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Part II - One Health and Contemporary Legal Structures

Published online by Cambridge University Press:  25 September 2025

Katie Woolaston
Affiliation:
Griffith University, Queensland
Jane Kotzmann
Affiliation:
Deakin University, Victoria

Information

Type
Chapter
Information
The Cambridge Handbook of One Health and the Law
Existing Frameworks, Intersections and Future Pathways
, pp. 87 - 180
Publisher: Cambridge University Press
Print publication year: 2025

Part II One Health and Contemporary Legal Structures

7 Human Rights and One Health Mutual Benefits or Irreconcilable Differences?

7.1 Introduction

The relationship between One Health and human rights is both symbiotic and antagonistic. The objectives of One Health align with human rights to the extent that they advance specific rights, particularly the rights to life, health, and an adequate standard of living. One Health also promotes human dignity, the foundation of human rights, by improving environmental conditions and addressing threats to health that impact people’s lives. Yet the inherent anthropocentrism of human rights sits uneasily with the tripartite balance of One Health’s commitment to human, animal, and environmental health. The growing field of environmental human rights may offer some way forward for resolving this tension and advancing the legal framework for One Health.

Early environmental human rights jurisprudence positioned the environment as a precondition for the enjoyment of human rights. Human rights courts found that violations had occurred where environmental conditions directly affected specific human rights for particular people.Footnote 1 However, they did not accept that environmental degradation generally was a human rights issue and gave almost no consideration to animal or wildlife health.Footnote 2 More recently, the right to a clean, healthy, and sustainable environment has been recognised more widely as a standalone right, expanding the potential for human rights objectives to include protection of environmental health, and perhaps also animal health. However, it remains to be seen whether the framing of a healthy environment as a human right will be able to enhance One Health in a meaningful way, as its inherent anthropocentrism remains at odds with One Health’s more balanced tripartite approach.

This chapter will explore the relationship between human rights and One Health and consider the contribution that human rights law might make to the implementation of a One Health approach and the realisation of its objectives. It argues that the One Health and human rights can be mutually beneficial, but that this effect is largely limited to the human health pillar of One Health. When it comes to advancing environmental and especially animal health, human rights have less to offer and may in fact create barriers to a truly integrated approach. However, there are ways that this relationship could potentially be improved, and on balance there is more to be gained than lost from an open dialogue between human rights and One Health.

The chapter begins by providing a brief overview of human rights law and the specific rights that align most closely with One Health. This section also includes a short history of environmental rights, critiquing the way that the environment has typically been framed as being instrumental to human rights through a process known as the ‘greening’ of human rights. Section 7.3 then explores the benefits that human rights and One Health might offer to one another. Section 7.4 moves on to elaborate on the tensions between One Health and human rights, focusing on the anthropocentrism of human rights and considering the extent to which this is relieved by the right to a healthy environment. The chapter concludes by outlining some areas of potential for capitalising on the mutually beneficial aspects of the relationship and mitigating the anthropocentrism of human rights in a way that better promotes the triple objectives of One Health.

7.2 A Brief Overview of Human Rights

Human rights have both moral and legal dimensions. As a concept within political philosophy, human rights encompass the basic rights and freedoms that citizens are entitled to claim from their government. There exist different theoretical explanations for why human rights exist, and over time there have been debates about which things should properly be considered to be human rights.Footnote 3 Yet, despite these differences, all versions of human rights theory agree that human rights are possessed by all people, without discrimination, and that they give rise to duties that sit with the state, other individuals, or both.

In human rights theory and law, different rights are understood to have positive and negative dimensions that affect the way that obligations are framed in relation to each right. Positive obligations require governments to take some action in order to assure the enjoyment of the right; for example, by building schools to deliver the right to education. Negative obligations, by contrast, constrain government action; for example, by prohibiting torture or unreasonable limits on free speech.

In most countries, human rights are protected by law, either in constitutions, legislation, or judicial decisions. Here too there are many variations, often influenced by the specific political, cultural, or religious traditions of the state, its colonial past, or other historical experiences. For some countries, the national human rights instrument emerged following a revolution or independence movement; for example, those in France and America. In more recent times, however, domestic human rights laws have been strongly influenced by international and regional human rights treaties.

This chapter will focus on human rights as they are articulated in these international and regional treaties. This is done for several reasons. First, they are the most widely accepted set of human rights and have been implemented in the domestic laws of many countries, providing a set of common norms that are well understood. Second, countries that have signed and ratified human rights treaties are legally bound to comply with them under international law, making them a strong set of standards that are supported by various enforcement processes. Third, the international human rights treaties adopted under the auspices of the United Nations represent a framework that underpins the work of many UN agencies across different fields of endeavour, including those involved with One Health.Footnote 4 That being said, while most of the discussion here refers to international and regional human rights treaties, many of the comments made are broadly applicable to any human rights laws.

7.2.1 International Human Rights Framework

The United Nations human rights system consists of nine core treaties, which build on the foundational human rights instrument, the Universal Declaration of Human Rights.Footnote 5 Two principal treaties are the International Covenant on Civil and Political Rights (ICCPR)Footnote 6 and the International Covenant on Economic, Social and Cultural Rights (ICESCR).Footnote 7 Alongside these general instruments are several more specific treaties that focus either on particular human rights issues (for example the Convention Against Torture)Footnote 8 or on protecting particular vulnerable groups (for example the Convention on the Rights of the Child (CRC)Footnote 9 and the Convention on the Rights of Persons with Disabilities).Footnote 10 Typically, these human rights treaties are supported by a dedicated committee of experts that monitors states’ performance of their obligations, raises issues of concern, and provides guidance on what actions they should take. In some cases, these committees are also empowered to hear complaints from individuals who allege that their rights have been violated. For example, the Human Rights Committee can hear complaints about alleged violations of the ICCPR, while the Committee on the Rights of the Child accepts complaints from children about breaches of the CRC. The ability of the human rights committee to hear a complaint will depend on the respondent state having agreed to be subject to the committee’s jurisdiction, and the applicant is usually required to have exhausted all options for a resolution within the domestic legal system.Footnote 11

Human rights treaties are also in place in several regional areas, such as the European Convention for the Protection of Human Rights and Fundamental Freedoms (ECHR), the American Convention on Human Rights, and the African Charter on Human and Peoples’ Rights.Footnote 12 The regional human rights systems usually have a court or commission (sometimes both) that has jurisdiction to hear complaints against states; for example, the European Court of Human Rights and the Inter-American Court of Human Rights.Footnote 13

7.2.2 Rights Most Relevant to One Health

One Health has been defined by the One Health High-Level Expert Panel (OHHLEP) as ‘an integrated, unifying approach that aims to sustainably balance and optimize the health of people, animals, and ecosystems. It recognizes the health of humans, domestic and wild animals, plants, and the wider environment (including ecosystems) are closely linked and inter-dependent.’Footnote 14

When discussing the relations between human rights and One Health, several specific human rights are immediately obvious as being relevant. These include the right to health, the right to an adequate standard of living, and the right to life. However, the list of rights that could be useful for achieving a One Health approach is broader than it might first appear.

The natural starting point for this discussion is the right to health. This is protected in international human rights law in Article 12 of the ICESCR. This is not a right to be healthy, but rather a right to the ‘highest attainable standard of health’.Footnote 15 The Committee on Economic, Social and Cultural Rights (CESCR) has explained that this is a relative standard, judged with regard to a person’s own circumstances and the available resources of the state.Footnote 16 It includes both freedoms – for example, to make choices about one’s own sexual and reproductive health – and entitlements, including access to quality health services, treatments, and medicines.Footnote 17 It also encompasses the full range of factors that contribute to a person’s standard of health, such as food, water, housing, sanitation, education, and safe working conditions.Footnote 18

The Committee has also acknowledged that enjoyment of the right to health depends on a healthy environment, recognising that environmental conditions like clean air, water, and soil are essential to a wide range of health outcomes, while a poor or polluted environment can have significant health ramifications.Footnote 19 For children, the right to health guaranteed in Article 24 of the CRC explicitly mentions the need to address environmental contamination.Footnote 20 The African Charter recognises the right of all people to environmental conditions that are favourable to their environment,Footnote 21 alongside the right to the best attainable state of physical and mental health.Footnote 22 The latter has been applied in cases of environmental pollution.Footnote 23 However, while the right to health has been interpreted by courts and committees to include the environmental determinants of health, in most international and regional treaties there is no explicit mention of the environment.

An important feature of human rights law is the understanding that all rights are interdependent. The CESCR has explained this in relation to the right to health:

The right to health is closely related to and dependent upon the realization of other human rights … including the rights to food, housing, work, education, human dignity, life, non-discrimination, equality, the prohibition against torture, privacy, access to information, and the freedoms of association, assembly and movement.Footnote 24

The right to an adequate standard of living is protected under Article 11 of the ICESCR. This provision guarantees ‘adequate food, clothing and housing, and the continuous improvement of living standards’.Footnote 25 The CESCR has expanded on the content of this right in several General Comments relating to food, water, and housing.Footnote 26 In this work, it has explained the importance of governments adopting appropriate environmental policies to ensure the availability of safe and adequate food, housing, and water.Footnote 27 It has also stressed the need to ensure that natural water resources are protected from contamination and managed in a way that addresses their potential as a habitat for disease vectors, noting the links between the right to water specifically and the right to health.Footnote 28

The right to water is included in other human rights treaties, including the CRC, which guarantees to all children the right to safe drinking water as a component of the right to health in Article 24. The Convention on the Elimination of All Forms of Discrimination Against Women (CEDAW) refers to water in relation to the provision of adequate living standards for all women.Footnote 29 Wherever environmental degradation affects the availability of clean and secure water, the right to an adequate standard of living will be impacted, with potential also to impinge upon the right to health and, where serious enough, even the right to life.

The right to life is protected in the ICCPR, along with all regional human rights instruments.Footnote 30 It includes both positive and negative components. In a negative sense, it operates as a prohibition against killing (at least arbitrarily; in some states, capital punishment is still permitted provided adequate legal processes are followed). In a positive sense, states are obliged to protect people against threats to life and provide the essential conditions for life.Footnote 31 The UN Human Rights Committee, which adjudicates on alleged breaches of the ICCPR, has recognised that environmental conditions can constitute a breach of the right to life where they are serious enough.Footnote 32

There are other rights that are also connected to human well-being, and these too have a role to play in relation to One Health. They include the right to social security, protected under the ICESCR, which provides an essential economic safety net that can help to avoid negative impacts on health.Footnote 33 Freedom from cruel, inhuman or degrading treatment or punishment is also an important right for promoting human health, as it prohibits any treatment of a person that could harm either their physical or mental well-being.Footnote 34 The rights to equality before the law and to be free from discrimination are found in various forms across international human rights law.Footnote 35 In the context of health, these are important rights for ensuring that all people can access health services and the necessary conditions for a healthy life regardless of race, religion, gender, sex, or any other factor.

When it comes to designing and implementing One Health policies, several other specific human rights may also be relevant. For example, under Article 13 of the ICESCR, states are required to realise the right to education, which ‘shall be directed to the full development of the human personality and the sense of its dignity, and shall strengthen the respect for human rights and fundamental freedoms’.Footnote 36 Education plays a critical role in developing One Health thinking. As Villanueva-Cabezas et al. have argued, achieving the sort of transdisciplinary, planetary-level understanding necessary to advance One Health requires early and holistic education.Footnote 37 While their work focused on undergraduate-level university training, there is arguably a role for secondary and even primary education to help embed long-lasting knowledges and practices in support of One Health.

Another relevant right is freedom of information, guaranteed under the ICCPR.Footnote 38 This protects the right of all people to access information in different forms and is an important component of ensuring transparency and accountability in the implementation of laws and policy. Its relevance to One Health-based policies can be seen in the fact that accurate, timely, and accessible information about health problems is necessary for public education and understanding. Not only does this enhance the effectiveness of response strategies but it also helps ensure that policy responses are viewed as legitimate by those who are affected by them.

The right to freedom of movement might also be relevant to One Health-based policies, especially those that are intended to respond to pandemics or other major health issues.Footnote 39 Freedom of opinion, expression and protest will also have a role to play in balancing state responses to public criticism of such policies.Footnote 40 These freedoms can be limited under human rights law, but only where these are necessary and proportionate to protecting other human rights or to addressing issues of public health and safety.Footnote 41

The relevance of these civil and political rights to One Health can be seen in some of the legal disputes that arose during the COVID-19 pandemic. Human rights law was used as the basis to challenge lock-downs,Footnote 42 travel restrictions,Footnote 43 border closures,Footnote 44 vaccine mandates,Footnote 45 access to vaccines,Footnote 46 and regulation of misinformation.Footnote 47 In many cases the need to safeguard public health and safety was viewed as a legitimate justification for the limitation of human rights, but courts have been clear that even then restrictions must be enacted via law, must remain reasonable, and should be the least restrictive means of protecting public health and safety.Footnote 48

Taken together, these various human rights help to advance the objectives and practice of One Health, while also providing important standards and safeguards for the implementation of One Health policies.

7.2.3 The ‘Greening’ of Human Rights

As identified above, some of the rights within international human rights law are defined to include an environmental dimension, for instance children’s right to health. Others have been interpreted by courts and committees to include environmental preconditions. Over the past couple of decades, the role of the environment in supporting the enjoyment of human rights generally has been increasingly recognised. This process has been referred to as the ‘greening’ of human rights.Footnote 49

In its early days, this approach framed environmental conditions as being instrumental to the enjoyment of human rights. For example, in several cases, courts and committees have found that air, water, or soil pollution constituted an unlawful interference with the enjoyment of human rights.Footnote 50 Other cases held that logging, mining or other environmental destruction could represent a breach of rights to property, subsistence, health and even the right to life, especially for Indigenous peoples.Footnote 51 More recently, human rights bodies have begun recognising climate change as a potential violation of human rights.Footnote 52

While these cases recognised the environmental preconditions for the enjoyment of human rights, courts were clear that there was no human right to a good environment per se. For environmental harm to constitute a breach of human rights it needed to result in an actual or imminent interference with human rights.Footnote 53 In other words, it was people who were protected through human rights law, not the environment. What is more, human rights complaints cannot usually be based on a general concern for the environment. Instead, specific people need to be identified as the ‘victims’ of environmental harm.Footnote 54 And because victimhood is based on experiencing actual or imminent harm, human rights law is ill-equipped to deal with long-term environmental risks.Footnote 55

The ‘greening’ of human rights has therefore been monodirectional and instrumental, built on an understanding that the environment is necessary for human well-being but is otherwise not the concern of human rights law. Some domestic jurisdictions have recognised a legal right to a healthy environment but as will be discussed below, in most cases this is still understood in rather anthropocentric terms.

As a result of this process of greening human rights, we now have a field of human rights known as ‘environmental rights’.Footnote 56 The evolution of environmental rights shows the extent to which human rights can advance environmental health and, by extension, helps us to understand the ways human rights can support One Health. The potential for a mutually beneficial relationship between human rights and One Health will be explored in more detail in the next section.

7.3 Synergy between Human Rights and One Health

This section outlines the extent to which One Health and human rights are mutually supportive. As will be explained, this is mostly limited to the ‘human health’ pillar of One Health, as this has a significant substantive overlap with several human rights.

7.3.1 One Health Supports Human Rights

Because One Health aims to advance human health as one of its objectives, it naturally has benefits for fulfilling health-related human rights. Pursuing a One Health approach to health policy and regulation will help to ensure respect for and protection of human rights, particularly the rights to health, life, and an adequate standard of living (discussed above). For example, addressing the causes and spread of zoonotic diseases through environmental and animal health policies minimises public health risks that might undermine the right to the highest attainable standard of health.

One Health’s contribution to environmental health and animal health is also positive for human rights because environmental conditions are critical to the enjoyment of many human rights. A good example of this can be seen in the connection between the environment and wildlife and the rights of many Indigenous peoples. Human rights case law has shown that where the environment is damaged, for example through the impacts of climate change, the rights of Indigenous people to practice and pass on their culture can be breached, along with their right to property over their traditional lands.Footnote 57 One Health-based policies that protect the environment and the species that live within it can help to protect these rights.

7.3.2 Human Rights Support One Health

Because of the thematic alignment of human rights with (at least) the human health pillar of One Health, the advancement of human rights will also likely help to support and promote the objectives of One Health. For example, many activities designed to address poverty and provide clean water, nutritious food, adequate housing, and essential healthcare will naturally promote the human health pillar of One Health. Beyond this alignment of purposes, human rights also support One Health through the framework of laws and principles on which modern human rights are built. This can provide valuable legal scaffolding to One Health policies. A key feature of this legal framework is the tripartite set of obligations that states take on; namely, the duties to respect, protect, and fulfil human rights. What is required by each level of duty will vary according to the specific right in question and, in some circumstances, the capacity of the state to perform its obligations.

The first level of obligation is the duty to respect human rights. This is a negative duty that requires states to refrain from actions that would interfere with human rights.Footnote 58 It is particularly relevant for civil and political rights like the right to freedom from torture or cruel and inhuman treatment or punishment, and states are expected to take immediate measures to ensure these things do not occur.Footnote 59 The next level up is the duty to protect human rights. This requires that states enact laws and adopt measures that will protect people from rights violations caused by private actors, such as corporations.Footnote 60 The third and most demanding level of obligation is the duty to fulfil human rights. This requires that states take positive steps to ensure all people can enjoy their human rights.Footnote 61 The duty to fulfil is typically more onerous for economic, social, and cultural rights, as these can require greater investment of resources to be fully realised.

Human rights law also provides a progressive scaffolding that could be used to achieve One Health goals. For many human rights, the standard of obligation on states is one of progressive realisation, having regard to their capabilities and resources. This is the approach taken to most economic, social, and cultural rights, like the right to health and the right to an adequate standard of living.Footnote 62 Significantly for the operationalisation of One Health, these rights are intended to be achieved through international cooperation and assistance. This expectation is potentially useful for implementing One Health policies on a global scale and aligns with our understanding of the interconnectedness of natural systems. Together, these standards of obligation potentially promote state investment in One Health both domestically and internationally, as well as an approach which is geared towards ambitious targets achieved progressively over time.

The interdependence of human rights noted above also aligns with the integrated approach envisaged by One Health and promotes a way of thinking about diverse objectives that recognises their close connections. Human rights law also provides principles for balancing objectives when they compete with one another. There are some human rights that are viewed as being ‘non-derogable’, meaning that no violation of them could ever be permitted. They include, for example, freedom from torture and slavery. Other rights can be validly restricted where doing so is necessary to achieve some legitimate aim, including the protection of other rights. The limitation must be proportionate, however, and should represent the least restrictive option available. These requirements of necessity and proportionality could help inform a One Health response in circumstances where the objectives of animal, human, and environmental health conflict, or where One Health conflicts with other social or economic objectives.

Human rights also provide important standards and safeguards that could apply to the design and implementation of One Health-based policies. These include rights relating to freedom of information, expression, and movement; Indigenous rights to self-determination, land, and culture; and rights to a fair trial and equality before the law. These rights can help to ensure that policies which, for example, prohibit certain uses of land in the name of One Health do not have disproportionately harmful collateral effects on human rights.

One area that has been identified as requiring more work in the One Health space is gender.Footnote 63 A commitment to human rights, particularly women’s rights, equality, and non-discrimination, could help to fill this gap. For example, this could occur by helping to focus attention on the different ways that women and girls are at risk of and experience infectious diseases and the factors that contribute to their vulnerability. For instance, a human rights-based approach helps to identify inequalities in distribution of work and economic power within communities that often leave women exposed to environmental health risks.Footnote 64

A human rights-based approach can better ensure that adequate work is done to address health issues that specifically affect women, girls, and non-binary people. It can also promote an intersectional approach to health that acknowledges the connected factors across gender, race, religion, socio-economic status, and other dimensions that impact on health. Further, attention to human rights can help improve representation of women throughout law and policy-making areas, including at the highest levels of government and institutions.

The extent to which these gains can be realised is limited by the tension that exists between the multidimensional focus of One Health and the fundamental anthropocentrism of human rights. This will be examined in the following section.

7.4 Tensions between Human Rights and One Health

As discussed above, there are clear overlaps between the content and objectives of human rights and One Health, which mean that they can be mutually supportive in their implementation. Further, the legal framework of human rights could provide important reinforcement for One Health strategies, while also ensuring that those policies adhere to minimum standards of human rights protections. However, these mutual benefits are most obvious in relation to the human health pillar of One Health and are less assured in relation to environmental and animal health. Perhaps more significantly, the inherent anthropocentrism in human rights may not sit comfortably with the more balanced approach of One Health, in which human well-being is intended to be integrated with environmental and animal health in a more equal partnership. At its worst, there is potential for human rights to frustrate One Health efforts by prioritising human concerns over those of nature and other species.

7.4.1 Anthropocentrism

Human rights are, by definition, anthropocentric. The theoretical foundations of human rights are heterogeneous, with modern human rights law being traceable back to various philosophical traditions. But while there are variations, these theories are rooted in inherent human value, dignity, interests, or some combination of these. Human rights are generally considered to be things that are necessary for humans to live a life of dignity or to fulfil their interests.

For example, modern human rights law draws heavily on natural rights theory.Footnote 65 This theory is based on the work of Western philosophers like Thomas Hobbes and John Locke, and posits that human rights are the entitlements that each human can claim based on their inherent human dignity. An alternative explanation is found in interest theories of rights, which view human rights as those things that are fundamentally in the human interest and weighty enough to impose an obligation on others.Footnote 66 Interest theory has been used by scholars like Feinberg to argue for recognition of the rights of animals as well, though these would not presently be considered to fall within the scope of ‘human’ rights.Footnote 67 Animal rights theorists like Saskia Stucki have argued for recognition of animals as rights-holders, based on their sentience or ‘self-hood’ and their inherent value. In this way, animal rights are framed in similar language to human rights: animals have rights by virtue of their being animals.Footnote 68 However, this is a novel approach and is not yet commonplace among human rights thinking, and especially not within human rights law.

Whichever philosophical version of human rights we adopt, it is hard to escape the centrality of the ‘human’, either as the locus of inherent dignity giving rise to rights or the subject whose interests we seek to protect. As a result, attempts to include the environment within the scope of human rights have traditionally framed the environment as being instrumental to human well-being, as is evident in the ‘greening’ of human rights, described above. In terms of achieving One Health’s environmental and animal health objectives, while this approach acknowledges some interconnectedness between humans and the natural world, it positions human health as the end, and animal/environmental health as merely means. Human health therefore takes priority, and animal and environmental issues are only relevant to human rights to the extent that they advance or impact on human well-being.

The issue of pandemic prevention provides some illustrations of how a human rights approach might complicate One Health efforts. Zoonotic spillover is a key risk factor for pandemics, which can occur where human activity moves into new areas of the environment, exposing people to zoonoses. For example, encroachment into and logging of forests for timber or to clear land for agriculture increases the risk of zoonosis, but also promises important economic benefits to communities.Footnote 69 Hunting of animals for food or commerce is another area of risk for zoonotic spillover, but again may be seen as an important activity for subsistence.Footnote 70 To the extent that these activities support livelihoods or provide a means of subsistence, they could be seen as important for the fulfilment of human rights. Policies that seek to regulate or prohibit them could consequently face allegations that they breach human rights. Once a pandemic begins, human rights to freedom of movement and opinion might be viewed as constraining potential response efforts. Alternatively, a government seeking to avoid international pandemic prevention expectations might use the language of human rights to justify its position.

While there is clearly potential for human rights to frustrate One Health efforts by prioritising human interests over those of other animals or the environment, the significance of this shouldn’t be overstated. Human rights law has tools for dealing with competing interests and will permit the limitation of some rights where doing so is necessary and proportionate to achieving another legitimate aim. It is not the case that human rights will always be trumps. Furthermore, when it comes to activities that are environmentally harmful or hazardous, supporting the full enjoyment of human rights like the right to an adequate standard of living can reduce the need for people to rely on those practices for their livelihoods. Nonetheless, there has always been an inevitable anthropocentrism in human rights and a sense that the environment is valuable because of its usefulness for humans, rather than valuable in its own right. This understanding is fundamentally different from the more evenly weighted approach of One Health.

7.4.2 The Right to a Healthy Environment

More recently, there has been a shift towards greater recognition of the right to a healthy environment, which could potentially open the way for a more ecocentric approach that is more closely aligned with the tripartite framing of One Health.Footnote 71

In 2022, the United Nations General Assembly adopted a resolution recognising that ‘all people have the right to a clean, healthy and sustainable environment’.Footnote 72 The resolution was widely supported, with over 160 states voting in favour.Footnote 73 It followed the adoption of a similarly worded resolution by the Human Rights Council the previous year.Footnote 74 The resolutions call on states to ‘scale up efforts’ to guarantee the right to a healthy environment (as it is commonly abbreviated), though this request is not legally binding. Indeed, the non-legally binding status of the resolutions may partly explain the strong positive reception from UN member states, who might have been more circumspect had there been legal duties involved.

The resolutions were adopted against the backdrop of considerable recognition of similar rights within domestic jurisdictions and regional human rights systems. A recent study found that over 130 countries recognise some form of enforceable environmental right.Footnote 75 Of these, eighty-four national constitutions included an explicit right to a healthy environment.Footnote 76 Some have argued that this provides evidence that the right exists as part of customary international law, though this is by no means settled.Footnote 77

Across these domestic jurisdictions, there is still considerable diversity in terms of how environmental rights are defined and, consequently, how well they might align with the three dimensions of One Health. Some rights have a more ecocentric approach, protecting the rights of animals, natural features like rivers or forests, or even the whole of nature.Footnote 78 Some constitutions protect people’s right to an ecologically balanced or sustainable environment.Footnote 79 Many constitutions guarantee a clean, safe, or unpolluted environment,Footnote 80 suggesting a more anthropocentric, instrumental understanding of the relationship between nature and humans. This diversity and ambiguity make it hard to pin down the content of environmental rights and their corresponding duties. Even the term ‘healthy environment’ is open to various meanings and could refer to an environment that is healthy in its own right or merely healthy for humans.

The recent UN resolutions indicate that the international human rights community is starting to recognise the more subtle interconnections between the environment and humans, and the fact that environmental degradation could be a violation of human rights, even where no direct impact on human lives is evident. However, this approach is still one of recognising the human right to a healthy environment. Equivalent discussions on animal or environmental rights are underdeveloped or lacking at the international level.Footnote 81 As a result, despite all these advances, the right to a healthy environment is unlikely ever to truly overcome the anthropocentrism inherent in human rights.

7.5 Conclusion and Possible Ways Forward

Looking at the current state of play within human rights, particularly environmental human rights, a few things seem clear about the relationship between human rights and One Health. Firstly, human rights are clearly relevant to the human health dimension of One Health. The substantive overlap between One Health and the right to health in particular, but also rights to adequate food, shelter, water, employment, and education, suggests that efforts to promote human well-being through a One Health approach will inevitably help to achieve some human rights objectives as well. Similarly, a human rights-based approach to health-related issues will likely be well-suited to achieving the human dimension of One Health. The legal framework of human rights law also provides some potentially useful standards and processes to help provide structure and authority to One Health activities in the human health domain.

The environmental and animal health dimensions of One Health are more difficult to reconcile with human rights, however. While there has been considerable progress on the recognition of environmental rights, and particularly the right to a healthy environment, these remain framed as human rights to an environment of a particular quality. Even where the right is defined in terms of ecological balance or sustainability, this almost always is justified because of its importance to humans. This goes some way to acknowledging the interdependence of humans, animals, and nature, but without affording rights to the non-human parties in the relationship, the prioritisation of the human remains inescapable.

The anthropocentrism of human rights will likely remain at odds with One Health’s tripartite approach, which aims for a much greater equilibrium between human, animal, and environmental health. At its worst, this may even hamper efforts to implement a One Health approach, as detrimental human rights impacts may be given more weight than beneficial environmental or animal outcomes where these are in conflict. However, a commitment to the fulfilment of human rights can lessen this by reducing the need for people to rely on environmentally harmful activities to provide for their livelihoods.

Bringing these points together, there are some lessons we can learn and steps we could take to enhance the mutually supportive relationship between One Health and human rights while mitigating the tensions. To begin with, One Health policies should be informed by human rights, particularly best practices for the right to health. This will help minimise any incompatibility.

Work on the right to a healthy environment should continue to find ways to promote a more integrated, ecocentric approach. In doing this, One Health can help to grow the understanding of the many and varied ways in which humans, animals, and the environment are interdependent. Ultimately this could lead to legal recognition that environmental degradation breaches human rights, even without a direct impact on human lives.

One Health policies can benefit from the standards and safeguards provided by human rights law, as well as from the widespread recognition and adoption of human rights around the world. However, we need to recognise that human rights alone will not achieve One Health. It would be counterproductive and inappropriate to reduce One Health to a human rights project or to put too great an emphasis on human rights. Instead, the synergies between the two frameworks should be understood so that they can be capitalised upon, while at the same time allowing them to diverge where it is necessary to do so.

8 Animal Rights and One Health Locating Animal Intrinsic Worth in the One Health Paradigm

8.1 Introduction

Our contemporary time period is now often referred to as the Anthropocene, a term which denotes that human activity has become the central influence on the planetary environment.Footnote 1 Human influence in this respect is a pressing issue because much of human activity is detrimental to Earth’s climate and environment. Human activities including animal agriculture, deforestation, and burning of fossil fuels contribute to global environmental challenges including climate change, biodiversity loss, and ocean acidification.Footnote 2 If these activities continue at their current pace, the Earth will quickly become uninhabitable for humans and many other animals.

Various legal and policy changes have and continue to be explored as potential solutions to the critical situation of life on Earth. Animal rights discourse, while predating much of this environmental concern, has been proposed as a means by which detrimental human impact on the environment can be mitigated.Footnote 3 While various proposals for legal animal rights exist, they commonly focus on the inherent worth of individual animals and the consequent need to recognise animals as legal rights holders.Footnote 4 Although figures vary, livestock produces approximately 15 per cent of total global greenhouse gas emissions and contributes significantly to deforestation, biodiversity loss, and environmental pollution.Footnote 5 Recognition of animals as legal rights holders would, by most accounts, require the cessation of intensive animal agriculture.Footnote 6 It would also improve legal protections for other animals with beneficial consequences for habitat protection and biodiversity.Footnote 7

One Health, which refers to a ‘collaborative, multisectoral and transdisciplinary approach’,Footnote 8 with the aim of optimising the health of people, animals, and the environment,Footnote 9 has also been promoted as a policy solution to issues of the Anthropocene. While at its inception One Health was largely focused on public health, contemporary literature has advocated for a broadening of One Health, to extend moral consideration to non-human animals,Footnote 10 and concern beyond health to encompass welfare and rights.Footnote 11 One Health recognises the interconnectedness of human, animal, and environmental health,Footnote 12 thus an approach underpinned by One Health principles should be more likely to limit human activities that are detrimental to the environment.

Animal rights and One Health discourses hold significant promise as potential legal and policy means to combat human activity that is destructive to the environment. While they may appear complementary, however, closer analysis reveals some fundamental tensions between their foundational commitments. Animal rights are premised on the inherent worth of individual animals, which accordingly should not be used – in Kantian terms – as a means to others’ ends.Footnote 13 One Health, in contrast, appears to be focused on the overall health of groups of people, animals, or ecosystems (in other words, on global health or planetary health), at least in practice.Footnote 14 Where individual interests of humans or animals conflict with group interests, One Health will prioritise the group. In essence, animal rights are underpinned by deontological philosophy, while One Health is utilitarian in nature.

To reconcile these promising theories, this chapter seeks to locate a recognition of animal intrinsic worth within the One Health paradigm. In pursuing this objective, it seeks to conceive of animal rights as compatible with and as part of a broader One Health paradigm. In this respect, it draws on literature from compassionate conservation, multispecies justice, and rights of nature that have grappled with similar issues. To ensure the viability and utility of such a conception for legal and policy practice, the chapter explores the theoretical implications of such an approach for contemporary societies and their common uses of animals.

The second part of this chapter commences with an exploration of the ethical foundations of One Health and animal rights to highlight and describe the apparent philosophical tensions between them. In the third part of this chapter, we put forward a way of conceiving of animal rights and One Health as complementary, by developing a three-layered value framework.Footnote 15 We explore the interpretive implications of this value framework for law and governance in the final part of the chapter.

8.2 One Health and Animal Rights: Conflicting Principles?
8.2.1 Ethical Foundations of One Health

The ethical foundations of One Health are highly contested. A key problem is that the framework has multiple definitions/interpretations that are polysemic and can have different ethical and normative consequences. Notwithstanding, some argue that One Health does not have its own ethical framework and does not need one as it relies on existing ethics and principles.Footnote 16 Others argue that One Health can benefit from its own ethical framework,Footnote 17 or that it is a requirement for sound implementation.Footnote 18

While there are some near-universal agreed ethical principles within the framework (collaboration, interdisciplinarity, justice, and/or equity)Footnote 19 a key ongoing debate centres on whether the framework is intended to be anthropocentric, ecocentric, or something else.Footnote 20 While the foundational premise is that public health, environmental health, and animal health are inherently interconnected and should be governed as such, the question remains as to whether environmental and animal health are managed for the benefit of public health, or because of their intrinsic value.

The recent definition of One Health, published by the One Health High-Level Expert Panel (OHHLEP), encourages equal consideration of animal, environmental, and human health, at least at face value: ‘One Health is an integrated, unifying approach that aims to sustainably balance and optimize the health of people, animals, and ecosystems. It recognizes the health of humans, domestic and wild animals, plants, and the wider environment (including ecosystems) are closely linked and interdependent.’Footnote 21 Similarly, the Berlin Principles adapted in 2019, authored by another group of world-leading One Health experts, and updating the 2004 Manhattan Principles, include increased reliance on biodiversity conservation as a means of adhering to a One Health framework.Footnote 22 They also include other principles of equity and justice inherent in the One Health approach.

What we see in the practice of One Health, however, is a very different ethical framework than that which is called for in the literature. At the ground level, One Health remains a public health framework, and so the ideology of the framework remains stuck within that paradigm. This dichotomy between the operationalisation and theory of One Health has also been noted by ethicists. Sironi calls the two approaches the ‘prudent’ and the ‘radical’ approach, with the former representing a forward step for human health and the latter a true epistemological and ethical change, including proper integration of animal value into human societal systems.Footnote 23 Beever and Morar distinguish between the ‘moderate’ and ‘strong’ approaches, with the former prioritising multidisciplinary collaboration and interconnectivity, and the latter focusing on interdisciplinarity and interdependence.Footnote 24 The term ‘interdependence’ implies symbiosis, where each sphere of health takes care of the other. Each of these distinctions bears weight, but not necessarily across each and every iteration of One Health.

This primary debate has very practical implications for how One Health is operationalised. By way of example, managing animals with disease depends very much on the value we place on individual animals, conservation, and public health. Ultimately though, it is generally agreed that the ethics of One Health both in theory and practice remain anthropocentric, despite its promising foundations. Diller and Williamson argue this is because it is premised on the individually focused bioethics,Footnote 25 and Coghlan argues that One Health has yet to expand its circle of moral concern.Footnote 26 Yet even the anthropocentric theory of One Health is not without critique. Lysaght argues that there is an absence of justice, although Johnson and Degeling argue that justice is a developing principle of the framework. Ramakrishnan, and Laine and Morand, argue that the historical coloniality of public health systems has embedded neocoloniality into the framework, and its operationalisation by international organisations.Footnote 27 Indeed, Ramakrishnan goes further to say that the One Health framework is ‘nothing but a vehicle enabling the incorporation of bio-surveillance obligations’.Footnote 28 This is certainly also arguable given the current OHHLEP Theory of Change, where One Health still appears to be primarily focused on animal disease surveillance.Footnote 29

This approach has very real implications for animal rights and welfare. If we view One Health as a way to conduct bio-surveillance, we are only focusing on the detection of the disease and not on the factors that cause the disease or its spread to people. For example, we would focus only on the detection of Hendra in flying foxes, and not protect the natural habitats in forests that feed them and prevent them feeding in human residential areas.Footnote 30 The implications for flying foxes can be dire, as feeding in human areas can lead to net entanglement and lethal management where they can be viewed as ‘pests’.Footnote 31

What we can see is that the ethical foundations of One Health are important in determining the scope of One Health, whether that be One Health as bio-surveillance, a public health framework, or something beyond that considers animals rights and/or welfare, as well as the rights and welfare of nature more generally. The ethical foundations are also vital for providing guidance on resolving the conflicts that are inevitable between the three areas of the framework that we outline below.

Over the remainder of this chapter, we consider One Health frameworks as if they were an embodiment of an expanded ideology advocated for in much of the ethical literature. We ask: if One Health was a true representation of the interdependence of animal, environmental, and human health, how do animal rights fit in? This itself is an interesting question that does not fit the standard debate about the ethical foundations of One Health, because the main competing paradigms are anthropocentrism and ecocentrism, neither of which prioritises animals outside their value as a species. Instead, ecocentrism is based on the ethical framework of ecological holism, espoused by Aldo Leopold and his utilitarian concept of conservation: that what is good for the ecosystem is good for the whole.Footnote 32 This form of ecocentrism allows the dismissal of individual interests if they are detrimental to a hubristic form of ‘the whole’.Footnote 33

Animal interests seem even further removed from a One Health ethical framework, except to the extent that animal disease can cause human health impacts. In practice, animal welfare is considered relevant in managing disease through, for example, the administration of antibiotics and other preventative medicine in agricultural animals. The question of whether intensive and industrial animal agriculture is problematic from the perspective of the animal is not seen as relevant. Coghlan and others argue that One Health operations work within the parameters set by industrial agriculture, through biosecurity laws and policies, and monitoring pathogens. They state that a bolder One Health ethic would recognise that the benefits of industrial agriculture do not outweigh the harm done to the billions of individual animals subject to its operations, in addition to the environmental damage caused as a result of the industry.Footnote 34 Even further removed from the ethical debate are wild animals, although there has recently been some interest in the welfare of wild animals sold in live animal markets.Footnote 35

So, One Health ethics have the potential to promote ecocentricity, but what can we learn regarding the inclusion of animal rights? And how do we fit all three paradigms into One Health law and governance? Philosophy and ethics already have much to offer on how to expand our circle of moral concern to animals, and this is the topic of the following section.

