Abstract
Objective
The objective of this study was to determine the prevalence of respiratory exposures and the association between respiratory exposures and respiratory disease among veterans deployed to Operation Enduring Freedom and Operation Iraqi Freedom (OEF/OIF) compared with nondeployed veterans of this era.
Methods
Data come from a national health survey of 20,563 deployed and nondeployed OEF/OIF era veterans. Prevalence estimates and adjusted odds ratios were calculated. Results were weighted to represent the population.
Results
Prevalence of at least one respiratory exposure was high among both deployed and nondeployed groups (95% and 70%, respectively). In both groups, those with any respiratory exposure were at an increased risk for reporting a respiratory disease.
Conclusion
Respiratory exposures are highly prevalent and are associated with increased odds of respiratory diseases among the OEF/OIF era population.
Veterans deployed to Afghanistan and Iraq in support of Operation Enduring Freedom (OEF) and Operation Iraqi Freedom (OIF) may encounter a number of potentially harmful respiratory exposures during their time in theater. In Southwest Asia, particulate matter levels are higher than in the U.S., and exposure may come from dust due to storms and motor vehicle disturbance, or emissions from local industries or burn pits.1 Veterans who served in Iraq and Afghanistan have reported concerns about smoke from burning trash and feces and poor air quality during deployment.2,3 This study examines the relationship between service in OEF or OIF, environmental exposures that may impact the respiratory system, and respiratory diseases using data from a population-based health survey of recent veterans.
A number of studies have reported new or increased respiratory diseases among OEF/OEF military personnel following deployment. A survey of returning OEF/OIF soldiers and Department of Defense (DoD) contractors found statistically significant increased respiratory symptoms during deployment compared with pre-deployment.4 In a health survey of returning OEF/OIF military personnel at the end of their deployment or during a rest and recuperation program, nearly 70% reported respiratory illnesses during their deployment, and 17% experienced symptoms severe enough to require medical care.5 A report of surveillance of ambulatory care and hospital visits among deployed OEF/OIF individuals described “excessive” cases of respiratory conditions among both males and females with repeated deployments.6 A study of deployment and medical records data of deployed OEF/OIF military personnel found an increased rate of obstructive pulmonary disease, mainly asthma and bronchitis, for those that deployed once, but not for those that deployed multiple times.7 The Millennium Cohort Study, in a prospective longitudinal study on the health effects of military service among OEF/OIF deployed and nondeployed military members, found those who were deployed had higher rates of new respiratory symptoms than the nondeployed group and a linear relationship between length of deployment and increased respiratory symptoms among Army respondents.8
A review of the literature by Falvo et al9 found that respiratory diseases are common among deployed service members.
Concerns of exposure to airborne hazards during deployment to this region are not unique to the OEF/OIF population. Studies have also evaluated the association between service in the 1990 to 1991 Persian Gulf War and respiratory illnesses, including asthma, bronchitis, and sinusitis. A study of Australian Gulf War veterans found that since their service in the Gulf War, veterans of this war had a higher than expected prevalence of respiratory symptoms and conditions, including asthma and bronchitis, but not poorer lung function, than a military comparison group without similar exposure.10 Another study found a significantly higher prevalence of asthma and bronchitis among deployed Gulf War military personnel than nondeployed military personnel.11 One study using hospitalization data of Gulf War veterans and nondeployed veterans found more hospitalizations for various respiratory diseases, including asthma.12 However, another study found no statistical difference in the prevalence of pulmonary function abnormalities between deployed Gulf War veterans and nondeployed veterans 10 years after the war.13
Several studies have reviewed the relationship between deployment to Southwest Asia, respiratory illnesses, and various environmental exposures. In a case-control study of Gulf War veterans, a significant association was found between asthma and oil well fire smoke exposure.14 Lange et al15 found a dose-response association between oil well fire smoke exposure and asthma and bronchitis among Gulf War veterans. A study on the effects of acute exposure to diesel vapors showed that ill Gulf War veterans had reduced end-tidal CO2; increased systolic blood pressure and respiratory variability; and disorientation, dizziness, and headache, compared with healthy Gulf War veterans.16 A study of deployed Gulf War veterans exposed to 1991 Kuwait oil well fires compared with unexposed veterans did not find that the exposure led to increased hospitalization after the war.17 Among Millennium Cohort Study participants who served in the Army or Air Force and were deployed during OEF/OIF, there was not an elevated risk of respiratory illnesses among those exposed within a three or 5 mile radius of open-air burn pits. However, there was a marginally significant increased risk for respiratory symptoms among Air Force personnel located within a 2 mile radius of the burn pit at Joint Base Balad, compared with Air Force personnel who were not located near a burn pit.18 A study of Army reserve personnel returning from OEF/OIF deployment found that those with more exposures reported greater severity of physical symptoms.19
This analysis describes the relationship between self-reported respiratory exposures during military service, self-reported doctor-diagnosed respiratory conditions, and OEF/OIF service in a sample of 20,563 veteran respondents to a population-based cohort study. Respiratory conditions in this study population were previously analyzed, and deployed veterans were 29% more likely to be diagnosed with sinusitis during or after the start of OEF and OIF than their nondeployed counterparts, but there was no significant difference in asthma or bronchitis risk between the deployed and nondeployed veterans.20 This paper expands on that knowledge by describing the relationship between respiratory exposures and respiratory diseases. The analysis described below addresses some of the weaknesses in the literature by using a population-based cohort from a national survey, including a comparison group for OEF/OIF deployment status, and controlling for smoking status in the analyses. It also adds to the literature on recent veterans and the possible health consequences of their environmental exposures.
