Most of the information and data presented in this paper is publicly available on the official EP-Web site and/or it is based on published material by academics, NGOs and finance ethics think tanks. Additional in-depth research—with the main purpose of verifying/falsifying certain information or data—has been conducted with the help of several semi-informal interviews with EPA-, IFC/World Bank- and NGO-officials and off-the-record conversations with top-level (European) EPFI-representatives.
In what follows, we assess the democratic qualities of the EPA by means of the framework we have developed above. This assessment shows that the specification of Habermas’ conception of deliberative democracy, developed in the foregoing section, can indeed be applied fruitfully to transnational regulatory networks. We first describe the general characteristics of the EPA followed by an analysis of how and to what extent the EPA’s Governance Rules institutionalize the engagement of stakeholder groups through the five Habermasian elements of deliberative democracy (including an identification of the most important stakeholder groups of the EPA).
General Characteristics
The EP-standards for environmental and social risk management apply globally to the following four financial market products.
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Project finance;
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Advisory services related to project finance;
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Project-related corporate loans; and
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Bridge loans.
The EPs are based on the Performance Standards on Environmental and Social Sustainability of the International Finance Corporation and the World Bank Group’s Environmental, Health, and Safety Guidelines. They are adopted by so-called Equator banks or EPFIs, that is, financial institutions which are active in the project finance sector. The EPFIs commit themselves to not providing loans and credits to projects where the borrower is not able or willing to comply with the respective social and environmental standards and guidelines. As of today, 89 financial institutions from 37 countries and six continents have adopted the EPs. According to official data provided by the EPA, the EPs cover over 70% of international project finance debt in emerging markets and developing countries (EPA 2016).
The overall aim of the EPs is the promotion of environmental (i.e., protection of project-affected ecosystems) and social (i.e., respect for human rights) sustainability in the (project) finance industry (EPA 2013, 20). To reach these goals, the EPs impose obligations on both lenders (EPFIs) and borrowers (clients), in particular with regard to review and categorization (principle 1); environmental and social impact assessment (principle 2); environmental and social management systems and action plans (principle 4); stakeholder engagement (principle 5); grievance mechanism (principle 6); monitoring (principle 9); and reporting (principles 9 and 10). These obligations get formalized as covenants (principle 8), which are part of the loan documentation or investment agreement between the EPFI and the project developer.
The EPA is the unincorporated association of EPFIs established in 2010. The association’s objective is the ‘management, administrationFootnote 8 and further development of the EPs’ (EPA 2016). It is governed by a set of Governance Rules which specify the internal governance structures as well as decision-making proceduresFootnote 9 within the EPA. Two governance levels have to be distinguished: the ‘management’ level and the ‘administrative’ level of the secretariat (Fig. 1).
The management level consists of the Steering Committee which is responsible for the management and further advancement of the EPs as well as the coordination of administrative tasks. EPFIs become members of the Steering Committee on the basis of a rotation principle for a maximum of three years. Among the members of the Steering Committee, one EPFI gets elected as chair of the Steering Committee. The chair functions as the speaker and provides coordination.
The Steering Committee can set up permanent or temporary working groups fostering the inclusion of stakeholder groups. One of the main tasks of these working groups is to discuss governance and implementation issues and to provide guidance to EPFIs with regard to the further advancement of the EPs. Currently, nine working groups exist, including the ones on capacity building and training, consistency, external relations (i.e., communication with external stakeholders such as NGOs and civil society organizations), biodiversity, climate change, social risk and regional outreach.
The second level of the EPA is the so-called administration level consisting of the EP-Secretariat. The Secretariat manages the everyday running of the EPA. In particular, the Secretariat is responsible for the EP-Web site, internal and external communications, public relations, advice and assistance with regard to adopting and implementing the EPs and the management of financial affairs.
Stakeholder Groups
By means of our previous definitions, we explain which groups belong to the dèmos of the EPA, that is, which groups are actors in the establishment of the EPs and which groups are addressed by them. We also indicate which groups are ‘otherwise affected’, and should therefore be engaged in stakeholder discussions, and influence EPA-decision-making.
The main stakeholders of the EPs include (a) the ‘Equator banks’ or EPFIs; (b) the EPFIs’ clients, that is, project developers and operators; (c) civil society organizations and NGOs; and (d) project-affected communities, such as indigenous peoples. Below we explain whether they belong to the group of actors, addressees or otherwise affected stakeholders.
