Table 3.
Association between ever-use of pesticides and incident shingles.
| Specific pesticides | Total sample | Without baseline autoimmune/lymphoid malignanciesa | ||||||
|---|---|---|---|---|---|---|---|---|
| Age (y) | Noncases | Cases | HR (95% CI)b | Age (y) | Noncases | Cases | HR (95% CI)b | |
| % | () % | () % | () % | |||||
| Insecticides | ||||||||
| Pyrethroids | ||||||||
| Permethrin (crops) | — | 13 | 14 | 1.25 (0.97, 1.60) | — | 13 | 14 | 1.24 (0.95, 1.60) |
| Permethrin (animals) | — | 15 | 13 | 1.02 (0.79, 1.32) | — | 15 | 13 | 1.05 (0.80, 1.37) |
| Organophosphates | ||||||||
| Coumaphos | — | 10 | 14 | 1.35 (1.06, 1.73) | — | 10 | 14 | 1.40 (1.08, 1.81) |
| Dichlorvos | — | 13 | 14 | 0.97 (0.76, 1.25) | — | 13 | 14 | 1.02 (0.79, 1.32) |
| Chlorpyrifos | 46 | 49 | 1.18 (0.91, 1.53) | — | 43 | 39 | 0.95 (0.80, 1.14) | |
| 40 | 33 | 0.78 (0.62, 0.98) | — | — | — | — | ||
| Diazinon | — | 37 | 44 | 1.15 (0.97, 1.36) | — | 38 | 43 | 1.12 (0.94, 1.34) |
| Fonofos | 22 | 22 | 0.91 (0.65, 1.26) | 23 | 21 | 0.88 (0.63, 1.23) | ||
| 24 | 27 | 1.24 (0.95, 1.62) | 24 | 28 | 1.27 (0.96, 1.67) | |||
| Malathion | — | 78 | 84 | 1.36 (1.09, 1.71) | — | 78 | 84 | 1.32 (1.05, 1.67) |
| Parathion | — | 17 | 24 | 1.30 (1.07, 1.59) | — | 17 | 24 | 1.36 (1.10, 1.67) |
| Phorateb | 38 | 44 | 1.20 (0.91, 1.60) | 37 | 44 | 1.22 (0.91, 1.64) | ||
| 43 | 40 | 0.83 (0.65, 1.06) | 43 | 39 | 0.79 (0.61, 1.02) | |||
| Terbufos | — | 40 | 42 | 1.12 (0.93, 1.34) | 42 | 49 | 1.59 (1.20, 2.10) | |
| — | — | — | — | 39 | 36 | 0.83 (0.64, 1.08) | ||
| Carbamates | ||||||||
| Aldicarb | — | 10 | 10 | 1.00 (0.75, 1.34) | — | 10 | 11 | 1.09 (0.81, 1.47) |
| Carbaryl | — | 62 | 70 | 1.12 (0.93, 1.35) | — | 63 | 68 | 1.07 (0.88, 1.30) |
| Carbofuran | — | 31 | 32 | 0.94 (0.79, 1.13) | — | 30 | 30 | 0.91 (0.75, 1.10) |
| Organochlorines | ||||||||
| Aldrin | — | 25 | 36 | 1.12 (0.93, 1.35) | — | 23 | 34 | 1.13 (0.92, 1.37) |
| Chlordaneb | 20 | 26 | 0.76 (0.56, 1.04) | 20 | 26 | 0.75 (0.53, 1.03) | ||
| 45 | 53 | 1.29 (1.04, 1.61) | 45 | 53 | 1.28 (1.02, 1.62) | |||
| Dieldrin | — | 9 | 13 | 0.93 (0.72, 1.20) | — | 9 | 13 | 0.94 (0.72, 1.23) |
| DDT | — | 32 | 47 | 1.01 (0.84, 1.21) | — | 31 | 46 | 1.02 (0.84, 1.23) |
| Heptachlor | — | 21 | 27 | 0.92 (0.75, 1.13) | — | 21 | 27 | 0.90 (0.73, 1.12) |
| Lindane | — | 26 | 33 | 1.25 (1.04, 1.49) | — | 26 | 32 | 1.21 (1.00, 1.46) |
| Toxaphene | — | 18 | 22 | 0.98 (0.81, 1.20) | — | 17 | 21 | 0.94 (0.76, 1.16) |
| Fumigants | ||||||||
| Methylbromide | — | 14 | 18 | 1.34 (1.04, 1.74) | — | 14 | 19 | 1.36 (1.03, 1.80) |
| Aluminum phosphide | — | 6 | 6 | 1.14 (0.82, 1.59) | — | 6 | 7 | 1.24 (0.87, 1.77) |
| Carbon tetrachloride/disulfide | — | 8 | 13 | 1.22 (0.95, 1.56) | — | 8 | 13 | 1.27 (0.97, 1.67) |
| Ethylene dibromide | — | 7 | 10 | 1.46 (1.10, 1.93) | — | 6 | 10 | 1.53 (1.13, 2.08) |
| Fungicides | ||||||||
| Benomylb | — | 11 | 14 | 1.34 (1.03, 1.73) | — | 11 | 14 | 1.30 (0.99, 1.70) |
| Captan | — | 12 | 13 | 1.12 (0.87, 1.44) | — | 12 | 13 | 1.12 (0.85, 1.47) |
| Chlorothalonil | — | 7 | 6 | 0.89 (0.62, 1.26) | — | 7 | 6 | 0.86 (0.59, 1.25) |
