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Query: UMLS:C0242379 (lung cancer)
 71,905 document(s) hit in 31,850,051 MEDLINE articles (0.00 seconds)

Three parallel cohort studies of asbestos factory workers were undertaken to investigate the effects of mineral fibre type and industrial process on malignant mesothelioma, respiratory cancer, and asbestosis. This report describes the mortality of a cohort of 2543 men, defined as all those employed for at least a month from 1938 to 1958 in a textile plant in South Carolina in which chrysotile was the only type of asbestos used. Of these, 863 men (34%) had died before 31 December 1977, one from malignant mesothelioma. Twenty one deaths were ascribed to asbestosis and 66 to cancer of the lung. Compared with the number expected from South Carolina, there was an excess of 30 deaths from respiratory cancer (ICD 160-164) in men 20 or more years after first employment (SMR 199.5). In men employed five years or more, no SMRs for this category rose above 300. Individual exposures were estimated (in mpcf X years) from recorded environmental measurements. Life table analyses and "log-rank" (case-control) analyses both showed a steep linear exposure-response that was some 50-fold greater at similar accumulated dust exposures than in Canadian chrysotile mining and milling. These findings agree closely with those from another study in this plant and confirm that mesothelioma is rarely associated with chrysotile exposure. Cigarette smoking habits did not greatly differ between the textile workers and the Canadian miners and millers. The far greater risk of lung cancer in the textile industry, if not attributable to other identified cocarcinogens, may be related to major differences in the size distribution of fibres in the submicroscopic range which are not detected by the usual fibre or particle counting procedures.
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PMID:Dust exposure and mortality in an American chrysotile textile plant. 631 32

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.
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PMID:Dust exposure and mortality in an American factory using chrysotile, amosite, and crocidolite in mainly textile manufacture. 631 33

Cohort studies in three American asbestos factories were undertaken to investigate the effect of fibre type and manufacturing process on lung cancer, mesothelioma, and asbestosis. Reports have been published on a chrysotile textile plant in South Carolina and a mainly textile plant in Pennsylvania, which also used amphiboles. In the third plant in Connecticut friction products and packings were made from chrysotile only. In a cohort of 3641 men employed for one month or more, 1938-58, 3513 (96.5%) were traced, 1267 (36%) had died, and death certificates were obtained for 1228 (96.9%). Individual exposures were estimated (in mcpf . years) from impinger measurements. Life table analyses using Connecticut mortality rates gave an SMR for all causes of 108.5 (USA 107.9). The SMR (all causes) for men who had worked for less than a year was 129.9 and for those who had worked for a year or more, 101.2. The equivalent SMRs for respiratory cancer were 167.4 and 136.7 respectively. Excluding men who had worked for less than a year, there was possible evidence of some increase in risk of lung cancer with increasing exposure, supported also by a "log-rank" (case-control) analysis, of the same order as that observed in chrysotile mining and milling. These findings may be compared with chrysotile textile manufacture where the risk of lung cancer was some 50-fold greater. It is suggested that the differences in risk are perhaps related to the higher proportion of submicroscopic fibres in textile manufacture that may result from the traumatic carding , spinning, and weaving processes. No case of mesothelioma was found, consistent with a much lower risk of this tumour with chrysotile than with amphiboles. Twelve deaths (nine in men with very short and low asbestos exposure) were given ICD code 523 (pneumoconiosis); all but two were ascribed to anthracosilicosis or silicosis and none to asbestosis.
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PMID:Dust exposure and mortality in an American chrysotile asbestos friction products plant. 632 94

In Israel, since the 1950s, at least several thousand workers, their wives and children, and possibly many others, have been or still may be exposed to hazardous amounts of airborne asbestos fibers. These are found both in asbestos-based industries (asbestos cement, textiles and brake linings) and trades with asbestos exposure (construction, shipyard repair, boiler maintenance, insulation work). These people are at increased risk for disability or illness, or for premature death from asbestosis, from lung cancer, from exacerbation of preexisting respiratory disease (especially if they smoke), from mesothelioma, from gastrointestinal cancer, and from other malignancies. Although there has been progress, much still has to be done in the areas of legislation, standard setting, exposure control, technology, surveillance, smoking cessation, and medical care and follow-up. Compensation is needed to care for those workers currently or previously exposed, as well as for their families and others at risk. A national policy for protecting and caring for those formerly or currently exposed is indicated by the review of the situation in Israel.
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PMID:Asbestos exposure in Israel: findings, issues and needs. 636 66

