Nitrate exposure from drinking water and dietary sources among Iowa farmers using private wells

被引:4
作者
Skalaban, Timothy G. [1 ,4 ]
Thompson, Darrin A. [2 ]
Madrigal, Jessica M. [1 ]
Blount, Benjamin C. [3 ]
Espinosa, Maria Morel [3 ]
Kolpin, Dana W. [5 ]
Deziel, Nicole C. [4 ]
Jones, Rena R. [1 ]
Freeman, Laura Beane [1 ]
Hofmann, Jonathan N. [1 ]
Ward, Mary H. [1 ,6 ]
机构
[1] NCI, Occupat & Environm Epidemiol Branch, Rockville, MD USA
[2] Univ Iowa, Ctr Hlth Effects Environm Contaminat, Iowa City, IA USA
[3] US Ctr Dis Control & Prevent, Tobacco & Volatiles Branch, Natl Ctr Environm Hlth, Atlanta, GA USA
[4] Yale Univ, Yale Sch Publ Hlth, Dept Environm Hlth Sci, New Haven, CT USA
[5] US Geol Survey, Cent Midwest Water Sci Ctr, Iowa City, IA USA
[6] Occupat & Environm Epidemiol Branch, 9609 Med Ctr Dr, SG6E138, Rockville, MD 20850 USA
关键词
Nitrate; Drinking water; Private wells; Biomarkers; Diet; Iowa; Water quality; CREATININE; HEALTH; RISK;
D O I
10.1016/j.scitotenv.2024.170922
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Nitrate levels are increasing in water resources across the United States and nitrate ingestion from drinking water has been associated with adverse health risks in epidemiologic studies at levels below the maximum contaminant level (MCL). In contrast, dietary nitrate ingestion has generally been associated with beneficial health effects. Few studies have characterized the contribution of both drinking water and dietary sources to nitrate exposure. The Agricultural Health Study is a prospective cohort of farmers and their spouses in Iowa and North Carolina. In 2018-2019, we assessed nitrate exposure for 47 farmers who used private wells for their drinking water and lived in 8 eastern Iowa counties where groundwater is vulnerable to nitrate contamination. Drinking water and dietary intakes were estimated using the National Cancer Institute Automated Self -Administered 24 -Hour Dietary Assessment tool. We measured nitrate in tap water and estimated dietary nitrate from a database of food concentrations. Urinary nitrate was measured in first morning void samples in 2018-19 and in archived samples from 2010 to 2017 (minimum time between samples: 2 years; median: 7 years). We used linear regression to evaluate urinary nitrate concentrations in relation to total nitrate, and drinking water and dietary intakes separately. Overall, dietary nitrate contributed the most to total intake (median: 97 %; interquartile range [IQR]: 57-99 %). Among 15 participants (32 %) whose drinking water nitrate concentrations were at/above the U.S. Environmental Protection Agency MCL (10 mg/L NO3-N), median intake from water was 44 % (IQR: 26-72 %). Total nitrate intake was the strongest predictor of urinary nitrate concentrations (R2 = 0.53). Drinking water explained a similar proportion of the variation in nitrate excretion (R2 = 0.52) as diet (R2 = 0.47). Our findings demonstrate the importance of both dietary and drinking water intakes as determinants of nitrate excretion.
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页数:8
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