and
benefits of participating. Written informed consent (Appendix I) will be obtained and preserved
for documentation. The informed consent document in Appendix I was reviewed for readability.
It shows a Flesch Reading Ease score of 60.6 (target is 60-80), and a Flesch-Kincaid grade level
of 9.5. This grade level should be sufficiently readable for the workers in this study, most of
whom have bachelor-level or higher degrees.
A waiver of consent for the records obtained from companies in the study will be based
on 8(c)(1) of the Occupational Safety and Health Act of NIOSH, which permits statutory
authority to collect these records.
Confidentiality
All data collected for this study will be maintained in accordance with the Federal
Privacy Act of 1974. All data for the study will be maintained in accordance with NIOSH and
CDC policies on data security for sensitive but unclassified data, including restricted access to
study team members with a “need to know” each data source. Hardcopy study records will be
maintained in locked rooms or file cabinets with access restricted to study team members with a
justified need to maintain access.

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Worker notification
All study subjects participating in this cross-sectional study will be informed of their
individual results of the exposure assessment, medical evaluation, and biomarker measurements.
Study participants will be notified on the day of the medical exam about their height, weight,
waist circumference, blood pressure, and heart rate (Addendum 1). They will be notified within
one month of all clinically relevant medical findings (the above measures, plus BMI, CBC, and
spirometry results; Addendum 2). They will be notified within approximately 6 months
(depending on time required for TEM analyses) of their exposure assessment results (Addendum
3). Participants will be notified of the results of their biomarker analyses within 3 months of
completion of these analyses (at the end of all data collection), and they will also be sent a
summary of study findings. Notification letters for the biomarker analysis results and summary
of study findings will be submitted to the NIOSH IRB for review.

Study	Risks	and	Benefits	
Assessment	of	Potential	Benefits	
Some of the information being collected during this study (i.e., blood pressure, CBC with
differential, spirometry findings) is clinically relevant for the individual participant and is
therefore of benefit to the individual. The participant and (if the participant consents) his or her
personal physician will receive written results of these tests within one month of the site visit,
along with appropriate interpretation of their clinical significance. The study participants will
also receive a report on the results of his or her carbon nanotube or nanofiber exposure
measurements, conducted via personal breathing zone and dermal sampling, together with an
interpretation of their meaning with respect to available guidelines or standards.

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More generally, this study will provide information on whether workplace exposure to
carbon nanotubes and nanofibers is related to measures and biomarkers of early pulmonary and
cardiovascular health effects. Individual participants will be notified of the results of the overall
study. If positive associations are found, the participants’ health may benefit by early
intervention to reduce the chances of progression to actual disease. Most of the biomarkers have
not been clinically validated; however, some (blood pressure, pulmonary function measured by
spirometry, complete blood count with differential) are clinically relevant. The study participants
will receive individual notification of the results of all clinically relevant tests and results, with
an indication of results that are outside of reference ranges or have clinical significance. The
study participants will also receive information on their workplace exposure to CNT and CNF
(and any other exposures that are measured), and of their individual results for any non-clinically
relevant biomarkers together with reference ranges for unexposed study participants. Other
workers (non-participants) who are exposed to CNT or CNF may also benefit from the findings
of this study.

Assessment	of	Potential	Risks	
The risk to participants of this study is minimal. They include answering questions that
may be sensitive (e.g., medications and history of illnesses). Respondents may choose not to
answer any questions at any time without penalty. There is a slight risk of unintended disclosure
of the data obtained from the questionnaire, medical examination and procedures, or biomarker
analyses. This risk will be minimized as described below.
Spirometry and sputum induction may involve slight, temporary, discomfort. Some
people feel lightheaded during or after performing spirometry or sputum induction, but this is
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

generally minor and goes away after sitting down. In some persons, spirometry or sputum
induction is contraindicated because it can cause adverse health effects.
A small percentage (<3%) of people who have the induced sputum procedure with
hypertonic saline may experience temporary bronchial spasm. The chances of this will be
minimized by using isotonic saline, which has a much lower risk. Nevertheless, a NIOSH
physician with extensive field medical experience and board certification in Internal Medicine
and/or Occupational Medicine (either Marie De Perio, MD, or Douglas Trout, MD, MHS) will
be monitoring the sputum induction procedure and will administer a bronchial dilator in the
event that bronchospasm should happen to any study participants. During the blood draw,
participants will feel a momentary prick when upon needle entry into the arm; some individuals
feel lightheaded or dizzy when their blood is drawn. Infrequently, an individual faints. Swelling,
bruising or discoloration may occur in the area where the needle was inserted; this will disappear
in about a week.
Another disadvantage of all the clinical and biomarker tests is that a test result may be
outside the range of "normal" even though nothing is wrong. Study participants may become
worried or anxious about test results outside the normal range, even though such results may not
indicate a clinical problem. To minimize this possibility, the letter communicating the findings of
the individual biomarker analyses will emphasize the fact that the biomarker tests are useful for
research only and have no clinical interpretation. The letter will use readily understandable
examples (e.g., height) to describe the meaning of falling outside the normal range for a given
measurement without a clinical (health) consequence.

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Description	of	Measures	Taken	to	Minimize	Potential	Risks	
Risk of unintended disclosure of the data in the study will be minimized by utilizing only
electronic records for the study (e.g., using a computer-assisted personal interview and “printing”
questionnaires and spirometry results only to electronic portable document format files saved on
password-protected, encrypted flash drives and laptops). Other steps being taken to minimize the
risk of disclosure of personal data are described in the “Confidentiality” section on p. 62 above.
Extensive efforts are undertaken to reduce adverse effects of the medical procedures
undertaken with study participants. They will be screened to minimize the chances of adverse
health effects from spirometry, sputum induction, or phlebotomy, as described above. Standard
procedures will be used to reduce infection and other adverse risks of phlebotomy. Risks of
bronchospasm from sputum induction will be minimized by use of an isotonic saline solution
with a low-flow-rate compressor nebulizer, rather than an ultrasonic (high-flow-rate) nebulizer
with hypertonic solution (Loh et al. 2004). Risks will be further reduced by monitoring of FEV1
via spirometry during the sputum collection process, to quickly identify any impairment of
airway function.
All personally identifiable information for studies collected by NIOSH is accorded
protections under the Federal Privacy Act. There is considerable physical security provided for
individually identifiable information at NIOSH. This information is identified as “Sensitive but
Unclassified”. Such data and records are stored in key-locked cabinets daily. Access to the
information is on a “need-to-know” basis. The work area is in a building with 24-hour security
guard service with access restricted to authorized keycard holders. The computer system is
maintained through highly secured software. Users, authorized by the systems security officer,
must enter user ID’s and passwords prior to achieving systems access. Furthermore, a security
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access matrix is maintained within the branch that restricts access to study data to users on a
need-to-know basis. Only NIOSH employees and their contractors who are directly working on
this study will be permitted access to the data.

Vulnerable	populations	
The worksites included in this study involve adult working populations, and thus our
study by design will exclude prisoners and children. Pregnant women are eligible to enroll and
thus receive the benefits of the study; however, they will be excluded from the sputum induction
procedure, as pregnancy is a contraindication. The blood collection volume is below the
“minimal risk” threshold of 50 mL. Spirometry is not contraindicated during pregnancy.
Pregnancy will be assessed by questionnaire.

Risk	versus	Benefit	Evaluation	
We will suggest a determination of the risks associated with this study to be minimal. As
noted above, steps will be taken to minimize and address any distress or discomfort that
participants may experience. Because the study participants will receive individual benefits from
information obtained for the study, and the fact that results of this study may impact the health of
the growing number of workers exposed to CNT and CNF, the anticipated benefits outweigh
potential harm and discomfort to the study participants. Peer reviewers of the protocol were
asked to specifically comment on whether the risks outweighed the benefits. The peer reviewers
indicated that the benefits outweighed the risks. This study will be reviewed by the Human
Subjects Review Board at NIOSH, which will be responsible for the determination of the level of
risk, benefit, and whether benefits outweigh the risk of participating.

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

STUDY STRENGTHS AND LIMITATIONS
Limitations of the study include the following:
1) The cross-sectional design precludes the establishment of temporality in exposure and
effect. For this reason, we are developing a protocol for a prospective cohort study, which will
permit the evaluation of health effects from a population that is disease-free at the start of followup. However, given the short time period that most workers have been handling CNT and CNF,
it is unlikely that elevated rates of disease (if they do occur) would be observable within the near
future.
2) The biomarkers of early effect to be used in this study have generally not been validated
for clinical use. Unfortunately, no clinically validated biomarkers of early effect have been
developed for the outcomes of primary interest (pulmonary fibrosis, cardiovascular disease, and
cancer). This limitation may reduce the interpretability of any associations that are observed
between exposure measurements and the biomarkers of early effect, although the incorporation
of clinically validated tests such as spirometry as an indication of restrictive lung disease does
serve to reduce this limitation. To further minimize this limitation, we will continue to search the
literature to update information about the biomarkers we have selected and any new biomarkers
that may show strong correlations between occupational exposures and early health effects as the
study proceeds. Any changes or additions to the biomarkers being evaluated will be submitted to
the NIOSH IRB for review. Any analyses not proposed specifically in this protocol will be
conducted only on deidentified specimens from participants who consent to such use.
Despite the limitations discussed above, this study has the following strengths:
1) The availability of concurrent exposure and biomarker/outcome data to evaluate
early possible pulmonary, genetic and cardiovascular effects associated with CNT and CNF
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exposure in workers.
2) Wide representation across a large number of companies manufacturing or using
CNT or CNF in the U.S. and across a range of exposure levels, relative to those for which health
effects have been observed.
3) A staged approach is being taken to permit the rapid evaluation of early health
effects among CNT or CNF workers, followed by a more thorough (and prospective) evaluation
of clinical health effects. This will maximize both the utility of the data (making use of the most
current biomarkers of exposure and effect) and the informativeness and representativeness of the
cohort study.

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REFERENCES
Akpinar-Elci M, Stemple KJ, Enright PL, Fahy JV, Bledsoe TA, Kreiss K, Weissman DN.
Induced sputum evaluation in microwave popcorn production workers. Chest 2005; 128:991997.
Allin KH, Bojesen SE, Nordestgaard BG. Baseline C-reactive protein is associated with incident
cancer and survival in patients with cancer. J Clin Oncol. 2009; 27:2217–2224.
Baccarelli A, Cassano PA, Litonjua A, Park SK, Suh H, Sparrow D, Vokonas P, Schwartz J.
Cardiac autonomic dysfunction: effects from particulate air pollution and protection by
dietary methyl nutrients and metabolic polymorphisms. Circulation 2008; 117:1802-1809.
Birch ME, Ku BK, Evans DE, Ruda-Eberenz T. Exposure and emissions monitoring during
carbon nanofiber production−part I: elemental carbon exposure marker. Ann Occup Hyg
2011; 55:1016-1036.
Birch ME. Exposure and emissions monitoring during carbon nanofiber production—part II:
polycyclic aromatic hydrocarbons Ann Occup Hyg 2011; 55:1037-1047.
Brichory FM, Misek DE, Yim AM, et al. An immune response manifested by the common
occurrence of annexins I and II autoantibodies and high circulating levels of IL-6 in lung
cancer. Proc Natl Acad Sci USA. 2001; 98:9824–9829.
Brook RD, Rajagopalan S, Pope CA 3rd, Brook JR, Bhatnagar A, Diez-Roux AV, Holguin F,
Hong Y, Luepker RV, Mittleman MA, Peters A, Siscovick D, Smith SC Jr, Whitsel L,
Kaufman JD. Particulate matter air pollution and cardiovascular disease: An update to the
scientific statement from the American Heart Association. Circulation. 2010; 121:2331-2378.
70

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Brook RD, Urch B, Dvonch JT, Bard RL, Speck M, Keeler G, Morishita M, Marsik FJ, Kamal
AS, Kaciroti N, Harkema J, Corey P, Silverman F, Gold DR, Wellenius G, Mittleman MA,
Rajagopalan S, Brook JR. Insights into the mechanisms and mediators of the effects of air
pollution exposure on blood pressure and vascular function in healthy humans. Hypertension.
2009; 54:659-667.
Calderón-Garcidueñas L, Vincent R, Mora-Tiscareño A, Franco-Lira M, Henríquez-Roldán C,
Barragán-Mejía G, Garrido-García L, Camacho-Reyes L, Valencia-Salazar G, Paredes R,
Romero L, Osnaya H, Villarreal-Calderón R, Torres-Jardón R, Hazucha MJ, Reed W.
Elevated plasma endothelin-1 and pulmonary arterial pressure in children exposed to air
pollution. Environ Health Perspect. 2007; 115:1248-1253.
Cassel SL, Eisenbarth SC, Iyer SS, Sadler JJ, Colegio OR, Tephly LA, Carter AB, Rothman PB,
Flavell RA, Sutterwala FS. The Nalp3 inflammasome is essential for the development of
silicosis. Proc Natl Acad Sci U S A. 2008; 105:9035-9040.
Channell MM, Paffett ML, Devlin RB, Madden MC, Campen MJ. Circulating factors induce
coronary endothelial cell activation following exposure to inhaled diesel exhaust and
nitrogen dioxide in humans: evidence from a novel translational in vitro model. Toxicol Sci.
2012; 127:179-186.
Chonan T, Taguchi O, Omae K. Interstitial pulmonary disorders in indium-processing workers.
Eur Respir J. 2007; 29:317-324.
Christoforou CS, Salmon LG, Hannigan MP, Solomon PA, Cass GR. Trends in fine particle
concentration and chemical composition in southern California. J Air Waste Manag Assoc.
2000; 50:43-53.
71

