Abstract
The European Union's asylum and international protection framework remains largely silent on displacement caused by environmental factors. Despite the growing reality of environmentally induced displacement, no binding legal instrument within EU law recognises or protects those forced to move due to environmental harm. Drawing on an analysis of the Common European Asylum System, the Charter of Fundamental Rights, EU founding treaties, and international environmental and human rights law, this article addresses the resulting protection gap and argues that this omission runs counter to the EU's Treaty principles, its human rights obligations, and its environmental commitments. The article demonstrates that the exclusion of environmentally displaced persons stems not from isolated omissions but from the structural fragmentation of EU legal regimes and the resulting policy inertia, the persistent inability to translate normative commitments into operational protection. The absence of legal recognition leaves affected individuals in a position of extreme vulnerability, with no access to territory, asylum procedures, or protection from refoulement. Moreover, this gap undermines the EU's legal consistency, violates the principle of solidarity among Member States, and diminishes the Union's credibility on the international stage. The article concludes that the EU faces a fundamental normative choice: either to establish a binding rights-based framework for environmentally displaced persons or to perpetuate a structural protection gap that excludes those most severely affected by environmental degradation from the scope of legal protection.
Keywords
Introduction
Environmental degradation and climate change are no longer distant threats but immediate drivers of human displacement. 1 Yet, the legal frameworks governing asylum and international protection remain largely anchored in traditional, non-environmental paradigms. 2 This disconnect has produced a critical normative protection gap: individuals forced to move due to environmental factors continue to fall outside the scope of existing international and regional protection regimes. 3 Within the European Union (EU), a self-proclaimed leader in climate action and human rights, 4 this omission reveals a profound tension between normative commitments and legal practice. Understanding the structural origins of this gap is therefore essential. This article argues that the EU's current legal architecture—comprising asylum and international protection law, human rights law, and environmental law—structurally excludes environmentally displaced persons (EDPs) due to its structural fragmentation and functional misalignment across legal regimes.
The core difficulty lies less in the existence of relevant norms than in their structural fragmentation and functional misalignment across EU legal domains. Fragmentation manifests in the operation of these regimes in silos, each governed by distinct criteria, procedures, and institutional logics: asylum and international protection law requires individualised persecution —a term traditionally linked to state action 5 but which this article argues should be reinterpreted to include severe environmental harm that renders return impossible—by a state 6 or state-like actor; 7 human rights law demands an imminent, serious threat to life or dignity attributable to a state's act or omission; 8 environmental law prioritises resource conservation, pollution control, and in situ adaptation over human displacement. 9 Misalignment, meanwhile, denotes the failure of these regimes’ goals and thresholds to converge or complement one another. Consequently, no single regime claims competence over EDPs, and the gaps between regimes foreclose protection altogether.
In this regard, this article adopts the term ‘EDPs’ to refer to individuals compelled to leave their habitual place of residence due to environmental degradation, including climate change, desertification, sea-level rise, and extreme weather events. The term is preferred for its descriptive precision and inclusiveness, capturing a broad spectrum of environmental drivers, including geological disasters and environmental degradation, while avoiding the legal inaccuracies associated with labels such as ‘climate refugees’ under Article 1A of the 1951 Geneva Convention Relating to the Status of Refugees 10 and its 1967 Protocol. 11 In this article, climate change is understood as one dimension of wider environmental degradation rather than as a distinct conceptual category. 12
To understand the origins of this contradiction, it is first necessary to delineate the contours of the EU's protection framework. However, a purely descriptive account remains insufficient, as it does not capture how these legal regimes interact in practice when confronted with environmentally induced displacement. The core difficulty lies less in the existence of relevant norms than in their functional separation and uneven articulation across different areas of EU law.
Although frequently treated as a coherent body of law, EU protection obligations in fact emerge from several distinct but interconnected legal regimes that collectively structure access to international protection. The Common European Asylum System (CEAS) 13 forms the central pillar, establishing the criteria and procedures governing refugee status and subsidiary protection. This secondary law framework operates within the broader constitutional structure of the EU, grounded in primary law—the Treaty on European Union (TEU) 14 and the Treaty on the Functioning of the European Union (TFEU) 15 —which enshrine foundational principles such as human dignity, solidarity, and respect for fundamental rights. These commitments are further reinforced by the Charter of Fundamental Rights of the European Union (CFR) 16 and by international human rights instruments binding upon Member States. Alongside these regimes, EU environmental and climate law, as well as international climate obligations such as the Paris Agreement, 17 establish an additional normative layer addressing environmental protection. Taken together, these regimes form a complex but internally differentiated structure governing protection within the EU legal order.
Yet, even when considered in its full normative scope, this structure reveals a deeper systemic misalignment. The EU legal framework for asylum and international protection remains anchored in a logic historically designed around persecution and state responsibility, reflecting the post-World War II origins of international refugee law. 18 Within this paradigm, environmental harm does not constitute an autonomous ground for protection under EU law. While this does not diminish the continued centrality of persecution-based protection within the CEAS, it exposes the framework's structural limitations in responding to the evolving and increasingly diversified drivers of forced displacement.
These limitations have become more pronounced given the growing scale, frequency, and intensity of environmental degradation and climate-related events, which generate forms of displacement that fall outside existing legal categories. As a result, affected individuals often remain in a protection limbo, while Member States operate without a coherent legal framework capable of addressing these movements systematically. The resulting exclusion is therefore not merely classificatory but structural, reflecting the inability of existing protection regimes to accommodate forms of harm that do not conform to established legal paradigms.
This conceptual disjunction underpins what this article conceptualises as ‘policy inertia’: the structural inability of EU institutions to translate existing legal principles into operational protection 19 for EDPs. Unlike persecution-based claims, environmental harm is typically characterised by diffuse causality, the absence of a singular responsible actor, and cumulative or slow-onset processes. 20 These characteristics sit uneasily with the conceptual foundations of both refugee status and subsidiary protection, which remain largely predicated on identifiable agents of harm and discrete acts triggering a well-founded fear of persecution or serious harm. This inertia stems not from a lack of normative resources but from the fragmentation of the EU protection framework and the absence of an explicit bridging logic between environmental governance and asylum law.
A further conceptual clarification is necessary. In this analysis, ‘protection’ operates on two interrelated levels: formal legal recognition under the EU asylum and international protection framework, which includes refugee status and subsidiary protection, and a wider normative framework grounded in fundamental rights derived from EU law, international human rights law, and international environmental law. This distinction is analytically significant, because without formal recognition, the practical effectiveness of the second, rights-based framework is severely undermined within the EU legal order.