METHODS
Data Collection
Data came from the “National Health Survey for a New Generation of U.S. Veterans” (NewGen), a population-based health survey of 30,000 OEF/OIF veterans and 30,000 nondeployed veterans who served in the military between October 2001 and 2008. This study was reviewed and approved by the Washington, DC, Veterans Affairs (VA) Medical Center Institutional Review Board.
The random sample, selected from the Defense Manpower Data Center at the DoD and VA/DoD Identity Repository database, was stratified by branch of service (Air Force, Army, Navy, Marine Corps), unit component (Active Duty, Reserve, National Guard), and sex. Women were oversampled by 20%. Survey questions covered a considerable range of topics such as self-reported mental health, health behaviors, health conditions, doctor and hospital visits, reproductive health, environmental exposures, and use of the VA health care system.
Following a modified Dillman method, veterans in the selected cohort were mailed a 16-page questionnaire package with the option to complete the survey on-line.21 The package contained a $10 check as an incentive to complete the survey. Those who did not respond to the mailing were contacted by telephone with the option to complete the survey by phone. Data collection occurred between August 2009 and January 2011 resulting in 20,563 accepted surveys (34% response rate). A detailed description of the survey methods has been published elsewhere.22
Measures
Asthma, sinusitis, and bronchitis measures were derived from the survey question “Has a doctor ever told you that you have any of the following conditions?” An additional variable for “any respiratory disease” was created to represent any combination of reporting asthma, sinusitis, or bronchitis.
Smoking status was coded as a categorical measure, including current smoker, recent former smoker, former smoker, or never smoked. This variable was developed using the survey question “During the past 12 months have you smoked cigarettes?” and the follow-up questions, “If no, have you ever smoked cigarettes even occasionally?” and “If yes, in what year did you last stop?” Current smokers were defined as those who answered the first question affirmatively; recent former smokers were defined as those who responded negatively to the first question and positively to the second question with year equal to 2001 or later; former smokers were defined as those who responded negatively to the first question and positively to the second question with year equal to 2000 or earlier; never smoked was defined as those who responded negatively to the first and second question.
Respiratory exposures were measured with the following survey questions: “During military service, were you exposed to or did you experience the following?” Response options included dust and sand; burning trash/feces; diesel, kerosene and/or other petrochemical fumes; smoke from oil fires; industrial pollution. Respondents could select “no” or “yes” for each exposure listed. A dichotomous variable was created to indicate an affirmative response to any of the above-listed respiratory exposures. In addition, the five respiratory exposures listed above were summed per individual to create a variable for the number of different exposures (low = one to two different exposures; high = three to five different exposures). Approximately 32% had low exposure count, 55% had high exposure count, and 13% had no exposure.
Self-reported race/ethnicity was coded as Hispanic, non-Hispanic black, non-Hispanic white, non-Hispanic other race, or unknown. Sex was also based on self-reported data. The self-reported education variable was grouped into three levels: high school or less, bachelor’s degree/some college, advanced degree. Respondents were also asked if they had ever used the VA health care system. Respondents reported the number of deployments to OEF and OIF. For these analyses, those who reported at least one deployment but were classified as nondeployed were deleted.
Birth year, unit component, and branch of service were based on administrative data. Birth year was grouped into the following categories: pre-1960, 1960 to 1969, 1970 to 1979, 1980, or later. Unit component was coded as Active Duty, National Reserve, or Guard. Service branch was coded as Army, Air Force, Marine Corps, or Navy.
Statistical Analyses
Weights were created to improve accuracy of the population prevalence estimates by adjusting for the sample design, nonresponse, and misclassification in the sampling frame. Detailed information about the weighting process can be found in a previous publication.23
Unweighted frequency counts and within-group weighted percentages of birth year, sex, service branch, unit component, race/ethnicity, education, smoking status, number of deployments, deployment status, and VA health care system user status were calculated for asthma, bronchitis, sinusitis, and any respiratory disease. Cross-tabs (unweighted frequencies and weighted percentage) of respiratory exposures reported among those reporting respiratory disease were also calculated.
Logistic regression analyses were used to calculate weighted, adjusted odds of respiratory disease stratified by deployment status (deployed to OEF/OIF vs not deployed) while controlling for sex, birth year, race/ethnicity, education, smoking status, unit component, and service branch, and number of OEF/OIF deployments. Adjusted odds ratios (aORs) with 95% confidence intervals (95% CIs) that did not include 1.00 were considered statistically significant. Statistical analyses were conducted using SAS software version 9.1.3 (SAS Institute Inc., Cary, North Carolina). Z-scores and associated P values were calculated to determine significant differences between deployed and nondeployed estimates.