8.2.2 Ethical Foundations of Animal Rights

Traditional ideas about morality focused on the way humans treat other humans. As Deborah Cao, Katrina Sharman, and Steven White identify, this conception of morality was ‘human-centred and human-exclusive’.Footnote 36 According to Cartesian philosophy, for example, other animals are unfeeling automata that ‘eat without pleasure, cry without pain, grow without knowing it; they desire nothing, fear nothing, know nothing’.Footnote 37 As a result, even vivisection could be considered morally justifiable.Footnote 38 Similarly, while Immanuel Kant expressly rejected the Cartesian view of animals as automata,Footnote 39 he claimed that humans only have indirect duties in relation to animals, on the basis that mistreating animals would harm human moral character.Footnote 40

In contrast, contemporary animal rights discourse ascribes moral status to other animals.Footnote 41 Prominent scholars that argue for animal moral rights,Footnote 42 including Tom Regan and Christine Korsgaard, base their arguments on a conception of other animals as living beings, many of whom have capacities for positive and negative feelings, who have inherent value. According to American philosopher Tom Regan, animals’ inherent worth stems from their individual subjective experience of life. He states, ‘the basic similarity is simply this: we are each of us [human and animal] the experiencing subject of a life, a conscious creature having an individual welfare that has importance to us whatever our usefulness to others’.Footnote 43 Importantly, this value is not dependent on how useful animals are to others; they are not merely a means to human ends, but must – as Korsgaard argues – be treated as ‘ends in themselves’.Footnote 44 From a moral standpoint, this places limits on how human should treat animals, because to treat animals in a way that fails to respect their inherent value is immoral and infringes their individual moral rights.Footnote 45 From an animal rights perspective then, animals possess equal inherent value to humans, and are part of our moral community whose interests require human consideration.

While many animal rights scholars employ deontological theory in their arguments, they reject Kant’s emphasis on rationality and autonomy as the foundation for individual rights and his conclusion that humans only owe indirect duties to animals. In this respect, Regan points out that many animals, such as non-human primates, share the cognitive characteristics that are claimed to give rise to human moral rights and should therefore share those rights.Footnote 46 On the other hand, many humans, including infants and persons experiencing severe mental disability, do not have these mental capacities and yet are recognised moral rights holders.Footnote 47 If rationality and autonomy are the foundations for moral rights, these positions are untenable.

Animal rights scholars suggest alternatives to rationality and autonomy as the foundation for individual moral rights. For Regan, the defining characteristic that gives rise to moral rights is being a ‘subject of a life’.Footnote 48 Similarly, Korsgaard argues that ‘all creatures who are capable of feeling pleasure and pain’ have moral standing.Footnote 49 For some scholars, their theories in this respect serve to provide the foundation for both human and animal moral rights.Footnote 50

The practical consequence of animal moral rights theories for One Health is that animal moral rights cannot be overridden solely on the basis that there might be an overall benefit to people and/or animals.Footnote 51 In contemporary public health practice, for example, the risk of an infectious disease spreading from animals to humans is often used to justify culling the diseased animals and those with whom they have been in contact.Footnote 52 This approach would be unacceptable if proposed in relation to humans, because humans are considered to have inherent value and moral rights. Similarly, if animals are considered to have inherent value and moral rights, their interests would need to be fully considered before deciding how best to respond to the disease threat.

8.2.3 Apparent Philosophical Conflict between One Health and Animal Rights

The philosophical conflict arising within the One Health framework is clear from competing ‘limbs’ of the framework itself; those being environmental, animal, and human health. The philosophical tension here arises from the focus on the macro (conceived holistically as nature as a whole, or the Earth, or conceived systemically as groups of people, other species or ecosystems),Footnote 53 versus a focus on the micro (individuals of all species). Although interdependence is a core principle of One Health, there are, and always will be, circumstances where two or more of these limbs conflict. For example, conservation can impact on human wellbeing when communities are forced to relocate from their traditional lands (known as ‘conservation displacement’).Footnote 54 Individual animals can be killed or relocated if they are viewed as not belonging to a particular ecosystem. Animals can also be killed and mistreated to provide sustenance for human health.Footnote 55

This tension between working towards the optimisation of the wellbeing of a collective versus seeking to protect the individual from pain and suffering can also be seen in the two most prominent approaches to animal advocacy; welfarist and rights approaches. Early supporters of animals, for example, included English philosopher Jeremy Bentham, who based his regard for other animals on their ability to feel.Footnote 56 Bentham’s concern with minimising pain and suffering underpinned his utilitarian ethic, reflecting a theory of morality that seeks to maximise happiness and minimise suffering for the greatest possible number of individuals.Footnote 57 Determining the morality of conduct under this approach involves a calculation of all the pleasure and pain that will result from the conduct. This focus on aggregate pleasure, however, can be used to justify practices like experimenting on animals that will cause immense individual suffering. In contrast, animal rights advocates like Regan focus on the inherent worth of the individual and argue for individual rights that cannot be outweighed by aggregate consequences.Footnote 58

Thus, the apparent conflict between animal rights and One Health has echoes both in similar debates of the past and in contemporary conceptualisations of One Health itself. While this makes resolving the apparent conflict challenging, it also means that developing an approach that reconciles the conflict need not require ‘reinventing the wheel’. In the next Part, we look at how similar conflicts have been addressed in compassionate conservation, multi-species justice, and rights of nature literature to develop a conception of animal rights as compatible with and as part of a broader One Health paradigm.

8.3 The Individual in One Health

One Health is, appropriately, the internationally adopted approach to managing public health.Footnote 59 As Degeling et al. identify in the context of responses to emerging infectious diseases, implementing One Health in an integrated and well-thought-out manner necessitates identifying some agreement over what constitutes the public interest and an awareness of the values that support it.Footnote 60 Here, we contend that animal wellbeing is one of these values and should inform any conception of the public interest. In this respect, there is a clear public acceptance of a greater need for animal welfare, at least in modern liberal democracies. For example, a survey conducted in 2023 by BehaviourWorks Australia identified that ‘9 in 10 Australians agree that animal welfare should be protected by the government through legislation’.Footnote 61 A survey undertaken in 2018 found that the Australian public has developed a ‘fundamental … belief that animals are entitled to the protection of relevant rights and freedoms, closely aligning with activist sentiment’.Footnote 62

Ample evidence also exists at the international level for the public acceptance of a greater need for animal welfare. Legal provisions recognising animals as sentient and as having intrinsic worth have proliferated and can be located in jurisdictions as diverse as the European Union,Footnote 63 Tanzania,Footnote 64 Chile,Footnote 65 the Netherlands,Footnote 66 Lithuania,Footnote 67 and Spain.Footnote 68 More broadly, in 2022, the United Nations’ resolution on the animal welfare environment–sustainable development nexusFootnote 69 recognised the key linkages between humans, animals, and environmental wellbeing, and thus accepted that considering animal interests is critical for the realisation of many of the sustainable development goals. Accordingly, the resolution encourages states to consider these key linkages in developing public policy. This public support for increased animal welfare points to the need to conceive of One Health as an approach that encompasses animal wellbeing, which experience and scholarly literature demonstrates is most likely to be achieved through recognition of animal rights.Footnote 70

8.4 Approaches in COMPASSIONATE Conservation, Multispecies Justice, and Rights of Nature

There are several existing ethical theories that could be used to inform a conception of One Health as encompassing animal rights, thus expanding the circle of moral concern for a One Health ethical theory. In this section, we explore the way scholars in compassionate conservation, multispecies justice and rights of nature have approached this challenge.

8.4.1 Compassionate Conservation

The theory of compassionate conservation seeks to mitigate the inherent conflict between the macro ecosystem and micro individual when making conservation decisions. It is premised on the ethical position that ‘all actions taken to protect biodiversity should be guided by compassion for all sentient beings’.Footnote 71 The theory argues against an either/or approach to conservation and individual animal welfare and instead posits that there are win-win solutions where both can be prioritised.Footnote 72 It is specifically contrasted against the apparent subordination of animals in traditional wildlife conservation practices that results from humans believing they have authority over decisions concerning animals and labelling certain animals problematic, thereby ignoring their sentience.Footnote 73

Despite protestations from traditional conservationists, compassionate conservation expands the scope of concern to give conservation a more holistic perspective. It seeks to be inclusive not only of different philosophical thought, but of animals and their intrinsic worth.Footnote 74 An additional major premise of compassionate conservation is that animal agency, and the effects of that agency on ecosystems and other species, is not systematically investigated in conservation research. This idea of agency is established by animals’ intelligence, sentience, social structures, and how they influence ecosystems and human–wildlife spaces.Footnote 75 A study conducted by Wallach and others that researched Australia’s migrant vertebrate species provides insight into the value that a compassionate conservation approach can add.Footnote 76 By adopting a more inclusive approach in their research, specifically an approach that does not solely focus on nativism, they were able to find that migrant species in Australia can act as safeguards for threatened native species.Footnote 77 Even in areas where there are increasing levels of extinction, migrant species have the potential to improve local species richness.

Like compassionate conservation, One Health has been limited by anthropocentric notions of the human–animal relationship. Animal agency is not considered within the One Health research paradigm. If, however, we extended the approach taken in compassionate conservation research to the One Health space, we may be able to move past understanding wildlife and animals as ‘problematic’ in terms of pandemic potential. In this respect, there is some evidence that increased biodiversity leads to less transmission of microbes from animals to people under certain circumstances; however, this research is limited.Footnote 78 It seems the traditional method of conservation research continues to impact One Health research in more than one way.

8.4.2 Multispecies Justice

The idea that humans exist within nature and are interdependent with other living things, embedded in the concept of One Health, is also central to multispecies justice theory. This theory operates to extend environmental justice theory through the inclusion of non-human animals, species, and ecosystems.Footnote 79 This theoretical extension results in an amalgamation of environmental, ecological, and social justice that embraces non-human animals. From a multispecies justice perspective, considering different beings’ subjective experiences of life is critical to multispecies flourishing. A more comprehensive understanding of multispecies justice theory can be seen in Indigenous approaches, whereby respect for all things is required, as ‘disrespect to any part is disrespect to everything’.Footnote 80 Aboriginal and Torres Strait Islanders, for example, would ensure that waterholes were kept clear, which maintained water supply for animals and thus contributed to their survival.Footnote 81 This approach clearly aligns with the Indigenous Australians’ law requiring care for country.Footnote 82

A key issue that arises in the application of multispecies justice theory is how to address conflicts of rights and justice that are more prolific in the context of an expanded circle of moral concern.Footnote 83 Nevertheless, there is evidence that individual rights and justice concepts can coexist, at least in some situations. An argument may be made, for example, that justice for sentient animals requires humans not to eat them. However, research is clear as to the human health benefits of a vegetarian diet, thus prohibiting the consumption of animals where plant-based foods are readily available may also work in favour of human justice.Footnote 84 Moreover, such an approach would potentially benefit not only animal and human justice, but also environmental justice, as plant-based foods are more environmentally friendly than animal food products. In this respect, Poore and Nemecek’s study demonstrated that a global transition to predominantly plant-based diets would result in a reduction in deforestation of 76 per cent and a decrease of 49 per cent in greenhouse gas emissions from food production.Footnote 85

8.4.3 Rights of Nature

Rights of nature refers to the conception of nature itself as a subject of rights. The importance of this conception lies in its contrast with traditional views of nature as human property that can be exploited.Footnote 86 In broad terms, while rights of nature ‘have both multiple histories and multiple meanings’,Footnote 87 it ‘propounds the inherent value of Nature, independent of its extractive value for humans, and seeks to give Nature a voice in decision-making structures’.Footnote 88 In this respect, nature is taken to include the holistic conception of nature as a whole, and also nature as specific places (for example, the Whanganui river in New Zealand, or the Mar Menor lagoon in Spain).Footnote 89

While nature would seemingly include animals, it is unclear whether rights of nature encompass animal rights. To understand rights of nature in this way would raise a similar issue to that which arises in compassionate conservation and multispecies justice: how should conflicts between the interests of nature/ecosystems and the interests of individual animals be resolved? Nevertheless, some courts have interpreted holistic forms of rights of nature as inclusive of individual animals. For example, in 2022 the Constitutional Court of Ecuador heard a case in which the release of a woolly monkey named Estrellita from a zoo was sought.Footnote 90 Estrellita had been transferred from her home of 18 years to the zoo on the basis that keeping a wild animal is banned in Ecuador. The Court held that ‘[w]ithin the levels of ecological organization, an animal is a basic unit of ecological organization, and being an element of Nature, it is protected by the rights of Nature and enjoys an inherent individual value’,Footnote 91 thus finding that non-human animals can have legal rights.

To reconcile this apparent ‘[p]hilosophical animosity’, legal scholar Eva Bernet Kempers proposes understanding rights of nature as a ‘three-dimensional concept’.Footnote 92 In this theory, she distinguishes between the holistic, systemic, and individualistic (sentient and non-sentient) dimensions of nature. Bringing the individual and collective into the same conceptual understanding of rights can help to resolve rights conflicts. Bernet Kempers provides some examples in this respect: while animal rights may outweigh plant rights, they also need to be understood in the context of the health of species or ecosystems of which they are a part. This may mean that an endangered plant’s rights could prevail over the rights of a non-native animal whose activities present a risk to the ecosystem. Bernet Kempers notes that while this approach reconciles the apparent philosophical incongruity between individual and collective rights, it also risks ‘naturalizing’ rights, meaning it risks strengthening the natural state in which stronger beings can exploit weaker ones.

8.5 Conceiving of One Health as a Three-Dimensional Framework for Moral Concern

Traditionally, One Health has been conceived of as involving three interconnected aspects: environmental, human, and animal health.Footnote 93 As discussed above, however, this approach raises questions as to the philosophical value of each of these limbs within the One Health approach. Building on the expanded ideology described in Part 8.2 above, and Bernet Kempers’ notion of rights of nature as including animal rights,Footnote 94 we propose that our understanding of One Health be supplemented with a three-dimensional concept for moral concern that embraces individual animal rights (the ‘framework’). In this framework, while nature encompasses humans, other animals, and the environment, it can also be reconceived to better understand tensions between the interests of individuals and collectives. In this respect, the Court in the Estrellita case helpfully sets out the six levels of ecological organisation into which nature may be categorised:

  1. (1) the individual or organism;

  2. (2) populations of the same species living in a particular area;

  3. (3) communities of different species living in an ecosystem;

  4. (4) ecosystems or sets of biological communities in a particular area;

  5. (5) ‘The biome or biotic area, which constitutes all those biogeographical zones into which the biosphere is divided, which are characterized by having common climates and biotic components (animals, vegetation, etc)’; and

  6. (6) nature or the Earth.Footnote 95

For our purposes and building on Bernet Kempers’ theory, this categorisation can be consolidated into three dimensions: individuals, groups, and nature or the whole. To account for the nature of human rights and animal rights as being those rights founded on individual sentience and intrinsic value,Footnote 96 we can further categorise individuals (and to some degree the groups in which they exist) into sentient and non-sentient beings/entities. The resulting framework, adapted from Bernet Kempers’ diagram and drawing on the Constitutional Court of Ecuador’s framework for ecological organisation, is depicted in Figure 8.1.

Three-dimensional hierarchical diagram showing the One Health concept. Structured into three dimensions: Top: earth/nature (whole). Middle: populations, ecosystems, communities (groups). Bottom: humans, sentient and non-sentient animals (individual). See long description.

Figure 8.1 Proposed One Health three-dimensional framework for moral concern

Figure 8.1Long description

Diagram illustrating a proposed One Health three-dimensional framework for moral concern. The framework is structured into three dimensions: the first dimension represents the whole, specifically Earth or nature; the second dimension categorizes groups such as populations, ecosystems, communities, and biomes; the third dimension identifies individuals within these groups, including humans, other sentient animals, and non-sentient animals or entities.

In this framework, value is ascribed to the holistic dimension of the Earth, or nature; the group dimensions of populations, communities, ecosystems, and biomes; and the individual dimensions of humans, other sentient animals, and non-sentient animals or entities. As Bernet Kempers observes, ‘[t]he different dimensions are interdependent: individual entities always exist as embedded in larger networks of collectives and ecosystems, which again exist in the context of the planet (or “nature”)’.Footnote 97 This interconnectedness and interdependence resonates with key principles of One Health and emphasises the need to recognise the inherent value of all dimensions.

This framework can assist in determining how to address conflicts between the interests of humans, other animals, and the environment when taking a One Health approach. Where there is a conflict of interests, a proportional approach should be taken that balances the relevant interests. Individual sentience merits recognition of a particular kind of interest in contrast with non-sentient entities or collectives, and this should be accounted for in this proportional approach.Footnote 98 The approach should include identification of potential risks to different dimensions, consideration of the source or cause of the risk (conceived broadly), consideration of the potential impact and likelihood of occurrence of the risks, and potentialities for prevention and mitigation of risks.Footnote 99 Such an approach brings together aspects of the literature discussed above. Like Bernet Kempers’ framework for Rights of Nature, this framework brings different notions of rights together into one theory. Like compassionate conservation, resolutions within this framework will cease viewing animals as inherently problematic because all dimensions and individuals are recognised as having inherent value and conflict resolution will favour win-win solutions. Like multispecies justice, determinations regarding rights conflicts should be based on broader perspectives of justice.

In her conceptualisation, Bernet Kempers identifies a risk of ‘naturalizing’ rights. We propose that a proper understanding of sentience as sometimes including the capacity to make moral choices operates to negate this risk. Within this framework, humans and other sentient animals are part of nature. As an aspect of their sentience, humans and some other species also have the capacity to make moral choices,Footnote 100 which may include choosing to protect others from harm or not to cause pain and suffering to others. While exploitation of weaker species is certainly a part of the state of nature, making moral choices not to exploit others in this way may also be considered part of the state of nature. This framework embraces human moral choice, which should be factored into determinations regarding conflicts between interests. It is incumbent on humans to try and make moral choices appropriately. In the next part of this chapter, we discuss how this framework can be integrated into law and policy, focusing on the context of zoonotic disease transmission.

8.6 Implementation of the Framework in Law and Policy Relating to Zoonotic Disease Transmission

To envisage how the framework might broaden current One Health approaches to better account for the moral value of animals and the environment, we will consider legal and policy approaches to zoonotic disease transmission, focusing particularly on intensive animal agriculture. Zoonotic disease transmission is a primary context in which the adoption of a One Health approach is advocated.Footnote 101 First, to establish common legal and policy approaches to zoonotic disease transmission, we establish some of the key features of zoonotic disease regulation in the systems of Australia, the United States, and China. These countries are among the biggest producers of farmed animal products globally.Footnote 102 We then examine how the framework could supplement these common legal and policy approaches to better account for the moral value of animals and the environment.

8.6.1 Common Legal and Policy Approaches to Zoonotic Disease Transmission

Most contemporary legal systems are underpinned by anthropocentrism, which is reflected in the legal status of animals as human property.Footnote 103 In anthropocentric legal systems, humans are at the centre of legal concern and other animals’ interests merit only indirect consideration, when they align with human interests.Footnote 104 Intensive animal agriculture can be considered an expression of anthropocentrism, as it utilises farming methods that sacrifice animal welfare concerns in order to maximise production and efficiency.Footnote 105 Legal regulation of zoonotic disease transmission in the context of intensive animal agriculture in Australia, the United States, and China is reflective of anthropocentric attitudes. In each of these countries, animals are legally categorised as property,Footnote 106 and intensive animal agriculture practices are widely employed.Footnote 107

A common approach to ensuring animal welfare in animal agriculture (and more broadly) is to enact legislation that restricts property owners’ rights in relation to their animals. Restrictions might include requirements such as, for example, space allowances for chickens.Footnote 108 Australia,Footnote 109 the United States,Footnote 110 and China,Footnote 111 all have laws that regulate what farmers can do in relation to their animals. Where, however, the interests of animals and productivity concerns misalign, commercial interests are likely to prevail. This is demonstrated through the broad failure of intensive farming systems to allow animals to engage in natural behaviours, like sows’ preference for nesting.Footnote 112 While safeguarding animal welfare in animal farming should help to prevent zoonotic disease transmission, restrictions on intensive farming are generally insufficient to manage the risk of transmission in these contexts, as evidenced by zoonotic disease outbreaks linked to intensive farming methods.Footnote 113

Approaches to regulation for the prevention of zoonotic disease transmission focus primarily on controlling disease rather than addressing ‘the structural drivers of emergence and transmission’.Footnote 114 One common approach is to use surveillance to identify emergent zoonotic diseases. Surveillance includes gathering and interpreting health data. Systems are intended to identify emerging diseases early to limit outbreaks.Footnote 115 Surveillance is ordinarily undertaken at different levels; for example, in Australia at national and state or territory levels.Footnote 116 In Australia, surveillance is supported by the National Health Security Act 2007 (Cth) and responsibilities are shared by the Australian Government Department of Health, the Communicable Diseases Network Australia, and OzFoodNet.Footnote 117 In the United States, federal responsibilities for surveillance activities are shared by the federal Commissioner of Food and Drugs, the Director of the Centers for Disease Control and Prevention (including the National Center for Emerging and Zoonotic Infectious Diseases), and the Secretary of Agriculture (including the Animal and Plant Health Inspection Service).Footnote 118 Nevertheless, states have the primary role in surveillance, and there is a strong focus on surveillance in states with high levels of animal agriculture.Footnote 119 In China, human health and veterinary departments are responsible for monitoring zoonotic diseases,Footnote 120 and the Law of Prevention and Treatment of Infectious Diseases governs infectious diseases divided into three classes.Footnote 121

Another common method to prevent the spread of zoonotic disease is biosecurity. This refers to procedures implemented to stop zoonotic disease from being introduced and spread amongst intensively farmed animals.Footnote 122 In these contexts, visiting wildlife are often responsible for the introduction of disease.Footnote 123 In Australia, biosecurity procedures are driven by industry.Footnote 124 In the United States, biosafety, biosecurity, and bio-surveillance are key activities implemented to reduce the risk of zoonotic disease spillover.Footnote 125 Biosecurity is also an important tool for prevention of zoonotic disease spread in China.Footnote 126 Nevertheless, significant obstacles exist to implementing effective biosecurity measures in intensive agricultural facilities. In particular, the scale and intensity of industrialised agriculture generate different and higher disease risks.Footnote 127

Where the spread of zoonotic disease cannot be controlled through surveillance and biosecurity measures, the common approach is to mandate animal culling.Footnote 128 Culling refers to killing diseased or at-risk agricultural animals to stop the spread of disease.Footnote 129 In Australia, the Australian Veterinary Emergency Plan outlines the policies that should be followed where an emergency animal disease is present, including policies requiring killing and disposal of diseased and at-risk animals.Footnote 130 The policy requires that ‘a high standard of euthanasia and respect for the animals is an essential consideration during an EAD response’Footnote 131 where a large number of animals may need to be quickly ‘destroy[ed]’.Footnote 132 In the US, zoonotic disease regulation provides for depopulation or culling, where a disease is identified in an animal population.Footnote 133 The American Veterinary Medical Association provides rules for undertaking mass culling. These include requirements as to appropriate methods.Footnote 134 States also have regulations in place in relation to culling.Footnote 135 In China, compulsory culling is required in relation to farmed animals that are infected by specified diseases.Footnote 136

8.6.2 Integrating the Three-Dimensional Framework for Moral Concern

The framework serves to highlight that humans are not the only stakeholder of moral concern in decisions relating to zoonotic disease transmission. Not only are humans, animals, and the environment interconnected – as acknowledged by the One Health approach – but they also all have moral value (individually and collectively) beyond their economic usefulness to humans. While all three limbs may be impacted by the negative consequences of zoonotic disease spillover in the context of intensive animal agriculture, under current legal and policy frameworks animals disproportionately suffer the worst consequences. Negative impacts for animals include loss of habitat to facilitate animal agriculture, poor welfare for farmed animals, infection, and potential culling (or death).

Changing the paradigm to acknowledge that humans, animals, and the environment are all of moral concern prompts a greater focus on tackling the structural drivers of zoonotic disease. This is because preventing initial spillover will minimise negative consequences for humans, animals, and the environment. The United Nations has identified seven key anthropogenic drivers of zoonotic disease spillover, which include an increasing demand for animal protein and unsustainable agricultural intensification.Footnote 137 Law and policy should be directed towards minimising these drivers. In this context, this would mean implementing laws and policies to reduce demand for animal protein and to shift towards a ‘de-intensification’ of animal agriculture.

In terms of the demand for animal protein, in high-income countries where alternatives to animal proteins are widely available and affordable, policies should encourage consumption of alternative proteins such as pulses rather than animal proteins. Policies could include, for example, removal of subsidies to intensive animal agriculture producers, restrictions or bans on advertising animal products, education initiatives to highlight the benefits of more plant-centric diets and restrictions on inclusion of animal proteins in publicly provided food (e.g. in publicly funded universities, prisons, and the public service). In low and middle-income countries where there are challenges in the availability of alternative proteins, policies should be directed towards increasing availability. Notably, while there is increasing demand for animal protein, ‘the long-term trend for pulses is of sustained consumption levels’.Footnote 138 Law and policy should be directed towards reversing these trends. In relation to ‘de-intensifying’ animal agriculture, legislators need to increase regulation of agricultural operations. Measures could include removing subsidies, use of competition laws to de-concentrate industry, prohibiting additional intensive agricultural farms, requiring intensive animal agricultural operations to internalise the true costs of production including environmental, animal, and human health and welfare costs, removing animal welfare exemptions for farmed animals, and strengthening regulations.Footnote 139

Where a zoonotic disease has emerged, the framework can be drawn upon to modify or at least prompt deep consideration of regulatory responses. Traditional approaches to control zoonotic diseases outbreaks include the culling of livestock and wildlife to limit their movement and their potential interaction with humans and other animals.Footnote 140 However, as Degeling, Lederman, and Rock explain, these approaches are founded on a harm principle that excludes the interests of other animals.Footnote 141 If we judge the appropriateness of regulatory responses on the basis of consequences for the collective (humans and other animals, groups, and the Earth) different conclusions may be drawn. For example, Lederman, Magalhães-Sant’Ana, and Chuan Voo explain how the use of vaccine baits would be more effective in controlling rabies than culling, which remains a mainstream method of disease control.Footnote 142 As a minimum threshold, clear scientific, social, and ethical justification should be required in relation to any decision to cull.Footnote 143

8.7 Conclusion

While One Health is internationally recognised as the optimum approach to the prevention and control of zoonotic disease transmission, in practice it remains confined to anthropocentric considerations of moral value. In this respect, while One Health recognises the interconnectedness of people, animals, and the environment, it does not approach them as having equal moral worth. Instead, as is the case with traditional approaches to public health, humans are considered superior, and where conflict between interests occurs, it is the interests of humans that prevail.

A deeper understanding of One Health, however, mandates that humans are not and should not be the only actors considered to have moral worth.Footnote 144 As Degeling et al. state, ‘[t]o be both ethical and effective, [One Health] approaches might require us to understand health as a universal good that is necessarily shared between species’.Footnote 145 Moreover, to provide a real policy solution to issues of the Anthropocene, One Health must be understood as an expanded ideology in the manner expounded in much of the ethical literature. To further develop this broader understanding of One Health, and to reconcile it with animal rights theory, which also provides a promising pathway towards mitigating the detrimental impact of humans on the Earth, this chapter has sought to demonstrate how a broader conception of One Health can, and should, be conceived of as inclusive of animal rights.

The One Health Three-Dimensional Framework for Moral Concern developed in this chapter is designed to be used as a tool to identify moral relevance in the human and non-human. In ascribing value to the Earth, to groups, and to individuals (human and non-human), the framework recognises interconnectedness and interdependence and emphasises the inherent value of all dimensions. The framework also understands animal rights as compatible with and part of the broader One Health paradigm and can help to determine how to address conflicts between the interests of humans, other animals, and the environment when adopting a One Health approach.

In developing the framework, this chapter has established a method by which to locate recognition of animal inherent worth within the One Health paradigm. Discussion of the potential implementation of this approach in the context of zoonotic disease prevention and control has assisted in demonstrating the theoretical implications of the approach for contemporary societies and their common uses of animals.

9 The One Health Approach and the Tackling of Drivers of Environmental Degradation The Case of the EU Deforestation-Free Products Regulation

9.1 Introduction

Forests cover about 30 per cent of the global land area and host about 80 per cent of its biodiversity.Footnote 1 They provide important ecosystem services, including subsistence and income to 25 per cent of the world’s population, clean air, water flow regulation, carbon sequestration, habitats for species,Footnote 2 and disease regulation and control.Footnote 3

However, forests are also seriously under threat due to deforestation and forest degradation.Footnote 4 The Food and Agriculture Organisation (FAO) estimates that 420 million hectares of forests (10 per cent of the remaining global forests), corresponding to an area larger than the European Union (EU), were lost between 1990 and 2020.Footnote 5 The FAO reports also noted increasing disturbances in relation to forest ecosystem health and observed that 10 per cent of forests are considered to be severely fragmented.Footnote 6

The causes behind such loss and fragmentation are traced back to the expansion of land used for agriculture (about 80 per cent of global deforestation), but also – to a lesser extent – urban expansion, infrastructure development, and mining, with differences in relation to the location, and between regions and within continents.Footnote 7 Additionally, the drivers of deforestation and forest degradation are not limited to the forestry sector itself, as there are also matters of weak land tenure regime, weak government and legal enforcement and protection of Indigenous rights and broader human rights, climate change, democracy and political freedoms, consumption levels of the commodities, dependence on feed imports, and agricultural and other policies.Footnote 8

In terms of the One Health framework, this loss comes with significant consequences for people, wildlife, and the environment, such as increased opportunities for contact between people and wildlife and related disease emergence and spread, human diseases linked to environmental degradation, loss of habitats, increase of greenhouse gas (GHG) emissions, and other effects.Footnote 9

To mitigate this loss, legislation can assist in three key ways. First, legislation can contribute to ecosystem and species protection,Footnote 10 as well as restoration.Footnote 11 Second, legislation can regulate the interface between nature and other policy fields (agriculture and food production, climate, and energy).Footnote 12 Third, legislation can regulate the value chains and supply chains. The term ‘supply chain’ has been defined as ‘a dynamic process that includes the continuous flow of materials, funds, and information across multiple functional areas within and between chain members’.Footnote 13 In simpler terms, supply chains refer to the sequence of linked processes and stages involved in product production, movement, distribution, and sale.Footnote 14 As such, ‘greening’ supply chains of products and materials represents a way in which nature loss and degradation can be prevented.

In recent years, the EU has initiated action on this third pathway and adopted the ‘Deforestation-free Products Regulation’ (The Regulation).Footnote 15 The Regulation contains rules on the placing and making available on the Union market and the export of certain products that contain, have been fed, or have been made with certain commodities (cattle, cocoa, coffee, oil palm, rubber, soya, and wood),Footnote 16 thus ‘targeting’ the EU consumption of these products, which accounts for a non-negligible amount of the global share of deforestation and forest degradation.Footnote 17 Indeed, the Regulation aims to minimise the contribution of the EU to deforestation and forest degradation that might accompany these products if there is a lack of a proper due diligence system in place. A second connected aim of the Regulation is to reduce the EU’s contribution to GHG emissions and biodiversity loss.Footnote 18

If this is an environmental instrument that touches on the supply chain of certain products with clear due diligence obligations in relation to these products, what does the Regulation have to do with health and the One Health approach? What are some elements of interest from a One Health point of view?

In the quest to find answers to the above questions, this chapter is structured as follows.

In Section 9.2, the systemic importance of forests and the interlinkages between forests and health will be illustrated. Section 9.3 will consider the relevance of environmental protection for disease prevention in the context of the One Health Approach. These two sections combined will provide the basis for Section 9.4, where the (hidden) health dimension of the Regulation and the Regulation itself will be explored. Section 9.5 will present a discussion on the themes covered and conclusions.

9.2 Forests and Health

Land use and land use change emissions (including deforestation) are among the biggest drivers of climate change, exerting a sizeable impact as the second most significant cause of climate change after fossil fuels.Footnote 19 In fact, forest harvesting and conversion to agricultural land release a substantial part of the carbon stored in biomass and soil.Footnote 20 In addition, forests act as carbon sinks and deforestation and forest degradation reduce the carbon-absorbing capacity of forests.Footnote 21 The contribution of deforestation and forest degradation to climate change is so substantial that estimates indicate that forest and natural ecosystem protection could potentially contribute to 16–30 per cent of climate change mitigation needs,Footnote 22 to meet the targets of the Paris Agreement.Footnote 23

Deforestation and forest degradation also cause loss of species, habitat loss, habitat fragmentation, and a consequent decreased capability of species to adapt to climate change and other pressures and stressors.Footnote 24 Population decline and/or local extinction of such species and a different biodiversity composition in these spaces may also have a domino effect on other species due to, e.g. food-web interactions and other ecosystem processes, with further potential future effects.Footnote 25

Finally, wider environmental degradation is often brought about by deforestation forest degradation, and land use change, namely water quality issues (e.g. linked to decreased soil filtration with possible effects on access to clean drinking water),Footnote 26 soil quality (e.g. erosion, which also may lead to an impacted capacity of rivers and dams and increased runoff),Footnote 27 and air quality (this might be especially true where deforestation is conducted through slash and burn techniques or where we have spontaneous fires).Footnote 28

The environmental issues connected to deforestation and forest degradation discussed above are notably woven together and, both singularly and cumulatively, have implications for animal and human health.

First, climate change and biodiversity loss have, on their own, been linked to a possible increase in disease emergence and spread.Footnote 29 Along with a more ‘obvious’ variation in temperature and climate, climate change causes the environmental conditions of habitats to change. A spatial rearrangement or shifting of habitats and species might also occur, depending on the internal species traits and external drivers of change: this would be, essentially, a ‘relocation’ of species out of certain areas and into other areas, in line with the shifting of habitats.Footnote 30 For example, climate change has already been linked to a change in the distribution of tick-borne pathogens.Footnote 31 This ‘movement’ could allow for changes in species composition and represent a suitable opportunity for new contact between species and between species and pathogens, potentially facilitating a disease spillover event (where disease spreads from non-human species to humans).Footnote 32 Additionally, climate change has been associated with increased health events due to higher temperatures.Footnote 33

As for the importance of biodiversity for health,Footnote 34 it has been hypothesised, for example, that a reduction of animal populations and biodiversity might result in the loss of the ‘dilution effect’ or ‘wasted transmission’ between (non-specific) hosts and (zoonotic) pathogen spread.Footnote 35 This hypothesis suggests that biodiverse communities limit the spread of diseases through several mechanisms,Footnote 36 essentially ‘diverting’ free-living parasites from suitable hosts (i.e. completely unsuitable hosts: decoy effect; or low competency hosts: alternative hosts).Footnote 37 Biodiversity is also an interesting ‘tool’ for the production of medicines,Footnote 38 meaning that biodiversity loss might be detrimental to their research and development, impairing the finding of disease cures or the use of better alternative ingredients for pharmaceuticals.Footnote 39

Second, there may be a causal link between deforestation and forest degradation, contact with, and trade of wildlife and virus emergence and spread.Footnote 40 This may be due to increased contact between humans and wildlife, causing viruses to cross barriers between species and may, eventually, lead to increased chances of a spillover event of a pathogen (with epidemic or pandemic potential) in cases of deforestation and forest degradation.Footnote 41 Regarding the degree of risks related to disease spread, habitat fragmentation is particularly problematic (besides the potential biodiversity loss associated with it) because the length of the perimeter of the forest edge where humans and livestock may more likely come into contact with wildlife increases.Footnote 42 Deforestation may also involve the creation of roads with potential consequences for disease emergence and transmission, such as via increased access and/or increased hunting behaviour.Footnote 43

Naturally, these aspects are not only relevant to human health. The route or direction of the transmission of the disease might not be a ‘one-way street’ as certain diseases can also be transmitted to (wild) animals by humans, thus adding another problematic dimension to the issue at hand: potential added biodiversity (and economic) loss among infected (domesticated or wild) animal populations.Footnote 44

Finally, looking beyond infectious diseases, there may be health consequences due to increased heat (for both humans and animals) and mental health issues associated with deforestation,Footnote 45 but also the potential for other diseases linked to environmental degradation, such as the already mentioned air quality, soil quality, and water quality issues.Footnote 46

Given the above, tackling deforestation and forest degradation and broader forest protection measures could be considered as having broader health implications and representing a strategy for disease prevention, and of benefit to human and animal health, and not just climate and biodiversity protection measures.

9.3 The Relevance of Environmental Protection for Disease Prevention in the One Health Approach

The One Health approach is an approach based on collaboration, multidisciplinarity, and multisectorality, founded on the notion that human health, animal, and environmental health are interdependent.Footnote 47 The approach should contribute to and inform the design and implementation of programmes, policies, legislation, and research and support the collaboration and communication between sectors and disciplines. The ultimate goal is to achieve better public health outcomes.Footnote 48 If one were to schematically represent One Health, the approach would appear as having different nexuses, which could be considered singularly (the human–animal nexus, the human–environment nexus, and the animal–environment nexus) or together (the human–animal–environment nexus).Footnote 49 Because the approach involves so many interfaces and elements, it can be an excellent tool in the pursuit of more effective measures and actions for problems that involve a systems approach.

Given that each of these nexuses forms part of the One Health approach, strategies tackling even one of its elements could be regarded as a factual operationalisation of the approach, perhaps even when the connection is not explicitly considered. Indeed, a One Health approach also implies the need to reduce human pressure on the environment, which could be seen as a medical intervention in itself, and calls for better integration of environmental and wildlife issues to address challenges related to disease spillover.Footnote 50

In particular, given that the origins and roots of diseases can often be found in ecological systems and their management, integrating ecological approaches along with the more ‘traditional’ biomedical approaches would make for a comprehensive and balanced disease prevention strategy.Footnote 51 In this sense, ecological countermeasures (strategic conservation and restoration of nature and, hence, the mitigation of risks for at-risk humans) can prevent spillovers and protect human and animal health, with the added benefit of addressing climate change and biodiversity loss.Footnote 52 In the optic of disease prevention in relation to ecological approaches, the focus would be on maintaining habitat integrity, heterogeneity, and connectivity to prevent new interfaces enabling disease emergence and spread.Footnote 53 From a legal standpoint, this would translate into establishing measures with protective, conservation, and restoration goals, which, if sufficiently ambitious and well implemented, could have positive One Health implications from a prevention angle.

