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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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2

Methods and Approach

This chapter describes the committee’s methods and approach to conducting an updated assessment (reassessment) of the Airborne Hazards and Open Burn Pit (AH&OBP) Registry or information collected by it, as required by the committee’s Statement of Task (see Chapter 1, Box 1-2). The first section describes how the committee interpreted its charge. The committee then describes its information-gathering process, which is limited to new data and information available since the 2017 initial assessment (NASEM, 2017), including information gathered through open sessions, information requests, and literature searches. Included in the targeted literature searches is a brief review of the current peer-reviewed literature on health effects associated with exposure to burn pit emissions. The committee then describes the use of exposure registries in general and the considerations that it kept at the forefront when using and interpreting data from the AH&OBP Registry. The final section of the chapter describes the AH&OBP Registry data that the committee requested and received and the methods used to analyze those data, which are then used to support the following chapters. The section also presents descriptive analyses and tables that update some of the analyses conducted for the 2017 initial assessment, including characteristics of the participants, their health, and their exposures. Eligibility to participate in the AH&OBP Registry is based on the locations of deployment and timeframes as defined in Chapter 1, footnotes 1 and 2.

INTERPRETATION OF THE STATEMENT OF TASK

The legislative language that directed the establishment and assessments of the AH&OBP Registry specifically focused on “health effects of exposure to toxic airborne chemicals and fumes caused by open burn pits.”1 Although burn pit emissions are one of the most visible and recognized exposures of military operations in the Southwest Asia theater, several other airborne hazards (e.g., desert dust, diesel exhaust, construction emissions, local industrial pollutants) also can have important impacts on the health of service members and veterans deployed to that environment (IOM, 2011; NASEM, 2016, 2020; NRC, 2010). Therefore, in its interpretation of the charge and at the urging of the Department of Veterans Affairs (VA), the reassessment committee did not limit its assessment to exposures of open burn pits only, but rather took a broader view of the AH&OBP Registry’s ability to ascertain and monitor health effects resulting from exposure to airborne hazards. As airborne hazards were the focus of the committee’s task, other sources of hazards that may have been present, such as those that may be found in water

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1 PL 112-260 Dignified Burial and Other Veterans’ Benefits Improvement Act of 2012 § 201 (a)(1)(B).

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

or soil, while important considerations for the overall deployed environment, were considered to be outside of the committee’s Statement of Task.

The initial assessment committee’s Statement of Task focused on conducting an analysis of data collected in the early months of the registry’s operation and offering observations and recommendations on its operation and the best use of the data; however, the reassessment committee’s Statement of Task is broader with less emphasis on the analysis of registry data. The initial assessment committee also thoroughly reviewed the registry’s self-assessment questionnaire, and the reassessment committee concurs with the previous committee’s findings, conclusions, and recommendations related to the questionnaire. The reassessment committee limited its comments primarily to the changes made to the questionnaire since the 2017 assessment (see Chapter 3).

The reassessment committee looked to related exposure registries, epidemiologic cohorts, and military data sources for best practices and for “effective and prudent” approaches to learning about health conditions likely to result from exposure to airborne hazards and open burn pits. The committee limited its discussion to active registries, cohorts, or data sources that share some characteristic, such as target population or exposure, with the AH&OBP Registry. Some of the data sources examined as alternative means or mechanisms to the registry—i.e., the Individual Longitudinal Exposure Record (ILER) and the Millennium Cohort Study—were specified in the Statement of Task. Other sources, such as the congressionally directed World Trade Center Health Registry and VA’s Gulf War Registry, were chosen because they rely on self-reported health and exposure information and had exposures to similar airborne hazards (e.g., exhaust, jet fuel, particulate matter). These other sources are described in detail in Chapter 4 and are also referenced in discussions throughout the report.

The primary purpose of the AH&OBP Registry is to “ascertain and monitor the health effects of the exposure of members of the Armed Forces to toxic airborne chemicals and fumes caused by open burn pits”;2 however, registries can serve multiple functions which can vary widely from promoting informal communication and outreach to complex, rigorous, long-term medical registries for specific diseases. Therefore, the reassessment committee considered whether the AH&OBP Registry might be of use for any or all of the following purposes or functions that were proposed by law or in publications and written materials, presentations, and open discussions with VA representatives:

  • Research to ascertain health effects associated with exposures to deployment-related airborne hazards and hypothesis generation about exposure–response relationships (etiologic research) (Chapter 5);
  • Population health surveillance to monitor the health of veterans exposed to burn pit emissions and other airborne hazards while deployed (Chapter 6);
  • Health care access and use to improve clinical care (Chapter 7);
  • Informing VA policies and processes, including claims, and improving VA programs to help veterans and service members with deployment exposure concerns (Chapter 8); and
  • Communications and outreach from VA to veterans who had exposure to airborne hazards during deployment, to health care providers, and to other stakeholders, and communications from veterans to VA (Chapter 9).

The committee’s conclusions and recommendations center on the ability of the registry in its current form to perform each stated purpose bulleted above and, when applicable, on ways to improve or augment it.

The Statement of Task asked the reassessment committee to consider the point at which this or any registry that is based on self-reported information would complete its intended purpose and to consider what an end state for the registry would look like. It also asked the committee to consider “what alternative form of surveillance and identification of research candidates would need to be identified if the AH&OBP Registry was closed.” Any policy decision to maintain, expand, or close the AH&OBP Registry will necessarily be based on a range of considerations, including congressional interest and action, VA’s priorities, costs and budget, competing priorities, and value to veterans and stakeholders. The relative weights of those considerations and priorities are not necessarily equal. Because of these competing priorities, which may change over time, the committee does not make a recommendation about the specific end state of the registry.

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2 PL 112-260 Dignified Burial and Other Veterans’ Benefits Improvement Act of 2012 § 201 (a)(1)(B).

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

INFORMATION GATHERING

The reassessment committee used a variety of information-gathering activities to inform its deliberations about the functioning and use of the AH&OBP Registry, including open sessions, information requests to VA and others, and targeted searches of the scientific literature. Prior National Academies’ reports provided additional background. The committee also examined the AH&OBP Registry data itself for likely sources of biases, representativeness, and validity. The descriptive analysis of the data is presented later in this chapter.

A series of virtual public information-gathering sessions were held for the reassessment committee to learn about the operation and use of the AH&OBP Registry and other information sources or exemplars.3 Veterans and veteran service organizations (VSOs) were invited to comment on the AH&OBP Registry at the committee’s first meeting and were encouraged to submit written comments and materials throughout the committee’s deliberations (through June 2022). In addition, the committee heard presentations about the following:

  • AH&OBP Registry operations and use, including a live demonstration and walk-through from VA;
  • VA’s Airborne Hazards and Burn Pits Center of Excellence;
  • ILER from VA and the Department of Defense (DoD);
  • The Millennium Cohort Study from DoD, and VA data linkages to it; and
  • World Trade Center Health Registry from the New York City Department of Health and Mental Hygiene.

Multiple information requests were submitted to the VA Post-Deployment Health Services (renamed to Health Outcomes Military Exposures in July 2021) staff; the committee’s questions and VA’s responses are available in the committee’s public access file.

The following National Academies’ reports provided background and context on burn pit and other deployment exposures and health outcomes:

  • Review of DoD’s Enhanced Particulate Matter Surveillance (NRC, 2010);
  • Long-Term Health Consequences of Exposure to Burn Pits in Iraq and Afghanistan (IOM, 2011);
  • Gulf War and Health, Volume 10: Update of Health Effects of Serving in the Gulf War (NASEM, 2016); and
  • Respiratory Health Effects of Airborne Hazards Exposures in the Southwest Asia Theater of Military Operations (NASEM, 2020).

Literature Searches of Burn Pit Exposures and Health Outcome Associations

The reassessment committee was not tasked with performing a comprehensive assessment of the scientific evidence on any associations between exposure to burn pit emissions (or any particular chemical or toxin) and other airborne hazards in the Southwest Asia theater and health outcomes or with making conclusions regarding the strength of that evidence. The literature search and this brief review are focused specifically on adverse health effects related to burn pit exposures to address service members’ and veterans’ concerns and the congressional intent of the AH&OBP Registry. However, the committee recognizes that the totality of airborne hazards exposures should be the focus of health effects research.

Potential health effects associated with exposure to burn pits have been thoroughly evaluated by earlier National Academies’ reports, as listed in the previous section. The committee examined publications since the last comprehensive search was conducted (NASEM, 2020) to characterize any recent developments about the health effects likely to result from exposure to burn pit emissions. Most studies of burn pit exposure–health outcome relationships rely on self-reports of burn pit exposures or location, such as a base or country (described in Chapter 5), as there is no comprehensive documentation on what was being burned and how often for any of the burn pits. Any air monitoring was infrequent, selective, and conducted at only a few sites and a few times.

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3 Agendas and recordings of the information gathering sessions are available at https://www.nationalacademies.org/our-work/reassessment-of-the-department-of-veterans-affairs-airborne-hazards-and-open-burn-pit-registry.

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

Targeted comprehensive literature searches were conducted of the published peer-reviewed and grey literature. Eight databases were searched by a National Academies professional research librarian—Embase, Medline, PubMed, PubMed Systematic Reviews, Scopus, Web of Science, Cochrane Database of Systematic Reviews, and ProQuest—using title, abstract, and key words. In addition to peer-reviewed articles, the committee examined government- and government-contractor-produced documents and reports and VSO reports when available. Because this report builds on the initial assessment of the AH&OBP Registry, the search covered publications from 2015 (to ensure none were missed) through June 2021; they were limited to English-language and human-only studies. An updated search of the published literature was performed in May 2022, using the same parameters as the first search, with the exception of date parameters from January 2020 to April 30, 2022. Box 2-1 lists the search terms and parameters used.

After combination and de-duplication, the two searches resulted in 81 publications. Studies reviewed by the initial assessment committee or in the recent National Academies’ report, Respiratory Health Effects of Airborne Hazards Exposures in the Southwest Asia Theater of Military Operations (NASEM, 2020), were excluded. Also excluded were reviews that did not offer new analyses, publications that were case studies or case series, conference abstracts, and publications that did not include health conditions or outcomes. After reviews of the full texts, seven studies were found to meet the inclusion criteria.

The included studies are summarized next. Studies of exposure to burn pit emissions and health outcomes that used the AH&OBP Registry questionnaire or data are presented in Chapter 5: Use for Etiologic Research.

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

Gordetsky et al. (2020) examined lung biopsies collected during 2004–2017 from 59 Southwest Asia veterans who underwent clinical evaluation for respiratory symptoms. Nearly half (47%) reported burn pit exposures. Non-necrotizing, poorly formed granulomas were identified in 22 cases (37.2%). The granulomas were mainly bronchiolocentric and were associated with chronic lymphoplasmacytic bronchiolitis, similar to hypersensitivity pneumonitis. Focal chronic lymphocytic pleuritis or focal pleural adhesions or both were seen in 43 (75.4%) biopsies. No stratification or statistical tests were conducted, thus precluding any conclusions about causal associations between exposure to burn pits and abnormal pathology.

In a study of rheumatoid arthritis and military-related exposures, Ebel et al. (2021) identified 1,566 living participants with rheumatoid arthritis in the Veterans Affairs Rheumatoid Arthritis Registry and mailed questionnaires focused on military, agricultural, and occupational inhalant exposures to them; the response rate was 50.9%. Using questionnaire responses and biomarker data from banked DNA/serum samples collected as part of this registry, associations between inhalant exposure and rheumatoid arthritis–related factors were found based on multivariable linear and logistic regression models adjusted for age, sex, race, and tobacco use. Results showed that anti-anti-cyclic citrullinated peptide (an antibody that is a biomarker of rheumatoid arthritis) positivity was statistically significantly associated with self-reported exposure to burn pits (odds ratio [OR] = 1.66, 95% confidence interval [CI] 1.02–2.69) and military waste disposal (OR = 1.74, 95% CI 1.04–2.93).

A new systematic review of studies published between 2001 and 2020 of upper and lower respiratory tract effects related to exposure to burn pits was identified (McLean et al., 2021). The review found that nine studies met inclusion criteria, but outcome measures were heterogeneous across all studies, precluding meta-analysis. Four of the studies (Klein-Adams et al., 2020; Morris et al., 2014, 2020; Powell et al., 2020) used a combination of objective (computerized tomography, pulmonary function tests, and other tests) and subjective measures such as self-reported surveys; four others (Abraham et al., 2014; Liu et al., 2016; Rohrbeck et al., 2016; Smith et al., 2012) used data from the Defense Manpower Data Center (DMDC) in combination with other sources such as AH&OBP Registry and the Defense Medical Surveillance System; and the last (Poisson et al., 2020) used data from a self-reported patient survey to identify any correlation between exposure to burn pits and lower respiratory tract diagnoses. While these studies found that self-reported lower respiratory tract diagnoses appeared to increase as exposure to burn pits increased, no association between burn pit exposure and objective measures of lower or upper respiratory tract disease was identified.

The committee also found two other studies (Mallon et al., 2016, 2019) that focused on novel biomarkers (miRNA, metabolomics, and other high-throughput measures of molecular profiling) and that provided more precise characterization of burn pit exposures and their association with deployment history and deployment outcomes. Preliminary findings from such studies would need to be replicated.

The epidemiologic studies available on airborne hazards—and on burn pits specifically—vary with regard to both their methods and their quality. The new publications discussed here show that health outcomes of burn pit exposures continue to be an area of research and concern. However, the evidence base remains sparse for understanding the association between respiratory and other health outcomes and exposure to airborne hazards encountered during deployment, particularly but not exclusively those due to burn pit emissions.

Searches of Funded Studies on Exposures to Burn Pit Emissions

Prospective, long-term, and outcome-based studies with well-defined a priori research hypotheses and improved exposure assessment are necessary to examine the effects of exposures to burn pit emissions and other airborne hazards related to deployment on the health of service members and veterans to establish causation. Other types of studies, such as mechanistic and toxicologic studies, can also inform causal relationships. The committee is aware of several ongoing research efforts that have been initiated to address the health effects of these exposures. However, VA and DoD and other associated federal agencies have not focused on conducting large, methodologically rigorous epidemiologic studies of the health effects of exposure to burn pit emissions specifically. This may be due, in part, to the limited amount of exposure assessment data and to the extremely difficult task of attempting to disentangle the effects or contribution of several sources of airborne hazards.

