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The association between silica exposure, silicosis and tuberculosis: a systematic review and meta-analysis



While the association between occupational inhalation of silica dust and pulmonary tuberculosis has been known for over a century, there has never been a published systematic review, particularly of experience in the current era of less severe silicosis and treatable tuberculosis. We undertook a systematic review of the evidence for the association between (1) silicosis and pulmonary tuberculosis, and (2) silica exposure and pulmonary tuberculosis controlling for silicosis, and their respective exposure-response gradients.


We searched PUBMED and EMBASE, and selected studies according to a priori inclusion criteria. We extracted, summarised and pooled the results of published case-control and cohort studies of silica exposure and/or silicosis and incident active tuberculosis. Study quality was assessed on the Newcastle-Ottawa Scale. Where meta-analysis was possible, effect estimates were pooled using inverse-variance weighted random-effects models. Otherwise narrative and graphic synthesis was undertaken. Confidence regarding overall effect estimates was assessed using the GRADE schema.


Nine studies met the inclusion criteria. Meta-analysis of eight studies of silicosis and tuberculosis yielded a pooled relative risk of 4.01 (95% confidence interval (CI) 2.88, 5.58). Exposure-response gradients were strong with a low silicosis severity threshold for increased risk. Our GRADE assessment was high confidence in a strong association. Meta-analysis of five studies of silica exposure controlling for or excluding silicosis yielded a pooled relative risk of 1.92 (95% CI 1.36, 2.73). Exposure-response gradients were observable in individual studies but not finely stratified enough to infer an exposure threshold. Our GRADE assessment was low confidence in the estimated effect owing to inconsistency and use of proxies for silica exposure.


The evidence is robust for a strongly elevated risk of tuberculosis with radiological silicosis, with a low disease severity threshold. The effect estimate is more uncertain for silica exposure without radiological silicosis. Research is needed, particularly cohort studies measuring silica exposure in different settings, to characterise the effect more accurately as well as the silica exposure threshold that could be used to prevent excess tuberculosis risk.

Peer Review reports


Occupational silica exposure continues to occur in almost all countries and in many industries and occupations: construction, agriculture and mining being among the largest employers. Consequently, millions of individuals are at risk of silica-associated disease. In South Africa between 1973 and 2013 an estimated minimum 1.2 million workers passed through the gold mining industry with its high silica dust exposures [1, 2]. Of other middle income countries India has approximately 11.5 million people working in silica-exposed jobs, Brazil over 2 million, while China is thought to have the largest number of silicosis cases, with 6000 new cases reported annually [3].

Tuberculosis is an infectious disease caused by Mycobacterium tuberculosis, most commonly affecting the lung. It may also occur in the form of latent tuberculosis, a dormant state which may progress to active disease many years after the initial infection. All of the countries mentioned above are classified by the World Health Organization (WHO) as high burden tuberculosis countries [4].

While the association between certain dusty occupations and “consumption” or “phthisis” was recognised in the nineteenth Century (C.), the acceptance of silicosis, the fibrotic lung disease due to silica dust inhalation, and pulmonary tuberculosis as distinct diseases dates from the early twentieth C. [5,6,7,8].Their aetiological relationship became widely accepted in settings where high silica exposures and untreatable tuberculosis prevailed [8,9,10]. However, doubts were still raised at public forums [11], including by the chief medical spokesperson of the South African gold mining industry between the 1930s and 1950s [12]. Whatever the case, with the decline in silicosis occurrence in high-income countries by the second half of the twentieth century owing to more effective dust control [13,14,15], the decline in tuberculosis transmission in such countries [16] and the advent of antituberculous chemotherapy, interest in the association and its implications waned.

However, silica exposure, silicosis and tuberculosis continue to co-occur in many working populations worldwide. There has recently been a renewal of international interest in the association as part of global efforts to stem the tuberculosis epidemic [17, 18]. The huge toll of silicosis and tuberculosis on South African gold miners over the past few decades has been extensively described [19, 20]. Co-occurrence of silicosis and tuberculosis is frequently reported from other high tuberculosis-burden countries with both small scale mineral working and large scale extractive industries – in India [21, 22], China [23] and Russia [24]. The association also remains relevant to low tuberculosis burden countries such as Portugal [25].

Despite the subject's continuing importance, reviews from the second half of the twentieth C. onwards which focus on the association between silica, silicosis and tuberculosis are scarce (e.g. [26]). There has never to our knowledge been a systematic review. More general reviews of silica and disease [8, 27,28,29,30] vary in their treatment of the silica exposure/silicosis-tuberculosis association, usually with limited critical attention to some important considerations. These include the distinction between silicosis and silica exposure in the absence of silicosis, the implication of a substantial proportion of silicosis being undetectable on the chest radiograph [31, 32] and the differences between studies of tuberculosis incidence and tuberculosis mortality as the outcome. Focus is typically on tuberculosis as a clinical complication of silicosis rather than on the shape and size of exposure-relationships between silica and tuberculosis that would enable thresholds to be discerned for prevention purposes. Examination of the quality of primary studies is generally absent.

Unanswered questions therefore remain with important implications for policies and practices to protect silica-exposed workers. In particular, are current standards for control of workplace silica exposure sufficient to prevent increased tuberculosis risk irrespective of whether silicosis is detectable on the chest x-ray? This requires knowledge of the shape of the silica-tuberculosis exposure-response gradient and the threshold above which excess tuberculosis risk attributable to dust would be controlled.

The association is relevant also to workers’ compensation for tuberculosis in industries with a silica hazard. The International Labour Organization (ILO) List of Occupational Diseases [33] includes silicotuberculosis (silicosis complicated by tuberculosis) and tuberculosis alone without specification of causal exposures. It is therefore unclear whether tuberculosis in silica-exposed workers in the absence of radiological silicosis is included. A review of compensation practices regarding miners’ occupational lung disease in a number of countries suggests that South Africa is one of the few or perhaps the only country where tuberculosis is recognised as an occupational disease in miners in the absence of radiological silicosis [34].

In this inquiry, we aimed to systematically review the evidence for the association between (1) silicosis and pulmonary tuberculosis, and (2) silica exposure and pulmonary tuberculosis excluding or controlling for radiological silicosis. Exposure-response gradients were examined for both objectives.


Systematic review and selection criteria

We carried out a systematic review to assess the evidence from human controlled studies conducted from the 1970s onwards for the associations between silica, silicosis and tuberculosis in adults. We excluded laboratory studies. We registered the protocol with PROSPERO (registration identification CRD 4201912696). Protocol development and review reporting were guided by the Preferred Reporting Items for Systematic Reviews and Meta-Analyses (PRISMA) checklist [35].

