Document 2jgy9pvkeXbG6nz0Va7NXa1D5
FILE NAME Brakes BRK
DATE 2016
DOC BRK250
DOCUMENT DESCRIPTION Journal Article - Factors Associated with Non-
Compliance of Asbestos Occupational Standards in Brake Repair Workers
Ann Occup Hyg 2016 1-16 10.1093 mew028
Factors Associated With compliance of
Asbestos Occupational Standards in Brake
Repair Workers
Mar^>aFernanda Garc^>aFrank C. Curriero
Margarita Giraldo Lorena M^'ndezP,,atrick N. Breysse
Mauricio Dur^nC,,arlos A. Duque45
Mauricio Gonz^lezCarolina P^'rezPatricia Parada and Juan Pablo Bonilla,,
Downlade
from 1.Department 1.Department of Civil and Environmental Engineering Universidad de Los Andes Carrera 1 Este 19A ML328 Bogot^111711 Colombia
http 2.Department ofEpidemiology Bloomberg School of Public Health Johns Hopkins University 615 N. Wolfe Street Baltimore MD 21205 USA,
3.Department of Environmental Health Sciences Johns Hopkins University Bloomberg School of Public Health
615 N. Wolfe Street Baltimore MD 21205 USA
4.Medical Department Fundaci^nNeumol^gicaColombiana Cra 13B 161-85 Bogot^110131 Colombia
anbyg
5.Research Department Fundaci^nNeumol^gicaColombiana Cia 13B 161-85 Bogot^110131 Colombia
Currently employed by the Centers for Disease Control and Prevention
Author to whom correspondence should be addressed Tel 571-3394949 fax 571-332-4313 mail jramos@uniandes.edu.co Submitted 8 January 2016 revised 19 April 2016 revised version accepted 25 April 2016
oxfrdjunals
org
ABSTRACT
by
Asbestos and asbestos containing brake products are currently used in low- and income
guest
countries like Colombia Because brake products are distributed detached from their supports they
on
June require manipulation before installation which release fibers and expose workers Previous studies of
our research group have documented exposures in excess of the widely accepted 0.1 cmexposure 8
guideline The aim of this study is to identify factors associated with compliance of the h time
weighted average TWA 0.1 cmasbestos occupational limit among brake mechanics i.e. riveters
2016
Eighteen brake repair shops BRS located in Bogot^Colombia were sampled during 3 to 6 consecu-
tive days for the entire work Personal and short personal samples were collected following
NIOSH methods 7400 and 7402 Longitudinal based logistic regression models were used to deter-
mine the association between the odds of exceeding the h TWA 0.1 cmasbestos occupational limit
and variables such as type of tasks performed by workers workload number of products manipulated
daily years of experience as riveters and shop characteristTihcesse models can be used to estimate
the odds of being currently or historically overexposed when sampling data do not exist Since the
information required to run the models can vary for both retrospective and current asbestos occupa-
tional exposure studies three models were constructed with different information requirements The
first model evaluated the association between the odds of compliance with variables related to
the workload the second model evaluated the association between the odds of compliance with
variables related to the manipulation tasks and the third model evaluated the association between the
'The Author 2016 Published by Oxford University Press on behaofltf he British Occupational Hygiene Society
Page compliance of asbestos standards brake mechanics
odds of compliance with variables related with both the type of tasks performed by workers and the workload Variables associated with the odds of compliance included conducting at least one manipulation activity with beveling and grinding of asbestos and asbestos containing brake products during the work shift the location of the worker in the shop during manipulation activities cleaning activities of the manipulation area the years of experience working as riveters and the number of asbestos and asbestos containing brake products manipulated daily These models could be useful for current and retrospective occupational studies in determining the odds of compliance of the asbestos occupational limit among brake mechanics
KEYWORDS asbestos exposures brake mechanics compliance occupational standards
INTRODUCTION
Recent studies performed by our research group
Asbestos is comprised of a group of minerals that have shown that brake mechanics are exposed to high
because of their physical and chemical characteristics asbestos concentrations exceeding in some cases the
have been extensively used in different types ofproducts US OSHA PEL and the Colombian standards Cely-
Downlade including brake and transmission products ATSDR
2001 OMS 2006 Asbestos is classified into two main groups amphiboles and serpentines ATSDR 2001
Garc^>aet al 2012 Garc^>aet al 2015 These findings are in contrast with studies conducted in income countries Hickish and Knight 1970
Chrysotile is the only type of asbestos of the serpen- Yeung et al 1999 Weir et al 2001 Blake et al
from
tine group and is currently the type of asbestos with 2003 Paustenbach et al 2003 Paustenbach et al
http
the most extended use worldwide ATSDR 2001 2004 Blake et al 2006 Madl et al 2009 One of
an hyg All types of asbestos are classified as carcinogenic to
humans IARC 1998 2012 and asbestos is one of
the most important reasons for this difference is that
in Colombia asbestos containing brake products are
the most important occupational carcinogens OMS distributed by the manufacturer detached from their
oxfrdjunals 2006 Asbestos is related with both malignant and support requiring manipulation in the shops before
malignant diseases ACCP 2012 IARC 2012
installation in the vehicles Garc^>aet al 2012
The most important asbestos exposures occur in Garc^>aet al 2015 Thus brake products are org
occupational environments ACSH 2007 Wagner drilled countersinked riveted beveled and grinded
by
and Lemen 2008 where the manipulation of asbes- and a specific group of mechanics known as riveters
tos containing products may result in excessive asbes- conducts these tasks Garc^>aet al 2012 Cely-
guest
tos exposures OIT 1986 Most of the legislation Garc^>aet al 2015 An additional manipulation task
on
and control activities regarding asbestos exposures observed include bonding the brake linings or brake
June
of brake mechanics and other occupational groups pads to the support in passenger vehicles In this case