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Cohen, J. Statistical Power Analysis for the Behavioral Sciences. Hillsdale NJ: Lawrence
Erlbaum Associates, 1988.
Dahm MM, Yencken MS, Schubauer-Berigan MK. Exposure control strategies in the
carbonaceous nanomaterial industry. J Occup Environ Med. 2011; 53:S68–S73.
Dahm MM, Evans DE, Schubauer-Berigan MK, Birch ME, Fernback JE. Exposure assessment
in carbon nanotube and nanofiber primary and secondary manufacturers. Ann Occup Hyg
56:542-556, 2012.
Dahm MM, Evans DE, Schubauer-Berigan MK, Birch ME, Deddens JA. Occupational exposure
assessment in carbon nanotube and nanofiber primary and secondary manufacturers: mobile
direct reading sampling. Ann Occup Hyg in press.
Davoodi G, Sharif AY, Kazemisaeid A, Sadeghian S, Farahani AV, Sheikhvatan M, Pashang M.
Comparison of heart rate variability and cardiac arrhythmias in polluted and clean air
episodes in healthy individuals. Environ Health Prev Med. 2010; 15:217-221.
Delfino RJ, Staimer N, Vaziri ND. Air pollution and circulating biomarkers of oxidative stress.
Air Qual Atmos Health. 2011; 4:37-52.
Demou E, Peter P, Hellweg S. Exposure to manufactured nanostructured particles in an industrial
pilot plant. Ann Occup Hyg. 2008; 52:695-706.
Dolinay T, Kim YS, Howrylak J, Hunninghake GM, An CH, Fredenburgh L, Massaro AF,
Rogers A, Gazourian L, Nakahira K, Haspel JA, Landazury R, Eppanapally S, Christie JD,
Meyer NJ, Ware LB, Christiani DC, Ryter SW, Baron RM, Choi AM. Inflammasomeregulated cytokines are critical mediators of acute lung injury. Am J Respir Crit Care Med.
2012; 185:1225-1234.
72

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Dostert C, Pétrilli V, Van Bruggen R, Steele C, Mossman BT, Tschopp J. Innate immune
activation through Nalp3 inflammasome sensing of asbestos and silica. Science 2008;
320:674-677.
Erdely A, Hulderman T, Salmen R, Liston A, Zeidler-Erdely PC, Schwegler-Berry D,
Castranova V, Koyama S, Kim YA, Endo M, Simeonova PP. Cross-talk between lung and
systemic circulation during carbon nanotube respiratory exposure. Potential biomarkers.
Nano Lett. 2009a; 9:36-43.
Erdely A, Hulderman T, Salmen R, Liston A, Zeidler-Erdely PC, Simeonova PP. Time course of
systemic effects following a single exposure to carbon nanotubes. [Abstract] Toxicologist
2009b; 108:279; #1351.
Erdely A, Liston A, Salmen-Muniz R, Hulderman T, Young S-H, Zeidler-Erdely PC, Castranova
V, Simeonova PP. Identification of systemic markers from a pulmonary carbon nanotube
exposures. J Occup Environ Med 2011; 53:S80-S86.
Evans DE, Ku BK, Birch ME, Dunn KH. Aerosol monitoring during carbon nanofiber
production: mobile direct-reading sampling. Ann Occup Hyg 2010; 54:514-531.
Fang SC, Eisen EA, Cavallari JM, Mittleman MA, Christiani DC. Acute changes in vascular
function among welders exposed to metal-rich particulate matter. Epidemiol 2008; 19:217225.
Gerritzen G, Huang L-C, Killpack K, Mircheva M, Conti J., 2007. A Review of Current
Practices in the Nanotechnology Industry: Survey of Current Practices in the
Nanotechnology Workplace. University of California, Santa Barbara in collaboration with

73

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

the International Council on Nanotechnology. Accessed November 15, 2007.
http://icon.rice.edu
Hamaguchi T, Omae K, Takebayashi T, Kikuchi Y, Yoshioka N, Nishiwaki Y, Tanaka A, Hirata
M, Taguchi O, Chonan T. Exposure to hardly soluble indium compounds in ITO production
and recycling plants is a new risk for interstitial lung damage. Occup Environ Med 2008; 65;
51-55.
Han SG, Kim Y, Kashon ML, Pack DL, Castranova V, Vallyathan V. Correlates of oxidative
stress and free-radical activity in serum from asymptomatic shipyard welders. Am J Respir
Crit Care Med. 2005; 172:1541-1548.
Hankinson JL, Odencrantz JR, Fedan KB. Spirometric reference values from a sample of the
general US population. Am J Respir Crit Care Med 1999; 159:179-187.
Hankinson JL, Kawut SM, Shahar E, Smith LJ, Stukovsky KH, Barr RG. Performance of
American Thoracic Society-recommended spirometry reference values in a multiethnic
sample of adults: the multi-ethnic study of atherosclerosis (MESA) lung study. Chest. 2010;
137:138-45.
Heikkila K, Ebrahim S, Lawlor DA. A systematic review of the association between circulating
concentrations of C reactive protein and cancer. J Epidemiol Community Health. 2007;
61:824–833.
Hieber L, Huber R, Bauer V, Schäffner Q, Braselmann H, Thomas G, Bogdanova T,
Zitzelsberger H. Chromosomal rearrangements in post-Chernobyl papillary thyroid
carcinomas: evaluation by spectral karyotyping and automated interphase FISH. J Biomed
Biotechnol. 2011; 2011:693691. Epub 2011 Mar 13.
74

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Heitbrink WA, Evans DE, Peters TM, Slavin TJ. Characterization and mapping of very fine
particles in an engine machining and assembly facility. J Occup Environ Hyg. 2007; 4:341351.
Hornung V, Bauernfeind F, Halle A, Samstad EO, Kono H, Rock KL, Fitzgerald KA, Latz E.
Silica crystals and aluminum salts activate the NALP3 inflammasome through phagosomal
destabilization. Nat Immunol. 2008; 9:847-856.
Hulderman T, Zeidler-Erdely PC, Kashon ML, Gu JK, Young SH, Salmen-Muniz R, Meighan T,
Antonini JM, Erdely A. Reduced responsiveness of circulating leukocytes following metalrich particulate matter exposure. [Abstract] Toxicologist 2012; 126:35.
Ichiyasu H, Ichikado K, Yamashita A, Iyonaga K, Sakamoto O, Suga M, Kohrogi H.
Pneumocyte biomarkers KL-6 and surfactant protein D reflect the distinct findings of highresolution computed tomography in nonspecific interstitial pneumonia. Respiration 2012;
83:190-197.
Il’yasova D, Colbert LH, Harris TB, et al. Circulating levels of inflammatory markers and cancer
risk in the health aging and body composition cohort. Cancer Epidemiol Biomarkers Prev.
2005; 14:2413–2418.
International Agency for Research on Cancer (IARC). Mechanisms of Fibre Carcinogenesis.
Kane AB, Boffetta P, Saracci R, Wilbourn JD. IARC Scientific Publication No. 140. Lyon,
France: International Agency for Research on Cancer; 1996, 135 pp.
IARC. IARC Monographs on the Evaluation of Carcinogenic Risks to Humans: Report of the
Advisory Group to Recommend Priorities for IARC Monographs during 2010–2014 . IARC
Internal Report 08/001; 2008, 25 pp.
75

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Kaminska J, Kowalska M, Kotowicz B, et al. Pretreatment serum levels of cytokines and
cytokine receptors in patients with non-small cell lung cancer, and correlations with
clinicopathological features and prognosis. M-CSF - an independent prognostic factor.
Oncology. 2006; 70:115–125.
Kaneko Y, Kikuchi N, Ishii Y, Kawabata Y, Moriyama H, Terada M, Suzuki E, Kobayashi M,
Watanabe K, Hizawa N. Upper lobe-dominant pulmonary fibrosis showing deposits of hard
metal component in the fibrotic lesions. Inter Med. 2010; 49:2143-2145.
Khare R, Bose S. Carbon nanotube based composites – a review. J Min Mat Char Eng 2005;
4:31-46.
Kim JY, Chen JC, Boyce PD, Christiani DC. Exposure to welding fumes is associated with acute
systemic inflammatory responses. Occup Environ Med. 2005; 62:157-163.
Kisin ER, Murray AR, Sargent L, Lowry D, Chirila M, Siegrist KJ, Schwegler-Berry D, Leonard
S, Castranova V, Fadeel B, Kagan VE, Shvedova AA. Genotoxicity of carbon nanofibers: are
they potentially more or less dangerous than carbon nanotubes or asbestos? Toxicol Appl
Pharmacol. 2011; 252:1-10.
Kuempel ED. Carbon nanotube risk assessment: implications for exposure and medical
monitoring. J Occup Environ Med. 2011; 53:S91-S97.
Lam CW, James JT, McCluskey R, Arepalli S, Hunter RL. A review of carbon nanotube toxicity
and assessment of potential occupational and environmental health risks. Crit Rev Toxicol
2006; 36:189–217.

76

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Laney AS, McCauley LA, Schubauer-Berigan MK. Workshop summary: epidemiologic design
strategies for studies of nanomaterial workers. J Occup Environ Med 2011; 53:S87-S90.
Lee M-S, Magari S, Christiani DC. Cardiac autonomic dysfunction from occupational exposure
to polycyclic aromatic hydrocarbons. Occup Environ Med 2011; 68:474-478.
Li N, Nel AE. Feasibility of biomarker studies for engineered nanoparticles: what can be learned
from air pollution research. J Occup Environ Med 2011; 53:S74-S79.
Link MS, Dockery DW. Air pollution and the triggering of cardiac arrhythmia. Curr Opin
Cardiol. 2010; 25:16-22.
Liou S-H. Cross-sectional study of health hazards among engineered nanomaterial exposed
workers. Presentation at 5th International Conference on Nanotechnology – Occupational and
Environmental Health, Lowell, MA. August 9-12, 2011.
Loh LC, Eg KP, Puspanathan P, Tang SP, Yip KS, Vijayasingham P, Thayaparan T, Kumar S. A
comparison of sputum induction methods: ultrasonic vs. compressed-air nebulizer and
hypertonic vs. isotonic saline inhalation. Asian Pacific J Allergy Immunol 2004;22:11-17.
Lund AK, Lucero J, Lucas S, Madden MC, McDonald JD, Seagrave JC, Knuckles TL, Campen
MJ. Vehicular emissions induce vascular MMP-9 expression and activity associated with
endothelin-1-mediated pathways. Arterioscler Thromb Vasc Biol. 2009; 29:511-517.
Lundgren L, Skare L, Liden C. Measuring dust on skin with a small vacuum sampler—a
comparison with other sampling techniques. Ann Occup Hyg 2005;50:95-103.
Ma C-M, Lin L-Y, Chen H-W, Huang L-C, Li J-F, Chuang K-J. Volatile organic compounds
exposure and cardiovascular effects in hair salons. Occup Med 2010; 60:624-630.
77

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Magliano KL, Hughes VM, Chinkin LR et al. Spatial and temporal variations in PM10 and
PM2.5 source contributions and comparison to emissions during the 1995 integrated
monitoring study. Atmos Environ 1999; 33:4757–4773.
McKay RT, Horvath E. Occupational Medicine: Pulmonary Function Testing in Industry,
3rd edition. Zenz, Dickerson, Horvath E, Eds. Mosby Publishers. Chapter 19, p. 229-238,
1994.
Methner M, Hodson L, Geraci C. Nanoparticle Emission Assessment Technique (NEAT) for the
identification and measurement of potential inhalation exposure to engineered nanomaterials
- Part A. 2010. J Occup Environ Hyg 2010; 7:127–132.
Miller MR, Crapo R, Hankinson J, Brusasco V, Burgos F, Casaburi R, Coates A, Enright P, van
der Grinten CPM, Gustafsson P, Jensen R, Johnson DC, MacIntyre N, McKay R, Navajas D,
Pedersen OF, Pellegrino R, Viegi G, Wanger J. General considerations for lung function
testing. Eur Respir J 2005; 26:153-161.
Mills NL, Finlayson AE, Gonzalez MC, Törnqvist H, Barath S, Vink E, Goudie C, Langrish JP,
Söderberg S, Boon NA, Fox KA, Donaldson K, Sandström T, Blomberg A, Newby DE.
Diesel exhaust inhalation does not affect heart rhythm or heart rate variability. Heart 2011;
97:544-50
Murphy FA, Poland CA, Duffin R, Al-Jamal KT, Ali-Boucetta H, Nunes A, Byrne F, PrinaMello A, Volkov Y, Li S, Mather SJ, Bianco A, Prato M, Macnee W, Wallace WA,
Kostarelos K, Donaldson K. Length-dependent retention of carbon nanotubes in the pleural
space of mice initiates sustained inflammation and progressive fibrosis on the parietal pleura.
Am J Pathol 2011; 178:2587-2600.
78

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

National Health and Nutrition Examination Survey (NHANES). Respiratory Health Spirometry
Procedures Manual. http://www.cdc.gov/nchs/data/nhanes/nhanes_07_08/spirometry.pdf
(accessed February 7, 2011). January 2008, 76 pp.
National Institute for Occupational Safety and Health (NIOSH). Current Intelligence Bulletin:
Occupational Exposure to Carbon Nanotubes and Nanofibers.
www.cdc.gov/niosh/docket/review/docket161A/pdfs/carbonNanotubeCIB_PublicReviewOf
Draft.pdf, draft Nov 2010.
NIOSH Manual of Analytical Methods (NMAM). Method 5040 Diesel Particulate Matter (as
Elemental Carbon). In: NIOSH Method of Analytical Methods 4th ed., Issue 1. Cincinnati,
OH: Department of Health and Human Services, Public Health Service, Centers for Disease
Control and Prevention, National Institute for Occupational Safety and Health. DHHS
(NIOSH) Publication 94-113, 2006a.
NIOSH Manual of Analytical Methods (NMAM). Method 7402 Asbestos by TEM (modified for
carbon nanotubes). In: NIOSH Method of Analytical Methods 4th ed., Issue 1. Cincinnati,
OH: Department of Health and Human Services, Public Health Service, Centers for Disease
Control and Prevention, National Institute for Occupational Safety and Health. DHHS
(NIOSH) Publication 94-113, 2006b.
Nolan A, Naveed B, Comfort AL, Ferrier N, Hall CB, Kwon S, Kasturiarachchi KJ, Cohen HW,
Zeig-Owens R, Glaser MS, Webber MP, Aldrich TK, Rom WN, Kelly K, Prezant DJ,
Weiden MD. Inflammatory biomarkers predict airflow obstruction after exposure to World
Trade Center dust. Chest. 2011 Oct 13. [Epub ahead of print] PubMed PMID: 21998260.

