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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 3.

Reduced regression models showing coefficient estimates for CRP.

Coefficient Estimate Standard error P-value N*
Model 1 249
 Age (years) −0.015 0.005 0.002
 BMI, kg/m2 0.038 0.014 0.007
Adjusted R2 = 0.085, AIC = 750.4, p = < 0.0001
Model 2 249
 Age (years) −0.016 0.005 0.001
 Female x BMI −0.059 0.03 0.049
Adjusted R2 = 0.092, AIC = 750.4, p = < 0.0001
Model 3 94
 Age (years) −0.019 0.007 0.011
 Female −0.327 0.205 0.115
 BMI, kg/m2 0.049 0.022 0.026
Adjusted R2 = 0.157, AIC = 263.1, p = 0.001
Model 4 94
 BMI, kg/m2 0.051 0.021 0.017
 Age x HbA1c bi −0.04 0.017 0.018
 Female x Urine U bi 1.296 0.589 0.031
Adjusted R2 = 0.246, AIC = 258.7, p = 0.0003

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.