asbestos--crocidolite and Neoplasms

There are few data on the long-term health outcomes of exposure to asbestos in childhood. This study investigated cancer and mortality of adults exposed to blue asbestos as children.. Data linkage to relevant health registries was used to identify cancers and mortality in a cohort of adults (n = 2,460) that had lived in an asbestos mining town during their childhood (<15 years).. There were 217 (93 female) incident cancers and 218 (70 female) deaths among the cohort. Compared with the Western Australian population females had elevated mesothelioma, ovarian and brain cancers, and increased "all cause" and "all cancer" mortality. Males had elevated mesothelioma, leukemia, prostate, brain, and colorectal cancers, and excess mortality from "all causes," "all cancers," circulatory disease, diseases of the nervous system, and accidents.. Exposure to blue asbestos in childhood is associated with an increased risk of cancer and mortality in adults.

Topics: Adolescent; Adult; Aged; Air Pollutants; Asbestos, Crocidolite; Child; Child, Preschool; Environmental Exposure; Environmental Monitoring; Female; Follow-Up Studies; Humans; Incidence; Infant; Infant, Newborn; Male; Middle Aged; Mining; Mortality; Neoplasms; Registries; Western Australia; Young Adult

Knowledge of mortality patterns following exposure to asbestos has been determined mostly from cohort studies of men who were exposed to asbestos in their workplace. Women are more likely to have obtained their asbestos exposure domestically or from their environment.. 2552 women and girls are documented to have lived in the blue asbestos mining and milling township of Wittenoom between 1943 and 1992 and were not involved in asbestos mining or milling. Quantitative asbestos exposure measurements were derived from periodic dust surveys undertaken in the industry and around the township. Death records were obtained for the period 1950-2004. Standardised mortality ratios (SMRs) were calculated to compare the Wittenoom women's mortality with that of the Western Australian female population.. There were 425 deaths, including 30 from malignant mesothelioma. There was excess mortality for all causes of death (SMR = 1.13), all neoplasms (SMR = 1.42), symptoms, signs and ill defined conditions (SMR = 6.35), lung cancer (SMR = 2.15) and pneumoconiosis (SMR = 11.8). Mortality from cancer of the ovary (SMR = 1.52), upper aerodigestive cancers (SMR = 2.70) and tuberculosis (SMR = 5.38) was increased but not significantly. The risk of death from mesothelioma was increased, but not significantly, in residents known to have lived with or washed the clothes of an Australian Blue Asbestos Company asbestos worker (HR = 2.67, 95% CI 0.77 to 9.21; HR = 2.61, 95% CI 0.85 to 7.99, respectively).. Women who were former residents of Wittenoom, exposed to asbestos in their environment or in their home, have excess cancer mortality, including mesothelioma, compared with the Western Australian female population.

Topics: Adolescent; Adult; Air Pollution, Indoor; Asbestos, Crocidolite; Child; Child, Preschool; Environmental Exposure; Environmental Monitoring; Epidemiologic Methods; Epidemiological Monitoring; Female; Housing; Humans; Mesothelioma; Middle Aged; Mining; Neoplasms; Western Australia

To evaluate the effects of environmental low-dose exposure to crocidolite on people's health and the society. METHODS The mortality data of cancer between 1994 and 2003 in an environmental crocidolite-contaminated area was obtained from hospital medical records of Dayao Center for Disease Prevention and Control, and Dayao Public Health Bureau. The years of life lost with premature death (YLLs), was used to measure and assess the death, health losses and social burden of cancer in this area.. In the environmental crocidolite-contaminated area, lung cancer was the prime cause of death in all kinds of cancers between 1994 and 2003, followed by liver cancer, mesothelioma stomach cancer and colorectal cancer, with mortality 10.15/10(5), 9.04/10(5), 8.48/10(5), 3.96/10(5) and 3.55/10(5) respectively. The mortality of main cancer in male and female increased with age growing except that of breast cancer in female. Results showed that the types of leading cancers of YLLs were liver cancer, lung cancer, mesothelioma, leukemia and stomach cancer with YLLs 1981.39 person-year, 1886.63 person-year, 1799.23 person-year, 948.01 person-year and 754.18 person-year respectively. The distribution of YLLs was similar in both sexes, higher in the middle age group (aged from 15 to 44 years and 45 to 59 years) and lower in other age groups. The indirect economic loss resulting from lung cancer (15.02% of the total loss), liver cancer (13.98% of the total loss) and mesothelioma (13.01% of the total loss) was relatively great. The YLLs and the indirect economic loss attributable to environmental low-dose exposure to crocidolite were 3092.23 person-year and 5,175,800 Yuan respectively.. Lung cancer, liver cancer, mesothelioma, leukemia and breast cancer are the major cancers with an important impact on people's health and premature mortality in the environmental crocidolite-contaminated area. The impact of cancer mortality is more severer in those aged over 45 years. Social burden of cancer is the greatest in persons aged from 15 to 59 years. Policies and plans should be worked out for the protection of environment and the prevention of cancer.

