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The State of the Netherlands v. Urgenda Foundation: Ruling of the Court of Appeal of The Hague (9 October 2018)

Published online by Cambridge University Press:  01 April 2019

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On 9 October 2018, the Court of Appeal of The Hague (the Netherlands) upheld the District Court’s decision in the case of Urgenda, thus confirming the obligation of the Netherlands to reduce its greenhouse gas (GHG) emissions by at least 25% by 2020 compared with levels in 1990. This case raised some of the thorniest issues in climate law. As the Netherlands is responsible for only a tiny fraction of global GHG emissions, is it right for a court to hold that a national emissions reduction mitigation target is necessary to prevent dangerous climate change and its impact on human rights? If so, how can this target be determined? The District Court and the Court of Appeal of The Hague have provided inspiring responses, although they are perhaps not entirely convincing.

Case Note
© Cambridge University Press 2019 


Urgenda was established in 2008 as a foundation in order to ‘stimulate and accelerate the transition processes to a more sustainable society, beginning in the Netherlands’.Footnote 1 In November 2012, Urgenda requested the State of the Netherlands (the State) to adopt a national climate change mitigation target of 40% emissions reduction by 2020 compared with levels in 1990.Footnote 2 The request was denied,Footnote 3 and Urgenda brought the case to court on its behalf and on behalf of 886 individuals. The District Court of the Hague (DC), deciding the case at first instance on 24 June 2015, ordered the State to reduce the greenhouse gas (GHG) emissions of the Netherlands by at least 25% below the level of 1990 by the end of 2020.Footnote 4 The State appealed on 29 grounds, and Urgenda cross-appealed on one ground. In its ruling of 9 October 2018, the Court of Appeal of The Hague (CA) upheld the judgment of the DC against the State’s challenges but, following Urgenda’s ground of cross-appeal, based its decision on slightly different reasoning.Footnote 5 Following the decision of the CA, the State announced that it would bring cassation proceedings for reasons of principle regarding the extent of judicial power,Footnote 6 while striving to adopt additional measures to achieve the 25% emissions reduction target by 2020.Footnote 7

As well as its obvious significance for climate law in the Netherlands, the Urgenda case raises questions of paramount importance from comparative and international perspectives. Building on the European Convention on Human Rights and Fundamental Freedoms (ECHR)Footnote 8 in a way that could certainly be replicated using other human rights treaties in other regions of the world, the case illustrates the relevance of human rights as the source of an obligation to mitigate climate change. Overall, the courts engage with the thorny issue of determining the obligation of a state in relation to a global problem to which it contributes only marginally – the current GHG emissions of the Netherlands were estimated to represent less than 0.5% of global GHG emissions.Footnote 9 In particular, the two judgments seek to establish methodologies to quantify the obligation of a state to reduce its GHG emissions within a particular period of time based on science, principles of fairness, and prior statements made by the Netherlands. The approach adopted by each court is groundbreaking but is certainly not free from criticism; lessons can be drawn to allow for a more consistent and persuasive approach in future cases.Footnote 10

This case note is organized as follows. Section 2 provides an overview of the case as adjudicated by both courts. Section 3 engages critically with some of the key issues underlying the case, namely the requirements of standing in relation to a global environmental issue, the legal obligation of a state to mitigate climate change, and the determination of the ambit of this obligation based on science, fairness, and the statements previously made by the Netherlands itself. Section 4 concludes with a discussion of the consequences of the case in the context of increasing public interest litigation relating to the failure of governments to mitigate climate change quickly enough.


This section presents a brief overview of the context in which the case took place, outlines the judgments of the DC and the CA, and discusses the aftermath of the case in the Netherlands.

2.1. The Context

The GHG emissions of the Netherlands are higher than one would expect from a small country with a high-income economy. According to the latest statistics communicated by the Netherlands, the country’s GHG emissions amounted to 195 MT CO2-eq in 2016.Footnote 11 While this represents a reduction of 12.5% compared with 1990 levels,Footnote 12 the rate of per capita GHG emissions in the Netherlands (11.6 T CO2-eq/year)Footnote 13 remains significantly higher than in most other European Union (EU) Member States.Footnote 14 Most of the country’s GHG emissions consist of carbon dioxide (CO2) from the energy sector,Footnote 15 a source which has not declined since 1990.Footnote 16

The EU, of which the Netherlands is a Member State, has committed to reduce its aggregate GHG emissions by 20% from a 1990 basis by 2020, first as a nationally appropriate mitigation commitment under the Cancún Pledges,Footnote 17 and again as a quantified emissions reduction commitment through the Doha AmendmentFootnote 18 to the Kyoto Protocol.Footnote 19 In both instruments, the EU and its Member States have also made a conditional offer to enhance their target to 30% ‘as part of a global and comprehensive agreement’Footnote 20 – a condition which, in the view of the European Commission, has not materialized.Footnote 21 The Urgenda case is concerned with the stringency of mitigation action carried out in the Netherlands with a view to reducing its GHG emissions by 2020. The case is not concerned with emissions reduction commitments applicable after 2020, such as the 2030 target (40% reduction compared with 1990 levels) included in the EU’s Nationally Determined Contribution (NDC)Footnote 22 under the Paris Agreement.Footnote 23

The EU-wide 20% emissions reduction target does not imply a uniform emissions reduction target in every Member State. The EU has long recognized that efforts should be shared among Member States based on ‘the principle of solidarity between Member States and the need for sustainable economic growth across the Community’.Footnote 24 The EU’s current mitigation efforts consist in part of an EU-wide Emissions Trading Scheme (ETS), first introduced in 2005.Footnote 25 The ETS covers parts of the energy, industrial and aviation sectors, which together represent about 45% of EU-wide GHG emissions.Footnote 26 Within these sectors, it is expected that by 2020 the EU ETS will achieve an EU-wide emissions reduction of 21%, compared with 2005 emissions.Footnote 27 On the other hand, emissions from sectors not covered by the EU ETS are to be addressed by Member States, in part by implementing other EU rules and in part through their own national initiatives. To ensure that Member States achieve sufficient emissions reduction in non-ETS sectors for the overall emissions reduction of the EU to comply with its 2020 target, the European Parliament and the Council have defined national targets for reduction of non-ETS emissions through the 2009 Effort Sharing Decision.Footnote 28 Accordingly, the Netherlands is to achieve at least a 16% reduction by 2020, on a 2005 basis, in non-ETS emissions within its territory.Footnote 29

As a result of the EU ETS and a range of other measures implemented in the Netherlands, GHG emissions originating from the Netherlands overall have been on a decreasing trend, although the changes have been slow.Footnote 30 In 2015, when the case brought by Urgenda was first decided by the DC, the government estimated that the Netherlands would have achieved a 14 to 17% emissions reduction by 2020 compared with 1990.Footnote 31 It is noteworthy, however, that this reduction in overall GHG emissions is being realized in large part through a reduction in the emission of GHGs other than CO2, especially methane from waste,Footnote 32 while the level of CO2 emissions overall has remained unchanged since 1990.Footnote 33 This suggests that the current trends are related to one-off measures, such as reform of waste management, and that they are not triggered by a process of structural transition towards more sustainable modes of production and consumption.

This, in the view of Urgenda, is highly unsatisfactory. After the government declined to adopt a more ambitious emissions reduction target by 2020, Urgenda sought a ruling from the DC that ‘the State acts unlawfully if it fails to reduce or have reduced the annual GHG emissions in the Netherlands by at least 40% compared to 1990, by the end of 2020’.Footnote 34 This claim was made on various legal bases, including the international law on climate change (the United Nations Framework Convention on Climate Change (UNFCCC),Footnote 35 the Kyoto ProtocolFootnote 36 and its Doha Amendment,Footnote 37 as well as the ‘no-harm’ and the precautionary principles);Footnote 38 the right to life and to family life as protected under the ECHR;Footnote 39 the constitutional law obligation of the State to protect the environment;Footnote 40 and tort law.Footnote 41 These arguments were informed by the findings of the Intergovernmental Panel on Climate Change (IPCC), in particular in its Fourth Assessment Report (AR4), on climate change, its impacts, and potential emissions reduction pathways.Footnote 42

2.2. The Judgment of the District Court of The Hague

Having established Urgenda’s standing, the DC rejected most of the legal sources Urgenda had invoked. In particular, it stated that the obligations of the Netherlands under international law on climate change are owed to other states, not to individuals or legal persons.Footnote 43 It interpreted the rights created by the ECHR in the light of its Article 34, which limits access to the European Court of Human Rights (ECtHR) to actual or potential victims of human rights violations, and held that Urgenda had neither claimed to be a victim of such a violation, nor established that any of its 886 individual co-plaintiffs were.Footnote 44 Similarly, the DC declined to interpret the constitutional obligation of the State to protect the environment as a distinct source of obligations of the State towards individuals or legal persons.Footnote 45 However, the DC held that, taken together, these sources of constitutional, European and international law help to determine the content of the duty of care that the State owes to society – including Urgenda – under a provision of the Dutch Civil Code and the doctrine of hazardous negligence.Footnote 46 Accordingly, the DC recognized, in tort law, an obligation for the State ‘to take measures in its own territory to prevent dangerous climate change’.Footnote 47