The Port Allegany Asbestos Health Program (PAAHP) is a unique, community-run program that resulted from the successful cooperative efforts of a labor union, a corporation, community health care providers, and a medical school. PAAHP's goal is to develop a permanent community health organization that will use the most advanced existing knowledge to mitigate the adverse health effects anticipated as a result of the use of amosite asbestos in a Port Allegany, Pa. factory. All 1,188 persons employed by the factory during the years 1964-72 and the 3,000-4,000 persons in household contact with them are eligible for the program. PAAHP's major services are intensive medical surveillance, smoking cessation assistance, health education for participants, and continuing education for area physicians about asbestos-related diseases. One of the program's policies is not to disturb the usual patterns of medical care. If further testing or treatment is needed, patients are referred to their usual personal physicians. PAAHP does not provide ordinary medical care or medical insurance. Across the nation, the number of workers estimated to have been exposed to asbestos is more than 20 million, and their household contacts are estimated to be about three to four times that number. Adverse health effects resulting from asbestos exposure include elevated risk of lung cancer, mesothelioma, gastrointestinal tumors, and asbestosis. The problem requires the development of public health solutions. PAAHP has demonstrated the feasibility of a community-based model as one useful approach.
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PMID:Port Allegany Asbestos Health Program: a community response to a public health problem. 642 68

Men who were first awarded compensation for asbestosis by the Cardiff, London or Swansea Pneumoconiosis Medical Panels in the period 1952 to 1976 have been followed up. Out of a total of 665 men, 283 have died: 36% of the deaths were due to lung cancer, 9% to mesothelioma and 20% to asbestosis. Compared with the death rates for England and Wales, the rate for all deaths was 2.6 times that expected and that for lung cancer 8.5 times that expected. Mortality was related to the rate of compensation awarded but was still high for all of the above three causes for those awarded the lowest rates. The excess death rates were apparent in the first year after certification and were still operating after 10 years in those who survived until then.
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PMID:The prognosis following certification with asbestosis in the United Kingdom. 645 84

Mortality among 172 workers who received workmen's compensation for asbestosis in Ontario was investigated and the causes of death were compared with those for the general male population in that province. The workers were found to have increased rates of death, relative to the general populations, for nonmalignant respiratory diseases, lung cancer and pleural and peritoneal mesothelioma. In comparison with the general population, the proportion of workers that survived was 69% of that expected 5 years after they were awarded compensation and 53% at 10 years.
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PMID:Mortality among workers receiving compensation for asbestosis in Ontario. 645 56

This article presents an evaluation model of the mortality attributed to asbestos occupational exposure. French workers exposed at least ten years between 1950 and 1979 constitute the population studied. Exposure-risk relations are used to estimate mortality from lung cancer, mesothelioma, or asbestosis, and the associated reduction of life expectancy among 76 groups (about 18,500 workers) defined by their level of asbestos exposure. The most important results are presented and discussed as are the main hypotheses regarding historical exposure parameters.
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PMID:[Model for evaluation of occupational mortality related to asbestos (the case of the asbestos industry in France between 1950 and 1980)]. 648 59

The current standard for occupational exposure to asbestos is 2 fibers/cm3 averaged over an 8-hr day. A NIOSH/OSHA committee has recently concluded that the 2 fiber/cm3 standard is grossly inadequate to protect workers from asbestos-related disease, and that all levels of asbestos exposure studied thus far have demonstrated asbestos-related disease. The committee recommends that a 0.1 fiber/cm3 limit replace the current 2 fiber/cm3 standard on the grounds that this is the lowest level detectable with currently available analytical techniques. Thus a 0.1 fiber/cm3 limit is not based on epidemiological data but on the presumption that any level of exposure is disease producing. This paper addresses the question of whether it would be possible to detect health effects of exposure below the current 2 fiber/cm3 standard. Five studies are reviewed which provide evidence on the strength of the relationship between asbestos fiber exposure and lung cancer. Calculation of sample sizes needed to be 95% certain of detecting the kind of excess probably associated with exposure to 2 fibers/cm3 suggests that epidemiology is not likely to be useful in detecting lung cancer below the current standard. Some outcome measures other than lung cancer or clinical asbestosis will be needed if observations on humans are to be used as evidence for a lowering of the present standard.
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PMID:Epidemiologic basis for the asbestos standard. 665 42

The paper describes the mortality experience of 5969 men employed in a factory where insulation board was manufactured using amosite asbestos from 1947 to 1979. 422 (7%) of the men were known to have died by the end of 1980. Among the 4820 men engaged in the manufacture of insulation board a doubling of the risk of lung cancer has occurred (57 deaths observed; 29 deaths expected). An excess is present both in men who entered the factory before and after 1960. Among the 2461 for whom smoking information is available a detectable excess risk is limited to current smokers exposed to higher levels of asbestos. Apart from five deaths from mesothelioma no statistically large or significant excesses of mortality from cancers of other sites have occurred, but further follow-up of the cohort is in progress. Nine deaths from asbestosis have been recorded. The results are discussed in the light of other studies of the effects of exposure to amosite asbestos.
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PMID:Cancer in a factory using amosite asbestos. 669 1


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