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. Author manuscript; available in PMC: 2024 Mar 1.
Published in final edited form as: Int J Hyg Environ Health. 2022 Nov 28;248:114078. doi: 10.1016/j.ijheh.2022.114078

Table 3.

Assessment of multiplicative effect measure modification by child sex for the relationship between gestational OPEs and preschool ADHD in a nested case-control study of preschool ADHD in MoBa, 2004–2007.

Exposure Combineda,b,c Boysd,e Girlsd,f P-valueg

Odds Ratio (95% CI) Odds Ratio (95% CI) Odds Odds Ratio (95% CI)
Log10 exposure
 DPhP 1.07 (0.77, 1.48) 0.95 (0.61, 1.49) 1.23 (0.76, 2.00) 0.45
 DnBP 1.30 (0.86, 1.97) 1.47 (0.84, 2.57) 1.12 (0.60, 2.11) 0.54
Exposure ≥ LODg
 BBOEP 0.94 (0.69, 1.28) 1.31 (0.86, 2.00) 0.58 (0.37, 0.93) 0.01
 BDCIPP 1.19 (0.83, 1.71) 1.25 (0.74, 2.11) 1.07 (0.63, 1.80) 0.67
a

Refers to full model without the incorporation of interaction terms.

b

Combined model contains 260 Preschool ADHD cases and 549 birth-year-stratified controls.

c

All models are derived from an imputed logistic regression model adjusted for total fish consumption, maternal education, financial difficulty, maternal age, and sex.

d

Stratum-specific estimates are derived from models that additionally include interaction terms for each included variable using an augmented product term approach to assess effect measure modification by sex.

e

Model for boys contains 145 Preschool ADHD cases and 275 birth-year-stratified controls.

f

Model for girls contains 115 Preschool ADHD cases and 274 birth-year-stratified controls.

g

P-value is derived from organophosphate ester*sex interaction.

g

Limit of detection.