The course of lung function in community members exposed to World Trade Center (WTC) dust and fumes remains undefined. We studied longitudinal spirometry among patients in the WTC Environmental Health Center (WTCEHC) treatment program.
Observational study of 946 WTCEHC patients with repeated spirometry measures analyzed on the population as a whole and stratified by smoking status, initial spirometry pattern and WTC-related exposure category.
Improvement in forced expiratory volume (FVC; 54.4 ml/year; 95% CI: 45.0-63.8) and forced expiratory volume in one second (FEV1; 36.8 ml/year; 95% CI: 29.3-44.3) was noted for the population as a whole. Heavy smokers did not improve. Spirometry changes differed depending on initial spirometry pattern and exposure category.
These data demonstrate spirometry improvement in select populations suggesting reversibility in airway injury and reinforcing the importance of continued treatment.
The destruction of the World Trade Center (WTC) towers on September 11, 2011 released massive amounts of dust, gas and fumes with potential environmental and occupational exposures for thousands of individuals, including community members who lived (Residents) and worked (Local workers) in the area, as well as for those involved in rescue, recovery (Rescue/recovery workers) and clean-up (Clean-up workers). These groups were potentially exposed via inhalation to the initial WTC dust clouds created as the buildings collapsed, resuspended dust from incompletely cleaned indoor and outdoor areas, fumes from fires that burned for four months, and exposure from prolonged clean-up activities. (
Persistent WTC-related adverse medical and mental health effects have been well described in rescue and recovery workers as well as in community members.(
The Bellevue Hospital Center World Trade Center Environmental Health Center (WTCEHC) is a medical and mental health treatment program that focuses on community members including Residents, Local workers, and Clean-up workers.(
Individuals were self-referred to the WTCEHC with medical and/or mental health symptoms related to September 11, 2001 exposures as previously described. (
At enrollment, patients responded to a multi-dimensional interviewer-administered questionnaire that included characterizations of WTC-related exposures and potential exposure category as Residents, Local worker, and Clean-up workers or Rescue/recovery, respiratory symptoms and history of tobacco use. The WTCEHC treatment protocol included treatment of asthma-like symptoms based on guidelines for asthma management,(
All individuals were referred for screening spirometry at time of enrollment, and at repeat clinic visits for therapeutic evaluation, or at visits scheduled for routine monitoring. Spirometry was performed in accordance with American Thoracic Society/European Respiratory Society standards (
Individuals were classified as having WTC dust cloud exposure if they reported being in the initial WTC dust cloud from the collapsing buildings. Patients were characterized as Resident, Local worker, Rescue/recovery worker, Clean-up worker, or Other, based on their initial questionnaire responses about residence and workplace.(
Patients were included for analysis if they had no respiratory symptom prior to September 11, 2001, had valid longitudinal spirometry defined as an acceptable baseline spirometry measurement, and had at least one valid repeated measurement. Patients with follow-up spirometry duration less than 90 days were excluded.
Continuous variables were summarized using mean and standard deviation (SD) and compared across groups using the nonparametric Kruskal-Wallis test. Categorical variables were summarized by counts and proportions and compared using Chi-square test. (
The final study population consisted of 946 subjects who enrolled in the WTCEHC between August 17, 2005 and December 14, 2011, had new onset and persistent respiratory symptoms, and fit criteria for longitudinal assessment (
When classified by baseline spirometry pattern (
The average number of repeated observations was 3 (range 2-10). The average duration of follow-up was 2.43 years (SD = 1.37 years) and the longest was 5.94 years. Initial analyses, based on crude estimates of individual annual change (
Annual change of FVC, % FVC, FEV1, and % FEV1 estimated via linear mixed-effects models adjusted for appropriate variables, as shown in
Changes in longitudinal spirometry differed between each spirometry pattern group (
We further examined spirometry measurements as predicted values at the participants' last visit to the WTCEHC stratified by initial spirometry patterns (
When stratified by WTC-related exposure category (
We report longitudinal assessment of spirometry parameters in a group of community members with potential for WTC dust exposures. Our analyses of a group of patients with heterogeneous exposures to environmental contaminants related to the September 11 disaster showed statistically significant temporal improvements in lung function in the group as a whole, with the degree of improvement varying by the pattern of spirometry at enrollment, the category of WTC-related exposure, and smoking status.