RESULTS
Table 1 presents the unweighted frequencies and weighted percentages of demographic and military characteristics by asthma, bronchitis, sinusitis, and any respiratory disease. Nearly 24% of all respondents reported at least one respiratory disease. The prevalence of having any respiratory disease increased with age, though this pattern was not observed for asthma or bronchitis when examined separately. More women reported respiratory disease diagnoses than men (35% of women reported at least one respiratory disease compared with approximately 22% of men). The Air Force had the highest prevalence of reporting any respiratory disease (26%). Twenty-nine percent of the nondeployed group and nearly 20% of the deployed group reported at least one respiratory disease. The prevalence for any respiratory disease among former smokers was greater than for any other smoking category (approximately 32%). VA health care users had a higher prevalence of reporting any respiratory disease than non-VA users (28% vs 21%, respectively).
TABLE 1.
Self-Reported Prevalence of Respiratory Exposure and Disease (Unweighted n, Weighted %) Among OEF/OIF Veteran Population by Demographic and Military Characteristics; National Health Study for a New Generation of U.S. Veterans, 2009–2011
| Asthma
|
Bronchitis
|
Sinusitis
|
Any Respiratory Disease
|
|||||
|---|---|---|---|---|---|---|---|---|
| N | % | n | % | n | % | N | % | |
| Total | 1,366 | 6.90 | 2,588 | 12.46 | 3,190 | 13.79 | 5,132 | 23.90 |
| Birth year* | ||||||||
| Pre-1960 | 217 | 7.39 | 449 | 14.45 | 725 | 24.67 | 989 | 32.96 |
| 1960–1969 | 418 | 7.84 | 821 | 14.92 | 1,212 | 21.88 | 1,704 | 31.02 |
| 1970–1979 | 386 | 6.80 | 734 | 12.54 | 832 | 13.89 | 1,413 | 23.81 |
| 1980 or later | 345 | 6.37 | 584 | 10.68 | 421 | 7.11 | 1,026 | 18.27 |
| Sex† | ||||||||
| Men | 937 | 6.12 | 1,783 | 11.27 | 2,208 | 12.10 | 3,615 | 21.71 |
| Women | 429 | 10.95 | 805 | 18.65 | 982 | 22.56 | 1,517 | 35.27 |
| Service branch* | ||||||||
| Army | 800 | 7.41 | 1,416 | 12.63 | 1,655 | 13.07 | 2,783 | 23.82 |
| Air Force | 240 | 6.20 | 578 | 13.48 | 810 | 17.63 | 1,147 | 26.13 |
| Navy | 214 | 6.99 | 388 | 12.34 | 525 | 15.15 | 804 | 24.78 |
| Marine Corps | 112 | 5.83 | 206 | 10.39 | 200 | 8.85 | 398 | 19.55 |
| Unit component* | ||||||||
| Active duty | 640 | 8.01 | 1,046 | 13.15 | 1,280 | 14.17 | 2,114 | 25.32 |
| National Guard | 294 | 4.99 | 684 | 11.55 | 815 | 12.63 | 1,301 | 21.47 |
| Reserve | 432 | 6.15 | 858 | 11.77 | 1,095 | 13.99 | 1,717 | 22.93 |
| Race/ethnicity† | ||||||||
| Hispanic | 162 | 7.43 | 207 | 9.41 | 301 | 11.43 | 483 | 20.46 |
| White non-Hispanic | 916 | 6.62 | 1,957 | 13.44 | 2,234 | 13.73 | 3,649 | 24.32 |
| Black non-Hispanic | 206 | 8.48 | 264 | 9.37 | 445 | 15.61 | 680 | 24.44 |
| Non-Hispanic other race | 76 | 6.41 | 149 | 12.94 | 190 | 15.02 | 290 | 23.99 |
| Missing | 6 | 5.07 | 11 | 9.60 | 20 | 15.23 | 30 | 25.07 |
| Education† | ||||||||
| High school or less | 175 | 5.88 | 311 | 10.77 | 300 | 8.45 | 602 | 19.47 |
| Bachelor’s degree/some college | 963 | 6.99 | 1,889 | 12.72 | 2,291 | 14.08 | 3,689 | 24.20 |
| Advanced degree | 227 | 8.24 | 387 | 14.06 | 594 | 22.02 | 834 | 30.46 |
| Missing | 1 | 2.54 | 1 | 1.77 | 5 | 7.42 | 7 | 11.74 |
| Smoking† | ||||||||
| Current smoker | 351 | 6.71 | 846 | 14.98 | 786 | 12.12 | 1,428 | 24.64 |
| Recent former smoker | 197 | 6.96 | 375 | 11.95 | 419 | 12.89 | 719 | 22.60 |
| Former smoker | 168 | 9.12 | 284 | 14.64 | 440 | 21.71 | 624 | 31.70 |
| Never smoked | 598 | 6.53 | 989 | 10.48 | 1,402 | 13.86 | 2,161 | 22.39 |
| Missing | 52 | 7.60 | 94 | 10.54 | 143 | 15.61 | 200 | 23.17 |
| Number of OEF/OIF deployments† | ||||||||
| 0 | 456 | 8.44 | 810 | 14.08 | 965 | 15.11 | 1,572 | 26.48 |
| 1 | 429 | 5.62 | 866 | 11.67 | 1,015 | 12.13 | 1,684 | 21.71 |
