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Abstract

Rudimentary methods for electronic waste (e-waste) recycling employed in developing countries are a source of work-related musculoskeletal disorders (WRMSDs). A summarized comparison of WRMSDs and preliminary exposure assessment among e-waste dismantlers (D) and burners (B) in Agbogbloshie, Ghana is presented. A cross-sectional study was conducted to investigate WRMSDs and associated risk factors using the Cornell Musculoskeletal Discomfort Questionnaire and a newly developed ergonomic assessment tool. Results indicated higher WRMSDs prevalence in the lower back (68% D vs. 52% B; p = 0.172), shoulder (41% D vs. 29% B; p = 0.279) and upper arm (33% D vs 5% B; p = 0.010). Moderate to severe trunk flexion, high force exertion, repetition and vibration were prevalent risk factors among workers and were significantly higher in dismantlers than burners ( p ≤ 0.001). Detailed ergonomic studies investigating the relationship between physical exposures and WRMSDs are needed to provide a deeper understanding of WRMSD causation in e-waste workers and more particularly in unstructured, unregulated work.
Comparison of ergonomic risk factors and work-related
musculoskeletal disorders among dismantler and burners of
electronic waste in Agbogbloshie, Accra Ghana
Augustine A. Acquah1, Clive D'Souza2, Bernard J. Martin2, John Arko-Mensah1, Niladri
Basu4, Isabella A. Quakyi1, Thomas G. Robins3, Julius N. Fobil1
1.Department of Biological Environmental and Occupational Health Sciences, School of Public
Health, University of Ghana, Accra, Ghana.
2.Center for Ergonomics, Department of Industrial and Operations Engineering, University of
Michigan, Ann Arbor, USA.
3.Environmental Health Sciences, School of Public Health, University of Michigan, Ann Arbor,
USA.
4.Faculty of Agricultural and Environmental Sciences, McGill University, Montréal, QC, Canada.
Abstract
Rudimentary methods for electronic waste (e-waste) recycling employed in developing countries
are a source of work-related musculoskeletal disorders (WRMSDs). A summarized comparison
of WRMSDs and preliminary exposure assessment among e-waste dismantlers (D) and burners
(B) in Agbogbloshie, Ghana is presented. A cross-sectional study was conducted to investigate
WRMSDs and associated risk factors using the Cornell Musculoskeletal Discomfort Questionnaire
and a newly developed ergonomic assessment tool. Results indicated higher WRMSDs prevalence
in the lower back (68% D vs. 52% B;
p
= 0.172), shoulder (41% D vs. 29% B;
p
= 0.279) and
upper arm (33% D vs 5% B;
p
= 0.010). Moderate to severe trunk flexion, high force exertion,
repetition and vibration were prevalent risk factors among workers and were significantly higher
in dismantlers than burners (
p
≤ 0.001). Detailed ergonomic studies investigating the relationship
between physical exposures and WRMSDs are needed to provide a deeper understanding of
WRMSD causation in e-waste workers and more particularly in unstructured, unregulated work.
INTRODUCTION
Technological advancement and the high demand for electronic and electrical appliances
generates huge quantities of discarded electronic waste (e-waste) annually (Perkins et al.,
2014). In developing countries such as Ghana, e-waste is recycled by low skilled, low wage
workers who use basic and informal recycling methods (Acquah et al., 2019b; Akormedi et
al., 2013; Amankwaa, 2013). Informal e-waste recycling includes scavenging for end-of-life
electronics, manual disassembly of e-waste items to separate the different metal constituents,
and open air burning of insulated components (e.g., copper cables) to retrieve valuable
metals for sale (Acquah et al., 2019b). The rudimentary methods used in informal e-waste
recycling presents enormous health risks to workers and the nearby population (Fischer et
al., 2020; Grant et al., 2013) due to exposure to air pollutants (Amoabeng Nti et al., 2020;
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Kwarteng et al., 2020), excessive noise levels (Burns et al., 2019; Burns et al., 2016) and
physical agents associated with poor work methods (Acquah, et al., 2021b; Acquah et al.,
2019b).