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

Because of the dearth of recent publications on burn pit exposure–health outcome associations, the committee searched for funded studies on this topic by federal agencies and programs, specifically VA, DoD, Congressionally Directed Medical Research Programs (CDMRP), the National Institute of Occupational Safety and Health (NIOSH), and the National Institute of Environmental Health Sciences (NIEHS). Each source has a different funding database structure and search options; the search strategy was tailored to each particular database but used the same set of search terms (open burn pit(s), burn pit(s), airborne hazard(s); open burn pit(s) AND exposure(s); burn pit(s) AND exposure(s); airborne hazard(s) AND exposure(s), cancer) and date parameters (2014–2021) to identify abstracts of funded studies. The search for abstracts of funded studies was not filtered by research topics (metabolism, biomarkers, etc.), institution (academic or foundation), principal investigator, research program (Defense Medical Research and Development program, Gulf War illness program, etc.), funding sources (Defense Threat Reduction Agency, Defense Advanced Research Projects Agency, etc.), or types of grants in order to capture any related funded research. The keyword parameters were applied to both public and technical abstracts. In addition to the federal agencies and programs most likely to fund research on exposures to burn pit emissions and health outcomes, the committee also searched for studies funded by VSOs and foundations, including HunterSeven Foundation, Iraq and Afghanistan Veterans of America (IAVA), and Burn Pits 360.

The search identified 8 studies funded by VA, 28 funded by CDMRP, and 38 funded by DoD (28 of which were the same as the CDMRP studies).4 No studies specific to burn pits were identified in the NIOSH or NIEHS databases. After 2021, the VA website search parameter options changed to only allow titles to be searched and not abstracts, resulting in 0 identified studies from 2014 to 2020. However, a search of the NIH RePORTER database for VA-funded studies from 2014 to 2020 resulted in six abstracts that were not identified from the VA database search.

Relevant abstracts included details on the populations of service member or veterans and on their deployment to Southwest Asia locations; used the AH&OBP Registry as the data source; or had methods to measure, quantify, or mitigate burn pit emissions or exposures. Basic science studies of disease in animal models or cell lines that were not caused directly by a simulated exposure to a burn pit or likely contaminants were excluded. The final selected abstracts and studies are given in Box 2-2.

VA Contractor Reports

VA has contracted for consultant analyses (not the National Academies) of the AH&OBP Registry data to be performed under its direction. The reassessment committee addresses these analyses where relevant throughout the report. Within the first year of AH&OBP Registry operations, selected analyses were performed on item nonresponse (Gasper and Kawata, 2015), validation of self-reported exposure to burn pits (Gasper and Kawata, 2015), deployment segments (Ciminera, 2015a), and time to complete the self-assessment questionnaire (Ciminera, 2015b). Other contracted analyses have included descriptions of respiratory morbidity associated with effects of burn pit exposure or country of deployment (VA, 2020a), agreement between self-reported conditions and diagnoses in medical records for Veteran Health Administration (VHA) users (Gasper and Kawata, 2015; VA, 2020b), and linkages with the Joint VA/DoD Mortality Data Repository and the National Death Index to obtain fact and cause of death for registry participants who died between 1997 and 2017 (VA, 2020c). Other contracted analyses have examined motivators and barriers to participation in the AH&OBP Registry (VA, 2021a). VA-directed contractor analyses often present descriptive statistics that use different inclusion or exclusion criteria, stratifications, or methods.

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4 Almost half of the Department of Defense’s medical research funding is administered by the Congressionally Directed Medical Research Programs (CDMRP) (Viergever and Hendriks, 2016), located within the U.S. Army Medical Research and Materiel Command. In 2022, CDMRP listed 30 health conditions or areas of medical research for which Congress has appropriated funding (CDMRP, 2022a), with a focus on the improved prevention, diagnosis, and treatment of diseases, injuries, or conditions that affect service members and their families, and the general public. Among the military-focused programs are the Toxic Exposures Research Program, the Joint Warfighter Medical Research Program, and the Gulf War Illness Research Program. All CDMRP research programs follow the same general multistep process for soliciting, reviewing, and making funding decisions for applications. The Toxic Exposures Research Program seeks to fund research that can advance the state of the science and improve patient care related to many military exposures, including exposures to airborne hazards and burn pits (CDMRP, 2022b).

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

CONSIDERATIONS OF EXPOSURE REGISTRY DATA

Well-designed epidemiologic studies are one of the best means of measuring the strength of associations between exposures and health outcomes, but large epidemiologic cohort studies are expensive and may take years to design, conduct, and assess. Therefore, epidemiologists may use other methods to conduct observational or experimental research studies. Epidemiologic study designs may identify and follow cohorts prospectively or retrospectively. A registry may be used to define a cohort if most of a group of individuals who meet some specified inclusion criteria are enrolled and are followed over time.

Registries are structured systems for collecting and maintaining data on a group of people characterized by a specific disease, condition, exposure, or event as a means to facilitate research, monitor health, or provide information to participants (Gliklich et al., 2014). A registry may be as simple as a patient list, or it may be developed by extensive outreach and require that participants complete lengthy self-assessment questionnaires and provide biologic samples or other physical health data. A registry may be established to serve one or more predetermined scientific, clinical, or policy purposes, such as addressing a public concern (Gliklich et al., 2014), or to help evaluate potential health outcomes resulting from an exposure, especially if the exposure is uncommon or its potential effects are not well characterized (Antao et al., 2015). Such registries are most useful when designed for a specific goal or research question that directs how and what data are to be collected. When designed appropriately, registry-based studies can be used to facilitate research, monitor health, inform policy, or to provide information to participants, especially when cost or time constraints do not allow for more robust epidemiologic studies to be conducted.

Although many registries are established to collect quantitative data, in reality they more often produce qualitative information. For example, registries may serve as a sponsor’s response to public concerns and provide

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

a forum for receiving information from the public or stakeholders. In this way, registries can be used to facilitate communication with and outreach to specific populations, including providing updates on scientific and medical developments, new programs, or new policies relevant to the participants (see Chapter 9). Several registries have been established by government agencies to be responsive to concerned constituents, but that should not be the primary motivation for establishing a registry. Rather, a registry should be based on “the potential for harm from exposure, the potential benefits of a registry, and public concerns” (Antao et al., 2015, p. 1544).

As noted in the 2017 initial assessment, there are inherent limitations in using registries to draw inferences on the strength of an association between an exposure and a health outcome. Registries generally lack the design features, such as sampling, that address biases and increase the representativeness of the cohort. Motivating factors for participation and retention in a registry vary but may include the apparent relevance, importance, and credibility of the registry or its sponsoring organization (Gliklich et al., 2014). Participants may be recruited through active or passive means (or a combination), and participant data may also be collected using active (e.g., clinical examination) or passive (e.g., administrative records) means, or a combination of the two. Registries may collect data on an ongoing basis or at a single point in time, whereas cohort studies typically collect data at specified times (Gliklich et al., 2014). Data based on a single point in time or that are infrequently updated lead to concerns about validity and generalizability. The inclusion criteria are another registry consideration; registries with broader eligibility or that are more easily accessible may include many individuals who are not representative of the eligible population. Other considerations when using registries to draw scientific conclusions about associations and inferences are summarized in Table 2-1. The committee kept these factors in mind as it directed updated analyses and reviewed the AH&OBP Registry data for each of its intended purposes.

TABLE 2-1 Limitations of Registries and Their Potential Effects

Limitation Definition Potential Effect
Self-selection bias Occurs when patients volunteer to enroll in a study because it is likely that their motivation for enrolling into the study makes them significantly different from the target population (Tripepi et al., 2010) Affects representativeness so that findings may not be generalizable to the broader, target population
Misclassification Occurs when sensitivity or specificity of the method to detect or assess exposure or effect is not perfect, that is, exposed or diseased subjects are classified as non-exposed or non-diseased and vice versa (Copeland et al., 1977) May result in distorted magnitude (exaggerated or underestimated) of estimates of an effect
Recall bias Results from imprecise memory of past exposures (Tripepi et al., 2008) Threatens internal validity and may result in distorted magnitude (exaggerated or underestimated) of the estimates of an effect
Self-report bias Occurs when individuals offer self-assessed measures or experiences on exposures, behaviors, or health outcomes. This may occur due to a misunderstanding of the question or response options or to respond in a way that is socially desirable (Rosenmen et al., 2011) May result in distorted magnitude (exaggerated or underestimated) of the estimates of an effect
Lack of follow-up Participants are not followed for development or resolution of health outcomes or experience of new or changes in exposures. Such follow-up can be active or passive May lead to incomplete ascertainment of outcomes and loss of statistical power
Passive data collection Data generated without the active participation of the subject, such as through administrative or electronic medical records (Maher et al., 2019) May lead to missing data
Large numbers of participants May lead to inflated “statistical significance” but not necessarily clinical relevance

SOURCE: Modified from Table 2-3 in NASEM, 2017.

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

DESCRIPTIVE REVIEW OF AH&OBP REGISTRY DATA

This section describes the AH&OBP Registry data and other related data sources received from VA to support the committee’s charge to update and augment the analyses in the initial assessment report (NASEM, 2017). Data presented in this chapter are cited throughout the report. Subsections describe the participants (basic demographics and military characteristics, representativeness to the eligible population, and so forth), reported health conditions, and reported exposures. All analyses were carried out under the committee’s direction by an external subcontractor, Westat, which was chosen because of its experience with and knowledge of VA systems and which maintains a current authority to operate with VA data systems. Data for the committee’s work were transferred directly to Westat by VA; neither committee members nor National Academies staff had access to the raw data, and to further protect the confidentiality of AH&OBP Registry participants only the aggregate results were provided to the committee.

Data Requested and Received

The committee began this aspect of its work by reviewing the analyses in the initial assessment and considering which ones might be augmented. It then drafted an analysis plan, and, based on VA clarifications and subcontractor expertise, the analysis plan was refined and a data request was submitted to VA on February 23, 2021. VA was asked to extend remote access to the committee’s subcontractor for all requested VA datasets through the VA Informatics and Computing Infrastructure (VINCI) workspace. Using VINCI would provide two advantages. First, the data in it are stored in complex relational databases, and access would allow the committee’s subcontractor to directly produce the analytic datasets rather than have VA do it. Second, VINCI access prevents the need for any data or personally identifiable information (such as Social Security numbers used to link datasets) to be stored on non-VA servers. This request was not granted by VA, and the committee’s subcontractor was only able to receive a select number of analysis files that were prepared by VA or its contractors, restricting the information available and the analyses that were possible. The data sources included the AH&OBP Registry self-assessment questionnaire responses, VA sources that would define the population of service members and veterans who are eligible to participate in the AH&OBP Registry, demographic and military characteristic information, and VA enrollment and health care use. The requested data sources, the reasons for requesting them, and the sources received by the committee are described next.

AH&OBP Registry

The AH&OBP Registry consists of two files that store questionnaire data and that are linked using a unique identification code. These are: a main dataset that contains responses to all of the exposure and health condition questions (SAQ Main/Questionnaire Dataset) and a data file that contains information on all deployment segments,5 both verified and added deployments (SAQ Deployment Segment Data/Deployment Dataset). The data request included the full contents of these two files, including paradata (administrative or related data about the questionnaire instrument that are outside of the questions or directions it contains)6 and information from partially completed but not submitted questionnaires, as well as any additional files outside of these two known sources where other data elements of the AH&OBP Registry may be stored. The request also specified a flag to indicate which participants used a waiver7 to enroll in the AH&OBP Registry, as the number of waivers may affect

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5 A deployment—defined as any movement from a service member’s home station to somewhere outside of the continental United States and its territories (VA, 2015) until the service member returns to his or her home station—may include several segments. For example, an individual whose military unit is based in the United States and who is deployed to Kuwait for several days or weeks, then enters Iraq for several months, and returns to Kuwait before returning to the United States would have three deployment segments that would be eligible to include in the AH&OBP Registry. Deployment in total or as individual segments is not restricted to combat areas or operations; individuals or units can be deployed to assist with humanitarian aid, evacuation of U.S. citizens, peacekeeping missions, or for increased security.

6 Paradata include the time that a respondent spent on each question or section, time to complete the entire questionnaire, time of day it was completed, and number of stops and starts. This information is important for assessing questionnaire quality and data accuracy.

7 The committee is aware that at least in the first few months of registry operation waivers were granted to allow individuals who did not meet the eligibility requirements based on deployment locations or timeframes to participate.

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

comparisons with other participants or with the eligible population. Data elements describing characteristics of participants but that were not collected by the registry questionnaire, such as fact of death and separation status, were also specifically requested.

The committee notes that deployment information is necessary to conduct an assessment of exposure information in the registry and should include:

  • Number of eligible deployments,
  • Country of deployment,
  • Primary base location for each deployment as available,
  • Month and year of deployment start and end (dates of deployment were not provided in the initial assessment and are necessary to examine the effects of time on potential recall bias, latency, and other issues related to the quality of data for longitudinal analyses), and
  • Number of days of each deployment.

VA provided a SAS dataset of the AH&OBP Registry data that was extracted June 3, 2021, a data dictionary, and an annotated questionnaire. The registry dataset contained responses to the questionnaire and several variables imported from other sources or calculated (e.g., gender, age, service branch; see Box 2-3), but the dataset did not include data from partially complete questionnaires beyond the last section of the questionnaire viewed. The data dictionary provided the following for each variable: the variable name, question wording, value labels, and notes. The annotated questionnaire included variable names and skip patterns.8

In order to provide the most updated information possible on registry participants, VA provided the committee with a second registry dataset extracted February 1, 2022. Along with the updated AH&OBP Registry data files, VA also provided paradata and clarifications regarding the source of some demographic characteristic variables that were imported from other VA databases into the AH&OBP Registry data files. The AH&OBP Registry data files did not contain information or responses on partial completers (those who did not click “submit”); in those cases the only information was the last questionnaire section viewed. By not having information on partial completers, the committee was not able to conduct analyses that might explain nonresponses in the questionnaire or examine differences between partial completers and full completers (participants) or between partial completers and the eligible population.

