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<article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" dtd-version="1.3" xml:lang="en" article-type="research-article"><?properties manuscript?><processing-meta base-tagset="archiving" mathml-version="3.0" table-model="xhtml" tagset-family="jats"><restricted-by>pmc</restricted-by></processing-meta><front><journal-meta><journal-id journal-id-type="nlm-journal-id">101698454</journal-id><journal-id journal-id-type="pubmed-jr-id">46215</journal-id><journal-id journal-id-type="nlm-ta">Ann Work Expo Health</journal-id><journal-id journal-id-type="iso-abbrev">Ann Work Expo Health</journal-id><journal-title-group><journal-title>Annals of work exposures and health</journal-title></journal-title-group><issn pub-type="ppub">2398-7308</issn><issn pub-type="epub">2398-7316</issn></journal-meta><article-meta><article-id pub-id-type="pmid">33009798</article-id><article-id pub-id-type="pmc">8802569</article-id><article-id pub-id-type="doi">10.1093/annweh/wxaa076</article-id><article-id pub-id-type="manuscript">HHSPA1764499</article-id><article-categories><subj-group subj-group-type="heading"><subject>Article</subject></subj-group></article-categories><title-group><article-title>Development of Job Exposure Matrices to Estimate Occupational
Exposure to Solar and Artificial Ultraviolet Radiation</article-title></title-group><contrib-group><contrib contrib-type="author"><name><surname>Boiano</surname><given-names>James M.</given-names></name><xref rid="A1" ref-type="aff">1</xref></contrib><contrib contrib-type="author"><name><surname>Silver</surname><given-names>Sharon R.</given-names></name><xref rid="A1" ref-type="aff">1</xref></contrib><contrib contrib-type="author"><name><surname>Tsai</surname><given-names>Rebecca J.</given-names></name><xref rid="A1" ref-type="aff">1</xref></contrib><contrib contrib-type="author"><name><surname>Sanderson</surname><given-names>Wayne T.</given-names></name><xref rid="A2" ref-type="aff">2</xref></contrib><contrib contrib-type="author"><name><surname>Liu</surname><given-names>Sa</given-names></name><xref rid="A3" ref-type="aff">3</xref></contrib><contrib contrib-type="author"><name><surname>Whitehead</surname><given-names>Lawrence W.</given-names></name><xref rid="A4" ref-type="aff">4</xref></contrib></contrib-group><aff id="A1"><label>1</label>Division of Field Studies and Engineering, National
Institute for Occupational Safety and Health, Centers for Disease Control and
Prevention, Cincinnati, Ohio 45226-1998</aff><aff id="A2"><label>2</label>College of Public Health, University of Kentucky,
Lexington, Kentucky 40536</aff><aff id="A3"><label>3</label>School of Health Sciences, Purdue University, West
Lafayette, Indiana 47907-2051</aff><aff id="A4"><label>4</label>Division of Epidemiology, Human Genetics and Environmental
Sciences, School of Public Health, University of Texas, Houston, Texas 77030</aff><author-notes><corresp id="CR1">Correspondence to: James M. Boiano, MS, CIH, Centers for Disease
Control and Prevention, National Institute for Occupational Safety and Health,
Division of Field Studies and Engineering, 1090 Tusculum Ave., MS R-17,
Cincinnati, OH 45226-1998. <email>jboiano@cdc.gov</email></corresp></author-notes><pub-date pub-type="nihms-submitted"><day>4</day><month>1</month><year>2022</year></pub-date><pub-date pub-type="ppub"><day>16</day><month>11</month><year>2020</year></pub-date><pub-date pub-type="pmc-release"><day>31</day><month>1</month><year>2022</year></pub-date><volume>64</volume><issue>9</issue><fpage>936</fpage><lpage>943</lpage><abstract id="ABS1"><sec id="S1"><title>Introduction</title><p id="P1">Job exposure matrices (JEMs) are important tools for estimating
occupational exposures in study populations where only information on
industry and occupation (I&#x00026;O) are available. JEMs were developed for
solar and artificial ultraviolet radiation (UVR) using a U.S standardized
coding scheme.</p></sec><sec id="S2"><title>Methods</title><p id="P2">Using U.S. Census Bureau industry and occupation codes, separate
lists of I&#x00026;O pairs were developed for solar and artificial UVR by a
panel of Certified Industrial Hygienists who assigned exposure ratings to
I&#x00026;O pairs with potential exposure. Parameters for exposure included
prevalence (P) and frequency (F) for solar UVR and P, F and intensity (I)
for artificial UVR. Prevalence, or percent of all workers employed in an
I&#x00026;O pair who were exposed, was categorically rated: 0-&#x0003c;1,
1-&#x0003c;20; 20-&#x0003c;80 and &#x02265;80. Frequency of exposure, defined
by the number of hours per week workers were exposed, was categorically
rated: 0-&#x0003c;5, 5-&#x0003c;20, 20-&#x0003c;35 and &#x02265;35 hours per
week. For artificial UVR only, intensity of exposure was assigned three
ratings: low, low with rare excursions, and &#x0003e;low under normal
conditions. Discrepant ratings were resolved via consensus.</p></sec><sec id="S3"><title>Results</title><p id="P3">After excluding I&#x00026;O pairs assigned P and F ratings of 0 (solar
UVR) and P, F and I ratings of 0 (artificial UVR) from the JEM, 9,206
I&#x00026;O pairs were rated for solar UVR and 2,010 I&#x00026;O pairs for
artificial UVR. For solar UVR, 723 (7.9% of all rated pairs) had ratings in
the highest category for P and F; this group included 45 occupations in
