16 August Recent legislative updates in Queensland August 16, 2024 By AMPLA Admin Energy, Environment, Mining, Oil and Gas, Resources and Energy 0 As the pressures of climate change and the energy transition continue to escalate, the Queensland government has introduced a new suite of laws aimed at bolstering resource management and enhancing environmental protection. These legislative changes reflect a growing commitment to foster development and balance economic growth with ecological preservation. As the pressures of climate change and the energy transition continue to escalate, the Queensland government has introduced a new suite of laws aimed at bolstering resource management and enhancing environmental protection. These legislative changes reflect a growing commitment to foster development and balance economic growth with ecological preservation. The Mineral and Energy Resources and Other Legislation Amendment Bill 2024 was passed in June. The objective of the Bill was to introduce a new framework to manage coal seam gas induced subsidence but this framework was removed as a result of industry consultation. The Bill also amended multiple acts in Queensland on a range of issues, some that we’ve outlined below. The Act amends the Gasfields Commission Act 2013 to rename the GasFields Commission Queensland to Coexistence Queensland. Coexistence refers to key stakeholders including industry and landholders fostering the State’s resources sector and emerging industries such as renewable energy together. The body will have expanded functions including providing advice to government and other stakeholders on systemic coexistence issues for the resources industry more broadly (previously it was limited to onshore gas only). The community leaders councils that are established by Coexistence Queensland will also now include representatives from local government, regional communities, the agricultural industry and the resources and renewable energy industries. In addition, the Act enables greenhouse gas storage and enhanced petroleum recovery activities to be banned in the Great Artesian Basin. In achieving this, the Act extinguishes greenhouse gas exploration permits and related environmental protection approvals that exist or were in train without any right to seek compensation. Existing wells and monitoring bores will also be decommissioned under the changes and after tenure is cancelled the site will be required to be rehabilitated. The Mineral and Energy Resources (Financial Provisioning) Act 2018 will also be amended to increase the prescribed Estimated Rehabilitation Costs for risks assessment from $100,000 to $10 million. This and other amendments are aimed at reducing the administrative burden for environmental authority holders under the scheme. Amendments have also been made to the Mineral and Energy Resources (Common Provisions) Act 2014 relating to the caveat regime and aerial surveys. The intention of these changes is to ensure requirements are not overly onerous where there is no impact to the underlying land holder. New environmental legislation and guidelines have also been introduced in the State in recent months. The Environmental Protection (Powers and Penalties) and Other Legislation Amendment Bill 2024 was passed in June in response to recommendations from the Independent Review of the Environmental Protection Act 1994 (Qld) that was released in 2022. The Bill introduces a new offence for failing to comply with the general environmental duty where the failure is likely to cause serious or material environmental harm. A defence to this offence is if the act causing the contravention was authorised under an instrument in section 493A(2) of the Environmental Protection Act, which includes environmental authorities. Wilful contravention of the general environmental duty carries a maximum penalty of 4,500 penalty units or two years imprisonment, while contravention of the duty carries a maximum penalty of 1,655 penalty units. Executive officers of companies that commit environmental offences may also be held personally liable for acts or omissions that occur. The liability remains even after they leave office if they are found to have contributed to the offence in some way. The Bill also gives the regulator additional powers when performing inspections. This includes allowing them to obtain criminal history reports, use drones for inspections and body-worn cameras when entering a premises. The Department of Environment, Science and Innovation also recently released its Greenhouse Gas (GHG) Emissions Guideline. The guideline doesn’t constitute new regulations, but rather clarifies the requirements under the Environmental Protection Act 1994 (Qld). The guideline sets out the minimum expectations for GHG emissions information to be provided with applications for new or amending environmental authorities (EAs) and how that information will be used. The guideline applies to EAs for resource and prescribed environmentally relevant activities. Related Articles 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. Legislative updates in Queensland and Western Australia The Governments in Queensland and Western Australia have recently released several consultation papers, reports and proposed legislation that impact the resources sector. Recent State legislative updates Both Victoria and South Australia have recently progressed significant legislation focused on renewable energy. The Victorian Government’s Climate Change and Energy Legislation Amendment (Renewable Energy and Storage Targets) Bill 2023 has had its second reading in the Legislative Assembly. The Bill is intended to reduce the cost of power bills, create tens of thousands of jobs and encourage investment in the State’s renewable energy industry. Recent updates in New Zealand, Canada, Indonesia and Vietnam The industry’s legal landscape continues to evolve across the world. This article outlines some recent updates from New Zealand, Canada, Indonesia and Vietnam. 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. ARELJ Recent Development - Industrial Manslaughter in the Queensland Resources Sector Showing 0 Comment Comments are closed.