Building on this foundation, the article advances a rights-based approach to protection—understood as enforceable individual entitlements rather than discretionary policy responses. This would require a binding legal framework establishing a specific protection status for EDPs, with procedural safeguards and substantive rights derived from the CFR and international human rights norms. This approach also engages the principle of European solidarity, requiring fair burden-sharing among Member States.
Methodologically, this article proceeds in two main steps. Section One examines the EU's internal legal framework governing asylum and international protection, identifying structural gaps that prevent the accommodation of environmentally induced displacement, and assessing their incompatibility with EU treaty obligations and fundamental rights guarantees under the CFR. Section Two shifts to the EU's external legal obligations under international environmental and human rights law, evaluating whether the EU's regulatory silence engages its international responsibility, particularly toward affected populations in the Global South.
Against the backdrop of accelerating environmental degradation, the EU faces a fundamental normative choice: either to translate its commitments to human rights, climate leadership, and solidarity into a coherent rights-based framework for EDPs, or to perpetuate a structural protection gap that systematically excludes those most affected by environmental harm from the scope of legal protection.
Identifying the gaps in the EU legal framework
This section examines the legal and policy limitations of the EU's response to environmental displacement. It first situates the issue within the EU asylum and international protection framework before identifying structural gaps in the CEAS that exclude EDPs from existing protection mechanisms. It then considers the implications of this exclusion in light of the EU Treaties and the CFR, alongside the Union's broader international commitments.
A preliminary clarification is necessary. The analysis distinguishes between the recognition of environmental displacement in EU policy discourse—increasingly visible in strategies and communications—and its legal operationalisation within binding instruments, which remains absent. This disjunction structures the present inquiry. Against this background, the section proceeds in three steps. The first subsection examines the CEAS and the legal gap on environmental displacement. The second subsection traces the consequences of this gap, including fragmentation among Member States and the violation of solidarity. The third subsection then assesses the legal incompatibility of this gap with EU treaty obligations, environmental commitments, and fundamental rights protection under the CFR.
The CEAS and the legal gap on environmental displacement
Building on the introduction's analysis of the EU's fragmented legal architecture, this subsection examines how the CEAS operationally excludes those displaced by environmental factors.
The CEAS is the EU's harmonised framework for asylum and international protection, established to ensure that Member States apply common standards for determining who qualifies for protection and what rights they receive. It consists of several legislative instruments, including the Qualification Directive (2011/95/EU), 21 the Asylum Procedures Directive (2013/32/EU), 22 the Reception Conditions Directive (2013/33/EU), and the Temporary Protection Directive (2001/55/EC). The CEAS remains firmly anchored in the normative framework of the 1951 Geneva Convention Relating to the Status of Refugees, which circumscribes refugee status through a persecution-based paradigm tied to specific grounds—namely, race, religion, nationality, political opinion, or membership of a particular social group, 23 resulting in a definition that remains inherently narrow in scope. 24 Environmentally induced displacement falls outside the scope of legal recognition. 25 Crucially, the absence of any binding international instrument defining or protecting EDPs has direct implications for EU law: it deprives the Union of an external normative catalyst for reform, thereby entrenching policy inertia and perpetuating the systemic exclusion identified in this article.
Within the EU, the CEAS operationalises international refugee law while adding a broader category of ‘international protection’—a set of complementary regimes extending safety to persons who do not meet the refugee definition but would face serious harm if returned. The Qualification Directive defines the criteria for both refugee status 26 and subsidiary protection 27 —the latter being a status for those facing a real risk of serious harm, namely torture, inhuman or degrading treatment, or serious threats arising from armed conflict. Environmental factors are not included among the grounds of serious harm. 28 This omission reflects a structural inability to adapt inherited legal categories to new forms of displacement.
Even in situations involving sudden or large-scale displacement, conditions under which the EU's response might be expected to function most effectively, the EU's existing mechanisms are still poorly equipped to handle environmental displacement. For example, the Temporary Protection Directive (TPD) 29 was created to offer immediate, short-term relief in cases of mass influx, providing a legal framework for temporary protection without requiring individual asylum applications. 30 However, despite its potential applicability, the directive has never been used to assist EDPs. One major limitation is that activating the TPD requires the formal decision of the EU Council, making it a political rather than an automatic response. 31 Additionally, the directive is designed primarily for short-term crises, such as armed conflicts or sudden political upheavals. Environmental displacement, on the other hand, often involves longer-term or even permanent displacement, as climate change and environmental degradation tend to unfold over extended periods. 32 This mismatch means that the TPD is not a practical solution for EDPs. The inapplicability of the TPD further illustrates the EU's policy inertia: although a flexible instrument exists in principle, its design, scope, and activation mechanisms remain anchored in traditional crisis scenarios, thereby preventing its extension to environmental displacement.
From legal gap to fragmentation
Even the EU's newest policy instruments fail to close the legal gap. The recently adopted New Pact on Migration and Asylum, 33 while proposing a more coordinated approach to ‘migration governance’ 34 and acknowledging climate-induced displacement in its policy discourse, does not create a legal status or concrete protection pathways for EDPs.
This omission reflects broader systemic deficiencies, insofar as neither EU lex primaria, namely the TEU and TFEU, nor EU lex secundaria, encompassing regulations and directives such as the CEAS instruments, provides any explicit provisions addressing environmental displacement. Consequently, it reinforces the pattern of policy inertia identified in this article, whereby institutional recognition of environmental displacement at the policy level fails to translate into binding legal innovation within the EU protection framework.
Such a gap is perhaps unsurprising, given the absence of any binding international framework defining EDPs or affording them specific protection. 35 Nevertheless, this absence reflects a clear legal and normative gap at the Union level, constituting a dual deficiency: first, a legal gap, namely the absence of binding rules conferring rights or status upon EDPs; and second, a normative gap, namely the absence of shared legal principles or standards to guide Member States’ responses.
This gap has a dual impact on EDPs and Member States. It sustains policy inertia by reducing incentives for institutional adaptation, allowing existing legal categories to persist despite their evident inadequacy. For EDPs, this may limit or entirely preclude access to protection, leaving them without clear legal recourse. For Member States, it generates uncertainty and leads to inconsistent, fragmented responses due to the lack of a unified EU framework.
Two consequences follow from this gap: at one end, the denial of protection for EDPs; at the other, the fragmentation of policy across Member States. Between these two outcomes, no stable, rights-based EU response to environmental displacement emerges. This fragmentation is reflected in unequal treatment across the EU, where some states offer temporary protection or humanitarian visas while others deny entry altogether, resorting instead to ad hoc and discretionary decision-making. Such fragmentation is not merely a coordination failure but a manifestation of policy inertia, insofar as the EU has not mobilised its legislative competences to replace divergent national responses with a coherent and harmonised framework.