The DC then applied this duty of care on the part of the State to the facts of the case. It noted conclusive evidence of the increasing social and ecological risks associated with climate change if the global average temperature exceeds 2°C above pre-industrial levels,Footnote 48 including their manifestation in the territory of the Netherlands,Footnote 49 and the need for deep cuts in GHG emissions to take place rapidly, especially in developed countries, in order to reduce the likelihood of this scenario.Footnote 50 In particular, building on the contribution of the IPCC’s Third Working Group (WG3) to AR4, the DC concluded that a reduction in the GHG emissions of Annex I countriesFootnote 51 of 25–40% by 2020 (from a 1990 basis) should be achieved in order to pursue the objective of holding the increase in global average temperatures below 2°C.Footnote 52 Noting that the specific circumstances of the Netherlands did not justify any lower mitigation efforts than an average Annex I country, the DC concluded that, in the application of its duty of care, the State had to pursue a target of at least a 25% reduction in GHG emissions by 2020 from a 1990 basis.Footnote 53

2.3. The Judgment of the Court of Appeal

The State submitted 29 grounds of appeal against the judgment of the DC, thus, as the CA noted, ‘seek[ing] to submit the dispute to the Court in its entirety’.Footnote 54 The CA did not give favourable consideration to any of these grounds. In contrast, it was persuaded by the unique ground raised in Urgenda’s cross-appeal relating to the opinion of the DC that Urgenda, considering Article 34 ECHR, cannot rely on Articles 2 and 8 ECHR in these proceedings.Footnote 55 Urgenda submitted that Article 34 ECHR is concerned with conditions of access to the ECtHR – by excluding public interest litigation before that court – rather than the admissibility of claims based on the ECHR before domestic courts.Footnote 56 The CA agreed and admitted that, in Dutch law, public interest litigation could invoke rights guaranteed under the ECHR.Footnote 57

This led the CA to justify the DC’s conclusions on an alternative legal basis – namely by interpreting the ‘positive obligation [of the State] to take concrete actions to prevent a future violation’ of Articles 2 and 8 ECHR.Footnote 58 The CA noted that dangerous climate change would result ‘in the serious risk that the current generation of citizens will be confronted with loss of life and/or a disruption of family life’,Footnote 59 referring to the rights protected under these two articles. However, like the DC in relation to tort law, the CA recognized that the content of the positive obligation of the Netherlands under the ECHR to prevent a future violation of protected rights could be interpreted in the light of other obligations of the State, including international law on climate change.Footnote 60

Accordingly, the CA upheld the judgment of the DC,Footnote 61 highlighting that ‘the State ha[d] done too little to prevent a dangerous climate change and [was] doing too little to catch up’.Footnote 62 The CA also noted that, as Urgenda had not put forward a ground of cross-appeal against the rejection of a more demanding target, ‘a reduction of more than at least 25% by 2020 [could not] be awarded’Footnote 63 on appeal.

2.4. The Aftermath of the Case

The most recent reports from the Netherlands estimate that by 2016 the country’s GHG emissions had decreased by 12.5% compared with 1990 levels.Footnote 64 This was achieved in part in an artificial way – namely through the application of a new methodology to the inventory of national GHG emissions, which the Netherlands adopted in 2016 in the implementation of international requirements.Footnote 65 Applied retroactively, the new methodology led the Netherlands to estimate higher GHG emissions for 1990 of certain types of GHG – emissions of which have since significantly decreased – and thus to report higher rates of emissions reductions compared with 1990.Footnote 66 All in all, while emissions of methane and some other highly potent GHGs have decreased sharply, the Netherlands’ CO2 emissions overall have remained stable since 1990.Footnote 67

The latest projections by the Dutch government suggest that the impact of current measures will achieve around a 23% emissions reduction by 2020 (on the 1990 basis), and that additional measures under consideration could bring this rate up to 24%.Footnote 68 As noted emphatically by the CA, however, these projections come with a high degree of uncertainty.Footnote 69 It is unclear whether the Netherlands will genuinely be able to achieve almost as much emissions reduction in two years as it has in the last 28 years. The Expert Review Team (ERT) which conducted the Technical Review of the Third Biennial Report of the Netherlands in August 2018 rightly noted that ‘[i]f a domestic target of a 25[%] emission reduction by 2020 below the 1990 level is formally confirmed’ – as it was two months later by the CA – ‘the Netherlands may face challenges in achieving its domestic target’.Footnote 70 Immediate action is required for the Netherlands to ensure compliance with this target.Footnote 71 Absent any mention in the judgments, one would not expect the State to rely on flexibility mechanisms to achieve compliance with its target.


The judgments of the DC and CA have raised some of the most difficult questions in climate law. Climate change results from GHG emissions occurring in multiple countries over a long period of time. Climate change mitigation requires ambitious efforts to take place concomitantly in multiple countries and pursued over decades. Yet, taken individually in the context of a particular dispute, the GHG emissions occurring within the territory of a country like the Netherlands are small, and incremental efforts to reduce these emissions hardly make any difference at all when assessed in isolation. This means that a particular measure on climate change mitigation is never indispensable for the achievement of global mitigation outcomes and, in fact, the global impact of an individual measure on the climate system is almost always negligible per se. Additional efforts by the Netherlands to reduce its GHG emissions by 2020 will be of very little help to any particular individual whose right to life or to family life could be threatened by the impacts of climate change.

Therefore, a judge could have been tempted to conclude that Urgenda had no standing, or that its claim that the State had an obligation to protect the rights of Dutch citizens by reducing GHG emissions in the Netherlands failed for lack of a causal link between the efforts of the State to reduce GHG emissions in the Netherlands and any hindrance to the effective enjoyment of their rights. This, however, would have led to the highly unsatisfactory result that were other courts in other countries to take the same approach, no obligation could ever be imposed on any state to address a critical problem the importance of which all states have recognized.

Instead, both courts in Urgenda held that the Dutch government must reduce the country’s GHG emissions as a matter of legal obligation and that Urgenda has a right to claim performance of this obligation. The following sub-sections discuss three key stages of the reasoning of the two courts – namely, in relation to the conditions for standing (Section 3.1); the existence of an obligation of the State to mitigate climate change (Section 3.2); and the scope of this obligation (Section 3.3).

3.1. Standing for the Impacts of Climate Change

A first issue relates to the discrepancy between the scope of the case brought by Urgenda and the scope of climate change. Climate change is a global phenomenon, most consequences of which will take decades or even centuries to unfold. The consequences of climate change will almost never materialize directly in distinct individual harm. By contrast, any litigation is confined to the rights and obligations of the parties to the dispute. This makes it remarkably difficult to bring to courts questions relating to the impacts of climate change. Framing a climate case in broad terms may raise questions of standing, but framing it too narrowly may exacerbate the difficulty of establishing the urgency of action on climate change mitigation.

Urgenda attempted to frame the case as broadly as it possibly could. It claimed to represent the interests of present and future generations in the Netherlands and abroadFootnote 72 – essentially anyone born or to be born. The State contested Urgenda’s standing in as much as it related to present or future populations abroad,Footnote 73 and it was not clear whether the State accepted Urgenda’s claim to stand for future generations in the Netherlands.Footnote 74 Yet, both courts accepted that Urgenda, as a foundation, had standing at least with regard to present generations living in the Netherlands.Footnote 75 Both courts also stated that, as a matter of standing, they did not need to decide on additional, contested grounds.Footnote 76

In particular, building on the legislative history of the Civil Code, the CA acknowledged that Urgenda could have standing even if only on the basis of ‘idealistic interests … that people want to advocate out of a particular conviction’.Footnote 77 This approach is certainly more convincing than trying to relate individual harm to the broad, systemic impact of climate change. This category of ‘idealistic interests’ could extend beyond the social impacts of climate change – to which the Urgenda case is mostly confined – to include considerations of the widespread impacts of climate change on cultural and ecological values. This interpretation led the courts to grant standing to Urgenda but, in fact, only displaced the question of causation to later stages of the reasoning.

3.2. The Legal Obligation of the State to Mitigate Climate Change

Another question raised in Urgenda relates to the existence of an obligation on the part of a state to mitigate climate change under domestic law. The two judgments illustrate the availability of various legal obligations requiring essentially the same conduct: while the DC based its judgment on the doctrine of hazardous negligence,Footnote 78 the CA focused on the positive obligation of the Netherlands to protect the rights to life and to family life under Articles 2 and 8 ECHR.Footnote 79 Urgenda invoked other grounds, such as Article 21 of the Constitution of the Netherlands and the international obligations of the Netherlands under climate treaties and the no-harm principle,Footnote 80 although the DC considered that, under Dutch law, Urgenda did not have the right to claim the performance of these obligations. Lastly, Urgenda invoked a provision of the Dutch Civil Code on the prohibition of nuisance, which the DC did not have to assess, having established a duty of care on another ground.Footnote 81

Climate change is an environmental issue with far-reaching consequences for global physical systems,Footnote 82 ecosystems and biological diversity,Footnote 83 at least as much as it is a human rights issueFootnote 84 or a cultural law issue.Footnote 85 As such, the general obligation of a state to mitigate climate change can most solidly be based on the no-harm principle,Footnote 86 and also, less directly, on a range of alternative rules of international law which relate, for instance, to the protection of biological diversity,Footnote 87 the marine environment,Footnote 88 the world cultural heritage,Footnote 89 and human rights.Footnote 90 Yet, opportunities for adjudication on the basis of these rules are often lacking. In contrast to most other fields, human rights law offers a high potential for adjudication by defining individual rights in the performance of state obligations and by establishing supranational courts and other institutions with a mandate to adjudicate disputes or, at least, interpret these rights. The CA judgment certainly confirmed a ‘rights turn’Footnote 91 in climate adjudication by basing its approach to the case not on tort law but entirely on human rights law.

