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.
[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.