Topics: Adolescent; Adult; Aged; Aged, 80 and over; Asbestos, Crocidolite; Child; Child, Preschool; China; Cost of Illness; Environmental Exposure; Environmental Pollution; Female; Humans; Infant; Life Expectancy; Male; Middle Aged; Neoplasms; Young Adult

Between 1940 and 1944 military gas masks with filter pads containing 20% crocidolite were assembled in a Nottingham factory.. Records supplied by the late Professor Stephen Jones were of 1154 persons, mainly women, who had worked in the factory during this period; they included many deaths from mesothelioma. A systematic effort was therefore made to establish causes of death for the whole cohort.. Of 640 employees with full name and sex recorded, 567 (89%) were traced. Of these, 491 had died, including 65 from mesothelioma, though only 54 were certified as such. After exclusion of these 54, standardised mortality ratios were significantly raised for respiratory cancer (SMR 2.5) and carcinomatosis (SMR 3.2). The pattern of mortality in the remaining 514 employees without full identification was similar, but a low tracing rate (40%) did not justify their further analysis. The first death from mesothelioma was in 1963 (22 years after first exposure) and the last in 1994, whereas a further 5.0 cases would have been expected between 1996 and 2003 (p = 0.0065).. These findings in a cohort followed over 60 years after brief exposure to crocidolite confirm a high and specific risk of mesothelioma (28% peritoneal) and perhaps of lung cancer some 20-50 years later. The statistically significant absence of further mesothelioma cases during the past eight years suggests that crocidolite, though durable, is slowly removed.

Topics: Asbestos, Crocidolite; Cause of Death; Cohort Studies; England; Female; Humans; Male; Mesothelioma; Neoplasms; Occupational Diseases; Occupational Exposure; Respiratory Protective Devices

The incidence of cancer among employees of a Norwegian asbestos-cement factory was studied in relation to duration of exposure and time since first exposure. The factory was active in 1942-1968. Most of the asbestos in use was chrysotile, but for technical reasons 8% amphiboles was added.. For the identification of cancer cases, a cohort of 541 male workers was linked to the Cancer Registry of Norway. The analysis was based on the comparison between the observed and expected number of cancer cases. Standardized incidence ratios (SIR) and 95% confidence intervals (95% CI) were estimated. Period of first employment, duration of employment, and time since first employment were used as indicators of exposure. Poisson regression analysis was used for the internal comparisons.. The standardized incidence ratio was 52.5 (95% CI 31.1-83.0) for pleural mesothelioma, on the basis of 18 cases. The highest standardized incidence ratio was found for workers first employed in the earliest production period (SIR 99.0, 95% CI 51.3-173). No peritoneal mesothelioma was found. The standardized incidence ratio for lung cancer was 3.1 (95% CI 2.14.3), but no dose-response effect was observed. The ratio of mesothelioma to lung cancer cases was 1:2.. This study showed a high incidence of mesothelioma and a high ratio of mesothelioma to lung cancer among asbestos-cement workers. The high incidence of mesothelioma was probably due to the fact that a relatively high proportion of amphiboles was used in the production process.

Topics: Aged; Asbestos; Asbestos, Amphibole; Asbestos, Crocidolite; Asbestos, Serpentine; Cohort Studies; Follow-Up Studies; Humans; Incidence; Industry; Lung Neoplasms; Male; Mesothelioma; Middle Aged; Neoplasms; Norway; Occupational Exposure; Poisson Distribution; Registries; Risk Factors; Time

To investigate effects of asbestos on the process of cancer development, the capacity of asbestos which increases cellular uptake of external carcinogens was tested for asbestos-mediated viral RNA transfection in cultured cells. For the transfection, crocidolite, amosite, anthophyllite and chrysotile were placed onto Vero-E6 cells with poliovirus RNA inoculum, respectively. All asbestos samples mediated viral RNA transfection compared with the background including only viral RNA. The transfection was much greater with combined exposure to asbestos and kaolin than with exposure to asbestos alone.

Topics: Animals; Asbestos; Asbestos, Amosite; Asbestos, Amphibole; Asbestos, Crocidolite; Asbestos, Serpentine; Asbestosis; Chlorocebus aethiops; Kaolin; Neoplasms; Poliovirus; RNA, Viral; Transfection; Vero Cells

