Marshall Guillermo, Ferreccio Catterina, Yuan Yan, Bates Michael N, Steinmaus Craig, Selvin Steve, Liaw Jane, Smith Allan H
Departamento de Salud Pública, Escuela de Medicina, Pontificia Universidad Católica de Chile, Santiago, Chile.
J Natl Cancer Inst. 2007 Jun 20;99(12):920-8. doi: 10.1093/jnci/djm004. Epub 2007 Jun 12.
Region II of Chile (the second most northerly administrative region) experienced dramatic increases in average arsenic water concentrations beginning in 1958, followed by marked declines in the 1970s when water treatment plants were installed. This history provides a unique opportunity to study time trends in the development of arsenic-related cancers, including lung and bladder cancers.
We investigated lung and bladder cancer mortality from 1950 to 2000 for region II compared with region V, where drinking water was not contaminated with arsenic. Mortality data were obtained from 218,174 death certificates for the two regions for 1950-1970 and from mortality data tapes that identified 307,541 deaths in the two regions for 1971-2000. Poisson regression models were used to identify time trends in rate ratios (RRs) of mortality from lung and bladder cancers comparing region II with region V.
Lung and bladder cancer mortality rate ratios for region II compared with region V started to increase about 10 years after high arsenic exposures commenced and continued to rise until peaking in 1986-1997. The peak lung cancer mortality RRs were 3.61 (95% confidence interval [CI] = 3.13 to 4.16) for men and 3.26 (95% CI = 2.50 to 4.23) for women. The peak bladder cancer RRs were 6.10 (95% CI = 3.97 to 9.39) for men and 13.8 (95% CI = 7.74 to 24.5) for women. Combined lung and bladder cancer mortality rates in region II were highest in the period 1992-1994, with mortality rates of 153 and 50 per 100,000 men and women, respectively, in region II compared with 54 and 19 per 100,000 in region V.
Such large increases in total population cancer mortality rates have, to our knowledge, not been documented for any other environmental exposure. The long latency pattern is noteworthy, with mortality from lung and bladder cancers continuing to be high until the late 1990s, even though major decreases in arsenic exposure occurred more than 25 years earlier.
智利第二大区(第二北部行政区)自1958年起平均砷水浓度急剧上升,随后在20世纪70年代安装了水处理厂后显著下降。这段历史为研究包括肺癌和膀胱癌在内的砷相关癌症发展的时间趋势提供了独特机会。
我们调查了1950年至2000年第二大区与第五大区的肺癌和膀胱癌死亡率,第五大区的饮用水未受砷污染。1950 - 1970年两个地区的死亡率数据来自218,174份死亡证明,1971 - 2000年两个地区的死亡率数据来自识别出307,541例死亡的死亡率数据磁带。使用泊松回归模型来确定第二大区与第五大区相比肺癌和膀胱癌死亡率比值比(RRs)的时间趋势。
与第五大区相比,第二大区的肺癌和膀胱癌死亡率比值比在高砷暴露开始约10年后开始上升,并持续上升直至1986 - 1997年达到峰值。男性肺癌死亡率RRs峰值为3.61(95%置信区间[CI]=3.13至4.16),女性为3.26(95%CI = 2.50至4.23)。男性膀胱癌RRs峰值为6.10(95%CI = 3.97至9.39),女性为13.8(95%CI = 7.74至24.5)。第二大区肺癌和膀胱癌合并死亡率在1992 - 1994年期间最高,第二大区每10万名男性和女性的死亡率分别为153和50,而第五大区每10万名分别为54和19。
据我们所知,总人口癌症死亡率如此大幅上升在任何其他环境暴露中都未有记录。这种长时间的潜伏期模式值得注意,尽管砷暴露在25多年前就大幅下降,但肺癌和膀胱癌死亡率直到20世纪90年代后期仍居高不下。