Skip to main content
Journal of Occupational Medicine and Toxicology (London, England) logoLink to Journal of Occupational Medicine and Toxicology (London, England)
. 2023 Jan 18;18:1. doi: 10.1186/s12995-023-00367-5

Exposure to cosmetic talc and mesothelioma

Jacqueline Moline 1,2,, Kesha Patel 1, Arthur L Frank 3
PMCID: PMC9847157  PMID: 36653798

Abstract

Aim

Mesothelioma is associated with asbestos exposure. In this case series, we present 166 cases of individuals who had substantial asbestos exposure to cosmetic talc products as well as some who had potential or documented additional exposures to other asbestos-containing products and who subsequently developed mesothelioma.

Methods

Data were gathered for all subjects referred to an occupational and environmental medicine specialist as part of medicolegal review. Years of total cosmetic talcum powder usage was noted as well as the latency from the onset of talcum powder use to the mesothelioma diagnosis. Alternate asbestos exposure in addition to the exposure from cosmetic talc was categorized as none, possible, likely, and definite.

Results

In 122 cases, the only known exposure to asbestos was from cosmetic talc. For 44 cases, potential or documented alternate exposures in addition to the cosmetic talc were described.

Conclusion

Cumulative exposure to asbestos leads to mesothelioma; for individuals with mixed exposures to asbestos, all exposures should be considered. Use of cosmetic talc is often overlooked as a source of asbestos exposure. All individuals with mesothelioma should have a comprehensive history of asbestos exposure, including cosmetic talc exposure.

Keywords: Malignant mesothelioma, Cumulative asbestos exposure, Cosmetic talcum powder

Introduction

Mesothelioma, described as a sentinel tumor, is intimately associated with asbestos exposure. Asbestos has been used for decades in thousands of products, both in occupational and non-occupational settings, historically accounting for the bulk of mesothelioma cases. Non-occupational exposures can be environmental in nature, from effluents from mines and factories, from para-occupational exposures such as “shade-tree mechanics” using friction products, and from home renovations [1]. Household exposures affecting family members, known as “take-home” exposure has been well described in the literature [25]. An underappreciated source of exposure is the use of cosmetic talc products. The International Agency for Research on Cancer (IARC) [6] states that asbestos contaminated talc is carcinogenic and should be treated as if one were dealing with asbestos. Asbestos levels in talcum powder are significantly above background ambient asbestos exposure levels [79]. Talc application simulation studies have been published [7, 8] where exposures to talcum powder were 1.9 f/cc and 2.57 f/cc, respectively. According to the Gramond et al. [10] categorization of intensity, asbestos exposure at these levels would be considered to be high (> 1–10 f/ml).

Historically, asbestos exposures at work have been linked to multiple products. The overall risk for asbestos related disease, including mesothelioma, is related to cumulative exposure. As agencies such as NIOSH, OSHA, the EPA, and others have recognized, there is no known safe exposure to asbestos. Low doses of exposure to asbestos contribute to mesothelioma [11]. Both time from first exposure (latency) and total exposure (cumulative dose) to asbestos must be taken into account when evaluating risk. With multiple repeated incidences of exposure, all those above background level should be thought of as “’substantial.” When considering the elevated risk of mesothelioma in sheet metal workers [12, 13], Zoloth and Michaels considered the multiple bystander exposures to different products, not simply one construction material. This case series presents 166 cases of individuals who had a minimum of five years and a mean of 40.8 years of exposure to asbestos through cosmetic talc products, some with possible other exposures, but all developed mesothelioma.

Methods

Data were gathered for all subjects referred to an occupational and environmental medicine specialist, JM, as part of medicolegal review. All cases were reviewed personally by an occupational medicine specialist with experience evaluating asbestos exposure in thousands of individuals. The individual’s medical records were reviewed and mesothelioma diagnoses were based on pathological reports that were performed as part of their diagnostic evaluation. Exposure data was obtained by sworn testimony of the mesothelioma patients in all cases, and/or from family members who had direct knowledge of the individual’s use of cosmetic talc and, if present, other sources of asbestos exposure. Use of talc was recorded as being diapered or powdered as a child; diapering or powdering children or others; applying talcum powder to oneself after bathing, or other personal applications of talc. Years of total cosmetic talcum powder usage was noted as well as the latency from the onset of talcum powder use to the mesothelioma diagnosis. Age was presented within a 10 year window to maintain confidentiality. Data reviewed included family occupational histories (parents or anyone cohabitating with the individual), hobbies, residence, living with or laundering clothes of an asbestos exposed worker, if indicated, home renovations that could have exposed the individual to asbestos containing construction materials, residence close to a facility with environmental contamination, or other potential asbestos exposures. In those individuals with potential asbestos exposure in addition to the cosmetic talc, categorization of these exposures was done by two occupational physicians, JM and ALF. Alternate asbestos exposure in addition to the exposure from cosmetic talc was categorized as none, possible, likely, and definite following the descriptions by Gramond et al. [10]. Non-occupational exposure to asbestos was characterized as paraoccupational (living with an asbestos worker or cleaning clothes), do-it-yourself home repair, domestic (handling asbestos material or living in the presence of asbestos material susceptible to damage at home), or environmental (living near and asbestos processing plant). This study was conducted with approval from the Human Research Protection Program at Northwell Health Feinstein Institute for Medical Research (#21–0897-OTH).

