asbestos--amosite and Lung-Neoplasms

An earlier meta-analysis of mortality studies of asbestos-exposed worker populations, quantified excess mesothelioma and lung cancer risks in relation to cumulative exposure to the three main commercial asbestos types. The aim of this paper was to update these analyses incorporating new data based on increased follow-up of studies previously included, as well as studies of worker populations exposed predominantly to single fibre types published since the original analysis. Mesothelioma as a percentage of expected mortality due to all causes of death, percentage excess lung cancer and mean cumulative exposure were abstracted from available mortality studies of workers exposed predominantly to single asbestos types. Average excess mesothelioma and lung cancer per unit of cumulative exposure were summarised for groupings of studies by fibre type; models for pleural and peritoneal mesothelioma risk and lung cancer risk in terms of cumulative exposure for the different fibre types were fitted using Poisson regression. The average mesothelioma risks (per cent of total expected mortality) per unit cumulative exposure (f/cc.yr), R

Topics: Asbestos; Asbestos, Amosite; Asbestos, Amphibole; Asbestos, Crocidolite; Asbestos, Serpentine; Humans; Lung Neoplasms; Mesothelioma; Microscopy, Phase-Contrast; Occupational Diseases; Occupational Exposure

Mesothelioma is a "new" malignant disease strongly associated with exposure to amphibole asbestos exposure (amosite and crocidolite) environmentally and in the work place. Nonetheless, in recent years, we have learned that many cases of mesothelioma are idiopathic, while some are caused by therapeutic irradiation or chronic inflammation in body cavities. This paper reviews the key epidemiological features of the malignancy in the context of the biological and mineralogical factors that influence mesothelioma development. These tumors challenge the diagnostic pathologist's acumen, the epidemiologist's skill in devising meaningful and definitive studies, the industrial hygienist's knowledge of environmental hazards in diverse occupational settings, and the clinician's skill in managing an intrepid and uniformly fatal malignancy.

Topics: Asbestos, Amosite; Asbestos, Amphibole; Asbestos, Crocidolite; Asbestos, Serpentine; Female; History, 20th Century; Humans; Lung Neoplasms; Male; Mesothelioma; Mining; Occupational Diseases

The strong relationship between mesothelioma and asbestos exposure is well established. The analysis of lung asbestos burden by light and electron microscopy assisted to understand the increased incidence of mesothelioma in asbestos mining and consuming nations.The data on the occupational exposure to asbestos are important information for the purpose of compensation of occupational disease No. 4105 (asbestos-associated mesothelioma) in Germany.However, in many cases the patients have forgotten conditions of asbestos exposure or had no knowledge about the used materials with components of asbestos. Mineral fiber analysis can provide valuable information for the research of asbestos-associated diseases and for the assessment of exposure. Because of the variability of asbestos exposure and long latency periods, the analysis of asbestos lung content is a relevant method for identification of asbestos-associated diseases. Also, sources of secondary exposure, so called "bystander exposition" or environmental exposure can be examined by mineral fiber analysis.Household contacts to asbestos are known for ten patients (1987-2009) in the German mesothelioma register; these patients lived together with family members working in the asbestos manufacturing industry.Analysis of lung tissue for asbestos burden offers information on the past exposure. The predominant fiber-type identified by electron microscopy in patients with mesothelioma is amphibole asbestos (crocidolite or amosite). Latency times (mean 42.5 years) and mean age at the time of diagnose in patients with mesothelioma are increasing (65.5 years). The decrease of median asbestos burden of the lung in mesothelioma patients results in disease manifestation at a higher age.Lung dust analyses are a relevant method for the determination of causation in mesothelioma. Analysis of asbestos burden of the lung and of fiber type provides insights into the pathogenesis of malignant mesothelioma. The most important causal factor for the development of mesothelioma is still asbestos exposure.

Topics: Aged; Asbestos; Asbestos, Amosite; Asbestos, Amphibole; Asbestos, Crocidolite; Asbestos, Serpentine; Female; Germany; Humans; Lung Neoplasms; Male; Mesothelioma; Microscopy, Electron; Middle Aged; Mineral Fibers; Occupational Diseases; Occupational Exposure; Pleural Neoplasms

Grunerite asbestos (amosite) has been shown in epidemiological and experimental animal studies to cause lung cancer, mesothelioma and pulmonary fibrosis commonly referred to as asbestosis. An overview of the human and experimental animal studies describing the health hazards of grunerite asbestos (amosite) is presented. Of the many human studies describing the health hazards of asbestos, only three factories using mainly, if not exclusively, grunerite asbestos (amosite) have been studied. The first is a series of reports on a cohort of 820 workers from a plant located in Paterson, NJ. Among this cohort, 18.7% died of lung cancer and 17 mesotheliomas occurred. The Paterson factory closed in 1954 and moved to Tyler, Texas where it operated until 1972. Among the 1130 former workers in the Tyler plant 6 mesotheliomas were reported with 15.8% lung cancer mortality. The third grunerite asbestos (amosite) exposed cohort was an insulation board manufacturing facility in Uxbridge, United Kingdom. Here 17.1% of the workers died of lung cancer and 5 mesotheliomas occurred. The lung content from 48 Uxbridge workers was analyzed by analytical transmission electron microscopy for mineral fibers. The relationship between grunerite asbestos (amosite) concentrations in the lung correlated with grades of fibrosis and asbestos bodies and was lower than the concentration found in the cases with malignant tumors. The lung cancer cases contained more grunerite asbestos (amosite) than mesothelioma cases, and in the cases of non-malignant disease the concentrations were still lower. In both types of malignancies the concentration of grunerite asbestos (amosite) was very high-over a billion fibers per gram of dried lung tissue. Occupational exposure to airborne concentrations of between 14 and 100 fibers of grunerite asbestos (amosite) per milliliter after 20 year latency causes marked increases in lung cancer, mesothelioma and pulmonary fibrosis (asbestosis).

Topics: Air Pollutants, Occupational; Animals; Asbestos, Amosite; Asbestosis; Cohort Studies; Disease Models, Animal; Humans; Lung; Lung Neoplasms; Mesothelioma; New Jersey; Texas; United Kingdom

Primary malignant mesothelial tumours were recognized by pathologists before asbestiform minerals (chrysotile, crocidolite and amosite) were mined commercially. The discovery, 40 yrs ago, of a causal link with crocidolite and the wide-ranging epidemiological studies which followed are the subject of this review. Early case-control and descriptive surveys, supplemented by cohort studies in insulation workers and chrysotile miners, quickly demonstrated major occupational and geographical differences, with high risk in naval dockyard areas and in the heating trades. In the 1980s, reliable cohort surveys showed that in mining and in the manufacture of asbestos products the mesothelioma risk was much higher when exposure included crocidolite or amosite than chrysotile alone. However, qualitative and quantitative information on exposure was too often inadequate for this evidence to be conclusive. Well-controlled lung fibre analyses have reduced these deficiencies and demonstrated the probable implications of the greater biopersistence of amphibole fibres. Chrysotile for industrial use often contains low concentrations of fibrous tremolite, which may well explain the few cases of mesothelioma associated with this type of asbestos. Progress in this field has been much retarded by controversy, for which the 20 year gap between the availability of reliable estimates of risk for the mining of chrysotile and that for crocidolite or amosite may have been largely responsible.

Topics: Asbestos; Asbestos, Amosite; Asbestos, Amphibole; Asbestos, Crocidolite; Asbestos, Serpentine; Carcinogens; Case-Control Studies; Cohort Studies; Female; History, 20th Century; Humans; Lung Neoplasms; Male; Mesothelioma; Mineral Fibers; Mining; Occupational Diseases; Reproducibility of Results; Risk Factors

A review of the literature on chronic inhalation studies in which rats were exposed to mineral fibres at known fibre number concentrations was undertaken to examine the specific roles of fibre length and composition on the incidences of both lung cancer and mesothelioma. For lung cancer, the percentage of lung tumours (y) could be described by a relation of the form y = a + bf + cf2, where f is the concentration of fibre numbers and a, b, and c are fitted constants. The correlation coefficients for the fitted curves were 0.76 for > 5 microns f/ml, 0.84 for > 10 microns f/ml, and 0.85 for > 20 microns f/ml. These seemed to be independent of fibre type. It has been shown that brief inhalation exposures to chrysotile fibre produces highly concentrated fibre deposits on bifurcations of alveolar ducts, and that many of these fibres are phagocytosed by the underlying type II epithelial cells within a few hours. Churg has shown that both chrysotile and amphibole fibres retained in the lungs of former miners and millers do not clear much with the years since last exposure. Thus, lung tumours may be caused by that small fraction of the inhaled fibres that are retained in the interstitium below small airway bifurcations where clearance processes are ineffective. By contrast, for mesothelioma, the (low) tumour yields seemed to be highly dependent upon fibre type. Combining the data from various studies by fibre type, the percentage of mesotheliomas was 0.6% for Zimbabwe (Rhodesian) chrysotile, 2.5% for the various amphiboles as a group, and 4.7% for Quebec (Canadian) chrysotile. This difference, together with the fact that Zimbabwe chrysotile has 2 to 3 orders of magnitude less than tremolite than Quebec chrysotile, provides support for the hypothesis that the mesotheliomas that have occurred among chrysotile miners and millers could be largely due to their exposures to tremolite fibres. The chrysotile fibres may be insufficiently biopersistent because if dissolution during translocation from their sites of deposition to sites where more durable fibres can influence the transformation or progression to mesothelioma.