The State, however, had a number of objections to the determination that it had an obligation to mitigate climate change, whether under the doctrine of hazardous negligence or under human rights law. The first objection relates to the integration of the Netherlands in the EU and, in particular, to the EU ETS. The second objection relates to the more fundamental question of the loose causal link between emissions reduction in the Netherlands and the impacts of climate change. These objections are discussed in turn.

First objection: Market integration and the waterbed effect

The State argued that EU legislation prevented it from taking additional measures to mitigate climate change.Footnote 92 The basis for the establishment of the EU ETS in 2005 lies in the Treaty on the Functioning of the European Union (TFEU), which gives a mandate to the European Parliament and the Council to decide actions to be taken on environmental protection.Footnote 93 The same treaty provides clearly that this does not prevent Member States from adopting more stringent protective measures compatible with EU treaties.Footnote 94 Thus, as the CA noted, EU climate law does not prevent the Netherlands from adopting more stringent measures on climate change mitigation.Footnote 95

A more persuasive argument of the State related to the effectiveness of mitigation action in relation to activities covered by a transnational market-based mechanism. The State submitted that additional emissions reduction in the Netherlands within the scope of the EU ETS would liberate emission allowances, which would be traded to other parts of the ETS, resulting in no net EU-wide emissions reduction. Hence, emissions reductions in the Netherlands would be balanced by increases (or less reduction) in other parts of the EU – a phenomenon sometimes referred to as ‘the waterbed effect’.Footnote 96

However, this argument is limited to those emissions in the Netherlands which fall within the scope of the EU ETS. Moreover, the argument assumes that the ETS operates like a natural market whereas, on the contrary, public authorities have frequently had to intervene to regulate the ‘market price’ of emission allowances,Footnote 97 and a mechanism for such intervention has been institutionalized.Footnote 98 In the short term, a surplus in emission allowances could be balanced by the cancellation of allowances while, in the longer term, less demand for emission allowances would facilitate the decision to issue fewer emission allowances in future trading periods. The Dutch government itself is contemplating the creation of additional incentives for reduction of emissions covered by the EU ETS,Footnote 99 knowing that this would contribute to overall mitigation efforts despite the risk of a waterbed effect. Thus, both courts rightly rejected this objection.Footnote 100

Second objection: The drop-in-the-ocean problem

A second objection, which extends far beyond the scope of a regional organization or that of a carbon market, lies at the very core of climate law. The State accurately contended that it could not possibly solve the problem of climate change on its own,Footnote 101 as the share of the Netherlands in global GHG emissions is small.Footnote 102 The lack of a causal link between emissions reduction in the Netherlands and the impacts of climate change could be invoked in relation to any legal basis for a mitigation obligation of a general nature: the duty of care to avert the imminent danger of climate law;Footnote 103 the positive obligation of a state to protect the right to life and to family life under Articles 2 and 8 ECHR;Footnote 104 or, indeed, the no harm principle.Footnote 105 Each state (except for the few largest ones) contributes only marginally to global GHG emissions; its efforts to reduce its emissions are a drop in the ocean. As the Netherlands contributes less than 0.5% of global GHG emissions,Footnote 106 any effort by the Netherlands to reduce its GHG emissions, even drastically, is unlikely to have any direct and measurable impact on the wellbeing of Dutch nationals or, indeed, anyone else.

Both courts rejected this objection. The CA, in particular, held that the small contribution of the Netherlands to global GHG emissions ‘does not release the State from its obligation to take measures in its territory, within its capabilities, which in concert with the efforts of other states provide protection from the hazards of dangerous climate change’.Footnote 107 Yet, neither of the two courts gave a complete justification for its finding. The DC, for instance, highlighted that ‘the possibility of damages for those whose interests Urgenda represents, including current and future generations of Dutch nationals, is … great and concrete’,Footnote 108 all but ignoring that imposing additional efforts on the State would make no significant difference. It referred to the case of the Potash Mines, in which the Dutch Supreme Court held that a polluter cannot ‘reject possible liability by stating that its contribution is minor’.Footnote 109 Yet, the case of the Potash Mines certainly does not imply liability for any negligible contributors to a global environmental issue, and the DC did not explain why the Netherlands’ GHG emissions were ‘minor’ rather than negligible.

The conclusion of the CA is far more convincing because it genuinely seeks to address the drop-in-the-ocean problem. If the objection of the State was to be allowed, the CA pointed out, ‘each state held accountable would then be able to argue that it does not have to take measures if other states do not [do] so either’.Footnote 110 As the CA noted, ‘[t]hat is a consequence that cannot be accepted’.Footnote 111 The CA highlighted the need for the availability of an effective legal remedy for a global problem such as climate change,Footnote 112 but this alone cannot be the justification for the obligation of the Netherlands since, in the absence of the obligation to mitigate, there would be no legal wrong to be remedied.

The maxim at which the CA hints is not limited to climate change, to states, or to law; rather, it is an essential feature of any normative system. It is by following the same maxim that states apply international law (most of the time) and that we, individual citizens, respect our environment, for instance, by refraining from littering (most of the time). An authoritative phrasing of this maxim in the ethical sphere, the first formulation of Immanuel Kant’s categorical imperative, reads as follows: ‘Act only on that maxim whereby thou canst at the same time will that it should become a universal law’.Footnote 113 The CA seems to imply, rightly, that each and every state should act in a way which, in a sound and reasonable assessment, would avert dangerous climate change if only other states were to act following the same maxim.Footnote 114 In a world where opportunities for the enforcement of international law obligations remain scarce, no effort to mitigate climate change can be successful if this rule is disregarded. Thus, this maxim is law not because it is written in any particular code or established through any particular case, but out of necessity.

3.3. The Ambit of the Obligation

Arguably the thorniest issue in the Urgenda case – as in many climate-related cases – was the determination of the ambit of the obligation of the Netherlands to reduce its GHG emissions.Footnote 115 The question involves a political arbitrage between various values and interests, such as between immediate economic benefits and deferred impact on human welfare. The question is often addressed (though it does not have to be) by determining, first, a global objective, and then the contribution that a state must make towards its achievement.Footnote 116 In addressing this question, a judge must, in addition, respect the degree of deference owed to elected branches of government.Footnote 117 To assess whether the State was doing enough to reduce GHG emissions in the Netherlands and what target, if any, should be imposed, the courts relied on scientific information, ethical criteria for differentiation, and some previous statements of the Dutch government.

Climate science

To determine the appropriate national target that could be imposed on the State, both courts relied heavily on scientific research on climate change, in particular on syntheses of economic studies. The starting point was the IPCC’s AR4, and in particular the contribution of WG3 on the mitigation of climate change, published in 2007.Footnote 118 Firstly, the contribution of WG3 to AR4 was taken as the main authority to establish the need to hold the increase in global average temperatures below 2°C above pre-industrial levels (the 2°C target),Footnote 119 an objective which had apparently been acknowledged by Urgenda and the Dutch government during the dispute.Footnote 120 Secondly, the WG3 contribution to AR4 was also taken as evidence of the need to stabilize GHG concentrations in the atmosphere at a level of about 450 ppm CO2-eq by the end of the 21st century in order to achieve the 2°C target (the 450 scenario).Footnote 121 Lastly, the WG3 contribution to AR4 was interpreted as establishing that this 450 scenario requires Annex I parties to the UNFCCC (developed countries) to reduce their GHG emissions by at least 25%, and possibly as much as 40%, by 2020, compared with 1990 levels (the Annex I 25–40% emissions reduction target).Footnote 122

In relying on the contribution by WG3 to AR4 as evidence of the 2°C target, of the 450 scenario and of the Annex I 25–40% emissions reduction target, the courts gave new authority to scientists.Footnote 123 Climate science, including economics, provides the most reliable estimates of the consequences of different choices, but climate science cannot determine what the objective should be; value-based judgments are indispensable for determining what societies should strive for. Contrary to observations by both courts, AR4 did not adopt the 2°C target for it then to be ‘endorsed’Footnote 124 by climate negotiations; this milestone was created entirely through political processes which were informed but not determined by climate science.Footnote 125 Similarly, the two courts overstated scientific evidence presented in AR4 that the 450 scenario was necessary to achieve the 2°C target: the 450 scenario was merely mentioned in a bracket in Chapter 3 of the WG3 contribution as a ‘best estimate’.Footnote 126 Furthermore, while Chapter 13 of the WG3 contribution suggests that the Annex I 25–40% emissions reduction target would be required to achieve the 450 scenario,Footnote 127 another section of the same chapter asserts that the 2°C target would require emissions reductions of 10–40% in Annex I countries within the same time frame, on the ground that higher concentration scenarios could also keep temperatures below 2°C warming.Footnote 128 This inconsistency, albeit apparent in the judgment of the DC,Footnote 129 is not explained by either court. Instead, ignoring the IPCC’s finding that ‘a considerable range of 2020 and 2030 emissions can be consistent with specific long-term goals’,Footnote 130 the DC held that the Annex I 25–40% reduction target was ‘scientifically proven’.Footnote 131

Courts should build on the latest authoritative scientific evidence – especially in a field as dynamic as climate science and economics. The contribution of WG3 to AR4 was published more than 10 years before the CA decision. While the IPCC’s Special Report Global Warming of 1.5°C was not available to the courts,Footnote 132 they could have built on the WG3 contribution to the Fifth Assessment Report of the IPCC (AR5), published in 2014,Footnote 133 which provided more advanced estimates of the mitigation scenarios consistent with a 2°C target. The contribution of WG3 to AR5 concluded with high confidence that, while a 450 scenario is ‘likely’ (which suggests more than a 66% chance) to hold temperatures below 2°C, a scenario reaching 500 ppm CO2-eq in 2100 (the 500 scenario) is also ‘more likely than not to limit temperature change to less than 2°C’.Footnote 134 Though both courts noted this finding,Footnote 135 on which the State tried to rely in its defence,Footnote 136 the courts maintained nonetheless, oddly, that a ‘450 scenario’, rather than a ‘500 scenario’, was required to pursue the 2°C target.