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The actors group comprises all stakeholders that are formally engaged in articulating, reviewing and updating the EPs and the rules and procedures of the EPA. This group contains the ‘Equator banks’ that are officially engaged in maintaining and adjusting the EP-framework.
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The addressees group contains all those financial institutions that are required to implement the EPs into their socio-environmental risk management and due diligence frameworks, namely the EPFIs. Furthermore, it contains all the EPFIs’ clients, that is, project developers and operators. They are expected to fulfill the requirements laid down in the EPs. These obligations are imposed by the lender upon the borrower, and they get formalized as covenants. The EPs thus regulate the business conduct of EPFIs as well as the business conduct of their clients. The actors and addressees together form the dèmos. Hence, the boundaries of the EPA-dèmos are somewhat fluid: Every time a new bank enters the EPA and becomes an EPFI, and every time a client decides to obtain financial means from an ‘Equator bank’ and thus submits itself to the EPs, the dèmos of the EPA changes, respectively.
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The group of all otherwise affected stakeholders consists of civil society organizations and NGOs as well as project-affected local communities: Neither the EPs nor the Governance Rules of the EPA apply to them directly; therefore, they do not belong to the dèmos of the EPA. These groups are nevertheless indirectly affected by the application of the EPs and in particular by the industrial and infrastructure projects that are financed under the EPs (e.g., coal, oil and gas projects; (mountaintop removal) mining projects; bridges, dams and power plants projects).
Although these communities and organizations are not part of the actual dèmos, they should be engaged following Habermas’ general discourse principle. That is, they should have access to stakeholder discussions and their interests and values should be considered in decision-making to obtain general legitimacy of the regulations established by the actors and addressees (Saunders 2012).
Stakeholder Discussions
At present, four main stakeholder discussions can be distinguished—two formal and two informal ones: The two formally organized discussions take place within the EPA and its working groups (cp. paragraphs 1 and 2 below), while the two informal discussions take place within the Thun Group of Banks, and other subgroups of (non-)EPFIs (3), and among finance NGOs, such as BankTrack, and the general public (4). In what follows, we describe for each of the discussions, first, the various types of (stakeholder) communication surrounding the EPs. In a second step, we critically analyze and evaluate them from a Habermasian perspective—based on the criteria of accessibility of the discussions for all stakeholders (which is a precondition for the articulation and clustering of meanings, topics, values and interests in typical discourses that can influence decision-making) and availability of relevant information to all (which is a precondition for meaningful discussions as such).
(ad 1) Discussions surrounding the official EPA-review and update process: The last review and update process took place between 2010 and 2013. It consisted of an internal consultation phase that yielded a first draft of EP III, a second phase that gave all other stakeholder groups the chance to comment on the initial draft and to make suggestions for further improvement, and a last phase in which the third generation of the EPs was finalized and launched The invitation to comment on the proposed revision of the EPs, in the second phase of the update process, provoked various responses from stakeholders (e.g., (finance) NGOs) and interactions among them (e.g., between NGOs, EPFIs and the EPA). These interactions in the context of the review process are a good example of a discussion among stakeholders from within and beyond the dèmos of the EPA. They can contribute to the transformation of interests and values and help to find ways to inform representative decision-making and thus jointly set and realize the goals of the EPA. The problem from a deliberative democracy perspective is that the EPFIs do not engage with NGOs and other stakeholders on a regular (formal) basis, e.g., within a stakeholder forum or advisory group being part of the EPA, but only incidentally.
(ad 2) Discussions within the working groups of the EPA: Many of the discussions about the purposes, content and functioning of the EPs take place within the working groups. Although these working groups cover the majority of the issues and discourses that may be important to other stakeholder groups of the EPs, they are solely accessible for bank representatives. Only the ‘Biodiversity for Bank’s (B4B) program, that was co-launched together with the World Wildlife Fund (WWF) and the Business and Biodiversity Offsets Program (BBOP),Footnote 10 contains (a basic form of) stakeholder engagement and makes use of civil society input and expertise. It is this severely limited access of other stakeholders to the working groups that hinders the development of stakeholder discussions that could form the basis for representational decision-making, administration and adjudication within the EPA.
