Ward Mary H, Cerhan James R, Colt Joanne S, Hartge Patricia
Division of Cancer Epidemiology and Genetics, National Cancer Institute, NIH/DHHS, Bethesda, MD 20892, USA.
Epidemiology. 2006 Jul;17(4):375-82. doi: 10.1097/01.ede.0000219675.79395.9f.
Nitrate and nitrite are precursors in the in vivo formation of N-nitroso compounds, potent animal carcinogens.
We conducted a population-based case-control study of non-Hodgkin lymphoma (NHL) in 1998 to 2000 in Iowa, Detroit, Seattle, and Los Angeles. Because nitrate levels were elevated in many drinking water supplies in Iowa, but not in the other study centers, we evaluated water nitrate levels and risk of NHL in Iowa only. Monitoring data for public supplies were linked to water source histories from 1960 onward. Nitrate was measured at interview homes with private wells. We limited most analyses to those with nitrate estimates for > 70% of their person-years since 1960 (181 cases, 142 controls). For those in the diet arm of the study (458 cases, 383 controls from 4 centers) and for Iowa participants in both the diet and drinking water analyses, we estimated dietary nitrate and nitrite intake using a 117-item food-frequency questionnaire that included foods high in nitrate and nitrite. Odds ratios and 95% confidence intervals were calculated using logistic regression, adjusting for the study matching factors, education, and caloric intake (diet analyses only).
We found no overall association with the highest quartile of average drinking water nitrate (> 2.90 mg/L nitrate-N: odds ratios = 1.2; 95% confidence interval = 0.6-2.2) or with years > or = 5 mg/L (10+ years: 1.4; 0.7-2.9). We observed no evidence of an interaction between drinking water nitrate exposure and either vitamin C or red meat intake, an inhibitor and precursor, respectively, of N-nitroso compound formation. Among those in the diet arm, dietary nitrate was inversely associated with risk of NHL (highest quartile: 0.54; 0.34-0.86). Dietary nitrite intake was associated with increasing risk (highest quartile: 3.1; 1.7-5.5) largely due to intakes of bread and cereal sources of nitrite.
Average drinking water nitrate levels below 3 mg/L were not associated with NHL risk. Our study had limited power to evaluate higher levels that deserve further study.
硝酸盐和亚硝酸盐是体内形成N-亚硝基化合物的前体物质,N-亚硝基化合物是强效动物致癌物。
1998年至2000年,我们在爱荷华州、底特律、西雅图和洛杉矶开展了一项基于人群的非霍奇金淋巴瘤(NHL)病例对照研究。由于爱荷华州许多饮用水供应中的硝酸盐水平升高,而其他研究中心未出现这种情况,因此我们仅评估了爱荷华州的饮用水硝酸盐水平与NHL风险。公共供水的监测数据与1960年以来的水源历史相关联。在有私人水井的受访家庭中测量硝酸盐含量。我们将大多数分析限制在自1960年以来其超过70%人年有硝酸盐估计值的人群(181例病例,142例对照)。对于研究饮食部分的人群(来自4个中心的458例病例,383例对照)以及参与饮食和饮用水分析的爱荷华州参与者,我们使用包含高硝酸盐和高亚硝酸盐食物的117项食物频率问卷估计饮食中的硝酸盐和亚硝酸盐摄入量。使用逻辑回归计算比值比和95%置信区间,并对研究匹配因素、教育程度和热量摄入(仅饮食分析)进行调整。
我们发现平均饮用水硝酸盐含量最高四分位数(>2.90 mg/L硝酸盐氮:比值比 = 1.2;95%置信区间 = 0.6 - 2.2)或含量≥5 mg/L(10年以上:1.4;0.7 - 2.9)与总体无关联。我们未观察到饮用水硝酸盐暴露与分别作为N-亚硝基化合物形成抑制剂和前体的维生素C或红肉摄入量之间存在相互作用的证据。在饮食部分的人群中,饮食中的硝酸盐与NHL风险呈负相关(最高四分位数:0.54;0.34 - 0.86)。饮食中亚硝酸盐摄入量与风险增加相关(最高四分位数:3.1;1.7 - 5.5),这主要归因于面包和谷物中亚硝酸盐的摄入量。
饮用水中平均硝酸盐水平低于3 mg/L与NHL风险无关。我们的研究评估较高水平的能力有限,这些较高水平值得进一步研究。