| Maneb/mancozeb | 9 | 18 | 1.93 (1.36, 2.74) | 9 | 18 | 2.01 (1.40, 2.89) | ||
| 14 | 15 | 1.10 (0.80, 1.51) | 14 | 14 | 1.11 (0.79, 1.56) | |||
| Metalaxylc | 23 | 30 | 1.14 (0.84, 1.56) | 23 | 30 | 1.24 (0.90, 1.71) | ||
| 26 | 23 | 0.87 (0.66, 1.14) | 26 | 24 | 0.86 (0.64, 1.16) | |||
| Herbicides | ||||||||
| Analides/analines | ||||||||
| Alachlor | — | 57 | 60 | 1.11 (0.93, 1.32) | — | 56 | 59 | 1.06 (0.88, 1.28) |
| Metolachlorb | — | 48 | 47 | 1.03 (0.86, 1.23) | 50 | 53 | 1.29 (0.97, 1.71) | |
| 45 | 43 | 0.90 (0.70, 1.16) | ||||||
| Pendimethalin | — | 46 | 46 | 1.10 (0.94, 1.30) | — | 46 | 45 | 1.06 (0.89, 1.26) |
| Trifluralin | — | 54 | 58 | 1.18 (0.98, 1.41) | — | 54 | 59 | 1.21 (1.00, 1.46) |
| Phenoxy | ||||||||
| 2,4-D | — | 79 | 84 | 1.30 (1.03, 1.64) | — | 79 | 84 | 1.26 (0.99, 1.61) |
| 2,4,5-T | — | 29 | 39 | 1.10 (0.92, 1.31) | — | 29 | 39 | 1.15 (0.96, 1.39) |
| 2,4,5-TP | — | 12 | 18 | 1.28 (1.03, 1.59) | — | 12 | 18 | 1.34 (1.07, 1.68) |
| Thiocarbamate | ||||||||
| EPTC | — | 22 | 20 | 1.01 (0.81, 1.25) | — | 21 | 21 | 1.07 (0.85, 1.34) |
| Triazine/triazinone | ||||||||
| Atrazine | — | 74 | 74 | 1.00 (0.84, 1.22) | — | 74 | 73 | 1.05 (0.85, 1.30) |
| Cyanazine | — | 45 | 48 | 1.22 (1.01, 1.47) | — | 45 | 49 | 1.29 (1.06, 1.58) |
| Metribuzin | — | 50 | 53 | 1.18 (0.98, 1.41) | — | 50 | 53 | 1.20 (0.99, 1.45) |
| Other | ||||||||
| Butylate | — | 37 | 39 | 1.12 (0.94, 1.33) | — | 37 | 39 | 1.12 (0.93, 1.34) |
| Chlorymuron ethyl | — | 40 | 40 | 1.12 (0.95, 1.33) | — | 40 | 39 | 1.08 (0.90, 1.29) |
| Dicamba | — | 54 | 54 | 1.05 (0.86, 1.28) | — | 55 | 54 | 1.08 (0.87, 1.33) |
| Glyphosate | — | 78 | 83 | 1.43 (1.14, 1.78) | — | 78 | 83 | 1.40 (1.11, 1.77) |
| Imazethapyr | 50 | 44 | 0.88 (0.67, 1.16) | — | 46 | 42 | 1.05 (0.86, 1.29) | |
| 40 | 41 | 1.18 (0.92, 1.50) | — | — | — | — | ||
| Paraquat | 22 | 27 | 1.15 (0.84, 1.56) | 22 | 27 | 1.20 (0.87, 1.65) | ||
| 24 | 30 | 1.38 (1.08, 1.75) | 24 | 31 | 1.42 (1.10, 1.82) | |||
| Petroleum oil/distillates | — | 51 | 53 | 1.11 (0.94, 1.31) | 51 | 54 | 1.16 (0.97, 1.38) | |
Note: Estimates were derived using Cox proportional hazard models with age as the time scale, limited to pesticides with at least 10 exposed cases. When proportional hazards were not met, HRs were stratified by median attained age (60 y). All models were adjusted for state, with additional adjustment for education or correlated pesticides as indicated for specific exposures. —, Not applicable; 2,4-D, 2,4-dichlorophenoxyacetic acid; 2,4,5-T, 2,4,5-trichlorophenoxyacetic acid; 2,4,5-TP, 2,4,5-trichlorophenoxy) propionic acid; CI, confidence interval; DDT, dichlorodiphenyltrichloroethane; EPTC, S-ethyl dipropylthiocarbamate; HR, hazard ratio.
Sensitivity analysis excludes those with prevalent autoimmune diseases or leukemia/lymphoma (645 controls and 58 cases); age group “overall” is listed when age stratification was no longer justified based on violation of proportional hazards assumption.
Adjusted for state and education.
Adjusted for state and methylbromide exposure.