Epidemiology Branch, National Institute of Environmental Health Sciences, NIH, Research Triangle Park, NC, USA.
Occupational and Environmental Epidemiology Branch, Division of Cancer Epidemiology and Genetics, National Cancer Institute, NIH, Rockville, MD, USA.
J Expo Sci Environ Epidemiol. 2024 Mar;34(2):322-332. doi: 10.1038/s41370-023-00625-y. Epub 2024 Jan 8.
Nitrate and nitrite ingestion has been linked to kidney cancer, possibly via the endogenous formation of carcinogenic N-nitroso compounds. These exposures might also contribute to end-stage renal disease (ESRD).
We investigated associations of drinking water nitrate and dietary nitrate and nitrite intakes (total and by food type) with incident ESRD in the Agricultural Health Study. We also explored modifying effects of vitamin C and heme iron intake, which may affect endogenous nitrosation.
We performed complete case analyses among private pesticide applicators and their spouses. We obtained water nitrate estimates for participants whose primary drinking water source at enrollment (1993-1997) was public water supplies (PWS) or private wells (N = 59,632). Average nitrate concentrations were computed from historical data for PWS users and predicted from random forest models for private well users. Analysis of dietary nitrate and nitrite was restricted to the 30,177 participants who completed the NCI Dietary History Questionnaire during follow-up (1999-2003). Incident ESRD through 2018 was ascertained through linkage with the U.S. Renal Data System. We estimated adjusted hazard ratios (HRs) and 95%CI for associations of tertiles (T) of exposure with ESRD overall and explored effects in strata of vitamin C and heme iron intake.
We identified 469 incident ESRD cases (206 for dietary analysis). Water nitrate and total dietary nitrate/nitrite were not associated with ESRD, but increased ESRD was associated with nitrate and nitrite from processed meats. We found apparent associations between nitrite and ESRD only among participants with vitamin C <median (T3 vs. T1 HR: 2.26, 95%CI: 1.05, 4.86) and with heme iron ≥median (T3 vs. T1 HR: 1.73, 95%CI: 0.89, 3.39).
ESRD incidence was associated with dietary nitrate/nitrite from processed meat among all study participants and with total dietary nitrite among participants with lower vitamin C or higher heme iron intake.
There are few well-established environmental risk factors for end-stage renal disease (ESRD), a worldwide public health challenge. Ingestion of nitrate and nitrite, which may lead to endogenous formation of carcinogenic N-nitroso compounds, has been linked to some cancers and chronic diseases. We investigated these exposures in relation to ESRD in an agricultural cohort. ESRD incidence was associated with dietary nitrate/nitrite from processed meat and with total dietary nitrite among subgroups with lower vitamin C or higher heme iron intake. This study provides preliminary evidence that points to dietary nitrite and possibly dietary nitrate intake as a potential contributor to ESRD.
硝酸盐和亚硝酸盐的摄入与肾癌有关,可能是通过内源性形成致癌的 N-亚硝基化合物。这些暴露也可能导致终末期肾病(ESRD)。
我们研究了饮用水硝酸盐和饮食硝酸盐和亚硝酸盐摄入量(总摄入量和按食物类型)与农业健康研究中 ESRD 的发生率之间的关联。我们还探讨了维生素 C 和血红素铁摄入的修饰作用,这些作用可能会影响内源性亚硝化作用。
我们在私人农药施药者及其配偶中进行了完整病例分析。我们获得了在入组时(1993-1997 年)主要饮用水源为公共供水系统(PWS)或私人水井的参与者的水硝酸盐估计值(N=59632)。PWS 用户的平均硝酸盐浓度是根据历史数据计算的,私人水井用户的平均硝酸盐浓度是根据随机森林模型预测的。饮食硝酸盐和亚硝酸盐的分析仅限于在随访期间(1999-2003 年)完成 NCI 饮食史问卷的 30177 名参与者。通过与美国肾脏数据系统的链接确定了截至 2018 年的 ESRD 事件。我们估计了暴露于 tertiles(T)的风险比(HR)和 95%CI,以评估总体 ESRD 的相关性,并在维生素 C 和血红素铁摄入的分层中探讨了影响。
我们发现了 469 例 ESRD 病例(饮食分析 206 例)。饮用水硝酸盐和总饮食硝酸盐/亚硝酸盐与 ESRD 无关,但加工肉类中的硝酸盐和亚硝酸盐与 ESRD 有关。我们仅在维生素 C <中位数(T3 与 T1 HR:2.26,95%CI:1.05,4.86)和血红素铁≥中位数的参与者中发现了亚硝酸盐与 ESRD 之间的明显关联(T3 与 T1 HR:1.73,95%CI:0.89,3.39)。
所有研究参与者的饮食硝酸盐/亚硝酸盐与加工肉类有关,维生素 C 较低或血红素铁摄入较高的参与者的总饮食亚硝酸盐与 ESRD 有关。
终末期肾病(ESRD)是一个全球性的公共卫生挑战,其明确的环境风险因素很少。摄入硝酸盐和亚硝酸盐可能导致致癌的 N-亚硝基化合物的内源性形成,与某些癌症和慢性疾病有关。我们在农业队列中研究了这些暴露与 ESRD 的关系。在维生素 C 较低或血红素铁摄入较高的亚组中,饮食中来自加工肉类的硝酸盐/亚硝酸盐和总饮食亚硝酸盐与 ESRD 发生率有关。这项研究提供了初步证据,表明饮食亚硝酸盐和可能的饮食硝酸盐摄入可能是 ESRD 的一个潜在原因。