79

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Nurkiewicz TR, Porter DW, Barger M, Millecchia L, Rao KM, Marvar PJ, Hubbs AF,
Castranova V, Boegehold MA. Systemic microvascular dysfunction and inflammation after
pulmonary particulate matter exposure. Environ Health Perspect. 2006; 114:412-419.
Osmond-McLeod MJ, Poland CA, Murphy F, Waddington L, Morris H, Hawkins SC, Clark S,
Aitken R, McCall MJ, Donaldson K. Durability and inflammogenic impact of carbon
nanotubes compared with asbestos fibres. Part Fibre Toxicol. 2011; 8:15 (Epub ahead of
print) doi:10.1186/1743-8977-8-15.
Palomäki J, Välimäki E, Sund J, Vippola M, Clausen PA, Jensen KA, Savolainen K, Matikainen
S, Alenius H. Long, needle-like carbon nanotubes and asbestos activate the NLRP3
inflammasome through a similar mechanism. ACS Nano. 2011; 5:6861-6870.
Panasevich S, Leander K, Rosenlund M, Ljungman P, Bellander T, de Faire U, Pershagen G,
Nyberg F. Associations of long- and short-term air pollution exposure with markers of
inflammation and coagulation in a population sample. Occup Environ Med. 2009; 66:747-53.
Park EK, Thomas PS, Johnson AR, Yates DH. Osteopontin levels in an asbestos-exposed
population. Clin Cancer Res. 2009; 15:1362-1366.
Pellegrino R, Viegi G, Brusasco V, Crapo RO, Burgos F, Casaburi R, Coates A, van der Grinten
CPM, Gustafsson P, Hankinson J, Jensen R, Johnson DC, MacIntyre N, McKay R, Miller
MR, Navajas D, Pedersen OF, Wanger J. Interpretative strategies for lung function tests. Eur
Respir J 2005; 26: 948–968.
Peters TM, Elzey, S, Johnson et al. Airborne monitoring to distinguish engineered nanomaterials
from incidental particles for environmental health and safety. J Occup Environ Hyg 2009; 6:
73–81
80

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Peters A, Rückerl R, Cyrys J. Lessons from air pollution epidemiology for studies of engineered
nanomaterials. J Occup Environ Med 2011; 53:S8-S13.
Pine SR, Mechanic LE, Enewold L, Chaturvedi AK, Katki HA, Zheng Y-L, Bowman ED,
Engels EA, Caporaso NE, Harris CC. Increased levels of circulating Interleukin 6,
Interleukin 8, C-Reactive Protein, and risk of lung cancer. JNCI 2011; 103:1–11; Advance
Access published June 17, 2011.
Rosas IO, Richards TJ, Konishi K, Zhang Y, Gibson K, Lokshin AE, Lindell KO, Cisneros J,
MacDonald SD, Pardo A, Sciurba F, Dauber J, Selman M, Gochuico BR, Kaminski N.
MMP1 and MMP7 as potential peripheral blood biomarkers in idiopathic pulmonary fibrosis.
PLoS Med 2008; 5:623-633.
Rougier A, Lotte C, Dupuis D. An original predictive method for in vivo percutaneous exposure
studies. J Soc Cosmet Chem 1987; 38:397-417.
Sager T, Wolfarth M, Porter D, Wu N, Castranova V, Hamilton R, Holian A. Activation of the
NLRP3 Inflammasome Correlates with the Pulmonary Bioactivity of Multi-Walled Carbon
Nanotubes. [Abstract] Toxicologist. 2012 126:A667(1):145
Sanchez VC, Weston P, Yan A, Hurt RH, Kane AB. A 3-dimensional in vitro model of
epithelioid granulomas induced by high aspect ratio nanomaterials. Part Fibre Toxicol 2011;
8:17. doi:10.1186/1743-8977-8-17.
Sargent LM, Shvedova AA, Hubbs AF, Solisbury JJ, Benkovic SA, Kashon ML, Lowry DT,
Murray AR, Kisin ER, Friend S, McKinstry KT, Battelli L, Reynolds SH. Induction of
aneuploidy by single-walled carbon nanotubes. Environ Mol Mutagen 2009; 50:708-717.

81

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Sargent LM, Reynolds SH, Castranova V. Potential pulmonary effects of engineered carbon
nanotubes: in vitro genotoxic effects. Nanotoxicology 2010; 4:396-408.
Schauer J. Evaluation of elemental carbon as a marker for diesel particulate matter. J Expo Anal
Environ Epidemiol 2003; 13: 443–53.
Scherzer CR, Eklund AC, Morse LJ, Liao Z, Locascio JJ, Fefer D, Schwarzschild MA,
Schlossmacher MG, Hauser MA, Vance JM, Sudarsky LR, Standaert DG, Growdon JH,
Jensen RV, Gullans SR. Molecular markers of early Parkinson's disease based on gene
expression in blood. Proc Natl Acad Sci USA. 2007; 104:955-960.
Schneider T, Cherrie JW, Vermeulen R, Kromhout H. Dermal exposure assessment. Ann Occup
Hyg 2000; 44:493-499.
Schubauer-Berigan MK, Dahm M, Yencken MS. Engineered carbonaceous nanomaterials
manufacturers in the United States: workforce size, characteristics and feasibility of
epidemiologic studies. J Occup Environ Med 2011; 53:S62-S67.
Schulte PA, Schubauer-Berigan MK, Geraci CL, Zumwalde RD, Mayweather CD, McKernan J.
Issues in the development of epidemiologic studies of workers exposed to engineered
nanoparticles. J Occ Environ Med 2009; 51:323-335.
Schulte PA, Mundt DJ, Nasterlack M, Mulloy KB, Mundt KA. Exposure registries: overview
and utility for nanomaterial workers. J Occ Environ Med 2011; 53:S42-S47.
Schulte PA, Trout DB. Nanomaterials and Worker Health: Medical Surveillance, Exposure
Registries, and Epidemiologic Research. J Occ Environ Med 2011; 53:S3-S7.

82

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Seaton A, Donaldson K. Nanoscience, nanotechnology, and the need to think small. The Lancet
2005; 365:923-924.
Sellamuthu R, Umbright C, Roberts JR, Chapman R, Young SH, Richardson D, Leonard H,
McKinney W, Chen B, Frazer D, Li S, Kashon M, Joseph P. Blood gene expression profiling
detects silica exposure and toxicity. Toxicol Sci. 2011; 122:253-264.
Siemes C, Visser LE, Coebergh JW, et al. C-reactive protein levels, variation in the C-reactive
protein gene, and cancer risk: the Rotterdam Study. J Clin Oncol. 2006; 24:5216–5222.
Sigurdson AJ, Bhatti P, Preston DL, Doody MM, Kampa D, Alexander BH, Petibone D, Yong
LC, Edwards AA, Ron E, Tucker JD. Routine diagnostic X-ray examinations and increased
frequency of chromosome translocations among U.S. radiologic technologists. Cancer Res.
2008; 68:8825-8831.
Simeonova PP, Erdely A. Engineered nanoparticles respiratory exposure and potential risks for
cardiovascular toxicity: predictive tests and biomarkers. Inhal Toxicol 2009; 21(S1):68-73.
Streets DG, Gupta S, Waldhoff ST et al. Black carbon emissions in China. Atmos Environ 2001;
35: 4281–4296.
Wang Q, Wang L, Chen X, Rao KM, Lu SY, Ma ST, Jiang P, Zheng D, Xu SQ, Zheng HY,
Wang JS, Yu ZQ, Zhang R, Tao Y, Yuan J. Increased urinary 8-hydroxy-2'-deoxyguanosine
levels in workers exposed to di-(2-ethylhexyl) phthalate in a waste plastic recycling site in
China. Environ Sci Pollut Res Int. 2011; 18:987-96.

83

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Weichenthal S, Kulka R, Dubeau A, Martin C, Wang D, Dales R. Traffic-related air pollution
and acute changes in heart rate variability and respiratory function in urban cyclists. Environ
Health Perspect. 2011 Jun 14. [Epub ahead of print]
Wones R, Radack K, Martin V, Mandell K, Pinney S, Buncher R. Do persons living near a
uranium processing site have evidence of increased somatic cell gene mutations? A first
study. Mut Res 335: 171-184, 1995.
Yencken M, Tucker K. Characterizing workforces exposed industrywide to carbonaceous
nanomaterials. Final Report. Battelle, CDC-NIOSH Contract No. 200-2000-08018, Task No.
21, July 2009.
Yokoyama A, Kohno N, Hamada H, Sakatani M, Ueda E, et al. Circulating KL-6 predicts the
outcome of rapidly progressive idiopathic pulmonary fibrosis. Am J Respir Crit Care Med
1998; 158:1680-1684.
Yong LC, Sigurdson AJ, Ward EM, Waters MA, Whelan EA, Petersen MR, Bhatti P, Ramsey
MJ, Ron E, Tucker JD. Increased frequency of chromosome translocations in airline pilots
with long-term flying experience. Occup Environ Med. 2009; 66:56-62.
Zhang R, Brennan ML, Fu X, Aviles RJ, Pearce GL, Penn MS, Topol EJ, Sprecher DL, Hazen
SL. Association between myeloperoxidase levels and risk of coronary artery disease. JAMA.
2001; 286:2136-2142.
Zhang XH, Zhang X, Wang XC, Jin LF, Yang ZP, Jiang CX, Chen Q, Ren XB, Cao JZ, Wang
Q, Zhu YM. Chronic occupational exposure to hexavalent chromium causes DNA damage in
electroplating workers. BMC Public Health 2011; 11:224.

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Zhou T, Rong Y, Liu Y, Zhou Y, Guo J, Cheng W, Wang H, Chen W. Association between
proinflammatory responses of respirable silica dust and adverse health effects among dustexposed workers. J Occup Environ Med 2012; 54:459-465.