The data required cleaning before they could be analyzed. For example, several questions that are part of skip patterns did not have the skip patterns coded in the data. These skip patterns had to be added, but the existence of a skip pattern was not always indicated in the data dictionary or in the questionnaire. Creating a value in the data for valid skips is necessary to conduct analyses, especially of item nonresponse. Some inconsistencies were observed among the annotated questionnaire, the data dictionary, and the data. For example, the response options or values for a given variable in the dataset were sometimes different than those indicated in the annotated questionnaire

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8 Skip patterns are a question or series of questions that are associated with a conditional response. For example, if a respondent answers that they have “never smoked,” questions pertaining to duration or frequency of smoking would not be applicable to them and would be skipped.

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

or the data dictionary. At the time of its deliberations, the committee was aware of several VA contractors and researchers that were also working with AH&OBP Registry data and notes that it is possible that if different cleaning methods or assumptions were applied, it may affect consistency across results.

The February 1, 2022, extract analysis file contained 300,472 registry respondents with a status of “participant.” After cleaning the file, 20,691 individuals (6.9%) had missing questionnaire completion date data, and 1,136 individuals (0.4%) were identified who had no eligible or validated deployment segments; these respondents were subsequently excluded from use in analyses of registry participants. The final dataset used for analysis includes 278,645 participants and 1,190,888 deployment segments. However, not all participants from the first dataset extract from June 3, 2021, remained in the final dataset. Of the 243,458 June 2021 extract participants, 81 had their status changed to a nonparticipant status (66 to eligible, 3 to review for eligibility, and 12 to missing [i.e., they were not in the February 2022 extract file]). The committee notes that additional extracts of these data files would have similar issues where participants do not match exactly between datasets, making it difficult to replicate prior analyses. Moreover, each new extract will need cleaning and cannot immediately be substituted into programs that were used for a prior extract, making the process less than user-friendly.

Veterans Affairs/Department of Defense Identity Repository

The VA/DoD Identity Repository (VADIR) contains the demographic and military characteristic data for AH&OBP Registry participants (and the eligible population). To understand how AH&OBP Registry participants differ from the eligible population, comparisons of demographic and military characteristics between participants and eligible nonparticipants are needed. This information addresses the representativeness of the AH&OBP Registry data, which is particularly important for etiologic research. Furthermore, it can be used to inform VA’s recruitment efforts and identify areas where these efforts could be improved, such as to groups that are underrepresented (e.g., a particular service branch or unit component). Previously, this information was made available by the Contingency Tracking System (CTS)9 extract provided by DMDC and the Gulf War Oil Well Fire Smoke Registry File. The following data were requested:

  • For all eligible service members: sex, month and year of birth, race, ethnicity, education, marital status, service branch, component, number of eligible deployment segments, separation status, separation date, fact of death, and date of death.
  • For each eligible deployment: rank, duty occupational specialty code, start month and year of deployment, end month and year of deployment, length of deployment, and country/countries of deployment.

Other data sources or roster files available to VA may be suitable sources of demographic and deployment information for individuals eligible for the AH&OBP Registry, for example, the United States Veterans Eligibility Trends and Statistics (USVETS) file. Because the CTS was not updated after 2015 and neither USVETS nor VADIR was made available to the committee’s subcontractor, a table shell of demographic and military characteristics was provided to VA to complete for the post-9/11 eligible population. VA used VADIR to complete this table (Table 2-4), and it included gender, age, race/ethnicity, service branch, unit component, number of deployment tours, and deployment country (limited to Afghanistan, Iraq, Kuwait, and other) for 2,368,542 post-9/11 veterans separated from the military as of November 30, 2021.

Gulf War Oil Well Fire Smoke Registry

This registry contains records of all service members who served in Operation Desert Storm and Operation Desert Shield while the oil-well fires were burning to allow for comparisons with eligible nonparticipants of that

___________________

9 In the initial assessment by NASEM (2017), that committee used the CTS, which is a subset of DMDC data, for service personnel who were physically located in the Operation Enduring Freedom and Operation Iraqi Freedom areas of operations or who were specifically identified as directly supporting those missions outside of the designated combat zone, such as aircrew or support personnel. The CTS contains demographic and military characteristics on respondents that is not collected by the registry. The committee was told that the CTS has not been updated since December 2015.

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

era. These data were provided to the National Academies for the initial assessment of the AH&OBP Registry. The request included the following variables:

  • For all eligible service members: sex, month and year of birth, race, ethnicity, education, marital status, service branch, component, number of eligible deployment segments, separation status, separation date, fact of death, and date of death.
  • For each eligible deployment: rank, duty occupational specialty code, start month and year of deployment, end month and year of deployment, length of deployment, and country/countries of deployment.

No data file from the Gulf War Oil Well Fire Smoke Registry was provided. However, because the demographic and military information from it is unlikely to have changed substantially since the initial assessment, this information was taken from Table 4-4 of the initial assessment report. It is presented later in this chapter (Table 2-4) where AH&OBP Registry participants are compared to the eligible population by service era. One limitation of reusing the Gulf War Oil Well Fire Smoke Registry file information as presented in the initial assessment is that the inclusion and exclusion factors cannot be revised.10 As such, the 545,383 individuals who constituted the eligible population for 1990–1991 Gulf War veterans as included in the Gulf War Oil Well Fire Smoke Registry in 2015 were used as the eligible comparison for the current update.11

VA Electronic Health Records

To examine self-reported and diagnosed health conditions, VA electronic health record data were requested for both the entire eligible population and the participants of the AH&OBP Registry who use VA health care. On December 2, 2021, VA provided a data file of 243,331 registry participants (using registry participants from the June 3, 2021, extract) with binary (yes or no) annual VA health care use flags from 1992 to 2021 (no months or days provided). VA did not provide data for 127 registry participants, so the analyses of health care use were restricted to 243,331 registry participants with eligible deployments and VA use data. On April 1, 2022, VA provided a data file of 23,249,138 VA health care system outpatient ICD-10 (International Classification of Diseases, 10th Revision) diagnosis codes and dates (October 2015 through February 1, 2022) corresponding to 199,735 AH&OBP Registry participants. Data for ICD-9 codes were not provided, and therefore diagnoses prior to October, 2015 were not available.

Assuring Quality Control of Analyses

The committee’s subcontractor, Westat, used a variety of systems and procedures to ensure that the committee’s analyses were performed accurately and that the results were high quality. Such processes included a review of the analysis plan and any modifications made to it based on what data were received, checks of raw data files, and a multistep review process of results, as described below.

The first step in ensuring the integrity of the data files received from VA—and therefore the accuracy of the committee’s data analysis—was to generate frequencies of each item in the data files. Data were examined for logic errors, range errors, and other types of errors. Several questions that were part of skip patterns did not

___________________

10 For example, in the initial assessment, a total of 5,621 1990–1991 Gulf War veterans completed the AH&OBP Registry questionnaire; of those, 496 were found to be ineligible and were excluded based on data from the Gulf War Oil Well Fire Smoke Registry file. The 801 participants who were eligible according to the Gulf War Oil Well Fire Smoke Registry file but were ineligible based on questionnaire deployment data were included in the analysis because the DoD data were considered to be the gold standard for determining eligibility when manual verification was not an option (NASEM, 2017).

11 The total number of 1990–1991 Gulf War veterans who served in Southwest Asia as part of Operation Desert Storm and Operation Desert Shield is 696,530 as reported by VA (U.S. Senate, 1998). The Gulf War Oil Well Fire Smoke Registry includes only those individuals who were present in Southwest Asia while the oil-well fires were burning (n = 545,383). The initial assessment committee determined that using the Gulf War Oil Well Fire Smoke Registry would more accurately reflect 1990–1991 Gulf War veterans who were eligible to participate in the Airborne Hazards and Open Burn Pit Registry for comparison purposes.

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

have the skip patterns coded in the SAS data files, making it impossible to distinguish valid skips from missing data; Westat coded the skip patterns in the data. All corrections, updates, or additions to the data were recorded and documented in the SAS analysis programs. Full documentation was maintained on all programs used in the process of building the analysis file.

Each analysis requested by the committee was first reviewed by the subcontractor to ensure that committee’s intent was clear and that the most appropriate statistical methods were used. Then, a research analyst translated the request into detailed specifications for a SAS programmer. Specifications included instructions for constructing new variables and for stratifying the data to specific subgroups (such as deployment by era) as well as statistical procedures to be used. The specifications were reviewed by senior staff prior to sending them to the programmer. All programs used to run the analyses were fully documented by the programmer.

The committee’s analyses required the construction of new variables, including disease measures, such as combining chronic obstructive pulmonary disease (COPD), emphysema, and chronic bronchitis into a single outcome. For each constructed variable, cross-tabulations of the raw variables and the constructed variables were made and reviewed to ensure that all of the variables were coded correctly in the constructed variable. As an additional check, a small sample of variables were selected and reviewed a second time to ensure that the constructed variables were properly coded based on the raw data.

Subcontractor staff met at least weekly to review output from the analyses for accuracy and to determine any potential revisions that the analysis required. National Academies’ staff and committee members were consulted during programing on an as-needed basis. Changes were communicated to the programmer via revised specifications. Before the final written results of an analysis were delivered to National Academies’ staff and committee, they were reviewed internally, typically by senior staff, for accuracy, completeness, and quality. Subcontractor staff who had performed the analyses attended the data-focused portions of the committee meetings. The results were described and reviewed in detail with the committee and requested changes to them or additional analyses were documented by National Academies’ staff and sent to Westat. This iterative process continued throughout the course of the committee’s deliberations.

Analyses Conducted

The reassessment committee has a different Statement of Task than the initial assessment committee, and as such, it was unnecessary to repeat several initial analyses such as the multivariable analyses. Those analyses that were not repeated are discussed first. Then, the committee presents those analyses that were repeated or updated since the initial assessment, including descriptive statistics of the AH&OBP Registry population. The final section describes new and augmented analyses.

Analyses Not Repeated

The initial assessment committee analyzed health outcomes with latencies of more than 6 months and less than 10 years after exposure. Health outcomes were limited to those associated with the respiratory and the cardiovascular systems because these are the most plausible and well-documented health effects associated with airborne hazards and are emphasized in the registry. The multivariable analysis included the outcomes of asthma; emphysema, chronic bronchitis, or COPD as a composite variable; any functional limitation due to a lung or breathing problem; respiratory symptoms as a composite variable; hypertension; and a composite variable of coronary artery disease, angina pectoris, and myocardial infarction. Although separate questions were asked for some of these conditions, that committee chose to group some of them as composite variables because it was concerned about the ability of participants to distinguish among them. A few outcomes in other organ systems were included in the questionnaire, but the initial assessment committee determined that those questions were too general to be of value in its analyses. The initial assessment committee also noted that the health outcomes were not captured with the specificity that would be necessary to draw conclusions about the presence or absence of specific diagnoses in the registry population.

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

The initial assessment committee concluded that the results of its analyses and any identified associations (or lack thereof) might be an artifact of the population’s selection and the limitations of voluntary participation, self-reported exposure and disease data, and potentially other factors unrelated to exposure–disease associations. That committee further stated that the registry analyses are not generalizable and can only describe what exposures and conditions the registry participants are reporting; the registry data cannot be used to determine cause or estimate disease prevalence in the total eligible population of service members or veterans.

The reassessment committee determined that there was no value in recreating or updating the multivariable analyses in the initial assessment because of (1) the lack of representativeness of the AH&OBP Registry participants (see subsequent discussion), (2) the initial assessment committee’s findings of implausible associations between exposures and disease that contradict known associations, and (3) the potential for misinterpreting spurious associations. The committee was concerned about over-interpreting the registry data, so it did not reconstruct the set of metrics to express exposure potential. The reassessment committee also did not repeat the formal nonresponse bias analysis using propensity scores (to compute adjusted disease prevalence estimates) of the initial assessment. This decision was made because without individual-level data for the eligible population (beyond demographic and military characteristics), minimal new information would be expected.

Repeated and Updated Analyses

Descriptive analyses of the participant population and comparisons with the eligible population were repeated, and updated tables are presented under the “Participants” subheading. Other repeated descriptive analyses include question-by-question responses, questions with limited variability, and nonresponse (missing, don’t know, and refused), all presented in Chapter 3. Using time stamp data, updated information on the average time needed to complete the self-assessment questionnaire was calculated.

New and Augmented Analyses

Descriptive analyses show changes of self-reported exposures and health conditions over time. The committee looked for trends based on time of participation, eligible deployment segments or eras, and time between first and last deployment and completion of the AH&OBP Registry questionnaire. Enrollment and VA health care use data were examined among registry participants. Descriptive statistics on reported cancers were calculated.

Time of Participation

The committee stratified registry participants by when they completed the self-assessment questionnaire. “Early” participants were defined as those who completed the questionnaire from AH&OBP Registry inception on June 14, 2014, through July 31, 2015; the same dates—and presumably participants—as in the initial assessment. “Late” participants were defined as those who completed the questionnaire from August 1, 2015, through the data extract date of February 1, 2022—an additional 232,201 individuals. Comparisons of early and late participants may reflect or inform changes in exposures or diagnoses of health conditions or changes in communication or outreach efforts about the AH&OBP Registry.

In other analyses, eligible deployment segments were examined by specific calendar years or era because different time periods may reflect shifts in environmental exposures or operational capabilities. For example, the installation of incinerators around 2009 would decrease exposure to emissions from burn pits. The time between first and last deployment and completion of the AH&OBP Registry questionnaire was also examined, as long periods of time between these two events may affect an individual’s ability to accurately recall the nature, frequency, or intensity of those exposures, or the temporal relationship between a particular exposure and health outcome.

VA Health Care Use

To augment the initial report’s analyses, the committee sought to examine the potential usefulness of and biases associated with linking AH&OBP Registry data to VA health care data to obtain longitudinal health information for registry participants and to compare it with the self-reported health information. VA health care data potentially offer a wealth of information about health outcomes, comorbidities, and health care use over a long period of time and with greater accuracy than self-reports. However, analyses of VA health care data are

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

only applicable for those veterans who are eligible for that health care and who choose to use it (see Chapter 7). Follow-up of active-duty service members, veterans not eligible for VA health care, and veterans who choose to receive care from non-VA providers is not possible using VA health care records. One analysis of VA health care services among 1990–1991 Gulf War veterans that used those services between January 1, 2008, and December 31, 2018, noted that more than 50% of veterans did not use the VA health care system (Dursa et al., 2020). Furthermore, the population of veterans who use VA health care for all of their health care needs differs from the entire veteran population and from those who do not use VA health care (e.g., VA users have higher prevalence of 21 chronic conditions than non-VA users [Dursa et al., 2016]). Therefore, the committee sought to link VA health care use with clinical encounter information for registry participants enrolled in VHA to understand whether their characteristics are connected to their use of VA health care.