Both formally organized discussions described above suffer from a lack of publicly disclosed information about the actual functioning of the EPA and the on-the-ground outcomes of the EPs. For many interested stakeholders, it is almost impossible to find out what has been discussed within the EPA in general and the Steering Committee in particular. The public disclosure of information and public consultation are often prevented by confidentiality duties toward the association and/or the EPFIs’ clients (Richardson 2005; Mikadze 2012; BankTrack 2011; Wright 2012). Both intransparency and the lack of information hinder the establishment of meaningful stakeholder dialogs.
(ad 3) Discussion within the Thun Group of Banks: The so-called Thun Group of Banks consists of seven leading international banks, six ‘Equator banks’ (Barclays, BBVA, Credit Suisse, ING Bank, RBS Group and UniCredit) and one non-EPFI (UBS). In 2013, the Thun Group of Banks published a draft paper on banks and human rights (Thun Group of Banks 2013). The paper provides a first guide to the banking sector for operationalizing the UN Guiding Principles on Business and Human Rights (Ruggie 2013; United Nations 2011).
During the drafting process itself, apparently no meaningful consultation and engagement took place with affected stakeholder groups such as NGOs, civil society organizations and human rights activists (BankTrack 2013, 2). This implies that the initial discussions within the Thun Group of Banks were insufficiently accessible for many stakeholder groups. As a consequence, the paper has been criticized for its poor stakeholder engagement (BankTrack 2013; de Felice 2015).
Interestingly, however, the exclusive discussions within the Thun Group of Banks provoked much broader and, in a sense, more fruitful discussions among financial institutions, practitioners and academics. Especially, the discussions on human rights due diligence might initiate and stimulate the next EPA-review and update process. If developed further (in particular with regard to the transparency and availability of information), these could be made open to all and could therefore provide a basis for representative decision-making, administration and adjudication.
(ad 4) Discussions initiated by NGOs and civil society organizations: Besides functioning as watchdogs, NGOs (and other civil society organizations) contribute to the EP-discussions among practitioners and academics by publishing case studies and project-related data on their Web sites (including data documenting the respective environmental, social and human rights violations associated with the different projects financed under the EPs). These reports help in assessing single companies (both financiers and project developers/operators), whole industry sectors and/or individual (controversial) projects. BankTrack and other finance NGOs have also released documents that propose reform measures that could help to prevent ‘dodgy deals’ and to strengthen the EP-framework. These documents point out institutional shortcomings as well as potential ways in how to overcome them (BankTrack 2011, 2012; Lazarus and Feldbaum 2011; Lazarus 2015). In short, finance NGOs are able to sensitize key actors in the project finance industry (and beyond); they help to raise awareness for crucial socio-environmental and human rights issues; and they are able to put pressure on the main stakeholders (i.e., EPFIs and EPA) to take further action toward the full realization of the EPs’ potential. The activities of NGOs thus constitute a stakeholder discussion in itself, but also initiate further dialogs among banks, civil society and researchers. These dialogs are in principle open to all, provide relevant information to the public, put major banks under reputational pressure, and challenge the organizational legitimacy of the EPA and their member institutions. If the EPA would institutionalize mechanisms to systematically consider these discussions in the development of the EPs, this would represent a move toward (more) deliberative democracy.
The analysis so far has shown that several stakeholder discussions take place inside and outside of the EPA. The formally organized discussions suffer from a lack of accessibility and limited availability of information. This diminishes the legitimacy of the EPs. Nevertheless, these somewhat underdeveloped formal stakeholder discussions have spurred various informal, open stakeholder discussions involving public information about a variety of issues and discourses that have emerged within civil society. These informal discussions could build the basis for representative decision-making, administration and adjudication.
Representative Decision-Making
At present, formal decision-making within the EPA is a matter of EPFIs only. The participating banks are the only (stakeholder) group that is officially engaged in maintaining and adjusting the EP-framework (recall that only banks can become member of the EPA’s Steering Committee and the respective working groups). Democracy, however, demands that (the representatives of) all stakeholder groups addressed by the respective rules (in this case, the EPA’s Governance Rules) should be involved in associational decision-making—at least with regard to the respective discourses. This is clearly not (yet) the case, since project developers and operators are excluded from associational decision-making procedures.
Besides, the Governance Rules concerning the Steering Committee and the working groups give no systematic, institutionalized voice to (the discourses of) otherwise affected stakeholder groups. This, however, is demanded to establish the general legitimacy of network regulation.