That said, pandemic and disease policy discussions generally focus more on enhancing preparedness and response.Footnote 54 It has also been noted that the environmental sector is often forgotten or left to the sidelines in national and global strategies for pandemic preparedness and mitigation,Footnote 55 and that current health security priorities and planning neglect the significant role of environmental factors in pandemic and disease prevention.Footnote 56

Tentative steps to further include the environmental element or environmental protection as a prevention measure have been attempted in the draft of the World Health Organisation’s Pandemic Treaty (yet to be adopted at the time of writing).Footnote 57 Article 4, dedicated to pandemic prevention, recognises that certain factors increase the risk of pandemics (i.e. environmental, climatic, social, anthropogenic, and economic factors), and places importance in their identification and in their consideration in the development and implementation of relevant policies, strategies, and measures at the international, regional, and national levels. Additionally, Article 5, where the One Health approach is further addressed after its definition in Article 1, expresses the commitment of the parties to identify and address the drivers of pandemics and the emergence and re-emergence of diseases at the interface between humans, animals, and the environment by introducing and integrating interventions into relevant pandemic plans.Footnote 58

Lastly, Article 3 includes the best available science and evidence as the basis for public health decisions for pandemic prevention among the principles guiding the parties:Footnote 59 theoretically, this could also include science advocating for area-based measures or other types of protective measures to maintain the integrity and coherence of habitats.Footnote 60

The above considerations denote that the inclusion of environmental considerations and environmental law measures in the fight against diseases in a One Health fashion is not as straightforward as one might expect; they do not mean to convey that overlaps do not exist in current legislation. Indeed, in the EU, a notable example of the integration of environmental and health considerations under one text is the Waste Framework Directive, where both environmental and human health protection have a prominent role.Footnote 61

Additionally, it should be noted that environmental law instruments have, at almost all times, developed independently from human health considerations.Footnote 62 This could be valid for the EU Nature Directives and for the Regulation on Deforestation-Free Products on forestry supply chains, which may nonetheless indirectly contribute to health objectives.

9.4 Regulation 2023/1115 on Deforestation-Free Products: A Regulation with a (Hidden) Health Dimension?
9.4.1 Preliminary Observations

The Regulation is part of a broader set of actions meant to address deforestation and forest degradation delineated in the European Green Deal:Footnote 63 the Biodiversity Strategy,Footnote 64 the Forest Strategy,Footnote 65 the Farm to Fork Strategy,Footnote 66 and the Commission’s Communication on stepping up EU action to protect and restore the world forests.Footnote 67 Together with the provisional agreement on the Nature Restoration Law concluded at the end of 2023 and its adoption in 2024 (which also covers forest ecosystems in the EU),Footnote 68 the Deforestation-free Products Regulation represents a significant step forward in the protection of the environment – forests in particular – both in the EU and in third countries.

The Regulation requires that the products it covers (products that contain, have been fed, or have been made with certain commodities, i.e. cattle, cocoa, coffee, oil palm, rubber, soya, and wood) are ‘deforestation-free’. This marks a bold difference from the EU Timber Regulation,Footnote 69 which only focused on the legal provenance of timber products and which is repealed by this new Regulation. Indeed, a significant part of ongoing deforestation is legal according to the laws of the country of production,Footnote 70 meaning that focusing only on the legality element has not been entirely effective.Footnote 71 The Regulation is meant to fill these gaps to minimise the connected risk of lowered environmental standards to obtain market access.Footnote 72

9.4.2 The (Hidden) Link with the One Health Approach

The Regulation is, quite clearly, an environmental measure. Yet, it also has links to human and animal health. Indeed, addressing the link between land and health should be considered as belonging to a wider One Health strategy for disease emergence and spread, an environment-targeted operationalisation of the One Health approach as an integrated approach.Footnote 73

As observed above, measures on nature and forest protection, conservation, and restoration, if sufficiently ambitious, may have positive One Health implications. Most notably, efforts to keep forests intact in the EU and outside the EU constitute an expression of the One Health approach in the form of preventative action. Targeting value chains and supply chains connected to deforestation and forest degradation, which is what the Regulation is set out to accomplish from the European Union’s side, may be considered one of these preventative actions.

The relevance of the Regulation and its measures would be higher in relation to the comprehensive nexus connecting humans, animals, and the environment, but it is also noticeable with respect to the individual nexuses of the One Health approach, especially the animal–environmental and environmental–human health nexuses.

That said, the protection of human and animal health in keeping with a One Health approach is not among the goals of the Regulation (Article 1). Preambular 20 of the Regulation, recalling the importance of measures against deforestation and forest degradation for achieving the Sustainable Development Goals (SDGs), does state that the Regulation should contribute to meeting the goals of SDG 3 – good health and well-being – among others,Footnote 74 but this is not reflected in the Articles and Article 1 in particular, which only expressly considers the link of deforestation and forest degradation with climate change and biodiversity.

Considering the above, it can be wondered how effective the Regulation could be in tackling deforestation and forest degradation, and thus be instrumental from a One Health perspective.

While it is true that most commodities may be consumed at the local or regional level, it is crucial to account for the relevance of imports and exports. The EU consumption of products such as palm oil, cattle, soy, cocoa, coffee, timber, and rubber, also in their processed forms, accounts for 10 per cent of the global share of deforestation and forest degradation when considering the total final consumption (which is, then, deforestation embodied in the consumption).Footnote 75 In this sense, tackling these commodities through Union policy intervention could bring the highest benefits for the unit value of trade,Footnote 76 and demand-side action seemed to hold the most substantial potential to deliver the EU’s commitments and ensure increased sustainability in supply practices:Footnote 77 indeed, the more significant the EU consumption and, thus, intra and extra EU imports, the larger the leverage can be expected from EU action targeting deforestation and forest degradation.Footnote 78

Further, from the list of commodities covered (wood, cattle, cocoa, coffee, palm oil, rubber, and soya), it can immediately be noted how this instrument could be interesting to consider from a One Health perspective. First, forest activities and forest work, which could be associated with any commodity linked to deforestation, are among the epidemiological risk factors for certain zoonotic diseases,Footnote 79 and a higher risk of deforestation for different commodities would likely be carried onto the epidemiological risk. A second relevant matter is the possibility of detrimental practices in the cultivation of these commodities. For example, palm oil plantations not only involve deforestation and biodiversity loss,Footnote 80 but are also linked to respiratory illnesses and pollution.Footnote 81 Third, and this specifically concerns the rearing of cattle, not only would deforestation be carried out to make space for cattle with all the environmental issues that this would entail, but cattle rearing in deforested land could lead to increased contacts between wildlife or disease vectors, farm animals, and humans.Footnote 82

Finally, the Regulation covers the supply chain of the concerned products deriving from these commodities (imports and exports), meaning that it can be considered as having some extraterritorial (extra-EU) effects, potentially making the Regulation a measure of global interest.Footnote 83 Indeed, the responsibility in relation to ensuring deforestation-free or forest degradation-free supply chains is placed on EU-based companies, but the impact of complying with the due diligence requirements is likely to be felt also in third countries.Footnote 84

What is more, the Regulation may encourage non-EU countries to take (similar) protective measures, which could be beneficial for forests and, in turn, for human and animal health: while the Regulation does not create obligations for non-EU countries (it does so only for operators and traders, EU member states, and competent authorities), it introduces facilitations for the tasks of companies under this Regulation if non-EU countries have undertaken actions to enhance deforestation-free supply chains and reinforce traceability systems on commodities.Footnote 85

9.4.3 Structural Elements of the Regulation Having Relevance from a One Health Perspective
9.4.3.1 Matters of Scope and Definitions

With the scope of the Regulation, the concepts to consider are those of ‘relevant commodities’ (wood, cattle, cocoa, coffee, palm oil, rubber, and soya)Footnote 86 and of ‘relevant products’ (‘products listed in Annex I that contain, have been fed with or have been made using relevant commodities’).Footnote 87

It is essential to note that the Regulation only applies to the ‘relevant products’. Cumulatively with the concept of relevant commodities, the notion of ‘relevant products’ helps more precisely identify the scope and the reach of the Regulation. However, it also limits its scope: with a list of defined products, there may be significant gaps concerning products that are not included in Annex I, and that contain, have been made, or have been fed with the relevant commodities.Footnote 88 This could limit the effectiveness of the Regulation in tackling deforestation phenomena.

Further, one of the most important definitions in this Regulation is the definition of ‘forest’. This definition is crucial for the scope of the legal act because the Regulation is built around the additional (and also critical) concepts of ‘deforestation’ and ‘forest degradation’, which can only occur in what is considered a ‘forest’ by the law. The definition of ‘forest’ in the RegulationFootnote 89 mirrors the FAO definition of forest.Footnote 90 This was a conscious choice as it was considered (particularly by the EU Council)Footnote 91 that the definitions in the Regulation should be built on internationally agreed concepts.Footnote 92 Accordingly, ‘forest’ in the Regulation is defined as: ‘land spanning more than 0,5 hectares with trees higher than 5 metres and a canopy cover of more than 10 per cent, or trees able to reach those thresholds in situ, excluding land that is predominantly under agricultural or urban land use’.Footnote 93

Given that the Regulation is built around the concept of ‘forest’, other ecosystems that are not ‘forest’, which could also be interesting to protect from a One Health perspective, are not covered by the Regulation. Forests are not the only ecosystems impacted by economic activities, and forest protection should not lead to the conversion or degradation of other natural ecosystems.Footnote 94 With this in mind, the possibility of extending the scope beyond forests was embedded in the law,Footnote 95 particularly with regard to land with high carbon stocks and with high biodiversity value, such as grassland, peatlands, and wetlandsFootnote 96 (with the potential challenges from a One Health point of view),Footnote 97 as these are also increasingly under pressure from conversion and degradation due to commodity production for the EU market.Footnote 98

Two other crucial definitions are those of ‘deforestation’ and ‘forest degradation’, which also carry the scope of the Regulation: the legal act is dedicated to market access and the export of deforestation-free products, and being ‘deforestation-free’ is one of the criteria for market access and export.Footnote 99

The Regulation defines ‘deforestation’ as ‘the conversion of forest to agricultural use, whether human-induced or not’,Footnote 100 where ‘agricultural use’ is ‘the use of land for the purpose of agriculture, including for agricultural plantations and set-aside agricultural areas, and for rearing livestock’.Footnote 101 It should be noted that ‘deforestation’ only includes situations of forest clearance for subsequent agricultural use, be it plant or animal agriculture, thus leaving out other important types of deforestation such as deforestation for infrastructure,Footnote 102 which is a relevant aspect for health considerations. With regard to this definition, questions arise in the case of deforestation aimed at timber harvesting not followed by conversion to agricultural or other use, as this does not seem to be included in the realm of situations covered by the definition of deforestation or forest degradation.

The definition of ‘forest degradation’ covers structural changes to forest cover in the form of specific forms of conversion: ‘conversion of (a) primary forests or naturally regenerating forests into plantation forests or into other wooded land; or (b) primary forests into planted forests’.Footnote 103

There is no definition of what degradation is beyond the indicated types of conversion. The justification for this specific choice is that it would make it possible to act quickly and in a manner that is instantly measurable and verifiable. This would be, at least, the initial definition, potentially subject to future expansion in the revision of the text.Footnote 104 While these reasons have some merit, opting for such a definition might lead to other types of degradation not being covered, such as timber harvesting not followed by conversion. That said, the door was left open (with careful wording) for reconsidering the definition of ‘forest degradation’, taking into account progress made in international discussions and forest diversity worldwide, after an in-depth analysis has been conducted regarding that process.Footnote 105

9.4.3.2 Requirements for ‘Access’ to, or Export from, the EU Market

The commodities and products covered by the Regulation must meet certain requirements to be placed or made available on the EU market or exported from the EU.

The requirements are cumulatively indicated in Article 3: such products and commodities (1) must be deforestation-free, (2) must be produced following the relevant legislation of the country of production, and (3) must be covered by a due diligence statement.Footnote 106

The status of ‘deforestation-free’, which also relies on the definitions above, indicates that only certain products can be considered ‘deforestation-free’ within the meaning of the Regulation: deforestation-free products are those that have not caused deforestation or forest degradation.Footnote 107 In principle, any commodity originating from a situation of deforestation or conversion to a plantation or planted forest is regarded as not deforestation-free, affecting the possibility of placing or making it available on the EU market or exporting it, as per Article 3.

This makes for a particularly interesting element from both environmental protection and a One Health perspective as it provides incisiveness to the Regulation by identifying clear and important consequences and, thus, potentially discouraging types of practices linked to deforestation and forest degradation worldwide.

The criterion of the legality of production relies necessarily on the definition of ‘relevant legislation of the country of production’. Interestingly, the definition includes not only land-use rights, environmental protection, and forest-related rules (e.g. forest management and biodiversity conservation) but also the rights of third parties; labour rights and human rights protected under international law; the principle of free, prior, and informed consent; and tax, anti-corruption, trade, and customs regulations.Footnote 108 While some criticisms can be formulated,Footnote 109 this broad definition of relevant legislation also makes the Regulation more incisive, with clear consequences.

The third criterion is related to the presence of a due diligence statement, entailing a due diligence process that operators have to carry out for all relevant products supplied by each supplier.Footnote 110 The due diligence system is a mechanism to ensure that the criteria of Article 3 (a) and (b) are complied with. Unless a simplified form of due diligence can be performed,Footnote 111 the ‘standard’ due diligence system foresees robust requirements in terms of: (1) mandatory information and proof;Footnote 112 (2) a robust risk assessment system to guarantee that there is no or only negligible risk that the products are not in line with Article 3;Footnote 113 and (3) a system of risk mitigation for those cases where the risk assessment has revealed that there is a risk or a non-negligible risk of non-compliance with the requirements in Article 3.Footnote 114

These due diligence rules present a comprehensive due diligence system that should be effective in ‘ferreting out’ non-deforestation-free and illegal products or commodities along the supply chain and indirectly contributing to the protection of the environment in the country of origin, thus strengthening the environmental–animal–human health nexus of the One Health framework.Footnote 115

9.4.3.3 Three-Tier System Regarding the Assessment of Countries

The three-tier system is envisaged in Article 29; it involves the assessment and classification of countries or parts of countries into three risk categories following an assessment: high-risk, low-risk, and standard-risk, respectively qualifying countries or parts of thereof where there is a corresponding risk of having relevant products not complying with the deforestation-free criterion (Article 3(a)).Footnote 116 The assessment needs to be based on certain criteriaFootnote 117 but may also consider additional criteria, such as information submitted by NGOs and other parties (e.g. Indigenous people), and transparency (or lack thereof) of the country concerned.Footnote 118

Such classification as low- or high-risk countries determines certain consequences. For example, products or commodities produced in low-risk countries enjoy certain facilitations, the most important of which is simplified due diligence.Footnote 119

The classification of countries according to a risk assessment is an interesting feature of the Regulation. If properly and objectively carried out, it could help modulate the efforts concerning the risks identified in the assessment and recognise the most problematic situations concerning deforestation and forest degradation, potentially generating positive environmental outcomes and positive effects on implementation and enforcement. This classification might also help steer consumption to safer (as in lower-risk) supply chains in low-risk countries due to the simplified due diligence required, and it might encourage higher-risk countries to take action against deforestation and forest degradation, with related health-connected outcomes. At the same time, aggregated assessments might overlook risks in key sourcing areas and risks associated with a specific supply chain.Footnote 120 With this in mind, the simplified due diligence as per Article 13 is, perhaps, too simplified as it represents quite a ‘dispensation’ from important provisions, warranting consideration of whether some form of risk assessment and risk mitigation should still be required.

9.5 Discussion and Conclusions: The Regulation as Part of a One Health Strategic Approach?

This chapter has highlighted the systemic importance of forests for the climate, the environment, and biodiversity and the specific value of forests for health, particularly in their role in disease regulation and of the interlinkages between climate change, environmental problems, biodiversity loss, and disease emergence and spread. This suggests that forest protection and care and avoiding deforestation and forest degradation should be a significant element of One Health-based preventative solutions.

The Deforestation-free Products Regulation inserts itself among the EU measures to counteract deforestation and forest degradation in the EU and abroad. The Regulation is bound to affect the supply chain of several products. While it might create additional burdens along the supply chains, it will be instrumental in ensuring that commodity and product production does not come at the price of deforestation and forest degradation.

The Regulation is a well-rounded text; it pays attention to many aspects related to forest commodities and their supply chain, deforestation, and forest degradation. It addresses not only the issue of the illegality of harvesting but also includes a more qualitative assessment with respect to deforestation and forest degradation with the central concept of ‘deforestation-free’. Admittedly, the definitions of forest, deforestation, and forest degradation could be more in line with scientific concepts, and the Regulation could be extended to cover more commodities, products, and different ecosystems. However, overall, the final result seems sufficiently tight and ambitious. Additionally, it should be noted that the Regulation also foresees several types of obligations on the EU member states or competent authorities on checks, controls, and reporting obligations,Footnote 121 which are instrumental for the effective implementation and enforcement of the Regulation.

The Regulation is not meant to address human and animal health but ‘only’ to respond to the climate and biodiversity crises. However, without expressly saying so in its objectives, it can be appreciated how the Regulation promotes healthier and more intact ecosystems, likely with worldwide effects, and can work to mitigate climate change and biodiversity loss, all elements linked to the potential for better health outcomes for people and animals. The relatively high ambition of the text and its ‘tightness’ (potentially not allowing for many loopholes) can be sufficient to reap certain benefits from a health perspective, including by steering and encouraging the adoption of forest-friendly practices and modes of agriculture which reduce deforestation. The Regulation’s incisiveness in relation to its implementation and enforcement is also an element of value for human and animal health, in addition to its obvious relevance for environmental health. In this perspective, the Regulation could serve as a way to kickstart the process of better forest care and protection outside the EU, complement the EU framework on nature protection and potentially contribute to disease prevention, especially if considered together with other vital measures (e.g. disease surveillance, public health measures) in true One Health fashion.

10 One Health among Many What Can One Health Learn from EcoHealth and Planetary Health Projects to Encourage Legal Reform?

10.1 Introduction

In the pursuit of more meaningful legal integration, the One Health practitioner can greatly benefit by learning from the unique accomplishments of their interdisciplinary neighbours. Amid a thriving global interest in interdisciplinarity, now is an apt moment to critically examine what applications of interdisciplinarity beyond One Health have been most effective and what lessons can be drawn from these applications. This chapter examines three leading interdisciplinary approaches to health problems: One Health, EcoHealth, and Planetary Health. We focus on lessons that One Health practitioners can learn from projects that have implemented EcoHealth and Planetary Health approaches to address health problems effectively and achieve legal reform in Mexico, Uganda, Ecuador, and Sri Lanka. We argue that by prioritising community engagement and limiting project scope creep, One Health practitioners can both deliver better health outcomes and create more conducive conditions for legal reform to occur.

10.2 Overview of the Health Frameworks
10.2.1 Historical Development
10.2.1.1 One Health

Current usage of the term ‘One Health’ can be most closely traced back to the ‘One Medicine’ concept coined by Calvin Schwabe in 1984 in his textbook Veterinary Medicine and Human Health.Footnote 1 This concept acknowledged the connection between the health of humans, animals, and ecosystems, and recognised that human and veterinary medicine could contribute to each other.Footnote 2 One Health perspectives have also been tied to writings ranging from the ancient world,Footnote 3 to the Enlightenment.Footnote 4 However, these associations primarily relate to the fact that medicine and health interventions do not always seek to exclusively benefit humans. Present-day uses of the term ‘One Health’ additionally emphasise wide interdisciplinary collaboration,Footnote 5 and certainly the use of the ‘One Health’ phrase specifically is comparatively modern.

Around the introduction of Schwabe’s ‘One Medicine’ terminology, similar acknowledgements of interconnection grew within the veterinary field. In 2004, health experts gathered for a Wildlife Conservation Society (WCS) symposium and developed the Manhattan Principles, which highlight links between human, animal, and wildlife health as essential.Footnote 6 By 2007, the American Veterinary Medical Association (AVMA) and American Medical Association (AMA) had both adopted the phrase ‘One Health’ for their own initiatives.Footnote 7 The term increased in popularity leading up to the early–mid 2000s, and developed primarily within both an American context and a medical and veterinary context. This inceptive context continues to pervade One Health articles advocating for or applying the One Health concept: 23.5 per cent of the articles (between 2015–2021) analysed by Byomkesh et al. focused on veterinary medicine and another 19.1 per cent focused on public health.Footnote 8

Although the ‘One Health’ framework has now become widely accepted and deployed by major international organisations – such as through the creation of the One Health High-Level Expert Panel (OHHLEP),Footnote 9 to advising the Food and Agriculture Organization (FAO), United Nations Environment Programme (UNEP), World Health Organization (WHO), and World Organisation for Animal Health (WOAH)Footnote 10 – the field retains many of its medicinal roots and perspectives. Additionally, One Health’s grounding in public health has directed it towards top-down governance, planning, and surveillance strategies; bottom-up approaches (that is, ‘grassroots’ projects or emergent behaviours) may remain comparatively innovative within the One Health paradigm.Footnote 11

10.2.1.2 EcoHealth

The term ‘EcoHealth’ was often used in co-occurring but not distinct or synonymous ways before concrete attempts were made to clarify its meaning. Lebel (2003) notably marked the emergence and consolidation of EcoHealth as ‘an historical step’, presenting it as an ecosystem-focused approach to health arising out of an appropriation of ‘ecological knowledge and methodology by the prescriptive sector of the social science’ in the post-1950s period.Footnote 12 By the 1990s, even the (previously narrowly focused) veterinary field was specifically considering the role of ecosystems in its approach,Footnote 13 suggesting that EcoHealth perspectives evolved concurrently with One Health perspectives in that domain. The establishment of Canada’s International Development Research Centre (IDRC) in 1996 represented one of the earliest milestones of a ‘deliberately transdisciplinary approach’ being used in a distinctively EcoHealth way and is now one of the foremost EcoHealth organisations in the world.Footnote 14

By 2012, in Kunming, China, 105 persons from 38 countries attended the fourth biennial conference of the International Association for Ecology and Health (IAEH),Footnote 15 which included a workshop on ‘ways to increase demand for EcoHealth-type research and practice’, including a further attempt to clarify and define the EcoHealth approach.Footnote 16 By 2016, EcoHealth International (EI) was established ‘building on the legacy of the International Association of Ecology and Health (founded in 2006)’ and ostensibly overtaking its work.Footnote 17 In practice, EcoHealth appears to place the greatest emphasis on ecosystem disruptions and ecological knowledge.Footnote 18

10.2.1.3 Planetary Health

Planetary Health is a relative newcomer to the field of interdisciplinary approaches to the global health scene. Formally conceived by the Rockefeller-Foundation-Lancet Commission in 2014, Planetary Health was preliminarily described as an ‘attitude towards life and a philosophy for living [that] emphasises people, not diseases, and equity, not the creation of unjust societies’.Footnote 19 The Commission first met in Italy in 2014, and claimed to represent a ‘diverse group of global experts in environmental health, medicine, biodiversity, and ecology’.Footnote 20

Today, Planetary Health collaboration, research, and activism is primarily co-ordinated by the Planetary Health Alliance (PHA). The PHA has grown to a consortium of over 400 organisations from 60+ countries around the world and continues to cite the Commission report as the basis of its work.Footnote 21 By the time of Planetary Health’s introduction, both One Health and EcoHealth had become widely known and consolidated paradigms, though academic interest in Planetary Health rose noticeably during 2019–2020.Footnote 22 Although the Commission’s report explicitly mentions these two frameworks and encourages unity with them, it also seems to have felt the burden of proving the need for yet another interdisciplinary approach; accordingly, it has taken more obvious steps to mark its conceptual distinction from the three frameworks considered.Footnote 23

10.2.2 Conceptual Comparisons
10.2.2.1 EcoHealth

One Health and EcoHealth are similar in concept and scope, and major EcoHealth organisations often view their approach as complementary with (or even intrinsically dependent on) the One Health framework. The EcoHealth Alliance (EA), when operational, had professed to ‘practice a One Health approach, incorporating the needs of humans, animals, and the environment in all dimensions of our work’.Footnote 24 Similarly, EI states that they ‘collaborate with members of One Health and Planetary Health initiatives around the world’.Footnote 25

Where there are foundational differences between One Health and EcoHealth, they seem likely to fade with increased interdisciplinary and inter-framework collaboration. For example, One Health may have drawn more from molecular- and micro-biological domains than EcoHealth, while EcoHealth gave greater emphasis to anthropological and rural/urban planning knowledge.Footnote 26 This gulf seems mostly a byproduct of their respective historical developments (rather than a genuine conceptual barrier between the two) and may disappear with time.

Broad similarities in concept and contributing expertise, however, do not guarantee that both frameworks will be implemented identically in practice. While both One Health and EcoHealth acknowledge and value the concept of ecosystem health in theory, it is difficult not to wonder if the active choice of the prefix ‘Eco’ (in ‘EcoHealth’) suggests a greater felt concern for ecosystem-centred health, analysis, and solutions. The One Health framework has often been criticised for gravitating towards human needs and outcomes, and is often viewed primarily as a public health framework;Footnote 27 an important caveat being One Health’s historical involvement in animal treatment and prevention of zoonoses.

The EcoHealth system additionally placed ‘participation’ as one of its three original methodological pillars,Footnote 28 (although these have subsequently been expanded to six)Footnote 29 and continues to place a particularly high degree of emphasis on community engagement (among other forms of participation) and understanding of local context.Footnote 30 We shall return to both of these themes of emphasis on participation and ecosystem matters later.

10.2.2.2 Planetary Health

Compared to EcoHealth and even One Health, the Planetary Health approach is ‘clearly anthropocentric and focuses primarily on human health’.Footnote 31 Although Planetary Health does take ecosystem and animal health into consideration (and climate change in particular), it does so almost exclusively with respect to their value and/or threat to humans and civilization. While the PHA expanded their goals in 2021 to also consider human effects on ‘all life on Earth’, the language used by the PHA and planetary health researchers is still skewed heavily towards human health. Similarly, although the One Health framework has been criticised for anthropocentrism (as above), its grounding in veterinary science and zoonoses has, at least, propagated a consideration of animal health (and related terms like ‘wildlife’, ‘cattle’, and ‘poultry’) heavily through related literature; a focus on animal welfare that Planetary Health research lacks in comparison.Footnote 32 While both frameworks have a tendency to put humans first, this tendency is more central to Planetary Health’s early conception.

This anthropocentrism, however, cuts both ways. Where Planetary Health researchers are primarily interested in environmental factors that may harm human health, they are equally intensely focused on potential human catalysts behind those environmental factors. Myers (2006) suggests that at least six dimensions of human activity – climate disruption, pollution, destruction of biodiversity, biogeochemical interference, land use, and inducement of resource scarcity – trickle down into ‘every dimension of our health and wellbeing’ under a Planetary Health model.Footnote 33

Planetary Health also focuses on empowering communities to create a planet that ‘nourishes and sustains the diversity of life with which we coexist and depend’ and highlights ‘collective action at every level of society’.Footnote 34 The Commission characterises those citizens they seek to include in solution-building as having been ‘often marginalised by prevailing sociopolitical systems and who are most susceptible to disruptions in natural systems’.Footnote 35 Of the three frameworks considered here, Planetary Health perhaps assigns the greatest recognition of the role of institutional and governance failures (as a consequence of ‘prevailing sociopolitical systems’).

This approach is thus somewhat divergent from both One Health and EcoHealth in emphasising ‘governance challenges’ as one of their three categories of challenges.Footnote 36 The Commission describes this challenge as including ‘how governments and institutions delay recognition and responses to threats, especially when faced with uncertainties, pooled common resources, and time lags between actions and effect’.Footnote 37 Likewise, the Commission stresses the importance of economic reform strategies, describing Planetary Health as an ‘unprecedented opportunity for advocacy of global and national reforms of taxes and subsidies for many sectors of the economy’.Footnote 38

In this way, the Planetary Health approach is inherently political in a way that One Health and EcoHealth are not. Where the other two approaches typically view community engagement as a means of achieving better outcomes within individual health projects, Planetary Health is the most forthright (right from its initial conception via manifesto) about the inextricability of legal and institutional reform from health outcomes; importing perhaps a wider view of project efficacy than the other two approaches.

10.2.3 Key Differentiating Elements

As interdisciplinary frameworks undergoing constant evolution, each of our three approaches lack ‘any generally, centrally agreed definitions, and are sometimes handled as almost synonymous, sometimes as overlapping and sometimes as quite distinctly separate’.Footnote 41 However, strictly for the purposes of this chapter, let us establish some key differentiating elements of each approach below, with an emphasis on conceptual differences that (although necessarily reductionist) will serve as useful premises for the remainder of this chapter’s analysis. These elements can be found in Table 10.1.

Table 10.1Key Differentiating Elements between the One Health, Eco Health and Planetary Health Frameworks
FrameworkKey Differentiating Elements
One Health
  • Aims to improve the health of humans, animals, and the environment.

  • Primarily grounded in veterinary, medical, and public health sciences (despite growing interdisciplinarity).

  • Broadly considers ‘health’ as a specific property that an individual human or animal may possess.Footnote 39

  • Projects and initiatives are generally top-down and reactive to health issues; particularly zoonoses, epidemics, etc.

Eco Health
  • Aims to improve the health of humans, animals, and the environment.

  • Primarily grounded in veterinary, medical, ecological, anthropological, and community planning sciences.

  • Conceives of ‘health’ equally as an individual attribute and an aggregate property of (eco)systems.Footnote 40

  • Likely bias towards ecosystem-focused perspectives and solutions.

  • Likely bias towards participatory approaches, particularly emphasising community engagement.

Planetary Health
  • Aims to improve the health of humans as its primary goal (considering animal and ecosystem health, but through an anthropocentric lens).

  • Primarily grounded in climate, agricultural, and ecological sciences.

  • Likely bias towards root cause analysis and identifying human impacts on the environment that later harm humans.

  • Likely bias towards participatory approaches; particularly emphasising legal, institutional, and governance roadblocks to long-term solutions.

10.3 Pathways to Legal Reform
10.3.1 Direct Legal Reform

If we seek to discover what One Health can learn from other health frameworks (in the context of seeking the institutionalisation of One Health into legal and governance structures), we must begin by answering two questions. First, what is the current status of these health frameworks in law and governance? Second, what is their desired status?

Let us begin with the current legal status of these health frameworks. As outlined elsewhere in this book, explicit recognition of the One Health approach in binding federal or international law is comparatively limited.Footnote 42 Although One Health has clearly formed the basis of many international collaborations and policy guidelines – and is now championed in several United Nations resolutions – it is difficult to determine the extent of any direct causal role that One Health has played in effecting permanent legislative change. Where legal instruments are implicitly compatible with a One Health approach, it typically remains an open question as to how concretely One Health informed that legal instrument’s development (as opposed to being developed or popularised in tandem).

EcoHealth and Planetary Health currently possess even more limited, if any, overt recognition in federal or international legislation. This is naturally to be expected, given their relative youth as formalised frameworks, but similarly makes it difficult to assess their direct impact on legislative and governance structures. Assessments of international law from EcoHealth and Planetary Health perspectives tend to regard the landscape as ‘fragmented’ and ‘weak’,Footnote 43 suggesting that the authors do not perceive the legal instruments considered as strongly aligned with EcoHealth or Planetary Health aspirations.

Let us secondly address the question of how these approaches aim to achieve legal reform. From a One Health perspective, this debate is still very much alive and this book will serve an important role in assessing potential routes forward. While Planetary Health explicitly aims to address legal and governance challenges and has broadly aligned with a rights-based approach to international environmental law,Footnote 44 the movement has yet to directly notch a victory in ‘hard law’ (i.e. binding legislation) or completely reconcile its anthropocentric roots with the potential rights of nature. And where EcoHealth practitioners consider their ability to influence policy, they consider primarily indirect mechanisms such as producing effective research to pass on to policymakers.Footnote 45

If One Health, EcoHealth, and Planetary Health so far have had ambiguous or limited success in achieving direct legal reform, and their aspirations for high-level integration into legal and governance structures continue to mature, what, then, can these approaches learn from each other? And how can they work together in overcoming legal and governance roadblocks in a way that does not privilege one of these approaches above the other (potentially hindering their ability to collaborate and co-evolve at the implementation level)?

EcoHealth and Planetary Health may have already stumbled upon the answer: legal reform does not only follow top-down consolidation of ideas and philosophies, but also often reflects bottom-up approaches that have already achieved success. It is this indirect approach to legal reform that we turn to now.

10.3.2 Indirect Legal Reform

This chapter recognises the value of a practical approach to legal reform. By more effectively delivering health outcomes to people, animals, and ecosystems in need, all three health frameworks dramatically increase the odds that supporting legal and institutional reforms will follow. We will examine several EcoHealth and Planetary Health case studies to assess both why the projects in question were successful, and how subsequent legal reforms emerged. By showing that effective health initiatives frequently precede related legal reforms, this chapter argues that a two-way causal link between the two likely exists; just as modernised legal structures could enable more effective health projects (a link that we will not explore in this chapter), so too can effective health projects lay the foundations for better legal structures to arise. These lessons can then inform One Health practitioners in seeking better health outcomes and effective reform of their own.

Such a bottom-up approach to legal reform recognises that substantial progress can still be made to improve health outcomes even within existing legal paradigms at national or international levels. Few countries strictly need a radically new legal conception of health or ecology to achieve better outcomes; for many problems, the solution can be as simple (in theory) as getting a local council to take a matter more seriously and finally implement basic but important regulations.

None of this is to imply that One Health practitioners can or should simply go about their business and rely on legal progress to occur purely incidentally to health work. Rather, this chapter suggests that One Health practitioners can consciously pursue methodologies that are conducive to legal reform through their projects even without a rigid preconception or expectation of what that reform may entail. Several projects that we will examine pursued methodologies, such as extensive community empowerment, which were conducive to subsequent legal or policy reform efforts. Engaging the public and relevant stakeholders in law reform processes habitually creates ‘strengthened democracy, more inclusive democracy, and efficacious law’.Footnote 46

Legal instruments do not need to explicitly or entirely adopt a One Health approach in order to align with it more closely. Indeed, as any legal system ‘is continually engaged in carrying out the self-reproduction (autopoiesis) of the overall social system as well as its own’,Footnote 47 those seeking to reform the system are bound to reflect and respect the social context within which each system functions. While attempts to homogenise the One Health framework for ease of practice (such as pushes towards a Global One Health Index weighting of factors)Footnote 48 are admirable, a globally uniform approach to seeking legal reform may be unnecessary to make tangible progress.

We are now equipped to dive into our EcoHealth and Planetary Health case studies. This chapter will organise them as supporting evidence under two theses, both of which are oriented towards actionable suggestions for One Health practitioners to work towards better health outcomes and improved odds of compatible legal reform. One Health projects should:

  1. (1) prioritise community engagement – and equip project stakeholders with the tools and confidence to pursue subsequent legislative change; and

  2. (2) limit project scope creep – especially in situations where the full scope of One Health’s framework risks becoming cumbersome

10.4 Case Study Analysis
10.4.1 Lesson #1: Prioritise Community Engagement

In our earlier table of key differentiating elements (Table 10.1), ‘community engagement’ was flagged as a distinct virtue of both the EcoHealth and Planetary Health frameworks. How can this be so, when there are many instances of One Health recognising the importance of community engagement and even elevating it as a ‘pillar’ of the approach?Footnote 49

The rationale for this distinction lies in practice, rather than in theory. A 2018 systematic analysis of One Health Networks (OHNs) found that ‘activities such as communication and collaboration, data and information sharing, and human resource capacity building were reported by OHNs far more often than were other activities, such as community engagement and education or implementation research’.Footnote 50 Moreover, the discrepancy is not a mild one: the analysis found that engagement with local populations to help adapt interventions to more specific socio-cultural contexts was ‘being done by less than 15% of OHNs’.Footnote 51 While certain OHNs do perform exceptional community outreach, they are so far the minority.Footnote 52 This discrepancy remains despite more recent attempts to by One Health institutions to recognise the importance of community engagement;Footnote 53 One Health research (from 2015–2021) demonstrated a ‘a gap between advocacy and implementation, indicating a need for closer coordination’.Footnote 54

This discrepancy is easily understood in the context of One Health’s empirical roots and rise to popularity. One Health draws primarily from scientific fields that are notoriously difficult to communicate as local knowledge: a rural village has little chance of independently formulating and producing a technical veterinary drug. Similarly, as a health approach geared particularly to the outbreak and spread of disease, One Health projects have likely uncovered greater attention and funding when addressing ‘outbreak narratives’ rather than fundamental and structural drivers like intensification of animal agriculture;Footnote 55 biasing the approach further towards reactive, top-down responses less likely to require long-term community engagement.

This chapter will present several EcoHealth and Planetary Health case studies that successfully prioritised community engagement. They did so not only in a manner that contributed to desired health outcomes but also facilitated future legal reform and recognition.

10.4.1.1 Manganese Mining in Mexico

One of the largest Manganese (Mn) deposits in the world is found in the tiny region of Molango, Mexico. With a population of barely 12,000 people,Footnote 56 the local economy is dominated by mining operations conducted by the Autlán Mining Company (AMC). In a now-archetypal dilemma for similar regions, these mining operations bring much-needed revenue to the local population while simultaneously damaging their health. Public complaints in the 1980s led the Hidalgo state government to commission a study into health risks in the area, which predictably uncovered elevated Mn concentrations in blood and associated neurobehavioural deficits.Footnote 57 These results were shared with various authorities and the AMC, catalysing a more comprehensive study and project (built on an EcoHealth framework) to begin in 2001.Footnote 58

An ongoing focus of this project was multistakeholder consultation. Meetings and workshops were held with community representatives (among others) throughout the study, from project planning to dissemination of results. One key discovery of this study was that AMC’s manganese emissions were very likely responsible for developmental delays in children. Documenting this link and providing the community with those results better equips the people of Molango to advocate for their health going forward.

After a decade of focused work in the region, the EcoHealth team saw tangible reward for their efforts: the AMC (in conjunction with the state government) launched an Environmental Improvement Program including community support programs, pavement of transited areas, and acquisition of new dust collectors and an emissions-reducing ball mill.Footnote 59 Additionally, although immediate legislative progress proved difficult due to close governance links between the AMC and municipal councils,Footnote 60 as well as a perception among municipal officers that they did not have the authority to act,Footnote 61 local health officials ‘clearly recognized that mining pollution affected the health-illness pattern’ of residents.Footnote 62

In September 2022, members of the local Ixcotla community blockaded a highway in a move to pressure the AMC to help fund community needs, including private medical insurance for each inhabitant.Footnote 63 This effort paid off, and the Hidalgo state government facilitated negotiations that led the AMC to invest a further US$715,600 into development programs for the region.Footnote 64 Almost half a century after locals had to pressure the state government to even investigate the health effects of AMC’s mining operations, their sustained commitment has enabled them to sit down at a negotiating table with that same government completely independently of any facilitating structure.

Mexico is also making progress at a federal level. The Mexican Congress introduced Mining Reform legislation in 2023, broadly cracking down on exploitative mining. The regulations establish ‘contamination with dangerous repercussions for the ecosystem or for public health’ as a rationale for cancellation of mining concessions,Footnote 65 include ‘revised and expanded indigenous public consultation rules and processes’,Footnote 66 and require concession holders to pay at least 5 per cent of net profits to affected indigenous communities.Footnote 67 Stricter environmental regulations were by no means guaranteed by the election of a broadly left-wing President (Andrés Manuel López Obrador), either; indeed, his administration allocated 35 per cent less funding to its environmental department than his predecessor.Footnote 68 In other words, the focus on environmental regulation that explicitly mandated community consultation was not a ‘given’ simply by virtue of the government’s general position on a left–right political continuum.