Exposure Concordance

The committee conducted analyses to determine crude concordance between self-reported exposure to burn pits and actual burn pit location data using two different methods. This is described at the end of the chapter under Exposures.

Participants

This section describes the demographic and military characteristics of individuals who chose to participate in the AH&OBP Registry. The committee examined how well the participants reflected the larger eligible population and whether the characteristics of late participants were different than early participants. The final AH&OBP Registry data analysis set contained 278,645 participants and a total of 1,190,888 deployment segments. There does not appear to be a minimum number of days for a deployment to be counted as eligible. Participants were separated into mutually exclusive eras based on their eligible deployment segments:

  • 1990–1991 Gulf War: deployment that started on or before April 6, 1991;
  • Peacetime: deployment between April 7, 1991, and October 6, 2001;
  • Operation Enduring Freedom (OEF)/Operation Iraqi Freedom (OIF)/Operation New Dawn (OND): deployment between October 7, 2001, and December 31, 2014; and
  • Combined Joint Task Force–Operation Inherent Resolve (OIR)/Operation Freedom’s Sentinel (OFS): deployment ended on or after January 1, 2015.

Deployments with more than one era flag were categorized as “multiple eras.” Among AH&OBP Registry participants, 1.5% served only in the 1990–1991 Gulf War and 76.2% of participants served post-9/11; 21.1% of participants served in multiple eras (Table 2-2). Of those who served in multiple eras, the majority (11.9% of all participants) served in OEF/OIF/OND and OIR/OFS.

Location of deployment was examined in two ways: first by individual and second by deployment segments. An individual may have had multiple deployments (mean = 4.3, median = 3) to several countries or areas in Southwest Asia. Therefore, in Table 2-3 there are 278,645 individual participants in the AH&OBP Registry, but the column totals are more than the number of participants. The countries with the highest percent of ever deployments are Iraq (58.2%), Kuwait (50.7%), and Afghanistan (45.2%), and very few deployments were to eligible bodies of water (i.e., Arabian Sea, Gulf of Aden, Gulf of Oman, Persian Gulf, or Red Sea).

When location by deployment segments was used, most were to Iraq (30.0%), Kuwait (34.3%), and Afghanistan (22.1%) (Table 2-3). As discussed in Chapter 1, deployment segment eligibility is expanding to additional countries, such as Syria, Uzbekistan, and Egypt; however, they are not yet captured in the registry data as of February 1, 2022, and therefore are not included as possible countries in the tables.

The committee then examined other military and demographic characteristics stratified by era of service (Table 2-4). Era of service is limited to 1990–1991 Gulf War and post-9/11 operations because information on the eligible population was not available for the Peacetime era or for specific post-9/11 operations (such as differentiating OFS and OIR from OEF, OIF, and OND). As a percentage of the entire eligible population, by 2015 only 1.0% of eligible 1990–1991 Gulf War era veterans had completed the registry questionnaire, and only 1.7% of eligible

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

TABLE 2-2 Number of AH&OBP Registry Participants by Era of Service

Deployment Era Total N
(n = 278,645)
Total % Early % Late %
Gulf War 4,260 1.5 2.2 1.4
Peacetime 3,223 1.2 0.5 1.3
OEF/OIF/OND 193,361 69.4 79.8 67.3
OIR/OFS 18,903 6.8 0.0 8.1
Multiple Eras 58,898 21.1 17.5 21.9
OEF/OIF/OND + OIR/OFS 33,147 11.9 5.0 13.3
Gulf War + Peacetime 9,617 3.5 5.3 3.1
Peacetime + OEF/OIF/OND 7,495 2.7 3.0 2.6
Gulf War + Peacetime + OEF/OIF/OND 4,955 1.8 2.9 1.6
Gulf War + OEF/OIF/OND 1,882 0.7 0.9 0.6
Peacetime + OEF/OIF/OND + OIR/OFS 1,236 0.4 0.2 0.5
Gulf War + Peacetime + OEF/OIF/OND + OIR/OFS 303 0.1 0.1 0.1
Gulf War + OEF/OIF/OND + OIR/OFS 130 0.1 <0.1 0.1
Peacetime + OIR/OFS 79 <0.1 0.0 <0.1
Gulf War + Peacetime + OIR/OFS 40 <0.1 <0.1 <0.1
Gulf War + OIR/OFS 14 <0.1 <0.1 <0.1

TABLE 2-3 Countries and Areas of Deployment by Participants and Eligible Segments

Country or Area of Deployment Unique Participants
n (%)
Deployment Segments
n (%)
Afghanistan 126,043 (45.2%) 262,992 (22.1%)
Arabian Sea 1,503 (0.5%) 2,523 (0.2%)
Bahrain 7,299 (2.6%) 10,749 (0.9%)
Djibouti 18,033 (6.5%) 27,773 (2.3%)
Gulf of Aden 378 (0.1%) 500 (<0.1%)
Gulf of Oman 426 (0.2%) 477 (<0.1%)
Iraq 162,183 (58.2%) 357,633(30.0%)
Kuwait 141,365 (50.7%) 407,984 (34.3%)
Oman 3,538 (1.3%) 4,098 (0.3%)
Persian Gulf 4,961 (1.8%) 7,005 (0.6%)
Qatar 37,007 (13.3%) 63,703 (5.4%)
Red Sea 1,731 (0.6%) 2,680 (0.2%)
Saudi Arabia 23,896 (8.6%) 28,173 (2.4%)
United Arab Emirates 9,788 (3.5%) 14,598 (1.2%)
Total 278,645 1,190,888

NOTE: Participants can be deployed to more than one country. Although Syria, Uzbekistan, and Egypt have become eligible deployment locations, they were not reflected in the AH&OBP Registry data as of February 1, 2022.

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

TABLE 2-4 Percent Differences of Select Demographic and Military Characteristics of Participants and Full Eligible Population, Stratified by Era of Service

1990–1991 Gulf War Post-9/11
Respondents
(n = 21,201)
All Eligibles
(n = 545,383)
Percent Difference* Respondents
(n = 261,423)
All Eligibles
(n = 2,368,542)
Percent Difference*
n (%) n (%) n (%) n (%)
Sex
Male 19,069 (89.9%) 507,167 (93.0%) -3.0 224,237 (85.8%) 2,076,591 (87.7%) -1.9
Female 1,724 (8.1%) 37,175 (6.8%) 1.3 28,240 (10.8%) 291,890 (12.3%) -1.5
Missing 408 (1.9%) 1,041 (0.2%) 1.7 8,946 (3.4%) 61 (0.0%) 3.4
Age (years)
<30 -- -- -- 33,280 (12.7%) 197,140 (8.3%) 4.4
30–39 -- -- -- 109,313 (41.8%) 994,807 (42.0%) -0.2
40–49 7,925 (37.4%) 265,696 (48.7%) -11.3 76,584 (29.3%) 647,210 (27.3%) 2.0
50–59 10,637 (50.2%) 148,541 (27.2%) 22.9 29,309 (11.2%) 394,467 (16.7%) -5.4
60+ 2,453 (11.6%) 45,140 (8.3%) 3.3 3,701 (1.4%) 134,902 (5.7%) -4.3
Missing 186 (0.9%) 86,006 (15.8%) -14.9 9,236 (3.5%) 16 (0.0%) 3.5
Mean age (years) 50.8 49.9 -- 38.1 41.5 --
Race
White 13,085 (61.7%) 362,828 (66.5%) -4.8 178,807 (68.4%) 1,533,417 (64.7%) 3.7
Black 4,887 (23.1%) 130,311 (23.9%) -0.8 31,133 (11.9%) 354,145 (15.0%) -3.0
Hispanic 1,045 (4.9%) 27,774 (5.1%) -0.2 28,922 (11.1%) 235,292 (9.9%) 1.1
Other 1,187 (5.6%) 22,755 (4.2%) 1.4 18,600 (7.1%) 224,677 (9.5%) -2.4
Missing 997 (4.7%) 1,715 (0.3%) 4.4 3,961 (1.5%) 21,011 (0.9%) 0.6
Branch
Air Force 2,274 (10.7%) 56,089 (10.3%) 0.4 63,960 (24.5%) 444,948 (18.8%) 5.7
Army 14,009 (66.1%) 306,834 (56.3%) 9.8 148,792 (56.9%) 1,103,078 (46.6%) 10.3
Marine Corps 2,208 (10.4%) 80,219 (14.7%) -4.3 27,328 (10.5%) 359,438 (15.2%) -4.7
Navy/Coast Guard 1,535 (7.2%) 102,241 (18.7%) -11.5 19,665 (7.5%) 461,078 (19.5%) -11.9
Other 59 (0.3%) -- 0.3 780 (0.3%) -- 0.3
Missing 1,116 (5.3%) -- 5.3 898 (0.3%) -- 0.3
Unit component
Active Duty 9,077 (48.4%) 460,153 (84.4%) -35.9 117,507 (51.4%) 1,777,161 (75.0%) -23.7
Reserves/National Guard 9,444 (50.4%) 85,229 (15.6%) 34.8 107,743 (47.1%) 591,381 (25.0%) 22.1
Missing 218 (1.2%) 1 (0.0%) 1.2 3,562 (1.6%) -- 1.6
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
1990–1991 Gulf War Post-9/11
Respondents
(n = 21,201)
All Eligibles
(n = 545,383)
Percent Difference* Respondents
(n = 261,423)
All Eligibles
(n = 2,368,542)
Percent Difference*
n (%) n (%) n (%) n (%)
Country of deployment
Iraq only 4,507 (21.3%) 108,978 (20.0%) 1.3 101,043 (38.7%) 597,856 (25.2%) 13.4
Kuwait only 3,160 (14.9%) 70,658 (13.0%) 1.9 -- -- --
Iraq and Kuwait 3,935 (18.6%) 90,734 (16.6%) 1.9 -- -- --
Neither Iraq nor Kuwait 9,599 (45.3%) 275,013 (50.4%) -5.1 -- -- --
Afghanistan only -- -- -- 68,224 (26.1%) 369,159 (15.6%) 10.5
Iraq and Afghanistan -- -- -- 57,797 (22.1%) 165,985 (7.0%) 15.1
Neither Iraq nor Afghanistan -- -- -- 34,359 (13.1%) 1,235,542 (52.2%) -39
Eligible deployment segments
1 11,815 (55.7%) 209,544 (38.4%) 17.3 58,458 (22.4%) 1,093,718 (46.2%) -23.8
2 2,946 (13.9%) 192,375 (35.3%) -21.4 46,145 (17.7%) 652,644 (27.6%) -9.9
3 1,684 (7.9%) 110,727 (20.3%) -12.4 34,827 (13.3%) 327,221 (13.8%) -0.5
4 1,115 (5.3%) 25,393 (4.7%) 0.6 26,332 (10.1%) 145,192 (6.1%) 3.9
5 748 (3.5%) 7,344 (1.3%) 2.2 21,522 (8.2%) 66,445 (2.8%) 5.4
6 541 (2.6%) -- 2.6 16,939 (6.5%) 33,459 (1.4%) 5.1
7 465 (2.2%) -- 2.2 12,779 (4.9%) 18,404 (0.8%) 4.1
8 413 (1.9%) -- 1.9 9,610 (3.7%) 10,552 (0.4%) 3.2
9 295 (1.4%) -- 1.4 7,409 (2.8%) 6,604 (0.3%) 2.6
10+ 1,179 (5.6%) -- 5.6 27,402 (10.5%) 14,303 (0.6%) 9.9

NOTES: Because of the way this table was generated for the initial assessment report and updated here, some categories are combined, whereas the preference would be to present them separately; these include National Guard and reserves (under Component), Navy and Coast Guard (under Branch), and countries that are not Iraq, Afghanistan, or Kuwait. Unit component was not included in the February 1, 2022, extract, but was included in the June 3, 2021, extract; therefore the unit component is based on the June 2021 extract, which had 18,739 1990–1991 Gulf War era participants and 228,812 post-9/11 era participants. The VA-provided data from VADIR on post-9/11 eligibles used the phrase “deployment tours,” and the metric does not appear comparable to deployment segments as reported on the registry. When asked for clarification on this variable, VA responded that it is from a VADIR variable called “Tour Count” and that it should not collapse shorter deployment segments, which the committee interpreted to mean that it should match, but as can be seen, there is a large discrepancy.

* Percent difference indicates the percentage differences for a characteristic, i.e., respondent percentages minus eligible percentages.

post-9/11 era veterans had initially completed the questionnaire. After nearly 7 years of AH&OBP Registry operations, the completion rate has increased to 3.9% and 11.0% for these eras, respectively. Although the questionnaire completion rate continues to be low, the absolute number of registry participants is large, as shown in Table 2-4.

Registry participants are not representative of the total eligible population or by the era of service based on their demographic and military characteristics. Notably, relative to the eligible 1990–1991 Gulf War population, registry participants who served in this era are more likely to be women and over 50 years of age. They were also more likely to have served in the Army and in the National Guard or reserves. Finally, they had a notably different distribution of eligible deployment segments, with 55.7% having a single deployment compared with 38.4% of the entire eligible population. Comparisons of post-9/11 participants to the eligible population of that era found that registry participants were less likely to be women and 50 years of age or older. They were more likely to be less than 30 years of age and of White race. Post-9/11 registry participants were more likely to have served in the Army

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

and Air Force and in the National Guard or reserves and more likely to have been deployed to Iraq or Afghanistan as well as to have had more deployment segments. Defining the eligible population is also difficult, as it is ever-growing as more service members are deployed or redeployed and new countries or deployment locations, such as Syria, Egypt, and Uzbekistan, are made eligible for the AH&OBP Registry (see Chapter 3).

Participants by Time of Completion

To examine how the characteristics of registry participants had changed since the initial assessment, participants were stratified into early and late by time of participation, as described previously. The initial assessment included 46,404 registry participants; however, in the committee’s AH&OBP Registry file extracted February 1, 2022, 46,444 registry participants had completed the questionnaire as of July 31, 2015—40 more participants than in the initial assessment. There is no way to verify that all of the 46,404 participants included in the initial assessment data are the exact same as those included in the early strata in the current dataset. Although this discrepancy is small, because access to the dataset used for the initial assessment was destroyed per the data use agreement at the release of that report, it is impossible to pinpoint the reason for this small discrepancy. This also reinforces the earlier observation that extracts of these data files do not match included participants exactly, making it difficult to replicate analyses.

