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Part II - Specific Procedures

Published online by Cambridge University Press:  15 February 2024

Christina Voigt
Affiliation:
Universitetet i Oslo
Caroline Foster
Affiliation:
University of Auckland

Summary

Type
Chapter
Information
International Courts versus Non-Compliance Mechanisms
Comparative Advantages in Strengthening Treaty Implementation
, pp. 97 - 168
Publisher: Cambridge University Press
Print publication year: 2024
Creative Commons
Creative Common License - CCCreative Common License - BYCreative Common License - NCCreative Common License - ND
This content is Open Access and distributed under the terms of the Creative Commons Attribution licence CC-BY-NC-ND 4.0 https://creativecommons.org/cclicenses/

5 The Advisory Procedure in Non-Compliance Procedures Lessons from the UNECE Water Convention

Carlos A. Cruz Carrillo
5.1 Introduction

The advisory function of international judicial bodies remains an important judicial tool to elucidate the scope and content of international obligations. Today, many international judicial bodies are entrusted with an advisory function under different architectures.Footnote 1 As is well known, advisory opinions are not binding but do entail legal effects in the interpretation and application of law.Footnote 2 Recently, the advisory function is likewise permeating some compliance mechanisms established by multilateral environmental agreements (hereinafter referred to as ‘MEAs’). This chapter examines the novelty of the advisory procedure envisaged in the mandate of non-judicial bodies as a new development in the implementation and compliance of MEAs.

Since the second half of the twentieth century, many MEAs have created an institutional framework to foster compliance with the agreement in question.Footnote 3 Particularly, MEAs usually provide for the establishment of compliance or implementation committees (hereinafter referred to as ‘CCs’) aimed at facilitating and monitoring compliance with the agreement in question.Footnote 4 Such compliance review bodies are mandated to carry out procedures that are mostly non-adversarial and non-punitive in nature. Yet the outcome of these procedures may in some cases entail the adoption of sanctions for Parties found to be in non-compliance, directly by said bodies, or by the Meeting of the Parties (hereinafter referred to as ‘MoP’ or ‘CoP’) on the recommendation of CCs. Few MEAs add a so-called ‘advisory procedure’ to these procedures. This chapter argues that an advisory procedure fosters effective implementation by offering tailored technical and legal advice to States, attending to their particular circumstances, without confrontation and intrusive sanctions. Drawing on the advisory procedure of the UNECE Convention on the Protection and Use of Transboundary Watercourses and International Lakes (hereinafter referred to as ‘UNECE Water Convention’), this chapter identifies areas of opportunity for enhancing implementation and compliance with current and future MEAs.

This chapter will be organized as follows. First, it will give a brief overview of the nature of non-compliance mechanisms (hereinafter referred to as ‘NCMs’). Second, it will examine the advisory procedure specifically provided for the Implementation Committee of the UNECE Water Convention (hereinafter referred to as ‘IC’). Third, it will identify areas of opportunity for adoption of a similar advisory procedure to help improve the implementation of other existing and future multilateral agreements.

5.2 Non-Compliance Procedures in a Nutshell

As anticipated, many MEAs envisage the possibility of establishing CCs managed by the CoP/MoP or by specialized subsidiary bodies. Their main objective is to foster the implementation of and compliance with an MEA, and prevent environmental damage.Footnote 5 According to the United Nations Environment Programme (UNEP), ‘compliance’ is the fulfilment by the contracting Parties of their obligations under a MEA, whereas ‘implementation’ refers to the measures that contracting Parties adopt to meet their obligations.Footnote 6 In this context, CCs have particular common features that may attract the interests of Parties as a venue to tackle their implementation issues. The first is their non-judicial and non-confrontational nature. Second, these mechanisms aim at facilitating compliance rather than stigmatizing the concerned Party with measures or sanctions. A third common feature is the relevance of the duty of Parties and the treaty bodies to co-operate as a cornerstone of these mechanisms.Footnote 7

Compliance or implementation committees’ procedures can be seen as a public interest process where great attention is paid to due process and independence as a guarantee of legitimacy.Footnote 8 Further, the options to trigger a non-compliance procedure reflect the Parties’ common interest in protecting the object of an MEA (watercourses, public participation, ozone layer, climate action, etc.).Footnote 9 The only precondition for triggering a compliance procedure is being a Party to the treaty and complying with the procedural requirements established to that end. Commonly, non-compliance procedures can be triggered by States and by particular bodies (e.g., CoP/MoP, implementation bodies). However, a few compliance mechanisms allow for broad public participation. For example, in the mechanisms established by the UNECE Aarhus Convention,Footnote 10 the Escazú AgreementFootnote 11 the UNECE Water ConventionFootnote 12 or the Protocol on Water, and HealthFootnote 13 members of the public can actively participate in non-compliance procedures, either by triggering a procedure or by submitting information. Some authors also consider CCs an effective alternative to a judicial dispute settlement mechanism, which could entail a long process before a judgment or award is rendered.Footnote 14 Moreover, the outcome of these mechanisms does not result in res judicata, which makes them a less intrusive procedure in terms of state sovereignty.Footnote 15

One of the very first NCMs to appear was that of the 1987 Montreal Protocol on Substances That Deplete the Ozone Layer.Footnote 16 Article 8 provided for the Parties to consider and approve mechanisms for determining non-compliance, which led to the establishment of the Implementation Committee in 1992.Footnote 17 A Party to the Protocol can trigger a procedure with respect to its non-compliance, or with respect to another Party. The Secretariat can also trigger the procedure. The Committee can adopt facilitative measures such as providing financial and technical assistance to foster the compliance of the concerned Party. However, the Committee can also adopt measures such as declarations of non-compliance, cautions and even the suspension of rights and prerogatives.Footnote 18

While the Implementation Committee of the Montreal Protocol stands as the model from which later NCMs were established,Footnote 19 one may refer also to the latest generation of such mechanisms provided for in the 2015 Paris Agreement,Footnote 20 the 2013 Minamata ConventionFootnote 21 and the 2018 Escazú Agreement.Footnote 22 The institutional and functional architecture of CCs under these agreements follows that of the Montreal Protocol, with some procedural adjustments concerning the actors entitled to initiate a procedure, or pertaining to the outcome of the procedure. For example, one may note the twofold CC established under the Kyoto Protocol, which comprises a facilitative and an enforcement branch. In certain circumstances, the outcome of the Kyoto Protocol procedures can result in binding recommendations.Footnote 23

This chapter proposes the following taxonomy of functions ascribed to CCs among MEAs:

  • Reporting/Monitoring procedure. This function is a traditional implementation technique used across MEAs and draws on the obligation of States to periodically report on the measures they have adopted to implement their obligations under the MEA in question.Footnote 24 Periodic reports enable the CoP or the CCs to foresee a State’s difficulties in complying with certain obligations of the MEA. In these cases, the CoP or the CC of an MEA may ask the Party concerned for additional information and decide whether to trigger a non-compliance procedure. Moreover, if a Party fails to comply with the obligation to report, the CC may trigger a non-compliance procedure.

  • Triggered by the Committee. The CC can initiate motu propio a compliance procedure against a member State when the Committee has knowledge that the Party is failing to comply with its obligations under an MEA. As a basis for its decisions, the Committee can rely on the national reports submitted by the Parties under a monitoring procedure, or on information submitted by bodies of an MEA or by members of the public.

  • Submission procedures. This procedure enables the mechanism to analyze particular non-compliance situations submitted by a Party with regard to its own performance (self-triggering); by a Party with regard to the performance of another Party; by the CoP; or by members of the public.Footnote 25 The outcome of a submission procedure generally entails facilitative measures such as technical and financial assistance to enhance compliance by the Party concerned. In a few cases, MEAs allow punitive measures, such as the suspension of rights and prerogatives.Footnote 26 The case law produced under this procedure is significant within the Aarhus Convention, mainly triggered by individuals and non-governmental organizations.Footnote 27 Similarly the case law of the Montreal Protocol,Footnote 28 the Espoo ConventionFootnote 29 or the Kyoto Protocol.Footnote 30

  • Advisory procedure. The advisory procedure enables a CC to deliver legal and technical advice upon the request of a CC Party, the CoP or other organs of an MEA. The ultimate goal of this procedure is to facilitate the compliance with and implementation of an MEA. Thus, the procedure results in advice with recommendations for the Party, or Parties, concerned, but without measures stigmatizing any Party, as may be perceived in a submission procedure.

This chapter will focus on examining the advisory procedure as one of the most recent procedures formally established as a means to provide facilitative assistance to the Parties of an MEA. The chapter looks particularly at the advisory procedure under the UNECE Water Convention, examining the architecture of this procedure and analyzing the potential benefits of employing similar procedures as part of implementation and compliance procedures across MEAs more widely.

5.3 Advisory Opinions in the UNECE Water Convention
5.3.1 General Overview of the Water Convention’s Compliance and Implementation Machinery

The UNECE Water Convention was adopted in 1992 and entered into force in 1996.Footnote 31 The main objective of the UNECE Water Convention is promotion of the sustainable management of transboundary waters, surface waters and ground waters. In order to help achieve that aim, the Convention sets out substantive and procedural obligations based on the principle of prevention, the obligation to co-operate, the principle of reasonable and equitable use and the no harm principle.Footnote 32 Moreover, this treaty includes a series of principles to be considered by the Parties when adopting measures to comply with and implement its obligations, namely, the precautionary principle, the polluter-pays principle and the principle of inter-generational equity.Footnote 33 Initially, this treaty remained a regional instrument for the European region. However, following a proposal by Switzerland, the Meeting of States Parties to the Convention adopted Decision III/1, allowing all United Nations member States to accede to the Convention.Footnote 34 Following this amendment, a number of countries from the AfricanFootnote 35 regions acceded.

As to implementation and compliance, Article 17(2)(f) of the UNECE Water Convention enabled the MoP to create an Implementation Committee, which was established in 2012 with the adoption of Decision VI/1 of the MoP.Footnote 36 The IC aims at facilitating, promoting and safeguarding the implementation and application of and compliance with the UNECE Water Convention.Footnote 37 The nature of the mechanism is non-confrontational, non-adversarial, transparent, supportive and co-operative.Footnote 38 The IC has an interdisciplinary composition of nine members with legal and scientific expertise.Footnote 39

The IC is entrusted with a submission procedure, a procedure triggered by the IC to request further information and an advisory procedure. The submission procedureFootnote 40 can be triggered by any Party to the Convention with regard to its own issues of non-compliance (self-referral), by a Party with regard to issues of another Party or by the IC initiative in the absence of submissions. The procedure triggered by the IC motu proprio operates when the IC is aware of difficulties in the implementation of or non-compliance with the Convention.Footnote 41 In making a determination on whether to trigger a procedure, the IC should consider the source, content and relevance of the information submitted to it, including information submitted by the public.Footnote 42 This factor may be regarded as an indirect substitute for procedures allowing for submissions, or referrals, from the public as in the Aarhus Convention or the Protocol on Water and Health.Footnote 43 The advisory procedure will be explained in a further section.

The outcome of a submission procedure is the adoption of facilitative measures aimed at supporting implementation of and compliance with the obligations in the Convention. In this regard, the IC can adopt one or more of the following measures:

  1. I. Provide advice and facilitate assistance to the concerned Parties, including:

    1. (i) Suggesting or recommending that domestic regulatory regimes be set up or strengthened, and relevant domestic resources be mobilized as appropriate;

    2. (ii) Assistance in establishing transboundary water cooperation agreements;

    3. (iii) Facilitating technical and financial assistance;

    4. (iv) Assistance in seeking support from specialized agencies and other competent bodies, as appropriate.

  2. II. Request and assist the concerned Parties in elaborating an action plan to facilitate implementation and compliance, within a time frame agreed by the Parties and the Committee;

  3. III. Request the submission of progress reports.Footnote 44

Furthermore, the IC can recommend the MoP adopt one or more of the above-mentioned measures or take other restrictive measures, including: issuing a statement of concern; issuing a declaration of non-compliance; issuing cautions; or the suspension of rights and privileges accorded to the Party concerned.Footnote 45 For this purpose, the MoP should consider the cause, type, degree and frequency of the Party’s difficulties with implementation and/or non-compliance.

5.3.2 Comparing the Water Convention’s Advisory Procedure with Implementation and Compliance Procedures in Other MEAs

As mentioned, the architecture of the NCM of the UNECE Water Convention follows the same pattern as the Montreal Protocol. However, the IC of the Water Convention has an advisory function, which is unusual when compared with the more standard procedures employed by other NCMs. The advisory function is implicitly included in many implementation mechanisms. For instance, CCs operating under the Nagoya Protocol,Footnote 46 the Cartagena ProtocolFootnote 47 and the London ProtocolFootnote 48 among others, deliver advice and recommendations, but only as a measure following a non-compliance procedure.

Other CCs can deliver advice as a separate procedure. For example,Footnote 49 the CC of the Protocol on Water and Health has a consultation process to facilitate and support implementation by issuing technical, scientific and legal advice.Footnote 50 This procedure only operates if a Party requests it or if the CC proposes it. The case of the compliance mechanism of the Aarhus Convention is distinct. The Convention and Decision I/7 (which establishes the Structure and Functions of the CC) did not include ab initio an advisory function for the CC.Footnote 51 Yet following a request for advice filed by Belarus, the MoP and the CC delineated such an advisory function. First, the Secretariat prepared a draft response which was circulated for the consideration of the CC and the Party concerned.Footnote 52 Afterwards, the CC adopted its recommendation ACCC/A/2014/1 with respect to Belarus.Footnote 53 In a second request for advice by Kazakhstan, the CC, without the support of the Secretariat, set out more clearly that its advisory function was founded in accordance with paragraphs 14, 36(a) and 37(a) of the annex to Decision I/7.Footnote 54 In both decisions, the outcome of the request for advice entailed recommendations with regard to the meaning and scope of particular terminology in the Convention, as well as a recommendation for the requesting Party to pursue certain measures at the domestic level. A third request for advice was filed by Ukraine and is pending.Footnote 55 What is uncertain in this new procedure is whether the requesting Party can become the object of measures by the CoP should it fail to implement the recommendations of the CC, and whether it remains potentially subject to a submission procedure in respect of the concerns addressed through the advisory function.

The UNECE Water Convention advisory procedure derives from the constitutive Decision by the MoP, which provides explicitly for it and underscores that the advisory procedure ‘shall not be regarded as alleging non-compliance’.Footnote 56 Therefore, as will be explained in detail, the outcome of the advisory procedure is legal and technical advice without the possibility that the Committee might suggest the MoP take action in respect of relevant concerns.Footnote 57 Another noteworthy aspect of the Convention’s advisory procedures is the clarity of the process regarding who can request an advisory opinion and the effects of an advisory opinion for the requesting entity. The scope of the advisory procedure embraces two situations. First, when a Party seeks advice on its difficulties in implementing the UNECE Water Convention. Second, when a Party or Parties seek advice on how to implement the Convention with respect to another Party and/or with non-Parties to the Convention. Thus, the advisory procedure has a facilitative and preventive dimension inasmuch as it seeks for the Parties to identify potential issues of non-compliance, request guidance to resolve them and, at the same time, prevent further disputes with other Parties or non-Parties with a legal interest.

The advisory procedure produces advice tailored to the needs of the requesting Party for the purposes of implementing the Water Convention. According to its constitutive Decision, the Committee may include inter alia the following in its advisory opinion:

  • Advice and assistance to an individual Party or group of Parties to facilitate the implementation of the Water Convention. The Committee can particularly recommend the enhancement of domestic regulatory regimes; provide assistance in establishing transboundary water co-operation agreements; facilitate technical and financial support, including information and technology transfer and capacity building; or provide assistance to seek support from specialized agencies;

  • Requesting and assisting the Party or Parties concerned to develop an action plan to facilitate implementation, within a timeframe agreed between the IC and the Parties;

  • Inviting the Party concerned to submit progress reports on the efforts that it is making to implement the Convention.Footnote 58

These suggestions are similar to the facilitative measures that the IC can adopt in the context of a submission procedure. However, it is not contemplated that, in the context of the advisory procedure, the Committee would recommend to the MoP the adoption of measures such as issuing statements of concern or a declaration of non-compliance, cautions or the suspension of rights and privileges. Therefore, an advisory opinion seems to be a way for States to seek guidance in the implementation of the Convention without being subject to such measures. Nevertheless, nothing prevents the Committee using the information derived from an advisory procedure to act motu proprio with regard to the same State, or States concerned, under a more stringent procedure.

In terms of standing, the advisory procedure is open to States Parties to the Water Convention, with regard to their own actions or those of other Parties, and to non-States Parties. In the case of non-States Parties, their participation in the advisory procedure is subject to their consent.Footnote 59 The opening of the Water Convention to all UN member States in 2003 has enabled the IC to expand its functions to regions beyond Europe. For example, if Ghana,Footnote 60 which recently acceded to the Water Convention, decides to request advice from the Committee on activities conducted on the Black Volta River, the Committee could consider inviting Burkina Faso or Côte d’Ivoire to participate in the advisory procedure as riparian States. However, since the latter two States are non-Parties to the Water Convention, their consent to participation is essential. In fact, the Committee is obliged to explain the advisory procedure to those Parties and suggest their participation.Footnote 61

Finally, public participation is possible within the functions of the IC and other mechanisms in at least in two ways. First, members of the public can transmit information to the Committee on a Party’s non-compliance, on the basis of which the Committee may initiate motu proprio a procedure against the concerned Party.Footnote 62 Second, during the advisory and submission procedures the Committee shall take into account the information submitted by the public.Footnote 63

5.3.3 An Example of the Water Convention’s Advisory Procedure: The Cijevna/Cem River Advisory Procedure (WAT/IC/AP/1 – Montenegro and Albania)

The Cijevna/Cem River advisory procedure provides a good example of the effectiveness of the Water Convention advisory procedure. On 22 November 2019, Montenegro filed a letter to the Secretariat of the UNECE Water Convention, afterwards circulated to the IC of the UNECE Water Convention. In its letter, Montenegro expressly requested the involvement of the IC in relation to the construction of small hydropower plants on the Cijevna/Cem River in Albania.Footnote 64 Montenegro was not clear as to the procedure under which it was approaching the IC, which appeared to fall somewhere between a submission and a request for the advisory procedure. The IC analyzed Montenegro’s letter and considered it a request for the exercise of its advisory function. Yet it also left open the possibility of initiation at a later stage of a motu proprio procedure.Footnote 65 In accordance with the established process, the IC invited Albania to participate in the advisory procedure. Albania agreed to do so on 31 January 2020.Footnote 66

The situation at Cijevna/Cem River is also the object of a submission procedure before the Implementation Committee of the Convention on Environmental Impact Assessment in a Transboundary Context (Espoo Convention). Montenegro instituted proceedings under the Espoo Convention on 11 September 2019,Footnote 67 and Albania replied on 30 December 2019, asserting compliance with its obligations under this treaty.Footnote 68 At the moment of writing this chapter, the procedure is ongoing and has not yet led to an outcome. In this context, an interesting preliminary aspect of the procedure is the co-ordination between the implementation committees of the UNECE Water Convention and the Espoo Convention,Footnote 69 who agreed on sharing information related to the matter through their secretariats.Footnote 70 A similar situation is less likely to occur among judicial and arbitral bodies.