Can the EcoHealth framework take full credit for the regulatory triumphs of the Obrador administration or the bold action of the Ixcotla peoples? No. But it must be acknowledged that a decade of community-inclusive health work in the region likely better equipped that community with strong arguments and data to lobby for their interests with the AMC and Hidalgo state government. Similarly, widespread projects of this nature can give policymakers both the popular support and understanding they need to pass more effective legislation.

10.4.1.2 Mangrove Conservation in Sri Lanka

Mangroves and their biomes (mangals) are vital to the health of the Sri Lankan population through a wide range of mechanisms. They support coastal fisheries that provide income and healthy proteins rich in iodine, vitamin D, and omega-3 fats. Their root systems dampen sea surges and protect the over 90 per cent of Sri Lanka’s coast considered vulnerable to tsunamis.Footnote 69 Their leaves and bark are widespread in traditional medicines that are known to exhibit effective antibacterial properties.Footnote 70 The Seacology-Sudeesa Sri Lanka Mangrove Conservation Project has made enormous strides in protecting these valuable habitats. As a member of the Planetary Health Alliance,Footnote 71 Seacology operates projects across the world to protect threatened island ecosystems. They paired with Sudeesa (an already existing local federation of small-scale fishing and farming community organisations) in 2001 to help educate community and government stakeholders about the financial and (human) health benefits of intact mangroves;Footnote 72 a people-focused lens that remains core to the Planetary Health approach.

Remarkably, the Seacology-Sudeesa project demonstrated both the ambition to seek national legal reform in Sri Lanka and the patience to pursue it through often indirect channels. While initiative leads always knew they ultimately sought country-wide legal protections, the project began more humbly by scaling Sudeesa’s grassroots activism across other coastal communities.Footnote 73 These activities involved direct education on mangrove conservation, but also included business training, replanting programs, and microloan support for local women.Footnote 74

By prioritising local community engagement in this way, Sudeesa has become ‘a bridge between community perspective and government policy’, able to inform the government about how the community is feeling. A government official from Sri Lanka’s Ministry of Mahaweli Development and Environment acknowledged that ‘the Seacology-Sudeesa project is the most direct way the ministry receives input from the community’.Footnote 75

Similarly, the project developed unprecedented support from the government (which had previously disregarded environmental assessments and advice) specifically because the project ‘never [tried] to interfere politically’.Footnote 76 This blossoming of both community education and government goodwill soon made a real impact at the governance level; when locals reported mangrove destruction, officials listened, and even the Navy became involved in replanting projects.Footnote 77

In 2015, the project finally accomplished the national legal reform it had sought all along. Seacology, Sudeesa, and the national government signed a tripartite Memorandum of Understanding (MoU), with Sri Lanka becoming ‘the first nation in history to make a pledge to preserve and replant all of its mangrove forests’.Footnote 78 Sudeesa’s trajectory from a local alliance of fisherfolk to a federal-level policy leader is a clear demonstration of the accomplishments that may be gained through grassroots activism.

How did Sudeesa achieve these considerable successes? Certainly not by fighting bureaucratic inertia head-on; community members have remarked that ‘top-down management hasn’t done anything in places like Chilaw Lagoon’,Footnote 79 and prior laws attempting to address the issue of illegal logging of mangroves did not achieve sustainable protection. Rather, the Seacology-Sudeesa project focused on community empowerment on its own merits, and slowly but steadily broke down trust barriers through emergent interactions. When the political climate was finally ready for legal reform, the project found strong and trusting communities willing to help lobby for change, and a government at last willing to listen.

10.4.1.3 Pesticide Regulation in Ecuador

The ‘once fertile’ slopes of the Ecuadorian Andes have been transformed by modern agricultural practices, and not for the better.Footnote 80 Widespread use of hazardous pesticides, primarily chosen for their lower cost and perceived efficacy, have led to declining production and increased reports of related neurotoxicity and poisonings.Footnote 81

The Ecosalud I and II projects, built on an EcoHealth approach and funded by Canada’s International Development Research Centre (IDRC),Footnote 82 worked to ‘tackle the complex drivers of inappropriate use of highly hazardous pesticides’ in the Carchi, Chimborazo, and Tungurahua regions.Footnote 83 Ecosalud I showed that ‘community-based educational activities (for example, farmer-field schools, women’s groups, school activities, and radio spots)’ could improve understanding of pesticide uses. Ecosalud II expanded the geographic reach of this work and collaborated with agronomists from partner institutions (such as the International Potato Center) to continue delivering community health interventions.Footnote 84

A particular feature of Ecosalud II was the creation of ‘potato platforms’: social spaces that brought together a wide range of community and authority figures to discuss issues related to potato farming every month.Footnote 85 Community consultations (including through these potato platforms) uncovered an important lesson: pesticides and their harms were often already important issues to local farmers, but they did not know how to apply related concepts in practice.

This community-driven lesson helped the Ecosalud II team make a lasting impact on local governance: the Ministry of Health would soon adopt the project’s information, training, tools, and even trainees, while one municipality even formed an entirely new Department for Agricultural Production and Development. Ultimately, continued pressure by Ecosalud and related networks led to the national cancellation of registration of type Ia and Ib pesticides;Footnote 86 showcasing again that health projects that begin with a community outreach focus can often later transform into effective channels for legal reform activism.

Of additional interest is the project’s development of a Charter of Farmer’s Rights (‘Charter’) related to pesticide use in Ecuador. This Charter was not a fundamentally new legal instrument, but rather a reframing of the United Nations FAO’s existing Code of Conduct on the Distribution and Use of Pesticides (‘Code’). By reformulating the Code to inform the community more clearly about what they could and should expect from pesticide manufacturers, Ecosalud II aimed to ‘transform the Code into a tool for community decision-making around–rather than technocratic management of–pesticide use’.Footnote 87 The Charter was subsequently recognised by the National Council of Citizen Participation as an important tool for farmers.Footnote 88

There is an important distinction to be made here: this EcoHealth project did not attempt to shoehorn a rights-based approach into Ecuadorian law as a legal philosophy preferred by the project team (or even EcoHealth itself as a framework). Rather, Ecosalud II succeeded because consistent community engagement helped the project team discover that a rights-based reinterpretation would be easier to understand and apply for the people who needed it most. A decade later, as Ecuador still struggles to implement pesticide regulations that are accessible and relevant to small farmers,Footnote 89 these community-centric approaches to legal reform are more desperately needed than ever.

10.4.2 Lesson #2: Limit Project Scope Creep

One Health’s determination to expand beyond its original veterinary and medicinal roots often left the framework in nebulous conceptual territory. As one public health practitioner put it, ‘we need to work a bit harder on defining what One Health actually is’.Footnote 90 In 2022, the OHHELP published an updated definition of the framework, along with a Theory of Change and outcome targets. These high-level objectives state that One Health aims to ‘sustainably balance and optimize the health of people, animals, and ecosystems’, recognises the ‘intrinsic value of all living things’, and values ‘equity between sectors and disciplines’, while retaining One Health’s historical duties (from its medicinal and veterinary roots) such as identification and treatment of zoonoses.Footnote 91

While it now seems settled that One Health aspires to be much more than a public health framework for doctors and veterinarians, the OHHELP’s language persistently frames One Health as a kind of panacea; potentially applicable to anybody, anywhere, working on anything related to the health of any other thing. All three frameworks considered here are broad umbrellas in nature, but arguably One Health most of all.

This approach has its virtues: openness to a wide range of definitions and implementations makes room for interdisciplinarity, and One Health’s ubiquity has facilitated adoption by several United Nations bodies. However, this approach also risks ‘suboptimal strategic planning, coordination, and stakeholder engagement’ and has made ‘determining what would constitute improvements … challenging’.Footnote 92 One Health initiatives can be bogged down at the emphasised ‘collaboration’ phase, and begin to work against their own values.Footnote 93 For instance, Degeling et al. (2017) note that ‘lack of evidence about how different sectors understand One Health, their roles and responsibilities, and how they pursue their priorities, could limit collaboration and its benefits.’Footnote 94

This challenge may be surmountable with time and sufficient communication, but these are luxuries that not all health projects can afford. Sparsely staffed or funded projects often only have the resourcing to operate for a few years and are often situated in developing nations with language barriers to overcome and scarcely any nearby OHNs. Expectations for these One Health practitioners to carefully consider and communicate an increasingly far-reaching framework may take valuable time away from the fieldwork that counts most.

This chapter will present EcoHealth and Planetary Health projects that – although still complex at the implementation level – benefitted from a high level of clarity. By choosing their objectives carefully, these projects delivered stronger health outcomes to the communities affected and helped catalyse future legal reform.

10.4.2.1 Family Planning in Uganda

Nestled in the heart of the African Great Lakes region and framed by mountain ranges to the east and west, Uganda continues a near-silent struggle against an equally quiet epidemic: population growth. From 2015–2020, the nation held the sixth-highest population growth rate in the world, at a staggering 3.2 per cent annually;Footnote 95 approximately the equivalent of 1 in 17 adults having a child each year.Footnote 96

This growth is at once causal and symptomatic of a range of health impacts. Poor rates of contraception use have skyrocketed both birth and disease rates, and the extra mouths to feed sparked a chain of environmental impacts from the depletion of local fish stocks in the Lake Victoria Basin (LVB) to increasing deforestation for both fuel and profit.Footnote 97

Since 2012, Pathfinder International has applied a Planetary Health approach to addressing this issue through the Health of People and Environment in the Lake Victoria Basin (HoPE-LVB) project. The three major arms of the project relate to sexual health and sanitation, family planning education, and sustainable use of the environment; a broad suite of objectives, but without One Health or EcoHealth’s prioritisation of animal/ecosystem health as their own intrinsic goods.Footnote 98

The project’s scope faced further pressure as HoPE-LVB got underway. Sono Aibe, Senior Program Advisor at Pathfinder found that ‘[t]here definitely was pushback [as] people thought [PHE] would be a mission creep … They envisioned us having to work with environmental groups, share resources, and learn about conservation terminology and monitoring indicators. There was this whole anxiety around going into a completely non-health sector’.Footnote 99

While this did not deter HoPE-LVB from continuing their work, it is clear that the team gradually learned to be selective about how they would operate. Planetary Health Alliance advocate Hilary Duff notes that the project ‘prefers to build the capacity of existing community groups’ rather than entirely new facilities to expand contraceptive delivery.Footnote 100 Similarly, although HoPE-LVB frames itself as a ‘rights-based approach’, it also seems to realise that gender-related rights advocacy can be tricky when engaging with faith-based or public organisations, and instead deploys a more inclusive framing around improving health and livelihoods.Footnote 101 The Pathfinder team identified what it could and could not accomplish, and adapted its framework and philosophy to that context.

This approach has worked to deliver strong health outcomes: over a third of nearby residents (especially women and those currently in sexual relationships) now have ‘good’ knowledge of family planning methods.Footnote 102 A US Agency for International Development (USAID) study found that even after the planned closure of the HoPE-LVB project in 2019, communities ‘have sustained many HoPE-LVB model household practices–for example, tree planting, awareness of modern contraception, improved sanitation, kitchen gardens, fruit cultivation, use of energy-efficient stoves, encouraging girls’ education, and promoting sustainable fishing practices’.Footnote 103

Over time, HoPE-LVB also became a major architect of policy and legal reform. In earlier years, the project took small steps, such as involving county officials in activities and creating district-level steering committees.Footnote 104 In 2015, HoPE-LVB signed an agreement with the Lake Victoria Basin Commission (LVBC), which in turn advocates for change to Ministers. Doreen Othero, Regional Programme Coordinator at the LVBC, believes that without crucial evidence from the HoPE-LVB project, ‘we would not have convinced our ministers’ to make policy changes.Footnote 105

Today, Pathfinder’s (Planetary Health Equity) PHE framework is integrated into virtually every level of Ugandan policy, including the Vision 2030 national development plan.Footnote 106 What began as a regional project tightly focused on sexual and reproductive health has become a federal framework underpinning a far wider range of activities, demonstrating that piecemeal institutionalisation of frameworks like Planetary Health or PHE can be just as viable as seeking adoption all at once.

10.4.2.2 Gold Mining in Ecuador

Precious metals are graded by the proportion of that metal within the surrounding ore. A commercially viable gold mine might possess just 4 grams of gold in every 1,000 kilograms; each speck being literally a ‘one in a million’ find. But nestled in the Puyango river basin of Ecuador, beneath forested towns like Zaruma and Portovelo, lie hidden gold veins yielding as much as 180 grams per ton; a treasure rich enough that many risk life and limb to extract it.Footnote 107 Gold miners in the region have created tunnels and caverns so fragile that sinkholes have swallowed up homes,Footnote 108 often built in secret and with minimal precaution.

Another symptom of local artisanal gold mining is pollution of the Puyango river itself: both from the toxic chemicals used to extract gold from the ore, and from other potentially harmful metals (like mercury and lead) that are naturally found in soils but are being disturbed and swept into the river at a heightened scale.Footnote 109 Locals always knew the river was contaminated, but the exact contaminants and their direct causes and effects were unknown.

EcoHealth-aligned research teams conducted several studies in the region to address this knowledge gap. They uncovered a range of culprits: high cyanide concentrations immediately downstream of mining activities, mercury exposure even further down (potentially inversely correlated with the cyanide concentration), and lead overexposure virtually everywhere.Footnote 110 These harms were indicated by a range of forms of evidence, including neurobehavioural test results from adult and children.

Curiously, lead levels in fish were moderate, suggesting that mining activities may not be the only cause of the issue, and researchers subsequently discovered that 84 per cent of local families were using kitchenware thought to have a high concentration of lead.Footnote 111 By approaching the problem through an ecosystem-based approach (instead of simply offering remedies for sicknesses caused by the contamination), researchers were able to identify where ecosystem exposure alone could not explain a health outcome, and inform both miners and non-miners of other practical actions they could take to reduce their risk. Similar complexities were discovered relating to the interaction between cyanide and mercury methylation in the river.Footnote 112

At this point, a project lead could be forgiven for radically widening the scope of the endeavour: perhaps spearheading kitchenware replacement across the region; seeking additional schooling resources in towns suffering most from contamination; or aiming to create alternative employment for local miners. A wide range of problems seems to enable and even demand a wide range of solutions.

Wisely, however, the EcoHealth team continued to focus on the water contamination issue as their primary concern. The researchers helped inform new municipal bylaws around the dumping of effluents in rivers, convinced mining organisations to adopt new pollution-control strategies, and persuaded canton (province subdivision) committees to develop related environmental and health management plans;Footnote 113 they even created a new municipal authority to handle related issues.Footnote 114 And shortly after Ecuador passed a ban on mercury use in the sector in 2015, mercury levels in the urine of miners in the region finally began to drop.Footnote 115 While illegal and unchecked gold mining continues to pose problems in the Puyango river basin, it is clear that ongoing, focused river contamination assessment projects will be necessary to provide evidentiary support for further reform.

10.5 Conclusion

One Health, EcoHealth, and Planetary Health are ultimately more alike than they are dissimilar. Each framework recognises the importance and interlinkage of human, animal, and ecosystem health, and has committed to interdisciplinary and interframework cooperation to achieve these goals. Borne of this cooperation is a new, shared challenge: how can each framework (or perhaps a coming merger of the three) continue to expand in scope and flexibility without losing the requisite clarity to support institutional reform? What will it mean to integrate One Health more tightly into law, even as it evolves to become an eclectic theory of health for all life, all practitioners, and all levels of governance?

The problem may well be a Gordian knot: an intractable problem best cut through by other means. What will matter to sick miners from Molango to Zaruma, and what will matter to the potato farmers of the Andes or to new mothers on the shores of Lake Victoria, is not what name a governance body goes by, or whether it pays heed to ‘This Health’ or ‘That Health’ as a conceptual framework; rather, what matters will simply be their health, and the health of the world around them. EcoHealth and Planetary Health have demonstrated that simply focusing on successful implementation of projects from the bottom up, and letting legal reform organically follow as it may (though not without effort!), is a viable way to effect institutional change in line with the principles of their framework. In the end, the most vital actors in the journey towards One Health’s implementation into governance structures may not be lawyers or politicians or bureaucrats, but the practitioners on the ground doing the work that matters most.

11 Drawing from AMR Experience for Better Prevention, Preparedness, and Response to Complex Health Threats under a One Health Approach

11.1 Introduction

Antimicrobial resistance (AMR) is the ability of microorganisms to resist the action of antimicrobials – including antibiotics, antivirals, antifungals, and antiparasitics – to which they were initially sensitive. While this phenomenon occurs naturally through genetic changes in pathogens, the overuse and misuse of antimicrobials, combined with their uncontrolled release into the environment, have accelerated the evolutionary process of microbes, making them more adept at developing drug resistance. The World Health Organization (WHO) considers this unnatural development of AMR as one of the top ten global public health and development threats.Footnote 1 The estimated impact of AMR suggests a global toll of 10 million human deaths annually by 2050 and a cumulative cost of US$100 trillion if urgent measures are not taken.Footnote 2 Consequently, AMR is often referred to as ‘the silent pandemic’.

As a global public good, safeguarding antimicrobials and mitigating the threat of AMR are the responsibilities of all countries and people.Footnote 3 Due to its complexity, AMR also requires coordinated efforts across various sectors, including human health, animal and plant health and production, and environmental protection, in line with the One Health approach. Overuses and misuses have been reported – both in the human healthcare sector and in animal and plant production – that require attention.Footnote 4 These include the excessive use of antimicrobials for non-therapeutic purposes, such as for growth promotion, as well as the availability of substandard and counterfeited antimicrobials that facilitate sub-therapeutic doses that are not effective and exacerbate further resistance development.Footnote 5 Unregulated discharges from hospitals, farms, and pharmaceutical companies that include antimicrobial-contaminated waste and other residues have transformed the environment into a reservoir for resistant bacteria and other pathogens.Footnote 6 The need for coordinated and collective multisectoral action has prompted the recognition of AMR as the ‘quintessential’ One Health challenge.Footnote 7

From a governance standpoint, a One Health approach to AMR underscores the need for multisectoral policy and regulatory responses that promote joint interventions. Policies and legal frameworks must create an environment where institutions and stakeholders work collaboratively and are accountable for contributing to common goals. International collaboration is essential for addressing AMR, as it knows no borders. Countries must ensure multisectoral coordination at the national, regional, and global levels, along with consistency between domestic policies and international trade. In this context, identifying regulatory areas and strategies to curb AMR serves as the first step in driving this action. Innovative governance mechanisms should be established to facilitate the transition from coordination to collaboration and, ultimately, to integrated actions.

This chapter’s objective is to derive lessons from the global, regional, and national governance of AMR under a One Health approach that may be successfully applied to other complex health challenges, with a focus on policies, institutional frameworks, and relevant legal aspects. The global governance of AMR will be described, along with governance challenges and regulatory solutions at the national level. The chapter proposes the regulatory framework of the European Union on AMR as a case study to conclude with concrete insights on AMR governance and regulation that can be applicable to other areas demanding a One Health response.

11.2 The Importance of Governance in Addressing AMR

There is broad consensus that appropriate governance structures are instrumental to addressing AMR. By Resolution WHA68.7 the World Health Assembly adopted the Global Action Plan (GAP) for AMR and urged WHO member states to develop National Action Plans (NAPs) in line with the GAP and international standards, while addressing national and local governance arrangements.Footnote 8 The GAP called upon member states to set up effective and enforceable regulation and governance for antimicrobial use.

Institutional fragmentation, scattered responsibilities and poor coordination are broadly recognised as drawbacks for the comprehensive, sustainable, and effective implementation of AMR objectives.Footnote 9 Dame Sally Davis, former Chief Medical Officer of the UK, has been quoted to affirm ‘the biggest problem of AMR is not the science, it is the governance’.Footnote 10 As a multifaceted problem, AMR requires inter/intra-institutional coordination to be addressed. Studies have shown that a fragmented institutional structure makes coherent action in dealing with issues such as AMR more difficult. Socioeconomic analysis has revealed correlations between strong governance and lower levels of AMR.Footnote 11 The sectors involved in AMR governance pursue different objectives and often lack understanding and communication of each others’ objectives and regulation, hindering collaboration and challenging the implementation of joint solutions.Footnote 12 Even in the absence of explicit conflict, the traditional separation between human, animal health, and the environment creates specific challenges for institutional coordination,Footnote 13 as does the fact that each of these areas is governed by different legal frameworks based on different international legal instruments and principles of international law. Finally, the fact that stakeholders are typically aligned with specific ministries and that resources differ greatly among sectors indicates serious barriers to coordinated or integrated governance. At the global level, Rogers Van Katwyk has highlighted that past attempts to tackle AMR have failed because stewardship regimes have been too narrow in national or sectoral scope, and policy responses too fragmented, pointing out the need for more structured and comprehensive AMR governance responses.Footnote 14

Under a One Health approach, AMR governance must encompass all relevant sectors under a framework of equity and transdisciplinarity. A framework of equity would require specific administrative structures and financial mechanisms that do not prioritise one sector over another, ensuring equal roles and responsibilities under a framework of shared accountability.

A systems approach to AMR governance would emphasise network-centric approaches that encourage relationship building among organisations, systems organisation to improve organisational structures and functions, and the flow of knowledge and data across institutions. Systems have been defined as a set of different elements so connected and interrelated as to perform a unique function not performable by the elements alone.Footnote 15 Systems thinking facilitates understanding of complex and wicked problems and is particularly useful in relation to areas such as health and food systems where contexts are often changing,Footnote 16 and interventions may yield unexpected results.Footnote 17 By promoting systems-based transdisciplinarity, members representing different fields work together to develop shared conceptual and methodological frameworks that not only integrate but transcend their respective perspectives.Footnote 18

11.3 Global Governance of AMR
11.3.1 Evolution of AMR Global Governance

To date, global action to address AMR has mostly relied on soft law instruments and political declarations led by different intergovernmental organisations. In 2011, the Food and Agriculture Organization (FAO), the World Health Organization (WHO), and the World Animal Health Organization (WOAH) recognised the significance of AMR as one of the three topics that require multisectoral collaboration to advance the One Health approach, alongside rabies and zoonotic influenza.Footnote 19

Following Resolution WHA68.7,Footnote 20 2015 was a crucial year for AMR, with the adoption of the GAP, the launching of the Global Antimicrobial Resistance and Use Surveillance System (GLASS),Footnote 21 and the establishment of the UK Fleming Fund to fight AMR. In May 2016 the landmark AMR report ‘Tackling Drug-resistant Infections Globally’ by Jim O’Neill was published. Commissioned by the UK government and the Wellcome Trust, this report illustrated the economic and social risks resulting from AMR and offered concrete actions to address the global AMR challenge.Footnote 22

At the 71st Session of the United Nations General Assembly (hereinafter General Assembly) in September 2016, the High-level meeting on AMR adopted a Political Declaration on antimicrobial resistance included in Resolution 73/1. This Resolution emphasised the relevance of the One Health approach, recognising the interconnection between the animal, human, and environmental dimensions in combating AMR. It also called for the engagement of relevant government sectors in developing and implementing multisectoral national action plans, policies, and regulations, tailored to each country’s context and legal system. With this declaration, countries committed to developing multisectoral One Health national action plans for AMR and ensuring their implementation through appropriate regulatory frameworks. The Declaration also called for the establishment of an ‘Ad hoc inter-agency coordination group’ to provide practical guidance for sustained global AMR action. As a follow-up to this Political Declaration, the different intergovernmental organisations working on matters relevant to AMR joined forces within the Interagency Coordination Group on Antimicrobial Resistance (hereinafter Interagency Coordination Group) to identify shared solutions.

In its 2019 report, the Interagency Coordination Group on AMR resulting from this UN General Assembly Resolution proposed the creation of a One Health Global Leadership Group on Antimicrobial Resistance, supported by a Joint Secretariat managed by FAO, WHO, and WOAH (at the time, OIE).Footnote 23 Additionally, the Interagency Coordination Group recommended the establishment of an Independent Panel on Evidence for Action against Antimicrobial Resistance for action against AMR in a One Health context.Footnote 24

In response to the mandates from UN General Assembly and the Interagency Coordination Group, FAO, WHO and WOAH signed a Memorandum of Understanding (MoU) in 2018,Footnote 25 which was later expanded to include UNEP in 2022, creating a quadripartite framework (the Quadripartite).Footnote 26 The MoU provides a legal and formal framework for the four organisations to enhance integrated and coordinated efforts at the human, animal, plant, and ecosystem interface to reinforce national and regional health systems and services. AMR is precisely one of the major areas of cooperation.

Over time, these partner organisations have created governance structures for AMR, including a Joint Secretariat with rotating chairmanship, an Executive Committee composed of the Directors-General, and a Senior Management Group. They have also developed mechanisms to enhance consultation and coordination, including cooperation among technical experts, the organisation of annual executive coordination meetings, and the appointment of liaison officers at the global level. Under the quadripartite framework, the Quadripartite Joint Secretariat on AMR supports global, regional, and national AMR initiatives. This includes the development of a Joint Strategy on AMR, facilitating effective policy and legislative responses to AMR in countries.Footnote 27

Established in November 2020, the Global Leaders Group on AMR (hereinafter Global Leaders Group) is composed of heads of state, regulators, and high-level public and private experts, including the principals of the Quadripartite. It collaborates with public and private stakeholders globally to prioritise AMR on international and national agendas. The Global Leaders Group has published several statements and guidance on topics such as AMR in food systems.Footnote 28 It has also advocated for AMR’s inclusion in the Pandemics Treaty and the organisation of a UN General Assembly High-level meeting in 2024.

The AMR Multi-Stakeholder Partnership Platform (the Platform) serves as a neutral forum for discussion among the various sectors relevant to AMR, fostering coordinated actions and facilitating engagement among governments, academia, civil society, the private sector, and intergovernmental organisations. It also serves as space for developing specific coordinated joint actions through members-driven action groups. The Platform was launched on 15 November 2023.

Furthermore, AMR has been a recurrent topic in G7 and G20 ministers’ declarations. G20 ministers have addressed AMR in their declarations since 2016 (Hangzou Summit) and including the 2017 Hamburg Summit, the G20 Action Plan on AMR approved in Buenos Aires in 2018, and the Bali Summit in 2022, in which ministers committed to embracing a multi-sectoral One Health approach to AMR. In August 2023, G20 Health Ministers recalled their commitment to ‘tackle AMR comprehensively following the One Health approach’ and indicated multi-sectoral governance and coordination as a necessary step. Also, G7 Ministers have consistently addressed AMR in their declarations since 2014 (Brussels summit declaration), and more substantially in the Leader’s declarations of 2015, 2016, 2018 (recalling the One Health approach), 2021, and 2022.

At the time of writing this chapter, countries were preparing for a forthcoming UN General Assembly High-Level meeting on AMR scheduled for September 2024.

In summary, the global governance of AMR has been spearheaded by intergovernmental organisations such as the UN and the Quadripartite. The UN General Assembly played a pivotal role by issuing landmark Resolutions that laid the groundwork for subsequent intergovernmental efforts. The resulting governance framework incorporated various components, including policy-makers represented by the Global Leaders Group, scientific expertise to be facilitated by the forthcoming Independent Panel of Experts, and stakeholders’ participation through the AMR Multistakeholders platform. This structure fosters multidisciplinary and multilevel knowledge exchange, political involvement, and widespread public participation; three fundamental elements consistent with the principles of One Health.

11.3.2 International Law Instruments Applicable to AMR

Besides the legal instruments and policy structures mentioned earlier, the multifaceted nature of issues pertinent to AMR spans across various international instruments. These instruments play a crucial role in shaping the global governance of AMR.Footnote 29

For instance, the International Health Regulations (IHR) provide a framework for cooperation among countries to prevent, protect against, control, and respond to the international spread of diseases, including those related to AMR. Some scholars have suggested that the emergence and spread of AMR bacteria,Footnote 30 especially those for which there is no suitable treatment, may constitute a public health emergency of international concern under the terms of the International Health Regulations. Under these circumstances, countries would be required to notify the WHO under Article 6 of the IHR.Footnote 31 Under this view, applying the IHR to AMR could serve to strengthen global AMR surveillance and response, and to contain AMR. This opinion, however, is debatable to the extent that AMR does not meet the definitional requirements of a Public Health Emergency of International Concern.Footnote 32 Moreover, relying on a possible declaration of a Public Health Emergency of International Concern to address AMR globally would not put sufficient emphasis on the need for ‘deep prevention’ to effectively address the AMR ‘silent pandemic’.Footnote 33

Beyond the IHR, several agreements under the World Trade Organization apply to AMR. The Agreement on Sanitary and Phytosanitary Measures (SPS Agreement) would be applicable for countries approving import restrictions to detect and stop the entrance of animals or animal products potentially contaminated with antimicrobial residues or resistant pathogens. In this respect, several international reference standards have approved detailed and granular guidance on antimicrobial use and AMR.Footnote 34 Quality standards for antimicrobials could also be influenced by the Agreement on Technical Barriers to Trade (TBT Agreement).

Similarly, access and availability of safe and effective antimicrobials are influenced by the intellectual property rights provisions in the Trade-Related Aspects of Intellectual Property Rights Agreement (TRIPS Agreement), which may have an impact on the equitable access to antimicrobials in all countries if the flexibilities granted under TRIPS are not taken into consideration.Footnote 35 Other potentially relevant international agreements include the International Convention on the Harmonized Commodity Description and Coding System concerning customs procedures.Footnote 36

The international trade of antimicrobials could be protected by the UN Convention of Contracts for the International Sale of Goods and, although soft law, the 2016 Principles of International Commercial Contracts of the International Institute for the Unification of Private Law (UNIDROIT). The UN Convention against Transnational Organized Crime could be also applicable to networks that trade in substandard, illegal, or counterfeit medicines, as long as they meet the definition of transnational crime. Finally, the illegal trade of animals, including wildlife, which could constitute an important avenue for the transmission of resistant pathogens across countries, is also influenced by the Convention on International Trade of Endangered Species of Wild Flora and Fauna (CITES).

The global governance of AMR is further shaped by international reference standards and guidance documents. The Quadripartite publication ‘International Instruments on the Use of Antimicrobials across the Human, Animal and Plant Sectors’ identifies key international guidance documents that may support the development of AMR policies and regulation across sectors.Footnote 37 In addition to different guidance documents published by the WHO, these standards include the updated Codex Alimentarius Code of Practice to Minimize and Contain Foodborne AMR,Footnote 38 the Guidelines for Risk Analysis of Foodborne AMR,Footnote 39 and the Guidelines on Integrated Monitoring and Surveillance of Foodborne AMR.Footnote 40 They also include the AMR-specific standards and articles introduced by the WOAH into the Terrestrial and the Aquatic Animal Health Codes,Footnote 41 which are periodically updated. These standards guide countries to apply a One Health approach to AMR governance and regulation and, while they are not legally binding in nature, the fact that both Codex and WOAH are nominated as reference international setting bodies in the SPS Agreement gives them a relevant regulatory role.

These international agreements and standards shape the regulatory framework for AMR at both the international and national levels. Conducting a mapping exercise of international obligations and the division of roles and functions at the national level helps identify the key actors and areas requiring coordination. Similarly, in the context of One Health, multisectoral governance mechanisms must consider existing international obligations across various sectors. This includes sectors such as health, agriculture, environment, trade, and intellectual property. Strengthening collaboration across these sectors is essential for addressing the complex challenges posed by One Health comprehensively.

11.3.3 From Soft Law to a Binding Global Framework for AMR

Global opinion has long debated the best international law instrument to address AMR. Some scholars advocate for flexible soft law instruments or a mix of binding and non-binding models.Footnote 42 These models propose progressively introducing new norms that create political momentum, fostering voluntary compliance and adaptive governance models,Footnote 43 and granting AMR the flexibility that is needed for every area based on science and uncertainty. Other academics signal the limitations of soft law and propose a legally binding instrument that anchors concrete binding obligations and provides for accountability mechanisms.Footnote 44 The Paris Agreement has been proposed as a model to develop a binding AMR instrument given the similarities between climate change and AMR and the challenges to be overcome.Footnote 45 Any successful legal intervention must strive for a balance between access, conservation, and innovation.Footnote 46 Measures must span across the human health, animal, agriculture, and environmental sectors and aim to preserve the efficacy of antimicrobials to achieve intergenerational justice, ensuring wins for present and future generations.Footnote 47 In summary, the adoption of a One Health approach to regulating AMR at a global level is imperative. This approach ensures that AMR regulation aligns with principles of multisectoriality, equity across sectors and disciplines, and stakeholder participation.

The COVID-19 pandemic strongly influenced the discussions on a potential global level response to AMR, connecting this to the more specific topic of pandemic prevention, preparedness, and response (PPPR). The devastating impact of the pandemic placed pandemic prevention high on the international agenda and the possibility of crystalizing AMR as a silent pandemic within an international treaty gained scholarly support.Footnote 48 At the time of writing this chapter, the negotiations for the drafting of a Pandemic Agreement by the Intergovernmental Negotiation Body have been further prolonged after the missed opportunity of reaching consensus at the 77th session of the World Health Assembly. That said, different countries, international and non-governmental organisations have strongly advocated for AMR to be considered as a silent pandemic. A strong recognition of AMR as part of the Agreement would offer an excellent opportunity to consolidate soft law rules that have been broadly accepted by countries. It would recognise the mandate of the Conference of Parties to develop intergovernmental and consensus-based implementation guidance and to negotiate complementary binding (including an additional protocol) or non-binding more granular instruments on AMR.Footnote 49

11.4 AMR Governance and Regulation at the National and Regional Levels
11.4.1 Trends in the Development and Implementation of the GAP and NAPs

Both the Global Action Plan for AMR and the Interagency Coordination Group report recommended that countries establish multisectoral coordination mechanisms for AMR governance and approve multisectoral National Action Plans (NAPs) to consolidate their policy objectives. Over the past years, many countries have advanced in establishing both. In 2023,Footnote 50 among the 175 countries responding to the Quadripartite Global Database for Tracking Antimicrobial Resistance Country Self-Assessment Survey (TraCSS), only eighteen declared not to have a multisectoral governance or coordination mechanism. A total of ninety-two countries reported having a formalised and functional multisectoral coordination mechanism, with thirty-five out of those countries utilizing these structures to implement integrated approaches to NAP implementation. This represents significant progress from the 2017 data, where forty-one countries declared lacking a multisectoral coordination mechanism, and only thirty-one reported having formal and functioning structures.

Regarding NAPs, a comparison between the TrACCS results of 2017 and 2023 under the topic ‘Country Progress with Development of a NAP’ reveals an observable increase in the number of countries incorporating a costed and budgeted operational plan and/or financial provisions for implementation.Footnote 51 Despite TrACSS being a voluntary self-assessment mechanism, the data indicates a positive shift towards more formalised governance structures such as joint work and integrated approaches. This positive movement is gradually followed by effective implementation, as reflected in financial allocations. This positive trend alleviates the pessimism regarding the implementation (or the lack thereof) of NAPs.Footnote 52 In 2018, FAO, WHO, and WOAH affirmed that despite countries declaring firm commitment, many countries had not implemented NAPs or aligned their domestic policies with global recommendations.Footnote 53 Empirical analysis also revealed that, following an initial momentum for NAP development and the establishment of multisectoral structures, collaborations were challenging to sustain due to reliance on voluntary partnerships.Footnote 54

The term ‘isomorfic mimicry’ was introduced to the AMR landscape to explain the differences between the content of the NAPs and their actual implementation.Footnote 55 This phenomenon elucidates why low and middle-income countries tended to develop NAPs following the recommendations of the GAP but were unable to implement them due to financial constraints, as well as institutional and political challenges. In 2022, the WHO published an ‘Implementation Handbook for National Action Plans on Antimicrobial Resistance in the Human Health Sector’ targeting national and subnational stakeholders working on AMR to help them ‘guide and accelerate sustainable implementation’ of NAPs-AMR.Footnote 56 This document includes concrete steps to set up a multisectoral governance mechanism promoting broad multisectoral engagement under the coordination of a higher-level authority.

TrACCS data allows for the conclusion that multisectoral AMR governance mechanisms have broadly been established with dissimilar success and standing challenges. However, informal mechanisms have shown signs of tiredness and weak accountability, compromising their long-term sustainability. Countries are facing challenges to setting up integrated mechanisms, such as integrated surveillance programs in the absence of a concrete framework for accountability and data sharing.

11.4.2 Elements and Principles of AMR National Governance and the Role of Legislation

Numerous authors have debated the best regulatory approach to establish a multisectoral governance mechanism for AMR at the national level. Some argue for flexible governance mechanisms to avoid the pitfalls of over-regulation. Rubin proposed a nuanced approach combining binding and non-binding instruments at multiple levels, emphasizing ‘glocalisation’, where global guidance adapts thoughtfully to local capacities and needs.Footnote 57 This chapter argues that national AMR governance should be based on horizontal and decentralised collaboration reflecting the principle of subsidiarity, by ensuring that global recommendations are adjusted to national regulatory and enforcement capacities and needs.Footnote 58 Birgand et al. suggested an AMR national governance model combining top-down power with ‘network governance’.Footnote 59 In this decentralised approach, the central level shapes policies, and the local level, including beneficiaries and the private sector, defines bottom-up implementation mechanisms, enhancing democratisation and collaboration. Spruijt and Petersen advocated for flexible governance arrangements for scientific areas marked by constant evolution, uncertainty, and adaptiveness.Footnote 60

However, flexible legal solutions must be coupled with clear roles and mandates and a functional accountability framework. In some legal systems, establishing a new interministerial group may require novel legislation that clarifies roles and responsibilities, introduces financial or reporting obligations, and sets up sustainable mechanisms for stakeholders’ participation. Such legislation can facilitate the transition from coordination to collaboration and integration, enabling joint interventions. The challenge is to ensure that legislation fosters an enabling environment, preserving its flexibility while building trust among all members, including the private sector.

Anderson, Schulze, and Cassini proposed a governance framework for AMR based on three core governance pillars:Footnote 61 policy, implementation, and monitoring and evaluation (M&E). Suggested indicators for policy include: multisectoral coordination, accountability, equity, transparency, and sustainability, among others. These indicators represent important foundational principles for the functioning of a multisectoral governance mechanism. Crucial for the implementation of AMR NAPs, accountability demands binding obligations for coordinating authorities and ensuring enforcement. This ties closely to sustainability, as accountability mechanisms influence long-term institutional engagement beyond the political momentum. Equity among countries and populations introduces a human rights dimension, ensuring equitable access to antimicrobials and sanitary care, particularly for vulnerable groups. This aligns with the One Health principle of equity,Footnote 62 emphasizing accessibility and affordability of healthcare for all, and considering gender and socio-economic factors affecting AMR exposure.

