Edoardo Chiti, Alberto di Martino, Gianluigi Palombella (a cura di)
L'era dell'interlegalità
DOI: 10.1401/9788815370334/c17
In similar vein, such expansive interpretation of the right to property in article 21 of the Convention allowed
{p. 480}the Court to promote environmental protection in indigenous lands in several other cases [62]
. However, at the same time, this method of greening indigenous property rights to foster environmental justice is not without limitations. First of all, as the IACtHR clarified in that same Sarayaku v. Ecuador case, natural resources on indigenous people’s lands enjoy protection under article 21 in so far as they are “traditionally used and (…) necessary for their physical and cultural survival and the development and continuation of their worldview” [63]
. In other words, the promotion of environmental protection under the umbrella of article 21 is limited to situations where it can be demonstrated that environmental degradation prevents indigenous people from enjoying their traditional ways of living and using natural resources [64]
. Secondly, in the Court’s view, article 21 does not per se prohibit the state from allowing third parties to exploit natural resources in indigenous land, even when such exploitation may cause environmental degradation and negatively affect indigenous ways of living [65]
. Indeed, according to the Court’s jurisprudence, limitations to the communal right to property of indigenous peoples are allowed, providing that “they are aimed at achieving a legitimate objective (…) without denying their right to exist as people” [66]
. {p. 481}
As this group of cases illustrate, the “greening approach” falls within the purely instrumental approach to environmental protection outlined above, as it only mitigates the adverse environmental impact on well-being of particular individuals or a group of individuals and is not concerned with the environmental protection per se [67]
. Instead, in these particular cases, it is the protection of indigenous people’s rights and their traditional ways of living that remain the center of the complaint, as opposed to the environmental degradation. To put it differently, from the perspective of inter-legality, “the human rights greening” amounts to a parochial approach, which merely advances the objective of the human rights regime, without taking into account the wider aim of protecting the environment as a value in its own right. Importantly, as a result of viewing the environmental issues exclusively through the human rights paradigm, this category of cases requires the proof that plaintiff’s rights are sufficiently affected by the environmental harm, in order to force the state to mitigate the environmental degradation [68]
. In other words, under the “human rights greening” approach, the individual will have no standing without the strong link between the environmental degradation and the human rights violation, thereby excluding the possibility of public interest litigation by wider civil society [69]
.
In fact, other cases before the IACtHR demonstrate that collective claims to enjoyment of natural resources from general population – coming outside the context of indigenous peoples’ rights – so far, have not been accepted in the Inter-American human rights system [70]
. This is illustrated by Metropolitan Nature Reserve case, in which the Inter-American Commission on Human Rights rejected the claim of citizens of Panama alleging the violation of the {p. 482}right to property under article 21 due to the construction of a roadway through protected area in Panama City [71]
. In particular, the Commission declared the complaint inadmissible as it concerned “abstract victims represented in an actio popularis”, rather than specifically identified and defined individuals” whose rights were violated [72]
.
To sum up, despite certain advancements, the self-referential approach of the Court to environmental issues consisting of greening the Convention rights has limited potential to foster the environmental justice as it is strictly operating within the logic of human rights, without treating the environment as a value in itself. Arguably, the “environmental democracy approach” focused on procedural environmental rights rates better in terms of balancing the objectives of the two regimes.

3.2. “Environmental Democracy” Approach: Procedural Environmental Rights Before the Inter-American Court

The second approach that can be identified in the case law of the Inter-American Court is the so-called “environmental democracy” theory, which seeks to empower citizens and civil society actors to influence public decisions and policies on environmental matters through procedural environmental rights [73]
. These rights normally include the right to information, the right to participation in the decision-making and the right to judicial remedies, which are provided in general form in the American Convention and other regional human rights treaties. In addition to these instruments, these rights have been reaffirmed explicitly as applicable in environmental field by the 1998 Aarhus Convention on Access to Information, Public Participation {p. 483}in Decision-Making and Access to Justice in Environmental Matters (“the Aarhus Convention”) [74]
.
The Aarhus Convention, adopted by the UN Economic Commission for Europe, despite its regional scope, was described by the former UN Secretary-General Kofi Annan as “the most ambitious venture in the area of ‘environmental democracy’ so far undertaken under the auspices of the United Nations” [75]
. The significance of the Convention is that it is the first international agreement that lays down the obligations of States towards their citizens and civil society actors in environmental matters [76]
. In doing so, it adopts a broader – in comparison to a human rights treaty – public interest approach to environmental protection, which manifests itself in more relaxed standing rules for petitioners, comprising not only individuals but also NGOs [77]
. To illustrate, article 4 of the Convention requires the State party to ensure that public authorities make environmental information available to the public concerned when requested, defining the latter as “the public affected or likely to be affected by, or having an interest in, the environmental decision-making”, including NGOs promoting environmental protection [78]
. In other words, individuals and civil society actors have a right to request environmental information without having to prove that they have been affected by environmental degradation. Similarly, the same threshold of “sufficient interest” applies to articles 6 and 9 of the Convention, providing for the {p. 484}rights to public participation in environmental executive decisions and access to justice if the requested environmental information is denied [79]
.