| 2 | 264 | 6.21 | 519 | 11.21 | 664 | 13.30 | 1,053 | 22.89 |
| 3+ | 89 | 5.61 | 206 | 12.94 | 273 | 15.46 | 413 | 24.74 |
| Missing | 128 | 7.45 | 187 | 10.96 | 273 | 13.88 | 410 | 22.47 |
| Deployment status† | ||||||||
| Deployed to OEF/OIF | 805 | 5.86 | 1,617 | 11.65 | 1,995 | 12.96 | 3,214 | 22.48 |
| Nondeployed | 561 | 8.24 | 971 | 13.51 | 1,195 | 14.87 | 1,918 | 25.74 |
| VA user status† | ||||||||
| User | 632 | 8.65 | 1,102 | 14.58 | 1,448 | 17.31 | 2,239 | 28.39 |
| Nonuser | 734 | 5.90 | 1,485 | 11.26 | 1,741 | 11.79 | 2,892 | 21.35 |
| Missing | 0 | 6.93 | 1 | 6.93 | 1 | 6.93 | 1 | 6.93 |
OEF/OIF, Operation Enduring Freedom and Operation Iraqi Freedom.
From sampling frame variable.
Self-reported variable.
Table 2 presents the unweighted frequencies and weighted percentages of asthma, bronchitis, sinusitis, and any respiratory disease by respiratory exposures, stratified by deployment status. This table also includes the total percentages of reported respiratory exposures among deployed and nondeployed veterans. Among deployed veterans, 95% reported at least one respiratory exposure; 92% reported dust and sand exposure; 66% reported exposure to burning trash/feces; 84% reported diesel, kerosene, and/or other petrochemical fumes; 38% reported smoke from oil fires; and 42% reported industrial pollution. When looking at exposure levels, 70% reported high exposure count and 25% reported low exposure count. Among the nondeployed, the prevalence of any respiratory exposure was 70%; 58% reported dust and sand; 18% reported burning trash/feces; 54% reported diesel, kerosene, and/or other petrochemical fumes; 10% reported smoke from oil fires; and 19% reported industrial pollution. Twenty-four percent of the nondeployed reported high exposure count and 47% reported low exposure count. Twenty-two percent of deployed veterans reported at least one respiratory condition, while the prevalence among nondeployed was slightly greater at nearly 26%. Within the deployed group reporting any respiratory exposure, approximately 23% reported at least one respiratory disease. Among the nondeployed with any respiratory exposure, 28% reported a respiratory disease. Among the deployed group, smoke from oil fires and industrial pollution had the highest prevalence of respiratory diseases. Reports of exposure to smoke from oil fires had the highest prevalence of respiratory conditions among the nondeployed group. For both the deployed and nondeployed veterans, those in the high exposure count group had greater prevalence of all respiratory diseases.
TABLE 2.
Self-Reported Prevalence (Unweighted n, Weighted %) of Respiratory Exposure and Disease Among OEF/OIF Veteran Population, National Health Study for a New Generation of U.S. Veterans, 2009–2011
| Total
|
Asthma
|
Bronchitis
|
Sinusitis
|
Any Respiratory Disease
|
||||||
|---|---|---|---|---|---|---|---|---|---|---|
| n | % | N | % | n | % | n | % | N | % | |
| Deployed to OEF/OIF | ||||||||||
| Total | 12,940 | 100.00 | 802 | 5.83 | 1,615 | 11.63 | 1,990 | 12.92 | 3,214 | 22.48 |
| Any respiratory exposure | 12,259 | 95.17 | 764 | 5.88 | 1,568 | 11.89 | 1,916 | 13.09 | 3,091 | 22.76 |
| Dust and sand | 11,823 | 91.51 | 742 | 5.95 | 1,517 | 11.94 | 1,860 | 13.25 | 2,997 | 22.95 |
| Burning trash/feces | 8,242 | 65.73 | 551 | 6.14 | 1,133 | 12.49 | 1,351 | 13.57 | 2,190 | 23.61 |
| Diesel, kerosene, and/or other petrochemical fumes | 10,547 | 83.55 | 651 | 5.88 | 1,401 | 12.40 | 1,670 | 13.35 | 2,705 | 23.30 |
| Smoke from oil fires | 4,892 | 38.17 | 354 | 6.94 | 721 | 14.02 | 875 | 15.30 | 1,388 | 26.12 |
| Industrial pollution | 5,462 | 42.18 | 385 | 6.98 | 808 | 13.95 | 1,009 | 15.62 | 1,571 | 26.46 |
| Exposure count | ||||||||||
| Low | 3,281 | 24.82 | 184 | 5.18 | 348 | 9.68 | 458 | 11.04 | 736 | 19.60 |