8
started in the 1970s OSHA 2013 and in 1994 the riveters have to grind and bevel the brake products in
2016
US Occupational Safety and Health Administration order to remove excess glue Garc^>aet al 2012
OSHA issued the current standards for personal The same riveters that manipulate asbestos containing
asbestos exposure in workplaces a personal exposure brake products may also manipulate asbestos con-
limit US OSHA PEL of 0.1 cmfor an h time taining brake products It is important to clarify that
weighted average TWA based on phase contrast blowing the brake drums with compressed air is not
microscopy equivalent PCM asbestos concen- a common practice of brake mechanics in Colombia
tration and an excursion limit US OSHA EL of 1 /
This study identifies factors associated with personal
cmfor a min exposure period PCM asbestos asbestos concentrations that exceed the h TWA of
concentration OSHA 1994a 2013 In Colombia 0.1 cmasbestos occupational limit among riveters
i.e. an upper income country asbestos expo-
sure standard is based on the American Conference
that manipulate asbestos containing brake products
of Governmental Industrial Hygienists ACGIH threshold limit value TLV of 0.1 cmfor TWA of h MSPS 2011
METHODS
Since 2010 several sampling campaigns were conducted in 18 brake repair shops BRS located in
Factors associated with compliance of asbestos Page 3 of 16
Bogot^Colombia Nine of these shops service passenger vehicles and nine service heavy vehicles Results of these sampling campaigns were used to
longer or shorter personal samples were collected during manipulation activities Each sampling day had one blank sample and each shop had one background
establish the factors associated with the odds of non- sample collected during one night of the sampling days
compliance of the h TWA occupational standard Detailed activity diaries were filled with all the activities
Ethics Committees from the Universidad de Los Andes performed by workers sampled during the entire sam-
and Fundaci^nNeumol^gicaColombiana approved pling campaigns Shop's owners and workers sampled
the sampling campaigns and the informed consent were informed of the results of the sampling campaigns
signed by the riveters that participated in this study
Samples were analyzed by Forensic Analytical
Laboratories Inc Forensic Analytical Laboratories
Sampling campaigns
Hayward CA USA an American Industrial Hygiene
The identification of the shops sampled was initially Association AIHA accredited laboratory The analy-
done using the phone book and in a subsequent stage sis of the samples was performed on a Philips CM12
of the project by walking through the zones of Bogot^ transmission electron microscopy TEM Philips
where BRS are clustered to identify additional shops Eindhoven The Netherlands Fibers with length
that could potentially participate in the project This second strategy has been performed since 2012 and
5 mwere counted at a magnification of 2500 For fibers close to 5 ...min length fiber dimension was
Downlade
from includes the application of a structured question- determined by using a magnification of 10 000. The
naire adapted from the OSHA Medical Questionnaire accelerating voltage used was 100 keV and an Energy
OSHA 1994b to characterize the working conditions Dispersive ray EDXA Evex NanoAnalysis System
http
of those riveters of the shops who agreed to voluntarily participate in the project The information collected was
IV Princeton NJ USA was also used Forensic Analytical Laboratories personal communication
anhyg
used to identify and select BRS that currently perform
Equivalent PCM asbestos concentra-
oxfrdjunals manipulation activities of brake products BRS were
also classified according to their workload based on the
average number of sets of asbestos and asbestos
tions were calculated multiplying the phase contrast microscopy PCM fiber concentration by the fraction of asbestos fibers to total fibers determined by
containing products that they manipulate daily
Transmission Electron Microscopy TEM NIOSH
org
,
Sample collection and analysis was similar to those 1994a 1994b To determine regulatory compliance
by
guest described in previous studies of our research group with the h TWA of 0.1 cmasbestos occupational
Garc^>aet al 2012 Garc^>aet al 2015 limit the h TWA PCM personal asbestos con-
on
June Salazar et al 2014 Shops were sampled during 3 to centration was estimated for each worker When the
6 consecutive days for the entire work Personal work exceeded h the worst period 8
2016 samples were collected following NIOSH methods
7400 NIOSH 1994a and 7402 NIOSH 1994b
sampling windows were used according with the rec-
ommendations of the US OSHA Technical Manual
Air samples were collected on mm MCE filters OSHA 2008 When the work was shorter
0.45 ...mpore size mounted on 50mm conducting than h i.e. due to overloaded samples or because
extension cowls cassettes SKC Preloaded Cassette the work ended early or the worker left the shop
SKC using AIRCheck XR5000 pumps SKC Eighty early the h TWA asbestos concentration was cal-
Four PA USA that operated at a flow rate of 2LPM culated assuming 0 cmfor the remaining time
Standard procedures were applied to measure flow Additionally when the PCM concentration was below
rates at the beginning and at the end of each sampling the limit of detection LOD one half of the LOD was
window using Defender 510 High or 520 High BIOS used for calculation purposes This last procedure was
International Calibrators MesaLabs Butler NJ USA applied because of the results of a sensitivity analysis
Personal samples were collected on riveters dur- performed by our research group in a previous study
ing the entire work All workers sampled were which showed no important differences in the TWA
instructed to keep their activities and working proce- concentration estimated using 0 cmor half the
dures as usual Thirty minutes short personal sam- LOD when samples are below the LOD Garc^>a
ples were collected during manipulation activities and et al 2015
Page . compliance of asbestos standards brake mechanics
Additionally bulk asbestos content of 18 duplicate linings pads or blocks from 12 of the most common brake product's brands that have been used at the shops sampled was estimated following EPA 93-116 PLM method EPA 1993 by an AIHA accredited laboratory Forensic Analytical Laboratories Hayward CA USA