Results

We identified 166 individuals with exposure to cosmetic talc who were diagnosed with a malignant mesothelioma between 2014 and 2021. None of these individuals were previously included in publications by the authors [14]. A summary of the case findings is found in Table 1. Overall, the average age of diagnosis was 63.3 (age range 26–94) years of age. The majority of cases were epithelioid mesothelioma (75.3%). The average length of exposure to cosmetic talc was 40.8 years (range 5–76 years of use), and the average latency period from the onset of talcum powder use to the development of mesothelioma was 52.4 (20—83 years). We identified 122 individuals with asbestos exposure solely through use of cosmetic talc. Exposure to talcum powder could have been for personal use, in an occupational setting (for example, a nurse applying talcum powder to a patient), or applying talcum powder to others such as children. For 122 individuals, they either used cosmetic talc while diapering children or recalled applying talc to others (such as their children). Overall, 80.6% of women and 52.4% of men used talcum powder for diapering or applying talc to others. For 44 individuals, potential alternate asbestos exposure in addition to cosmetic talc was reported. Table 1 presents the 44 cases with alternate exposure ranked by possible, likely, and definite asbestos exposure. Twenty-two women (17.8%) and fifteen men (35.7%) had likely or definite alternate exposure to asbestos in addition to their talcum powder usage. [Details of the exposure history of all 166 individuals with cosmetic talc exposure is presented in Table 2, including a description of the alternate exposure.] Table 1  also shows the site of the tumor by gender. Of the 166 cases, 109 were pleural, 52 were peritoneal, 4 were discovered in both the pleura and peritoneum and the original site could not be determined. One case of pericardial mesothelioma was noted out of the 166 cases, which reflects the rarity of this site for mesothelioma. The percentages of peritoneal mesothelioma were similar for women (29.8%) and men (35.7%). The high proportion of peritoneal mesothelioma tumors relative to pleural tumors, consistent with prior case series of patients with malignant mesothelioma after cosmetic talc use [14, 15], is unusual and deserves further investigation.

Table 1.

Characteristics of 166 mesothelioma cases with cosmetic talc usage

Total (N = 166) Female (n = 124) Male (n = 42)
Average Age (range) 63.3 (26 – 94) 64.3 (26 – 94) 60.9 (28 – 83)
Years of Talc Use* (range) 40.8 (5 – 76) 40.4 (6 – 76) 42.0 (5 – 74)
Talc Latency in Years (range) 52.4 (20 – 83) 53.3 (20 – 83) 49.9 (28 – 74)
Diapering or Applying Talc to Others** 122 (73.5%) 100 (80.6%) 22 (52.4%)
Talc Use Only 122 (73.5%) 97 (78.2%) 25 (59.5%)
Talc Use and Alternate Exposure 44 (26.5%) 27 (21.8%) 17 (40.5%)
Certainty of Alternate Exposure (n = 44) (26.5%) Possible 7 (4.2%) 5 (4.0%) 2 (4.8%)
Likely 17 (10.2%) 14 (11.3%) 3 (7.1%)
Definite 20 (12.0%) 8 (6.5%) 12 (28.6%)
Tumor Location Pleura 109 (65.7%) 83 (66.9%) 26 (61.9%)
Peritoneum 52 (31.3%) 37 (29.8%) 15 (35.7%)
Both Pleura & Peritoneum 4 (2.4%) 3 (2.4%) 1 (2.4%)
Pericardium 1 (0.6%) 1 (0.8%) 0
Tumor Subtype Biphasic 24 (14.5%) 18 (14.5%) 6 (14.3%)
Epithelial 125 (75.3%) 92 (74.2%) 33 (78.6%)
Sarcomatoid 16 (9.6%) 13 (10.5%) 3 (7.1%)
Not specified 1 (0.6%) 1 (0.8%) 0

*Years of Talc Use: includes years of being diapered or powdered with talc as a child; years of diapering or powdering children or others with talc; and years applying talcum powder to oneself after bathing or other personal use

**Diapering or Applying Talc: restricted to diapering or powdering children with talc or applying talcum powder to others, including occupational use

Table 2.

