Table 5.
Linear Mixed-Effects Longitudinal Modela: Endometrial Thicknessb Response Across Time Points (N=208, compliant model)
Outcome Variable | Independent Variable | Parameter Estimate |
Standard Error |
pValuec |
---|---|---|---|---|
Endometrial Thicknessb |
Intercept | −0.401 | 0.262 | 0.13 |
Site (ISU=0) | 0.528 | 0.049 | ≤0.0001 | |
Treatment (80 mg) | 0.032 | 0.056 | 0.57 | |
Treatment (120 mg) | 0.043 | 0.055 | 0.43 | |
Time (mo) | −0.008 | 0.001 | ≤0.0001 | |
Estrogen Exposured (y) | 0.022 | 0.007 | 0.0013 | |
Plasma 17-β Estradiol (pg/mL) | 0.006 | 0.002 | 0.0086 | |
Alcohol Intakee (g/week) | −0.001 | 0.0004 | 0.023 | |
Serum Thyroid-Stimulating Hormone (µIU/L) | −0.020 | 0.011 | 0.066 |
Overall model vs model with obligatory design variables only: likelihood ratio = 12.149; df=4; p≤0.0001. Likelihood ratio based on maximum likelihood estimation; estimates and significances based on restricted maximum likelihood estimation.
Natural logarithm of endometrial thickness as variance stabilizing transformation.
P values are based on asymptotic normality of t-distribution; variables left in model were significant at p≤0.10 level (acceptable Type I error rate in modeling endometrial thickness). Additional variables (i.e., body weight, lactation duration, etc.) did not remain in model. The interaction between treatment and time (log likelihood ratio=3.996; df=2) was not significant (p=0.14).
Calculated at baseline, estrogen exposure in years = age at menopause – age at menarche; estrogen exposure was not related to plasma 17-β estradiol (Pearson correlation coefficient = −0.05).
Represents usual weekly alcohol intake at baseline, which was assessed at baseline from a dietary questionnaire.