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. Author manuscript; available in PMC: 2021 Jan 1.
Published in final edited form as: Epidemiology. 2020 Jan;31(1):136–144. doi: 10.1097/EDE.0000000000001112

Table 2.

Drinking water nitrate from public water supplies and measured and modeled private wells and the risk of bladder cancer among New England Bladder Cancer Study participants with a nitrate estimate for >=70% of exposure-years from 1970 to diagnosis/reference date (987 cases and 1180 controls)a

Average nitrate concentration (mg/L NO3-N)b Cases Controls OR (95% CI)c p-trendd

≤0.21 mg/L 259 293 1.0 Ref.
>0.21-0.37 mg/L 212 294 0.81 (0.61-1.1)
>0.37-0.68 mg/L 229 294 0.89 (0.68-1.2)
>0.68-2.07 mg/L 221 241 1.0 (0.79-1.4)
>2.07 mg/L 66 58 1.5 (0.97-2.3)
p-trendd 0.01

Average daily nitrate intake (mg NO3-N)b Cases Controls OR (95% CI)c

≤0.30 mg 214 295 1.0 Ref.
>0.30-0.62 mg 227 295 1.1 (0.87-1.5)
>0.62-1.29 mg 244 295 1.1 (0.86-1.5)
>1.29-4.59 mg 243 236 1.5 (1.1-1.9)
>4.59 mg 59 59 1.4 (0.89-2.2)
0.06
a

Both residential and workplace measures were included where available, as well as measured and modeled private well values; participants with missing water intake were excluded

b

Exposure categories represent quartiles, with the top category reflecting an additional cut at 95th percentile

c

Adjusted for age, gender, smoking status, high-risk occupation, race, ethnicity, state, and average TTHM concentration for all models, as well as total water intake (L/d) for average nitrate concentration model

d

Based on median values for quantiles of drinking water nitrate entered into the model as a continuous variable; median for top 95th percentile average nitrate was 3.64 mg/L

CI indicates confidence interval, OR odds ratio.