Description of 166 mesothelioma cases

Age at Diagnosis Sex Tumor Location Tumor Subtype Occupation(s) Talc Latency (years) Years of Talc Use* Diapering/ Applying Talc to Others** Certainty of Alternate Exposure Type of Alternate Exposure
51–60 F Pleura Epithelial Cosmetics factory 41 36 Yes None
31–40 F Peritoneal Biphasic Marketing 39 12 No None
91–100 F Pleura Epithelial Clerical worker 69 57 Yes Definite Smoked Kent cigarettes in 1950s
51–60 M Pleura Biphasic Warehouse supervisor 54 22 No Definite Home renovations as child
21–30 M Peritoneal Epithelial Aircraft technician 28 5 No None
41–50 F Pleura Biphasic Marketing 47 47 Yes Definite Automotive friction exposure
41–50 F Peritoneal Epithelial Operator technician 37 36 Yes Likely Parents worked in chemical plant/with automotive friction materials; no work clothes laundered at home
61–70 F Peritoneal, pleura Epithelial Hairdresser 65 57 Yes Definite Household exposures laundering clothes (automotive friction materials)
41–50 F Pleura Epithelial Industrial engineer 45 10 Yes None
71–80 M Pleura Biphasic Firefighter, painter 59 59 No Definite Occupational exposures to industrial talc, firefighting
51–60 F Peritoneal Epithelial Dental assistant, secretary, logging business 58 57 Yes Definite Automotive friction product exposure
51–60 F Peritoneal, pleura Epithelial Nurse 50 20 Yes None
71–80 F Pleura Epithelial Secretary 60 61 No None
61–70 M Peritoneal Epithelial Software engineer 53 53 No Likely Construction work as teenager; family member machinist
61–70 F Pleura Epithelial Secretary 61 20 Yes None
61–70 M Pleura Epithelial Law professor 46 45 No None
21–30 F Peritoneal Biphasic Customer service manager 26 12 No None
51–60 F Pleura Epithelial Dental assistant, sales 50 17 Yes Likely Dental tape used in office
21–30 F Pleura Epithelial Programmer 29 17 Yes None
51–60 F Pleura Epithelial Clerical worker 54 48 No None
71–80 F Pleura Biphasic Dental assistant, receptionist 64 34 Yes Possible Possible household exposure from parental occupations
61–70 F Pleura Epithelial Systems analyst 62 61 Yes None
51–60 F Peritoneal Epithelial Clerical worker 59 31 Yes Likely Asbestos shingle exposure as child
71–80 F Peritoneal Epithelial Teacher's aide, customer service 46 46 No None
51–60 M Pleura Epithelial Baked goods manufacturer 55 49 Yes None
61–70 F Pleura Epithelial Housekeeping, packaging 51 23 No None
41–50 M Peritoneal Epithelial Lawyer 46 23 Yes None
51–60 M Pleura Sarcomatoid IT 30 30 Yes None
61–70 F Peritoneal Epithelial Bookkeeper 62 15 Yes None
71–80 M Pleura Epithelial Engineer 71 20 No Definite Home renovations, automotive friction products, cement in molds
41–50 F Pleura Epithelial Restaurant 46 12 No None
81–90 F Pleura Epithelial Not provided 62 62 Yes Likely Household exposures laundering clothes (automotive friction materials)
81–90 F Pleura Epithelial LPN 67 18 Yes Likely Household exposures laundering clothes (automotive friction materials)
31–40 F Peritoneal Epithelial Nanny, teacher 26 7 Yes Definite Home renovations
61–70 M Peritoneal Epithelial Packaging, machine operator, welding 48 48 Yes Definite Cut transite and cement pipes; automotive friction exposure (“shade tree”)
71–80 F Peritoneal Biphasic Clerical worker 61 39 Yes None
51–60 F Peritoneal Epithelial Lawyer 54 18 No None
41–50 F Pleura Sarcomatoid Research 44 45 Yes None
51–60 F Peritoneal Epithelial Variety of jobs 50 48 Yes Definite Home renovation
41–50 M Peritoneal Epithelial Farrier, mechanic, general labor 41 35 Yes Definite Occupational exposure
81–90 M Pleura Epithelial Barber 50 36 Yes Likely Boiler work in rail yards
71–80 M Pleura Biphasic Bus driver, factory worker 47 47 Yes None
51–60 F Peritoneal Epithelial Physician 20 12 Yes None
61–70 F Pleura Epithelial Cashier, sales, clerical worker, wire assembler 53 53 No None
51–60 F Peritoneal Epithelial Laborer 41 50 Yes Likely Home renovations, family member worked with clay
61–70 M Pleura Epithelial Accountant 69 69 Yes Definite Home renovations during 1970s
81–90 F Pleura Biphasic Bookkeeping, rehab counseling 83 32 Yes None
71–80 F Pleura Sarcomatoid Office manager 75 75 Yes None
61–70 F Pleura Epithelial Merchandising manager 31 18 Yes None
41–50 F Pleura, peritoneal Epithelial Teacher 46 22 Yes None
51–60 M Pleura Epithelial Automechanic, pipefitter 31 44 Yes Definite Occupational and take home exposure (shipyard)
51–60 F Peritoneal Epithelial Clerical worker 40 38 Yes None
41–50 F Pericardium Sarcomatoid Medical center 50 31 Yes None
71–80 M Pleura Epithelial Mechanic, parts manager 61 50 No Definite Occupational naval exposure to asbestos, automotive friction material handling
71–80 F Pleura Epithelial Secretary, cosmetics, cashier 50 25 No Definite Household exposures laundering clothes (automotive friction materials)
61–70 F Pleura Sarcomatoid Catering 45 40 Yes None
61–70 F Pleura Epithelial Cleaner, personal assistant 52 50 Yes None
51–60 M Pleura Epithelial Meat inspector 41 26 No None
71–80 F Pleura Epithelial Office manager 65 55 Yes Possible Household exposure from husband (drilling wells, pipes)
71–80 F Pleura Epithelial Clerical worker 60 59 Yes Possible Family member worked at service station (no details on work)
71–80 M Pleura Sarcomatoid Accountant 47 39 Yes None
61–70 F Pleura Epithelial Sales, business 60 16 No None
81–90 M Peritoneal Epithelial Accountant 68 56 No None
51–60 F Pleura Epithelial Social worker 40 6 No None
71–80 F Pleura Epithelial Hairdresser 60 49 Yes None
41–50 M Pleura, peritoneal Epithelial Warehouse worker 47 8 No Definite Automotive filler exposure
51–60 F Pleura Epithelial Retail, bankteller, work at school 56 56 Yes None
61–70 F Pleura Biphasic Bakery 64 49 Yes None
71–80 F Pleura Epithelial Hospitality 61 58 Yes None
51–60 F Pleura Epithelial Cashier 57 56 Yes None
81–90 F Peritoneal Epithelial Teacher 40 50 Yes Possible Abatement done at work
81–90 F Pleura Epithelial Physical therapy assistant 64 62 Yes None