Agbogbloshie, in Accra Ghana is one of the largest e-waste dumpsites and informal e-waste
processing hubs in Africa. A recent assessment of physical work exposures at this site found
that prolonged walking (often over uneven terrain), sitting, standing and performing manual
material handling (MMH) tasks such as carrying, lifting, and pushing of loaded collection
carts were prominent among e-waste workers (Acquah et al., 2021b). These exposures are
known risk factors for the development of WRMSDs (Jaffar et al., 2011; Kwon, et al., 2011;
Marshall et al., 2000; Wai et al., 2010) and might explain the high prevalence (~90%) of
MSD symptoms in this population (Acquah et al., 2019a; Acquah, et al., 2021a).
To better understand and systematically characterize the type, duration and intensity of
ergonomic risk factors among informal e-waste workers, Acquah et al. (2020) developed an
observation-based tool specifically adapted to unstructured work settings such as e-waste
recycling operations at the Agbogbloshie dumpsite, in Accra. The present study aimed to
provide a summary comparison of WRMSDs and likely associated ergonomic risk factors
using pilot data from the newly developed ergonomic assessment tool (Acquah et al., 2020)
among e-waste dismantlers and burners.
METHODS
Study Procedure
This study was approved by the College of Health Sciences Ethical Review Committee
at the University of Ghana. All participants provided written informed consent prior to
data collection. The Cornell Musculoskeletal Discomfort Questionnaire (Cornell-University,
1999) was used to collect information on MSD symptoms reported among 103 male e-waste
workers in Agbogbloshie, comprising 82 dismantlers and 21 burners (Acquah et al., 2021a).
This was followed by a pilot assessment of risk factors based on a newly developed
tool adapted for unstructured work (Acquah et al., 2020). This pilot phase included 3
dismantlers and 3 burners at Agbogbloshie. The workers were observed for a full work-day
with observations coded at 60s intervals onto a paper template (Acquah et al., 2020) and
subsequently entered into Microsoft Excel for data processing and analysis. The proportion
of time workers were exposed to various ergonomic risk factors such as posture, force,
repetition, vibration, contact stress, and MMH activities (e.g., lifting and carrying) were
computed as a function of their severity.
Statistical Analysis
Descriptive statistics were used to identify the most prevalent body parts for which MSD
symptoms were reported. Separate Chi-square test were used to compare differences in the
proportion of e-waste dismantlers and burners reporting MSD symptoms for each of the four
body parts most frequently affected. Ergonomic exposure was reported as the proportion of
work time dismantlers and burners were exposed to the various physical risk factors. The
proportions were computed for each worker category by dividing the total observed time the
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workers were exposed to the specific risk factor being investigated by the total full day work
time the worker was observed. A two-sample test of proportions was used to compare the
difference in proportion of time dismantlers and burners were exposed to specific ergonomic
risk factors. Statistical analyses were performed using STATA v.15 and the significance level
was set at
p
< 0.05.
RESULTS
Participants’ ages ranged from 18 to 42 years. The mean ± SD age was significantly higher
(
p
= 0.012) for dismantlers (26.4 ± 6.5) than burners (22.9 ± 3.8). Job experience ranged
from 1 to 25 years. The number of years on the job was significantly higher (
p
= 0.007) for
dismantlers (7.6 ± 5.3) than burners (5.5 ± 3.1). Days worked per week ranged from 2 to
7 days with a mean of 6.1 ± 1.0 days but did not differ between dismantlers and burners.
Hours worked per day ranged from 1 to 14 hours with a mean ± SD of 9.7 ± 3.0 hours but
did not differ significantly between groups.
The four body parts most frequently affected by MSD symptoms were the lower back
(65%), shoulders (39%), upper arms (27%), and neck (27%). MSD symptoms prevalence
were higher for dismantlers compared to burners (Table 1), and this difference was
statistically significant for the upper arm (33% vs. 5%;
p
= 0.010).
Sustained non-neutral neck posture is a known ergonomic risk factor for WRMSDs in the
neck. Dismantlers spent a significantly higher percentage of their work time in non-neutral
neck postures compared to burners (99% vs. 81%;
p
≤ 0.001). Ergonomic exposures related
to lower back pain included the total duration of moderate and severe trunk flexion, which
was significantly longer for dismantlers than burners (80% vs. 1%;
p
≤ 0.001). MMH is also
a risk factor for low back pain, and was almost negligible for both dismantlers (1%) and
burners (1.5%;
p
= 0.513).