A valid ground for this could have been that states need to pursue scenarios that imply at least a 66% chance of achieving the 2°C target. Yet, neither court discussed the level of certainty that should be associated with efforts towards the 2°C target. Instead, the DC contended that AR5 shows ‘a strong preference for the 450 scenario, as the risks are much higher with a 500 scenario’.Footnote 137 Yet, it is not clear how this ‘strong preference’ was expressed, and presumably it was not: any such preference would be inconsistent with the principle of policy neutrality that guides the work of the IPCC.Footnote 138 It is also unclear how this preference could be established based on science alone: as climate risks are always lower with a more ambitious scenario, scientists would certainly prefer a lower concentration scenario even more.Footnote 139 The 450 scenario inevitably involves a political arbitrage between the costs and benefits of climate change mitigation, an arbitrage which cannot be based only on science.

Going even further than the DC, the CA threaded into the scientific arena and questioned the reliability of emissions pathways in the WG3 contribution to AR5. The CA first noted that most mitigation scenarios presented in AR5 are based on the use of ‘negative emissions technologies’ (NETs),Footnote 140 a concept that refers to a broad range of technologies that would remove large quantities of CO2 from the air, such as a combination of bioenergy and carbon capture and storage.Footnote 141 The CA cited a report by the European Academies Science Advisory Council, brought to its attention by Urgenda, which suggests that NETs ‘offer only limited realistic potential to remove carbon from the atmosphere and not at the scale envisaged in some climate scenarios’.Footnote 142 On this basis, the government having failed to provide any counter-evidence, the CA concluded that the mitigation scenarios in AR5 ‘might thus have painted too rosy a picture’,Footnote 143 and denied their relevance.

In doing so, the CA did not assess the scientific authority of the report by the European Academies Science Advisory Council; nor did it draw any conclusion from the highly speculative phrasing of its own conclusion. Anecdotally, as the Dutch government had not raised the point, the CA ignored the fact that AR4 had also assumed that NETs could play a role in achieving a 450 scenario.Footnote 144 It is inevitable for an emissions reduction pathway to rely on a number of assumptions, including assumptions of technological development.Footnote 145 Even if some of these assumptions are highly speculative and many are the object of continuing debate, the IPCC’s Assessment Reports aim to establish best estimates based on a general understanding of the scientific community through an open deliberative process. The findings of such reports should not be discarded without strong and convincing evidence that, on a particular point, the report does not reflect the best scientific knowledge.

As such, it is regrettable that the CA rejected the conclusions of the IPCC’s most recent Assessment Report on the basis of a single sceptical publication. Relying on the latest climate science would have been essential for the analysis that the CA attempted to develop because estimated least-cost mitigation pathways are highly time-dependent: a 2020 mitigation target that appears feasible at an acceptable price in 2007 (when the relevant part of AR4 was published) may have become significantly more expensive in 2015 (when the DC first decided the case) if states have not followed a consistent mitigation pathway in the meantime. It would have been preferable for the CA to conduct a comprehensive review of the recent scientific literature on emissions reduction pathways in order to assess whether the mitigation scenarios presented in the WG3 contribution to AR5 fail to represent the best scientific knowledge and, if so, to determine the best current understanding of least-cost mitigation pathways. Alternatively – and perhaps more realistically, given resource constraints both for the court and for the parties themselves – the CA could have noted the high level of international recognition of the IPCC and placed a very high burden of proof on any party willing to challenge the conclusions of the IPCC’s latest Assessment Report.

Based on AR5, the objective of achieving the 2°C target does not seem to justify a 450 scenario, unless one considers that the scenario in question should be ‘likely’ (as opposed to ‘more likely than not’) to achieve the target.Footnote 146 Yet, the need to pursue a 450 scenario could have been argued in the light of the objective – already recognized at the outset of the dispute in a number of COP decisions (and subsequently integrated in the Paris Agreement) – of holding the increase in the global average temperature to ‘below 2°C’ (or ‘well below 2°C’ in the Paris Agreement), leaning towards 1.5°C.Footnote 147 On the other hand, as GHG concentrations in the atmosphere are in all likelihood already above 450 ppm CO2-eq,Footnote 148 and even though most emissions pathways compatible with the 450 scenario involve a transient overshoot,Footnote 149 the question needs at least to be asked whether achieving a 450 scenario remains possible at all, especially if one follows the CA in its dismissal of NETs.

Altogether, science offers much weaker support for Urgenda’s claim that Annex I states as a whole had to achieve at least a 25% emissions reduction by 2020 than the DC and the CA appeared to accept. Urgenda is reported to have argued that a 2020 emissions reduction target of 25% (from a 1990 basis) in the Netherlands ‘is not only necessary to continue to have a prospect of a limitation of global warming of up to (less than) 2°C, but is furthermore the most cost-effective’.Footnote 150 Formally, this statement is incoherent: the target is either ‘necessary’, which means that there is no alternative way to achieve the 2°C target, or it is ‘the most cost-effective’, which implies that there are alternative ways to achieve the 2°C target. In reality, no effort whatsoever on the part of the Netherlands is strictly ‘necessary’ for achieving a global temperature objective as the GHG emissions from the Netherlands make very little difference at the global scale: climate change could effectively be resolved through international cooperation without any mitigation effort by the Netherlands.Footnote 151

Rather than necessity, the courts appear to have been persuaded by the argument based on cost-effectiveness.Footnote 152 Yet, little attention was paid in the proceedings to the great uncertainty associated with the works of AR4 and AR5 on the most effective mitigation pathways.Footnote 153 Moreover, one could wonder how helpful a range as large as that accepted by the courts (from 25 to 40% emissions reduction) can be in determining precisely what states must do. More or less might be needed, and more or less might be realistically achievable, from Annex I states in general and from the Netherlands in particular, in order to contribute effectively to global cooperation on climate change mitigation.

Grounds for differentiation

Determining the emissions reduction target of a state based on a collective mitigation objective requires a determination of the contribution that this state must make to collective efforts towards the realization of this objective. The parties to climate treaties, including the Netherlands, have recognized a principle of common but differentiated responsibilities and respective capabilities (CBDR-RC), and have agreed that developed states ‘should take the lead in combating climate change’.Footnote 154 Beyond this, however, there has been little agreement regarding the criteria and scope for differentiation.Footnote 155 Even though there is a general consensus in climate politics that developed states have to do more than is required of developing states, there is no common understanding of how much more they ought to do and how this should be distributed among them.Footnote 156

As far as the differentiation between Annex I and non-Annex I countries is concerned, both courts appeared reluctant to interpret the CBDR-RC principle.Footnote 157 Yet, an interpretation of the CBDR-RC principle necessarily underlies the Annex I 25–40% emissions reduction target on which the judgments are based. For instance, neither court discussed the ‘equity interpretations’Footnote 158 on which WG3 had relied in AR4 to suggest that Annex I countries would most likely need to decrease their GHG emissions by 10–40% by 2020 (from a 1990 basis) in order to achieve the 2°C target. The DC simply noted that this target was necessary to achieve the 2°C ‘with due regard for a fair distribution’.Footnote 159 While the two courts attributed the Annex I 25–40% emissions reduction target to ‘international climate policy’,Footnote 160 the Bali Action PlanFootnote 161 and ‘virtually all COPs’,Footnote 162 this particular range has only been mentioned in the preamble to a decision adopted in 2010 by the meeting of the parties to the Kyoto Protocol.Footnote 163 COP decisions such as the Bali Action Plan call on global emissions reductions ‘consistent’ with AR4 but do not mention any particular range, thus reflecting, more than anything else, the absence of a global consensus on the 25–40% emissions reduction target.Footnote 164

The modalities of differentiation nevertheless had to be discussed when the courts turned to consider what the Annex I 25–40% emissions reduction target meant for the Netherlands. In this regard, both courts interpreted the situation of the Netherlands as requiring at least as much as the average Annex I country. The CA thus noted that the Netherlands had to ‘assume its responsibility’Footnote 165 given its higher-than-average per capita gross domestic product (GDP) and per capita GHG emissions – all the more so because it had ‘profited from fossil fuels for a long time’.Footnote 166 The DC also mentioned the need to consider ‘the onerousness of taking precautionary measures’Footnote 167 in the Netherlands, noting that the burden of proof would have been for the State to establish that it had ‘insufficient financial means to realize higher reduction measures’.Footnote 168

While the most often heard considerations for differentiation were mentioned, none was discussed at any length, and the reader of the judgments is likely to find the approach of differentiation by the courts somewhat expeditious. If the Netherlands has greater responsibility and greater capacity than most Annex I countries, as both courts suggest, and assuming an uncontested need for at least 25% emissions reduction in Annex I countries as a whole, thorough consideration should have been given to the possibility for the DC to impose a target higher than a 25% emissions reduction. Instead, the DC noted, perhaps too swiftly, that it saw ‘insufficient grounds to compel the State to adopt a higher level’ of ambition,Footnote 169 in light of the limitation of the court’s discretionary power.Footnote 170 Urgenda did not bring up the question on appeal. This, in itself, constitutes a major flaw in the treatment of this case. As Robiou du Pont and Meinshausen have noted, ‘systematic court decisions that governments must follow the least-ambitious end of an equity range would be insufficient to achieve the Paris Agreement’.Footnote 171

