Abstract
Adverse environmental exposures worsened by our changing climate threaten respiratory health and exacerbate existing social inequities that further undermine environmental justice (EJ). EJ is the capacity of all people, regardless of sociodemographic characteristics, to minimize harmful exposures and live a healthy life. EJ is achieved through the development, implementation, and enforcement of environmental laws, regulations, and policies. In 2023, an American Thoracic Society workshop convened a group of 39 clinicians, researchers, community advocates, research program administrators, and health policy experts to characterize the respiratory health threats and EJ concerns arising from climate change. The workshop explored four main climate areas through a socioecological and EJ perspective: 1) respiratory health risks, 2) respiratory health impacts in low- and middle-income countries, 3) climate mitigation and adaptation strategies, and 4) priority research infrastructure needs. The workshop committee concluded that climate change can directly and indirectly impair respiratory health and that persistently excluded or marginalized communities (including those in low- and middle-income countries) are disproportionately impacted. These disproportionately impacted communities also lack hazard monitoring and resources to evaluate and advocate for mitigation of adverse environmental exposures. Future respiratory health research must inform mitigation strategies to reduce climate-related emissions from industry to net zero. Researchers, communities, and policymakers require training and support to meaningfully engage with systems-thinking research as well as policy solutions focused on mitigating and adapting to climate change. Finally, the workshop committee recommends a rapid transition away from fossil fuel dependence to a world that provides an equitable allocation of clean transportation options and renewable sources of energy production.
Keywords: respiratory health, climate change, environmental justice, social determinants of health, air pollution
Contents
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Introduction/Overview
EJ Definitions
Methods
Climate Change, Respiratory Health Effects, and Inequities
Addressing Environmental Injustice and Health Effects of Climate Change
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EJ and Respiratory Health Issues Affecting LMICs
Inequities in Exposures
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EJ and Community Partnerships in Climate Mitigation and Adaptation
Community Empowerment and Partnership
Solutions to Overcome Barriers to Partnership
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Including EJ in Policy and Priority Research Infrastructure Needs to Address Climate Change
Tools to Approach Climate, Health, and EJ on a Legislative Level
Agricultural Policy
Global Climate EJ Issues: Research and Data Needs
Data Policies
Building Resilience to Climate Change
Education of Health Professionals to Promote Civic Engagement
Sustainable Healthcare/Sustainable Academics
Role of Medical Societies
Other Technologies
Conclusions
Introduction/Overview
Climate change will make the inequities and disparities worse, and widen that gap. That’s why, this time, we have to get this right.—Dr. Robert Bullard, father of environmental justice (1)
Human activities have permanently altered the Earth’s ecosystems and have led to increased concentrations of carbon dioxide (CO2) and other greenhouse gases (GHGs) in the atmosphere, contributing to global temperature rise, sea level rise, and more extreme climate-sensitive events (e.g., wildfire, storms) (2). Worldwide, communities are experiencing adverse health effects as a result of climate change through multiple direct (e.g., heatwaves, increased storm frequency and intensity) and indirect (e.g., food and water insecurity, social instability, increases in air pollution) pathways (3). Specifically, with more frequent extremes in precipitation patterns and increasing temperatures, some regions will experience worsening desertification, leading to more frequent dust storms than in previous decades (4) and worsened droughtlike conditions by 2050 (5), whereas other regions will experience increased rain and flooding (6). The health impacts of climate change are far reaching, with a strong literature base of impact on respiratory diseases, cardiovascular diseases, infectious diseases, allergies, undernutrition (predominately in low-resource countries and low-income communities within high-resource countries), and physical injuries (7–9). In addition to these multisystem effects of climate change, we are at the nascent stages of understanding climate impacts on health issues, including cancer, mental health, endocrine disruption, and sleep deficiencies (10–13). Furthermore, the health impacts of climate change are unevenly distributed, with the highest risks experienced by economically, geographically, and/or socially marginalized communities, including minoritized races and ethnicities, older adults, women, young children, and people with disabilities (7, 14). To help address these inequities in exposure and health outcomes, we must focus on improving environmental justice (EJ).
EJ Definitions
EJ is defined by the U.S. Environmental Protection Agency (EPA) as “the fair treatment and meaningful involvement of all people regardless of race, color, national origin, or income, with respect to the development, implementation, and enforcement of environmental laws, regulations, and policies” (Table 1) (15). The communities that experience environmental injustice can be referred to as “environmental justice communities (EJCs),” “disproportionately affected communities,” or “overburdened communities.” The EPA defines “overburdened communities” as “minority, low‐income, tribal and indigenous populations, or communities in the United States (US) that potentially experience disproportionate environmental harms and risks due to exposures or cumulative impacts or greater vulnerability to environmental hazards” (16). The language in our workshop report focused on describing external pressures on communities is compatible with the terminology of the U.S. government’s Justice 40 initiative including the term “underserved-disadvantaged communities” (17).
Table 1.
Glossaries of climate terms
| Environmental Protection Agency Climate Glossary: https://19january2017snapshot.epa.gov/climatechange/glossary-climate-change-terms_.html Climate Dictionary: United Nations Development Program. The Climate Dictionary: An everyday guide to climate change | Climate Promise (undp.org) |
The essence of successfully incorporating EJ into society is captured by Professor Bunyan Bryant, Jr., a pioneer in the field: “EJ is supported by decent paying and safe jobs; quality schools and recreation; decent housing and adequate health-care; democratic decision-making and personal empowerment; and communities free of violence, drugs, and poverty” (18).
Methods
With the overall goals to define challenges related to the potential impact of climate change on respiratory health in EJ communities, describe evidence-based approaches for improving public health resilience to climate change related respiratory health threats, and review potential EJ-focused solutions to the identified challenges, we convened a workshop of several sessions from May through June 2023, which included academic pulmonary clinicians and researchers, community advocates, federal partners, and health policy experts (Table 2). This workshop served as an update of the 2012 American Thoracic Society (ATS) Climate Change Workshop by Pinkerton and colleagues (19) and expanded on that prior work by examining climate change from an EJ perspective and a focus on strategies for improvement. Four sessions used a “flipped classroom” (20, 21) model in which presentations were viewed independently by workshop members, who were then brought together for discussion and consensus building. The four sessions covered the following topics: 1) defining the respiratory health effects of climate change through the lens of EJ, 2) EJ and respiratory health issues impacting disproportionately affected low- and middle-income countries (LMICs), 3) considering EJ and communities in climate change mitigation and adaptation strategies, and 4) including EJ in priority research infrastructure needs to address climate change. This narrative review was constructed on the basis of the workshop sessions, offering a broad perspective on climate change and EJ, with a focus on complex topics that require further investigation and identification of gaps in knowledge.
Table 2.
Workshop participants
Academia: United States
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Academia/governmental: international
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Professional societies
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Community organizations
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Governmental agencies
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The workshop chairs (Drs. Croft, Lee, Nordgren, and Thakur) and the writing committee identified the key topics of discussion and conclusions based on a review of meeting recordings, transcripts, and notes from the workshop sessions. The chairs and writing committee then drafted the initial report, which was subsequently shared with all workshop members for feedback on the content of this report. Of note, the link between the respiratory health benefit of mitigating climate change is primarily discussed in Introduction/Overview and EJ and Respiratory Health Issues Affecting LMICs, but because of the complexity of describing the strategies and potential solutions in EJ and Community Partnerships in Climate Mitigation and Adaptation and Including EJ in Policy and Priority Research Infrastructure Needs to Address Climate Change, addressing climate change is the main focus in these sections. Our workshop report includes discussion of areas of the response to climate change (e.g., EJ and renewable energy) that some may view as outside of our scope as clinicians, scientists, and community members (22). We assert that narrow views of professional “scope” have hindered the response to the climate crisis (in part by siloing responses) and that health professionals and scientists are essential in both leading and supporting advocacy efforts for equitable climate solutions.
Climate Change, Respiratory Health Effects, and Inequities
We must consider the direct and indirect impacts of climate change on respiratory health and the differential response to climate change across communities and social dynamics. There is clear documentation in the literature either directly or indirectly linking climate change to respiratory health conditions, including obstructive lung disease (asthma and chronic obstructive pulmonary disease [COPD]), respiratory infections, and upper airway disease (irritant and allergic rhinosinusitis) (23–25). Climate change augments exposure risk through a multitude of climate-sensitive exposures (considered exposures that can be worsened by climate change) (26). Climate change can directly worsen air quality through higher temperatures increasing ozone and volatile organic compound formation (both are respiratory irritants) and indirectly worsen air quality through increased fossil fuel use for heating and cooling demand during extreme temperatures (24, 27). Wildfire smoke is an example of a climate-sensitive exposure that results in an increase in the concentration and potentially the toxicity of the ambient air pollutant particulate matter ⩽2.5 μm in aerodynamic diameter (PM2.5) (28, 29). Increases in PM2.5 concentrations are known to increase healthcare encounters for new or preexisting pulmonary conditions such as asthma (particularly children and elderly patients), COPD, pneumonia, and interstitial lung disease through inflammation and oxidative stress (30, 31). Extreme heat is another climate-sensitive exposure that also poses a unique risk to respiratory health, particularly for the young and elderly and those with underlying respiratory disease (32). Mechanistically, extreme heat from climate change can exacerbate asthma and some patients with COPD by directly triggering bronchospasm and cough through a cholinergic reflex (33), and is being studied as a potential synergistic risk factor with air pollution in threatening respiratory health (34). The combination of increased heat, increase in allergens, and worsened air quality related to climate change represents an important threat to respiratory health.
Climate-related respiratory health threats are not experienced equally among all populations. When compared with high-income non-Hispanic White communities, historically marginalized/excluded and low-income communities are disproportionately exposed to air pollution and experience barriers to accessing quality health care to mitigate their impacts (35, 36). These factors increase the susceptibility of community members when climate-sensitive events occur. For example, in the United States, Kerr and colleagues found that NO2 and PM2.5 concentrations in the census tracts with predominately marginalized groups were 110% and 16% higher, respectively, than in the most-White census tracts (37). Such unequal exposures are rooted in structural racism and manifest in health disparities (35). Structural racism, including historical redlining, residential segregation, poor education systems, workplace policies, and other forms of discrimination, limit opportunities, impair wealth, and threaten the well-being of people based on race, ethnicity or other status (38). Historical redlining (and modern housing segregation), as a manifestation of structural racism, as well as subsequent wealth inequities, is associated with increased exposure (e.g., heat and pollution) and worse respiratory outcomes, including increased risks of childhood asthma and COPD diagnoses (39). EJCs often reside within “sacrifice zones,” regions of unwanted land resulting from purposeful divestment or decades of damage from pollution and climate change such that it is deemed to be permanently impaired. Examples include the “cancer corridor” adjacent to refineries and fossil fuel operations in Louisiana or the community in Port Neches, TX, that resides near a chemical plant (40). Such disproportionate exposure and impact of climate change on EJCs emphasizes the need to better understand the drivers of the observed inequities. Generally, we distinguish three types of climate-sensitive exposure inequity: 1) differential exposure, 2) differential susceptibility, and 3) differential resilience or access to climate adaptation resources (41–43). As Dr. Robert Bullard stated, communities that are disproportionately exposed experience disproportionate disease “first, worst, and longest” (44).
Although each climate-sensitive exposure can be a threat to respiratory health, cumulative exposure in an EJC can lead to particularly harmful health effects. EJCs are at a baseline increased risk of heat-related disease because of increased ambient temperature from the physical built environment (asphalt, limited greenspace), causing a heat island effect (an example of a type 1 inequity, differential exposure) (45). Multiple climate-sensitive exposure events (i.e., compound events), such as extreme heat and wildfires (46, 47), can jointly occur in marginalized communities with higher rates of chronic diseases, leading to worse health outcomes (example of type 2 inequity, differential susceptibility). Moreover, extreme heat can compromise electrical grid resilience and operationality. Although wealthier communities have more access to cooling infrastructure with backup power sources during outages, lower-income communities may not have access to air conditioning, backup power, or the ability to escape the heat (an example of type 3 inequity, differential resilience) (48, 49). Natural disasters such as tropical cyclones and flooding can also lead to worsened respiratory health through the promotion of mold and other allergens (31) and can worsen already existing exposures from industrial sites or legacy cleanup sites, further threatening the health of adjacent communities (50). Because episodes of concomitant climate-sensitive exposures are most likely to impact already disproportionately affected communities (51), future research should focus on mitigation and adaptation approaches during these extreme events. Although we have provided a brief review of climate change related health effects, regular reports by the Intergovernmental Panel on Climate Change (2), Integrated Science Assessments by the EPA on air pollution (30), and the annual Lancet Countdown (52) are examples of helpful resources for regularly updated information on the health effects of climate change.
Addressing Environmental Injustice and Health Effects of Climate Change
Workshop participants identified changes, within a socioecological framework, needed at the individual, community, and societal (including global, regulatory, and legislative) levels to decelerate the climate crisis and improve health, particularly within EJCs (Figure 1). The following discussion describes the details of Figure 1, which serves as a preview of the potential strategies that are discussed in EJ and Community Partnerships in Climate Mitigation and Adaptation and Including EJ in Policy and Priority Research Infrastructure Needs to Address Climate Change. At the global/societal level, emphasis on policies and regulations that reverse the harms from structural racism, eliminate environmental injustice, and address agricultural mismanagement is critical. There is also a need to focus on changing societal behavior to curtail harmful human activities that worsen climate change, including minimizing fossil fuel burning and use (transportation, energy, manufacturing). Furthermore, an equitable world needs to incorporate restorative justice practices, push for global renewable energy together with ecological preservation, and call for adaptative behavioral changes. From the community level to the individual level, behavioral change is needed to decrease wasteful consumerism (including fast fashion and excessive use of plastics), and to support smoking cessation. Governmental incentives are needed to support the creation of necessary infrastructure (including improved rail systems and public transportation) to shift our demand away from fossil fuel–intensive activities (e.g., flying and driving internal combustion vehicles) in a cost-appropriate way to ensure equitable green infrastructure expansion in all communities. With similar incentive support, society will need to increase the demand for the use of renewable energy in homes and mindful travel, including active transport (walking/cycling) and public transportation (rail/bus) when possible. For impactful and sustainable change, this approach needs to center on EJ concerns, prioritizing and creating fluid channels of communication between communities, large corporations, and governments to facilitate the codevelopment of solutions that are equitable and effective for all.