Inclusion criteria, grouped according to the population–exposure–comparator-outcome (PECO) framework [36], were as follows:

  • Population - populations in which individuals were or had been exposed to crystalline silica dust and in which incident tuberculosis was recorded;

  • Exposures - studies of individuals with silicosis; and/or with respiratory exposure to silica dust, explicitly measured or inferred from occupation or industry;

  • Comparators - studies reporting comparative effect estimates, specifically case-control or cohort studies reporting risk, rate or odds across groups exposed to different levels of silica (including binary comparisons of exposed/unexposed), and across groups with silicosis (including different grades) and without;

  • Outcome - studies reporting incident active pulmonary tuberculosis, with or without extrapulmonary tuberculosis. Diagnosis must have been made on histological or microbiological grounds, or an explicit combination of clinical assessment, radiology and/or response to treatment. Tuberculosis must have been diagnosed after the onset of silica exposure or silicosis diagnosis;

  • English-language full-text available;

  • Publication 1970 to April 2020 inclusive.

We excluded studies without comparison between higher and lower (or zero) levels of silica exposure or with insufficient information to assign or impute different levels of silica exposure; and for silicosis, without a comparison between those with and without the disease. We also excluded studies of latent tuberculosis infection or of tuberculosis self-reported or based on radiology alone, cross-sectional studies and mortality studies, solely autopsy based studies, and studies of tuberculosis cases from registers without the diagnostic method specified.

Search terms, sources and strategy

We searched the following healthcare and biomedical electronic databases up to 30 April 2020 using a comprehensive search strategy as outlined in Table S1: (1) PUBMED via; and (2) EMBASE via The strategy was translated into the appropriate syntax for each database (Additional File 1, Table S1). The search strategy included database-specific and free text terms for [silicosis] and [tuberculosis] and was not limited by study design filters, language, or publication date. We checked reference lists of studies screened as relevant, as well as review articles for additional relevant citations. Where necessary we contacted authors of published studies for information.

Study selection

The selection process is presented in Fig. 1. Duplicate records were identified and removed. Two authors with expertise in the subject (RE, DR) independently identified potentially eligible studies based on article abstracts, applying the inclusion and exclusion criteria above. Full-text articles were obtained for further independent eligibility assessment. Disagreement was settled through joint re-assessment of the article and discussion with a third reviewer (NS).

Fig. 1
figure 1

Flow diagram of search and selection

Data extraction

Data from alternate articles were extracted by two of the authors (DR, RE) using a piloted template, checked by the other and disagreement resolved by discussion with NS. Data included first author, publication date, location/industry, study design, study population, calendar period of study, number of individuals included [i.e. silica exposed and unexposed, with and without silicosis (including grades of exposure/disease where available), and with and without tuberculosis], method of silica exposure estimation and/or silicosis identification, method of tuberculosis diagnosis, confounders measured and/or controlled for, and overall measure of effect (relative risk - rate, risk or hazard ratio, or odds ratio) by exposure or diagnosis category, both unadjusted and adjusted where available, with 95% confidence intervals. Where degree of silica exposure or silicosis was stratified, stratum-specific measures of association were extracted.

Study quality assessment

Risk of bias of each eligible study was assessed independently by two authors (RE and DR) using the Newcastle Ottawa Scale (NOS) for case-control and cohort studies, and disagreements settled through discussion and consultation with a third author (NS). The NOS was developed by the University of Newcastle, Australia, and the University of Ottawa, Canada, to assess the quality of nonrandomized studies included in systematic reviews [37]. There was no modification of the instrument for this review. The questions and score assignment for each study design are included as Table S2 (Additional File 1). Quality assessment scores were not used to exclude studies.

Confounding by risk factors for tuberculosis likely to be associated independently with silica exposure or silicosis, was considered in relation to study design. In these occupational (adult) cohorts, age, and in some settings HIV, were judged to be the most important potential confounders [38, 39]. Additional confounders of relevance, particularly in cohort studies that were population rather than industry based, or where the general population was used as the reference population, included smoking, congregate settings (in transport, housing and the workplace), socioeconomic status, undernutrition and indoor air pollution [40,41,42]. Heavy alcohol intake and diabetes were considered as potential confounders as they are established risk factors for tuberculosis [41, 42]. Finally, bias arising from an increased likelihood of investigating for and diagnosing tuberculosis among those with silica exposure or silicosis was considered as a potential selection bias.

Standardisation of results and summary presentation

Where studies were sufficiently clinically and methodologically homogeneous, we conducted a meta-analysis for the selected outcome of tuberculosis. Aggregated participant data were used for data synthesis. Meta-analysis was conducted on RevMan version 5.3 [43] using the random effects model given anticipated statistical heterogeneity. We assessed the presence of heterogeneity in study results using the chi-square test and quantified the degree of heterogeneity using the I2 statistic.

We preferentially report on the adjusted analysis using the estimate of effect reported in the study rather than calculating estimates of effects based on the crude data. Where only crude data were presented, we calculated the crude risk ratio and 95% confidence interval for dichotomous data if appropriate, and combined these with the adjusted estimates using the generic inverse variance function in RevMan 5.3 [43]. We explored anticipated heterogeneity by tuberculosis burden in country of study, i.e. high burden versus low and intermediate burden as defined by the WHO [4]. We further examined heterogeneity by study design (cohort vs case-control) and conducted a sensitivity analysis by examining the impact on overall findings of removing studies at risk of bias.

For those studies where we were not able to pool data, we provide a narrative and graphic synthesis using histograms showing relative risk or odds over different metrics for the individual studies. Disease severity-response gradients were analysed by extent of silicosis, and silica exposure-response relationships using stratified exposure metrics (e.g. cumulative dust exposure, duration of employment, or occupational dustiness category). To study the effect of silica exposure in the absence of silicosis, we included only studies which controlled for silicosis in the analysis though adjustment or excluded those with the diagnosis.

Evidence synthesis and assessment of certainty

GRADE was used to judge the overall quality of the evidence with data directly imported from Revman into GRADEPro (GRADEpro Guideline Development Tool. McMaster University, 2020) [44]. Using this instrument in our context, overall quality reflects our confidence that the effect estimates are adequate to support an aetiological inference. Owing to the observational nature of the included studies, the overall confidence commences as low on the GRADE schema. We considered the following characteristics to mark quality up or down: risk of bias (individual study limitations); consistency, directness and precision of the evidence; and publication bias and selective reporting. We also considered the following as reasons to mark upwards: the magnitude of the effect, exposure-response gradient, and the likelihood that any residual confounding would have reduced rather than exaggerated the true effect [45].


Study selection

The PUBMED and EMBASE searches yielded 1674 and 1607 records respectively. Following electronic deduplication, one author (NS) reviewed all potentially duplicate records and removed 798 true duplicates, resulting in a total of 2483 records (Fig. 1). From these, two of the authors (RE, DR) identified 34 potentially eligible records, of which 23 full text articles were obtained for full eligibility assessment. Fourteen of the 23 articles were excluded after assessment (Additional File 1, Table S3). Nine articles reporting on separate studies met the inclusion criteria.