Topics: Asbestos; Asbestos, Amosite; Asbestos, Serpentine; Humans; Incidence; Lung Neoplasms; Mesothelioma

The authors briefly reviewed the literature concerning the risk factors for primary pleural tumors in humans. The results from the most relevant studies emphasize the fact that the large majority of mesotheliomas are associated with exposure to asbestos or asbestiform fibers. Exposure to asbestos is mainly through industrial use, and mesotheliomas result from occupational, para-occupational, or environmental exposure. Fibers of crocidolite, amosite, and chrysotile appear to be, in descending order, more carcinogenic for pleural tissues. The authors summarize the available data on consumption of asbestos and asbestos-based products in Italy. The chrysotile-asbestos mine in Balangero (Piedmont) stimulated the industrial production of asbestos-cement; asbestos has been largely sprayed among shipyards and user for insulating railroad coaches and carriages. Italy had the greatest consumption of crocidolite in Europe, which was not banned until 1986. The authors discuss the major findings derived from descriptive epidemiological data presented in previous papers dealing with this issue. In addition, standardized mortality rates of primary pleural tumors for European countries are shown. A clearly increasing trend for mortality is observed in Italy, which has also the provinces with the highest mortality rates in Europe. Among Italian provinces, the mortality rates are consistent with the number of asbestosis cases receiving workman's compensation. The authors present the results of both cohort and case-control analytical studies performed in Italy, and provide suggestions for further research.

Topics: Asbestos; Asbestos, Amosite; Asbestos, Crocidolite; Asbestos, Serpentine; Asbestosis; Construction Materials; Europe; Female; Humans; Italy; Lung Neoplasms; Male; Mesothelioma; Occupational Diseases; Pleural Neoplasms; Prevalence; Risk Factors

Topics: Asbestos; Asbestos, Amosite; Asbestos, Crocidolite; Asbestos, Serpentine; Canada; Humans; Lung Neoplasms; Maximum Allowable Concentration; Mesothelioma; New Zealand; Occupational Diseases; Risk; South Africa; United Kingdom; United States

Tissues obtained at autopsy or biopsy from 81 workers and 2 household persons, were chemically digested. The asbestos fibres recovered were characterized by analytical transmission electron microscopy. Among the 83 causes of death were 33 mesotheliomas, 35 lung cancers, 12 asbestosis and 3 from other cancers. Of the three major commercial asbestos fibre types, amosite was found to be the most prevalent fibre, occurring in approximately 76% of the cases, followed by chrysotile in approximately 60% and crocidolite in approximately 24%. Amosite and chrysotile were observed as the single commercial fibre in approximately 22 and approximately 17% of the cases respectively, whereas crocidolite and tremolite were found as the single fibre type in only approximately 2.5% of the cases. Among the fifteen cases where chrysotile and tremolite occurred together, the amount of chrysotile fibre always exceeded tremolite. However, tremolite was also found in ten additional cases where chrysotile was not detected. Amosite was present in four, amosite plus crocidolite in three, and crocidolite alone in one. Amosite was present in all of the insulation workers' lungs studied and was found in the highest concentration in this exposure category. The highest chrysotile concentration was found among workers in general trades. Although most prevalent in shipyard workers lungs, crocidolite concentration is not statistically different among the exposure groups studied. Although crocidolite was found in twenty cases, amosite accompanied it in eighteen of these. Eleven of the 20 cases were from shipyard workers. Of the 8 mesothelioma cases, 7 also contained amosite. Crocidolite alone only occurred in 1 of the 33 mesothelioma cases analysed. We concluded the following: crocidolite exposure occurred among USA insulators and a large percentage of other workers as well; insulation workers are primarily exposed to amosite; mixed fibre exposures are associated with more mesotheliomas than single fibre exposures; chrysotile only exposure is associated with approximately 12% of the mesothelioma cases studied; and if tremolite exposure is associated with chrysotile exposure, the chrysotile amount exceeds that for the associated tremolite.

Topics: Aged; Asbestos; Asbestos, Amosite; Asbestos, Amphibole; Asbestos, Crocidolite; Asbestos, Serpentine; Asbestosis; Autopsy; Biopsy; Female; Humans; Lung; Lung Neoplasms; Male; Microscopy, Electron; Middle Aged; Occupational Exposure; Organ Culture Techniques; United States

We have conducted a population-based study of pleural mesothelioma patients with occupational histories and measured asbestos lung burdens in occupationally exposed workers and in the general population. The relationship between lung burden and risk, particularly at environmental exposure levels, will enable future mesothelioma rates in people born after 1965 who never installed asbestos to be predicted from their asbestos lung burdens.. Following personal interview asbestos fibres longer than 5 µm were counted by transmission electron microscopy in lung samples obtained from 133 patients with mesothelioma and 262 patients with lung cancer. ORs for mesothelioma were converted to lifetime risks.. Lifetime mesothelioma risk is approximately 0.02% per 1000 amphibole fibres per gram of dry lung tissue over a more than 100-fold range, from 1 to 4 in the most heavily exposed building workers to less than 1 in 500 in most of the population. The asbestos fibres counted were amosite (75%), crocidolite (18%), other amphiboles (5%) and chrysotile (2%).. The approximate linearity of the dose-response together with lung burden measurements in younger people will provide reasonably reliable predictions of future mesothelioma rates in those born since 1965 whose risks cannot yet be seen in national rates. Burdens in those born more recently will indicate the continuing occupational and environmental hazards under current asbestos control regulations. Our results confirm the major contribution of amosite to UK mesothelioma incidence and the substantial contribution of non-occupational exposure, particularly in women.

Topics: Adult; Aged; Asbestos, Amosite; Asbestos, Amphibole; Asbestos, Crocidolite; Asbestos, Serpentine; Asbestosis; Employment; Female; Humans; Lung; Lung Neoplasms; Male; Mesothelioma; Mesothelioma, Malignant; Middle Aged; Mineral Fibers; Occupational Diseases; Occupational Exposure; Pleural Neoplasms; Risk Assessment

In 2013 the International Journal of Surgical Pathology published a case report of intrasplenic malignant mesothelioma (MM) in a 48-year-old man: it was the first report in literature describing a case of primitive intra-splenic MM, described without  a history of asbestos exposure.. To verify the possible past exposure to asbestos, ignored by the patient himself, by studying in depth his environmental and occupational history.. Information about the occupational and non-occupational history of the subject was collected by Experts of the Operational Unit of Occupational Health and Safety Control (UOC PSAL) of the Local Health Unit Umbria 1 - Perugia, using the Italian National Mesothelioma Register (ReNaM) questionnaire and guide lines; an inspection was  carried out at the past canning industry where the patient worked in the period 1982-1990 and material was taken to be analysed by MOCF and SEM.. Samples showed the presence of asbestos  fibres belonging to the amphibole class (amosite and crocidolite) and to the serpentine class (chrysotile).. The survey described the past occupational exposure to asbestos in a canning industry, where  the subject worked in the period 1982-1990,  unknown to the patient himself. The authors strongly confirm the  usefulness of standardized methods, such as the ReNaM Questionnaire, and the importance of technical expertise of the investigator to find and analyse the suspect materials and to demonstrate  possible past occupational exposure to asbestos.