Figure 1.
Outline of recommended activities to stop (left, red background) and activities to start (right, blue background) to address climate change and environmental justice. Rings of activities represent global societal level (outer ring) to individual level changes needed to reach the ultimate inner goals of environmental justice and human health (teal center section). Image produced with Biorender. GHG = greenhouse gas.
EJ and Respiratory Health Issues Affecting LMICs
Climate change, air pollution, and environmental injustice threaten respiratory health worldwide. Despite minimal contribution to the worsening of climate change, LMICs are suffering from severe climate-sensitive exposures. Areas such as Sahel and East Africa, the Middle East, the Indian subcontinent, and parts of northern and western China are expected to be most adversely impacted by climate events (e.g., desertification) (4, 5, 53). When discussing LMICs, workshop participants focused on inequity in exposure while highlighting issues within two important industrial sectors, agriculture and healthcare, because these sectors have global relevance and are expected to be put under stress by the changing climate. Although workshop participants recognized that energy production is another crucial sector driving climate change and air pollution, forming country-specific recommendations in the setting of complex global geopolitical forces and differing economic systems was judged to be beyond the scope of the workshop. Rather, changes to energy production are discussed within the context of the workshop aims.
Inequities in Exposures
Persons at highest risk for the health impacts of climate change are in vulnerable groups, including people who are pregnant, children, and those with chronic diseases in under-resourced and/or marginalized communities (54, 55). Globally, 90% of the poorest 1 billion people live in sub-Saharan Africa, and, of these, over 80% experience five or more deprivations defined by the global multidimensional poverty index (56), including climate-relevant risk factors such as nutrition, use of solid cooking fuel (biomass), and access to clean drinking water and electricity. In addition to being hazardous to health, these deprivations are amplified by a changing climate that threatens food security and increases the likelihood of housing displacement from natural disasters. Furthermore, adaptation tools to offset climate change, such as air conditioning or indoor air cleaners, are not always accessible. These inequities necessitate an EJ perspective in all programs that seek to address climate and health.
In the setting of droughts related to accelerating climate change, and desertification, dust clouds and storms are expected to increase in frequency (57). These sand and dust storms lead to soil salinity and widespread rangeland degradation and pollute the environment and agricultural production by deteriorating the physiological functions of plants, especially during pollination and inflorescence (53). Furthermore, dust-related events can increase exposure to Coccidioides spores and hazardous conditions for automobile and aviation safety (58). Epidemiological studies observe an association between desert dust storms and emergency department visits, hospitalizations, and death from respiratory diseases, including asthma, COPD, respiratory infections, and pulmonary emboli, and these studies also suggest that individuals in LMICs are more susceptible to these deleterious effects (5, 59). Although complex interactions between climate, pollution, and respiratory health can have unique features in different geographic areas, two industrial sectors central to EJ worldwide are agriculture and healthcare (Figure 2).
Figure 2.
Summary of exposure and respiratory health in LMICs. Image produced with Biorender. HIC = high-income countries; LMICs = low- and middle-income countries.
Agriculture
Desertification and resultant dust storms can combine with other climate forces to threaten food security through reduction in crop yields and nutritional quality, potentially turning 12 million hectares of land (20 million tons of grain) into deserts each year (60). The yields and nutritional content of crops can be reduced from increased pests, extreme weather, drought, and reduced land use (61, 62). These climate impacts disproportionately affect small farm holders, island communities, and LMICs with limited monetary/resource capacities to adapt to climate change (61, 63, 64). For example, decreases in grain and wheat crop production from climate change are expected to negatively impact inhabitants in 30 countries in Africa and Asia, who are highly dependent on grain production (5). The resultant impact on food security is a major concern for already overburdened populations (65–67). Furthermore, undernourishment is a risk factor for chronic pulmonary diseases such as COPD and asthma, as well as respiratory infections such as tuberculosis (8). Lack of access to nutrient-dense food also affects educational attainment, career advancement, and social capital (68–70). Increased temperatures and reduced rainfall leading to desertification, as well as deforestation, water overuse, and overgrazing of farmlands, increase the risk of food insecurity and its adverse effects on human health (71). In addition to global food insecurity, farm workers are directly affected by a disproportionate exposure to chemicals, dust, and heat, leading to lifetime increased risks of injury and disease, including respiratory illnesses such as asthma, COPD, sleep apnea, and lung cancer (72–75).
Industrial agriculture accounts for ∼10–12% of total climate-forcing human-made emissions and contributes to climate change (76). The greatest contributors to agricultural emissions are methane from dairies and animal husbandry, fossil fuel use for fertilizer and pesticide production/application, water consumption for animal and crop production, and deforestation (77–80). Thus, current agricultural practices harm human health indirectly by imperiling food security and worsening global climate change, and directly by exposing farm workers (including migrant populations) to respiratory and other health risks (81). Adding to these risks is the increased reliance on antibiotics in industrial animal husbandry (e.g., concentrated animal feeding operations), leading to the emergence of new antibiotic resistance among pathogens that can infect humans directly and more broadly through environmental contamination via ineffective waste management tactics (82–84). Notably, the development of antibiotic resistance in these pathogens threatens human health and puts global food security at further risk because of potential loss of animals from infections and from the culling of herds or flocks to prevent spread of emerging pathogens (85, 86). Climate change acts as a “threat multiplier” that increases the risk of conflict over increasingly scarce resources such as food and water, further displacing populations into overcrowded living conditions, with subsequent morbidity and mortality from health- and violence-related threats (87, 88).
Health care
Health and, we posit by extension, health care are human rights necessary for a productive and just society. LMICs and marginalized communities in high-income countries often lack access to basic health care (89). Although necessary for human health, the healthcare system is also a major contributor to climate change (90). For example, the U.S. healthcare sector accounts for 17.3% of the gross domestic product (91), 8.5% of the U.S. GHG emissions, and one-fourth of all global healthcare GHGs (90, 92). Of the 5–6 million tons of healthcare-generated waste each year, 75–90% is considered nonhazardous (and thus disposed together with normal trash in landfills and incinerators), and the rest is considered regulated medical waste destined for incineration or autoclaving (93). Landfills and waste incinerators are disproportionately located in marginalized communities. Indeed, 79% of municipal solid waste incinerators were in low-income communities or communities of color in 2019 (93–95). Although assessing health effects of waste incineration is challenging because of the heterogeneity in exposure (including PM, dioxins, heavy metals, and polycyclic aromatic hydrocarbons), concerns for carcinogenicity, adverse birth outcomes, and other organ-specific diseases are present (96, 97). Though the literature base on medical waste is stronger in high-income countries, healthcare systems in LMICs are also faced with the challenge of responsibly handling medical waste. For example, in Africa, over 67,740 health facilities generate roughly 282,447 tons of medical waste each year, with incineration being the main approach to disposal (98). The enhancement of medical waste–handling strategies in LMICs that also emphasize the principles of the circular economy (recirculating products at highest value and eliminating waste) (99) has the potential to improve human, environmental, and economic health (98). In summary, combining the direct and indirect emissions from energy use and other operations of the healthcare industry outlines the duality of health care being both a benefit and a threat to health. Building a less wasteful and more sustainable healthcare system can help reduce the health effects of climate change on disproportionately impacted communities.
EJ and Community Partnerships in Climate Mitigation and Adaptation
Community Empowerment and Partnership
Partnering with communities is important to achieving sustainable and equitable climate solutions, which will help mitigate climate-related respiratory health effects. In an effort to emphasize the community as the focal point of this section, we focus on the rationale and strategies for partnerships rather than the respiratory health outcomes discussed previously. Research and public health organizations, in partnership with EJCs, need to coidentify needs and priorities and codevelop strategies for climate adaptation and resilience. In traditional research models, the line of inquiry is dictated by the subject matter expert, and research is completed on or for a specific community. In such models, the researcher determines the research question, study design, and analytical plan, leaving the community as a passive participant in the process, even when the research conducted may be beneficial. When facing complex social problems, such as combating the effects of climate change on the health of socially vulnerable communities, traditional models break down. An approach that incorporates community knowledge and is aligned with community-defined priorities is essential to addressing structural and social factors that compound the health effects of climate change and developing mitigation strategies to reduce health effects. Although principles of community-based participatory action research are an effective mechanism for engaging communities to address the negative effects of climate change, it is neither appropriate nor feasible for every research question (100, 101). For example, although a study using a large administrative dataset may be informed by community groups, it may not be feasible for such groups to partner in the study design if highly specialized biostatistical methods are employed (e.g., unacceptably high time demand to learn these methods). If a research group lacks appropriate training in engagement practices and understanding research ethics, concerns of research “tourism” could foster mistrust within a community. However, all research would benefit from shifting toward centering community voices and priorities. To move away from research models that traditionally, at best, only inform communities, we use the National Institutes of Health (NIH) continuum to describe how the scientific community may take purposeful actions to consult, involve, collaborate, and share leadership with community members and groups (102).
Figure 3 shows an ascending degree of engagement from a small amount of community involvement (Outreach) to a robust partnership with the community (Shared Leadership). Ultimately, academic scientists must leave their “ivory towers” and better connect with communities to achieve the trust and respect required to relay the dire circumstances associated with inaction in the context of our changing climate. Outreach to communities fosters information sharing, where the research team decides how best to translate results in understandable ways and demystify scientific concepts by conveying key points via accessible videos, using comedy and/or audience-appropriate language (e.g., different ages, levels of expertise). An example of this would be personalized messaging to help older adults prepare for extreme heat events (103). By Consulting, the research team creates a formal process, such as advisory boards, to facilitate feedback on the research agenda. Assessing the perceptions of climate adaptive strategies in Nepal is an example of the information sharing that is facilitated by consulting (104). Increasing levels of engagement includes Involving community members as active contributors in research plans and actions (e.g., as coinvestigators or community health workers in the Nature’s Cooling Systems project [105]). Collaborative approaches are centered on partnered work, such as assisting communities with scientific endeavors (such as characterizing the health effects of air pollution as part of an effort to reduce burning of plastic waste in Guatemala [106]) that are more easily managed by the academic community. Shared Leadership represents a true, cohesive collective effort where researchers and communities are equal participants in all decisions, plans, and processes. The Food Equity and Environmental Data Sovereignty Project highlights the benefit of citizen scientists working collaboratively with research teams (107).
Figure 3.
Adaptation of the National Institutes of Health Continuum for Community Engagement (source: National Institutes of Health).
Although we have reviewed a small number of aspirational examples that exist, there have been limited efforts to engage communities in the design, testing, and implementation of community-based mitigation strategies, despite the success of these efforts being dependent on matching interventions to local needs and priorities (108). Furthermore, although increasing literature documents the disproportionate impact of climate change in socially vulnerable and marginalized communities (5), these groups have not been engaged in decision making for climate mitigation, strategy, and adaptation testing. To accelerate our understanding of which mitigation interventions should be widely implemented and incorporated into policy, community stakeholder priorities should be atop the research agenda. For wide-reaching policies to address climate change, we must expand the definition of community to include policymakers at the regional, national, and international levels.
Solutions to Overcome Barriers to Partnership
To achieve authentic partnerships, we must 1) acknowledge historical and current actions that have contributed to ongoing mistrust of climate change efforts, 2) value sociocultural differences and skill-set differences to reduce overt and unconscious power imbalances, and 3) emphasize a community-first model that brings community partners to the table at the start of planning and increases transparency in decision making. Two programs that address these barriers include the HERCULES program in Europe (Sustainable Futures for Europe’s Heritage in Cultural Landscapes) (109) and the Center for Ecoliteracy in California (110). Community-based participatory research incorporates features that facilitate many of the research, policy, and patient care goals of the ATS (111). Active community involvement in research has been shown to address environmental injustice, particularly when community members are included in leadership roles (112) (Figure 4).
Figure 4.
Summary of community involvement in climate mitigation and adaptation. Image produced with Biorender.
Several U.S. federal agencies have shifted their framework to center on community engagement to develop transdisciplinary transformative research. As described by the NIH Climate Change and Health Initiative Strategic Framework, public health interventions that are rooted in partnerships with vulnerable communities will ensure recognition of community-relevant impacts of climate change and create evidence for equitable practices for climate adaptation and building health resilience (113). To support a foundational structure of community engagement in climate research, the NIH launched the Alliance for Community Engagement – Climate and Health to empower community-driven sustainable strategies to address the impacts of climate change on vulnerable communities. A similar effort was recently launched by the EPA. The Inflation Reduction Act (IRA) Community Change Grant Program has earmarked US $2 billion for EJ communities to address pollution, increase climate resilience, and build capacity to address climate change (114). The Centers for Disease Control and Prevention (CDC) is also shifting focus from simply listing the markers of health disparities to identifying and addressing the drivers of those inequities as a foundational element across all CDC activities. The CDC’s CORE commitment strategy is working with multidisciplinary partners to Cultivate comprehensive health equity science, Optimize interventions, Reinforce and expand robust partnerships, and Enhance capacity and workforce engagement. This shift represents a growing understanding that top-down approaches will not be as successful as community-engaged and -centered approaches. For example, the small, historically Black community in Elba, MS, named Shiloh is receiving attention as a bellwether of how the IRA can affect meaningful change. Because of worsened rainfall from climate change, Shiloh has suffered from flooding after construction of a nearby highway in 2018. The suspected culprit of the severe flooding that is destroying homes’ foundations and septic fields are the highway’s drainage systems that “are pointed like cannons into the community.” A community-informed investment would be to address the drainage system of the highway. Robert Bullard has said that as part of the U.S. White House EJ Advisory Council, “if I can’t get justice for Shiloh, I need to knock my name off of that, quote, ‘father of environmental justice’” (115).
