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. Author manuscript; available in PMC: 2020 Apr 1.
Published in final edited form as: Environ Res. 2018 Dec 25;171:177–184. doi: 10.1016/j.envres.2018.12.061

Table 5.

Association between RyR Active PCB concentration sum1 (dichotomized using a median split) and ASD and Non-TD

ASD vs. TD Non-TD vs. TD
Exposure TD (n = 60) ASD (n = 21) Non-TD (n = 23) OR (95% CI) P-Value OR (95% CI) P-Value
Frequency (%)
RyR Active PCB Lipid-Standardized Crude Model
M1 (4.68 – 16.31 ng/g of lipid) 33 (55) 6 (29) 13 (57) Reference Reference
M2 (16.74 – 170.03 ng/g of lipid) 27 (45) 15 (71) 10 (43) 3.06 (1.04 to 8.95) 0.04 0.94 (0.36 to 2.48) 0.90
RyR Active PCB Lipid-Standardized Adjusted Model2,3
M1 (4.68 – 16.31 ng/g of lipid) 33 (56) 6 (29) 12 (57) Reference Reference
M2 (16.74 – 170.03 ng/g of lipid) 26 (44) 15 (71) 9 (43) 2.63 (0.87 to 7.97) 0.09 0.77 (0.27 to 2.25) 0.64

PCB = Polychlorinated Biphenyl, TD = Typical Development, ASD = Autism Spectrum Disorder, Non-TD = Non-Typical Development, RyR = Ryanodine receptor, M1 = Lowest 50% PCB concentration, M2 = Highest 50% PCB concentration

1

Sum included concentration from: PCB 52, PCB 84, PCB 95, PCB 136, and PCB 176 collected during the 3rd trimester of pregnancy

2

Loss of 3 observations due to missing prenatal vitamin use,

3

Adjusted for maternal education and prenatal vitamin use in month 1 of pregnancy