varied industries. Construction and extraction occupations represented most
of the occupations (n=20; 44%), followed by farming, fishing and forestry
occupations (n=6; 13%). For artificial UVR, 87 I&#x00026;O pairs (4.3% of all
rated pairs) had maximum ratings for P, F, and I; these comprised a single
occupation (welding, soldering and brazing workers) in diverse
industries.</p></sec><sec id="S4"><title>Conclusion</title><p id="P4">JEMs for solar and artificial UVR were developed for a broad range of
I&#x00026;O pairs in the U.S. population and are available for use by
researchers conducting occupational epidemiological studies.</p></sec></abstract><kwd-group><kwd>job exposure matrix</kwd><kwd>solar ultraviolet radiation</kwd><kwd>artificial ultraviolet radiation</kwd><kwd>industry and occupation codes</kwd><kwd>prevalence, frequency, intensity ratings</kwd><kwd>industrial hygienist, exposure estimates</kwd></kwd-group></article-meta></front><body><sec id="S5"><title>Introduction</title><p id="P5">Job exposure matrices (JEMs) are an important approach for estimating
occupational exposures retrospectively. Researchers often rely on expert raters to
assess exposure histories retrospectively when exposures cannot be directly
measured, and historical exposure records and matrices do not exist. Expert opinion
is considered more accurate than self-report for broad job groupings (<xref rid="R11" ref-type="bibr">Kromhout et al., 1987</xref>; <xref rid="R25" ref-type="bibr">Teschke et al., 2002</xref>). JEMs can be linked to job
histories to facilitate assessment of relations between these exposures and risk of
cancer and other adverse health outcomes in study populations (<xref rid="R3" ref-type="bibr">Fischer et al., 2017</xref>; <xref rid="R21" ref-type="bibr">Peters et al., 2016</xref>; <xref rid="R5" ref-type="bibr">Goldberg and
Imbernon, 2002</xref>). A NIOSH project designed to link state cancer registry
data to potential occupational exposures included the development of JEMs for solar
and artificial ultraviolet radiation (UVR). The JEMs were developed by a panel of
Certified Industrial Hygienists (CIHs) who assigned exposure ratings to standardized
industry and occupation (I&#x00026;O) codes.</p><p id="P6">Solar and artificial UVR were of interest because of uncertainties about the
health effects of exposure. Adverse outcomes that have been reported for UVR
exposure are malignancies, including non-melanoma (basal cell carcinoma, squamous
cell carcinoma), with estimates of four million incident cases in the 2012 U.S.
population (<xref rid="R23" ref-type="bibr">Rogers et al., 2015</xref>), and both
cutaneous and ocular melanoma, with incidence of the former projected at just over
100,000 new cases in 2020 (<xref rid="R24" ref-type="bibr">SEER, 2020</xref>) and
the latter accounting for nearly 4% of incident melanoma cases (<xref rid="R9" ref-type="bibr">Jovanovic et al. 2013</xref>).These estimates reflect disease
resulting from both occupational and non-occupational exposures. Positive effects of
UVR exposure include enhanced production of vitamin D, which is necessary for
calcium homeostasis (<xref rid="R14" ref-type="bibr">Lukas and Wolf, 2019</xref>)
and protection against seasonal affective disorder (<xref rid="R31" ref-type="bibr">WHO, 2006</xref>). Studies of the effects of UVR on the immune system are less
uniform, with evidence of protection against multiple sclerosis, mixed results for
different lymphomas, deleterious effects related to skin cancer, and suggestions
that the immunologic effects may be dose-dependent (<xref rid="R13" ref-type="bibr">Lu et al., 2017</xref>; <xref rid="R12" ref-type="bibr">Liu-Smith et al.,
2017</xref>; <xref rid="R7" ref-type="bibr">Hart et al. 2011</xref>; <xref rid="R29" ref-type="bibr">van der Mei et al., 2003</xref>; <xref rid="R2" ref-type="bibr">Cartwright et al., 1994</xref>).</p><p id="P7">While JEMs have been developed for solar and artificial UVR (<xref rid="R4" ref-type="bibr">Freedman et al., 1997</xref>; <xref rid="R6" ref-type="bibr">Guenel et al., 2001</xref>; <xref rid="R15" ref-type="bibr">Lutz JM,
2005</xref>; <xref rid="R21" ref-type="bibr">Peters et al., 2016</xref>; <xref rid="R20" ref-type="bibr">Peters et al., 2015</xref>; <xref rid="R1" ref-type="bibr">CANJEM, 2019</xref>; <xref rid="R30" ref-type="bibr">Vested et
al., 2019</xref>), most focus on occupation (and do not account for industry),
are limited to broad I&#x00026;O categories, or were developed for case-control studies
(<xref rid="R4" ref-type="bibr">Freedman et al., 1997</xref>; <xref rid="R6" ref-type="bibr">Guenel et al., 2001</xref>; <xref rid="R15" ref-type="bibr">Lutz
et al., 2005</xref>) and therefore do not cover a wide range of jobs. No
published JEM was found that included exposure ratings for solar or artificial UVR
across a wide range of I&#x00026;O combinations or pairs. Pilot testing by the panel
determined that prevalence ratings could be assigned for both solar and artificial
UVR; therefore, JEMs were constructed for both exposures.</p></sec><sec id="S6"><title>Methods</title><sec id="S7"><title>Industry and Occupation Information</title><p id="P8">The U.S. Census 2007 industry and 2010 occupation codes were used for
this project (<xref rid="R27" ref-type="bibr">U.S. Census Bureau, 2019a</xref>).