Study characteristics

Table 1 sets out the characteristics of the nine included studies [46,47,48,49,50,51,52,53,54]. There were two case-control studies [50, 54], and seven cohort studies [46,47,48,49, 51,52,53]. Publication ranged from 1986 to 2013 and included five low or intermediate tuberculosis burden countries, Sweden, Denmark, Taiwan, Hong Kong (prior to unification with China), and Iran; and only one high tuberculosis country, South Africa, predominating with four studies. There were six industry-specific studies, including mining and quarrying (46, 48–51] and foundries (46, 47]; one regional population study [54]; one based on a national kidney disease register [53]; and one on a national silicosis register [52].

Table 1 Silica exposure, silicosis and tuberculosis: study characteristics, sample size, and definition of exposure and outcome

Risk of bias assessment

Figure 2 summarises the risk of bias in the reviewed studies by nine NOS characteristics, one set for case-control and one for cohort studies. In six of the studies [47,48,49,50,51,52], all criteria were assessed as low risk of bias except for comparability of the study groups on “any additional factor” (other than age, and interpreted here as controlling for relevant additional factors) which was assessed as a source of uncertain risk of bias. Based on a close analysis of confounding and selection bias (See Additional File 1: Note and Tables S4 and S5), we concluded that although studies dealt with confounding in different ways, the overall risk of bias in these six studies was plausibly low.

Fig. 2
figure 2

Risk of bias in nine studies of silica exposure, silicosis and tuberculosis

There were additional sources of uncertain bias in the remaining three studies. In the Swedish registry study [46], there was an 11-year gap between the inception of the silicosis cohort and the first ascertainment of tuberculosis, and no information on how tuberculosis was excluded at baseline. In the Taiwan study [53] based on an end stage renal disease register there was lack of information on definition of silicosis and on how tuberculosis at baseline was excluded. Finally, the Iranian community study [54] was judged as having a high risk of bias owing to low response rates, uncertain risk of bias in the representativeness of cases and the lack of blinding in interviewing cases and controls about past silica exposure.

Titles and abstracts reported in languages other than English were excluded from the review but were screened for relevance. A single study, in Czech, was identified on abstract (as the article was unobtainable) which might have qualified for inclusion [56].

Studies of the association between silicosis and tuberculosis

Table 2 summarises the results of eight studies of silicosis as a binary exposure and Fig. 3 presents the meta-analysis. All except Yarahmadi et al. [54] adjusted for age but differed in their other covariates. All effect measures, both crude and adjusted, showed a substantial effect of silicosis, ranging from 2.2 [51] to 32.99 [46]. The summary relative risk, preferentially combining adjusted estimates where these were reported with crude estimates, was 4.01 (95% confidence interval (CI) 2.88, 5.58) with I2 = 53%, indicating moderate statistical heterogeneity. Given the large outlier effect size of Westerholm et al. [46], omission of this study resulted in a reduced summary relative risk of 3.70 (95% CI 2.78, 4.93) and statistical heterogeneity of 41%. Removing, in addition, the one study with an overall high risk of bias as described earlier [54] did not change the summary relative risk (3.69, 95% CI 2.59, 5.25).

Table 2 Tuberculosis risk or odds by silicosis relative to no silicosis or general population
Fig. 3
figure 3

Forest plot: Studies of the association between silicosis and tuberculosis

The summary relative risk for studies in low and intermediate burden tuberculosis countries was 6.59 (95% CI 3.36, 12.94) with I2 = 49%, indicating moderate statistical heterogeneity. Omission of Westerholm et al. [46] reduced this summary relative risk to 4.97 (95% CI 3.18, 7.77) and statistical heterogeneity to 14%. In high tuberculosis burden setting (all South Africa) the summary risk ratio was 3.16 (95% CI 2.31, 4.32), and statistical heterogeneity 35%. Sub-group analysis by study design (case control vs. cohort) did not explain residual heterogeneity within tuberculosis burden country strata, nor overall. The difference in relative risk between the two tuberculosis burden country groups was not statistically significant (p = 0.10) after omitting the outlier study (Fig. 3).

With regard to exposure-response, Table 3 summarises the findings of five studies which used grade of silicosis severity as the exposure, four cohort studies and one case control study. Since the ordinal scale did not allow pooling, a graphic synthesis is provided in Fig. 4. Two studies included some minor scale grades of the ILO classification for silicosis (0/1, 1/0, 1/1 and >  1/1), i.e. distinguished borderline categories from more advanced disease [50, 51], while a third used only the major scale grades (0, 1, 2 and 3) [48]. Hnizdo et al. [49] based their exposure-response analysis on subradiological (histological) silicosis and active tuberculosis detected at autopsy. Of note is that just under half to two thirds of the identified silicosis cases in these studies were at the lowest grades, i.e. ILO 1/0 or 1/1, or “negligible” to “slight” on histology. All controlled for age. Four were South African studies of goldminers - two controlled for HIV directly [50, 51], one covered a low HIV period [48] and the other a low HIV prevalence population [49]. Chang et al. [52] used progressive massive fibrosis as an indirect measure of severity. Table 3 and Fig. 4 shows a consistent monotonic increase in the risk or odds of tuberculosis with increasing grade of silicosis.

Table 3 Risk or odds of tuberculosis by severity of silicosis
Fig. 4
figure 4

Tuberculosis risk/odds ratio (y-axis) by severity of silicosis. Definition of severity “level” varies by study. See Table 3 for detail

Using the GRADE schema (Table 4) we rated our confidence in the evidence for a strong aetiological association (relative risk > 2.5) between silicosis and tuberculosis as high. This judgement was based on a low risk of bias (following close consideration of confounding and a sensitivity analysis), a consistent, large effect size, directness and the presence of an observed exposure response gradient. To reduce across-study bias, all study outcomes were reported. However, there were too few studies to perform a funnel plot to exclude publication bias [57].

Table 4 Silicosis and tuberculosis (adjusted and crude GIV), GradePro schema

Studies of the association between silica exposure and tuberculosis, controlling for silicosis

Table 5 and Fig. 5 summarise the results of five studies which reported on silica exposure and controlled for silicosis, either by exclusion [46, 47], modelling [50, 51], or both [49]. The meta-analysis is presented in Fig. 6. In all of these studies, the association of silica exposure with tuberculosis persisted after excluding radiological silicosis (including at least one of the study analyses in those studies in which two metrics were used [50, 51]. The effect measures ranged from 1.00 (dusty occupation vs none) [50] to 2.85 (any vs no silica exposure) [54].