In addition to the proposed principles of accountability and equity, an effective AMR governance structure should embody the principles of good governance, solidarity, and subsidiarity.Footnote 63 A well-established principle in public international law, solidarity safeguards human dignity amidst the reality of our shared vulnerabilities to the challenge of antimicrobial effectiveness reduction, an issue demanding integrated management. Subsidiarity directs the management to commence at the local level, acknowledging local communities’ better understanding of their specific AMR challenges.

For effective multisectoriality under the equity principle, all relevant ministries should be involved in AMR management. The Global Leaders Group ‘Pocket Guide for Ministers across Sectors’ identifies as potentially relevant for AMR governance not only the ministries of health, agriculture, and the environment, but also the ministries in charge of finance, industry, education, research, and innovation.Footnote 64 Depending on a country’s constitutional structure, decentralised and local authorities might be directly responsible for certain elements of AMR management and deserve recognition of their roles and mandate. Collaborating with the diversity of actors that are part of the private sector (from the pharmaceutical industry to farmers) is also vital, as they can contribute significantly to NAP development and implementation and to AMR effective regulation, through co-regulation and self-regulation strategies.

A rapid check of national legislation using AMRLex,Footnote 65 a FAO-based repository of AMR relevant policies and legislation in the food and agriculture sectors, reveals that, while most countries have adopted policies, strategies, or national action plans for AMR (155 are included in the WHO NAP Library), only a few have translated these commitments into specific legislation. Most of these instruments establish multisectoral governance mechanisms and define their composition and functions. Typically led by the Ministries of Health, these bodies vary widely in composition, with Ministries of Health, Agriculture, and Environment often included, alongside a diverse array of other entities, as exemplified by the national committees established in Guinea and Algeria.Footnote 66 There are exceptions to this trend where members have a shared responsibility to lead coordination. For instance, in Ecuador’s Comité Nacional de Prevención y Control de la Resistencia Antimicrobiana,Footnote 67 the Presidency alternates among members. The Executive Order issued by the President of the United States of America of 2014 provides another interesting example, by establishing a multisectoral task force and a Presidential Advisory Council.Footnote 68 This global, albeit partial, overview emphasises the diverse strategies nations employ in translating AMR objectives into legislative action and highlights the importance of learning from innovative approaches across different jurisdictions.

11.4.3 The Role of Sector-Specific Legislation

In addition to a multisectoral governance mechanism backed by appropriate legislation, a conducive legal framework for AMR should encompass sector-specific laws that not only incorporate international guidance and best practices but also promote collaboration and coordination across various sectors and foster effective compliance and enforcement.

Sector-specific legislation is instrumental in shaping the availability and access to antimicrobials. It can introduce antimicrobial use requirements for products entering the food supply chain and regulate the disposal and release of antimicrobials into the environment. Jeleff’s empirical research underscores the need for a shift from non-binding to legally binding obligations, particularly in antimicrobial stewardship programs and consumption surveillance in hospitals.Footnote 69 Legally binding individual responsibilities, as suggested by Munkholm and Rubin,Footnote 70 can enhance implementation and enforcement. Hoffman, Bakshi and Van Katwyk argue that effective AMR strategies must extend beyond individual behaviour change and incorporate institutional-level action.Footnote 71

Relevant legal sectors for AMR include, among others, public health, animal health, food safety laws, and laws regulating the environment, waste, and pollution control. These sectors have traditionally been regulated in silos, with one sector usually regulated under specific legislation implemented by one Minister. While it is probably neither possible nor desirable to fully eliminate these silos, sector-specific legislation should incorporate appropriate mechanisms to enable multisectoral coordination across them.

The Quadripartite One Health Legislative Assessment Tool for AMR, launched in November 2023, warns against the risks of horizontal cross-sectoral AMR legal instruments that regulate fragments of different sectors. The Tool proposes a combination of horizontal AMR legislation addressing multisectoral issues, such as multisectoral governance, coupled with legal responses to be addressed in sector-specific laws.Footnote 72

As results from this section, implementation of AMR under a One Health approach demands national mechanisms for coordination, collaboration, or integration of policies and strategies of common interest. While these mechanisms can take various shapes, it is important that they are accompanied by a substantive accountability mechanism that facilitates their long-term sustainability. Legislation can serve to provide legal basis to these mechanisms. This legislation should co-exist with sector-specific legal instruments incorporating international guidance into national law. Sector-specific legislation should preserve its internal consistency avoiding fragmentation. The solution is not to merge laws for AMR but to ensure that all sector-specific laws include the appropriate cross-references to work harmoniously, contributing to common goals.

11.5 Case Study: The EU Regulatory Framework for AMR

In 2022 the European Commission and its member states identified AMR as one of their top three priority health threats.Footnote 73 This recognition underscores the EU’s strong commitment to combating AMR. Since the early years of the twenty-first century, the EU has been at the forefront, championing an active regulatory agenda targeting AMR and acting as a catalyst for global efforts.

While the EU’s regulatory experience in tackling AMR is specific to its constitutional structure and division of powers between the regional and national levels, it provides an interesting model that integrates overarching cross-sectoral instruments with sector-specific legal reforms. Furthermore, it demonstrates a gradual and holistic incorporation of a One Health approach to multisectoral coordination that began with the health and agriculture sectors, and progressively integrated environment. This final stage aligns with the adoption of ambitious EU environmental initiatives exemplified by the European Green Deal.Footnote 74

The EU is supported by several scientific agencies whose competences are particularly relevant to AMR, and more in general, to the implementation of the One Health approach. The European Food Safety Authority (EFSA), the European Medicines Agency (EMA), and the European Centre for Disease Prevention and Control (ECDC) work together in the development of Joint Interagency Antimicrobial Consumption and Resistance Analysis (JIACRA). The European Environment Agency (EEA) also has a preeminent and increasing role.Footnote 75

Against this background, this section presents a non-comprehensive overview of the various regulatory initiatives pursued by the EU to tackle AMR. While this model may not be directly applicable at the national level, its clear sectoral approach to AMR interventions, coupled with targeted cross-sectoral actions and robust financial support, positions the EU as an instructive case study.

11.5.1 Public Health Regulation in the European Union

The EU’s approach to public health has been shaped by its distinctive constitutional framework, regulatory nature, and its historical emphasis on internal market development.Footnote 76 The delineation of competencies between the EU and its member states is meticulously outlined in its foundational treaties. These treaties have evolved over the years from an initial focus on the establishment of an internal market, to increased integration in areas of common interest. The Treaty of Lisbon of 2007 recognised public health as a shared competency between the EU institutions and the member states, unlike policies such as the agricultural policy, where sovereignty is largely transferred to the EU institutions. This acknowledgment underscores the EU’s commitment to a collaborative approach in addressing health challenges, achieving a nuanced balance between central coordination and member state autonomy.

EU member states have traditionally hesitated to transfer sovereignty powers in public health from the state to the EU level.Footnote 77 This reluctance is attributed, in part, to the significance of the health budget and the nature of health systems, which gain legitimacy through a direct political process.Footnote 78 For these reasons, despite the heightened attention to health policies prompted by the COVID-19 pandemic, with both global and EU health policies experiencing expansion, scholars caution that this focus might be ephemeral, drawing parallels with historical trends in the field.Footnote 79

Before 1992, references to public health were primarily associated with the establishment of the internal market and were regulated as exceptions to free trade arrangements, echoing international trade law and the SPS agreement.Footnote 80 The Cassis de Dijon case at the European Court of Justice exemplifies this, confirming that countries can only impose restrictions on the free movement of goods under certain exceptions, including the protection of public health and the defence of consumers.Footnote 81

Following the Maastricht Treaty in 1992, and more prominently with the revisions of the EU foundational treaties in Amsterdam (1997), Nice (2002), and finally in Lisbon (2007), the EU progressively gained the capacity to intervene in public health. Article 168 of the Lisbon Treaty recognises a high level of health protection as a core objective and principle for all EU policies and activities with EU action, complementing national policies and fostering cooperation between member states. The EU acquired the ability to initiate the establishment of common guidance and conduct periodic monitoring and evaluation (Article 168.2). Under this article, the regulatory capacity of the European Parliament and the Council over health matters is limited to the quality and safety of human tissues, veterinary, and phytosanitary fields, and the quality and safety of medicinal products and devices. Additionally, the EU Parliament and the Council may approve incentives to protect and improve human health (Article 168.4), with the Council empowered to adopt recommendations upon the Commission’s proposal (Article 168.5).

This background is essential to understand the evolution of AMR regulation in the EU. To dig into this topic, this section identifies some of the key elements of the EU regulatory framework for antimicrobial resistance, emphasizing its character as a shared policy marked by diverse and dissimilar responses across the EU member states. The intention is not to provide an exhaustive account of the very prolific legislative production and accompanying initiatives of the EU, but to show growth and evolution in the development of a robust AMR regulatory framework under a One Health approach.

11.5.2 EU Cross-Sectoral AMR Regulatory Instruments

The EU institutions have led the way in developing policies and regulatory frameworks to address antimicrobial resistance. The first Community Strategy to combat AMR was approved in 2001,Footnote 82 alongside Council Recommendations regarding the prudent use of antimicrobial agents in human medicine.Footnote 83 Framed by the above-mentioned constitutional division of powers and responsibilities, the regulatory framework for AMR primarily comprises soft law instruments, including Council recommendations and Conclusions, the Commission Action Plan on AMR, and the monitoring reports approved by the Commission and its specialised agencies on AMR, AMR surveillance and other specific AMR aspects of cross-cutting nature. These soft law instruments have influenced the revision and update of various sector-specific AMR-relevant legislation across various domains such as food and veterinary controls, veterinary medicines, feed, waste, wastewater, and soon, the authorisation of pharmaceuticals for human use.

Early documents, such as the Community Action Plan 2001 and the Council Recommendations and Conclusions of 2001, 2002,Footnote 84 and 2008,Footnote 85 focused on both the human and animal sectors, addressing aspects related to the coordinated management of medicines, antimicrobial stewardship, and the development of new medicines.Footnote 86 The slightly later second Commission Action Plan of 2011 and the Council Conclusions of 22 June 2012 introduce references to the One Health approach emphasizing the intersection between the human and the veterinary sectors.Footnote 87 One Health is also expressly mentioned in the European Parliament Resolutions on AMR adopted in May,Footnote 88 and October 2011,Footnote 89 2012,Footnote 90 and 2015.Footnote 91

However, it was in 2017, with the introduction of the last EU One Health Action Plan Against AMR (the 2017 AMR Action Plan) that the role of the environment was highlighted, and thus better encompassing the overarching One Health approach to the AMR issue and challenges.Footnote 92 EU actions under the plan aimed at focusing on the areas with the highest added value for member states such as promoting the prudent use of antimicrobials, enhancing cross-sectorial work, improving infection prevention, consolidating surveillance of AMR and antimicrobial consumption, and reporting.

In the same vein, the 2023 Council Recommendations on stepping EU actions to combat AMR under a One Health approachFootnote 93 encourages member states to implement One Health Action Plans for coordinated AMR response involving all sectors, including the environment, to ensure their full implementation. The recommendations further suggest concrete and measurable targets to reduce antimicrobial use, which consider national situations. Similarly, the European Parliament resolution of 1 June 2023 on EU action to combat AMR adopts a One Health approach and encourages members to foster multisectoral and sustainable AMR coordination and integrated surveillance addressing the environmental sector.Footnote 94

The Commission’s overview report of member states’ One Health National Action Plans against AMR of November 2022 showed that while most member states have enacted NAPs under a One Health approach,Footnote 95 these Action Plans varied considerably in terms of implementation, with measures related to the environment often missing. Furthermore, weaknesses in the areas of financing, monitoring, control, and evaluation were identified that could compromise the long-term sustainability of the NAPs.

11.5.3 Sector-Specific Legislation

In addition to the aforementioned cross-cutting AMR legal soft law instruments, the EU has undergone a comprehensive revision of sector-specific legislation across key legal areas crucial for AMR. This revision encompasses the regulation of antimicrobials, measures to prevent the contamination of food and the environment with antimicrobials, and initiatives related to disease prevention and animal welfare that minimise the need for antimicrobials.

11.5.3.1 Regulation of Antimicrobials

A robust legal framework for medicines and medical devices is in place to protect the access, safety, and quality of these products.Footnote 96 It covers the whole life cycle, from authorisation to recall and surveillance, as well as monitoring, control, and disposal.

11.5.3.2 Human Medicines

In the realm of human medicines, the need for addressing AMR and the demand for new antimicrobials are at the basis of the Commission’s proposed legislative package to revise the EU pharmaceutical legislation.Footnote 97 Comprising proposals for a Regulation,Footnote 98 and a Directive,Footnote 99 this package seeks to reform the current system governing the development, authorisation, and distribution of medicines. Its objectives include improving accessibility, affordability, and availability while addressing the environmental impact of medicine production and the presence of antimicrobials in the environment under a One Health approach. The proposed legislation aims to provide incentives for innovation and research to facilitate the development of new antimicrobials. Furthermore, in alignment with the 2017 AMR Action Plan, the Commission has adopted EU Guidelines for the prudent use of antimicrobials in human health.Footnote 100

11.5.3.3 Veterinary Medicines

AMR considerations have played a pivotal role in the revision of the EU Regulation 2019/6 on veterinary medicinal products.Footnote 101 This regulation encompasses all stages of the veterinary medicine life cycle, including stewardship and use, access, pharmacovigilance, and control. It emphasises that veterinary medicines must be used for therapeutic purposes rather than for prophylaxis. The implementation of this regulation involves various delegated regulations, including those governing data collection on the volume of sales and use of antimicrobial medicinal products in animals.Footnote 102 Additionally, it serves as the foundation for Commission delegated Regulation (2021/1760) that establishes the criteria to reserve certain antimicrobials for the treatment of human infections only.Footnote 103 Finally, in the implementation of this Regulation, the EU introduced a common logo that must appear on websites offering veterinary medicines for sale at a distance.Footnote 104

Regulation 2019/6 consolidates an evolution that was initiated with the prohibition of antibiotic growth promoters in 2003,Footnote 105 the 2015 EU Guidelines on the prudent use of antimicrobials in animal health,Footnote 106 and the revised rules for the packaging and labelling of veterinary medicinal products in 2022.Footnote 107 Additionally, in 2019, and as part of the implementation of the 2017 AMR Action Plan, Regulation 2019/4 introduced revised rules on the manufacture, authorisation, and use of medicated feed, including rules on the prescription and safe disposal of unused or expired products.Footnote 108

11.5.3.4 Food Safety

AMR has also influenced the regulation of food production and controls in Europe. The EU’s 2020 Farm to Fork Strategy incorporates specific AMR objectives, including a reduction by 50 per cent in the sales of antimicrobials for farmed animals and in aquaculture.Footnote 109 Furthermore, Regulation 2017/625 on official controls on food and feed, animal health and welfare, plant health and plant protection products, includes several references to antimicrobial resistance. Finally, the establishment of maximum residue limits for pharmacologically active substances in food of animal origin is regulated through Regulation 470/2009.Footnote 110

11.5.3.5 Integrated Surveillance

Compliance with food and veterinary legislation falls under the oversight of the Food and Veterinary Office (FVO), a division of the Directorate General for Health and Food Safety with a dedicated focus on Commission controls. The FVO conducts targeted audits on antimicrobial resistance and the findings are presented in various reports available in the FVO website.Footnote 111 These reports delve into One Health antimicrobial resistance policies and regulation and evaluate key aspects such as multisectoral coordination mechanisms, NAP, environmental monitoring, antimicrobial use, and laboratory capacity. The audits provide useful insight into the effectiveness of policies and serve as mechanism for the implementation and enforcement of the legislation.

Additionally, in the early twenty-first century, the EU established an integrated framework to facilitate cross-border controls relevant to the identification and control of AMR bacteria. Directive 2003/99/EC on the monitoring of zoonoses and zoonotic agents incorporates antimicrobial resistance monitoring related to zoonoses within its scope.Footnote 112 This Directive mandates member states to ensure the comprehensive collection, analysis, and publication of data concerning the occurrence of antimicrobial resistance-related zoonoses. Similarly, Regulation (EU) 2022/2371 addressing serious cross-border threats to health encompasses the collection of comparable and compatible data and information on AMR within the context of national prevention, preparedness, and response plans.Footnote 113

11.5.3.6 Environmental Protection

The 2017 EU AMR Action Plan recognises the environment as one of the important pillars to address AMR, emphasizing the need for an EU strategic approach to pharmaceuticals in the environment. The plan highlights the need to revise key directives, including the Urban Waste Water Treatment Directive and the Water Framework Directive to understand the occurrence and spread of antimicrobials in the environment.Footnote 114

In 2019, the Commission published a Communication outlining a Strategic Approach to Pharmaceuticals in the Environment.Footnote 115 This document identified six action areas covering all stages of the pharmaceutical life cycle, from production to disposal and waste management. This Communication aligns with the later EU Action Plan ‘Towards a Zero Pollution for Air, Water, and Soil’ adopted by the Commission in 2021 and approved as part of the European Green Deal.Footnote 116 This includes a zero pollution vision for 2050 and key targets to reduce pollution by 2030, including the reduction by 50 per cent in the use of antimicrobials in farm animals and aquaculture.

In 2022 the Commission put forth two directives on water and wastewater.Footnote 117 Both Directives include several references to AMR and introduce new mechanisms to collect AMR data in water and wastewater. Lastly, it is worth noting the Commission proposal on nature restoration,Footnote 118 which expressly mentions One Health and pollution from pharmaceuticals.

11.5.3.7 Prevention

As an integral aspect of AMR prevention and control, the EU has implemented new legislation aimed at enhancing animal health and resilience to disease threats, thereby reducing the reliance on antimicrobials. Regulation (EU) 2016/429 on transmissible animal diseases (‘Animal Health Law’) incorporates several references to antimicrobial resistance.Footnote 119 This regulation sets up the basis to regulate AMR surveillance in veterinary medicine,Footnote 120 facilitating the listing of diseases when the disease agent has developed resistance to treatment posing a danger to human or animal health.Footnote 121 It also includes resistance as part of the capacity development requirements for operators and animal health professionals,Footnote 122 and their awareness-raising responsibilities.Footnote 123

11.5.3.8 Financing

Beyond common harmonisation rules, encompassing common objectives and obligations, the EU regulatory framework for AMR includes several financial mechanisms that contribute to the deployment of various incentives to tackle antimicrobial resistance. Among these instruments, the Common Agriculture Policy plays a significant role by providing financial incentives to enhance animal welfare,Footnote 124 improve biosecurity in farms, and promote organic farming and eco-schemes, thereby reducing the reliance on antimicrobials and implementing control mechanisms to prevent environmental pollution. The EU4Health programme (2021–2027)Footnote 125 includes AMR as one of its key areas of action. Similarly, the Horizon Europe programme for research and innovation provides funding for research and development in AMR.Footnote 126

In conclusion, the EU has played a pioneering role in the regulation of AMR across its 27 members. The structure of the EU regulatory framework effectively combines cross-cutting and sector-specific legal instruments, establishing a holistic and comprehensive coordination framework. Instead of creating overarching AMR legislation leading to legal fragmentation, the EU regulatory spans various sectors, highlighting a One Health approach that recognises the interconnectedness of human, animal, and environmental health. The implementation of this framework is supported by specific monitoring and control mechanisms, involving data collection, sharing, and direct oversight through dedicated audits. Sustainability is further promoted through financial mechanisms encouraging the implementation of good practices, innovation, research, and development. The participatory approach to law-making, involving extensive consultations with stakeholders and bottom-up development, facilitates consensus building and fosters effective behavioural change.

However, the challenge lies in ensuring sustainable implementation at the country level, where EU countries exhibit varying levels of compliance with EU acquis. This diversity in implementation and compliance underscores the need for concerted efforts to enhance uniformity and effectiveness across member states.

11.6 Insights from AMR Governance That Might Be Further Applicable to Other Complex Health Threats under the One Health Approach

This chapter aims to derive insights from the global, regional, and national governance and regulation of AMR, as detailed in the preceding sections. These lessons are intended to provide a broader applicability beyond AMR, to other areas benefiting from a One Health approach.Footnote 127

In this section, One Health is understood as an approach dedicated to providing a collaborative and integrated response to health-related topics that demands a multisectoral and multidisciplinary perspective encompassing human, animal, and environmental factors. As defined by OHHLEP, this approach should embody the principles of equity across sectors, maintaining sociological equilibrium, fostering inclusivity and parity, stewardship in resources management, and embracing transdisciplinarity.Footnote 128

AMR governance provides an excellent example of the implementation of the One Health approach and One Health principles in practice. International governance and regulation of AMR have solidified over the years, gaining broad recognition at the UN General Assembly and through collaborative efforts by the Quadripartite and other Intergovernmental Organisations. The GAP for AMR served as a pivotal milestone, offering countries a structured governance model with concrete sector-specific objectives, necessitating a combination of cross-sectoral and sector-specific efforts. The Interagency Coordination Group contributed to a transparent, comprehensive, and inclusive process, paving the way to a solid international governance framework. This might further consolidate within the Pandemics Agreement.

At the national level, AMR regulation demands a combination of cross-sectoral coordination mechanisms and sector-specific legislation to enable multisectoral coordination and the incorporation of international guidance into sectoral laws. Multisectoral and multidisciplinary mechanisms should facilitate equitable involvement and leadership capacity for all sectors to avoid perpetuating existing power dynamics. All relevant stakeholders should have the opportunity to voice their concerns and see their rights represented with particular attention to Indigenous Peoples, local communities, and vulnerable populations. Equity across sectors and parity among stakeholders, combined with transparency and access to information, facilitate stewardship of natural resources and a renewed attention to all species and living organisms in socioecological equilibrium. An enabling regulatory framework, with a clear delineation of roles and responsibilities, would provide these multisectoral mechanisms with a structure, solidifying shared obligations for data sharing and reporting. Legislation may further facilitate the introduction of a common accountability framework and joint indicators, securing participation rights for all stakeholders and financial resources.

The experience of AMR further underscores the potential role of legislation in facilitating data sharing for integrated surveillance. Integrated data management encompasses obligations for data collection and reporting, interoperability, protection, exchange, and joint analysis among institutions, alongside rules governing the publication and access to data, and the right to information. Caution must be paid when engaging the private sector in data generation to avoid overriding data, reporting obligations, and imposing unnecessary burdens, particularly on smallholders.Footnote 129 In cases where data involve the collection of genetic or biological information, an appropriate mechanism for benefit sharing must be in place, ensuring that communities or countries producing such data have the right to enjoy the benefits generated.

Beyond the coordination mechanism, every specific sector should adhere to the principles of equity, sociopolitical parity, and socioecological equilibrium in their sector-specific interventions. In the context of One Health collaboration, every sector must ensure that sector-specific legislation pays attention to its potential impact on the environment, biodiversity, animal health and welfare, plant health, and human health and wellbeing. Sector-specific policies and legislation should facilitate the stewardship of common public goods. Similar to antimicrobials, stewardship should guarantee the sustainable management of other public goods and natural resources, particularly in situations of shared rights over such resources.

The main research argument of this chapter is that the elements discussed could apply to other complex global health challenges that require a One Health approach. These challenges include the management of complex zoonoses such as rabies and avian influenza, but also broader areas such as sustainable wildlife management, a multisectoral response to pollution control, climate change or agri-food systems transformation.

Introducing a One Health approach will indeed vary across the different topics, depending on their objectives, stakeholders involved, and areas of focus. Nevertheless, drawing from the analysis of AMR, several principles can be extrapolated and applied, with necessary adjustments, to regulate other topics within a One Health framework.

At the international level, effective implementation requires political commitment, scientific expertise, and inclusive stakeholder engagement to integrate a One Health approach comprehensively. This entails fostering collaboration across sectors, disciplines, and nations to address complex health challenges holistically. At the national and regional levels, establishing robust multistakeholder mechanisms is crucial for promoting multisectoral coordination and integration. Such mechanisms should be underpinned by comprehensive and multisectoral frameworks, ensuring clear delineation of roles and responsibilities for each stakeholder. Legislation can support these frameworks by introducing long-term accountability mechanisms.

Additionally, it is imperative for countries to enact separate sector-specific legislation for each relevant area, aligning with international standards and best practices, thereby facilitating the incorporation of global guidelines into national regulatory frameworks and preventing legal fragmentation. Strengthening the regulatory landscape does not entail the consolidation or merging of different legal instruments, but their harmonisation. Laws that have traditionally operated in isolation must incorporate provisions for cross-referencing and cross-fertilisation, thereby facilitating coordinated action across diverse sectors. By integrating complementary laws and regulations, nations can optimise their regulatory frameworks to effectively address complex health challenges under the One Health approach.

In conclusion, AMR is a complex intersectoral challenge requiring a One Health approach. Led by the Quadripartite, the development of an AMR governance framework has rapidly evolved, resulting in consolidated and new structures at the national, regional, and global levels. The lessons learnt in the governance and regulation of AMR serve as insightful references in structuring the path forward for other One Health issues and their governance and regulation in other areas of priority for global/planetary health. By embracing the One Health principles of equity, socioecological equilibrium, transdisciplinarity, sociopolitical parity, and stewardship within national institutional and regulatory frameworks, a balance can be achieved that fosters an equilibrium among the health of humans, animals, plant, and the environment.

Footnotes

7 Human Rights and One Health Mutual Benefits or Irreconcilable Differences?

1 For example, in Lopez Ostra v. Spain (1994), the European Court of Human Rights found that the noise, smell, and fumes from a waste treatment plant close to the applicant’s home was a breach of the right to privacy and home under Article 8 of the European Convention on Human Rights. More recently, in Solyanik v. Russia (2022), contamination of land and water from a cemetery close to the applicant’s house constituted a breach of Article 8. In the Inter-American Commission and Court of Human Rights, environmental degradation like logging and mining has been held to be a breach of Indigenous peoples’ right to property and to use their traditional lands, see e.g. Maya Indigenous Community of Toledo Case (Commission, 2004); Case of the Saramaka People v. Suriname (2007).

2 By comparison, in Kyrtatos v. Greece (2003), the European Court of Human Rights held that there is no right to a good environment as such and found that the impact of urban development on ecosystems was not a breach of human rights.

3 See the discussion in Section 7.4 for more detail on the theoretical bases for human rights.

4 For example, the Constitution of the World Health Organization recognises that ‘the enjoyment of the highest attainable standard of health is one of the fundamental rights of every human being without distinction of race, religion, political belief, economic or social condition.’ Constitution of the World Health Organization 1946 preamble.

5 Universal Declaration of Human Rights, United Nations General Assembly Resolution 217 (III) A, Paris, entered into force on 10 December 1948.

6 International Covenant on Civil and Political Rights 1966, United Nations General Assembly Resolution 2200A (XXI), New York City, 16 December 1966, entered into force on 23 March 1976.

7 International Covenant on Economic, Social and Cultural Rights 1966, United Nations General Assembly Resolution 2200A (XXI), 16 December 1966, entered into force on 3 January 1976.

8 Convention against Torture and Other Cruel, Inhuman or Degrading Treatment or Punishment 1984, United Nations General Assembly Resolution 39/46, 10 December 1984, entered into force on 26 June 1987.

9 Convention on the Rights of the Child 1989, United Nations General Assembly Resolution 44/25, 20 November 1989, entered into force on 2 September 1990.

10 Convention on the Rights of Persons with Disabilities 2006, United Nations General Assembly Resolution A/RES/61/106, 12 December 2006, entered into force on 3 May 2008.

11 First Optional Protocol to the International Covenant on Civil and Political Rights 1966, United Nations General Assembly Resolution 2200A (XXI), 16 December 1966, Articles 1, 2, and 5; Optional Protocol to the Convention on the Rights of the Child on a Communications Procedure 2011, United Nations General Assembly Resolution A/RES/66/138, 19 December 2011, entered into force on14 April 2014, Articles 1, 7(e).

12 European Convention for the Protection of Human Rights and Fundamental Freedoms 1950, Italy, 4 November 1950, entered into force on 3 September 1953; African Charter on Human and Peoples’ Rights 1986, 27 June 1981, entered into force on 21 October 1986 ILM 58 (1982).

13 European Convention for the Protection of Human Rights and Fundamental Freedoms, Article 34; African Charter on Human and People’s Rights 1986, Article 55.

14 One Health High Level Expert Panel, ‘Definition of One Health’.

15 International Covenant on Economic, Social and Cultural Rights 1966, Article 12.

16 Committee on Economic Social and Cultural Rights, ‘General Comment No. 14: The Right to the Highest Attainable Standard of Health’ (2000) 14.

18 Footnote Ibid., 14.

19 Committee on Economic Social and Cultural Rights, ‘General Comment No. 14’, 4, 11, and 15.

20 Convention on the Rights of the Child, Article 24(2)(c).

21 African Charter on Human and Peoples’ Rights, Article 24.

22 Footnote Ibid., Article 16.

23 Social and Economic Rights Action Center and the Center for Economic and Social Rights v. Nigeria [2002] African Commission on Human and Peoples’ Rights No 155/96.

24 Committee on Economic Social and Cultural Rights, ‘General Comment No. 14’, 3.

25 International Covenant on Economic, Social and Cultural Rights, Article 11.

26 Committee on Economic Social and Cultural Rights, ‘General Comment No. 12: The Right to Adequate Food’, Article 11 (1999); ‘General Comment No. 4: The Right to Adequate Housing’, 7; Committee on Economic Social and Cultural Rights, ‘General Comment No. 15: The Right to Water’ (2003).

27 Committee on Economic Social and Cultural Rights, ‘General Comment No. 12’, 14.

28 Committee on Economic Social and Cultural Rights, ‘General Comment No. 15’, 8.

29 Convention on the Elimination of All Forms of Discrimination against Women 1979, United Nations General Assembly, 18 December 1979, entered into force on 3 September 1981, Article 14.2(h).

30 International Covenant on Economic, Social and Cultural Rights, Article 6; European Convention for the Protection of Human Rights and Fundamental Freedoms, Article 2; African Charter on Human and Peoples’ Rights, Article 4; American Convention on Human Rights, Article 4.

31 Human Rights Committee, ‘General Comment No. 36: Article 6 (the Right to Life)’ (30 October 2018).

32 Port Hope Environmental Group v. Canada [1984] Human Rights Committee Communication No. 67/1980; Ioane Teitiota v. New Zealand [2019] Human Rights Committee Communication No 2728/2016.

33 Committee on Economic Social and Cultural Rights, ‘General Comment No. 19: The Right to Social Security (Art. 9 of the Covenant)’.

34 Human Rights Committee, ‘General Comment No. 20: Article 7 (Prohibition of Torture, or Other Cruel, Inhuman or Degrading Treatment or Punishment)’ (1992); Convention against Torture and Other Cruel, Inhuman or Degrading Treatment or Punishment.

35 International Covenant on Economic, Social and Cultural, Articles 2 and 26; International Convention on the Elimination of All Forms of Racial Discrimination 1965, United Nations General Assembly Resolution 2106 (XX), 21 December 1965, entered into force on 4 January 1969; Convention on the Elimination of All Forms of Discrimination against Women.

36 International Covenant on Economic, Social and Cultural, Article 13(1).

37 Juan Pablo Villanueva-Cabezas, Kenneth D. Winkel, Patricia T. Campbell, Anke Wiethoelter, and Caitlin Pfeiffer, ‘One Health Education Should Be Early, Inclusive, and Holistic’ (2022) 6(3) The Lancet Planetary Health e188; Juan Pablo Villanueva-Cabezas, Arjun Rajkhowa, and Angus J. D. Campbell, ‘One Health Needs a Vision beyond Zoonoses’ (2020) 67(6) Transboundary and Emerging Diseases 2271.

38 International Covenant on Civil and Political Rights, Article 19(2).

39 Footnote Ibid., Article 12.

40 Footnote Ibid., Articles 18, 19, and 21.

41 Footnote Ibid., Articles 12(3) and 19(3).

42 De Beer and Others v. Minister of Cooperative Governance [2020] High Court of South Africa (Gauteng Division, Pretoria) 21542/2020.

43 Charles Mwenda v. Inspector General of Police, National Police Service & 2 others [2021] eKLR High Court of Kenya Petition 8 of 2020.

44 Grounded Kiwis Group Inc v. Minister of Health [2022] NZHC 832.

45 BST Holdings, LLC v. Occupational Safety & Health Admin [2021] United States Court of Appeals, Fifth Circuit No. 21-60845.

46 Supreme Court of Justice of Costa Rica (Constitutional Chamber), Case No. 02924 – 2022 [2022] Costa Rica, Supreme Court of Justice Constitutional Chamber, 9 February 2022, No. 02924 – 2022 02924 – 2022.

47 District of Columbia v. Meta Platforms [2022] Superior Court of the District of Columbia (Civil Division) 2021 CA 004450 2.

48 For a full range of caselaw, see Faculty of Law, University of Trento, ‘Covid-19 Litigation: Open-Access Case Law Database’, Covid-19 Litigation. Available at: www.covid19litigation.org/.

49 See for example Alan Boyle, ‘Human Rights and the Environment: Where Next?’ (2012) 23(3) European Journal of International Law 613; Clive Miller, ‘The Greening of Human Rights’ (1998) 30(6) Environment and Planning A: Economy and Space 954; John H. Knox, ‘Greening Human Rights’, openDemocracy (14 July 2015). Available at: www.opendemocracy.net/en/openglobalrights-openpage/greening-human-rights/.

50 Lopez Ostra v. Spain [1994] Eur Court HR 16798/90; Guerra v. Italy [1998] Eur Court HR App No 14967/89; Fadeyeva v. Russia [2005] Eur Court HR App No 55723/00; Tatar v. Romania [2009] Eur Court HR 67021/01; Saramaka People v. Suriname (Preliminary Objections, Merits, Reparations, and Costs) (28 November 2007); Port Hope Environmental Group v. Canada.

51 Mayagna (Sumo) Awas Tingni Community v. Nicaragua (Merits, Reparations and Costs) (Inter-American Court of Human Rights, 31 August 2001); Saramaka People v. Suriname (Preliminary Objections, Merits, Reparations, and Costs); Comunidad Yanomami Caso No 7615 Resolución No 12/85 [ENG]; Case of the Sawhoyamaxa Indigenous Community v. Paraguay (Merits, Reparations and Costs) [2006] Inter-American Court of Human Rights Petition No. 0322/2001.

52 Sacchi et al v. Argentina [2021] Committee on the Rights of the Child Communication No. 104/2019; Ioane Teitiota v. New Zealand; Daniel Billy and others v. Australia (Torres Strait Islanders Petition) [2022] Human Rights Committee Communication No. 3624/2019; Cláudia Duarte Agostinho and others v. Portugal and 32 Other States (European Court of Human Rights, App No. 29371/20); Inter-American Court of Human Rights, Environment and Human Rights: Advisory Opinion OC-23/17 of November 15, 2017 Requested by the Republic of Colombia (official summary issued by the Inter-American Court, 15 November 2017). Available at: www.corteidh.or.cr/docs/opiniones/resumen_seriea_23_eng.pdf.

53 EW et al v. The Netherlands [1993] UN Doc. CCPR/C/47/D/429/1990 (1993) Human Rights Committee Communication No. 429/1990; Balmer-Schafroth and others v. Switzerland [1996] Eur Court HR App No 22110/93; Ioane Teitiota v. New Zealand.

54 Andersen v. Denmark [2010] Human Rights Committee Communication No. 1868/2009; SC and GP v. Italy [2019] Committee on Economic, Social and Cultural Rights Communication No. 22/2017.

55 See for example, Ioane Teitiota v. New Zealand [2019] Human Rights Committee Communication No. 2728/2016; Bridget Lewis, ‘Protecting Environmental Human Rights for Future Generations’ in Walter F. Baber and James May (eds.), Environmental Human Rights in the Anthropocene: Concepts, Contexts, and Challenges (Cambridge University Press, 2023). Available at: www-cambridge-org.demo.remotlog.com/core/books/environmental-human-rights-in-the-anthropocene/A9B9003BCCE93051C516945B06425F2F.

56 Bridget Lewis, Environmental Human Rights and Climate Change: Current Status and Future Prospects (Springer, 2018); Bridget Lewis, ‘Environmental Rights or a Right to the Environment? Exploring the Nexus between Human Rights and Environmental Protection’ (2012) 8 Macquarie Journal of Comparative and International Environmental Law 36.

57 For example, Daniel Billy and Others v. Australia (Torres Strait Islanders Petition); Case of the Sawhoyamaxa Indigenous Community v. Paraguay (Merits, Reparations and Costs); Mayagna (Sumo) Awas Tingni Community v. Nicaragua (Merits, Reparations and Costs); Stacey Lee, ‘Sacchi v. Argentina: Fighting for Indigenous Children’s Climate Rights’, UCLA Law Review (27 March 2020). Available at: www.uclalawreview.org/sacchi-v-argentina-fighting-for-indigenous-childrens-climate-rights/.

58 Ryan Goodman, Henry J. Steiner, and Philip Alston, International Human Rights in Context. 3rd ed. (Oxford University Press, 2007) 187.

59 International Covenant on Civil and Political Rights, Article 2.

60 Manfred Nowak, U.N. Covenant on Civil and Political Rights: CCPR Commentary. 2nd rev. ed. (N.P. Engel, 2005) 3739.

61 Goodman, Steiner and Alston, ‘International Human Rights in Context’, 118.

62 International Covenant on Economic, Social and Cultural Rights, Article 2.

63 Julie Garnier, Sara Savic, Elena Boriani, Brigitte Bagnol, Barbara Häsler, and Richard Kock, ‘Helping to Heal Nature and Ourselves through Human-Rights-Based and Gender-Responsive One Health’ (2020) 2(1) One Health Outlook 22; Julie Garnier et al., ‘Mainstreaming Gender-Responsive One Health: Now Is the Time’ (2022) 10 Frontiers in Public Health 10:845866; Claudia Cataldo, Maria Bellenghi, Roberta Masella, and Luca Busani, ‘One Health Challenges and Actions: Integration of Gender Considerations to Reduce Risks at the Human-Animal-Environmental Interface’ (2023) 16 One Health 100530.

64 M O’Leary et al., A Gender-Transformative Framework for Nutrition: Advancing Nutrition and Gender Equality Together (2020); Esther Onyango and Rowena Maguire, ‘Gendered Exposure, Vulnerability, and Response: Malaria Risk in a Changing Climate in Western Kenya’ (2022) 4 Frontiers in Climate.

