24 September (R)evolution: How new CNH reporting frameworks are shifting boards’ engagement on sustainability September 24, 2024 By ER Law Admin Conference 0 Dr Pamela Hanrahan MAICD is Emeritus Professor of Commercial Law and Regulation at the UNSW Business School, Chair of the Business Law Section of the Law Council of Australia, and a Consultant with Johnson Winter Slattery. Energy and resources (E&R) companies have always been at the centre of contemporary conversations about sustainability. Most people forget that the concept of a “social licence to operate” first emerged late last century in the extractive industries, as a response to growing social and political concern over the negative impacts of some projects on the environment and local communities. The concept of social licence has its critics but is a useful reminder that all businesses rely on the ongoing support – or at least tolerance – of their stakeholders to succeed, including their investors and lenders, employees, customers and suppliers, and communities. A business that operates in a manner that is unacceptable to key stakeholders will lose that support; stakeholders are increasingly focusing on sustainability and as a result it has become a key factor in the financial prospects and performance of projects. Boards now recognise that operating sustainably involves managing the impact of their company’s operations in the three broad “CNH” domains: climate and the energy transition; nature, biodiversity and the environment; and humans and societies. The third domain includes areas like human rights, modern slavery, labour rights and WHS, First Nations engagement, equity and diversity, data governance and privacy, tax transparency, foreign bribery, and sustainable development. An expanding body of hard and soft law regulates corporate behaviour in all three domains. Hard law – including Commonwealth, state and territory legislation – often includes sanctions for non-compliance by companies and their officers. Soft laws such as codes, principles and policies are also influential. These include the Ruggie Principles on Business and Human Rights, the UN Global Compact and the OECD Guidelines for Multi-national Enterprises. Importantly, these hard and soft laws are now supplemented by rapidly maturing mandatory and voluntary disclosure frameworks. And these disclosure frameworks are having a significant impact on how issues of sustainability are viewed from the boardroom. Sustainability disclosure is changing Sustainability disclosure is not new. Many Australian E&R companies have been reporting on their climate, environmental and societal impacts for years. Larger entities are required by law to report on modern slavery risks and workplace gender equity, and high greenhouse gas (GHG) emitters are subject to NGER reporting. Where sustainability factors have a material impact on the matters required to be disclosed in the company’s annual report (currently comprising its financial statements, directors’ report and auditor’s report) that impact must be appropriately captured. The focus is on identifying the likely financial implications for the company of the risks and opportunities involved. Many companies also elect to report against voluntary frameworks such as the Global Reporting Initiative (GRI) Standards, the Sustainability Accounting Standards Board (SASB) Mining and Metals Standards, and the recommendations of the Taskforce on Climate-related Financial Disclosures (TCFD). A smaller number report voluntarily against the 2015 United Nations Sustainable Development Goals (SDGs) covering “people, planet and prosperity” and are engaging with the new recommendations of the Taskforce on Nature-related Financial Disclosures (TNFD). Outside the formal reporting required by law, sustainability disclosure has sometimes been seen as an opportunity to burnish the company’s reputation by emphasising positive commitments, subject only to the overarching constraint that the content should not be misleading (for example, greenwashing). In some companies, sustainability reporting is largely the responsibility of the public relations or investor relations functions. However, that is likely to change with the recent enactment of laws to mandate the inclusion of climate-related financial disclosure as a stand-alone component of annual reports. The new law is part of the evolution of globally standardised sustainability reporting following the creation of the International Sustainability Standards Board (ISSB) in 2021 and the release in 2023 of its standards IFRS S1 General Requirements for Disclosure of Sustainability-related Financial Information and IFRS S2 Climate-related Disclosures. In September 2024, the Australian Government legislated to require the inclusion of a Sustainability Report in many larger companies’ annual reports, initially containing climate-related information to be prescribed by the Australian Accounting Standards Board based on IFRS S2. Including information about climate-related risks, opportunities, metrics and targets (including scope 1, 2 and 3 GHG emissions) in annual reports has significant ramifications for Australian boards, as the law requires that directors personally sign-off the disclosure (as for