| High | 8,978 | 70.35 | 580 | 6.13 | 1,220 | 12.67 | 1,458 | 13.82 | 2,355 | 23.88 |
| Not deployed to OEF/OIF | ||||||||||
| Total | 7,006 | 100.00 | 559 | 8.20 | 970 | 13.46 | 1,195 | 14.87 | 1,918 | 25.74 |
| Any respiratory exposure | 5,013 | 70.44 | 440 | 8.83 | 759 | 14.94 | 946 | 16.38 | 1,510 | 28.15 |
| Dust and sand | 4,140 | 57.78 | 363 | 8.76 | 641 | 15.30 | 817 | 17.19 | 1,271 | 28.61 |
| Burning trash/feces | 1,421 | 17.64 | 158 | 11.64 | 251 | 17.55 | 336 | 21.52 | 499 | 33.26 |
| Diesel, kerosene and/or other petrochemical fumes | 3,960 | 54.19 | 351 | 8.98 | 613 | 15.22 | 783 | 17.34 | 1,234 | 29.18 |
| Smoke from oil fires | 878 | 10.31 | 87 | 11.32 | 157 | 19.08 | 221 | 24.26 | 321 | 37.10 |
| Industrial pollution | 1,452 | 19.28 | 159 | 10.81 | 271 | 18.15 | 379 | 23.24 | 535 | 34.17 |
| Exposure count | ||||||||||
| Low | 3,126 | 46.68 | 242 | 7.74 | 419 | 13.39 | 480 | 13.22 | 834 | 25.00 |
| High | 1,887 | 23.76 | 198 | 10.96 | 340 | 17.97 | 2,083 | 22.60 | 676 | 34.32 |
OEF/OIF, Operation Enduring Freedom and Operation Iraqi Freedom.
Table 3 presents the aORs and 95% CIs of models calculating odds for self-report of asthma, bronchitis, or sinusitis, stratified by deployment status among those with respiratory exposures compared with those without. For both deployed and nondeployed veterans, those with any respiratory exposure were at an increased risk for reporting at least one respiratory disease (deployed: aOR = 1.80, 95% CI = 1.41 to 2.29; nondeployed: aOR = 1.70, 95% CI = 1.45 to 2.00). This pattern is demonstrated for each of the separate exposures, as well as high and low exposure counts.
TABLE 3.
Weighted, Adjusted Odds Ratios (aORs), and 95% Confidence Intervals (95% CIs) of Respiratory Diseases Stratified by Deployment Status; National Health Study for a New Generation of U.S. Veterans, 2009–2011
| Asthma | Bronchitis | Sinusitis | Any Respiratory Disease | |
|---|---|---|---|---|
| aOR (95% CI)* | aOR (95% CI)* | aOR (95% CI)* | aOR (95% CI)* | |
| Deployed to OEF/OIF | ||||
| Any respiratory exposure | 1.35 (0.93–1.97) | 2.04 (1.41–2.96) | 1.82 (1.37–2.41) | 1.80 (1.41–2.29) |
| Dust and sand | 1.46 (1.06–2.00) | 1.57 (1.20–2.05) | 1.80 (1.44–2.23) | 1.65 (1.37–2.01) |
| Burning trash/feces | 1.24 (1.01–1.53) | 1.37 (1.18–1.60) | 1.45 (1.27–1.65) | 1.37 (1.23–1.54) |
| Diesel, kerosene, and/or other petrochemical fumes | 1.11 (0.89–1.39) | 1.79 (1.48–2.16) | 1.57 (1.34–1.83) | 1.57 (1.37–1.79) |
| Smoke from oil fires | 1.36 (1.14–1.62) | 1.50 (1.31–1.70) | 1.49 (1.33–1.67) | 1.45 (1.31–1.60) |
| Industrial pollution | 1.39 (1.18–1.65) | 1.49 (1.31–1.69) | 1.51 (1.35–1.69) | 1.50 (1.36–1.65) |
| Exposure count | ||||
| Low | 1.19 (0.80–1.77) | 1.55 (1.05–2.30) | 1.56 (1.16–2.10) | 1.49 (1.15–1.93) |
| High | 1.49 (1.01–2.20) | 2.49 (1.70–3.63) | 2.11 (1.58–2.81) | 2.10 (1.63–2.70) |
| Not deployed to OEF/OIF | ||||
| Any respiratory exposure | 1.44 (1.12–1.86) | 1.76 (1.43–2.15) | 1.68 (1.39–2.03) | 1.70 (1.45–2.00) |
| Dust and sand | 1.23 (0.99–1.53) | 1.60 (1.34–1.91) | 1.67 (1.41–1.98) | 1.51 (1.32–1.73) |
| Burning trash/feces | 1.64 (1.29–2.08) | 1.52 (1.25–1.86) | 1.46 (1.22–1.75) | 1.40 (1.23–1.54) |
| Diesel, kerosene, and/or other petrochemical fumes | 1.38 (1.11–1.71) | 1.55 (1.30–1.85) | 1.68 (1.42–1.98) | 1.62 (1.41–1.87) |
| Smoke from oil fires | 1.53 (1.14–2.04) | 1.67 (1.33–2.09) | 1.55 (1.26–1.91) | 1.61 (1.34–1.93) |
| Industrial pollution | 1.50 (1.19–1.89) | 1.67 (1.38–2.03) | 1.81 (1.52–2.15) | 1.60 (1.37–1.86) |
| Exposure count | ||||
| Low | 1.26 (0.96–1.66) | 1.55 (1.25–1.93) | 1.45 (1.19–1.78) | 1.53 (1.30–1.81) |
| High | 1.92 (1.40–2.62) | 2.32 (1.79–3.00) | 2.54 (2.00–3.21) | 2.27 (1.86–2.77) |
OEF/OIF, Operation Enduring Freedom and Operation Iraqi Freedom.