Including EJ in Policy and Priority Research Infrastructure Needs to Address Climate Change
Tools to Approach Climate, Health, and EJ on a Legislative Level
Approaches to reducing human-generated GHG range from global, societal, and resource-appropriate individual-level efforts to reduce the use of fossil fuels to power automobiles and heat and cool houses and businesses. Both state and privately owned fossil fuel companies will need to be incentivized to minimize their extraction of fossil fuels and support retraining programs for existing employees to renewable energy projects, particularly those that can reuse existing infrastructure (e.g., converting onshore oil/gas wells to geothermal energy generation) (116). Simultaneously, manufacturers will need to account for and manage direct emissions (scope 1 emissions) and emissions that arise as consequences of the company’s activities (scope 2 and 3 emissions) (117). Elimination of our dependence on fossil fuels will need a comprehensive, multilevel strategy that includes governmental incentivization and corporate realignment to accelerate the development and implementation of renewable energy (e.g., solar power), electrification and weatherization of homes with optimal ventilation, buttressing the electric grid to handle the increased demand, and engaging in individual-level climate adaptation behaviors, including using active transport, avoiding retail overconsumption, and limiting meat intake (118) (Figure 1). Within this multilevel strategy, a just transition will need to be supported to ensure equitable access to resources such as renewable energy and electric vehicles because the relative benefits can be greatest to groups with low income (119).
Healthcare and research partnerships with EJ communities can help identify priorities and potential solutions for climate change and environmental injustice. In turn, adopting and implementing policies to address priorities in climate change will require legislative and regulatory actions at the local, state, federal, and international levels. To date, enactment of the IRA (P.L. 117-169) has been the most significant legislative action the United States has taken on climate change. Although containing other consequential tax and healthcare provisions, the IRA is primarily a climate change law designed to move U.S. industrial policy on a path toward GHG emissions reduction. The law takes a “carrot” approach (e.g., federal subsidies) to encourage adopting technologies to reduce GHG emissions and adopt low or GHG-free energy sources. Although not certain, many climate policy experts believe the IRA gives the United States a chance at meeting its goals of 50% GHG reduction from 2005 levels by 2030, 100% carbon pollution-free electricity by 2035, and net zero economy emissions by 2050.
Although effective, using “carrots” as a policy tool will not suffice to realize essential climate goals, and, as such, “sticks” (regulations) will need to be simultaneously implemented. Effective May 7, 2024, the EPA has implemented 89 Fed. Reg. 16820, which will significantly reduce fugitive methane gas emissions from petroleum extraction and refinement. The EPA has implemented other major rules to reduce GHG emissions from the electrical power industry and car and truck tailpipe emissions. An underappreciated benefit of the EPA’s rules on reducing criteria pollutant emissions (PM), including the recent reduction of the annual PM2.5 standard to 9 μg/m3 (120), is that these changes also will reduce GHG emissions. With the optimal combination of incentives and regulations, a senior climate reporter has assessed that “it’s now cheaper to save the world than destroy it” (121).
States also have a role in both creating and enforcing environmental regulations. For example, the Clean Air Act allows California, the world’s fifth largest economy, to set state emission rules that are more protective than the federal EPA policy. California has successfully used its authority to develop regulations to reduce emissions from maritime vessels, cars, and heavy-duty trucks. Several states have adopted California standards, helping accelerate U.S. efforts to reduce GHG emissions. Although California is a clear leader in this area, many U.S. states (33 of 50) have released a climate action plan that either mirrors the California “100% carbon-free electricity by 2045” plan or is unique to their own geography and industries (122). Specifically, 23 states plus the District of Columbia and Puerto Rico have set aggressive carbon-free (or zero-emissions) electricity goals with target years ranging from 2032 to 2050 (123). Although tremendous progress has been made nationwide, there have been calls by specific communities for equitable enforcement of environmental regulation. Communities in Southern California recently reached a legal settlement with the South Coast Air Quality Management District (AQMD) to compel the South Coast AQMD to collect fines from major polluters in the region that had previously escaped penalties (124). Other communities may lack the resources to take legislative action, but the National Caucus of Environmental Legislators is a nationwide group able to support legislative solutions to environmental problems and to help communities across the nation achieve EJ goals (125). Legislative efforts tie into the concept of restorative justice, which seeks to repair a harm that is done while holding the offender accountable (126). Although restorative justice is typically thought of at an individual level, the “polluter pays” principle could be thought of as a societal level restorative justice action.
Agricultural Policy
Agriculture plays an essential role in maintaining global health and can be considered multipronged in its relationship to climate change and health impacts. Common practices in the agriculture industry (e.g., use of monoculture farming, feedlots/confined animal feeding operations, antibiotic overuse) significantly contribute to GHG emissions and climate change while also harming ecosystems and soil health and making inefficient use of land resources. Specifically, large-scale monoculture/crop practices deplete soil health while also increasing susceptibility to plant disease and pests that threaten crop viability (127). Because the agriculture industry is also central to food security, these current practices threaten the sustainability of nutritious crops. Thus, changes to the agriculture industry must address soil and ecosystem health, GHG/climate change contributions, land resources, and food security.
Regenerative agriculture practices (e.g., reduced water use, cover cropping and polyculture, crop rotations, minimal tilling) can improve crop adaptability/resilience to climate change and pests and promote both crop biodiversity and soil health, thereby creating an opportunity to promote more ecologically friendly and nutritious food options. Because regenerative practices promote soil health, there can be a reduction in the loss of phosphorous from farmland into waterways, thereby preserving limited phosphorous resources and limiting damage to aquatic ecosystems (128, 129). Climate benefits can also be realized by shifting conventional agricultural methods toward regenerative agricultural practices, including increasing soil carbon capture and lowering GHG emissions (e.g., decreased tractor use for tillage) (130). A multidisciplinary task force in Europe published a recent report detailing that the strategies needed to mitigate the climate effects of agriculture (including promotion of plant-based diets, reducing food waste, and more efficient fertilizer application) would also substantially decrease wasteful nitrogen losses within food systems (131). Because global nitrogen and phosphorous loss threatens food security, improving agricultural practices can benefit climate change and food security.
Effective policies must focus on promoting crop viability and diversity and on responsible livestock and milk production to reduce methane emissions, use available land, and prevent habitat destruction (132, 133). Although changes may not be feasible in LMICs, industrialized nations—as the largest contributors—hold the fiscal and resource capacity (including the additional land and initial investment needed for regenerative practices) to adapt current agricultural practices (134, 135). Specific to crop farming, although pesticides can help preserve harvests in monoculture farms, care must be taken because pesticide changes can yield new resistance and/or the emergence of new occupational hazards (136). Within the animal husbandry industry, reducing reliance on antibiotics, improving waste management protocols, and implementing sewage monitoring systems have the potential to reduce the emergence of antibiotic-resistant pathogens within animal and human communities (84, 137).
Shifting perception on agricultural approaches and how to manage land will be a key challenge. In addition to regenerative agricultural practices to address lack of soil health (or inefficient land use), the appropriate use for retired farmland will need to be considered. Although renewal energy options such as solar panels are typically discussed as an “either/or” proposition, pitting energy against food production, this can be a false choice. A recent U.S. Department of Energy study of solar energy sites on retired farmland reported increased biodiversity of plant life and native insect pollinators in the solar panel field (138), which has an additional potential benefit to adjacent active farming fields. This example highlights the bidirectional nature of the benefits of improving agriculture and climate-related practices.
To make these regenerative options more “mainstream,” industry- and government-supported financial and cultural programs designed to encourage climate-friendly diets are also critically important, including campaigns that encourage regional, culturally appropriate foods and limit meat consumption. Other potential solutions include having local farms’ produce available through federal voucher programs, as well as using more specific language to define the problem of climate change. For example, when engaging with communities in agriculture, focusing on the topics of “soil conservation” and “changing ecosystems” rather than the broader term “climate change” may be more meaningful. Specific and relevant communication to community needs is likely to lead to greater productive engagement (see EJ and Community Partnerships in Climate Mitigation and Adaptation).
Global Climate EJ Issues: Research and Data Needs
Although climate change is driven by fossil fuel combustion in high-income countries and LMICs with rapid economic growth, climate change disproportionately affects those who have contributed the least (44), including persons living in LMICs without rapid economic growth. For example, although Africa has experienced large public health gains over the past decades, climate change threatens to slow or even reverse this progress (139). Compounding this, many LMIC governments do not routinely collect or leverage administrative data to quantify key societal vulnerabilities. Indeed, the Climate Impacts Lab estimated that “the effect of an additional very hot day (35°C/95°F) on mortality in the >64 age group is ∼50% larger in regions of the world where mortality data are unavailable” (140). Thus, policymakers and communities are effectively operating in a data vacuum with respect to the health impacts of a changing climate. LMIC-led climate programs that integrate community and policy partner engagement, capacity building, and resilience will be most impactful for increasing meaningful collective participation and mitigating risk.
Data Policies
Differences in spatiotemporal resolution and data availability to the public increase the challenge of studying the health and EJ impacts of climate change across high- and low-income countries. By working with federal agencies, nongovernment organizations, and other community partners, experts can develop and refine tools that aid in screening (e.g., EPA EJScreen, CalEnviroScreen, and the US Climate Vulnerability Index) [141–143], as well as incorporate citizen science applications for data collection such as the Partnerships for Environmental Public Health (144).
Interagency collaborations, including the Environmental Public Health Tracking Program, and Climate and Health Outcomes Research Data Systems, can offer valuable opportunities to bridge scientific data portals, adopt a holistic perspective of relevant public health data sources, and strengthen public trust through building community communication and rapport. For datasets that do not fall under the purview of archival activities from any one federal agency or multiple agencies, investigators and their institutions should also find FAIR (findable, accessible, interoperable, and reusable)-compliant repositories for their datasets, seeking agency support when needed. We propose the following recommendations to improve data access, commensurability, and transparent community engagement, which should be supported by U.S. federal agencies on the basis of their established mandates and policies (e.g., Open Government Data Act of 2018, Year of Open Science 2023):
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•
Data discovery: Develop repositories summarizing the vast quantity of health and environmental data (>50 petabytes annually) (145), potential applications, and associated limitations.
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Data access and processing: Spatiotemporally align and distill big data in FAIR formats (146) to support diverse end users and enable multiscale analyses.
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Centering EJ: Adopt a systems-thinking and community-driven approach to generate or collect and own data (147), eliminating any further stigmatization of marginalized populations.
Considering health and equity impacts within governmental decision-making contexts is critical to designing mitigation and adaptation actions that improve EJ. Assessing quantitative impacts to population subgroups (e.g., children and persons with chronic respiratory diseases) and at higher spatial resolutions (e.g., at the census tract level) within regulatory impact analyses would provide more detailed information about how different policies would affect equity. For these reasons, integrated cumulative health impact assessments are needed to help influence data policies focused on EJ (148). Because these analyses are often constrained by data availability, modeling tools, and computational power, additional work to develop feasible approaches to quantifying distributional impacts, such as reduced form models (149), may be necessary. Attention should be given to hazardous air pollutants and markers of traffic-related air pollution, such as nitrogen dioxide (NO2) and black carbon, in evaluating equity impacts of policies targeting pollution emissions. Metrics used to evaluate societal improvements from reducing GHG, such as the Social Cost of Greenhouse Gases, should also incorporate distributional impacts (150, 151). Committees developing and reviewing such approaches should include health expertise to ensure that health and equity are considered and that evidence-based approaches are used.
Building Resilience to Climate Change
Similar to the resource scarcity in LMICs, low-income and marginalized communities in high-income countries typically have less capacity to adapt to climate change. These communities have greater exposure to air pollution, lower housing quality, fewer green spaces, and limited access to high-quality health care (152, 153). Furthermore, these communities may have language and/or educational barriers to learning about strategies to adapt to climate change. Underlying the so-called climate gap between rich and poor communities, the most impactful of the structural determinants that lead to low resilience to climate change is poverty (153). Interventional strategies that overcome this “climate gap” must include interventions that put the onus on government and industry sectors to support changes versus relying on bootstrap efforts of the communities that are being impacted.
Despite increased exposure to air pollution, low-income and marginalized communities rarely have targeted monitoring of their exposures because EPA air quality monitoring and enforcement are done at the regional level. In addition, the pollution burden of a vibrant in-person economy (shopping/restaurants/entertainment) can be disproportionately placed on low-income and racially minorized communities. Specifically, a study during the COVID-19 pandemic lockdowns in California observed reductions in pollution for Asian and Hispanic communities near in-person economy hubs, whereas predominantly Black communities did not experience a reduction in pollution exposure, because their sources (e.g., power plants) were not shut down (154). Given community-specific exposures, an exemplary policy action that empowers communities to self-monitor is California Assembly Bill 617 (AB617). AB617 mandates developing air quality monitoring and an emission reduction plan for disadvantaged communities (as designated by the California Air Resources Board) deemed to be overburdened by air pollution (155). This bill is designed to address historical environmental injustice and requires that local air districts work with community steering committees to develop both community air quality monitoring and emission reduction plans.
Decision support tools using Earth observation data can provide insight to community stakeholders on pressing health concerns and protecting population health. The tool developed by the University of Puerto Rico-Medical Sciences Campus Environmental Health Department now operational at the Caribbean Coastal Ocean Observing System, a government, academic, and community partnership, provides real-time usable data to those most burdened during an emergency. The Commonwealth of Puerto Rico (U.S. territory in the Caribbean region) recently experienced the disastrous effects of Hurricane Maria (2017), together with frequent earthquakes (e.g., 2020) and ongoing power outages because of an unstable power grid. One local research team in Puerto Rico identified Saharan dust storms as a naturally occurring phenomenon that impacted public health. This team formed more than 19 multidisciplinary community partnerships and used remotely sensed satellite data from MODIS (Moderate Resolution Imaging Spectroradiometer), VIIRS (Visible Infrared Imaging Radiometer Suite), and GOES (Geostationary Operational Environmental Satellites)-16 EAST data to track seasonal dust particles and develop an air quality forecasting tool to inform policy decisions and educate the public on the health risks of dust storms (156). This prototype application was launched by the University of Puerto Rico Environmental Health Department in June 2020, just before the historic (“Godzilla”) dust storm (157). With this information, the Puerto Rico Department of Health added Saharan dust events to the list of emergencies that solicited seasonal (PM2.5) public health advisories. Additional community outreach activities using in-person and virtual formats were made available to health centers and science museums, thereby increasing awareness about the harmful effects of PM2.5 from dust events (158). This team’s efforts represent a significant application of changes being supported by academic, government, and/or industry partners that led to increased community resilience while avoiding placing the burden of creating resilience on the community members themselves. To help support these climate programs worldwide, the ATS has invested in research capacity building in LMICs through the MECOR (Methods in Epidemiologic, Clinical, and Operations Research) Program (159). The historic measure to create a loss and damage fund for LMICs by international leaders at the Conference of the Parties will provide additional financial support for capacity building related to climate action (160).