65 See John Finnis, Natural Law and Natural Rights (Oxford University Press, 2011); Philip Alston, ‘Making Space for New Human Rights: The Case of the Right to Development’ (1988) 1 Harvard Human Rights Year Book 3.

66 See Joseph Raz, The Morality of Freedom (Oxford University Press, 1988).

67 Joel Feinberg, ‘The Rights of Animals and Future Generations’, Conference paper – presented to the Fourth Annual Conference in Philosophy at the University of Georgia (18 February 1971). Published in William Blackstone (ed.) Philosophy and Environmental Crisis (University of Georgia Press 1974) 43–68; see also Saskia Stucki, ‘Towards a Theory of Legal Animal Rights: Simple and Fundamental Rights’ (2020) 40(3) Oxford Journal of Legal Studies 533; Saskia Stucki, One Rights: Human and Animal Rights in the Anthropocene (Springer International Publishing, 2023).

68 Saskia Stucki, ‘Towards a Theory of Legal Animal Rights’, 533.

69 Serge Morand and Claire Lajaunie, ‘Outbreaks of Vector-Borne and Zoonotic Diseases Are Associated with Changes in Forest Cover and Oil Palm Expansion at Global Scale’ (2021) 8 Frontiers in Veterinary Science 661063.

70 Charlotte Milbank and Bhaskar Vira, ‘Wildmeat Consumption and Zoonotic Spillover: Contextualising Disease Emergence and Policy Responses’ (2022) 6(5) The Lancet Planetary Health e439; Lucy O. Keatts et al., ‘Implications of Zoonoses from Hunting and Use of Wildlife in North American Arctic and Boreal Biomes: Pandemic Potential, Monitoring, and Mitigation’ (2021) 9 Frontiers in Public Health.

71 For analysis of the concept of a right to a healthy environment, see John H. Knox and Ramin Pejan (eds.), The Human Right to a Healthy Environment (Cambridge University Press, 2018); John H. Knox, ‘Constructing the Human Right to a Healthy Environment’ (2020) 16(1) Annual Review of Law and Social Science 79; David Boyd, John Knox, and Marc Limon, The Time Is Now: The Case for Universal Recognition of the Right to a Safe, Clean, Healthy and Sustainable Environment (Universal Rights Group, 2021).

72 United Nations General Assembly, ‘Resolution 76/300: The Human Right to a Clean, Healthy and Sustainable Environment’.

73 UN Press, ‘With 161 Votes in Favour, 8 Abstentions, General Assembly Adopts Landmark Resolution Recognizing Clean, Healthy, Sustainable Environment as Human Right’ (28 July 2022). Available at: https://press.un.org/en/2022/ga12437.doc.htm.

74 United Nations Human Rights Council, ‘Resolution 48/13: The Human Right to a Clean, Healthy and Sustainable Environment’. Available at: https://documents-dds-ny.un.org/doc/UNDOC/GEN/G21/289/50/PDF/G2128950.pdf?OpenElement.

75 James R. May, ‘The Case for Environmental Rights: Recognition, Implementation and Outcomes’ (2021) 42(3) Cardozo Law Review 983.

76 For example, the constitutions of Colombia, Nicaragua, and Slovenia guarantee the right to live in a healthy environment, while the constitutions of Costa Rica, Mozambique, and Portugal protect the right to a healthy and ecologically balanced environment.

77 César Rodríguez-Garavito, ‘A Human Right to a Healthy Environment?: Moral, Legal, and Empirical Considerations’ in John H. Knox and Ramin Pejan (eds.), The Human Right to a Healthy Environment (Cambridge University Press, 2018) 155; Rebecca M. Bratspies, ‘Reasoning Up: Environmental Rights as Customary International Law’ in John H. Knox and Ramin Pejan (eds.), The Human Right to a Healthy Environment (Cambridge University Press, 2018) 122; Sumudu Atapattu, ‘The Right to a Healthy Life or the Right to Die Polluted: The Emergence of a Human Right to a Healthy Environment under International Law’ (2002) 16(1) Tulane Environmental Law Journal 65; John Lee, ‘The Underlying Legal Theory to Support a Well-Defined Human Right to a Healthy Environment as a Principle of Customary International Law’ (2000) 25 Columbia Journal of Environmental Law 283; Lewis, ‘Environmental Rights or a Right to the Environment?’ 40–43; Lewis, Environmental Human Rights and Climate Changes, 86–89 and 139–140.

78 For example, Ecuador. Countries like Bhutan, Lithuania, and Uzbekistan impose obligations on the government to protect flora and fauna, though they do not explicitly recognise the rights of nature.

79 For example, Brazil.

80 For example, Ethiopia, Togo, Chile, Ukraine.

81 There is a campaign for a Convention on Animal Health and Protection, but this has yet to be endorsed by the United Nations. See ‘UN Convention on Animal Health and Protection’. Available at: www.uncahp.org/. See also Chapter 13 of this book.

8 Animal Rights and One Health Locating Animal Intrinsic Worth in the One Health Paradigm

Many thanks to Aleesha Simoncini, Hayden Clift, and Sophie Farnsworth for their excellent research assistance that informed this chapter.

1 Chen Ly, ‘Has Human Activity Put Earth into a New Epoch?’ (2023) 260(3471) New Scientist 15.

2 See, for example, L. Godden and J. Peel, Environmental Law: Scientific, Policy and Regulatory Dimensions (Oxford University Press, 2010) 290; Sverker C. Jagers, Simon Matti, Anne-Sophie Crépin, et al., ‘Societal Causes of, and Responses to, Ocean Acidification’ (2019) 48 Ambio 816830; Shanna McCormack, ‘Climate Change and Animal Agriculture: Federal Actions Protect the Biggest Contributors from the Disasters they Cause’ (2021) 51(3) Environmental Law 745769; European Commission, ‘Causes of Climate Change’. Available at: https://climate.ec.europa.eu/climate-change/causes-climate-change_en.

3 See, for example, Carter Dillard, ‘Environmentalism as a Form of Animal Rights’ (Animal Legal Defense Fund). Available at: https://aldf.org/article/environmentalism-as-a-form-of-animal-rights/; Saskia Stucki, ‘Ethical and Practical Arguments for Animal Rights’ (22 May 2024) Politics and Rights Review. Available at: https://politicsrights.com/ethical-practical-arguments-animal-rights/.

4 Saskia Stucki and Visa Kurki, ‘Animal Rights’ in M. Sellers and S. Kirste (eds.), Encyclopedia of the Philosophy of Law and Social Philosophy (Springer, 2020) 98; Tom Regan, ‘The Case for Animal Rights’ in P. Singer (ed.), In Defense of Animals (Basil Blackwell, 1985) 21; Jane Kotzmann, ‘Sentience and Intrinsic Worth as a Pluralist Foundation for Fundamental Animal Rights’ (2023) 43(2) Oxford Journal of Legal Studies 405.

5 Food and Agriculture Organization of the United Nations, ‘Tackling Climate Change Through Livestock: A Global Assessment of Emissions and Mitigation Opportunities’ (Report, 2013) xii, 1–2; Food System Impacts on Biodiversity Loss, 19; and Energy, Environment and Resources Programme, ‘Food System Impacts on Biodiversity Loss; Three Levers for Food System Transformation in Support of Nature’ (Research paper, 3 February 2021) 2–3, 10. Available at: www.unep.org/resources/publication/food-system-impacts-biodiversity-loss.

6 See, for example, Gary L. Francione, ‘The Abolition of Animal Exploitation’ in Gary L. Francione and Robert Garner (eds.), The Animal Rights Debate: Abolition or Regulation? (Columbia University Press, 2010) 1; Sue Donaldson and Will Kymlicka, Zoopolis: A Political Theory of Animal Rights (Oxford University Press, 2011) 49, 76–77.

7 Donaldson, ‘Zoopolis’, 160; Andrea Schapper and Cebuan Bliss, ‘Transforming our World? Strengthening Animal Rights and Animal Welfare at the United Nations’ (2023) 37(3) International Relations 514, 529.

10 Simon Coghlan, Benjamin John Coghlan, Anthony Capon, and Peter Singer, ‘A Bolder One Health: Expanding the Moral Circle to Optimize Health for All’ (2021) 3(1) One Health Outlook 21.

11 Laurie Sellars, Kimberly Bernotas, and Jeff Sebo, ‘One Health, COVID-19, and a Right to Health for Human and Nonhuman Animals’ (2021) 23(2) Health and Human Rights Journal 35, 36.

12 See ‘One Health’. Available at: www.who.int/health-topics/one-health#tab=tab_1.

13 Regan, ‘The Case for Animal Rights’, 21.

14 See Chapter 11.

15 Eva Bernet Kempers, ‘Do Rights of Nature Include Animal Rights?’ (Helsinki Animal Law Blog, 4 May 2023). Available at: https://blogs.helsinki.fi/animallawblogseries/2023/05/04/do-rights-of-nature-include-animal-rights/.

16 Marcel Verweij and Bernice Bovenkerk, ‘Ethical Promises and Pitfalls of OneHealth’. Available at: https://academic.oup.com/phe/article-abstract/9/1/1/2362819.

17 Jane Johnson and Chris Degeling, ‘Does One Health Require a Novel Ethical Framework?’ (2019) 45(4) Journal of Medical Ethics 239.

18 Felicitas Selter and Sabine Salloch, ‘Whose Health and Which Health? Two Theoretical Flaws in the One Health Paradigm’ (2023) 37(7) Bioethics 674.

19 Chris Degeling, Jane Johnson, Ian Kerridge, et al., ‘Implementing a One Health Approach to Emerging Infectious Disease: Reflections on the Socio-Political, Ethical and Legal Dimensions’ (2015) 15 BMC Public Health 4; One Health High-Level Expert Panel (OHHLEP), Wiku B. Adisasmito, Salama Almuhairi, et al., ‘One Health: A New Definition for a Sustainable and Healthy Future’ (2022) 18(6) PLOS Pathogens e1010537; Kim Gruetzmacher, William B Karesh, John H. Amuasi, et al, ‘The Berlin Principles on One Health – Bridging Global Health and Conservation’ (2021) 764 Science of The Total Environment 142919.

20 See, for example, Vittorio A. Sironi, Silvia Inglese, and Andrea Lavazza, ‘The “One Health” Approach in the Face of Covid-19: How Radical Should It Be?’ (2022) 17(3) Philosophy, Ethics and Humanities in Medicine 3.

21 One Health High-Level Expert Panel (OHHLEP) ‘One Health’, 2–4.

22 Gruetzmacher, ‘The Berlin Principles on One Health’, 3.

23 Vittorio A. Sironi, Silvia Inglese, and Andrea Lavazza, ‘The “One Health” Approach in the Face of Covid-19: How Radical Should It Be?’ (2022) 17(1) Philosophy, Ethics, and Humanities in Medicine 3.

24 Jonathan Beever and Nicolae Morar, ‘The Epistemic and Ethical Onus of “One Health”’ (2019) 33(1) Bioethics 185.

25 Elena R Diller and Laura Williamson, ‘Supporting One Health for Pandemic Prevention: The Need for Ethical Innovation’ (2023) 20(3) Journal of Bioethical Inquiry 345.

26 Simon Coghlan, Benjamin John Coghlan, Anthony Capon, and Peter Singer, ‘A Bolder One Health: Expanding the Moral Circle to Optimize Health for All’ (2021) 3(1) One Health Outlook 21.

27 Nicolas Lainé and Serge Morand, ‘Linking Humans, Their Animals, and the Environment Again: A Decolonized and More-than-Human Approach to “One Health”’ (2020) 27 Parasite 55; Nithin Ramakrishnan, ‘Bio-Surveillance as One Health: A Critique of Recent Definitions and Policy Initiatives’ (2023) 66(3) Development 215; Tamra Lysaght, Benjamin Capps, Michele Bailey, et al., ‘Justice Is the Missing Link in One Health: Results of a Mixed Methods Study in an Urban City State’ (2017) 12(1) PLoS One, 2.

28 Ramakrishnan, ‘Bio-Surveillance as One Health’ 215.

30 For more on the need to protect feeding habitat, see Peggy Eby, Alison J Peel, Andrew Hoegh, et al., ‘Pathogen Spillover Driven by Rapid Changes in Bat Ecology’ (2023) 613(7943) Nature 340.

31 See for example the Australian ‘flying fox case’, Booth v. Bosworth (2001) 114 FCR 39.

32 Aldo Leopold, ‘A Sand County Almanac. 1949’ [1970] New York: Ballantine. Available at: https://jdyeakel.github.io/teaching/ecology/papers/Leopold_Excerpts.pdf.

33 For more on this see Katie Woolaston, Ecological Vulnerability; The Law and Governance of Human-Wildlife Conflict (Cambridge University Press, 2022), chapter 2.

34 Coghlan, ‘A Bolder One Health’.

35 See, for example, Clifford Warwick and Catrina Steedman, ‘Wildlife-Pet Markets in a One-Health Context’ (2021) 7(1) International Journal of One Health 42; Amanda Whitfort, ‘COVID-19 and Wildlife Farming in China: Legislating to Protect Wild Animal Health and Welfare in the Wake of a Global Pandemic’ (2021) 33(1) Journal of Environmental Law 57.

36 Deborah Cao, Katrina Sharman, and Steven White, Animal Law in Australia, 3rd ed. (Lawbook Co, 2023).

37 Nicolas Malebranche, Euvres completes, ed. G. Rodis-Lewis (Paris: J. Vrin, 1958–70), II, 394. The philosophy is named after the seventeenth-century philosopher Rene Descartes; however, the extent to which he held such views is disputed: see Peter Harrison, ‘Descartes on Animals’ (1992) 42 Philosophy Quarterly 219.

38 See Leonora C. Rosenfield, Beast-Machine to Man-Machine: Animal Soul in French Letters from Descartes to La Mettrie (New York: Oxford University Press, 1941), 54.

39 Steve Naragon, ‘Kant on Descartes and the Brutes’ (1990) 81(1) Kant-Studien 123.

40 I. Kant, Louis Infield (Translator), and Lewis White Beck (Foreword), Lectures on Ethics (New York: Harper & Row Publishers, 1963) 239; Lucy Allais and John J. Callanan, ‘Introduction: Kant and Other Animals: An Overview’ in John J Callanan and Lucy Allais (eds.), Kant and Animals (Oxford University Press, 2020) 1011.

41 This section focuses on animal moral rights rather than legal rights, as legal rights are not essential to the adoption of a One Health approach that recognises and respects animals. In this respect, moral rights are ‘an entitlement which confers moral libertiesi on those who have them to do certain things, and the moral constraint on others to abstain from interference’: Raymond Wacks, Animal Lives Matter: The Continuing Quest for Justice (Routledge, 2024) 54.

42 In contrast with animal legal rights, which are often informed by conceptions of animal moral rights.

43 Tom Regan, ‘The Case for Animal Rights’, 22.

44 Christine M. Korsgaard, Fellow Creatures: Our Obligations to the Other Animals (Oxford: Oxford University Press, 2018).

45 Tom Regan, ‘The Case for Animal Rights’ 21.

46 Footnote Ibid., 155.

47 Footnote Ibid., 154–155.

48 Footnote Ibid., 248–250.

49 Korsgaard, ‘Fellow Creatures’, 155.

50 See for example, Tom Regan, ‘The Case for Animal Rights’.

51 See Tom Regan, The Case for Animal Rights (Berkeley: University of California Press, 1983) 240250.

52 W. A. Geering, M. L. Penrith, and D. Nyakahuma, ‘FAO Manual on Procedures for Disease Eradication by Stamping Out.’ (2001) 12 Manual on Procedures for Disease Eradication by Stamping Out, Foreword. Available at: www.fao.org/3/y0660e/y0660e.htm; Maria Vang Johansen and Mary-Lou Penrith, ‘Has Culling Been Properly Assessed as a Valid and Justified Control Intervention Measure for Zoonotic Diseases?’ (2009) 3(10) PLOS Neglected Tropical Diseases e541.

53 See Eva Bernet Kempers, ‘Do Rights of Nature Include Animal Rights?’ (Helsinki Animal Law Blog, 4 May 2023). Available at: https://blogs.helsinki.fi/animallawblogseries/2023/05/04/do-rights-of-nature-include-animal-rights/.

54 Daniel Brockington and James Igoe, ‘Eviction for Conservation: A Global Overview’ (2006) 4(3) Conservation and Society 424.

55 Although we note that animal meat is not vital for a healthy diet in many Western societies where options are unlimited, this is often not the case in many communities in the Global South. See generally Callum Brockett and Katie Woolaston, ‘Environmental Justice in the Post Covid-19 Regulation of Wildlife Trade and Markets’ (2022) 13(2) Journal of Human Rights and the Environment 371398.

56 Jeremy Bentham famously stated, ‘The question is not, “Can they reason?” nor, “Can they talk?” but Can they suffer? Introduction to the Principles of Morals and Legislation’ in B. J. H. Burns and H. L. A. Hart (eds.), The Collected Works of Jeremy Bentham (Oxford University Press, 1789, published in print in 1970), 283.

57 Bentham’s approach is broadly adopted by Peter Singer, who argues for preference utilitarianism, which ‘judges actions, not by their tendency to maximise pleasure or minimise pain, but by the extent to which they accord with the preferences of any being affected by the action or its consequences’: P. Singer, Writings on an Ethical Life (London: Fourth Estate Publishers (Harper Collins), 2001), 133.

58 R. Sandoe and R. Crisp, ‘Ethics’ in M. Appleby and B. Hughes (eds.), Animal Welfare, (CAB International 1997) 10.

59 See FAO, UNEP, WHO, and WOAH. One Health Joint Plan of Action (2022–2026). (Rome 2022) Available at: https://doi.org/10.4060/cc2289en.

60 Degeling, ‘Implementing a One Health Approach to Emerging Infectious Disease’, 5.

61 Alexander Saeri and Emily Grundy, ‘Australian Animal Welfare Survey 2023 Summary Report’ (Research Report, 2023) 2, 13, 15. https://osf.io/download/b694p/.

62 Futureye, ‘Commodity or Sentient Being? Australia’s Shifting Mindset on Farm Animal Welfare’ (Research Report, 2018) 4. www.sheepcentral.com/wp-content/uploads/2019/05/190129-Commodity-or-Sentient-Being-Australias-Shifting-Mindset-on-Farm-Animal-Welfare-v.-7.0.pdf.

63 Protocol annexed to the Treaty of the European Community – Protocol on Protection and Welfare of Animals [1997] OJ C340/110.

64 Animal Welfare Act 2008 (TZ), Sections 3 and 4(b)(i).

65 Ley 20.380, 2009 (CL), Article 2.

66 Wet dieren 2011 (Animals Act) (NL), Article 1.3.

67 Gyvūnų Gerovės Ir Apsaugos Įstatymas (Law on Welfare and protection of Animals) No. XI-2271, Valstybės Žinios, 20 October 2012 No. 122-6216 (LT) (2012), Article 1(a).

68 Civil Code of Catalonia (Ley de 2006), Article 511-1 (3). For further examples, see Jane Kotzmann, ‘Sentience Recognition as a Means for Moving beyond Animal Welfare to Animal Rights’ in Jane Kotzmann and M. B. Rodriguez Ferrere (eds.), The Legal Recognition of Animal Sentience: Principles, Approaches and Applications (Hart Publishing, 2024) 6378, 68–69.

69 UNEP/EA.5/Res.1.

70 Jane Kotzmann and Nicholas Pendergrast, ‘Animal Rights: Time to Start Unpacking What Rights and for Whom’ (2019) 46(1) Mitchell Hamline Law Review 157, 160.

71 Arian D. Wallach, Chelsea Batavia, Marc Bekoff et al., ‘Recognizing Animal Personhood in Compassionate Conservation’ (2020) 34(5) Conservation Biology 1097, 1097.

72 Arian D. Wallach, Marc Bekoff, Chelsea Batavia, Michael Paul Nelson, Daniel Ramp, ‘Summoning Compassion to Address the Challenges of Conservation’ (2018) 32(6) Conservation Biology 1255.

73 Émilie Edelblutte, Roopa Krithivasan, and Matthew Nassif Hayek, ‘Animal Agency in Wildlife Conservation and Management’ (2022) 37(1) Conservation Biology 1, 7.

74 Arian D. Wallach et al., ‘When All Life Counts in Conservation’ (2019) 34(4) Conservation Biology 997, 1004; Edelblutte, ‘Animal Agency in Wildlife Conservation and Management’, 1, 9.

75 Edelblutte, ‘Animal Agency in Wildlife Conservation and Management’, 1, 3.

76 Wallach, ‘When All Life Counts in Conservation’, 1002.

77 Footnote Ibid., 1004.

78 IPBES Workshop Report on Biodiversity and Pandemics, 11.

79 Thom van Dooren and Deborah Bird Rose, ‘Lively Ethography: Storying Animist Worlds’ (2016) 8(1) Environmental Humanities 77, 82; Krithika Srinivasan and Rajesh Kasturirangan, ‘Political Ecology, Development, and Human Exceptionalism’ (2016) 75 Geoforum 125, 126.

80 Danielle Celermajer, David Schlosberg, Lauren Rickards et al, ‘Multispecies Justice: Theories, Challenges, and a Research Agenda for Environmental Politics’ (2021) 30(1-2) Environmental Politics 119, 129.

81 Kerrin O’Dea, ‘Traditional Diet and Food Preferences of Australian Aboriginal Hunter-Gatherers’ (1991) 334(1270) Philosophical Transactions: Biological Sciences 233, 235.

82 Bill Gammage, The Biggest Estate on Earth: How Aborigines Made Australia (Allen & Unwin 2011) 2.

83 Danielle Celermajer, ‘Multispecies justice’.

84 Elizabeth Cripps, ‘Saving the Polar Bear, Saving the World: Can the Capabilities Approach do Justice to Humans, Animals and Ecosystems?’ (2010) 16 Res Publica 1, 6; Christine J Winter, ‘Introduction: What’s the Value of Multispecies Justice?’ (2022) 31(2) Environmental Politics 251, 252.

85 J. Poore and T. Nemecek, ‘Reducing Food’s Environmental Impacts through Producers and Consumers’ (2018) 360(6392) Science 987, 991.

86 See Becca Blease, ‘The Rights of Nature’ (July/August 2024) 345(8) Resurgence & Ecologist 8.

87 Mihnea Tӑnӑsescu, Understanding the Rights of Nature: A Critical Introduction [transcript] (New Ecology, 2022) 15.

88 See Blease, ‘The Rights of Nature’, 9.

89 Tӑnӑsescu, ‘Understanding the Rights of Nature’, 47–71; Javier Tous, ‘Book Review: Understanding the Rights of Nature: A Critical Introduction and The Politics of Rights of Nature: Strategies for Building a More Sustainable Future’ (2022) 11(2) Transnational Environmental Law 441, 442.

90 Corte Constitucional del Ecuador [Constitutional Court of Ecuador], Rights of Nature and Animals as Subject of Rights, ‘Estrellita Monkey’ Case, No. 253-20-JH/22, 27 January 2022; ‘A Landmark Ruling for Animal Rights in Ecuador’, Nonhuman Rights (Blog Post, 23 March 2022). Available at: www.nonhumanrights.org/blog/landmark-ruling-animal-rights-ecuador/; ‘Historic Milestone in Ecuador: Constitutional Court Recognizes Individual Animals as Subjects of Rights Protected by the Rights of Nature’, World Lawyers’ Pledge on Climate Action (8 May 2022). Available at: https://lawyersclimatepledge.org/historic-milestone-in-ecuador-constitutional-court-recognizes-individual-animals-as-subjects-of-rights-protected-by-the-rights-of-nature/.

92 Eva Bernet Kempers, ‘Do Rights of Nature Include Animal Rights?’ (Helsinki Animal Law Blog, 4 May 2023). Available at: https://blogs.helsinki.fi/animallawblogseries/2023/05/04/do-rights-of-nature-include-animal-rights/.

94 Eva Bernet Kempers, ‘Do Rights of Nature Include Animal Rights?’.

95 Corte Constitucional del Ecuador [Constitutional Court of Ecuador], Rights of Nature and Animals as Subject of Rights, ‘Estrellita Monkey’ Case, No. 253-20-JH/22, 27 January 2022, fn 68, 23.

96 See generally Jane Kotzmann, ‘Sentience and Intrinsic Worth as a Pluralist Foundation for Fundamental Animal Rights’ (2023) 43(2) Oxford Journal of Legal Studies 405.

97 Eva Bernet Kempers, ‘Do Rights of Nature Include Animal Rights?’. Understanding individuals as existing within these frameworks and relations is helpful in addressing critiques regarding the excessive individuality of human rights: See David Hollenbach, ‘A Relational Understanding of Human Rights: Human Dignity in Social Solidarity’ (2022) 71(7) Emory Law Journal 1487, 1488–1493.

98 Contemporary international law seeks to protect individual human interests through human rights that are limited in some circumstances, although some rights are considered non-derogable. Animal rights may be protected in a similar way. See generally Teraya Koji, ‘Emerging Hierarchy in International Human Rights and Beyond: From the Perspective of Non-derogable Rights’ (2001) 12(5) European Journal of International Law 917.

99 Note this approach is inspired to some degree by the risk management principles set out in AS/NZS ISO 31000:2018 Risk Management – Principles and Guidelines.

100 James William Yeates states that ‘Animal sentience is therefore an aspect or part of nature: specifically, it is a capacity of components of nature’: ‘Sentience, Harmony and the Value of Nature’ (2023) 13(38) Animals 29. See also Frans de Waal and Stephen A. Sherblom, ‘Bottom-Up Morality: The Basis of Human Morality in Our Primate Nature’ (2018) 47(2) Journal of Moral Education 248.

101 Delia Grace Randolph, Johannes Refisch, Susan MacMillan et al., Preventing the Next Pandemic: Zoonotic Diseases and How to Break the Chain of Transmission (United Nations Environment Programme Report, 6 July 2020) 1517; Joost van Herten, Bernice Bovenkerk, and Marcel Verweij, ‘One Health as a Moral Dilemma: Towards a Socially Responsible Zoonotic Disease Control’ (2019) 66(1) Zoonoses Public Health 26. Available at: https://doi.org/10.1111/zph.12536.

103 Peter D. Burdon, ‘Earth Jurisprudence and the Project of Earth Democracy’ in Peter Burdon and Michelle Maloney (eds.), Wild Law: In Practice (Taylor & Francis, 2014) 1920; Alex Bruce, Animal Law in Australia: An Integrated Approach, 2nd ed. (LexisNexis Butterworths 2018) 77.

104 Jane Kotzmann and Gisela Nip, ‘Bringing Animal Protection Legislation into Line with Its Purported Purposes: A Proposal for Equality amongst Non-Human Animals’ (2020) 37(2) Pace Environmental Law Review 247, 250.

105 Rachel Carey, Christine Parker, and Gyorgy Scrinis, ‘How Free Is Sow Stall Free? Incremental Regulatory Reform and Industry Co-optation of Activism’ (2020) 42(3) Law and Policy 284, 289. Available at: https://doi.org/10.1111/lapo.12154.

106 In relation to Australia this is the case under common law and statute; see for example, Alex Bruce, Animal Law in Australia: An Integrated Approach, 2nd ed. (LexisNexis Butterworths 2018) 77; Competition and Consumer Act 2010 (Cth) Section 4, where ‘goods’ are defined to include animals as well as ships, aircraft, and other vehicles.

107 K. Sharman, ‘Farm Animals and Welfare Law: An Unhappy Union’ in P. Sankoff, S. White, and C. Black (eds.), Animal Law in Australasia, 2nd ed. (Federation Press, 2013) 6183. Available at: https://vaci.voiceless.org.au/countries/australia/; https://vaci.voiceless.org.au/countries/china/; and https://vaci.voiceless.org.au/countries/united-states/. Jay P. Graham, Jessica H Leibler, Lance B Price, et al, ‘The Animal-Human Interface and Infectious Disease in Industrial Food Animal Production: Rethinking Biosecurity and Biocontainment’ (2008) 123 Public Health Reports 282, 283.

108 See Primary Industries Standing Committee, Model Code of Practice for the Welfare of Animals: Domestic Poultry, 4th ed. (CSIRO Publishing 2002) 17 [12.5] 25–6 app 1.

112 Jed Goodfellow, ‘Animal Welfare Regulation in the Australian Agricultural Sector: A Legitimacy Maximising Analysis’ (PhD Thesis, Macquarie University, September 2015) 85. Caveat for ACT prohibitions.

113 For example, Nipah virus, the 1997 Bird flu (‘H5N1’) and 2009 Swine flu (‘H1N1’). For discussion see Jane Kotzmann and Morgan Stonebridge, ‘Considering Zoonotic Disease Risk in Australia: An Analysis of the Adequacy of Intensive Animal Agriculture Regulation’ (2022) 45(3) UNSW Law Journal 1220, 1227–1228.

114 Degeling, ‘Implementing a One Health Approach to Emerging Infectious Disease’, 4. See also, P. Daszak, J Amuasi, CG das Neves, et al., IPBES Workshop on Biodiversity and Pandemics (Report, 2020) 29. Available at: https://doi.org/10.5281/zenodo.4147317.

115 Animal and Plant Health Inspection Service – US Department of Agriculture, ‘APHIS’ American Rescue Plan (ARP) Surveillance Program: Strategic Framework’ (2022). Available at: www.aphis.usda.gov/publications/aphis_general/arp-strategic-framework.pdf. Also see https://perma.cc/5NPX-RMJ4 at 1.

116 I. Johnson, A. Hansen, and P. Bi, ‘The Challenges of Implementing an Integrated One Health Surveillance System in Australia’ (2018) 65(1) Zoonoses and Public Health 229, 230. Available at: https://doi.org/10.1111/zph.12433.

117 Department of Health and Aged Care, ‘Communicable Diseases Network Australia (CDNA)’, Australian Government (12 July 2022). Available at: www1.health.gov.au/internet/main/publishing.nsf/Content/cda-cdna-index.htm; ‘OzFoodNet: Enhancing Surveillance for Foodborne Disease in Australia’, Australian Government Department of Health (30 September 2020). Available at: www1.health.gov.au/internet/main/publishing.nsf/Content/cdna-ozfoodnet.htm.

118 7 U.S.C § 8319; 2157 U.S.C. § 8310(a); Our Partners, National Center for Emerging and Zoonotic Infections Diseases (NCEZID), Centers for Disease Control and Prevention (CDC). Available at: https://perma.cc/P4GZ-EED4; National Center for Emerging and Zoonotic Infectious Diseases (NCEZID), Centers for Disease Control and Prevention (CDC), www.cdc.gov/ncezid/index.html [https://perma.cc/7BY6-82CA].

119 For discussion, see Jane Kotzmann and Morgan Stonebridge, ‘Preventing Another Pandemic: How Changing the Legal Paradigm Governing Intensive Animal Agriculture Will Reduce the Risk of Future Zoonoses’ (2022) 47(2) Columbia Journal of Environmental Law 457, 491–492.

120 Hongying Li, Yufei Chen, Catherine C Machalaba, et al., ‘Wild Animal and Zoonotic Disease Risk management and Regulation in China: Examining Gaps and One Health Opportunities in Scope, Mandates, and Monitoring Systems’ (2021) 13 One Health 4.

121 Law of The People’s Republic of China on Prevention and Treatment of Infectious Diseases (2013 Amendment). Available at: bit.ly/4jSciHx.

122 Jane Kotzmann and Morgan Stonebridge, ‘Considering Zoonotic Disease Risk in Australia: An Analysis of the Adequacy of Intensive Animal Agriculture Regulation’ (2022) 45(3) UNSW Law Journal 1220, 1235. See also World Organisation for Animal Health, Office of Innovation and Entrepreneurship. Terrestrial animal health code glossary 2018. [cited 1 November 2021]. Available at: www.oie.int/fileadmin/Home/eng/Health_standards/tahc/2018/en_glossaire.htm.

123 Bryony A. Jones, Delia Grace, Richard Kock, et al., ‘Zoonosis Emergence Linked to Agricultural Intensification and Environmental Change’ (2013) 110(21) Proceedings of the National Academy of Sciences 8399, 8401. Available at: https://doi.org/10.1073/pnas.1208059110.

124 J. W. Aleri and M. Laurence, ‘A Description of Biosecurity Practices among Selected Dairy Framers across Australia’ (2020) 60(14) Animal Production Science 1711. Available at: https://doi.org/10.1071/AN19340.

125 National Biodefense Strategy and Implementation Plan for Countering Biological Threats, Enhancing Pandemic Preparedness, and Achieving Global Health Security (October 2022). Available at: www.whitehouse.gov/wp-content/uploads/2022/10/National-Biodefense-Strategy-and-Implementation-Plan-Final.pdf.

126 Zinjie Wei, Wanlong Lin, and David A. Hennessy, ‘Biosecurity and Disease Management in China’s Animal Agriculture Sector’ (2015) 54 Food Policy 52.

127 Marco Liverani, Jeff Waage, Tony Barnett, et al., ‘Understanding and Managing Zoonotic Risk in the New Livestock Industries’ (2013) 121(8) Environmental Health Perspectives 873, 874. Available at: https://doi.org/10.1289/ehp.1206001; J. Otte, D. Roland-Holst, D. Pfeiffer, et al., Industrial Livestock Production and Global Health Risks (Research Report, June 2007) 6–10. For discussion see Jane Kotzmann and Morgan Stonebridge, ‘Considering Zoonotic Disease Risk in Australia: An Analysis of the Adequacy of Intensive Animal Agriculture Regulation’ (2022) 45(3) UNSW Law Journal 1220, 1235–1237.

128 J. Van Herten and B. Bovenkerk, ‘The Precautionary Principle in Zoonotic Disease Control’ (2021) 14(2) Public Health Ethics 180, 181; Chris Degeling, Zohar Lederman, and Melanic Rock, ‘Culling and the Common Good: Re-evaluating Harms and Benefits Under the One Health Paradigm’ (2016) 9(3) Public Health Ethics 244, 244.

129 Royal Society of Prevention of Cruelty to Animals, ‘What Is Mass Euthanasia?’, RSPCA Knowledge Base (31 May 2022). Available at: https://kb.rspca.org.au/knowledge-base/what-is-mass-euthanasia/.

130 Animal Health Australia, ‘Australian Veterinary Emergency Plan Operational Manual: Disposal’ (Manual, Version 5.0, 2021) 95.

131 Animal Health Australia, ‘Australian Veterinary Emergency Plan Operational Manual: Destruction of Animals’ (Manual, Version 3.2, 2015) 9 (‘Destruction of Animals’).

133 See US Department of Agriculture, Emergency Response Procedures – Depopulation and Disposal (2015). Available at: www.aphis.usda.gov/animal_health/downloads/animal_diseases/ai/ERDepopDisposal.pdf.

134 232AM. Veterinary Medical Association, ‘AVMA Guidelines for the Euthanasia of Animals’ (2020) ed. 111. Available at: www.avma.org/resources-tools/avma-policies/avma-guidelines-euthanasia-animals.

135 See e.g. IOWA CODE §163.2 (2021).

136 Xinjie Wei, Wanlong Lin, and David A. Hennessy, ‘Biosecurity and Disease Management in China’s Animal Agriculture Sector’ (2015) 54 Food Policy 52, 59.

137 Delia Grace Randolph et al., ‘Preventing the Next Pandemic: Zoonotic Diseases and How to Break the Chain of Transmission’ (United Nations Environment Programme Report, 6 July 2020) 15.

139 For detailed discussion see Lindsay Walton and Kristen King Jaiven, ‘Regulating CAFOs for the Well-Being of Farm Animals, Consumers, and the Environment’ (2020) 50(6) Environmental Law Reporter 10485.

140 Chris Degeling, Zohar Lederman, and Melanie Rock, ‘Culling and the Common Good: Re-evaluating Harms and Benefits Under the One Health Paradigm’ (2016) 9(3) Public Health Ethics 244, 245.

141 Footnote Ibid., 244, 245.

142 Zohar Lederman, Manuel Magalhaes-Sant’Ana, and Teck Chuan Voo, ‘Stamping Out Animal Culling: From Anthropocentrism to One Health Ethics’ (2021) 34 Journal of Agricultural and Environmental Ethics 3.

143 Lederman, ‘Stamping Out Animal Culling’, 10.

144 Footnote Ibid., 6.

145 Degeling, ‘Culling and the Common Good’, 244–251.

9 The One Health Approach and the Tackling of Drivers of Environmental Degradation The Case of the EU Deforestation-Free Products Regulation

1 European Commission, ‘Stepping up EU Action to Protect and Restore the World’s Forests’ COM (2019) 352 final, 23 July 2019.

3 See, e.g.: J. A. Foley, G. P. Asner, M. H. Costa, et al., ‘Amazonia Revealed: Forest Degradation and Loss of Ecosystem Goods and Services in the Amazon Basin’ (2007) 5 Frontiers in Ecology and the Environment 125; S. Morand and C. Lajaunie, ‘Outbreaks of Vector-Borne and Zoonotic Diseases are Associated with Changes in Forest Cover and Oil Palm Expansion at Global Scale’ (2021) 8 Frontiers in Veterinary Science 230; E. Karjalainen, T. Sarjala, and H. Raitio, ‘Promoting Human Health through Forests: Overview and Major Challenges’ (2010) 15(1) Environmental Health Preventive Medicine 18.

4 European Commission, ‘Factsheet – Protecting and Restoring the World’s Forests: Stepping up EU Action to Halt Deforestation and Forest Degradation’, Available at: https://commission.europa.eu/publications/eu-communication-2019-stepping-eu-action-protect-and-restore-worlds-forests_en.

5 Regulation (EU) 2023/1115 of the European Parliament and of the Council of 31 May 2023 on the Making Available on the Union Market and the Export from the Union of Certain Commodities and Products Associated with Deforestation and Forest Degradation and Repealing Regulation (EU) No. 995/2010 (2023) OJ L 150/206. Recital 2.

6 FAO – Food and Agriculture Organisation and UNEP – United Nations Environment Programme, ‘The State of the World’s Forests 2020. Forests, Biodiversity and People’ (Rome: FAO and UNEP, 2020). Available at: www.fao.org/documents/card/en/c/ca8642en; K. Bougas, V. Cherrier, L. Constantine, et al., ‘Service Contract on EU Policy on Forest Products and Deforestation. Task 3 – Impact Assessment on Demand-side Measures to Address Deforestation – Final report’ (Report for DG Environment – European Commission, Brussels, Belgium, Wood, Trinomics, Ricardo, WUR, Tyrsky, 2021). Available at: https://circabc.europa.eu/ui/group/34861680-e799-4d7c-bbad-da83c45da458/library/5d098237-8bab-48a6-a6c8-2a907d80c791/details?download=true.

