Table 4.
Results for linear regressions, adjusted for age and smoking, of POP concentrations (log-transformed) on %5-mC.a
Alu |
LINE-1
|
|||
---|---|---|---|---|
Chemical | β-Estimate | p-Value | β-Estimate | p-Value |
DDT | −0.26 | 0.01* | 0.06 | 0.87 |
DDE | −0.38 | 0.01* | −0.02 | 0.97 |
β-HCH | −0.48 | < 0.01* | −0.90 | 0.09 |
Hexachlorobenzene | 0.06 | 0.72 | −0.72 | 0.19 |
Chlordane | −0.21 | 0.11 | −0.46 | 0.27 |
cis-Chlordane | 0.02 | 0.91 | −0.01 | 0.99 |
Oxychlordane | −0.32 | < 0.01* | −0.66 | 0.09 |
α-Chlordane | −0.75 | 0.05* | −0.62 | 0.60 |
Mirex | −0.27 | 0.01* | −0.23 | 0.51 |
Toxaphene | 0.09 | 0.51 | −0.16 | 0.72 |
PCB-28 | −0.42 | < 0.01* | −0.55 | 0.23 |
PCB-52 | −0.12 | 0.36 | −0.05 | 0.91 |
PCB-99 | −0.51 | < 0.01* | −0.55 | 0.22 |
PCB-101 | −0.25 | 0.05* | 0.33 | 0.44 |
PCB-105 | −0.51 | < 0.01* | −0.71 | 0.08 |
PCB-118 | −0.49 | < 0.01* | −0.73 | 0.12 |
PCB-128 | −0.52 | < 0.01* | −0.01 | 0.99 |
PCB-138 | −0.54 | < 0.01* | −0.52 | 0.24 |
PCB-153 | −0.52 | < 0.01* | −0.47 | 0.22 |
PCB-156 | −0.66 | < 0.01* | −0.48 | 0.26 |
PCB-170 | −0.54 | < 0.01* | −0.48 | 0.15 |
PCB-180 | −0.54 | < 0.01* | −0.43 | 0.24 |
PCB-183 | −0.57 | < 0.01* | −0.20 | 0.67 |
PCB-187 | −0.49 | < 0.01* | −0.15 | 0.77 |
∑PCBs | −0.56 | < 0.01* | −0.49 | 0.23 |
∑POPs | −0.48 | < 0.01* | −0.46 | 0.32 |
Age variable was continuous; smoking variable was continuous, reflecting number of cigarettes per day (or zero if a non-smoker).
Estimate is statistically significant at α≤0.05.