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202 Relations Between Asbestos Exposure and Lung Cancer SNnRs in Occupational Cohort Studies. Liddell, F.D.K., Hanley, J.A. Department of Epidemiology and Biostatistics, McGill University, Montreal, Canada. Br. J. Ind. Med. 42: 389-396, 1985. It has long been accepted that exces- sive exposure to asbestos may produce lung cancer but not that there is a con- sistent 'biological gradient'. This can only be evaluated reliably in studies where, for every individual, exposure has been measured in terms of both dura- tion and intensity. Even now, there are only at most eight such cohort studies of asbestos workers, while formal methods of analysis have been available only recently. These methods, applied in these studies, yield good evidence that the 'exposure-response' relation between ac- cumulated exposure to asbestos and stan- dardised mortality ratios (SMRs) for lung cancer may be taken as linear, but that at zero exposure the lung cancer SMR is not always unity - not surprising, because of well known difficulties with the choice of reference population and selection problems. This leads to a concept of 'relative slopes' that take account of the background mortality in the cohort and make what appears to be the best use of the available data. Other approaches to the same data, and indeed to all cohort data known, are also considered. Each study is examined as closely as is possible in a short review, and the concepts of line- arity and relative slopes appear justified. The relative slopes (b/a) in the line SMR = a(1 + (b/a).(exposure)) vary much more widely than can be accounted for by dif- ferences in epidemiological methodology; as discussed elsewhere, reasons for the variation seem to lie rather in type and dimensions of asbestos fiber, industrial process, etc. Slopes in the line SMR = 1 + b I (exposure) vary about twice as much ~s do the relative slopes. Lung Cancer Cell Type and Asbestos Expo- sure. Churg, A. Department of Pathology, Univer- sity of British Columbia, Vancouver, BC V6T IW5, Canada. J. Am. Med. Ass. 253: 2984-2985, 1985. It is often claimed that adenocarcinoma is the most frequent type of lung cancer seen in workers exposed to asbestos. Careful review of the published data, how- ever, fails to support this claim. Rather, it seems that all types of lung cancers occur in asbestos workers, and the pre- sence or absence of a specific cell type cannot be used to prove or disprove an association of carcinoma and asbestos exposure. Lung Cancer Mortality Among Men Living Near an Arsenic-Emitting Smelter. Pershagen, G. National Institute of Environmental Medicine, Karolinska Institute, S-I0401 Stockholm, Sweden. Am. J. Epidemiol. 122: 684-694, 1985. Etiologic factors for lung cancer were studied by the case-control technique among 636 men, in- cluding 212 with pulmonary carcinoma, who had died between 1961 and 1979 in a county in northern Sweden. Data on smoking habits, occupation, and residence were obtained from a next of kin to each study subject. Validation against data from other sources indicated that the exposure information Was of high quality. A relative risk of 2.0 for lung cancer was seen among men who had lived with- in approximately 20 km from a large copper smelter. The increased risk, which is statistically signi- ficant (p < 0.05), could not be explained by smo- king habits or occupationsl backgrounds. Smelter workers and miners had relative risks for lung cancer of 3.0 and 4.1, respectively. No firm con- clusions can be drawn on the cause of excess lung cancer risk in the smelter area, but it seems plausible that the very substantial emissions to air from the smelter, especially of arsenic, may have played a role. Underground Mining, Smoking, and Lung Cancer: A Case-Control Study in the Iron Ore ~micipalities in Northern Sweden. Damber, L., Larsson, L.-G. Centre of Oncology, Uni- versity Hospital, University of Umea, S-901 85 Umea, Sweden. J. Natl. Cancer Inst. 74: 1207-1213, 1985. A case-control study of lung cancer in males was performed in two municipalities in northern Sweden with large iron ore mines. Previous studies had revealed an increased lung cancer risk for underground workers in these mines, with al pro- bability related to radon daughter exposure. Data concerning underground mining and smoking were obtained from questionnaires. All analyses sugge- sted an interaction of a multiplicative type be- tween underground mining and smoking in the causa- tion of lung cancer in this population. The cal- culated population etiologic fraction was about 45% for underground mining and about 80% for smo- king. The Role of Radon-222 in the Formation of Bron- chial Carcinoma. Merkel, K. Forschungszentrum Seibersdorf, A-2444 Seibersdorf, Austria. Atemwegs-Lungenkrankh. ii: 109-110, 1985. In the discussion of the biological effects of ionizing radiation attention paid to radon-222 has increased during the last decades. The nuclide is formed by the decay of radium-226 which is present in small quantities practically everywhere, so also in building materials. Radon is a gaseous, radio- active natural element. From building materials is diffuses out of the walls of buildings; from outer walls it is blown away by the wind, from

Lung cancer cell type and asbestos exposure

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Relations Between Asbestos Exposure and Lung Cancer SNnRs in Occupational Cohort Studies. Liddell, F.D.K., Hanley, J.A. Department of Epidemiology and Biostatistics, McGill University, Montreal, Canada. Br. J. Ind. Med. 42: 389-396, 1985.