Topics: Asbestos; Asbestos, Amosite; Asbestos, Crocidolite; Asbestos, Serpentine; Carcinogens; Food Packaging; Humans; Lung Neoplasms; Male; Medical History Taking; Mesothelioma; Mesothelioma, Malignant; Middle Aged; Risk Assessment; Splenic Neoplasms

Human exposure to Libby amphibole (LA) asbestos increases risk of lung cancer, mesothelioma, and non-malignant respiratory disease. This study evaluated potency and time-course effects of LA and positive control amosite (AM) asbestos fibers in male F344 rats following nose-only inhalation exposure.. Rats were exposed to air, LA (0.5, 3.5, or 25.0 mg/m(3) targets), or AM (3.5 mg/m(3) target) for 10 days and assessed for markers of lung inflammation, injury, and cell proliferation. Short-term results guided concentration levels for a stop-exposure study in which rats were exposed to air, LA (1.0, 3.3, or 10.0 mg/m(3)), or AM (3.3 mg/m(3)) 6 h/day, 5 days/week for 13 weeks, and assessed 1 day, 1, 3, and 18 months post-exposure. Fibers were relatively short; for 10 mg/m(3) LA, mean length of all structures was 3.7 μm and 1% were longer than 20 μm.. Ten days exposure to 25.0 mg/m(3) LA resulted in significantly increased lung inflammation, fibrosis, bronchiolar epithelial cell proliferation and hyperplasia, and inflammatory cytokine gene expression compared to air. Exposure to 3.5 mg/m(3) LA resulted in modestly higher markers of acute lung injury and inflammation compared to AM. Following 13 weeks exposure, lung fiber burdens correlated with exposure mass concentrations, declining gradually over 18 months. LA (3.3 and 10.0 mg/m(3)) and AM produced significantly higher bronchoalveolar lavage markers of inflammation and lung tissue cytokines, Akt, and MAPK/ERK pathway components compared to air control from 1 day to 3 months post-exposure. Histopathology showed alveolar inflammation and interstitial fibrosis in all fiber-exposed groups up to 18 months post-exposure. Positive dose trends for incidence of alveolar epithelial hyperplasia and bronchiolar/alveolar adenoma or carcinoma were observed among LA groups.. Inhalation of relatively short LA fibers produced inflammatory, fibrogenic, and tumorigenic effects in rats which replicate essential attributes of asbestos-related disease in exposed humans. Fiber burden, inflammation, and activation of growth factor pathways may persist and contribute to lung tumorigenesis long after initial LA exposure. Fiber burden data are being used to develop a dosimetry model for LA fibers, which may provide insights on mode of action for hazard assessment.

Topics: Adenocarcinoma, Bronchiolo-Alveolar; Adenoma; Animals; Apoptosis; Asbestos, Amosite; Asbestos, Amphibole; Cell Proliferation; Cell Transformation, Neoplastic; Cytokines; Dose-Response Relationship, Drug; Epithelial Cells; Hyperplasia; Inflammation Mediators; Inhalation Exposure; Lung; Lung Neoplasms; Male; Pneumonia; Pulmonary Fibrosis; Rats, Inbred F344; Risk Assessment; Signal Transduction; Time Factors

In former mine workers of Libby, MT, exposure to amphibole-containing vermiculite was linked to increased rates of asbestosis, lung cancer, and mesothelioma. Although many studies showed adverse effects following exposure to Libby amphibole (LA; a mixture of winchite, richterite, and tremolite), little is known regarding the relative toxicity of LA compared to regulated asbestos, or regarding the risks associated with acute high-dose exposures relative to repeated low-dose exposures. In this study, pulmonary function, inflammation, and pathology were assessed after single or multiple intratracheal (IT) exposures of LA or a well-characterized amosite (AM) control fiber with equivalent fiber characteristics. Male F344 rats were exposed to an equivalent total mass dose (0.15, 0.5, 1.5, or 5 mg/rat) of LA or AM administered either as a single IT instillation, or as multiple IT instillations given every other week over a 13-wk period, and necropsied up to 20 mo after the initial IT. When comparing the two fiber types, in both studies LA resulted in greater acute neutrophilic inflammation and cellular toxicity than equal doses of AM, but long-term histopathological changes were approximately equivalent between fibers, suggesting that LA is at least as toxic as AM. In addition, although no dose-response relationship was discerned, mesothelioma or lung carcinomas were found after exposure to low and high dose levels of LA or AM in both studies. Conversely, when comparing studies, an equal mass dose given over multiple exposures instead of a single bolus resulted in greater chronic pathological changes in lung at lower doses, despite the initially weaker acute inflammatory response. Overall, these results suggest that there is a possibility of greater long-term pathological changes with repeated lower LA dose exposures, which more accurately simulates chronic environmental exposures.

Topics: Air Pollutants, Occupational; Animals; Asbestos, Amosite; Asbestos, Amphibole; Dose-Response Relationship, Drug; Drug Administration Schedule; Inflammation; Lung; Lung Neoplasms; Male; Mesothelioma; Rats; Rats, Inbred F344; Toxicity Tests, Acute; Toxicity Tests, Chronic

A diagnosis of asbestosis, lung fibrosis due to asbestos exposure, was proposed in 2003 in a 64-year-old woman on the basis of the history, computed tomography appearances, lung function studies, and biometric data. This diagnosis was confirmed by the pathological examination of a lung lobe resected surgically for bronchial carcinoma in 2010. The diagnosis of asbestosis is now rarely made as a result of a substantial decrease in dust exposure over the past decades and mainly because of the interdiction of asbestos use in western countries. Currently, the most frequent thoracic manifestations of asbestos exposure are benign pleural lesions and mesothelioma. It has also become exceptional to have pathological confirmation of the diagnosis, obtained in this woman thanks to the surgical treatment of another complication of her occupational exposure.

Topics: Antineoplastic Combined Chemotherapy Protocols; Asbestos, Amosite; Asbestosis; Bronchoalveolar Lavage Fluid; Carcinoma, Bronchogenic; Cisplatin; Combined Modality Therapy; Female; Humans; Incidental Findings; Industry; Lung; Lung Neoplasms; Middle Aged; Mineral Fibers; Occupational Exposure; Pleura; Pulmonary Aspergillosis; Respiratory Function Tests; Tomography, X-Ray Computed; Vinblastine; Vinorelbine

Asbestos is a potent carcinogen associated with increased risks of malignant mesothelioma and lung cancer in humans. Although the mechanism of carcinogenesis remains elusive, the physicochemical characteristics of asbestos play a role in the progression of asbestos-induced diseases. Among these characteristics, a high capacity to adsorb and accommodate biomolecules on its abundant surface area has been linked to cellular and genetic toxicity. Several previous studies identified asbestos-interacting proteins. Here, with the use of matrix-assisted laser desorption ionization-time of flight mass spectrometry, we systematically identified proteins from various lysates that adsorbed to the surface of commercially used asbestos and classified them into the following groups: chromatin/nucleotide/RNA-binding proteins, ribosomal proteins, cytoprotective proteins, cytoskeleton-associated proteins, histones and hemoglobin. The surfaces of crocidolite and amosite, two iron-rich types of asbestos, caused more protein scissions and oxidative modifications than that of chrysotile by in situ-generated 4-hydroxy-2-nonenal. In contrast, we confirmed the intense hemolytic activity of chrysotile and found that hemoglobin attached to chrysotile, but not silica, can work as a catalyst to induce oxidative DNA damage. This process generates 8-hydroxy-2'-deoxyguanosine and thus corroborates the involvement of iron in the carcinogenicity of chrysotile. This evidence demonstrates that all three types of asbestos adsorb DNA and specific proteins, providing a niche for oxidative modification via catalytic iron. Therefore, considering the affinity of asbestos for histones/DNA and the internalization of asbestos into mesothelial cells, our results suggest a novel hypothetical mechanism causing genetic alterations during asbestos-induced carcinogenesis.

Topics: 8-Hydroxy-2'-Deoxyguanosine; Aldehydes; Animals; Asbestos, Amosite; Asbestos, Crocidolite; Asbestos, Serpentine; Chromatin; Cytoskeleton; Deoxyguanosine; DNA; DNA Damage; Hemoglobins; Histones; Iron; Lung Neoplasms; Mesothelioma; Mice; Oxidation-Reduction; Proteins; Rats; Ribosomal Proteins; RNA-Binding Proteins; Spectrometry, Mass, Matrix-Assisted Laser Desorption-Ionization; Surface Properties

Lung tissue from 15 women who died from mesothelioma was evaluated for tissue burden of ferruginous bodies and uncoated asbestos fibers. The group contained individuals who had occupational exposure to asbestos and others had family members whose work history included vocations where contact with asbestos containing materials occurred.. Tissue samples from tumor free lung were digested and filtered and then investigated for ferruginous bodies by light microscopy and asbestos and non-asbestos fibers by analytical transmission electron microscopy (ATEM). Size and type of fibers were also analyzed.. Asbestos bodies were found in 13 of the 15 samples and asbestos fibers were found in all cases. The most commonly found uncoated asbestos fiber in these individuals was amosite whereas tremolite was the second most commonly found form. The asbestos fiber burden in these females was often of mixed types.. The asbestos body and fiber burden in these cases show variation in tissue burden. Some cases in this study had appreciable burden, which was attributed to secondhand exposure from occupationally exposed family members. Mesothelioma can occur also in individuals with comparatively low tissue burdens of asbestos.