performed during each sample collection the location of the worker during manipulation activities and the number of asbestos and asbestos containing products manipulated daily could be identified
Since information on all the covariates proposed are not always available especially for retrospective expo-
sure assessments three models were evaluated accord-
ing with the type of information that may be obtained
Data analysis Three longitudinal based logistic regression models
and would be available for analysis The first model Model Workload assumes that the information
were used to identify variables significantly associated with the odds of compliance of the h TWA 0.1 cmasbestos occupational limit according with the type of information available to develop the models
available is related with the work load i.e. how many brake products were manipulated and some characteristics of the workers and shops The second model Model Work tasks assumed that the informa-
Eight TWA PCM personal asbestos concen- tion available is related with the work tasks i.e. type of
trations below or equal to 0.1 cmwere classified as
Downlade in compliance and h TWA PCM personal asbes-
tos concentrations exceeding 0.1 cmwere classified
from as compliant The h TWA PCM asbestos
manipulation performed and some characteristics of the workers and shops The third model Model 3Complete was developed for those cases in which the information regarding both work tasks and workload
concentrations calculated for workers sampled were was available
http
an hyg approximated to three decimals and compared against
the 0.100 cmvalue
Samples collected during work with at least
The description of the covariates evaluated and the model in which they were used are detailed in Table 1
Detailed descriptions of the covariates related with
oxfrdjunals one manipulation activity or at least one dry clean- the work tasks i.e. shown in Table ) can be found
ing activity of the manipulation area were analyzed by in previous studies of our research group Garc^>a
both PCM and TEM allowing for the estimation of the et al 2012 Garc^>aet al 2015
PCM asbestos concentration and this information
All models have the following logistic regression
org
was used for the analysis Because a worker could have format for identifying variables significantly associ-
by
more than one h TWA PCM personal asbestos
concentration observations within workers could not
be considered independent Stata 2015 Thus regres-
sion inference utilized robust estimates of standard
ated with the odds of compliance
In OR non compliance ) = ^ o+ ^
+X ^
.X.. ^
guest
on
X
June
8
errors to accommodate the within person correlation Where OR denotes the odds ratio of compliance
UCLA 2015c This was accomplished clustering by relative to compliance X
) are the covariates
2016
riveter in the longitudinal logistic regression models so available based on the model type Table ) and pos-
that estimation of the regression coefficient standard sible interactions and " 'sare their associated effects
errors are adjusted for the lack independence between
All covariates were evaluated and the model build-
the h TWA PCME personal asbestos concentrations ing process started with those predictors statistically
collected on the same riveter on different days
significantly associated with the odds of compli-
Regression covariates evaluated included the type ance in univariate models 1.e. each variable separately
of tasks performed by the workers the workload one at a time Model fit and multicollinearity were
defined as the number of asbestos or asbestos con- evaluated and selection of models was performed
taining products manipulated daily disregarding the type of manipulation performed the shop character-
according with the Akaike's Information Criterion AIC the individual and general results obtained
istics 1.e. ventilation presence of control systems and and personal judgment UCLA 2015b Interactions
type of vehicle serviced and the number of years of were also analyzed in the models The statistical analy-
experience working as riveters Based on observations sis was conducted using the software Stata 12.1
and the detailed activity diaries the type of activities StataCorp College Station TX USA
Factors associated with compliance of asbestos Page 5 of 16
Table 1. Description of the covariates used in the three models evaluated to establish the odds of compliance of the h TWA of 0.1 cmasbestos occupational limit
Covariate
Type of covariate
Description of the covariate
Model that included the covariate
Number asbestos products manipulated daily
Integer variable
Represents the number of asbestos containing brake products i.e. brake linings brake pads or brake blocks
manipulated daily without considering the type of manipulation
performed
Model Workload
Model Complete
Number asbestos
Integer variable
Represents the number of
Model Workload
products manipulated
daily
asbestos containing brake products i.e. brake linings brake
Model Complete
pads or brake blocks manipulated daily without considering the type of
Downlade manipulation performed
from Manipulation w beveling _Indicator variable
Represents at least one
Model Work tasks
http
and grinding of asbestos
manipulation that included
Model Complete
drilling countersinking riveting and bonding asbestos
anhyg
containing brake products one
Manipulation w
oxfrdjunals Indicator variable
or more manipulations = 1 no manipulations = )
Represents at least one
Model Work tasks
o beveling and grinding of
asbestos
manipulation that included Model Complete obryg
drilling countersinking riveting
and bonding asbestos
guest
containing brake products one
on
or more manipulations = 1 no
June
manipulations = 0
8
Manipulation w beveling
Indicator variable
Represents at least one
Model Work tasks
2016
and grinding of asbestos
manipulation that included beveling grinding and cutting with
Model CompleteComplete
electric saw asbestos containing
brake products one or
more manipulations = 1 no
manipulations = ) These tasks
release important amounts of fibers and may also include drilling
countersinking riveting and
bonding asbestos containing
brake products
Page of compliance of asbestos standards brake mechanics
