Skip to main content Accessibility help
×
Hostname: page-component-586b7cd67f-dsjbd Total loading time: 0 Render date: 2024-11-28T23:34:32.492Z Has data issue: false hasContentIssue false

12 - SDG13, climate action: health systems as stakeholders and implementors in climate policy change

Published online by Cambridge University Press:  11 January 2024

Scott L. Greer
Affiliation:
University of Michigan
Michelle Falkenbach
Affiliation:
European Observatory on Health Systems and Policies
Josep Figueras
Affiliation:
European Observatory on Health Systems and Policies
Matthias Wismar
Affiliation:
European Observatory on Health Systems and Policies

Summary

Climate Action is one of the United Nation’s Sustainable Development Goals. Yet, despite calls for action, global governments have broadly not taken consequential change to reduce carbon outputs and mitigate warming. Our chapter argues that a primary cause of this inaction is political conflict and policy capacity. Without strong economic incentives and facing constrained resources, governments may opt to proceed with the status quo. Here, health systems present a critical resource to engage nations in climate action. Health systems produce political leverage as major political stakeholders across nations, globally, for engaging in broader climate policy and a wealth of resources inherent to health systems – expertise, funding – to directly implement climate policy. The case study of the city of Toronto in Canada offers lessons for directly involving health systems in subnational climate action as policy stakeholders and implementors, and the co-benefits health system engagement brings to promote climate action intersectorally. Toronto provides an important case for high-latitude countries that will soon be facing climate hazards tropical nations have been grappling with for centuries. Engaging health systems in climate action policy processes may improve the likelihood of success for strengthening resilience and adaptivity to climate related hazards.

Type
Chapter
Information
Health for All Policies
The Co-Benefits of Intersectoral Action
, pp. 219 - 246
Publisher: Cambridge University Press
Print publication year: 2024
Creative Commons
Creative Common License - CCCreative Common License - BYCreative Common License - NCCreative Common License - ND
This content is Open Access and distributed under the terms of the Creative Commons Attribution licence CC-BY-NC-ND 4.0 https://creativecommons.org/cclicenses/

12.1 Introduction

In August 2021 and March 2023, the Intergovernmental Panel on Climate Change (IPCC) starkly outlined humanity’s inflection point with climate change: we must act now or face severe and irreversible consequences resulting from global warming driven by human emissions. Climate events directly threaten human health across a broad spectrum of issues – communicable diseases, heat events and natural disasters – which all present acute and chronic threats to human morbidity and mortality. Climate Action is one of the United Nation’s Sustainable Development Goals. Yet despite calls for action, global governments have broadly not taken consequential change to reduce carbon outputs and mitigate warming. Our chapter argues that a primary cause of this inaction is political conflict and policy capacity. Without strong economic incentives and facing constrained resources, governments may opt to proceed with the status quo. Here, health systems present a critical resource to engage nations in climate action. Health systems produce political leverage as major political stakeholders across nations, globally, for engaging in broader climate policy and a wealth of resources inherent to health systems – expertise, funding – to directly implement climate policy.

The case study of the city of Toronto in Canada offers lessons for directly involving health systems in subnational climate action as policy stakeholders and implementors, and the co-benefits health system engagement brings to promote climate action intersectorally. Toronto provides an important case for high-latitude countries that will soon be facing climate hazards tropical nations have been grappling with for centuries. Engaging health systems in climate action policy processes may improve the likelihood of success for strengthening resilience and adaptivity to climate-related hazards.

12.2 What is SDG13 and how can health policy contribute?

Planetary health is inextricably related to human health. Anthropogenic climate change has been measurable since approximately 1900 CE (Reference CrowleyCrowley, 2000). The measurable effects of climate change increased substantially over the past two decades and will continue to accelerate in the future. We see these changes visibly in the increased frequency of natural and co-occurring natural and human-made disasters, adverse weather events including heat waves, sea level rise, and possibly the most salient, communicable disease transmission. The increase in individual events and their overlap necessitate immediate action to protect the health of the planet and the health of humans. This chapter outlines the unique position of health systems as 1) primary economic and political stakeholders in climate change policymaking and 2) essential actors in mitigating the adverse effects of climate change on human health. In both ways, health systems are vital actors in “strengthening resilience and adaptivity to climate related hazards and natural disasters” (SDG13 UN) related to anthropogenic climate change.

Health systems are primary parts of the economy and the political arena across all nations. In OECD nations, health accounts for a large part of government spending (OECD, 2019). While this amount varies across countries, health care systems across OECD countries account for a substantial proportion of social spending (OECD, 2019, 11). In some nations, health accounts for the greatest proportion of government spending on social programmes (for example, the United States). Spending on health systems in OECD nations will very likely increase in coming decades as population growth slows and citizens age substantially, necessitating increased health spending (OECD, 2021). Low-income countries will see increased need for spending on health systems as health risks increase with climate change (UNFCC, 2018).

While spending does not always translate directly to political engagement, health care sectors are major political stakeholders in OECD nations. High degrees of political leverage were engendered from long histories of policy engagement due to the professionalism of medicine and science (Reference BestBest, 2019; Reference StarrStarr, 1982; Reference StrachStrach, 2015). Sustained political leverage for health systems also arises from the ways in which social policy systems have most often been structured around health care, as opposed to welfare, in OECD nations (Reference Lynch and PereraLynch & Perera, 2017; Reference StarrStarr, 1982; Reference TuohyTuohy, 2018). This centring of health care as opposed to social policy persists across OECD nations, even among lower-income OECD nations, where health systems may have sustained political leverage, even if publicly funded bureaucratic counterparts do not.

Health systems are also major contributors to climate change. For example, emissions from the US health care sector are among the highest (in absolute and per capita terms) of any health care system in the world, accounting for 8.5% of total greenhouse gas emissions nationwide in 2018 (Reference Karliner, Slotterback and BoydKarliner et al., 2019; Medical Society Consortium on Climate and Health, 2021, 9; Reference Pichler, Jaccard and WeiszPichler et al., 2019). Health care systems also exert substantial influence as consumers in general and are primary consumers for a number of specific industries. Examples include pharmaceutical manufacturing, which accounts for up to 10% of total greenhouse gas emissions in the United States (Reference 240Belkhir and ElmeligiBelkhir & Elmeligi, 2019), and medical disposables (Reference Campion, Thiel and WoodsCampion et al., 2015), which can produce more carbon by up to a factor of ten than non-disposable alternatives (Reference McGain, McAlister, McGavin and StoryMcGain et al., 2010; Reference McPherson, Sharip and GrimmondMcPherson et al., 2019; Reference Sherman, Raibley and EckelmanSherman et al., 2018). Per unit carbon emissions vary across pharmaceutical manufacturers (Reference 240Belkhir and ElmeligiBelkhir & Elmeligi, 2019), implying that consumer choice by health care systems, or broad regulatory reforms, can lead to industry-wide improvements in emissions. In addition to consumption practices, simple, low-cost modifications to standard operating procedures can lead to significant energy and carbon savings. Surgical procedures in particular can be carbon intensive (Reference MacNeill, Lillywhite and BrownMacNeill, Lillywhite & Brown, 2017). Much like pharmaceutical manufacturing, the carbon impact of different surgical approaches varies, implying potential for industry-wide improvement (Reference Sherman, Le and LamersSherman et al., 2012).

Health systems can engage as leaders in reducing their outputs to mitigate climate change and have a direct interest in doing so to reduce the adverse health effects of climate change. Health systems around the globe will be a first line of defence for humans against the short- and long-term adverse health outcomes arising from climate change. Engaging health systems as key stakeholders in climate action policy processes upstream and downstream may improve the likelihood of success for strengthening resilience and adaptivity to climate-related hazards and natural disasters.

12.3 Causal pathways between health systems, climate change health action and co-benefits

Climate change is inextricably related to health outcomes. Health systems, as upstream key stakeholders in the political arena of most countries and downstream responders, or implementors to short- and long-term adverse health effects of climate change, are essential actors in achieving SDG13 climate change goals (see Fig. 12.1). The actions health systems take will likely produce co-benefits to other sectors through policy diffusion to produce intersectoral action in climate policy across other sectors, or direct climate mitigation benefits through internal health system changes.