7 European Commission, ‘Factsheet – Protecting and Restoring the World’s Forests: Stepping up EU Action to Halt Deforestation and Forest Degradation’; FAO – Food and Agriculture Organisation and UNEP – United Nations Environment Programme, The State of the World’s Forests 2020. Forests, Biodiversity and People.

8 European Parliament, ‘Report with Recommendations to the Commission on an EU Legal Framework to Halt and Reverse EU-driven Global Deforestation’ (2020/2006(INL)) (2020). Available at: www.europarl.europa.eu/doceo/document/A-9-2020-0179_EN.html; Bougas, ‘Service Contract on EU Policy on Forest Products and Deforestation’.

9 E.g: Peter Daszak, C. das Neves, J. Amuasi, et al., ‘Workshop Report on Biodiversity and Pandemics of the Intergovernmental Platform on Biodiversity and Ecosystem Services’ (Intergovernmental Platform on Biodiversity and Ecosystem Services – IPBES, 2020). Available at: www.ipbes.net/events/ipbes-workshop-biodiversity-and-pandemics; C. J. P. Colfer, D. Sheil, and M. Kishi, Forests and Human Health: Assessing the Evidence (Center for International Forestry Research, 2006); Karjalainen ‘Promoting Human Health through Forests’.

10 In the EU, this is done through the so-called Nature Directives: Council Directive 92/43/EEC of 21 May 1992 on the Conservation of Natural Habitats and of Wild Fauna and Flora (1992) OJ L206/7; Directive 2009/147/EC of the European Parliament and of the Council of 30 November 2009 on the Conservation of Wild Birds (2009) OJ L20/7.

11 In the EU, a Nature Restoration Law has just been adopted. The agreed text: Council of the European Union, ‘Interinstitutional Agreement or Provisional Deal on the Proposal for Regulation of the European Parliament and of the Council on Nature Restoration’ Interinstitutional File: 2022/0195(COD) (2023). Available at: https://data.consilium.europa.eu/doc/document/ST-15907-2023-INIT/en/pdf. Retrievable at: www.consilium.europa.eu/en/press/press-releases/2023/11/09/nature-restoration-council-and-parliament-reach-agreement-on-new-rules-to-restore-and-preserve-degraded-habitats-in-the-eu/.

12 In the EU, this is pursued (with varying results) with different instruments: among others, the agricultural policy, legislative measures on land use and land use change and forestry, and renewables.

13 Payman Ahi and Cory Searcy, ‘A Comparative Literature Analysis of Definitions for Green and Sustainable Supply Chain Management’ (2013) 52 Journal of Cleaner Production 329.

14 Karl Montevirgen, ‘Supply Chain Management: From Raw Materials to Retail’ (Encyclopedia Britannica | Britannica, n.d.). Available at: www.britannica.com/money/what-is-supply-chain-management.

15 Regulation 2023/1115 of 31 May 2023, Deforestation-free Products Regulation.

16 Footnote Ibid., Article 1.

17 Dieter Cuypers, T. Geerken, L. Gorissen, et al., ‘The Impact of EU Consumption on Deforestation: Comprehensive Analysis of the Impact of EU Consumption on Deforestation’ (Study funded by the European Commission, DG ENV Contract N° 070307/2010/577031/ETU/E2 and carried out by VITO, the IIASA, CICERO, 2013). Available at: https://pure.iiasa.ac.at/14868/1/1.%20Report%20analysis%20of%20impact.pdf.

18 Regulation 2023/1115 of 31 May 2023, Deforestation-free Products Regulation, Article 1.

19 European Commission, ‘Factsheet – Protecting and Restoring the World’s Forests: Stepping up EU Action to Halt Deforestation and Forest Degradation’. See also data from: P. R. Shukla, J. Skea, E. Calvo Buendia, et al., ‘Climate Change and Land: An IPCC Special Report on Climate Change, Desertification, Land Degradation, Sustainable Land Management, Food Security, and Greenhouse Gas Fluxes in Terrestrial Ecosystems ‘(IPCC, 2019). Available at: www.ipcc.ch/site/assets/uploads/sites/4/2020/08/200730-IPCCJ7230-SRCCL-Complete-BOOK-HRES.pdf.

20 Bougas, ‘Service Contract on EU Policy on Forest Products and Deforestation’.

22 See, e.g.: S. Roe, C. Streck, M. Obersteiner, et al., ‘Contribution of the Land Sector to a 1.5 C World’ (2019) 9 Nature Climate Change 817; B. W. Griscom, J. Adams, P. W. Ellis, et al., ‘Natural Climate Solutions’ (2017) 114(11645) Proceedings of the National Academy of Sciences 44. As considered in Bougas, ‘Service Contract on EU Policy on Forest Products and Deforestation’.

23 Paris Agreement. Adopted on 12 December 2015; entered into force on 4 November 2016. Paris, Conference of the Parties, Twenty-first session (United Nations Framework Convention on Climate Change, 2015).

24 Bougas, ‘Service Contract on EU Policy on Forest Products and Deforestation’.

25 K. Norris, ‘Ecology: The Tropical Deforestation Debt’ (2016) 26 Current Biology 16. R770. I. M. Rosa, M. J. Smith, O. R. Wearn, D. Purves, and R. M. Ewers, ‘The Environmental Legacy of Modern Tropical Deforestation’ (2016) 26(16) Current Biology 2161; Bougas, ‘Service Contract on EU Policy on Forest Products and Deforestation’.

26 A. M. Mapulanga and H. Naito, ‘Effect of Deforestation on Access to Clean Drinking Water’ (2019) 116(17) Proceedings of the National Academy of Sciences 8249. As considered in Bougas, ‘Service Contract on EU Policy on Forest Products and Deforestation’.

27 See: W. Huang, M. Zong, Z. Fan, et al., ‘Determining the Impacts of Deforestation and Corn Cultivation on Soil Quality in Tropical Acidic Red Soils Using a Soil Quality Index’ (2021) 125 Ecological Indicators 107580; E. Amoakwah, M. A. Rahman, K A. Nketia, R. Djouaka, N. O. Didenko, and K. R. Islam, ‘Impact of Deforestation and Subsequent Land-use Change on Soil Quality’ (2021) 10(2) Eurasian Journal of Soil Science 150.

28 See: C. Reddington, E. W. Butt, D. A. Ridley, et al., ‘Air Quality and Human Health Improvements from Reductions in Deforestation-related Fire in Brazil’ (2015) 8(10) Nature Geoscience 768; E. W. Butt, L. Conibear, C. Knote, and D. V. Spracklen, ‘Large Air Quality and Public Health Impacts due to Amazonian Deforestation Fires in 2019’ (2021) 5(7) GeoHealth e2021GH000429.

29 This will not happen in all cases, but in many cases: B. Slenning, ‘Global Climate Change and Implications for Disease Emergence’ (2010) 47(1) Veterinary Pathology 28. See, also: A. El-Sayed and M. Kamel, ‘Climatic Changes and Their Role in Emergence and Re-emergence of Diseases’ (2020) 27 Environmental Science and Pollution Research 22336; D. S. Schmeller, F. Courchamp, and G. Killeen, ‘Biodiversity Loss, Emerging Pathogens and Human Health Risks’ (2020) 29 Biodiversity and Conservation 3095; J. N. Mills, ‘Biodiversity Loss and Emerging Infectious Disease: An Example from the Rodent-Borne Hemorrhagic Fevers’ (2006) 7(1) Biodiversity 9.

30 See, e.g.: I.-C. Chen, J. K. Hill, R. Ohlemüller, D. B. Roy, and C. D. Thomas, ‘Rapid Range Shifts of Species Associated with High Levels of Climate Warming’ (2011) 333 Science 6045.

31 Daszak, ‘Workshop Report on Biodiversity and Pandemics of the Intergovernmental Platform on Biodiversity and Ecosystem Services’.

32 C. J. Carlson, G. F. Albery, C. Merow, et al., ‘Climate Change Increases Cross-Species Viral Transmission Risk’ (2022) 607(7919) Nature 555. For an overview on research progress and gaps and for a predictive framework, see: S. Altizer, R. S. Ostfeld, P. T. Johnson, S. Kutz, and C. D. Harvell, ‘Climate Change and Infectious Diseases: from Evidence to a Predictive Framework’ (2013) 341(6145) Science 514.

33 A. Kazmierczak, R. Lowe, K. R. van Daalen, K. Johnson, S. Dasgupta, and E. Robinson, ‘Climate Change as a Threat to Health and Well-being in Europe: Focus on Heat and Infectious Diseases’ (EEA Report No 07/2022, European Environment Agency, 2022).

34 For a broad overview transcending forest biodiversity, see: S. Prakash, C. Estreguil, A. Neuville, E. Chinchio, and M. Baccaro, ‘Biodiversity and Health – A Knowledge Synthesis and Analysis of the Complex Connections between Biodiversity and Health Highlighting the Relevant EU Policies Projects and Initiatives.’ (2023). Available at: https://publications.jrc.ec.europa.eu/repository/handle/JRC134740.

35 See e.g.: Jessica Scott, ‘Proposed Integrated Control of Zoonotic Plasmodium Knowlesi in Southeast Asia using Themes of One Health’ (2020) 5(4) Tropical Medicine and Infectious Disease 175.

36 For example, through the regulation of populations of susceptible hosts or interference with parasite transmission.

37 See, e.g.: David J. Civitello, J. Cohen, H. Fatima, et al., ‘Biodiversity Inhibits Parasites: Broad Evidence for the Dilution Effect’ (2015) 112(28) Proceedings of the National Academy of Sciences 8667; Serge Morand, S. Jittapalapong, Y. Suputtamongkol, M. T. Abdullah, and T. B. Huan, ‘Infectious Diseases and Their Outbreaks in Asia-Pacific: Biodiversity and Its Regulation Loss Matter’ (2014) 9(2) PloS one e90032; P. T. J. Johnson and D. W. Thieltges, ‘Diversity, Decoys and the Dilution Effect: How Ecological Communities Affect Disease Risk’ (2010) 213(6) Journal of Experimental Biology 961.It should be noted that, in matters of dilution effect, studies have also reported a highly heterogeneous relationship between host biodiversity and disease, leading to heterogeneous effects. See: Daniel J. Salkeld, Kerry A. Padgett, and James Holland Jones, ‘A Meta‐Analysis Suggesting that the Relationship between Biodiversity and Risk of Zoonotic Pathogen Transmission is Idiosyncratic’ (2013) 16(5) Ecology Letters 679.

38 See, e.g.: G. M. Cragg and D. J. Newman, ‘Biodiversity: A Continuing Source of Novel Drug Leads’ (2005) 77(1) Pure and Applied Chemistry 7.

39 See, e.g.: Y. Linhares, A. Kaganski, C. Agyare, et al., ‘Biodiversity: The Overlooked Source of Human Health’ (2023) 29(3) Trends in Molecular Medicine 173.

40 See, among others: J. H. Ellwanger, B. Kulmann-Leal, V. L. Kaminski, et al., ‘Beyond Diversity Loss and Climate Change: Impacts of Amazon Deforestation on Infectious Diseases and Public Health’ (2020) 92(1) Anais da Academia Brasileira de Ciências.

41 A. P. Dobson, S. L. Pimm, L. Hannah, et al., ‘Ecology and Economics for Pandemic Prevention’ (2020) 369(6502) Science 379; J. H. Ellwanger and J. A. B. Chies, ‘Zoonotic Spillover: Understanding Basic Aspects for Better Prevention’ (2021) 44(1) Genetics and Molecular Biology 1; M. C. Rulli, M. Santini, D. T. S. Hayman, and P. D’Odorico, ‘The Nexus between Forest Fragmentation in Africa and Ebola Virus Disease Outbreaks’ (2017) 7(1) Scientific Reports 41613.

42 Dobson, ‘Ecology and Economics for Pandemic Prevention’.

43 N. D. Wolfe, M. N. Eitel, J. Gockowski, et al., ‘Deforestation, Hunting and the Ecology of Microbial Emergence’ (2000) 1 Global Change and Human Health 10.

44 E.g.: J. H. Epstein and J. T. Price, ‘The Significant but Understudied Impact of Pathogen Transmission from Humans to Animals’ (2009) 76(5) Mount Sinai Journal of Medicine: A Journal of Translational and Personalized Medicine 448; C. C. Tan, S. D. Lam, D. Richard, et al., ‘Transmission of SARS-CoV-2 from Humans to Animals and Potential Host Adaptation’ (2022) 13(1) Nature Communications 2988; L. Fernández-Bastit, J. Vergara-Alert, and J. Segalés, ‘Transmission of Severe Acute Respiratory Syndrome Coronavirus 2 from Humans to Animals: Is There a Risk of Novel Reservoirs?’ (2023) 63 Current Opinion in Virology 101365; M. Marrana, ‘Chapter 3 – Epidemiology of Disease through the Interactions between Humans, Domestic Animals, and Wildlife’ in Joana C. Prata, Ana Isabel Ribeiro and Teresa Rocha-Santos (eds.), One Health (Academic Press 2022).

45 For more information on the links between forests and health, see: C. Beatty, M. Stevenson, P. Pacheco, A. Terrana, M. Folse, and A. Cody, ‘The Vitality of Forests: Illustrating the Evidence Connecting Forests and Human Health’ (World Wildlife Fund – WWF, 2022). Available at: www.worldwildlife.org/publications/the-vitality-of-forests-illustrating-the-evidence-connecting-forests-and-human-health. On forests and heat, see: J. Palmer, ‘No Escape from the Heat: The Cost of Deforestation on Human and Animal Health’ (2022) 72(11) BioScience 1037. For a broad overview on forest and health, see, also: C. J. P. Colfer, D. Sheil, and M. Kishi, Forests and Human Health: Assessing the Evidence (Center for International Forestry Research, 2006). Also see Karjalainen ‘Promoting Human Health through Forests’.

46 Bougas, ‘Service Contract on EU Policy on Forest Products and Deforestation’.

47 On this, see also: Ronald M. Atlas, ‘One Health: Its Origins and Future’ in J. Mackenzie, M. Jeggo, P. Daszak, and J. Richt (eds.), One Health: The Human-Animal-Environment Interfaces in Emerging Infectious Diseases Current Topics in Microbiology and Immunology, vol. 365 (Springer, 2012); John S. Mackenzie and Martyn Jeggo, ‘The One Health Approach – Why Is It So Important?’ (2019) 4(2) Tropical Medicine and Infectious Disease 88.

48 World Health Organisation – WHO, ‘One Health’ (2017). Available at: www.who.int/news-room/q-a-detail/one-health; World Organisation for Animal Health – OIE, ‘One Health “at a Glance”’ (n.d.). Available at: www.oie.int/en/for-the-media/onehealth/; World Health Organisation – WHO, ‘Tripartite (FAO, OIE, WHO) and UNEP support OHHLEP’s definition of “One Health”’ (n.d.). Available at: www.who.int/news/item/01-12-2021-tripartite-and-unep-support-ohhlep-s-definition-of-one-health.

49 See, e.g.: Centers for Diseases Control and Prevention, ‘One Health Basics’ (n.d.). Available at: www.cdc.gov/onehealth/basics/index.html#:~:text=One%20Health%20is%20a%20collaborative,plants%2C%20and%20their%20shared%20environment. World Health Organisation – WHO, ‘One Health’.

50 One Health: A Call for Ecological Equity’ (2023) 401(10372) Lancet 169.

51 Raina K. Plowright, A. N. Ahmed, T. Coulson, et al., ‘Ecological Countermeasures to Prevent Pathogen Spillover and Subsequent Pandemics’ (2024) 15(1) Nature Communications 2577. Along these lines, see also: Daszak, ‘Workshop Report on Biodiversity and Pandemics of the Intergovernmental Platform on Biodiversity and Ecosystem Services’; A. S. Bernstein, A. W. Ando, T. Loch-Temzelides, et al., ‘The Costs and Benefits of Primary Prevention of Zoonotic Pandemics’ (2022) 8(5) Science Advances; United Nations Environment Programme and International Livestock Research Institute, ‘Preventing the Next Pandemic: Zoonotic Diseases and how to Break the Chain of Transmission’ (2020). Available at: www.unep.org/resources/report/preventing-future-zoonotic-disease-outbreaks-protecting-environment-animals-and; M. N. Hayek, ‘The Infectious Disease Trap of Animal Agriculture’ (2022) 8(44) Science Advances.

52 Plowright et al., ‘Ecological Countermeasures’.

54 Neil M. Vora, L. Hannah, S. Lieberman, M. M. Vale, R. K. Plowright, and A. S. Bernstein, ‘Want to Prevent Pandemics? Stop Spillovers’ (2022) 605(7910) Nature 419; Pallavi A. Kache, S. Cook, N. Sizer, L. Hannah, and N. M. Vora, ‘Urgent Need for Integrated Pandemic Policies on Pathogen Spillover’ (2021) 5(10) The Lancet Planetary Health e668. As considered in: Plowright, ‘Ecological Countermeasures to Prevent Pathogen Spillover and Subsequent Pandemics’.

55 See, e.g, Kache, ‘Urgent Need for Integrated Pandemic Policies on Pathogen Spillover’. S. H. Olson, A. E. Fine, M. Pruvot, L. O. Keatts, and C. Walzer, ‘Ground Zero for Pandemic Prevention: Reinforcing Environmental Sector Integration’ (2023) 8(10) BMJ Global Health.

56 Catherine Machalaba, M. Uhart, M. Ryser-Degiorgis, and W. B. Karesh, ‘Gaps in Health Security Related to Wildlife and Environment Affecting Pandemic Prevention and Preparedness, 2007–2020’ (2021) 99(5) Bulletin of the World Health Organization 342; Olson, ‘Ground Zero for Pandemic Prevention’.

57 Proposal for the WHO Pandemic Agreement (A/INB/9/3 Rev.1 – 22 April 2024) Resumed Ninth Meeting of the Intergovernmental Negotiating Body to Draft and Negotiate a WHO Convention, Agreement or Other International Instrument on Pandemic Prevention, Preparedness and Response, Provisional Agenda Item 2.

60 It should be noted that these provisions have yet to be agreed at the time of writing.

61 Directive 2008/98/EC of the European Parliament and of the Council of 19 November 2008 on Waste and Repealing Certain Directives (2008) OJ L312/3. Articles 1 and 13.

62 For more on this see Chapter 5.

63 European Commission, ‘The European Green Deal’ (Communication) COM (2019) 640 final, 11 December 2019. Available at: https://eur-lex.europa.eu/legal-content/EN/TXT/?qid=1576150542719&uri=COM%3A2019%3A640%3AFIN.

64 European Commission, ‘EU Biodiversity Strategy for 2030. Bringing Nature Back into our Lives’ (Communication) COM (2020) 380 final, 20 May 2020. Available at: https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=celex%3A52020DC0380.

65 European Commission, ‘New EU Forest Strategy for 2030 – To Improve the Quantity and Quality of EU Forests’ (n.d.). Available at: https://environment.ec.europa.eu/strategy/forest-strategy_en.

66 European Commission, ‘A Farm to Fork Strategy for a Fair, Healthy and Environmentally-friendly Food System’ (Communication) COM (2020) 381 final, 20 May 2020. Available at: https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=celex:52020DC0381.

67 European Commission, ‘Stepping up EU Action to Protect and Restore the World’s Forests’.

68 Council of the European Union, ‘Interinstitutional Agreement or Provisional Deal on the Proposal for Regulation of the European Parliament and of the Council on Nature Restoration’.

69 Regulation (EU) 995/2010 of the European Parliament and of the Council of 20 October 2010 Laying Down the Obligations of Operators who Place Timber and Timber Products on the Market (2010) OJ L295/23.

70 See: C.Dummett, A. Blundell, K. Canby, M. Wolosin, and E. Bodnar, Illicit Harvest, Complicit Goods: The State of Illegal Deforestation for Agriculture (Forest Policy Trade and Finance Initiative Report, 2021) 3.

71 European Commission, ‘Commission Staff Working Document – Fitness Check on Regulation (EU) No 995/2010 of the European Parliament and of the Council of 20 October 2010 Laying Down the Obligations of Operators who Place Timber and Timber Products on the Market (the EU Timber Regulation) and on Regulation (EC) No 2173/2005 of 20 December 2005 on the Establishment of a FLEGT Licensing Scheme for Imports of Timber into the European Community (FLEGT Regulation)’ SWD(2021) 328 final, 17 November 2021.

72 See: Regulation 2023/1115 of 31 May 2023, Deforestation-free Products Regulation. Recital 34.

73 See, e.g.: United Nations Convention to Combat Desertification, ‘Supporting the Global Response to the COVID-19 Pandemic: Land-based Solutions for Healthy People and a Healthy Planet’ (2020). Available at: www.unccd.int/sites/default/files/documents/2020-06/1498_UNCCD_%20Covid_%20layout-low%20res-1.pdf.

74 Regulation 2023/1115 of 31 May 2023, Deforestation-free Products Regulation. Recital 20.

75 Cuypers, ‘The Impact of EU Consumption on Deforestation’. See, also: European Commission, ‘Stepping up EU Action to Protect and Restore the World’s Forests’.

76 Regulation 2023/1115 of 31 May 2023, Deforestation-free Products Regulation. Recital 38.

77 European Commission, ‘Commission Staff Working Document – Accompanying the Document “Stepping up EU Action to Protect and Restore the World’s Forests”’ SWD (2019) 307 final, 23 July 2019. Available at: https://commission.europa.eu/system/files/2019-07/communication-eu-action-protect-restore-forests_swd_en.pdf.

78 See: Bougas, ‘Service Contract on EU Policy on Forest Products and Deforestation’.

79 E.g: A. Y. Vittor, B. Armien, P. Gonzalez, et al., ‘Epidemiology of Emergent Madariaga Encephalitis in a Region with Endemic Venezuelan Equine Encephalitis: Initial Host Studies and Human Cross-sectional Study in Darien, Panama’ (2016) 10(4) PLoS Neglected Tropical Diseases e0004554; A. Erhart et al., ‘Epidemiology of Forest Malaria in Central Vietnam: A Large Scale Cross-sectional Survey’ (2005) 4(1) Malaria Journal 1.

80 V. Vijay, S. L. Pimm, C. N. Jenkins, and S. J. Smith, ‘The Impacts of Oil Palm on Recent Deforestation and Biodiversity Loss’ (2016) 11(7) PloS one e0159668.

81 S. Kadandale, R. Marten, and R. Smith, ‘The Palm Oil Industry and Noncommunicable Diseases’ (2019) 97(2) Bulletin of the World Health Organization 118.

82 See, e.g.: D. I. Ortiz, M. Piche-Ovares, L. M. Romero-Vega, J. Wagman, and A. Troyo, ‘The Impact of Deforestation, Urbanization, and Changing Land Use Patterns on the Ecology of Mosquito and Tick-borne Diseases in Central America’ (2022) 13(1) Insects 20.

83 It should be noted that an analysis on the compatibility with World Trade Organisation rules is not within the scope of this contribution but is an important element for the viability and operability of this Regulation.

84 See: European Commission, ‘Implementation of the EU Deforestation Regulation – Traceability’ (n.d.). Available at: https://green-business.ec.europa.eu/implementation-eu-deforestation-regulation/traceability_en.

85 See: Footnote ibid., More in Section 9.4.3 herein.

86 Regulation 2023/1115 of 31 May 2023, Deforestation-free Products Regulation. Article 2(1).

87 Regulation 2023/1115 of 31 May 2023, Deforestation-free Products Regulation. Article 2(2).

88 To be noted: the list might be amended to include additional products following a Commission assessment. Footnote Ibid., Article 34(3).

90 See: P. Holmgren and R. Davis, ‘FRA 2000. On Definitions of Forest and Forest Change’ (Food and Agriculture Organization – FAO, Forestry Department. Working Paper 33, Rome, 2000). Note that the FAO definition of forest was criticised: Rainforest Movement et al., ‘Open Letter from Various NGOs to FAO on the Occasion of the International Day of Forests 2014’ (2014). Available at: www.wrm.org.uy/all-campaigns/open-letter-to-fao-on-the-occasion-of-the-international-day-of-forests-2014.

91 Council of the European Union, ‘Council General Approach – Draft Regulation of the European Parliament and of the Council on the Making Available on the Union Market as well as Export from the Union of Certain Commodities and Products Associated with Deforestation and Forest Degradation and Repealing Regulation (EU) No. 995/2010 – General approach’ (2022). Point no. 12.

92 Regulation 2023/1115 of 31 May 2023, Deforestation-free Products Regulation. See Recital 44.

93 Footnote Ibid., Article 2(4).

94 Regulation 2023/1115 of 31 May 2023, Deforestation-free Products Regulation. See Recital 82.

95 Footnote Ibid., Articles 31(1) and (2).

97 In particular, the management of wetlands represents an interesting challenge in relation to disease control. On this, see: P. E. R. Dale and J. M. Knight, ‘Wetlands and Mosquitoes: A Review’ (2008) 16 Wetlands Ecology and Management 255. See also: C. M. Finlayson and P. Horwitz, ‘Wetlands as Settings for Human Health – The Benefits and the Paradox’ in C. Max Finlayson, Pierre Horwitz and Philip M. Weinstein (eds.), Wetlands and Human Health (Springer, 2015).

98 Regulation 2023/1115 of 31 May 2023, Deforestation-free Products Regulation, Recital 82.

99 Regulation 2023/1115 of 31 May 2023, Deforestation-free Products Regulation. Article 3(a).

100 Footnote Ibid., Article 2(3).

101 Footnote Ibid., Article 2(5).

102 See also the analysis of: B. G. Da Silva and P.-N. Milcamps, ‘The Regulation on Deforestation-Free Products: When the EU Takes on Deforestation’s Corrupted Roots’ (2023) 32(6) European Energy and Environmental Law Review 293310.

103 Regulation 2023/1115 of 31 May 2023, Deforestation-free Products Regulation. Article 2(7).

104 Council of the European Union, ‘Council General Approach – Draft Regulation of the European Parliament and of the Council on the Making Available on the Union Market as well as Export from the Union of Certain Commodities and Products Associated with Deforestation and Forest Degradation and Repealing Regulation (EU) No. 995/2010 – General approach’. Point no. 13.

105 Regulation 2023/1115 of 31 May 2023, Deforestation-free Products Regulation. Articles 34(6) and Recital 44.

106 Regulation 2023/1115 of 31 May 2023, Deforestation-free Products Regulation. Article 3.

107 Footnote Ibid., Article 2(13).

108 Footnote Ibid., Article 2(40).

109 Da Silva, ‘The Regulation on Deforestation-Free Products’.

110 Regulation 2023/1115 of 31 May 2023, Deforestation-free Products Regulation. Article 8.

111 Footnote Ibid., Article 13.

112 Footnote Ibid., Article 9.

113 Footnote Ibid., Article 10.

114 Footnote Ibid., Article 11.

115 For a more detailed analysis, see: Da Silva, ‘The Regulation on Deforestation-Free Products’. For an analysis of the initial Proposal (some elements were maintained in the final text), see: Client Earth, ‘The Proposed EU Law on Deforestation-Free Products. What is in the European Commission’s Proposal and what is Left Out?’ (2021). Available at: www.clientearth.org/media/sbjhtw3c/eu-deforestation-proposal_main-elements-and-omissions_dec21.pdf.

116 Regulation 2023/1115 of 31 May 2023, Deforestation-free Products Regulation, Article 29(1).

117 Footnote Ibid., Article 29(3).

118 Footnote Ibid., Article 29(4).

119 Footnote Ibid., Article 13(1).

120 See: Client Earth, ‘The Proposed EU Law on Deforestation-Free Products.’

121 Regulation 2023/1115 of 31 May 2023, Deforestation-free Products Regulation, Article 16.

10 One Health among Many What Can One Health Learn from EcoHealth and Planetary Health Projects to Encourage Legal Reform?

1 J. S. Mackenzie, M. McKinnon, and M. Jeggo (eds.), One Health: From Concept to Practice. Confronting Emerging Zoonoses: The One Health Paradigm. 3rd ed. (2014) 163189, citing C. W. Schwabe, Veterinary Medicine and Human Health (Baltimore: Williams and Wilkins 1984).

2 J. Zinsstag, E. Schelling, D. Waltner-Toews, and M. Tanner, ‘From “One Medicine” to “One Health” and Systemic Approaches to Health and Well-being’ (2011) 101(3–4) Preventive Veterinary Medicine 148156 at 151.

3 Such as Charlotte Berg, who linked the One Health perspective to King Ashoka’s (ca. 304 BCE to 232 BCE) Fourteen Rock Edicts. See H. Lerner and C. Berg, ‘The Concept of Health in One Health and Some Practical Implications for Research and Education: What Is One Health?’ (2015) 5(1) Infection Ecology & Epidemiology 1.

4 See, for instance: When founding the first veterinary school in Lyon, France in 1761, Claude Bourgelat emphasised the importance of comparative biopathology in Samantha E. J. Gibbs and E. Paul J. Gibbs, ‘The Historical, Present, and Future Role of Veterinarians in One Health’ in J. Mackenzie, M. Jeggo, P. Daszak, and J. Richt (eds). One Health: The Human-Animal-Environment Interfaces in Emerging Infectious Diseases: The Concept and Examples of a One Health Approach (2013) 3147, 33, citing W. R. Waters, M. V. Palmer, B. M. Buddle, et al. ‘Bovine Tuberculosis Vaccine Research: Historical Perspectives and Recent Advances’ (2012) 30(16) Vaccine 26112622.

5 E. P. J. Gibbs, ‘The Evolution of One Health: A Decade of Progress and Challenges for the Future’ (2014) 174(4) Veterinary Record 8591, at 85.

6 Robert A. Cook, William B. Karesh, and Steven A. Osofsky, ‘The Manhattan Principles’ (WCS, 2021). Available at: https://oneworldonehealth.wcs.org/About-Us/Mission/The-Manhattan-Principles.aspx.

8 Talukder Byomkesh, Nilanjana Ganguli, Eunice Choi, Mohammadali Tofighi, Gary W. vanloon, and James Orbinski, ‘Exploring the Nexus: Comparing and Aligning Planetary Health, One Health, and EcoHealth’ (2024) 6 Global Transitions 6675, at 7071.

9 World Health Organisation, ‘One Health: Questions and Answers’ (2017). Available at: www.who.int/news-room/questions-and-answers/item/one-health.

10 The implications of this focus may be subject to subsequent review but are beyond the purview of this piece.

11 C. Dos, S. Ribeiro, L. H. M. van de Burgwal, and B. J. Regeer, ‘Overcoming Challenges for Designing and Implementing the One Health Approach: A Systematic Review of the Literature’ (2019) 18(7) One Health 100085.

12 J. Lebel, ‘Health: An Ecosystem Approach; The Issue, Case Studies, Lessons and Recommendations’ (Ottawa: International Development Research Centre, 2003), vii.

13 D. Waltner-Toews, ‘Eco-Health: A Primer for Veterinarians’ (2009) 50(5) The Canadian Veterinary Journal 519.

14 Footnote Ibid., xii.

15 Established by the IDRC in 2006. See E. Mi, E. Mi, and M. Jeggo, ‘Where to Now for One Health and Ecohealth?’ (2016) 13(1) EcoHealth at 1217.

16 J. Saint-Charles, J. Webb, A. Sanchez, H. Mallee, B. van Wendel de Joode, and H. Nguyen-Viet, ‘EcoHealth as a Field: Looking Forward’ (2014) 11 EcoHealth 300307 at 301.

17 EcoHealth International (2018) Home. Available at: www.EcoHealthinternational.org/.

18 For instance, the top ‘fundamental questions’ for EcoHealth as listed by Byomkesh et al. were ‘How do ecosystem changes and disruptions affect human health?’ and ‘How can traditional ecological knowledge be integrated with scientific research to inform EcoHealth interventions?’: Talukder Byomkesh, ‘Exploring the Nexus’, 72.

19 R. Horton, R. Beaglehole, R. Bonita, J. Raeburn, M. McKee, and S. Wall, ‘From Public to Planetary Health: A Manifesto’ (2014) 383(9920) The Lancet 847.

20 R. Horton and S. Lo, ‘Planetary Health: A New Science for Exceptional Action’ (2015) 386(10007) The Lancet 19211922 at 1922.

21 Planetary Health Alliance: About Us. Available at: www.planetaryhealthalliance.org/about-the-pha.

22 Byomkesh et al. posit that this interest may have stemmed from the pandemic. See Talukder Byomkesh, ‘Exploring the Nexus’, 70.

23 Notably by prioritising the importance of human health, but additionally the role of humans in creating environmental issues impacting human health. For instance, the top ‘fundamental questions’ for Planetary Health as listed by Byomkesh et al. were ‘How do changes in earth systems affect human health?’ and ‘What are the fundamental drivers of environmental change and their impact on health?’. Footnote Ibid. 72.

24 EcoHealth Alliance, ‘Fiscal Year 2021 Annual Report’ (2021). Available at: www.ecohealthalliance.org/wp-content/uploads/2023/03/FY2021-Annual-Report.pdf.

25 EcoHealth International, ‘Home’ (2018). Available at: www.ecohealthinternational.org/.

26 H. Lerner and C. Berg, ‘A Comparison of Three Holistic Approaches to Health: One Health, Ecohealth, and Planetary Health’ (2017) 4 Frontiers in Veterinary Science 163166.

27 See, generally, Jane Kotzmann and Morgan Stonebridge, ‘Considering Zoonotic Disease Risk in Australia: An Analysis of the Adequacy of the Intensive Animal Agriculture Regulation’ (2022) 45 UNSWLJ 1220. A. Davis and J. Sharp, ‘Rethinking One Health: Emergent Human, Animal and Environmental Assemblages’ (2020) 258 Social Science & Medicine 1.

28 J. Lebel, ‘EcoHealth and the Development World’ (2004) 1 EcoHealth 325326.

29 Dominique F. Charron (ed.), ‘EcoHealth Research in Practice: Innovative Applications of an Ecosystem Approach to Health’ in EcoHealth Research in Practice (New York: Springer, 2011) 255271.

30 Talukder Byomkesh, ‘Exploring the Nexus’, 73.

31 H. Lerner, ‘A Comparison of Three Holistic Approaches to Health’, 6.

32 Rafael Ruiz de Castañeda, Jennifer Villersa, Carlos A. Faerron Guzmánc, et al., ‘One Health and Planetary Health Research: Leveraging Differences to Grow Together’ (2023) 7(2) The Lancet Planetary Health e109e111 at e109.

33 S. Myers, ‘Planetary Health: Protecting Human Health on a Rapidly Changing Planet’ (2006) 390(10114) The Lancet 28602868.

34 R. Horton, R. Beaglehole, R. Bonita, J. Raeburn, M. McKee, and S. Wall, ‘From Public to Planetary Health: A Manifesto’ (2014) 383(9920) The Lancet 847.

35 Sarah Whitmee, Andy Haines, Chris Beyrer, et al., ‘Safeguarding Human Health in the Anthropocene Epoch: Report of The Rockefeller Foundation–Lancet Commission on Planetary Health’ (2015) 386(10007) The Lancet 19732028 at 2017.

36 The other two being ‘imagination’ and ‘research and information’ challenges.

37 Whitmee, ‘Safeguarding Human Health in the Anthropocene Epoch’, 1973.

41 Lerner, ‘A Comparison of Three Holistic Approaches to Health’, 163–166.

42 H. De Pooter, G. L. Burci, P. A. Villarreal, A. Berman, M. M. Mbengue, and D. Yeow, ‘White Paper 22 – One Health’ (2022) Association de droit International/International Law Association.

43 Eric Ip, ‘An Emergent Planetary Health Law’ (2023) 72(4) International & Comparative Law Quarterly 10471067 at 1053, citing L. O. Gostin, Global Health Law (Harvard University Press, 2014) 59; James Wingard, Sofija Belajcic, Manohar Samal, et. al. (2020) Wildlife Trade, Pandemics and the Law: Fighting This Year’s Virus with Last Year’s Law. Legal Atlas, LLC.

44 Ip, ‘An Emergent Planetary Health Law’, 1056.

45 Charron, ‘EcoHealth Research in Practice’.

46 Natalina Nheu, ‘By the People, For the People? Community Participation in Law Reform’ (2010) 6 Law and Justice Foundation 269.

47 Niklas Luhmann, ‘Law as a Social System’ (1988) 83 Northwestern University Law Review 136138.

48 Xiao-Xi Zhang, Jing-Shu Liu, Le-Fei Han et al., ‘Towards a Global One Health Index: A Potential Assessment Tool for One Health Performance’ (2022) 11(1) Infect Dis Poverty 57.

49 Paul Gwakisa, Janeth George, Calvin Sindato, et al. ‘Pillars for Successful Operationalization of One Health as an Ecosystem Approach: Experience from a Human-animal Interface in the Maasai Steppe in Tanzania’ (2023) 5(11) One Health Outlook.

50 Mishal S. Khan, Peregrine Rothman-Ostrow, Julia Spencer, et al., ‘The Growth and Strategic Functioning of One Health Networks: A Systematic Analysis’ (2018) 2(6) The Lancet Planetary Health e264e273.

52 We acknowledge that the OHHLEP has since released a technical document (‘One Health Theory of Change’) that includes as one of its main ‘Pathways’ the need to prioritise ‘Actions related to implementation of One Health including scaling up of capacity development, community engagement and mobilization for action, multisectoral coordination, collaboration and communication, and equitable integration of sectors’ (at 16) (emphasis added). However, the release of this more institutionalised policy position, while encouraging, does not counter the historical failure of OHNs in this regard, especially considering that OHNs are not always clearly motivated in their project implementation by the OHHLEP. See OHHLEP, ‘One Health Theory of Change’ (2022) at www.who.int/publications/m/item/one-health-theory-of-change.

54 Talukder Byomkesh, ‘Exploring the Nexus’, 74.

55 Jane Kotzmann and Morgan Stonebridge, ‘Considering Zoonotic Disease Risk in Australia: An Analysis of the Adequacy of the Intensive Animal Agriculture Regulation’ (2022) 45 UNSWLJ 1220.

56 Gobierno de Mexico, ‘Molango de Escamilla’. Available at: www.economia.gob.mx/datamexico/en/profile/geo/molango-de-escamilla.

57 H. Riojas-Rodriguez and S. Rodriguez-Dozal, ‘An Ecosystem Study of Manganese Mining in Molango, Mexico’ (2012) 1 Ecohealth Research in Practice 8796.

59 M. Catalán-Vázquez, H. Riojas-Rodríguez, M. Cortez-Lugo, S. L. Rodríguez-Dozal, D. Hernández-Bonilla, and B. E. Pelcastre-Villafuerte, ‘Social Representations of Mining Activity after an Environmental Improvement Program in the Manganese District of Molango, in Mexico, and Their Implications for Risk Management’ (2019) 62(10) Journal of Environmental Planning and Management 17141735.