Table 1. Continued
Covariate
Type of covariate
Description of the covariate
Model that included the covariate
Manipulation w beveling and grinding of
asbestos
Indicator variable
Represents at least one
manipulation that included beveling grinding and cutting
with electric saw asbestos
Model Work tasks
Model Complete
containing brake products one
or more manipulations = , no manipulations = 0 These tasks release important amounts of fibers and may
also include drilling countersinking riveting and bonding asbestos
Dry cleaning activities the
Dofwnrloadem manipulation area
_Indicator variable
containing brake products
Represents at least one cleaning activity of the manipulation area performed under dry conditions
Model Work tasks
Model 3 Complete
one or more cleaning activity = , no
http
cleaning = 0
Location of worker during
Indicator variable
Incorporate the location of the
Model Workload
anhyg
manipulation activities
worker during manipulation
Model Work tasks
oxfrdjunals activities either inside ofthe
manipulation area X = ) or outside of the manipulation area X = 0
Model Complete
Ventilation conditions the Indicator variable Represents the ventilation condition Model Workload
org
shop
of the shop good X = ) or bad
Model Work tasks
by
guest X = 0 This classification was based
on the near field concept Cherrie Model Complete on
and Schneider 1999 Tielemans
June
et al 2008 Cherrie et al 2011 If
8
manipulation equipment was within
2016
1 m of a window or door ventilation
was considered good
Presence of control system
Indicator variable
Represents the presence of local
control ventilation in the
manipulation equipment such as fans or extraction systems disregarding
their performance presence of
control system = 1 no control
system = 0
Model Workload Model Work tasks
Model Complete
Experience of worker
Continuous variable
Represents the number of years of
experience working as riveter
Model Workload Model Work tasks
Model Complete
Factors associated with compliance of asbestos Page 7 of 16
Table 1. Continued
Covariate
Type of vehicle serviced in the shop
Type of covariate
Description of the covariate
Model that included the covariate
Indicator variable
Represents the type of shop sampled passenger vehicles BRS X = 0 or heavy duty vehicles BRS X = ) If shop serviced both types of vehicles
it was classified based on the type of
vehicle most commonly served during sampling campaigns
Model Workload
Model - Work tasks Model Complete
hr TWA asbestos concentrations for riveters sampled
90 rm
o
cc
05 _
fe}
0%
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40
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passenger vehicles BRS = heavy duty vehicles BRS |
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Figure 1 Eight TWA PCM asbestos personal concentrations for workers sampled
by
RESULTS
guest measurements five riveters had three repeated measure- on
A total of 28 riveters were sampled Thirteen out the ments and two riveters had one measurement
June twenty riveters were from the nine passenger vehi- Twenty h TWA PCM personal samples 8
2016 cles BRS sampled and the remaining 15 were from the
nine heavy vehicles BRS sampled Forty h
24 exceeded both the US OSHA PEL and the
Colombian standard of 0.1 cmSome of these con-
TWA PCM asbestos exposures were calculated for centrations were up to six times the standard as can be
passenger vehicles riveters and 60 were calculated for observed in Figure 1. Seventeen out of the twenty
heavy vehicles riveters for a total of one hundred h TWA PCM asbestos concentrations above the
three h TWA PCM personal asbestos concentra- occupational standard were collected on riveters from
tions The number of riveters based on both the type of passenger vehicles BRS and the remaining eight were
vehicle serviced and the number of repeated h TWA collected on riveters from heavy vehicles BRS
PCME personal asbestos concentrations each riveter The only type of asbestos identified in personal samples
had was For passenger vehicles BRS i.e. 13 riveters was chrysotile Owners and brake mechanics involved
one riveter had six repeated measurements three riveters in the study were informed regarding the results of the
had five repeated measurements two riveters had four sampling campaigns and we also explained to them
repeated measurements one riveter had three repeated some preventive strategies they could implement to
measurements five riveters had two repeated measure- reduce or eliminate asbestos exposure
ments and one riveter had one measurement For heavy-
The bulk asbestos analysis of 18 duplicate samples
duty vehicles BRS i.e. 15 riveters three riveters had six repeated measurements five riveters had five repeated
oflinings pads or blocks from 12 brands ofbrake products distributed in Bogot^is presented in Table 2. The
Page 8 of 16 compliance of asbestos standards brake mechanics
Table 2. Bulk asbestos content obtained for two linings pads or blocks of 18 product's brands of brake products distributed in Bogot^
Manufacturer
Brand
Type of brake product
Asbestos content %
Sample 1
Sample 2
1
1
Brake lining
10
10
2
Brake block
15
15
2
Brake lining
15
15
Brake block
10
10
Brake block
ND
ND
3
Brake lining
ND
ND
Downlade 4
Brake lining
15
15
3
5
Brake liningb
10
10
Brake blockb
15
15
from
Sheet for brake pads
ND
ND
http
4
67
Brake lining
10
10
anhyg
67
Brake liningab
10
10
oxfrdjunals S
8
Brake liningab
15
15
Brake lining
10
10
org 9 Brake lining 10 10 by
6
10
Sheet for brake pads
10
10
guest
on
June 7
11
Roll for brake lining
S
5
8
12
Brake liningh
15
15
8
ND detected
2016
Product distributed in Bogot^more than 20 years ago
Label ofthe product does not specify that it contain asbestos
Label of the product does not report the asbestos content following standard recommendations EPA 2011 OIT 1984
bulk asbestos analysis showed that only three brake products one brake lining one sheet that is cut into pads and one brake block from three different brands did not contain asbestos fibers 1.e. reported as nondetected For the other 15 brake products analyzed the chrysotile asbestos content ranged between
5 and 15 Asbestos content did not differ between
duplicate samples As shown in Table 2 four brake linings from brands 1 7 and 8 that were used in the past but are no longer distributed were also analyzed i.e.