High force exertion, repetition and vibration, which are known risk factors for shoulder and
upper arm MSDs, were also observed (Table 2). Dismantlers were exposed to high force
exertion and repetition for 67% and 85% of their work time, respectively, compared to
0.1% and 74% respectively for burners. These higher exposure to force and repetition for
dismantlers compared to burners were statistically significant (
p
≤ 0.001; Table 2).
WRMSDs in the upper extremities were also common, e.g., 39% shoulder pain and 27%
upper arm pain. Shoulder pain was higher among dismantlers compared to burners (41% vs.
29%) although the difference was not statistically significant. However, the prevalence of
WRMSD symptoms in the upper arm was significantly higher in dismantlers compared to
burners (33% vs. 5%;
p
= 0.010). In addition, both dismantlers and burners spent 99% of
their time working with their hands below waist height, which is outside the preferred range
between the shoulder and waist height, i.e., recommended “power zone”, for safe MMH.
DISCUSSION
Informal e-waste workers in low and middle income countries have a high prevalence of
work-related MSDs (Acquah et al., 2021a; Fischer et al., 2020; Acquah et al., 2019a;
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Ohajinwa et al., 2018). Lower back pain (LBP) is generally the most commonly reported
MSD symptom (Fischer et al., 2020; Ohajinwa et al., 2018; Acquah et al., 2021a). Not
surprisingly, LBP was the most prevalent MSD reported in this study. LBP reported in this
study (65%) was higher than LBP prevalence among e-waste workers in Nigeria reported by
Ohajinwa et al. (2018), but lower than work-related back pain prevalence (91.6%) reported
by Fischer et al. (2020) among e-waste workers in Ghana. The higher prevalence by Fischer
et al. (2020) may have been due to a broader categorization which included all back pain as
opposed to a more specific categorization of "lower back" pain in the present study. Among
the known risk factors for LBP, the present study found prolonged exposures to moderate
and severe trunk flexion and to MMH activities such as carrying and lifting. However, MMH
(e.g., lifting and carrying) was seldom performed (~2% of total work time) by the few
observed workers. This could imply a minimal contribution of carrying and lifting to work-
related LBP compared to other risk factors such as non-neutral trunk posture. However,
handling of heavy loads even for short durations could contribute to the development of
LBP if performed with an incorrect posture (e.g., stooped vs. squat posture). Acquah et al.
(2021b) found that e-waste workers perform lifting, carrying, and pushing/pulling tasks on
five or more days in a work week; however, their study relied on self-reported data unlike
the present study which used direct observations. Hence, the cumulative effect of MMH
activities may be worth considering in future studies.
Considering the inconsistent findings in prior studies, a detailed assessment of ergonomic
exposures is needed. Given the high variability in recycling tasks performed by this
population (Acquah et al., 2021b), the preferred method to study physical exposure and
MSD relationships among this population may be to observe workers for the entire work
week and their MSD symptoms assessed before and at the end of the work week.
Upper extremity pain has also been reported among e-waste workers in Chile (51% pain
prevalence in the wrist/hand) and Nigeria (14% prevalence in shoulder pain). Our results
differ slightly. These differences may stem from differences in the categories of workers
observed, the diversity of their tasks, as well as the work methods used (e.g., use of
manual hand tools). In our study, job category (dismantler vs. burner) appears to be a
significant factor as dismantlers used higher force exertion for much longer periods than
burners. The repetition of manual activities was also greater for dismantlers than burners.
The combination of the observed risk factors might explain the higher prevalence of upper
extremity WRMSDs in dismantlers compared to burners.
Overall, comparison of WRMSD prevalence between studies may be difficult as exposure
assessment may not be detailed. Furthermore, our pilot work indicates substantial work
variability within and between workers, and thus requires an assessment method adapted to
unstructured work. Limited access to measurement instrumentation and financial resources
for ergonomics research in Ghana present additional challenges to using direct methods for
measuring physical exposures among informal e-waste workers.
Study Implications and Limitations
The present study attempted to provide an overview of WRMSD prevalence among e-waste
dismantlers and burners. Findings draw attention to the identification of ergonomic risk
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factors that may be associated with these MSDs. Despite the preliminary nature of this
study with a small number of participants, it shows the importance of using a low-cost
method adapted to this type of informal work and for differentiating exposures between
worker categories. This study was not intended to determine precise associations between
work-related MSDs and physical exposures. The MSD and physical exposure data were
obtained about a year apart. Considering these limitations, the information presented should
be considered preliminary. However, the findings are potentially useful for guiding the study
design of more rigorous investigations of physical exposures in unstructured work, and for
developing a method to identify the most harmful risk factors, such as by computing severity
scores, when prioritizing targets for ergonomics interventions.