60 Gobierno de Mexico, ‘Molango de Escamilla’. Available at: www.economia.gob.mx/datamexico/en/profile/geo/molango-de-escamilla.

61 Catalan-Vazquez, ‘Social Representations of Mining Activity After an Environmental Improvement Program in the Manganese District of Molango, in Mexico’, 1714–1735.

63 K. Dilge, ‘Minera Autlán Reaches an Agreement to Stop Blockade’ (2022) Mexico Business News. Available at: https://mexicobusiness.news/mining/news/minera-autlan-reaches-agreement-stop-blockade.

64 F. Mares, ‘Minera Autlán to Invest a Further US$700,000 In Social Programs’ (2022) Mexico Business News. Available at: https://mexicobusiness.news/mining/news/minera-autlan-invest-further-us700000-social-programs.

65 A. Lieja, ‘Mining Reform in Mexico: Principal Amendments, Effect, and Implications for Foreign Investors’ (2023) Jones Day. Available at: www.jonesday.com/en/insights/2023/06/mining-reform-in-mexico-amendments-and-impact.

66 D. Trevedan and H. Gonzalez, ‘Major Overhaul to Mexico’s Mining Regulation’ (2023) Norton Rose Fulbright. Available at: www.nortonrosefulbright.com/en/knowledge/publications/04715af1/major-overhaul-to-mexicos-mining-regulation.

68 D. Shailer, ‘More Parks, Less Money: Advocates Say Mexico’s New Budget Doesn’t Add Up for Natural Protected Areas’ (2023) Associated Press, https://apnews.com/article/mexico-budget-environment-park-protection-funding-6d26b85334069269362b5686344cf92b.

69 Behara Satyanarayana, Tom Van der Stocken, Guillaume Rans, et al. ‘Island-wide Coastal Vulnerability Assessment of Sri Lanka Reveals that Sand Dunes, Planted Trees and Natural Vegetation may Play a Role as Potential Barriers Against Ocean Surges’ (2023) 12 Global Ecology and Conservation 144157.

70 P. D. AbeysingheAntibacterial Activity of some Medicinal Mangroves against Antibiotic Resistant Pathogenic Bacteria’ (2010) 72(2) Indian Journal of Pharmaceutical Sciences 167172.

71 Planetary Health Alliance Members. Available at: www.planetaryhealthalliance.org/pha-members-sz.

72 H. Duff, C. Faerron Guzmán, A. Almada, C. Golden, and S. Myers, Planetary Health Case Studies: An Anthology of Solutions (Planetary Health Alliance 2020).

73 Footnote Ibid., 440.

74 Footnote Ibid., 442.

75 Footnote Ibid., 447.

76 Footnote Ibid., 446–447.

78 United Nations Framework Convention on Climate Change website. Available at: https://unfccc.int/climate-action/momentum-for-change/planetary-health/sri-lanka-mangrove-conservation-project.

79 Duff, Planetary Health Case Studies, 446.

80 F. A. Orozco and D. C. Cole, ‘Tackling Challenges to Farmers: Health and Agro-ecosystem Sustainability in Highland Ecuador’ (2012) 1 Ecohealth Research in Practice 4758.

81 Footnote Ibid., 47.

82 D. C. Cole, C. C Crissman, and F. A. Orozco, ‘Canada’s International Development Research Centre’s Eco-Health Projects with Latin Americans’ (2006) 97(6) Canadian Journal of Public Health I8I14.

83 Orozco, ‘Tackling Challenges to Farmers’, 48.

84 F. A. Orozco, Donald C. Cole, Selahadin Ibrahim, and Susitha Wanigaratne, ‘Health Promotion Outcomes Associated with a Community-based Program to Reduce Pesticide-related Risks among Small Farm Households’ (2011) 26(4) Health Promotion International 432446.

85 Orozco, ‘Tackling Challenges to Farmers’, 49.

86 Orozco, ‘Tackling Challenges to Farmers’, 56.

87 F. A. Orozco, Donald C. Cole, Greg Forbes, Jürgen Kroschel, Susitha Wanigaratne, and Denis Arica, ‘Monitoring Adherence to the International Code of Conduct Highly Hazardous Pesticides in Central Andean Agriculture and Farmers’ Rights to Health’ (2009) 15(3) International Journal of Occupational and Environmental Health 255–68.

88 Orozco, ‘Tackling Challenges to Farmers’, 53.

89 E. Mollocana-Lara and F. Gonzales, ‘Control of Pesticides in Ecuador: An Underrated Problem?’ (2020) 5(3) Revista Bionatura 12571263.

90 I. Johnson, A. Hansen, and P. Bi, ‘The Challenges of Implementing an Integrated One Health Surveillance System in Australia’ (2018) 65(1) Zoonoses and Public Health e229e236.

91 See n 12 (OHHLEP, W. B. Adisasmito, S. Almuhairi, et al., ‘One Health: A New Definition for a Sustainable and Healthy Future’ (2022) 18(6) PLoS Pathogens e1010537). See also n 52 (OHHLEP, ‘One Health Theory of Change’ (2022) at www.who.int/publications/m/item/one-health-theory-of-change).

92 Mishal S. Khan ‘The Growth and Strategic Functioning of One Health Networks’, e70–e271.

93 Byomkesh et al. found that the greatest emphases of One Health are on ‘collaboration across multiple disciplines’, rather than on a substantive subject matter like its neighbours (i.e. ‘ecosystem and community well-being’ for EcoHealth, and ‘sustainability’ for Planetary Health). Talukder Byomkesh, ‘Exploring the Nexus’, 72 (table 4).

94 Chris Degeling, Jane Johnson, Michael Ward, Andrew Wilson, and Gwendolyn Gilbert, ‘A Delphi Survey and Analysis of Expert Perspectives on One Health in Australia’ (2017) 14 EcoHealth 783792.

95 Global population data. United Nations Department of Economic and Social Affairs – Population Division. Available at: https://population.un.org/wpp/Download/Standard/Population/.

96 Around 55 per cent of Uganda’s population is aged 15 years or older: 3.2 per cent population growth per year implies that for each 100 people (55 of whom are 15+), 3.2 new births will occur; or around 1 birth for every 17th person aged 15+.

97 H. Duff, C. Faerron Guzmán, A. Almada, C. Golden, and S. Myers, ‘Family Planning for People and Planet’ (2020) Planetary Health Case Studies: An Anthology of Solutions 363401.

98 Pathfinder’s framing of environmental impacts almost always ties them back to harms to humans ‘such as high maternal mortality rates and poor sexual and reproductive health outcomes’. Pathfinder International. ‘Scaling-Up the Population, Health, And Environment Approach in the Lake Victoria Basin: A Review of the Results from Phases I And II of the HoPE-LVB Project’ (2018) Hope-LVB Project Report.

99 Duff, ‘Family Planning for People and Planet’, 380.

100 Footnote Ibid., 388.

101 Footnote Ibid., 389.

102 A. Nanvubya, Rhoda K. Wanyenze, Teddy Nakaweesa, et al. ‘Correlates of Knowledge of Family Planning among People Living in Fishing Communities of Lake Victoria, Uganda’ (2020) 20 BMC Public Health 1642.

103 USAID and Johns Hopkins Center for Communication Programs, ‘What happened to the HoPE-LVB project post-closure?’ (2022). Available at: https://peopleplanetconnect.org/wp-content/uploads/2020/12/Brief-PHELakeVictoria_v3-digital.pdf.

104 Duff, ‘Family Planning for People and Planet’, 398401.

106 USAID and Johns Hopkins Center for Communication Programs, ‘What happened to the HoPE-LVB project post-closure?’.

107 Peter Millard and Stephan Kueffner, ‘The Sinking Gold Town’ (2022) Bloomberg News. Available at: www.bloomberg.com/features/2022-illegal-gold-mining-sinkhole-zaruma-ecuador.

109 O. Betancourt, Ramiro Barriga, Jean Remy Davée Guimarães, Edwin Cueva, and Sebastián Betancourt, ‘Impacts on Environmental Health of Small-Scale Gold Mining in Ecuador’ in Ecohealth Research in Practice (2012) 119130.

110 Betancourt, ‘Impacts on Environmental Health of Small-Scale Gold Mining in Ecuador’, 119–130.

114 Lisa Waldick, ‘Mining, Contamination, and Health in Ecuador’ (2011) International Development Research Centre (IDRC). Available at: https://idrc-crdi.ca/en/stories/mining-contamination-and-health-ecuador.

115 Paul Schutzmeier, Ursula Berger, and Stephan Bose-O’Reilly, ‘Gold Mining in Ecuador: A Cross-Sectional Assessment of Mercury in Urine and Medical Symptoms in Miners from Portovelo/Zaruma’ (2016) 14(1) International Journal of Environmental Research and Public Health 34.

11 Drawing from AMR Experience for Better Prevention, Preparedness, and Response to Complex Health Threats under a One Health Approach

The Authors appreciate the comments provided by Juan Lubroth, Katie Woolaston, Jane Kotzmann, Elien Verniers, Elisa Cavallin, Francesca Coli, and Maurizio Aragrande.

1 ‘Ten Threats to Global Health in 2019’. Available at: www.who.int/news-room/spotlight/ten-threats-to-global-health-in-2019.

2 Jim O’Neill, ‘Tackling Drug-Resistant Infections Globally. Final Report and Recommendations’ (2016). Available at: https://amr-review.org/sites/default/files/160518_Final%20paper_with%20cover.pdf; See also, Interagency Coordination Group on Antimicrobial Resistance (IACG). ‘No Time to Wait: Securing the Future from Drug-resistant Infections. Report to the Secretary-General of the United Nations’ (2019) Available at: www.who.int/docs/default-source/documents/no-time-to-wait-securing-the-future-from-drug-resistant-infections-en.pdf.

3 Ponnu Padiyara, Hajime Inoue, and Marc Sprenger, ‘Global Governance Mechanisms to Address Antimicrobial Resistance’ (2018) 11 Infectious Diseases: Research and Treatment 1178633718767887.

4 O’Neill, ‘Tackling Drug-resistant Infections Globally’; Interagency Coordination Group on Antimicrobial Resistance (IACG), ‘No time to wait’.

5 Interagency Coordination Group on Antimicrobial Resistance (IACG), ‘No time to wait’, 4.

6 United Nations Environment Programme, Bracing for Superbugs: Strengthening Environmental Action in the One Health Response to Antimicrobial Resistance (Geneva, 2023) 10, 14.

7 T. P. Robinson, D. P. Bu, J. Carrique-Mas, E. M. Fèvre, M. Gilbert, and D. Grace, ‘Antibiotic Resistance Is the Quintessential One Health Issue’ (2016) 110(7) Transactions of the Royal Society of Tropical Medicine and Hygiene 377380.

8 Resolution WHA68.7, ‘Global Action Plan on Antimicrobial Resistance’, 26 May 2015, paras 1–2 and Annex 3, para. 49.

9 Jon Pierre, Daniel Carelli, and Guy Peters, ‘The Four Worlds of Politics and Administration in the EU: How Institutional Arrangements Shape the Struggle against Antimicrobial Resistance’ (2023) 31(12) Journal of European Public Policy 40884115.

11 Peter Collingnon, Prema-chandra Athukorala, Sanjaya Senanayake, and Fahad Khan, ‘Antimicrobial Resistance: The Major Contribution of Poor Governance and Corruption to This Growing Problem’ (2015) 3(e0116746) PLoSONE 10. Available at: https://doi.org/10.1371/journal.pone.0116746. See also Andrea Maugeri, Martina Barchitta, Federico Puglisi, and Antonella Agodi, ‘Socio-Economic, Governance and Health Indicators Shaping Antimicrobial Resistance: An Ecological Analysis of 30 European Countries’ (2023) 19(1) Global Health 12.

12 Arne Ruckert, Patrick Fafard, Suzanne Hindmarch, et al., ‘Governing Antimicrobial Resistance: A Narrative Review of Global Governance Mechanisms’ (2020) 41(4) Journal of Public Health Policy 515528.

13 D. Wallinga, G. Rayner, and T. Lang, ‘Antimicrobial Resistance and Biological Governance: Explanations for Policy Failure’ (2015) 129(10) Public Health 1314–25. See also Pita Spruijt and Arthur C. Petersen, ‘Multilevel Governance of Antimicrobial Resistance Risks: A Literature Review’ (2015) 25(8) Journal of Risk Research 945958.

14 Susan Rogers Van Katwyk, Alberto Giubilini, Class Kirchhelle, et al., ‘Exploring Models for an International Legal Agreement on the Global Antimicrobial Commons: Lessons from Climate Agreements’ (2023) 31 Health Care Anal 2546. Available at: https://doi-org.fao.idm.oclc.org/10.1007/s10728-019-00389-3.

15 Eberhardt Rechtin and Mark W. Maier, ‘The Art of Systems Architecting’ in Annette J. Krygiely (ed.), Behind the Wizard’s Curtain. An Integration Environment for a System of Systems. (Cooperative Research Program (CCRP), US Library of Congress 1999). Available at: www.dodccrp.org/files/Krygiel_Wizards.pdf.

16 Ross Arnold and Jon Wade, ‘A Definition of Systems Thinking: A Systems Approach’ (2015) 44 Procedia Computer Science 669678.

17 Kevin Queenan, Julie Garnier, Liza Rosenbaum Nielsen, et al., ‘Roadmap to a One Health Agenda’ (2017) CABI Reviews 117. Available at: https://doi.org/10.1079/PAVSNNR201712014.

18 Scott J. Leischow, Allan Best, William M. Trochim, et al., ‘Systems Thinking to Improve the Public’s Health’ (2008) 35(2 Suppl) American Journal of Preventive Medicine S196203.

19 Food and Agriculture Organization of the United Nations (FAO), The World Organisation for Animal Health, and the World Health Organization (WHO), ‘High Level Technical Meeting to Address Health Risks at the Human-Animal-Ecosystems interface’ (Mexico City, 2011). Available at: www.fao.org/4/i3119e/i3119e.pdf.

20 Resolution WHA68.7, ‘Global Action Plan on Antimicrobial Resistance’, 26 May 2015. Available at: https://iris.who.int/bitstream/handle/10665/193736/9789241509763_eng.pdf?sequence=1

22 O’Neill J, Tackling drug-resistant infections globally: Final report and recommendations (Review on Antimicrobial Resistance, Wellcome Trust & HM Government, May 2016) https://amr-review.org/sites/default/files/160518_Final%20paper_with%20cover.pdf

23 IACG, ‘No Time to Wait: Securing the Future from Drug-resistant Infections’. Report to the Secretary-General of the United Nations, p. 21, recommendation E2. Available at: www.who.int/publications/i/item/no-time-to-wait-securing-the-future-from-drug-resistant-infections.

24 Footnote Ibid., recommendation E3.

25 ‘Memorandum of Understanding between the United Nations Food and Agriculture Organization and the World Organization for Animal Health and the World Health Organization Regarding Cooperation to Combat Health Risks at the Animal-Human-Ecosystem Interface in the Context of the One Health Approach and Including Antimicrobial Resistance’ (30 May 2018). Available at: www.who.int/zoonoses/MoU-Tripartite-May-2018.pdf.

26 ‘Memorandum of Understanding between the Food and Agriculture Organization of the United Nations and the World Organization for Animal Health and the World Health Organization and the United Nations Environment Programme Regarding Cooperation to Combat Health at the Animal-Human-Ecosystem Interface in the Context of the “One Health” Approach and Including Antimicrobial Resistance’ (17 March 2022). Available at: www.fao.org/3/cb9403en/cb9403en.pdf.

27 Jorge Pinto Ferreira, Daniela Battaglia, Alejandro Dorado García, et al., ‘Achieving Antimicrobial Stewardship on the Global Scale: Challenges and Opportunities’ (2022) 10(8) Microorganisms 1599.

28 Global Leaders Group, ‘A Pocket Guide for Ministers across Sectors’ (2022). Available at: www.amrleaders.org/docs/librariesprovider20/default-document-library/a6-pocket-guide_final.pdf?sfvrsn=797cf4cb_5&download=true.

29 Van Katwyk, ‘Exploring Models for an International Legal Agreement on the Global Antimicrobial Commons’, 2546.

30 Didier Wernli, Thomas Haustein, John Conly, et al., ‘A Call for Action: The Application of The International Health Regulations to the Global Threat of Antimicrobial Resistance’ (2011) 8(4) PLoS Medicine e1001022.

31 It is noteworthy that the proposals for amendment of the IHR submitted by WHO member states and some regional integration organisations, currently under consideration of the Working Group on Amendments to the International Health Regulations (2005), do not include any new provision incorporating the One Health approach. A stronger collaboration between the WHO and the other partners from the Quadripartite is only foreseen in a proposal advanced by India for revision of Article 6, where it is added that if the notification received by WHO involves the competency of FAO, WOAH, or UNEP, these entities should be immediately notified. All relevant information on the revision process are available at www.who.int/teams/ihr/working-group-on-amendments-to-the-international-health-regulations-(2005).

32 According to Article 1 IHR, a PHEIC is a ‘an extraordinary event which is determined, as provided in these Regulations: (i) to constitute a public health risk to other States through the international spread of disease and (ii) to potentially require a coordinated international response’.

33 On the concept of ‘deep prevention’ see J. Vinuales, S. Moon, G. Le Moli, and G. L. Burci, ‘A Global Pandemic Treaty Should Aim for Deep Prevention’ (2021) 397(10287) The Lancet 17911792; G. Le Moli, J. E. Viñuales, G. L. Burci, A. Strobeyko, and S. Moon, ‘The Deep Prevention of Future Pandemics through a One Health Approach: What Role for a Pandemic Instrument?’ (2022) Global Health Centre Policy Brief. Retrieved from https://hdl.handle.net/1887/3561531.

34 See, among others, the standards approved by the Codex Alimentarius Commission in www.fao.org/fao-who-codexalimentarius/thematic-areas/antimicrobial-resistance/en/.

35 Joanna Hanefeld, Mishal Khan, Goran Tomson, and Richard Smith, ‘Trade Is Central to Achieving the Sustainable Development Goals: A Case Study of Antimicrobial Resistance’ (2017) 358 BMJ j3505.

36 Van Katwyk, ‘Exploring Models for an International Legal Agreement on the Global Antimicrobial Commons’ 25–46.

37 FAO, OIE, and WHO, ‘International Instruments on the Use of Antimicrobials across the Human, Animal and Plant Sectors’ (2019). Available at: www.who.int/publications/i/item/9789240013964 (last accessed on 22 October 2023).

38 Codex Alimentarius, ‘Code of Practice to Contain Foodborne Antimicrobial Resistance’ (CXC 61-2005).

39 ‘Guidelines for Risk Analysis of Foodborne Antimicrobial Resistance’ (CXG 77-2011).

40 ‘Guidelines on Integrated Monitoring and Surveillance of Foodborne AMR’ (CXG 94-2021).

42 Padiyara, ‘Global Governance Mechanisms to Address Antimicrobial Resistance’; Arne Ruckert, Patrick Fafard, Suzanne Hindmarch, et al., ‘Governing Antimicrobial Resistance: A Narrative Review of Global Governance Mechanisms’ (2020) 41(4) Journal of Public Health Policy 515528; Ruckert, ‘Governing antimicrobial resistance: a narrative review of global governance mechanisms’.

43 Rubin, Olivier. ‘The Glocalization of Antimicrobial Stewardship’ (2019) 15 Global Health 54. Available at: https://doi.org/10.1186/s12992-019-0498-2.

44 Padiyara, ‘Global Governance Mechanisms to Address Antimicrobial Resistance’; Connor Rochford, Devi Sridhar, Ngaire Woods, et al., ‘Global Governance of Antimicrobial Resistance’ (2018) 391(10134) The Lancet 19761978. Available at: https://doi.org/10.1016/S0140-6736(18)31117-6.

45 Van Katwyk, ‘Exploring Models for an International Legal Agreement on the Global Antimicrobial Commons’ 25–46.

48 See, among others, Andrea M. Caceres, Kshitji K. Singh, T. Minssen, S. R. Van Katwyk, and S. J. Hoffman, ‘Using the International Pandemic Instrument to Revitalize the Innovation Ecosystem for Antimicrobial R&D’ (2022) 50(S2) Journal of Law, Medicine & Ethics 4754.

49 Arne Ruckert, S. Lake, and Susan Rogers Van Katwyk, ‘Developing a Protocol on Antimicrobial Resistance through WHO’s Pandemic Treaty Will Protect Lives in Future Pandemics’ (2024) 20(1) Global Health 10.

52 Mohan P. Joshi, Chifumbe Chintu, Mirfin Mpundu, et al., ‘Multidisciplinary and Multisectoral Coalitions as Catalysts for Action against Antimicrobial Resistance: Implementation Experiences at National and Regional Levels’ (2018) 13(12) Global Public Health 17811795.

53 FAO, OIE, WHO. Monitoring Global Progress on Addressing Antimicrobial Resistance. 2018. Available at: https://iris.who.int/bitstream/handle/10665/273128/9789241514422-eng.pdf?sequence=1.

54 Alvin Q. Chua, Monica Verma, Li Yang Hsu, and Helena Legido-Quigley, ‘An Analysis of National Action Plans on Antimicrobial Resistance in Southeast Asia Using a Governance Framework Approach’ (2021) 7 Lancet Regional Health Western Pacific 100084.

55 Louise Munkholm and Olivier Rubin, ‘The Global Governance of Antimicrobial Resistance: A Cross-Country Study of Alignment between the Global Action Plan and National Action Plans’ (2020) 16 Global Health 109. Available at: https://doi.org/10.1186/s12992-020-00639-3. Olivier Rubin and Louise Munkholm, ‘Isomorphic Dynamics in National Action Plans on Antimicrobial Resistance’ (2022) 42(2) Public Administration & Development 142153.

56 World Health Organization, ‘WHO Implementation Handbook for National Action Plans on Antimicrobial Resistance: Guidance for the Human Health Sector’ (2022). Available at: www.who.int/publications/i/item/9789240041981.

57 Rubin, ‘The Glocalization of Antimicrobial Stewardship’.

59 Gabriel Birgand, Enrique Castro-Sánchez, Sonja Hansen, et al., ‘Comparison of Governance Approaches for the Control of Antimicrobial Resistance: Analysis of Three European Countries’ (2018) 7 Antimicrobial Resistance Infection Control 28.

60 Pita Spruijt and Arthur Petersen, ‘Multilevel Governance of Antimicrobial Resistance Risks: A Literature Review’ (2020) 25 Journal of Risk Research 114.

61 Michael Anderson, Kai Schulze, Alessandro Cassini, Diamantis Plachouras, and Elias Mossialos, ‘A Governance Framework for Development and Assessment of National Action Plans on Antimicrobial Resistance’ (2019) 19(11) Lancet Infectious Diseases e371e384.

62 See the principles of One Health enunciated by OHHLEP in One Health High-Level Expert Panel (OHHLEP). One Health: A New Definition for a Sustainable and Healthy Future’ (2022) 18(6) PLoS Pathogens e1010537. Available at: https://doi.org/10.1371/journal.ppat.1010537.

63 Thana Campos-Rudinsky, ‘A Principled Account of AMR Global Governance Solidarity, Subsidiarity, and Stewardship’ (2023) 31 Health Care Analysis 16.

64 Global Leaders Group, ‘Pocket Guide for Ministers across Sectors’ (2022). Available at: www.amrleaders.org/resources/m/item/pocket-guide.

66 Guinea – Arrêté A/2021/1238/MS/SGG portant Création, Organisation, Composition et Fonctionnement du Comité National de Pilotage de la Lutte Contre la Résistance aux Antimicrobiens. Available at: https://faolex.fao.org/docs/pdf/gui219519.pdf; Algeria – Décret exécutif n° 17–310 du 4 Safar 1439 correspondant au 24 octobre 2017 portant création, missions, organisation et fonctionnement du comité national multisectoriel de lutte contre la résistance aux antimicrobiens. Available at: https://faolex.fao.org/docs/pdf/Alg172305.pdf.

67 Ecuador – Acuerdo Interinstitucional Nº 1-2020 – Crea el Comité Nacional de Prevención y Control de la Resistencia Antimicrobiana. Available at: https://faolex.fao.org/docs/pdf/ecu196277.pdf.

68 United States of America, ‘Executive Order – Combating Antibiotic-Resistant Bacteria’. Available at: https://faolex.fao.org/docs/pdf/usa176919.pdf.

69 Maren Jeleff, Christian Haddad, and Ruth Kutalek, ‘Between Superimposition and Local Initiatives: Making Sense of ‘implementation gaps’ as a Governance Problem of Antimicrobial Resistance’ (2023) 4 SSM – Qualitative Research in Health 100332. Available at: https://doi.org/10.1016/j.ssmqr.2023.100332.

70 Munkholm and Rubin, ‘The Global Governance of Antimicrobial Resistance’.

71 Stephen J. Hoffman, Reema Bakshi, and Susan Rogers Van Katwyk, ‘How Law Can Help Solve the Collective Action Problem of Antimicrobial Resistance’ (2019) 33(7) Bioethics 798804.

72 See www.qjsamr.org/technical-work/one-health-legislative-assessment-tool-on-amr. See also Ambra Gobena, Carmen Bullon, and Teemu Viinikainen, ‘Regulatory Frameworks to Address Antimicrobial Resistance in the Food and Agriculture Sectors’ (2024) FAO Legislative Study 122.

73 HERA Factsheet, ‘HEALTH UNION: Identifying Top 3 Priority Health Threats’ (8 July 2022). Available at: https://health.ec.europa.eu/publications/hera-factsheet-health-union-identifying-top-3-priority-health-threats_en.

74 ‘Communication from the Commission to the European Parliament, the Council, the European Economic and Social Committee and the Committee of the Regions The European Green Deal’ COM/2019/640 final (2019).

75 It is noteworthy that, in November 2023, the five European Agencies relevant to One Health published the document ‘Cross-Agency Knowledge for One Health Action’, which includes references to AMR. Available at: www.efsa.europa.eu/sites/default/files/2023-11/one-health-2023-joint-statement.pdf.

76 Scott Greer and Holly Jarman, ‘What Is EU Public Health and Why? Explaining the Scope and Organization of Public Health in the European Union’ (2021) 46(1) Journal of Health Politics, Policy Law 2347.

77 Eleanor Brooks and Anniek de Ruijter, ‘Towards More Comprehensive Health Law and Policy Research’ (2021) 16 Health Economics, Policy, and Law 104110.

78 Brooks and de Ruijter, ‘Towards more comprehensive health law and policy research’.

79 Eleanor Brooks, Anniek de Ruijter, and Scott Greer, ‘Covid19 and European Union Health Policy: From Crisis to Collective Action’ in Vanhercke, Spasova, and Fronteddu (eds.) Social Policy in the European Union: State of Play 2020 (ETUI aibsl, Brussels, 2020) 220. Available at: www.etui.org/sites/default/files/2020-12/Social%20policy%20in%20the%20European%20Union%20state%20of%20play%202020-web.pdf.

80 Anniek de Ruijter, EU Health Law and Policy: The Expansion of EU Power in Public Health and Health Care (Oxford University Press, 2019). Cited in Scott Greer and Holly Jarman, ‘What Is EU Public Health and Why? Explaining the Scope and Organization of Public Health in the European Union’ (2021) 46(1) Journal of Health Politics, Policy and Law.

81 Judgment of the Court of Justice of 20 February 1979, Rewe-Zentral AG v. Bundesmonopolverwaltung für Branntwein. Case 120/78. Available at: https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX%3A61978CJ0120.

82 Communication from the Commission on a Community Strategy Against Antimicrobial Resistance, COM/2001/0333 final Volume I, 26 June 2001.

83 Council Recommendation of 15 November 2001 on the Prudent Use of Antimicrobial Agents in Human Medicine, OJ L 34, 5 February 2002, 13.

84 Council Recommendation (2002/77/EC) on the Prudent Use of Antimicrobial Agents in Human Medicine.

85 Council Conclusions on Antimicrobial Resistance (10 June 2008). Available at: www.consilium.europa.eu/uedocs/cms_data/docs/pressdata/en/lsa/101035.pdf.

86 Council Conclusions of 23 November 2009 on Innovative Incentives for Effective Antibiotic, OJ C 302 (12 December 2009) 10.

87 Council Conclusions of 22 June 2012 on the Impact of Antimicrobial Resistance in the Human Health Sector and in the Veterinary Sector – a ‘One Health’ Perspective, OJ C, C/211, 18.07.2012, p. 2, CELEX. Available at: https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:52012XG0718(01).

88 European Parliament Resolution of 12 May 2011 on Antibiotic Resistance. Available at: www.europarl.europa.eu/doceo/document/TA-7-2011-0238_EN.html.

89 European Parliament Resolution of 27 October 2011 on the Public Health Threat of Antimicrobial Resistance. Available at: www.europarl.europa.eu/doceo/document/TA-7-2011-0473_EN.html.

90 European Parliament Resolution of 11 December 2012 on the Microbial Challenge – Rising Threats from Antimicrobial Resistance (2012/2041(INI)). Available at: www.europarl.europa.eu/doceo/document/TA-7-2012-0483_EN.html.

91 European Parliament Resolution of 13 September 2018 on a European One Health Action Plan against Antimicrobial Resistance (AMR) (2017/2254(INI)). Available at: www.europarl.europa.eu/doceo/document/TA-8-2018-0354_EN.html.

92 Commission’s Communication of 29 June 2017 ‘A European One Health Action Plan against AMR’ (the ‘2017 AMR Action Plan’). Available at: https://health.ec.europa.eu/system/files/2020-01/amr_2017_action-plan_0.pdf.

94 European Parliament Resolution on EU Action to Combat Antimicrobial Resistance. 2023/2703(RSP).

95 Overview report: Member States’ One Health National Action Plans against Antimicrobial Resistance (17 November 2022). Available at: https://health.ec.europa.eu/publications/overview-report-member-states-one-health-national-action-plans-against-antimicrobial-resistance_en.

98 Proposal for a Regulation of the European Parliament and of the Council laying down Union procedures for the authorisation and supervision of medicinal products for human use and establishing rules governing the European Medicines Agency, amending Regulation (EC) No. 1394/2007 and Regulation (EU) No. 536/2014 and repealing Regulation (EC) No. 726/2004, Regulation (EC) No. 141/2000 and Regulation (EC) No. 1901/2006 COM/2023/193 final.

99 Proposal for a Directive of the European Parliament and of the Council on the Union Code relating to medicinal products for human use, and repealing Directive 2001/83/EC and Directive 2009/35/EC. COM/2023/192 final.

100 Commission notice – EU Guidelines for the prudent use of antimicrobials in human health. C/2017/4326 OJ C 212 (1 July 2017).

101 Regulation (EU) 2019/6 of the European Parliament and of the Council of 11 December 2018 on veterinary medicinal products and repealing Directive 2001/82/EC (1) and in particular Article 37(4) thereof. OJL4/43 (7 January 2019).

102 Commission Delegated Regulation (EU) 2021/578 of 29 January 2021 supplementing Regulation (EU) 2019/6 of the European Parliament and of the Council with regard to requirements for the collection of data on the volume of sales and on the use of antimicrobial medicinal products in animals OJ L 123, 9.4.2021, 7–20. Also, Commission Implementing Regulation (EU) 2022/209 of 16 February 2022 establishing the format of the data to be collected and reported in order to determine the volume of sales and the use of antimicrobial medicinal products in animals in accordance with Regulation (EU) 2019/6 of the European Parliament and of the Council OJ L 35 (17 February 2022).

103 Commission Delegated Regulation (EU) 2021/1760 of 26 May 2021 supplementing Regulation (EU) 2019/6 of the European Parliament and the Council by establishing the criteria for the designation of antimicrobials to be reserved for the treatment of certain infections in humans. C/2021/3552 OJ L 353 (6 October 2021).

104 Commission Implementing Regulation (EU) 2021/1904 of 29 October 2021 adopting the design of a common logo for the retail of veterinary medicinal products at a distance OJ L 387 (3 November 2021).

105 Regulation (EC) No. 1831/2003 of the European Parliament and of the Council of 22 September 2003 on additives for use in animal nutrition prohibiting the use of antibiotic growth promoters OJ L 268 (18 October 2003) 29.

106 Commission notice – EU Guidelines for the prudent use of antimicrobials in animal health. C/2015/4326 OJ C 299/7 (11 September 2015).

107 Regulation (EU) 2022/839 of the European Parliament and of the Council of 30 May 2022 laying down transitional rules for the packaging and labelling of veterinary medicinal products authorised or registered in accordance with Directive 2001/82/EC or Regulation (EC) No 726/2004 OJ L 148 (31 May 2022) 6–7.

108 Regulation (EU) 2019/4 of the European Parliament and of the Council of 11 December 2018 on the manufacture, placing on the market and use of medicated feed, amending Regulation (EC) No. 183/2005 of the European Parliament and of the Council and repealing Council Directive 90/167/EEC OJ L 4 (7 January 2019) 1–23.

109 Communication from the Commission to the European Parliament, the Council, the European Economic and Social Committee and the Committee of the Regions A Farm to Fork Strategy for a fair, healthy, and environmentally friendly food system. COM/2020/381 final (20 May 2020).

110 Regulation (EC) No. 470/2009 of the European Parliament and of the Council of 6 May 2009 laying down Community procedures for the establishment of residue limits of pharmacologically active substances in foodstuffs of animal origin, repealing Council Regulation (EEC) No. 2377/90 and amending Directive 2001/82/EC of the European Parliament and of the Council and Regulation (EC) No. 726/2004 of the European Parliament and of the Council OJ L 152 (16 June 2009).

112 Directive 2003/99/EC of the European Parliament and of the Council of 17 November 2003 on the monitoring of zoonoses and zoonotic agents, amending Council Decision 90/424/EEC and repealing Council Directive 92/117/EEC OJ L 325 (12 December 2003) 31–40. This Directive is complemented by the Commission implementing decisions on the monitoring and reporting of AMR, including the Commission Implementing Decision (EU) 2020/1729 of 17 November 2020 on the monitoring and reporting of antimicrobial resistance in zoonotic and commensal bacteria and repealing Implementing Decision 2013/652/EU OJ L 387 (19 November 2020) 8–21.

113 Regulation (EU) 2022/2371 of the European Parliament and of the Council of 23 November 2022 on serious cross-border threats to health and repealing Decision No. 1082/2013/EU [2022] OJ L 314/26 (6 December 2022).

114 Directive 2000/60/EC of the European Parliament and of the Council of 23 October 2000 establishing a framework for Community action in the field of water policy OJ L 327 (22 December 2000).

115 Communication from the Commission to the European Parliament, the Council and the European Economic and Social Committee, European Union Strategic Approach to Pharmaceuticals in the Environment. COM (2019) 128 final.

116 Communication from the Commission to the European Parliament, the Council and the European Economic and Social Committee, and the Committee of the Regions Pathway to a Healthy Planet for All EU Action Plan: ‘Towards Zero Pollution for Air, Water and Soil’. COM/2021/400 final/.

117 Proposal for a Directive of the European Parliament and of the Council amending Directive 2000/60/EC establishing a framework for Community action in the field of water policy; Directive 2006/118/EC on the protection of groundwater against pollution and deterioration; and Directive 2008/105/EC on environmental quality standards in the field of water policy. COM (2022) 540 final (26 October 2022). Also, Proposal for a Directive of the European Parliament and of the Council concerning urban wastewater treatment (recast). COM/2022/541 final (26 October 2022).

118 Proposal for a Regulation of the European Parliament and of the Council on nature restoration. COM/2022/304 final (22 June 2022).

119 Regulation (EU) 2016/429 of the European Parliament and of the Council of 9 March 2016 on transmissible animal diseases and amending and repealing certain acts in the area of animal health (‘Animal Health Law’). OJ L 153 (3 May 2021).

120 Policy brief: European Antimicrobial Resistance Surveillance Network in Veterinary Medicine (EARS-VET). Available at: https://eu-jamrai.eu/wp-content/uploads/2021/02/201116_EUJAMRAI_policy-brief_WP7_EARS-Vet.pdf.

121 Regulation (EU) 2016/429. Article 5.3(b)(ii).

122 Footnote Ibid., Article 11.1.(e).

123 Footnote Ibid., Article 12.1.(c)(iv).

124 Regulation (EU) 2021/2115 of the European Parliament and of the Council of 2 December 2021 establishing rules on support for strategic plans to be drawn up by member states under the common agricultural policy (CAP Strategic Plans) and financed by the European Agricultural Guarantee Fund (EAGF) and by the (EAFRD) and repealing Regulations (EU) No. 1305/2013 and (EU) No. 1307/2013. OJ L 435 (6 December 2021).

125 Regulation (EU) 2021/522 of the European Parliament and of the Council of 24 March 2021 establishing a Programme for the Union’s action in the field of health (‘EU4Health Programme’) for the period 2021–2027, and repealing Regulation (EU) No. 282/2014. OJ L 107 (26 March 2021).

126 Regulation (EU) 2021/695 of the European Parliament and of the Council of 28 April 2021 establishing Horizon Europe – the Framework Programme for Research and Innovation, laying down its rules for participation and dissemination, and repealing Regulations (EU) No. 1290/2013 and (EU) No. 1291/2013 OJ L 170 (12 May 2021).

127 See for example, the proposals advanced by Negri and Eccleston-Turner concerning the application of the AMR pilot experience to the prevention of and response to zoonoses with pandemic potential, in Stefania Negri and Mark Eccleston-Turner, ‘One Health and Pathogen Sharing: Filling the Gap in the International Health Regulations to Strengthen Global Pandemic Preparedness and Response’ (2022) 19(1) International Organizations Law Review 188214 (Special Issue ‘Reforming the International Health Regulations’ with guest editors Gian Luca Burci, Lisa Forman, and Steven J. Hoffman).

128 One Health High-Level Expert Panel (OHHLEP), ‘One Health: A New Definition for a Sustainable and Healthy Future’.

129 Si Ruishi, Yumeng Yao, Xin Liu, Qian Lu, and Mingyue Liu, ‘Role of Risk Perception and Government Regulation in Reducing Over-Utilization of Veterinary Antibiotics: Evidence from Hog Farmers of China’ (2022) 15 One Health 100448. Maria Paula and David Demeritt, ‘Paperwork and the Decoupling of Audit and Animal Welfare: The Challenges of Materiality for Better Regulation’ (2017) 35 Environment and Planning C: Politics and Space 169190.

Figure 0

Figure 8.1 Proposed One Health three-dimensional framework for moral concernFigure 8.1 long description.

Figure 1

Table 10.1 Key Differentiating Elements between the One Health, Eco Health and Planetary Health Frameworks

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