While some EU Member States have attempted piecemeal solutions, introducing—or subsequently withdrawing—temporary protection measures for EDPs, 36 these fragmented national responses only highlight the broader lack of coherence in EU law. Despite these national efforts, the EU's current legal and policy frameworks remain inadequate to address the growing challenges of displacement driven by environmental and climate crises. Furthermore, the absence of a legal framework for environmental displacement hinders the EU's ability to anticipate and manage large-scale migration driven by environmental factors. Without a proactive and coordinated approach, the EU risks being unprepared for the scale of displacement caused by environmental degradation. This lack of coordination exacerbates existing disparities, as the burden falls disproportionately on individual Member States, particularly those most affected by climate-related migration.
Mediterranean EU Member States such as Greece, Italy, and Spain 37 share a set of pre-existing vulnerabilities: structural, geographic, and economic conditions that intensify the effects of climate change. As a result, they are already under considerable strain from rising sea levels, desertification, 38 and increasing migration flows. In the event of large-scale environmental displacement triggered by severe droughts, coastal erosion, extreme weather events, water scarcity, land degradation, or food insecurity in Africa 39 or the Middle East, 40 these countries would likely face an even greater challenge.
This situation of fragmented national responses, lack of coordination at the EU level, and disproportionate pressure on frontline Member States not only hinders the EU's ability to adopt a cohesive and effective response but also leads to an inequitable distribution of responsibilities and resources, directly contradicting the principle of solidarity enshrined in EU law.
The principle of solidarity is found in multiple treaty provisions: Article 2 TEU lists solidarity as a foundational value; Article 3(3) TEU mandates the EU to promote solidarity among Member States, and Article 80 TFEU explicitly provides that EU policies on border checks, asylum, and immigration shall be governed by the principle of solidarity and fair sharing of responsibility, including its financial implications. Accordingly, a harmonised EU-wide response, encompassing financial and logistical assistance, is imperative to prevent any single Member State from bearing a disproportionate share of the crisis's repercussions.
While these challenges persist, there are signs of progress at the EU level. The Union has increasingly acknowledged through policy discourse and non-binding instruments the urgent need to respond to this emerging category of displacement, signalling a gradual, though insufficient, shift toward engagement. The insufficiency of this shift lies in the fact that these acknowledgements have not translated into binding legal measures. Specifically, no legislative proposal has been adopted that would create a protection status for EDPs, no directive has been amended to include environmental grounds for protection, and no binding instrument requires Member States to recognise EDPs. The EU remains at the level of policy discourse and non-binding resolutions, which lack enforceability and justiciable rights for individuals. This reliance on soft law further exemplifies policy inertia: while discursive recognition of environmental displacement has evolved, it has not been accompanied by the adoption of binding legal measures capable of altering the structure of protection.
This recognition is not entirely new. European institutions first acknowledged the link between environmental factors and migration in 1999, when a European Parliament resolution highlighted ‘environmental refugees’ as a major humanitarian crisis with implications for the stability and security of the affected countries, including those within the EU. 41
Over the following decades, this initial recognition slowly translated into broader policy frameworks, though often indirectly or as a secondary consideration. The EU's policy evolution on this issue has been incremental, but increment without legislative action does not suffice to create binding obligations.
The Global Approach to Migration and Mobility 42 constituted an early acknowledgement of environmental degradation as a structural driver of displacement, framing multilateral cooperation as a necessary response. Subsequent initiatives further developed this link: while the European Green Deal 43 primarily advanced mitigation objectives, its provisions on adaptation and resilience implicitly acknowledged displacement risks.
A pivotal moment came in 2019 with the European Parliament's resolution on climate change and migration, which explicitly called for enhanced protections for climate-displaced persons and formalised legal pathways. 44 This trajectory continued with the EU Adaptation Strategy, which further crystallised this linkage by explicitly integrating human mobility 45 into climate adaptation governance and advocating anticipatory measures to mitigate displacement. 46
Despite these engagements, the EU asylum and international protection framework does not currently regulate the definition, acquisition, 47 or protection rights of EDPs. Articles 77 to 80 TFEU provide a potential legal basis for EU action on EDPs. Article 78(2) TFEU explicitly authorises the European Parliament and the Council to adopt measures for a uniform status of refugee and subsidiary protection. Article 78(3) TFEU allows for provisional measures in the event of a sudden inflow of third-country nationals. Article 79(2) TFEU authorises measures to combat illegal immigration. Article 80 TFEU enshrines the principle of solidarity and fair sharing of responsibility. Taken together, these provisions confer legislative competence on the EU to adopt binding instruments that could recognise EDPs and establish protection pathways.
However, the absence of binding obligations – meaning no EU regulation or directive has been adopted pursuant to these articles specifically addressing environmental displacement – leaves EDPs in a state of legal limbo. They remain excluded from existing frameworks, including the CEAS, reinforcing the earlier analysis of the gaps in the current legal framework.
The foundational principles of solidarity, human rights, and global responsibility are directly implicated by this failure, as discussed in detail in the following subsection with reference to Article 2 TEU, Article 3(3) TEU, and Article 21 TEU, and in the next section in relation to international environmental and human rights law.
The consequences of this inaction are stark. The EU's reliance on non-binding instruments, while indicative of its acknowledgement of the issue, highlights a significant disjunction between recognition and substantive action. In practice, the absence of enforceable legal measures renders the EU's commitments largely aspirational, lacking the requisite mechanisms to ensure implementation. This deficiency not only exposes systemic shortcomings but also raises pertinent questions regarding the Union's adherence to its own foundational commitments.
Legal incompatibility with EU commitments
This subsection examines how the EU's inaction regarding EDPs—reflected in both the absence of legal recognition and the lack of effective protection—sits uneasily with its treaty obligations, environmental commitments, and human rights guarantees. Building on the legal gap identified above, it argues that the absence of a coherent EU legal framework may amount to a breach of binding commitments under the TEU, TFEU, and the CFR. This inconsistency manifests in two interrelated domains: the EU's treaty and environmental obligations on one hand and its fundamental rights commitments under the CFR on the other.
Treaty and environmental obligations
The EU is bound by its foundational treaties, including TEU, TFEU, and CFR, 48 which collectively enshrine commitments to the protection of human rights, sustainable development, and environmental protection.
Article 2 TEU expressly enumerates the values of respect for human dignity and equality.
It identifies solidarity as a value, but the principle of solidarity imposes a legal obligation derived from Article 3(3) TEU and the general principles of EU law on the EU and its Member States to address transboundary challenges collectively, 49 a mandate that logically encompasses environmental displacement.
