Table 4.
Multivariate analysis of the association between 8-hour TWA 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 | 0.431 | 0.002 | 0.787 | 0.006 | 0.778 | −0.002 | 0.901 |
| 1,500 - 2,300 | 0.009 | 0.691 | 0.022 | 0.040 | 0.066 | 0.011 | 0.028 | 0.159 |
| 2,300 - 3,900 | −0.013 | 0.535 | −0.010 | 0.333 | −0.010 | 0.693 | −0.016 | 0.421 |
| > 3,900 | −0.007 | 0.765 | 0.009 | 0.411 | 0.024 | 0.380 | 0.013 | 0.538 |
| Survey Year 2016 | ||||||||
| ≤ 50 | - | - | - | - | - | - | - | - |
| 50 - 1,500 | −0.001 | 0.972 | 0.008 | 0.354 | 0.023 | 0.255 | 0.010 | 0.547 |
| 1,500 - 2,300 | 0.019 | 0.390 | 0.023 | 0.035 | 0.071 | 0.006 | 0.033 | 0.100 |
| 2,300 - 3,900 | 0.014 | 0.525 | −0.003 | 0.754 | 0.009 | 0.719 | 0.012 | 0.532 |
| > 3,900 | 0.001 | 0.972 | 0.021 | 0.070 | 0.051 | 0.060 | 0.028 | 0.181 |
| Difference | ||||||||
| ≤ 50 | - | - | - | - | - | - | - | - |
| 50 - 1,500 | 0.013 | 0.435 | 0.006 | 0.507 | 0.018 | 0.385 | 0.012 | 0.487 |
| 1,500 - 2,300 | 0.010 | 0.634 | 0.001 | 0.948 | 0.005 | 0.842 | 0.005 | 0.823 |
| 2,300 - 3,900 | 0.027 | 0.193 | 0.007 | 0.508 | 0.019 | 0.444 | 0.028 | 0.171 |
| > 3,900 | 0.008 | 0.723 | 0.011 | 0.298 | 0.028 | 0.289 | 0.015 | 0.472 |
| Cotton worker, N = 178 | ||||||||
| Survey year 2011 | ||||||||
| ≤ 50 | - | - | - | - | - | - | - | - |
| 50 – 1,500 | 0.033 | 0.412 | 0.039 | 0.036 | 0.087 | 0.060 | 0.055 | 0.126 |
| 1,500 - 2,300 | 0.057 | 0.179 | 0.059 | 0.003 | 0.144 | 0.003 | 0.087 | 0.023 |
| 2,300 - 3,900 | 0.033 | 0.453 | 0.030 | 0.143 | 0.080 | 0.107 | 0.042 | 0.276 |
| > 3,900 | 0.046 | 0.302 | 0.052 | 0.013 | 0.113 | 0.027 | 0.075 | 0.063 |
| Survey year 2016 | ||||||||
| ≤ 50 | - | - | - | - | - | - | - | - |
| 50 - 1,500 | 0.052 | 0.202 | 0.050 | 0.008 | 0.114 | 0.014 | 0.075 | 0.038 |
| 1,500 - 2,300 | 0.072 | 0.091 | 0.064 | 0.001 | 0.159 | 0.001 | 0.099 | 0.010 |
| 2,300 - 3,900 | 0.065 | 0.137 | 0.041 | 0.041 | 0.109 | 0.028 | 0.079 | 0.044 |
| > 3,900 | 0.057 | 0.208 | 0.067 | 0.001 | 0.149 | 0.004 | 0.097 | 0.018 |
| Difference | ||||||||
| ≤ 50 | - | - | - | - | - | - | - | - |
| 50 – 1,500 | 0.019 | 0.602 | 0.010 | 0.520 | 0.028 | 0.492 | 0.020 | 0.560 |
| 1,500 - 2,300 | 0.015 | 0.692 | 0.005 | 0.756 | 0.015 | 0.728 | 0.012 | 0.732 |
| 2,300 - 3,900 | 0.032 | 0.386 | 0.012 | 0.484 | 0.030 | 0.484 | 0.036 | 0.312 |
| > 3,900 | 0.011 | 0.773 | 0.016 | 0.363 | 0.036 | 0.393 | 0.022 | 0.545 |
Note: Coefficients and p-Values from the linear mixed model with a random intercept were reported. p < 0.05 was considered significantly different from zero. SAD quantified by small airway measures was outcome and 8-hour TWA endotoxin was the exposure variable in the model. The linear mixed models were adjusted for age, gender, height, smoking intensity, survey year, and the interaction between 8-hour TWA endotoxin and survey year (8-hour TWA endotoxin × survey year). Abbreviations: TWA, Time-weighted Average; FEV1, Forced Expiratory Volume in the first 1 second; pp FEV1, percent predicted FEV1; FVC, Forced Vital Capacity; Exp−856, percent gas trapping; E/I MLA, expiratory to inspiratory ratio of mean lung attenuation; RVC−856 to 950, relative volume change of voxels with attenuation between −856 HU and −950 HU; Residual−856, residuals from the linear regression of Exp−856 on the percent of voxels with attenuation less than −950 HU.
50 EU/m3 represents the reference level. 1500 EU/m3 is the 40th percentile, 2300 EU/m3 is the 60th percentile, and 3900 EU/m3 is the 80th percentile. There are 237 textile workers exposed to ≤ 50 EU/m3 endotoxin, 61 workers exposed to 50 - 1,500 EU/m3 endotoxin, 35 workers exposed to 1,500 - 2,300 EU/m3 endotoxin, 37 workers exposed to 2,300 - 3,900 EU/m3 endotoxin, and 34 workers exposed to more than 3,900 EU/m3.