A cohort study was carried out in order to evaluate the cancer risk in the asbestos-cement industry workers. The cohort consisted of workers employed in four asbestos-cement plants. One of those plants was established in 1924, the other three in the 1960s and 1970s. Currently only two of these plants continue their production. The plants used mainly chrysotile asbestos as well as crocidolite and amosite. Amphibolite asbestos was used before the mid-nineteen eighties in production of pressure pipes utilising about 15% of the total quantity of asbestos used. The measurements of the asbestos fibre concentration at work-sites have been taken occasionally since the mid 1980s, thus, the determination of a cumulative dose for individual persons in the cohort and the evaluation of the dose-effect relationship were not feasible. It could only be supposed that the concentrations at the preparatory work-site during first years of the plants' operation accounted for several tens fibres/cm3 in the production that employed the dry method. The cohort consisted of workers employed in the plant for at least three months between beginning of the plant during the post-war period, and 1980, that is during the period when amphibolite asbestos was in use. The retrospective observation was completed on 31 December 1991. The analysis of the death risk by causes was based on a standardized mortality ratios (SMRs) calculated using the person-years method. Statistical significance of SMRs was assessed by means of Poisson distribution one-sided test. The general population of Poland was used as the reference population to estimate the death risk. The cohort comprised 4,712 persons (3,563 males and 1,149 females). Of this number 4,500 persons (3,405 males and 1,095 females) were followed. The cohort availability were 95.5%. Male mortality, both total (473 deaths; SMR = 83) and due to malignant neoplasms (108 deaths; SMR = 86) was lower than in the general population. An excess of deaths from neoplasm of the pleura was by about 23 times higher (5 deaths; SMR = 2,288) and from neoplasm of the large intestine by two times higher (7 deaths; SMR = 214). Among females (41 deaths; SMR = 50) death risk was lower than in the reference population. At a low level of total mortality from neoplasms (13 deaths; SMR = 52) a statistically significant excess of deaths from neoplasm of the pleura (2 deaths; SMR = 2,112) was observed. In the plants investigated the analysis revealed a considerably dive

Topics: Aged; Asbestos; Asbestos, Amosite; Asbestos, Crocidolite; Cohort Studies; Environmental Monitoring; Epidemiological Monitoring; Female; Humans; Incidence; Male; Mesothelioma; Middle Aged; Neoplasms; Occupational Diseases; Pleural Neoplasms; Poland; Risk Assessment; Sex Distribution; Survival Rate

Plain chest radiographs from a one in six random sample of the workforce of the asbestos industry at Wittenoom, Western Australia between 1943 and 1966 have been classified for degree of profusion and pleural thickening by two independent observers according to the 1980 UICC-ILO Classification of Radiographs for the pneumoconioses to clarify the effect of degree of radiological abnormality on survival. A total of 1106 subjects were selected. Each subject's age, cumulative exposure to crocidolite, and time since first exposure were determined from employment records, the results of a survey of airborne concentrations of fibres > 5 mu in length conducted in 1966, and an exposure rating by an industrial hygienist and an ex-manager of the mine and mill at Wittenoom. By the end of 1986 193 subjects had died. Conditional logistic regression was used to model the relative risk of death in five separate case-control analyses in which the outcomes were deaths from: (1) all causes, (2) malignant mesothelioma, (3) lung cancer, (4) asbestosis, and (5) other causes excluding cancer and asbestosis. Up to 20 controls per case were randomly chosen from all men of the same age who were not known to have died before the date of death of the index case. After adjustment for exposure and time since first exposure, there were significant and independent effects of radiographic profusion and pleural thickening on all cause mortality. The effect of profusion was largely a result of the effect on mortality from malignant mesothelioma and asbestosis but not lung cancer. The effect of pleural thickening was greatest on mortality from other causes, mainly ischaemic heart disease. This study has shown that degree of radiographic abnormality has an independent effect on mortality from malignant mesothelioma, asbestosis, and all causes even after allowing for the effects of age, degree of exposure, and time since first exposure.

Topics: Asbestos, Crocidolite; Asbestosis; Cause of Death; Cohort Studies; Humans; Male; Mesothelioma; Neoplasms; Occupational Diseases; Occupational Exposure; Pleura; Pleural Diseases; Radiography; Random Allocation; Western Australia

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

Topics: Asbestos; Asbestos, Crocidolite; Humans; Neoplasms; Occupational Diseases

Topics: Air Pollutants; Air Pollutants, Occupational; Asbestos; Asbestos, Amosite; Asbestos, Amphibole; Asbestos, Crocidolite; Asbestos, Serpentine; Asbestosis; Humans; Neoplasms; Risk

The mortality of a complete cohort of 1506 French asbestos cement workers employed for at least five years is related to the time elapsed since first exposure. The mortality from all causes (analysed by the "man-years method") has been found to be above normal only in those subjects employed for more than 20 years, with more than 35 years of follow up. Standardised mortality ratios for cancers of all sites (ICD 140-209) and pulmonary cancer (ICD 162-163.0) have been assessed in subjects whose first exposure dates go back more than 20 years. Mortalities from cancer of all sites and from pulmonary cancer have been detected in excess in workers employed for more than 20 years and originally hired when aged 25 or under.

Topics: Adolescent; Adult; Aged; Asbestos; Asbestos, Crocidolite; Asbestos, Serpentine; Calcium Hydroxide; Chemical Industry; Child; France; Humans; Lung Neoplasms; Male; Mesothelioma; Middle Aged; Neoplasms; Occupational Diseases; Risk; Time Factors

Topics: Animals; Asbestos; Asbestos, Amosite; Asbestos, Crocidolite; Asbestos, Serpentine; Cell Division; Eating; Intestines; Male; Neoplasms; Rats; Rats, Inbred Strains; Tissue Distribution