This obligation is further reinforced by Article 3(3) TEU, which imposes a binding duty on the EU to ‘promote… economic, social and territorial cohesion, and solidarity among Member States.’ The imperative term ‘shall’ establishes a positive legal obligation requiring EU institutions to take concrete measures. 50
In the context of environmental displacement, given the disparate exposure of Member States to environmental-induced displacement pressures, the current framework risks creating asymmetrical burdens in the allocation of responsibility across national asylum and international protection systems. Such imbalances contravene the principle of solidarity under Article 3(3) TEU, which mandates equitable burden-sharing and collective action to preserve cohesion. 51
Consequently, the EU is legally compelled to adopt a coordinated, Union-wide response encompassing both legal harmonisation and policy coordination. This includes harmonisation through binding instruments such as directives and regulations establishing uniform standards for EDP protection, as well as non-binding coordination mechanisms, including guidelines, recommendations, and financial instruments. Non-compliance may give rise to infringement proceedings under Article 258 TFEU against Member States that fail to act and to judicial review before the Court of Justice of the European Union (CJEU) for breaches of Treaty obligations.
Importantly, this obligation of coordinated action also requires that such measures be internally consistent across EU policy fields, thereby bringing into focus the broader requirement of policy consistency as a structural feature of Union governance. This requirement, often referred to in doctrine as coherence, is distinct from the principle of solidarity, although the two are related. It refers to the obligation, reflected in Article 7 TFEU, for the Union to ensure consistency between its different policies and activities. While cohesion under Article 3 TEU focuses on equitable burden-sharing among Member States, coherence under Article 7 TFEU is understood as requiring that different policy areas, including environment, asylum, and migration, are developed and implemented in a manner that avoids mutually contradictory objectives or outcomes.
The relationship between the two is that coherence in policy outcomes supports cohesion among Member States: inconsistent policies lead to unequal burdens. This connection becomes particularly relevant when read in conjunction with Article 77 TFEU, which governs border checks, asylum, and immigration. 52 Article 77(1)(c) TFEU calls for ‘the gradual establishment of an integrated management system for external borders’, a framework that could accommodate environmental displacement scenarios by, for example, creating expedited or differentiated entry procedures for persons displaced by environmental disasters, as the provision does not limit the scope of border management to existing categories of displaced persons.
Moreover, Article 77(2)(b) TFEU allows for the adoption of measures relating to ‘the checks to which persons crossing external borders are subject,’ thus opening the possibility for differentiated procedures for persons displaced by environmental factors. This is because it authorises the EU legislature, through the ordinary legislative procedure, to determine what checks apply to which categories of persons; nothing in the text prevents the creation of a distinct procedural category for EDPs, such as simplified border checks or humanitarian entry permits. Additionally, Article 77(2)(d) TFEU authorises ‘any measure necessary for the gradual establishment of an integrated management system for external borders’, granting the Union flexibility to adapt its border and asylum and international protection framework to emerging challenges, including environmental migration.
While these provisions offer a legal basis for action, their potential remains untapped because the EU has not exercised its legislative competence under these articles to adopt specific measures for EDPs – a gap that becomes even more apparent when examining the EU's broader environmental and human rights obligations, as discussed in the next section. This disconnect leads directly to the second dimension.
Turning to environmental commitments, while Articles 191–194 TFEU do not explicitly address environmental displacement, systematic interpretation—reading environmental objectives together with EU human rights and solidarity obligations—implies an obligation to mitigate its human consequences. However, this implied obligation has not been operationalised: the absence of a dedicated framework creates a normative gap, as the EU's environmental acquis is predicated on preventing harm but fails to extend this logic to protecting displaced individuals. The existing legal order provides no pathway from environmental protection to displacement protection without legislative intervention. This gap becomes even more apparent when examining the preventive logic of the EU's environmental acquis.
The Union's environmental acquis, the body of EU environmental law, is predicated on a preventive logic. This logic focuses on avoiding environmental harm before it occurs through emission limits, impact assessments, and precautionary measures, yet it fails to extend this logic to the protection of individuals displaced by the very harms it seeks to regulate. This constitutes a paradoxical disconnect: while the EU legislates extensively to reduce environmental degradation, it neglects the most acute human ramifications. The treaties impose an obligation to combat climate change through three instruments: Article 191(1) TFEU, which lists climate change mitigation as a Union objective; the EU's ratification of the Paris Agreement, binding on the EU under Article 216 TFEU; and the European Green Deal, which operationalises these Treaty commitments. The ramifications of this gap extend directly into fundamental rights law, which forms the second dimension.
Fundamental rights
The relationship between CFR rights and EDPs requires careful specification. The preceding subsection has already established the existence of a ‘legal gap’, defined as the absence of binding EU rules conferring rights or status upon EDPs. The analysis here focuses on the consequences that flow from it. The CFR enshrines rights to dignity, 53 life, 54 integrity of the person, 55 and non-discrimination. 56 The legislative gap produces distinct and justiciable violations of the CFR. First, the right to life under Article 2 is engaged where return to an environmentally degraded country of origin would expose the individual to life-threatening harm, such as extreme food insecurity or lack of potable water. Whether return violates Article 2 CFR depends on the severity of environmental harm in the country of origin. Drawing on CJEU case law on subsidiary protection, notably Case Elgafaji (2009), the Court's reasoning on Article 15(c) of the Qualification Directive indicates that a ‘serious and individual threat’ arises where generalised conditions create a real risk to life or person (paras. 43–45). 57 Applied by analogy to environmental harm, this suggests that only extreme situations such as severe desertification, total crop failure, or complete lack of access to potable water could meet the threshold of life-threatening harm. The lack of any protection status for EDPs means that return remains legally permissible under EU law unless such exceptional thresholds are reached, thereby enabling a potential violation of Article 2 CFR.
Second, the right to dignity and the prohibition of inhuman or degrading treatment 58 are implicated where EDPs are left without any legal status, documentation, housing, or healthcare—conditions the CJEU has consistently held to constitute degrading treatment. Third, the right to non-discrimination is violated where EDPs are treated less favourably than refugees or beneficiaries of subsidiary protection without objective justification, given that environmental displacement is no less involuntary than persecution. The EU's failure to address environmental displacement thus risks violating its fundamental rights obligations under the CFR in a manner that is distinct from the general gap identified above: here, the violation is not merely the absence of a rule but the concrete, justiciable harm that absence produces for identifiable individuals. The absence of a legal framework for EDPs does not simply represent a policy gap; it risks violating the EU's constitutional obligations regarding environmental sustainability and fundamental rights. These obligations are firmly established under the TEU, Articles 2 and 3; the TFEU, Articles 191 and 192; and the CFR, notably Article 37 on environmental protection, together with Articles 1, 2, 3, 6, and 7 on fundamental rights.