The Committee held several information-gathering and consultation sessions with Albania and Montenegro. The Committee decided to adopt a two-track approach: to facilitate the exchange of information between both countries and to assist in the establishment of a joint monitoring and assessment framework for surface waters, groundwater and ecosystems in the Cijevna/Cem River.Footnote 71 During the process, Albania proposed the existing bilateral commission established under the 2018 Framework Agreement on Mutual Relations in the Field of Management of Transboundary Waters as a forum for consultations with Montenegro. The Committee proposed a joint technical working group within the framework of this bilateral commission. Albania underscored the importance of avoiding duplication with the existent mechanisms, such as the efforts adopted in the framework of the mechanism governing the Drin River basin.Footnote 72 The Committee clarified the scope of the advisory procedure as limited to the Cijevna/Cem River and not the Drin River.Footnote 73

The Committee delivered its legal and technical advice in March 2021.Footnote 74 The Committee held that due to the absence of sufficient monitoring information and data, it was unable to confirm or deny the likelihood of a cumulative transboundary impact caused by the planned construction.Footnote 75 However, the Committee elaborated on the potential difficulty of implementing certain obligations of the Water Convention. In this regard, the Committee recognized that the Convention’s procedural obligations are instrumental in operationalizing substantive obligations such as the obligations to prevent, control and reduce transboundary impact. The Committee examined the matter of the Cijevna/Cem River in the context of the procedural obligations of establishing joint bodies, concluding transboundary water agreements, holding consultations, joint monitoring and assessment and exchanging data and information.

Particularly, the Committee advised Albania and Montenegro to enhance their efforts in implementing the obligation of carrying out joint monitoring and assessment by establishing a joint or co-ordinated monitoring and assessment framework. Similarly, the Committee advised the Parties on developing a practice of exchanging information and data, and procedures in pursuit of that aim.Footnote 76 Albania and Montenegro engaged in a joint effort to implement the Committee’s advice. In particular, both countries are working on establishing the joint technical working group for monitoring and assessment of the Cijevna/Cem River. The Parties submitted to the IC a first briefing on the implementation on 20 May 2021.Footnote 77 The IC continues to assist Albania and Montenegro.

5.3.4 Contributions of the Advisory Procedure to the Implementation of MEAs

This section of the chapter will elaborate on three valuable dimensions of the Water Convention’s advisory procedure. First, the role of the advisory procedure in water diplomacy and the prevention of further disputes. Second, the importance of having a tailored legal and technical advisory opinion to assist in the implementation of an MEA. Third, the areas of opportunity where the advisory procedure may enhance the implementation of current and future MEAs.

5.3.4.1 The Conciliatory Role of the Advisory Procedure in the Context of Water Diplomacy

Water diplomacy mainly hinges on co-operation agreements such as the recent co-operation framework on the Senegal–Mauritanian Aquifer Basin.Footnote 78 In the absence of co-operation agreements and the will to implement them, States may engage in long-lasting and costly disputes such as the dispute relating to the Gabčíkovo–Nagymaros Project or the ‘Dispute over the Status and Use of the Waters of the Silala’,Footnote 79 both before the ICJ. In this context, the first remarkable feature of the advisory procedure is its role in fostering water diplomacy to help prevent long-lasting and costly disputes.

In particular, the advisory procedure provides alternative ways forward to two or more States with competing interests in a shared resource. This feature is not present in other non-compliance procedures, and it is unique because its main objective is to explore potential solutions with the concerned Parties and non-Parties, without triggering a confrontational judicial or quasi-judicial procedure. This may prove to be attractive to States. Arguably, the advisory procedure offers a cheaper way forward than recourse to judicial or arbitral proceedings. One could assert that the advisory procedure is a conciliatory way to prevent a dispute, and to prevent environmental damageFootnote 80 or, as expressed by some former judges, it is a form of ‘advisory arbitration’.Footnote 81 Indeed, the engagement of the IC in facilitating a solution among the Parties makes of the advisory procedure a new development among non-compliance procedures. The Cijevna/Cem River advisory procedure is a clear example of this. The Parties consented to participating in the procedure and are currently working together to prevent environmental damage in this watercourse.

If the Parties fail to reach an agreement through the advisory procedure, they may resort to other means of dispute settlement. Most MEAs are clear in recognizing the independence of the non-compliance procedure from dispute settlement processes.Footnote 82 For example, the UNECE Water Convention recognizes that the procedure to facilitate and support implementation and compliance shall be without prejudice to Article 22 of the Convention on the settlement of disputes.Footnote 83 The next question is whether the advisory opinion rendered by the IC has any value in a further judicial or non-judicial proceeding. To contextualize this point, let us go back to the Cijevna/Cem River advisory procedure, where the IC was unable to confirm or deny the likelihood of cumulative transboundary impact caused by the planned hydropower plants.Footnote 84 What would have been the legal consequence of a determination confirming cumulative environmental impact? A first point to remember is that non-compliance procedures, even if some of them entail sanctions, are not judicial processes. Therefore, the principle of res judicata cannot be invoked as a basis to request a tribunal not to exercise its jurisdiction over a dispute.Footnote 85 However, the findings of the IC can assist a judicial/arbitral organ in adopting an interpretation of the treaty and may provide elements of fact-finding.Footnote 86 For example in the Diallo case, the ICJ ascribed great weight to the interpretation of the International Covenant on Civil and Political Rights (ICCPR) adopted by the Human Rights Committee, as an independent body that was established specifically to supervise the application of the ICCPR.Footnote 87 Yet the facilitative nature of the advisory procedure differs from the advisory function of a judicial body. The goal of judicial advisory proceedings is delivering an authoritative statement of law on a legal question requested by an entity (international organizations, States or NGOsFootnote 88) for the fulfilment of its obligations and/or functions. An advisory opinion constitutes a source of international law and entails legal effects for the requesting entity and the legal system.Footnote 89

5.3.4.2 Tailored Technical and Legal Advice

One of the most crucial roles of a CC is identifying the main reasons why a Party is failing to implement its obligations under an MEA. The reasons for non-compliance can go beyond a problem with political will. Instead, a Party might be in the position of lacking the technical and financial capacity to implement its obligations. For these reasons, States need an IC from which they can request technical and legal advice without being accused of non-compliance by another Party, the public or the CC. Submission, reviewing and self-trigger procedures generate a certain level of stigmatization against the concerned Party, which may help tackle the absence of political will to implement an MEA. However, despite the recommendations that may follow these procedures, States may be reluctant to implement them because of their confrontational and punitive nature.Footnote 90 As underscored by Judge Buergenthal, ‘it is easier for governments to comply with advisory opinions because such rulings do not stigmatize them’.Footnote 91

In this context, the advisory procedure, as envisaged in the UNECE Water Convention, goes beyond the traditional role of ICs by offering a procedure to those Parties with the political will to implement an MEA but with a lack of capacity to do so. Under the advisory procedure, a Party can have recourse to the IC to expose its situation and to request financial, technical or legal advice. On this point, the IC has underscored the benefit of the Committee’s interdisciplinary composition.Footnote 92 As explained, the outcome of an advisory procedure entails recommendations aimed at enhancing domestic regulatory regimes or facilitating technical and financial support for the requesting Party. Furthermore, the IC can bring to the attention of the CoPs/MoPs the financial and technical difficulties of a Party with the aim of seeking support among other Parties.

5.3.4.3 Assessing the Utility of Employing an Advisory Procedure in other MEAs

As discussed, the advisory procedure has emerged within an IC of an MEA governing the management of international watercourses and lakes. Yet, this procedure can be easily adapted for use under other MEAs addressing the management of common/shared resources or addressing a common concern. The inclusion of a similar procedure in other compliance mechanisms could foster a more active engagement in the implementation of the related treaties and ensure the prevention of environmental damage and health risks. This improvement could be made in existing compliance mechanisms among MEAs by vesting in them the power to conduct an advisory procedure. For example, the CC of the Protocol on Water and Health adopted in 2014 a consultation process to facilitate and support implementation by issuing technical, scientific and legal advice.Footnote 93 Like the advisory procedure of the Water Convention, the consultation process is not a compliance review procedure and, thus, it doesn’t establish whether a Party is non-compliant.Footnote 94 The consultation is requested by a Party or by invitation from the CC.Footnote 95 To date, the CC of the Protocol on Water and Health has dealt with seven consultation processes.

The second pathway of opportunity for introducing an advisory procedure is in the context of negotiations on compliance mechanisms of new multilateral treaties. This chapter underscores three of them:

  • BBNJ Agreement.Footnote 96 The draft text of the international legally binding Instrument on the Conservation and Sustainable Use of Marine Biological Diversity of Areas Beyond National Jurisdiction (BBNJ), would establish in Article 53 ter an Implementation and Compliance Committee to facilitate and review the implementation of the agreement. The modalities and procedures would be adopted during the first CoP.Footnote 97 In this scenario, the advisory procedure could be a function considered by the CoP when establishing the Implementation and Compliance Committee. It should be noted that the draft text includes a proposal for the CoP to request advisory opinions from the International Tribunal for the Law of the Sea.Footnote 98 Establishing advisory procedures to be conducted, respectively, by a non-compliance body and a judicial body may complement authoritative statements of law with tailored facilitative advice for implementing the treaty.

  • Plastic pollution Treaty. In March 2022, the United Nations Environment Assembly (UNEA) decided to convene an intergovernmental negotiating committee to develop a binding instrument on plastic pollution.Footnote 99 Despite its early stage of development, it is probable that the Intergovernmental Negotiating Committee (INC) will be considering the appropriate mechanisms to address compliance with the treaty.Footnote 100 Stakeholders have expressed the importance of adopting an instrument that takes into account countries’ different capacities, as well as their need for financial and technical assistance.Footnote 101 In this context, the INC might draw on the advisory procedure under the Water Convention.

  • Pandemic Treaty. In December 2021, the World Health Organization agreed on establishing an intergovernmental negotiating body to negotiate a binding instrument to strengthen pandemic prevention, preparedness and response.Footnote 102 Given the preventive nature of the upcoming instrument, an IC or similar body will be useful to implement the treaty.Footnote 103

In sum, the advisory procedure established in the UNECE Water Convention and other MEAs constitutes a truly facilitative non-compliance procedure capable of offering advice to tackle technical and financial implementation issues, to prevent environmental damage and to help prevent further disputes. The advisory procedure could prove to be an efficient tool in the implementation of multilateral treaties addressing common concerns or the management of shared resources.

5.4 Conclusions

This chapter has explored the potential of the advisory procedure in CCs by drawing on the advisory procedure employed by the IC of the UNECE Water Convention and recent experience with this procedure. The chapter has highlighted the benefits of non-confrontational and non-punitive NCMs and procedures. While most of these procedures can be useful to address the lack of political will to implement MEAs, it is true that they may be more limited in their contribution to addressing other compliance issues, such as lack of capacity or the emergence of a dispute. The chapter draws the following conclusions on the advisory procedure:

  1. (1) The tailored and technical advice offered through an advisory procedure stands out as one of the unique features of the advisory procedure as compared with the outcome of a submission, reporting or self-triggered procedure. This feature may prove to be attractive for States willing to implement an MEA but struggling to do so for technical or financial reasons. Moreover, the interdisciplinary composition of non-compliance bodies enables the production of advisory opinions with technical and legal recommendations, tailored to the specific needs of the requesting Party.

  2. (2) The advisory procedure offers a conciliatory avenue for the prevention of potentially long-standing and costly disputes before judicial or arbitral bodies. Relying on the principle of cooperation, the concerned States can request an advisory opinion from the IC to obtain guidance on how to implement treaty obligations in respect to a particular project or a situation that may entail environmental harm. On the one hand, the advisory procedure seeks to prevent a dispute, and on the other, it offers alternatives to prevent further damage.

  3. (3) The non-inquisitorial nature of the advisory procedure fosters a more facilitative approach across MEAs. Bearing this in mind, existing CCs should consider the establishment of an advisory procedure, adopting a similar architecture to that in the UNECE Water Convention. Furthermore, the advisory procedure could be considered for inclusion in designing compliance and implementation mechanisms in the course of the negotiation of new treaties such as the BBNJ Agreement, the Plastic Pollution Treaty or a new treaty on pandemic preparedness and response.

6 State-to-State Procedures before Environmental Compliance Committees: Still Alive?

Justine Bendel and Yusra Suedi
6.1 Introduction

Many multilateral environmental agreements (MEAs) have established committees that monitor compliance and/or facilitate State parties’ implementation.Footnote 1 They offer an alternative to traditional judicial dispute settlement and are designed with a slightly different purpose in mind. One of the ways they are different from international courts is the way in which a procedure can be triggered.Footnote 2 Indeed, there are many ways such committees may be triggered to take action: the committee could act proprio motu (committee trigger), or any State party could trigger the committee with respect to its own compliance or implementation (self-trigger) or sometimes an NGO or member of the public can trigger the committee (third-party trigger). However, most compliance committees also have a more ‘traditional’ way to initiate a procedure before them, reminiscent of a judicial procedure: a State party may seize the committee concerning the compliance or implementation of another State party.Footnote 3 This type of trigger has only been used a handful of times across the existing environmental committees that provide for it, most famously in the context of the Aarhus Convention. However, this trigger has deliberately not been included in the list of the various options triggering the Paris Agreement Implementation and Compliance Committee (PAICC). It is also interesting to see that, in the human rights context, the UN Convention on Racial Discrimination’s Committee has been triggered only twice.

One may ask: What is to be achieved through State-to-State triggers that is not achieved through other triggers? Why should they exist? Arguments for their existence and added value are twofold. The main objective of State-to-State triggers is to give responsibility to States themselves to make sure that every party implements the treaty, and to reinforce norms as community interests. Many rules contained in MEAs are arguably obligations erga omnes partes, which can and should be implemented and complied with by all parties to the treaty. While compliance committees are tasked with monitoring States’ compliance with such obligations, State-to-State triggers reflect States’ primary role in their implementation and compliance. The existence of State-to-State triggers is also justified as it creates another means, alongside other types of triggers, to implement and ensure compliance with a multilateral treaty. Having multiple ways to access the compliance mechanism of a treaty is beneficial, as more actors can be involved in the compliance process.

As a result, this chapter explores the following question: What are the challenges and obstacles of State-to-State triggers that can explain their sparse use? Focussing on compliance committees for MEAs, we identify two types of challenges faced by State-to-State triggers: challenges related to the perception and behaviour of States vis-à-vis State-to-State triggers (Section 6.3) and challenges related to the institutional design and procedural mechanisms of State-to-State procedures (Section 6.4). While the methodology is doctrinal in essence, we also conducted interviews with three negotiators of the Paris Agreement, in order to better understand the process that led to the creation of the PAICC. We also refer to examples in the human rights context where relevant. Before delving into the challenges identified, we first explain how State-to-State triggers were established (Section 6.2.1) and describe the instances in which they have been used (Section 6.2.2).

6.2 Overview of State-to-State Compliance Procedures

In order to understand the challenges faced by State-to-State triggers, we first explain the negotiation process leading up to their creation and present the instances in which they have been employed.

6.2.1 Establishment

The inclusion of State-to-State triggers as a means to encourage compliance with MEAs has historically been a contentious matter. Indeed, there has long been an ideological conflict within the international community about the best approach to guarantee States’ compliance with their international environmental obligations. The adversarial approach, on one hand, is typically where one State will ‘sue’ another for non-compliance in a confrontational manner. The State-to-State trigger is representative of this approach. The facilitative approach, on the other hand, involves ‘non-confrontational means to persuade State parties into compliance, through technical and financial assistance, aid with reporting requirements, advice, technology transfers and capacity building’.Footnote 4

Such tension is reflected in the negotiation processes to establish a number of MEAs. During negotiations on the compliance committee for the 1989 Basel Convention on the Control of Transboundary Movements of Hazardous Wastes and Their Disposal (Basel Convention), for instance, Australia argued that ‘a right to raise the performance of other parties would not be consistent with the consultative, non-confrontational nature of the mechanism’,Footnote 5 and that ‘compliance should not be secured through threats or by creating a mechanism equipped with strong enforcement procedures’.Footnote 6 The draft decision from the ad hoc Legal Working Group that established the compliance mechanism was a matter of lengthy and heated debate,Footnote 7 resulting in a consensus that was not satisfactory to all States.Footnote 8 Similarly, provisions on the State-to-State trigger in MEAs such as the 1998 Rotterdam Convention on the Prior Informed Consent Procedure for Certain Hazardous Chemicals and Pesticides in International Trade (Rotterdam Convention) and the 2001 International Treaty on Plant and Genetic Resources were enclosed in square brackets during the drafting process ‘as no agreement [had] been reached on this issue between the Parties’.Footnote 9

The tension was particularly high in the context of the Paris Agreement. This was considered to be more ‘more sensitive’Footnote 10 than other MEA negotiations due to the high political implications, the focus on the complex matter of climate change and a wide range of issues covered in the Agreement (such as mitigation, adaptation, finance, transparency and technical support). The mere inclusion of a compliance mechanism was difficult to negotiate in the first place, but certain States managed to convince the majority that the inclusion of a compliance committee would add value and guarantee accountability to the world.Footnote 11 However, reluctance remained regarding the acceptable ways to trigger such a committee. While many were initially willing to retain only a self-trigger,Footnote 12 a committee trigger was eventually added.Footnote 13 Unfortunately, State-to-State triggers were ‘shut down immediately by some parties’.Footnote 14 Deemed ‘impossible to include’ and ‘something parties would never agree to’, this proposal was abandoned by its negotiators in favour of other ideas that could be more readily accepted.Footnote 15

Today, most MEAs contain many features that lean towards a facilitative rather than an adversarial approach. This facilitative approach is the essence of environmental compliance procedures, within which more adversarial State-to-State triggers can exist. While some may believe that an adversarial approach to non-compliance is more efficient, most opine that the facilitative approach characterising compliance procedures is ‘better suited to promoting compliance’ in this context, particularly as it is ‘easier to sell to states’.Footnote 16 It can therefore be said that the facilitative approach is at the core of the existence of compliance procedures.Footnote 17 However, compromises have been reached in some MEAs to allow a State party preferring a more adversarial approach to seize the compliance committee against another State party if so desired. When featured, the State-to-State trigger has therefore found itself incorporated as a concession; a square peg in a round hole.

6.2.2 Practice

This context indicates why the facilitative approach has become the preference in the majority of MEAs. To date, only three compliance committees have been triggered for review by a State against another State: the Aarhus Compliance Committee (twice), the Espoo Implementation Committee (nine times) and the Kyoto Protocol Facilitative Branch (once).

The Aarhus Convention Compliance Committee saw its first State-to-State procedure in 2004 when Romania triggered a non-compliance procedure against Ukraine, in relation to the Bystre Canal project in the Danube Delta.Footnote 18 It alleged that the Ukrainian authorities had not complied with the obligations of public participation and had not let various local and international NGOs participate throughout the planning of the project. The second procedure triggered before the Aarhus Convention Compliance Committee was submitted by Lithuania against Belarus in 2015 with regard to the construction of a nuclear power plant in Belarus. Lithuania claimed that Belarus had denied the right to access detailed information of citizens to Lithuania during the preparatory and project implementation phases of the construction of the nuclear power plant.Footnote 19

The Espoo Implementation Committee has seen nine procedures initiated by a State party against another, making it the most successful to date. They are all related to large projects with transnational effects, such as nuclear power plants, oil and gas projects, mining, hydropower plants or modifications to river waterways.Footnote 20 In these cases, the triggering parties argued that the transboundary environmental impact assessments were not carried out in accordance with the Espoo Convention.

Another interesting procedure was triggered before the Kyoto Protocol Facilitative Branch in 2006 by South Africa. In this case, South Africa made a submission, in its capacity as Chairman of the Group of 77 and China and on their behalf, about State parties’ non-compliance with Article 3.1 of the Kyoto Protocol.Footnote 21 The alleged non-compliance concerned the submission of national progress reports, as several countries had not submitted theirs six months after the set deadline.

There is further evidence of a sparing use of State-to-State procedures even beyond MEAs. For instance, before the UN human rights treaty bodies, the first inter-State communications ever to be submitted both occurred in 2018 before the Committee on the Elimination of Racial Discrimination (CERD).Footnote 22 The CERD dealt with an inter-State communication submitted by Qatar on 8 March 2018 against Saudi Arabia and the United Arab Emirates (UAE), and an inter-State communication submitted on 23 April 2018 by the State of Palestine against Israel.

