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9 - The One Health Approach and the Tackling of Drivers of Environmental Degradation

The Case of the EU Deforestation-Free Products Regulation

from 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

Summary

The adoption of the Deforestation-free Products Regulation represents a significant step forward in the protection of forests, both in the EU and in non-EU countries. In particular, it aims at minimising the risk of deforestation and forest degradation associated with products that contain, have been fed with, or have been made using certain commodities (cattle, cocoa, coffee, oil palm, rubber, soya, and wood). Environmental protection is achieved through provisions affecting the placing and making available of and export from the EU market of the relevant products, including a due diligence framework to ensure that such commodities are deforestation-free and legal under the law of the country of origin. While the Regulation has a clear environmental goal, it could also be seen as an operationalisation of the One Health approach as it tackles several drivers of environmental degradation (land-use change, biodiversity decline, and GHG emissions/climate change). In particular, this Regulation makes for a noteworthy case study in light of its extraterritorial reach, and it is examined in view of the unacknowledged ramifications for the One Health.

Information

Type
Chapter
Information
The Cambridge Handbook of One Health and the Law
Existing Frameworks, Intersections and Future Pathways
, pp. 123 - 138
Publisher: Cambridge University Press
Print publication year: 2025

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.

Footnotes

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.

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