Use of more detailed I&#x00026;O codes (e.g., North American Industry Classification
System (NAICS), Standard Occupation Classification (SOC) code) was considered
but not used because free text I&#x00026;O information in the state cancer
registries was not consistently detailed enough to support their use (<xref rid="R28" ref-type="bibr">U.S. Census Bureau, 2019b</xref>; <xref rid="R26" ref-type="bibr">U.S. Bureau of Labor Statistics, 2020</xref>).</p></sec><sec id="S8"><title>Selection of I&#x00026;O Pairs for Solar and Artificial UVR</title><p id="P9">Because of the large number of I&#x00026;O pairs (nearly 145,000 combinations
from 269 unique Census industry codes and 539 unique Census occupation codes), a
two-step process was used to limit the number of I&#x00026;O pairs rated to those:
1) potentially exposed; and 2) likely to correspond to jobs in the U.S.
population. The potential or likelihood of exposure was determined by assigning
one of four prevalence ratings (<xref rid="T1" ref-type="table">Table 1</xref>)
to each industry and each occupation separately. Industries and occupations with
exposure potential were then crossed to create a list of all possible I&#x00026;O
pairs. I&#x00026;O pairs with either industry or occupation rated as a 1 or higher
(&#x0003e;1% prevalence) were retained for subsequent rating of two exposure
parameters for solar UVR (prevalence and frequency) and three for artificial UVR
(prevalence, frequency and intensity). The steps are listed below:</p><list list-type="order" id="L1"><list-item><p id="P10">Each of the 269 U.S. Census industries and the 539 U.S. Census
occupations was evaluated separately by CIHs to assess whether
&#x0003e;1% of workers in that industry or occupation are exposed to
solar UVR on the job.</p></list-item><list-item><p id="P11">If the CIH ratings agree, the I or O was determined to be
unexposed (and excluded) or exposed (and included).</p></list-item><list-item><p id="P12">Discrepant ratings were resolved through consensus discussion,
an approach previously shown (<xref rid="R22" ref-type="bibr">Rocheleau
et al., 2011</xref>) to improve inter-rater agreement on future
ratings of the same exposures and categorized as in step 2.</p></list-item><list-item><p id="P13">Each &#x0201c;exposed&#x0201d; industry was crossed with each
&#x0201c;exposed&#x0201d; occupation to form potential pairs for
rating.</p></list-item><list-item><p id="P14">To identify jobs occurring in the U.S. during the time period of
interest, potential I&#x00026;O pairs were compared to a dataset of I&#x00026;O
pairs occurring in one of two national surveys (American Community
Survey 2003&#x02013;2015 and Current Population Survey 2003&#x02013;2015),
or one of three state cancer registries (included due to aims of the
larger cancer registry study): California (partial entries
1998&#x02013;2010; all entries 2011&#x02013;2012), Iowa
(2007&#x02013;1013), and Texas (2012). I&#x00026;O pairs occurring at least 5
times in the combined dataset were retained for full rating.</p></list-item><list-item><p id="P15">Each pair was rated by CIHs for frequency and prevalence.</p></list-item><list-item><p id="P16">For each I&#x00026;O pair, for each metric, ratings that matched
were retained as concordant.</p></list-item><list-item><p id="P17">I&#x00026;O pairs with discrepant ratings for a metric were rated by
a third CIH. If the third CIH&#x02019;s rating matched one of the
original ratings and differed by no more than one category from the
other original rating, the matching rating was assigned to the pair.</p></list-item><list-item><p id="P18">Ratings for I&#x00026;O pairs that differed by more than one
category were resolved by further research and consensus discussion.</p></list-item><list-item><p id="P19">I&#x00026;O pairs with final ratings for all metrics assigned as 0
were excluded from the final JEM. All other I&#x00026;O pairs were
included.</p></list-item></list><p id="P20">The process was similar for artificial UVR. This process yielded a total
of 9,206 I&#x00026;O pairs for rating of solar UVR and 2,010 I&#x00026;O pairs for
artificial UVR.</p></sec><sec id="S9"><title>Exposure parameters</title><p id="P21">Occupational solar UVR exposure was defined as exposure to the sun at
work, not including artificial sources of UVR. Occupational exposure to
artificial UVR was defined as exposure to non-solar sources of UVR at work
(e.g., welding, UV lasers, UV disinfection lamps). For solar UVR, prevalence and
frequency were each given categorical ratings (<xref rid="T1" ref-type="table">Table 1</xref>). Prevalence (P) was defined as the percent of all workers
employed in the specified I&#x00026;O workforce who were exposed. Frequency (F) was
defined as the number of hours per week workers were exposed. Because intensity
of solar UVR is dependent on season and geographical location, it was not rated
as the ratings were designed to estimate an average exposure for U.S. workers.