There are several reasons that could explain the very sparing use of State-to-State triggers, despite their appearance in the guidelines or rules of procedure of all compliance committees. We identify two types of challenges: challenges related to the perception and behaviour of States vis-à-vis State-to-State triggers and challenges related to the institutional design and procedural mechanisms of State-to-State procedures.

6.3 Reluctance of States to Use Compliance Procedures

Although it is not within the scope of this chapter to empirically assess why States are reluctant to use State-to-State triggers, we identify two circumstances that may make State-to-State compliance procedures seem undesirable to States. First, State-to-State compliance procedures can be perceived as hostile mechanisms by States (Section 6.3.1). Second, States may lack the motivation to defend communal interests through State-to-State triggers (Section 6.3.2).

6.3.1 Hostile Perception of State-to-State Compliance Procedures

The principal reason States may be discouraged from using State-to-State procedures is the adversarial and hostile perception of those State-to-State triggers, as mentioned in Section 6.2.1. This hostile perception means that States may think that triggering a compliance procedure against another State may be perceived as an escalation of tensions in their diplomatic relations. This is because the process of one State complaining about another State before a third party (judicial, quasi-judicial or non-judicial) is perceived negatively in international relations. Indeed, while the judicial avenue is theoretically an equal alternative to other forms of peaceful dispute settlement provided in the UN Charter,Footnote 23 it tends to be a last resort in practice. Certain MEAs or international human rights conventions even provide that a court (most commonly, the International Court of Justice (ICJ)) may only be seized once negotiations have been exhausted.Footnote 24 This indicates that States may turn to a third party when they are unable to communicate successfully between themselves, or, worse, when they have reached a political ‘boiling point’ or deadlock.Footnote 25 In the context of human rights compliance committees, notable examples include the Israeli–Palestinian dispute before the CERD as part of a decades-long historical conflict with deadlocked negotiations.Footnote 26 The other dispute before the same committee between Qatar and the UAE is also in the context of an important political conflict between these two countries which also made its way onto the ICJ’s docket.Footnote 27

Tensions that lead to the triggering of a State-to-State procedure escalate more easily between neighbouring countries. In addition to the two disputes between neighbouring countries before the CERD, all procedures before the Espoo Implementation Committee have involved neighbouring States, where projects have had clear transboundary effects. Obligations around transboundary environmental impact assessments lend themselves naturally towards a bilateral and adversarial conflict, as they are easily ‘bilateralisable’. For instance, in 2019, Montenegro started a procedure against Albania regarding the ongoing build of a small hydropower plant on the Cijevna River, which is shared with Montenegro. It alleged that Albania had not considered the potential adverse impacts of the project on Montenegrin territory and people.Footnote 28 This is a clear case of a ‘bilateralisable’ and adversarial problem arising within a multilateral treaty, where Montenegro is using similar rhetoric and seeking a similar outcome to what it would use, and seek, in a judicial procedure.

Any compliance arrangements in general may already be viewed as hostile, discouraging States from setting ambitious environmental targets or even joining the MEA altogether.Footnote 29 However, State-to-State triggers would naturally be seen as particularly undesirable. One participant recalled that ‘parties are very reluctant to be pointed the finger at. They want to avoid that’.Footnote 30 This could, at least partly, be due to the disclosure of sensitive information or the attraction of potentially negative public opinion during proceedings.Footnote 31 It could also be due to costs associated with such proceedings where relevant. Another reason could be the risk of a ‘boomerang effect’, whereby the initiating State may be under closer scrutiny from the alleged non-complying State, who is looking for retaliation. The latter may become vindictive and look into whether the triggering State is also complying. Such a ‘boomerang effect’ could also take place with respect to another MEA, as there are chances that both States are parties to multiple treaties. States could even bring other issues beyond the scope of the MEA in question to the forefront. The committee would be ‘open to misuse’,Footnote 32 creating a space for political issues other than the compliance with the treaty in question. However, such risks can and will be mitigated by the committee itself, which will decide on its jurisdiction and the scope of its work. Unfortunately, this was not a sufficient guarantee in the negotiations of the PAICC, possibly because of the high political stakes under the Paris Agreement.

The hostile perception of State-to-State triggers could also explain why the dispute settlement mechanisms featured in MEAs are rarely used.Footnote 33 Indeed, a few MEAs feature a clause giving State parties the option to resort to the ICJ or possibly arbitration if a dispute arises about the interpretation, application of or compliance with the relevant convention.Footnote 34 Therefore, in theory, a State could resort directly to judicial bodies as opposed to non-compliance procedures on a matter of another State’s non-compliance with their shared convention. These procedures are separate.Footnote 35 However, ‘there appears to be widespread avoidance of resort to third-party dispute resolution’.Footnote 36 This may in part be due to the fact that most non-compliance is due to capacity issues as opposed to the legal interpretation of a provision in an MEA.Footnote 37 It is however mainly due to the confrontational nature of dispute settlement, requiring the existence of a dispute where States ‘hold clearly opposite views concerning the question of the performance or non-performance of certain international obligations’,Footnote 38 with one party’s claim being ‘positively opposed’ by the other.Footnote 39 It is also likely due to the binding nature of dispute resolution procedures, disliked by States who prefer more flexibility with regard to their environmental commitments.Footnote 40

6.3.2 Lack of Motive to Defend Communal Interests

Many of the obligations contained in MEAs are arguably obligations erga omnes partes. This means that a State party owes such obligations towards all the other States parties to the same treaty, due to the treaty’s protection of collective interests. Therefore, all State parties have their own interests on the one hand and communal interests on the other hand.Footnote 41 By ratifying those treaties, they have agreed that the protection of environmental rights is worth joint efforts. The pursuit of this ‘common good’, however, does not seem to have inspired many States to date. They may lack motivation to pursue such proceedings due to both the absence of perceived personal gain and the novelty of the practice itself. Indeed, from a jurisdictional perspective, States have a legal interest in safeguarding community interests before a judicial body or a compliance committee, if such obligations are erga omnes partes. However, international jurisprudence has recently distinguished between specially affected States – directly and tangibly impacted by the breach of an obligation – and non-specially affected States that may be concerned about ensuring respect for the erga omnes partes obligation but are not directly and tangibly impacted by its breach.Footnote 42 While States occasionally demonstrate altruism in international relations,Footnote 43 they may generally hesitate to start a procedure against another State if they are not specially affected by the breach in question. This may particularly be the case as the practice is quite novel.

As much as this can explain some of the reasons States are reluctant to use State-to-State compliance procedures, it does not make such procedures redundant. Contrary to the common perception that State-to-State proceedings are hostile, it can be argued that they were designed to allow for collegial co-operation and solidarity between States. Indeed, a State-to-State compliance procedure is communal in nature.Footnote 44 Even if the procedure itself opposes two parties, the purpose of the procedure has a larger communal objective. In this sense, it is possible to view such procedures not as hostile, but as co-operative, aspiring towards a ‘common good’.

On one hand, there are many instances where the initiating State is specially affected by another State’s non-compliance, and therefore communal obligations can be ‘bilateralisable’ such as the case of the Espoo Convention on Transboundary Environmental Impact Assessments. On the other hand, there are instances where a State can be non-specially affected by another State’s non-compliance with communal obligations, such as in the case of the Kyoto Protocol. In both types of cases, a shift in States’ understanding of State-to-State procedures may be used as is necessary: individual adversarial procedures can be conducted for the defence of community interests. Although the more bilateral nature of a State-to-State procedure may be at odds, from the perspective of State parties, with the communal spirit of the treaties under review, they are not incompatible.

6.4 Procedural and Institutional Challenges

Since State-to-State compliance procedures are adversarial in nature, opposing two States, the type of procedural rules applicable become central to the conduct of such procedures. Certain well-established procedural principles developed in the judicial context become essential to the State-to-State compliance procedure, such as questions of jurisdiction (Section 6.4.1), evidence (Section 6.4.2), expertise (Section 6.4.3), independence and impartiality (Section 6.4.4), participation and transparency (Section 6.4.5) and outcomes (Section 6.4.6). This section will argue that the design and practice surrounding these identified procedural and institutional features of State-to-State triggers can contribute to their scarce use by States.

6.4.1 Jurisdiction

Questions such as when a compliance committee should pursue a State-to-State procedure are worth exploring, as they show that it is not only States that can be the reason why State-to-State procedures do not proliferate, but it is also committees themselves that can prevent procedures from being heard. This means that even when State-to-State triggers are initiated, the process can be impeded by a hesitant committee.

The case submitted by South Africa to the Kyoto Protocol Facilitative Branch – one of the two branches of the Protocol’s compliance committee – shows that the committees themselves may not be as familiar as expected in dealing with State-to-State compliance procedures. Potential reasons for this may be that they have so little prior experience. In this case, as soon as the submission was not exactly in line with the set procedures, the committee decided to end the procedure altogether.

As mentioned, the submission by South Africa was made, on behalf of the Group of 77 and China, against various parties for failure to communicate national reports. The Facilitative Branch dismissed the submission on procedural grounds. Indeed, two questions needed to be answered: Can a party submit on behalf of a group, and can a party submit against multiple other parties? These questions were not answered clearly in the Branch’s rules of procedures. Therefore, the committee decided the procedure could not continue. In only two instances, concerning Slovenia and Latvia, the Branch closed the procedure, as these two countries had in the meantime complied with their obligations, making the compliance procedure redundant.Footnote 45

The fact that the Branch did not engage with the merits of the claim brought by South Africa shows a strict application of the rules of procedures, despite there being easily justifiable grounds to continue the procedure. Indeed, the committee decided that South Africa did not name the States against which it was making its submission, but South Africa stated clearly that those States who were six months late in submitting their reports were the object of the submission, and sent the submission to the relevant fifteen States. Therefore, despite the fact that it did not clearly name the parties against which it was initiating the procedure, it was in fact clear who it was aimed at. This level of respect for the procedural rules may be seen as contrary to the Kyoto Protocol’s objective to, inter alia, ‘[c]ooperate with other … Parties to enhance the individual and combined effectiveness of their policies and measures’.Footnote 46 The decision shows great commitment to the wording of the rule, which could be explained by a lack of confidence on the part of the committee in its own ‘jurisdiction’ to rule on such matters. It also shows an unwillingness on the part of the committee to take matters into its own hands. An explanation for this behaviour may be that the committee does not have a traditionally ‘judicial’ mandate as do international courts and tribunals, and may have hesitated to take action without such traditionally understood ‘judicial’ legitimacy. This may contribute to an unclear institutional framework for the use of State-to-State procedures.

6.4.2 Evidence

Another procedural hurdle contributing to the scarce use of State-to-State triggers is the requirements for and handling of evidence during a State-to-State procedure. State-to-State triggers in MEAs allow for a State party to seize another State party before the compliance committee on the grounds of concern alone. In the 1972 London Convention on the Prevention of Marine Pollution by Dumping of Wastes and Other Matter the party must have an interest where it is affected or likely to be affected.Footnote 47 In the 2000 Cartagena Protocol on Biosafety and in the Rotterdam Convention it must be ‘directly affected or likely to be directly affected’.Footnote 48 The Basel Convention Compliance Mechanism is the most demanding in this respect, requiring a specific, bilateral relationship between the two parties involved in order to be triggered.Footnote 49 In all other MEAs, however, State parties may trigger this procedure without having to prove involvement or interest.Footnote 50 The benefit of this is that it facilitates the ability for States to easily trigger the procedure.

However, non-specially affected States may have more difficulty obtaining evidence that a certain State has violated an obligation in their shared convention. Indeed, States are still required to provide evidence of their claim in the form of an informational report. However, there are two obstacles to fulfilling this requirement.

First, it is perhaps difficult to imagine how a State would substantiate its claims in such a report if it were not directly affected. It is easier to substantiate claims and provide information for a matter that is of direct relevance to a State, as more information about the effects of the non-compliance is in the country itself. This closely mirrors traditional judicial inter-State disputes before international courts and tribunals.

Second, it is generally difficult for State parties to be aware of the level of compliance of other States. This would not be as much of a problem before international courts and tribunals because, at the ICJ for instance, proceedings involving erga omnes partes obligations have tended to be high-profile cases where evidence has already been collected by UN fact-finding missions or media outlets.Footnote 51 Therefore, even if the effects of the violation could not be measured on the State’s territory, it could still obtain enough evidence to support its claim.Footnote 52 States’ compliance with MEAs, however, does not garner the same level of publicity.

It is therefore more difficult for States who are not directly affected to corroborate their claims before compliance committees. This could explain why, in practice, only specially affected States have resorted to State-to-State triggers to date.Footnote 53 Regarding the attempt made by South Africa before the Kyoto Protocol Facilitative Branch, its submission was also rejected because it ‘was not supported by corroborating information and did not substantiate how the question related to any of the specific commitments of the relevant parties under the Protocol.Footnote 54

6.4.3 Expertise of Members of Compliance Committees

State-to-State procedures would also benefit from clearer rules surrounding the appointment and expertise of compliance committee members, if their use is to be enhanced. The range of expertise needed in order to be able to sit on a compliance committee is a point of contention, as the technical nature of a compliance committee may require non-legal skills, yet legal knowledge is essential to make adequate decisions. In order to make a decision on compliance, compliance committees need to rely on both legal and scientific or technical knowledge. This is often reflected in the rules, which might say for example that members ‘shall have expertise relating to the subject matter of the Convention in areas including scientific, technical, socio-economic and/or legal fields’, in the case of the Basel Convention Implementation and Compliance Committee.Footnote 55 Similar language is used for the PAICC.Footnote 56 This is an advantage that compliance committees may have over international courts, as the latter are often criticised for their lack of ability to handle scientific evidence.Footnote 57 One of the challenges of international adjudication, especially in an environmental context, is how judges handle complex facts, especially when they involve complex science, and how that affects their decision-making.Footnote 58

However, it is not always clear whether the requirements concerning the legal and/or scientific skills of the committee members are fulfilled in practice. Before the Montreal Protocol Implementation Committee, member States of the Montreal Protocol appoint their representatives. This means there is no requirement to co-ordinate between member States, and therefore no guarantee that the committee itself will be composed of individuals with balanced and complementary expertise.Footnote 59 Even in the human rights context, the CERD stated explicitly in the Qatar v Saudi Arabia case that it initially could not take any decisions due to ‘the legal complexity of the issues broached and a lack of resources’.Footnote 60

6.4.4 Impartiality and Independence of Members of the Compliance Committees

Another difficulty in relation to the members of the compliance committees contributing to the limited use of State-to-State triggers relates to their impartiality and independence. An important procedural safeguard that ensures a fair procedure is to separate the relationship between the individual members and the State(s) of which they are citizens. Guaranteeing that the members are not influenced or manipulated by outside forces, especially by potential parties to a compliance procedure, is a key element to achieving a fair outcome. It is a well-established rule in the judicial context and has also been integrated into the provisions and rules governing most compliance committees.Footnote 61 The reason why the two notions of impartiality and independence are especially important in State-to-State compliance procedures is that the role of the compliance committee is more akin to that of an arbiter between two parties in such a procedure. This role requires the committees to show fairness and equality in the process, and this is ensured, inter alia, by having impartial and independent members.

In order to ensure independence, a lot of compliance committees require that their members act in their personal capacities, and not as representatives of their member States.Footnote 62 Indeed, once they have been elected, often according to rules of geographical and/or gender representation, they need to be able to decide in their own name, separately from the States that nominated them. An example of how to operationalise the concept of impartiality can be seen in the context of the PAICC, where ‘[m]embers and alternate members shall perform any duties and exercise any authority in an honourable, independent, impartial and conscientious manner’,Footnote 63 and they have to confirm in writing that they will do so at the beginning of their mandate.Footnote 64 They also have to ‘disclose immediately any interest in any matter under discussion before the Committee that may constitute a real or apparent, personal or financial conflict of interest or that might be incompatible with the objectivity, independence and impartiality expected of a member’, which then prevents them from being involved in matters related to the issues they disclosed.Footnote 65

However, not all compliance committees are structured in the same way, and some important committees still have their members sit as representatives of parties, such as the Montreal Protocol and CITES.Footnote 66 When rules on impartiality and independence are not as clear, it can negatively affect the functioning of the committee. For instance, issues may arise when a member of the committee has a duty, as a civil servant, to relay information to its State.Footnote 67 This can impact the procedures and decision-making processes of the committee, as States before the committee may not feel free to share all necessary information for the committee to decide in the best possible way.

These guarantees of impartiality and independence may not be as essential in other roles performed by the compliance committees, especially as facilitators in compliance processes. However, when they act as arbiters in adversarial procedures, these guarantees are necessary and when they are lacking, this seriously undermines the State-to-State compliance procedures.

6.4.5 Participation and Transparency

Another procedural challenge in State-to-State procedures is the transparency of proceedings from the moment a State triggers the procedure against another State. While the State whose compliance is being called into question fully partakes in the proceedings and has the right to be heard, the same cannot systematically be said for the State who initiated the procedure. Typically, the latter State will be excluded from the procedure going forward and will have no opportunity to take stock of matters with which it was initially concerned. In fact, meetings between the compliance committee and the party whose compliance is in question are closed to the public.Footnote 68 This is possibly favourable towards the party in question who can avoid public scrutiny, potential embarrassment and the divulging of sensitive information. However, it does an injustice to the State triggering the procedure who has expressed concern.

This is particularly so in instances whereby the State triggering the procedure is required to be affected or have an interest of some sort. For instance, regarding the 2001 Stockholm Convention on Persistent Organic Pollutants, one author has observed a contradiction between the fact that a party must be particularly affected in order to trigger the procedure – reflective of a more ‘traditional, bilateral, state-to-state dispute approach’ – but cannot participate in the consequent proceedings.Footnote 69 Similarly, transparency before the Basel Convention has been described as ‘remarkably poor as far as … the Party triggering the mechanism [is] concerned’.Footnote 70

Before international courts and tribunals, State litigants are given equal rights of participation. Third States making requests for intervention are likewise fully integrated in written and oral proceedings if their request is granted.Footnote 71 Transparency is also an important feature of proceedings before international courts and tribunals. Before the ICJ, for example, written parties’ submissions may be made public on or after oral proceedings with the parties’ consent,Footnote 72 while oral hearings are made open to the publicFootnote 73 and streamed live online.Footnote 74 At the International Tribunal for the Law of the Sea (ITLOS), written pleadings of the parties are publicly accessible even before oral pleadings commence.Footnote 75 The World Trade Organization (WTO) Dispute Settlement Mechanism’s contrasting practices (confidential submissions by parties and closed oral hearings) have been widely criticised, demonstrating the increasing importance that transparency yields in international law.Footnote 76 Generally, participation and transparency have become increasingly significant in international judicial processes.

Greater transparency and participation are certainly imaginable before non-compliance procedures,Footnote 77 without jeopardising their facilitative spirit. In the case of the 1987 Montreal Protocol on Substances That Deplete the Ozone Layer, for example, ‘[a]lthough [it] is based on facilitative and amicable principles, it also envisages principles of due process, such as notification, right to a fair hearing and impartiality, which are usually found in traditional dispute settlement mechanisms’.Footnote 78

6.4.6 Outcomes of State-to-State Compliance Procedures

The lack of clarity in the outcome that States can get from triggering such procedures may further discourage their use. Indeed, the political cost of triggering a compliance procedure may not justify such an uncertain outcome. The question States may ask is: What can they get out of a State-to-State compliance procedure? The answer to this question is twofold and can partly explain why State-to-State compliance procedures have not been popular so far.