Statements made on behalf of the Netherlands

As well as science and principles of fairness, the courts relied on statements made on behalf of the Government of the Netherlands as a way to determine the ambit of its obligation on climate change mitigation. In a policy on climate change communicated in 2007, the government had expressed the objective of 30% emissions reduction by 2020 (from a 1990 basis).Footnote 172 This target was abandoned following, it seems, the growing understanding that neither Annex I countries as a whole, nor even the EU, would unconditionally commit to a 30% emissions target. The Netherlands had also actively supported an international target of a 25–40% emissions reduction in Annex I countries by 2020 (from a 1990 basis) during international negotiations – in particular, at the 2009 Copenhagen summit – as essential in order ‘to stay on credible track to keep the 2 degrees objective within reach’.Footnote 173

Both courts interpreted these developments as evidence that the Netherlands had once recognized both the need for a national target of 30% emissions reduction by 2020 (from a 1990 basis) and its ability to achieve it.Footnote 174 The courts highlighted that the State had provided no scientific justification for abandoning its 30% emissions reduction target, and no economic justification for its inability to achieve this target.Footnote 175 Furthermore, the courts interpreted the EU’s conditional target of a 30% emissions reduction by 2020 and statements associated with it as evidence that the EU had also acknowledged the shortcoming of its mitigation action.Footnote 176

This reasoning could have offered the strongest basis for the courts to determine the ambit of the obligation of the Netherlands to mitigate climate change. Admittedly, it is not clear whether the declarations made by the Netherlands in relation to its initial target were manifested with the will to be bound under international law,Footnote 177 as might be the case with the Cancún Pledges or the EU NDC, documents which were communicated to international institutions in a formal manner.Footnote 178 Nevertheless, having clearly admitted its responsibility, the Netherlands could not then deny the same without producing any sort of scientific or economic justification for its turnabout.Footnote 179 Interesting arguments could have been made in relation to the emerging principles of non-regression and progression, the central importance of which in relation to climate change mitigation was recognized in the Paris Agreement.Footnote 180 On the other hand, a difficulty is that what was considered feasible in 2007 might have become considerably more expensive in 2015 because of the failure of the State to take steps in the meantime.

Instead, having put much emphasis on scientific assessments and some emphasis on grounds for differentiation, the DC appeared to give only marginal importance to such statements. It determined, without much justification, that the State had to achieve at least a 25% emissions reduction by 2020 (from a 1990 basis), rather than the 30% emissions reduction announced in past policy documents.Footnote 181 Regrettably, Urgenda did not bring up the question in its cross-appeal.Footnote 182


The two judgments in Urgenda are, to date, the only judgments to have imposed a specific emissions reduction target on a state. Yet, they did not take place in isolation. Cases have been brought to courts in various countries – in particular, in the United States (US) – to determine the obligation of national authorities to mitigate climate change. In Juliana v. United States, 21 individual plaintiffs and two non-governmental organizations allege that the US government is violating its obligations under the public trust doctrine by its failure to commit sufficient efforts to the mitigation of climate change.Footnote 183 Public interest litigation focusing on the obligations of public authorities under the public trust doctrine is ongoing in several US states, which include Alaska,Footnote 184 Florida,Footnote 185 and Oregon,Footnote 186 while cases have been dismissed in various other states.Footnote 187 Outside the US, public interest litigation is ongoing against the governments of Belgium,Footnote 188 India,Footnote 189 Ontario (Canada),Footnote 190 Pakistan,Footnote 191 and the United Kingdom,Footnote 192 as well as against the institutions of the EU,Footnote 193 among many others.

Each case is likely to raise unique questions relating to the context in which it takes place. In particular, the question of standing may unfold differently depending on national rules. Yet, other aspects of the judgments in Urgenda may be of direct relevance to discussions of other cases, including the courts’ approach to the drop-in-the-ocean problem and the determination of the ambit of a state’s obligation. Some aspects of the judgments in Urgenda may read as cautionary tales – in particular, the arguably misleading treatment of scientific literature as normative authority and the exclusion of the latest IPCC report on insufficient grounds. As commentators of the judgment of the DC have noted, it would be desirable in such cases that courts appoint scientific experts,Footnote 194 who may help the court to understand climate science.Footnote 195 Other aspects of the two judgments in Urgenda highlight the potential for fruitful arguments based, for instance, on prior statements made by national authorities about the determination of their own responsibility to mitigate climate change. This argument could be particularly effective in the US, as the Trump administration does little to ensure the implementation of national targets on climate change mitigation previously communicated under the Obama administration with a relatively clear will to be bound under international law.Footnote 196 In Indigenous Environmental Network v. Department of State, the District Court of Montana quashed the decision of the Department of State under the Trump administration to authorize the construction of the Keystone XL Pipeline, which the same department had prevented in 2015 under the Obama administration, on the ground that the agency had failed to provide ‘a reasoned explanation’ for disregarding prior factual findings relating to the impact of the project on climate change.Footnote 197

Urgenda can also be viewed as a cautionary tale for the prospects of climate change litigation. The State’s concern about the extent of the power of the judge is not entirely groundless. The treatment of particularly complex scientific and ethical questions by the courts is certainly questionable. The outcome – the order to achieve a 25% emissions reduction by 2020 compared with 1990 – relies on a succession of questionable assumptions. Any variation of any of these assumptions would lead a court to dramatically different conclusions, which jeopardizes legal determinacy. An alternative reading of the contribution of WG3 to AR4, for instance, would have suggested that a 10% emissions reduction by 2020 (from a 1990 basis) was sufficient for Annex I parties taken as a whole.Footnote 198 The adoption of two temperature targets (‘well below 2°C’ and efforts towards 1.5°C) in the Paris Agreement only adds to the complexity of determining a state’s mitigation obligation.Footnote 199

Yet, the conclusion of this tale does not have to be that courts have no role to play in interpreting states’ mitigation obligations.Footnote 200 Rather, it should lead litigants and the courts they seize to question whether a purely top-down approach to the interpretation of a state’s obligation to mitigate climate change, based on the determination of global mitigation objectives and an analysis of effort-sharing criteria, is the best approach. To reduce the risk of a cassation in Urgenda, greater weight could have been given in the appeal proceedings to prior statements made on behalf of the State, whereby specific mitigation targets were determined nationally as both feasible and appropriate. International processes whereby states are invited to determine and communicate their contribution to global cooperation on climate change mitigation seek to ensure that such statements are made in a transparent manner – and can then be relied upon, if needed, as a basis for the interpretation of a state’s mitigation obligation. Absent such statements, or if the ambition announced inthese statements appears to be insufficient, it would be preferable for a court to trigger national processes through which appropriate mitigation action can be defined by way of procedural injunctions.Footnote 201 For instance, Urgenda could have asked the courts to order the government to develop an analysis of plausible global mitigation pathways leading to the achievement of globally agreed mitigation objectives, and to devise and implement a national mitigation strategy consistent with this analysis.

Overall, what should really be retained from Urgenda is the need for more refined methodology to interpret the mitigation obligations of states which can be inferred from general norms (such as human rights law, tort law, or international environmental law). This note aims to show that the arguments deployed by Urgenda and accepted by the courts to assess the necessary mitigation target of the Netherlands were rudimentary and often unconvincing. Yet, what is the alternative? Little methodological research has been carried out so far to determine the requisite level of ambition for a state to comply with its general mitigation obligations. These methodological questions are here to stay and will become increasingly relevant as more cases are brought before various courts throughout the world.



The Chinese University of Hong Kong Faculty of Law (Hong Kong).


The author is thankful to three anonymous TEL reviewers for insightful comments and advice.


1 By-laws of Urgenda, Art. 2, as cited in the District Court of The Hague (DC), Urgenda Foundation v. The State of the Netherlands, Case No. C/09/456689 / HA ZA 13-1396, 24 June 2015, para. 2.2, available at: (Urgenda 1). Quotations are from the translation provided by the Court.

2 Urgenda 1, para. 2.6.

3 See the letter of the State Secretary for Infrastructure and the Environment of 11 Dec. 2012, cited ibid., para. 2.7.

4 Ibid., para. 5.1.

5 Court of Appeal of The Hague (CA), The State of the Netherlands (Ministry of Infrastructure and the Environment) v. Urgenda Foundation, C/09/456689 / HA ZA 13-1396, 9 Oct. 2018, available at: (Urgenda 2). Quotations are from the translation provided by the Court.

6 See Government of the Netherlands, ‘State to Bring Cassation Proceedings in Urgenda Case’, 16 Nov. 2018, available at:

7 Statement by Ivo de Zwaan on behalf of the Netherlands during the Multilateral Assessment of the Third Biennial Report of the Netherlands, held in Katowice (Poland), 7 Dec. 2018, available at: Additional measures under consideration include the anticipated shutdown of a coal-fired power plant.

8 Rome (Italy), 4 Nov. 1950, in force 3 Sept. 1953, available at:

9 See n. 106 below.

10 Numerous pending cases raise similar questions: e.g., ENvironnement JEUnesse v. Canada; VZW Klimaatzaak v. Belgium; Klimaatzaak v. Belgium; and Ali v. Pakistan. Information on these and other cases can be found on Climate Change Litigation Databases developed by the Sabin Center for Climate Change Law at Columbia Law School (United States), available at:; and in the database of ‘Climate Change Law of the World’, developed by the Grantham Research Institute on Climate Change and the Environment at the London School of Economics and Political Science (United Kingdom), available at:

11 United Nations (UN) Climate Change, ‘Netherlands National Inventory Report 2018’, 13 Apr. 2018, p. 26, available at:, for data excluding land use, land-use change and forestry (LULUCF). MT CO2-eq indicates GHG emissions the warming effect of which is equivalent to that of a megatonne of carbon dioxide.