Fig. 12.1 Co-benefits for climate change through health system actions

12.3.1 Responding to upstream climate change: health systems as critical economic and political stakeholders in driving support for climate change policy

By virtue of the large proportion of political debates across OECD nations centred around health care and the economic prowess of health systems themselves, health systems are critical climate policy actors with the ability to shape agenda setting, influence political decisionmaking, and implement policies on the ground. Health systems can lead in climate policy debates and initiate policy change in other sectors and communities. Too long have health care and public health remained siloed from environmental health and climate concerns. Health systems are in a unique position to shift this notion and adopt a One-Health approach to climate action.

Many countries around the world are taking action to mitigate and prepare for climate change. Yet many more countries remain held back by various political factors contingent upon perceived benefits of engaging in climate change policy and institutional arrangements that may make policy action more or less viable. Agenda setting refers to whether or not topics become available to be considered for policy action (Reference KingdonKingdon, 1990; Reference Schneider and IngramSchneider & Ingram, 1993; Reference StoneStone, 1989). In countries where climate change is highly controversial, at the national or subnational level, engaging health systems as critical political players or stakeholders may improve the likelihood that climate policy is considered as a part of the political agenda in a jurisdiction (Reference StokesStokes, 2020).

Policy decisionmaking refers to the process by which political decisions are made that influence what policy outcomes, or formal or informal governmental actions on a specific topic, are generated or not. Policy decisionmaking is also influenced by a variety of complex factors. One critically important factor is the role of stakeholder groups. Stakeholder groups with stronger economic positions and coalitions of actors – large groups of well organized actors, such as professional organizations – wield more influence in political decisionmaking (Reference Eaton and WeirEaton & Weir, 2015). Health care systems across OECD nations persist as strong stakeholder coalitions because of their firm foothold in governmental spending valuing health care over other types of social policy, and economic power in privatized health systems (Reference Béland and WaddanBeland & Waddan, 2012; Reference FoxFox, 2016; Reference HackerHacker et al., 2004; Reference KingdonKingdon, 1990; Reference StarrStarr, 1982; Reference TuohyTuohy, 2018). Once climate policy is on the agenda, organized mobilization by health systems may positively influence the likelihood of tipping national and subnational governments in favour of climate action, producing climate action co-benefits across jurisdictions.

Finally, health systems have crucial roles to play in policy implementation. Health system engagement in climate policy implementation may not only help speed implementation once policy has been generated but also help initiate policy action through diffusion. Policy diffusion is defined as occurring when one government’s decision about whether to adopt a policy innovation is influenced by the choices made by other governments (Reference Graham, Shipan and VoldenGraham, Shipan & Volden, 2013, 675). Health systems, as key public or private stakeholders heavily involved in political decisionmaking across nations, have the ability to influence policy diffusion by acting as early adopters in climate change policy, while continuing to advocate for societal transition to renewable energy (Reference Karliner, Slotterback and BoydKarliner et al., 2019, 36). Extensive co-benefits are produced when health systems engage in climate policy implementation across sectors, strengthening overall resilience and adaptivity (United Nations, 2021). Examples of climate policy implementation actions are outlined in the next section.

Policy diffusion is especially important in federated systems, where subnational governments may have varying degrees of adoption or movement towards climate policy. Yet policy diffusion can also happen intersectorally and internationally. Here, climate policy adaptation by health systems as primary components of a state may increase the likelihood of adoption of climate mitigation strategies by other state sectors (infrastructure, housing, education) or by other peer-countries (Reference BernauerBernauer, 2013, 437). There is much evidence to support policy diffusion as a mechanism for innovative or evidence-based health policies (Reference Adolph, Amano and Bang-JensenAdolph et al., 2020; Reference 242Grogan, Jones and PachecoGrogan, Jones & Pacheco, 2017; Reference Shipan and VoldenShipan & Volden, 2008; Reference TarrTarr, 2001), and a growing body of evidence to support policy diffusion as a mechanism for environmental policies (Reference Bromley-Trujillo, Butler and PoeBromley-Trujillo et al., 2016). Health systems may help bridge the gap to facilitate policy diffusion across sectors. Health systems engaging in housing policy investments in the United States or lobbying for social spending in European nations (Reference LynchLynch, 2019), are notable examples.

12.3.2 Responding to downstream climate effects on health: health systems as essential actors in responding to and mitigating adverse effects of climate change in the short and long term

The IPCC identifies major greenhouse gas emitting sectors as transport, buildings, industry, electricity, and land use practices, including agriculture and forestry. According to the COP21 glossary, decarbonization refers to the goal of energy-consuming processes producing no net (uncaptured) CO2. As major consumers of energy and custodians of large building complexes, health care systems may be most directly positioned to influence those sectors toward decarbonization through the policy channels outlined above. In addition to upstream policy activities aimed at major and more formalized regulatory or legislative climate policy interventions, health care systems can act as policy implementors by taking immediate action within their own systems. Within-system changes may be particularly valuable in high-conflict contexts, which will be discussed shortly.

Downstream, direct actions taken by health care systems directly address a variety of climate-related health effects, while producing many intersectoral co-benefits. For example, health care systems can influence industry by setting low-carbon standards for their consumables, which account for 71% of the sector’s emissions (Reference Karliner, Slotterback and BoydKarliner et al., 2019, 5). Specific steps that health care systems could advocate for include investing in greener building materials for new construction or retrofitting old buildings to reduce carbon consumption for indoor climate control (Reference Karliner, Slotterback and BoydKarliner et al., 2019). Additional benefits can be realized through investment in carbon-capturing green infrastructure, including living roofs and walls (Reference 241Coutts and HahnCoutts & Hahn, 2015). Green buildings and open spaces provide important co-benefits particularly in the urban context, increasing the effectiveness and value of local ecosystem services such as runoff management (Reference Bao Jie, Zhu and Xue ZhaoHe et al., 2019) and capturing airborne particulate matter (Reference 241Coutts and HahnCoutts & Hahn, 2015). Health outcomes and the importance of health care systems have historically been absent from the policy discussion around ecosystems services (Reference Ford, Graham and WhiteFord, Graham & White, 2015; Reference 245Sandifer, Sutton-Grier and WardSandifer, Sutton-Grier & Ward, 2015). Health systems engaging in this area of policy could expand and improve the economic valuation of the quantifiable benefits (ecosystem services) provided by natural systems for human health as well as climate mitigation (de Groot et al., 2010; Reference Van Ripervan Riper et al., 2017).

In addition to longer-term decarbonization investment, climate change is driving acute but unpredictable adverse events that are placing, and will continue to place, strong demands on health care systems. Health care systems are ideally situated to initiate or support policies designed to mitigate and manage the impacts of these events. Heat waves and emerging infectious diseases are classic examples of acute climate-driven hazards with unpredictable onset times that require management through policy. Natural disasters, such as hurricanes and wildfires, are described in more detail in the supplemental case study (Appendix 1). We describe the health threats posed by each category of event (heat waves and infectious diseases); discuss mitigation and planning strategies that would benefit from health system involvement; and demonstrate potential co-benefits emerging from action on these threats.

12.3.3 Heat waves

Climate change is predicted to drive longer, more intense, and more frequent heat waves, particularly in temperate regions that are not equipped to manage extreme heat (Reference Arnell, Lowe and ChallinorArnell, Lowe & Challinor, 2019; Reference Meehl and TebaldiMeehl & Tebaldi, 2004). Heat waves are defined as “a period of abnormally hot weather lasting longer than two days” by the United States National Weather Service. Heat waves increase morbidity and mortality, particularly in young children and the elderly (Reference Haines, Kovats and Campbell-LendrumHaines et al., 2006; Reference Herrmann and SauerbornHerrmann & Sauerborn, 2018; Reference Knowlton, Rotkin-Ellman and KingKnowlton et al., 2009; Reference O’Neill and EbiO’Neill & Ebi, 2009). Exposure to chronic heat stress can lead to cardiovascular illness, chronic kidney disease, and mental health impacts (Reference Kjellstrom, Butler and LucasKjellstrom et al., 2009; Reference O’Neill and EbiO’Neill & Ebi, 2009; Reference Xiang, Bi and PisanielloXiang et al., 2014). Manual labourers, including those who work outdoors such as farmers and construction workers, and those who may work with process-generated heat, such as factory workers and food service workers, are particularly at risk of negative impacts due to occupational exposure (Reference Venugopal, Latha and ShanmugamVenugopal et al., 2020; Reference Xiang, Bi and PisanielloXiang et al., 2014).