EU responsibility and accountability for environmental displacement
Building on the identification of internal legal and normative gaps, this section shifts the analysis outward to assess the EU's position under international law, with particular attention to affected populations in the Global South. The central question is whether the EU's inaction on environmental displacement engages its international responsibility vis-à-vis these populations, and if so, under what conditions this responsibility may give rise to accountability.
A preliminary conceptual clarification is required. In this article, ‘responsibility’ refers to the existence of a primary legal obligation—that is, a duty to act arising from treaties, customary international law, or general principles of law. 59 By contrast, ‘accountability’ concerns the secondary legal consequences that follow from a breach of such an obligation. 60 The distinction is not merely semantic: the EU may be under a legal responsibility to address environmental displacement without yet being held accountable, as accountability presupposes the additional elements of breach, attribution, and harm.
The EU's obligations in this field derive from its dual character as both an autonomous legal order and an international actor. 61 On the one hand, Article 21 TEU requires the Union to ensure that its external action is guided by and consistent with international law, including human rights protection and environmental sustainability. On the other hand, the EU is bound by international obligations arising from treaties it has concluded—such as the Paris Agreement—as well as from customary international law, which consists of general and consistent state practice accepted as legally binding (opinio juris). These sources impose duties not only to mitigate environmental harm but also to prevent and address its foreseeable human consequences, including displacement.
Against this background, this section examines the EU's responsibility under two complementary legal regimes. The first subsection addresses international environmental law, while the second subsection focuses on international human rights law. Though analytically distinct, these frameworks converge in suggesting that the EU cannot remain legally neutral in the face of environmental displacement. The following subsections assess the extent to which these bodies of law establish binding obligations and whether the EU's current inaction may ultimately engage its accountability under international law.
The EU'S responsibility under international environmental law
The EU, together with its Member States, is a major historical contributor to global environmental degradation through industrialisation, 62 colonialism, 63 unsustainable resource extraction, 64 and consumption patterns and therefore bears a legal responsibility to address the consequences of its actions. This includes, among other measures related to mitigating adverse effects, the establishment of a robust legal framework to address environmental displacement and ensure accountability for past actions and the harm caused. While this responsibility is not explicitly codified in a single legal instrument, it can be inferred from a plurality of frameworks that impose obligations on the EU to address environmental degradation, including climate change and its cascading effects.
Treaty, COP decisions, and EU implementation
The EU's commitments under international environmental law, including the United Nations Framework Convention on Climate Change (UNFCCC) 65 and its legally binding implementing agreement, the Paris Agreement, 66 provide an indirect normative framework for addressing environmental displacement. While neither treaty explicitly mentions ‘environmental displacement’ or ‘climate displacement’, several decisions adopted under the Conference of the Parties, or COP, do. Notably, COP16 Decision 1/CP.16, para 14(f), 67 recognises the need to consider ‘measures to enhance understanding, coordination and cooperation with regard to climate change-induced displacement, migration and planned relocation.’
This was reaffirmed at COP21 in Paris in 2015, which established the Task Force on Displacement under the Warsaw International Mechanism for Loss and Damage to develop recommendations on climate-related displacement, a category of environmental displacement that the Paris Agreement explicitly addresses. 68 Both the adaptation and loss and damage dimensions of the Paris Agreement are directly relevant to environmental displacement: adaptation measures address displacement by strengthening in situ resilience, while loss and damage mechanisms address displacement as an unavoidable consequence when adaptation fails. Together, they capture the full cycle of climate-induced movement.
These COP decisions do not create binding obligations in the treaty sense but are interpretive instruments that inform the implementation of the Paris Agreement, especially in its adaptation and loss and damage dimensions. In this way, together they suggest a policy framework through which the EU's responsibility to address displacement may be inferred. These developments support the view that an emerging normative expectation exists under international climate law 69 for developed countries, including EU Member States, to address climate-induced displacement. 70
The Paris Agreement requires all Parties to submit Nationally Determined Contributions (NDCs) reflecting their highest possible ambition in mitigation and adaptation. However, an examination of the EU's 2020 NDC reveals no explicit reference to climate-related displacement. This omission highlights the absence of a structured and explicit approach to displacement within EU climate planning. 71 From a doctrinal perspective, this gap also reflects policy inertia, as climate governance frameworks fail to integrate displacement despite its recognition within international climate and environmental discourse.
Such an absence does not imply that NDCs should regulate cross-border displacement into the EU; rather, they should acknowledge climate-induced displacement as a critical adaptation and loss and damage challenge. This applies both internally within the EU 72 and externally in the context of international cooperation with third countries affected by climate impacts.
The EU already possesses a range of financial instruments capable of addressing these challenges, including the Green Climate Fund, 73 the Adaptation Fund, 74 and internal budgetary tools such as the Neighbourhood, Development and International Cooperation Instrument (NDICI)–Global Europe. 75 These mechanisms could be further mobilised or expanded to support EDPs within the EU's jurisdiction, for example through funding resettlement programmes, legal assistance, housing, healthcare, and livelihood support, framed within adaptation and loss and damage strategies. Such an approach aligns with COP Decision 1/CP.16 and the work of the Task Force on Displacement, as well as Article 7 of the Paris Agreement, which emphasises resilience-building and vulnerability reduction. These objectives are undermined when displaced persons lack adequate protection and support.
Nevertheless, the absence of displacement considerations in EU NDCs reveals a broader structural gap: existing climate instruments offer financial and strategic tools but fail to provide concrete legal protections for individuals affected by climate-induced displacement. Addressing this deficiency requires more than interpretive obligations—it demands the creation of a dedicated legal framework within the EU to operationalise commitments. 76 Such a framework would establish enforceable rights and procedures for EDPs, including temporary protection status, residence permits, climate-adapted asylum procedures, or a specific legal status for climate-displaced persons. This instrument could take the form of an EU directive or regulation that (1) defines EDPs and/or related categories; (2) establishes rights related to residence, employment, social protection, and family unity; (3) allocates responsibilities and funding among Member States; and (4) introduces monitoring and accountability mechanisms. This would transform indirect, interpretive commitments into enforceable legal protections.
Customary principles and state responsibility
The EU's responsibility to address environmental displacement finds direct normative support in customary international law, independent of the treaty and COP-based framework discussed above in the preceding subsection. It is not an explicitly codified treaty obligation but rather a legal conclusion drawn from the EU's duty to act in good faith in implementing its climate commitments and its responsibility to prevent harm within its jurisdiction and control.
