Table 5. Adjusted ORs and 95% CIs of the use of plastics in refrigerator food storage with high concentration of urine phthalate metabolites.
| Category | Men | Women | ||||||
|---|---|---|---|---|---|---|---|---|
| Unadjusted | Multivariable adjusted modela | Unadjusted | Multivariable adjusted modela | |||||
| The others | Plastics | The others | Plastics | The others | Plastics | The others | Plastics | |
| MEHHP | 1 | 1.42 (1.13–1.79) | 1 | 1.35 (1.05–1.72) | 1 | 1.15 (0.91–1.46) | 1 | 0.94 (0.72–1.22) |
| MEOHP | 1 | 1.56 (1.24–1.97) | 1 | 1.48 (1.16–1.88) | 1 | 1.17 (0.88–1.41) | 1 | 1.05 (0.81–1.34) |
| MECPP | 1 | 1.36 (1.09–1.70) | 1 | 1.32 (1.04–1.66) | 1 | 1.12 (0.89–1.42) | 1 | 1.06 (0.83–1.35) |
| ∑DEHP | 1 | 1.43 (1.14–1.80) | 1 | 1.37 (1.08–1.74) | 1 | 1.19 (0.94–1.50) | 1 | 1.08 (0.84–1.38) |
| MnBP | 1 | 1.47 (1.17–1.86) | 1 | 1.44 (1.13–1.84) | 1 | 1.30 (1.03–1.64) | 1 | 1.17 (0.92–1.50) |
| MBzP | 1 | 1.34 (1.05–1.70) | 1 | 1.22 (0.95–1.56) | 1 | 1.09 (0.86–1.39) | 1 | 0.93 (0.72–1.20) |
| MCPP | 1 | 1.03 (0.83–1.28) | 1 | 0.97 (0.77–1.22) | 1 | 1.19 (0.95–1.49) | 1 | 1.18 (0.93–1.48) |
| MCOP | 1 | 1.10 (0.89–1.36) | 1 | 1.09 (0.88–1.36) | 1 | 0.82 (0.66–1.03) | 1 | 0.85 (0.68–1.07) |
| MCNP | 1 | 0.90 (0.72–1.12) | 1 | 0.84 (0.67–1.05) | 1 | 0.88 (0.70–1.10) | 1 | 0.86 (0.68–1.09) |
OR: odds ratio; CI: confidence interval; MEHHP: mono-(2-ethyl-5-hydroxyhexyl) phthalate; MEOHP: mono-(2-ethyl-5-oxohexyl) phthalate; MECPP: mono-(2-ethyl-5-carboxypentyl) phthalate; ∑DEHP: ∑di(2-ethylhexyl) phthalate; MnBP: mono-n-butyl phthalate; MBzP: mono-benzyl phthalate; MCPP: mono (3-carboxypropyl) phthalate; MCOP: mono-carboxyoctyl phthalate; MCNP: mono-carboxy-isononly phthalate.
aMultivariable adjusted model: adjusted for age, body mass index, marital status, smoking, food storage(freezer), type of drinking water, and consumption of plastic bag drink, wrap packing delivery food, PET drinks, microwave food, cup noodles, grilled meat, milk, dairy products, hamburgers, pizza, seafood.