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. Author manuscript; available in PMC: 2019 Apr 11.
Published in final edited form as: J Toxicol Environ Health A. 2018 Apr 11;81(13):535–548. doi: 10.1080/15287394.2018.1443860

Table 2.

Reduced regression models showing coefficient estimates for oxLDL.

Coefficient Estimate Standard error P-value N
Model 1 249
 Water Asbi 10.98 3.788 0.004
Adjusted R2 = 0.029, AIC = 2121, p = 0.004
Model 2 249
 Age (years) −0.052 0.081 0.526
 Female −1.12 2.288 0.625
 Water Asbi 10.05 4.232 0.018
 Water Ubi −31.66 14.73 0.033
Adjusted R2 = 0.037,AIC = 2123, p = 0.02
Model 3 94
 Water Asbi 15.9 7.086 0.027
 Water Ubi −11.66 5.305 0.031
 Urine As −3.889 1.916 0.045
 Urine Ubi 11.68 4.392 0.009
Adjusted R2 = 0.106,AIC = 800.7, p = 0.007
Model 4 94
 Age (years) −1.568 0.823 0.06
 Female −54.19 24.07 0.027
 Water Asbi 16.09 6.978 0.024
 Water Ubi −35.28 17.89 0.052
 Urine As −6.023 2.143 0.006
 Urine Ubi 8.833 4.281 0.042
 Urine Cu −25.14 13.84 0.073
 Female x Urine Cu 17.42 7.427 0.021
Adjusted R2 = 0.203, AIC = 797, p = 0.002

P < 0.05 was considered statistically significant.

Reduced models are shown. All full models included demographic (age, gender) and physiologic variables (BMI, HbA1c), and estimated annual water intakes of U and As as predictors.

*

Models 1 and 2 included data from 249 participants. Models 3 and 4 include a subset of 94 participants with available data for urinary Cu. Models 3 and 4 also included continuous concentrations of urinary copper (Cu), vanadium (V), and nickel (Ni), As (log transformed), and U (binary). Models 2 and 4 included second order interactions and significant interactions are reported.