The Rio Declaration, 77 while not a binding treaty, provides evidence of state practice and opinio juris relevant to principles that have, at least in part, crystallised into customary international law, particularly the polluter-pays principle. Soft law may also provide more immediate evidence of international support and consensus than a treaty. 78 Its invocation here is not to assert a direct legal obligationbut to support the normative foundation of customary rules binding on the EU. Although the precise customary status of the principle remains contested at the global level, 79 it nonetheless reinforces the expectation that the EU, as a major historical contributor to environmental degradation, should bear the financial costs of mitigation, including those arising from displacement. 80
It is necessary here to distinguish the normative weight of the principles invoked. The no-harm principle is widely regarded as customary international law and therefore binding on states and, increasingly, on international organisations such as the EU. 81 By contrast, the polluter-pays principle, although firmly embedded in EU law and Organisation for Economic Co-operation and Development practice and reflected in instruments such as the Kyoto Protocol, 82 has a more contested status in general customary international law. While the Rio Declaration is formally soft law, it has contributed to the crystallisation of certain principles into customary norms through consistent state practice and opinio juris. This distinction is important: the no-harm principle provides the strongest customary basis for deriving binding obligations, whereas the polluter-pays principle reinforces the normative and policy framework guiding EU climate responsibility without yet constituting a universally binding rule.
Building on this normative foundation, the polluter-pays principle further reinforces the expectation that the EU should bear the costs of mitigating environmental damage, including its displacement effects. In this sense, it extends the broader logic of responsibility beyond prevention alone, linking environmental harm to financial accountability for its consequences.
Together, these principles suggest a dual obligation for the EU: preventing harm and remedying its consequences. This combined reading supports the view that responsibility under environmental law is not limited to ex ante prevention but also extends to post facto remedial action, including responses to displacement linked to environmental degradation. 83
Crucially, the polluter-pays principle and the law of state responsibility operate in a complementary rather than parallel manner. The polluter-pays principle supplies a substantive rule of attribution: it identifies who should bear the costs of environmental harm—here, the EU as a historical contributor to global emissions. The law of state responsibility, by contrast, provides the remedial framework that activates only upon breach, determining the legal consequences of cessation, non-repetition, and reparation that follow from a failure to meet substantive obligations. Together, they transform a normative expectation into a legally cognisable claim, provided that a substantive primary obligation exists under international law: the polluter-pays principle answers the question of who should pay, while state responsibility answers the question of what happens if they do not.
These normative foundations are further reinforced by state responsibility under customary international law. The International Law Commission's Draft Articles on State Responsibility, 84 though not a treaty, reflect widely accepted legal standards, affirming that states are accountable for internationally wrongful acts, including environmental harm, and must provide reparations, a duty that could extend to addressing displacement resulting from such harm. 85
Importantly, this framework operates as a secondary rule system: it does not define the substantive obligations of states, but it determines the legal consequences when such obligations are breached, including those arising in the environmental field. The substantive content of these obligations is primarily informed by international environmental law, in particular the no-harm principle.
Recognised since the Trail Smelter Arbitration 86 and reaffirmed in Principle 2 of the Rio Declaration, this principle requires states to ensure that activities within their jurisdiction do not cause significant environmental damage beyond their borders. In the context of climate change, this obligation becomes particularly relevant where anthropogenic emissions contribute cumulatively to global environmental degradation.
The question of causation requires careful handling. Environmentally-induced displacement is rarely monocausal; poverty, governance failures, and conflict interact with environmental change. 87 This analysis does not require but-for causation. It suffices that EU emissions are a substantial contributing factor to the environmental changes that foreseeably produce displacement. If the EU's historical and ongoing emissions contribute to significant environmental degradation resulting in human displacement, then a legally relevant causal chain (based on substantial contribution rather than sole causation) emerges between emissions, environmental harm, and displacement. This chain engages not only in preventive duties to mitigate emissions but also responsibility for the foreseeable consequences of such harm.
The International Court of Justice, in Pulp Mills (Argentina v. Uruguay) (2010), 88 further clarifies the content of this due diligence obligation, holding that the duty to prevent transboundary harm requires continuous monitoring, risk assessment, and equitable cooperation (Paras 197, 204–205, 266).
Crucially, it also emphasised procedural obligations such as environmental impact assessment, notification, and consultation. Applied to the EU, these standards support an argument that climate governance must incorporate systematic assessment of displacement risks and meaningful engagement with populations affected by environmental harm linked to EU emissions. In the context of displacement, this due diligence obligation requires the EU to systematically assess how its climate policies and historical emissions contribute to displacement risk—both within its territory and, through transboundary harm, in third countries—and to adopt corresponding preventive and remedial measures.
A related yet distinct issue concerns the EU's unique international legal personality. The EU and its Member States are parties to the UNFCCC and the Paris Agreement as a mixed agreement. Under international law, as confirmed in Article 216(2) of the TFEU and in Opinion 2/91 concerning the ILO Convention, 89 the EU bears independent responsibility for fulfilling its treaty obligations within its areas of competence. Accordingly, references to ‘EU responsibility’ in this section denote the EU as an independent legal person, without prejudice to the shared responsibility of Member States under the principle of loyal cooperation.
As such, the law of state responsibility does not create new primary obligations but rather provides the remedial architecture through which the EU's failure to address environmental displacement – should such a failure amount to a breach of a primary rule – could give rise to legal consequences, including reparation.
Synthesis
In sum, the convergence of treaty obligations (The Paris Agreement), interpretive COP decisions, customary principles (the no-harm rule), general principles (polluter-pays, within the EU context), and international jurisprudence (Trail Smelter and Pulp Mills) establishes a strong prima facie legal case for the EU's responsibility to address environmental displacement. These frameworks imply that the EU cannot remain passive in the face of growing displacement. However, this argument is prima facie rather than conclusive. Full doctrinal confirmation would require further development of three elements: (1) a primary rule of international law imposing a specific duty on the EU to address climate-induced displacement; (2) a breach of that duty through the EU's failure to establish a protection framework, allocate adequate funding, or include mobility measures in its NDCs; and (3) attribution of that breach to the EU as an international legal person with separate legal personality under international law. This article does not conclusively resolve all three elements but proceeds on the basis that the foregoing analysis makes a legally cognisable case for responsibility.
The EU's responsibility under international human rights law
While the preceding subsection addressed international environmental law, the present subsection turns to the distinct and complementary framework of international human rights law.