12 Ibid., p. 28.

13 Ibid., pp. 6 and 87.

14 Per capita emissions in the EU are estimated at 8.4 T CO2-eq/year in 2016, based on the EU’s GHG emissions without LULUCF (reported in UN Climate Change, ‘European Union National Inventory Report 2018’, 15 May 2018, p. vii, available at:, and a population of 511.8 million (according to Eurostat, ‘Population and Population Change Statistics’, July 2017, available at: See also Urgenda 2, para. 26.

15 Netherlands National Inventory Report 2018, n. 11 above, p. 25 and passim.

16 Ibid., p. 70 (Table 3.1).

17 See UNFCCC Secretariat, ‘Compilation of Economy-wide Emission Reduction Targets to be Implemented by Parties included in Annex I to the Convention’ (4–15 June 2014), UN Doc. FCCC/SBSTA/2014/INF.6, para. 11, available at:

18 Doha Amendment to the Kyoto Protocol, in Decision 1/CMP.8, ‘Amendment to the Kyoto Protocol pursuant to its Article 3, para. 9 (the Doha Amendment)’ (8 Dec. 2012), UN Doc. FCCC/KP/CMP/2012/13/Add.1, Annex. While the Doha Amendment has not yet entered into force, it was ratified by the EU and its Member States on 21 Dec. 2017.

19 Kyoto (Japan), 11 Dec. 1997, in force 16 Feb. 2005, available at:

20 UNFCCC Secretariat, n. 17 above, para. 12; Doha Amendment, n. 18 above, note 7 under revised Annex B.

21 It has repeatedly been pointed out, however, that the EU has no institutional mechanism to assess the fulfilment of the condition associated with its 30% emissions reduction target: see, e.g., UNFCCC Subsidiary Body for Implementation (SBI), 49th Session, ‘Multilateral Assessment Questions and Answers: The European Union’ (Sept.–Nov. 2018), p. 7 (question posed by Brazil), available at:

22 See Latvia et al., ‘Intended Nationally Determined Contribution of the EU and its Member States’, 6 Mar. 2015, available at:

23 Paris (France), 12 Dec. 2015, in force 4 Nov. 2016, available at:

24 Decision No. 406/2009/EC on the Effort of Member States to Reduce their Greenhouse Gas Emissions to Meet the Community’s Greenhouse Gas Emission Reduction Commitments up to 2020 [2009] OJ L 140/136 (Effort Sharing Decision), recital 8.

25 Directive 2003/87/EC establishing a Scheme for Greenhouse Gas Emission Allowance Trading within the Community and amending Council Directive 96/61/EC [2003] OJ L 275/32.

26 European Commission, ‘7th National Communication & 3rd Biennial Report from the European Union under the UN Framework Convention on Climate Change (UNFCCC)’, Dec. 2017, p. 237, available at:

27 Directive 2009/29/EC amending Directive 2003/87/EC so as to Improve and Extend the Greenhouse Gas Emission Allowance Trading Scheme of the Community [2009] OJ L 140/63, recital 5. The year 2005 is used as the baseline in EU climate law because estimates are more accurate than those for 1990.

28 N. 24 above.

29 Ibid., Annex II.

30 Netherlands National Inventory Report 2018, n. 11 above.

31 Urgenda 1, para. 4.26 (based on domestic policy documents). See also The Netherlands, ‘Second Biennial Report under the United Nations Framework Convention on Climate Change’, 31 Dec. 2015, p. 54, available at: (projecting a decrease in GHG emissions of 18% by 2020 (1990 basis) with existing measures, or 19% with additional measures).

32 Netherlands National Inventory Report 2018, n. 11 above, pp. 26 and 63.

33 Centraal Bureau voor de Statistiek (CBS), ‘CO2 Emissions in 2017 the Same as in 1990’, 10 Sept. 2018, available at:

34 Urgenda 1, para. 3.1(6).

35 New York, NY (US), 9 May 1992, in force 21 Mar. 1994, available at:, in particular Art. 4.2(a) and (b).

36 N. 19 above.

37 N. 18 above.

38 Urgenda 1, para. 4.42. See also Mayer, B., ‘The Relevance of the No-Harm Principle to Climate Change Law and Politics’ (2016) 19(1) Asia Pacific Journal of Environmental Law, pp. 79104 CrossRefGoogle Scholar .

39 N. 8 above, Arts 2 and 8.

40 The Constitution of the Kingdom of the Netherlands (2008), published by the Ministry of the Interior and Kingdom Relations, Constitutional Affairs and Legislation Division in collaboration with the Translation Department of the Ministry of Foreign Affairs, Art. 21, available at: (according to which ‘[i]t shall be the concern of the authorities to keep the country habitable and to protect and improve the environment’).

41 Burgerlijk Wetboek (Dutch Civil Code), Book 5, Section 37 (prohibition of nuisance).

42 See IPCC (B. Metz et al. (eds)), Climate Change 2007: Mitigation of Climate Change. Contribution of Working Group III to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change (Cambridge University Press, 2007).

43 Urgenda 1, para. 4.42.

44 Ibid., para. 4.45. This aspect of the judgment was criticized, among others, in A. Tabau & C. Cournil, ‘New Perspectives for Climate Justice: District Court of The Hague, 24 June 2015, Urgenda Foundation versus the Netherlands’ (2015) 12(3–4) Journal for European Environmental & Planning Law, pp. 221–40, at 229.

45 Urgenda 1, para. 4.36.

46 See Burgerlijk Wetboek, n. 41 above, Book 6, Art. 162. See Urgenda 1, n. 1 above, paras 4.46 and 4.55.

47 Urgenda 1, para. 4.65.

48 Ibid., para. 4.14.

49 Ibid., para. 4.17.

50 Ibid., para. 4.20.

51 Annex I of the UNFCCC, n. 35 above, contains a list of developed countries with more stringent obligations under the UNFCCC.

52 Urgenda 1, para. 4.29.

53 Ibid., para. 5.1.

54 Urgenda 2, para. 31.

55 Ibid., para. 32.

56 Ibid., para. 35.

57 Ibid., para. 36.

58 Ibid., para. 41.

59 Ibid., para. 45.

60 See, in particular, ibid., para. 63 (on the precautionary principle).

61 Ibid., para. 76.

62 Ibid., para. 71.

63 Ibid., para. 75.

64 See Netherlands National Inventory Report 2018, n. 11 above, p. 28. See also Centraal Bureau voor de Statistiek (CBS), ‘Greenhouse Gas Emissions Slightly Down in 2017’, 9 May 2018, available at: (for a preliminary estimate of 2017 GHG emissions at 193 MT CO2-eq, representing a reduction of 13.4% below 1990 emissions as previously reported. All data are without LULUCF).

65 See Decision 15/CP.17, ‘Revision of the UNFCCC Reporting Guidelines on Annual Inventories for Parties included in Annex I to the Convention’ (11 Dec. 2011), UN Doc. FCCC/CP/2011/9/Add.2.

66 See Netherlands National Inventory Report 2015, 31 Mar. 2016, p. 25, available at: The application of the 2006 methodology ascribes a higher global warming potential value to methane, emissions of which have rapidly decreased in the Netherlands since 1990. This was discussed briefly in Urgenda 2, paras 21 and 47.

67 See, e.g., CBS, n. 33 above.

68 UNFCCC Secretariat, ‘Report on the Technical Review of the Third Biennial Report of the Netherlands’, 1 Aug. 2018, UN Doc. FCCC/TRR.3/NLD, p. 18, available at: (emissions without LULUCF). See also The Netherlands, ‘Third Biennial Report under the United Nations Framework Convention on Climate Change’, 31 Dec. 2017, pp. 67–8, available at:

69 The Netherlands, ibid., p. 85 (noting that GHG emissions in 2020 could range from 163 to 181 MT CO2-eq (90% reliability interval). This corresponds with a reduction from 19 to 17%. All data are without LULUCF).

70 UNFCCC Secretariat, n. 68 above, para. 88.

71 On the measures under consideration, see n. 7 above.

72 Urgenda 1, para. 3.3.

73 Ibid., para. 3.3.

74 See ibid., para. 4.5 (noting that the State ‘defers to the court’s opinion’ on the question); but see also Urgenda 2, para. 37 (according to which ‘the State argued, as understood by the Court, that Urgenda cannot act on behalf of future generations of Dutch nationals’).

75 See Dutch Civil Code, n. 41 above, Art. 305a.

76 See Urgenda 1, para. 4.92; Urgenda 2, para. 37.

77 Urgenda 2, para. 38 (citing the legislative history behind Book 3, Art. 305a of the Dutch Civil Code, n. 41 above).

78 See section 2.2 above.

79 See section 2.3 above.

80 Urgenda 1, paras 4.36 and 4.38–4.39.

81 Ibid., para. 4.51.

82 IPCC, Climate Change 2014: Synthesis Report. Contribution of Working Groups I, II and III to the Fifth Assessment Report of the Intergovernmental Panel on Climate Chang (IPCC, 2015), pp. 40–4, 60–2.

83 Ibid., p. 67.

84 Ibid., pp. 67–73. See also Boyle, A., ‘Climate Change, the Paris Agreement and Human Rights’ (2018) 67(4) International & Comparative Law Quarterly, pp. 759777 CrossRefGoogle Scholar ; Mayer, B., ‘Human Rights in the Paris Agreement’ (2016) 6(1–2) Climate Law, pp. 109117 CrossRefGoogle Scholar .