Topics: Aged; Aged, 80 and over; Asbestos, Amosite; Asbestos, Amphibole; Asbestos, Crocidolite; Asbestosis; Body Burden; Environmental Exposure; Female; Humans; Lung; Lung Neoplasms; Mesothelioma; Microscopy, Electron; Middle Aged; Mineral Fibers; Occupational Exposure; Reproducibility of Results

A factory fire in Tranmere, Merseyside, England, deposited asbestos containing fallout in an urban area. There was considerable community anxiety for months after the incident. Therefore an assessment of the long term health risks of this acute environmental incident were requested by the local health authority.. The facts of the incident were gathered and appraised from unpublished and press reports, involved personnel, and further analysis of material collected at the time of the incident. The literature on the long term health risks of asbestos was reviewed, and combined with evidence on asbestos exposure to estimate community health risk.. Risk was almost entirely from exposure to fire fallout of chrysotile in asbestos bitumen paper covering the factory roof. Amosite was only detected in a few samples and in trace amounts. The number of people who lived in the area of fallout was 16 000 to 48 000. From a non-threshold model with assumptions likely to overestimate risk, the lung cancer risk is estimated to be undetectably small. Risk of mesothelioma from chrysotile exposure, and risks of lung cancer and mesothelioma from amosite exposure were based on observational studies and were estimated to be even lower than that of lung cancer risk from chrysotile exposure. Academically, there are assumptions that while reasonable cannot be proven, for example, the validity of extrapolating observed risk from much higher exposures to lower exposures, estimates of individual exposure, and that there is no threshold for asbestos to cause cancer.. The author is unaware of a similar study on long term health risks in a community exposed to asbestos in a fire. It is concluded that, using methods that do not underestimate risk, risk is undetectably small. Practical lessons from this methodology and approach to health risk assessment are discussed.

Topics: Asbestos; Asbestos, Amosite; Asbestos, Serpentine; England; Environmental Exposure; Environmental Pollutants; Fires; Humans; Industry; Linear Models; Lung Neoplasms; Mesothelioma; Risk Assessment; Survival Rate

This article describes the activity of an E-glass microfiber (104E) during chronic inhalation and intraperitoneal injection studies in rats. Results are compared with another microfiber of similar dissolution rate (k(dis)), code 100/475, and the more durable amosite asbestos, both of which we had previously used in similar experiments (Davis et al., 1996). Rats were exposed to aerosol concentrations of 1000 fibers (longer than 5 microm)/ml, as measured by optical microscopy, for 7 h/day, 5 days/wk. Subgroups of rats were followed for mean lung burden, early and late signs of fibrosis, and tumor incidence. At the end of 12 mo of exposure, the mean number of 104E fibers of all lengths in the lungs was approximately double that for amosite but two-thirds of that for 100/475. For fibers longer than 15 microm, the mean 104E burden was similar to that for the amosite and more than twice that of the 100/475. After a 12-mo recovery period, the retained lung burdens (of fibers of all lengths) were approximately 30% of those at 12 mo for both microfibers, and somewhat higher (approximately 44%) for amosite. Amosite and 100/475 fibers longer than 15 microm were more persistent in the lungs than 104E fibers. The chemical composition of 104E fibers did not appear to have been significantly altered by up to 24 mo of residence in lung tissue, whereas the composition of 100/475 was substantially altered over the same time period. From the inhalation study, out of the pathology subgroup of 43 animals exposed to 104E microfibers, 10 had lung tumors (7 carcinoma, 3 adenoma) and 2 had mesotheliomas, whereas in 42 rats exposed to amosite asbestos, there were 16 lung tumors (7 carcinoma, 9 adenoma) and 2 mesotheliomas. The 104E- and amosite-treated animals had similar levels of fibrosis. In contrast, 38 animals treated with 100/475 had little fibrosis, 4 lung tumors (adenomas), and no mesotheliomas. The greater pathogenicity of the 104E fibers, compared to 100/475 fibers, might be partly explained by the greater numbers of long fibers retained in the lung after 12 mo of inhalation. However, we speculate that modification of surface properties by extensive selective leaching of some glass components reduces the toxic potential of 100/475. In a parallel intraperitoneal injection study, 104E caused considerably more mesotheliomas (21 rats out of 24) than 100/475 (8 rats out of 24). In addition, 104E appeared to be more active than amosite asbestos, since mesotheliomas appeared mu

Topics: Administration, Inhalation; Aerosols; Animals; Asbestos, Amosite; Body Burden; Carcinoma; Glass; Inhalation Exposure; Injections, Intraperitoneal; Lung; Lung Neoplasms; Male; Mesothelioma; Mineral Fibers; Neoplasms, Experimental; Particle Size; Pulmonary Fibrosis; Rats; Rats, Wistar; Survival Analysis; Survival Rate; Toxicity Tests

Recent studies have shown that iron is an important factor in the chemical activity of asbestos and may play a key role in its biological effects. The most carcinogenic forms of asbestos, crocidolite and amosite, contain up to 27% iron by weight as part of their crystal structure. These minerals can acquire more iron after being inhaled, thereby forming asbestos bodies. Reported here is a method for depositing iron on asbestos fibers in vitro which produced iron deposits of the same form as observed on asbestos bodies removed from human lungs. Crocidolite and amosite were incubated in either FeCl(2) or FeCl(3) solutions for 2 h. To assess the effect of longer-term binding, crocidolite was incubated in FeCl(2) or FeCl(3) and amosite in FeCl(3) for 14 days. The amount of iron bound by the fibers was determined by measuring the amount remaining in the incubation solution using an iron assay with the chelator ferrozine. After iron loading had been carried out, the fibers were also examined for the presence of an increased amount of surface iron using X-ray photoelectron spectroscopy (XPS). XPS analysis showed an increased amount of surface iron on both Fe(II)- and Fe(III)-loaded crocidolite and only on Fe(III)-loaded amosite. In addition, atomic force microscopy revealed that the topography of amosite, incubated in 1 mM FeCl(3) solutions for 2 h, was very rough compared with that of the untreated fibers, further evidence of Fe(III) accumulation on the fiber surfaces. Analysis of long-term Fe(III)-loaded crocidolite and amosite using X-ray diffraction (XRD) suggested that ferrihydrite, a poorly crystallized hydrous ferric iron oxide, had formed. XRD also showed that ferrihydrite was present in amosite-core asbestos bodies taken from human lung. Auger electron spectroscopy (AES) confirmed that Fe and O were the only constituent elements present on the surface of the asbestos bodies, although H cannot be detected by AES and is presumably also present. Taken together for all samples, the data reported here suggest that Fe(II) binding may result from ion exchange, possibly with Na, on the fiber surfaces, whereas Fe(III) binding forms ferrihydrite on the fibers under the conditions used in this study. Therefore, fibers carefully loaded with Fe(III) in vitro may be a particularly appropriate and useful model for the study of chemical characteristics associated with asbestos bodies and their potential for interactions in a biosystem.

Topics: Adenocarcinoma; Aged; Asbestos, Amosite; Asbestos, Crocidolite; Asbestosis; Chlorides; Ferric Compounds; Ferrous Compounds; Humans; In Vitro Techniques; Lung; Lung Neoplasms; Male; Microscopy, Atomic Force; Microscopy, Electron, Scanning; Models, Biological; Spectrometry, X-Ray Emission

Cigarette smoke augments asbestos-induced bronchogenic carcinoma by mechanisms that are not established. Alveolar epithelial cell (AEC) injury due to oxidant-induced DNA damage and depletion of glutathione (GSH) and adenosine triphosphate (ATP) may be one important mechanism. We previously showed that amosite asbestos-induces hydroxyl radical production and DNA damage to cultured AEC and that phytic acid, an iron chelator, is protective. We hypothesized that whole cigarette smoke extracts (CSE) augment amosite asbestos-induced AEC injury by generating iron-induced free radicals that damage DNA and reduce cellular GSH and ATP levels. Asbestos or CSE each caused dose-dependent toxicity to AEC (WI-26 and rat alveolar type I-like cells) as assessed by 51chromium release. The combination of asbestos (5 microg/cm2) and CSE (0.O1-0.1%) caused synergistic injury whereas higher doses of each agent primarily had an additive toxic effect. Asbestos (5 microg/cm2) augmented CSE-induced (0.01-1.0%) AEC DNA damage over a 4 h exposure period as assessed by an alkaline unwinding, ethidium bromide fluorometric technique. These effects were synergistic in A549 cells and additive in WI-26 cells. Asbestos (5 microg/cm2) and CSE (0.5-1.0%) reduced A549 and WI-26 cell GSH levels as assessed spectrophotometrically and ATP levels as assessed by luciferin/luciferase chemiluminescence but a synergistic interaction was not detected. Phytic acid (500 microM) and catalase (100 microg/ml) each attenuated A549 cell DNA damage and depletion of ATP caused by asbestos and CSE. However, neither agent attenuated WI-26 cell DNA damage nor the reductions in GSH levels in WI-26 and A549 cells exposed to asbestos and CSE. We conclude that CSE enhance asbestos-induced DNA damage in cultured alveolar epithelial cells. These data provide additional support that asbestos and cigarette smoke are genotoxic to relevant target cells in the lung and that iron-induced free radicals may in part cause these effects.

