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.
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.