31–40 M Peritoneal Epithelial IT 35 25 No None
51–60 F Pleura Epithelial Housekeeper 42 34 Yes None
81–90 F Pleura Epithelial Teacher 54 50 Yes Likely Home renovations
61–70 M Pleura Epithelial Accounting 63 63 Yes None
71–80 M Pleura Epithelial Tractor driver, race track 62 60 No Likely Oil drilling
71–80 F Pleura Epithelial Research 62 42 Yes None
51–60 F Peritoneal Epithelial Agriculture consultant 53 53 Yes None
31–40 F Peritoneal Epithelial Clerical worker 39 27 Yes None
41–50 F Pleura Biphasic Clerical worker 49 49 No Likely Ceramics use
71–80 M Pleura Epithelial Communications system/office 47 49 Yes None
81–90 F Pleura Not specified Nurse 76 70 Yes Likely Family member worked in shipyard
71–80 F Peritoneal Epithelial Meat wrapper 56 47 Yes None
71–80 M Pleura Biphasic Advertising 62 62 Yes None
71–80 F Peritoneal Epithelial Teacher, hospital administration 70 70 Yes None
41–50 M Peritoneal Epithelial Chef 37 36 No None
51–60 F Peritoneal Epithelial Case manager 53 52 Yes None
41–50 F Peritoneal Epithelial Finance and marketing 42 34 No None
51–60 M Pleura Epithelial Painter, carpet installer 38 38 Yes Definite Automotive friction product use
81–90 F Pleura Epithelial Secretary 63 45 Yes None
71–80 F Pleura Epithelial Nursing 69 40 Yes None
51–60 F Peritoneal Epithelial Nurse 46 22 Yes None
41–50 M Peritoneal Epithelial Industrial engineer 48 53 Yes None
71–80 F Peritoneal Epithelial Librarian 55 44 Yes None
51–60 F Pleura Biphasic Clerical worker, hostess 53 15 No None
71–80 F Pleura Epithelial Secretary 67 55 Yes None
71–80 F Pleura Epithelial Clerical worker 64 20 Yes None
71–80 F Peritoneal Sarcomatoid Secretary, medical billing 47 47 Yes None
81–90 F Pleura Epithelial Communications and real estate 69 69 Yes None
41–50 F Peritoneal Epithelial Home health 42 24 Yes None
51–60 F Pleura Biphasic Clerical worker, hostess 53 15 Yes None
71–80 F Pleura Biphasic Therapy aid 67 67 Yes None
61–70 M Pleura Biphasic Restaurant, lead technician 50 47 Yes None
61–70 F Pleura Sarcomatoid Teacher 51 43 Yes None
51–60 F Pleura Epithelial Sales 44 16 Yes None
41–50 F Pleura Epithelial Chicken farming, medical assistant 48 48 Yes None
41–50 M Peritoneal Epithelial Physician 40 17 No None
71–80 F Pleura Epithelial Secretary 69 64 No None
61–70 F Pleura Epithelial Assembly line worker 51 52 Yes None
61–70 F Pleura Epithelial X-ray technician 40 40 Yes None
51–60 F Pleura Biphasic Factory worker, housekeeper 33 14 Yes None
51–60 F Pleura Epithelial Clerical worker 38 29 Yes None
61–70 F Pleura Epithelial Clerical worker 54 27 Yes None
81–90 F Pleura Epithelial Variety of jobs 76 76 Yes None
71–80 F Peritoneal Epithelial Receptionist, dental assistant 45 35 Yes None
71–80 F Pleura Epithelial Midwife 55 47 Yes None
81–90 F Pleura Epithelial Seamstress 63 56 Yes None
71–80 F Peritoneal Epithelial Accounting 65 65 Yes None
61–70 F Pleura Epithelial Nurse 57 57 Yes None
71–80 M Peritoneal Epithelial Sales, truck driver 45 32 No Definite Automotive friction products use
51–60 M Pleura Epithelial Lawyer 48 48 Yes None
51–60 F Pleura Sarcomatoid Customer service 56 27 Yes None
81–90 F Pleura Sarcomatoid Teacher 53 47 Yes None
71–80 F Peritoneal Epithelial Not provided 67 48 No Definite Smoked Kent cigarettes in 1950s
31–40 F Peritoneal Biphasic Banking 39 19 Yes None
71–80 M Pleura Epithelial Logger, run loader 74 74 Yes Possible Automotive friction product use and home renovations
71–80 F Peritoneal Epithelial Hairdresser 50 50 Yes Likely Hairdryers present in salon
31–40 F Pleura Sarcomatoid Certified Nursing Assistant and phlebotomist 39 24 Yes None
71–80 F Pleura Epithelial Seamstress 62 52 Yes None
31–40 F Peritoneal Epithelial Variety of jobs 27 20 Yes None
61–70 F Pleura Epithelial Laborer 51 51 Yes None
41–50 M Peritoneal Biphasic Casino worker 47 47 Yes None
81–90 F Pleura Epithelial Nurse 67 18 Yes None
71–80 M Pleura Epithelial Accountant, comptroller 70 30 Yes Possible Home renovations
61–70 F Pleura Sarcomatoid Clerical worker 60 27 No None
61–70 F Pleura Biphasic Secretary, cleaner 52 52 Yes Likely Home renovations in 1970s
61–70 F Pleura Sarcomatoid Office cleaner, food prep 64 64 Yes None
61–70 F Pleura Epithelial Insurance agent 58 57 Yes None
71–80 F Pleura Epithelial Cook, cleaner, concierge 54 44 Yes None
31–40 M Peritoneal Epithelial Lab technician 36 36 No None
91–100 F Pleura Epithelial Variety of jobs 60 60 No None
51–60 F Pleura Epithelial Real estate broker 36 35 Yes None
41–50 F Pleura Biphasic PhD in astronomy, dance teacher 37 37 No None
71–80 F Pleura Epithelial Switchboard operator, HR 64 50 No None
51–60 F Peritoneal Epithelial Nurse 50 46 Yes Likely Ceramics work for 4–5 years
41–50 F Peritoneal Epithelial Lawyer 44 20 No None
71–80 F Pleura Epithelial Quality control 67 67 Yes None
51–60 F Pleura Sarcomatoid Counselor 55 54 No None
71–80 F Pleura Biphasic Certified nursing assistant, ranch work 62 35 Yes Likely Vermiculite exposure
71–80 M Peritoneal Epithelial Physician 67 67 Yes None
41–50 F Peritoneal Epithelial Nurse Practitioner 44 34 Yes None
31–40 M Pleura Epithelial Not provided 29 30 No None
61–70 F Pleura Epithelial Banking 60 50 Yes None
51–60 F Peritoneal Epithelial Nurse 56 45 Yes None
71–80 F Pleura Sarcomatoid Hairdresser 61 25 Yes None
71–80 M Pleura Sarcomatoid Mechanic 60 48 No Definite Occupational exposure and home renovations
61–70 M Peritoneal Epithelial Worked at special education preschool 57 50 No None
71–80 F Peritoneal Biphasic Teacher 65 46 Yes None
71–80 F Pleura Biphasic Teacher 71 59 Yes Possible Family member was Linotype operator
81–90 F Pleura Epithelial Cashier, waitress 60 58 Yes None
31–40 F Pleura Epithelial Administrator 28 7 No None
71–80 F Peritoneal Epithelial Teacher 50 51 Yes Likely Household exposure to laundry (automotive friction materials)
31–40 M Pleura Epithelial Homeland Security 33 33 No None
61–70 M Pleura Epithelial Trucking company 55 56 Yes None
71–80 F Pleura Epithelial Office worker 62 45 Yes None