Topics: Adenosine Triphosphate; Antioxidants; Asbestos, Amosite; Cell Line; DNA Damage; Epithelium; Glutathione; Humans; Lung Neoplasms; Phytic Acid; Pulmonary Alveoli; Smoking; Tars

To analyze the correlation between asbestos lung burden and lung cancer, lungs of 211 female cases with and without lung cancer were examined. Phase-contrast microscopic (PCM) counting of ferruginous (FBs) and uncoated fibers (UFs), which had length longer than 5 microns and aspect ratios greater than 3:1, revealed a significantly higher level of FBs plus UFs in urban lung cancer cases than urban non-lung cancer cases (1380.5 vs. 550.3; p < 0.001). No difference was noted between rural lung cancer and non-lung cancer cases. Analytical electron microscopic studies identified various kinds of mineral fibers with an aspect ratio greater than 3:1 in the lung tissue including chrysotile, actinolite/tremolite, amosite/crocidolite, fibrous talc, mica, silica, iron, wollastonite, chlorite, kaoline, and others. The most frequently detected fibers were thin, short chrysotile fibers, most of which could not be found by PCM, followed by relatively thick, long actinolite/tremolite fibers, fibrous talc, and in a smaller number, amosite/crocidolite of intermediate length and width. Amosite/crocidolite and fibrous talc counts in urban lung cancer cases were greater than those of urban non-lung cancer cases, rural lung cancer, and rural non-lung cancer cases; these findings were consistent with PCM analysis. Therefore, it is suggested that fibers detected in PCM observation may be mainly amosite/crocidolite with some parts fibrous talc and that fibrous talc in urban environments may be another candidate for carcinogenic or cocarcinogenic factors of female lung cancer.

Topics: Adult; Aged; Asbestos, Amosite; Asbestos, Crocidolite; Asbestosis; Carcinogens; Case-Control Studies; Female; Humans; Japan; Lung Neoplasms; Microscopy, Electron, Scanning Transmission; Microscopy, Phase-Contrast; Middle Aged; Rural Health; Talc; Urban Health

Standard asbestos samples to be used for biomedical research were first prepared by the International Union Against Cancer (UICC) in 1966 in the United Kingdom and South Africa. Using modern techniques, X-ray diffractometry, analytical transmission electron microscopy, and thermal analysis, we have now analyzed these UICC samples to determine the mineral compositions (mineral phases) and their respective quantities. UICC chrysotile A (from Zimbabwe) contains 2% fibrous anthophyllite as impurity; chrysotile B (from Canada) does not contain any fibrous impurities, only non-fibrous minerals. UICC amosite and crocidolite are almost pure. UICC anthophyllite has 20-30% talc as impurity. The chemical compositions and fiber size distributions of the UICC asbestos samples have also been determined. The mean widths of the fibers of chrysotile A and B are smaller than those of the amphibole fibers. This agrees well with the earlier results which showed the two chrysotile samples to have a larger respirable fraction than the amphiboles.

Topics: Asbestos, Amosite; Asbestos, Amphibole; Asbestos, Crocidolite; Asbestos, Serpentine; Canada; Carcinogens; Differential Thermal Analysis; Humans; Lung Neoplasms; Mesothelioma; Microscopy, Electron; Mineral Fibers; Occupational Diseases; Reference Standards; X-Ray Diffraction; Zimbabwe

Data from inhalation studies in which AF/HAN rats were exposed to nine different types of asbestos dusts (in 13 separate experiments) are employed in a statistical analysis to determine if a measure of asbestos exposure (expressed as concentrations of structures with defined sizes, shapes and mineralogy) can be identified that satisfactorily predicts the observed lung tumor or mesothelioma incidence in the experiments. Due to limitations in the characterization of asbestos structures in the original studies, new exposure measures were developed from samples of the original dusts that were re-generated and analyzed by transmission electron microscopy using a direct transfer technique. This analysis provided detailed information on the mineralogy (i.e., chrysotile, amosite, crocidolite or tremolite), type (i.e., fiber, bundle, cluster, or matrix), size (length and width) and complexity (i.e., number of identifiable components of a cluster or matrix) of each individual structure. No univariate measure of exposure was found to provide an adequate description of the lung tumor responses observed among the inhalation studies, although the measure most highly correlated with tumor incidence is the concentration of structures > or = 20 microns in length. Multivariate measures of exposure were identified that do adequately describe the lung tumor responses. Structures contributing to lung tumor risk appear to be long (> or = 5 microns) thin (0.4 microns) fibers and bundles, with a possible contribution by long and very thick (> or = 5 microns) complex clusters and matrices. Potency appears to increase with increasing length, with structures longer than 40 microns being about 500 times more potent than structures between 5 and 40 microns in length. Structures < 5 microns in length do not appear to make any contribution to lung tumor risk. This analysis did not find a difference in the potency of chrysotile and amphibole toward the induction of lung tumors. However, mineralogy appears to be important in the induction of mesothelioma with chrysotile being less potent than amphibole.

Topics: Administration, Inhalation; Animals; Asbestos; Asbestos, Amosite; Asbestos, Crocidolite; Asbestos, Serpentine; Dust; Environmental Exposure; Incidence; Information Systems; Likelihood Functions; Lung Neoplasms; Male; Mesothelioma; Microscopy, Electron; Multivariate Analysis; Rats; Rats, Inbred Strains; Risk Factors; Surface Properties

Twenty cases of mesothelioma among miners of the township of Asbestos, Quebec, Canada, have been reported. To further explore the mineral characteristics of various fibrous material, we studied the fibrous inorganic content of postmortem lung tissues of 12 of 20 available cases. In each case, we measured concentrations of chrysotile, amosite, crocidolite, tremolite, talc-anthophyllite, and other fibrous minerals. The average diameter, length, and length-to-diameter ratio of each type of fiber were also calculated. For total fibers > 5 microns, we found > 1,000 asbestos fibers per mg tissue (f/mg) in all cases; tremolite was above 1,000 f/mg in 8 cases, chrysotile in 6 cases, crocidolite in 4 cases, and talc anthophyllite in 5 cases. Among cases with asbestos fibers, the tremolite count was highest in 7 cases, chrysotile in 3 cases, and crocidolite in 2 cases. The geometric mean concentrations of fibers > or = 5 microns were in the following decreasing order: tremolite > crocidolite > chrysotile > other fibers > talc-anthophyllite > amosite. For total fibers < 5 microns, we found > 1,000 fibers per mg tissue (f/mg) in all cases; tremolite was above 1,000 f/mg in 12 cases, chrysotile in 8 cases, crocidolite in 7 cases, and talc-anthophyllite in 6 cases. Tremolite was highest in 8 cases, chrysotile in 2 cases, and crocidolite and amosite in 2 cases. The geometric mean concentrations of fibers < 5 microns were in the following decreasing order: tremolite > other fibers > chrysotile > crocidolite > talc-anthophyllite > amosite. We conclude, on the basis of the lung burden analyses of 12 mesothelioma cases from the Asbestos township of Quebec, that the imported amphibole (crocidolite and amosite) were the dominant fibers retained in the lung tissue in 2/12 cases. In 10/12 cases, fibers from the mine site (chrysotile and tremolite) were found at highest counts; tremolite was clearly the highest in 6, chrysotile in 2, and 2 cases had about the same counts for tremolite and chrysotile. If a relation of fiber burden-causality of mesothelioma is accepted, mesothelioma would be likely caused by amphibole contamination of the plant in 2/12 cases and by the mineral fibers (tremolite and chrysotile) from the mine site in the 10 other cases.

Topics: Aged; Asbestos; Asbestos, Amosite; Asbestos, Amphibole; Asbestos, Crocidolite; Asbestos, Serpentine; Culture Techniques; Humans; Lung Neoplasms; Male; Mesothelioma; Middle Aged; Mining; Occupational Diseases; Quebec; Textile Industry

This study investigates reactive oxygen species generation and oxidant-related cytotoxicity induced by amosite asbestos fibers and polymorphonuclear leucocytes (PMNs) in human mesothelial cells and human bronchial epithelial cells in vitro. Transformed human pleural mesothelial cells (MET 5A) and bronchial epithelial cells (BEAS 2B) were treated with amosite (2 micrograms/cm2) for 48 h. After 24 h of incubation, the cells were exposed for 1 h to nonactivated or amosite (50 micrograms) activated PMNs, washed, and incubated for another 23 h. Reactive oxygen species generation by the PMNs and the target cells was measured by chemiluminescence. Cell injury was assessed by cellular adenine nucleotide depletion, extracellular release of nucleotides, and lactate dehydrogenase (LDH). Amosite-activated (but also to a lesser degree nonactivated) PMNs released substantial amounts of reactive oxygen metabolites, whereas the chemiluminescence of amosite-exposed mesothelial cells and epithelial cells did not differ from the background. Amosite treatment (48 h) of the target cells did not change intracellular adenine nucleotides (ATP, ADP, AMP) or nucleotide catabolite products (xanthine, hypoxanthine, and uric acid). When the target cells were exposed to nonactivated PMNs, significant adenine nucleotide depletion and nucleotide catabolite accumulation was observed in mesothelial cells only. In separate experiments, when the target cells were exposed to amosite-activated PMNs, the target cell injury was further potentiated compared with the amosite treatment alone or exposure to nonactivated PMNs. In conclusion, this study suggests the importance of inflammatory cell-derived free radicals in the development of amosite-induced mesothelial cell injury.