the financial statements). As is demonstrated by ASIC v Healey [2011] FCA 717, where directors were found personally liable in connection with misstatements in the Centro Group’s financial statements, this has liability implications for individuals that are different from those that arise for corporate publications more generally. And the disclosure will now be made in circumstances covered by s 1308 of the Corporations Act 2001 (Cth), which imposes liability on a person who authorises disclosure if they fail to take all reasonable steps to ensure that disclosure is not materially false or misleading. This is already influencing how E&R boards approach sustainability disclosure, and we are seeing a much higher level of board attention given to how information is collected, presented and assured. Much of this falls squarely within the CFO function. The flow-on effect seems to be that sustainability considerations across all three domains are increasingly part of discussions about strategy and financial performance. Executives and in-house counsel need to be prepared for this new boardroom view. Dr. Pamela Hanrahan will deliver the keynote address on Day 2 of the ER Law Annual Conference, taking place from October 16-18 in Brisbane. To register, please follow this link here. Related Articles COMMUNITY LEGAL RIGHTS IN MINE CLOSURE PLANNING; A COMPARATIVE ANALYSIS OF THREE AUSTRALIAN STATES Professor Alex Gardner, University of Western Australia Law School, and Laura Hamblin, formerly research associate at the UWA Law School, 2021 Why does the Mining Act 1978 (WA) not provide secure legal rights for community consultation in relation to mining lease proposals and mine closure plans? Addressing this question presents an important theme for this comparative review of some core features of the regulatory frameworks for mine closure in three Australian States. It also raises important questions for future legal research. Western Australia, Queensland and Victoria have prominent but vastly different, and thus uniquely significant, mining industries. Western Australia’s mining industry has a long history of large and smaller scale mining of a diverse range of minerals by various methods that pose significant mine rehabilitation challenges.[i] Queensland’s mining industry is similarly large and diverse, dominated by export coal production, and planning future minerals development in a decarbonising world.[ii] Victoria has a smaller mining industry with a large historical legacy dominated by a coal mining industry for domestic electricity generation in the Latrobe Valley, which is closing as the State actively transitions to renewable power sources.[iii] These States also have significant differences in the regulation of their mining industries. What all three States do have in common is the significance of their mining industries to both the State economy and the communities who depend on or live near mining operations. Importantly, all three States are confronting large legal and regulatory challenges in managing mine rehabilitation and closure. The key to addressing these challenges is effective mine closure planning: the closure of a mine site has ripple effects that are not merely environmental and economic, but social and cultural too. The initial approval of a mine closure plan occurs before any mining has begun and, with the life cycle of a mine often spanning decades, regulatory bodies are approving hypothetical closure scenarios, potentially subject to vast changes. Regulatory bodies may then seek to enforce closure requirements enshrined in a plan that may wane in relevance as mining operations progress, the updating of which may depend on the miner. Yet remedying the regulatory system so that it creates adaptable but consistently effective mine closure outcomes for affected communities still begins at planning. Although that planning is an iterative process across the life of the mine, it is very important at the initial stage of approval. Recent legislative reforms in all three States are adding to the regulatory rigour and adaptability of mine closure planning, though there are very different legal requirements for community consultation. This article aims to explain and assess the regulatory reforms by undertaking a comparative analysis of mine closure planning across Western Australia, Queensland and Victoria, with a focus on the initial approval stage and how stakeholders and communities are brought into that process. The facilitation of continuous and comprehensive community engagement is critical to ensuring that mine closure planning accounts for environmental, economic, social, cultural and safety outcomes after mine closure, but it has not been possible to consider here the process of ongoing mine closure planning, especially for amending mine closure plans and determining satisfaction of mine closure plans leading to resource tenure relinquishment.