*Years of Talc Use: includes years of being diapered or powdered with talc as a child; years of diapering or powdering children or others with talc; and years applying talcum powder to oneself after bathing or other personal use

**Diapering or Applying Talc: restricted to diapering or powdering children with talc or applying talcum powder to others, including occupational use

Discussion

This paper presents 166 individuals with malignant mesothelioma and asbestos exposure through documented use of cosmetic talcum powder. For 122 of 166, their only known exposure to asbestos was their use of cosmetic talcum powder. Without the recognition of asbestos exposure through cosmetic talcum powder, 73.5% of the cases might well have been considered “idiopathic.” Similarly, for those 26.5% of cases with additional asbestos exposure along with the talc, those alternate exposures would have been mistakenly considered as the sole, and sufficient, cause of the mesothelioma. Historically, the attributable risk of asbestos for mesothelioma in women ranged from around 20–50%. However as Baur et al. point out, misclassification or inadequate exposure ascertainment has led to this low attributable risk for women compared to men. [16]. Data from occupationally exposed cohorts that included men and women actually show that compared to similarly exposed men, women had higher mortality rates from mesothelioma [1720]. Lacourt found that at low-level cumulative asbestos exposure ((0 – 0.1 f-cc/year) women were more likely to develop mesothelioma than men [21]. Magnani (2008) found the SMR for mesothelioma was higher for women than for men among workers at an asbestos cement plant [22]. Frank et al. (2009) found mesothelioma rates in the Qingdao region of China were correlated with a higher proportion of women employed in asbestos manufacturing industries. [23] In some instances authors limited the characterization of asbestos exposure in women to certain industries, such as shipbuilding during wartime [24], thus neglecting other potential sources and decreasing the attributable risk. Conversely, when non-occupational exposures were included for women, even with low-intensity domestic exposure considered, the attributable risk increased from 40% to 64.8% [21].