Education of Health Professionals to Promote Civic Engagement
Although health professionals may not be the first group the public currently turns to for information on the health effects of climate change, emerging global health risks, such as climate change, air pollution, and zoonotic spillover, directly impact the delicate balance of living organisms within surrounding ecosystems. The complexity is captured by the concept of One Health, defined as “a collaborative, multisectoral, and transdisciplinary approach—working at the local, regional, national, and global levels—to achieve optimal health outcomes while recognizing the interconnection between people, animals, plants, and their shared environment” (161). As global leaders have recognized the interconnectedness of human, animal, and environmental health, the need for multidisciplinary collaborations that leverage expertise and data resources (such as GeoHealth sciences) has become evident (162). In support of these collaborations, education and training resources are essential to reinforce clinical and public health competencies on complex environmental topics. Because clinician-researchers will be a key group using improved data from understudied areas, training is needed for professionals involved in research to engage with the communities they serve. Such advocacy training and community involvement should also be moved into health professions education (163). Health professionals and researchers need training in risk communication for broad audiences, a base understanding of how environmental exposures can affect human health, and improved understanding of injustices in communities historically and currently affected by environmental health hazards, as well as climate mitigation and adaptation efforts. Recognizing the fast-paced learning environment of the health professions, the 4Cs of the One Health definition—communication, collaboration, coordination, and capacity building—can serve as a framework to help master acquired skills and competencies and apply the One Health approach to practice (164).
Although many ideas for improving environmental health and climate change education have been proposed (165, 166), the need remains (167, 168). A medical student–driven effort over the last 5 years, the Planetary Health Report Card, has systematically reviewed planetary health material within health sciences schools and identified multiple gaps in curricula (169). Existing efforts to improve environmental health education have included organization-wide faculty development initiatives (170), as well as “train the trainer” type models such as the Pediatric Environmental Health Specialty Units (PEHSUs) (171). PEHSU funds a network of environmental health professionals who educate a broad group of health professionals on environmental concerns for children, including EJ and climate change. The PEHSU network’s Pediatric Environmental Health Toolkit (https://peht.ucsf.edu/) includes climate health information in a mobile-friendly format for just-in-time education of health professionals. Those in leadership positions within health professions schools should add climate action and environmental justice objectives as part of the curricula and leverage existing educational resources (172). Those learning objectives could include material on action-oriented steps that health professionals can take, including how to advocate for justice-based climate health policies in their local areas and how to provide expert testimony.
Resources can include continued medical education courses by professional medical societies such as the American Medical Association, the American Public Health Association, the American Academy of Pediatrics, and the ATS, as well as the Global Consortium on Climate and Health Education. Additional opportunities to join work groups or communities of practice, such as the ATS Environmental, Occupational and Population Health Assembly’s Early Career Professional Working Group or the Group on Earth Observations Health Community of Practice (173), can help physicians leverage their clinical expertise, share data and resources, and expand professional networks.
Sustainable Healthcare/Sustainable Academics
Although incorporating climate health effects into the education and training of health professionals in community engagement are needed, we must also address the climate impact of medical institutions. Reducing the carbon footprint of the healthcare system is achievable with a focus on 1) decarbonizing the supply chain, which accounts for 82% of the emissions from U.S. health care, primarily related to pharmaceuticals and chemicals (90); 2) optimizing healthcare use and delivery (e.g., eliminating unnecessary procedures, prioritizing primary care to reduce resource-intense healthcare use); and 3) supporting local sustainability practices (e.g., energy conservation, zero waste, sustainable food, green commuting).
Healthcare organizations and environmentally focused governmental agencies, including the Agency for Healthcare Research and Quality and the EPA, have launched efforts to identify and find alternatives to suppliers with high GHG emissions, with funding support from the IRA (174). Transitioning to renewable energy to power hospitals must also be a priority, because eliminating fossil fuel burning benefits urban- to regional-scale air quality by reducing power plant emissions, thereby reducing the contributions of health care to global climate change. Indeed, the partnership between the Massachusetts Institute of Technology and the Boston Medical Center already obtains 100% of its power from renewable energy sources (175). Avoiding unnecessary tests and procedures is another way to improve the patient experience, save costs, and reduce waste. In the selection of products and supplies, healthcare institutions can formally incorporate the climate impact into decision making by performing life cycle assessments that evaluate the comparative costs and carbon footprints of each alternative, such as reusable and single-use devices (e.g., laryngoscopes), personal protective equipment, and medications (e.g., inhalers) (176–178). Reconsideration of which patients require contact precautions in hospitals can also reduce waste without harming patient care (177, 179). Such actions can be institutionalized by creating a team within a hospital network with diverse skills, including life cycle assessments, waster, sustainability, clinical care, and quality improvement.
As the medical field attempts to reduce its GHG emissions, we must recognize the fossil fuel industry’s inaction despite decades-old knowledge of its harmful contribution to climate change (180). Taking a comprehensive view of industry emissions is important when considering the pros and cons of potential solutions for our healthcare systems. For example, when considering the relatively small but present emissions from hydrofluorocarbon (HFC) inhalers, we must weigh the potential reduction in GHG emissions with impacts on the respiratory health of patients with respiratory disease. Currently, many metered-dose inhalers (MDIs) use HFCs (powerful GHGs with a global warming potential [GWP] more than 1,000 times that of CO2) as a propellent. The U.S. Food and Drug Administration, EPA, and European Medicines Agency are encouraging drug manufacturers to transition from MDI propellants with high GWP to alternative propellants with lower or no GWP. As the Global Initiative for Asthma considered the trade-offs of the possible benefit of moving away from fluorinated gases or polyfluoroalkyl substances in inhalers, the unintended consequence of cost-driven restrictions on inhaler access for patients with asthma in LMICs was discussed (181). In addition, children, elderly patients with poor lung function, and patients with neurologic or cognitive limitations will require MDIs because they cannot effectively use alternative inhalers (dry powder inhalers) (182). Finally, awareness and avoidance of creating “green guilt” in patients who use HFC MDIs were raised as potential barriers to adherence and a risk factor for exacerbations. Other examples of opportunities to save emissions within health care include using telemedicine visits to lower transportation-associated emissions and digitizing educational or care instruction printouts to save paper. Although beneficial to the environment, these approaches may restrict access to care or information for individuals with limited or no telephone or internet connection. With no simple answers in advancing climate goals while ensuring equitable patient care, we must think carefully about trade-offs within our climate policy positions. Although MDIs, telemedicine, and paper usage are within our practice sphere, we must recognize that aggressive reduction of emissions from any one of these activities without significant reductions in emissions from fossil fuel extraction and use is unlikely to achieve our goal to slow the harmful effects of climate change. The summation of research and policy needs is detailed in Table 3.
Table 3.
Key research priorities to close the climate gap
Academic
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Research
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Policy
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Role of Medical Societies
Professional medical societies such as the ATS and other members of the Forum of International Respiratory Societies (183) have a responsibility to respond to climate change, a health and EJ issue. ATS has served as a policy leader in climate change since 2008, after ATS members authored a policy statement characterizing climate change as a human-made threat to health (184). This ATS stance was later adopted by the American Medical Association. ATS has commented in support of several EPA-proposed regulations to reduce GHG emissions, advocated in Congress for climate-responsive policy, and participated in several court cases to preserve EPA’s authority under the Clean Air Act to regulate GHG emissions. The ATS Environmental Health Policy Committee has helped define the health consequences of increased heat (185), estimated the burden of wildland fire smoke exposure (a consequence of climate change) in the United States, and developed a more comprehensive social cost of carbon estimates (150, 186), which are essential to guiding effective climate change policies. As part of these efforts, ATS has called for additional research on the social cost of carbon, climate change adaptations and remediations, and wildfire smoke (e.g., characterization, chronic effects, and prevention).
The ATS can contribute to the call to action by engaging in multisector activities that result in reduced emissions and protect respiratory health. Given the need for public health interventions to promote sleep health (187), the ATS should help champion the actions recommended by the International Pediatric Sleep Association and World Sleep Society (188): 1) advancing research on the effects of climate change on health inequities and catalyzing transformative actions to translate research into practice (e.g., California’s Fourth Climate Change Assessment [189]), 2) disclosing the energy impact of long-term ventilation of indoor spaces and consideration of renewable energy sources, 3) refusing sponsorship of society meetings by the fossil fuel industry, and 4) reducing carbon footprints associated with professional meetings (e.g., choosing Leadership in Energy and Environmental Design (LEED)-certified facilities for meetings, reducing meeting waste, facilitating reductions of meeting transportation emissions [e.g., hybrid meetings]). In addition, there are important “niche” issues such as MDI propellants, which, although a small contributor to overall global GHG, can help treat patients with respiratory diseases. The ATS will continue to play a role in clinical decarbonization efforts by working with the drug industry, regulators, patient groups, and physicians to ensure a potential MDI propellant switch is conducted in a way that responds to climate change while ensuring access and affordability of MDI medications for all patients. ATS can also engage with medical boards to ensure that the health effects of climate change and pollution, together with environmental equity considerations, are adequately represented in standardized testing. Because ATS is a leader within the policy field, we must innovate in our approach to maximize our impact. Specifically, when considering climate and health policy going forward, the ATS will endeavor to start with health equity as a central tenet of policy development to ensure we develop and support policies that will be effective, durable, and equitable. The ATS will continue to be a vigilant advocate for respiratory health and EJ as the global economy moves to carbon-free energy sources and equitable adaptation to future climate-forced health and environmental challenges.
Other Technologies
In addition to the many beneficial approaches to climate mitigation and adaptation mentioned, there is active research and investment in other potential solutions to climate change, including carbon capture, use, and storage (CCUS) technologies. Although discussing the pros/cons of these approaches is beyond the scope of this report, avoidance of creating GHGs in the first place using previously mentioned approaches can help avoid the inefficiencies and potential inequities of trying to remove CO2 from the environment after its creation (190). Although we acknowledge the likelihood of CCUS being one strategy employed by governments to mitigate the harmful effects of climate change, we advise against it being viewed as replacing the necessary transition to renewable energy, reducing energy use, or improving the efficiency of energy use. Specifically, we must also consider the EJ impact of CCUS, which has the potential to cause air and water pollution and other harms in vulnerable communities. Because CCUS is a component of California’s plan to reach carbon neutrality by 2045, a coalition of EJ groups in the state assessed that “most engineered carbon capture increases air pollution, water pollution, and other harms for frontline communities” and urged avoidance of wasting resources on current CCUS, calling it a “climate dead end” (191).
Conclusions
Although mitigating the respiratory health effects of climate change is challenging, the benefit to the disproportionately affected EJ communities will be immense. To make a meaningful change in the current climate crisis, there will need to be changes to the status quo approach to transportation, energy production, and everyday life activities. By involving without overburdening our communities in climate policymaking, we can expect maximal benefits. As clinicians, researchers, policymakers, and advocates for equity and improvement of respiratory health, we have a duty to improve the future for citizens. As Hazel Johnson, the “mother of EJ” said, “If we want a safe environment for our children and grandchildren, we must clean up our act, no matter how hard a task it might be” (192).
Acknowledgments
This workshop report was prepared by an ad hoc subcommittee of the ATS Assembly on Environmental, Occupational and Population Health and by members of the ATS Environmental Health Policy Committee.
Members of the subcommittee and the committee are as follows:
Daniel P. Croft, M.D., M.P.H., A.T.S.F. (Co-Chair)1
Alison Lee, M.D., M.S., A.T.S.F. (Co-Chair)2
Tara M. Nordgren, Ph.D. (Co-Chair)3
Neeta Thakur, M.D., M.P.H. (Co-Chair)4
Eddie Ahn, J.D.8*
Preshona Ambri, M.Ed.9‡
Susan Anenberg, Ph.D.10‡
Isabella Annesi-Maesano, M.D., Ph.D., D.Sc.12,13§
Kalpana Balakrishnan, Ph.D.14‖
John Balbus, M.D., M.P.H.15‖¶
John R. Balmes, M.D., A.T.S.F.4,5,16‡
Hasan Bayram, M.D., Ph.D., A.T.S.F.17‡
Tarik Benmarhnia, Ph.D.18,19,20‡
Juan C. Celedón, M.D., Dr.P.H., A.T.S.F.21‖
Kevin Cromar, Ph.D.23**
Shereen D’Souza, M.S.26‖¶
Gary Ewart, M.H.S.27‖
Gillian C. Goobie, M.D., Ph.D.22,28,29‡
Jack R. Harkema, D.V.M., Ph.D., A.T.S.F.30§
Stephanie M. Holm, M.D., Ph.D., M.P.H.5,25‡
Chandra L. Jackson, Ph.D., M.S.31,34‖
Ilona Jaspers, Ph.D.35§
Vikas Kapil, D.O., M.P.H.36‖
Gaige H. Kerr, Ph.D., M.A.11‖
Peggy Lai, M.D., M.P.H., A.T.S.F.37**
Jennifer Maccarone, M.D.38‡‡
Cecilia Mejia8‖¶
Pablo Méndez-Lázaro, Ph.D.39,40‖
Sri Nadadur, Ph.D.33§¶
Nicholas Nassikas, M.D.41**
Alexandra Noël, Ph.D.42‡
Laura M. Paulin, M.D., M.H.S.43**
Kent E. Pinkerton, Ph.D.44,45‡
Meghan E. Rebuli, Ph.D., A.T.S.F.35‡
Mary B. Rice, M.D., M.P.H.41,46‖
Arianne Teherani, M.D.6,7‖
Claudia Thompson, Ph.D.32‖¶
George Thurston, Sc.D.24‡
Sacoby Wilson, Ph.D., M.S.47,48§§
*Participant.