12.3.4 Heat waves: the role of health systems and evidence-based actions

Health systems can work to mitigate the health impacts of heat waves in several specific ways. First, building green buildings and modifying open spaces to include tree cover can help mitigate the impacts of heat waves in buildings and in neighbouring areas, respectively (Reference Aflaki, Mirnezhad and GhaffarianhoseiniAflaki et al., 2017; Reference Onishi, Cao and ItoOnishi et al., 2010). In addition to saving cooling costs and the carbon emissions that come with air conditioning (Reference Wong, Cheong and YanWong et al., 2003), these steps can help to buffer patients from indoor temperature swings, and will minimize impacts on particularly at-risk groups of employees such as food service workers and construction workers employed by health systems (Reference Xiang, Bi and PisanielloXiang et al., 2014). Higher vegetation cover at the neighbourhood scale (between 300m and 1km) can be correlated with improved health outcomes across a variety of measures, when neighbourhood and personal socioeconomic status are controlled for (Reference BeckerBecker et al., 2019; Reference JeneretteJenerette et al., 2016; Reference MaasMaas et al., 2009), indicating that investment in tree cover around health care facilities could benefit the surrounding neighbourhood as well as the specific buildings. Health systems can also participate in planning for heat waves. Many municipalities lack heat-wave response plans (Reference Bernard and McGeehinBernard & McGeehin, 2004). Health systems are well placed to raise awareness of the health impacts of heat waves, which may be less visible than those of other weather-related disasters. In addition, health systems have the expertise to help local governments develop plans for heat-wave response.

12.3.5 Emerging and migrating communicable diseases

Climate change is predicted to cause shifts in the ranges of many diseases currently restricted to warmer areas (Reference Ciota and KeyelCiota & Keyel, 2019; Reference Tesla, Demakovsky and MordecaiTesla et al., 2018) and to alter the relative prevalence and severity of pathogens throughout their ranges (Reference Mordecai, Ryan and CaldwellMordecai et al., 2020). High-latitude nations currently focused on chronic disease treatment will need to adapt their models of care to address emerging communicable diseases and should learn lessons from warm climate nations (Reference Kavanagh and SinghKavanagh & Singh, 2020). Due to increasing temperatures, mosquito vectors of infectious disease are expanding their ranges toward the poles (Reference BartlowBartlow et al., 2019; Reference CarvalhoCarvalho et al., 2015), as are parasites (Reference YorkYork et al., 2015) and pathogens (Reference GonzálezGonzalez et al., 2010; Reference MaroliMaroli et al., 2008). From the perspective of any given location, the climate-driven shift in disease prevalence is unlikely to be predictable or orderly (Reference Ciota and KeyelCiota & Keyel, 2019). At local levels, small differences in temperature microclimate can drive large differences in disease risk, particularly in vector-borne pathogens such as malaria, dengue or zika virus (Reference WimberlyWimberly et al., 2020). Health systems will naturally be at the forefront of coping with emerging or migrating infectious diseases as they occur, but they can also play a role in preparing governments to cope with future threats.

12.3.6 Emerging and migrating communicable diseases: the role of health systems and evidence-based actions

Health systems can prepare for unpredictable and novel disease surges by planning for emerging epidemic diseases following procedures used to prepare for natural disasters. In addition to preparing for novel diseases, using green infrastructure in hospital grounds will reduce the local temperature and therefore the likelihood of an on-grounds disease outbreak. Incidence of viral diseases can track local temperature microclimates at the spatial scale of city blocks, with hotter neighbourhoods experiencing higher disease incidence (Reference WimberlyWimberly et al., 2020), although socioeconomic status can be confounded with high local temperatures (Reference SantosSantos et al., 2020; Reference TelleTelle et al., 2021). Reducing local heat island effects could therefore mitigate the risk of a local outbreak.

Urban greening can also produce benefits for infectious disease management through a variety of mechanisms beyond reduction in local temperature. Vegetation increases surface permeability across cities, thereby slowing down runoff (Reference Bao Jie, Zhu and Xue ZhaoHe et al., 2019; Reference Li, Liu and HuLi et al., 2018; Reference Mentens, Raes and HermyMentens, Raes & Hermy, 2006). Slowing or reducing runoff volumes decreases the risk of runoff being contaminated with untreated sewage and other potentially dangerous substances (Reference Zhang, Miao and WangZhang et al., 2015). Urban runoff often contains high concentrations of human-associated pathogens (Reference ColfordColford et al., 2012; Reference Mallin and McIverMallin & McIver, 2012), as well as pharmaceuticals, including antibiotics (Reference Almakki, Jumas-Bilak and MarchandinAlmakki et al., 2019). This combination can lead to the evolution of antibiotic resistance in potentially pathogenic bacteria strains (Reference Almakki, Jumas-Bilak and MarchandinAlmakki et al., 2019). Urban runoff can impact humans through direct contact and by contaminating agricultural systems and impacting food chains (Reference GillisGillis, 2012). Health care buildings concentrate both pharmaceuticals and potential pathogens, making runoff management a high priority for the built environment of health care facilities (Reference Devarajan, Laffite and Kyela MulajiDevarajan et al., 2016; Reference Kilunga, Kayembe and LaffiteKilunga et al., 2016; Reference Laffite, Kilunga and KayembeLaffite et al., 2016).

12.4 Governance and politics: conceptual issues

As discussed above, health systems bring an enormous amount of value to the table in their 1) upstream ability to promote climate change policy investments and 2) downstream, direct involvement in climate change mitigation through health and climate co-benefits, both short term and long term. Yet, while health systems have such substantial potential, the essential question persists: how do we attain these benefits? To answer this question, we must ask: 1) how do we actually engage health systems in climate change policy processes and 2) once health systems are on board, how do we mitigate conflict and constraints from other actors and systems to successfully promote climate change policy? To answer both questions, it is useful to think about: the degrees of conflict involved in climate policy discourse across governance systems; institutional constraints; and investments in health care systems.

Despite overwhelming and indisputable evidence of the reality of anthropogenic climate change from around the world, climate change is a policy space that still evokes high levels of conflict (see Table 12.1). High levels of conflict arise in this policy space as a result of the threat (real and perceived) to existing economies and entrenched systems (Reference StokesStokes, 2020; Reference StoneStone, 1989). Thus, even when nations may place high degrees of political importance on addressing climate change, it may be met with substantial policy conflict arising from entrenched actors or coalitions, political parties, and the public (see Table 12.1) (Reference Ansolabehere and KoniskyAnsolabehere & Konisky, 2014; Reference Peluso, Kearney and LesterPeluso, Kearney & Lester, 2020). Coalitions and political parties centring opposition to climate policy starkly oppose climate interventions to protect status quo political economies they rely on (for example, fossil fuel industries and political parties with primary coalitions tied to these industries).

Table 12.1 Health systems’ potential to promote climate change policy

Conflict
HighLow
Political importanceHighHealth systems engage in bureaucratic decisionmaking, implementors in low-conflict jurisdictionsHealth systems agenda setting, decisionmaking and implementation for policy diffusion
LowHealth systems implementors in low-conflict jurisdictionsHealth systems agenda setting, engage as implementors for policy diffusion

Institutional constraints interact with policy conflict. Institutional constraints refer to governance arrangements that make policy action more, or less, difficult at different levels (subnational vs. national) by placing different restrictions or checks on actors across multiple levels. Institutional constraints act as important accountability mechanisms and checks on power but may also inadvertently create barriers to policy action through fragmented systems and by gatekeeping political participation (see Tables 12.1 and 12.2). For example, highly fragmented and decentralized governance systems, such as in the United States, may necessitate more subnational action across policy mechanisms (agenda setting, decisionmaking and implementation) even in cases of high political importance and low policy conflict. Country context is very important in discerning institutional constraints that may impede or promote policy action and potential co-benefits (see Tables 12.1 and 12.2).