Given that all types of asbestos can cause mesothelioma [6], it is important to consider every source of exposure to asbestos in an individual. Talcum powder has been contaminated with both chrysotile and amphibole asbestos (predominately anthophyllite and tremolite) [8, 25, 26]. Recently, Wong et al. (2021) found significantly elevated risks of mesothelioma among individuals with only chrysotile exposure and for mixed fiber exposure. [27]. Chrysotile alone (OR = 3.8) and in combination with tremolite/anthophyllite asbestos (OR = 3.9) were associated with similar increases in risk of mesothelioma. These three fiber types are most commonly found in cosmetic talc, and given that different ore sources were used in manufacturing over time, it is likely that many formulations and uses of talcum powder involved mixed fiber type exposure. There is no scientific basis to state that one type of exposure was the sole cause of the mesothelioma in a mixed exposure scenario. For example, rates of mesothelioma have been evaluated based on either job type or locale (e.g., construction, shipping) rather than on each specific task or exposure within the job category. Furthermore, mesothelioma is a disease that occurs following a long latency period. It is important to consider whether the latency period for all exposures, whether due to asbestos in talcum powder, or through occupational or para-occupational exposures meets the minimum latency period.

Subgroups of individuals not traditionally known to be exposed to asbestos have been identified, such as teachers. In this case series, 12 teachers (7.2% of cases) were diagnosed with mesothelioma. Anderson et al. identified 12 school teachers with mesothelioma in Wisconsin (6 male, 6 female). [28]. Nine cases had no known exposure to asbestos, although several worked in school buildings with asbestos containing building materials (ACBM) present, but the condition of the ACBR while the teachers were present in the school was unknown. No history of talcum powder use was elicited. Marianaccio et al. identified mesotheliomas in 11 female teachers in Italy. [29]. Mazurek et al. evaluated mesothelioma deaths in women in the United States from 1999–2020 using death certificate data. [30]. Mesothelioma was noted in 32 female elementary and middle school teachers. No information on exposure to asbestos or specific tasks at work or a comprehensive exposure history was available; no history of talcum powder use was elicited, as the study was based solely on death certificates. Tomasallo et al. found increased mortality among school teachers in Wisconsin, USA. [31]. They noted that para-occupational or take home exposure could be responsible for the increased risk. Again, no history of asbestos exposure through talcum powder usage was ascertained. It might be possible that exposure to ACBM played some role in these mesotheliomas, however, the notable history of exposure to asbestos-containing talcum powders among teachers in this case series, highlights the importance of assessing this source of exposure in future studies of mesothelioma in teachers and other predominantly female professions.

Mazurek et al. found seven cases of mesothelioma among female hairdressers. [30]. Our series identified five hairdressers/barbers with documented occupational exposure to asbestos containing talcum powder. Moline et al. found three hairdressers who used cosmetic talc as part of their occupation, [14] and Emory et al. [15] found 4 hairdressers out of 75 patients. Pavlisko et al. identified a hairdresser in their study of mesothelioma in women, but classified the case in the non-occupational/paraoccupational exposure category. [32] McDonald attributed the finding of tremolite in the lung tissue of a chrysotile worker to his prior occupational exposure to talc as a barber [33]. Rodelsberger recognized talc as a source of asbestos exposure and identified hairdressers and barbers as asbestos-exposed industries [34]. The examples of these two occupational subgroups, teachers with personal use of cosmetic talc, and hairdressers with occupational use of cosmetic talc, show the importance of obtaining a thorough history and determining all potential sources of asbestos exposure.

This case series describes mesotheliomas in end-users of cosmetic talcum powder, thus using no personal protective equipment or dust suppression activities, unlike some cohorts with occupational exposures [35]. Prior mortality studies of talc miners and millers in Italy (and other countries) have not identified mesotheliomas in their populations, although two cases of peritoneal cancer were identified by Pira et al. [36]. The Rubino, Coggiola and Pira et al. studies used mortality data collected prior to an ICD mesothelioma code, which could impact proper classification of mesothelioma. [3537]. The studies had a relatively small sample size, which given the rarity of mesothelioma, even among highly exposed individuals, would have led to insufficient statistical power [38]. Fordyce studied Vermont talc miners and found two mesotheliomas in the small cohort of 427 miners; Vermont talc has been used in cosmetic talcum powder [39].

Fiber burden studies were done in some individuals from the two prior case series of mesothelioma among individuals with cosmetic talcum powder use. Moline et al. reported on tissue fiber analysis in six of 33 individuals. Asbestos fibers, of the types found in cosmetic talc, were found in all six samples. Emory et al. found anthophyllite asbestos in all 9 individuals for whom tissue fiber analysis was done. Tremolite was found in six of the cases in addition to the anthophyllite. Hull et al. [40] looked at New York State talc miners and found anthophyllite, tremolite/actinolite, chrysotile and talc in their lungs. There were over a dozen cases of mesothelioma identified in these talc miners. Our case series did not include data on tissue sampling, which is not typically done for clinical purposes; rather we relied on patient history. For occupational exposures to asbestos, fiber analysis is not required to ascertain a history of exposure, rather the history of exposure to asbestos is sufficient [41]. This should be no different for environmental exposures, such as asbestos exposure in cosmetic talcum powder, or even para-occupational exposures.