‡Facilitator.
§Mentor.
‖Speaker.
¶Not a part of the writing group.
**Advisor.
‡‡Fellow mentee.
§§Keynote.
1Division of Pulmonary and Critical Care, Department of Medicine, University of Rochester Medical Center, Rochester, New York; 2Division of Pulmonary, Critical Care and Sleep Medicine, Department of Medicine, Icahn School of Medicine at Mount Sinai, New York, New York; 3Department of Environmental and Radiological Health Sciences, Colorado State University, Fort Collins, Colorado; 4Division of Pulmonary and Critical Care Medicine, 5Division of Occupational, Environmental and Climate Medicine, and 6Division of General Internal Medicine, Department of Medicine, and 7Center for Climate Health and Equity University of California, San Francisco, San Francisco, California; 8Brightline Defense Project, San Francisco, California; 9The Peoples’ Justice Coalition, Washington, District of Columbia; 10Milken Institute School of Public Health and 11Department of Environmental and Occupational Health, George Washington University, Washington, District of Columbia; 12Desbrest Institute of Epidemiology and Public Health, University of Montpellier, National Institute of Health and Medical Research, Montpellier, France; 13Division of Respiratory Medicine, Allergology, and Thoracic Oncology, University Hospital of Montpellier, Montpellier, France; 14Indian Council of Medical Research Centre for Advanced Research on Air Quality, Climate and Health, Department of Environmental Health Engineering, Sri Ramachandra Institute for Higher Education and Research, Chennai, India; 15U.S. Department of Health and Human Services, Washington, District of Columbia; 16Division of Environmental Health Sciences, School of Public Health, University of California, Berkeley, Berkeley, California; 17Department of Pulmonary Medicine, School of Medicine, Koç University, Istanbul, Turkey; 18Scripps Institution of Oceanography, University of California, San Diego, San Diego, California; 19Research Institute for Environmental and Occupational Health, UMR-S 1085, National Institute of Health and Medical Research Institute, University of Rennes, Rennes, France; 20French School of Public Health, Rennes, France; 21Division of Pediatric Pulmonary Medicine, University of Pittsburgh Medical Center Children’s Hospital of Pittsburgh, and 22Division of Pulmonary, Allergy, Critical Care, and Sleep Medicine, Department of Medicine, University of Pittsburgh, Pittsburgh, Pennsylvania; 23Marron Institute of Urban Management, Environmental Medicine and Population Health, and 24Division of Environmental Medicine, Department of Medicine, New York University Grossman School of Medicine, New York, New York; 25Office of Environmental Health Hazard Assessment and 26California Environmental Protection Agency, Oakland, California; 27Washington Office, American Thoracic Society, Washington, District of Columbia; 28Division of Respiratory Medicine, Department of Medicine, and 29Centre for Heart Lung Innovation, St. Paul’s Hospital, University of British Columbia, Vancouver, British Columbia, Canada; 30Department of Pathobiology and Diagnostic Investigation, College of Veterinary Medicine, Michigan State University, East Lansing, Michigan; 31Epidemiology Branch, 32Population Health Branch, and 33Exposure, Response, and Technology Branch, National Institute of Environmental Health Sciences, National Institutes of Health, Research Triangle Park, North Carolina; 34Division of Intramural Research, National Institute on Minority Health and Health Disparities, National Institutes of Health, Bethesda, Maryland; 35Center for Environmental Medicine, Asthma, and Lung Biology, Department of Pediatrics, University of North Carolina at Chapel Hill, Chapel Hill, North Carolina; 36Emory University, Rollins School of Public Health, Atlanta, Georgia, and 37Manipal Academy of Higher Education, Prasanna School of Public Health, Manipal, India; 38Division of Pulmonary, and Critical Care, Harvard Medical School, Boston, Massachusetts; 38The Pulmonary Center, Boston University School of Medicine, Boston, Massachusetts; 39Environmental Health Department, Graduate School of Public Health, Medical Sciences Campus, and 40Environmental Translational Cancer Program, Division of Cancer Biology, Comprehensive Cancer Center, University of Puerto Rico, San Juan, Puerto Rico; 41Division of Pulmonary, Critical Care, and Sleep Medicine, Beth Israel Deaconess Medical Center, Boston, Massachusetts; 42Department of Comparative Biomedical Sciences, School of Veterinary Medicine, Louisiana State University, Baton Rouge, Louisiana; 43Section of Pulmonary and Critical Care Medicine, Department of Medicine, Dartmouth-Hitchcock Medical Center, Lebanon, New Hampshire; 44Center for Health and the Environment, Institute of the Environment, and 45Western Center for Agricultural Health and Safety, University of California, Davis, Davis, California; 46Department of Environmental Health, Harvard Chan School of Public Health, Boston, Massachusetts; and 47Department of Global, Environmental, and Occupational Health and 48Department of Epidemiology and Biostatistics, College Park School of Public Health, University of Maryland, College Park, Maryland
Footnotes
This Official Workshop Report of the American Thoracic Society was approved February 2025
This official workshop report of the American Thoracic Society was approved February 2025. Project initiation: January 1, 2023. Manuscript submission: July 19, 2024. Manuscript acceptance: December 31, 2024. Board approval: February 13, 2025.
Supported by the American Thoracic Society. C.L.J. was supported by the Intramural Program at the NIH, National Institute of Environmental Health Sciences (Z1AES103325-01). D.P.C. was supported by the National Institute of Environmental Health Sciences Research Career Development Award K23 ES032459 and NIH grant P30 ES001247. N.N., M.B.R., and T.M.N. report receiving grants from the NIH.
The views expressed herein are those of the authors and do not reflect the official policy or position of their respective affiliations.
Artificial Intelligence Disclaimer: No artificial intelligence tools were used in writing this manuscript.
Subcommittee Disclosures: J.R.B. is an employee of the California Air Resources Board. G.E. holds stock in ConocoPhillips, Ford Motor Company, and Tesla. M.B.R. served as an expert witness for the Conservation Law Foundation. J.C.C. received research support from Merck. G.H.K. served as a consultant for the California Air Resources Board, the Environmental Defense Fund, the New York State Office of the Attorney General, and the U.S. Department of Justice. G.C.G. served as a consultant for Boehringer Ingelheim, and received research support from Boehringer Ingelheim, the British Columbia Lung Association, the Canadian Institutes of Health Research, the Canadian Lung Association, Genome British Columbia, the Michael Smith Foundation for Health Research, and the Pulmonary Fibrosis Foundation. L.M.P. received research support from NIH/NIGMS. N.T. received research support from PCORI and NIH. D.P.C., A.L., T.M.N., C.L.J., H.B., N.N., T.B., S.M.H., S.A., P.M.L., P.A., M.E.R., S.W., I.A.M., K.B., K.C., I.J., J.R.H., V.K., P.L., J.M., A.N., K.E.P., A.T., E.A., G.T., J. Balbus, S.D., C.M., S.N., and C.T. reported no commercial or relevant non-commercial interests from ineligible companies.
References
- 1.At 75, the father of environmental justice meets the moment. New York Times . 2022. https://www.nytimes.com/2022/09/12/climate/robert-bullard-environmental-justice.html
- 2.Lee H, Romero J, editors. Climate change 2023: synthesis report, summary for policymakers. contribution of working groups I, II and III to the Sixth Assessment Report of the Intergovernmental Panel on Climate Change. Geneva, Switzerland: Intergovernmental Panel on Climate Change (IPCC); 2023. [Google Scholar]
- 3.National Research Council. Advancing the science of climate change. Washington, DC: National Academies Press; 2011. [Google Scholar]
- 4. Goudie AS. Dust storms: recent developments. J Environ Manage . 2009;90:89–94. doi: 10.1016/j.jenvman.2008.07.007. [DOI] [PubMed] [Google Scholar]
- 5. Bayram H, Rice MB, Abdalati W, Akpinar Elci M, Mirsaeidi M, Annesi-Maesano I, et al. Impact of global climate change on pulmonary health: susceptible and vulnerable populations. Ann Am Thorac Soc . 2023;20:1088–1095. doi: 10.1513/AnnalsATS.202212-996CME. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 6. Tabari H. Climate change impact on flood and extreme precipitation increases with water availability. Sci Rep . 2020;10:13768. doi: 10.1038/s41598-020-70816-2. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 7. Watts N, Adger WN, Agnolucci P, Blackstock J, Byass P, Cai W, et al. Health and climate change: policy responses to protect public health. Lancet . 2015;386:1861–1914. doi: 10.1016/S0140-6736(15)60854-6. [DOI] [PubMed] [Google Scholar]
- 8. Murray CJL, Aravkin AY, Zheng P, Abbafati C, Abbas KM, Abbasi-Kangevari M, et al. Global burden of 87 risk factors in 204 countries and territories, 1990–2019: a systematic analysis for the Global Burden of Disease Study 2019. Lancet . 2020;396:1223–1249. doi: 10.1016/S0140-6736(20)30752-2. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 9. Jackson CL, Walker JR, Brown MK, Das R, Jones NL. A workshop report on the causes and consequences of sleep health disparities. Sleep . 2020;43:zsaa037. doi: 10.1093/sleep/zsaa037. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 10. Gaston SA, Singh R, Jackson CL. The need to study the role of sleep in climate change adaptation, mitigation, and resiliency strategies across the life course. Sleep . 2023;46:zsad070. doi: 10.1093/sleep/zsad070. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 11. Hannan FM, Leow MKS, Lee JKW, Kovats S, Elajnaf T, Kennedy SH, et al. Endocrine effects of heat exposure and relevance to climate change. Nat Rev Endocrinol . 2024;20:673–684. doi: 10.1038/s41574-024-01017-4. [DOI] [PubMed] [Google Scholar]
- 12.Gaston SA, Singh R, Jackson CL. In: Advances in the psychobiology of sleep and circadian rhythms. Jackson ML, Drummond SPA, editors. New York: Routledge; 2024. Health disparities in sleep and mental health: examining the role of sleep disturbances in the relationship between climate change-related traumatic childhood experiences and mental health as an exemplar; pp. 175–194. [Google Scholar]
- 13. Agache I, Akdis C, Akdis M, Al-Hemoud A, Annesi-Maesano I, Balmes J, et al. Immune-mediated disease caused by climate change-associated environmental hazards: mitigation and adaptation. Front Sci . 2024;2:1279192. [Google Scholar]
- 14. Shonkoff SB, Morello-Frosch R, Pastor M, Sadd J. The climate gap: environmental health and equity implications of climate change and mitigation policies in California—a review of the literature. Clim Change . 2011;109:485–503. [Google Scholar]
- 15.U.S. Environmental Protection Agency (EPA) Environmental justice. 2023. https://19january2021snapshot.epa.gov/environmentaljustice/learn-about-environmental-justice_.html
- 16.U.S. Environmental Protection Agency (EPA) What is the definition of “overburdened community” that is relevant for EPA Actions and Promising Practices? 2023. https://www.epa.gov/caa-permitting/what-definition-overburdened-community-relevant-epa-actions-and-promising-practices#:~:text=The%20term%20is%20used%20to,greater%20vulnerability%20to%20environmental%20hazards
- 17.The White House. Justice40: a whole-of-government-initiative. 2024. https://bidenwhitehouse.archives.gov/environmentaljustice/justice40/#:~:text=For%20the%20first%20time%20in,by%20underinvestment%20and%20overburdened%20by
- 18.Environmental Transformation Movement of Flint. What are environmental justice and restorative practices. 2023. https://www.etmflint.org/ej-rp-defined
- 19. Pinkerton KE, Rom WN, Akpinar-Elci M, Balmes JR, Bayram H, Brandli O, et al. American Thoracic Society Environmental Health Policy Committee An official American Thoracic Society workshop report: climate change and human health. Proc Am Thorac Soc . 2012;9:3–8. doi: 10.1513/pats.201201-015ST. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 20. Gilboy MB, Heinerichs S, Pazzaglia G. Enhancing student engagement using the flipped classroom. J Nutr Educ Behav . 2015;47:109–114. doi: 10.1016/j.jneb.2014.08.008. [DOI] [PubMed] [Google Scholar]
- 21. Thai NTT, De Wever B, Valcke M. The impact of a flipped classroom design on learning performance in higher education: looking for the best “blend” of lectures and guiding questions with feedback. Comput Educ . 2017;107:113–126. [Google Scholar]
- 22. Maibach EW, Sarfaty M, Mitchell M, Gould R. Limiting global warming to 1.5 to 2.0°C—a unique and necessary role for health professionals. PLoS Med . 2019;16:e1002804. doi: 10.1371/journal.pmed.1002804. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 23. Mirsaeidi M, Motahari H, Taghizadeh Khamesi M, Sharifi A, Campos M, Schraufnagel DE, et al. Climate change and respiratory infections. Ann Am Thorac Soc . 2016;13:1223–1230. doi: 10.1513/AnnalsATS.201511-729PS. [DOI] [PubMed] [Google Scholar]
- 24. D’Amato G, Cecchi L, D’Amato M, Annesi-Maesano I. Climate change and respiratory diseases. Eur Respir Rev . 2014;23:161–169. doi: 10.1183/09059180.00001714. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 25. D’Amato G, Holgate ST, Pawankar R, Ledford DK, Cecchi L, Al-Ahmad M, et al. Meteorological conditions, climate change, new emerging factors, and asthma and related allergic disorders. A statement of the World Allergy Organization. World Allergy Organ J . 2015;8:25. doi: 10.1186/s40413-015-0073-0. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 26. van Daalen KR, Tonne C, Semenza JC, Rocklöv J, Markandya A, Dasandi N, et al. The 2024 Europe report of the Lancet Countdown on health and climate change: unprecedented warming demands unprecedented action. Lancet Public Health . 2024;9:e495–e522. doi: 10.1016/S2468-2667(24)00055-0. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 27. Zhao W, Zhu B, Davis SJ, Ciais P, Hong C, Liu Z, et al. Reliance on fossil fuels increases during extreme temperature events in the continental United States. Commun Earth Environ . 2023;4:473. [Google Scholar]