Table 12.2 Potential to engage health systems in climate change policy

Stakeholder capacity
HighLow
Bureaucratic capacityHighHealth systems agenda setting, decisionmaking and implementation for policy diffusionHealth systems implementation for policy diffusion; localized or subnational decisionmaking
LowHealth systems agenda settingHealth system engagement challenging

When seeking to engage health systems in climate change policy, the capacity of health systems and their capabilities or visibility as prominent stakeholders in a country context need to be considered (Reference Gailmard and PattyGailmard & Patty, 2007). While health systems may be aware of the intractable relationships between climate change and health, both their bureaucratic and stakeholder capacity will likely determine health systems’ ability to engage in policymaking and the potential for that engagement to be successful (see Table 12.2). Health systems’ capacity or bureaucratic capacity refers to resource investments in health systems such as knowledge or expertise and resources to carry out expert recommendations (funding and staffing). For example, do health systems in a nation or jurisdiction have sufficient funding to make investments in decarbonization, ecosystem services, or disaster planning and mitigation?

Do health systems in a nation or jurisdiction have the expertise (internal and/or scientific and public health expertise through intersectoral co-benefits) to make systems investments through policy implementation or advocate on behalf of climate change policy through agenda setting and decisionmaking? Stakeholder capacity is related to bureaucratic capacity but refers to the degree to which health systems are considered prominent political actors or stakeholders in a country context. OECD nations, which invest substantial amounts of GDP in health systems, are likely to perceive health systems as high-capacity stakeholders, even if there is variation in subnational bureaucratic capacity of health systems (see Table 12.2). Low-income countries may see different arrangements regarding health system engagement in climate change policy dependent on policy context (see Table 12.2). For example, while having lower traditional measures of bureaucratic capacity for health systems in terms of spending and expertise, many low-income countries have very high levels of bureaucratic expertise in health systems specific to infectious diseases. Here, intersectoral action produces co-benefits between health systems’ engagement with public health to generate high levels of policy mobilization in agenda setting and decisionmaking regarding communicable diseases and climate change, as seen in the COVID-19 pandemic (Reference Kavanagh and SinghKavanagh & Singh, 2020). Higher levels of bureaucratic capacity broadly or in specific policy spaces related to climate change, paired with higher levels of stakeholder capacity, may make health systems more likely to be engaged or become engaged in upstream climate change policy processes.

12.5 Case study: Toronto heat islands

12.5.1 Toronto as a case of health system solutions to climate-exacerbated heat islands

The case of solutions to climate-exacerbated urban heat islands (UHI) in the city of Toronto, Canada, acts as an exemplar case study of how health systems may act as policy implementors, driving action for policy diffusion in governmental climate debates. Toronto is a case of health systems policy engagement upstream and in policy implementation, producing co-benefits across sectors in climate change policy development.

Toronto is an ideal case for many reasons that may make it generalizable to other subnational and municipal governments around the globe. Toronto is a major, international city, comparable to other major metropolitan cities in OECD nations (City of Toronto, 2021). Major, global municipalities not only are primary sites of adverse effects of climate change including flooding and urban heat effects but also are experiencing increasing waves of growth and immigration. As major international city centres expand, municipalities like Toronto face domestic and international pressure to address these adverse effects, while also often having the ideology, wealth and intergovernmental transfers to do so (Reference SellersSellers, 2002). Canada, like many OECD nations, is a Westminster system, with strong federated governance promulgating discretion in many policy spaces to subnational, here provincial, governments. In Canada, this federated arrangement plays a key role in the nation’s national health system where the primary payer is the federal government, yet provinces have high degrees of autonomy on health care system delivery (Reference TuohyTuohy, 2018).

Heat islands are an ideal substantive policy case to examine the role of co-benefits because of their overlap in processes and outcomes related to health care systems, public health, ecosystems and disaster response. A set of mitigation strategies for Toronto’s UHIs have now been in place for a decade or more, allowing comparisons between them and comparisons to the previous status quo. Modelling studies show that Toronto’s ongoing mitigation strategies, including reflective pavement and building materials, green roofs and urban tree planting, can reduce mean temperatures in some areas by up to a degree during summer (Reference Wang, Berardi and AkbariWang, Berardi & Akbari, 2016). This contribution improves human wellbeing directly and reduces energy demand on indoor climate control (Reference Wang, Berardi and AkbariWang, Berardi & Akbari, 2016). These interventions reduce spending on energy, saving consumers up to $11 million CAD per year (Reference Akbari and KonopackiAkbari & Konopacki, 2004). Such interventions are particularly critical, and particularly high-payoff, in areas zoned for commercial and industrial use (Reference Rinner and HussainRinner & Hussain, 2011; Reference Wang, Berardi and AkbariWang, Berardi & Akbari, 2016). Heat waves in Toronto drive an approximate 10% increase in emergency services use over the baseline expectation, particularly in industrial areas (Reference Dolney and SheridanDolney & Sheridan, 2006).

Increasing urban tree cover is correlated to measurable health benefits, significantly reducing the need for emergency care for heat-related morbidity during heat waves (Reference Graham, Vanos and KennyGraham et al., 2016). Tree cover over 5% of ground surface was found to have a statistically significant association with heat-related health impacts in this study. By engaging in strategies such as urban greening and green roofs that both mitigate local health effects caused by the Toronto heat islands and capture carbon from the atmosphere, the Toronto approach furthers SDG13. Both the city’s current efforts and the framework for future planning allow a proactive approach to reducing climate change and mitigating its ongoing impact. We investigate the development of UHIs to understand the role of health systems in upstream and downstream climate change policy processes, and the development of co-benefits produced from direct or indirect intersectoral engagement in these policy processes.

12.5.2 How SDG13 in Toronto produces co-benefits for other SDGs

Reducing climate change and mitigating its impact will further many of the UN’s SDGs.Footnote 1 The case study of climate-related heat stress solutions in Toronto is an excellent example of these intersections. Climate change-related droughts resulting from and exacerbated by heat effects are already limiting the availability of food and water to many vulnerable groups worldwide. SDG1, no poverty, and SDG2, zero hunger, are therefore made more challenging by climate change. SDG3, good health and wellbeing, is furthered by reducing heat stress within health system infrastructure and in surrounding areas. Evidence shows that reducing UHI effects and providing green spaces have broad impacts on health and wellbeing within local communities.

Many of the local climate mitigation strategies that health systems can engage in to reduce UHI, such as green infrastructure and urban greening, also reduce runoff and provide filtered urban water systems, contributing to SDG6, clean water and sanitation. Since health systems are major landowners within many cities, a pivot towards greener infrastructure can further SDG11, sustainable cities and communities. Health systems can participate in the political process of developing local or regional plans to mitigate and manage climate change, and can underline the urgency of such planning by providing evidence of ongoing climate-change-driven health impacts.

12.5.3 Policy timeline

Toronto was an early actor in North America and worldwide in preparedness for climate-exacerbated heat effects and in efforts to reduce and mitigate climate change. A series of policies enacted in Toronto, starting in 1999 (Clean Air Partnership, 2008), aimed at reducing climate change and mitigating adverse effects of climate change. For this case study we are focusing on policies targeting UHIs within the city, though there are many other climate policies in place. These policies targeting UHIs include: the Heat Health Alert System, a Green Roof Bylaw, the Toronto Green Standard, an Eco-Roof Incentive Programme, Doubling the Tree Canopy Initiative, and “Greening” Surface Parking Lot guidelines (Reference Pacheco and GowerPacheco & Gower, 2016). Many of these policies relevant to UHI reductions have broader benefits to other categories of adverse climate events mitigation and preventing adverse health effects associated with climate change. We are focusing on the catalysing events for intersectoral policy action during the turn of the twenty-first century and will make comparisons across the past two decades to examine how Toronto has sustained these climate mitigation strategies to reduce UHIs.

12.5.4 Policy stakeholders

A key part of Toronto’s success in early and sustained climate action is participation across a wide array of stakeholders relevant to heat stress mitigation. This stakeholder network includes actors involved in climate change mitigation strategies and those involved in responding to the downstream, adverse events arising from UHIs such as increased morbidity and mortality, adverse weather events, and infectious diseases (as outlined in Section 12.2). A key component of this process is that health systems were perceived to be both mitigators and responders to UHI climate events (Reference Karliner, Slotterback and BoydKarliner et al., 2019). Health systems have also been involved as key stakeholders in these upstream and downstream roles in the policy process since 1999 and continue to be active today in climate policy agenda setting, decisionmaking and implementation. Toronto Public Health has also taken a direct role in all these policy activities since 1999, often leading policy decisionmaking and working to coordinate with health systems in their mitigation and response efforts (Acting Medical Officer of Health, 2016; Clean Air Partnership, 2008).