First, the fact that the decisions are not final and binding renders the overall effect of the decisions weaker. Indeed, the decisions taken by compliance committees ‘generally do not possess any legally binding force. Even if a non-compliance procedure results in giving an appropriate response to non-compliance, such a response would still be of only a preliminary nature, because it is up to the Conference of the Parties to take a final decision’.Footnote 79 The decisions taken by compliance committees are mostly endorsed by the Conference of the Parties – the governing body of the treaty – but theoretically the latter could depart from the initial decisions, or only adopt a part of them. In many instances, the compliance committee can take some decisions that are facilitative in nature, but when more punitive measures have to be taken, or those with financial consequences, the Conference of the Parties is the body that will take this type of decision.Footnote 80 This is contrary to judicial decisions rendered by international courts and tribunals, which are binding and final.

Second, the range of options available to compliance committees is also uncertain, rendering the outcome less predictable. Some measures that can be decided upon by compliance committees may also not necessarily suit a State-to-State compliance procedure. Facilitative measures include providing advice and information about how to facilitate compliance and requesting special reporting or action plans from the non-complying party. These may not be the desired outcome of a State-to-State compliance procedure.

Some potential outcomes could be more suitable from the perspective of a State triggering a non-compliance procedure, such as a declaration of non-compliance or a suspension of specific rights under the treaty. For instance, in the case between Lithuania and Belarus concerning Belarus’ non-compliance with the Aarhus Convention, the Committee was able to conclude that Belarus had ‘failed to comply’ with a number of provisions of the ConventionFootnote 81 and therefore recommended that ‘the Party concerned takes the necessary legislative, regulatory and administrative measures and establishes practical arrangements’.Footnote 82 This type of decision raises a number of questions pertaining to the law of State responsibility and the law of treaties, which have been the object of debate.Footnote 83 The lack of clarity on these points may contribute to a misunderstanding of the role of State-to-State compliance procedures.

In sum, it is not the case that compliance committees do not have the means to address State-to-State requests, as shown in the Aarhus Committee decision regarding Belarus’ compliance, but their role encompassing a broad range of actions may deter States from triggering them. Moreover, the frameworks within which compliance committees operate may prevent the latter from being more assertive in their decision-making, since they can only make recommendations that have to be adopted by the Conference of the Parties, which is constituted of States parties to the treaty in question. In other words, compliance committees may not have the tools necessary to make bolder decisions, as their overarching aim is still only facilitative – even in a more adversarial procedure – and their decisions are not final.

6.5 Conclusion

This chapter has sought to shed light on the reasons why State-to-State triggers are seldom used by State parties to MEAs. The reluctance of States is due firstly to the hostile perception of State-to-State compliance procedures and States’ lack of motivation to defend communal interests in the environmental context. A number of procedural and institutional challenges were additionally identified, such as issues with jurisdiction, evidence, participation, impartiality and independence, the expertise of such compliance committees, and the outcomes of proceedings.

The chapter observed that, regarding procedural and institutional challenges, international courts and tribunals have more rigorous and effective practices than compliance committees. Not only do international courts and tribunals perform better in many of these respects, but their decisions generate a higher level of authority in the international legal system.Footnote 84 Therefore, a combination of the efficient procedural practices of international courts and tribunals and their authority make them a more suitable venue for States to take environmental disputes. This can partly explain why there is an undeniable increase in inter-State environmental disputes before international courts and tribunals.Footnote 85

In an international legal system abundant with choices to keep States accountable to their obligations, compliance committees complement international courts and tribunals: compliance procedures provide a soft way to advise, encourage and influence States to comply with their obligations through assistance, aid and capacity building.Footnote 86 They are also helpful where State responsibility is difficult to establish in the environmental context. As Klabbers stated, ‘there is … often no real wrongfulness at issue – causality between behaviour and environmental degradation is frequently difficult to establish with the degree of precision that the law would insist on’.Footnote 87 Judicial procedures, on the other hand, through binding judgments, force States into compliance where State responsibility for environmental degradation can be established. Non-compliance procedures may also be viewed as instruments of ‘political rationality’ or a ‘symbolic exercise’ attempting to demonstrate effort to address an issue, while judicial enforcement embodies an ‘instrumental rationality’ attempting to achieve a desired result.Footnote 88 Both may be used concurrentlyFootnote 89 and both, in different yet complementary ways, push States to respect their international environmental obligations.

Where, in the midst of this, does this leave State-to-State triggers? They have certain judicial or quasi-judicial features, but the procedures they trigger under MEAs will take place before compliance committees rather than in international courts or tribunals. They are also part of a menu of other triggers designed to be facilitative and to provide support for capacity issues impeding States’ compliance with MEAs – but are perceived to be more confrontational as opposed to facilitative in their nature. State-to-State triggers therefore sit in between judicial and non-judicial procedures, and between facilitation on one hand and enforcement on the other.

There is, however, room for State-to-State triggers to evolve out of this supposed identity crisis. This could involve mirroring judicial procedures to align more with the practices of international courts and tribunals. This may not be appealing to States but would give more teeth to environmental obligations. Especially in light of current global environmental crises, we believe that this direction is the most desirable for the future of our planet.

7 Compliance with Science-Based Treaties

Rukmini Das
7.1 Introduction

International law, from its very origins, has developed without a central authority. Consequently, mechanisms for settling disputes or for ensuring compliance with international treaties have not been uniform or even coordinated. There is a wide array of courts and tribunals for judicial settlement of international disputes. There are also multiple non-judicial mechanisms to address treaty breaches or non-compliance, to interpret treaty provisions, or for dispute prevention. Judicial dispute settlement is thus not the only means of ensuring adherence to treaty provisions.

International legal agreements in recent times, especially those on various environmental or other technical or scientifically complex subject matters, envisage mechanisms for facilitating, promoting, and enforcing compliance with the commitments undertaken by the parties to these treaties.Footnote 1 Such mechanisms for assessing the compliance of parties with their obligations under that treaty have been referred to as non-compliance mechanisms (NCMs). Such NCMs are usually non-confrontational. As such they are markedly different from judicial dispute settlement, which is adversarial or confrontational by its very nature. For this reason, these NCMs may provide innovative alternatives to traditional dispute resolution procedures.Footnote 2

Another kind of treaty body often seen in international instruments of this nature is the Scientific Committee. Scientific committees have varying names under different treaty regimes.Footnote 3 This kind of committee, often with an advisory role, exists in treaty regimes related to, for example, environment and health, where scientific research is critically important to establishing agreed procedures and for effectively administering the treaty regime. Though not specifically established for the purposes of bringing about treaty compliance, these committees may make pronouncements that assist States to implement provisions of treaties or ascertain whether treaty obligations have been violated. This has the potential to go beyond mere application of treaty provisions, leading to the interpretation of certain (usually scientific) aspects of the treaty, thus overlapping to an extent with the powers of international courts or tribunals (ICTs) or avoiding recourse to them by pre-empting a dispute. The work of such committees and their impact is also examined in this chapter, along with NCMs and ICTs.

The focus on ‘science-based’ treaties in this chapter stems from the unique nature of the compliance issues that may arise in the context of treaties that govern complex technical or scientific subject matters. In the context of compliance with treaty obligations, a single treaty might provide for an NCM, provide for recourse to an ICT as a dispute settlement forum, and might also have a scientific committee whose role may involve indirectly interpreting treaty provisions. This chapter therefore analyses the various institutional contributions towards implementation and compliance of science-based treaties made through NCMs, other treaty bodies including scientific committees and dispute resolution before an ICT. The focus is on how best to address potential or actual treaty breaches, and the possible interactions among these different bodies.

Considering the evidently disparate natures of these processes – NCMs, the activities of scientific committees, and ICT dispute settlement – concerns exist with respect to the selection of members serving on the relevant bodies, their qualifications, expertise, and independence. Some of these concerns may arise out of a perception that scientific committees of a treaty would tend to be biased in favour of conservation or protection of the environment, while on the other hand, judges of ICTs may be considered less qualified to rule on matters involving scientific issues. The way in which judicial decision-making works, as distinct from a scientific body feeding its views into issues of treaty compliance, may also lead to particular questions of legitimacy of the outcome. It is however unclear which options may lend themselves to greater legitimacy. Would a judicial process with all its trappings of due process and reasoned decision-making, or the recommendation of a group of individuals with technical expertise in the relevant subject matter be more legitimate? Is it perhaps a combination of both?

This chapter takes a look at the various modes of enhancing the compliance of State parties with treaty obligations – whether with the aid of ICTs, scientific committees, or NCMs. In doing so, the chapter examines how procedures in NCMs, scientific committees, and international courts relate to each other and how they may operate in conjunction with one another. Scientific committees, on the one hand, and ICTs, on the other, are not presented as two dispute settlement choices emanating from a fork-in-the-road clause. Their spheres of influence may operate independently of each other in the treaty system. They may also be arranged sequentially with a committee serving as a first step in efforts to clarify facts about obligations and facilitate compliance, or to address a difference before it becomes a dispute.

A question that arises in this context is whether a judicial body should decide a case in the situation where there exists an expert scientific body under the relevant treaty, such as the International Whaling Commission (IWC) or the Commission on the Limits of the Continental Shelf (CLCS) under the UN Convention for the Law of the Sea (UNCLOS). Should an ICT necessarily defer to a competent scientific body, or can it decide not to rule on the issue?

It could be argued that in the Whaling case,Footnote 4 the definitive assessment of Japan’s actions should have been undertaken by the Scientific Committee of the IWC, a body truly competent to do so.Footnote 5 Similarly, in the Bay of Bengal delimitation case, the International Tribunal for the Law of the Sea (ITLOS) determined that it was able to delimit the continental shelf between the parties in the area beyond 200 nautical miles (‘nm’) from the respective States’ coasts, notwithstanding the role of the CLCS in issuing recommendations to States regarding the outer limits of the continental shelf.Footnote 6 The International Court of Justice (ICJ) adopted a similar approach in Delimitation of the Continental Shelf between Nicaragua and Colombia beyond 200 Nautical Miles.Footnote 7 In this context it is useful to remember the words of Arbitrator Wolfrum in the Chagos arbitration, in the context of leaving matters of scientific debate to scientists – ‘lawyers can do nearly everything’.Footnote 8 It is clear from the jurisprudence, and it is also the author’s opinion, that a judicial body is well within its jurisdictional limits to decide a legal dispute having scientific aspects.Footnote 9 It is indeed a fulfilment of its judicial function.

This chapter first examines NCMs (Section 7.2) and scientific committees (Section 7.3) in a range of treaties that cover environmental or other issues of a scientific character. This is followed by an examination of reference to ICTs for dispute settlement in the context of violations of treaties that also have an NCM alternative or a scientific committee making pronouncements on overlapping issues (Section 7.4). Thereafter, the chapter engages in a further discussion with specific case studies involving the crossing of paths between ICTs and certain scientific committees (Section 7.5). The chapter ends with concluding observations arising out of this analysis (Section 7.6).

7.2 Non-Compliance Mechanisms and Their Contribution to Compliance

This section provides an overview of compliance mechanisms (NCMs),Footnote 10 their working methods generally and in specific contexts, the scope of their powers, and the nature of their pronouncements, that is, the outcome of the compliance procedure.

NCMs in the form of compliance committees (with some having wider powers) can often be found in treaties, conventions, or protocols relating to the environment, or scientific issues generally (such as technical aspects of health, food, and agriculture). These include, inter alia, the Aarhus Convention,Footnote 11 the Kyoto Protocol,Footnote 12 the Kiev Protocol,Footnote 13 the London Protocol on Water and Health,Footnote 14 the Convention on the Conservation of Antarctic Marine Living Resources,Footnote 15 the Basel Convention on Transboundary Movement of Hazardous Wastes,Footnote 16 the Paris Agreement,Footnote 17 and the International Treaty on Plant Genetic Resources for Food and Agriculture.Footnote 18

Non-compliance committees such as those under the above-mentioned conventions and protocols are generally established to review compliance under that protocol or treaty. An NCM commonly goes through the following steps. Review of a party’s compliance may be triggered usually in several ways: by a submission to the treaty committee from another party, or from the party itself concerning its own compliance, or by referrals from the secretariat of the treaty body, or by the committee itself. In case of the Aarhus Convention, submissions may even come from members of the public.Footnote 19 Non-compliance committees are empowered and required to examine the question of non-compliance before them. However, they cannot issue binding decisions. Instead, these committees make ‘recommendations’ to the parties collectively, or to individual parties. The members of these NCMs are appointed in their personal capacity and are therefore expected to remain independent as opposed to being State representatives. This should depoliticise their work and give them greater independence and credibility. Unlike ICTs,Footnote 20 such NCMs tend to include in their membership technical or scientific experts as well as lawyers or diplomats.

Pursuant to an NCM’s recommendation, the final output is often a decision by the Conference of Parties to the treaty. Substantively, an NCM procedure could lead to financial or technical incentives to assist the party concerned in becoming compliant, or it could lead to penalties, sanctions, or suspension of privileges. Despite these possible consequences, the procedures before NCMs remain less adversarial and thus non-confrontational.Footnote 21

One of the earliest NCMs can be seen within the framework of the Montreal Protocol.Footnote 22 It may be triggered by any party, or the secretariat.Footnote 23 Once the NCM is invoked, the Implementation Committee, a standing body elected by the Meeting of the Parties, considers the situation of non-compliance, with a view to securing an amicable solution. Recommendations of this committee can be adopted as decisions of the Meeting of the Parties. The Kyoto Protocol’s comprehensive compliance mechanism includes an enforcement branch that determines non-compliance followed by a consequent course of action.Footnote 24

The compliance committee under the Aarhus Convention has been established pursuant to Article 15 of the Convention, which requires the Meeting of the Parties to establish ‘optional arrangements of a non-confrontational, non-judicial and consultative nature for reviewing compliance with the provisions of the Convention’. On the recommendations of this committee, parties to the Convention adopt decisions on general issues of compliance as well as compliance by individual parties. Under the Escazú Agreement, a Committee to Support Implementation and Compliance is establishedFootnote 25 as a subsidiary body of the Conference of Parties to promote the implementation of the treaty and to support the parties in that regard. The nature and role of this committee is clarified in this provision itself, as ‘consultative and transparent’, ‘non-adversarial, non-judicial and non-punitive’, while it reviews compliance with treaty provisions and makes recommendations. Its functioning is further defined by the rules promulgated at the first meeting of the Conference of Parties to this treaty.Footnote 26 Similar to the Aarhus Convention, here too, members of the public have the option to file communications regarding non-compliance by a treaty party.Footnote 27 Article 15 of the Minamata Convention on Mercury establishes an Implementation and Compliance Committee as a subsidiary body of the Conference of Parties. It functions according to its own rules of procedure, drawn up at its first meeting.Footnote 28 The Espoo Convention has an Implementation Committee, established by a Meeting of the Parties,Footnote 29 to review party compliance with treaty objectives. The procedures of this committee have been referred to as non-adversarial and assistance-oriented,Footnote 30 and they are without prejudice to provisions for dispute settlement under the Convention.

Most recently, the Paris Agreement, under Article 15, established the Committee to Facilitate Implementation and Promote Compliance, whose role is to function in a transparent, non-adversarial, and non-punitive manner. It will function according to its rules of procedure, adopted at CMA4 in Egypt,Footnote 31 and the committee’s work is guided by the modalities and procedures for its effective functioning.Footnote 32

A potential weakness of compliance committees is that the committee decisions cannot have the same legal weight as those of judicial bodies. However, this may also be viewed instead as an advantage. The procedures of compliance committees are still too often considered only in comparison to those of judicial organs, leading to the conclusion that they are similar to judicial bodies, but without the same capacity for action.Footnote 33 A number of them are composed of legal, as well as other expert members, with recognised competence in the field to which the treaty or protocol relates. Yet they have distinct procedures for determining facts and for discussing different points of view. And, in essence, a compliance committee often provides a non-confrontational means of preventing and addressing situations of non-compliance, with legal as well as technical expert involvement.

Due to their quasi-judicial nature, compliance committees are half-way between scientific committees and ICTs from an institutional perspective.Footnote 34 However, they are suitable for minor breaches,Footnote 35 especially when the party in breach is willing to comply, or for serious issues of non-compliance in the first instance (before seeking recourse to an ICT), in cases involving systemic concerns, or when penalties for non-compliance are severe. In the case of serious breaches or when it is foreseen that a treaty party may be unwilling to comply, ICTs have the advantage of providing a more public forum of redress, bringing widespread attention to the non-complying party’s infractions.

7.3 Scientific Committees and Their Contribution to Compliance

Scientific committees contribute to treaty compliance in a number of ways, although their primary role can be seen as an advisory one, on scientific and technical matters, usually advising a treaty’s Conference of Parties. This function helps in strengthening the treaty regime, making it more robust, defensible, and progressive. There are, however, other ways in which scientific bodies could contribute to treaty compliance. This may take the form of contributions to treaty interpretation, or even determining treaty infractions,Footnote 36 though such roles are rarely seen.

Scientific committees are a sub-class of a wider range of treaty bodies. Under various treaties with environmental or scientific subject matters, as under certain other treaties, there are often treaty bodies which effectively monitor implementation of or compliance with the treaty (such as the IWC Infractions Sub-Committee),Footnote 37 or provide advice or recommendations on the interpretationFootnote 38 or application of the concerned treaty (such as the CLCS).Footnote 39 Treaty bodies may be legal or technical depending on the body. The Infractions Sub-Committee of the IWC is an intergovernmental body, while the CLCS is a technical body. Examples of other intergovernmental treaty bodies include fisheries commissions such as the Commission for the Conservation of Southern Bluefin Tuna (CCSBT)Footnote 40 or regional seas bodies such as the OSPAR Commission.Footnote 41 These latter treaty bodies are advised in turn by scientific committees established under these treaties.

Undoubtedly, the role of scientific committees is distinct from that of other treaty bodies as well as from both NCMs and ICTs. Scientific committees exist to ensure smooth and uniform functioning of the treaty regime, along with pushing forward the growth of scientific knowledge in the specific field pertaining to the treaty. For selected examples of scientific committees, we can refer to the scientific committees under the IWCFootnote 42 or the Convention for the Conservation of Southern Bluefin Tuna, the Scientific Committee of which performs an important role in advising the intergovernmental CCSBT.Footnote 43

However, as in other regional fisheries management organisations, it is the intergovernmental Commission that is the decision-making organ under the Convention. The CCSBT exists to ensure the conservation and optimum utilisation of Southern Bluefin Tuna. Similar to the IWC, the CCSBT is responsible for setting a total allowable catch and its allocation among the members, it can administer regulatory measures to meet Convention objectives, and also take decisions to support and implement fishery management. The CCSBT has also adopted a compliance plan, providing a framework for States to improve compliance. Moreover, non-compliance with the total allowable catch attracts ‘corrective action’. The compliance plan includes policy guidelines such as the Corrective Actions Policy, which sets out a framework to respond to evidence of non-compliance by a treaty party.Footnote 44 This includes details of the decision-making process of the compliance committee of the CCSBT and a list of corrective actions that the committee may recommend. As in the IWC, the Commission’s Scientific Committee acts as an advisory body and makes recommendations to the CCSBT.

We likewise see both non-scientific and scientific treaty bodies under the Convention on International Trade in Endangered Species (CITES), which has a Standing Committee, Secretariat, and two scientific committees – the Animals and Plants Committees – who all play their roles in ensuring treaty implementation and compliance. The Standing Committee provides policy guidance to the Secretariat concerning the implementation of CITES, while also co-ordinating the work of the other committees. The two scientific committees are composed of scientific experts and were established at the sixth meeting of the Conference of Parties in 1987. Their function is to provide technical support to decision-making about species of plants or animals that are or may become subject to CITES trade controls. They provide scientific advice and guidance to the other bodies involved in ensuring compliance, and their membership ensures geographic diversity.

Scientific committees, as distinguished from NCMs and other treaty bodies, are usually composed of scientific members,Footnote 45 and their working procedures vary. Their strength lies in providing authoritative pronouncements on scientific issues. Their recommendations may be used by another treaty body (such as a commission) in arriving at its decisions (as is the case with the IWC relying on its Scientific Committee’s reports in making recommendations and the CCSBT drawing on its Scientific Committee’s advice).