Pleural mesothelioma is more common than peritoneal mesothelioma [42], with estimates of pleural mesothelioma occurring approximately 80–90% of the time compared to peritoneal mesothelioma. The presenting location for the tumor, either pleural or peritoneal, was similar in all three recent case series. In Moline et al., 11 of 33 patients had peritoneal mesothelioma and in Emory et al., 23 of 75 cases were peritoneal mesothelioma. In this larger case series, the proportion of peritoneal mesotheliomas was 31.3%. The proportion of men in each of the three case series was similar. In Emory et al., 15% of the cases were men, compared with 18% of the cases in Moline et al. In the current case series, among 122 cases with talc-only exposure, 20.5% were men, slightly above the proportion in two previous case series. This might reflect growing awareness among men that talcum powder use could explain their mesothelioma, particularly when no other identifiable source of asbestos was identified. Few individuals in this case series underwent testing for the tumor suppressor gene, BAP-1, which is associated with an increased risk for mesothelioma when associated with asbestos exposure, [43] including greater susceptibility at low doses of asbestos such as exposures from cosmetic talcum powder use. Interestingly, there was a greater frequency of peritoneal mesothelioma cases in those with the BAP-1 mutation and asbestos exposure [44].

Several authors have written about the importance of the cumulative dose, which has been related to several asbestos-caused diseases, both non-malignant and non-malignant. Luberto et al. discussed the “increased mortality risk due to asbestos exposure for malignant neoplasm of pleura, peritoneum, lung and ovary, as well as asbestosis, all increasing with cumulative exposure.” [19] Henderson et al. commented on the use of the cumulative exposure model in the Helsinki Criteria. [45] Iwastsubo and colleagues, citing only low exposures leading to disease noted that “excess of mesothelioma was observed for levels of cumulative exposure.” [46] Ferrante and her colleagues [47] found that the “risk of pleural malignant mesothelioma increased with cumulative asbestos exposure and also in analyses limited to subjects non-occupationally exposed,” comparable to the current case series. Albin et al. [48] even noted that “colorectal cancer displayed a clear relation with cumulative dose,” as one would reasonably expect with asbestos-related diseases.

This case series may reflect the potential sources of bias that impact all studies that use cases in which litigation is occurring. However, because mesothelioma is a rare disease and full environmental histories are rarely obtained or documented, it would be impossible to amass so many cases with one type of exposure using standard sources such as hospital or cancer registry records. Furthermore, most patients (and their clinicians) are unaware of the presence of asbestos in talcum powder, leading them to report no known asbestos exposure. The data related to years of exposure to cosmetic talcum powder was obtained and typically described in great detail during sworn testimony. For nearly one-quarter of the individuals in this series, additional exposures to asbestos were reported along with the cosmetic talcum powder. When available, information regarding talcum powder usage was corroborated by sworn testimony of family members. Typically, the questioning of individuals about alternate exposures to asbestos as part of litigation is fairly comprehensive, but it is possible that there were additional, unknown sources. This presents a challenge for any study of asbestos exposure and, in particular, mesothelioma, given the long latency period from the onset of exposure to the development of disease.

Conclusion

For individuals with exposure to asbestos through cosmetic talc usage and additional alternate sources, all exposures contribute to the development of mesothelioma. Published case reports and case series have identified over 100 individuals whose sole exposure to asbestos was through cosmetic talcum powder usage [14, 15, 49]. Thus, is it critical to obtain a history of all potential exposures to asbestos. In this case series, 122 cases would have had no source of asbestos identified if a history of asbestos-containing cosmetic talc had not been elicited. The other 44 would have likely been misclassified as having only alternate exposures. It is indisputable that asbestos causes mesothelioma, therefore, it is critical to elicit all potential sources of asbestos exposure so that we can better understand, and prevent, future cases of this deadly cancer.

Acknowledgements

Not applicable.

Authors’ contributions

Jacqueline Moline conceived of the manuscript, and was involved in the acquisition of data, analysis and writing of the manuscript. Kesha Patel was involved in data presentation and analysis. Arthur L. Frank was involved in writing and evaluation of alternative exposures. The author(s) read and approved the final manuscript.

Funding

No funds or external assistance were obtained by any outside source in the development, writing, analysis or conclusions of this manuscript.

Availability of data and materials

The datasets generated and/or analyzed during the current study are not publicly available. Individuals of details of cases will not be provided to protect the confidentiality of the cases presented in the study. Efforts to minimized identification, such as describing age in a range were employed.

Declarations

Ethics approval and consent to participate

The project received approval from the Institutional Review Board and we received a waiver of consent to include the participants in the study. (IRB #: 21–0897).

Consent for publication

Not applicable.

Competing interests

Authors Jacqueline Moline and Arthur L. Frank have served as expert witnesses in asbestos litigation, including talc litigation for plaintiffs.