- 28. Aguilera R, Corringham T, Gershunov A, Benmarhnia T. Wildfire smoke impacts respiratory health more than fine particles from other sources: observational evidence from Southern California. Nat Commun . 2021;12:1493. doi: 10.1038/s41467-021-21708-0. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 29. Long E, Rider CF, Carlsten C. Controlled human exposures: a review and comparison of the health effects of diesel exhaust and wood smoke. Part Fibre Toxicol . 2024;21:44. doi: 10.1186/s12989-024-00603-8. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 30.U.S. Environmental Protection Agency (EPA) Integrated Science Assessment (ISA) for particulate matter 2019. https://www.epa.gov/isa/integrated-science-assessment-isa-particulate-matter [PubMed]
- 31. Poole JA, Barnes CS, Demain JG, Bernstein JA, Padukudru MA, Sheehan WJ, et al. Impact of weather and climate change with indoor and outdoor air quality in asthma: a work group report of the AAAAI Environmental Exposure and Respiratory Health Committee. J Allergy Clin Immunol . 2019;143:1702–1710. doi: 10.1016/j.jaci.2019.02.018. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 32. Anderson GB, Dominici F, Wang Y, McCormack MC, Bell ML, Peng RD, et al. Heat-related emergency hospitalizations for respiratory diseases in the Medicare population. Am J Respir Crit Care Med . 2013;187:1098–1103. doi: 10.1164/rccm.201211-1969OC. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 33. Hayes D, Collins PB, Khosravi M, Lin R-L, Lee L-Y., Jr. Bronchoconstriction triggered by breathing hot humid air in patients with asthma: role of cholinergic reflex. Am J Respir Crit Care Med . 2012;185:1190–1196. doi: 10.1164/rccm.201201-0088OC. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 34. Anenberg SC, Haines S, Wang E, Nassikas N, Kinney PL. Synergistic health effects of air pollution, temperature, and pollen exposure: a systematic review of epidemiological evidence. Environ Health . 2020;19:130. doi: 10.1186/s12940-020-00681-z. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 35. Nardone A, Casey JA, Morello-Frosch R, Mujahid M, Balmes JR, Thakur N, et al. Associations between historical residential redlining and current age-adjusted rates of emergency department visits due to asthma across eight cities in California: an ecological study. Lancet Planet Health . 2020;4:e24–e31. doi: 10.1016/S2542-5196(19)30241-4. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 36. Bowe B, Xie Y, Yan Y, Al-Aly Z. Burden of cause-specific mortality associated with PM2.5 air pollution in the United States. JAMA Netw Open . 2019;2:e1915834. doi: 10.1001/jamanetworkopen.2019.15834. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 37. Kerr GH, van Donkelaar A, Martin RV, Brauer M, Bukart K, Wozniak S, et al. Increasing racial and ethnic disparities in ambient air pollution-attributable morbidity and mortality in the United States. Environ Health Perspect . 2024;132:37002. doi: 10.1289/EHP11900. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 38. Braveman PA, Arkin E, Proctor D, Kauh T, Holm N. Systemic and structural racism: definitions, examples, health damages, and approaches to dismantling: study examines definitions, examples, health damages, and dismantling systemic and structural racism. Health affairs . 2022;41:171–178. doi: 10.1377/hlthaff.2021.01394. [DOI] [PubMed] [Google Scholar]
- 39. Gaffney AW, Himmelstein DU, Christiani DC, Woolhandler S. Socioeconomic inequality in respiratory health in the US from 1959 to 2018. JAMA Intern Med . 2021;181:968–976. doi: 10.1001/jamainternmed.2021.2441. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 40. Juskus R. Sacrifice zones: a genealogy and analysis of an environmental justice concept. Environ Humanit . 2023;15:3–24. [Google Scholar]
- 41. Casey JA, Daouda M, Babadi RS, Do V, Flores NM, Berzansky I, et al. Methods in public health environmental justice research: a scoping review from 2018 to 2021. Curr Environ Health Rep . 2023;10:312–336. doi: 10.1007/s40572-023-00406-7. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 42. Forastiere F, Stafoggia M, Tasco C, Picciotto S, Agabiti N, Cesaroni G, et al. Socioeconomic status, particulate air pollution, and daily mortality: differential exposure or differential susceptibility. Am J Ind Med . 2007;50:208–216. doi: 10.1002/ajim.20368. [DOI] [PubMed] [Google Scholar]
- 43. Mohai P, Saha R. Which came first, people or pollution? A review of theory and evidence from longitudinal environmental justice studies. Environ Res Lett . 2015;10:125011. [Google Scholar]
- 44.National Heart. Lung, and Blood Advisory Council September 2022 Meeting Summary. https://www.nhlbi.nih.gov/events/2022/national-heart-lung-and-blood-advisory-council-september-2022-meeting-summary
- 45. McIntyre AM, Scammell MK, Botana Martinez MP, Heidari L, Negassa A, Bongiovanni R, et al. Facilitators and barriers for keeping cool in an urban heat island: perspectives from residents of an environmental justice community. Environ Justice . 2023;16:410–417. doi: 10.1089/env.2022.0019. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 46. Rosenthal N, Benmarhnia T, Ahmadov R, James E, Marlier ME. Population co-exposure to extreme heat and wildfire smoke pollution in California during 2020. Environ Res Climate . 2022;1:025004. [Google Scholar]
- 47. Schwarz L, Hansen K, Alari A, Ilango SD, Bernal N, Basu R, et al. Spatial variation in the joint effect of extreme heat events and ozone on respiratory hospitalizations in California. Proc Natl Acad Sci U S A . 2021;118:e2023078118. doi: 10.1073/pnas.2023078118. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 48. Stone B, Gronlund CJ, Mallen E, Hondula D, O’Neill MS, Rajput M, et al. How blackouts during heat waves amplify mortality and morbidity risk. Environ Sci Technol . 2023;57:8245–8255. doi: 10.1021/acs.est.2c09588. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 49. Klinsky S, Mavrogianni A. Climate justice and the built environment. Build Cities . 2020;1:412–428. [Google Scholar]
- 50. Berberian AG, Morello-Frosch R, Karasaki S, Cushing LJ. Climate justice implications of natech disasters: excess contaminant releases during hurricanes on the Texas Gulf Coast. Environ Sci Technol . 2024;58:14180–14192. doi: 10.1021/acs.est.3c10797. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 51. Pacheco SE, Guidos-Fogelbach G, Annesi-Maesano I, Pawankar R, D’Amato G, Latour-Staffeld P, et al. American Academy of Allergy, Asthma & Immunology Environmental Exposures and Respiratory Health Committee Climate change and global issues in allergy and immunology. J Allergy Clin Immunol . 2021;148:1366–1377. doi: 10.1016/j.jaci.2021.10.011. [DOI] [PubMed] [Google Scholar]
- 52. Romanello M, Walawender M, Hsu S-C, Moskeland A, Palmeiro-Silva Y, Scamman D, et al. The 2024 report of the Lancet Countdown on health and climate change: facing record-breaking threats from delayed action. Lancet . 2024;404:1847–1896. doi: 10.1016/S0140-6736(24)01822-1. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 53.Bayram H, Öztürk AB. In: Climate change and global public health. 2nd ed. Pinkerton KE, Rom WN, editors. Cham, Switzerland: Humana; 2021. Global climate change, desertification, and its consequences in Turkey and the Middle East; pp. 445–458. [Google Scholar]
- 54. Kadir MM, McClure EM, Goudar SS, Garces AL, Moore J, Onyamboko M, et al. Global Network Tobacco Study Group Exposure of pregnant women to indoor air pollution: a study from nine low and middle income countries. Acta Obstet Gynecol Scand . 2010;89:540–548. doi: 10.3109/00016340903473566. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 55. Pope DP, Mishra V, Thompson L, Siddiqui AR, Rehfuess EA, Weber M, et al. Risk of low birth weight and stillbirth associated with indoor air pollution from solid fuel use in developing countries. Epidemiol Rev . 2010;32:70–81. doi: 10.1093/epirev/mxq005. [DOI] [PubMed] [Google Scholar]
- 56. Bukhman G, Mocumbi AO, Atun R, Becker AE, Bhutta Z, Binagwaho A, et al. Lancet NCDI Poverty Commission Study Group The Lancet NCDI Poverty Commission: bridging a gap in universal health coverage for the poorest billion. Lancet . 2020;396:991–1044. doi: 10.1016/S0140-6736(20)31907-3. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 57. Pu B, Ginoux P. Projection of American dustiness in the late 21st century due to climate change. Sci Rep . 2017;7:5553. doi: 10.1038/s41598-017-05431-9. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 58. Tong DQ, Gill TE, Sprigg WA, Van Pelt RS, Baklanov AA, Barker BM, et al. Health and safety effects of airborne soil dust in the Americas and beyond. Rev Geophys . 2023;61:e2021RG000763. [Google Scholar]
- 59. Boğan M, Kul S, Al B, Oktay MM, Akpinar Elçi M, Pinkerton KE, et al. Effect of desert dust storms and meteorological factors on respiratory diseases. Allergy . 2022;77:2243–2246. doi: 10.1111/all.15298. [DOI] [PubMed] [Google Scholar]
- 60.United Nations. United Nations Convention to Combat Desertification (UNCCD) Secretariat policy brief. 2012. https://catalogue.unccd.int/58_Zero_Net_Land_Degradation.pdf
- 61. Rossati A. Global warming and its health impact. Int J Occup Environ Med . 2017;8:7–20. doi: 10.15171/ijoem.2017.963. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 62. Shahzad A, Ullah S, Dar AA, Sardar MF, Mehmood T, Tufail MA, et al. Nexus on climate change: agriculture and possible solution to cope future climate change stresses. Environ Sci Pollut Res Int . 2021;28:14211–14232. doi: 10.1007/s11356-021-12649-8. [DOI] [PubMed] [Google Scholar]
- 63. Lin BB, Chappell MJ, Vandermeer J, Smith G, Quintero E, Bezner-Kerr R, et al. Effects of industrial agriculture on climate change and the mitigation potential of small-scale agro-ecological farms. CABI Rev . 2011:1–18. [Google Scholar]
- 64. Harvey CA, Rakotobe ZL, Rao NS, Dave R, Razafimahatratra H, Rabarijohn RH, et al. Extreme vulnerability of smallholder farmers to agricultural risks and climate change in Madagascar. Philos Trans R Soc Lond B Biol Sci . 2014;369:20130089. doi: 10.1098/rstb.2013.0089. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 65. Watts N, Amann M, Ayeb-Karlsson S, Belesova K, Bouley T, Boykoff M, et al. The Lancet Countdown on health and climate change: from 25 years of inaction to a global transformation for public health. Lancet . 2018;391:581–630. doi: 10.1016/S0140-6736(17)32464-9. [DOI] [PubMed] [Google Scholar]
- 66. Fanzo J, Davis C, McLaren R, Choufani J. The effect of climate change across food systems: implications for nutrition outcomes. Glob Food Sec . 2018;18:12–19. [Google Scholar]
- 67. Myers SS, Smith MR, Guth S, Golden CD, Vaitla B, Mueller ND, et al. Climate change and global food systems: potential impacts on food security and undernutrition. Annu Rev Public Health . 2017;38:259–277. doi: 10.1146/annurev-publhealth-031816-044356. [DOI] [PubMed] [Google Scholar]
- 68. Berkowitz SA, Gao X, Tucker KL. Food-insecure dietary patterns are associated with poor longitudinal glycemic control in diabetes: results from the Boston Puerto Rican Health study. Diabetes Care . 2014;37:2587–2592. doi: 10.2337/dc14-0753. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 69. Morales ME, Berkowitz SA. The relationship between food insecurity, dietary patterns, and obesity. Curr Nutr Rep . 2016;5:54–60. doi: 10.1007/s13668-016-0153-y. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 70. Seligman HK, Laraia BA, Kushel MB. Food insecurity is associated with chronic disease among low-income NHANES participants. J Nutr . 2010;140:304–310. doi: 10.3945/jn.109.112573. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 71. Wu Y, Wen B, Li S, Guo Y. Sand and dust storms in Asia: a call for global cooperation on climate change. Lancet Planet Health . 2021;5:e329–e330. doi: 10.1016/S2542-5196(21)00082-6. [DOI] [PubMed] [Google Scholar]
- 72. Applebaum KM, Graham J, Gray GM, LaPuma P, McCormick SA, Northcross A, et al. An overview of occupational risks from climate change. Curr Environ Health Rep . 2016;3:13–22. doi: 10.1007/s40572-016-0081-4. [DOI] [PubMed] [Google Scholar]
- 73. Ebi KL, Vanos J, Baldwin JW, Bell JE, Hondula DM, Errett NA, et al. Extreme weather and climate change: population health and health system implications. Annu Rev Public Health . 2021;42:293–315. doi: 10.1146/annurev-publhealth-012420-105026. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 74.Nelson GC, Rosegrant MW, Palazzo A, Gray I, Ingersoll C, Robertson R, et al. Food security, farming, and climate change to 2050: scenarios, results, policy options. Washington, DC: International Food Policy Research Institute; 2010. [Google Scholar]
- 75. Baumert BO, Carnes MU, Hoppin JA, Jackson CL, Sandler DP, Freeman LB, et al. Sleep apnea and pesticide exposure in a study of US farmers. Sleep Health . 2018;4:20–26. doi: 10.1016/j.sleh.2017.08.006. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 76.Intergovernmental Panel on Climate Change (IPCC) Climate change 2007: mitigation of climate change. Contribution of Working Group III to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change. New York: Cambridge University Press; 2007. [Google Scholar]
- 77. Tilman D, Cassman KG, Matson PA, Naylor R, Polasky S. Agricultural sustainability and intensive production practices. Nature . 2002;418:671–677. doi: 10.1038/nature01014. [DOI] [PubMed] [Google Scholar]