The influence of the Aarhus Convention has been significant in the development of the above-mentioned procedural rights in the case law of the ECtHR, the African Commission and the Inter-American Court [80]
. In particular, in several cases, the said human rights courts adopted a particularly broad understanding of their own treaty provisions with regard to environmental matters by incorporating the elements of the Aarhus Convention rights [81]
. At the Inter-American Court, the influence of Aarhus Convention can be illustrated by Claude Reyes and others v. Chile case [82]
. The case arose out of refusal of the Chilean Foreign Investment Committee to disclose, upon request of several interested citizens, information regarding the “Rio Condor” project. The said project aimed at large-scale exploitation of forests in the southern region of Chile and sparked considerable public debate regarding its potential environmental impact [83]
. Thus, several Chilean citizens decided to inquire about the suitability of the chosen investor, as well as the potential environmental impact of the project and after their request had been denied, filed for the violation of their right to seek and receive
{p. 485}information under article 13(1) of the Convention [84]
. Unlike in the “human rights greening” cases, the Court accepted the claim, despite the fact that the petitioners in question were not directly affected by the Rio Condor project. In doing so, it explicitly referred to the Aarhus Convention [85]
and stressed that the right to obtain information of public interest, including those pertaining to environmental matters, belong to all citizens in a democratic society:
Note
[62] On this point, see cases cited supra at note 58; Thériault, Environmental Justice and the Inter-American Court of Human Rights, cit., pp. 322-324; Pavoni, Environmental Jurisprudence of the European and Inter-American Courts of Human Rights, cit., pp. 97-98.
[63] Case of the Kichwa Indigenous People of Sarayaku v. Ecuador, cit., par. 146, as cited in Thériault, Environmental Justice and the Inter-American Court of Human Rights, cit., p. 324.
[64] See ibidem.
[65] See ibidem.
[66] Case of the Kichwa Indigenous People of Sarayaku v. Ecuador, cit., par. 156. See also Thériault, Environmental Justice and the Inter-American Court of Human Rights, cit., p. 324. In addition, prior to allowing the exploitation of natural resources that are essential to indigenous peoples’ existence, the State must consult the affected communities, conduct an environmental impact assessment and subsequently ensure that the latter receive reasonable benefits from these activities, see ibidem, par. 157; Thériault, Environmental Justice and the Inter-American Court of Human Rights, cit., pp. 324-325, for discussion.
[67] See Boyle, Human Rights or Environmental Rights? A Reassessment, cit., p. 472.
[68] See ibidem, p. 505.
[69] See ibidem, p. 506.
[70] See Pavoni, Environmental Jurisprudence of the European and Inter-American Courts of Human Rights, cit., p. 98.
[71] Metropolitan Nature Reserve v. Panama, IACommHR, Case No. 11.533, Report No. 88/03 (22 October 2003).
[72] Ibidem, as cited in Pavoni, Environmental Jurisprudence of the European and Inter-American Courts of Human Rights, cit., p. 94.
[73] For an overview of the rights, see Leib, Human Rights and the Environment, cit., pp. 81-88.
[74] Aarhus Convention on Access to Information, Public Participation in Decision-Making and Access to Justice in Environmental Matters (25 June 1998), UNECE, 2161 UNTS 447. See also the Regional Agreement on Access to Information, Public Participation and Justice in Environmental Matters in Latin America and the Caribbean (the Escazú Agreement) (4 March 2018), CEPAL, LC/PUB.2018/8/-*, which entered into force on 22 April 2021.
[75] UN Economic Commission for Europe, The Aarhus Convention – An Implementation Guide (2000), as cited in A. Boyle, Human Rights and the Environment: Where Next?, in «European Journal of International Law», 23, 2012, n. 3, pp. 613 ff., 621-622.
[76] See Leib, Human Rights and the Environment, cit., p. 83.
[77] See ibidem, p. 85; Boyle, Human Rights and the Environment: Where Next?, cit., p. 625.
[78] Aarhus Convention, cit., artt. 2(5), 4(1).
[79] Ibidem, artt. 6, 9. For discussion, see Boyle, Human Rights and the Environment: Where Next?, p. 625; Leib, Human Rights and the Environment, pp. 84-85.
[80] See Boyle, Human Rights and the Environment: Where Next?, cit., pp. 623-626.
[81] See ibidem, p.624.
[82] See Pavoni, Environmental Jurisprudence of the European and Inter-American Courts of Human Rights, cit., p. 72. For an overview of the Court’s jurisprudence on procedural environmental rights, see ibidem, pp. 72-76; Shelton, Human Rights, Environmental Rights, and the Right to Environment, cit., pp. 768-774; Thériault, Environmental Justice and the Inter-American Court of Human Rights, cit., pp. 318-321.
[83] Claude Reyes and others v. Chile (Merits, Reparations and Costs), IACtHR, Case No. 161 (19 September 2006). For discussion, see Pavoni, Environmental Jurisprudence of the European and Inter-American Courts of Human Rights, cit., pp. 75-76; Thériault, Environmental Justice and the Inter-American Court of Human Rights, cit., pp. 318-320.
[84] Claude Reyes and others v. Chile, cit., par. 57(13).
[85] Ibidem, par. 81.