Footnotes

Publisher’s Note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

References

  • 1.Olsen NJ, Franklin PJ, Reid A, et al. Increasing incidence of malignant mesothelioma after exposure to asbestos during home maintenance and renovation. Med J Aust. 2011;195(5):271–274. doi: 10.5694/mja11.10125. [DOI] [PubMed] [Google Scholar]
  • 2.Bourdès V, Boffetta P, Pisani P. Environmental exposure to asbestos and risk of pleural mesothelioma: review and meta-analysis. Eur J Epidemiol. 2000;16(5):411–417. doi: 10.1023/a:1007691003600. [DOI] [PubMed] [Google Scholar]
  • 3.Epler GR, Fitz Gerald MX, Gaensler EA, Carrington CB. Asbestos-related disease from household exposure. Respiration. 1980;39(4):229–240. doi: 10.1159/000194221. [DOI] [PubMed] [Google Scholar]
  • 4.Miller A. Mesothelioma in household members of asbestos-exposed workers: 32 United States cases since 1990. Am J Ind Med. 2005;47(5):458–462. doi: 10.1002/ajim.20167. [DOI] [PubMed] [Google Scholar]
  • 5.Schneider J, Straif K, Woitowitz HJ. Pleural mesothelioma and household asbestos exposure. Rev Environ Health. 1996;11(1–2):65–70. doi: 10.1515/REVEH.1996.11.1-2.65. [DOI] [PubMed] [Google Scholar]
  • 6.IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, International Agency for Research on Cancer, World Health Organization, eds. Carbon Black, Titanium Dioxide, and Talc. International Agency for Research on Cancer ; Distributed by WHO Press; 2010.
  • 7.Steffen JE, Tran T, Yimam M, et al. Serous ovarian cancer caused by exposure to asbestos and fibrous talc in cosmetic talc powders—a case series. J Occup Environ Med. 2020;62(2):e65–e77. doi: 10.1097/JOM.0000000000001800. [DOI] [PubMed] [Google Scholar]
  • 8.Gordon RE, Fitzgerald S, Millette J. Asbestos in commercial cosmetic talcum powder as a cause of mesothelioma in women. Int J Occup Environ Health. 2014;20(4):318–332. doi: 10.1179/2049396714Y.0000000081. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 9.U.S. Public Health Service USD of H& HS. Public Health Statement Asbestos CAS#: 1332–21–4. Atlanta Agency Toxic Subst Dis Regist. Published online September 2001.
  • 10.Gramond C, Rolland P, Lacourt A, et al. Choice of rating method for assessing occupational asbestos exposure: Study for compensation purposes in France. Am J Ind Med. 2012;55(5):440–449. doi: 10.1002/ajim.22008. [DOI] [PubMed] [Google Scholar]
  • 11.Tossavainen A. Asbestos, asbestosis, and cancer: the Helsinki criteria for diagnosis and attribution. Scand J Work Environ Health. 1997;4:311–316. doi: 10.5271/sjweh.226. [DOI] [PubMed] [Google Scholar]
  • 12.Michaels D, Zoloth S. Asbestos disease in sheet metal workers: Proportional mortality update. Am J Ind Med. 1988;13(6):731–734. doi: 10.1002/ajim.4700130612. [DOI] [PubMed] [Google Scholar]
  • 13.Zoloth S, Michaels D. Asbestos disease in sheet metal workers: the results of a proportional mortality analysis. Am J Ind Med. 1985;7(4):315–321. doi: 10.1002/ajim.4700070407. [DOI] [PubMed] [Google Scholar]
  • 14.Moline J, Bevilacqua K, Alexandri M, Gordon RE. Mesothelioma associated with the use of cosmetic talc. J Occup Environ Med. 2020;62(1):11–17. doi: 10.1097/JOM.0000000000001723. [DOI] [PubMed] [Google Scholar]
  • 15.Emory TS, Maddox JC, Kradin RL. Malignant mesothelioma following repeated exposures to cosmetic talc: a case series of 75 patients. Am J Ind Med. 2020;63(6):484–489. doi: 10.1002/ajim.23106. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 16.Baur X, Frank AL, Soskolne CL, Oliver LC, Magnani C. Malignant mesothelioma: ongoing controversies about its etiology in females. Am J Ind Med. 2021;64(7):543–550. doi: 10.1002/ajim.23257. [DOI] [PubMed] [Google Scholar]
  • 17.Newhouse ML, Berry G, Wagner JC, Turok ME. A study of the mortality of female asbestos workers. Br J Ind Med. 1972;29(2):134–141. doi: 10.1136/oem.29.2.134. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 18.Berry G. Mortality from all cancers of asbestos factory workers in east London 1933–80. Occup Environ Med. 2000;57(11):782–785. doi: 10.1136/oem.57.11.782. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 19.Luberto F, Ferrante D, Silvestri S, et al. Cumulative asbestos exposure and mortality from asbestos related diseases in a pooled analysis of 21 asbestos cement cohorts in Italy. Environ Health. 2019;18(1):71. doi: 10.1186/s12940-019-0510-6. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 20.Pira E, Pelucchi C, Buffoni L, et al. Cancer mortality in a cohort of asbestos textile workers. Br J Cancer. 2005;92(3):580–586. doi: 10.1038/sj.bjc.6602240. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 21.Lacourt A, Gramond C, Rolland P, et al. Occupational and non-occupational attributable risk of asbestos exposure for malignant pleural mesothelioma. Thorax. 2014;69(6):532–539. doi: 10.1136/thoraxjnl-2013-203744. [DOI] [PubMed] [Google Scholar]
  • 22.Magnani C, Ferrante D, Barone-Adesi F, et al. Cancer risk after cessation of asbestos exposure: a cohort study of Italian asbestos cement workers. Occup Environ Med. 2008;65(3):164–170. doi: 10.1136/oem.2007.032847. [DOI] [PubMed] [Google Scholar]
  • 23.Frank AL, Zengchang P, Huaqiang Z, Yun Z. Mesothelioma in Qingdao, PRC (2000–2007) J Phys Conf Ser. 2009;151:012007. doi: 10.1088/1742-6596/151/1/012007. [DOI] [Google Scholar]
  • 24.Price B. Mesothelioma trends in the United States: an update based on surveillance, epidemiology, and end results program data for 1973 through 2003. Am J Epidemiol. 2004;159(2):107–112. doi: 10.1093/aje/kwh025. [DOI] [PubMed] [Google Scholar]
  • 25.Bird T, Steffen JE, Tran TH, Egilman DS. A review of the talc industry’s influence on federal regulation and scientific standards for asbestos in talc. NEW Solut J Environ Occup Health Policy. 2021;31(2):152–169. doi: 10.1177/1048291121996645. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 26.Cralley LJ, Key MM, Groth DH, Lainhart WS, Ligo RM. Fibrous and mineral content of cosmetic talcum products. Am Ind Hyg Assoc J. 1968;29(4):350–354. doi: 10.1080/00028896809343015. [DOI] [PubMed] [Google Scholar]
  • 27.Wong JYY, Rice C, Blair A, Silverman DT. Mesothelioma risk among those exposed to chrysotile asbestos only and mixtures that include amphibole: a case–control study in the USA, 1975–1980. Occup Environ Med. 2021;78(3):199–202. doi: 10.1136/oemed-2020-106665. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 28.Anderson HA, Hanrahan LP, Schirmer J, Higgins D, Sarow P. Mesothelioma among employees with likely contact with in-place asbestos-containing building materials. Ann N Y Acad Sci. 1991;643:550–572. doi: 10.1111/j.1749-6632.1991.tb24506.x. [DOI] [PubMed] [Google Scholar]
  • 29.Marinaccio A, Corfiati M, Binazzi A, et al. The epidemiology of malignant mesothelioma in women: gender differences and modalities of asbestos exposure. Occup Environ Med. 2018;75(4):254–262. doi: 10.1136/oemed-2016-104119. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 30.Mazurek JM, Blackley DJ, Weissman DN. Malignant mesothelioma mortality in women — United States, 1999–2020. MMWR Morb Mortal Wkly Rep. 2022;71(19):645–649. doi: 10.15585/mmwr.mm7119a1. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 31.Tomasallo CD, Christensen KY, Raymond M, Creswell PD, Anderson HA, Meiman JG. An occupational legacy: malignant mesothelioma incidence and mortality in wisconsin. J Occup Environ Med. 2018;60(12):1143–1149. doi: 10.1097/JOM.0000000000001461. [DOI] [PubMed] [Google Scholar]
  • 32.Pavlisko EN, Liu B, Green C, Sporn TA, Roggli VL. Malignant diffuse mesothelioma in women: a study of 354 cases. Am J Surg Pathol. 2020;44(3):293–304. doi: 10.1097/PAS.0000000000001418. [DOI] [PubMed] [Google Scholar]
  • 33.Mcdonald A, Case B, Churg A, et al. Mesothelioma in Quebec chrysotile miners and millers: epidemiology and aetiology. Ann Occup Hyg. 1997;41(6):707–719. doi: 10.1016/S0003-4878(97)00020-3. [DOI] [PubMed] [Google Scholar]
  • 34.Rödelsperger K, Jöckel KH, Pohlabeln H, Romer W, Woitowitz HJ. Asbestos and man-made vitreous fibers as risk factors for diffuse malignant mesothelioma: results from a German hospital-based case-control study. Am J Ind Med. 2001;39(3):262–275. doi: 10.1002/1097-0274(200103)39:3<262::AID-AJIM1014>3.0.CO;2-R. [DOI] [PubMed] [Google Scholar]
  • 35.Coggiola M, Bosio D, Pira E, et al. An update of a mortality study of talc miners and millers in Italy. Am J Ind Med. 2003;44(1):63–69. doi: 10.1002/ajim.10240. [DOI] [PubMed] [Google Scholar]
  • 36.Pira E, Coggiola M, Ciocan C, et al. Mortality of talc miners and millers from Val Chisone, Northern Italy: an updated cohort study. J Occup Environ Med. 2017;59(7):659–664. doi: 10.1097/JOM.0000000000000992. [DOI] [PubMed] [Google Scholar]
  • 37.Rubino G, Scansetti G, Piolatto G, Romano C. Mortality study of talc miners and millers. J Occup Med. 1976;18(3):187–193. doi: 10.1097/00043764-197603000-00013. [DOI] [PubMed] [Google Scholar]
  • 38.Finkelstein MM. Re: mortality of talc miners and millers from Val Chisone, Northern Italy. J Occup Environ Med. 2017;59(10):e194. doi: 10.1097/JOM.0000000000001139. [DOI] [PubMed] [Google Scholar]
  • 39.Fordyce TA, Mowat FS, Leonhard MJ, Moolgavkar SH. Letter to the Editor: misrepresentation by Egilman et al. of the Fordyce et al. (2019) vermont talc miners and millers cohort study update. J Occup Environ Med. 2020;62(1):e19-e21. doi:10.1097/JOM.0000000000001784 [DOI] [PubMed]
  • 40.Hull MJ, Abraham J, Case B. Mesothelioma among workers in asbestiform fiber-bearing talc mines in New York State. Ann Occup Hyg. 2002;46(Supplement 1):132–135. doi: 10.1093/annhyg/46.suppl_1.132. [DOI] [Google Scholar]
  • 41.Wolff H, Vehmas T, Oksa P, Rantanen J, Vainio H. Asbestos, asbestosis, and cancer, the Helsinki criteria for diagnosis and attribution 2014: recommendations. Scand J Work Environ Health. 2015;41(1):5–15. doi: 10.5271/sjweh.3462. [DOI] [PubMed] [Google Scholar]
  • 42.Kim J, Bhagwandin S, Labow DM. Malignant peritoneal mesothelioma: a review. Ann Transl Med. 2017;5(11):236–236. doi: 10.21037/atm.2017.03.96. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 43.Xu J, Kadariya Y, Cheung M, et al. Germline mutation of Bap1 Accelerates development of asbestos-induced malignant mesothelioma. Cancer Res. 2014;74(16):4388–4397. doi: 10.1158/0008-5472.CAN-14-1328. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 44.Ohar JA, Cheung M, Talarchek J, et al. Germline BAP1 mutational landscape of asbestos-exposed malignant mesothelioma patients with family history of cancer. Cancer Res. 2016;76(2):206–215. doi: 10.1158/0008-5472.CAN-15-0295. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 45.Henderson DW, Rödelsperger K, Woitowitz HJ, Leigh J. After Helsinki: a multidisciplinary review of the relationship between asbestos exposure and lung cancer, with emphasis on studies published during 1997–2004. Pathology (Phila) 2004;36(6):517–550. doi: 10.1080/00313020400010955. [DOI] [PubMed] [Google Scholar]
  • 46.Iwatsubo Y, Pairon JC, Boutin C, et al. Pleural mesothelioma: dose-response relation at low levels of asbestos exposure in a French population-based case-control study. Am J Epidemiol. 1998;148(2):133–142. doi: 10.1093/oxfordjournals.aje.a009616. [DOI] [PubMed] [Google Scholar]
  • 47.Ferrante D, Mirabelli D, Tunesi S, Terracini B, Magnani C. Pleural mesothelioma and occupational and non-occupational asbestos exposure: a case-control study with quantitative risk assessment. Occup Environ Med. 2016;73(3):147–153. doi: 10.1136/oemed-2015-102803. [DOI] [PubMed] [Google Scholar]
  • 48.Albin M, Jakobsson K, Attewell R, Johansson L, Welinder H. Mortality and cancer morbidity in cohorts of asbestos cement workers and referents. Occup Environ Med. 1990;47(9):602–610. doi: 10.1136/oem.47.9.602. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 49.Andrion A, Bosia S, Paoletti L, et al. Malignant peritoneal mesothelima in a 17-year-old boy with evidence of previous exposure to chrysotile and tremolite asbestos. Hum Pathol. 1994;25(6):617–622. doi: 10.1016/0046-8177(94)90230-5. [DOI] [PubMed] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Data Availability Statement

The datasets generated and/or analyzed during the current study are not publicly available. Individuals of details of cases will not be provided to protect the confidentiality of the cases presented in the study. Efforts to minimized identification, such as describing age in a range were employed.


Articles from Journal of Occupational Medicine and Toxicology (London, England) are provided here courtesy of BMC

RESOURCES