The limitations of representation in formal decision-making are understandable against the background of the characteristics of the dèmos of the EPA: All EPFIs’ clients belong to the dèmos, but they are dispersed all over the world. In addition, they are not necessarily aware of the affairs of the EPA and they may not be familiar with democratic decision-making. Moreover, the boundaries of the dèmos are rather fluid since its composition changes each time an EPFI acquires a new client or loses one. A problem that complicates the systematic consideration of the views of otherwise affected stakeholders in decision-making is the high number of very diverse local communities that are (potentially) affected by the EP-framework, as well as the many NGOs and civil society organizations that bring forward numerous socio-environmental interests.
These circumstances suggest that representative decision-making may be better served by a representation of discourses, rather than by a (proportional) representation of stakeholders. Indeed, various discourses can be distinguished within the stakeholder discussions that we identified above. For instance, there are discourses related to banks and human rights (e.g., with regard to human rights due diligence and covenants); climate change (e.g., whether banks should divest from fossil fuel industries and coal, oil and gas companies); (FPIC-based) stakeholder dialog and engagement (in particular with regard to indigenous communities); or the extension of the (regional) scope of the EP-framework (e.g., ‘going beyond project finance’ and/or whether an outreach strategy toward the emerging markets is required to level the playing field). These discourses could serve as a basis for the representation of the addressees of the EPs and for the systematic consideration of the view of otherwise affected stakeholders in decision-making.
Administration
From a Habermasian perspective, the administration of an MSI has three major roles to fulfill: (1) concretizing and specifying the rules for implementation; (2) monitoring (non)compliance; and (3) sanctioning rule-infringement.
(ad 1) Providing concrete guidelines for the implementation of MSI-regulations: The EP-Secretariat, currently consisting of two members of staff, is responsible—among other things—for giving advice and assistance with regard to adopting and implementing the EPs. The EP-implementation note ‘… contains selected information and examples to support the understanding of the requirements in, and implementation of, the Equator Principles …’ (EPA 2014, title page). Both the EPA’s Governance Rules and the EP-disclaimer state however that ‘… the Equator Principles do not create any rights in, or liability to, any person, public or private’ (EPA 2013, 11). This implies that the EPFIs can adopt and implement the EPs at their own discretion. Therefore, at present the EPA is to be considered a rather informal organization mainly based on individualized (voluntary and self-regulatory) rule-specification.
(ad 2) Monitoring (non-)compliance: In reality, the EPs suffer from inadequate monitoring mechanisms. For instance, up to today, EP-compliance relies mainly on passive (non-EPA) monitoring (Sarro 2012 1542ff.): Civil society organizations and NGOs function as informal monitoring institutions and watchdogs (O’Sullivan and O’Dwyer 2009). In case of apparent non-compliance, they might start advocacy campaigns and/or protest movements and customer boycotts. This form of civil society criticism often causes public outcry and thus exposes non-compliance to the EPA, its members and other stakeholders. Yet, so far there is (almost) no proactive engagement in terms of monitoring; a credible independent and transparent form of monitoring and control is (mainly) lacking.
(ad 3) Sanctioning non-compliance: The self-regulatory EP-regime lacks a credible deterrent, since effective sanctions for rule-violations are lacking. The question therefore comes up whether the EPs have enough ‘legal bite’ to penalize participants that fall behind their voluntary socio-environmental commitments? Currently, the EPFIs face only little sanctions from the side of the EPA should they not comply with the EPs. A (temporary) delisting is possible according to the EPA’s Governance Rules, if ‘Equator banks’ fail to report publicly or if they fail to pay the annual membership fee. Only in these cases will ‘Equator banks’ be excluded from EPA-membership. A re-adoption, however, is still possible. The regulations of the EPA do not entail the possibility to delist a company because of non-compliance and/or violation of the EPs (EPA 2010/2013, 26). So far only public naming and shaming campaigns initiated by NGO–watchdogs might put EPFIs and their clients under (reputational) pressure. Yet this ex-post way of sanctioning cannot be steered and/or applied by the EPA for rule-enforcement. It is thus insufficient to prevent non-compliance and practical failure, e.g., in the form of financing ‘dodgy deals’.