We demonstrated overall improvement in spirometry parameters during an average 2.4-year follow-up period in this community cohort enrolled in a treatment program about four years after the WTC disaster on September 11, 2001. These data are in contrast to longitudinal analyses of lung function in those involved in rescue and recovery.(
We demonstrated heterogeneity in response over time among the spirometry patterns. The distribution of the four spirometry patterns in our population was consistent with other populations (
The WTCEHC includes individuals with a variety of potential exposures to the WTC dust and fumes and we grouped patients according to their potential for exposure. Longitudinal changes in lung function differed in these WTC exposure categories, with the Local workers demonstrating the least improvement. The Local worker category included people who worked either within the WTC towers or worked in surrounding buildings, many of whom evacuated on September 11, 2001 and returned to work in the surrounding buildings one week later. This category also had the highest likelihood of dust cloud exposure. We did not see a relationship with dust cloud exposure and temporal longitudinal changes in lung function in the cohort as a whole, however, the possibility remains that this intense exposure combined with subsequent exposures influenced disease pattern and longitudinal change in a specific category. Further detailed characterization of the specific exposure within each of these categories is warranted to improve our understanding of a dose-response relationship. Moreover, the data suggest that close observation of the Local worker group is warranted.
The use of tobacco had an important influence in our findings. In contrast to the group as a whole, we did not detect temporal improvement in lung function among heavy smokers. The finding of a lack of improvement among heavy smokers may be particularly important as the information can be used in counseling WTC-affected patients regarding the importance of smoking cessation.
The longitudinal analyses were modeled with a linear time trend for changes in spirometry over time and showed improvement in lung function over the observation period. However, it would be unreasonable to expect that this improvement would be sustained over prolonged periods of time and we expect the positive changes to be counterbalanced by normal age-related decline in spirometry measurements. Our current data were too sparse at the longer time points for a definitive long-term analysis of this issue. Exploratory analysis using an alternate model with quadratic time trend (data not shown) suggested an initial improvement in lung function followed by a subsequent decline. Future studies with a longer follow-up period will fully characterize the long-term changes in lung function in this population.
There are several potential limitations to this study. Although patients were treated in a standardized manner and were provided medications free of charge, we do not have data to assess medication adherence and thus cannot directly attribute changes in lung function to treatment. Nevertheless, the improvements in FVC and FEV1 suggest the potential for reversibility of airway injury. The possibility exists that the initial spirometry measurements were suboptimal and improved over time with patient experience. However, we used stringent criteria for inclusion of spirometry values making this explanation unlikely. Previous investigators have demonstrated that the reduced FVC pattern is associated with weight gain;(
In summary, we have observed an improvement in lung function among community members of the WTCEHC during their initial years of enrollment. The improvement in lung function suggests reversible injury amenable to treatment. The different initial lung function patterns and their varied responses over time reinforce the heterogeneity of potential lung injury. The effect of tobacco use on lung function reinforces that WTCEHC patients should be urged to avoid other potential sources of lung injury and in particular to stop all exposures to tobacco. Although subjects with abnormal lung function improved, predicted spirometry measurements did not return to normal values and differences were noted between exposure categories. The residual abnormalities reinforce the need for treatment and continued monitoring for populations affected by this environmental disaster and suggest the importance of clinical interventions for other environmental disasters.
We would like to thank Terry Miles for his continued support and advice. We would like to thank Ruchel Ramos and Edith Davis for all their help in administering the program. We would like to thank the members of the WTC Community Advisory Committee for their invaluable advice and efforts on behalf of the program.
The authors have no potential conflicts of interest.