For artificial UVR, prevalence and frequency were given the same four
categorical ratings as solar UVR. Intensity (I) of exposure was also included
and given three categorical ratings (<xref rid="T1" ref-type="table">Table
1</xref>). Initial selection of categorical boundaries for prevalence,
frequency and intensity were made via iterative discussions among the panel,
with the aim of creating prevalence categories of 0 (almost no exposed workers);
1 (few exposed workers); 2 (a moderate number of exposed workers); and 3 (a
large majority of the workforce exposed). Frequency metrics were set a 0 (less
than half a day per week); 1 (half a day but less than half the work week); 2
(at least half, but not all, of the workweek); and 3 (essentially the full
workweek). A small pilot sample (n=53) of I&#x00026;O pairs was initially evaluated
by a panel of four CIHs to assess feasibility of assigning prevalence and
frequency ratings and whether categorical boundaries needed refinement, followed
by iterative discussions to resolve discrepancies and align ratings.</p></sec><sec id="S10"><title>Exposure rating process</title><p id="P23">The CIHs involved in the rating process included three from academic
institutions (contractors) and one from NIOSH. As the initial scope of the
project included development of JEMs for multiple substances, the CIHs were
selected based on their familiarity with wide range of exposures, rather than
knowledge of specific industries or hazards. Because the JEMs were designed to
be linked to cancer registry data, the panel was instructed to consider
potential exposures in the first decade of the 2000s to allow for latency
considerations. Peer-reviewed journal articles, technical references,
information from the O*NET database (<xref rid="R17" ref-type="bibr">O*NET,
2019</xref>), and expert judgement based on the collective experience of the
CIH raters were used to guide exposure assignments. O*NET includes information
about numerous aspects of occupations in the SOC taxonomy and, for solar UVR,
the prevalence of outdoor work reported by workers surveyed including detailed
occupations but only broad industry groupings. No exposure measurement data were
used in the assignments.</p><sec id="S11"><title>Solar UVR</title><p id="P24">Exposure P and F ratings were independently assigned to each
industry and each occupation by two contractor CIHs, with the NIOSH CIH
independently assigning prevalence ratings to discrepant ratings (i.e., all
three ratings were different or two of the ratings were the same and the
third was two points higher/lower). Discrepant ratings were researched
further if necessary, discussed among the CIHs, and resolved via
consensus.</p></sec><sec id="S12"><title>Artificial UVR</title><p id="P25">A similar process to that described above for solar UVR was used to
assign artificial UVR exposure P, F and I ratings. Three contractor CIHs
were involved in the rating process - one assigned ratings to all I&#x00026;O
pairs and the other two CIHs each assigned ratings to half of the I&#x00026;O
pairs since neither were available to do all of the ratings.</p></sec></sec><sec id="S13"><title>Statistical methods</title><sec id="S14"><title>Inter-rater agreement</title><p id="P26">Inter-rater agreement statistics for solar and artificial UVR were
calculated using SAS PROC FREQ (SAS version 9.4 (SAS Institute Inc., Cary,
NC). Fleiss-Cohen kappa weights (mean and 95% confidence interval, CI) were
used to maximize weight given to ratings falling in adjacent categories
compared to ratings assigned to distant categories. Cohen considered kappas
&#x02264; 0 to indicate complete disagreement, 0.01&#x02013;0.20 none to
slight, 0.21&#x02013;0.40 fair, 0.41&#x02013; 0.60 moderate, 0.61&#x02013;0.80
substantial, and 0.81&#x02013;1.00 as near perfect agreement (<xref rid="R16" ref-type="bibr">McHugh, 2012</xref>).</p></sec><sec id="S15"><title>Assessment of differences in ratings for occupations across
industries</title><p id="P27">JEMs are sometimes created based on occupation alone. Constructing
the solar and artificial UVR JEMs based on I&#x00026;O combinations provided an
opportunity to assess the extent of variation in ratings for occupations
across industries. Percentages of occupations in the JEM falling into more
than one category for each exposure parameter for 1) solar UVR and 2)
artificial UVR were calculated after completion of the rating process.</p></sec></sec></sec><sec id="S16"><title>Results</title><p id="P28">Summary distributions for solar UVR across P and F categories and for
artificial UVR across P, F, and I are shown in <xref rid="T2" ref-type="table">Table
2</xref>.</p><sec id="S17"><title>Solar UVR JEM</title><p id="P29">P and F ratings for the 9,206 I&#x00026;O pairs with non-zero ratings for at
least one exposure parameter are presented in <xref rid="SD2" ref-type="supplementary-material">Table S1</xref> (online only <xref rid="SD2" ref-type="supplementary-material">Appendix</xref>). Nearly a third
(32%, n=2,948) of the I&#x00026;O pairs were assigned a rating of 2 or higher for P
and F; a rating of 3 for both exposure parameters was assigned to 7.9% of the
pairs (n=723). Forty-five different occupations are included in the I&#x00026;O