12.5.5 Co-benefits as an argument

In the policy discourse, co-benefits emerged in policy deliberations and rationale later on in the time period, appearing closer to 2020 (City of Toronto and Sustainability Solutions Group, 2019a). Co-benefits for climate resilience are now being adapted for measurable outcomes in the city of Toronto (City of Toronto and Sustainability Solutions Group, 2019b). While ‘co-benefits’ have not been consistently used until recently, Toronto’s advocacy for intersectoral action and partnership across relevant actors in mitigation and response persisted across the two-decade time-period. Rationale for these intersectoral partnerships were based on the benefits to different actors and the necessity for partnerships to generate comprehensive and effective policy responses (Acting Medical Officer of Health, 2016; Health Canada, 2020). The recent emergence of co-benefits may be a product of the proliferation of this language by the UN, IPCC and other international climate change organizations.

12.5.6 Factors related to Toronto’s success

Toronto’s ability to lead as an early actor in various policies targeting UHIs is likely related to multiple political and governance factors. These factors are related to a high level of intergovernmental and intersectoral collaboration, and high levels of policy capacity to further these collaborations (see Table 12.3). High policy capacity in Toronto’s case specifically included high capacity within the health system and the Toronto Department of Public Health to link health effects and target health outcomes to ecosystems services utilized to mitigate heat effects. Most important in many ways is the low level of political conflict and the high level of political support across levels and sectors of government (see Table 12.4). In these ways, Toronto’s success may be relevant to other major metropolitan areas around the world. Major metropolitan areas, globally, tend to be more liberal and more progressive in climate policy action. In country contexts where either intersectoral or intergovernmental collaboration is missing or hindered, resulting from capacity or political conflict, health systems as major stakeholders may still be able to engage in action as implementors or spur action as agenda setters at the metropolitan level.

Table 12.3 Intersectoral governance structures in Toronto urban heat islands policies

ToolsPossible governance actions with these tools
Goals and targetsEvidence supportPolicy guidanceImplementation and managementCoordinationAdvocacyMonitoring and evaluationFinancial supportLegal mandate
PlanPlanXXXXXXXXX
Indicators and targetsIndicatorsXXXX
TargetsXXXX
BudgetingPooled budget
Shared objectives
Coordinated budgetingFootnote 2XX
OrganizationMinisterial linkagesFootnote 3XXXXXXX
Specific ministers
OrganizationXXXXX
Legislative committees
Interdepartmental committees/unitsXXXXX
Departmental mergers
Civic engagementFootnote 4XXXXXXX
AccountabilityTransparent data
Regular reporting
Independent agency/evaluatorsFootnote 5XXXXXXX
Support for civil societyFootnote 6XX
Legal rights

Table 12.4 Political importance and conflict: the context of policymaking and implementation of Toronto urban heat islands policies

Conflict
LowHigh
Political importanceHighx
Low

12.6 Discussion and conclusion

As key political stakeholders, health systems have the potential to promote substantial climate policy reforms. Health systems can take climate policy action to support SDG13 through upstream agenda-setting, and as directly implementing policy within their systems. We describe three categories of climate-driven, acute adverse events that are particularly amenable to mitigation through health system involvement: climate-driven natural disasters (discussed in the supplemental case study (Appendix 1)), communicable disease outbreaks, and heat waves. We conduct a case study analysis of the influence of health systems in climate policy development for responses to urban health islands (UHI) in Toronto, Canada. In Toronto, health system actors provided crucial policy capacity and stakeholder mobilization advocating for policy agenda-setting, policy design and implementation, while simultaneously producing policy co-benefits to other sectors through UHI mitigation.

Successful climate mitigation strategies will need to address governance challenges associated with political conflict and resource capacity, both upstream and downstream in policy design and implementation. Engaging health systems as primary economic stakeholders in national political economies may enhance the likelihood of climate policy success by generating upstream advocacy for climate policies and downstream capacity to implement policies on the ground. Toronto demonstrates this potential through intergovernmental health systems mobilization in response to UHIs. Even in cases where political conflict is high and capacity is low, health system climate policy action will produce cross-sectoral co-benefits arising from health systems as high-capacity implementors.

Health systems not only have capacity for policy change, but also have notable skin in the game as first-line responders to the adverse effects of climate change. Based on our findings from the analysis of co-benefits, governance challenges and Toronto as a case study, health systems as implementors may take immediate steps through both: 1) participating in local planning for adverse weather events, and 2) making direct infrastructure investments in sustainable buildings and materials. These actions will promote immediate progress for SDG13 and mitigate the health impacts of natural disasters, heat waves and emerging disease outbreaks.

Footnotes

1 By encouraging investment in greener technologies through their purchasing power, health systems can spur innovation and encourage scaling in clean energy, thereby forwarding SDG7. SDG8, decent work and economic growth, can be forwarded by the materials, labour and innovation necessary to retrofit health care infrastructure to reduce fuel waste or build new green infrastructure. Investment by such a large sector of the economy will provide jobs in the short term and build local skills for similar work throughout the economy. In addition, improving the physical environment within buildings will increase wellbeing among employees. Both through direct investment in sustainable buildings and through using their purchasing power to convince upstream industries to adopt greener manufacturing processes, health systems can impact SDG9, industry, innovation and infrastructure. Improvements in physical infrastructure and manufacturing processes driven by health system investment will spread to other, non-health-related, sectors of the economy. By more effectively managing their waste and investing in responsible waste-management infrastructure, health systems can further SDG12, responsible consumption and production. Because of the necessity of single-use, sterile items in health care, health care systems generate large volumes of waste. Using their purchasing power to encourage sustainable and equitable waste management systems will reduce both the carbon footprint of health care and make waste management infrastructure available to other sectors.

2 Ontario Provincial Government (Acting Medical Officer of Health, 2016, 6).

3 Toronto Environmental and Energy Departments (City of Toronto and Sustainability Solutions Group, 2019a, 26–28; Penney, 2012).