- 78. Robertson GP, Paul EA, Harwood RR. Greenhouse gases in intensive agriculture: contributions of individual gases to the radiative forcing of the atmosphere. Science . 2000;289:1922–1925. doi: 10.1126/science.289.5486.1922. [DOI] [PubMed] [Google Scholar]
- 79. Garnier J, Le Noë J, Marescaux A, Sanz-Cobena A, Lassaletta L, Silvestre M, et al. Long-term changes in greenhouse gas emissions from French agriculture and livestock (1852–2014): from traditional agriculture to conventional intensive systems. Sci Total Environ . 2019;660:1486–1501. doi: 10.1016/j.scitotenv.2019.01.048. [DOI] [PubMed] [Google Scholar]
- 80. Menegat S, Ledo A, Tirado R. Greenhouse gas emissions from global production and use of nitrogen synthetic fertilisers in agriculture. Sci Rep . 2022;12:14490. doi: 10.1038/s41598-022-18773-w. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 81. Donley N, Bullard RD, Economos J, Figueroa I, Lee J, Liebman AK, et al. Pesticides and environmental injustice in the USA: root causes, current regulatory reinforcement and a path forward. BMC Public Health . 2022;22:708. doi: 10.1186/s12889-022-13057-4. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 82. Kimera ZI, Mshana SE, Rweyemamu MM, Mboera LEG, Matee MIN. Antimicrobial use and resistance in food-producing animals and the environment: an African perspective. Antimicrob Resist Infect Control . 2020;9:37. doi: 10.1186/s13756-020-0697-x. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 83. EMA Committee for Medicinal Products for Veterinary Use (CVMP) and EFSA Panel on Biological Hazards (BIOHAZ); Murphy D. Ricci A. Auce Z. Gabriel Beechinor J. Bergendahl H. Breathnach R. et al. EMA and EFSA joint scientific opinion on measures to reduce the need to use antimicrobial agents in animal husbandry in the European Union, and the resulting impacts on food safety (RONAFA) EFSA J . 2017;15:e04666. doi: 10.2903/j.efsa.2017.4666. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 84. Casanova LM, Hill VR, Sobsey MD. Antibiotic-resistant Salmonella in swine wastes and farm surface waters. Lett Appl Microbiol . 2020;71:117–123. doi: 10.1111/lam.13242. [DOI] [PubMed] [Google Scholar]
- 85. Elstrøm P, Grøntvedt CA, Gabrielsen C, Stegger M, Angen Ø, Åmdal S, et al. Livestock-associated MRSA CC1 in Norway; introduction to pig farms, zoonotic transmission, and eradication. Front Microbiol . 2019;10:139. doi: 10.3389/fmicb.2019.00139. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 86. EFSA Panel on Biological Hazards (BIOHAZ); Koutsoumanis K. Allende A. Álvarez‐Ordóñez A. Bolton D. Bover‐Cid S. Chemaly M. et al. Role played by the environment in the emergence and spread of antimicrobial resistance (AMR) through the food chain. EFSA J . 2021;19:e06651. doi: 10.2903/j.efsa.2021.6651. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 87.United Nations. Five ways the climate crisis impacts human security. https://www.un.org/en/climatechange/science/climate-issues/human-security
- 88. Roman J, Viegi G, Schenker M, Ojeda VD, Pérez-Stable EJ, Nemery B, et al. Research needs on respiratory health in migrant and refugee populations. An official American Thoracic Society and European Respiratory Society workshop report. Ann Am Thorac Soc . 2018;15:1247–1255. doi: 10.1513/AnnalsATS.201807-478ST. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 89.World Health Organization. Health is a fundamental human right. 2017. https://www.who.int/news-room/commentaries/detail/health-is-a-fundamental-human-right
- 90. Eckelman MJ, Huang K, Lagasse R, Senay E, Dubrow R, Sherman JD. Health care pollution and public health damage in the United States: an update. Health Aff (Millwood) . 2020;39:2071–2079. doi: 10.1377/hlthaff.2020.01247. [DOI] [PubMed] [Google Scholar]
- 91.Centers for Medicare and Medicaid Services. National health expenditure data: historical. 2023. https://www.cms.gov/data-research/statistics-trends-and-reports/national-health-expenditure-data/historical#:~:text=US%20health%20care%20spending%20grew,spending%20accounted%20for%2017.3%20percent
- 92. Eckelman MJ, Sherman J. Environmental impacts of the US health care system and effects on public health. PLoS One . 2016;11:e0157014. doi: 10.1371/journal.pone.0157014. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 93. American Public Health Association. Advancing environmental health and justice: a call for assessment and oversight of health care waste (APHA Policy Statement Number 20224, Adopted November 2022) New Solut . 2023;33:51–59. doi: 10.1177/10482911231167166. [DOI] [PubMed] [Google Scholar]
- 94. Faber DR, Krieg EJ. Unequal exposure to ecological hazards: environmental injustices in the Commonwealth of Massachusetts. Environ Health Perspect . 2002;110 Suppl 2:277–288. doi: 10.1289/ehp.02110s2277. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 95. Norton JM, Wing S, Lipscomb HJ, Kaufman JS, Marshall SW, Cravey AJ, et al. Race, wealth, and solid waste facilities in North Carolina. Environ Health Perspect . 2007;115:1344–1350. doi: 10.1289/ehp.10161. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 96. Tait PW, Brew J, Che A, Costanzo A, Danyluk A, Davis M, et al. The health impacts of waste incineration: a systematic review. Aust N Z J Public Health . 2020;44:40–48. doi: 10.1111/1753-6405.12939. [DOI] [PubMed] [Google Scholar]
- 97. Vinti G, Bauza V, Clasen T, Medlicott K, Tudor T, Zurbrügg C, et al. Municipal solid waste management and adverse health outcomes: a systematic review. Int J Environ Res Public Health . 2021;18:4331. doi: 10.3390/ijerph18084331. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 98. Chisholm JM, Zamani R, Negm AM, Said N, Abdel Daiem MM, Dibaj M, et al. Sustainable waste management of medical waste in African developing countries: a narrative review. Waste Manag Res . 2021;39:1149–1163. doi: 10.1177/0734242X211029175. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 99.U.S. Environmental Protection Agency (EPA) What is a circular economy? 2024. https://www.epa.gov/circulareconomy/what-circular-economy
- 100. Bacon C, deVuono-Powell S, Frampton ML, LoPresti T, Pannu C. Introduction to empowered partnerships: community-based participatory action research for environmental justice. Environ Justice . 2013;6:1–8. [Google Scholar]
- 101. Belone L, Lucero JE, Duran B, Tafoya G, Baker EA, Chan D, et al. Community-based participatory research conceptual model: community partner consultation and face validity. Qual Health Res . 2016;26:117–135. doi: 10.1177/1049732314557084. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 102.Clinical and Translational Science Awards Consortium; Community Engagement Key Function Committee Task Force on the Principles of Community Engagement. Bethesda, MD: National Institutes of Health; 2011. Principles of community engagement.https://stacks.cdc.gov/view/cdc/11699 [Google Scholar]
- 103. Nitschke M, Krackowizer A, Hansen AL, Bi P, Tucker GR. Heat health messages: a randomized controlled trial of a preventative messages tool in the older population of South Australia. Int J Environ Res Public Health . 2017;14:992. doi: 10.3390/ijerph14090992. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 104. Regmi BR, Star C, Leal Filho W. An overview of the opportunities and challenges of promoting climate change adaptation at the local level: a case study from a community adaptation planning in Nepal. Clim Change . 2016;138:537–550. [Google Scholar]
- 105. Guardaro M, Messerschmidt M, Hondula DM, Grimm NB, Redman CL. Building community heat action plans story by story: a three neighborhood case study. Cities . 2020;107:102886. [Google Scholar]
- 106.Ecolectivos. About Ecolectivos. 2024. https://ecolectivosguatemala.org/en/nosotros/
- 107. Bhawra J, Skinner K, Favel D, Green B, Coates K, Katapally TR, et al. The Food Equity and Environmental Data Sovereignty (FEEDS) project: protocol for a quasi-experimental study evaluating a digital platform for climate change preparedness. JMIR Res Protoc . 2021;10:e31389. doi: 10.2196/31389. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 108. Williamson DHZ. Using the community engagement framework to understand and assess EJ-related research efforts. Sustainability . 2022;14:2809. [Google Scholar]
- 109.von Hackwitz K, Löwenborg D.HERCULES—sustainable futures for Europe’s HERitage in CULtural landscapES: tools for understanding, managing, and protecting landscape functions and values: D2.3 Dynamic models for analyzing long-term landscape change. 2016.
- 110.Center for Ecoliteracy. What we do. 2024. https://www.ecoliteracy.org/about
- 111. Harris DA, Pensa MA, Redlich CA, Pisani MA, Rosenthal MS. Community-based participatory research is needed to address pulmonary health disparities. Ann Am Thorac Soc . 2016;13:1231–1238. doi: 10.1513/AnnalsATS.201601-054PS. [DOI] [PubMed] [Google Scholar]
- 112. Davis LF, Ramírez-Andreotta MD. Participatory research for environmental justice: a critical interpretive synthesis. Environ Health Perspect . 2021;129:26001. doi: 10.1289/EHP6274. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 113.National Institutes of Health (NIH) NIH climate change and health strategic framework. 2022. https://www.nih.gov/sites/default/files/research-training/initiatives/climate-change/nih-climate-change-framework.pdf
- 114.U.S. Environmental Protection Agency (EPA) Inflation Reduction Act community change grants program. 2024. https://www.epa.gov/inflation-reduction-act/inflation-reduction-act-community-change-grants-program
- 115.Inside Climate News. Q&A: Robert Bullard says 2024 is the year of environmental justice for an inundated Shiloh, Alabama. https://insideclimatenews.org/news/24022024/robert-bullard-says-2024-is-year-of-environmental-justice-for-shiloh-alabama/
- 116. Li J, Tarpani RRZ, Gallego-Schmid A, Stamford L. Life cycle assessment of repurposing abandoned onshore oil and gas wells for geothermal power generation. Sci Total Environ . 2024;907:167843. doi: 10.1016/j.scitotenv.2023.167843. [DOI] [PubMed] [Google Scholar]
- 117.U.S. Environmental Protection Agency (EPA) Scope 1 and scope 2 inventory guidance. 2024. https://www.epa.gov/climateleadership/scope-1-and-scope-2-inventory-guidance
- 118.Intergovernmental Panel on Climate Change. Global warming of 1.5 °C: IPCC special report on impacts of global warming of 1.5 °C above pre-industrial levels in context of strengthening response to climate change, sustainable development, and efforts to eradicate poverty. New York: Cambridge University Press; 2022. [Google Scholar]
- 119. Dokshin FA, Gherghina M, Thiede BC. Closing the green gap? Changing disparities in residential solar installation and the importance of regional heterogeneity. Energy Res Soc Sci . 2024;107:103338. doi: 10.1016/j.erss.2023.103338. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 120.U.S. Environmental Protection Agency (EPA) National Ambient Air Quality Standards (NAAQS) for PM. 2024. https://www.epa.gov/pm-pollution/national-ambient-air-quality-standards-naaqs-pm
- 121.World Economic Forum. ‘It’s now cheaper to save the world than destroy it’: author Akshat Rathi on climate capitalism. 2024. https://www.weforum.org/agenda/2024/04/climate-capitalism-akshat-rathi-radio-davos-podcast/
- 122.Center for Climate and Energy Solutions. State climate policy maps. https://www.c2es.org/content/state-climate-policy/
- 123.Clean Energy States Alliance. Table of 100% clean energy states. https://www.cesa.org/projects/100-clean-energy-collaborative/guide/table-of-100-clean-energy-states/
- 124.Earth Justice. Environmental groups, SCAQMD reach settlement to adopt rule that could financially penalize major polluters. 2024. https://earthjustice.org/press/2024/environmental-groups-scaqmd-reach-settlement-to-adopt-rule-that-could-financially-penalize-major-polluters
- 125.National Caucus of Environmental Legislators. About: we are your remote environmental staff. https://www.ncelenviro.org/about/
- 126.University of Wisconsin–Madison Law School. About restorative justice. https://law.wisc.edu/fjr/rjp/justice.html#:~:text=Restorative%20justice%20seeks%20to%20examine,to%20repair%20the%20harm%20done
- 127. Gepts P. Biocultural diversity and crop improvement. Emerg Top Life Sci . 2023;7:151–196. doi: 10.1042/ETLS20230067. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 128. Ockenden MC, Hollaway MJ, Beven KJ, Collins AL, Evans R, Falloon PD, et al. Major agricultural changes required to mitigate phosphorus losses under climate change. Nat Commun . 2017;8:161. doi: 10.1038/s41467-017-00232-0. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 129. Montgomery DR, Biklé A, Archuleta R, Brown P, Jordan J. Soil health and nutrient density: preliminary comparison of regenerative and conventional farming. PeerJ . 2022;10:e12848. doi: 10.7717/peerj.12848. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 130. Newton P, Civita N, Frankel-Goldwater L, Bartel K, Johns C. What is regenerative agriculture? A review of scholar and practitioner definitions based on processes and outcomes. Front Sustain Food Syst . 2020;4:577723. [Google Scholar]
- 131.Leip A, Wollgast J, Kugelberg S, Leite JC, Maas RJM, Mason KE, et al. Appetite for change: food system options for nitrogen, environment & health. 2nd European Nitrogen Assessment Special Report on Nitrogen & Food. Edinburgh, UK: UK Centre for Ecology & Hydrology; 2023. [Google Scholar]