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| FVC | FVC% | FEV1 | FEV1% | |||||
|---|---|---|---|---|---|---|---|---|
| Estimate | 95% CI | Estimate | 95% CI | Estimate | 95% CI | Estimate | 95% CI | |
| Yes | 7 | (-14.3,28.4) | 0.06 | (-0.54, 0.66) | 7.4 | (-9.5,24.3) | 0.32 | (-0.30,0.95) |
| No | Ref | Ref | Ref | Ref | ||||
| Heavy | -49.4 | (-74.8, -24.0) | -1.13 | (-1.85, -0.41) | -25.2 | (-45.3,-5.1) | -0.97 | (-1.72, -0.23) |
| Light/none | Ref | Ref | Ref | Ref | ||||
| Normal | Ref | Ref | Ref | Ref | ||||
| Low FVC | 42.2 | (16.7, 67.7) | 0.85 | (0.13, 1.58) | 22.6 | (2.1,43.0) | 0.81 | (0.53,1.56) |
| Obstructed | -15.8 | (-52.9, 21.3) | -0.55 | (-1.59, 0.49) | 13 | (-17.0, 42.9) | 0.32 | (-0.79,1.43) |
| Obstructed and low FVC | 80.1 | (25.2,135.0) | 2.55 | (1.04,4.07) | 87.2 | (42.1,132.4) | 3.31 | (1.68,4.94) |
| Local workers | Ref | Ref | Ref | Ref | ||||
| Clean-up workers | 35.2 | (4.5, 65.9) | 0.45 | (-0.42,1.31) | 31.7 | (7.4,56.0) | 0.65 | (-0.26,1.55) |
| Resident | 45.8 | (16.6,75.0) | 0.81 | (-0.01,1.63) | 21.6 | (-1.6, 44.8) | 0.6 | (-0.27,1.46) |
| Rescue/recovery | 22.5 | (38.1,126,2) | 2.62 | (1.44,3.80) | 43.4 | (8.7,78.1) | 1.07 | (-0.17,2.31) |
| other | -11.7 | (-79.8,56.5) | -0.71 | (-2.53, 1.10) | 13.2 | (-42.3,68.6) | -0.22 | (-2.19,1.74) |
| No | 27.1 | (-1.9,56.1) | 0.71 | (-0.11, 1.53) | 8.5 | (-14.5, 31.4) | 0.39 | (-0.46, 1.25) |
| Yes | Ref | Ref | Ref | Ref | ||||
All results were from linear regression models adjusted with age, gender, race, BMI, income, and lower respiratory symptom.
After removing outliers, regression models were fit with 820, 841, 828, and 825 subjects for FEV1, FEV1%, FVC, and FVC% respectively.
: P-value<0.05;
: P-value<0.005;
: P-value<0.0005
1Outlier data points more than 1.5 times the interquartile range from the box are not shown.
Baseline characteristics of the WTC EHC longitudinal population (N=946) as whole and stratified by baseline spirometry pattern.
| Variable | Longitudinal population N=946 | Normal N=642 | Low FVC N=193 | Obstructed N=75 | Low FVC/obstructed N=36 | p-value |
|---|---|---|---|---|---|---|
| 0.16 | ||||||
| Mean(SD) | 50.2(11.1) | 50.0(11.4) | 50.5(10.2) | 49.6(10.8) | 53.5(11.3) | |
| 0.08 | ||||||
| Female | 478(50.5) | 340 (53.0) | 93 (48.2) | 32(42.7) | 13(36.1) | |
| Male | 468(49.5) | 302 (47.0) | 100(51.8) | 43(57.3) | 23(63.9) | |
| <.0001 | ||||||
| Hispanic | 429 (52.5) | 304(47.4) | 88(45.6) | 28(37.3) | 9(25.0) | |
| White | 257 (27.2) | 173(27.0) | 41(21.2) | 25(33.3) | 18(50.0) | |
| Black | 163(17.2) | 118(18.4) | 26(13.5) | 15(20.0) | 4(11.1) | |
| Asian | 68(7.2) | 32(5.0) | 28(14.5) | 5(6.7) | 3(8.3) | |
| Other | 29(3.1) | 15(2.3) | 10(5.2) | 2(2.7) | 2(5.6) | |
| 0.05 | ||||||
| ≤15K | 434(46.8) | 284(45.0) | 104(55.3) | 33 (45.2) | 13 (37.1) | |
| 15K-30K | 155(16.7) | 108(17.1) | 31(16.5) | 13 (17.8) | 3(8.6) | |
| >30K | 338(36.5) | 239(37.9) | 53(28.2) | 27(37.0) | 19(54.3) | |
| 0.0023 | ||||||
| Normal | 249(26.3) | 164(25.6) | 47(24.4) | 33(44.0) | 5(13.9) | |
| Over weight | 353(37.3) | 248(38.6) | 63(32.6) | 25(33.3) | 17(47.2) | |
| Obesity | 344(36.4) | 230(35.8) | 83(43.0) | 17(22.7) | 14(38.9) | |
| 0.0016 | ||||||
| ≤5pack-year | 733(78.9) | 512(81.1) | 151(79.5) | 46(63.0) | 24(68.6) | |
| >pack-year | 196(21.1) | 119(18.9) | 39(20.5) | 27(37.0) | 11(31.4) | |
| 0.93 | ||||||
| No | 489(52.4) | 330(52.1) | 104(54.2) | 37(50.0) | 18(51.4) | |
| Yes | 445(47.6) | 303(47.9) | 88(45.8) | 37(50.0) | 17(48.6) | |
| 0.014 | ||||||
| Local worker | 438(46.3) | 294(45.8) | 94(48.7) | 30(40.0) | 20(55.6) | |
| Clean up worker | 247(26.1) | 185(28.8) | 45(23.3) | 12(16.0) | 5(13.9) | |
| Resident | 172(18.2) | 108(16.8) | 39(20.2) | 20(26.7) | 5(13.9) | |
| Rescue/recovery | 67(7.1) | 42(6.5) | 13(6.7) | 8(10.7) | 4(11.1) | |
| Other | 22(2.3) | 13(2.0) | 2(1.0) | 5(6.7) | 2(5.6) | |
| 0.21 | ||||||
| No | 130(13.9) | 94(14.8) | 28(14.7) | 6(8.2) | 2(5.7) | |
| Yes | 802(86.1) | 540(85.2) | 162(85.3) | 67(91.8) | 33(94.3) |
Data were missing on “Caught in WTC dust cloud” for 12 subjects, “Income” for 19 subjects, “Tobacco” for 17 subjects, and “Lower respiratory symptom” for 14 subjects.