purchased from old stocks of one of the BRS sampled
Daily workload can be expressed in terms of the number of asbestos containing products manipulated daily ranging from 0 to 50 and the number of asbestos containing products manipulated daily ranging from 0 to 52. Workers experience ranged from 1 to 34 years
Table 3 presents the results of the models evalu-
ated including the longitudinal based univariate logistic regression models for each covariate analyzed and the three longitudinal based multivariate logistic regression models evaluated according with the type
of information available
Factors associated with non-compliance of asbestos
Page 9 of 16
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Page 10 of 16
Non-compliance of asbestos standards brake mechanics
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Factors associated with compliance of asbestos Page 11 of 16
Based on the univariate regression analysis the odds of compliance are 45 times higher with at least one manipulation with beveling and grinding ofasbestos containing products than when this activity is not performed
not shown the value of the interaction term was no longer significant and the AIC coefficient indicated
that the model was more parsimonious without it Thus
this interaction was excluded from Model 1
value = 0.000 are seven times higher with at least one manipulation with beveling and grinding ofasbestos
Model 2 which evaluated the association between
compliance of the asbestos occupational limit and
containing products than when this activity is not performed value = 0.002 and are three times higher with at least one dry cleaning activity of the manipulation area than when this activity is not performed value = 0.063 The odds of compliance are
the work tasks performed by the workers sampled showed that the odds of compliance are 30 times higher with at least one manipulation with beveling and grinding of asbestos containing products than when this activity is not performed value = 0.001 and are
eight times higher when the worker remains inside of the manipulation area than when the worker remains outside
nine times higher when the worker remains inside of the manipulation area during manipulation activi-
during manipulation activities value = 0.039 are ties than when he remains outside value = 0.040
1.1 times higher with each additional asbestos containing and these two associations are statistically significant
products manipulated daily value = 0.082 are 1.1
Downlade times higher with each additional asbestos contain-
ing products manipulated daily value = 0.093 and
from are 77 times lower in heavy duty vehicles BRS than in
The odds of compliance are four times higher with at least one manipulation with beveling and grinding of asbestos containing products than when this activity is not performed value = 0.096 and this association
passenger vehicles BRS value = 0.102
is marginally significant The odds of compliance
http
an hyg Model 1 which was focused on the association
between compliance of the asbestos occupa-
are three times higher with at least one manipulation without beveling and grinding of asbestos contain-
tional limit and the workload of the workers sampled ing products than when this activity is not performed
oxfrdjunals showed that the odds ofcompliance are 1.1 times
higher with each additional asbestos containing product manipulated daily disregarding the type of
value = 0.149 and are two times higher with at least one dry cleaning activity of the manipulation area than when this activity is not performed value = 0.522
manipulation performed and this association is signif- although these two associations are not significant
org
/
icant value = 0.004 The odds of compliance
Several interactions were tested and a potential
by
guest increases six times if the worker remains inside of the effect modifier was identified in Model 2. Similarly to
manipulation area during manipulation activities Model 1 interactions were initially tested with mod-
on
June than when he remains outside and this association els that only included two covariates and their inter-
is marginally significant value = 0.059 Although action term The presence of a control system and at 8
2016 significant the odds of compliance increases
1.1 times with each additional asbestos contain-
least one manipulation without beveling and grinding of asbestos containing products was identified as
ing product manipulated daily disregarding the type of manipulation performed value = 0.277 and
a significant and meaningful interaction Although the
inclusion of the interaction term in Model 2 favored the
increases 1.04 times per each additional year of experi- AIC coefficient it increased the robust standard errors
ence working as riveter value = 0.428
and the 95 confidence intervals were wider For this
Several interactions were tested and a potential reason the interaction term was excluded from Model 2
effect modifier was identified in Model 1. Interactions
Model 3 which evaluated the association between
were initially tested with models that only included two compliance of the asbestos occupational limit and
covariates and their interaction term With these mod- both the workload and work tasks of the workers sam-
els the presence of a control system and the effect of the number of asbestos containing products manipu-
lated daily disregarding the type of manipulation performed was identified as a significant and meaningful
interaction However when the interaction term and
the two covariates were included in Model 1 i.e. results
pled show that the odds of compliance are 49 times higher with at least one manipulation with beveling and grinding of asbestos containing products than when this activity is not performed value = 0.000 and this association is statistically significant The odds of compliance are seven times higher when the
Page of . compliance of asbestos standards brake mechanics
worker remains inside of the manipulation area during
Additional models for the odds of compliance
manipulation activities than when he remains out- were constructed i.e. not shown with detail informa-
side value = 0.058 and this association is marginally tion regarding the number of manipulations and the
significant Although significant the odds of non- tasks involved in each manipulation No significant
compliance are three times higher with at least one dry associations were found Considering that this level
cleaning activity ofthe manipulation area than when this of detail information is difficult and in retrospective
activity is not performed value = 0.249 and increase studies almost impossible to obtain the three models
with each additional asbestos containing product presented in the current study require information
manipulated daily disregarding the type of manipulation that is reasonable to obtain for both current and retro-
performed value = 0.994 and with each additional spective studies which favors these models
year of experience working as riveter value = 0.775
Three different models were constructed offer-
Both interaction terms previously identified in ing different options depending on the information
Model 1 and 2 were evaluated by separate in Model 3 required to run the models The results when analyz-
i.e. results not shown In both cases the AIC coeffi- ing the workload Model ) show that both the num-
cient favored the model with the interactions but nei- ber of asbestos and asbestos containing products
ther was included because they increased the robust
standard errors and the 95 confidence intervals were
manipulated daily increase the odds of compliance The results when analyzing the work tasks per-
Downlade
from wider with the terms Additionally when the interac- formed by workers Model 2 suggest that tasks that
http tions were included the odds of compliance for the
covariate number asbestos products decreased i.e. OR
can potentially release important amounts of fibers are highly associated with the odds of compliance 1.e.