RECOMMENDATION
The present findings emphasize variability in the context of unstructured work. Hence,
we recommend use of an observation-based exposure assessment tool adapted to the work
context and extending the observation sampling over periods of at least a week to obtain
stable estimates of key exposure variables associated with WRMSDs. Findings also point to
the need for stratifying exposures by job category.
ACKNOWLEDGEMENTS
This work was supported by the West Africa-Michigan Charter II in GEOHealth; jointly funded by the US
NIH Fogarty International Center under award #U01 TW010103 and by the Canadian International Development
Research Centre under award #108121-001. Co-authors CD and BM were supported in part by the training grant
T42-OH008455 from the National Institute for Occupational Safety and Health (NIOSH), Centers for Disease
Control and Prevention (CDC). The views expressed in this publication do not necessarily reflect the official
policies of nor endorsement by NIH, NIOSH, CDC, and/or the Canadian and US Governments.
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Acquah et al. Page 7
Table 1:
Comparison of MSD discomfort prevalence among e-waste dismantlers (n = 82) and burners (n = 21).
Body Part MSD Prevalence (% work time) Test Statistic
Dismantlers (n = 82) Burners (n = 21)
Neck 23 (28%) 5 (24%) χ2 = 1.51,
p
= 0.697
Lower back 56 (68%) 11 (52%) χ2 = 1.86,
p
= 0.172
Shoulder 34 (41%) 6 (29%) χ2 = 1.17,
p
= 0.279
Upper arm 27(33%) 1(5%) χ2 = 6.70, p = 0.010
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Acquah et al. Page 8
Table 2:
Comparison of ergonomic exposures among e-waste dismantlers (n = 3) and burners (n = 3).
Risk Factor Average Exposure (% work time) Two-sample test
Dismantlers Burners
Non-neutral neck posture 99% 81% p ≤ 0.001
Moderate trunk flexion 80% 1% p ≤ 0.001
Severe trunk flexion 19% 76% p ≤ 0.001
Working with hands below waist height 99% 100%
p
= 0.098
High force exertion 67% 0% p ≤ 0.001
High repetitions 85% 74% p ≤ 0.001
Vibration 78% 3% p ≤ 0.001
Lifting/Carrying 1% 2%
p
= 0.513
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... Table S1: PRISMA 2020 checklist, Table S2: Search strategies and results from different electronic databases, Table S3: Methodological quality of included cross-sectional studies, Table S4: Methodological quality of included cohort studies, Table S5: List of excluded studies at full-text screening stage with brief reasons, Table S6: JBI Critical Appraisal Checklist for Analytical Cross Sectional Studies, Table S7: JBI Critical Appraisal Checklist for Cohort Studies. References [62][63][64][65][66][67][68][69][70] are cited in the supplementary materials. ...
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Abstract Air quality information is scarce in low‐ and middle‐income countries. This study describes the application of moderate cost approaches that can provide spatial and temporal information on concentrations of particulate matter (PM) needed to assess community and occupational exposures. We evaluated PM levels at the Agbogbloshie e‐waste and scrap yard site in Accra, Ghana, and at upwind and downwind locations, obtaining both optical and gravimetric measurements, local meteorological data and satellite aerosol optical depth. Due to overload issues, the gravimetric 24‐hr samplers were modified for periodic sampling and some optical data were screened for quality assurance. Exceptionally high concentrations (e.g., 1‐hr average PM10 exceeding 2000 μg/m3) were sometimes encountered near combustion sources, including open fires at the e‐waste site and spoil piles. 24‐hr PM2.5 levels averaged 31, 88 and 57 μg/m3 at upwind, e‐waste and downwind sites, respectively, and PM10 averaged 145, 214 and 190 μg/m3, considerably exceeding air quality standards. Upwind levels likely reflected biomass burning that is prevalent in the surrounding informal settlements; levels at the e‐waste and downwind sites also reflected contributions from biomass combustion and traffic. The highest PM levels occurred in evenings, influenced by diurnal changes in emission rates, atmospheric dispersion and wind direction shifts. We demonstrate that moderate cost instrumentation, with some modifications, appropriate data cleaning protocols, and attention to understanding local sources and background levels, can be used to characterize spatial and temporal variation in PM levels in urban and industrial areas.