pairs with the highest rated exposure, 30 (67%) of them represent three broad
occupational groups: construction and extraction (n=20, 44%), farming, fishing
and forestry (n=6, 13%), and installation, maintenance and repair (n=4, 9%). The
number of different industries associated with each of the 45 occupations ranged
from one (e.g., pile-driver operator in construction) to as many as 107
industries (for grounds maintenance workers).</p></sec><sec id="S18"><title>Artificial UVR JEM</title><p id="P30">P, F and I ratings for the 2,010 I&#x00026;O pairs are presented in <xref rid="SD1" ref-type="supplementary-material">Table S2</xref> (online only
<xref rid="SD1" ref-type="supplementary-material">Appendix</xref>). Nearly
15% (n=294) of the I&#x00026;O pairs were assigned ratings of at least 2 for P and F
and 2 for I. Eighty-seven (4.3%) I&#x00026;O pairs were assigned the highest rating
for each of the three exposure parameters, all from a single occupation:
welding, soldering and brazing workers. I&#x00026;O pairs with ratings of 2 or
higher spanned multiple industries and included the following occupations:
pipelayers, plumbers, pipefitters and steamfitters; structural iron and steel
workers; boilermakers; reinforcing iron and rebar workers; rail-track laying and
maintenance equipment operators; structural metal fabricators and fitters; and
metal furnace operators, tenders, pourers and casters.</p></sec><sec id="S19"><title>Inter-rater Agreement</title><p id="P31">Inter-rater agreement was evaluated using weighted kappa statistics for
all exposure parameters for solar and artificial UVR. For solar UVR, the
weighted kappa for prevalence (0.29, 95% CI=0.28&#x02013;0.30) was much lower
than that for frequency (0.52, 95% CI=0.50&#x02013;0.53). In contrast, for
artificial UVR, the weighted kappa for prevalence was 0.49 (95%
CI=0.46&#x02013;0.52), for frequency, 0.39 (95% CI=0.26&#x02013;0.41), and for
intensity, 0.28 (95% CI=0.25&#x02013;0.30).</p></sec><sec id="S20"><title>Differences in final ratings for occupations across industries</title><p id="P32">For solar UVR, 34% of occupations received final ratings (after
concordance discussions) in more than one prevalence category, while 43% were
rated in more than one frequency category (<xref rid="T3" ref-type="table">Table
3</xref>). The percentages were larger for two of the three artificial UVR
exposure parameters, with 57% of occupations spanning multiple prevalence
categories and 45% spanning multiple intensity categories; for frequency, 40% of
occupations spanned multiple prevalence categories.</p></sec></sec><sec id="S21"><title>Discussion</title><p id="P33">JEMs that incorporate industry and occupation can be used to identify and
protect workers at risk of adverse outcomes due to high UVR exposure. The exposure
assignments can also be used with surveillance data and in etiologic studies to
investigate relations among UVR exposed workers and health outcomes.</p><p id="P34">Strengths of this project include the incorporation of both I&#x00026;O in the
JEMs and the wide range of U.S. based I&#x00026;O combinations incorporated. The data
for both JEMs are contained in Excel files and rank ordered from highest to lowest
P, F, and I exposure ratings, and then by occupation code. The data can be quickly
sorted by other variables including industry code, industry title, and occupation
title. We did not combine exposure ratings for P, F and I, so this can be done by
individual researchers based on research needs. For example, the solar UVR JEM did
not incorporate 1) regional differences, 2) seasonal variation, 3) protective
clothing and exposure mitigation practices, 4) shiftwork, or 5) non-occupational
solar UVR; keeping the exposure parameters separate facilitates application of
modifying factors specific to the study population and research objectives.
Moreover, some researchers will be interested in more or less refined
categorizations for specific parameters; in the case of the former, these JEMs offer
a starting point and, for the latter, categories can be collapsed.</p><p id="P35">Several caveats should be considered when using the solar and artificial UVR
JEMs. It was not uncommon for the raters to initially assign discrepant exposure
ratings to the I&#x00026;O pairs. The raters were selected for overall industrial
hygiene experience rather than for knowledge of specific industries or hazards.
Solar UVR was rated before artificial UVR. While the raters clearly understood the
frequency (and for artificial UVR, intensity) parameters, prevalence for solar UVR
was initially problematic, as evidenced by the particularly low inter-rater
agreement. Discussions of the reasons for assigning prevalence ratings identified
some confusion about whether raters were to identify the prevalence of all solar
UVR-exposed workers who were in a specific industry, or to identify the prevalence
of all workers employed in the industry who were exposed to solar UVR; the latter
was the intended rating target. Following intensive concordance discussions, this
confusion abated. This clearer understanding of the scope of this parameter likely
explains much of the higher concordance rating for prevalence for artificial UVR.