Adjusted models control for number of deployments, sex, age, race/ethnicity, education, smoking, branch of service, unit component.
Among deployed veterans, those reporting any respiratory exposure were more than two times as likely to report bronchitis (aOR = 2.04, 95% CI = 1.41 to 2.96) and 80% more likely to report sinusitis (aOR = 1.82, 95% CI = 1.37 to 2.41). Among the nondeployed, those with any respiratory exposure were at an increased risk for asthma (aOR = 1.44, 95% CI = 1.12 to 1.86), bronchitis (aOR = 1.76, 95% CI = 1.43 to 2.15), or sinusitis (aOR = 1.68, 95% CI = 1.38 to 2.03). For all veterans, reporting an exposure was associated with an increased risk for bronchitis and sinusitis for each of the separate exposures.
Both low and high exposure counts were associated with bronchitis and sinusitis among deployed and nondeployed veterans. In both groups, only those in the high exposure count group were associated with asthma. When looking at odds ratios resulting from the exposure count models, a dose-response pattern was observed. Z-score tests were calculated to compare differences in point estimates between the deployment groups. Statistically significant differences were found for many comparisons. Notably, among the majority of significant comparisons, the nondeployed veterans had greater odds of respiratory conditions.
DISCUSSION
Findings from this study demonstrate that veterans from the OEF/OIF era have high prevalence levels of respiratory exposures. Ninety-five percent of deployed veterans reported at least one of the five respiratory exposures queried in this study. Dust and sand exposure and diesel, kerosene, and/or other petrochemical fumes were the most frequently reported (92% and 84%, respectively). Our data suggest that respiratory exposures are not only a concern among deployed veterans, but also among nondeployed veterans. Prevalence of exposures was remarkable even among the nondeployed group, with 70% of veterans in the nondeployed group reporting at least one of the five respiratory exposures at some point during their military service. These results indicate that respiratory exposure concerns are a characteristic of all military personnel, not specifically those who deployed to OEF/OIF.
We found an increased risk for respiratory disease among all categories of exposures reported, within both the deployed and nondeployed groups. Consistent with previous reports,15 we found a dose-response relationship between level of exposure and risk for respiratory disease among both deployed and nondeployed, though our findings must be interpreted with caution. Higher number of summed exposures do not necessarily equal greater exposure, as information on the duration, frequency, and magnitude of each exposure was not collected on the survey. In addition, due to the differing time periods of the disease and exposure questions, we are unable to determine temporal causality.
There are some limitations to this study that should be taken into consideration when interpreting the findings. Recall bias is a potential problem with survey data. We are unsure of the actual dates of OEF/OIF deployment, as the survey asks only for the date of last deployment and number of deployments. In addition, we do not know dates of respondents’ entry into the military. Without this information, we were unable to determine if the respiratory condition occurred before or after joining the military or deployment episodes. The survey question regarding respiratory exposures inquires about exposures during military service, not specifically OEF/OIF deployment. Veterans who were not deployed to OEF/OIF but were deployed to other conflicts may have experienced these respiratory exposures. For example, veterans reporting exposure to oil fire smoke may have experienced this during deployment to the 1990 to 1991 Gulf War. In addition, media coverage of respiratory disease among veterans may have influenced reporting in the OEF/OIF deployed group.
There are several notable strengths to this study. Smoking history questions were included on the survey allowing for smoking status to be controlled for in logistic regression models. Although the response rate was 34%, the number of responses was large at 20,563. In addition, the cohort is population-based and survey weights allow for estimates to represent the population. The cohort included both users and nonusers of the VA health care system, as well as deployed and nondeployed veterans.