Treaty sources and EU human rights obligations
The EU, as a prominent global actor and staunch advocate for human rights, 90 bears a significant responsibility to address environmental displacement. The EU's human rights commitments derive from multiple legal sources: its own treaties (CFR and Article 2 TEU); its Member States’ obligations under international human rights law, including UN treaties and the European Convention on Human Rights (ECHR); and general principles of EU law.
In this article, ‘international human rights law’ refers to a body of legally binding international norms that establish minimum standards of protection owed to all individuals, requiring states and supranational entities such as the EU to respect, protect, and fulfil rights grounded in the principle of human dignity, 91 while ‘fundamental rights’ refers to the rights protected within the EU legal order, particularly under the CFR. 92 The ‘human rights obligations’ of the EU discussed below arise from both its duty to respect fundamental rights when implementing its own policies and the fact that all Member States are bound by international human rights treaties, which the EU itself must not undermine.
The absence of a legal framework to protect those displaced by environmental degradation and climate change risks undermining its human rights commitments and may amount to a violation of international human rights law. 93 This legal framework requires states, and by extension, regional bodies like the EU, to protect fundamental rights. These rights are increasingly at risk because of the impacts of environmental degradation and climate change, which disproportionately affect vulnerable populations, particularly in the Global South. 94 These communities bear the brunt of environmental degradation despite contributing the least to its causes.
Given this disparity, the EU's failure to establish a proper legal framework for EDPs is especially concerning. By denying access to territory, asylum procedures, and protection from refoulement, it exacerbates human rights violations against individuals already affected by environmental degradation. Those fleeing life-threatening conditions are either returned to harm or pushed into irregular channels, rendering their human rights protections effectively illusory.
This omission also raises questions under Articles 2, 6, and 8 TEU, which require the EU to respect fundamental rights and promote international human rights standards. In the absence of any viable legal avenue for protection, EDPs remain exposed to foreseeable risks of inhuman treatment or death upon return. This inaction is not neutral; it actively perpetuates the vulnerability of EDPs. Under international law principles of due diligence and state responsibility for acts within a state's jurisdiction or control, the EU's indirect contribution to environmental degradation through its consumption patterns and global economic activities further strengthens the case for its legal responsibility.
One of the pressing questions this article seeks to answer is whether, by failing to uphold its obligations, the EU is complicit in systemic human rights violations against those disproportionately affected by environmental and climate-induced displacement.
Customary principles, jurisprudence, and state responsibility
The disconnect between the EU's human rights obligations and its lack of protections for EDPs becomes apparent when examining the Universal Declaration of Human Rights (UDHR). 95 While not a treaty, the UDHR has profoundly shaped customary international law and influenced EU treaties, CFR, and policies. 96 It explicitly recognises the right to life and the right to seek asylum from persecution, though it is silent on environmental harm.
The EU's failure to provide explicit legal protections for EDPs violates these rights because the absence of protection denies access to asylum procedures and exposes individuals to life-threatening conditions upon return – conditions that, if state-caused, would clearly trigger UDHR protections.
More broadly, the EU is bound by international human rights principles, including the prohibition of refoulement, the duty to respect and ensure human rights without discrimination, and the obligation to protect individuals from foreseeable harm. These principles bind the EU both because its Member States have ratified the underlying treaties and because the EU has recognised them as general principles of EU law. Indeed, environmental degradation undermines fundamental rights, depriving people of clean water, food security, and liveable conditions. 97
Those displaced face a double injustice: first, from environmental harm in their home countries, and second, from the EU's failure to recognise environmental displacement under its EU asylum and international protection framework. By denying protection, the EU may be complicit in perpetuating human rights violations, effectively disregarding its obligations under international human rights principles. This exclusion has tangible consequences. Consider, for instance, a farmer displaced by prolonged drought in sub-Saharan Africa, unable to grow crops or access clean water. Under current EU laws, they would not qualify for asylum, despite the clear threat to their basic human rights.
While the UDHR upholds universal rights to life and protection from persecution, including from severe environmental harm that renders return impossible, the EU's framework does not extend these principles to those fleeing environmental crises. The core principles of the UDHR are reinforced by major international human rights treaties, such as the International Covenant on Civil and Political Rights 98 (ICCPR) and the International Covenant on Economic, Social and Cultural Rights 99 (ICESCR). While these agreements do not directly bind the EU as an institution, they influence its human rights framework, as all Member States have ratified them. As a result, the EU is obliged to ensure its policies adhere to these standards. Under the ICCPR and ICESCR, Member States are legally required to safeguard fundamental rights, including the right to life 100 and the rights to health, adequate living conditions, and housing. 101
The UN Human Rights Committee (HRC) jurisprudence has expanded the interpretation of the right to life 102 to encompass environmental threats, as demonstrated in two key cases. In Teitiota v. New Zealand (2020), 103 the Committee acknowledged that climate-induced conditions, such as rising sea levels rendering Kiribati uninhabitable, could trigger non-refoulement obligations if return would expose individuals to life-threatening harm. 104 Although the claim was dismissed because of ‘insufficient imminence’ – the risk of harm, while serious, was not yet immediate enough to trigger Article 6 on the specific facts – the ruling established a precedent that environmental degradation may violate the right to life under the ICCPR.
Similarly, in Daniel Billy & Ors. v. Australia (2022), 105 the Committee found that Australia's failure to implement adequate climate adaptation measures for Torres Strait Islanders violated their rights to private and family life and cultural rights under Articles 17 and 27 of the ICCPR. Although the right to life claim in Billy was dismissed because of the 10–15 year timeframe for projected inundation, dissenting opinions contended that Australia's insufficient mitigation efforts posed a foreseeable threat to life.
Having examined the ICCPR and ICESCR framework, the analysis now turns to the ECHR, which exerts a more direct legal influence on the EU through the accession obligation in Article 6(2) TEU and the case law of the CJEU. While the EU is not yet a formal party to the ECHR, it operates under a clear duty to uphold its provisions through the legal commitments of its Member States and its own foundational treaties. Article 6(2) of the TEU explicitly requires the EU to accede to the ECHR, affirming that the Convention's principles form part of EU law. Furthermore, the CFR incorporates ECHR protections and mandates their interpretation in line with the jurisprudence of the European Court of Human Rights (ECtHR). 106 The CJEU has reinforced this alignment in rulings such as Bosphorus v. Ireland, 107 upholding the primacy of ECHR rights, particularly the prohibition of inhuman or degrading treatment under Article 3, within EU law.