Table 5 Tuberculosis risk/odds by silica exposure, dustiness of occupation or exposure duration, controlling for silicosis
Fig. 5
figure 5

Tuberculosis risk/odds ratio (y-axis) by dust exposure, occupation or duration employed, controlling for silicosis. Metric and definition of “level” vary by study. See Table 5 for detail

Fig. 6
figure 6

Forest plot: Studies of the association between silica exposure and tuberculosis, controlling for silicosis

The summary relative risk, preferentially combining adjusted estimates where these were reported with crude estimates, was 1.92 (95% CI 1.36, 2.73), with I2 = 59%. This moderate statistical heterogeneity could be explained by study design difference: specifically, omission of the two case-control studies [50, 54] increased the relative risk to 2.13 (95% CI 1.70, 2.67) while reducing I2 to zero.

The summary relative risk for studies in low and intermediate burden tuberculosis countries was 2.75 (95% CI 1.70, 4.45) with I2 = zero. In high tuberculosis burden countries (South Africa) the summary risk ratio was 1.66 (95% CI 1.04, 2.66), and statistical heterogeneity high at I2 = 73%. As above, omission of the case-control study [50] increased the relative risk to 2.11 (95% CI 1.68, 2.66) while reducing I2 to zero. The difference in summary relative risk between the two tuberculosis burden country groups was not statistically significant (p = 0.14) (Fig. 6).

Using GRADE, we rated our confidence in the effect estimate for silica exposure and tuberculosis in the absence of silicosis as low (Table 6). Although exposure-response gradients and relative risks greater than two were observed in most of the analyses, this was not the case in all - we therefore did not mark up for magnitude of association nor exposure-response gradient. We considered there to be sufficient precision, consistency and directness not to mark down on these criteria. A risk of bias stemmed from the use of proxy metrics for silica exposure, with the potential for exposure misclassification bias [58]. Given that all of the studies except one were based on registers and not self-report, we regarded this risk as being non-differential with respect to tuberculosis, and therefore highly unlikely to have produced spurious associations. We therefore did not mark down further for risk of bias.

Table 6 Silica exposure controlled for silicosis and tuberculosis (adjusted and crude GIV), GradePro schema

Silicosis grade threshold for increased risk of tuberculosis

For radiological silicosis, an increase in the risk or odds of tuberculosis was seen at the ILO profusion grade 1/0 in two studies relative to the stratum of no silicosis [50, 51] (Table 3, Fig. 4). A third study used only major ILO grades and found an increased relative risk of 2.2 (95% CI 0.7, 3.6) at ILO grade 1 and 2.9 (95% CI 1.1, 4.6) at grade 2.

Threshold effects were difficult to infer from the four studies of silica exposure that controlled for silicosis and provided exposure-response gradients (Table 5) [47, 49,50,51]). One showed no duration effect [51], while in the two that did, the first increment in risk was estimated across wide strata: 10–14 vs <  10 years [50] and > 15 years vs 0.5–14.5 years [47]. The same applied to the one study which measured cumulative dust exposure, i.e. 10–14 mg-years/m3 vs < 9 mg-years/m3 [49].


Summary of evidence

We have high confidence on the GRADE schema that further evidence would not change the conclusion that silicosis strongly increases the risk of tuberculosis, i.e. with a relative risk > 2.5 With regard to silica exposure controlling for radiological silicosis, the evidence suggests an elevated risk of tuberculosis with a exposure-response gradient. However, our confidence in the effect estimate is low and future studies, particularly those with more accurate measures of silica exposure, may change this estimate.

Overall completeness and applicability of evidence

This is to our knowledge the first review to provide a meta-analysis and critically summarise the evidence of the association between silica exposure, and separately radiological silicosis, and pulmonary tuberculosis. The evidence covered spans the 1960s to 2013, with a large proportion of silicosis cases in the lower ILO (or histological severity) grades, distinguishing it from that of the first part of the century characterised by very high levels of silica dust exposure, severe silicosis and untreatable tuberculosis.

The co-modelling of silicosis and silica exposure in one study (which used both radiological and autopsy findings) [49] allowed an estimate of the combined independent effects of silicosis and cumulative dust exposure. The risk of tuberculosis in silicotic miners in the highest category of dust exposure was 13.4 times greater (multiplying the independent effects of 4.18 and 3.22 for silicosis and dust exposure category, respectively), than that of miners without silicosis in the lowest category of dust exposure.

Exposure-response gradients showed an increased risk of tuberculosis at an early radiologic grade of silicosis [50, 51]. Further, since a significant proportion of silicosis is subradiological [31, 32] the finding of an increased risk of tuberculosis at early histological grades [49] suggests an even lower threshold than that revealed radiologically. This is consistent with an earlier autopsy study showing an elevated proportion of tuberculosis even with a “slight degree of silicosis not detected radiologically in life” [59]. The excess risk of tuberculosis in silica exposed workers without radiological silicosis may thus be due to subradiological silicosis or cumulative silica dust each on its own, or to the combination. The implication of these findings is that radiological silicosis should not be required for attribution of the excess risk of tuberculosis to silica exposure in members of silica exposed workforces. However, there remains uncertainty about the threshold, in exposure or duration (as a proxy for exposure), at which excess risk of tuberculosis begins.

The review covered six countries, both high and low/intermediate tuberculosis burden, using different metrics of exposure. The overall estimates of effect for both silicosis and silica controlling for silicosis was higher in low/intermediate tuberculosis countries, arguably because of a relatively low baseline or population incidence of tuberculosis. However, only one high tuberculosis burden country, South Africa, was included. Workers on the South African gold mines and particularly black miners have a history of high rates of tuberculosis related to the migrant labour system and deep level gold mining going back 130 years. In addition to silica exposure, this system has entailed oscillation between mines and rural areas and congregate exposures in transport, accommodation and underground work, greatly aggravated by the HIV epidemic from the 1990s onwards [60, 61]. Studies are needed from other high tuberculosis burden countries such as India, China, Indonesia and Brazil, to determine if their patterns of risk differ.

A range of industries, occupations and settings were covered – gold mining, iron and steel foundries and caisson construction work [55] with one population based study covering a wide range of occupations [54]. This is, however, still relatively low coverage of the full range of occupations involving significant silica exposure, such as construction, agriculture, ceramics, stone work, sandblasting and fabrication of artificial stone. Besides differences in local tuberculosis epidemiology, differences in industry-associated potency factors for silicosis [62] may be relevant to the silica-tuberculosis association.