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
APPENDICES: DOCUMENTS PERTAINING TO CROSS-SECTIONAL BIOMARKER
STUDY

Appendix I: Fact sheet and informed consent documents for biomarker study participants
Appendix II: Medical history questionnaire to be administered to biomarker study participants
Appendix III: Exposure factors related to company and employee (to be completed by NIOSH
investigator)
Appendix IV. Emergency plan while conducting medical examinations and collecting
biospecimens

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
Appendix I. Fact sheet and informed consent documents
Fact sheet for participants in the Study of US Workers Exposed to Carbon Nanotubes and
Nanofibers
National Institute for Occupational Safety and Health
Centers for Disease Control and Prevention
Cincinnati, OH
October 2012
Project officer contact information:
Mary K. Schubauer-Berigan, PhD
National Institute for Occupational Safety and Health
4676 Columbia Pkwy, MS-R15
Cincinnati, OH 45226
Phone: 513-841-4251
Email: [email protected]
Or
Matthew M. Dahm, MPH
National Institute for Occupational Safety and Health
4676 Columbia Pkwy, MS-R14
Cincinnati, OH 45226
Phone: 513-458-7136
Email: [email protected]
Why is this study being done?
The National Institute for Occupational Safety and Health (NIOSH) does studies to see whether
possibly harmful substances in the workplace are related to health of the workers using these
materials. NIOSH is doing this study to measure your workplace exposure to carbon nanotubes
(CNT) and carbon nanofibers (CNF) and to measure factors related to your health, to see if they
are related to CNT or CNF exposure. We are doing this study to look at early markers for the
following possible health effects in this study:




Lung disease, such as pulmonary fibrosis
Heart disease, such as high blood pressure and atherosclerosis
DNA changes and inflammation that may lead to cancer

We do not think that exposure levels in workplaces are high enough, or have happened for a long
enough time, to cause these diseases at this time. Instead, we are looking at biomarkers of early
possible effects in body tissues (blood, phlegm, and cheek or nasal cells). In this study, we will be
comparing workers who have higher exposures to workers from the same workplaces who have
lower or no exposures to CNT or CNF. We will be including 100 workers from at least ten
worksites where CNT or CNF are manufactured and/or used, including yours.
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

What will I be asked to do in this study?
All parts of this study will be done during your normal workday, and you will not need to take
time off from work to participate. We will visit your worksite for several days during one week.
On this visit, we will measure your workplace exposure to CNT and/or CNF. This will involve
your wearing a vest that has three small pumps that will collect samples in your breathing space.
Your exposure will be measured in this way through your entire work shift for one or two days.
We will also look at whether CNT or CNF may be present on your skin after your work shift by
placing and then removing a small piece of adhesive tape on the skin of your fingers, palms and
wrists. Back in the lab, we will look at the adhesive under a microscope to see if CNT or CNF are
present on the sample.
One time during the study, you will also be asked to have an interview and a medical
examination, which will take about 90 minutes. The interview will take between 15 and 30
minutes to complete. More information about the interview is given below. You will then be
examined by a NIOSH physician, who will take your pulse and blood pressure, height, weight,
and waist circumference, and will make sure you are healthy enough to take part in the rest of the
study. You will be fully clothed for this examination, which will take 10-15 minutes.
After the medical exam, you will then have a lung function test, called spirometry, which will
take about 15 minutes. In the lung function test, you will be asked to take a very deep breath and
then blow it out as fast as you can, until all the air is gone (at least 6 seconds). The test will be
repeated at least three times, to get an accurate enough result.
After the lung function test, you will be asked to provide a blood sample, totaling about 44
milliliters (3 tablespoons). A trained phlebotomist will draw a blood sample from the inside of
your arm. This will take about 10 minutes.
Lastly, we will ask you to cough up a sputum (phlegm) sample, after first breathing in a fine mist
of salt solution. This is a method that is often used in patients with asthma or emphysema to break
up phlegm in the lungs. This will take about 30 minutes. A technician will recheck your lung
function during this test.
What type of questions will I be asked in the interview?
You will be asked questions about
 Your current and past work and hobbies that have involved carbon nanotubes or
nanofibers, chemicals, dusts or fumes
 Illnesses, especially those that affect your lungs or breathing
 The medicines you take (such as, aspirin, beta blockers and other drugs to lower
blood pressure)
 Tobacco smoking use
 Alcohol use
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
You can choose not to answer any question, but if you do choose to answer, it is very
important that you answer questions honestly.
What should I bring with me to the study?



The name and address of your current doctor, if you would like us to send him or
her a copy of your test results
A list of the medicines you take (including non-prescription medicines, such as
aspirin) or your medicine bottles

Can I eat or drink before my blood tests?


Yes, you may eat and drink before your blood tests but you should not eat or drink
the hour before giving a sputum sample.

Who should not participate?




People with the following conditions should not have the spirometry test or have
sputum induced with a nebulizer
o Eye surgery in the last 3 months
o Chest or abdominal surgery in last 3 months
o Self or household member with tuberculosis exposure in the past year
o History of aneurysm, collapsed lung, or detached retina
o Heart attack or stroke within the past three months
People with the following conditions should not have sputum induced
o Current beta-blocker medication use
o Certain cardiac conditions
o Recent surgery or collapsed lung
o Current pregnancy

If you have any questions about whether you have an illness or take medicine like this, you may
discuss this with us when we visit for the survey.
What tests will be done on the biological specimens I provide?
We will do four types of tests:
 Tests to look for carbon nanotubes or nanofibers in your sputum or nasal samples
 Tests of possible DNA changes in your sputum, cheek, or nasal cells
 A complete blood count will be done to see if the number of red blood cells and different
types of white blood cells is normal, and whether it is related to your carbon nanotube or
nanofiber exposure.
 Tests to look for proteins that may be present at higher or lower levels than normal in your
blood or sputum samples. Some of these proteins are possible early markers of lung or
cardiovascular disease, but most of them do not have a clear medical meaning that tells
useful information about your health, but they are useful for research purposes. We are
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers



analyzing them to see if they show a possible relationship with exposure to carbon
nanotubes and nanofibers in this research study.
Research tests on your blood sample to see if your white blood cells respond to a stimulant
in a way that is related to your carbon nanotube or nanofiber exposure.

Your blood and sputum samples will be split into different components for the various
measurements. Since there will be more than enough of some components than is needed to run
the tests, we would like your permission to store the extra for possible future research. This
research might involve laboratory tests that have not yet been developed.
Will my results be confidential?






Information collected about you will be protected by the Privacy Act of 1974.
NIOSH has very strict practices in place to ensure that information we collect
about you will be protected from unintentional disclosure. Under the Privacy
Act, your information may be disclosed only to private contractors assisting
NIOSH; to collaborating researchers under certain limited circumstances to
conduct further investigations; to the Department of Justice in the event of
litigation; and to a congressional office assisting individuals in obtaining their
records. An accounting of the disclosures that have been made by NIOSH will
be made available to you upon request. Except for these and other permissible
disclosures expressly authorized by the Federal Privacy Act, no other
disclosure may be made without your written consent.
Your employer will not have access to any information you provide.
The results of the study will be presented in a way so that you cannot be identified.
With your permission, we will send some of your results (the ones that have clinical
meaning, such as spirometry results and blood cell type profiles) to your doctor.

Will I receive the results of the study?




You will receive a copy of your own test results.
o Some of the tests have clinical (medical) meaning, in that they give an indication
of your possible health status. These include your blood pressure, heart rate,
complete blood count, and spirometry. We will inform you of the results of these
tests in writing within one month of our visit. We will also send these results to
your personal physician if you choose to have us do so.
o Some of the tests do not tell us direct information about your health. These include
the biomarker tests that we will be doing. We will send the results of these tests to
you within six months after we finish measuring these tests. For these tests, we
will tell you how your results compared to other people in the study with similar
exposure as you, and to people with no exposure in the study.
We will also let you know the overall results of the study.

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
Cross-sectional epidemiologic study of carbon nanotube and nanofiber workers
NATIONAL INSTITUTE FOR OCCUPATIONAL SAFETY AND HEALTH (NIOSH)
CENTERS FOR DISEASE CONTROL AND PREVENTION (CDC)
U.S. PUBLIC HEALTH SERVICE
CONSENT TO PARTICIPATE IN A RESEARCH STUDY
------------------------------------------You have been asked to take part in a CDC/NIOSH research study. We explain here the nature of
your participation, describe your rights, and tell you how NIOSH will treat your records.
-------------------------------------------I. DESCRIPTION
1.

Study Title: Industrywide Exposure Assessment and Epidemiologic Studies of Workers at
Facilities Manufacturing, Distributing, or Using Carbon Nanotubes or Carbon Nanofibers
in the United States

2.

Sponsor and Project Officer: This project is to be done by the National Institute for
Occupational Safety and Health (NIOSH) of the Centers for Disease Control and
Prevention, 4676 Columbia Parkway, Cincinnati, OH 45226. NIOSH project officers are
Mary Schubauer-Berigan, PhD and Matthew Dahm, MPH

3.

Purpose and Benefits: The overall purpose of this study is to find out whether U.S.
workers exposed to carbon nanotubes (CNT) or carbon nanofibers (CNF) have early signs
of health effects, such as lung disease, heart disease, or cancer. At this time, no certain
tests exist to tell whether any health effects are occurring in workers exposed to CNT or
CNF. But this study will measure markers of early health effects to see if they may be
related to CNT or CNF exposure.
The purposes of this study are:
(a) Measure Exposure: to measure exposure to CNT and CNF in the work place and in the
personal breathing zone of the worker. We will also measure whether there are CNT or
CNF particles on the worker’s skin after a work shift.
(b) Measure possible clinical health effects: to measure lung function using spirometry,
and to measure blood pressure, heart rate, body mass index, waist circumference, and a
complete blood count. We will interview you about your lung and heart health and past
work. We will look at these health measures and interview responses together with the
exposure measurements to see if CNT or CNF exposure is related to health status.
(c) Study Biomarkers: to look at proteins in some body tissues [sputum (phlegm), nasal
cells or cheek swabs] and blood that may be biomarkers (early indicators) of health
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
effects. These could include genetic changes, lung impairment, or oxidative stress and
inflammation. These biomarkers may be related to early lung disease, heart disease or
cancer. We will look at these biomarker results to see if they are related to your measured
CNT or CNF exposure.
Answers to these questions will help NIOSH, companies, and workers understand whether
exposure to CNT or CNF may be related to early health effects in U.S. workers. Similar
studies are being done in workers exposed to CNT or CNF in other countries.
The benefits to you from being in the study include:
(a) You will receive the results of your lung function test, blood pressure and heart rate
tests, complete blood count tests, and other tests using blood, sputum, cheek cells or nasal
swipes, and of your exposure measurements to CNT and/or CNF.
You will receive a verbal summary of the results of the lung function, blood pressure and
heart rate tests on the day these tests are done. NIOSH will send you written results and
copies of these tests and of the complete blood count within one month of your exam. We
will also send suggestions (if any) for follow-up care to be discussed with your personal
physician
NIOSH will send you results of your personal air samples (or those of a co-worker
performing the same job as you) within about 6 months of our site visit. NIOSH will send
you all remaining test results done on your blood, sputum, nasal or cheek cells, within one
month of us getting the results. It may take up to 18 months before we can share these
results with you, because we must store these samples until all the workers are enrolled in
our study. Study enrollment could take more than one year.
NIOSH will also send you the results of some research tests done on your samples, but the
health importance of these tests is not known.
(b) Your being in the study may also help fellow workers and others exposed to CNT or
CNF, as a result of what is learned from this study. NIOSH will provide you and your
personal doctor (if you wish) with all findings. We will do this when the study is finished,
or sooner, for some findings. You will also receive a copy of the study report along with a
brief summary of the study results.
Besides the information about your exposure, health status, biomarker results, and the
results of the study, which we will send to you, there are no other benefits to you of being
the study.
II.

CONDITIONS OF THE STUDY

1.

All parts of this study will be done during your normal workday. You will not need to take
time off from work to be in the study. Being in the study will involve:

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
i.

Exposure measurements will be done at your workplace for two to three days.
During this period, most of you will be asked to wear three small sampling pumps
placed in the pockets of a fishing vest. The sampling pumps pull air through (1) a
filter to measure amounts of elemental carbon (a marker for CNT or CNF) and (2)
a filter used to count the number of structures containing CNT and CNF in the air
you are breathing. We ask you to wear the pumps so we can measure the amount
of CNT or CNF in the air around you. Other than the inconvenience, there should
be no discomfort from wearing the pumps. We will also look at whether CNT or
CNF may be present on your skin after your work shift by placing and then
removing a small piece of adhesive tape on the skin of your fingers, palms and
wrists. Back in the lab, we will look at the adhesive under a microscope to see if
CNT or CNF are present on the sample.

ii.

Once during the study, you will be asked to have an interview and medical
examination, which will take about 90 minutes. The interview will take 30 minutes
or less. The interview will be done in a private area near the NIOSH mobile study
trailer or other private place. We will ask about your work history, medical history,
lung and heart health, smoking, drinking, and other topics. We realize that some
questions are sensitive. We need to ask them so we make sure that you are healthy
enough to have the medical tests done. We also need them to interpret the results
of your laboratory tests. Your answers to these and any other questions will remain
private, as detailed in the Federal Privacy Act of 1974. You may decline to answer
any question for any reason.

iii.

After completing the interview, you will undergo a clinical examination by a
physician. This examination will take about 10 minutes. This will take place in a
private area of the NIOSH mobile study trailer. First, a physician will take a pulse
and blood pressure reading. Your height, weight and waist circumference will be
measured. The health-care staff will also ask some questions about your medical
history. You will remain clothed during the examination, except that your height
and weight will be measured in stocking-feet.

iv.

After the clinical exam, you will have a spirometry test to measure lung function.
This test will take about 15 minutes. This test measures the volume of air that you
can blow out after taking a very deep breath. It also measures how fast you can
blow out the air. The test will be repeated at least three times (but no more than
eight times), in order to measure your lung function accurately. If you are feeling
dizzy or faint at all while taking the test, you should stop and tell the spirometry
technician.

v.

After having the lung function test, you will be asked to provide a blood sample of
44 milliliters, about 3 tablespoons. The sample will be drawn from your inside
arm, opposite the elbow, by a trained phlebotomist. This will take about 15
minutes.

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
Measurements that will be done on your blood samples include: (1) tests to
measure any changes to the chromosomes within your white blood cells; (2) levels
of certain proteins in your blood, which may be early indicators of lung or heart
disease; (3) complete blood count; and (4) levels of some proteins produced in
your blood indicating a possible inflammatory response to exposure.
vi.

After collecting your blood sample, the technician will collect a sample of your
sputum (phlegm), nasal or cheek cell. If you have a cold or asthma, you will not be
able to give a sputum sample. If you are healthy enough for the sputum sample
collection, you will breathe an aerosol of sterile saline solution through a
mouthpiece. This will take about 30 minutes in total. Every two minutes, you will
remove the mouthpiece, spit out saliva into a cup, take a deep breath through the
mouthpiece, and then cough phlegm into a collection cup. You will do this five or
six times. After the first six minutes, we will check your lung function again using
spirometry.
If you cannot or choose not to give a sputum sample, we will ask to collect a swab
of the inside of your cheek or nose.
We will do three tests on these sputum, nasal or cheek cell samples. First, we will
measure whether any CNT or CNF structures can be observed in them. Second, we
will measure any changes to the chromosomes within these cells. Third, we will
measure some of the same proteins as in your blood samples.

vii.