Topics: Adenine Nucleotides; Antioxidants; Asbestos, Amosite; Bronchi; Cell Death; Cell Line, Transformed; Epithelial Cells; Epithelium; Free Radicals; Humans; Hydrogen Peroxide; Inflammation; L-Lactate Dehydrogenase; Luminescent Measurements; Lung Neoplasms; Mesothelioma; Neutrophils; Pleura; Reactive Oxygen Species

The Cape Boards Plant at Uxbridge produced insulation board containing amosite asbestos between 1947 and 1973 with only small amounts of chrysotile. After 1973 only amosite was used. In this study we examined lung samples from 48 workers who had been employed at the plant and who had come to autopsy. The study investigated the fiber levels against the lung pathology including amount of interstitial fibrosis and numbers of ferruginous bodies. The degree of interstitial fibrosis and number of asbestos bodies were graded and the tissues were analyzed by transmission electron microscopy and energy dispersive X-ray analysis and the fibers counted and typed. The 48 cases included 5 mesotheliomas and 14 lung cancers. The mineral analysis results were dominated by the amosite fiber levels. The amounts of chrysotile were relatively small. There were higher levels in lung cancer cases than mesotheliomas and higher levels in mesothelioma cases than those who had died from nonasbestos related diseases. Analysis of the lung tissues showed a consistent pattern of high amosite levels, which confirms the impression that amosite was the predominant form of asbestos used and also indicates that the factory had been a very dusty one.

Topics: Asbestos, Amosite; Asbestosis; Humans; Lung Diseases; Lung Neoplasms; Mesothelioma; Occupational Diseases; Pulmonary Fibrosis

Experimental inhalation in a number of studies has demonstrated that chrysotile asbestos can cause pulmonary fibrosis and both benign and malignant pulmonary tumours, two lesions which are associated in that the studies reporting high tumour rates also found high levels of asbestosis. One comparison reported that animals with malignant tumours had approximately twice the amount of fibrosis in the lung parenchyma as those of similar age without tumours. Many studies have examined the pathogenicity of asbestos administered by ingestion and most of these included chrysotile asbestos: the results have been universally negative apart from one study with amosite that contained no control animals and is best discarded. Only one inhalation study has reported an examination of the larynxes of animals: this found no pathological changes. In many studies, tumours other than the lung had been listed, but significant numbers of kidney tumours have never been recorded. Injection studies inducing mesothelioma have indicated that fibre geometry is important with long thin fibres (> 8 microns in length and < 0.25 microns in diameter) being the most carcinogenic. This has been difficult to confirm for inhaled fibres although fibres less than 5 microns in length appear to cause neither fibrosis nor pulmonary tumours. Similar results have been found with amosite for fibres up to 10-15 microns although longer fibres do produce these conditions. It is suggested that to produce pulmonary fibrosis and neoplasia fibres may need to be longer than 20 microns. Chrysotile has been shown in many studies to be removed from lung tissue much more rapidly than amphibole fibres.(ABSTRACT TRUNCATED AT 250 WORDS)

Topics: Administration, Inhalation; Animals; Asbestos, Amosite; Asbestos, Amphibole; Asbestos, Serpentine; Asbestosis; Cricetinae; Dust; Injections; Laryngeal Neoplasms; Lung Neoplasms; Mesothelioma; Pleural Neoplasms; Pulmonary Fibrosis; Rats

To clarify co-carcinogenic effects of chrysotile (Chry) and amosite (Amo) asbestos with benzo(a)pyrene (Bap), 0.2 mg UICC (International Union against Cancer) standard reference sample of asbestos and 0.4 mg Bap were applied intratracheally once a week for 6 weeks. Eighteen and 24 months after the last instillation the number of tumors was examined. The Chry + Bap group yielded 37 tumors including 16 carcinomas in 12 animals, and the Amo + Bap group yielded 30 tumors including 11 carcinomas in 12 animals. Tumor-bearing animals were 100% in the Chry + Bap group and 92% in the Amo + Bap group, and carcinoma-bearing animals were 83% and 67%, respectively. The animals injected with Chry, Amo, and Bap alone developed no tumors. The number of tumors and carcinomas and the frequency of the tumor- or carcinoma-bearing animals in Chry + Bap and Amo + Bap were significantly higher than those of the groups injected independently. The number of tumors or the frequency of tumor-bearing animals was higher in Chry + Bap than in Amo + Bap; however, these differences were not significant. These results indicate that both Chry and Amo play an important role in the genesis of bronchogenic carcinoma.

Topics: Adenoma; Animals; Asbestos; Asbestos, Amosite; Asbestos, Serpentine; Benzo(a)pyrene; Carcinogenicity Tests; Carcinoma; Cocarcinogenesis; Cricetinae; Lung Neoplasms; Mesocricetus

We conducted a clinical, environmental, pathologic, and mineral lung burden investigation of a 61-year-old man with malignant mesothelioma. For 35 years, up until three weeks prior to pneumonectomy, the patient made asbestos soldering forms at a costume jewelry production facility. Only chrysotile asbestos was used at the plant during the last decade of the patient's employment, and recent environmental sampling of the work-place identified no other asbestos fiber type. Anticipating that the patient would add to the very small number of cases of mesothelioma attributable solely to chrysotile, we found instead that the patient's lung tissue contained large numbers of both coated and uncoated amosite asbestos fibers but, surprisingly, no chrysotile. We subsequently learned that a distributor of both chrysotile and amosite supplied the company during the first 25 years the patient was fabricating soldering forms. The findings underscore the futility of estimating environmental exposure to chrysotile on the basis of fiber counts in lung tissue. Although we previously described non-neoplastic asbestos-related disease among patients engaged in similar work, this case, to the best of our knowledge, represents the first report of mesothelioma in the commercial jewelry industry. As such, it prompted us to initiate a public health campaign to replace asbestos soldering forms in this industry with readily available, safer alternatives.

Topics: Air Pollutants, Occupational; Asbestos; Asbestos, Amosite; Asbestos, Serpentine; Humans; Lung Neoplasms; Male; Mesothelioma; Middle Aged; Occupational Diseases

Histological observations were performed on female Syrian hamsters 2 years after the intratracheal administration of amphibole asbestos, amosite, and crocidolite to evaluate the tumorigenicity of six types of fine manmade fibers (reported previously). A mesothelioma and a lung tumor were induced in 20 animals administered amosite, but no tumors were found in the crocidolite group. Because this incidence is not higher than that of manmade fibers, such as basic magnesium sulfate fiber [9 tumor-bearing hamsters in 20 hamsters (9/20)], metaphosphate fiber (5/20), calcium sulfate fiber (3/20), and fiberglass (2/20), it is suggested that some types of manmade fibers have a greater ability than asbestos to induce tumors. Moreover, as a specific observation in manmade fiber groups, tumors were induced at intracelial organs rather than at the pleural cavity. On the other hand, the average thickness of visceral pleura was higher in all asbestos and manmade fiber groups than in the control (2.9 microns), for instance, 36.95 microns in potassium titanate fiber group, 15.90 microns crocidolite group, 13.00 microns basic magnesium sulfate fiber group, and 10.45 microns in the rockwool group. Although both pleural thickening and mesothelioma are known as peculiar lesions in asbestos-exposed people, it might also be suggested that these lesions could be induced by different mechanisms from the result that there was no relation between the pleural thickening and mesothelioma incidence in hamsters.

Topics: Adenoma; Animals; Asbestos; Asbestos, Amosite; Asbestos, Amphibole; Asbestos, Crocidolite; Calcium Sulfate; Carbon; Cricetinae; Female; Glass; Lung Neoplasms; Magnesium Sulfate; Mesocricetus; Mesothelioma; Pleura; Pleural Neoplasms; Silicon Dioxide; Titanium

To determine if asbestos exposure could contribute to mesothelial cell carcinogenesis by selection and/or expansion of an initiated cell population, we compared normal human pleural mesothelial cells to either human mesothelioma cell lines or mesothelial cells transfected with cancer-related genes for sensitivity to amosite fibers in vitro. Neither normal nor mesothelioma cells were directly stimulated to replicate or increase DNA synthesis by any of the asbestos exposure conditions tested. The potential selective effect of asbestos exposure was demonstrated by a differential sensitivity of normal mesothelial cells and mesothelioma cells to amosite: for example, up to 20-fold higher concentrations of amosite fibers were required to inhibit replication of mesothelioma cell lines than normal mesothelial cells. In addition, a significant resistance (4-fold) to amosite toxicity was observed for SV40 immortalized mesothelial cell lines that had previously been selected in vitro for resistance to asbestos. SV40 immortalized cells that have become tumorigenic after transfection with either Ha-ras or PDGF A-chain genes were not significantly more resistant to the cytotoxic effects of amosite than primary normal cells, and the primary cells were equally sensitive to amosite as mesothelial cells that were only immortalized by SV40. The sensitivity of normal mesothelial cells to asbestos does not appear to be simply a result of general fragility of the mesothelial cells, since similar levels of hydrogen peroxide and silica were cytotoxic for normal mesothelial cells and mesothelioma cell lines. Because mesothelioma cells have a greater resistance to asbestos cytotoxicity than normal mesothelial cells, we hypothesize that a differential resistance to cell killing by asbestos fibers in vivo may result in a selective expansion of an initiated or transformed cell population and thus contribute to the carcinogenesis process. Since tumorigenicity and asbestos resistance occur independently of one another in genetically altered mesothelial cell lines, genotypic and phenotypic alterations that lead to tumorigenic conversion may not be the same changes that provide resistance to cell killing by asbestos.