[iv] The article begins by considering core concepts of mine closure planning and the regulatory goals that inform it. It then provides a comparative overview of each State’s mine closure planning requirements under the mineral resources, environmental and land use planning laws and draws out some of the different regulatory structures and processes for mine closure within each State. The third step in our analysis compares the ways in which those laws provide for local communities’ participation in mine closure planning, with specific attention to whether the regulatory provisions create legally enforceable rights for effective community engagement. The article concludes with a summary of the key points from the discussion of three themes in our analysis: (i) the importance of clear definitions of core concepts and key goals, (ii) mine closure planning as an essential part of a mining proposal, and (iii) the legal definition of community engagement and consultation rights. Mine closure planning and implementation is necessarily influenced by many other spheres of law including taxation law, investment law, water law, and the rights of traditional owners, to name a few. A potentially directly relevant Commonwealth law is the Environment Protection and Biodiversity Conservation Act 1999 (Cth), which may require environmental impact assessment of a mining proposal and closure plan and lead to approval conditions supplementing State requirements.[v] Whilst acknowledging the importance of these adjacent spheres of the regulatory frameworks for effective mine closure planning, this article does not attempt to address their impact. In particular, the rights of Traditional Custodians are a crucial part of mine closure planning that are only briefly noted here and that would benefit from future research. WA Department of Mines, Industry Regulation and Safety, Major Commodities Review 2022-23”. Qld Government, Department of Resources, Queensland Resources Industry Development Plan, June 022. Vic Government, Department of Jobs, Precincts and Regions, Latrobe Valley Regional Rehabilitation Strategy. See L Hamblin, A Gardner, Y Haigh, Mapping the Regulatory Framework of Mine Closure, May 2022, CRC TiME, for a broader exploration of the full life cycle of mine closure regulation. In Buzzacott v Minister for Sustainability, Environment, Water, Population and Communities [2013] FCAFC 111; (2013) 214 FCR 301, [144], [227]-[230], referring to the range of approval conditions, which included mine closure. In setting conditions under the EPBC Act, the Commonwealth Minister must consider any relevant conditions under State or Territory law: at [80] citing Lansen v Minister for Environment and Heritage (2008) 174 FCR 14. Potential changes to Environmental, Social and Governance reporting Environmental, Social and Governance (ESG) isn’t new to Australia, but it’s expected to become a more important aspect of business in the coming years. With shareholders and institutional investors paying close attention to business activities with an ESG lens we can expect more focus on this area. A recent example is the HESTA superannuation fund choosing to very publicly vote against the AGL demerger proposal on ESG grounds. POWERING CONSUMER PROTECTIONS: WHY DECENTRALISED AND DISTRIBUTED ENERGY RESOURCES WARRANT A NEW LENS ON CONSUMER PROTECTION REGULATIONS Recent years have seen distributed energy resources usher in a new era of self-generation and reduced reliance on traditional centralised energy networks. Australian customers are increasingly enabled to access unconventional “behind the meter” energy sources and contribute to a two-way flow of energy back to the grid. Renewable Energy Guidelines and Accelerated Approvals The Clean Energy Council, in collaboration with KPMG, has released its Leading Principles: First Nations and Renewable Energy Projects. The document provides detailed guidelines on how to address challenges to effective engagement and sets out best practice principles to engage with First Nations People on renewable energy projects. Greenwashing is now a global issue Businesses and governments are now realising that being green is no longer nice to have, it’s an integral part of operations. There are also benefits, perceived and real, to both consumers and business customers to being involved in programs that are environmentally friendly or have an ethical or sustainable edge. This has given rise to a new risk - ‘greenwashing’ - that governments around the world are now grappling with. Greenwashing refers to misrepresenting a product, policy or purpose as environmental, ethical or sustainable. It applies not only to companies but also non-profits, investors or anyone seeking to represent themselves in that light. QUEENSLAND’S MINE REHABILITATION REQUIREMENTS FOR VOIDS: ENSHAM CASE STUDY The State of Queensland reformed its mine rehabilitation legislation, namely the Environmental Protection Act 1994 (Qld) (EP Act), in 2018 through the Mineral and Energy Resources (Financial Provisioning) Act 2018 (Qld) (MERFP Act). A case study of the Ensham open-cut coal mine[i] in central Queensland highlights three issues for the efficacy of this regulatory framework. The first issue concerns an available exclusion of rehabilitation requirements for existing mining voids (the area of excavation created by open cut mining) in flood plains. Under the EP Act, as amended by the MERFP Act, a holder of an environmental authority (EA) may, in its Progressive Rehabilitation and Closure Plan (PRCP) and PRCP Schedule, identify land as a Non-use Management Area (NUMA).