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. 2025 Jan 18;168(1):43–55. doi: 10.1016/j.chest.2024.12.037

Table 4.

Multivariate Analysis of Association Between 8-Hour Time-Weighted Average Endotoxin and Quantitative Small Airway Measures

8-Hour TWA Endotoxina (EU/m3) Exp−856 P Value E/I MLA P Value RVC−856 to −950 P Value Residual−856 P Value
All (N = 404)
Survey year 2011
 ≤ 50
 50-1,500 –0.014 .431 0.002 .787 0.006 .778 –0.002 .901
 1,500-2,300 0.009 .691 0.022 .040 0.066 .011 0.028 .159
 2,300-3,900 –0.013 .535 –0.010 .333 –0.010 .693 –0.016 .421
 > 3,900 –0.007 .765 0.009 .411 0.024 .380 0.013 .538
Survey year 2016
 ≤ 50
 50-1,500 –0.001 .972 0.008 .354 0.023 .255 0.010 .547
 1,500-2,300 0.019 .390 0.023 .035 0.071 .006 0.033 .100
 2,300-3,900 0.014 .525 –0.003 .754 0.009 .719 0.012 .532
 > 3,900 0.001 .972 0.021 .070 0.051 .060 0.028 .181
Difference
 ≤ 50
 50-1,500 0.013 .435 0.006 .507 0.018 .385 0.012 .487
 1,500-2,300 0.010 .634 0.001 .948 0.005 .842 0.005 .823
 2,300-3,900 0.027 .193 0.007 .508 0.019 .444 0.028 .171
 > 3,900 0.008 .723 0.011 .298 0.028 .289 0.015 .472
Cotton workers (n = 178)
Survey year 2011
 ≤ 50
 50-1,500 0.033 .412 0.039 .036 0.087 .060 0.055 .126
 1,500-2,300 0.057 .179 0.059 .003 0.144 .003 0.087 .023
 2,300-3,900 0.033 .453 0.030 .143 0.080 .107 0.042 .276
 > 3,900 0.046 .302 0.052 .013 0.113 .027 0.075 .063
Survey year 2016
 ≤ 50
 50-1,500 0.052 .202 0.050 .008 0.114 .014 0.075 .038
 1,500-2,300 0.072 .091 0.064 .001 0.159 .001 0.099 .010
 2,300-3,900 0.065 .137 0.041 .041 0.109 .028 0.079 .044
 > 3,900 0.057 .208 0.067 .001 0.149 .004 0.097 .018
Difference
 ≤ 50
 50-1,500 0.019 .602 0.010 .520 0.028 .492 0.020 .560
 1,500-2,300 0.015 .692 0.005 .756 0.015 .728 0.012 .732
 2,300-3,900 0.032 .386 0.012 .484 0.030 .484 0.036 .312
 > 3,900 0.011 .773 0.016 .363 0.036 .393 0.022 .545

Coefficients and P values from the linear mixed model with a random intercept are reported. P < .05 was considered significantly different from zero. Small airway disease quantified by small airway measures was the outcome, and 8-h TWA endotoxin was the exposure variable in the model. The linear mixed models were adjusted for age, sex, height, smoking intensity, survey year, and the interaction between 8-h TWA endotoxin and survey year (8-h TWA endotoxin × survey year). E/I MLA = expiratory-to-inspiratory ratio of mean lung attenuation; Exp−856 = percentage of voxels with attenuation less than -856 HU on expiratory CT scans; HU = Hounsfield unit; pp FEV1 = percent predicted FEV1; Residual–856 = residuals from the linear regression of Exp−856 on the percentage of voxels with attenuation less than –950 HU; RVC−856 to −950 = relative volume change in voxels with attenuation between –856 HU and –950 HU; TWA = time-weighted average.

a

50 EU/m3 represents the reference level. 1,500 EU/m3 is the 40th percentile, 2,300 EU/m3 is the 60th percentile, and 3,900 EU/m3 is the 80th percentile. There are 237 textile workers exposed to ≤ 50 EU/m3 endotoxin, 61 workers exposed to 50 to 1,500 EU/m3 endotoxin, 35 workers exposed to 1,500 to 2,300 EU/m3 endotoxin, 37 workers exposed to 2,300 to 3,900 EU/m3 endotoxin, and 34 workers exposed to more than 3,900 EU/m3.