85 See, e.g., Reimann, L. et al., ‘Mediterranean UNESCO World Heritage at Risk from Coastal Flooding and Erosion Due to Sea-level Rise’ (2018) 9 Nature Communication online articlesCrossRefGoogle ScholarPubMed , article no. 4161 (2018), available at:

86 See Mayer, B., The International Law on Climate Change (Cambridge University Press, 2018)Google Scholar ; Mayer, n. 38 above. See also Rio Declaration on Environment and Development, adopted by the UN Conference on Environment and Development, Rio de Janeiro (Brazil), 3–14 June 1992, UN Doc. A/CONF.151/26/Rev.1 (Vol. I), Principle 2, available at:; International Court of Justice (ICJ), Legality of the Threat or Use of Nuclear Weapons, Advisory Opinion of 8 July 1996, ICJ Reports 1996, p. 226, para. 29.

87 See, e.g., Convention on Biological Diversity (CBD), Rio de Janeiro (Brazil), 5 June 1992, in force 29 Dec. 1993, available at:

88 See UN Convention on the Law of the Sea (UNCLOS), Montego Bay (Jamaica), 10 Dec. 1982, in force 16 Nov. 1994, Art. 192, available at:

89 See UNESCO Convention concerning the Protection of the World Cultural and Natural Heritage (WHC), Paris (France), 16 Nov. 1972, in force 17 Dec. 1975, Art. 4, available at:

90 See, in particular, International Covenant on Economic, Social and Cultural Rights (ICESCR), New York, NY (US), 16 Dec. 1966, in force 3 Jan. 1976, Art. 2, available at:; International Covenant on Civil and Political Rights (ICCPR), New York, NY (US), 16 Dec. 1966, in force 23 Mar. 1976, Art. 2, available at:

91 See Peel, J. & Osofsky, H.M., ‘A Rights Turn in Climate Change Litigation?’ (2018) 7(1) Transnational Environmental Law, pp. 3767 CrossRefGoogle Scholar .

92 Urgenda 1, para. 4.80; Urgenda 2, para. 54.

93 Lisbon (Portugal), 13 Dec. 2007, in force 1 Dec. 2009, consolidated version [2012] OJ C 326/47, Art. 192, available at:

94 Ibid., Art. 193.

95 Urgenda 2, para. 54; see also Urgenda 1, para. 4.80.

96 Urgenda 1, para. 4.81; Urgenda 2, para. 55.

97 See, e.g., Regulation (EU) No. 1210/2011 amending Regulation (EU) No. 1031/2010 in particular to Determine the Volume of Greenhouse Gas Emission Allowances to be Auctioned Prior to 2013 [2011] OJ L 56/11.

98 Decision (EU) 2015/1814 concerning the Establishment and Operation of a Market Stability Reserve for the Union Greenhouse Gas Emission Trading Scheme and amending Directive 2003/87/EC [2015] OJ L 264/1. See Urgenda 2, para. 56.

99 UNFCCC Secretariat, n. 68 above, para. 38.

100 Urgenda 1, para. 4.81; Urgenda 2, para. 56. On the DC’s confusion between the waterbed effect and the question of carbon leakage in its judgment, see Peeters, M., ‘Urgenda Foundation and 886 Individuals v. The State of the Netherlands: The Dilemma of More Ambitious Greenhouse Gas Reduction Action by EU Member States’ (2016) 25(1) Review of European, Comparative and International Environmental Law, pp. 123129 CrossRefGoogle Scholar , at 126.

101 Urgenda 2, para. 61.

102 See n. 106 below.

103 Urgenda 1, paras 4.78 and 4.90.

104 Urgenda 2, para. 61.

105 See Zahar, A., ‘The Contested Core of Climate Law’ (2018) 8(3–4) Climate Law, pp. 244260 CrossRefGoogle Scholar .

106 In 2010, about 0.42% of global GHG emissions occurred in the Netherlands, according to the Emissions Database for Global Atmospheric Research (EDGAR), cited in Urgenda 1, para. 2.27.

107 Urgenda 2, para. 62; see also Urgenda 1, para. 4.79.

108 Urgenda 1, para. 4.89.

109 Supreme Court of the Netherlands, HR 23 Sept. 1968, NJ 1989, 743; Urgenda 1, para. 4.79.

110 Ibid., para. 64.

111 Ibid.

112 Ibid.

113 I. Kant, Fundamental Principles of the Metaphysic of Morals (Thomas Kingsmill Abbott transl., 1785), Section 2, available at:

114 See Urgenda 2, para. 62 (noting the responsibility of the State, ‘in its territory, within its capabilities … in concert with the efforts of other states’).

115 See, e.g., van Zeben, J., ‘Establishing a Governmental Duty of Care for Climate Change Mitigation: Will Urgenda Turn the Tide?’ (2015) 4(2) Transnational Environmental Law, pp. 339357 CrossRefGoogle Scholar , at 344.

116 See Arts 2.1 and 3 Paris Agreement. See generally Mayer, B., ‘Construing International Climate Change Law as a Compliance Regime’ (2018) 7(1) Transnational Environmental Law, pp. 115137 CrossRefGoogle Scholar ; and Mayer, n. 86 above, pp. 218–37.

117 See Urgenda 1, para. 102; Urgenda 2, para. 69.

118 IPCC, n. 42 above.

119 Urgenda 1, para. 4.14; Urgenda 2, para. 12.

120 See Urgenda 2, para. 44.

121 See Urgenda 1, para. 4.20; Urgenda 2, para. 12.

122 See Urgenda 1, para. 4.23 (with a mistake in the translation: the original version of the judgment mentions a rate of 25%–40%, not 20%–40%); Urgenda 2, para. 12.

123 See generally Hulme, M., Why We Disagree about Climate Change: Understanding Controversy, Inaction and Opportunity (Cambridge University Press, 2009)CrossRefGoogle Scholar .

124 Urgenda 1, para. 4.11; see also Urgenda 2, para. 12.

125 See S. Gupta et al., ‘Policies, Instruments and Co-operative Arrangements’, in IPCC, n. 42 above, pp. 746–807, at 769 (refraining from taking a position when noting the ‘option … to set a goal for long-term GHG concentrations or maximal temperature rise (such as the 2°C goal proposed by the EU)’). See also Randalls, S., ‘History of the 2°C Climate Target’ (2010) 1(4) WIREs Climate Change, pp. 598605 CrossRefGoogle Scholar ; Knutti, R. et al., ‘A Scientific Critique of the Two-Degree Climate Change Target’ (2016) 9(1) Nature Geoscience, pp. 1318 CrossRefGoogle Scholar .

126 B. Fisher et al., ‘Issues related to Mitigation in the Long-Term Context’ in IPCC, n. 42 above, pp. 169–250, at 227.

127 Gupta et al., n. 125 above, p. 776.

128 Ibid., p. 748.

129 Urgenda 1, para. 2.16.

130 See also L. Clarke et al., ‘Assessing Transformation Pathways’, in IPCC (O. Edenhofer et al., eds), Climate Change 2014: Mitigation of Climate Change. Contribution of Working Group III to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change (Cambridge University Press, 2014), pp. 413–510, at 433.

131 Urgenda 1, para. 4.85.

132 IPCC, Global Warming of 1.5°C (2018), available at:

133 IPCC, n. 130 above.

134 O. Edenhofer et al., ‘Summary for Policymakers’, in IPCC, n. 130 above, pp. 1–30, at 10 (emphasis added), cited in Urgenda 1, para. 2.19.

135 Urgenda 2, para. 12.

136 See Urgenda 1, para. 4.21; Urgenda 2, para. 49.

137 See, in particular, Urgenda 1, para. 4.22.

138 See IPCC, Principles Governing IPCC Work (approved 1–3 Oct. 1998, last updated 14–18 Oct. 2013), para. 2, available at:–principles/ipcc–principles.pdf.

139 The pre-industrial atmospheric concentration in GHGs is estimated at around 280 ppm CO2-eq: IPCC, n. 82 above, p. 3.

140 Urgenda 2, paras 12 and 49.

141 Clarke et al., n. 130 above, pp. 485–6.

142 European Academies Science Advisory Council, Negative Emission Technologies: What Role in Meeting Paris Agreement Targets? (EASAC Policy Report 35, Feb. 2018), p. 1, available at: (emphasis added), cited in Urgenda 2, para. 49.

143 Urgenda 2, para. 49 (emphasis added).

144 Fisher et al., n. 126 above, p. 198.

145 Ibid., p. 172.

146 See Lambrecht, J. & Ituarte-Lima, C., ‘Legal Innovation in National Courts for Planetary Challenges: Urgenda v. State of the Netherlands’ (2016) 18(1) Environmental Law Review, pp. 5764 CrossRefGoogle Scholar , at 62 (suggesting that even a 66% chance of achieving the 2°C target may not be sufficient).

147 See, e.g., UNFCCC Secretariat, Decision 1/CP.16, ‘The Cancún Agreements: Outcome of the Work of the Ad Hoc Working Group on Long-Term Cooperative Action under the Convention’ (10–11 Dec. 2010), UN Doc. FCCC/CP/2010/7/Add.1, para. 4; UNFCCC Secretariat, Decision 1/CP.20, ‘Lima Call for Climate Action’ (14 Dec. 2014), UN Doc. FCCC/CP/2014/10/Add.1, Rec. 7. See also Art. 2.1(a) Paris Agreement, which adds ‘well below 2°C’ (emphasis added).