There has been recent international awakening to the fact that control of silica dust is important not only for preventing silicosis but also for control of tuberculosis [17, 18]. The summary relative risk (excluding one outlier study) of 3.65 (lower confidence limit 2.79) for silicosis and tuberculosis is of the same order as that of other common risk factors for tuberculosis [42] with the exception of HIV which is associated with a very high risk [39]. However, the impact of silica exposure on miners goes beyond the workforce. A modelling study of South African gold mining communities concluded that miners and members of mining communities contributed a disproportionately large share of new tuberculosis cases nationally in relation to their proportion of the population, although the main transmission impact was local [63].

Potential biases in the review process

Potential biases in the review process were controlled via a structured and transparent approach. The study protocol followed PRISMA and was registered on Prospero. Structured searches of PUBMED and EMBASE were undertaken and articles selected independently by two subject experts and agreed by consensus. Studies were limited to those published after 1970 in English; however, only one potentially relevant abstract was identified among those records not reported in English. A structured tool for assessment of risk of bias was applied independently by two subject experts and agreed by consensus. In-depth exploration of confounding was undertaken along the lines recently recommended [64]. In studies with more than one outcome, all were considered; however, there were too few studies to explore for publication bias. Finally, GradePro was used to assess the degree of confidence in the effect estimate for the two primary associations studied.

Agreements and disagreements with other studies or reviews

The findings are consistent with those from mortality studies. Workers in silica exposed occupations have been found to have standardised mortality ratios (SMRs) for tuberculosis ranging from 329 (95% CI 233, 452) [65] to 2175 (95% CI 1837, 2556) [66]. Studies specifically of radiological silicosis have shown similarly elevated SMRs, reaching 564 (95% CI 411, 754) in silicotic subjects who had claimed workers’ compensation [67].

We excluded mortality studies from the review and meta-analysis for several reasons. Death certificate studies generally provide no information on how the initial tuberculosis diagnosis was made. Substantial misclassification of tuberculosis as the cause of death has been shown in the South African gold mining context of very high rates of silicosis, tuberculosis and HIV infection [68]. Further, silicosis may contribute to tuberculosis mortality without an association with incident tuberculosis, for example, by creating diagnostic confusion and delaying TB treatment [69], or acting as an effect modifier by aggravating the course of tuberculosis through coexistent fibrosis, lung function impairment or reducing the effectiveness of standard treatment. Some such effect is suggested by the finding of the case fatality rate among those being treated for tuberculosis to be three times higher in silicotics than non-silicotics [70].

The findings are also consistent with cross-sectional studies (Additional File 1, Table S3) which reported positive associations between tuberculosis and silicosis and metrics of silica exposure controlling for silicosis [38, 58]. However, we excluded cross-sectional studies because of potential biases arising from exposure or disease related selection of workers with silicosis or tuberculosis out of the workforce prior to the sampling; underestimation of effect by including only prevalent active tuberculosis; or uncertainty associated with a diagnosis of past tuberculosis based on self-report or old radiologic features and the temporal relationship of such diagnosis with silica exposure.

The increased risk of pulmonary tuberculosis associated with silica exposure found in observational epidemiologic studies is supported by animal experiment studies. From as early as the first decades of the twentieth century, experiments on small laboratory animals showed that exposure to silica dust and tubercle bacilli resulted in greater proliferation of bacilli, faster development of tuberculosis or more severe disease in exposed compared to control animals [71,72,73,74,75]. More recent work has shown that silica exposure markedly increases susceptibility to mycobacterial infection in mice, and that macrophages transplanted from exposed into unexposed mice reproduce this susceptibility without concomitant dust exposure [76]. Biological plausibility has been further strengthened by the demonstration or elaboration of possible underlying biologic mechanisms [77, 78]. Silica inhalation or silicosis should therefore be considered an effect modifier of the progression of tuberculosis from recent infection or latent infection to active disease.

Considerations in future research

Interpretation of studies of silica exposure, silicosis and tuberculosis needs to take the phenomenon of subradiological silicosis into account in terminology, causal contrast and interpretation. Computerised tomographic (CT) scanning may improve sensitivity to a variable degree [31] but remains impractical for large scale studies and medical surveillance.

There is a need for studies which are able to provide a more accurate measure of the dose of respirable silica dust, controlling for radiological silicosis, and its relationship to incident pulmonary tuberculosis. Given that exposure is a continuous variable, the goal should be a exposure-response curve, as has been achieved for respirable silica and silicosis [79]. This is best achieved through cohort studies, ideally prospective. Such studies would provide a more accurate estimate of the size of the effect of a given cumulative silica exposure on tuberculosis risk than presently available. For prevention purposes, a central question is the exposure threshold below which there is no excess risk of tuberculosis. The question of whether elimination of radiological silicosis, i.e. under current protective dust standards, would be sufficient to protect against tuberculosis, is a corollary of this.

Understanding of time dependent phenomena is also required. This includes the effect of short-term high intensity silica exposure on tuberculosis risk as opposed to long-term lower exposure; or the extent to which, in the absence of radiological silicosis, excess risk persists once silica exposure has ended.

More explicit attention to potential confounding is needed, in this case ensuring that risk factors for tuberculosis are evenly distributed across comparison groups or controlled in the analysis. Even if age is adjusted for, general populations may be an inadequate control for silica-exposed populations or silicosis cases without additional information on confounders. Including relevant covariates would also allow assessment of effect modification of the silica exposure/silicosis tuberculosis thresholds by covariates such as age, HIV, smoking and diabetes.


The study provides to our knowledge the first systematic review of the epidemiological evidence for an association identified at least a century ago, viz. that occupational inhalation of silica dust increases the risk of pulmonary tuberculosis in co-exposed populations. In the current era, even with less severe forms of silicosis in traditional dusty industries, the evidence remains strong for a substantially elevated risk of tuberculosis in those with radiologically diagnosed disease. While there is evidence for an elevated risk of tuberculosis in those who have not been radiologically diagnosed with silicosis, the effect size is subject to uncertainty. Further studies are needed to characterise this effect, and particularly the exposure threshold that would avoid an excess risk of tuberculosis.

Availability of data and materials

The data that support the findings of this study are all derived from published material as referenced in the main article or Supplementary Material.



Confidence interval


International Labour Organization


Human immunodeficiency virus


Newcastle Ottawa Scale


Preferred Reporting Items for Systematic Reviews and Meta-Analyses


Standardised mortality ratios


World Health Organization


  1. Ehrlich RI, Montgomery A, Akugizibwe P, Gonsalves G. Health implications of changing trends in the origins and characteristics of mineworkers in South Africa, 1973-2012. BMC Public Health. 2017;8(1):93.

    Article  Google Scholar 

  2. Brouwer DH, Rees D. Can the South African milestones for reducing exposure to respirable crystalline silica and silicosis be achieved and reliably monitored? Front Public Health. 2020;8:107.

  3. Rees D, Murray J. Silica. In: Newman Taylor A, Cullinan P, Blanc P, Pickering A, editors. Parkes’ Occupational Lung Disorders. 4th ed., chapter 18. Boca Raton: CRC Press; 2016. p. 187–205.