There has been heightened concern about respiratory diseases and exposures within the DoD and VA since the 1991 Gulf War and VA has taken several steps to address this issue. VA health care facilities employ Environmental Health Coordinators to assist with health concerns related to exposures during military service. Veterans may file a claim for compensation for health conditions they believe were caused by exposure to burn pits during military service. Mandated by Public Law 112–260, the Airborne Hazards and Open Burn Pit (AH&OBP) Registry was opened to eligible service members and veterans on June 19, 2014, with the purpose of determining and monitoring exposure to airborne hazards.24
Results from this study were comparable to similar studies. The 2011 Institute of Medicine (IOM) study found inadequate or insufficient evidence for respiratory diseases related to burn pit exposures.3 A report on exposures and health conditions using data from the AH&OBP Registry reported that working in burn pits was associated with chronic obstructive pulmonary disease, chronic bronchitis, or emphysema.24 Similar to our findings, Lange et al15 found an increased risk for asthma and bronchitis among Gulf War veterans self-reporting exposure to oil well fire smoke. Consistent with our findings, an analysis from the Airborne Hazards and Open Burn Pit Registry found that asthma and chronic bronchitis were associated with dust storm exposure, though these data must be interpreted with caution given the potentially biased nature of the voluntary registry.24
To our knowledge, this is the first study to investigate multiple military respiratory exposures and correlations with respiratory diseases among OEF/OIF veterans and nondeployed veterans at a population level. These findings indicate that, in the OEF/OIF era veteran population, respiratory exposures are highly related to respiratory diseases, and that respiratory exposures and diseases are a concern of deployed and nondeployed veterans. Respiratory exposures should be considered a hazard of military service in general, not solely deployment. Future research on this topic is needed to determine if a causal relationship exists between these exposures and diseases, ideally including biological indicators, such as pre-military and pre-deployment lung capacity measurements.
Acknowledgments
This work was funded by the Department of Veterans Affairs.
Footnotes
The authors report no conflicts of interest and sources of funding.
Contributor Information
Shannon K. Barth, Department of Veterans Affairs, Office of Patient Care Services, Post-Deployment Health Epidemiology Program, Washington, DC.
Erin K. Dursa, Department of Veterans Affairs, Office of Patient Care Services, Post-Deployment Health Epidemiology Program, Washington, DC.
Robert Bossarte, Department of Veterans Affairs, Office of Patient Care Services, Post-Deployment Health Epidemiology Program, Washington, DC; Injury Control Research Center and Department of Behavioral Medicine and Psychiatry, West Virginia University, Morgantown, West Virginia.
Aaron Schneiderman, Department of Veterans Affairs, Office of Patient Care Services, Post-Deployment Health Epidemiology Program, Washington, DC.
References
- 1.US Army Public Health Command, Environmental Medicine Program. Fact Sheet 64-009-0414. “Particulate Matter (PM) Air Pollution Exposures During Military Deployments”. Aberdeen Proving Ground; Maryland: Jun 27, 2014. Available at: https://phc.amedd.army.mil/PHC%20Resource%20Library/Particulate_Matter_Factsheet_64-009-0414.pdf. Accessed September 14, 2016. [Google Scholar]
- 2.Helmer DA, Rossignol M, Blatt M, Agarwal R, Teichman R, Lange G. Health and exposure concerns of Veterans deployed to Iraq and Afghanistan. J Occup Environ Med. 2007;49:475–480. doi: 10.1097/JOM.0b013e318042d682. [DOI] [PubMed] [Google Scholar]
- 3.Institute of Medicine. Long-Term Health Consequences of Exposure to Burn Pits in Iraq and Afghanistan. Washington, DC: The National Academies Press; 2011. Available at: http://www.nationalacademies.org/hmd/Reports/2011/Long-Term-Health-Consequences-of-Exposure-to-Burn-Pits-in-Iraq-and-Afghanistan.aspx. Accessed September 14, 2016. [Google Scholar]
- 4.Roop SA, Niven AS, Calvin BE, Bader J, Zacher LL. The prevalence and impact of respiratory symptoms in asthmatics and nonasthmatics during deployment. Mil Med. 2007;172:1264–1269. doi: 10.7205/milmed.172.12.1264. [DOI] [PubMed] [Google Scholar]
- 5.Sanders JW, Putnam SD, Frankart C, et al. Impact of illness and non-combat injury during Operations Iraqi Freedom and Enduring Freedom (Afghanistan) Am J Trop Med Hyg. 2005;73:713–719. [PubMed] [Google Scholar]
- 6.Department of Defense. Associations between repeated deployments to OEF/OIF/OND, October 2001–December 2010, and post-deployment illnesses and injuries, active component, U.S. Armed Forces. MSMR. 2011;18:2–11. [PubMed] [Google Scholar]