an hyg below ) per each additional asbestos containing prod-
uct manipulated daily disregarding the type of manipu-
manipulation ofbrake products that include beveling
grinding and cutting Furthermore this associa-
lation performed which is a counter intuitive behavior tion was observed not only with asbestos containing
oxfrdjunals DISCUSSION
This study analyzed factors that could be associated with
products but also when asbestos containing products were manipulated This is something also found in
Model 1 with the number of asbestos containing
the odds of compliance of the h TWA 0.1 cm products and is something we have reported in previ-
org
asbestos occupational limit in riveters exposed to chry- ous studies Garc^>aet al 2012 Garc^>aet al
by
guest sotile asbestos that work in BRS in Bogot^Among the 2015 Salazar et al 2014 Two probable reasons why
variables tested the most unportant ones that were asso- the odds of compliance of the asbestos occupa-
on
June ciated with the odds of compliance were the types tional limit could be associated with the manipulation
of tasks performed during the work and the loca- of brake products that do not contain asbestos include 8
2016 tion of the worker during manipulation activities
The number of products manipulated daily 1.e. work-
poor hygiene of the manipulation equipment and lack of maintenance of the shops Poor hygiene and lack
load showed significant associations in the longitudinal based multivariate logistic regression models
of maintenance could result in the accumulation of
asbestos fibers on different surfaces and the subse-
One of the potential uses of the models constructed in the current study is to determine the risk of com-
quent resuspension of the fibers during other activities such as the manipulation of brake products that do not
pliance experienced by workers in countries or situations in which conducting sampling campaigns is not possible Using the models presented in this study compliance of the h TWA 0.1 cmasbestos occupational limit could
contain asbestos Another explanation could be that asbestos containing products were not labeled correctly which may create a false sense of safety in the workers that manipulate these products
be estimated by determining the type of manipulations performed on asbestos and asbestos containing brake products and the number of asbestos and nonasbestos containing brake products manipulated daily This information could be obtained using occupational
The analysis of asbestos content of brake products confirmed the presence of chrysotile asbestos in a range between 5-15 in most of the brake products used in the shops sampled and no other asbestos type
was identified As can be observed in Table 2 the asbes-
questionnaires or observations during work
tos content of brands distributed in the past does not
Factors associated with compliance of asbestos Page 13 of 16
differ from the asbestos content of some of the brands compliance increased i.e. significantly
currently distributed Most of the brands analyzed are
manufactured in Colombia except for Brand 11 which
Since the models were adjusted for the workload higher efficiency of experienced mechanics in per-
has the lowest asbestos content % Furthermore the forming the manipulations which may result in
asbestos content does not seem related with the type higher exposures is already considered in the analysis
of brake product lining block or sheet for pads It is
important to highlight that brands 2 and 5 i.e. manufacturer 2 and 3 respectively have both asbestos and asbestos containing products This seems to contradict one of the arguments of the asbestos industry
against an asbestos ban and is the lack of safer substi-
Experienced mechanics having higher odds of noncompliance contradicts the findings of other occupational groups where it has been observed that less years of experience can result in poor skills to perform the work tasks which may result in higher occupational exposures Andjelkovich et al 1977 Delzell
tutes Furthermore since some of the brake industry is et al 1982
already manufacturing asbestos containing brake
Several authors have recognized the importance ofthe
products a transition to asbestos substitutes in a future workplace characteristics in the estimation of personal
asbestos ban seems to be feasible in the short term
exposures Cherrie and Schneider 1999 Tielemans
Downlade The results suggest that the manipulation equip-
ment used and the type of manipulation performed
et al 2008 Cherrie et al 2011 Ventilation conditions of the shops are one of these characteristics The
from i.e. with or without grinding beveling and cutting longitudinal based univariate logistic regression model
http tasks have a stronger association with the risk of non-
compliance than the number of asbestos containing
performed with the ventilation conditions of the shops showed a significant decrease of the odds of non-
products manipulated daily Furthermore the odds of compliance in shops with good ventilation compared to
compliance are higher when asbestos containing poorly ventilated shops OR 0.4 P = 0.425 However
/anhyg.oxfrdjuls products are manipulated compared to the manipula-
tion of asbestos containing products as expected For all three models Model 1 2 3 the location
of the worker during manipulation activities was
the classification of the ventilation conditions was based
on qualitative assessment of specific characteristics of the shops such as the distance of the manipulation equip-
ment to doors or windows and not quantitative assess-
org marginally or significantly associated with the odds of ment of the air exchange rates The AIC indicated that
compliance This covariate was included because including this covariate did not contribute to the models
by
some personal samples collected during manipu-
Regarding other workplace characteristic the results
guest
lation activities contained asbestos fibers which could of the longitudinal based univariate logistic regression
on
June indicate that asbestos fibers could remain suspended model suggest that the presence of control systems 1.e.