P-value were from Chi-square or ANOVA tests comparing baseline characteristic across spirometry pattern subgroups of the longitudinal population.
Estimates of the linear annual change of FEV1 and FVC (ml/year) and FEV1% and FVC% (percent/year) from the linear mixed-effects model for the total longitudinal population
| FVC | FVC% | FEV1 | FEV1% | ||||||
|---|---|---|---|---|---|---|---|---|---|
| No. | Estimate | 95% CI | Estimate | 95% CI | Estimate | 95% CI | Estimate | 95% CI | |
| 946 | 54.4 | (45.0,63.8) | 1.37 | (1.11,1.64) | 36.8 | (29.3,44.3) | 1.12 | (0.85,1.38) | |
| Light/none | 733 | 60.2 | (50.3,70.2) | 1.49 | (1.21,1.78) | 41.9 | (33.7,50.2) | 1.25 | (0.96,1.54) |
| Heavy | 196 | 25.6 | (-1.1,52.3) | 0.81 | (0.14,1.49) | 13.1 | (-4.7,30.9) | 0.47 | (-0.17,1.11) |
| Normal | 642 | 47.3 | (36.5,58.2) | 1.16 | (0.85,1.47) | 29.2 | (20.7,37.7) | 0.82 | (0.50,1.14) |
| Low FVC | 193 | 72.8 | (52.9,92.6) | 2.02 | (1.50,2.54) | 37.8 | (22.9,52.8) | 1.31 | (0.81,1.82) |
| Obstructed | 75 | 17.9 | (-26.5,62.4) | 0.14 | (-1.18,1.45) | 50.2 | (14.2,84.2) | 1.45 | (0.21,2.69) |
| Low FVC/Obstructed | 36 | 122.4 | (45.0,199.8) | 3.93 | (2.18,5.68) | 153.1 | (82.0,224.3) | 5.13 | (2.98,7.28) |
| Local worker | 438 | 28 | (13.0,43.0) | 0.91 | (0.51,1.32) | 24.6 | (12.3,36.8) | 0.81 | (0.39, 1.23) |
| Resident | 172 | 59.5 | (31.3,87.7) | 1.71 | (0.84,2.57) | 44.5 | (25.4,63.5) | 1.57 | (0.76,2.38) |
| Rescue/recovery | 67 | 122.8 | (86.1,159.6) | 3.01 | (2.22,3.81) | 80.4 | (52.3,108.5) | 2.47 | (1.68,3.26) |
| Clean-up worker | 247 | 61.3 | (46.3,76.3) | 1.42 | (1.02,1.82) | 36.3 | (24.2,48.4) | 0.95 | (0.53,1.37) |
Linear mixed effects model with a linear term of time was adjusted for baseline age, BMI, gender, race/ethnicity, income, dust-cloud exposure, WTC exposure category, smoking status, and baseline spirometry pattern.
Linear mixed effects model with a linear term of time within each smoking group was adjusted for baseline age, BMI, gender, race/ethnicity, income, dust-cloud exposure, WTC exposure category, and baseline spirometry pattern.
Linear mixed effects model with a linear term of time within each spirometry pattern group was adjusted for baseline age, BMI, gender, race/ethnicity, income, dust-cloud exposure, WTC exposure category, and smoking status.
Linear mixed effects model with a linear term of time within each exposure category was adjusted for baseline age, BMI, gender, race/ethnicity, income, dust-cloud exposure, smoking status, and baseline spirometry pattern.
: P-value<0.01;
: P-value<0.001;
: P-value<0.0001