Department of Public Health, Danish Ramazzini Centre, Aarhus University, Aarhus, Denmark; National Research Center for the Working Environment, Copenhagen, Denmark.
Cesare Maltoni Cancer Research Center, Ramazzini Institute, Bologna, Italy.
Environ Int. 2023 Aug;178:107980. doi: 10.1016/j.envint.2023.107980. Epub 2023 May 21.
The World Health Organization (WHO) and the International Labour Organization (ILO) are developing joint estimates of the work-related burden of disease and injury (WHO/ILO Joint Estimates), with contributions from a large number of individual experts. Evidence from human, animal and mechanistic data suggests that occupational exposure to dusts and/or fibres (silica, asbestos and coal dust) causes pneumoconiosis. In this paper, we present a systematic review and meta-analysis of the prevalences and levels of occupational exposure to silica, asbestos and coal dust. These estimates of prevalences and levels will serve as input data for estimating (if feasible) the number of deaths and disability-adjusted life years that are attributable to occupational exposure to silica, asbestos and coal dust, for the development of the WHO/ILO Joint Estimates.
We aimed to systematically review and meta-analyse estimates of the prevalences and levels of occupational exposure to silica, asbestos and coal dust among working-age (≥ 15 years) workers.
We searched electronic academic databases for potentially relevant records from published and unpublished studies, including Ovid Medline, PubMed, EMBASE, and CISDOC. We also searched electronic grey literature databases, Internet search engines and organizational websites; hand-searched reference lists of previous systematic reviews and included study records; and consulted additional experts.
We included working-age (≥ 15 years) workers in the formal and informal economy in any WHO and/or ILO Member State but excluded children (< 15 years) and unpaid domestic workers. We included all study types with objective dust or fibre measurements, published between 1960 and 2018, that directly or indirectly reported an estimate of the prevalence and/or level of occupational exposure to silica, asbestos and/or coal dust.
At least two review authors independently screened titles and abstracts against the eligibility criteria at a first stage and full texts of potentially eligible records at a second stage, then data were extracted from qualifying studies. We combined prevalence estimates by industrial sector (ISIC-4 2-digit level with additional merging within Mining, Manufacturing and Construction) using random-effects meta-analysis. Two or more review authors assessed the risk of bias and all available authors assessed the quality of evidence, using the ROB-SPEO tool and QoE-SPEO approach developed specifically for the WHO/ILO Joint Estimates.
Eighty-eight studies (82 cross-sectional studies and 6 longitudinal studies) met the inclusion criteria, comprising > 2.4 million measurements covering 23 countries from all WHO regions (Africa, Americas, Eastern Mediterranean, South-East Asia, Europe, and Western Pacific). The target population in all 88 included studies was from major ISCO groups 3 (Technicians and Associate Professionals), 6 (Skilled Agricultural, Forestry and Fishery Workers), 7 (Craft and Related Trades Workers), 8 (Plant and Machine Operators and Assemblers), and 9 (Elementary Occupations), hereafter called manual workers. Most studies were performed in Construction, Manufacturing and Mining. For occupational exposure to silica, 65 studies (61 cross-sectional studies and 4 longitudinal studies) were included with > 2.3 million measurements collected in 22 countries in all six WHO regions. For occupational exposure to asbestos, 18 studies (17 cross-sectional studies and 1 longitudinal) were included with > 20,000 measurements collected in eight countries in five WHO regions (no data for Africa). For occupational exposure to coal dust, eight studies (all cross-sectional) were included comprising > 100,000 samples in six countries in five WHO regions (no data for Eastern Mediterranean). Occupational exposure to silica, asbestos and coal dust was assessed with personal or stationary active filter sampling; for silica and asbestos, gravimetric assessment was followed by technical analysis. Risk of bias profiles varied between the bodies of evidence looking at asbestos, silica and coal dust, as well as between industrial sectors. However, risk of bias was generally highest for the domain of selection of participants into the studies. The largest bodies of evidence for silica related to the industrial sectors of Construction (ISIC 41-43), Manufacturing (ISIC 20, 23-25, 27, 31-32) and Mining (ISIC 05, 07, 08). For Construction, the pooled prevalence estimate was 0.89 (95% CI 0.84 to 0.93, 17 studies, I 91%, moderate quality of evidence) and the level estimate was rated as of very low quality of evidence. For Manufacturing, the pooled prevalence estimate was 0.85 (95% CI 0.78 to 0.91, 24 studies, I 100%, moderate quality of evidence) and the pooled level estimate was rated as of very low quality of evidence. The pooled prevalence estimate for Mining was 0.75 (95% CI 0.68 to 0.82, 20 studies, I 100%, moderate quality of evidence) and the pooled level estimate was 0.04 mg/m (95% CI 0.03 to 0.05, 17 studies, I 100%, low quality of evidence). Smaller bodies of evidence were identified for Crop and animal production (ISIC 01; very low quality of evidence for both prevalence and level); Professional, scientific and technical activities (ISIC 71, 74; very low quality of evidence for both prevalence and level); and Electricity, gas, steam and air conditioning supply (ISIC 35; very low quality of evidence for both prevalence and level). For asbestos, the pooled prevalence estimate for Construction (ISIC 41, 43, 45,) was 0.77 (95% CI 0.65 to 0.87, six studies, I 99%, low quality of evidence) and the level estimate was rated as of very low quality of evidence. For Manufacturing (ISIC 13, 23-24, 29-30), the pooled prevalence and level estimates were rated as being of very low quality of evidence. Smaller bodies of evidence were identified for Other mining and quarrying (ISIC 08; very low quality of evidence for both prevalence and level); Electricity, gas, steam and air conditioning supply (ISIC 35; very low quality of evidence for both prevalence and level); and Water supply, sewerage, waste management and remediation (ISIC 37; very low quality of evidence for levels). For coal dust, the pooled prevalence estimate for Mining of coal and lignite (ISIC 05), was 1.00 (95% CI 1.00 to 1.00, six studies, I 16%, moderate quality of evidence) and the pooled level estimate was 0.77 mg/m (95% CI 0.68 to 0.86, three studies, I 100%, low quality of evidence). A small body of evidence was identified for Electricity, gas, steam and air conditioning supply (ISIC 35); with very low quality of evidence for prevalence, and the pooled level estimate being 0.60 mg/m (95% CI -6.95 to 8.14, one study, low quality of evidence).