148 See European Environment Agency, ‘Atmospheric Greenhouse Gas Concentrations’, 31 Jan. 2018, available at: (indicating 444 ppm CO2-eq in 2015 with an increase of around 4 ppm CO2-eq per year, thus suggesting that the threshold of 450 ppm CO2-eq was passed around 2017).

149 See O. Edenhofer et al., ‘Technical Summary’ in IPCC, n. 130 above, pp. 31–108, at 52; Gupta et al., n. 125 above, p. 776. Temporary overshoots may be caused by short-lived non-CO2 GHGs.

150 Urgenda 1, para. 3.2.

151 See A. Zahar, ‘The Urgenda Appeal Decision and the Argument from Physical Necessity’, 3 Dec. 2018, available at:

152 Gupta et al., n. 125 above, p. 776.

153 See, e.g., Fisher et al., n. 126 above, pp. 197–200 and 203–6; Clarke et al., n. 130 above, pp. 433–4 (on timing) and 448–62 (on costs).

154 Art. 3(1) UNFCCC; Art. 2(2) Paris Agreement.

155 See, e.g., Rajamani, L., ‘Common But Differentiated Responsibilities’, in M. Faure (ed.), Elgar Encyclopedia of Environmental Law (Edward Elgar, 2018), pp. 291302 Google Scholar ; Cullet, P., ‘Common But Differentiated Responsibilities’, in M. Fitzmaurice, D.M. Ong & P. Merkouris (eds), Research Handbook on International Environmental Law (Edward Elgar, 2010), pp. 161181 Google Scholar .

156 Cf. Galvão Ferreira, P., ‘“Common But Differentiated Responsibilities” in the National Courts: Lessons from Urgenda v. The Netherlands ’ (2016) 5(2) Transnational Environmental Law, pp. 329351 CrossRefGoogle Scholar (which emphasizes the consensus more than its limitations).

157 The principle is not even formally cited by the CA: see Urgenda 2, para. 8, for the closest allusion to equity, responsibilities and capacities. In the judgment of the DC, the principle is mentioned only in the section on ‘facts’, not in the section on their ‘assessment’, although, arguably, its ‘spirit’ is present: see Lambrecht & Ituarte-Lima, n. 146 above, p. 63.

158 T. Barker et al., ‘Technical Summary’ in IPCC, n. 42 above, pp. 25–94, at 90.

159 Urgenda 1, para. 4.23.

160 See Urgenda 1, paras 4.31, 4.84 and passim.

161 Urgenda 2, para. 11.

162 Ibid., para. 51.

163 UNFCCC Secretariat, Decision 1/CMP.6, ‘The Cancún Agreements: Outcome of the Work of the Ad Hoc Working Group on Further Commitments for Annex I Parties under the Kyoto Protocol at its Fifteenth Session’ (10–11 Dec. 2010), UN Doc. FCCC/KP/CMP/2010/12/Add.1, Rec. 6. See also UNFCCC Secretariat, Decision 1/CP.13, ‘Bali Action Plan’ (14–15 Dec. 2007), UN Doc. FCCC/CP/2007/6/Add.1, Rec. 5 (which emphasizes the urgency to address climate change and is accompanied by a footnote containing a reference to the WG3 contribution to AR4. Far from endorsing any particular target, the decision did not even formally ‘take note’ or ‘acknowledge’ the findings of the report).

164 Decisions 1/CP.16, n. 147 above, para. 37; UNFCCC Secretariat Decision 1/CP.18, ‘Agreed Outcome pursuant to the Bali Action Plan’ (8 Dec. 2012), UN Doc. FCCC/CP/2012/8/Add.1, para. 7.

165 Urgenda 2, para. 66.

166 Ibid., paras 26, 44, 60 and 66. See also Urgenda 1, para. 4.57.

167 Urgenda 1, para. 4.63; see also ibid., paras 4.67 et seq. The DC thus alluded to a range of geographical and economic circumstances which may hinder or facilitate climate change mitigation in the country, such as the potential for producing renewable energy.

168 Urgenda 2, para. 4.77.

169 Urgenda 1, para. 4.86.

170 Ibid.

171 Robiou du Pont, Y. & Meinshausen, M., ‘Warming Assessment of the Bottom-up Paris Agreement Emissions Pledges’ (2018) 9(4810) Climate Change Nature, pp. 110 Google ScholarPubMed , at 2.

172 Government of the Netherlands, ‘Nieuwe Energie voor het Klimaat’ [New Energy for the Climate], 3 Sept. 2007, available at: (cited in Urgenda 1, para. 2.71). See also Urgenda 1, para. 4.26; Urgenda 2, para. 28.

173 See letter of the Minister of Housing, Spatial Planning and the Environment to the House of Representatives, 12 Oct. 2009 (cited in Urgenda 2, para. 19).

174 Urgenda 2, para. 52; see also Urgenda 1, para. 4.29.

175 See, e.g., Urgenda 1, paras 4.29 and 4.70; Urgenda 2, para. 52.

176 See Urgenda 2, para. 52. See generally, e.g., Directive 2009/29/EC, n. 27 above, recital 6 (stating that the European Council’s objective of a 30% emissions reduction by 2020 was ‘scientifically necessary to avoid dangerous climate change’).

177 See International Law Commission, ‘Guiding Principles Applicable to Unilateral Declarations of States Capable of Creating Legal Obligations’ (2006) Yearbook of the International Law Commission, Vol. II, Pt Two, Principle 1. See also ICJ, Nuclear Tests (Australia v. France), Judgment of 20 Dec. 1974, ICJ Reports 1974, pp. 267–8, paras 43 and 46.

178 See Mayer, B., ‘International Law Obligations Arising in Relation to Nationally Determined Contributions’ (2018) 7(2) Transnational Environmental Law, pp. 251275 CrossRefGoogle Scholar , at 262–70.

179 Such a turnabout might be viewed as an estoppel in common law countries and even under international law: see, e.g., T. Cottier & J.P. Müller, ‘Estoppel’, in Max Planck Encyclopedia of Public International Law (Oxford University Press, 2012), pp. 671–7.

180 See Arts 3 and 4.3 Paris Agreement. See generally Club des Jurists, ‘Preliminary Draft of a Global Pact for the Environment’, 24 June 2017, Art. 17, available at:; Prieur, M., ‘Non-Regression in Environmental Law’ (2012) 5(2) Surveys and Perspectives Integrating Environment & Society, pp. 5356 Google Scholar .

181 See Urgenda 1, para. 4.86 (alluding only to ‘insufficient grounds to compel the State to adopt a higher level than the minimum level of 25%’).

182 See Urgenda 2, paras 3 and 75.

183 The case was still ongoing as of Oct. 2018: Climate Case Chart, Juliana v. United States, available at:

184 Climate Case Chart, Sinnok v. Alaska, available at:

185 Climate Case Chart, Reynolds v. Florida, available at:

186 Chernaik v. Brown, Or. Cir. Ct, 16-11-09273 (11 May 2015), currently on appeal.

187 See, e.g., AJI P. v. State, 2018 WL 3978310 (Superior Court of Washington, 14 Aug. 2018); Funk v. Wolf, 638 Pa. 726 (Supreme Court of Pennsylvania, 28 Mar. 2017); Sanders-Reed v. Martinez, 350 P.3d 1221 (Court of Appeal of New Mexico, 12 Mar. 2015); Kanuk v. State of Alaska, 335 P.3d 1088 (Supreme Court of Alaska, 12 Sept. 2014). A notable success for climate plaintiffs was reached in Kain v. Department of Environmental Protection, 474 Mass. 27849 N.E.3d 1124 (17 May 2016), but on the basis of a clear statutory requirement that the Department of Environmental Protection promulgate regulations on the reduction of GHG emissions.

188 See generally the website of Klimaatzaak, available at:

189 Climate Case Chart, Pandey v. India, available at: The case is pending before the National Green Tribunal of India.

190 Climate Case Chart, Greenpeace Canada v. Minister of the Environment, Conservation, and Parks; Lieutenant Governor in Council, available at:

191 Climate Change Laws of the World, Ali v. Federation of Pakistan (Supreme Court of Pakistan), available at:

192 Climate Case Chart, Plan B Earth and Others v. Secretary of State for Business, Energy, and Industrial Strategy’, available at: (pending, on appeal).

193 Case T-330/18, Carvalho and Others v. Parliament and Council [2018] OJ C 285/34.

194 Roy, S. & Woerdman, E., ‘Situating Urgenda v The Netherlands within Comparative Climate Change Litigation’ (2016) 34(2) Journal of Energy & Natural Resources Law, pp. 165189 CrossRefGoogle Scholar , at 165.

195 See Peeters, n. 100 above, p. 128.

196 See, e.g., US, ‘Nationally Determined Communication’, 3 Sept. 2016, available at:; US–China Joint Announcement on Climate Change, Beijing (China), 12 Nov. 2014, available at: See generally Sabin Center for Climate Change Law, ‘Climate Deregulation Tracker’, available at:

197 Indigenous Environmental Network v. US Department of State (2018) —F.Supp.3d —, 2018 WL 5840768 (DC Mont.).

198 See n. 128 above and accompanying text. For an entirely different methodology suggesting a very different interpretation of the EU’s general mitigation obligation, see also Memorandum for the Applicants in Carvalho v. European Parliament and Council (23 May 2018), available at:

199 Art. 2.1(a) Paris Agreement.

200 See Zahar, n. 151 above.

201 See by analogy Plan B Earth and Others, ‘Statement of Facts and Grounds’, 8 Dec. 2017, available at: See also Memorandum for the Applicants in ENvironnement JEUnesse v. Canada, 26 Nov. 2018, available at: (unofficial English translation).

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