in the air for long periods of time and migrate to other that in most cases included a general extraction system
8
2016 areas of the shop Thus workers that stay or work at the
proximity of the manipulation equipment during non-
does not guarantee the protection ofworkers Although the objectives of this study did not include an evalua-
manipulation activities could be also at risk of asbes- tion of the performance of the existing control systems
tos exposure This is supported by inhalation exposure it was observed that in some occasions workers did not
studies that evaluate both near- and field compart- use them and it seemed i.e. just by observation that
ments Cherrie and Schneider 1999 Tielemans et al in some instances the control system did not redirect
2008 Cherrie et al 2011 De Vocht et al 2013
Dry cleaning activities of the manipulation area
which can suspend fibers had a significant associa-
tion with the odds of compliance using a longitudi-
and extract the fibers released during the manipulation processes This was corroborated by the results of the longitudinal based univariate logistic regression model which showed OR values above 1 although in this case
nal based univariate logistic regression model OR 3.33
P = 0.063 The importance of dry cleaning activities in
predicting the odds of compliance of the asbestos occupational limit was also observed in models 2 and 3
One unexpected result was that as the years of
experience of the mechanic increased the odds of
the association was not statistically significant Additionally the association between the odds
of compliance and the type of vehicle serviced i.e. passenger versus heavy duty showed an OR of 0.235 in the longitudinal based univariate logistic regression model value = 0.102 Thus the type
Page 16 compliance of asbestos standards brake mechanics
of vehicle serviced does not seem to have an influ- Ciencia Tecnolog^>a e Innovaci^n Colciencias
ence on the odds of compliance Moreover the Contract 760-2013 project code 120456933509
convergence of the models evaluated was bad when and grant 567-2012 for doctoral students from
this covariate was included because it increased the the same institution Financial support was also
robust standard errors and made the confidence obtained from the Department of Civil and
intervals very wide
Environmental Engineering and the School of
To the best of our knowledge a sampling cam- Engineering from Universidad de Los Andes and
paign of this size to understand the risk of elevated Fundaci^nMAPFRE
asbestos exposures of brake mechanics has never been
done in low- and income countries However
ACKNOWLEDGEMENTS
as authors we recognize that a larger sample could improve the results in the longitudinal based logistic regression models with the cluster analysis applied in
P.N.B. is serving in his personal capacity The opinions expressed in this article are the author's own and
do not reflect the views of the Centers for Disease
this study UCLA 2015a
Control the Department of Health and Human
Downlade As we have explained in previous studies Cely-
Garc^>aet al 2012 Garc^>aet al 2015 Salazar al 2014 the results ofthe models evaluated confirm
Services and the US government We thank the owners administrative staff brake mechanics and rivet-
ers from the BRS sampled We also acknowledge the
that the physical form some of these brake products are
from distributed i.e. detached from the support results in
http an unavoidable manipulation of asbestos containing
undergraduate students who collected information in the zones where BRS are clustered and to Juliana Uribe and Natalia Salazar for their assistance during
an hyg brake products at the shops making the controlled or
safe use difficult if not impossible to achieve
the sampling campaigns Additionally we acknowledge Mar^>aGrau P^'rezfor her advice in the statistical
Finally it is also important to highlight once analysis Finally we want to thank Alonso Rojas for his
oxfrdjunals again the unacceptable working conditions of these
workers Out of the one hundred three h TWA
PCM personal asbestos concentrations esti-
help during the sampling campaigns The authors have
no conflict of interest to declare
org mated 24 exceeded the Colombian standard and
REFERENCES
guest the US OSHA PEL of 0.1 cmasbestos occupa-
by
ACCP 2012 Chapter 18. Pneumoconiosis In Kamp DW
tional limit Furthermore 15 of the samples were
editor American College of Chest Physicians Pulmonary
in compliance but above the USA OSHA PEL action
Medicine Board Review 26th edn Glenview IL American
on
June level of 0.050 cmThe highest exposures were
College of Chest Physicians pp 259-83
observed in three riveters that had high workloads ACSH 2007 Asbestos exposure How risky is it Available
8
2016 and that worked in two poorly ventilated passenger
vehicles BRS who also bond and grind the brake products to remove excess glue and in two riveters from another poorly ventilated passenger vehicle
at http://www.acsh.org/docLib/20071015_Asbestos.pdf Accessed 5 April 2011
Andjelkovich D TaulbeeJSymons M et al 1977 Mortality of
rubber workers with reference to work experience J Occup
Med 19 397 405
BRS with a medium workload In this last shop ATSDR 2001 Toxicology profile for asbestos Atlanta GA
asbestos fibers accumulated over the floor and the
Agency for Toxic Substances and Disease Registry U.S
manipulation equipment Similarly to the conclu-
Department of Health and Human Services Available at
sions of previous studies conducted by our research
http://www.atsdr.cdc.gov/toxprofiles/tp61http://www.atsdr.cdc.gov/toxprofiles/tp61 pdf Accessed
group with auto mechanics these workers experi-
ence high asbestos occupational personal exposures and because of this they are at excessive risk of developing asbestos related diseases
5 April 2011 Blake CL Dotson GS Harbison RD 2006 Assessment of an-
borne asbestos exposure during the servicing and handling of automobile containing gaskets Regul Toxicol Pharmacol 45 214 22
Blake CL Van Orden DR Banas~-kM et al 2003 Airborne
FUNDING
asbestos concentration from brake changing does not
This study was funded with a grant from the Colombian Departamento Administrativo de