We will send you the results of each test after the analysis is completed. Some of
the tests will be done after all the workers are enrolled in the study, so results may
not be available for some time to come (a year or more). It may not be possible to
do every test on every person in the study. Some of the tests are research tests and
the significance of the results of these tests for indicating your health is not known.
You will receive your test results for every test done on your blood, sputum, nasal
or cheek samples, as well as information on the reference or group range found in
the study. Reference ranges will be given for laboratory tests that have a known
relationship to your health, and group ranges will be provided for tests that do not.
If any of your test results fall outside the reference range, the findings will be
reviewed by a doctor, who will explain the possible significance of the test result
to you by letter or telephone. No tests for drugs or alcohol will be conducted on
your blood, sputum, nasal or cheek samples.
Your blood, sputum, nasal and cheek samples will be split into different parts for
the various measurements. Since there will be more than enough of some parts
than is needed to run the tests, we would like your permission to use the extra for
methods development or future research. These samples would be coded so that
they cannot be linked back to your name. You will not receive any results of tests
done on the samples. Any information that can be linked to the samples will be
saved in broad categories (such as age 40-60) so that it cannot be used to identify
you. If tests are developed using your samples that are clearly important to your
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
health, we will notify all participants about this and offer you the chance to have
the test done and the individual results reported to you. When you sign the consent
form to be in the study, you will be asked for separate permission to store your
samples for future research.
2.

There is a slight risk of unintentional disclosure of your information in the questionnaire
and medical examination, but we will take extensive steps to minimize this risk. Your
questionnaire data will be kept only in electronic form on a password-protected, encrypted
laptop or thumb drive while away from NIOSH. Your data will be stored in highly
protected electronic systems at NIOSH, and will be accessible only to those with a need to
use the data for the purposes of the study.
There should be no discomfort from the blood pressure or heart rate readings, or the
collection of nasal or cheek samples. There should be no more than slight discomfort from
the lung function (spirometry) and induced sputum tests. Each spirometry test involves
taking a deep breath and blowing all the inhaled air out as fast as possible. Some people
feel lightheaded during or after the test. This is generally minor and goes away after sitting
down. A small percentage (<3%) of people who have the induced sputum procedure may
have temporary bronchial spasm. Bronchial spasm gives a sensation of tightness in the
chest, difficulty breathing air out, or wheezing. Sometimes the only symptom is a drop in
how well you can breathe out air quickly, measured by spirometry. We are minimizing the
chance of this happening to you by using a less irritating form of saline solution. We will
check your lung function with a spirometer midway through the sputum procedure to see
if you may be having bronchial spasm. We will have a physician in the NIOSH mobile
trailer to administer a bronchial dilator if this should happen to you. The bronchial dilator
we will use is an emergency inhaler of albuterol (Proventil), which is often used by people
with asthma. The other alternatives to using albuterol are (1) using a different type of betaadrenergic receptor agonist that has a similar mode of action, or (2) doing nothing to
reverse the bronchospasm. Doing nothing is not recommended as it may lead to further
difficulties in breathing.
During the blood draw, you will feel a slight prick when the needle enters your arm; some
people feel lightheaded or dizzy when their blood is drawn. Infrequently, an individual
faints. You may also have swelling, bruising or discoloration in the area where the needle
was inserted; this will disappear in about a week. Another disadvantage of all the clinical
and biomarker tests is that a test result may be outside the range of "normal" even though
nothing is wrong. This could result in a recommendation for further evaluation that,
ultimately, may not have been necessary. If you have any reaction to or concerns about
these procedures you should contact Mary Schubauer-Berigan, Ph.D., at (513) 841-4251.

3.

There are no alternative procedures that would provide more information about your
specific workplace exposures and possible associated health effects.

4.

Injury or harm from this project is unlikely. But if it results, medical care is not provided,
other than emergency treatment as described in item #2 above. If you are injured through
negligence of a NIOSH employee you may be able to obtain compensation under Federal
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
Law. If you want to file a claim against the Federal government your contact point is:
General Law Division of the Office of General Counsel, request the Claims Office: (202)
233-0233. If an injury or harm should occur to you as the result of your participation, you
also should contact:
Mary Schubauer-Berigan, Ph.D.
Epidemiologist
NIOSH
Division of Surveillance, Hazard Evaluations, and Field Studies
4676 Columbia Parkway R15
Cincinnati, OH 45226
(513) 841-4251
or
Mark A. Toraason, PhD
Chair
NIOSH Human Subjects Review Board
4676 Columbia Parkway
Cincinnati, OH 45226
(513) 533-8591
5.

If you have questions about this research, contact Dr. Mary Schubauer-Berigan at the
address and phone number above. If you have questions about your rights as a member of
this study, contact Dr. Mark A. Toraason, Chair, Human Subjects Review Board, at 513533-8591.

6.

Your participation in this study is voluntary and you may withdraw your consent and your
participation in this study at any time without penalty or loss of benefits to which you are
otherwise entitled. By agreeing to be in the study, you should understand that the most
important parts of this study are the interview, the spirometry and blood pressure tests, the
blood tests, and the exposure measurements.

7.

NIOSH will provide you and your doctor (if you wish) with your results in writing when
the study is completed, or sooner, if they have clinical meaning. NIOSH will send you a
copy of the final report, and a brief summary of the study results. This summary report
will not contain any information that could identify people in the study.

III.

USE OF INFORMATION

This study is being done by The National Institute for Occupational Safety and Health (NIOSH).
NIOSH is part of the Centers for Disease Control and Prevention (CDC), a government agency in
the Department of Health and Human Services. We collect this information in order to learn about
various kinds of work hazards that may influence the health of the American worker.

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
NIOSH is allowed to collect and keep information about you, including your results from this
study along with your social security number, because of two laws passed by Congress. These
laws are:
1. The Public Service Act, Section 301 (42 U.S.C. 241);
2. The Occupational Safety and Health Act, Section 20 (29 U.S.C. 669).
The information you supply is voluntary and there is no penalty for not providing it. You are free
to choose not to be in this study. It is up to you. We collect your SSN so that we can link your
information with your work history records, and so that we can find your updated mailing address
so that we can notify you of your individual results and about overall study findings.
The data from this study will be used to evaluate associations between early lung and heart
disease and other health effects and exposure to carbon nanotubes and carbon nanofibers. Data
will become part of CDC Privacy Act system 09-20-0147, "Occupational Health Epidemiological
Studies" and may be disclosed to private contractors assisting NIOSH; to collaborating
researchers under certain limited circumstances to conduct further investigations; to the
Department of Justice in the event of litigation; and to a congressional office assisting individuals
in obtaining their records. An accounting of the disclosures that have been made by NIOSH will
be made available to you upon request. Except for these and other permissible disclosures
expressly authorized by the Federal Privacy Act, no other disclosure may be made without your
written consent.

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
IV.

SIGNATURES
I have read this consent form and I agree to participate in this study (Title: Industrywide
Exposure Assessment and Epidemiologic Studies of Workers at Facilities Manufacturing,
Distributing, or Using Carbon Nanotubes or Carbon Nanofibers in the United States)
PARTICIPANT____________________________________DATE_______
(signature)
I give permission for extra amounts of my blood, sputum, nasal or cheek specimens to be
stored and used for future research in laboratory tests. I understand that my name and
identification number will be taken off these stored specimens and that I will not receive
the results of any of the research tests. I understand I will not be contacted again before
these analyses are performed.
____ GIVE PERMISSION ____ DO NOT GIVE PERMISSION
PARTICIPANT____________________________________DATE_______
(signature)
PARTICIPANT'S
NAME:____________________________________________________
Address:_________________________________________________
City:________________________State:_______Zip:___________
Phone:(____)________________
Email address:
Participant Social Security number:__________________
Participant ID number:________
I, the NIOSH/CDC representative, have accurately described this study to the participant.
REPRESENTATIVE_________________________________DATE_______
(signature)

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
REQUEST AND AUTHORIZATION FOR RELEASE OF INFORMATION
I,
request and permit NIOSH/CDC to inform the
doctors or health care facilities whose names and addresses I have entered below of any
significant findings from this study that concern me. (Do not leave blank. Write "NO" where you
do not wish to give a name and address).
1. My personal doctor(s):
Dr.
Street
City

State

Zip

State

Zip

2. Other doctors or health care providers:
Dr.
Street
City

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Appendix	II.	Questionnaire	for	participants	in	study	of	lung	and	cardiovascular	function,	and	biomarkers	of	
early	health	effects	among	CNT	and	CNF	workers		
(necessary for interpretation of biomarker results)
This questionnaire is based almost entirely on previously validated and tested questionnaires. Questions pertaining to respiratory
symptoms are obtained from the American Thoracic Society’s 1978 Adult Questionnaire. Questions related to fitness for undergoing
spirometry are drawn from the National Health and Nutrition Examination Survey Respiratory Health Spirometry Procedures Manual
(NHANES 2008). All other questionnaire sections are from the NIOSH Immunotox Questionnaire (somewhat abridged). Questions on
diseases with known renal effects (diabetes, gout, etc.) have been added to the disease sections in the same format as the questions already
in those sections. Questions on lifetime alcohol consumption, condensed from the NIOSH Upper Midwest Health Study, have been added
to the alcohol section (the Immunotox Questionnaire asks only about alcohol consumption in the past six months).
INTERVIEWER: PLEASE READ THIS TO PARTICIPANT PRIOR TO BEGINNING INTERVIEW
If you are concerned about providing sensitive information or have questions about participating, feel free to discuss this with me
now. If you choose not to participate, you can quit now or at any time during the study. You may decline to answer any question,
for any reason, and continue with the rest of the interview.
The purpose of this questionnaire is to obtain information about factors other than carbon nanotube or nanofiber exposures at
your present job that might affect your health. The subjects that will be covered are your personal characteristics (that is, your
birth date, race or ethnicity, and sex), your work history involving exposure to carbon nanotubes or nanofibers or other
chemicals, dusts or fumes at (name of company under study), your hobbies, your history of certain illnesses, your use of certain
prescription medications, your tobacco smoking habits, and your alcohol consumption patterns.
The information you provide will be protected under the Federal Privacy Act. Your personal information will not be shared with
anyone in a way that allows you to be identified. We ask about your Social Security Number (SSN) so that we can link information
about your health to your work history records at your company. However, you do not have to provide us your SSN.
1. STUDY ID NUMBER: |__|__|__|__|__| (completed by NIOSH)
2. NAME: a. |__|__|__|__|__|__|__|__|__|__|__|__|__|__|__|

b. |__| c. |__|__|__|__|__|__|__|__|__|__|__|__|__|__|__|__|__|
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
(first)

(middle)

(last)

3. ADDRESS: a. |__|__|__|__|__|__|__|__|__|__|__|__|__|__|__|__|__|__|__|__|__|
(street)

b. |__|__|__|__|__|__|__|__|__|__|__|__|__|__|__|__|__|__|__|__|__|

c. |__|__|

(city)

4. TELEPHONE:

(state)

d. |__|__|__|__|__|
(zip code)

|__|__|__| / |__|__|__| - |__|__|__|__|
(area code)

5. SOCIAL SECURITY NUMBER:

|__|__|__| - |__|__| - |__|__|__|__|
PERSONAL AND MEDICAL HISTORY

6. Interviewer’s Initials |__|__|__|
7. Interview date: a. Day |__|__| b. Month |__|__| c. Year |__|__|__|__|
FIRST, I WOULD LIKE TO ASK YOU SOME QUESTIONS ABOUT YOUR PERSONAL CHARACTERISTICS.
8.

WHAT IS YOUR DATE OF BIRTH? a. Day |__|__| b. Month |__|__| c. Year |__|__|__|__|

9.

WHAT IS YOUR SEX OR GENDER?
|__| 0. Male; 1. Female; 8. Refused; 9. Other)

10.

WOULD YOU DESCRIBE YOUR RACE AS: (Read choices & indicate response to each)
a. |__| White (0. No; 1. Yes; 8. Refused; 9. Don’t know)
b. |__| Black or African American (0. No; 1. Yes; 8. Refused; 9. Don’t know)
c. |__| American Indian or Alaska Native (0. No; 1. Yes; 8. Refused; 9. Don’t know)
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
d. |__| Asian (0. No; 1. Yes; 8. Refused; 9. Don’t know)
e. |__| Native Hawaiian or other Pacific Islander (0. No; 1. Yes; 8. Refused; 9. Don’t know)
11.