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Background: Direct and continuous exposure to particulate matter (PM), especially in occupational settings is known to impact negatively on respiratory health and lung function. Objective: To determine the association between concentrations of PM (2.5, 2.5-10 and 10 µm) in breathing zone and lung function of informal e-waste workers at Agbogbloshie. Methods: To evaluate lung function responses to PM (2.5, 2.5-10 and 10 µm), we conducted a longitudinal cohort study with three repeated measures among 207 participants comprising 142 healthy e-waste workers from Agbogbloshie scrapyard and 65 control participants from Madina-Zongo in Accra, Ghana from 2017-2018. Lung function parameters (FVC, FEV1, FEV1/FVC, PEF, and FEF 25-75) and PM (2.5, 2.5-10 and 10 µm) concentrations were measured, corresponding to prevailing seasonal variations. Socio-demographic data, respiratory exposures and lifestyle habits were determined using questionnaires. Random effects models were then used to examine the effects of PM (2.5, 2.5-10 and 10 µm) on lung function. Results: The median concentrations of PM (2.5, 2.5-10 and 10 µm) were all consistently above the WHO ambient air standards across the study waves. Small effect estimates per IQR of PM (2.5, 2.5-10 and 10 µm) on lung function parameters were observed even after adjustment for potential confounders. However, a 10 µg increase in PM (2.5, 2.5-10 and 10 µm) was associated with decreases in PEF and FEF 25-75 by 13.3% % [β = −3.133; 95% CI: −0.243, −0.022) and 26.6% [β = −0.266; 95% CI: −0.437, 0.094]. E-waste burning and a history of asthma significantly predicted a decrease in PEF by 14.2% [β = −0.142; 95% CI: −0.278, −0.008) and FEV1 by 35.8% [β = −0.358; 95% CI: −0.590, 0.125] among e-waste burners. Conclusions: Direct exposure of e-waste workers to PM predisposes to decline in lung function and risk for small airway diseases such as asthma and COPD.
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Informal e-waste recycling is associated with several health hazards. Thus far, the main focus of research in the e-waste sector has been to assess the exposure site, such as the burden of heavy metals or organic pollutants. The aim of this study was to comprehensively assess the health consequences associated with informal e-waste recycling. A questionnaire-based assessment regarding occupational information, medical history, and current symptoms and complaints was carried out with a group of n = 84 e-waste workers and compared to a control cohort of n = 94 bystanders at the e-waste recycling site Agbogbloshie. E-waste workers suffered significantly more from work-related injuries, back pain, and red itchy eyes in comparison to the control group. In addition, regular drug use was more common in e-waste workers (25% vs. 6.4%). Both groups showed a noticeable high use of pain killers (all workers 79%). The higher frequency of symptoms in the e-waste group can be explained by the specific recycling tasks, such as burning or dismantling. However, the report also indicates that adverse health effects apply frequently to the control group. Occupational safety trainings and the provision of personal protection equipment are needed for all workers.
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Electronic waste (e-waste) is a worldwide problem in terms of increasing production rate in the global waste stream. Its recycling is known to be associated with adverse health outcomes. The recycling site at Agbogbloshie is a major e-waste recycling hub which presents enormous health threats to the residents in this community as a result of exposure to complex mixtures of chemicals associated with the poor work methods employed. This paper describes the processes involved in e-waste recycling at Agbogbloshie and discusses some of the associated health and psychosocial challenges. Direct field observations and in-depth interviews of eight e-waste workers were conducted from November, 2017 to December, 2017. Results from a thematic analysis of the data gathered; suggest that inappropriate recycling methods, financial constraints, and the high physical demands of e-waste recycling work were associated with adverse musculoskeletal health conditions among the workers. A more systematic ergonomic study is currently being undertaken to quantify the associations between physical work exposures and worker musculoskeletal health among e-waste workers in Agbogbloshie. Further studies that focus on locally adapted ergonomic interventions for effective recycling of e-waste and reducing the health risk to workers are needed.