exceed permissible exposure limit Regul Toxicol Pharmacol
38 58-70
Factors associated with compliance of asbestos Page 15 of 16
Cely Garc^>a MF S^nchez M Breysse PN et al 2012 Personal exposures to asbestos fibers during brake maintenance of passenger vehicles Ann Occup Hyg 56
NIOSH 1994a 7400 Asbestos and other fibers by PCM Available at http://www.cdc.gov/niosh/docs/2003-154/ 7400.pdf Accessed February 2010
985-99
NIOSH 1994b 7402 Asbestos by TEM Available at http
Garc^>aMF Duque CA M Dur^n et al 2015
Personal exposure to asbestos and respiratory health of
www.cdc.gov/niosh/docs/2003-154/pdfs/7402.pdf Accessed February 2010
heavy vehicle brake mechani] Ecxpso Sci Environ Epidemiol
25 26-36
OIT 1984 Seguridad en la Utilizaci^ndel Anuanto Ginebra Suiza Organizaci^nInternacional del Trabajo Available at
CherriJeW Maccalman L W Fransman et al 2011 Revisiting
the effect of room size and general ventilation on the rela-
http://aragon.ugt.org/slaboral/normativa/europea/am~-anto.pdf Accessed 5 April 2011
tionship between near- and field air concentrations Ann OIT 1986 Convenio 162 de la OIT sobre la utilizaci^n del
Occup Hyg 55 1006 15
asbesto en condiciones de seguridad Ginebra Suiza Instituto
Cherrie JW Schneider T. 1999 Validation of a new method
Nacional de Seguridad e Higiene en el Trabajo Organizaci^n
for structured subjective assessment of past concentrations
Internacional del Trabajo Available at //www.insht
Ann Occup Hyg 43 235-45
Contenidos
De Vocht F Northage C Money C et al 2013 The future
162delaoitsobreutiliza-
of exposure assessment perspectives from the X2012
ciondelasbestoencondiciones.pdf Accessed 5 April 2011
Conference Ann Occup Hyg 57 280 5
Delzell E Andjelkovich D Tyroler HA 1982 A control
Downlade study of employment experience and lung cancer among
from rubber workers Am J Ind Med 3 393 404
OMS 2006 Eliminaci^nde las enfermedades relacionadas con asbestos Available at http://apps.who.int/iris/bit-
WHO_SDE_OEH_06.WHO_S0 DE_OEH_06.3 03_spa W_ HO_SDE_OEs H_06.03_sp pa WHO_SDEa _OEH_06.03_spa
pdf Accessed 2 May 2011
EPA 1993 EPA Method for the OSHA 1994a Occupational Safety and Health Standards Toxic
http
Determination of Asbestos in Bulk Building Materials
and Hazardous Substances Standards 29CFR
Available at http://www.epa.gov/region1/info/test-
1910-1001 Available at htps:/ww.osha.gov/pls/oshaweb/ https://www.osha.gov/pls/oshaweb/
EPA_600R93116_bulk_asbestos
owadisp.show_document
part1.pdf
9995 Accessed November 2013
/anhyg.oxfrdjuls EPA 2011 40 CFRPart763 Subpart I -- Prohibitionofthe Manufacture Importation Processing and Distribution in Commerce of Certain Contianing products Labeling Requirements Available at www gpo.gov/fdsys/pkg/CFR-2011-title gpo.gov/fdsys/pkg/CFR-2011-title CFR-
OSHA 1994b Regulations Standards CFR Medical questionnaires mandatory Available at www osha.gov/pls/oshaweb/owadisp.show_document?p_ STANDARDS Accessed September 2011
OSHA 2008 Personal sampling for air contaminants OSHA
title40 part763 I.pdf Accessed 27
Technical Manual OTM Section II Chapter 1. Available
by
guest October 2015
at https://www.osha.gov/dts/osta/otm/otm_u/otm_i_1
Hickish DE Knight KL 1970 Exposure to asbestos during
order_sampling_media Accessed July 2013
on
brake maintenance Ann Occup Hyg 13 17 21
OSHA 2013 TODO SOBRE LA OSHA 3171-01R
IARC 1998 Asbestos Actinolite Amosite Anthophyllite
Available at http://www.osha.gov/Publications/osha3173
June
Chrysotile Crocidolite Tremolite Supplement 7 1987
pdf Accessed June 2013
8
Available at h_ttp://www.inchem.org/documents/iarc/ Paustenbach DJ Finley BL Lu ET et al 2004 Environmental
2016
asbestos.html Accessed 24 September 2013
and occupational health hazards associated with the pres-
IARC 2012 IARC Monographs on the Evaluation of
ence of asbestos in brake linings and pads 1900 to pre-
Carcinogenic Risks to Humans Asbestos chrysotile
sent a state review J Toxicol Environ Health
amosite crocidolite tremolite actinolite and anthophyl-
7 33
110
lite Volume 100C Available at //monographs.iarc Paustenbach DJ Richter RO Finley BL et al 2003 An evalu-
Monographs Accessed 31
ation of the historical exposures of mechanics to asbestos in
October 2015
brake dust Appl Occup Environ Hyg 18 786 804
Madl AK Gaffney SH BalzeJrL et al 2009 Airborne asbes-
tos concentrations associated with heavy equipment brake
Salazar N Garc^>aMF Breysse PN et al 2014 Asbestos
exposure among transmission mechanics in automotive
removal Ann Occup Hyg 53 839 57
repair shops Ann Occup Hyg 59 292-306
MSPS 2011 Ministerio de Salud y Protecci^nSocial 2011 Stata 2015 vce_options estimators Available
Resoluci^n007 de 2011 polra cual se adopta el Reglamento
de Higiene y Seguridad del Crisotilo y otras fibras de uso
at http://www.stata.com/manuals
Accessed 6 October 2014
similar Available at htp:/fondoriesgoslaborales.gov.co/ http://fondoriesgoslaborales.gov.co/
Normatividad
Tielemans E Schneider T Goede H et al 2008 Conceptual model for assessment of inhalation exposure defining mod-
pdf Accessed November 2011
ifying factors Ann Occup Hyg 52 577-86
Page 16 compliance of asbestos standards brake mechanics
UCLA 2015a UCLA Statistical Consulting Group Analyzing Correlated Clustered Data Available at //www.ats.ucla cpsu.htm Accessed 10 November 2014
UCLA 2015b UCLA Statistical Consulting Group Lesson 3 Logistic Regression Diagnostics Available at http www.ats.ucla.edu/stat/stata/webbooks/logistic/chapter3/ www.ats.ucla.edu/stat/stata/webbooks/logistic/chapter3/ statalog3.htm Accessed 10 November 2014
UCLA 2015c UCLA Statistical Consulting Group Regression with Stata Chapter Beyond OLS Available at http://www.ats.ucla.edu/stat/stata/webbooks/reg/chapstatareg4.htm Accessed 10 November 2014
Wagner GR Lemen R. 2008 Asbestos In Heggenhougen K editor International Encyclopedia of Public Health San Diego CA Academic Press pp 238 45
Weir FW Tolar G Meraz LB. 2001 Characterization of vehicular brake service personnel exposure to airborne asbestos and particulate Appl Occup Environ Hyg 16
1139-46
Yeung P Patience K Apthorpe L et al 1999 An Australian
study to evaluate worker exposure to chrysotile in the automotive service industry Appl Occup Environ Hyg 7
449-58
Downlade
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