WOULD YOU DESCRIBE YOURSELF AS OF HISPANIC OR LATINO/LATINA ORIGIN?
|__| (0. No; 1. Yes; 8. Refused; 9. Don’t know)

12. Current height? a. |__| feet b. |__|__| inches
13. Current weight? |__|__|__| pounds (888=refused to answer, 999=don’t know)
14. What is your level of schooling? |__| (0 = None 1 = 1-7 years, 2 = elementary school graduate, 3=9-11 years, 4= high school
graduate, 5= vocational school, 6=some college, 7=college graduate, 8=postgraduate, 9=refused)
NOW I WOULD LIKE TO ASK YOU ABOUT SYMPTOMS THAT PERTAIN MOSTLY TO YOUR CHEST. PLEASE
ANSWER YES OR NO IF POSSIBLE. IF A QUESTION DOES NOT APPEAR TO BE APPLICABLE TO YOU, LET ME
KNOW. (For questions 15-48, if the participant is in doubt about whether his or her answer is yes or no, record no.)
15. COUGH
a. Do you usually have a cough?
(Count a cough with first smoke or on first going out-of-doors.
Exclude clearing of throat.) [If no, skip to question 15c.]

|__| 0. No; 1. Yes; 8. Ref

b. Do you usually cough as much as 4 to 6 times a day, 4 or more days out of the week?

|__| 0. No; 1. Yes; 8. Ref

c. Do you usually cough at all on getting up, or first thing in the morning?

|__| 0. No; 1. Yes; 8. Ref

d. Do you usually cough at all during the rest of the day or at night?

|__| 0. No; 1. Yes; 8. Ref

IF YES TO ANY OF THE ABOVE (15a-d), ANSWER THE FOLLOWING:
IF NO TO ALL, SKIP TO 16a.
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
e. Do you usually cough like this on most days for 3 consecutive months or more during the year?

|__| 0. No; 1. Yes; 8. Ref

f. For how many years have you had this cough?

|__|__| Number of years

================================================================================
16. PHLEGM
a. Do you usually bring up phlegm from your chest?
|__| 0. No; 1. Yes; 8. Ref
(Count phlegm with the first smoke or on first going out-of-doors. Exclude phlegm from the nose. Count swallowed phlegm)
[If no, skip to 16c.]
b. Do you usually bring up phlegm like this as much as twice a day, 4 or more days out of the week?

|__| 0. No; 1. Yes; 8. Ref

c. Do you usually bring up phlegm at all on getting up or first thing in the morning?

|__| 0. No; 1. Yes; 8. Ref

d. Do you usually bring up phlegm at all during the rest of the day or at night?

|__| 0. No; 1. Yes; 8. Ref

IF YES TO ANY OF THE ABOVE (16a-d), ANSWER THE FOLLOWING:
IF NO TO ALL, SKIP TO 17a.
e. Do you bring up phlegm like this on most days for 3 consecutive months or more during the year?

|__| 0. No; 1. Yes; 8. Ref

f. For how many years have you had trouble with phlegm?

|__|__| Number of years

==============================================================================
17 EPISODES OF COUGH AND PHLEGM
a. Have you had periods or episodes of (increased*) cough and phlegm lasting for 3 weeks or more
each year?
*(For individuals who usually have cough and/or phlegm)
103

|__| 0. No; 1. Yes; 8. Ref

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

IF YES TO 17a:
b. For how long have you had at least 1 such episode per year?

|__|__| Number of years

==============================================================================
WHEEZING
18a. Does your chest ever sound wheezy or whistling:
1. When you have a cold?
|__| 0. No; 1. Yes; 8. Ref
2. Occasionally apart from colds?
|__| 0. No; 1. Yes; 8. Ref
3. Most days or nights?
|__| 0. No; 1. Yes; 8. Ref
IF YES TO 1, 2, OR 3 IN 18a:
b. For how many years has this been present?

|__|__| Number of years

19a. Have you ever had an ATTACK of wheezing that has made you feel short of breath?

|__| 0. No; 1. Yes; 8. Ref

IF YES TO 19a, ANSWER 19b-d (IF NO, SKIP TO 20):
b. How old were you when you had your first such attack?

|__|__|__| Age in years (888 Ref; 999 Don’t know)

c. Have you had 2 or more such episodes?

|__| 0. No; 1. Yes; 8. Ref

d. Have you ever required medicine or treatment for the(se) attack(s)?

|__| 0. No; 1. Yes; 8. Ref

==============================================================================
BREATHLESSNESS
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
20a. Are you disabled from walking?
IF YES TO 20a, answer 20b (IF NO OR REFUSED, SKIP TO 21a)
b. Is this disability due to heart or lung disease?
IF NO to 20b, SKIP TO 22

|__| 0. No; 1. Yes; 8. Ref

21a. Do you have shortness of breath when hurrying on the level or walking up a slight hill?

|__| 0. No; 1. Yes; 8. Ref

|__| 0. No; 1. Yes; 8. Ref

IF YES TO 21a, ANSWER 21b-e (IF NO, SKIP TO 22):
b. Do you have to walk slower on the level than people of your age because of breathlessness?

|__| 0. No; 1. Yes; 8. Ref

c. Do you ever have to stop for breath when walking at your own pace on the level?

|__| 0. No; 1. Yes; 8. Ref

d. Do you ever have to stop for breath after walking about 100 yards (or after a few minutes) on
the level?

|__| 0. No; 1. Yes; 8. Ref

e. Are you too breathless to leave the house or breathless on dressing or undressing?

|__| 0. No; 1. Yes; 8. Ref

==============================================================================
CHEST COLDS AND CHEST ILLNESSES
22. If you get a cold, does it usually go to your chest? (Usually means more than 1/2 the time)

|__| 0. No; 1. Yes; 7. No colds; 8. Ref

23a. During the past 3 years, have you had any chest illnesses that have kept you off work, indoors
at home, or in bed?

|__| 0. No; 1. Yes; 8. Ref

IF YES TO 23a, ANSWER 23b-c (IF NO, SKIP TO 23d):
b. Did you produce phlegm with any of these chest illnesses?

|__| 0. No; 1. Yes; 8. Ref

c. In the last 3 years, how many such illnesses, with (increased) phlegm, did you have which
105

_____Number of illnesses

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
lasted a week or more?
d. Do you currently have a cold or other upper airway infectious disease?

|__| 0. No; 1. Yes; 8. Ref

==============================================================================
PAST ILLNESSES
24a. Have you ever had pneumonia (include bronchopneumonia)?

|__| 0. No; 1. Yes; 8. Ref

IF YES TO 24a, ANSWER b and c (IF NO, SKIP TO 25a):
b. Was it confirmed by a doctor?

|__| 0. No; 1. Yes; 8. Ref

c. At what age did you first have it?

|__|__|__| Age in years (888 Ref; 999 Don’t know)

25a. Have you ever had hay fever or respiratory allergies?

|__| 0. No; 1. Yes; 8. Ref

IF YES TO 25a, ANSWER b and c (IF NO, SKIP TO 26a):
b. Was it confirmed by a doctor?

|__| 0. No; 1. Yes; 8. Ref

c. At what age did it start?

|__|__|__| Age in years (888. Ref; 999 Don’t know)

26a. Have you ever had chronic bronchitis?

|__| 0. No; 1. Yes; 8. Ref

IF YES TO 26a, ANSWER b-d (IF NO, SKIP TO 27a):
b. Do you still have it?

|__| 0. No; 1. Yes; 8. Ref

c. Was it confirmed by a doctor?

|__| 0. No; 1. Yes; 8. Ref

d. At what age did it start?

|__|__|__| Age in years (888 Ref; 999 Don’t know)

27a. Have you ever had emphysema?

|__| 0. No; 1. Yes; 8. Ref
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

IF YES TO 27a, ANSWER b-d (IF NO, SKIP TO 28a):
b. Do you still have it?

|__| 0. No; 1. Yes; 8. Ref

c. Was it confirmed by a doctor?

|__| 0. No; 1. Yes; 8. Ref

d. At what age did it start?

|__|__|__| Age in years (888 Ref; 999 Don’t know)

28a. Have you ever had asthma?

|__| 0. No; 1. Yes; 8. Ref

IF YES TO 28a, ANSWER 28b-e (IF NO, SKIP TO 29a):
b. Do you still have it?

|__| 0. No; 1. Yes; 8. Ref

c. Was it confirmed by a doctor?

|__| 0. No; 1. Yes; 8. Ref

d. At what age did it start?

|__|__|__| Age in years (888 Ref; 999 Don’t know)

e. If you no longer have it, at what age did it stop?

|__|__|__| Age in years (888 Ref; 999 Don’t know)

29. Have you ever had:
a. Any other chest illnesses?
If yes, please specify ____________________________________________

|__| 0. No; 1. Yes; 8. Ref

b. Any chest operations?
If yes, please specify ____________________________________________

|__| 0. No; 1. Yes; 8. Ref

c. Any chest injuries?
If yes, please specify ____________________________________________

|__| 0. No; 1. Yes; 8. Ref

30a. Has a doctor ever told you that you had heart trouble?

|__| 0. No; 1. Yes; 8. Ref
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

IF YES to 30a, ANSWER 30b-c (IF NO, GO TO 31a):
b. Have you had treatment for heart trouble in the past 10 years?

|__| 0. No; 1. Yes; 8. Ref

c. Has a doctor ever told you that you have had a heart attack?

|__| 0. No; 1. Yes; 8. Ref

31a. Has a doctor ever told you that you have high blood pressure?

|__| 0. No; 1. Yes; 8. Ref

IF YES to 31a, ANSWER 31b (IF NO, GO TO 32a):
b. Have you had any treatment for high blood pressure (hypertension) in the past 10 years?

|__| 0. No; 1. Yes; 8. Ref

==============================================================================
NOW I WOULD LIKE TO ASK YOU ABOUT CERTAIN OTHER ILLNESSES OR HEALTH CONDITIONS YOU MAY HAVE HAD
(Note: affirmative responses to any questions 40-45, or stroke or heart attack within the past 3 months (questions 30c, 33a and 46),
involve exclusions for spirometry):
HAVE YOU EVER HAD:
(Did you have any other?)

WHEN WAS THIS CONDITION FIRST
DIAGNOSED?

32a. Malignant tumor or cancer? (including leukemia or lymphoma)
|__| 0. No; 1. Yes; 8. Ref
(Describe):

b. Mo |__|__| c. Yr |__|__|__|__|

33a. Diagnosed heart disease? (Describe):
|__| 0. No; 1. Yes; 8. Ref
b. Mo |__|__| c. Yr |__|__|__|__|

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

HAVE YOU EVER HAD:
(Did you have any other?)

WHEN WAS THIS CONDITION FIRST
DIAGNOSED?

34a. Diabetes?
|__| 0. No; 1. Yes; 8. Ref

b. Mo |__|__| c. Yr |__|__|__|__|

35a. Kidney disease? (Describe):
|__| 0. No; 1. Yes; 8. Ref

b. Mo |__|__| c. Yr |__|__|__|__|

36a. Cystic fibrosis?
|__| 0. No; 1. Yes; 8. Ref

b. Mo |__|__| c. Yr |__|__|__|__|

37a. Scleroderma?
|__| 0. No; 1. Yes; 8. Ref

b. Mo |__|__| c. Yr |__|__|__|__|

38a. Lupus (systemic lupus erythromatosus)?
|__| 0. No; 1. Yes; 8. Ref

b. Mo |__|__| c. Yr |__|__|__|__|

39a. Any other autoimmune disease? (Describe):
|__| 0. No; 1. Yes; 8. Ref

b. Mo |__|__| c. Yr |__|__|__|__|

40a. Eye surgery? (other than cosmetic surgery on the eyelid or skin around the
eye)
|__| 0. No; 1. Yes; 8. Ref

b. Mo |__|__| c. Yr |__|__|__|__|

41a. Open chest or abdominal surgery?
|__| 0. No; 1. Yes; 8. Ref

b. Mo |__|__| c. Yr |__|__|__|__|

42. Did you or anyone in your household have tuberculosis in the past year?
|__| 0. No; 1. Yes; 8. Ref
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

HAVE YOU EVER HAD:
(Did you have any other?)

WHEN WAS THIS CONDITION FIRST
DIAGNOSED?

43. Has a doctor or other health professional told you that you had an
aneurysm?
|__| 0. No; 1. Yes; 8. Ref
44. Has a doctor or other health professional told you that you had a
collapsed lung?
|__| 0. No; 1. Yes; 8. Ref
45. Has a doctor or other health professional told you that you had a
detached retina?
|__| 0. No; 1. Yes; 8. Ref
46a. Has a doctor or other health professional told you that you had a stroke?
|__| 0. No; 1. Yes; 8. Ref
47. In the past month, have you coughed up blood?
|__| 0. No; 1. Yes; 8. Ref
48. Are you currently taking any prescription or nonprescription medication,
including aspirin?
|__| 0. No; 1. Yes; 8. Ref
49. Please list all prescription and non-prescription medication you are
currently taking.
50. Are you currently pregnant?
|__| 0. No; 1. Yes; 8. Ref 9. Don’t Know

110

b. Mo |__|__| c. Yr |__|__|__|__|

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
NOW I WOULD LIKE TO ASK YOU ABOUT YOUR WORK HISTORY.
51.

WHAT IS YOUR REGULAR WORK SHIFT? (If response is 4 or 8, skip to question 53)
|__| 1. Days; 2. Evenings; 3. Nights; 4. Rotating; 8. Refused

52.

WHAT ARE YOUR REGULAR SHIFT HOURS?
From a. |__|__|__|__|__|__| (incl. am/pm) to b. |__|__|__|__|__|__| (incl. am/pm)

53.

HOW MANY HOURS PER WEEK DO YOU USUALLY WORK? |__|__| Hours (888 – Refused; 999 –Don’t Know)

NOW I WOULD LIKE TO ASK YOU ABOUT THE JOBS YOU’VE HAD.
54.