5 Canadian Federal Government (Health Canada, 2020; Toronto Medical Officer of Health, 2018).

6 United Nations SDGs (Acting Medical Officer of Health, 2016, 10).

References

Acting Medical Officer of Health (2016). Climate Change and Health Strategy: 2016 Update. (http://www.toronto.ca/legdocs/mmis/2014/hl/bgrd/backgroundfile-73622.pdf, 31 August 2021).Google Scholar
Adolph, C, Amano, K, Bang-Jensen, B et al. (2020). Pandemic Politics: Timing State-Level Social Distancing Responses to COVID-19. medRxiv. (https://doi.org/10.1101/2020.03.30.20046326)CrossRefGoogle Scholar
Aflaki, A, Mirnezhad, M, Ghaffarianhoseini, A et al. (2017). Urban Heat Island Mitigation Strategies: A State-of-the-Art Review on Kuala Lumpur, Singapore and Hong Kong. Cities, 62(Feb):131–45. (https://doi.org/10.1016/J.CITIES.2016.09.003)CrossRefGoogle Scholar
Akbari, H, Konopacki, S (2004). Energy Effects of Heat-Island Reduction Strategies in Toronto, Canada. Energy, 29(2):191210. (https://doi.org/10.1016/J.ENERGY.2003.09.004)CrossRefGoogle Scholar
Almakki, A, Jumas-Bilak, E, Marchandin, H et al. (2019). Antibiotic Resistance in Urban Runoff. Sci Total Environ, 667:6476. (https://doi.org/10.1016/J.SCITOTENV.2019.02.183)CrossRefGoogle ScholarPubMed
Ansolabehere, S, Konisky, DM (2014). Cheap and Clean How Americans Think about Energy in the Age of Global Warming. Cambridge MA: MIT Press. (https://mitpress.mit.edu/books/cheap-and-clean)CrossRefGoogle Scholar
Arnell, NW, Lowe, JA, Challinor, AJ (2019). Global and Regional Impacts of Climate Change at Different Levels of Global Temperature Increase. Clim Change, 155(3):377391. (https://doi.org/10.1007/S10584-019-02464-Z)CrossRefGoogle Scholar
Bartlow, AW et al. (2019). Forecasting zoonotic infectious disease response to climate change: mosquito vectors and a changing environment. Vet sci, 6(2):40.CrossRefGoogle Scholar
Becker, DA et al. (2019). Is green land cover associated with less health care spending? Promising findings from county-level Medicare spending in the continental United States. Urban For Urban Green, 41:3947.CrossRefGoogle Scholar
Béland, D, Waddan, A (2012). The politics of policy change: welfare, medicare, and social security reform in the United States. Georgetown University Press.Google Scholar
Belkhir, L, Elmeligi, A (2019). Carbon Footprint of the Global Pharmaceutical Industry and Relative Impact of Its Major Players. J Clean Prod, 214:185194. (https://doi.org/10.1016/J.JCLEPRO.2018.11.204)CrossRefGoogle Scholar
Bernard, SM, McGeehin, MA (2004). Municipal Heat Wave Response Plans. Am J Public Health, 94(9):1520. (https://doi.org/10.2105/AJPH.94.9.1520)CrossRefGoogle ScholarPubMed
Bernauer, T (2013). Climate Change Politics. Annu Rev Polit Sci. Annual Reviews. (https://doi.org/10.1146/annurev-polisci-062011-154926)CrossRefGoogle Scholar
Best, RK (2019). Common Enemies: Disease Campaigns in America. Oxford University Press.CrossRefGoogle Scholar
Bromley-Trujillo, R, Butler, JS, Poe, J et al. (2016). The Spreading of Innovation: State Adoptions of Energy and Climate Change Policy. Rev Policy Res, 33(5):544565. (https://doi.org/10.1111/ropr.12189)CrossRefGoogle Scholar
Campion, N, Thiel, CL, Woods, NC et al. (2015). Sustainable Healthcare and Environmental Life-Cycle Impacts of Disposable Supplies: A Focus on Disposable Custom Packs. J Clean Prod, 94:4655. (https://doi.org/10.1016/J.JCLEPRO.2015.01.076)CrossRefGoogle Scholar
Carvalho, BM et al. (2015). Ecological niche modelling predicts southward expansion of Lutzomyia (Nyssomyia) flaviscutellata (Diptera: Psychodidae: Phlebotominae), vector of Leishmania (Leishmania) amazonensis in South America, under climate change. PLoS One, 10(11):e0143282.CrossRefGoogle ScholarPubMed
Ciota, AT, Keyel, AC (2019). The Role of Temperature in Transmission of Zoonotic Arboviruses. Viruses, 11(11). (https://doi.org/10.3390/V11111013)CrossRefGoogle ScholarPubMed
City of Toronto and Sustainability Solutions Group (2019a). TransformTO: Climate Action for a Healthy, Equitable, Prosperous Toronto. (https://www.ssg.coop/transformto/, 24 September 2022)Google Scholar
City of Toronto and Sustainability Solutions Group (2019b). Benefits of Actions to Reduce Greenhouse Gas Emissions in Toronto: Climate Resilience. (https://www.toronto.ca/wp-content/uploads/2019/06/971c-Benefits-of-Actions-to-Reduce-Greenhouse-Gas-Emissions-in-Toronto-Climate-Resilience.pdf, 31 August 2021)Google Scholar
Clean Air Partnership (2008). Climate Change Adaptation in the City of Toronto Lessons for Great Lakes Communities Clean Air Partnership. (https://glslcities.org/wp-content/uploads/2015/05/Toronto_ClimateChangeAdaptation.pdf)Google Scholar
Colford, JM Jr et al. (2012). Using rapid indicators for Enterococcus to assess the risk of illness after exposure to urban runoff contaminated marine water. Water res, 46(7):21762186.CrossRefGoogle ScholarPubMed
Counts, NZ, Taylor, LA, Willison, CE, Galea, S (2021). Healthcare Lobbying on Upstream Social Determinants of Health in the US. Prev med, 153.CrossRefGoogle Scholar
Coutts, C, Hahn, M (2015). Green Infrastructure, Ecosystem Services, and Human Health. Int J Environ Res Public Health, 12(8):97689798. (https://doi.org/10.3390/IJERPH120809768)CrossRefGoogle ScholarPubMed
Crowley, TJ (2000). Causes of Climate Change Over the Past 1000 Years. Science, 289:5477. (https://science.sciencemag.org/content/289/5477/270/tab-pdf)CrossRefGoogle ScholarPubMed
De Groot, R et al. (2012). Integrating the ecological and economic dimensions in biodiversity and ecosystem service valuation. In Kumar, P (ed.), The economics of ecosystems and biodiversity: Ecological and economic foundations (London: Routledge), 940.Google Scholar
Devarajan, N, Laffite, A, Kyela Mulaji, C et al. (2016). Occurrence of Antibiotic Resistance Genes and Bacterial Markers in a Tropical River Receiving Hospital and Urban Wastewaters. PloS One, 11(2):e0149211. (https://doi.org/10.1371/JOURNAL.PONE.0149211)CrossRefGoogle Scholar
Dolney, T, Sheridan, S (2006). The Relationship between Extreme Heat and Ambulance Response Calls for the City of Toronto, Ontario, Canada. Environ Res, 101(1):94103. (https://doi.org/10.1016/J.ENVRES.2005.08.008)CrossRefGoogle ScholarPubMed
Eaton, C, Weir, M (2015). The power of coalitions: advancing the public in California’s public-private welfare state. Polit Soc, 43(1):332.CrossRefGoogle Scholar
Ford, AES, Graham, H, White, PCL (2015). Integrating Human and Ecosystem Health Through Ecosystem Services Frameworks. EcoHealth, 12(4):660671. (https://doi.org/10.1007/S10393-015-1041-4)Google Scholar
Fox, DM (2016). Health Policies, Health Politics. The British and American Experience, 19111965.Google Scholar
Gailmard, S, Patty, JW (2007). Slackers and Zealots: Civil Service, Policy Discretion, and Bureaucratic Expertise. Am J Pol Sci, 51(4):873889. (http://www.jstor.org/stable/4620105)CrossRefGoogle Scholar
Gillis, PL (2012). Cumulative Impacts of Urban Runoff and Municipal Wastewater Effluents on Wild Freshwater Mussels (Lasmigona Costata). Sci Total Environ, 431:348356. (https://doi.org/10.1016/J.SCITOTENV.2012.05.061)CrossRefGoogle ScholarPubMed
González, C et al. (2010). Climate change and risk of leishmaniasis in North America: predictions from ecological niche models of vector and reservoir species. PLoS Negl Trop Dis, 4(1):e585.CrossRefGoogle ScholarPubMed
Graham, DA, Vanos, JK, Kenny, NA et al. (2016). The Relationship between Neighbourhood Tree Canopy Cover and Heat-Related Ambulance Calls during Extreme Heat Events in Toronto, Canada. Urban For Urban Green, 20:180186. (https://doi.org/10.1016/J.UFUG.2016.08.005)CrossRefGoogle Scholar
Graham, ER, Shipan, CR, Volden, C (2013). The Diffusion of Policy Diffusion Research in Political Science. Br J Polit Sci, 43(3):673701. (https://doi.org/10.1017/S0007123412000415)CrossRefGoogle Scholar
Grogan, CM, Jones, DK, Pacheco, J (2017). Diffusion of ACA Policies across the American States. J Health Polit Policy Law, 42(2). (https://doi.org/10.1215/03616878-3766691)CrossRefGoogle Scholar
Hacker, JS et al. (2004). Privatizing Risk without Privatizing the Welfare State: The Hidden Politics of Social Policy Retrenchment in the United States. Am Polit Sci Rev, 98(2).CrossRefGoogle Scholar
Haines, A, Kovats, RS, Campbell-Lendrum, D et al. (2006). Climate Change and Human Health: Impacts, Vulnerability and Public Health. Public Health, 120(7):585–96. (https://doi.org/10.1016/J.PUHE.2006.01.002)CrossRefGoogle ScholarPubMed
Bao Jie, He, Zhu, Jin, Xue Zhao, Dong et al. (2019). Co-Benefits Approach: Opportunities for Implementing Sponge City and Urban Heat Island Mitigation. Land Use Policy, 86:147157. (https://doi.org/10.1016/J.LANDUSEPOL.2019.05.003)Google Scholar
Health Canada (2020). Reducing Urban Heat Islands to Protect Health in Canada. (https://www.canada.ca/en/services/health/publications/healthy-living/reducing-urban-heat-islands-protect-health-canada.html, 31 August 2021).Google Scholar
Herrmann, A, Sauerborn, R (2018). General Practitioners’ Perceptions of Heat Health Impacts on the Elderly in the Face of Climate Change—A Qualitative Study in Baden-Württemberg, Germany. Int J Environ Res Public Health 15(5). (https://doi.org/10.3390/IJERPH15050843)CrossRefGoogle Scholar
Jenerette, GD, Harlan, SL, Buyantuev, A et al. (2015). Micro-Scale Urban Surface Temperatures Are Related to Land-Cover Features and Residential Heat Related Health Impacts in Phoenix, AZ USA. Landsc Ecol, 31(4):745760. (https://doi.org/10.1007/S10980-015-0284-3)CrossRefGoogle Scholar
Jenerette, GD et al. (2016). Micro-scale urban surface temperatures are related to land-cover features and residential heat related health impacts in Phoenix, AZ, USA. Landsc Ecol, 31:745760.CrossRefGoogle Scholar
Permanente, Kaiser (2021). A Place to Call Home. Kaiser Permanente News. (https://about.kaiserpermanente.org/community-health/news/a-place-to-call-home, 16 January 2022)Google Scholar
Karliner, J, Slotterback, S, Boyd, R et al. (2019). Health Care’s Climate Footprint: How the Health Sector Contributes to the Global Climate Crisis and Opportunities for Action. (https://noharm-global.org/sites/default/files/documents-files/5961/HealthCaresClimateFootprint_092319.pdf)Google Scholar
Kavanagh, MM, Singh, R (2020). Democracy, Capacity, and Coercion in Pandemic Response: COVID-19 in Comparative Political Perspective. J Health Polit Policy Law, 45(6):9971012. (https://doi.org/10.1215/03616878-8641530)CrossRefGoogle ScholarPubMed
Kilunga, PI, Kayembe, JM, Laffite, A et al. (2016). The Impact of Hospital and Urban Wastewaters on the Bacteriological Contamination of the Water Resources in Kinshasa, Democratic Republic of Congo. J Environ Sci Health, 51(12):10341042. (https://doi.org/10.1080/10934529.2016.1198619)CrossRefGoogle Scholar