Table 2-5 presents descriptive statistics of demographic and military characteristics for the eligible population (does not include Peacetime era and not all characteristics are available), all the AH&OBP Registry participants in the committee’s dataset, and participants by date of registry participation (i.e., early and late participation). Several differences in these demographic and military characteristics can be seen, especially between early and late participants as shown in the “percent difference” column. These statistics are described in more detail in Chapter 3. With regard to the deployment era, 79.8% of early participants served during OEF/OIF/OND only, 2.2% during the 1990–1991 Gulf War only, and 17.5% during multiple eras. The late participants had fewer 1990–1991 Gulf War–only (1.4%) and OEF/OIF/OND-only (67.3%) deployments and more deployments for Peacetime-only (1.3%), OIR/OFS-only (8.1%), and multiple eras (21.9%). Late participants had fewer eligible deployment segments and shorter cumulative deployment durations than early participants. In general, early and late registry participants vary slightly in demographic and service characteristics, with the most notable variation being in deployments, military branches, and age (Table 2-5).

Verification of Deployment Segments

Eligible individuals who consent to participate in the registry are first asked to verify the dates and locations of eligible deployment segments according to information contained in VADIR. The questionnaire lists the individual’s eligible deployment segment records, and participants can confirm the system data, correct them, or enter additional deployment history information. Individuals can modify the dates of deployment, add missing deployments, and select or enter the bases they served at while deployed. The initial assessment report committee heard from veterans who had participated in the registry that the process of updating deployment information and entering the names of bases and dates was difficult and frustrating. A 2021 demonstration of this questionnaire to the reassessment committee confirmed that this process of entering names of bases and dates remains difficult (VA, 2021b).

The registry records whether the deployment segment information was indicated by the participant as accurate (verified) or the participant changed the presented information (user-entered). Of the total 1,190,888 eligible deployment segments in the committee’s registry data file, 77.4% (n = 921,203) were verified as correct and 22.6% (n = 269,685) were user-entered. To determine why so many deployment segments had inaccurate information for registry participants, the committee conducted several analyses that examined whether certain military- or deployment related characteristics were more likely to be associated with either verified or user-entered deployments. The analyses might indicate whether system-level changes are necessary to more accurately identify or code deployment segments as eligible. Whether a segment was verified or user-entered was strongly related to

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

TABLE 2-5 Percent Distribution of Various Characteristics of Early and Late Participants

Characteristic Population Total
(n = 2,913,925)
(%)
All Participants
(n = 278,645)
(%)
Early Participants
(n = 46,444)
(%)
Late Participants
(n = 232,201)
(%)
Percent Difference**
Sex
Male 88.7 86.0 76.6 87.9 11.3
Female 11.3 10.7 8.8 11.1 2.3
Missing 0.0 3.3 14.7 1.0 -13.6
Age at questionnaire completion (years)
<30 6.8 11.9 17.0 10.9 -6.1
30–39 34.1 39.3 38.7 39.4 0.7
40–49 31.3 29.8 31.0 29.5 -1.5
50–59 18.6 13.4 11.6 13.8 2.2
60 or older 6.2 2.2 1.7 2.3 0.6
Missing 3.0 3.4 <0.1 4.0 4.0
Race
White 65.1 68.1 73.3 67.0 -6.3
Black 16.6 12.6 10.3 13.0 2.7
Hispanic 9.0 10.6 8.0 11.2 3.1
Other 8.5 7.0 6.1 7.1 1.0
Missing 0.8 1.8 2.3 1.7 -0.6
Branch
Air Force 17.2 23.9 18.2 25.0 6.8
Army 48.4 56.9 65.4 55.2 -10.2
Marine 15.1 10.5 10.3 10.5 0.2
Navy* 19.3 7.4 5.0 7.9 2.9
Coast Guard* 0.2 0.3 0.2 -0.1
Other (includes Public Health Service, missing and unknown service branches) 0.0 1.1 0.8 1.2 0.4
Unit component
Active Duty 76.8 50.8 46.5 51.9 5.4
Reserves* 23.2 30.9 31.4 30.8 -0.6
National Guard* -- 16.7 20.2 15.9 -4.3
Missing 0.0 1.5 1.9 1.5 -0.4
First deployment
Before 1990 -- <0.1 0.0 <0.1 0.0
Before 1992 -- 8.4 12.3 7.6 -4.7
Before 2001 -- 4.4 3.7 4.6 0.9
Before 2015 -- 80.4 84.0 79.7 -4.3
2015 or later -- 6.8 <0.1 8.1 8.1
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Characteristic Population Total
(n = 2,913,925)
(%)
All Participants
(n = 278,645)
(%)
Early Participants
(n = 46,444)
(%)
Late Participants
(n = 232,201)
(%)
Percent Difference**
Last deployment
Before 1992 -- 5.1 7.6 4.6 -3.0
Before 2001 -- 1.1 0.4 1.2 0.8
Before 2015 -- 74.5 86.6 72.0 -14.6
2015 or later -- 19.3 5.4 22.1 16.8
Deployment era
Gulf War only -- 1.5 2.2 1.4 -0.8
Peace Time only -- 1.2 0.5 1.3 0.8
OEF/OIF/OND only -- 69.4 79.8 67.3 -12.5
OIR/OFS only -- 6.8 <0.1 8.1 8.1
Multiple Eras -- 21.1 17.5 21.9 4.4
Gulf War + Peacetime -- 3.5 5.3 3.1 -2.2
Gulf War + OEF/OIF/OND -- 0.7 0.9 0.6 -0.3
Peacetime + OEF/OIF/OND -- 2.7 3.0 2.6 -0.3
Gulf War + Peacetime + OEF/OIF/OND -- 1.8 2.9 1.6 -1.4
Gulf War + OIR/OFS -- <0.1 <0.1 <0.1 0.0
Peacetime + OIR/OFS -- <0.1 0.0 <0.1 0.0
Gulf War + Peacetime + OIR/OFS -- <0.1 <0.1 <0.1 0.0
OEF/OIF/OND + OIR/OFS -- 11.9 5.0 13.3 8.2
Gulf War + OEF/OIF/OND + OIR/OFS -- <0.1 <0.1 0.1 0.1
Peacetime + OEF/OIF/OND + OIR/OFS -- 0.4 0.2 0.5 0.3
Gulf War + Peacetime + OEF/OIF/OND + OIR/OFS -- 0.1 0.1 0.1 0.0
Number of deployments
1 44.7 26.2 22.4 26.9 4.5
2 29.0 17.2 14.3 17.8 3.5
3 15.0 12.7 11.6 12.9 1.3
4 5.9 9.5 9.6 9.5 -0.1
5 2.5 7.8 8.6 7.6 -1.0
6 1.1 6.1 7.3 5.8 -1.5
7 0.6 4.6 5.6 4.4 -1.2
8 0.4 3.5 4.3 3.3 -1.1
9 0.2 2.7 3.4 2.5 -0.9
10 or more 0.5 9.8 12.9 9.2 -3.6
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Characteristic Population Total
(n = 2,913,925)
(%)
All Participants
(n = 278,645)
(%)
Early Participants
(n = 46,444)
(%)
Late Participants
(n = 232,201)
(%)
Percent Difference**
Duration of deployments
<3 months -- 5.0 2.9 5.4 2.5
3–6 months -- 13.0 11.2 13.3 2.2
6–9 months -- 18.8 16.8 19.2 2.4
9–12 months -- 16.3 17.0 16.1 -0.9
1–2 years -- 30.8 33.9 30.1 -3.8
Longer than 2 years -- 16.2 18.2 15.8 -2.3

NOTE: This eligible population excludes the Peacetime era between the Gulf War and post-9/11 eras.

* Percent distributions for these sections have been merged; the percentage applies to the combined total population distribution.

Because of the way this table was generated for the initial assessment report and updated here, some categories are combined, where the preference would be to present them separately; these include National Guard and reserves (under Component), Navy and Coast Guard (under Branch), and countries that are not Iraq, Afghanistan, or Kuwait. Unit component was not included in the February 1, 2022, extract, but was included in the June 3, 2021, extract; therefore, the unit component is based on the June 2021 extract, which had 46,444 early participants and 232,201 late participants.

** Percent difference indicates the difference in percentages between early and late participants in each of the characteristics, i.e., early participant percentages minus late participant percentages.

era of service, with pre-2001 deployments much more likely to be user-entered. In particular, of the 40,963 eligible 1990–1991 Gulf War and Peacetime deployment segments, 92.1% were user-entered, whereas 20.2% of all eligible post-9/11 segments (n = 1,149,925) were user-entered (see Table 2-6). When user-entered deployment segments were examined by country of deployment for those participants with a deployment start date before September 11, 2001, all deployment segments to Afghanistan, the Arabian Sea, Djibouti, the Gulf of Aden, the Gulf of Oman, the Persian Gulf, and the Red Sea were user-entered. For post-9/11 deployments, the areas with the highest proportion of user-entered deployments were to the Gulf of Oman (59.0%), the Gulf of Aden (47.0%), Djibouti (36.3%), Oman (32.5%), and the Persian Gulf (30.4%); about 26% of deployment segments to both Iraq and Afghanistan were user-entered.

The data were then examined to determine whether participants who had more eligible deployments were adding those deployments manually (as opposed to verifying existing deployments). Participants were stratified based on having at least one user-entered deployment (n = 128,769) segment or no user-entered (all system-generated) deployment segments (n = 149,876), and the numbers of deployments were then compared (see Figure 2-1). The number of deployments for a single individual (including those with 0 days; see below) ranged from 1 to 148, with a mean of 4.3 deployments and standard deviation 4.0. Only 2% of participants had 16 or more eligible deployment segments.

The average number of deployments is lower among those with at least one user-entered deployment than among those with all verified deployments (3.9 vs 4.7 deployments). Often, participants with many deployments had all their deployments generated by the system. Of those participants with fewer than 20 total deployments, 54% had no user-entered deployments, and for those participants with 20 or more deployments, 59% had no user-entered deployments. Therefore, having many eligible deployments does not appear to be due to individual participants adding these deployments manually, and, moreover, adding deployments manually is not shown to be a primary reason why a participant would have a high number of eligible deployments.

To further examine the issue, a selection of participants with very large numbers of deployments were manually examined. Nearly all of their deployments were system-generated, and many of the corresponding exposures questions asked for each deployment had missing or “Don’t know” responses. In some instances, a participant would leave missing all the exposure questions for system-generated deployments and then manually enter one deployment and answer the exposure questions for only that single deployment. One observed anomaly was a

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

TABLE 2-6 Percent User-Entered Deployments by Country of Deployment and Post-9/11

Deployment Start before 9/11 (n = 40,963) Deployment Start on or after 9/11 (n = 1,149,925)
Country of Deployment % User-entered % User-entered
Afghanistan 100.0 26.3
Arabian Sea 100.0 12.1
Bahrain 93.3 22.8
Djibouti 100.0 36.3
Gulf of Aden 100.0 47.0
Gulf of Oman 100.0 59.0
Iraq 80.4 26.7
Kuwait 96.0 8.9
Oman 96.6 32.5
Persian Gulf 100.0 30.4
Qatar 98.0 17.9
Red Sea 100.0 15.5
Saudi Arabia 91.6 28.7
United Arab Emirates 95.5 28.1
TOTAL 92.1 20.2

NOTE: Deployments that started before September 11, 2001, include the 1990–1991 Gulf War and Peacetime deployments.

Image
FIGURE 2-1 Distribution of deployments of registry participants by user-entered status.
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

participant who manually entered over 100 deployment segments, including answers to the deployment exposure questions for all of these deployment segments.

The committee examined participant characteristics that may be driving verification of system-generated versus user-entered deployment segments. Participants were first stratified by date of last deployment (before or after September 11, 2001) before being sub-stratified by none or at least one user-entered deployment (see Table 2-7). Only 6% (n = 17,222) of participants had no deployments after September 11, 2001, and, of these, 83% (n = 14,280) had at least one user-entered deployment. Those 1990–1991 Gulf War participants with at least one user-entered deployment were more likely than those participants of the same era with no user-entered deployments to be 50 years of age or older (at the time of questionnaire completion), to be White race, to have served in the Air Force or Navy, to have served during Peacetime, to have had two or more deployments, and to have had spent a total of 9 months or more deployed. Comparatively, the proportion of post-9/11 participants with at least one user-entered deployment was much less than for the 1990–1991 Gulf War participants.

Of the participants who had at least one deployment after September 11, 2001, 43.8% (n = 114,489) had at least one user-entered deployment. Those post-9/11 participants with at least one user-entered deployment were more likely than those participants with no user-entered deployments to be 40 years of age or older (at the time of questionnaire completion), to have served in the Air Force, to have had their first deployment before 1992 or after 2015, to have served in multiple eras, to have had two to nine deployments, and to have had spent a total of at least 12 months or more deployed.

The duration of deployment segments was examined next. Nearly 40% (n = 461,277; 38.7%) of deployment segments were found to be of less than 30 days duration. To gain a better understanding of very short deployment segments (<30 days), the committee compared them with longer deployments (≥30 days). Three findings stood out regarding very short deployments: they were less likely to have been user-entered (8% vs 28%), they were less likely to have self-reported burn pit exposure (39% vs 72%), and they were more likely to have been to Kuwait (64% vs 17%).

Another difference noted was that the percentage of “Don’t know” responses for question 1.2.D (which asks whether a respondent had been exposed to a burn pit on deployment) for deployments of 0–30 days was more than twice as high as for deployments of 31 days or longer. In addition, nearly 6% of all eligible deployments have the same start date and end date, resulting in 0 days duration, and 4% have a 1-day duration (see Table 2-8). These 0- and 1-day deployments were disproportionately system-generated rather than user-entered (96.5% vs 24.9%), were more likely to be from the post-9/11 era than the 1990–1991 Gulf War era (99.7% vs 96.0%), and were more likely to have had a deployment segment to Kuwait than not (65.2% vs 30.7%). Another difference was that the percentage of “Don’t know” responses for segments of 0–30 days was more than twice as high as for deployment segments of 31 days or longer.