Topics: Asbestos; Asbestos, Amosite; Cells, Cultured; Colony-Forming Units Assay; DNA Replication; Dose-Response Relationship, Drug; Epithelium; Humans; Hydrogen Peroxide; Lethal Dose 50; Lung Neoplasms; Mesothelioma; Silicon Dioxide; Tumor Cells, Cultured

A cohort was established in 1981 of all 7317 white male employees in the amosite and crocidolite mines in South Africa whose names had appeared in the personnel records (initiated between 1945 and 1955) of the major companies. Some of the men had been employed as early as 1925, but only 8% had had more than 10 years of service. Three subcohorts were defined: 3212 men whose only exposure to asbestos was to amosite; 3430 exposed to crocidolite; and 675 to both amphiboles. No deaths or losses to view occurred before 1946, and 5925 men (81%) were known to be alive at the end of 1980. Losses to view numbered 167 (2%), and there had been 1225 deaths (17%), an excess of 331 over the number of deaths expected on the basis of the mortality of all white South African males. The fibre related excesses were of mesothelioma, lung cancer, and other respiratory diseases, but there were other excesses perhaps mainly related to socioeconomic factors including lifestyle. When cause of death was determined according to "best evidence" (after study of clinical, radiological, biopsy, and necropsy reports in conjunction with the death certificate), there were 30 deaths due to mesothelioma (22 pleural, six peritoneal, two other) and 65 due to cancer of trachea, bronchus, and lung. Various analyses of these deaths showed that crocidolite had higher toxicity than amosite for lung cancer and this was most pronounced for mesothelioma; there can now be no question that crocidolite is far more dangerous than amosite at least in so far as mesothelioma is concerned. Nevertheless, crocidolite induced mesothelioma appeared only in men who had been exposed for long periods, at least 12 months, but on average about 15 years.

Topics: Asbestos; Asbestos, Amosite; Asbestos, Crocidolite; Cause of Death; Cohort Studies; Humans; Incidence; Lung Neoplasms; Male; Mesothelioma; Mining; Neoplasms; Occupational Diseases; Risk Factors; South Africa; Survival Analysis

The concentration of airborne fibers longer than 5 microns, thinner than 3 microns, and with an aspect ratio exceeding 3 as counted by phase contrast optical microscopy is the most widely used fiber exposure index. Recently, more adequate, specific exposure indices for asbestosis, lung cancer, and mesothelioma risk have been suggested by Lippmann (1988, Environ. Res., 46, 86-106). The consequences of using these indices are examined on the basis of calculations for a broad range of theoretical and published size distributions. Optical microscopy appears to be a good predictor of the exposure indices for asbestosis and for lung cancer after scaling. Only fibers longer than about 3 microns need to be counted in a transmission electron microscope. The lung cancer index still cannot explain the large differences of risk among chrysotile exposures. Both the mesothelioma exposure index and the ratio mesothelioma to lung cancer index ranks in order of increasing risk: wollastonite, glass and mineral wool, amosite, glass microfibers, chrysotile, and crocidolite. Amosite is thus not ranked according to epidemiological evidence. Detailed size information should be made available so that the size criteria can be adjusted. It may still prove necessary to use fiber type specific concentration limits.

Topics: Asbestos; Asbestos, Amosite; Asbestos, Crocidolite; Asbestos, Serpentine; Asbestosis; Environmental Exposure; Environmental Monitoring; Humans; Lung Neoplasms; Mesothelioma; Microscopy, Electron; Microscopy, Phase-Contrast; Minerals; Risk Factors

The lungs from 36 former workers at an East London asbestos factory dying of asbestos-related disease were compared with lung tissue from 56 matched control patients operated on in East London for carcinoma of the lung. The severity of asbestosis and the presence of pulmonary carcinoma or mesothelioma of the pleura or peritoneum were correlated with an asbestos exposure index and with the type and amount of mineral fibre of the lungs. Asbestosis was associated with far heavier fibre burdens than mesothelioma. Moderate or severe asbestosis was more common among those with carcinoma of the lung than in those with mesothelial tumours. Crocidolite and amosite asbestos were strongly associated with asbestosis, carcinoma of the lung and mesothelial tumours, whereas no such correlation was evident with chrysotile or mullite. It is suggested that greater emphasis should be placed on the biological differences between amphibole and serpentine asbestos fibre.

Topics: Aluminum Silicates; Asbestos; Asbestos, Amosite; Asbestos, Crocidolite; Asbestos, Serpentine; Asbestosis; Female; Humans; London; Lung; Lung Diseases; Lung Neoplasms; Male; Mesothelioma; Middle Aged; Occupational Diseases; Pleural Neoplasms

We have previously shown that there are differences in the sizes of fibers of amosite asbestos in different parts of the lung in workers with relatively high asbestos exposure and malignant pleural mesothelioma. To determine whether this distribution pattern is specific to cases of mesothelioma, we compared the fiber distribution in the lungs of 20 cases of mesothelioma and 10 cases of carcinoma of the lung. The two test groups were statistically identical in terms of age, and exposure period, and overall both groups had very similar mean fiber concentrations and mean fiber sizes. When individual sampling sites within the lung were considered, neither group showed preferential fiber concentration in any area. However, there were definite differences in the intrapulmonary fiber size distribution both within and between the two groups: Cases of mesothelioma showed accumulation of lung fibers in the peripheral upper lobe with shorter central upper lobe fibers. The lung cancer cases demonstrated a reverse pattern, with shorter fibers in the peripheral compared to central upper lobe, but accumulations of long fibers in the peripheral lower lobe. Fiber surfaces and masses showed similar differences among sample sites. We conclude that (1) there is no evidence for fiber concentration variations in different portions of the lung; (2) there is strong evidence for variations in fiber sizes in different portions of the lung, and these differences are most clearly related to fiber length, surface area, and mass; (3) contrary to data from experimental animals, there are no clear gravitational effects on fiber distribution in humans; and (4) there are reproducible differences in intrapulmonary fiber size distribution between mesothelioma and lung cancer cases. These differences may be a manifestation of individual handling of mineral particles because of structural variations in individual lungs.

Topics: Aged; Asbestos; Asbestos, Amosite; Carcinoma; Humans; Lung Neoplasms; Mesothelioma; Middle Aged; Smoking; Tissue Distribution

Topics: Asbestos; Asbestos, Amosite; Health Education; Humans; Lung Neoplasms; Male; Occupational Diseases; Smoking; Smoking Prevention; United Kingdom

Animal studies suggest that mesothelioma is most effectively induced by fibers longer than 8 mu. However, studies of asbestos fibers recovered from human lungs in cases of mesothelioma indicate that, at least in large-scale samples, relatively few fibers meet this size criterion, perhaps implying that the animal data do not apply to man. Since asbestos concentration in lung is known to be extremely inhomogeneous, it is also possible that long fibers may selectively accumulate in specific sites, such as under the pleura. To examine this possibility, we selected ten cases of mesothelioma that contained relatively large amounts of amosite asbestos and extracted fibers from an 0.5-cm-thick strip of subpleural tissue and an area 3-cm deep to the subpleural sample for upper and lower lobes. Amosite fibers were identified and sized by electron microscopic techniques. Fibers in the peripheral upper lobe were significantly longer, broader, and of higher aspect ratio than those in the central upper lobe. The lower lobe showed a reverse pattern, with longer fibers and broader fibers in the central sample. These data indicate that the two lobes behave differently in regard to fiber size, with selective accumulation of long fibers in the peripheral upper lobe, but not in the peripheral lower lobe. Whether these differences reflect differences in initial deposition of fibers within the lung, or, more likely, specific redistribution of fibers, is unclear, but in either case, accumulation of long fibers immediately under the upper lobe pleura may be important in the genesis of mesothelioma.