In summary, we can conclude that the EP-framework suffers from a lack of adequate administrative mechanisms. A major underlying problem relates to the EPA being understaffed and underfunded: The budget remains low compared to other MSIs and covers only the costs for the secretariat, the Web site and annual meetings. Moreover, the management structure of the EPA is rather loose and ‘handled by EPFIs, who, in addition to their other responsibilities within their financial institutions, volunteer their time as EP-chair, Steering Committee members and leaders and members of Working Groups’ (Lazarus 2015, 134). So, while the autonomy and independency of the functions of specification, monitoring and sanctioning is central to democracy in the EPA, these functions are—out of necessity—executed by the EPFIs in a more or less arbitrary way.
Adjudication
The EPs in their current version suffer from a lack of implementation, due to the absence of an independent adjudicating body. Such a body is all the more important considering the existence of various governance gaps and ambiguities within the EP-framework: The EPs and the EPA’s Governance Rules are vaguely and sometimes even ambiguously formulated leaving discretionary leeway for diverging interpretations and exit door strategies. The language used is often declaratory rather than compulsory and imperative; some principles are conditional in nature and/or contain mere recommendations. As a consequence, both borrowers and lenders are able to circumvent the contractual obligations of the EPs (Marco 2011, 470). Banks, for example, can redefine their project finance activities as representing something else, such as corporate or export finance. Project financiers can classify their projects as category B or C to avoid a stricter A-classification (Haack et al. 2010, 21; Wright 2012, 68). Last but not least, financial institutions can provide loans in different tranches to not meet the respective financial thresholds of the EPs.Footnote 11
Especially under this condition of serious ambiguity, an independent adjudicating body is essential for arriving at interpretations of regulations that are fair (with regard to the engaged stakeholders), consistent (with the overall rules) and predictable (given earlier adjudications). Interpretations are now made by the EPFIs themselves without a further systematic consideration of other stakeholders. This implies that the act of solving potential conflicts between legitimate claims of stakeholders while maintaining the consistency of the regulations lies solely in the hands of some of the EPFIs without much guarantees for independent adjudication. In the absence of a developed administration and independent adjudicating body, the specification and interpretation of the EPs and other regulations of the EPA remains arbitrary, and disconnected from the values and expectations of the other members of the dèmos as well as the otherwise affected stakeholders.
Constitutionalization
The constitutionalization of the EP-framework and the EPA can be found in the EPs themselves as well as in the EPA’s Governance Rules. Both documents provide descriptive and normative stipulations with regard to (1) the main aims and key issues of the association; (2) the core members of the association and its other (external) stakeholders; (3) the participation of the respective stakeholders in discussion and decision-making; and (4) the organization of implementation and rule-enforcement.
(ad 1) The main aims of the EP-framework, formulated in the principles, include the identification, assessment and management of environmental and social risks and impacts in project finance. In doing so, the EPs seek to promote ‘sustainable environmental and social performance’ and ‘improved financial, environmental and social outcomes.’ They also acknowledge ‘the importance of climate change, biodiversity, and human rights, and believe negative impacts on project-affected ecosystems, communities, and the climate should be avoided where possible. If these impacts are unavoidable they should be minimized, mitigated, and/or offset’ (all: EPA 2013, 2; cp. EPA 2010/2013, 4). These aims and issues clearly state which values and goals should be considered important and thus give the EPA a framework for the evaluation and improvement of existing institutional provisions, in case they appear to be insufficient for their realization.
(ad 2) The definition of the dèmos of the EPA is part of the official statement of the EPs and includes all EPFIs; that is, all those financial institutions that are active in project finance, project finance advisory services and project-related corporate loans (and bridge loans) (EPA 2010/2013, 1). Every financial institution that is active in the project finance industry and that wants to commit itself to the EP-framework can become a member of the EPA and can thus be represented in associational decision-making. To remain a member, EPFIs need to report on an at least annual basis and pay the annual membership fee. Further (minimum) entry criteria that have to be met prior to becoming a member of the EPA do not exist. On the basis of our conceptualization, the dèmos of the MSI should be made up of all those addressed by the regulations that have been drawn up for a collective purpose. In the EP-framework, the EPFIs recognize merely their own role as financiers with ample ‘opportunities to promote responsible environmental stewardship and socially responsible development, including fulfilling [the] responsibility to respect human rights’ (EPA 2013, 2). However, they neglect the equally important role of the financed projects in promoting these goals as well as the fact that (most of) the regulations of the EPA apply to the EPFIs’ clients, which make them an essential part of the dèmos. The present EPA-definition narrows down the dèmos of the EPs too much by excluding project developers and operators from the EP-dèmos.