Among participants with a deployment segment of less than 31 days, 99% had at least one additional deployment, and most often these deployment segments lasting less than 31 days were contiguous with other, longer deployments. Some of the very short deployments may represent anomalies in the data, or they may potentially reflect the use of Kuwait for the movement of U.S. troops in and out of the Southwest Asia theater.

Time to Complete Each Questionnaire Section

Although the registry website states that the questionnaire may take up to an hour to complete (VA, 2022), the registry factsheet available on VA’s website states that the questionnaire takes about 40 minutes to complete (VA, 2018). An early analysis of the time required to complete the questionnaire, which did not include the first section of deployment segment verification, found that of the nearly 37,000 participants who had completed the questionnaire, about 75% completed it in 45 minutes or less (Ciminera, 2015b); the median time of completion was 31 minutes. An internal VA analysis of time to complete the questionnaire using a smart phone or tablet found that the average same-day completion time was 61 minutes12—double the median time. The longer completion time on a smart phone or tablet may be because it is not formatted for these modes.

___________________

12 Personal communication, Michael Montopoli, director, Post-9/11 Era Environmental Health Program, VA, September 15, 2016.

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

TABLE 2-7 Percentage of Characteristics of Participants by Any Post-9/11 Deployment and Any User-Entered Deployment

Characteristic No Deployment after 9/11/01
(n = 17,222)
At Least 1 Deployment after 9/11/2001
(n = 261,423)
No User-Entered Deployments
(n = 2,942) (%)
At Least 1 User-Entered Deployment
(n = 14,280) (%)
No User-Entered Deployments
(n = 146,934) (%)
At Least 1 User-Entered Deployment
(n = 114,489) (%)
Sex
Male 85.9 89.7 86.0 85.5
Female 10.1 9.4 10.3 11.4
Missing 4.1 0.9 3.7 3.1
Age at questionnaire completion (years)
<30 0.0 0.0 14.8 10.0
30–39 0.1 1.0 43.2 40.0
40–49 52.9 33.2 27.1 32.2
50–59 37.1 49.3 10.0 12.7
60 or older 10.0 15.5 1.3 1.5
Missing 0.0 1.0 3.6 3.5
Race
White 59.6 63.6 67.6 69.4
Black 26.3 22.2 12.7 10.9
Hispanic 3.0 4.3 11.1 11.0
Other 3.6 4.7 7.0 7.3
Missing 7.5 5.2 1.5 1.5
Branch
Air Force 5.1 16.6 20.0 30.2
Army 85.9 50.6 60.0 52.9
Marine 4.7 12.0 12.1 8.3
Navy 3.8 10.5 7.3 7.4
Coast Guard 0.0 0.3 0.2 0.2
Other 0.4 0.2 0.3 0.3
Missing <0.1 9.8 <0.1 0.8
First deployment
Before 1990 0.0 <0.1 0.0 <0.1
Before 1992 98.9 84.6 <0.1 7.2
Before 2001 1.1 15.4 1.5 6.9
Before 2015 0.0 0.0 93.4 75.9
2015 or later 0.0 0.0 5.0 10.0
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Characteristic No Deployment after 9/11/01
(n = 17,222)
At Least 1 Deployment after 9/11/2001
(n = 261,423)
No User-Entered Deployments
(n = 2,942) (%)
At Least 1 User-Entered Deployment
(n = 14,280) (%)
No User-Entered Deployments
(n = 146,934) (%)
At Least 1 User-Entered Deployment
(n = 114,489) (%)
Last deployment
Before 1992 98.8 79.4 0.0 0.0
Before 2001 1.0 20.2 0.1 0.1
Before 2015 0.2 0.4 86.4 70.3
2015 or later 0.0 <0.1 13.5 29.7
Deployment era
Gulf War 28.0 24.1 0.0 0.0
Peacetime 2.0 22.1 <0.1 <0.1
OEF/OIF/OND 0.0 0.0 85.7 58.9
OIR/OFS 0.0 0.0 5.0 10.0
Multiple eras 70.0 53.8 9.3 31.0
Number of deployments
1 99.8 80.4 24.0 20.3
2 0.1 12.8 15.6 20.3
3 0.1 4.0 11.3 15.9
4 0.0 1.6 9.1 11.3
5 0.0 0.7 8.4 8.1
6 0.0 0.2 6.8 6.1
7 0.0 0.1 5.3 4.3
8 0.0 0.1 4.0 3.3
9 0.0 0.1 3.2 2.4
10 or more 0.0 0.1 12.4 8.1
Duration of deployments
<3 months 11.9 13.2 6.4 2.0
3–6 months 43.9 41.4 13.4 8.2
6–9 months 41.4 31.3 20.4 14.5
9–12 months 2.5 6.2 18.4 15.2
1–2 years 0.3 5.2 28.9 37.1
Longer than 2 years <0.1 2.7 12.6 23.0

TABLE 2-8 Frequency and Item Nonresponse of Short-Duration Deployments

Deployment Duration All Registry Deployments
(n = 1,071,085)
n % of Deployments % Missing % Do Not Wish to Answer % Don’t Know
0 days 62,738 5.9 7.7 0.6 31.2
1 day 47,575 4.4 10.0 0.6 31.6
2 days 32,588 3.0 12.1 0.5 30.7
3 days 23,864 2.2 10.9 0.6 30.9
4–30 days 276,120 23.2 8.1 0.5 27.2
31 or more days 729,611 61.3 7.6 0.2 12.5
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

Registry participants told the initial assessment committee that in practice the questionnaire took closer to 60 minutes to complete (NASEM, 2017). Several veterans reported that the website would freeze and they would have to start again, sometimes requiring multiple attempts before the questionnaire could be completed and submitted. Indeed, during the 2021 live demonstration of the questionnaire to the reassessment committee, the website was slow to load, often took multiple reviews to identify questions that had not been answered, or would load followup items in the same section only after the screen had been saved.

The initial assessment committee found that the time required to complete the AH&OBP Registry questionnaire was directly related to the number of deployment segments for an individual (NASEM, 2017). For example, 51% of participants who had 1 to 3 deployment segments completed the questionnaire in 30 minutes or less, whereas 41% of participants who had 10 or more deployment segments completed the questionnaire in 30 minutes or less. Since the deployment verification section was not included in the time to completion analyses, the times are underestimates and likely increase with the number of deployment segments that an individual needs to verify or manually input (NASEM, 2017).

The time data concerning the completion of the questionnaire that were provided by VA for the reassessment committee differ in structure from what was provided to the initial assessment committee, but they also exclude section 1.1. Time begins with section 1.2, which has questions about exposures on each deployment segment. About one-fifth (21%) of registry participants had more than 24 hours between questionnaire start and end times, which may indicate that they completed the questionnaire over multiple sessions, supported by the fact that more than 10% of participants had start and end times greater than 90 days apart. Because information about multiple logins is not available, the committee first chose to exclude participants with completion times of more than 24 hours. Participants with missing time data, with a completion time prior to start time, or with the same start and completion time were also excluded. Then participants with total times greater than 360 minutes (6 hours), which was the 99th percentile, were excluded from the analysis (n = 68,825; 25%) in order to reduce the influence of extreme completion times on the average. After removing these 68,930 participants, the time-of-completion analysis was based on 209,715 registry participants with valid questionnaire completion times under 6 hours.

Table 2-9 shows the distribution of time to complete the questionnaire among those who completed it within 6 hours of starting. About three-quarters of participants were able to complete the questionnaire in less than 60 minutes. Nearly one-third (31.4%) of participants took between 16 and 30 minutes to complete the questionnaire. Another 30.4% of participants took 31–45 minutes to complete it, 14.6% took 46–60 minutes, and 22.3% took more than 60 minutes to complete it. Table 2-10 shows that the median time was 38 minutes, and the mean completion time was 52.1 minutes.

Consistent with the initial assessment, the time to complete the questionnaire was related to the number of deployment segments. As shown in Table 2-5, about 34% of participants had 5 or more deployment segments, and

TABLE 2-9 Distribution of Time to Complete the AH&OBP Registry Questionnaire

Time to Complete Number Percent
Less than 15 minutes 2,977 1.4
16–30 minutes 65,815 31.4
31–45 minutes 63,689 30.4
46–60 minutes 30,604 14.6
61–90 minutes 24,319 11.6
91–120 minutes 8,524 4.1
More than 120 minutes 13,787 6.6
Total 209,715 100.0

NOTE: Excludes respondents who completed the questionnaire more than 6 hours after starting.

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

TABLE 2-10 Median and Mean Time (in minutes) to Complete the AH&OBP Registry Questionnaire by Number of Deployment Segments

Number of Deployments Median (minutes) Mean (minutes)
1 33 45.8
2 36 48.6
3 37 51.2
4 39 53.1
5 40 54.4
6 42 56.4
7 43 57.4
8 44 59.1
9 46 61.6
10+ 51 68.3
Overall 38 52.1

NOTE: Analysis based on 209,715 participants who completed the questionnaire within 360 minutes (6 hours) after starting.

approximately 10% had 10 or more. Table 2-10 shows that the median time to complete was below 40 minutes for those with 1–4 deployment segments, compared with 51 minutes for those with 10 or more deployment segments, a difference of 11 minutes or more. Thus, on average, each additional deployment segment adds 1–3 minutes to the median questionnaire-completion time and 1.1–2.8 minutes to mean questionnaire–completion time. Therefore, given the additional time required for verifying and correcting deployment information, participation in the registry can be a very time-consuming process, which may contribute to not all of the eligible segments being completed or to dropout at that or later stages, which would introduce additional forms of selection or nonresponse bias.

Participation and Completion by Questionnaire Section

The February 1, 2022, data extract did not contain any information on eligible noncompleters, but the committee’s registry data files extracted on June 3, 2021, included 243,458 participants and information on 131,645 eligible noncompleters, which was used for analyses of noncompleters. An eligible noncompleter was defined as an individual who logged in to the registry, completed the consent form, and was found to have at least one eligible deployment segment, but who did not complete the full questionnaire or submit it. Table 2-11 shows the last section of the questionnaire viewed by noncompleters, which was found to be an acceptable proxy for questionnaire section completion. This was confirmed by the committee during the live demonstration of the questionnaire which showed that participants are required to answer all the displayed questions to move onto the next set of questions or section.

Similar to prior VA analyses of noncompleters, the committee found that 42.9% of eligible individuals accepted the consent but did not answer a single question and that 33.8% did not proceed past the first section on deployment history. The detailed review of verified versus user-entered deployment segments presented in the previous section highlights the difficulty of completing the self-assessment questionnaire for some participants, as the first section of the questionnaire requires a great deal of manual review and entry, which is likely a reason for noncompletion.

VA Health Care Users

According to the VA-provided data on 228,696 AH&OBP Registry participants matched to VA health care data between 2001 and 2021, 170,122 (74.4%) of those participants had used VA at least once. Table 2-12 shows the demographic and military characteristics of VA users and non-VA users. Registry participation appears to be

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

TABLE 2-11 Last Questionnaire Section Viewed Among Eligible Noncompleters

Total Among Those Who Started
Last Section Viewed Number Percent Number Percent
Missing (questionnaire not started) 56,516 42.9
Eligible Deployment History 44,531 33.8 44,531 59.3
Symptoms and Medical History 2,276 1.7 2,276 3.0
Health Concerns 1,027 0.8 1,027 1.4
Places You’ve Lived 488 0.4 488 0.6
Work History 18,559 14.1 18,559 24.7
Home Environment and Hobbies 2,456 1.9 2,456 3.3
Health Care Utilization 1,207 0.9 1,207 1.6
Contact Preferences 4,585 3.5 4,585 6.1
TOTAL 131,645 100 75,129 100

NOTE: Data from June 3, 2021, extract.

associated with an increased use of VA health care, as discussed in more detail in Chapter 7. Registry participants who used VA health care at least once between 2001 and 2021 were more likely to be over 40 years of age, to be Black or Hispanic, to be retired or separated from the military, to have served in the Army, to have served in the reserves or National Guard, to have served in OEF/OIF/OND, and to have had five or more deployments.

Health Conditions

The AH&OBP Registry questionnaire asks about a wide range of symptoms and health conditions, but the questions and the response options do not have the specificity necessary to allow them to be used to draw conclusions about the presence or absence of specific diagnoses among the registry participants. This section describes the health status of registry participants: overall, by early and late time of participation, and by VA enrollment status.

The health outcomes included in the questionnaire and the proportion of all participants who indicated an affirmative diagnosis stratified by early and late participation are shown in Table 2-13. Three questions that pertain to health conditions ask about frequency (how many days or how often) instead of a yes or no response (1.4.E, 2.2.3.H, 2.2.3.I); for these questions, a response was counted as an affirmative diagnosis if the frequency was greater than 0.

The percentage point difference between early and late participants for health outcomes is relatively small. The greatest differences were for seeking medical care during deployment for wheezing, difficulty breathing, or other symptoms (4.0%); experiencing wheezing, difficulty breathing, or other symptoms during deployment (3.1%), and having neurologic problems in the past 12 months (3.1%). When examining respiratory health conditions specifically (questions 2.2.1.A–H), the differences in percentage points were 1.1% or less. Slightly higher affirmative responses for respiratory conditions among the early participants are observed for asthma; emphysema, chronic bronchitis, COPD; some other lung disease; and constrictive bronchiolitis. Although the difference in percentage points is small, early participants were less likely than late participants to report having hay fever or allergies (-0.8%), hypertension (-0.8%), other heart conditions (-0.9%), stopping breathing during sleep (-2.6%), and having a cancer diagnosis (-0.2%). Given the differences in personal or military characteristics, such as age, number of deployments, cumulative length of deployments (see Table 2-5), it is possible that these characteristics account for the modest differences in health outcomes. Early respondents have lower item nonresponse rates than later respondents on almost every item (data not shown). One possible explanation for this difference is that the early participants had higher levels of engagement in the registry and thus had higher item completion rates.