    Google Scholar 

  4. World Health Organization (WHO). Use of high burden country lists for TB by WHO in the post-2015 era. WHO/HTM/TB/2015.29. WHO: Geneva; 2015. Accessed 19 Oct 2020.

  5. Mintz F. Hard rock miners` phthisis in 19th and early 20th century Britain: from diagnosis to compensation. UC Berkeley Electronic Theses and Dissertations 2009. Accessed 19 Oct 2020.

  6. International Labour Office (ILO). Silicosis. Records of the International Conference held at Johannesburg 13–27 August 1930 (Studies and Reports Series F Industrial Hygiene No. 13). Geneva: International Labour Office; 1930. Accessed 25 June 2015.

  7. Rosner D, Markowitz H. Consumption, silicosis, and the social construction of industrial disease. Yale J Biol Med. 1991;64(5):481–98.

    CAS  PubMed  PubMed Central  Google Scholar 

  8. Madl AK, Donovan EP, Gaffney SH, McKinley MA, Moody EC, et al. State-of-the-science review of the occupational health hazards of crystalline silica in abrasive blasting operations and related requirements for respiratory protection. J Toxicol Environ Health Part B. 2008;11(7):548–608.

    Article  CAS  Google Scholar 

  9. Irvine LG. Notes on Silicosis. In: Silicosis. Proceedings of the International Conference held in Geneva from 19 August to 9 September 1938, Appendix VI. London: International Labour Office; 1938. p. 151–66.

    Google Scholar 

  10. Oosthuizen SF, Snyman HW, Barnetson J, Bloom A, Irving JT, Radford A, et al. Report of the Departmental Committee of Inquiry into the Relationship between Pneumoconiosis and Pulmonary Disability and the Relationship Between Pneumoconiosis and Tuberculosis. Part II. Government Printer. Pretoria: Union of South Africa; 1955. p. 81–138.

    Google Scholar 

  11. International Labour Conference. Record of Proceedings. Eighteenth Session: Workmen's Compensation for Occupational Diseases. Appendix X. Geneva: International Labour Office; 1934. p. 639–46.

  12. McCulloch J. Mining evidence: South Africa’s gold mines and the career of A. J Orenstein. Soc History Med. 2018;31(1):61–78.

    Article  Google Scholar 

  13. Ashe HB, Bergstrom DE. Twenty-six years’ experience with dust control in the Vermont granite industry. Ind Med Surg. 1964;33:73–8.

    CAS  PubMed  Google Scholar 

  14. Gerhardsson G. The end of silicosis in Sweden—a triumph for occupational hygiene engineering. OSH Dev. 2002:13–25.

  15. International Labour Organization (ILO). Undated. Occupational health: Silicosis. Accessed 25 July 2020.

  16. Sander OA. Pneumoconiosis and infection. JAMA. 1948;141(2):813–7.

    Google Scholar 

  17. International Commission on Occupational Health (ICOH). Preventing tuberculosis among silica dust exposed workers. Occup Environ Med. 2018;5(11):765–6.

    Article  Google Scholar 

  18. United Nations (UN). Political declaration of the UN General Assembly high-level meeting. United to end tuberculosis: an urgent global response to a global epidemic. Resolution A/RES/73/3, 10 October 2018. Accessed 23 July 2020.

  19. Murray J, Davies T, Rees D. Occupational lung disease in the south African mining industry: research and policy implementation. J Public Health Policy. 2011;32(Suppl 1):S65–79.

    Article  PubMed  Google Scholar 

  20. Maboso BM, Moyo DM, Muteba KM, Govender VG, Barnes DF, Maama-Maime LBM, et al. Burden of disease among Basotho ex-miners in a large outreach medical assessment programme. Occup Health Southern Afr. 2020;26(4):145–52.

    Google Scholar 

  21. Sharma N, Kundu D, Dhaked S, Das A. Silicosis and silicotuberculosis in India. Bull World Health Organ. 2016;94(10):777–8.

    Article  PubMed  PubMed Central  Google Scholar 

  22. Tiwari RR, Sharma YK, Saiyed HN. Tuberculosis among workers exposed to free silica dust. Indian J Occup Environ Med. 2007;11(2):61–4.

    Article  PubMed  PubMed Central  Google Scholar 

  23. Xia Y, Liu J, Shi T, Xiang H, Bi Y. Prevalence of pneumoconiosis in Hubei, China from 2008 to 2013. Int J Environ Res Public Health. 2014;11(9):8612–21.

    Article  PubMed  PubMed Central  Google Scholar 

  24. Goto A, Nawata S. Clinical analysis of 130 cases of Siberian silicosis. [article in Japanese, English abstract]. Nihon Igaku Hoshasen Gakkai Zasshi. 1995;55(3):121–8.

    CAS  PubMed  Google Scholar 

  25. Coutinho D, Sousa P, Oliveira O, Gaio AR, Duarte R. Does silicosis explain it all? (Letter). Rev Port Pneumol. 2016;22(6):358–60.

    Article  CAS  PubMed  Google Scholar 

  26. Barboza CEG, Winter DH, Seiscento M, Santos U d P, Filho MT. Tuberculosis and silicosis: epidemiology, diagnosis and chemoprophylaxis. J Bras Pneumol. 2008;34(11):961–8.

    Article  Google Scholar 

  27. Ziskind M, Jones RN, Weill H. Silicosis. Am Rev Respir Dis. 1976;113(5):643–64.

    Article  CAS  PubMed  Google Scholar 

  28. American Thoracic Society (ATS). Committee of the Scientific Assembly on Environmental and Occupational Health. Adverse effects of crystalline silica exposure. Am J Respir Crit Care Med. 1997;155(2):761–7.

    Article  Google Scholar 

  29. National Institute of Safety and Health (NIOSH). Health Effects of Occupational Exposure to Respirable Crystalline Silica. Centers for Disease Control and Prevention. DHHS (NIOSH) Publication Number 2002–129. 2002. Accessed 25 July 2020.

  30. Leung CC, Yu ITS, Chen W. Silicosis. Lancet. 2012;379(9830):2008–18.

    Article  CAS  PubMed  Google Scholar 

  31. Ehrlich R, Murray J, Rees D. Subradiological silicosis. Am J Ind Med. 2018;61(11):877–85.

    Article  PubMed  Google Scholar 

  32. Hnizdo E, Murray J, Sluis-Cremer GK, Thomas RG. Correlation between radiological and pathological diagnosis of silicosis: an autopsy population based study. Am J Ind Med. 1993;24(4):427–45.

    Article  CAS  PubMed  Google Scholar 

  33. Kim EA, Kang SK. Historical review of the list of occupational diseases recommended by the international labour organization (ILO). Ann Occup Environ Med. 2013;25(1):14.