Overall, we judged the bodies of evidence for occupational exposure to silica to vary by industrial sector between very low and moderate quality of evidence for prevalence, and very low and low for level. For occupational exposure to asbestos, the bodies of evidence varied by industrial sector between very low and low quality of evidence for prevalence and were of very low quality of evidence for level. For occupational exposure to coal dust, the bodies of evidence were of very low or moderate quality of evidence for prevalence, and low for level. None of the included studies were population-based studies (i.e., covered the entire workers' population in the industrial sector), which we judged to present serious concern for indirectness, except for occupational exposure to coal dust within the industrial sector of mining of coal and lignite. Selected estimates of the prevalences and levels of occupational exposure to silica by industrial sector are considered suitable as input data for the WHO/ILO Joint Estimates, and selected estimates of the prevalences and levels of occupational exposure to asbestos and coal dust may perhaps also be suitable for estimation purposes. Protocol identifier: https://doi.org/10.1016/j.envint.2018.06.005. PROSPERO registration number: CRD42018084131.
世界卫生组织(世卫组织)和国际劳工组织(劳工组织)正在联合制定工作相关疾病和伤害负担(世卫组织/劳工组织联合估计)的估算,由大量个体专家提供协助。人类、动物和机械数据证据表明,职业性接触粉尘和/或纤维(二氧化硅、石棉和煤尘)会导致尘肺。在本文中,我们对二氧化硅、石棉和煤尘的职业暴露的流行率和水平进行了系统评价和荟萃分析。这些流行率和水平的估算将作为输入数据,用于估计(如果可行的话)职业性接触二氧化硅、石棉和煤尘导致的死亡人数和伤残调整生命年,以便为世卫组织/劳工组织联合估计的制定提供数据。
我们旨在系统地评估和荟萃分析工作年龄段(≥ 15 岁)工人职业性接触二氧化硅、石棉和煤尘的流行率和水平。
我们在发表和未发表的研究中搜索了电子学术数据库,包括 Ovid Medline、PubMed、EMBASE 和 CISDOC。我们还搜索了电子灰色文献数据库、互联网搜索引擎和组织网站;手动搜索了以前系统评价的参考文献列表和包含的研究记录;并咨询了其他专家。
我们纳入了在任何世卫组织和/或劳工组织成员国的正规和非正规经济部门工作的年龄在 15 岁及以上的工人,但排除了儿童(< 15 岁)和无薪家庭佣工。我们纳入了所有类型的研究,这些研究都具有客观的粉尘或纤维测量,发表时间在 1960 年至 2018 年之间,直接或间接报告了二氧化硅、石棉和/或煤尘职业暴露的流行率和/或水平的估计。
在第一阶段,至少两名综述作者根据入选标准筛选标题和摘要,在第二阶段筛选可能符合条件的记录的全文,然后从合格研究中提取数据。我们使用随机效应荟萃分析,按照国际标准产业分类(ISIC)第四位数字水平(2 位数),并在采矿、制造和建筑等行业内进行合并,对工业部门(ISIC-4 2 位数水平,以及采矿、制造和建筑行业内的进一步合并)的流行率估计值进行了综合。两名或更多的综述作者评估了偏倚风险,所有可用的作者都使用 ROB-SPEO 工具和 QoE-SPEO 方法评估了证据质量,该方法是专门为世卫组织/劳工组织联合估计开发的。