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

TABLE 2-12 Demographic and Military Characteristics of AH&OBP Registry Participants by Use of VA Health Care, 2001–2021

Characteristic Used VA Care at Least Once,
2001–2021
(n = 170,122) (%)
Never Used VA Care,
2001–2021
(n = 58,574) (%)
Sex
Male 87.3 80.7
Female 11.2 8.9
Missing 1.5 10.5
Age at questionnaire completion
<30 11.1 12.5
30–39 41.2 40.3
40–49 31.4 25.9
50–59 13.7 5.8
60 or older 1.9 0.5
Missing 0.5 15.0
Race
White 67.2 72.9
Black 13.0 8.6
Hispanic 11.2 10.0
Other 5.9 5.0
Unknown 1.4 3.3
Missing 1.4 0.2
Service status
Retiree 35.1 12.5
National Guard/Reserves 22.5 21.1
Active duty 3.6 57.1
Separated 37.9 8.1
Unknown 0.5 0.9
Missing 0.4 0.2
Branch
Air Force 19.0 36.8
Army 62.4 45.9
Marine 11.6 7.8
Navy 6.7 8.7
Coast Guard 0.2 0.4
Public Health Service <0.1 <0.1
Unknown <0.1 <0.1
Missing 0.1 0.5
Unit component
Active duty 47.4 62.8
Reserves 32.5 22.5
National Guard 19.2 11.2
Unknown 0.2 2.7
Missing 0.7 0.8
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Characteristic Used VA Care at Least Once,
2001–2021
(n = 170,122) (%)
Never Used VA Care,
2001–2021
(n = 58,574) (%)
First deployment
Before 1990 <0.1 0.0
Before 1992 4.0 1.3
Before 2001 4.1 3.4
Before 2015 88.9 80.8
2015 or later 3.0 14.5
Last deployment
Before 2001 0.1 <0.1
Before 2015 88.4 61.7
2015 or later 11.5 38.3
Deployment era
Peacetime only <0.1 0.0
OEF/OIF/OND 81.9 58.8
OIR/OFS 3.0 14.5
Multiple eras 15.1 26.7
Number of deployments
1 21.3 22.0
2 17.0 17.7
3 12.8 14.2
4 9.9 10.6
5 8.5 8.2
6 6.8 6.3
7 5.3 4.6
8 4.0 3.3
9 3.1 2.7
10 or more 11.5 10.3
Duration of deployments
<3 months 3.7 4.5
3–6 months 10.1 12.2
6–9 months 17.2 18.5
9–12 months 18.4 13.8
1 year or more 50.6 51.0
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

TABLE 2-13 Health Outcomes Collected by the AH&OBP Registry by Early (June 1, 2014–July 31, 2015) and Late (August 1, 2015–February 1, 2022) Participants

Question Number and Text Eligible Total Reported (Yes)
n (%)
Early Participants
n (%)
Late Participants
n (%)
Percent Difference*
1.4.D – During your deployment(s), did you experience wheezing, difficulty breathing, an itchy or irritated nose, eyes, or throat that you thought was the result of poor air quality? 278,645 238,910
(85.7%)
41,008
(88.3%)
197,902
(85.2%)
3.1
1.4.E – How many days in an average month did you experience wheezing, difficulty breathing, an itchy or irritated eyes, nose, or throat that you thought was the result or poor air quality? 238,910 198,972
(83.3%)
34,857
(85%)
164,115
(82.9%)
2.1
1.4.F – During your deployment(s), did you seek medical care for wheezing, difficulty breathing, an itchy or irritated nose, eyes, or throat that you thought was the result of poor air quality? 278,645 87,593
(31.4%)
16,148
(34.8%)
71,445
(30.8%)
4.0
2.2.1.A – Have you ever been told by a doctor or other health professional that you had hay fever or allergies to pollen, dust, or animals? 278,645 111,246
(39.9%)
18,221
(39.2%)
93,025
(40.1%)
-0.8
2.2.1.B – Have you ever been told by a doctor or other health care professional that you had asthma? 278,645 37,991
(13.6%)
6,765
(14.6%)
31,226
(13.4%)
1.1
2.2.1.C – Have you ever been told by a doctor or other health care professional that you had emphysema? 278,645 3,028
(1.1%)
588
(1.3%)
2,440
(1.1%)
0.2
2.2.1.D – Have you ever been told by a doctor or other health care professional that you had chronic bronchitis? 278,645 7,366
(2.6%)
1,530
(3.3%)
5,836
(2.5%)
0.8
2.2.1.E – Have you ever been told by a doctor or other health care professional that you had chronic obstructive pulmonary disease, also called COPD? 278,645 33,032
(11.9%)
5,923
(12.8%)
27,109
(11.7%)
1.1
2.2.1.F – Have you ever been told by a doctor or other health care professional that you had some lung disease or condition other than asthma, emphysema, chronic bronchitis, or COPD? 278,645 23,480
(8.4%)
4,342
(9.3%)
19,138
(8.2%)
1.1
2.2.1.G – Have you ever been told by a doctor or other health care professional that you had constrictive bronchiolitis (CB)? 278,645 2,204
(0.8%)
501
(1.1%)
1,703
(0.7%)
0.3
2.2.1.H – Have you ever been told by a doctor or other health care professional that you had idiopathic pulmonary fibrosis (IPF)? 278,645 557
(0.2%)
99
(0.2%)
458
(0.2%)
0.0
2.2.2.A – Have you ever been told by a doctor or other health care professional that you had hypertension, also called high blood pressure? 278,645 100,919
(36.2%)
16,516
(35.6%)
84,403
(36.3%)
-0.8
2.2.2.B – Have you ever been told by a doctor or other health care professional that you had coronary artery disease? 278,645 4,854
(1.7%)
860
(1.9%)
3,994
(1.7%)
0.1
2.2.2.C – Have you ever been told by a doctor or other health care professional that you had angina pectoris? 278,645 3,431
(1.2%)
577
(1.2%)
2,854
(1.2%)
0.0
2.2.2.D – Have you ever been told by a doctor or other health care professional that you had a heart attack, also called myocardial infarction? 278,645 3,641
(1.3%)
643
(1.4%)
2,998
(1.3%)
0.1
2.2.2.E – Have you ever been told by a doctor or other health care professional that you had a heart condition other than coronary artery disease or angina or myocardial infarction? 278,645 20,123
(7.2%)
3,022
(6.5%)
17,101
(7.4%)
-0.9
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Question Number and Text Eligible Total Reported (Yes)
n (%)
Early Participants
n (%)
Late Participants
n (%)
Percent Difference*
2.2.3.A – During the past 12 months, have you regularly had insomnia or trouble sleeping? 278,645 220,007
(79%)
36,982
(79.6%)
183,025
(78.8%)
0.8
2.2.3.B – During the past 12 months, have you had Neurological problems? (Some examples of neurological problems may include numbness, tingling, or weakness in your arms or legs or difficulties with thinking or memory) 278,645 190,600
(68.4%)
32,958
(71.0%)
157,642
(67.9%)
3.1
2.2.3.C – During the past 12 months, have you had problems of the immune system? 278,645 49,097
(17.6%)
8,524
(18.4%)
40,573
(17.5%)
0.9
2.2.3.D – During the past 12 months, have you been told by a doctor or other health professional that you had any kind of liver condition? 278,645 18,752
(6.7%)
3,108
(6.7%)
15,644
(6.7%)
0.0
2.2.3.E – During the past 12 months, have you been told by a doctor or other health professional that you had a chronic multi-symptom illness (examples include irritable bowel syndrome, chronic fatigue syndrome, and fibromyalgia)? 278,645 48,424
(17.4%)
8,297
(17.9%)
40,127
(17.3%)
0.6
2.2.3.H – How often do you snore? 278,645 241,128
(86.5%)
40,321
(86.8%)
200,807
(86.5%)
0.3
2.2.3.I – How often do you have times when you stop breathing during your sleep? 278,645 129,020
(46.3%)
20,482
(44.1%)
108,538
(46.7%)
-2.6
2.4.A – Have you ever been told by a doctor or other health professional that you had Cancer or a malignancy (tumor) of any kind? 278,645 16,072
(5.8%)
2,598
(5.6%)
13,474
(5.8%)
-0.2

NOTE: *Percent difference indicates the difference in percentages between early and late participants for each health outcome question, i.e., early participant percentages minus late participant percentages.

Table 2-13 shows that 16,072 (5.8%) of participants responded “Yes” to registry question 2.4.A, “Have you ever been told by a doctor or other health professional that you had Cancer or a malignancy (tumor) of any kind?” Of those, 15,170 (5.4%) of registry participants went on to specify one (n = 12,729), two (n = 1,904), or three (n = 537) types of cancer diagnoses. There were 18,148 cancer diagnoses reported among these participants (Table 2-14), the most common being skin cancers and melanoma, followed by prostate cancer.

Exposures

The reassessment committee updated and augmented specific exposure analyses presented in the initial assessment. The analysis of the registry exposure data included a careful inspection of descriptive data and a consideration of qualitative exposure variables. This section describes the exposure experience of registry participants: overall, stratified by early and late time of participation, and by VA enrollment status. It also presents the methods used to crudely assess concordance of self-reported exposures with known time frames and locations where burn pits were operating.

Table 2-15 shows deployment-specific and any military-service-specific exposures collected by the questionnaire for all participants stratified by early and late participation. With the exception of question 1.3.A, the questions

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

TABLE 2-14 Types of Cancer Diagnoses Reported

Cancer Type Frequency
Skin (non-melanoma) 4,433
Skin (don’t know what kind) 2,048
Melanoma 1,720
Prostate 1,145
Other 890
Lymphoma 873
Testis 784
Thyroid 779
Colon 699
Breast 550
Cervix 513
Soft tissue (muscle or fat) 491
Kidney 472
Brain 362
Lung 362
Leukemia 319
Bladder 256
Blood 176
Mouth/tongue/lip 174
Throat–pharynx 169
Bone 162
Uterus 139
Rectum 128
Liver 119
Ovary 98
Esophagus 94
Stomach 88
Pancreas 60
Larynx–windpipe 23
Gallbladder 22
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

TABLE 2-15 Deployment and Military Service Exposures Collected by the AH&OBP Registry by Early (June 1, 2014–July 31, 2015) and Late (August 1, 2015–February 1, 2022) Participants

Question Number and Text Eligible Total Reported Yes
n (%)
Early Participants
n (%)
Late Participants
n (%)
Percent Difference*
1.3.A – Were you ever close enough to feel the blast from an IED (improvised explosive device) or other explosive device? 278,645 184,691
(66.3%)
33,536
(72.2%)
151,155
(65.1%)
7.1
1.3.B – In a typical month, how many days were you near heavy smoke from weapons, signal smoke, markers, or other combat items? 278,645 166,891
(59.9%)
28,876
(62.2%)
138,015
(59.4%)
2.7
1.3.C – In a typical month, how many days were you in a convoy or other vehicle operations? 278,645 199,782
(71.7%)
35,415
(76.3%)
164,367
(70.8%)
5.5
1.3.D – In a typical month, how many days did you perform refueling operations? 278,645 175,218
(62.9%)
30,686
(66.1%)
144,532
(62.2%)
3.8
1.3.E – In a typical month, how many days did you perform aircraft, generator, or other large-engine maintenance? 278,645 108,437
(38.9%)
18,524
(39.9%)
89,913
(38.7%)
1.2
1.3.F – In a typical month, how many days did you perform construction duties? 278,645 94,248
(33.8%)
16,770
(36.1%)
77,478
(33.4%)
2.7
1.3.G – In a typical month, how many days did you perform pesticide duties for your unit? 278,645 29,502
(10.6%)
5,109
(11%)
24,393
(10.5%)
0.5
1.4.C – In a typical month during your deployment(s), how many days did you experience dust storms? 278,645 231,091
(82.9%)
39,580
(85.2%)
191,511
(82.5%)
2.7

NOTE: *Percent difference indicates the difference in percentages between early and late participants for each military or deployment exposure question, i.e., early participant percentages minus late participant percentages.

that ask about experiencing these exposures ask about frequency (how many days in a typical month) instead of a yes or no response. Therefore, an exposure was counted as yes if the frequency was greater than 0 days. The early participants reported all exposures more frequently than the late participants. The largest percentage point difference between early and late participants was 7.1, for being close enough to feel the blast of an improvised explosive device (IED) or other explosive device (72.2% of early participants vs 65.1% of late participants).

VA Health Care Users

Using the VA data file of registry participants who used VA health care between 2001 and 2021, Table 2-16 shows unadjusted responses to the exposure-related questions. When stratified by registry participants who used VA health care at least once versus those who never used VA health care over the same period, 74.4% used VA health care at least once. Those using VA care were more likely to respond yes than those who did not use VA health care to all questions about exposures. This was also observed for the highest stratum of all military- and deployment-related exposures that asked about days per month of exposures. Some of the largest differences between users and non-users of VA health care were for being close enough to feel a blast from an IED (71.8% vs 58.5%, respectively), exposure to heavy combat smoke for 25–31 days per month (23.7% vs 12.8%, respectively), being in a convoy for 25–31 days per month (31.7% vs 20.3%, respectively), experiencing respiratory symptoms

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

TABLE 2-16 Number and Percent of Responses to Exposure Questions of AH&OBP Registry Participants Who Used VA Health Care, 2001–2021