It has long been accepted that exces- sive exposure to asbestos may produce lung cancer but not that there is a con- sistent 'biological gradient'. This can

only be evaluated reliably in studies where, for every individual, exposure has been measured in terms of both dura- tion and intensity. Even now, there are only at most eight such cohort studies of asbestos workers, while formal methods of analysis have been available only recently. These methods, applied in these studies, yield good evidence that the 'exposure-response' relation between ac- cumulated exposure to asbestos and stan- dardised mortality ratios (SMRs) for lung

cancer may be taken as linear, but that at zero exposure the lung cancer SMR is not always unity - not surprising, because of well known difficulties with the choice of reference population and selection problems. This leads to a concept of 'relative slopes' that take account of the background mortality in the cohort and make what appears to be the best use of the available data. Other approaches to the same data, and indeed to all cohort data known, are also considered. Each study is examined as closely as is possible in a short review, and the concepts of line- arity and relative slopes appear justified. The relative slopes (b/a) in the line SMR = a(1 + (b/a).(exposure)) vary much more widely than can be accounted for by dif- ferences in epidemiological methodology; as discussed elsewhere, reasons for the variation seem to lie rather in type and dimensions of asbestos fiber, industrial process, etc. Slopes in the line SMR =

1 + b I (exposure) vary about twice as much ~s do the relative slopes.

Lung Cancer Cell Type and Asbestos Expo- sure. Churg, A. Department of Pathology, Univer- sity of British Columbia, Vancouver, BC V6T IW5, Canada. J. Am. Med. Ass. 253: 2984-2985, 1985.

It is often claimed that adenocarcinoma is the most frequent type of lung cancer seen in workers exposed to asbestos. Careful review of the published data, how- ever, fails to support this claim. Rather, it seems that all types of lung cancers occur in asbestos workers, and the pre- sence or absence of a specific cell type cannot be used to prove or disprove an

association of carcinoma and asbestos exposure.

Lung Cancer Mortality Among Men Living Near an Arsenic-Emitting Smelter. Pershagen, G. National Institute of Environmental Medicine, Karolinska Institute, S-I0401 Stockholm, Sweden. Am. J. Epidemiol. 122: 684-694, 1985.

Etiologic factors for lung cancer were studied by the case-control technique among 636 men, in- cluding 212 with pulmonary carcinoma, who had died between 1961 and 1979 in a county in northern Sweden. Data on smoking habits, occupation, and residence were obtained from a next of kin to each study subject. Validation against data from other sources indicated that the exposure information Was of high quality. A relative risk of 2.0 for lung cancer was seen among men who had lived with- in approximately 20 km from a large copper smelter. The increased risk, which is statistically signi- ficant (p < 0.05), could not be explained by smo- king habits or occupationsl backgrounds. Smelter workers and miners had relative risks for lung cancer of 3.0 and 4.1, respectively. No firm con- clusions can be drawn on the cause of excess lung cancer risk in the smelter area, but it seems plausible that the very substantial emissions to air from the smelter, especially of arsenic, may have played a role.

Underground Mining, Smoking, and Lung Cancer: A Case-Control Study in the Iron Ore ~micipalities in Northern Sweden. Damber, L., Larsson, L.-G. Centre of Oncology, Uni- versity Hospital, University of Umea, S-901 85 Umea, Sweden. J. Natl. Cancer Inst. 74: 1207-1213, 1985.

A case-control study of lung cancer in males was performed in two municipalities in northern Sweden with large iron ore mines. Previous studies had revealed an increased lung cancer risk for underground workers in these mines, with al pro- bability related to radon daughter exposure. Data concerning underground mining and smoking were obtained from questionnaires. All analyses sugge- sted an interaction of a multiplicative type be- tween underground mining and smoking in the causa-

tion of lung cancer in this population. The cal- culated population etiologic fraction was about 45% for underground mining and about 80% for smo- king.

The Role of Radon-222 in the Formation of Bron- chial Carcinoma. Merkel, K. Forschungszentrum Seibersdorf, A-2444 Seibersdorf, Austria. Atemwegs-Lungenkrankh. ii: 109-110, 1985.

In the discussion of the biological effects of ionizing radiation attention paid to radon-222 has

increased during the last decades. The nuclide is formed by the decay of radium-226 which is present in small quantities practically everywhere, so also in building materials. Radon is a gaseous, radio- active natural element. From building materials is diffuses out of the walls of buildings; from outer walls it is blown away by the wind, from