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. 2016 Jun 3;124(11):1751–1758. doi: 10.1289/EHP191

Table 4.

Association between dietary nitrate and nitrite and bladder cancer in the Iowa Women’s Health Study (= 33,964a).

Nitrate/nitrite sources Cases n Age-adjusted HR (95% CI) Fully adjustedb HR (95% CI)
Dietary nitrate (mg NO3-N/dayc)
All sources
< 16.2 67 8,467 1.00 (Reference) 1.00 (Reference)
16.2–23.9 68 8,489 1.00 (0.72, 1.41) 1.01 (0.72, 1.43)
24.0–34.2 64 8,506 0.92 (0.66, 1.30) 0.94 (0.66, 1.35)
> 34.2 59 8,502 0.86 (0.60, 1.22) 0.85 (0.58, 1.26)
ptrendd 0.32 0.34
Continuouse 258 33,964 0.85 (0.69, 1.04) 0.83 (0.65, 1.05)
Dietary nitrite (mg/day)
All sources
< 0.86 63 8,450 1.00 (Reference) 1.00 (Reference)
0.86–1.12 66 8,514 1.01 (0.71, 1.42) 1.15 (0.78, 1.70)
1.13–1.43 73 8,487 1.12 (0.80, 1.56) 1.38 (0.89, 2.16)
> 1.43 56 8,513 0.85 (0.60, 1.22) 1.15 (0.65, 2.03)
ptrend 0.44 0.69
Continuous 258 33,964 0.95 (0.70, 1.29) 1.59 (0.89, 2.84)
Plant sources
< 0.51 62 8,461 1.00 (Reference) 1.00 (Reference)
0.51–0.67 75 8,507 1.17 (0.84, 1.64) 1.33 (0.92, 1.91)
0.68–0.90 69 8,490 1.08 (0.76, 1.52) 1.32 (0.88, 1.99)
> 0.90 52 8,506 0.81 (0.56, 1.17) 1.05 (0.64, 1.72)
ptrend 0.15 0.82
Continuous 258 33,964 0.86 (0.66, 1.12) 1.10 (0.74, 1.63)
Animal sources
< 0.29 67 8,474 1.00 (Reference) 1.00 (Reference)
0.29–0.40 54 8,443 0.79 (0.55, 1.14) 0.86 (0.59, 1.25)
0.41–0.56 64 8,533 0.92 (0.66, 1.30) 1.03 (0.70, 1.53)
> 0.56 73 8,514 1.06 (0.76, 1.47) 1.24 (0.79, 1.95)
ptrend 0.53 0.22
Continuous 258 33,964 1.10 (0.86, 1.39) 1.31 (0.93, 1.86)
Processed meats
< 0.01 69 8,718 1.00 (Reference) 1.00 (Reference)
0.01–0.03 75 8,707 1.00 (0.72, 1.40) 0.95 (0.68, 1.33)
0.04–0.06 54 8,107 0.89 (0.63, 1.26) 0.86 (0.60, 1.22)
> 0.06 60 8,432 0.95 (0.67, 1.33) 0.88 (0.61, 1.26)
ptrend 0.68 0.46
Continuous 258 33,964 0.99 (0.95, 1.02) 0.98 (0.94, 1.02)
Abbreviations: CI, confidence interval; HR, hazard ratio. aAfter excluding 744 women with missing covariate data. bAdjusted for age, smoking status, pack-years of smoking, and ln-transformed total energy intake. Nitrate models were also adjusted for total ln-transformed dietary nitrite from all sources, and nitrite models were adjusted for total ln-transformed dietary nitrate from all sources. cNO3 converted to NO3-N. Nitrate intakes came almost exclusively from plant sources. dEstimated by modeling a continuous variable derived from the median value within each exposure category. eHR per 1 natural log increase in intake (milligrams/day).