    Article  PubMed  PubMed Central  Google Scholar 

  34. Boyko R, Darby S, Goldberg RC, Milin Z. Fulfilling broken promises. Reforming the century-old compensation system for occupational lung disease in the South African mining sector. Yale Global Health Justice Partnership Policy Paper (No. 2/2013). 2013. p. 10–69. [Accessed 23 July 2020].

  35. Liberati A, Altman DG, Tetzlaff J, Mulrow C, Gøtzsche PC, Ioannidis JP, et al. The PRISMA statement for reporting systematic reviews and meta-analyses of studies that evaluate healthcare interventions: explanation and elaboration. BMJ. 2009;339(jul21 1):b2700.

    Article  PubMed  PubMed Central  Google Scholar 

  36. Morgan RL, Whaley P, Thayer KA, Schünemann HJ. Identifying the PECO: a framework for formulating good questions to explore the association of environmental and other exposures with health outcomes. Environ Int. 2018;121(Pt 1):1027–31.

    Article  PubMed  PubMed Central  Google Scholar 

  37. Wells GA, Shea B, O’Connell D, Peterson J, Welch V, Losos M, et al. The Newcastle-Ottawa scale (NOS) for assessing the quality of nonrandomised studies in meta-analyses. 2009. Accessed 27 Dec 2019.

    Google Scholar 

  38. Kleinschmidt I, Churchyard G. Variation in incidences of tuberculosis in subgroups of south African gold miners. Occup Environ Med. 1997;54(9):636–41.

    Article  CAS  PubMed  PubMed Central  Google Scholar 

  39. Martinson NA, Hoffmann CJ, Chaisson RE. Epidemiology of tuberculosis and HIV: recent advances in understanding and responses. Proc Am Thorac Soc. 2011;8(3):288–93.

    Article  PubMed  PubMed Central  Google Scholar 

  40. Hessel PA, Gamble JF, Nicolich M. Relationship between silicosis and smoking. Scand J Work Environ Health. 2003;29(5):329–36.

    Article  PubMed  Google Scholar 

  41. Lönnroth K, Castro KG, Chakaya JM, Chauhan LS, Floyd K, Glaziou P, et al. Tuberculosis control and elimination 2010-50: cure, care, and social development. Lancet. 2010;375(9728):1814–29.

    Article  PubMed  Google Scholar 

  42. Narasimhan P, Wood J, MacIntyre CR, Mathai D. Risk factors for tuberculosis. Pulm Med. 2013;828939:1–11.

    Article  Google Scholar 

  43. Review Manager (RevMan) [Computer program]. Version 5.3. Copenhagen: The Nordic Cochrane Centre, The Cochrane Collaboration; 2014.

  44. Guyatt G, Oxman AD, Akl EA, Kunz R, Vist G, Brozek J, et al. GRADE guidelines: 1. Introduction-GRADE evidence profiles and summary of findings tables. J Clin Epidemiol. 2011;64(4):383–94.

    Article  PubMed  Google Scholar 

  45. Guyatt GH, Oxman AD, Sultan S, Glasziou P, Akl EA, Alonso-Coello P, et al. GRADE guidelines: 9. Rating up the quality of evidence. J Clin Epidemiol. 2011;64(12):1311–6.

    Article  PubMed  Google Scholar 

  46. Westerholm P, Ahlmark A, Maasing R, Segelberg I. Silicosis and risk of lung cancer or lung tuberculosis: a cohort study. Environ Res. 1986;41(1):339–50.

    Article  CAS  PubMed  Google Scholar 

  47. Sherson D, Lander F. Morbidity of pulmonary tuberculosis among silicotic and nonsilicotic foundry workers in Denmark. J Occup Med. 1990;32(2):110–3.

    CAS  PubMed  Google Scholar 

  48. Cowie RL. The epidemiology of tuberculosis in gold miners with silicosis. Am J Respir Crit Care Med. 1994;150(1):1460–2.

    Article  CAS  PubMed  Google Scholar 

  49. Hnizdo E, Murray J. Risk of pulmonary tuberculosis relative to silicosis and exposure to silica dust in south African gold miners. Occup Environ Med. 1998;55(7):496–502.

    Article  CAS  PubMed  PubMed Central  Google Scholar 

  50. Corbett EL, Churchyard GJ, Clayton T, Herselman P, Williams B, Hayes R, et al. Risk factors for pulmonary mycobacterial disease in south African gold miners: a case-control study. Am J Respir Crit Care Med. 1999;159(2):94–9.

    Article  CAS  PubMed  Google Scholar 

  51. Corbett EL, Churchyard GJ, Clayton TC, Williams BG, Mulder D, Hayes RJ, et al. HIV infection and silicosis: the impact of two potent risk factors on the incidence of mycobacterial disease in south African miners. AIDS. 2000;14(17):2759–68.

    Article  CAS  PubMed  Google Scholar 

  52. Chang KC, Leung CC, Tam CM. Tuberculosis risk factors in a silicotic cohort in Hong Kong. Int J Tuberc Lung Dis. 2001;5(2):177–84.

    CAS  PubMed  Google Scholar 

  53. Li SY, Chen TJ, Chung KW, Tsai LW, Yang WC, Chen JY, et al. Mycobacterium tuberculosis infection of end-stage renal disease patients in Taiwan: a nationwide longitudinal study. Clin Microbiol Infect. 2011;17(11):1646–52.

    Article  PubMed  Google Scholar 

  54. Yarahmadi A, Zahmatkesh MM, Ghaffari M, Mohammadi S, Labbafinejad Y, Seyedmehdi SM, et al. Correlation between silica exposure and risk of tuberculosis in Lorestan Province of Iran. Tanaffos. 2013;12(2):34–40.

    PubMed  PubMed Central  Google Scholar 

  55. Ng TP, Yeung KH, O'Kelly FJ. Silica hazard of caisson construction in Hong Kong. Occup Med. 1987;37(1):62–5.

    Article  CAS  Google Scholar 

  56. Jindrichova J. Incidence of tuberculosis in workers in East Bohemia region exposed to the risk of silicosis. Studia Pneumologica et Phtiseologica Cechoslovaca. 1973;33(8):516–20.

    Google Scholar 

  57. Sterne JAC, Sutton AJ, Ioannidis JPA, Terrin N, Jones DR, Lau J, et al. Recommendations for examining and interpreting funnel plot asymmetry in meta-analyses of randomised controlled trials. BMJ. 2011;343(jul22 1):d4002.

    Article  PubMed  Google Scholar 

  58. te Waternaude JM, Ehrlich RI, Churchyard GJ, Pemba L, Dekker K, Vermeis M, et al. Occup Environ Med. 2006;63(3):187–92.