PLEASE DESCRIBE YOUR CURRENT JOB.

a. WHAT IS THE
NAME &
LOCATION
(City/State) OF THE
COMPANY?

b. WHAT IS
YOUR
DEPARTMENT?

c. WHAT
IS YOUR
JOB
TITLE?

d. WHEN DID YOU
START WORKING IN
THIS JOB?
(Month/Year)

Start:
|__|__|/|__|__|__|__|

111

e. WHAT ARE
YOUR
ACTIVITIES &
DUTIES?

f. DESCRIBE ANY CNT OR
CNF, CHEMICALS, DUSTS,
OR FUMES, INCLUDING
DIESEL EXHAUST THAT
YOU HAVE BEEN EXPOSED
TO IN THIS JOB.

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
55a.

OTHER THAN YOUR CURRENT JOB, WHICH YOU JUST DESCRIBED, HAVE YOU WORKED IN ANY JOBS
WHERE YOU WERE EXPOSED TO CARBON NANOTUBES (CNT) OR CARBON NANOFIBERS (CNF) OR
CHEMICALS, DUSTS OR FUMES, INCLUDING DIESEL EXHAUST?
0 |__|
1 |__|
8 |__|
9 |__|

No (Go to #56)
Yes (complete table below)
Refused (Go to #56)
Don’t know (Go to #56)

PLEASE DESCRIBE THE OTHER JOB(S) YOU HAD WHERE YOU WERE EXPOSED TO CNT, CNF, OR CHEMICALS,
DUSTS OR FUMES.
b. WHAT WAS
THE NAME &
LOCATION
(City/State) OF THE
COMPANY?

c. WHAT
WAS YOUR
DEPARTMENT?

d. WHAT
WAS
YOUR
JOB
TITLE?

WHEN DID YOU e.
START AND f. STOP
WORKING IN THIS
JOB?
(Month/Year)

i.

Start:
|__|__|/|__|__|__|__|
Stop:
|__|__|/|__|__|__|__|

ii.

Start:
|__|__|/|__|__|__|__|
Stop:
|__|__|/|__|__|__|__|

iii.

Start:
|__|__|/|__|__|__|__|
112

g. WHAT WERE
YOUR
ACTIVITIES AND
DUTIES?

h. DESCRIBE ANY CNT OR
CNF, CHEMICALS, DUSTS,
OR FUMES, INCLUDING
DIESEL EXHAUST, THAT
YOU WERE EXPOSED TO.

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
Stop:
|__|__|/|__|__|__|__|
iv.

Start:
|__|__|/|__|__|__|__|
Stop:
|__|__|/|__|__|__|__|

56a. NOW I WOULD LIKE TO ASK YOU ABOUT YOUR HOBBIES.
IN THE PAST 6 MONTHS, HAVE YOU HAD ANY HOBBIES WHERE YOU WORKED WITH ANY CHEMICALS OR
HAD EXPOSURE TO CHEMICAL VAPORS, DUSTS OR FUMES, INCLUDING DIESEL EXHAUST? (SOME
EXAMPLES MIGHT BE CARPENTRY OR FURNITURE REFINISHING, OR MAKING STAINED GLASS AS A
HOBBY. INCLUDE ACTIVITIES ONLY IF YOU HAVE DONE THEM AT LEAST ONE HOUR A WEEK).
0 |__| No (Go to #56)
1 |__| Yes (Complete table below)
8 |__| Refused (Go to #56)
9 |__| Don’t know (Go to #56)

b. WHAT IS THE EXACT
NATURE OF THE HOBBY?

c. HOW MANY
HOURS PER
WEEK DID YOU
DO THIS
IN THE PAST 6
MONTHS?

d. WHAT CHEMICALS, DUSTS, OR FUMES (INCLUDING
DIESEL EXHAUST) ARE YOU EXPOSED TO IN THIS
HOBBY?

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

i.
ii.

IN THE NEXT PART OF THE QUESTIONNAIRE, I WOULD LIKE TO ASK YOU ABOUT YOUR TOBACCO HISTORY AND YOUR ALCOHOL
CONSUMPTION PATTERNS.
DID YOU EVER:

b. DO YOU
CURRENTLY:

c. WHAT AMOUNT, ON AVERAGE,
DO/DID YOU SMOKE/USE PER DAY?

d-e. DURING WHICH
YEARS DID YOU:

(one pack = 20 cigarettes)

57a. SMOKE CIGARETTES |__| 0. No; 8. Ref
(at least 100 in your lifetime)
|__| 1. Yes

58. SMOKE CIGARS
(at least once/day for 6 months)

59. SMOKE A PIPE
(at least once/day for 6 months)

|__| 0. No; 1. Yes; 8.

|__|__|__| cigarettes/day
or |__| packs/day

|__|__|__|__| to |__|__|__|__|

Ref

|__| 0. No; 8. Ref
|__| 1. Yes

|__| 0. No; 1. Yes; 8.

|__|__| cigars/day

|__|__|__|__| to |__|__|__|__|

|__| 0. No; 8. Ref
|__| 1. Yes

|__| 0. No; 1. Yes; 8.

|__|__| pipesful/day

|__|__|__|__| to |__|__|__|__|

|__|__| ounces /day

|__|__|__|__| to |__|__|__|__|

Ref

Ref

60. Chew tobacco or use snuff? |__| 0. No;
(at least once/day for 6 months)
|__| 1. Yes
8. Ref

|__| 0. No; 1. Yes; 8.

61a. LIVE with a regular smoker? (daily for 6

|__| 0. No; 1. Yes; 8.

months or more)

Ref

|__| 0. No; 8. Ref
| | 1. Yes

Ref

114

|__|__|__|__| to |__|__|__|__|

Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

62. Did you ever drink alcoholic beverages at least 12 or more times in a single year?
1 |__| Yes
0 |__| No (End interview)
8 |__| Refused (End interview)
63. How many years total did you drink at least 12 or more alcoholic beverages in a single year?

|__|__|__| Years, or 888 Refused, or 999 Don’t Know or

year |__|__|__|__|to|__|__|__|__|

or

Age |__|__|to|__|__|

64. During this period, about how many drinks (cans or glasses of beer, glasses of wine, shots of hard liquor straight or in a mixed drink) did you usually have per
week? |__|__|__| (number of drinks, or 888 Refused or 999 Don’t know)
65a. OVER THE PAST 6 MONTHS, HAVE YOU
CONSUMED, ON AVERAGE, AT LEAST 1
ALCOHOLIC BEVERAGE PER WEEK SUCH AS
BEER, WINE, MIXED DRINKS, OR HARD LIQUOR?
0 |__| No (End interview)
1 |__| Yes (Continue) --------------------->
2 |__| Chooses not to respond (End interview)

b. PLEASE ESTIMATE HOW MANY TIMES, PER WEEK, YOU DRANK
ALCOHOLIC BEVERAGES ON AVERAGE, OVER THE PAST 6 MONTHS,.
|__|__| per week

c. PLEASE ESTIMATE THE NUMBER OF DRINKS YOU HAVE, ON AVERAGE, ON
EACH OCCASION.
|__|__|__| (drinks; 888 Refused; 999 Don’t know)

Thank you! This completes the interview.

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
Appendix	III:	Exposure	factors	related	to	company	and	employee	(to	be	completed	by	NIOSH	investigator)	
I. COMPANY-SPECIFIC INFORMATION
Company Name:
Company Address (for facility under study):
Site Visit Dates:
Information related to use of carbon nanotubes (CNT) or carbon nanofibers (CNF)
Primary manufacturer of:

Secondary manufacturer of:

CNT or CNF material #1:
Synthesis method, if a primary manufacturer:
Precursor & catalyst used, if a primary manufacturer:
CNT or CNF source, if a secondary manufacturer:
Nominal aspect ratio:

Measured in bulk material
Reported by company

Chemicals used in purification:
CNT or CNF material #2:
Synthesis method, if a primary manufacturer:
Precursor & catalyst used, if a primary manufacturer:
CNT or CNF source, if a secondary manufacturer:
Nominal aspect ratio:

Measured in bulk material
Reported by company

Chemicals used in purification:
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

CNT or CNF material #3:
Synthesis method, if a primary manufacturer:
Precursor & catalyst used, if a primary manufacturer:
CNT or CNF source, if a secondary manufacturer:
Nominal aspect ratio:

Measured in bulk material
Reported by company

Chemicals used in purification:
Other chemical or physical agents used at the facility:

Cleaning operations:
Waste disposal practices:
Personal protective equipment required:

Engineering and administrative exposure control devices and methods:

Other relevant information:
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
II. WORKER-SPECIFIC INFORMATION (to be completed for every participant in the exposure assessment study)

NIOSH_ID:
Length of shift (observed):
Time spent per shift working directly with CNT or CNF (observed):
Time spent per shift potentially indirectly exposed to CNT or CNF (observed):
Processes and tasks performed by employee:
Task #1: Description:
Date:

Time:

Monitored by NIOSH? (Yes/No)
If no, NIOSH_ID of employee performing similar task who was monitored:
Form of CNT and CNF used (e.g., dry powder or liquid emulsion):
Personal protective equipment, used correctly?:
Engineering controls used:
Other potentially relevant information:

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
Task #2: Description:
Date:

Time:

Monitored by NIOSH? (Yes/No)
If no, NIOSH_ID of employee performing similar task who was monitored:
Form of CNT and CNF used (e.g., dry powder or liquid emulsion):
Personal protective equipment, used correctly?:
Engineering controls used:
Other potentially relevant information:
Task #3: Description:
Date:

Time:

Monitored by NIOSH? (Yes/No)
If no, NIOSH_ID of employee performing similar task who was monitored:
Form of CNT and CNF used (e.g., dry powder or liquid emulsion):
Personal protective equipment, used correctly?:
Engineering controls used:
Other potentially relevant information:

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
Task #4: Description:
Date:

Time:

Monitored by NIOSH? (Yes/No)
If no, NIOSH_ID of employee performing similar task who was monitored:
Form of CNT and CNF used (e.g., dry powder or liquid emulsion):
Personal protective equipment, used correctly?:
Engineering controls used:
Other potentially relevant information:
(use additional sheets as necessary)

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Appendix	IV.	Emergency	plan	while	conducting	medical	examinations	and	collecting	
biospecimens	
AT FIELD LOCATIONS:
1.

Call for help from another field team member.

2.

Call 911 - which is the local emergency number.

3.

Notify the NIOSH physician on-site.

4.

Follow basic CPR and first-aid guidelines.

5.

Notify one of the study field coordinators
Field coordinators (Mary Schubauer-Berigan, NIOSH Division of Surveillance,
Hazard Evaluations, and Field Studies, 4676 Columbia Parkway R15, Cincinnati,
OH 45226, office: 513.841.4251; cell: 513.417.9486 or Matthew Dahm, Division
of Surveillance, Hazard Evaluations, and Field Studies, 4676 Columbia Parkway
R14, Cincinnati, OH 45226, office: 513.458.7136; cell: 618.560.0076).

6.

Notify the facility Health and Safety coordinator.

6.

If appropriate, arrange transportation to a local emergency care facility (will be specified
when shop and clinic locations are known).

After the emergency has been handled, immediately call the following individuals:
Mary Schubauer-Berigan, Ph.D.
NIOSH Division of Surveillance, Hazard Evaluations, and Field Studies
4676 Columbia Parkway R15
Cincinnati, OH 45226
(513) 841-4251
or
Douglas Trout, M.D., M.P.H
NIOSH Division of Surveillance, Hazard Evaluations, and Field Studies
4676 Columbia Parkway R12
Cincinnati, OH 45226
(513) 841-4558

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
Addendum 1: Notification letter #1: immediately available medical results	(approved by NIOSH

IRB on 11/29/2012)	

Information sheet from NIOSH Epidemiological Study: Clinical Examination Results
For employee:
Weight:______________ lb
Height:_______________ inches
Waist circumference: ________________ inches
Average blood pressure: __________

(systolic)
(diastolic)

Average heart rate (pulse): _____________ (beats per minute)
GUIDANCE:
Blood Pressure

Recommendation

Systolic BP 120-139 or Diastolic BP 80-89
(Pre hypertension)

Confirm within 2 months
Evaluate within 1 week if
TOD/CCD/DM*

Systolic BP 140-159 or Diastolic BP 90-99

Evaluate within 1 month
Evaluate within 1 week if
TOD/CCD/DM*

Systolic BP>160-179 or Diastolic BP>100-109
Systolic BP>180 or Diastolic BP >110

Evaluate within 1 week

Immediate treatment
Refer to private physician or an urgent care facility

Normal Blood Pressure
Systolic blood pressure < 120
Diastolic Blood Pressure < 80

Normal Pulse 60-100 beats per minute

*Target Organ Damage / Clinical Cardiovascular Disease/Diabetes Mellitus (TOD/CCD/
DM)
 Heart disease
 Stroke or mini stroke TIA
 Kidney damage
 Poor leg circulation


Damage to the retina of the eye

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
Addendum 2: Notification letter #2: clinically significant medical findings		
(approved by NIOSH IRB on 12/17/12, revised 2/5/13)

DEPARTMENT OF HEALTH & HUMAN SERVICES
Centers for Disease Control and Prevention
Safety and Health
Robert A. Taft Laboratories
4676 Columbia Parkway
Cincinnati, OH 45226-1998