The probability of misclassification of ratings between adjacent categories is
substantially higher than for non-adjacent categories. Therefore, the exposure
ratings are perhaps most suitable for contrasting industries with high vs. low
prevalence, frequency, or intensity of exposure, rather than a fully populated
continuum of exposures</p><p id="P36">In addition, UVR exposures change over time, and these changes should be
considered for application of the JEMs to exposure periods other than
2000&#x02013;2009 (the focus of this project). Intensity of solar UVR changes with
calendar time, season, and location, so the intensity parameter was not included in
the solar UVR JEM. Growing public awareness of the hazards of solar UVR exposure
over time could also affect exposure prevalence and frequency. In contrast, use of
artificial UVR is evolving rapidly, with use likely increasing as an
antimicrobial/disinfection method but perhaps decreasing in other applications due
to increased hazard awareness (<xref rid="R18" ref-type="bibr">OR Today,
2018</xref>; <xref rid="R10" ref-type="bibr">Katara et al., 2008</xref>);
increasingly, UVR is used in some scenarios where robots, not people, are present.
Therefore, application of the artificial UVR JEM to exposure periods other than
2000&#x02013;2009 requires consideration of these changes.</p><p id="P37">A number of other JEMS have been developed for solar and artificial UVR. The
majority of these JEMs incorporated measurement data, an advantage over the reliance
on expert-opinion only in the current project. The lack of measurement data for UVR
exposures for industry-occupation combinations across large numbers of industries
would have precluded consistent application of measurement data to our JEMs, and is
the reason the previous JEMs that were comprehensive with respect to job types, such
as CAREX, accounted for occupation alone. However, evaluation of the distribution of
occupation ratings across industries suggests that for some exposures, including UVR
(both solar and artificial) JEMs based solely on occupation, may provide
insufficient information for JEMs intended to cover a wide range of industries. This
difference in approach precludes direct comparison between these new JEMs and those
developed previously. Between-country differences in both jobs and solar UVR
exposure also hinder comparisons. Some of the variation in ratings is likely due to
misclassification, and some might be ameliorated using a more detailed occupation
coding scheme that narrows the range of industries corresponding to each occupation.
However, the finding that at least one third, and in the case of artificial UVR
prevalence, more than half of occupations, spanned multiple ratings categories
across industries suggest the need to carefully consider the question of differences
within occupational groupings when constructing JEMs.</p></sec><sec sec-type="supplementary-material" id="SM1"><title>Supplementary Material</title><supplementary-material id="SD2" position="float" content-type="local-data"><label>Supp Table 1</label><media xlink:href="NIHMS1764499-supplement-Supp_table_1_Boiano.xlsx" id="d64e379" position="anchor"/></supplementary-material><supplementary-material id="SD1" position="float" content-type="local-data"><label>Supp Table 2</label><media xlink:href="NIHMS1764499-supplement-Supp_Table_2_Boiano.xlsx" id="d64e382" position="anchor"/></supplementary-material></sec></body><back><ack id="S22"><title>Acknowledgements</title><p id="P38">The authors thank Geoff Calvert, Jun Ju, and Marie Haring Sweeney of the
Division of Field Studies and Engineering, NIOSH, Centers for Disease Control and
Prevention, for their valuable contributions to this project.</p></ack><fn-group><fn id="FN1"><p id="P39">Supplementary Data &#x02013; Due to the size of the JEMs they are
included as supplementary data available at <italic toggle="yes">Annals of Work Exposures and
Health</italic> online.</p></fn><fn id="FN2"><p id="P41">Declaration for publication &#x02013; This work was funded by the
National Institute for Occupational Safety and Health/Centers for Disease
Control and Prevention. The authors declare no conflict of interest relating to
the material presented in this Article. The findings and conclusions presented
in this article are those of the authors and do not necessarily represent the
official position of the National Institute for Occupational Safety and
Health/Centers for Disease Control and Prevention, or their Contractors.</p></fn></fn-group><ref-list><title>References</title><ref id="R1"><mixed-citation publication-type="other"><source>CANJEM Occupational Exposure Information System</source>
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UVR</p></caption><table frame="box" rules="all"><colgroup span="1"><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/></colgroup><thead><tr><th align="center" valign="top" rowspan="1" colspan="1">Categorical<break/>Rating</th><th align="center" valign="top" rowspan="1" colspan="1">Prevalence<sup><xref rid="TFN1" ref-type="table-fn">1</xref></sup> within