[ii] This is land that would not be rehabilitated “to a stable condition” and not have a post-mining land use. This rehabilitation exception as a NUMA is not applicable to mining voids wholly or partly in flood plains – these must be rehabilitated to a “stable condition”,[iii] as defined in the EP Act. This is the “section 126D(3) rehabilitation obligation”.[iv] However, the transitional provisions of the mining rehabilitation reforms differentiate the rehabilitation obligations of pre-existing mines (those existing at the time of the reforms, such as the Ensham Mine) and new site-specific mines.[v] Pre-existing mines with a “land outcome document” that presents an outcome similar to a NUMA can establish criteria for rehabilitation or management of a void in a flood plain that supersede this section 126D(3) rehabilitation obligation.[vi] The MERFP Bill Explanatory Notes for the transitional provisions reveal that this exemption from section 126D(3) “does not retrospectively breach existing rights and provides certainty to industry on the transitional process”.[vii] However, this grandfathering is arguably disconnected from environmental risks of such residual voids, creating two classes of mines based on the timing of a mine’s existence (pre-existing versus new). This Ensham case study provides an example of a pre-existing mine’s use of a “land outcome document” to exempt rehabilitation of residual voids in a flood plain but without clarity around the non-use management status of the area of the residual voids. The second issue discussed in this case study is progressive rehabilitation. The design of a financial assurance system to increase progressive rehabilitation was “a clear objective of the EPA’s work in 2004”, yet the EP Act fell short by failing to clearly outline criteria for certification of final rehabilitation for industry, and a scheme of refunding financial assurances at the termination of mining activity.[viii] These issues remained unaddressed until the 2015 State election when the then Labor Opposition ran on the campaign “[to] investigate the expansion of upfront rehabilitation bonds for resource companies to fully fund long-term rehabilitation activities”.[ix] Thereafter, the Queensland Treasury Corporation published a number of discussion papers advising of the shortcomings of the current financial assurance framework and that, in 2017, there were “220,000 hectares of disturbance, with an estimated rehabilitation cost of $8.7 billion”.[x] Queensland’s 2018 mining regulation amendments concerning progressive rehabilitation were intended to ensure “rigorous” review of NUMA approvals in PRCPs, “through an objective public interest evaluation” for future or newly established mines.[xi] However, the reforms may not effectively address instances in which progressive rehabilitation has been lacking in large, open-cut, mature mines in operation at the time of these legislative changes. As of 2021, approximately 33% of the Ensham Mine’s 4,944.7 ha of scheduled rehabilitation areas had been progressively rehabilitated.[xii] According to Ensham’s PRCP, this level of progressive rehabilitation exceeds that of other open-cut mines in Queensland.[xiii] For established mines, such as Ensham, that are approaching closure and have large voids that have not been substantially progressively rehabilitated across their mine life, the most economical rehabilitation option may be to rehabilitate residual voids to accord with legislated requirements. Under Queensland’s legislation, “rehabilitation” does not necessarily mean these voids will be re-filled. This may be contrary to community understanding of what rehabilitation is. Thirdly, this case study highlights areas in the regulatory framework in which information transparency could be improved – particularly public access to information – which raises issues of accountability, quality of community engagement and, ultimately, social licence on the part of mining companies and government. Information transparency is also relevant to community engagement and expectations for rehabilitation, such as the meaning of “rehabilitation” of residual voids (i.e., refilling to establish a pre-mining state versus the legislated “stable condition” standard). This article is structured as follows. Part 2 presents the legal and operational context of the Ensham Mine. It also describes the operational history of flooding and its relevance to rehabilitation and management of post-mining residual risks, which leads to a discussion of the rehabilitation legal reforms. Part 3 discusses the reform of Queensland’s rehabilitation legislation framework as it concerns residual voids, including the transitional provisions of the EP Act. Part 3 also explores Ensham’s Residual Void Project (RVP) for the development of the rehabilitation criteria for residual voids and considers the community engagement process. Part 4 comments on the transitional regulatory design issues in Queensland’s framework, issues concerning progressive rehabilitation of pre-existing open-cut mines such as Ensham, as well as transparency of information and community consultation. Part 5 concludes and suggests future research. Showing 0 Comment Comments are closed.