The IWC is composed of Commissioners, one from each party to the International Convention for the Regulation of Whaling (ICRW). Its tasks include designating whale sanctuaries, setting catch limits on whales by species and area, and imposing restrictions on hunting methods. In the absence of any explicit compliance mechanism under the ICRW, the IWC has established an Infractions Sub-Committee. Breaches of the Convention must be reported to the IWC and are discussed by this Sub-Committee. It is not always easy to determine the existence of an infraction, due to ‘wider issues within the Commission’.Footnote 46 Infractions within a country’s national jurisdiction are dealt with by that nation itself, and these countries often impose penalties in the form of fines or imprisonment. The Scientific Committee of the IWC provides scientific advice to the Commission on matters under the Convention. Its tasks have included, for example, review of the second phase of Japan’s Whale Research Programme under Special Permit in the Antarctic (JARPA II),Footnote 47 which was the subject matter of a dispute before the ICJ,Footnote 48 discussed in Section 7.5.1. Thus, a scientific review of whaling research programmes such as JARPA II falls within the purview of the Scientific Committee. The IWC, on the advice of its Scientific Committee, has the power to amend the schedule to the ICRW by adopting regulations with respect to the conservation and utilisation of whale resources.Footnote 49 The Commission may also make recommendations to the State parties.Footnote 50

Established under the UNCLOS is the CLCS. The CLCS is a sui generis body. Like scientific committees under the various conventions, it is comprised of technical experts. It is composed of twenty members, experts in the fields of geology, geophysics, or hydrography, who are elected by States parties to the Convention from among their nationals.Footnote 51 They serve in their personal capacities.Footnote 52 Yet its role differs markedly from that of scientific committees. The primary function of the CLCS is to implement Article 76 of UNCLOS, dealing with the definition of the continental shelf, and to establish the outer limit of the continental shelf beyond 200 nautical miles (nm). More specifically, the CLCS considers data from coastal States (UNCLOS parties) concerning the outer limits of the continental shelf beyond 200 nm, provides scientific or technical advice to the State if so asked during preparation of this data, and makes recommendations on the same. The CLCS also has detailed rules of procedure governing not just its composition, conduct of business, and voting, but also the procedure to be followed when receiving submissions from a coastal State and in giving advice to such States.Footnote 53 It is important to note that the limits of the continental shelf beyond 200 nm established by coastal States based on CLCS recommendations are final and binding.Footnote 54 This is an important distinguishing feature of this body, and is one of the features setting it apart both from traditional scientific committees and from the NCMs discussed so far.

7.4 Recourse to ICTs

Apart from the above-mentioned non-judicial, non-confrontational mechanisms to ensure compliance, many of the treaties or protocols also envisage the option for dispute settlement before an ICT. As the following discussion reveals, these could be the same treaties that also include NCMs. This section looks at the dispute settlement clauses in these kinds of treaties and how ICTs may therefore contribute to treaty compliance, focussing on the examples of the ICRW, UNCLOS, and the CCSBT.

ICTs are certainly not incapable of resolving disputes involving complex scientific issues. An advantage of resorting to judicial means would be that judges have fresh eyes on the matters which treaty bodies deal with on a daily (or at least annual) basis. Judges would thus have some distance and an independent perspective on the matter. This perceived independence also arises out of a perception that scientific committees of a treaty system would tend to be biased in favour of conservation or protection of the environment.

Apart from the IWC and its various committees keeping a check on compliance by treaty parties, there is no dispute resolution clause in the ICRW, providing for recourse to arbitration or judicial settlement by the ICJ, for example. The dispute between Australia and Japan under this Convention was brought before the ICJ through the optional clause of the Statute of the ICJ, that allows States to opt into accepting the compulsory jurisdiction of the ICJ.Footnote 55

On the other hand, the UNCLOS has a robust system of compulsory dispute settlement laid out in Part XV of the Convention. This Part provides a number of options to Contracting Parties, after attempting to settle a dispute through peaceful means, negotiation, or conciliation: recourse to either the ICJ, ITLOS or arbitration under Annex VII or Annex VIII of the Convention. All matters covered by the UNCLOS fall within the jurisdiction of these courts and tribunals. A few specific matters may be expressly excluded by a Contracting Party, as listed in Section 3 of Part XV. UNCLOS tribunals will otherwise have jurisdiction over disputes relating to the continental shelf, and indeed a number of disputes have come up, as discussed in Section 7.5.2.Footnote 56

Parties to the Southern Bluefin Tuna Convention may submit any dispute concerning its interpretation or application, that is not settled amicably to the ICJ or to arbitration under the Annex to the Convention.Footnote 57 However, prior consent of all parties concerned is required before resorting to either of these judicial means of dispute settlement. In the Southern Bluefin Tuna cases,Footnote 58 the Tribunal established under Annex VII of UNCLOS declined jurisdiction since it found that these provisions of the Southern Bluefin Tuna Convention excluded dispute settlement under UNCLOS.

The treaties and conventions discussed in Section 7.2, all possessing NCMs to oversee compliance with treaty obligations, also provide for dispute settlement through ICTs, as in the Southern Bluefin Tuna Convention. Under the Aarhus Convention, parties, after attempting to resolve a dispute by negotiation, have the option to accept the compulsory jurisdiction of the ICJ or of arbitrationFootnote 59 for disputes arising under this treaty.Footnote 60 The Escazú AgreementFootnote 61 and the Espoo ConventionFootnote 62 follow an identical procedure to the Aarhus Convention. The CITES follows a similar route, however including only the possibility of arbitration at the Permanent Court of Arbitration, if negotiations fail.Footnote 63 The Convention on Biological Diversity envisages a few more amicable means of resolving disputes. Failing resolution through negotiations, parties in dispute could jointly seek good offices or mediation.Footnote 64 Failing both these stages, the modes of ICT dispute settlement as in the Aarhus Convention are also envisaged here.Footnote 65

7.5 Relationship between ICTs and Scientific Committees

The preceding sections have mapped broadly three kinds of mechanisms that operate simultaneously towards treaty implementation and compliance: NCMs, treaty bodies including scientific committees, and ICTs. This chapter now focusses on the latter two mechanisms. This section investigates the relationship between the work of scientific committees and ICTs through a focus on two examples: the Japanese whaling programme in the Antarctic, and selected disputes regarding continental shelf delimitation beyond 200 nm.

First, examining the dispute over the Japanese whaling programme in the ICJ, a proposal is made for the greater involvement of scientific treaty bodies in decision-making by ICTs. Second, examining the selected continental shelf disputes, we look at situations where a specialised scientific body (the CLCS) may issue its recommendations on matters before they proceed to an ICT. This is a unique situation and in the author’s opinion deserves a brief discussion.

7.5.1 Whaling in the Antarctic: The ICJ and IWC’s Scientific Committee

The preceding sections have examined the contributions of different international bodies to treaty compliance. In focussing this section on the relationship between two of these fora (scientific committees and ICTs), a case study on the Whaling case before the ICJ leads to a proposal to involve scientific treaty bodies in the decision-making of ICTs.

In the Whaling case, Australia brought a dispute against Japan (with New Zealand intervening) under the ICRW before the ICJ claiming that Japan’s whaling programme was in breach of its obligations under the Convention.Footnote 66 Although twelve judges were in favour of the majority in its final decision on the merits, eleven judges appended separate or dissenting opinions to the judgment. A reading of these opinions indicates that judges were divided on whether it was the Court’s task to judicially review the Japanese whale research programme, and decide whether the same was ‘for the purpose of scientific research’, or whether it could only be subject to scientific review by the IWC.Footnote 67 According to Judge Xue, the question whether activities under Japan’s whaling research programme , ‘JARPA II’, involved scientific research was a matter of fact rather than a matter of law, and thus should be subject to scientific, not judicial review.Footnote 68 On the other hand, Judge Keith’s declaration emphasised the ICJ’s power to judicially review a State’s granting of special permits under the ICRW.Footnote 69 Judge Bennouna raised the issue that perhaps instead of the ICJ sitting in judgment over such matters of science, these issues could best be left to the IWC and the Scientific Committee to determine at the appropriate times, as determined by the ICRW.Footnote 70 In Judge Bennouna’s opinion, the Court had usurped the powers of these treaty-based bodies. Judge Owada agreed with this proposition,Footnote 71 though he further argued that certain aspects of these issues were subject to legal scrutiny – such as whether procedural requirements were followed, or whether the activities in question met the ‘general accepted notion of scientific research’.Footnote 72 In the context of adherence to procedural requirements, the Court ruled that Japan had complied with the obligations under paragraph 30 of the Schedule to the ICRW, that is, submitting proposed scientific permits for review by the Scientific Committee. It is interesting to note the interaction between the Court and the Scientific Committee in this analysis, in the sense that the Court went into detail regarding the Committee’s practice and arrived at its decision on this point based on that practice.Footnote 73

Thus in the Whaling case, although parties presented expert witnesses who testified and were cross-examined in the oral proceedings, a few judges were of the opinion that the expertise most suited to decide these scientific issues was situated outside the Court.Footnote 74 It is important to note that in accordance with its Statute, the ICJ Registrar had notified the IWC of the proceedings before the Court; however, the IWC chose not to submit any observations.Footnote 75 The Court also noted that the Scientific Committee of the IWC is not empowered to make binding assessments on special whaling permits, the subject of contention before the Court.Footnote 76 Rather, the Committee sends ‘recommendations’ to the IWC regarding its views on programmes for scientific research. The Court considered that Japan should have given ‘due regard’ to the Scientific Committee’s recommendations since States parties to the treaty had a duty to co-operate with the IWC and Committee.Footnote 77 However, a point of contention in this dispute included an assessment of whether all the required reviews had been conducted by the Scientific Committee.

The dissenting judges’ critiques raise important questions regarding the processes most suited to resolve disputes of a scientific nature, especially in the context of treaties which have constituted scientific bodies to advise and provide recommendations on the same scientific issues. One may even consider how ICTs could benefit from the expertise of scientific bodies in their decision-making. The involvement of scientific bodies could be envisaged in two ways: either as consultants involved in the selection of court-appointed experts, or as experts themselves, advising the court or tribunal. Such involvement would provide the dual benefits of uniform treaty compliance and enhanced legitimacy of the judicial decision.

The question of legitimacy of outcome hinges on the legitimacy of the judicial process versus the legitimacy of scientific findings. An ICT could combine the two if it involved the relevant scientific bodies in its decision-making process, perhaps through seeking expert opinions from these bodies. Dispute settlement panels of the World Trade Organization receive advice from international organisations that have the necessary expertise on the subject in dispute before them.Footnote 78 They may also rely on international organisations to suggest names of experts who could aid in fact-finding.Footnote 79 At the same time, certain scientific bodies have often been criticised as being politicised. Some disputing parties may also be of the opinion that scientific committees will always have a bias in favour of the treaty’s objectives (not necessarily a disadvantage). If there is merit in these arguments, it may be better for ICTs to go through their own processes of seeking expert advice (or relying on parties’ expert evidence) and reaching a decision.

7.5.2 Delimitation of the Continental Shelf: Judicial Bodies and the CLCS

This section looks at a specific scientific treaty body, the CLCS, and how its activities intertwine with those of ICTs. In examining selected decisions by the ICJ and ITLOS, this section proposes that for a specialised scientific body like the CLCS, it may be more conducive to compliance if the parties were to wait until the CLCS issues its recommendations prior to initiating dispute settlement proceedings before an ICT.

A series of cases before different ICTs have highlighted the interactions between these judicial bodies and the CLCS. Before the ICJ, in the case concerning Delimitation of the Continental Shelf between Nicaragua and Colombia,Footnote 80 Colombia made a preliminary objection to admissibility of the dispute on the ground that Nicaragua had not obtained the requisite recommendation from the CLCS. While the Court decided on this point that it could undertake the delimitation of the continental shelf beyond 200 nm independently of a recommendation of the CLCS,Footnote 81 Judge Bhandari’s declaration on this issue is also interesting to note. In his opinion, the CLCS, a specialised agency with a specific mandate to investigate and pronounce upon continental shelf claims, consisting of members who are world-renowned experts in such relevant fields as geology, geophysics, and hydrology, are better equipped to resolve a continental shelf dispute such as the one before the ICJ. He was not in favour of relying on expert testimony from the parties either, since that would not only constitute an

inefficient use of valuable Court resources, but … Parties would bring witnesses most likely to advance their respective and competing claims, whose opinions could … be at odds with those of the expert members of the CLCS. This, in turn, could potentially lead to the uneasy situation wherein the CLCS and the Court reach incompatible conclusions regarding Nicaragua’s continental shelf claim.Footnote 82

While Judge Bhandari’s comment brings forth the general question of the ICJ being able to adjudicate scientific claims, in this particular instance, it must be read with Article 9 of Annex II to UNCLOS, which states that the ‘actions of the Commission shall not prejudice matters relating to delimitation of boundaries between States with opposite or adjacent coasts’. This could, however, lead to conflicting pronouncements from two different authorities. Scholarly opinion leans towards the Court appointing experts under Article 50 of its Statute, for a transparent evaluation of the scientific evidence.Footnote 83

In another ICJ dispute between Somalia and Kenya, the Court noted unequivocally that

a lack of certainty regarding the outer limits of the continental shelf, and thus the precise location of the endpoint of a given boundary in the area beyond 200 nautical miles, does not, however, necessarily prevent either the States concerned or the Court from undertaking the delimitation of the boundary in appropriate circumstances before the CLCS has made its recommendations.Footnote 84

This pronouncement is a step towards embracing the legal aspect of scientific issues and responds to the challenge to the ICJ’s capability to evaluate the scientific evidence supporting a claim of continental shelf beyond 200 nm.Footnote 85 Thus, issues of maritime delimitation require international tribunals ‘to make a conclusive decision as to whether the continental shelves beyond 200 nm exist and to what extent they are overlapping’.Footnote 86

Like the ICJ, the ITLOS has also faced the question of its competence to decide technical questions of boundary delimitation as opposed to the CLCS. While the Tribunal decided that it is competent to decide the legal aspects of these issues, strong opposing views contend that the CLCS being an expert body would be best placed to ascertain the scientific facts, perhaps in contradiction to uncontested evidence before the ITLOS. The significance of the Bangladesh/Myanmar caseFootnote 87 lies in the examination of the relationship between the dispute-settling role of the Tribunal and the recommendatory (though almost decision-making) role of a body composed of scientific experts, the CLCS.Footnote 88 The determination of entitlement on the continental shelf beyond the 200 nm limit requires interpretation of Article 76 of UNCLOS, which, inter alia, defines the continental shelf and its limits. It is with respect to this task that the judgment made important remarks regarding the Tribunal’s authority to interpret and apply Article 76, relying on scientific evidence as appropriate. The ITLOS noted that

as this article contains elements of law and science, its proper interpretation and application requires both legal and scientific expertise. While the CLCS is a scientific and technical body with recommendatory functions entrusted by the Convention to consider scientific and technical issues arising in the implementation of article 76 on the basis of submissions by coastal States, the Tribunal can interpret and apply the provisions of the UNCLOS, including article 76. This may include dealing with uncontested scientific materials or require recourse to experts.Footnote 89

Moreover, since the question before the Tribunal regarding the parties’ entitlement to a continental shelf beyond 200 nm was largely legal in nature, the ITLOS ruled that it ‘can and should determine entitlements of the Parties in this particular case’. However since the application of Article 76(4) required scientific and technical expertise, the ITLOS considered that it ‘would have been hesitant to proceed with the delimitation of the area beyond 200 nm had it concluded that there was significant uncertainty as to the existence of a continental margin in the area in question’.Footnote 90 Due to the ‘uncontested scientific material’ before it (Bangladesh’s expert reports that Myanmar did not challenge), it could proceed to decide the legal question, by interpreting Article 76.Footnote 91 It would have been interesting to see the steps taken by the Tribunal if there were no such uncontested scientific evidence before it.Footnote 92 The facts of this case also raise the question as to whether uncontested scientific evidence should in principle relieve the ITLOS of its obligation to evaluate the evidence on its merits.

An interesting aspect of this unchallenged acceptance of scientific evidence comes to light from Judge Ndiaye’s Separate Opinion in Bangladesh/Myanmar.Footnote 93 He notes that under UNCLOS the power to assess the scientific and technical data submitted by a coastal State to the CLCS is vested exclusively in the CLCS. According to him, an ‘exercise in maritime delimitation consists of applying the natural sciences to ascertain the extent of the natural prolongation under the sea of each of the two States and of making a finding on – not awarding – the extent of the submarine basement nature has placed before each of the two States.’Footnote 94 While it is true that under Article 9 of Annex II to UNCLOS, actions of the CLCS do not prejudice matters regarding delimitation of coastal boundaries between States, according to Judge Ndiaye, the subject matter of this dispute called for a factual determination, rather than the Tribunal’s acceptance of ‘uncontested scientific evidence’. The CLCS, conducting an independent, objective analysis,Footnote 95 might have found the uncontested scientific evidence to be incorrect. This reasoning goes a step further than that of Judge Bhandari in Nicaragua v Colombia before the ICJ.

More recently, in the maritime boundary dispute between Ghana and Côte d’Ivoire, the CLCS had already made its recommendations in respect of Ghana, thus there was no risk that a judicial pronouncement would interfere with the functions of the CLCS. The Special Chamber of the ITLOS constituted to deal with the dispute, following the Tribunal in the Bangladesh/Myanmar case, also decided that it had the jurisdiction to delimit the continental shelf beyond 200 nm.Footnote 96 In this case, it justified its decision in light of the circumstances of the case: ‘there [was] no doubt that a continental shelf beyond 200 nm exists in respect of the two Parties.’Footnote 97

The exercise of delimitation of the continental shelf has both legal and scientific components. Although scientifically based,Footnote 98 it is legal in nature since it prescribes the entitlement of coastal States to the continental shelf.Footnote 99 Conversely, although legal in nature, the establishment of entitlement to the continental shelf beyond 200 nm involves evaluation of scientific evidence from geology or geomorphology or both. While Article 76 of the UNCLOS sets out specific criteria for the determination of the outer edge of the continental margin and the outer limits of the legal continental shelf, the task of application is not straightforward. Although Article 76 uses scientific terminology, the terms do not necessarily have the same meaning as in science. As pointed out in the Scientific and Technical Guidelines adopted by the CLCS, ‘[t]he Convention makes use of scientific terms in the legal context which at times departs significantly from accepted scientific definitions and terminology’.Footnote 100

Two main options are thus presented to disputing parties: first, if States dealing with a continental shelf delimitation were consistently to follow a sequence of approaching the CLCS before resorting to ICTs (if necessary), these courts and tribunals would have the benefit of a CLCS recommendation before issuing their decisions. It is in States’ interests to avoid inconsistency between recommendations and rulings in these different fora. Second, in the event that such disputes are brought before ICTs, if the courts’ decision-making involves assessment of scientific evidence, the use of experts by ICTs could grant greater legitimacy to their decisions and might increase the possibility of the courts’ operating in harmony with the recommendations of the CLCS. Of course, it must be borne in mind that, thus far, consultation of experts by the ICJ has been sparse, and by the ITLOS non-existent.Footnote 101

7.6 Conclusion

This chapter has examined how treaty compliance could be strengthened through the spectrum of a variety of fora – NCMs, scientific committees, and ICTs. The goal has been to examine their roles in treaty compliance both separately and in conjunction with each other. The chapter concludes that, to the extent possible, treaty parties should aim for a sequential approach, with ICTs being the last resort. This would provide the ICTs with the technical expertise of the scientific committees, and could enhance the legitimacy of the judicial decision, also avoiding inconsistencies between the outcomes of different fora. States parties should operate on a basis informed by the advice of scientific committees and the guidance of NCMs and thereafter, if necessary, an ICT could rely on this Scientific Committee’s findings or recommendations in arriving at its decision.