Workforce<break/>(solar and artificial UVR)</th><th align="center" valign="top" rowspan="1" colspan="1">Frequency (for exposed
workers)<break/>(solar and artificial UVR)</th><th align="center" valign="top" rowspan="1" colspan="1">Intensity (for exposed
workers)<break/>(artificial UVR only)</th></tr></thead><tbody><tr><td align="center" valign="top" rowspan="1" colspan="1">0</td><td align="left" valign="top" rowspan="1" colspan="1">0 - &#x0003c;1%</td><td align="left" valign="top" rowspan="1" colspan="1">0 - &#x0003c;5 hours/week</td><td align="left" valign="top" rowspan="1" colspan="1">Low</td></tr><tr><td align="center" valign="top" rowspan="1" colspan="1">1</td><td align="left" valign="top" rowspan="1" colspan="1">1 - &#x0003c;20%</td><td align="left" valign="top" rowspan="1" colspan="1">5 - &#x0003c;20 hours/week</td><td align="left" valign="top" rowspan="1" colspan="1">Low under normal conditions, although rare
excursions possible</td></tr><tr><td align="center" valign="top" rowspan="1" colspan="1">2</td><td align="left" valign="top" rowspan="1" colspan="1">20 - &#x0003c;80%</td><td align="left" valign="top" rowspan="1" colspan="1">20 - &#x0003c;35 hours/week</td><td align="left" valign="top" rowspan="1" colspan="1">&#x0003e; Low under normal conditions</td></tr><tr><td align="center" valign="top" rowspan="1" colspan="1">3</td><td align="left" valign="top" rowspan="1" colspan="1">&#x02265;80%</td><td align="left" valign="top" rowspan="1" colspan="1">&#x02265;35 hours/week</td><td align="left" valign="top" rowspan="1" colspan="1">Not applicable</td></tr></tbody></table><table-wrap-foot><fn id="TFN1"><label>1</label><p id="P44">Percent of all workers employed in the industry who were exposed at
work</p></fn></table-wrap-foot></table-wrap><table-wrap position="float" id="T2"><label>Table 2.</label><caption><p id="P45">Summary of exposure ratings for solar and artificial UVR (number of I/O
pairs included in final JEM per category)</p></caption><table frame="box" rules="all"><colgroup span="1"><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/></colgroup><thead><tr><th align="center" valign="top" rowspan="1" colspan="1">Categorical<break/>Rating<break/></th><th align="center" valign="top" rowspan="1" colspan="1">Prevalence<sup><xref rid="TFN2" ref-type="table-fn">1</xref></sup> within
Workforce<break/>(solar and artificial UVR)</th><th align="center" valign="top" rowspan="1" colspan="1">Frequency (for exposed
workers)<break/>(solar and artificial UVR)</th><th align="center" valign="top" rowspan="1" colspan="1">Intensity (for exposed
workers)<break/>(artificial UVR only)</th></tr></thead><tbody><tr><td colspan="4" align="left" valign="top" rowspan="1">Solar UVR</td></tr><tr><td align="center" valign="top" rowspan="1" colspan="1">0</td><td align="center" valign="top" rowspan="1" colspan="1">Not applicable<sup><xref rid="TFN3" ref-type="table-fn">2</xref></sup></td><td align="center" valign="top" rowspan="1" colspan="1">1392</td><td align="center" valign="top" rowspan="1" colspan="1">Not applicable<sup><xref rid="TFN4" ref-type="table-fn">3</xref></sup></td></tr><tr><td align="center" valign="top" rowspan="1" colspan="1">1</td><td align="center" valign="top" rowspan="1" colspan="1">4121</td><td align="center" valign="top" rowspan="1" colspan="1">4679</td><td align="center" valign="top" rowspan="1" colspan="1">Not applicable<sup><xref rid="TFN4" ref-type="table-fn">3</xref></sup></td></tr><tr><td align="center" valign="top" rowspan="1" colspan="1">2</td><td align="center" valign="top" rowspan="1" colspan="1">2503</td><td align="center" valign="top" rowspan="1" colspan="1">2405</td><td align="center" valign="top" rowspan="1" colspan="1">Not applicable<sup><xref rid="TFN4" ref-type="table-fn">3</xref></sup></td></tr><tr><td align="center" valign="top" rowspan="1" colspan="1">3</td><td align="center" valign="top" rowspan="1" colspan="1">2582</td><td align="center" valign="top" rowspan="1" colspan="1">730</td><td align="center" valign="top" rowspan="1" colspan="1">Not applicable<sup><xref rid="TFN4" ref-type="table-fn">3</xref></sup></td></tr><tr><td colspan="4" align="left" valign="top" rowspan="1">Artificial UVR</td></tr><tr><td align="center" valign="top" rowspan="1" colspan="1">0</td><td align="center" valign="top" rowspan="1" colspan="1">Not applicable<sup><xref rid="TFN3" ref-type="table-fn">2</xref></sup></td><td align="center" valign="top" rowspan="1" colspan="1">1158</td><td align="center" valign="top" rowspan="1" colspan="1">524</td></tr><tr><td align="center" valign="top" rowspan="1" colspan="1">1</td><td align="center" valign="top" rowspan="1" colspan="1">1412</td><td align="center" valign="top" rowspan="1" colspan="1">522</td><td align="center" valign="top" rowspan="1" colspan="1">1136</td></tr><tr><td