Exposure Total Number of Responses Used VA Care at Least Once, 2001–2021
(n = 170,122) (%)
Never Used VA Care, 2001–2021
(n = 58,574) (%)
1.3.A – Close enough to feel the blast from IED
Yes 156,445 71.8 58.5
No 62,725 23.9 37.6
Do not wish to answer 2,520 1.1 1.0
Don’t know 4,515 2.0 1.9
Missing 2,491 1.1 1.0
1.3.B – Near heavy combat smoke (days per month)
1–4 days 25,397 10.5 12.8
5–9 days 16,269 7.1 7.1
10–14 days 15,210 6.9 6.0
15–19 days 17,203 7.9 6.4
20–24 days 16,463 7.8 5.5
25–31 days 47,772 23.7 12.8
Never 38,561 13.6 26.4
Do not wish to answer 3,036 1.3 1.4
Don’t know 46,264 20.1 20.7
Missing 2,521 1.1 1.0
1.3.C – Convoy (days per month)
1–4 days 23,755 10.1 11.3
5–9 days 16,675 7.3 7.1
10–14 days 15,620 7.0 6.4
15–19 days 18,233 8.2 7.3
20–24 days 25,024 11.4 9.7
25–31 days 65,844 31.7 20.3
Never 48,102 17.4 31.7
Do not wish to answer 2,232 0.9 1.1
Don’t know 10,696 4.8 4.2
Missing 2,515 1.1 1.0
1.3.D – Refueling operations (days per month)
1–4 days 22,551 9.4 11.1
5–9 days 20,647 9.1 8.8
10–14 days 15,709 7.1 6.2
15–19 days 16,593 7.5 6.4
20–24 days 15,936 7.3 6.1
25–31 days 53,420 25.2 18.0
Never 64,264 25.3 36.1
Do not wish to answer 1,191 0.5 0.5
Don’t know 15,865 7.3 5.9
Missing 2,520 1.1 1.0
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Exposure Total Number of Responses Used VA Care at Least Once, 2001–2021
(n = 170,122) (%)
Never Used VA Care, 2001–2021
(n = 58,574) (%)
1.3.E – Perform large engine maintenance (days per month)
1–4 days 12,914 5.7 5.6
5–9 days 10,685 4.8 4.2
10–14 days 7,674 3.6 2.7
15–19 days 7,609 3.5 2.7
20–24 days 6,252 2.8 2.5
25–31 days 43,431 19.6 17.2
Never 124,236 52.5 59.7
Do not wish to answer 1,168 0.5 0.5
Don’t know 12,228 5.8 4.0
Missing 2,499 1.1 1.0
1.3.F – Construction duties (days per month)
1–4 days 21,219 9.3 9.3
5–9 days 18,313 8.3 7.2
10–14 days 12,374 5.8 4.3
15–19 days 8,045 3.8 2.6
20–24 days 4,630 2.2 1.5
25–31 days 14,348 6.8 4.7
Never 125,460 52.3 62.3
Do not wish to answer 1,343 0.6 0.5
Don’t know 20,463 9.8 6.5
Missing 2,501 1.1 1.0
1.3.G – Pesticide duties (days per month)
1–4 days 10,675 4.9 4.0
5–9 days 4,843 2.3 1.7
10–14 days 2,603 1.3 0.8
15–19 days 1,643 0.8 0.5
20–24 days 688 0.3 0.2
25–31 days 3,170 1.6 0.7
Never 179,023 76.3 84.1
Do not wish to answer 1,553 0.7 0.6
Don’t know 21,986 10.7 6.6
Missing 2,512 1.1 1.0
1.4.C – Experience dust storms (days per month)
1–4 days 68,761 28.3 35.2
5–9 days 48,696 21.2 21.5
10–14 days 31,935 14.5 12.4
15–19 days 20,627 9.7 7.0
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Exposure Total Number of Responses Used VA Care at Least Once, 2001–2021
(n = 170,122) (%)
Never Used VA Care, 2001–2021
(n = 58,574) (%)
20–24 days 10,344 5.0 3.1
25–31 days 10,778 5.4 2.8
Never 5,260 1.7 4.1
Do not wish to answer 635 0.3 0.3
Don’t know 28,279 12.4 12.3
Missing 3,381 1.6 1.2
1.4.D – Respiratory symptoms due to air quality (yes/no)
Yes 196,548 87.7 80.9
No 9,983 3.3 7.5
Do not wish to answer 624 0.2 0.4
Don’t know 18,199 7.2 10.1
Missing 3,342 1.5 1.2
1.4.E – Respiratory symptoms due to air quality (days per month)
1–4 days 20,632 8.0 11.9
5–9 days 29,453 12.2 14.8
10–14 days 27,731 12.1 12.3
15–19 days 25,677 11.7 9.8
20–24 days 19,531 9.1 6.9
25–31 days 43,510 21.1 13.1
Never 156 0.1 0.1
Not applicable/Not asked 32,148 12.3 19.1
Do not wish to answer 849 0.4 0.4
Don’t know 28,996 13.1 11.5
Missing 13 <0.1 0.0
Some indication of Gulf War smoke exposure on at least one deployment 6,115 3.2 1.0
No exposure/no data 222,581 96.8 99.0
Some indication of exposure to burn pits on at least one deployment 210,198 92.7 89.7
No exposure/no data 18,498 7.3 10.3
Some burn pit duties on at least one deployment 129,404 59.7 47.5
No exposure/no data 99,292 40.3 52.5
Some deployment hours outside on at least one deployment 221,142 96.7 96.6
No exposure/no data 7,554 3.3 3.4
Some indication of exposure to sewage on at least one deployment 165,415 59.7 47.5
No exposure/no data 63,281 40.3 52.5

NOTE: Column 3 lists the percentage of individuals (n = 170,112) who ever used the VA to access care and responded to the question listed in column 1, whereas column 4 lists the percentage of individuals (n = 58,574) who never used VA to access care and responded to the question listed in column 1. The total number of responses in column 2 is calculated by adding the % of total n in column 3 with the % of total n in column 4.

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

due to air quality (21.1% vs 13.1%, respectively), and having some burn pit duties on at least one deployment (59.7% vs 47.5%, respectively). Although this table presents a simplistic univariable analysis that may suggest that use of VA health care is associated with high exposure and high symptom burden, without properly adjusting for potential confounders and characterizing the two populations of users and non-users it is difficult to determine the direction of association with certainty.

Self-Reported Exposure Concordance

The committee examined self-reported burn pit exposure to check for concordance of this information against DoD location data using two methods. For both analysis methods, the deployment base was first identified using responses to two questions. First, if participants added a deployment segment in response to question 1.1, they could enter a base name. Second, question 1.2.B asked participants about the base at which they spent most of their time during the deployment segment. Only one base name can be entered for either question. If a participant indicated one of the bases of interest for either of these variables, they were considered to have been at that base during the deployment. The same three burn pit exposure questions were used for both analysis methods: 1.2.D–near a burn pit on this deployment; 1.2.F–duties that included the burn pit on this deployment; and 1.2.G–number of hours per day smoke or fumes entered your worksite or housing on this deployment.

In the first method used to check for concordance, participants were restricted to those with deployment segments to Joint Base Balad, Iraq, because it was documented to have the largest burn pit in the Southwest Asia theater (IOM, 2011). Self-reported burn pit exposure was determined using responses from the three questions from section 1.2. Comparisons of self-reported exposure to burn pits were made before and after burn pit operations were closed at Joint Base Balad. Between July 2007 and October 2009, four incinerators were put into operation at Joint Base Balad, resulting in 100% of solid waste disposal via incineration or off-site recycling (AFHSC et al., 2010). Using base information provided in section 1.2 of the self-assessment questionnaire, participants with deployments at Joint Base Balad were identified and divided into three periods: before incinerator installation (January 2003–June 2007), during incinerator installation (July 2007–October 2009), and after incinerator installation (November 2009–present). Participants with a deployment in two or more of the periods were put into the period during which they were deployed the greatest number of days. Self-reported exposure to burn pits was then compared among deployments in each period (Table 2-17). However, the committee is aware that the implementation of the incinerators did not result in an immediate cessation of the burn pit and that this concordance analysis is quite crude.

For all three of the burn pit exposure questions, the number of “Yes” responses to these exposures for deployments that occurred during and after incinerator installation decreased relative to deployments that occurred before the incinerators were installed. The affirmative response to these three burn pit-specific exposure questions was higher than what would be expected for burn pits no longer in operation, which goes to the point above that the implementation of the incinerators did not result in an immediate cessation of the burn pit. As described in Chapter 1, the information regarding the locations and dates of operation—let alone contents—of burn pits is incomplete and there is no gold standard with which to compare self-report of these exposures.

In the second method used to examine the concordance of self-reported burn pit exposure, deployment segments were used to compare three locations (Joint Base Balad, Camp Taji, and Contingency Operating Base Speicher in Iraq) with known burn pits versus two locations (Camp Arifjan and Camp Buehring, Kuwait) without known burn pits. These locations with and without known burn pits have been used in other epidemiologic studies of health effects of exposure to burn pit emissions which have been summarized in previous National Academies’ reports (Abraham et al., 2014; AFHSC et al., 2010, Smith et al., 2012). A difference between those studies and this analysis is that those analyses limited the location cohorts to those who were deployed within a 3-mile radius of the burn pit, based on DMDC deployment information, whereas the committee was limited to working with the base name alone because information on longitude and latitude for each deployment was not provided. Deployment dates were not restricted for this analysis and generally started in 2003 for these bases, although Camp Arifjan had a small number of deployments in 2002.

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

TABLE 2-17 Percentage of Self-Reported Exposure to Burn Pits on Deployments Before, During, and After Incinerator Installation at Joint Base Balad

Time of Deployment Number of Deployments Yes (%) No (%) Don’t Know (%) Refused (%) Missing (%)
Near a burn pit on deployment (1.2.D)
Before 38,118 95.0 1.3 2.7 0.1 1.0
During 22,208 92.4 2.1 4.7 0.1 0.7
After 9,627 77.8 6.1 15.0 0.1 1.0
Duties included the burn pit on deployment (1.2.F)
Before 36,224 47.8 49.8 1.3 0.6 0.5
During 20,521 33.7 63.6 1.5 0.8 0.5
After 7,492 38.9 57.4 2.2 0.8 0.7
24 hours per day smoke or fumes entered the worksite or housing (1.2.G)
Before 36,224 32.4 53.1 13.8 0.2 0.5
During 20,521 29.6 54.0 15.6 0.3 0.6
After 7,492 22.7 55.4 20.9 0.3 0.7

NOTE: “Before” indicates deployment between January 2003 and June 2007, before the incinerator installation; “during” indicates deployment between July 2007 and October 2009, while incinerators were being installed; and “after” indicates deployment from November 2009 through February 2022, after incinerator installation and when the AH&OBP Registry data were extracted.

Table 2-18 shows the responses to the three deployment exposure questions by location; shaded locations denote where burn pits were known to be operating. While the proportion of deployments with “Yes” responses to “Were you near a burn pit on this deployment?” (1.2.D) is much lower for the two locations (camps Arifjan and Buehring) without burn pits, more than one-third of deployments to these bases still reported burn pit exposure. The proportion responding “Don’t know” to this question for these two bases without burn pits is nearly the same as those reporting “Yes.” The proportion of “Don’t know” responses for locations without documented burn pits is nearly four times higher than for bases with documented burn pits. Moreover, for approximately one-third of deployments to locations without documented burn pits, the respondent indicated having had duties that involved the burn pit. Given that this is a crude analysis for determining concordance of exposure to burn pits, one explanation for the discrepancy may be that there were situations in which a participant responded that his or her primary base location was one that did not have burn pits but actually was at a base with burn pits for at least part of the deployment; because only one base name can be provided, the participant was indeed exposed to burn pits but not at the location where he or she spent the majority of that deployment.

The second concordance method confirms the findings of the first concordance method regarding the difficulty with obtaining quality exposure data on the basis of the questionnaire responses. However, in the absence of a gold-standard exposure-assessment tool, it is difficult to conclude with any reasonable certainty the direction and magnitude of exposure measurement error in the self-reported exposure information.

Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×

TABLE 2-18 Percentage of Self-Reported Exposure to Burn Pits on Deployment by Location Cohort

Location Cohort Number of Deployments Yes
(%)
No
(%)
Don’t Know
(%)
Refused
(%)
Missing
(%)
Near a burn pit on deployment (1.2.D)
Balad 69,953 91.8 2.2 5.0 0.1 0.9
Speicher 21,749 88.1 3.8 7.4 0.1 0.6
Taji 27,951 86.7 3.7 8.7 0.1 0.9
Arifjan 57,000 37.7 27.9 33.6 0.3 0.5
Buehring 67,107 35.2 28.9 35.2 0.3 0.4
Worked at burn pit on deployment (1.2.F)
Balad 64,237 42.3 55.1 1.5 0.7 0.5
Speicher 19,159 57.4 40.3 1.2 0.5 0.6
Taji 24,236 50.1 46.9 1.6 0.7 0.7
Arifjan 21,478 34.3 61.5 2.4 0.9 0.9
Buehring 23,617 35.7 60.6 2.3 0.6 0.7
24 hours per day smoke or fumes entered the worksite or housing (1.2.G)
Balad 64,237 30.4 53.6 15.2 0.2 0.5
Speicher 19,159 24.1 56.8 18.2 0.3 0.6
Taji 24,236 25.6 56.6 16.8 0.3 0.7
Arifjan 21,478 20.5 55.8 22.4 0.4 0.9
Buehring 23,617 22.8 53.8 22.3 0.4 0.7

NOTE: Shading denotes locations with known burn pits.

This chapter described the committee’s approach to responding to its Statement of Task, gathering information to address its charge, considering exposure registries in general, and, finally, offering a descriptive review of the AH&OBP Registry data. Information on registry participants, exposures, and the health conditions will be used in chapters 59 to inform the committee’s assessment of the ability of the AH&OBP Registry to perform each of its five stated purposes. Chapter 3: Development and Operations, describes the development and implementation of the registry, including eligibility, the process for participating, and changes that have been made to it since it launched in June 2014. Additional factors of representativeness, participation, and nonresponse are also examined.

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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Page 46
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Page 47
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Page 48
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Page 49
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Page 50
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Page 51
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Page 52
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Page 53
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Page 54
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Page 55
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Page 56
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Page 57
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Page 58
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Page 59
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Page 60
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Page 61
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
Page 62
Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
×
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Suggested Citation:"2 Methods and Approach." National Academies of Sciences, Engineering, and Medicine. 2022. Reassessment of the Department of Veterans Affairs Airborne Hazards and Open Burn Pit Registry. Washington, DC: The National Academies Press. doi: 10.17226/26729.
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Beginning with the 1990–1991 Gulf War, more than 3.7 million U.S. service members have been deployed to Southwest Asia, where they have been exposed to a number of airborne hazards, including oil-well fire smoke, emissions from open burn pits, dust and sand, diesel exhaust, and poor-quality ambient air. Many service members, particularly those who served in Iraq and Afghanistan, have reported health problems they attribute to their exposure to emissions from open-air burn pits on military installations.

In 2013, Congress directed the Department of Veterans Affairs (VA) to establish and maintain the Airborne Hazards and Open Burn Pit (AH&OBP) Registry to "ascertain and monitor" the health effects of such exposures. This report serves as a follow-up to an initial assessment of the AH&OBP Registry completed by an independent committee of the National Academies in 2017. This reassessment does not include any strength-of-the-evidence assessments of potential relationships between exposures to burn pits or airborne hazards and health effects. Rather, this report assesses the ability of the registry to fulfill the intended purposes that Congress and VA have specified for it.

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