Public Health Service
National Institute for Occupational

Name (first, last)
Street Address
City, State, Zip
Dear Mr. (Ms.) (last name):
Thank you again for taking part in the National Institute for Occupational Safety and Health
(NIOSH) Study of U.S. Workers Exposed to Carbon Nanotubes and Nanofibers. During our
recent visit to (company name) on (date range), we conducted a number of assessments for our
study, including (choose the consented and completed evaluations from among the following list)
body measurements, blood pressure and heart rate measurements, spirometry, a complete blood
count, and collection of specimens (blood and sputum) for future analysis of other biomarkers.
This letter includes your personal results from the tests that have direct clinical (medical)
meaning for you and your doctor (choose the consented and completed evaluations from among
the following list): the body measurements, blood pressure and heart rate, the complete blood
count, and the spirometry. It also contains some information to help you interpret these results.
I. Body Measurements
Your measured height is:
Your measured weight is:

inches
pounds

Your measured waist circumference is:

inches

Your calculated body mass index (BMI) is:
The standard weight status categories associated with BMI ranges for adults are shown in the
table below:
BMI
Weight status
Below 18.5
Underweight
18.5 – 24.9
Normal
25.0 – 29.9
Overweight
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
30.0 and Above

Obese

Choose 1:
(For BMI below 18.5): Your BMI indicates that your weight is in the Underweight category for
adults of your height.
(For BMI 18.5-24.9): Your BMI indicates that your weight is in the Normal category for adults
of your height.
(For BMI 25.0-29.9): Your BMI indicates that your weight is in the Overweight category for
adults of your height.
(For BMI 30.0 and above): Your BMI indicates that your weight is in the Obese category for
adults of your height.
Maintaining a healthy weight may reduce the risk of chronic diseases associated with overweight
and obesity.
II. Blood Pressure and Heart Rate Measurements
Your average blood pressure is:
(diastolic)

(systolic)

Normal blood pressure is 120/80.
Choose 1:
(For systolic BP <120 and diastolic BP <80): Your blood pressure is within the normal range.
(For systolic BP 120-139 or diastolic BP 80-89): Your blood pressure is elevated. We
recommended that you share your results with your personal physician and undergo a medical
evaluation within 2 months or sooner.
(For systolic BP 140-159 or diastolic BP 90-99): Your blood pressure is elevated. We
recommended you share your results with your personal physician and undergo a medical
evaluation within 1 month or sooner.
(For systolic BP >160-179 or diastolic BP>100-109): Your blood pressure is elevated.
We recommended you share your results with your personal physician and undergo a medical
evaluation within 1 week or sooner.
(For systolic BP>180 or diastolic BP >110): Your blood pressure was elevated. During
our site visit we recommended immediate treatment and referred you to an urgent care facility.
Your average heart rate is:
beats per minute. Normal heart rate is 60–100 beats per minute.
Choose 1:
(For heart rate < 60): Your heart rate was below the lower limit of normal. We
recommend you share this result and discuss its importance with your personal physician.
(For heart rate 60-100): Your heart rate was within the normal range.
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
(For heart rate > 100): Your heart rate was above the lower limit of normal. We
recommend you share this result and discuss its importance with your personal physician.
III. Complete blood count
The attached report contains the results of your complete blood count. A complete blood count is
typically not a definitive diagnostic test. Results outside the normal range may or may not
require follow-up so it is important to share these results with your personal physician. Your
physician may need to evaluate the results along with results of other blood tests, or additional
tests may be necessary to determine next steps.
The table below contains your personal results and the laboratory reference ranges of the 4
clinically most important tests in your complete blood count. White blood cells help fight
infection. Hemoglobin is the oxygen-carrying protein in red blood cells. Hematocrit is the
proportion of red blood cells to the fluid component, or plasma, in your blood. Platelets help with
blood clotting.
Test name
White blood cell count
Hemoglobin

Your result

Laboratory reference range
3.8–10.8 thousand/µL
Choose 1: 13.2–17.1 g/dL
(males) or 11.7–15.5 g/dL
(females)
Choose 1: 38.5–50.0% (males)
or 35.0–45.0% (females)
140–400 thousand/µL

Hematocrit
Platelet count

WBC:
Choose 1:
(For WBC < 3.8 or > 10.8): Your white blood cell count is outside the laboratory reference
range. This may be caused by a medical condition or a side effect of a medication. We
recommend you share this result and discuss its importance with your personal physician within
one month.
(For WBC 3.8-10.8): Your white blood cell count is within the laboratory reference range.
Hemoglobin and hematocrit:
Choose 1:
(For Hb or Hct outside the normal reference range): Your hemoglobin and/or hematocrit are
outside the laboratory reference range. This may be caused by a medical condition or a side
effect of a medication. We recommend you share this result and discuss its importance with your
personal physician within one month.
(For Hb 13.2-17.1 and Hct 38.5-50 [males] or Hb 11.7-15.5 and Hct 35.0-45.0 [females]): Your
hemoglobin and hematocrit are within the laboratory reference range.
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers

Platelet count:
Choose 1:
(For Pl < 140 or > 400): Your platelet count is outside the laboratory reference range. This may
be caused by a medical condition or a side effect of a medication. We recommend you share this
result and discuss its importance with your personal physician within one month.
(For Pl 140-400): Your platelet count is within the laboratory reference range.
(Text to be used if other values in the complete blood count are outside the laboratory reference
range): As you may notice on your complete results, one or more of the other values on your
blood test were outside the laboratory reference range. These tests cannot be evaluated without a
more thorough clinical evaluation than we were able to conduct for our study. Therefore, we
recommend you share this result and discuss its importance with your personal physician within
one month.
IV. Spirometry
The purpose of the coached breathing test (known as spirometry) is to determine how your lung
function compares to expected normal lung function. The test includes measurements of the
forced vital capacity (FVC) (this is the maximal or total amount of air you can forcefully breathe
out after taking a deep breath) and the one-second forced expiratory volume (FEV1) (this is the
amount of air that you can breathe out in the first second of exhaling), and the calculation of the
ratio of FEV1 to FVC.
The results of your spirometry test were {SpirometryInterp}.
{SpirometryInterp} =
(1)

within normal limits.

(2)

interpreted as having an obstructive abnormality.

(3)

interpreted as having a restrictive abnormality.

(4)

interpreted as having a mixed abnormality.

(5)

not interpretable.

In the enclosed report entitled "Report of Spirometry Findings", your test results are compared to
predicted values for a healthy, non-smoking person of the same age, height, sex, and race. We
recommend you share this report with your personal physician so that it may be added to your
medical records. Any abnormal test results should not be considered a diagnosis of disease; that
determination can only be made by your personal physician following a complete medical
evaluation, (following phrase to be included for those with options 2-5 below) which we
recommend within the next two months. A graph of your breathing tests appears on the third
page of the report. [ SPIROMETRY OPTIONS]
[SPIROMETRY OPTIONS]
(1)
Your lung function was within normal limits.
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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
(2)
An obstructive abnormality indicates that air is exhaled from the lungs more slowly than
normal. This can be seen in certain lung conditions such as asthma, bronchitis, or emphysema.
The greater the obstruction (the lower the FEV1), the more difficult it is to exhale the air from the
lungs.
(3)
A restrictive abnormality indicates that the amount of air exhaled is smaller than normal.
This can be seen in certain lung conditions such as lung scarring or fibrosis, or in people who are
considerably overweight. It can also be seen in people who have a severe obstructive
abnormality. The greater the restriction (the lower the FVC), the greater will be the possible
physical limitation.
(4)
A mixed abnormality is the combination of obstructive and restrictive abnormalities. It
indicates that air is exhaled from the lungs more slowly than normal and the amount of air
exhaled is also smaller than normal. This can be seen in people who have a severe obstructive
abnormality.
(5)
Unfortunately, the tests were not performed in an adequate manner for us to be able to
interpret your test results. In part, this may represent a failure on our part to properly train you to
perform this test. We recommend that you share these results with your physician and ask him or
her whether you should have the spirometry test repeated.
Choose 1:
(For those who did not consent to having results sent to their personal physician)Your individual
results have been sent only to you.
(For those who consented to having results sent to their personal physician)Your individual
results have been sent to you and, at your request, to your personal physician.
Your individual results are important because they contribute to our evaluation of occupational
exposure to carbon nanotubes or nanofibers. Only the grouped results for all worksites that
participated in the study will be shared with your workplace.
We encourage you to discuss all of your test results with your personal physician. If you or your
physician has any questions about these results or our study, please feel to contact me at 513841-4116, or the study Principal Investigator, Mary Schubauer-Berigan, PhD, at 513-841-4251.
Sincerely yours,
Marie A. de Perio, MD
Medical Officer
Division of Surveillance, Hazard
Evaluations and Field Studies
Enclosures

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
Addendum 3: Notification letter #3: Exposure assessment results
DEPARTMENT OF HEALTH & HUMAN SERVICES

Public Health Service
Centers for Disease Control and Prevention
National Institute for Occupational
Safety and Health
Robert A. Taft Laboratories
4676 Columbia Parkway
Cincinnati, OH 45226-1998

Name (first, last)
Street Address
City, State, Zip
Dear Mr. (Ms.) (last name):
Thank you again for taking part in the National Institute for Occupational Safety and Health
(NIOSH) Study of US Workers Exposed to Carbon Nanotubes and Nanofibers. During the
NIOSH visit to (company name) on (date range), we collected a number of air samples over your
entire work shift to determine your exposure to carbon nanotubes or nanofibers. The air samples,
worn by you, were collected on one or two separate days. We also collected samples of carbon
nanotubes or nanofibers that may have been on the skin of your wrists and hands. This letter
includes your personal results from those samples.
What we did
We collected three air samples, worn by you on each day, to determine your exposure. The air
samples included two samples to measure elemental carbon, which is a marker for carbon
nanotube exposure, at two different sizes (inhalable and respirable). Inhalable particles are less
than about 100 micrometers (µm) in size and when these particles are breathed in, they can
deposit in the nose, mouth, windpipe (trachea), and the upper portions of the lung. Respirable
particles are less than about 4 µm in size and when they are breathed in, they can enter the
deepest parts of the lung, the alveoli. One air sample and one skin sample were also analyzed by
microscope for visual evidence of carbon nanotubes in the air and on your palm and wrist.
How we determine if exposures are acceptable
Occupational exposure limits (OELs) have been developed by federal agencies such as NIOSH,
the Occupational Safety and Health Administration (OSHA), and other safety and health
organizations such as the American Conference of Governmental Industrial Hygienists
(ACGIH®) to prevent harmful health effects from workplace exposures. OELs established by
OSHA are enforced by law.
Currently, NIOSH is the only U.S. organization with an OEL for carbon nanotubes and
nanofibers. The NIOSH OEL is x1 micrograms per cubic meter (µg/m3) of elemental carbon at
the respirable particle size. In instances where there are no established OELs, such as for
elemental carbon at the inhalable particle size or the microscopy samples, we have compared
1 Note to NIOSH IRB: The currently published NIOSH draft REL is 7 µg/m3, but the draft currently under final
review by the NIOSH Director has been reduced to 1 µg/m3. In each notification letter, we will use the current
published NIOSH value.

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Protocol for an Exposure Assessment and Epidemiological Study of U.S. CNT & CNF Workers
your exposure to the average exposures of your co-workers at your workplace. We have also
compared your exposure to the average exposures of other workers at different companies,
performing similar work as you, from whom NIOSH has previously collected air samples.
What we found in air for elemental carbon
Respirable Mass
Your air levels of elemental carbon at the respirable particle size were X µg/m3 and X µg/m3.
These samples were collected over your entire work shift. The air levels were (choose 1:
above/below) the OEL of xa µg/m3 established by NIOSH.
Inhalable Mass
Your air levels of elemental carbon at the inhalable particle size were X µg/m3 and X µg/m3. The
air levels were (choose 1: above/below) the average concentration of X µg/m3 for co-workers at
your workplace. The air levels were also (choose 1: above/below) the average concentration of X
µg/m3 collected from other workers at different companies performing similar work as you.
Microscopy Air Samples
Your air levels of visual carbon nanotubes and carbon nanotube clusters (agglomerates) were X
CNT Structures/m3 and X CNT Structures/m3. These samples were collected over your entire
work shift. The air levels were (choose 1: above/below) the average concentration of X CNT
Structures/m3 for co-workers at your workplace. The air levels were also (choose 1:
above/below) the average concentration of X CNT Structures/m3 collected from other workers at
different companies performing similar work as you.
Microscopy Skin Samples
We took a sample from your palm and wrist at the end of your shift. The laboratory results of
this sample confirmed the (choose 1: presence/absence) of carbon nanotubes on your palm and
the (choose 1: presence/absence) of carbon nanotubes on your wrist.
Summary
A full report will be sent to the company contact at (company name) which summarizes all of
our results. This report will not mention you by name. The report will also contain a discussion
of what the exposure sampling means in terms of possible health effects along with our
recommendations on how to reduce your exposures and better protect employees at your
workplace. We encourage you to discuss your work and possible exposures with your healthcare
providers. If you have any questions, please call me at (513) 458-7136 or email me at
[email protected].
Sincerely Yours,
Matthew Dahm, MPH
Research Industrial Hygienist
4676 Columbia Parkway, MS R-14
Cincinnati, OH 45226
O: 513-458-7136
F: 513-841-4486
E: [email protected]
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