(ad 3) EPA-membership is restricted to project finance banks. Consequently, they are the only members represented in the associational decision-making bodies. This implies the exclusion of other groups of addressed stakeholders, that is, the project developers and operators. Moreover, the consideration of otherwise affected stakeholders is insufficiently embedded in the constitutional documents of the EPA. Neither the EPs nor the EPA’s Governance Rules stipulate how these stakeholders could be represented or considered in associational decision-making. Seen from the perspective of legitimate self-regulation and given the established goals and values of the association, the ‘EP-constitution’ is too restrictive in its articulation of representative decision-making.
(ad 4) So far, there are no basic rules and/or organizational mechanisms defined in the constitutional documents of the EPA that state how the EPA should deal with adjudication, monitoring and sanctioning.
In sum, we can conclude that the main issues the EPs aim to address are officially established in the constitutional documents of the EPA and that a relatively precise, yet (too) narrow definition of the dèmos is explicitly formulated there. Moreover, the currently existing arrangements for decision-making are laid down in the EPA’s constitutional documents. However, the current arrangements exclude several groups of addressed stakeholders from representation, and all affected stakeholders from consideration in decision-making. The other regulative elements of deliberative democracy (administration and adjudication) are largely absent in the EPA, and this is—unfortunately—also reflected in its constitutional documents.
From our perspective of deliberative democracy, the present constitutionalization is nevertheless an important element of democracy for the EPA as it facilitates institutional learning processes. Even a constitution that is insufficiently developed from this perspective can serve as a starting point for reflection and improvement if the stated aims are (a) considered in relation to the ideal of deliberative democracy and (b) compared to the present arrangements (or lack thereof) for the demarcation of the demos as well as for stakeholder dialogs, decision-making, administration and adjudication.
Reform Proposals
Below, we summarize some reform proposals that directly follow from the deliberative democracy framework proposed in the section ‘A Habermasian Account of Deliberative Democracy in MSIs’ that would enhance the legitimacy of the EPA. These measures consist of suggestions for a wider demarcation of the dèmos (that would also include the EPFIs’ clients), the institutionalization of consideration of otherwise affected stakeholders in associational decision-making, and the further elaboration on and institutionalization of administration, adjudication and constitutionalization.Footnote 12
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Stakeholder discussions should be open to all, and relevant information should be available to all participants. This could be achieved by opening up the formal discussion among EPFIs for other stakeholders (e.g., NGOs, civil society organizations and project-affected communities) and by providing the necessary information to all interested stakeholders. Moreover, a change from incidental stakeholder consultations that can spur discussions—such as in the EP-revision and update processes—to a continuous and ongoing dialog related to human rights and environmental, social and governance issues seems necessary.
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Provided that stakeholder discussions are working properly, the institutionalization of the representation of discourses in decision-making would provide a solution for the representation of EPFIs and their clients. That is, the discourses of project developers and operators (the constituents of the dèmos) should be represented in associational decision-making. This form of discourse representation à la Dryzek could be achieved by changing the decision-making rules of the EPA that presently give voice/vote only to EPFIs. The consideration of (all) otherwise affected stakeholders in decision-making could be organized by means of (more or less) continuous consultation of representatives of the discourses that otherwise affected stakeholders maintain within the stakeholder discussions. Consultation of the discourses of stakeholders such as environmental, social and finance NGOs and local communities could be achieved via an EP-stakeholder forum as suggested by the reform commission of the EPA.
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Administration requires the institutionalization of the three functions of specification, adequate monitoring and (automatic) sanctioning (including delisting of non-compliant EPFIs and the public announcement of delisting decisions made by the EPA). They all demand the further development of the secretariat as well as changes in various EP-regulations.Footnote 13
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To harden the governance structures of the EP-framework, the interpretation of the EPs (and other EPA-rules) in cases of conflict should not be left to the stakeholders engaged in a specific project. Of particular importance is the establishment of an independent adjudicating body through an associational conflict-resolution mechanism which might help with these issues (i.e., ‘soft case law’).
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The above reform proposals for the institutionalization of deliberative democracy should be constitutionalized through an update of the EPs as well as the EPA’s Governance Rules. This could (further) facilitate future discussions about EP-modifications.