Smith Allan H, Ercumen Ayse, Yuan Yan, Steinmaus Craig M
Arsenic Health Effects Research Program, School of Public Health, University of California, Berkeley, California 94720-7360, USA.
J Expo Sci Environ Epidemiol. 2009 May;19(4):343-8. doi: 10.1038/jes.2008.73. Epub 2009 Feb 4.
In 1980, the International Agency for Research on Cancer (IARC) determined there was sufficient evidence to support that inorganic arsenic was a human lung carcinogen based on studies involving exposure through inhalation. In 2004, IARC listed arsenic in drinking water as a cause of lung cancer, making arsenic the first substance established to cause human cancer through two unrelated pathways of exposure. It may initially seem counterintuitive that arsenic in drinking water would cause human lung cancer, and even if it did, one might expect risks to be orders of magnitude lower than those from direct inhalation into the lungs. In this paper, we consider lung cancer dose-response relationships for inhalation and ingestion of arsenic by focusing on two key studies, a cohort mortality study in the United States involving Tacoma smelter workers inhaling arsenic, and a lung cancer case-control study involving ingestion of arsenic in drinking water in northern Chile. When exposure was assessed based on the absorbed dose identified by concentrations of arsenic in urine, there was very little difference in the dose-response findings for lung cancer relative risks between inhalation and ingestion. The lung cancer mortality rate ratio estimate was 8.0 (95% CI 3.2-16.5, P<0.001) for an average urine concentration of 1179 microg/l after inhalation, and the odds ratio estimate of the lung cancer incidence rate ratio was 7.1 (95% CI 3.4-14.8, P<0.001) for an estimated average urine concentration of 825 microg/l following ingestion. The slopes of the linear dose-response relationships between excess relative risk (RR-1) for lung cancer and urinary arsenic concentration were similar for the two routes of exposure. We conclude that lung cancer risks probably depend on absorbed dose, and not on whether inorganic arsenic is ingested or inhaled.
1980年,国际癌症研究机构(IARC)基于涉及吸入暴露的研究,确定有充分证据支持无机砷是人类肺癌致癌物。2004年,IARC将饮用水中的砷列为肺癌病因,使砷成为首个经两种不相关暴露途径被证实可导致人类癌症的物质。饮用水中的砷会导致人类肺癌,这乍一看可能有违直觉,即便确实如此,人们可能会认为其风险比直接吸入肺部的风险低几个数量级。在本文中,我们通过聚焦两项关键研究来探讨吸入和摄入砷的肺癌剂量反应关系,一项是美国涉及塔科马冶炼厂工人吸入砷的队列死亡率研究,另一项是智利北部涉及饮用水中摄入砷的肺癌病例对照研究。当根据尿中砷浓度确定的吸收剂量来评估暴露时,吸入和摄入途径导致肺癌相对风险的剂量反应结果差异极小。吸入后尿平均浓度为1179微克/升时,肺癌死亡率比值估计为8.0(95%可信区间3.2 - 16.5,P<0.001);摄入后估计尿平均浓度为825微克/升时,肺癌发病率比值比估计为7.1(95%可信区间3.4 - 14.8,P<0.001)。两种暴露途径下,肺癌超额相对风险(RR - 1)与尿砷浓度之间的线性剂量反应关系斜率相似。我们得出结论,肺癌风险可能取决于吸收剂量,而不取决于无机砷是经摄入还是吸入进入人体。