Topics: Asbestos; Asbestos, Amosite; Humans; Lung; Lung Neoplasms; Male; Mesothelioma; Occupational Diseases; Particle Size

For many years it has been accepted that fibre dimensions are the most important factor in the development of asbestos related disease with long fibres being more dangerous than short for all types of asbestos. This information has been derived from in vitro experiments and injection or implantation experiments since the kilogramme quantities of specially prepared dusts that are necessary for long term inhalation have not been available. The present study has taken advantage of the availability of a sample of amosite produced so that almost all fibres were less than 5 micron in length. The effects of this dust were compared to dust prepared from raw amosite that contained a very high proportion of long fibres. Previous data from studies with UICC amosite, which was intermediate in length, were also available for comparison. At the end of 12 months of dust inhalation, significantly more short fibre amosite was present in the lung tissue compared to the long but while the long fibre dust caused the development of widespread pulmonary fibrosis, no fibrosis at all was found in animals treated with short fibre. One third of animals treated with long fibre dust developed pulmonary tumours or mesotheliomas but no pulmonary neoplasms were found in animals treated with short fibre dust. Following intraperitoneal injection, the long fibre amosite produced mesotheliomas in 95% of animals with a mean induction period of approximately 500 days. With short fibre dust, only a single mesothelioma developed after 837 days. In previous inhalation studies with UICC amosite, relatively little pulmonary fibrosis had developed and only two benign pulmonary tumours. This would suggest that to produce a significant carcinogenic response in rat lung tissue amosite fibres must be longer than those in the UICC preparation. Following the injection of UICC amosite, however, mesotheliomas developed in the same proportion of animals and with the same mean induction period as with long fibre dust. From this it would appear that while very short fibres exhibit little carcinogenicity to either lung or mesothelial tissues, mesotheliomas can be produced by dust preparations consisting of shorter fibres than are needed to produce tumours.

Topics: Animals; Asbestos; Asbestos, Amosite; Bronchi; Granulation Tissue; Lung; Lung Neoplasms; Macrophages; Male; Microscopy, Electron; Pulmonary Fibrosis; Rats; Rats, Inbred Strains

A cohort of 820 men in a Paterson, New Jersey, amosite asbestos factory which began work during 1941-1945 was observed from 5 to 40 years after start of work. Most of the cohort had limited duration of work experience (days, weeks, months), though some men worked for several years until the factory closed in 1954. With white males of New Jersey as the control population, Standardized Mortality Ratios (SMRs) of 500 are evident for the cohort for lung cancer and for noninfectious pulmonary diseases (including asbestosis), while being almost 300 for total cancer and about 170 for all causes of death. A statistically significant SMR of almost 200 is seen for colon-rectum cancer. Mesothelioma incidence initially shows a strong relationship with advancing time since onset of exposure and then tails off. The main concern of the study is with dose-response patterns. Response is measured by the mortality for relevant causes of death, while the direct asbestos dosage was measured in two ways. One way was the length of time worked in the factory and the other was the individual's accumulated fiber exposure, calculated by multiplying the aforementioned length of time worked by the estimated fiber exposures associated with the particular job that the worker had in the factory. Whichever measure of dosage is used, it was found that, in general, the lower the dose, the longer it took for adverse mortality to become evident and, also, the smaller the magnitude of that adverse mortality.

Topics: Adult; Asbestos; Asbestos, Amosite; Colonic Neoplasms; Dose-Response Relationship, Drug; Humans; Lung Diseases; Lung Neoplasms; Male; Mesothelioma; Middle Aged; New Jersey; Occupational Diseases; Rectal Neoplasms; Risk; Time Factors

Topics: Adult; Aged; Asbestos; Asbestos, Amosite; Asbestos, Crocidolite; Asbestos, Serpentine; Australia; Humans; Lung; Lung Neoplasms; Male; Mesothelioma; Microscopy, Electron; Middle Aged

Previous reports have indicated that a majority of the population has asbestos bodies within their lungs. These studies generally have been carried out using cohorts from urban environments. The present study compares the asbestos body levels from three unique cohorts: (1) a nonoccupationally exposed group from a large urban environment having a relatively low asbestos content, (2) patients with lung cancer from a nonurban setting, and (3) amosite asbestos workers, who worked and lived in a rural setting. The number of asbestos bodies in both the urban nonoccupationally exposed group and the patients with lung cancer was generally found to be low or below limits of detectability, with the exceptions being those persons in whom an occupational exposure was eventually found. The ferruginous body content of the occupationally exposed group varied considerably between individuals as well as between sites within the same individual.

Topics: Adult; Aged; Asbestos; Asbestos, Amosite; Environmental Exposure; Female; Humans; Infant, Newborn; Lung; Lung Neoplasms; Male; Middle Aged; Occupational Diseases; Occupations; Urban Health

This report describes the second in a series of three parallel cohort studies of asbestos factories in South Carolina, Pennsylvania, and Connecticut to assess the effects of mineral fibre type and industrial process on mortality from malignant mesothelioma, respiratory cancer, and asbestosis. In the present plant (in Pennsylvania) mainly chrysotile, with some amosite and a small amount of crocidolite, were used primarily in textile manufacture. Of a cohort of 4137 men comprising all those employed 1938-59 for at least a month, 97% were traced. By the end of 1974, 1400 (35%) had died, 74 from asbestosis and 70 from lung cancer. Mesothelioma was mentioned on the certificate in 14 deaths mostly coded to other causes. All these deaths occurred after 1959, and there were indications that additional cases of mesothelioma may have gone unrecognised, especially before that date. The exposure for each man was estimated in terms of duration and dust concentration in millions of dust particles per cubic foot (mpcf) from available measurements. Analyses were made both by life table and case referent methods. The standardised mortality ratio for respiratory cancer for the whole cohort was 105.0, but the risk rose linearly from 66.9 for men with less than 10 mpcf.y to 416.1 for those with 80 mpcf.y or more. Lines fitted to relative risks derived from SMRs in this and the textile plant studied in South Carolina were almost identical in slope. This was confirmed by case referent analysis. These findings support the conclusion from the South Carolina study that the risk of lung cancer in textile processing is very much greater than in chrysotile production and probably than in the friction products industry. The much greater risk of mesothelioma from exposure to processes in which even quite small quantities of amphiboles were used was also confirmed.

Topics: Adult; Aged; Asbestos; Asbestos, Amosite; Asbestos, Crocidolite; Asbestos, Serpentine; Asbestosis; Dust; Humans; Lung Neoplasms; Male; Mesothelioma; Middle Aged; Occupational Diseases; Textile Industry

The predominant asbestos fibre type used in the production of asbestos cement is chrysotile. The use of asbestos in relation to fibre type in a Norwegian asbestos cement plant during 1942-80 was 91.7% chrysotile, 3.1% amosite, 4.1% crocidolite, and 1.1% anthophyllite respectively. Electron microscopy and x ray microanalysis of lung tissue samples of asbestos cement workers who had died of malignant pleural mesothelioma or bronchogenic carcinoma showed a completely inverse ratio with regard to fibre type. The percentage of chrysotile asbestos in lung tissue varied between 0% and 9% whereas the corresponding numbers for the amphiboles were 76% and 99%. These differences are discussed with respect to the behaviour of different fibre types in the human body and to the occurrence of malignant mesothelioma in this asbestos cement factory.

Topics: Aged; Asbestos; Asbestos, Amosite; Asbestos, Amphibole; Asbestos, Crocidolite; Asbestos, Serpentine; Carcinoma, Bronchogenic; Humans; Lung; Lung Neoplasms; Mesothelioma; Middle Aged; Occupational Diseases; Pleural Neoplasms; Silicon Dioxide

Oncogenesis and in vitro data (reported elsewhere in detail) are compared on the basis of relative activity by mass and by dimensional fiber parameters. When tumor induction is compared to the number of fibers of various lengths and aspect ratios in the dose in rats to the degree of tumor induction, a degree of difference with the long thin fiber concept of tumorigenesis by mineral fibers is noted. Consistency is re-established, however, when cognizance is taken of the change in the length and aspect ratio that took place during residence in the lung. This change resulted in a severalfold excess for ferroactinolite of all fiber lengths with high aspect ratios, produced as a result of longitudinal splitting of the introduced fibers. The response by mass in the in vitro procedures did not mimic oncogenesis. When mass was so adjusted that there were an equal number of mineral fibers, aspect ratio greater than 3, for dose for the two minerals, agreement was closer in both the rabbit alveolar macrophage toxicity test and the clonal cytotoxicity assay in Chinese hamster ovary cells. When activity was related to the number of mineral fibers, the same aspect ratio computed to have been contained in the mass dose, agreement with the relative induction of lung tumors was closer. In all cases, erythrocyte lysis was more active in reflecting the number of mineral fibers.

Topics: Animals; Asbestos; Asbestos, Amosite; Asbestos, Amphibole; Lung; Lung Neoplasms; Minerals; Pleura; Pleural Neoplasms; Rats; Rats, Inbred F344