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. 2022 Mar 18;51(4):1106–1119. doi: 10.1093/ije/dyac046

Table 4.

Associations between nitrite and nitrate exposures by sources and prostate cancer risk, NutriNet-Santé cohort, France, 2009–2021 (N = 21 772 men)

Exposure Sex-specific categories of intakesa
P trend
1 2 3
Total nitrites N cases/N total 95/7258 169/7257 136/7257
HR (95% CI) Ref. 1.27 (0.97–1.65) 1.28 (0.95–1.73) 0.2
Nitrites from natural sources N cases/N total 94/7258 167/7257 139/7257
HR (95% CI) Ref. 1.19 (0.91–1.55) 1.25 (0.92–1.68) 0.2
Nitrites from food additives N cases/N total 56/5443 182/8165 162/8164
HR (95% CI) Ref. 1.30 (0.95–1.77) 1.58 (1.14–2.18) 0.008
 Sodium nitrite (e250) N cases/N total 56/5456 181/8159 163/8157
HR (95% CI) Ref. 1.31 (0.96–1.79) 1.62 (1.17–2.25) 0.004
Total nitrates N cases/N total 74/7258 146/7258 180/7256
HR (95% CI) Ref. 1.16 (0.87–1.55) 1.18 (0.87–1.60) 0.4
Nitrates from natural sources N cases/N total 74/7258 146/7258 180/7256
HR (95% CI) Ref. 1.16 (0.87–1.55) 1.16 (0.86–1.58) 0.4
Nitrates from food additives N cases/N total 198/13 622 133/4075 69/4075
HR (95% CI) Ref. 1.38 (1.10–1.74) 0.99 (0.74–1.33) 0.9
 Potassium nitrate (e252) N cases/N total 198/13 623 133/4074 69/4075
HR (95% CI) Ref. 1.39 (1.10–1.75) 1.03 (0.77–1.38) 0.9

HR, cause-specific hazard ratio.

Median follow-up time: 6.8 years. Person-years: 139 334.

Multivariable Cox proportional hazard models were adjusted for: age (timescale), energy intake without alcohol (kcal/d, continuous), alcohol, sugar, saturated fatty acids and fibre intakes (g/d, continuous), sodium and heme iron intakes (mg/d, continuous), body mass index (kg/m2, continuous), height (cm, continuous), physical activity (high, moderate, low, calculated according to International Physical Activity Questionnaire recommendations), smoking status (never, former, current smokers), number of 24-h dietary records (continuous), family history of cancer (yes/no) and educational level (primary, secondary, undergraduate, post-graduate). All models were mutually adjusted for nitrate/nitrite intakes other than the specific one studied.

a

For nitrites and nitrates from overall exposure and from natural sources, sex-specific tertiles of consumption were defined.

Cut-offs were: 5.18 and 7.44 mg/d in men for overall nitrites, 162.11 and 251.59 mg/d in men for overall nitrates, 4.92 and 7.07 mg/d in men for nitrites from natural sources and 161.94 and 251.32 mg/d in men for nitrates from natural sources.

For nitrites and nitrates from food additives, three categories of consumption were defined: non-consumers, low consumers and high consumers (separated by sex-specific median among consumers). Cut-offs were: 0.25 mg/d in men for nitrites from food additives, 0.46 mg/d in men for nitrates from food additives, 0.25 mg/d in men for sodium nitrite (e250) and 0.46 mg/d in men for potassium nitrate (e252).

During men's follow-up, 84 competing deaths occurred and 649 competing cases of cancers other than prostate. Cause-specific HRs for death in the high consumers of total nitrites, nitrites from natural sources, nitrites from food additives, sodium nitrite (e250), total nitrates, nitrates from natural sources, nitrates from food additives and potassium nitrate (e252) were respectively: 0.58 (0.32–1.06), P = 0.1; 0.45 (0.24–0.85), P = 0.02; 1.37 (0.73–2.54), P = 0.4; 1.31 (0.70–2.43), P = 0.4; 1.04 (0.53–2.04), P = 0.7; 1.15 (0.59–2.28), P = 0.9; 1.01 (0.55–1.86), P = 1; 1.00 (0.54–1.84), P = 1. Cause-specific hazard ratios for all cancers except prostate in the high consumers of total nitrites, nitrites from natural sources, nitrites from food additives, sodium nitrite (e250), total nitrates, nitrates from natural sources, nitrates from food additives and potassium nitrate (e252) were respectively: 0.86 (0.69–1.08), P = 0.2; 0.88 (0.70–1.10), P = 0.3; 0.96 (0.76–1.22), P = 0.7; 0.96 (0.76–1.22), P = 0.7; 1.15 (0.91–1.45), P = 0.3; 1.13 (0.90–1.43), P = 0.4; 1.05 (0.85–1.30), P = 0.6; 1.05 (0.85–1.30), P = 0.6.