Footnotes

5 The Advisory Procedure in Non-Compliance Procedures Lessons from the UNECE Water Convention

The author wishes to thank Professor Christina Voigt, Professor Caroline Foster, Professor Attila Tanzi and Professor Martins Paparinskis for their insightful commentaries on previous versions of this chapter; and to PluriCourts, University of Oslo for their kind support. The views expressed remain my own.

1 For a comparative study on the advisory jurisdiction, see A Sandoval Bernal, La Jurisdicción Consultiva de las Cortes Internacionales (Tirant lo Blanch 2019); M Runavot, La competence consultative des jurisdictions internationals: Reflet des vicissitudes de la foncion judiciaire internationale (LGDJ 2009).

2 See Delimitation of the Maritime Boundary in the Indian Ocean (Mauritius/Maldives), Preliminary Objections, Judgment, ITLOS Reports 2020–2021, 17, para 203; S Rosenne, The International Court of Justice: An Essay in Political and Legal Theory (A.W. Sijthoff 1957) 492–93; L Boisson de Chazournes, ‘Advisory Opinions and the Furtherance of the Common Interest of Mankind’ in L Boisson de Chazournes, C Romano and R Mackenzie (eds), International Organizations and International Dispute Settlement: Trends and Prospects (Transnational Publishers 2002) 107.

4 See UNEP, Compliance Mechanism under Selected Multilateral Environmental Agreements (UNEP 2007); T Treves, L Pineschi, A Tanzi, et al. (eds), Non–Compliance Procedures and Mechanisms and the Effectiveness of International Environmental Agreements (TMC Asser Press 2009); M Fitzmaurice, Environmental Compliance Control (Max Planck Encyclopedia of Public International Law 2021).

5 J Viñuales and P Marie Dupuy, International Environmental Law (2nd ed., Cambridge University Press 2018) 343–51; M Fitzmaurice, Environmental Compliance Control (Max Planck Encyclopedia of Public International Law 2021) paras 5255; P Sands, J Peel, A Fabra and R Mackenzie, Principles of International Environmental Law (4th ed., Cambridge University Press 2018) 172–78; A Boyle, C Redgwell and P Birnie, International Law and the Environment (4th ed., Oxford University Press 2021) 254–60.

6 UNEP, Manual on Compliance with and Enforcement of Multilateral Environmental Agreements (UNEP 2006) 59.

7 A Tanzi and C Pitea, ‘Non-Compliance Mechanisms: Lessons Learned and the Way Forward’ in T Treves, L Pineschi, A Tanzi, et al. (eds), Non–Compliance Procedures (Footnote n 5) 569–70; Viñuales and Dupuy (Footnote n 6) 343–44.

8 Cf. A Boyle, C Redgwell and P Birnie, International Law and the Environment (4th ed., Oxford University Press 2021) 255; M Doelle, ‘Non-Compliance Procedures’ in L Rajamani and J Peel (eds), The Oxford Handbook of International Environmental Law (Oxford University Press 2021) 982.

9 On this point, see J Brunnée, ‘International Environmental Law and Community Interests’ in E Benvenisti, G Nolte and K Yalin-Mor (eds) Community Interests across International Law (Oxford University Press 2018) 172–74; Viñuales and Dupuy (Footnote n 6) 347.

10 The Aarhus Convention enables NGOs to initiate a procedure against a Party. See UNECE, Decision 1/7: Review of Compliance, UN Doc ECE/MP.PP/2/Add.8, 2 April 2014, para 18.

11 ECLAC, Decision I/3: Rules Relating to the Structure and Functions of the Committee to Support Implementation and Compliance, Doc 22-00344, 22 April 2022, Rule V(1).

12 The Water Convention enables members of the public to submit information concerning the non-compliance of a Party. See UNECE, Support to Implementation and Compliance, Decision VI/1, UN Doc ECE/MP.WAT/37/Add.2, 2012, para 28.

13 UNECE, Annex to Decision I/2: Review of Compliance, UN Doc ECE/MP.WH/2/Add.3, 3 July 2007, para 16.

14 E Milano, ‘The Outcomes of the Procedure and Their Legal Effects’ in T Treves, L Pineschi, A Tanzi, et al. (eds), Non–Compliance Procedures (Footnote n 5) 413.

15 G Ulfstein, T Marauhn and A Zimmermann (eds), Making Treaties Work: Human Rights, Environment and Arms Control (Cambridge University Press 2007) 10.

16 Montreal Protocol on Substances That Deplete the Ozone Layer, signed 25 November 1992, entered into force 14 June 1994, 1785 UNTS 517, 3.

17 UNEP, Decision IV/5, 4th Meeting of the Parties to the Montreal Protocol on Substances That Deplete the Ozone Layer (1992).

18 For a detailed overview of the Implementation Committee of the Montreal Protocol, see O Yoshida, The International Regime for the Protection of the Stratospheric Ozone Layer (Brill 2018) 209–85; E Barratt-Brown, ‘Building a Monitoring and Compliance Regime under the Montreal Protocol’ (1991) 16(2) Yale Journal of International Law 519–70; M Koskenniemi, ‘Breach of Treaty or Non-Compliance? Reflections on the Enforcement of the Montreal Protocol’ (1992) 3(1) Yearbook of International Environmental Law 123–62.

19 Viñuales and Dupuy (Footnote n 6) 334, M Fitzmaurice, Environmental Compliance Control (Max Planck Encyclopedia of Public International Law 2021) para 56.

20 UNFCCC, Modalities and Procedures for the Effective Operation of the Committee to Facilitate Implementation and Promote Compliance Referred to in Article 15, paragraph 2, of the Paris Agreement, Decision 20/CMA.1, UN Doc FCCC/PA/CMA/2018/3/Add.2, 19 March 2019. See C Voigt, ‘The Compliance and Implementation Mechanism of the Paris Agreement’ (2016) 25(2) Review of European, Comparative and International Environmental Law 113.

21 See UNEP, MC-2/4: Rules of Procedure for the Implementation and Compliance Committee of the Minamata Convention on Mercury, UN Doc UNEP/MC/COP.2/Dec.4, 6 December 2018. For an overview on this Committee, see J Templeton and P Kohler, ‘Implementation and Compliance under the Minamata Convention on Mercury’ (2014) 23(2) Review of European, Comparative and International Environmental Law 211–20.

22 ECLAC, Decision I/3: Rules Relating to the Structure and Functions of the Committee to Support Implementation and Compliance, Doc 22-00344, 22 April 2022.

23 UNFCCC, Procedures and Mechanisms Relating to Compliance under the Kyoto Protocol, Decision 27/CMP.1, Doc FCCC/KP/CMP/2005/8/Add.3, 9–10 December 2005, 94–96.

24 UNEP, Compliance Mechanism under Selected Multilateral Environmental Agreements (UNEP 2007) 9–10; Viñuales and Dupuy (Footnote n 6) 294–96.

25 Particularly, the mechanisms of the Aarhus Convention and the Escazú Agreement provide for this option.

26 For example, the mechanisms of the UNECE Aarhus Convention, Espoo Convention and Water Convention include the suspension of rights and prerogatives as a measure in response to non-compliance.

27 See UNECE, Compilation of Findings of the Aarhus Convention Compliance Committee adopted 18 February 2005 to date, 5 February 2021.

28 See UNEP, Implementation Committee Recommendations, Implementation Committee of the Montreal Protocol, available at https://ozone.unep.org/list-of-implementation-committee-recommendations.

29 UNECE, Submissions Overview: Implementation Committee of the Espoo Convention, available at https://unece.org/submissions-overview; UNECE, Opinions of the Implementation Committee of the Espoo Convention (2001–2020), (2020). Available at https://unece.org/sites/default/files/2021-02/Implementation%20Committee%20opinions%20to%202020_MOP-8_2020.pdf.

30 UNFCCC, Compliance under the Kyoto Protocol, available at https://unfccc.int/process/the-kyoto-protocol/compliance-under-the-kyoto-protocol.

31 UNECE Convention on the Protection and Use of Transboundary Watercourses and International Lakes, signed 17 March 1992, entered into force 6 October 1996, 1936 UNTS 269 (hereinafter referred to as ‘UNECE Water Convention’).

32 UNECE Water Convention, Articles 2 to 6; A Tanzi, A Kolliopoulos and N Nikiforova, ‘Normative Features of the UNECE Water Convention’ in A Tanzi, O McIntyre, A Kolliopoulos, A Rieu-Clarke et al. (eds) The UNECE Convention on the Protection and Use of Transboundary Watercourses and International Lakes (Brill Nijhoff 2015) 11.6; L Boisson de Chazournes, Fresh Water in International Law (Oxford University Press 2013) 3337.

33 UNECE Water Convention, Article 2(5). Although the intergenerational equity principle is not expressly included, the elements of this obligation are referred to in Article 2(5)(c) of the Convention.

34 UNECE, Decision III/1: Amendment to the Water Convention, adopted on 28 November 2003, UN Doc ECE/MP.WAT/14, Annex; for an overview of this amendment, see I Trombitcaia and S Koppel, ‘From a Regional towards a Global Instrument: The 2003 Amendment to the UNECE Water Convention’ in A Tanzi et al (eds) UNECE Convention (Footnote n 33) 15–31.

35 Cameroon, Gambia, Namibia, Nigeria, Chad, Ghana, Guinea-Bissau, Senegal and Togo.

36 UNECE (Footnote n 13).

37 Footnote Ibid., para 1.

38 Footnote Ibid., para 2.

39 Footnote Ibid., paras 3 and 4.

40 Footnote Ibid., paras 24–27.

41 Footnote Ibid., paras 28–29.

42 Footnote Ibid., paras 28 and 29.

43 UNECE, Annex to Decision I/2 Review of Compliance, UN Doc ECE/MP.WH/2/Add.3, 3 July 2007, para 16.

44 UNECE (Footnote n 37) para 41.

45 Footnote Ibid., para 42.

46 CBD, Cooperative Procedures and Institutional Mechanisms to Promote Compliance with the Nagoya Protocol and to Address Cases of Non-Compliance, Decision NP-1/4, UNEP/CBD/NP/COP-MOP/DEC/1/4, 20 October 2014, Section F(2)(a).

47 CBD, Establishment of Procedures and Mechanisms on Compliance under the Cartagena Protocol on Biosafety, Decision BS-1/7, 2004, Section VI(1)(a).

48 IMO, Revised 2017 Compliance Procedures and Mechanisms Pursuant to Article 11 of the 1996 Protocol to the London Convention 1972, Doc LC 39/16/Add.1, 2017, Section 5.1.1.

49 Other examples include the Facilitative Branch of the Kyoto Protocol, which provides advice to the Parties.

50 UNECE, Annex: Consultation Process of the Compliance Committee under the Protocol on Water and Health, as amended by the Committee at its tenth meeting, UN Doc ECE/MP.WH/C.1/2014/2, 17 December 2014, para 1.

51 UNECE, Decision 1/7: Review of Compliance, MoP of the Aarhus Convention, UN Doc ECE/MP.PP/2/Add.8, 2 April 2004.

52 See the procedure proposed by the MoP: UNECE, Report of the Fifth Session of the MoP, UN Doc ECE/MP.PP/2014/2, 11 October 2014, para 53.

53 UNECE, Recommendations with Regard to Request for Advice ACCC/A/2014/1 by Belarus, Compliance Committee of the Aarhus Convention, UN Doc ECE/MP.PP/C.1/2017/11, 18 June 2017, para 3.

54 UNECE, Recommendations with Regard to Request for Advice ACCC/A/2020/2 by Kazakhstan, Compliance Committee of the Aarhus Convention, UN Doc. ECE/MP.PP/C.1/2021/6, 1 July 2020, para 14.

55 UNECE, Request for Advice by Ukraine ACCC/A/2022/3, Letter of the Secretary of the CC of 21 July 2022.

56 UNECE (Footnote n 37) para 18.

57 This feature is also present in the advisory procedure/consultative process of the Protocol on Water and Health and the Facilitative Branch of the Kyoto Protocol.

58 UNECE (Footnote n 37) para 22.

59 Footnote Ibid., para 19–20.

60 Ghana acceded to the Water Convention on 22 June 2020.

61 UNECE (Footnote n 37) para 23.

62 Footnote Ibid., paras 28 and 29.

63 Footnote Ibid., para 31.

64 UNECE, Report of the Preparatory Meeting for the Eleventh Meeting of the Implementation Committee, UN Doc. ECE/MP.WAT/IC/2020/2, 13 October 2020, para 6.

65 UNECE, Report of the Implementation Committee on Its Tenth Meeting, UN Doc ECE/MP.WAT/IC/2019/2, 27 May 2020, paras 7–8.

66 UNECE (Footnote n 65) para 7.

67 UNECE, EIA/IC/S/7 Albania, Submission by Montenegro to the Implementation Committee of the Espoo Convention, 11 September 2019.

68 UNECE, EIA/IC/S/7 Albania, Response from Albania, 30 December 2019.

69 UNECE (Footnote n 66) para 7 to 10.

70 UNECE (Footnote n 65) para 11.

71 See UNECE, Report of the Implementation Committee on its Twelfth Meeting, UN Doc ECE/MP.WAT/IC/2021/1, 18 March 2021, para 7.

72 Adopted by the riparian states Albania, Greece, Montenegro, North Macedonia and Kosovo.

73 UNECE (Footnote n 72) paras 11–14.

74 For the summary of the legal and technical advice provided by the Committee, see UNECE, Annex to the Report of the Implementation Committee on its Twelfth Meeting, UN Doc ECE/MP.WAT/IC/2021/1, 18 March 2021.

75 UNECE (Footnote n 75) 6.

76 Footnote Ibid., 6–8.

77 See UNECE, Report of the Implementation Committee on Its Thirteenth Meeting, UN Doc ECE/MP.WAT/IC/2021/3, 21 July 2021, para 7.

78 UNECE, The Gambia, Guinea Bissau, Mauritania and Senegal Commit to Cooperate on Shared Groundwater as Foundation for Regional Stability, Sustainable Development and Climate Adaptation, Press Release, 29 September 2021.

79 Currently under deliberation. ICJ, ‘Dispute over the Status and Use of the Waters of the Silala (Chile v. Bolivia) – Conclusion of the Public Hearing’, Press Release 2022/13, 14 April 2022.

80 For some considerations on conciliation and NCMs, see M Fitzmaurice, ‘The Potential of Inter-State Conciliation within the Framework of Environmental Treaties’ in C Tomuschat and M Kohen, Flexibility in International Dispute Settlement: Conciliation Revisited (Brill Nijhoff 2020) 95110.

81 Judges Lapradelle and Negulesco coined the term: ‘The procedure which allows States to apply to the Court through the Council for an opinion constitutes a new dispute settlement mechanism. This mechanism differs from the opinion properly provided for in Article 14 of the Covenant, in that it is similar to arbitration, but has certain features peculiar to it. It could be called advisory arbitration.’ MA Lapradelle and D Negulesco, ‘Rapport sur la nature Juridique des Avis Consultatifs de la Cour Permanente de Justice Internationale - leur valeur et leur portée positive en droit International’ (1928) 34 Annuaire Institut de Droit International 453.

82 See T Treves, ‘The Settlement of Disputes and Non-Compliance Procedures’ in T Treves, L Pineschi, A Tanzi et al. (eds), Non–Compliance Procedures (Footnote n 5) 505–11.

83 UNECE (Footnote n 13) para 45.

84 UNECE (Footnote n 75) 6.

85 For a punctual discussion on the interlinkage between NCMs and dispute settlement, see P Sands, ‘Non-Compliance and Dispute Settlement’ in R Wolfrum, P-T Stoll and U Beyerlin (eds) Ensuring Compliance with Multilateral Environmental Agreements: A Dialogue between Practitioners and Academia (Brill 2006) 356–58; T Treves, ‘The Settlement of Disputes and Non-Compliance Procedures’ in T Treves, L Pineschi, A Tanzi, et al. (eds), Non–Compliance Procedures (Footnote n 5) 505–11.

86 See the replies of the IC to questions received from Latin American countries: UNECE, Annex to the Report of the Implementation Committee on its Fourteenth Meeting, UN Doc ECE/MP.WAT/IC/2022/2, 24 May 2022, 7.

87 Ahmadou Sadio Diallo (Republic of Guinea v Democratic Republic of the Congo), Merits, Judgment, ICJ Reports 2010, 639, para 66.

88 Only possible at the African Court of Human and People’s Rights. Protocol to the African Charter on Human and People’s Rights on the Establishment of an African Court on Human and People’s Rights, 10 June 1998, Article 4(1).

89 See Delimitation of the Maritime Boundary in the Indian Ocean (Mauritius/Maldives), Preliminary Objections, Judgment, ITLOS Reports 2020–2021, 17, paras 203–5.

90 See F Romanin Jacur, ‘Triggering Non-Compliance Procedures’ in T Treves, L Pineschi, A Tanzi, et al. (eds), Non–Compliance Procedures (Footnote n 5) 375–77.

91 T Buergenthal, ‘The Inter-American Court of Human Rights’ (1982) 76(2) The American Journal of International Law 245. See also Interpretation of Peace Treaties, Advisory Opinion, ICJ Reports (1950) 65, para 71.

92 UNECE, Report of the Implementation Committee to the MoP and Draft Decision on General Issues of Implementation, UN Doc ECE/MP.WAT/2021/5, 6 July 2021, paras 13–31.

93 UNECE (Footnote n 51) para 1.

94 Footnote Ibid., para 4.

95 Footnote Ibid., para 5.

96 International legally binding instrument under the United Nations Convention on the Law of the Sea on the Conservation and Sustainable Use of Marine Biological Diversity of Areas Beyond National Jurisdiction, UNGA Res 72/249, 24 December 2017, UN Doc A/RES/72/249.

97 UN, Revised Draft Text of an Agreement under the United Nations Convention on the Law of the Sea on the Conservation and Sustainable Use of Marine Biological Diversity of Areas Beyond National Jurisdiction, UN Doc A/CONF.232/2022/5, Articles 53 and 53 ter.

98 Footnote Ibid., Article 55 ter.

99 UNEA, End Plastic Pollution: Towards an International Legally Binding Instrument, UNEP/EA.5/L.23/Rev.1, 2 March 2022, Operative 1 and 3.

100 UNEA (n 100) para 3(p); UNEP, Note by the Secretariat, UNEP/PP/INC.1/5, 14 October 2022, para 22.

101 UNEP-IISD, ‘Marine Litter and Plastic Pollution Bulletin’, Earth Negotiations Bulletin, September 2021, 4; Ministerial Calls for Global Agreement on Marine Litter, Plastic Pollution, International Institute for Sustainable Development, 7 September 2021.

102 WHO, The World Together: Establishment of an Intergovernmental Negotiating Body to Strengthen Pandemic Prevention, Preparedness and Response, World Health Assembly, Second Special Session, Doc SSA2(5), 1 December 2021.

103 H Nikogosian, A Guide to a Pandemic Treaty: Things You Must Know to Help You Make a Decision on a Pandemic Treaty (The Graduate Institute of International and Development Studies – Global Health Centre 2021) 23–24; See Chapter 2, this volume.

6 State-to-State Procedures before Environmental Compliance Committees: Still Alive?

1 The difference between implementation and compliance is defined clearly by C Voigt, ‘The Compliance and Implementation Mechanism of the Paris Agreement’ (2016) 25(2) Review of European Community and International Environmental Law 161–73, 166.