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Background/Aim: E-waste recycling at Agbogbloshie consists mainly of collection, dismantling and burning of electronic waste. Processes involved are highly informal and physically demanding, consisting of varying levels of lifting, torso bending and twisting, prolonged sitting and standing. These activities are likely to cause musculoskeletal disorders (MSDs). Thus far, studies on adverse health effects of e-waste recycling have focused ostensibly on chemicals and/or particulate matter. This study investigated the prevalence of MSDs among e-waste workers at Agbogbloshie, Accra Ghana; one of the world’s largest e-waste recycling sites. Methods: The Cornell musculoskeletal discomfort questionnaire was used to obtain information on the occurrence of MSDs in 11 specific body regions of 163 e-waste workers. Descriptive statistics was used to summarize information on MSD prevalence. Chi-squared and regression analyses were used to examine relationships between e-waste recycling job categories and MSD frequency and severity. Results: The study sample consisted of 70 collectors, 73 dismantlers and 20 burners working an average of 6 days per week, for an average duration of 9.95  2.43 hours per day. Analysis indicated an overall MSD prevalence of 90% among e-waste workers. The 6 body regions where MSDs were most commonly reported included the lower back (65%), knee (39%), shoulder (37%), upper arm (30%), lower leg (27%) and neck (26%) respectively. Significant associations between e-waste job category and the frequency (p = 0.032) and severity (p = 0.005) of MSDs were found. For collectors the odds of developing knee and lower leg MSDs were 0.08(0.01-0.67) and 0.17(0.07-0.43) respectively compared to dismantlers. For dismantlers, the odds of developing MSD in the upper arm was 0.08(0.01-0.67) compared to burners. Conclusions: E-waste workers in Agbogbloshie experience an alarmingly high prevalence of MSDs. Reducing the occurrence of MSDs among e-waste workers will require effecting change through contextually and locally adapted ergonomic interventions.
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Background Electronic waste (e-waste) recycling workers in low and middle-income countries have the potential for occupational injuries due to the nature of their work at informal e-waste sites. However, limited research exists on stress, noise, occupational injuries, and health risks associated with this work environment. This study evaluated injury experience, noise exposures, and stress risk factors among e-waste workers at the large recycling site in the Agbogbloshie market, Accra, Ghana. Methods Participants completed a survey addressing their work, health status, stress, exposures to several occupational hazards (including noise), use of personal protective equipment at work, and injury experience. A subset of participants also completed personal noise dosimetry measurements. Poisson regression was used to evaluate the association between the number of injuries experienced by participants and various factors evaluated in the survey. Results Forty-six male e-waste workers completed the survey, and 26 completed a noise dosimetry measurement. Participants experienced an average of 9.9 ± 9.6 injuries per person in the previous 6 months (range: 1–40). The majority of injuries were lacerations (65.2%), and the most common injury location was the hand (45.7%). Use of personal protective equipment was rare. The mean time-weighted average noise level was 78.8 ± 5.9 dBA. Higher perceived stress, greater age, poorer health status, not using gloves, and involvement in dismantling activities were associated with an increased number of injuries. After controlling for each of these risk factors, perceived stress level and perceived noise exposure were associated with a significantly greater number of injuries. Conclusions Our study identified a large number of injuries among informal e-waste recyclers, and we found that higher levels of perceived stress and perceived noise were associated with an increased number of occupational injuries, even after controlling for other injury risk factors.
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Waste collection workers are frequently exposed to significant occupational hazards. Even though ergonomic interventions can mitigate these occupational hazards, only a few studies have attempted to study the importance of the interventions. The current review identifies the gaps in ergonomic interventions among waste collection workers. A systematic review and a bibliometric analysis of the literature on the assessment of occupational hazards and ergonomic interventions in different countries were performed to identify the scope of the interventions. A literature search was carried out in Web of Science, PubMed and Scopus for articles published until December 2018. The search yielded seventy articles on the assessment of occupational health and ten articles on ergonomic interventions among waste collection workers. Based on the review, this paper proposes a hierarchical framework for the implementation of ergonomic interventions in waste associated occupations. The problems faced by formal and informal waste collectors are critical, particularly in developing countries and there is a growing need for low-cost interventions. It is suggested that the potential interventions have to be implemented based on the nature of occupational hazard considering social, cultural and economic factors.