- 132. Kazimierczuk K, Barrows SE, Olarte MV, Qafoku NP. Decarbonization of agriculture: the greenhouse gas impacts and economics of existing and emerging climate-smart practices. ACS Eng Au . 2023;3:426–442. doi: 10.1021/acsengineeringau.3c00031. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 133. LaCanne CE, Lundgren JG. Regenerative agriculture: merging farming and natural resource conservation profitably. PeerJ . 2018;6:e4428. doi: 10.7717/peerj.4428. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 134. Samson J, Berteaux D, McGill BJ, Humphries MM. Geographic disparities and moral hazards in the predicted impacts of climate change on human populations. Glob Ecol Biogeogr . 2011;20:532–544. [Google Scholar]
- 135.FAO. The future of food and agriculture—alternative pathways to 2050. 2018. https://www.fao.org/global-perspectives-studies/resources/detail/en/c/1157074/
- 136. Röösli M, Fuhrimann S, Atuhaire A, Rother HA, Dabrowski J, Eskenazi B, et al. Interventions to reduce pesticide exposure from the agricultural sector in Africa: a workshop report. Int J Environ Res Public Health . 2022;19:8973. doi: 10.3390/ijerph19158973. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 137. Hendriksen RS, Munk P, Njage P, van Bunnik B, McNally L, Lukjancenko O, et al. Global Sewage Surveillance project consortium Global monitoring of antimicrobial resistance based on metagenomics analyses of urban sewage. Nat Commun . 2019;10:1124. doi: 10.1038/s41467-019-08853-3. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 138. Walston LJ, Hartmann HM, Fox L, Macknick J, McCall J, Janski J, et al. If you build it, will they come? Insect community responses to habitat establishment at solar energy facilities in Minnesota, USA. Environ Res Lett . 2024;19:014053. [Google Scholar]
- 139.United Nations Climate Change. Climate change is an increasing threat to Africa. 2020. https://unfccc.int/news/climate-change-is-an-increasing-threat-to-africa
- 140.Carleton TA, Jina A, Delgado MT, Greenstone M, Houser T, Hsiang SM, et al. Valuing the global mortality consequences of climate change accounting for adaptation costs and benefits (no. w27599) Cambridge, MA: National Bureau of Economic Research; 2020. [Google Scholar]
- 141.The Public Environmental Data Partners. Data + Screening Tools. https://screening-tools.com/epa-ejscreen
- 142.California Office of Environmental Health Hazard Assessment. CalEnviroScreen. https://oehha.ca.gov/calenviroscreen
- 143.Environmental Defense Fund. The U.S. Climate Vulnerability Index. https://map.climatevulnerabilityindex.org/map/cvi_overall/usa?mapBoundaries=Tract&mapFilter=0&reportBoundaries=Tract&geoContext=State
- 144.National Institute of Environmental Health Science (NIEHS) Air pollution monitoring turns students into citizen scientists. 2024. https://www.niehs.nih.gov/research/supported/translational/peph/podcasts/2022/feb15_airpollution
- 145. Shaw J, Sekalala S. Health data justice: building new norms for health data governance. NPJ Digit Med . 2023;6:30. doi: 10.1038/s41746-023-00780-4. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 146. Wilkinson MD, Dumontier M, Aalbersberg IJJ, Appleton G, Axton M, Baak A, et al. The FAIR guiding principles for scientific data management and stewardship. Sci Data . 2016;3:160018. doi: 10.1038/sdata.2016.18. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 147. Van Horne YO, Alcala CS, Peltier RE, Quintana PJE, Seto E, Gonzales M, et al. An applied environmental justice framework for exposure science. J Expo Sci Environ Epidemiol . 2023;33:1–11. doi: 10.1038/s41370-022-00422-z. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 148.U.S. Environmental Protection Agency (EPA) Cumulative impacts research. 2024. https://www.epa.gov/healthresearch/cumulative-impacts-research
- 149. Sacks JD, Lloyd JM, Zhu Y, Anderton J, Jang CJ, Hubbell B, et al. The Environmental Benefits Mapping and Analysis Program–Community Edition (BenMAP–CE): a tool to estimate the health and economic benefits of reducing air pollution. Environ Model Softw . 2018;104:118–129. [PMC free article] [PubMed] [Google Scholar]
- 150.National Academies of Sciences, Engineering, and Medicine. Valuing climate damages: updating estimation of the social cost of carbon dioxide. Washington, DC: National Academies Press; 2017. [Google Scholar]
- 151. Rennert K, Errickson F, Prest BC, Rennels L, Newell RG, Pizer W, et al. Comprehensive evidence implies a higher social cost of CO2. Nature . 2022;610:687–692. doi: 10.1038/s41586-022-05224-9. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 152. Tessum CW, Paolella DA, Chambliss SE, Apte JS, Hill JD, Marshall JD. PM2.5 polluters disproportionately and systemically affect people of color in the United States. Sci Adv . 2021;7:eabf4491. doi: 10.1126/sciadv.abf4491. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 153. Morello-Frosch R, Obasogie OK. The climate gap and the color line—racial health inequities and climate change. N Engl J Med . 2023;388:943–949. doi: 10.1056/NEJMsb2213250. [DOI] [PubMed] [Google Scholar]
- 154. Bluhm R, Polonik P, Hemes KS, Sanford LC, Benz SA, Levy MC, et al. Disparate air pollution reductions during California’s COVID-19 economic shutdown. Nat Sustain . 2022;5:509–517. [Google Scholar]
- 155. MacIver L, London J, Sampson N, Gordon M, Grow R, Eady V, et al. West Oakland’s experience in building community power to confront environmental injustice through California’s Assembly Bill 617. Am J Public Health . 2022;112:262–270. doi: 10.2105/AJPH.2021.306592. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 156.Caribbean Coastal Ocean Observing System (CARICOOS) CARICOOS buoys. 2024. https://www.caricoos.org/
- 157.National Aeronautics and Space Administration (NASA) Godzilla dust storm. 2021. https://svs.gsfc.nasa.gov/4849
- 158. Morales-Medina M, Ortíz-Martínez AP, Pérez-Cardona CM, Rueda-Roa D, Otis D, Pérez-Matías E, et al. Who is affected by Saharan dust in the Caribbean? A spatial analysis and citizen’s perspective from Puerto Rico during the Godzilla dust event in June 2020. Weather Clim Soc . 2024;16:205–219. [Google Scholar]
- 159.American Thoracic Society. ATS MECOR 2.0 program. https://www.thoracic.org/about/global-public-health/mecor-program/
- 160. Vaidyanathan G. A giant fund for climate disasters will soon open. Who should be paid first? Nature . 2024 doi: 10.1038/d41586-024-00149-x. [DOI] [PubMed] [Google Scholar]
- 161.Centers for Disease Control and Prevention (CDC) One Health basics. 2023. https://www.cdc.gov/one-health/about/index.html
- 162. Gorris ME, Anenberg SC, Goldberg DL, Kerr GH, Stowell JD, Tong D, et al. Shaping the future of science: COVID-19 highlighting the importance of GeoHealth. Geohealth . 2021;5:e2021GH000412. doi: 10.1029/2021GH000412. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 163. Teherani A, Nicastro T, Clair MS, Nordby JC, Nikjoo A, Collins S, et al. Faculty development for education for sustainable health care: a university system-wide initiative to transform health professional education. Acad Med . 2023;98:680–687. doi: 10.1097/ACM.0000000000005137. [DOI] [PubMed] [Google Scholar]
- 164. Adisasmito WB, Almuhairi S, Behravesh CB, Bilivogui P, Bukachi SA, Casas N, et al. One Health High-Level Expert Panel (OHHLEP) One Health: a new definition for a sustainable and healthy future. PLoS Pathog . 2022;18:e1010537. doi: 10.1371/journal.ppat.1010537. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 165. Tinney VA, Paulson JA, Bathgate SL, Larsen JW. Medical education for obstetricians and gynecologists should incorporate environmental health. Am J Obstet Gynecol . 2015;212:163–166.e1. doi: 10.1016/j.ajog.2014.07.038. [DOI] [PubMed] [Google Scholar]
- 166. Gehle KS, Crawford JL, Hatcher MT. Integrating environmental health into medical education. Am J Prev Med . 2011;41:S296–S301. doi: 10.1016/j.amepre.2011.06.007. [DOI] [PubMed] [Google Scholar]
- 167. Goshua A, Gomez J, Erny B, Burke M, Luby S, Sokolow S, et al. Addressing climate change and its effects on human health: a call to action for medical schools. Acad Med . 2021;96:324–328. doi: 10.1097/ACM.0000000000003861. [DOI] [PubMed] [Google Scholar]
- 168. Philipsborn RP, Sheffield P, White A, Osta A, Anderson MS, Bernstein A, et al. Climate change and the practice of medicine: essentials for resident education. Acad Med . 2021;96:355–367. doi: 10.1097/ACM.0000000000003719. [DOI] [PubMed] [Google Scholar]
- 169.Planetary Health Report Card. The planetary health report card. https://phreportcard.org/
- 170. Nordrum OL, Kirk A, Lee SA, Haley K, Killilea D, Khalid I, et al. Planetary health education in medical curricula in the Republic of Ireland. Med Teach . 2022;44:1237–1243. doi: 10.1080/0142159X.2022.2072279. [DOI] [PubMed] [Google Scholar]
- 171. Paulson JA, Karr CJ, Seltzer JM, Cherry DC, Sheffield PE, Cifuentes E, et al. Development of the pediatric environmental health specialty unit network in North America. Am J Public Health . 2009;99 Suppl 3:S511–S516. doi: 10.2105/AJPH.2008.154641. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 172.Medical Students for a Sustainable Future. Guide to climate and health curriculum reform in medical schools: medical students for a sustainable future. 2023. https://docs.google.com/document/d/1lwLv-PZXZTymWbPLTB3604dvnOvg2gKntIoBo7QH-6c/edit
- 173.Group on Earth Observations. Group on Earth Observations Health Community of Practice. http://www.geohealthcop.org/
- 174. Lee VS, Gerwig K, Hough E, Mate K, Biggio R, Kaplan RS, et al. Decarbonizing health care: engaging leaders in change. NEJM Catal Innov Care Deliv . 2023;4 [Google Scholar]
- 175.Ferenc J. Health Facilities Management; 2016. Solar agreement keeps Boston Medical Center on emissions-cutting track.https://www.hfmmagazine.com/articles/2598-solar-agreement-keeps-boston-medical-center-on-emissions-cutting-track [Google Scholar]
- 176. Sherman JD, Raibley LA, Eckelman MJ. Life cycle assessment and costing methods for device procurement: comparing reusable and single-use disposable laryngoscopes. Anesth Analg . 2018;127:434–443. doi: 10.1213/ANE.0000000000002683. [DOI] [PubMed] [Google Scholar]
- 177. Vozzola E, Overcash M, Griffing E. Environmental considerations in the selection of isolation gowns: a life cycle assessment of reusable and disposable alternatives. Am J Infect Control . 2018;46:881–886. doi: 10.1016/j.ajic.2018.02.002. [DOI] [PubMed] [Google Scholar]
- 178. Jeswani HK, Azapagic A. Life cycle environmental impacts of inhalers. J Clean Prod . 2019;237:117733. [Google Scholar]
- 179. Schrank GM, Snyder GM, Davis RB, Branch-Elliman W, Wright SB. The discontinuation of contact precautions for methicillin-resistant Staphylococcus aureus and vancomycin-resistant Enterococcus: impact upon patient adverse events and hospital operations. BMJ Qual Saf . 2020;29:1–2. doi: 10.1136/bmjqs-2018-008926. [DOI] [PubMed] [Google Scholar]
- 180. Franta B. Early oil industry knowledge of CO2 and global warming. Nat Clim Change . 2018;8:1024–1025. [Google Scholar]
- 181. Levy ML, Bateman ED, Allan K, Bacharier LB, Bonini M, Boulet L-P, et al. Global access and patient safety in the transition to environmentally friendly respiratory inhalers: the Global Initiative for Asthma perspective. Lancet . 2023;402:1012–1016. doi: 10.1016/S0140-6736(23)01358-2. [DOI] [PubMed] [Google Scholar]
- 182. Keeley D, Scullion JE, Usmani OS. Minimising the environmental impact of inhaled therapies: problems with policy on low carbon inhalers. Eur Respir J . 2020;55:2000048. doi: 10.1183/13993003.00048-2020. [DOI] [PubMed] [Google Scholar]
- 183.Forum of International Respiratory Societies. Members. https://www.firsnet.org/about/members
- 184. Rom WN, Pinkerton KE, Martin WJ, Forastiere F. Global warming: a challenge to all American Thoracic Society members. Am J Respir Crit Care Med . 2008;177:1053–1054. doi: 10.1164/rccm.200801-052ED. [DOI] [PubMed] [Google Scholar]
- 185. Cromar KR, Anenberg SC, Balmes JR, Fawcett AA, Ghazipura M, Gohlke JM, et al. Global health impacts for economic models of climate change: a systematic review and meta-analysis. Ann Am Thorac Soc . 2022;19:1203–1212. doi: 10.1513/AnnalsATS.202110-1193OC. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 186. Cromar K, Howard P, Vásquez VN, Anthoff D. Health impacts of climate change as contained in economic models estimating the social cost of carbon dioxide. Geohealth . 2021;5:e2021GH000405. doi: 10.1029/2021GH000405. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 187. Lim DC, Najafi A, Afifi L, Bassetti CLA, Buysse DJ, Han F, et al. World Sleep Society Global Sleep Health Taskforce The need to promote sleep health in public health agendas across the globe. Lancet Public Health . 2023;8:e820–e826. doi: 10.1016/S2468-2667(23)00182-2. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 188. Magda LN, Chan K, Bin-Hasan S, Gringras P. Endorsement of the International Pediatric Association’s declaration on the impact of climate change on children by the International Pediatric Sleep Association and World Sleep Society. Sleep Med . 2023;104:56–57. doi: 10.1016/j.sleep.2023.01.029. [DOI] [PubMed] [Google Scholar]
- 189.State of California. Sacramento, CA: E4 Strategic Solution; 2018. Climate justice summary report. California’s fourth climate change assessment.https://resourceslegacyfund.org/wp-content/uploads/2018/09/Climate-Justice-Report-4CCCA-v.4-00455673xA1C15.pdf [Google Scholar]
- 190. Zickfeld K, MacIsaac AJ, Canadell JG, Fuss S, Jackson RB, Jones CD, et al. Net-zero approaches must consider Earth system impacts to achieve climate goals. Nat Clim Change . 2023;13:1298–1305. [Google Scholar]
- 191.California Air Resources Board. Collective EJ statement on engineered carbon capture, use, and storage (CCUS) in California. 2022. https://ww2.arb.ca.gov/sites/default/files/2022-08/Collective%20EJ%20Statement%20on%20Engineered%20Carbon%20Capture%2C%20Use%2C%20and%20Storage%20%28CCUS%29.pdf
- 192.Holmström L.The mother of environmental justice. 2018. https://q.sustainability.illinois.edu/hazel-johnson-and-the-toxic-doughnut/