2 While ‘trigger’ is the most common term used in literature, States have also used ‘referral’ and ‘initiation’ in negotiations. See S Oberthür and E Northrop, ‘Towards an Effective Mechanism to Facilitate Implementation and Promote Compliance under the Paris Agreement’ (2018) 8(1–2) Climate Law 3969, 53, fn 44; Ad-hoc Working Group on the Paris Agreement, Third Part of the First Session, Bonn, 8–18 May 2017, Agenda Item 7: Modalities and Procedures for the Effective Operation of the Committee to Facilitate Implementation and Promote Compliance Referred to in Article 15.2 of the Paris Agreement, Informal Note by the Co-Facilitators, Final Version, available at https://unfccc.int/files/meetings/bonn_may_2017/application/pdf/apa_item7_informalnote_provisional_17may2017@1100_final.pdf.

3 For an overview of existing triggers, see J Bendel, Litigating the Environment: Process, and Procedure before International Courts and Tribunals (Edward Elgar 2023) 218–22.

4 N Goeteyn and F Maes, ‘Compliance Mechanisms in Multilateral Environmental Agreements: An Effective Way to Improve Compliance?’ (2011) 10 Chinese Journal of International Law 36.

5 Monitoring the Implementation of and Compliance with the Obligations set out by the Basel Convention, comment submitted by Australia, UNEP/CHW/LWG/2/3/Add.1, 2000.

6 A Shibata, ‘The Basel Compliance Mechanism’ (2003) 12(2) Review of European, Comparative & International Environmental Law 183–98, 184, citing Draft Decision for the Sixth Meeting of the Conference of the Parties Establishing a Mechanism for the Basel Convention, Rome, 15–17 October 2001, available at www.basel.int/meetings/LWG/index.html.

7 UNEP, Conference of the Parties to the Basel Convention on the Control of Transboundary Movements of Hazardous Wastes and Their Disposal, Geneva, 9–12 December 2002, Report of the Conference of the Parties to the Basel Convention on the Control of Transboundary Movements of Hazardous Wastes and Their Disposal, UNEP/CHW.6/40, para 57, available at www.basel.int/TheConvention/ConferenceoftheParties/Meetings/COP6/tabid/6149/Default.aspx.

8 Footnote Ibid., para 65.

9 Rotterdam Convention on the Prior Informed Consent Procedure for Certain Hazardous Chemicals and Pesticides in International Trade, signed 10 September 1998, entered into force 24 February 2004, 2244 UNTS 337, para 12(b). S Bugnatelli, ‘The 1998 Rotterdam Convention on the Prior Informed Consent Procedure’ in T Treves, L Pineschi, A Tanzi et al. (eds), Non-Compliance Procedures and Mechanisms and the Effectiveness of International Environmental Agreements (TMC Asser Press 2009) 93; L Crema, ‘The 2001 International Treaty on Plant and Genetic Resources’ in Treves et al. (eds.), Non-Compliance Procedures (Footnote n 9) 147.

10 Participant 2, question 1.

11 Participant 1, question 2: ‘We insisted that this shouldn’t be an ATM machine, where you say “I have problems, give me money” – it should add value in the context of the whole Paris Agreement’; ‘Listen, when you go back home, you will have journalists, academia and students asking you this one question: “What happens if a state doesn’t comply?” If we don’t have this body, your answer will be extremely complicated! But with Article 15 of the Paris Agreement establishing a compliance committee, you will have a straight-forward answer.’

12 The committee trigger was successfully included after difficult negotiations in Katowice. Participant 1, question 1: ‘The options were secretariat: that didn’t work either; the Committee itself, which is what it is there in the text. And other triggers were not even considered, like NGOs. That was completely unacceptable for many.’ Informal note, May 2017, 4: ‘Other referrals would risk the Committee becoming politicized, adversarial, intrusive and redundant.’

13 Participant 3 questions 3 and 4.

14 Participant 3, question 1; participant 2, questions 2 and 3.

15 Participant 2, question 2.

16 D Bodansky, J Brunnée and L Rajamani, International Climate Change Law (Oxford University Press 2017) 68 ‘ … One might add that this “softer touch” on compliance has also been easier to sell to states than a harder-edged approach would have been.’; M Doelle, ‘In Defence of the Paris Agreement’s Compliance System: The Case for Facilitative Compliance’ in B Mayer and A Zahar (eds), Debating Climate Law (Cambridge University Press 2021) 8698; J von Stein, ‘The International Law and Politics of Climate Change: Ratification of the United Nations Framework Convention and the Kyoto Protocol’ (2008) 52(2) Journal of Conflict Resolution 243–44.

17 J Klabbers, ‘Compliance Procedures’ in D Bodansky, J Brunnée and E Hey (eds), The Oxford Handbook of International Environmental Law (Oxford University Press 2007) 1004; A Chayes and AH Chayes, The New Sovereignty: Compliance with International Regulatory Agreements (Harvard University Press 1995).

18 Aarhus Convention’s Compliance Committee, ‘Findings and Recommendations with Regard to Compliance by Ukraine with the Obligations under the Aarhus Convention in the Case of Bystre Deep-water Navigation Canal Construction’, Doc ECE/MP.PP/C.1/2005/2/Add.3, 18 February 2005 (14 March 2005), available at https://unece.org/DAM/env/documents/2005/pp/c.1/ece.mp.pp.c1.2005.2.Add.3.e.pdf.

19 Ministry of Environment of Lithuania, ‘Submission to the Compliance Committee by the Republic of Lithuania Requesting to Investigate the Compliance of the Republic of Belarus’, 25 March 2015, available at https://unece.org/DAM/env/pp/compliance/S2015-02_Belarus/Submission/Submission_by_Lithuania_concerning_Belarus_27.03.2015.pdf.

20 All submissions can be found at https://unece.org/submissions-overview.

21 Submission by South Africa, CC-2006-1-1/FB, available at https://unfccc.int/files/kyoto_mechanisms/compliance/application/pdf/cc-2006-1-1-fb.pdf.

22 OHCHR, ‘Inter-State Communications: Committee on the Elimination of Racial Discrimination’, available at www.ohchr.org/en/treaty-bodies/cerd/inter-state-communications.

23 See Article 33(1) UN Charter.

24 See, for example, Article 20 of the Basel Convention. In another instance, the ICJ declared the Georgia v Russia dispute inadmissible as Georgia had made no attempt at negotiations prior to Case Concerning Application of the International Convention on the Elimination of All Forms of Racial Discrimination (Georgia v Russian Federation), Preliminary Objections, Judgment, 1 April 2011, para 182.

25 For example, in Obligation to Negotiate Access to the Pacific Ocean (Bolivia v Chile), Judgment, ICJ Reports 2018, 507.

26 On 30 April 2021, the CERD declared Palestine’s submission admissible. See ‘Inter-State Communication Submitted by the State of Palestine against Israel: Decision on Admissibility’, CERD/C/103/4, available at https://documents-dds-ny.un.org/doc/UNDOC/GEN/G21/150/90/PDF/G2115090.pdf?OpenElement.

27 Application of the International Convention on the Elimination of All Forms of Racial Discrimination (Qatar v United Arab Emirates), Preliminary Objections, ICJ Reports 2021.

28 ‘Submission by Montenegro having concerns about the Compliance of the Republic of Albania with Its Obligations under the Convention on Environmental Impact Assessment in a Transboundary Context: Espoo and the Protocol on Strategic Environmental Assessment (SEA) in Respect of the Activity of the Construction of the Small Hydropower Plants on the Cijevna River’, 11 September 2019 (submission was received by the secretariat on 25 September 2019), available at https://unece.org/DAM/env/documents/2019/ece/IC/Submission/Albania/Submission_to_the_Implementation_Committee__Espoo_11._IX_2019.pdf.

29 Voigt (Footnote n 1) 162.

30 Participant 1, question 1.

31 State-to-State triggers are by default closed to the public: see Section 6.4.3. See also F Romanin Jacur, ‘Triggering Non-Compliance Procedures’ in Treves et al. (eds), Non-Compliance Procedures (Footnote n 9) 374.

32 Participant 3, question 1; Participant 1, question 3; Participant 2, question 3; Informal note May 2017 (Footnote n 2) 4; Draft Elements for APA Agenda Item 7: Modalities and Procedures for the Effective Operation of the Committee to Facilitate Implementation and Promote Compliance Referred to in Article 15.2 of the Paris Agreement, Informal note by the Co-facilitators, Final Version, 13 November 2017, 7.

33 Notable exceptions include cases brought before the ICJ regarding the Genocide Convention, the CERD and the Whaling Convention.

34 See, for example, Basel Convention Article 20; Rotterdam Convention Article 20; Stockholm Convention on Persistent Organic Pollutants, signed 22 May 2001, entered into force 17 May 2004, 2256 UNTS 119, Article 18.

35 See, for example, Cartagena Protocol on Biosafety to the Convention on Biological Diversity, signed 29 January 2000, entered into force 11 September 2003, 2226 UNTS 208, Article 34.

36 U Beyerlin, P-T Stoll and R Wolfrum, ‘Conclusions Drawn from the Conference on Ensuring Compliance with MEAs’ in U Beyerlin, P-T Stoll and R Wolfrum (eds), Ensuring Compliance with Multilateral Environmental Agreements: A Dialogue between Practitioners and Academia (Brill 2006) 369.

37 Goeteyn and Maes (Footnote n 4) 37–38, para 43.

38 Application of the Convention on the Prevention and Punishment of the Crime of Genocide (The Gambia v Myanmar), Provisional Measures, Order of 23 January 2020, ICJ Reports 2020, 10, para 20; Application of the International Convention for the Suppression of the Financing of Terrorism and of the International Convention on the Elimination of All Forms of Racial Discrimination (Ukraine v Russian Federation), Provisional Measures, Order of 19 April 2017, ICJ Reports 2017, 115, para 22; Interpretation of Peace Treaties with Bulgaria, Hungary and Romania, First Phase, Advisory Opinion, ICJ Reports 1950, 74.

39 Application (The Gambia v Myanmar) (Footnote n 37); South West Africa (Ethiopia v South Africa; Liberia v South Africa), Preliminary Objections, Judgment, ICJ Reports 1962, 328.

40 United Nations Environmental Programme (UNEP), Compliance Mechanism under Selected Multilateral Environmental Agreements, available at https://wedocs.unep.org/bitstream/handle/20.500.11822/7507/-Compliance%20Mechanisms%20under%20selected%20Multilateral%20Environmental%20Agreements-2007761.pdf?sequence=3&amp%3BisAllowed=, 119.

41 A Fodella, ‘Structural and Institutional Aspects of Non-Compliance Mechanisms’ in Treves et al. (eds), Non-Compliance Procedures (Footnote n 9) 366; Romanin Jacur (Footnote n 31) 376; L Pineschi, ‘Non-Compliance Procedures and the Law of State Responsibility’, in Treves et al. (eds), Non-Compliance Procedures (Footnote n 9) 494; T Treves, ‘The Settlement of Disputes and Non-Compliance Procedures’, in Treves et al. (eds), Non-Compliance Procedures (Footnote n 9) 513–14.

42 Application (The Gambia v Myanmar) (Footnote n 38) paras 41–42.

43 J Rudall, Altruism in International Law (Cambridge University Press 2021).

44 U Fastenrath, D-E Khan, R Geiger, A Paulus and S von Schorlemer (eds), From Bilateralism to Community Interest: Essays in Honour of Bruno Simma (Oxford University Press 2011).

45 Goeteyn and Maes (Footnote n 4) 33.

46 Article 2(1)(b) Kyoto Protocol to the United Nations Framework Convention on Climate Change, signed 11 December 1997, entered into force 16 February 2005, 2303 UNTS 162. See also Article 18.

48 Cartagena Protocol, available at https://bch.cbd.int/protocol/cpb_art34_cc.shtml; Rotterdam Convention, Article 12(b) (emphasis added).

49 A Fodella, ‘Mechanism for Promoting Implementation and Compliance with the 1989 Basel Convention on the Transboundary Movements of Hazardous Wastes and their Disposal’ in Treves et al. (eds), Non-Compliance Procedures (Footnote n 9) 40; A Shibata, ‘Ensuring Compliance with the Basel Convention: Its Unique Features’ in Beyerlin et al. (eds), Conclusions (Footnote n 36) 81.

50 VI.1(b) Kyoto Protocol; Montreal Protocol; LRTAP; Kyoto Protocol; Aarhus Convention; Espoo Convention; Water Protocol para 12(b); Rotterdam Convention.

51 For example, in Armed Activities on the Territory of the Congo (Democratic Republic of the Congo v Uganda); Application of the Convention on the Prevention and Punishment of the Crime of Genocide (Bosnia and Herzegovina v Serbia and Montenegro).

52 Application (The Gambia v Myanmar) (Footnote n 38) paras 71–72.

53 For example, Aarhus Convention Decision Romania v Ukraine, available at https://unece.org/DAM/env/documents/2005/pp/c.1/ece.mp.pp.c1.2005.2.Add.3.e.pdf; Aarhus Convention Decision Lithuania v Belarus, available at https://unece.org/env/pp/cc/accc.s.2015.2_belarus.

54 S Oberthür and R Lefeber, ‘Holding Countries to Account: The Kyoto Protocol’s Compliance System Revisited after Four Years of Experience’ (2010) 1 Climate Law 138–39; Report of the Compliance Committee on the Deliberations in the Facilitative Branch Relating to the Submission, FCCC/KP/CMP/2006/6, 22 September 2006, available at http://unfccc.int/kyotoprotocol/compliance/plenary/items/3788.php.

55 Sixth Meeting of the Conference of Parties to the Basel Convention, Decision VI/12, Terms of Reference, UNEP/CHW.6/40, para 5. Available at www.basel.int/Portals/4/Basel%20Convention/docs/meetings/cop/cop6/english/Report40e.pdf#page=45.

56 ‘ … members with recognized competence in relevant scientific, technical, socioeconomic or legal fields’. Decision 20/CMA.1, FCCC/PA/CMA/2018/3/Add.2, para 5. Available at https://unfccc.int/sites/default/files/resource/cma2018_3_add2_new_advance.pdf.

57 MM Mbengue, ‘International Courts and Tribunals as Fact-Finders: The Case of Scientific Fact-Finding in International Adjudication’ (2011) 34 Loyola of Los Angeles International and Comparative Law Review 53.

58 K Sulyok, Science and Judicial Reasoning: The Legitimacy of International Environmental Adjudication (Cambridge University Press 2021); C Foster, Science and the Precautionary Principle in International Courts and Tribunals (Cambridge University Press 2011).

59 F Romanin Jacur, ‘The Non-Compliance Procedure of the 1987 Montreal Protocol to the 1985 Vienna Convention on Substances That Deplete the Ozone Layer’ in Treves et al. (eds), Non-Compliance Procedures (Footnote n 9) 17.

60 OHCHR (Footnote n 22); OHCHR, ‘Committee on the Elimination of Racial Discrimination Concludes its Ninety-Eighth Session’ (10 May 2019), available at www.ohchr.org/EN/NewsEvents/Pages/DisplayNews.aspx?NewsID=24601&LangID=E.

61 R Mackenzie and P Sands, ‘International Courts and Tribunals and the Independence of the International Judge’ (2003) 44 Harvard International Law Journal 271; D Shelton, ‘Form, Function, and the Powers of International Courts’ (2009) 9 Chinese Journal of International Law 537, 545.

62 A few examples can be found in the Cartagena Protocol (2000), the Aarhus Convention (1998), the Paris Agreement (2015) and the Rotterdam Convention (1998).

63 Decision 24/CMA.3, Annex, ‘Rules of Procedure of the Committee to Facilitate Implementation and Promote Compliance Referred to in Article 15, paragraph 2, of the Paris Agreement’, FCCC/PA/CMA/2021/10/Add.3, Rule 3.3, para 1.

64 Footnote Ibid., para 3.

66 Montreal Protocol MOP Decision X/10, Annex II: ‘Non-Compliance Procedure (1998): Tenth Meeting of the Parties’; CITES Resolution Conf 18.2 Establishment of Committees, available at https://cites.org/sites/default/files/document/E-Res-18-02.pdf.

67 Participant 2, question 4.

68 See for example, the Stockholm Convention, Terms of Reference para 16.

69 Fodella (Footnote n 49) 40.

71 Articles 62 and 63 ICJ Statute.

72 Rules of the Court, 14 April 1978, entered into force 1 July 1978, Article 53(2).

73 Unless the Court or both parties decide otherwise. See Article 46, ICJ Statute; Article 59, Rules of the Court.

74 They are streamed on UN Web TV, available at http://webtv.un.org/.

75 Rule 67(2) ITLOS Rules of Procedure.

76 S Charnovitz, ‘Transparency and Participation in the World Trade Organization’ (2004) 56 Rutgers Law Review 927; G Villalta Puig and B Al-Haddab, ‘The Transparency Deficit of Dispute Settlement in the World Trade Organization’ (2011) 8 Manchester Journal International Economic Law 2; G Marceau and M Hurley, ‘Transparency and Public Participation: A Report Card on WTO Transparency Mechanisms’ (2012) IV(1) Trade, Law and Development; L Wallach, ‘Transparency in WTO Dispute Resolution’ (1999-2000) 31 Law & Policy International Business 773; see also A Bianchi and A Peters (eds), Transparency in International Law (Cambridge University Press 2013) 4.

77 G Handl, ‘Compliance Control Mechanisms and International Environmental Obligations’ (1997) 5 Tulane Journal of International and Comparative Law 2949, 42–43.

78 Romanin Jacur (Footnote n 59) 21.

79 Beyerlin, Stoll and Wolfrum (Footnote n 36) 369.

80 This separation exists for instance in the Basel Convention (1989), the Cartagena Protocol (2000), CITES (1973) and the Nagoya Protocol (2010). For a detailed list, see the overview provided by the Compliance Committee under the Cartagena Protocol on Biosafety, UNEP/CBD/BS/CC/13/INF/2, Annex I, 22 January 2016, 29–35.

81 ‘Findings and Recommendations with Regard to Submission ACCC/S/2015/2 Concerning Compliance by Belarus’, para 161. Available at https://unece.org/sites/default/files/2021-07/S2_Belarus_findings_advance_unedited.pdf.

82 Footnote Ibid., para 162.

83 See for instance, M Fitzmaurice and C Redgwell, ‘Environmental Non-Compliance Procedures and International Law’ (2000) 31 Netherlands Yearbook of International Law 5262; M Koskenniemi, ‘Breach of Treaty or Non-Compliance? Reflections on the Enforcement of the Montreal Protocol’ (1992) 3(1) Yearbook of International Environmental Law 123–62.

84 F Zarbiyev, ‘Saying Credibly What the Law Is: On Marks of Authority in International Law’ (2018) 9(2) Journal of International Dispute Settlement 291314; AV Huneeus, ‘Compliance with International Court Judgments and Decisions’ in KJ Alter, C Romano and Y Shany (eds), Oxford Handbook of International Adjudication (2013) 437–63.

85 For example, Obligations of States in respect of climate change (Request for an Advisory Opinion), ICJ, Order of 20 April 2023; Request for an Advisory Opinion submitted by the Commission of Small Island States on Climate Change and International Law (Request for Advisory Opinion submitted to the Tribunal), ITLOS, 12 December 2022; Certain Activities varied out by Nicaragua in the Border Area (Costa Rica v Nicaragua), Compensation, Judgment, ICJ Reports 2018, 15; Dispute Concerning Delimitation of the Maritime Boundary between Ghana and Côte d’Ivoire in the Atlantic Ocean (Ghana/Côte d’Ivoire), Provisional Measures, Order of 25 April 2015, ITLOS Reports 2015, 146 (on the marine environment).

86 Goeteyn and Maes (Footnote n 4) 36.

87 Klabbers (Footnote n 16) 1001. See more generally, M Bowman and A Boyle (eds), Environmental Damage in International and Comparative Law: Problems of Definition and Valuation (Oxford University Press 2002).

88 Klabbers (Footnote n 17) 1005.

89 P Sands, ‘Non-Compliance and Dispute Settlement’ in U Beyerlin, P-T Stoll and R Wolfrum (eds), Ensuring Compliance with Multilateral Environmental Agreements: A Dialogue between Practitioners and Academia (Brill 2006) 353–58.