    Article  Google Scholar 

  59. Sluis-Cremer GK. Active pulmonary tuberculosis discovered at post-mortem examination of the lungs of black miners. Brit J Dis Chest. 1980;74(4):374–8.

    Article  CAS  PubMed  Google Scholar 

  60. Smith J, Blom P. Those who don't return: improving efforts to address tuberculosis among former miners in southern Africa. New Solut. 2019;29(1): 76–104.

  61. Rees D, Murray J, Nelson G, Sonnenberg P. Oscillating migration and the epidemics of silicosis, tuberculosis, and HIV infection in south African gold miners. Am J Ind Med. 2010;53(4):398–404.

    Article  PubMed  Google Scholar 

  62. Meldrum M, Howden P. Crystalline silica: variability in fibrogenic potency. Ann Occup Hyg. 2002;46(Suppl 1):27–30.

    Google Scholar 

  63. Chang ST, Chihota VN, Fielding KL, Grant AD, Houben RM, White RG, et al. Small contribution of gold mines to the ongoing tuberculosis epidemic in South Africa: a modeling-based study. BMC Med. 2018;16(1):52.

    Article  PubMed  PubMed Central  Google Scholar 

  64. Ioannidis JPA, Tan YJ, Blum MR. Limitations and misinterpretations of e-values for sensitivity analyses of observational studies. Ann Intern Med. 2019;170(2):108–11.

    Article  PubMed  Google Scholar 

  65. Cocco PL, Carta P, Belli S, Picchiri GF, Flore MV. Mortality of Sardinian lead and zinc miners: 1960-88. Occup Environ Med. 1994;51(10):674–82.

    Article  CAS  PubMed  PubMed Central  Google Scholar 

  66. Vacek PM, Verma DK, Graham WG, Callas PW, Gibbs GW. Mortality in Vermont granite workers and its association with silica exposure. Occup Environ Med. 2011;68(5):312–8.

    Article  CAS  PubMed  Google Scholar 

  67. Goldsmith DF, Beaumont JJ, Morrin LA, Schenker MB. Respiratory cancer and other chronic disease mortality among silicotics in California. Am J Ind Med. 1995;28(4):459–67.

    Article  CAS  PubMed  Google Scholar 

  68. Field N, Murray J, Wong ML, Dowdeswell R, Dudumayo N, Rametsi L. Missed opportunities in TB diagnosis: a TB process-based performance review tool to evaluate and improve clinical care. BMC Public Health. 2011;11(1):127.

    Article  PubMed  PubMed Central  Google Scholar 

  69. Diez M, Bleda MJ, Alcaide J, Castells C, Cardenal JI, Dominguez A, et al. Determinants of health system delay among confirmed tuberculosis cases in Spain. Eur J Pub Health. 2005;15(4):343–9.

    Article  CAS  Google Scholar 

  70. Churchyard GJ, Kleinschmidt I, Corbett EL, Murray J, Smit J, De Cock KM. Factors associated with an increased case-fatality rate in HIV-infected and non-infected south African gold miners with pulmonary tuberculosis. Int J Tuberc Lung Dis. 2000;4(8):705–12.

    CAS  PubMed  Google Scholar 

  71. Mavrogordato A. The mode of action of dust in relation to respiratory disease. S Afr Med Record June. 1922;24:226–8.

    Google Scholar 

  72. Gye WE, Kettle EH. Silicosis and miners’ phthisis. Br J Exp Pathol. 1922;3(5):241–51.

    PubMed Central  Google Scholar 

  73. Kettle EH. Inflammation and infection. Lancet. 1927;11:1225–30.

    Article  Google Scholar 

  74. Vorwald AJ, Delahant AB. The influence of silica on the natural and acquired resistance to tubercle infection. Am Rev Tuberc. 1938;38(3):347–62.

    CAS  Google Scholar 

  75. Allison AC, Hart PD. Potentiation by silica of the growth of mycobacterium tuberculosis in macrophage culture. Br J Exp Pathol. 1968;49(5):465–76.

    CAS  PubMed  PubMed Central  Google Scholar 

  76. Pasula R, Britigan BE, Turner J, Martin WJ. Airway delivery of silica increases susceptibility to mycobacterial infection in mice: potential role of repopulating macrophages. J Immunol. 2009;182(11):7102–9.

    Article  CAS  PubMed  PubMed Central  Google Scholar 

  77. Chavez-Galan L, Ramon-Luing LA, Torre-Bouscoulet L, Perez-Padilla R, Sada-Ovalle I. Pre-exposure of Mycobacterium tuberculosis-infected macrophages to crystalline silica impairs control of bacterial growth by deregulating the balance between apoptosis and necrosis. PLoS One. 2013;8(11):e80971.

    Article  CAS  PubMed  PubMed Central  Google Scholar 

  78. Konecny P, Ehrlich R, Gulumian M, Jacobs M. Immunity to the dual threat of silica and Mycobacterium tuberculosis. Front Immunol. 2019;9:3069.

    Article  CAS  PubMed  PubMed Central  Google Scholar 

  79. Chen W, Zhuang Z, Attfield MD, Chen BT, Gao P, Harrison JC, et al. Exposure to silica and silicosis among tin miners in China: exposure-response analyses and risk assessment. Occup Environ Med. 2001;58(1):31–7.

    Article  CAS  PubMed  PubMed Central  Google Scholar 

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We thank Joy Oliver, South African Medical Research Council, for the literature search and Profs. E. Corbett and D. Goldsmith for responses to written queries.


There was no funding for this study.

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This work developed out of an MPH dissertation written by author PA. The protocol was developed jointly by all authors. NS oversaw the literature search and advised on the review method, data management, quality assessment and GRADE analysis. RE and DR carried out the article selection and quality assessment. The article was drafted by RE and DR. All authors approved and contributed to successive drafts and finalisation of the manuscript.

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Correspondence to Rodney Ehrlich.

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Competing interests

Prof. Ehrlich has prepared expert reports for lawyers acting for plaintiffs in silicosis litigation matters. Prof. Rees has prepared medico-legal reports on individuals with silicosis for plaintiff attorneys in silicosis litigation. The other authors report no actual or potential conflicts of interest.

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Supplementary Information

Additional file 1: Table S1.

Search strings. Table S2. Newcastle-Ottawa quality assessment scales. Table S3. Exclusions on full article. Supplementary Note: Consideration of confounding and bias. Table S4. Potential confounders of the association between silica, silicosis and tuberculosis. Table S5. E-values for potential confounders of the association between silicosis and tuberculosis.

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Ehrlich, R., Akugizibwe, P., Siegfried, N. et al. The association between silica exposure, silicosis and tuberculosis: a systematic review and meta-analysis. BMC Public Health 21, 953 (2021).

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