有 88 项研究(82 项横断面研究和 6 项纵向研究)符合纳入标准,涵盖了来自所有世卫组织区域(非洲、美洲、东地中海、东南亚、欧洲和西太平洋)的 23 个国家的超过 240 万次测量。所有纳入的 88 项研究中的目标人群均来自主要的国际标准职业分类(ISCO)群体 3(技术和相关专业人员)、6(熟练的农业、林业和渔业工人)、7(手工艺和相关贸易工人)、8(植物和机器操作人员及装配工)和 9(体力劳动者),以下简称体力劳动者。大多数研究是在建筑、制造和采矿行业进行的。对于职业性接触二氧化硅,有 65 项研究(61 项横断面研究和 4 项纵向研究)纳入了 22 个国家的超过 230 万次测量,涉及所有六个世卫组织区域。对于职业性接触石棉,有 18 项研究(17 项横断面研究和 1 项纵向研究)纳入了来自五个世卫组织区域的 8 个国家的超过 20,000 次测量(东地中海没有数据)。对于职业性接触煤尘,有 8 项研究(均为横断面研究)纳入了来自五个世卫组织区域的 6 个国家的超过 100,000 个样本(东地中海没有数据)。职业性接触二氧化硅、石棉和煤尘是通过个人或固定主动采样器进行评估的;对于二氧化硅和石棉,采用重量法进行评估,然后进行技术分析。在研究参与者的选择方面,证据体的偏倚风险各不相同,而且在不同的工业部门之间也存在差异。然而,偏倚风险普遍在石棉、二氧化硅和煤尘方面的证据体最高。与建筑(ISIC 41-43)、制造(ISIC 20、23-25、27、31-32)和采矿(ISIC 05、07、08)等工业部门相关的最大证据体是关于二氧化硅的。对于建筑行业,汇总的流行率估计值为 0.89(95%置信区间 0.84 至 0.93,17 项研究,I² 91%,中等质量的证据),水平估计值被评为低质量的证据。对于制造行业,汇总的流行率估计值为 0.85(95%置信区间 0.78 至 0.91,24 项研究,I² 100%,中等质量的证据),汇总的水平估计值被评为低质量的证据。采矿行业的汇总流行率估计值为 0.75(95%置信区间 0.68 至 0.82,20 项研究,I² 100%,中等质量的证据),汇总的水平估计值为 0.04mg/m(95%置信区间 0.03 至 0.05,17 项研究,I² 100%,低质量的证据)。对于作物和动物生产(ISIC 01;流行率和水平的证据均为低质量)、专业、科学和技术活动(ISIC 71、74;流行率和水平的证据均为低质量)和电力、燃气、蒸汽和空调供应(ISIC 35;流行率和水平的证据均为低质量)等工业部门,较小的证据体被确定。对于建筑(ISIC 41、43、45),石棉的汇总流行率估计值为 0.77(95%置信区间 0.65 至 0.87,6 项研究,I² 99%,低质量的证据),水平估计值被评为低质量的证据。对于制造(ISIC 13、23-24、29-30),流行率和水平的汇总估计值被评为低质量的证据。对于其他采矿和采石(ISIC 08;流行率和水平的证据均为低质量)、电力、燃气、蒸汽和空调供应(ISIC 35;流行率和水平的证据均为低质量)和水供应、污水、废物管理和补救(ISIC 37;水平的证据为低质量)等工业部门,较小的证据体被确定。对于采矿的煤炭和褐煤(ISIC 05),煤尘的汇总流行率估计值为 1.00(95%置信区间 1.00 至 1.00,6 项研究,I² 16%,中等质量的证据),汇总的水平估计值为 0.77mg/m(95%置信区间 0.68 至 0.86,3 项研究,I² 100%,低质量的证据)。对于电力、燃气、蒸汽和空调供应(ISIC 35),发现了一个较小的证据体;对于流行率,证据质量为低质量,汇总的水平估计值为 0.60mg/m(95%置信区间 -6.95 至 8.14,1 项研究,低质量的证据)。
总体而言,我们认为,职业性接触二氧化硅的证据质量因工业部门而异,从流行率来看,在非常低和中等质量之间,从水平来看,在非常低和低质量之间。对于职业性接触石棉的证据质量,因工业部门而异,从流行率来看,在非常低和低质量之间,从水平来看,在非常低质量。对于职业性接触煤尘的证据质量,因工业部门而异,从流行率来看,在非常低和中等质量之间,从水平来看,在低质量。纳入的研究中没有一项是基于整个工业部门的人群的(即涵盖了工业部门中所有工人的研究),这被我们认为是间接性的严重问题,除了采矿的煤炭和褐煤这一工业部门,因为在该部门中,职业性接触煤尘的流行率估计值可能适合用于估计目的。选择的职业性接触二氧化硅按工业部门划分的流行率和水平估计值被认为适合作为世卫组织/劳工组织联合估计的输入数据,并且职业性接触石棉和煤尘的选择的流行率和水平估计值可能也适合用于估计目的。方案标识符:https://doi.org/10.1016/j.envint.2018.06.005。PROSPERO 注册号:CRD42018084131。