- 7.Abraham JH, DeBakey SF, Reid L, Zhou J, Baird CP. Does deployment to Iraq and Afghanistan affect respiratory health of U.S. military personnel? J Occup Environ Med. 2012;54:740–745. doi: 10.1097/JOM.0b013e318252969a. [DOI] [PubMed] [Google Scholar]
- 8.Smith B, Wong CA, Smith TC, et al. Newly reported respiratory symptoms and conditions among military personnel deployed to Iraq and Afghanistan: a prospective population-based study. Am J Epidemiol. 2009;170:1433–1442. doi: 10.1093/aje/kwp287. [DOI] [PubMed] [Google Scholar]
- 9.Falvo MJ, Osinubi OY, Sotolongo AM, Helmer DA. Airborne hazards exposure and respiratory health of Iraq and Afghanistan veterans. Epidemiol Rev. 2015;37:116–130. doi: 10.1093/epirev/mxu009. [DOI] [PubMed] [Google Scholar]
- 10.Kelsall HL, Sim MR, Forbes AB, et al. Respiratory health status of Australian veterans of the 1991 Gulf War and the effects of exposure to oil fire smoke and dust storms. Thorax. 2004;59:897–903. doi: 10.1136/thx.2003.017103. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 11.Iowa Persian Gulf Study Group. Self-reported illness and health status among Gulf War veterans. A population-based study. The Iowa Persian Gulf Study Group. JAMA. 1997;277:238–245. [PubMed] [Google Scholar]
- 12.Gray GC1, Smith TC, Kang HK, Knoke JD. Are Gulf War veterans suffering war-related illnesses? Federal and civilian hospitalizations examined, June 1991 to December 1994. Am J Epidemiol. 2000;151:63–71. doi: 10.1093/oxfordjournals.aje.a010123. [DOI] [PubMed] [Google Scholar]
- 13.Karlinsky JB, Blanchard M, Alpern R, et al. Late prevalence of respiratory symptoms and pulmonary function abnormalities in Gulf War I veterans. Arch Intern Med. 2004;164:2488–2491. doi: 10.1001/archinte.164.22.2488. [DOI] [PubMed] [Google Scholar]
- 14.Cowan DN, Lange JL, Heller J, Kirkpatrick J, DeBakey S. A case-control study of asthma among U.S. Army GW veterans and modeled exposure to oil well fire smoke. Mil Med. 2002;167:777–782. [PubMed] [Google Scholar]
- 15.Lange JL, Schwartz DA, Doebbeling BN, Heller JM, Thorne PS. Exposures to the Kuwait oil fires and their association with asthma and bronchitis among Gulf War veterans. Environ Health Perspect. 2002;110:1141–1146. doi: 10.1289/ehp.021101141. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 16.Fiedler N, Giardino N, Natelson B, et al. Responses to controlled diesel vapor exposure among chemically sensitive Gulf War veterans. Psychosom Med. 2004;66:588–598. doi: 10.1097/01.psy.0000127872.53932.75. [DOI] [PubMed] [Google Scholar]
- 17.Smith TC, Heller JM, Hooper TI, Gackstetter GD, Gray GC. Are Gulf War veterans experiencing illness due to exposure to smoke from Kuwaiti oil well fires? Examination of Department of Defense hospitalization data. Am J Epidemiol. 2002;155:908–917. doi: 10.1093/aje/155.10.908. [DOI] [PubMed] [Google Scholar]
- 18.Smith B, Wong CA, Boyko EJ, et al. The effects of exposure to documented open-air burn pits on respiratory health among deployers of the millennium cohort study. J Occup Environ Med. 2012;54:708–716. doi: 10.1097/JOM.0b013e31825107f9. [DOI] [PubMed] [Google Scholar]
- 19.Quigley KS, McAndrew LM, Almeida L, et al. Prevalence of environmental and other military exposures concerns in Operation Enduring Freedom and Operation Iraqi Freedom veterans. J Occup Environ Med. 2012;54:659–664. doi: 10.1097/JOM.0b013e3182570506. [DOI] [PubMed] [Google Scholar]
- 20.Barth SK, Dursa EK, Peterson MR, Schneiderman AI. Prevalence of respiratory diseases among veterans of Operation Enduring Freedom and Operation Iraqi Freedom: results from the National Health Study for a New Generation of U.S. Veterans. Mil Med. 2014;179:241–245. doi: 10.7205/MILMED-D-13-00338. [DOI] [PubMed] [Google Scholar]
- 21.Dillman DA. Mail and Internet Surveys: The Tailored Design Method. Hoboken, New Jersey: John Wiley & Sons, Inc; 2007. [Google Scholar]
- 22.Eber S, Barth S, Kang H, Mahan C, Dursa E, Schneiderman A. The National Health Study for a New Generation of United States Veterans: methods for a large-scale study on the health of recent veterans. Mil Med. 2013;178:966–969. doi: 10.7205/MILMED-D-13-00175. [DOI] [PubMed] [Google Scholar]
- 23.Yoon FB, Jang D, Sukasih AM, et al. JSM Proceedings, Mental Health Statistics Section. Alexandria, VA: American Statistical Association; 1996–2008. Adjustments for Misclassification of Deployment Status in a Population Based Health Study of Operation Enduring Freedom and Operation Iraqi Freedom Veterans. 2013. [Google Scholar]
- 24.Post-9/11 Era Environmental Health Program, Post-Deployment Health, Public Health Service, Patient Care Services, Veterans Health Administration, Department of Veterans Affairs. Report on Data from the Airborne Hazards and Open Burn Pit (AH&OBP) Registry. 2015 Jun; Available at: http://www.publichealth.va.gov/docs/exposures/va-ahobp-registry-data-report-june2015.pdf. Accessed May 23, 2016.