Kingdon, J (1990). Agendas, Alternatives and Public Policies. New York: Harper Collins.Google Scholar
Kjellstrom, T, Butler, AJ, Lucas, RM et al. (2009). Public Health Impact of Global Heating Due to Climate Change: Potential Effects on Chronic Non-Communicable Diseases. Int J Public Health, 55(2):97103. (https://doi.org/10.1007/S00038-009-0090-2)CrossRefGoogle ScholarPubMed
Knowlton, K, Rotkin-Ellman, M, King, G et al. (2009). The 2006 California Heat Wave: Impacts on Hospitalizations and Emergency Department Visits. Environ Health Perspect, 117(1):6167. (https://doi.org/10.1289/EHP.11594)CrossRefGoogle ScholarPubMed
Laffite, A, Kilunga, PI, Kayembe, JM et al. (2016). Hospital Effluents Are One of Several Sources of Metal, Antibiotic Resistance Genes, and Bacterial Markers Disseminated in Sub-Saharan Urban Rivers. Front Microbiol, 7:1128. (https://doi.org/10.3389/FMICB.2016.01128)CrossRefGoogle ScholarPubMed
Li, C, Liu, M, Hu, Y et al. (2018). Effects of Urbanization on Direct Runoff Characteristics in Urban Functional Zones. Sci Total Environ, 643:301–11. (https://doi.org/10.1016/J.SCITOTENV.2018.06.211)CrossRefGoogle ScholarPubMed
Lynch, J (2019). Populism, partisan convergence, and mobilization in Western Europe. Polity, 51(4):668677.CrossRefGoogle Scholar
Lynch, JF, Perera, IM (2017). Framing health equity: US health disparities in comparative perspective. J Health Polit Policy Law, 42(5):803839.CrossRefGoogle ScholarPubMed
Maas, J et al. (2009). Morbidity is related to a green living environment. J Epidemiol Community Health, 63(12):967973.CrossRefGoogle ScholarPubMed
McGain, F, McAlister, S, McGavin, A, Story, D (2010). The financial and environmental costs of reusable and single-use plastic anaesthetic drug trays. Anaesth intensive care, 38(3):538544.CrossRefGoogle ScholarPubMed
MacNeill, AJ, Lillywhite, R, Brown, CJ (2017). The Impact of Surgery on Global Climate: A Carbon Footprinting Study of Operating Theatres in Three Health Systems. Lancet Planet Health, 1(9):e381388. (https://doi.org/10.1016/S2542-5196(17)30162-6)CrossRefGoogle ScholarPubMed
McPherson, B, Sharip, M, Grimmond, T (2019). The impact on life cycle carbon footprint of converting from disposable to reusable sharps containers in a large US hospital geographically distant from manufacturing and processing facilities. Peer J, 7:e6204.CrossRefGoogle Scholar
Mallin, MA, McIver, MR (2012). Pollutant Impacts to Cape Hatteras National Seashore from Urban Runoff and Septic Leachate. Mar Pollut Bull, 64(7):13561366. (https://doi.org/10.1016/J.MARPOLBUL.2012.04.025)CrossRefGoogle ScholarPubMed
Maroli, M et al. (2008). The northward spread of leishmaniasis in Italy: evidence from retrospective and ongoing studies on the canine reservoir and phlebotomine vectors. Trop Med Int Health, 13(2):256264.CrossRefGoogle ScholarPubMed
Medical Society Consortium on Climate and Health (2021). The Costs of Inaction: The Economic Burden of Fossil Fuels and Climate Change on Health in the United States. (https://www.nrdc.org/sites/default/files/costs-inaction-burden-health-report.pdf)Google Scholar
Meehl, GA, Tebaldi, C (2004). More Intense, More Frequent, and Longer Lasting Heat Waves in the 21st Century. Science, 305(5686):994997. (https://doi.org/10.1126/science.1098704)CrossRefGoogle ScholarPubMed
Mentens, J, Raes, D, Hermy, M (2006). Green Roofs as a Tool for Solving the Rainwater Runoff Problem in the Urbanized 21st Century? Landsc Urban Plan, 77(3):217226. (https://doi.org/10.1016/J.LANDURBPLAN.2005.02.010)CrossRefGoogle Scholar
Mordecai, EA, Ryan, SJ, Caldwell, JM et al. (2020). Climate Change Could Shift Disease Burden from Malaria to Arboviruses in Africa. Lancet Planet Health, 4(9):e416423. (https://doi.org/10.1016/S2542-5196(20)30178-9)CrossRefGoogle ScholarPubMed
Muturi, EJ, Alto, BW (2011). Larval Environmental Temperature and Insecticide Exposure Alter Aedes Aegypti Competence for Arboviruses. Vector borne and zoonotic diseases (Larchmont, N.Y.), 11(8):11571163.Google Scholar
O’Neill, MS, Ebi, KL (2009). Temperature Extremes and Health: Impacts of Climate Variability and Change in the United States. J Occup Environ Med, 51(1):1325. (https://doi.org/10.1097/JOM.0B013E318173E122)CrossRefGoogle ScholarPubMed
OECD (2019). Health at a Glance 2019: OECD Indicators. Paris: OECD Publishing. (https://www.oecd-ilibrary.org/social-issues-migration-health/health-at-a-glance-2019_4dd50c09-en)Google Scholar
OECD (2021). Ageing and Long-Term Care – OECD. OECD. (https://www.oecd.org/els/health-systems/long-term-care.htm)Google Scholar
Onishi, A, Cao, X, Ito, T et al. (2010). Evaluating the Potential for Urban Heat-Island Mitigation by Greening Parking Lots. Urban For Urban Green, 9(4):323332. (https://doi.org/10.1016/J.UFUG.2010.06.002)CrossRefGoogle Scholar
Pacheco, E, Gower, S (2016). Toronto’s Heat Health Alert System Proactive Adaptation Can Help Save Lives Now and Prepare for Future Climate Change. (https://www.nrcan.gc.ca/changements-climatiques/impacts-adaptation/torontos-heat-health-alert-system/16295)Google Scholar
Peluso, N, Kearney, M, Lester, R (2020). Assessing the Role of Public Policy in Industrial Transitions: How Distinct Regional Contexts Inform Comprehensive Planning. (https://ceepr.mit.edu/workingpaper/assessing-the-role-of-public-policy-in-industrial-transitions-how-distinct-regional-contexts-inform-comprehensive-planning/)Google Scholar
Pichler, P-P, Jaccard, IS, Weisz, U et al. (2019). International Comparison of Health Care Carbon Footprints. Environ Res Lett, 14. (https://doi.org/10.1088/1748-9326/ab19e1)CrossRefGoogle Scholar
Rinner, C, Hussain, M (2011). Toronto’s Urban Heat Island—Exploring the Relationship between Land Use and Surface Temperature. Remote Sens, 3(6):12511265. (https://doi.org/10.3390/RS3061251)CrossRefGoogle Scholar
Sandifer, PA, Sutton-Grier, AE, Ward, BP (2015). Exploring Connections among Nature, Biodiversity, Ecosystem Services, and Human Health and Well-Being: Opportunities to Enhance Health and Biodiversity Conservation. Ecosyst Serv, 12:115. (https://doi.org/10.1016/J.ECOSER.2014.12.007)CrossRefGoogle Scholar
Santos, JPC et al. (2020). A perspective on inhabited urban space: land use and occupation, heat islands, and precarious urbanization as determinants of territorial receptivity to dengue in the city of Rio de Janeiro. Int J Environ Res Public Health, 17(18):6537.CrossRefGoogle ScholarPubMed
Schneider, A, Ingram, H (1993). Social Construction of Target Populations: Implications for Politics and Policy. Am Polit Sci Rev, 87(2):334347. (http://www.jstor.org/stable/2939044)CrossRefGoogle Scholar
Sellers, JM (2002). Governing from Below: Urban Regions and the Global Economy. Cambridge University Press.CrossRefGoogle Scholar
Sherman, JD, Raibley, IV LA Eckelman, MJ, (2018). Life cycle assessment and costing methods for device procurement: comparing reusable and single-use disposable laryngoscopes. Anesth Analg, 127(2):434443.CrossRefGoogle ScholarPubMed
Sherman, J, Le, C, Lamers, V et al. (2012). Life Cycle Greenhouse Gas Emissions of Anesthetic Drugs. Anesth Analg, 114(5):10861090. (https://doi.org/10.1213/ANE.0B013E31824F6940)CrossRefGoogle ScholarPubMed
Shipan, CR, Volden, C (2008). The Mechanisms of Policy Diffusion. Am J Polit Sci, 52(4). (https://www.jstor.org/stable/25193853?seq=1)CrossRefGoogle Scholar
Starr, P (1982). The Social Transformation of American Medicine. Basic Books.Google Scholar
Stokes, LC (2020). Short circuiting policy: Interest groups and the battle over clean energy and climate policy in the American States. USA: Oxford University Press.CrossRefGoogle Scholar
Stone, DA (1989). Causal Stories and the Formation of Policy Agendas. Polit Sci Q, 104.CrossRefGoogle Scholar
Strach, P (2015). Hiding Politics in Plain Sight: Cause Marketing, Corporate Influence, and Breast Cancer Policymaking. New York: Oxford University Press.Google Scholar
Tarr, GA (2001). Laboratories of Democracy? Brandeis, Federalism, and Scientific Management. Publius, 31(1):3746. (https://doi.org/10.1093/oxfordjournals.pubjof.a004880)CrossRefGoogle Scholar
Telle, O et al. (2021). Social and environmental risk factors for dengue in Delhi city: A retrospective study. PLoS Negl Trop Dis, 15(2):e0009024.CrossRefGoogle ScholarPubMed
Tesla, B, Demakovsky, LR, Mordecai, EA et al. (2018). Temperature Drives Zika Virus Transmission: Evidence from Empirical and Mathematical Models. Proc Royal Soc B, 285:20180795. (https://doi.org/10.1098/RSPB.2018.0795)CrossRefGoogle ScholarPubMed
Tuohy, C (2018). Remaking Policy: Scale, Pace and Political Strategy in Health Care Reform. University of Toronto Press. (https://www.remakingpolicy.com/)CrossRefGoogle Scholar
UNFCC (2018). Low-Income Countries Hit Hardest by Soaring Costs of Climate-Related Disasters. UNFCC News. (https://unfccc.int/news/low-income-countries-hit-hardest-by-soaring-costs-of-climate-related-disasters)Google Scholar
United Nations (2021). Goal 13 Climate Action: Take Urgent Action to Combat Climate Change and Its Impacts. Sustainable Development Goals. (https://www.un.org/sustainabledevelopment/climate-change/)Google Scholar
Van Riper, CJ et al. (2017). Incorporating sociocultural phenomena into ecosystem-service valuation: the importance of critical pluralism. BioScience, 67(3):233244.CrossRefGoogle Scholar
Venugopal, V, Latha, PK, Shanmugam, R et al. (2020). Occupational Heat Stress Induced Health Impacts: A Cross-Sectional Study from South Indian Working Population. Adv Clim Chang Res, 11(1):3139. (https://doi.org/10.1016/J.ACCRE.2020.05.009)CrossRefGoogle Scholar
Wang, Y, Berardi, U, Akbari, H (2016). Comparing the Effects of Urban Heat Island Mitigation Strategies for Toronto, Canada. Energy Build, 114:219. (https://doi.org/10.1016/J.ENBUILD.2015.06.046)CrossRefGoogle Scholar
Wimberly, MC et al. (2020). Land cover affects microclimate and temperature suitability for arbovirus transmission in an urban landscape. PLoS Negl Trop Dis, 14(9):e0008614.CrossRefGoogle Scholar
Wong, NH, Cheong, DKW, Yan, H et al. (2003). The Effects of Rooftop Garden on Energy Consumption of a Commercial Building in Singapore. Energy Build, 35(4):353364. (https://doi.org/10.1016/S0378-7788(02)00108-1)CrossRefGoogle Scholar
Xiang, J, Bi, P, Pisaniello, D et al. (2014). Health Impacts of Workplace Heat Exposure: An Epidemiological Review. Ind Health, 52(2):91101. (https://doi.org/10.2486/INDHEALTH.2012-0145)CrossRefGoogle ScholarPubMed
York, EM et al. (2015). Geographic range expansion for rat lungworm in North America. Emerging Infect Dis, 21(7):1234.CrossRefGoogle ScholarPubMed
Zhang, Q, Miao, L, Wang, X et al. (2015). The Capacity of Greening Roof to Reduce Stormwater Runoff and Pollution. Landsc Urban Plan, 144:142–50. (https://doi.org/10.1016/J.LANDURBPLAN.2015.08.017)CrossRefGoogle Scholar
Figure 0