7 Compliance with Science-Based Treaties

1 See, e.g., Convention on International Trade in Endangered Species of Wild Fauna and Flora, signed 3 March 1973, entered into force 1 July 1975, 1453 UNTS 243 (CITES); Convention on Biological Diversity, signed 5 June 1992, 1760 UNTS 79; Cartagena Protocol on Biosafety to the Convention on Biological Diversity, signed 29 January 2000, entered into force 11 September 2003, 2226 UNTS 208; United Nations Framework Convention on Climate Change 1992, signed 9 May 1992, entered into force 21 March 1994, 1771 UNTS 107; Kyoto Protocol to the United Nations Framework Convention on Climate Change, signed 11 December 1997, entered into force 16 February 2005, 2303 UNTS 162.

2 Y Lador, ‘Access to Justice and Public Participation in the Water Sector: A Promising Legal Development’ in M Tignino and K Sangbana (eds), Public Participation and Water Resources Management: Where Do We Stand in International Law? International Conference, Geneva 13 December 2013 Proceedings (UNESCO 2015) 147–53, 150.

3 These include the Scientific Committee of the International Whaling Commission (IWC) and the Commission on Conservation of Southern Bluefin Tuna (CCSBT). See Section 7.3.

4 Whaling in the Antarctic (Australia v Japan: New Zealand intervening), Judgment [2014] ICJ Reports 226.

5 Whaling in the Antarctic (Australia v Japan: New Zealand intervening), Judgment, Dissenting Opinion of Judge Bennouna [2014] ICJ Reports 341, 346.

6 Delimitation of the Maritime Boundary in the Bay of Bengal (Bangladesh/Myanmar), Judgment [2012] ITLOS Reports 4, 107.

7 Question of the Delimitation of the Continental Shelf between Nicaragua and Colombia beyond 200 Nautical Miles from the Nicaraguan Coast (Nicaragua v Colombia), Preliminary Objections, Judgment [2016] ICJ Reports 100, 137.

8 Chagos Marine Protected Area Arbitration (Mauritius v United Kingdom), Hearing Transcript Day 11, available at pcacases.com/web/sendAttach/1581 (accessed 22 November 2022) 1344.

9 Scientific aspects would include those issues that involve diverging views on science and may require specialised scientific knowledge for their resolution.

10 See, e.g., T Stephens, International Courts and Environment Protection (Cambridge University Press 2009) 8189; T Treves, L Pineschi, A Tanzi et al. (eds), Non-Compliance Procedures and Mechanisms and the Effectiveness of International Environmental Agreements (TMC Asser Press 2009); M Fitzmaurice and P Merkouris, ‘Environmental Compliance Mechanisms’ (Oxford Bibliographies Online, 2021) http://doi.org/10.1093/obo/9780199796953-0010.

11 Convention on Access to Information, Public Participation in Decision-Making and Access to Justice in Environmental Matters, signed 25 June 1998, entered into force 29 October 2001, 2161 UNTS 447.

12 Kyoto Protocol to the United Nations Framework Convention on Climate Change.

13 Protocol on Pollutant Release and Transfer Registers to the Convention on Access to Information, Public Participation in Decision-Making and Access to Justice in Environmental Matters, signed 21 May 2003, entered into force 8 October 2009, 2626 UNTS 119.

14 Protocol on Water and Health to the 1992 Convention on the Protection and Use of Transboundary Watercourses and International Lakes, 17 June 1999, entered into force 4 August 2005, 2331 UNTS 202.

15 Standing Committee on Implementation and Compliance, established by the Commission for the Conservation of Antarctic Marine Living Resources (CCAMLR) with terms of reference available at www.ccamlr.org/en/system/files/e-pt8_0.pdf (accessed 11 November 2022). The CCAMLR was established under Article VII, Convention for the Conservation of Antarctic Marine Living Resources, signed 20 May 1980, entered into force 7 April 1982, 1329 UNTS 47.

16 Implementation and Compliance Committee, established by the Conference of Parties under Article 15, Basel Convention on the Control of Transboundary Movements of Hazardous Wastes and Their Disposal, signed 22 March 1989, entered into force 5 May 1992, 1673 UNTS 57.

17 Paris Agreement, signed 12 December 2015, entered into force 4 November 2016, UNTS 3156, UN Doc FCCC/CP/2015/L.9/Rev/1.

18 Compliance Committee, established under Article 21 of the International Treaty on Plant Genetic Resources for Food and Agriculture, signed 3 November 2001, entered into force 29 June 2004, 2400 UNTS 303.

19 UNECE, ‘Guidance Document on the Aarhus Convention Compliance Mechanism’, 2, available at www.unece.org/fileadmin/DAM/env/pp/compliance/CC_GuidanceDocument.pdf (accessed 2 October 2021).

20 See, e.g., referring to dispute resolution by the ICJ: Convention on Biological Diversity, Art 27(3)(b); United Nations Framework Convention on Climate Change, Article 14(2)(a); UNECE Convention on Environmental Impact Assessment in a Transboundary Context, signed 25 February 1991, entered into force 10 September 1997, 1989 UNTS 309, Article 15(2); Protocol on Further Reduction of Sulphur Emissions to the 1979 Convention on Long-Range Transboundary Air Pollution, Article 9.

21 For the issue of State-to-State triggers, see Chapter 6.

22 Montreal Protocol on Substances That Deplete the Ozone Layer, signed 16 September 1987, entered into force 1 January 1989, 1522 UNTS 3, Article 8.

23 Decision IV/5, Report of the Fourth Meeting of the Parties to the Montreal Protocol on Substances That Deplete the Ozone Layer, UN Doc UNEP/Oz.L.Pro.4/15 (1992) (as revised by Decision X/10, Report of the Tenth Meeting of the Parties to the Montreal Protocol on Substances That Deplete the Ozone Layer, UN Doc UNEP/OzL.Pro.10/9 (1998)).

24 See UNFCCC, ‘An Introduction to the Kyoto Protocol Compliance Mechanism’, available at http://unfccc.int/process/the-kyoto-protocol/compliance-under-the-kyoto-protocol/introduction (accessed 15 April 2022). See also Chapter 3. The course of action depends on the nature of non-compliance and could take the form of making up the difference in emissions exceeding the assigned amount, or suspension of eligibility to make transfers under emissions trading.

25 Regional Agreement on Access to Information, Public Participation and Justice in Environmental Matters in Latin America and the Caribbean, 4 March 2018, Article 18.

26 Rules Relating to the Structure and Functions of the Committee to Support Implementation and Compliance of the Regional Agreement on Access to Information, Public Participation and Justice in Environmental Matters in Latin America and the Caribbean, Annex 1 of Decision I/3, First Meeting of Conference of Parties.

27 Footnote Ibid., Rule V(1).

28 Decision Adopted by the Second Conference of the Parties to the Minamata Convention on Mercury, Second Meeting, Geneva, 19–23 November 2018, UNEP/MC/COP.2/Dec.4.

29 Decision II/4 of the Second Meeting of the Parties, revised as Decision III/2.

30 Structure and Functions of the Implementation Committee and Procedures for Review of Compliance, Decision III/2, Appendix (ECE/MP.EIA/6) as Amended by Decision VI/2 (ECE/MP.EIA/20/Add.1− ECE/MP.EIA/SEA/4/ Add.1), Article 14, available at http://unece.org/DAM/env/eia/documents/ImplementationCommittee/2014_Structure_and_functions/Implementation_Committee_structure_functions_procedures_rules.e_2014.pdf (accessed 6 February 2022).

31 Decision 24-/CMA.4, Rules of Procedure of the Committee to Facilitate Implementation and Promote Compliance Referred to in Article 15, paragraph 2, of the Paris Agreement, UN Doc FCCC/PA/CMA/2022/L.1.

32 Decision 20/CMA.1, available at http://unfccc.int/process-and-meetings/bodies/constituted-bodies/committee-to-facilitate-implementation-and-promote-compliance-referred-to-in-article-15-paragraph-2 (accessed 15 April 2022). See also, ‘Report of the Conference of the Parties Serving as the Meeting of the Parties to the Paris Agreement on the Third Part of Its First Session, Katowice 2–15 December 2018, UN Doc FCCC/PA/CMA/2018/3/Add.2 (19 March 2019).

33 M Tignino, ‘Quasi-Judicial Bodies’ in CM Brölmann and Y Radi (eds), Research Handbook on the Theory and Practice of International Law-Making (Edward Elgar 2016) 242–61.

34 See V Roben, ‘Institutional Developments under Modern International Environmental Agreements’ in JA Frowein and R Wolfrum (eds), Max Planck Yearbook of United Nations Law (Kluwer Law International 2000) 363443; G Samvel, ‘Non-Judicial, Advisory, Yet Impactful? The Aarhus Convention Compliance Committee as a Gateway to Environmental Justice’ (2020) 9 Transnational Environmental Law 211–38; C Zengerling, Greening International Jurisprudence: Environmental NGOs before International Courts, Tribunals, and Compliance Committees (Brill 2013) 1, 4, 9–10.

35 As opposed to a serious, significant, or material breach; or in other words, a breach that can be remedied without much difficulty. A minor breach by its nature would not be the subject of much disagreement that may otherwise necessitate recourse to ICTs.

36 For example, special permit whaling, in compliance with Article VIII of the Whaling Convention, is regularly reviewed by the Scientific Committee established under the International Whaling Commission. See e.g., Scientific Committee, ‘Report, Annex P: Process for the Review of Special Permit Proposals and Research Results from Existing and Completed Permits’ (2015) 16(Suppl) Journal of Cetacean Resource Management, 349.

37 International Whaling Commission, Infractions Sub-Committee, available at http://iwc.int/index.php?cID=html_513 (accessed 15 April 2022).

38 See S Suarez, The Outer Limits of the Continental Shelf: Legal Aspects of Their Establishment (Springer 2008) 122.

39 Commission on the Limits of the Continental Shelf (CLCS): Purpose, Functions and Sessions, available at www.un.org/depts/los/clcs_new/commission_purpose.htm (accessed 15 April 2022).

40 See Commission for the Conservation of Southern Bluefin Tuna, available at www.ccsbt.org/ (accessed 15 April 2022).

41 See Ospar Commission, available at www.ospar.org/about/how/ (accessed 11 November 2022).

42 Established by the IWC under Article III(4) of the ICRW.

43 Established by the CCSBT under Article 9 of the Convention for the Conservation of Southern Bluefin Tuna, 10 May 1993, 1819 UNTS 359.

44 Corrective Actions Policy, Compliance Policy Guideline 3 (updated at the Twenty-Fifth Annual Meeting, 18 October 2018), available at www.ccsbt.org/sites/default/files/userfiles/file/docs_english/operational_resolutions/CPG3_CorrectiveActions.pdf (accessed 15 April 2022).

45 It must be noted that while the SBSTTA of the CBD is composed of parties, specific committees are composed of individuals.

46 International Whaling Commission (Footnote n 37).

47 Report of the Scientific Committee (Footnote n 36).

48 Whaling in the Antarctic (Footnote n 4).

49 International Convention for the Regulation of Whaling, 2 December 1946, 161 UNTS 72, Article V(1). See Art V(2): ‘based on scientific findings.’

50 ICRW, Article VI.

51 UNCLOS Annex II, Article 2. See also, Commission on the Limits of the Continental Shelf (CLCS): Members of the Commission, available at www.un.org/depts/los/clcs_new/commission_members.htm (accessed 15 April 2022).

52 See UNCLOS Rules of Procedure of the Commission on the Limits of the Continental Shelf, 17 April 2008, UN Doc CLCS/40/Rev.1, Article 11: Duty to Act Independently.

53 UNCLOS, Rules of Procedure of the Commission, available at www.un.org/depts/los/clcs_new/commission_rules.htm (accessed 15 April 2022).

54 UNCLOS, Article 76(8).

55 Statute of the International Court of Justice (1945) 33 UNTS 993, Article 36(2). See also Whaling in the Antarctic (Footnote n 4) 234.

56 Question of the Delimitation (Footnote n 7); Delimitation of the Maritime Boundary (Footnote n 6); Dispute Concerning Delimitation of the Maritime Boundary between Ghana and Côte d’Ivoire in the Atlantic Ocean (Ghana/Côte d’Ivoire), Judgment [2017] ITLOS Reports 4.

57 Convention for the Conservation of Southern Bluefin Tuna, Article 16(2).

58 Southern Bluefin Tuna Cases (New Zealand v Japan; Australia v Japan) (Award on Jurisdiction and Admissibility) (2000) XXIII UNRIAA 1.

59 In accordance with the procedure set out in Annex II of the Convention.

60 Aarhus Convention (Footnote n 11) Article 16.

61 Escazú Agreement (Footnote n 25) Article 19.

62 Convention on Environmental Impact Assessment in a Transboundary Context, Article 15.

63 CITES, Article XVIII.

64 Convention on Biological Diversity (Footnote n 1) Article 27(1) and (2).

65 Convention on Biological Diversity (Footnote n 1) Article 27(3).

66 Whaling in the Antarctic (Footnote n 4).

67 MM Mbengue and R Das, ‘The ICJ’s Engagement with Science: To Interpret or Not To Interpret?’ (2015) 6 Journal of International Dispute Settlement 568, 573–74; J Morishita, ‘IWC and the ICJ Judgment’ in M Fitzmaurice and D Tamada (eds), Whaling in the Antarctic: The Significance and the Implications of the ICJ Judgment (Brill 2016) 238–67, 253.

68 Whaling in the Antarctic (Australia v Japan: New Zealand intervening), Judgment, Separate Opinion of Judge Xue [2014] ICJ Reports 420, para 15.

69 Whaling in the Antarctic (Australia v Japan: New Zealand intervening), Judgment, Declaration of Judge Keith [2014] ICJ Reports 336, para 7.

70 Whaling in the Antarctic (Australia v Japan: New Zealand intervening), Judgment, Dissenting Opinion of Judge Bennouna [2014] ICJ Reports 341, 346: ‘In engaging in an evaluation of the programme, the Court has, in a sense, substituted itself for these two bodies.’

71 Whaling in the Antarctic (Australia v Japan: New Zealand intervening), Judgment, Dissenting Opinion of Judge Owada [2014] ICJ Reports 301, 312.

73 Whaling in the Antarctic (Footnote n 4) 297.

74 Whaling in the Antarctic, Separate Opinion of Judge Xue (Footnote n 70) 420, 425; Whaling in the Antarctic (Australia v Japan: New Zealand intervening), Judgment, Separate Opinion of Judge Sebutinde [2014] ICJ Reports 431, 433; Whaling in the Antarctic, Dissenting Opinion of Judge Bennouna (Footnote n 72) 341, 346–47.

75 Whaling in the Antarctic (Footnote n 4) 234.

76 Whaling in the Antarctic (Footnote n 4) 248.

77 Whaling in the Antarctic (Footnote n 4) 257, 271. The Court noted that by using lethal methods and not assessing the feasibility of non-lethal alternatives in its new proposed research programme, Japan was clearly not giving due regard to the IWC and scientific committee recommendations calling for an assessment of non-lethal alternatives.

78 See e.g., Saudi Arabia – Protection of IPR (DS567) (consulting WIPO); Korea – Radionuclides (DS495) (consulting Codex Alimentarius Commission, IAEA, and International Commission on Radiological Protection); Australia – Tobacco Plain Packaging (DS435, DS441, DS458, DS467) (consulting, among others, the WHO Framework Convention on Tobacco Control).

79 See e.g., Russia – Pigs (DS475) (consulting FAO and World Organisation for Animal Health – OIE); India – Agricultural Products (DS430) (consulting the WHO, FAO, and OIE); Australia – Apples (DS367) (consulting the Secretariat of the International Plant Protection Convention).

80 Question of the Delimitation (Footnote n 7) 100.

81 Question of the Delimitation (Footnote n 7) 100, 137.

82 Question of the Delimitation of the Continental Shelf between Nicaragua and Colombia beyond 200 Nautical Miles from the Nicaraguan Coast (Nicaragua v Colombia), Preliminary Objections, Declaration of Judge Bhandari [2016] ICJ Reports 204, 206.

83 X Liao, ‘Evaluation of Scientific Evidence by International Courts and Tribunals in the Continental Shelf Delimitation Cases’ (2017) 136(48) Ocean Development & International Law 150–51.

84 Maritime Delimitation in the Indian Ocean (Somalia v Kenya), Preliminary Objections, Judgment [2017] ICJ Reports 3, 38.

85 G Vega-Barbosa, ‘The Admissibility of Outer Continental Shelf Delimitation Claims before the ICJ Absent a Recommendation by the CLCS’ (2018) 49 Ocean Development & International Law 103, 111.

86 Liao (Footnote n 85) 139; Vega-Barbosa (Footnote n 87) 112.

87 Delimitation of the Maritime Boundary (Bangladesh/Myanmar) (Footnote n 6).

88 T Treves, ‘Law and Science in the Interpretation of the Law of the Sea Convention: Article 76 between the Law of the Sea Tribunal and the Commission on the Limits of the Continental Shelf’ (2012) 3 Journal of International Dispute Settlement 483, 484.

89 Delimitation of the Maritime Boundary (Bangladesh/Myanmar) (Footnote n 6), 107.

90 Footnote Ibid., 115.

91 Liao (Footnote n 85) 144.

92 Treves (Footnote n 90) 491.

93 Delimitation of the Maritime Boundary in the Bay of Bengal (Bangladesh/Myanmar), Judgment, Separate Opinion of Judge Ndiaye [2012] ITLOS Reports 151.

95 Footnote Ibid., 183.

96 Dispute Concerning Delimitation (Ghana/Côte d’Ivoire) (Footnote n 58) 136.

97 Footnote Ibid., 138: ‘… the Special Chamber has no doubt that a continental shelf beyond 200 nm exists for Côte d’Ivoire since its geological situation is identical to that of Ghana, for which affirmative recommendations of the CLCS exist.’

98 RW Smith and G Taft, ‘Legal Aspects of the Continental Shelf’ in PJ Cook and C Carleton (eds), Continental Shelf Limits: The Scientific and Legal Interface (Oxford University Press 2000) 17.

99 Delimitation of the Maritime Boundary in the Gulf of Maine Area (Canada/United States of America), Judgment [1984] ICJ Reports 246, 296: ‘Legal title to certain maritime or submarine areas is always and exclusively the effect of a legal operation.’

100 Commission on the Limits of the Continental Shelf, ‘Scientific and Technical Guidelines of the Commission on the Limits of the Continental Shelf, CLCS/11’, adopted 13 May 1999, para 1.3, available at www.un.org/depts/los/clcs_new/commission_documents.htm#Guidelines (accessed 19 October 2021).

101 MM Mbengue and R Das, ‘Experts’ in Max Planck Encyclopaedia of International Procedural Law (2022); C Foster, ‘Court-Appointed Expert’ in Max Planck Encyclopaedia of International Procedural Law (2019).

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  • Specific Procedures
  • Edited by Christina Voigt, Universitetet i Oslo, Caroline Foster, University of Auckland
  • Book: International Courts versus Non-Compliance Mechanisms
  • Online publication: 15 February 2024
  • Chapter DOI: https://doi.org/10.1017/9781009373913.008
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  • Specific Procedures
  • Edited by Christina Voigt, Universitetet i Oslo, Caroline Foster, University of Auckland
  • Book: International Courts versus Non-Compliance Mechanisms
  • Online publication: 15 February 2024
  • Chapter DOI: https://doi.org/10.1017/9781009373913.008
Available formats
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  • Specific Procedures
  • Edited by Christina Voigt, Universitetet i Oslo, Caroline Foster, University of Auckland
  • Book: International Courts versus Non-Compliance Mechanisms
  • Online publication: 15 February 2024
  • Chapter DOI: https://doi.org/10.1017/9781009373913.008
Available formats
×