Despite these legal safeguards, the EU's failure to formally recognise EDPs as eligible for protection under EU law creates a stark contradiction with its human rights obligations. The ECtHR has progressively interpreted Article 2 108 of the Convention, ruling that state inaction on climate change can violate fundamental rights. Similarly, cases like López Ostra v. Spain 109 and Budayeva v. Russia 110 have affirmed that states may be held liable for failing to prevent or mitigate environmental disasters that infringe upon human rights. These rulings highlight a clear legal imperative: governments must take proactive measures to protect individuals from environmental harm that threatens their right to life.
The same legal logic extends to the EU because the EU exercises sovereign powers over asylum and return and because under Article 51(1) of the CFR, the EU's institutions are bound to respect fundamental rights when implementing Union law. Accordingly, if member states are obliged under the ECHR to prevent foreseeable environmental harm, the EU – as the entity that has harmonised asylum policies and controls external border management through agencies such as Frontex – cannot evade a parallel obligation. However, this obligation remains unfulfilled in practice. The EU's asylum and international protection framework, though incorporating protections against refoulement under Article 3 ECHR, fails to explicitly acknowledge the vulnerabilities of those displaced by environmental-related disasters.
This legal gap not only disregards the ECtHR's evolving jurisprudence
Compounding this issue, the EU's ongoing accession process to the ECHR underscores the urgency of policy coherence. Without explicit recognition of climate displacement – meaning a legal provision acknowledging that severe environmental harm can be a basis for international protection, whether subsidiary or humanitarian – the EU's legal framework continues to treat EDPs as invisible, forcing them into irregular channels or return. This omission represents a legal failure, one that demands urgent reform to align the EU's policies with its foundational principles and international obligations.
Synthesis
The UDHR, ICCPR, ICESCR, and ECHR, together with the jurisprudence of the UN Human Rights Committee and the ECtHR, converge on a clear legal principle: states and regional organisations must protect individuals from foreseeable, life-threatening environmental harm. Applied to the EU, this principle generates legal responsibility on three grounds. First, the EU is directly bound by the CFR and by Article 6(2) TEU's obligation to accede to the ECHR. Second, the EU exercises effective control over harmonised asylum and border policies, engaging state responsibility under international law. Third, the EU's due diligence obligations are engaged by its indirect contribution to environmental degradation through consumption patterns and economic activities.
Consequently, the EU's failure to recognise EDPs within its asylum and international protection framework is not a mere policy gap but a legal failure that breaches its own fundamental rights commitments and international human rights obligations. Taken together, these developments confirm that policy inertia operates not only within the EU asylum and international protection framework, but also across its external environmental and climate governance regimes, thereby reinforcing the systemic nature of the gap identified in this article.
Conclusion
This article has demonstrated that the exclusion of EDPs from international protection under EU law is not the result of incidental normative gaps, but rather of a deeper structural fragmentation and functional misalignment across the Union's asylum and protection framework. Three interrelated findings emerge.
First, the CEAS remains anchored in a persecution-centred paradigm derived from the 1951 Refugee Convention, rendering it structurally ill-suited to environmental forms of harm. Neither refugee status nor subsidiary protection extends to environmental drivers of displacement as autonomous grounds, while the Temporary Protection Directive—though theoretically adaptable—remains politically constrained and normatively misaligned with the slow-onset, often irreversible character of environmental displacement. The resulting lacuna is twofold: the absence of a binding protection status for EDPs and the absence of common interpretive principles capable of guiding Member State practice. This vacuum has produced regulatory fragmentation across the Union, undermining the principle of solidarity embedded in Articles 2 TEU, 3(3) TEU, and 80 TFEU.
Second, this absence of protection cannot be characterised as legally neutral. Read in light of the Treaties and the CFR, it raises serious questions of compatibility with the Union's constitutional order. The combined requirements of solidarity, cohesion, and policy coherence under Article 7 TFEU, together with the binding force of the CFR, impose obligations that are engaged where individuals face foreseeable exposure to life-threatening environmental harm, inhuman or degrading treatment, or discriminatory exclusion from protection regimes. In this context, regulatory inaction risks crystallising into prima facie violations of Articles 2, 3, 4, and 21 of the CFR.
Third, the EU's legal responsibility extends beyond its internal order to its position within international law. Under international environmental law, the interaction between the Paris Agreement, COP interpretative practice, and customary principles—most notably the no-harm rule articulated in Trail Smelter and Pulp Mills—supports the view that states may incur responsibility for transboundary harm linked to climate change. Parallel developments in international human rights law, including the UN Human Rights Committee's reasoning in Teitiota and Billy, as well as emerging climate jurisprudence at the European level, confirm that failure to protect individuals against foreseeable life-threatening environmental risks may engage binding obligations. Through Article 6(2) TEU and the CFR, these standards are increasingly integrated into the EU legal order.
Taken together, these findings demonstrate that the EU's ‘protection gap’ for EDPs is not a contingent policy failure but a systemic consequence of a fragmented legal architecture that is increasingly difficult to reconcile with the Union's own constitutional and international commitments. The EU is therefore confronted with a clear normative choice. It may continue to rely on discretionary, non-binding instruments that externalise environmental displacement from the scope of legal protection, thereby perpetuating a structural protection vacuum. Or it may give legal effect to its foundational commitments to solidarity, human rights, and climate leadership by establishing a binding protection framework for EDPs, ensuring fair responsibility-sharing among Member States, and aligning its asylum and protection regime with the Union's environmental and human rights obligations.
The legal foundations for such a development already exist within the treaties; what remains unresolved is not the availability of legal authority but the willingness to deploy it.
Footnotes
Acknowledgments
The author wishes to express gratitude to the Max Weber Programme and to Prof. Joanne Scott for her valuable feedback on earlier drafts, as well as to Alyson Price for her careful and thoughtful editing. Further thanks are extended to the anonymous reviewers for their rigorous and perceptive comments, which contributed meaningfully to the refinement of this work, and to Prof. Bharat H. Desai, Editor-in-Chief of Environmental Policy and Law, for his careful stewardship of the manuscript throughout the publication process.
Ethical approval and informed consent statements
This research did not involve human or animal subjects and therefore did not require ethical approval or informed consent.
Funding
This work was supported by the Max Weber Programme for Postdoctoral Studies of the European University Institute. The European Commission supports the EUI through the European Union budget.
Declaration of conflicting interests
The author declared no potential conflicts of interest with respect to the research, authorship, and/or publication of this article.
Data availability statement
This manuscript is a legal analysis and does not report on original empirical data. All sources used are publicly available and cited in the references.
Prior publication disclaimer
An earlier version of this manuscript was previously posted as a working paper in the Max Weber Programme for Postdoctoral Studies series at the European University Institute. The preprint is available in Cadmus, the EUI Research Repository:
. The preprint version has not been updated since its initial deposition in September 2025.