Fig. 12.1 Co-benefits for climate change through health system actions

Figure 1

Table 12.1 Health systems’ potential to promote climate change policy

Figure 2

Table 12.2 Potential to engage health systems in climate change policy

Figure 3

Table 12.3 Intersectoral governance structures in Toronto urban heat islands policies

Figure 4

Table 12.4 Political importance and conflict: the context of policymaking and implementation of Toronto urban heat islands policies

Save book to Kindle

To save this book to your Kindle, first ensure [email protected] is added to your Approved Personal Document E-mail List under your Personal Document Settings on the Manage Your Content and Devices page of your Amazon account. Then enter the ‘name’ part of your Kindle email address below. Find out more about saving to your Kindle.

Note you can select to save to either the @free.kindle.com or @kindle.com variations. ‘@free.kindle.com’ emails are free but can only be saved to your device when it is connected to wi-fi. ‘@kindle.com’ emails can be delivered even when you are not connected to wi-fi, but note that service fees apply.

Find out more about the Kindle Personal Document Service.

Available formats
×

Save book to Dropbox

To save content items to your account, please confirm that you agree to abide by our usage policies. If this is the first time you use this feature, you will be asked to authorise Cambridge Core to connect with your account. Find out more about saving content to Dropbox.

Available formats
×

Save book to Google Drive

To save content items to your account, please confirm that you agree to abide by our usage policies. If this is the first time you use this feature, you will be asked to authorise Cambridge Core to connect with your account. Find out more about saving content to Google Drive.

Available formats
×