align="center" valign="top" rowspan="1" colspan="1">2</td><td align="center" valign="top" rowspan="1" colspan="1">483</td><td align="center" valign="top" rowspan="1" colspan="1">198</td><td align="center" valign="top" rowspan="1" colspan="1">350</td></tr><tr><td align="center" valign="top" rowspan="1" colspan="1">3</td><td align="center" valign="top" rowspan="1" colspan="1">115</td><td align="center" valign="top" rowspan="1" colspan="1">132</td><td align="center" valign="top" rowspan="1" colspan="1">Not applicable<sup><xref rid="TFN5" ref-type="table-fn">4</xref></sup></td></tr><tr><td align="center" valign="top" rowspan="1" colspan="1">&#x000a0;</td><td align="left" valign="top" rowspan="1" colspan="1">&#x000a0;</td><td align="left" valign="top" rowspan="1" colspan="1">&#x000a0;</td><td align="left" valign="top" rowspan="1" colspan="1">&#x000a0;</td></tr></tbody></table><table-wrap-foot><fn id="TFN2"><label>1</label><p id="P46">Percent of all workers employed in the industry who were exposed at
work</p></fn><fn id="TFN3"><label>2</label><p id="P47">I&#x00026;O pairs with exposure prevalence for either industry or
occupation=0 were not further rated</p></fn><fn id="TFN4"><label>3</label><p id="P48">Solar UVR was not rated for intensity</p></fn><fn id="TFN5"><label>4</label><p id="P49">Intensity has 3 rating categories</p></fn></table-wrap-foot></table-wrap><table-wrap position="float" id="T3"><label>Table 3.</label><caption><p id="P50">Distribution of ratings for an occupation across industries for solar
and artificial UVR</p></caption><table frame="box" rules="all"><colgroup span="1"><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/><col align="left" valign="middle" span="1"/></colgroup><thead><tr><th align="center" valign="top" rowspan="1" colspan="1"/><th colspan="2" align="center" valign="top" rowspan="1">Solar UVR</th><th colspan="3" align="center" valign="top" rowspan="1">Artificial UVR</th></tr><tr><th align="center" valign="top" rowspan="1" colspan="1">% of occupations rated in:</th><th align="center" valign="top" rowspan="1" colspan="1">Prevalence<sup><xref rid="TFN6" ref-type="table-fn">1</xref></sup></th><th align="center" valign="top" rowspan="1" colspan="1">Frequency</th><th align="center" valign="top" rowspan="1" colspan="1">Prevalence<sup><xref rid="TFN6" ref-type="table-fn">1</xref></sup></th><th align="center" valign="top" rowspan="1" colspan="1">Frequency</th><th align="center" valign="top" rowspan="1" colspan="1">Intensity</th></tr></thead><tbody><tr><td align="center" valign="top" rowspan="1" colspan="1">One category</td><td align="center" valign="bottom" rowspan="1" colspan="1">65.9</td><td align="center" valign="bottom" rowspan="1" colspan="1">57.1</td><td align="center" valign="bottom" rowspan="1" colspan="1">43.4</td><td align="center" valign="bottom" rowspan="1" colspan="1">60.5</td><td align="center" valign="bottom" rowspan="1" colspan="1">55.3</td></tr><tr><td align="center" valign="top" rowspan="1" colspan="1">Two categories</td><td align="center" valign="bottom" rowspan="1" colspan="1">21.7</td><td align="center" valign="bottom" rowspan="1" colspan="1">27.6</td><td align="center" valign="bottom" rowspan="1" colspan="1">48.7</td><td align="center" valign="bottom" rowspan="1" colspan="1">32.9</td><td align="center" valign="bottom" rowspan="1" colspan="1">44.7</td></tr><tr><td align="center" valign="top" rowspan="1" colspan="1">Three categories</td><td align="center" valign="bottom" rowspan="1" colspan="1">12.4</td><td align="center" valign="bottom" rowspan="1" colspan="1">12</td><td align="center" valign="bottom" rowspan="1" colspan="1">7.9</td><td align="center" valign="bottom" rowspan="1" colspan="1">6.6</td><td align="center" valign="bottom" rowspan="1" colspan="1">0</td></tr><tr><td align="center" valign="top" rowspan="1" colspan="1">Four categories</td><td align="center" valign="bottom" rowspan="1" colspan="1">0</td><td align="center" valign="bottom" rowspan="1" colspan="1">3.2</td><td align="center" valign="bottom" rowspan="1" colspan="1">0</td><td align="center" valign="bottom" rowspan="1" colspan="1">0</td><td align="left" valign="bottom" rowspan="1" colspan="1">Not applicable<sup><xref rid="TFN7" ref-type="table-fn">2</xref></sup></td></tr><tr><td align="center" valign="top" rowspan="1" colspan="1">Total occupations rated</td><td align="center" valign="top" rowspan="1" colspan="1">217</td><td align="center" valign="top" rowspan="1" colspan="1">217</td><td align="center" valign="top" rowspan="1" colspan="1">76</td><td align="center" valign="top" rowspan="1" colspan="1">76</td><td align="center" valign="top" rowspan="1" colspan="1">76</td></tr></tbody></table><table-wrap-foot><fn id="TFN6"><label>1</label><p id="P51">Percent of all workers employed in the industry who were exposed at
work</p></fn><fn id="TFN7"><label>2</label><p id="P52">Intensity has 3 rating categories</p></fn></table-wrap-foot></table-wrap></floats-group></article>