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China’s approach to voluntary carbon markets and Article 6 of the Paris Agreement

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Introduction

Carbon markets can play a critical role in responding to climate change by incentivising emissions[1] reductions and carbon offsetting.

There is no ‘one size fits all’ approach. What is considered to be ‘best practice’ in the context of carbon market ambition, infrastructure, and regulation, will continue to evolve over time and should be applied with pragmatism (having regard to the needs of, and the challenges faced by, individual jurisdictions).

The Asia Pacific region comprises a diverse mix of:

  • emerging and frontier markets that face the challenge of developing carbon markets at speed and at scale;
  • economies that have historically relied heavily on fossil fuels; and
  • economies that are highly vulnerable to the adverse effects of climate change.

At the same time, APAC’s geographical diversity and high-growth markets also means that the region has significant scope to support carbon removal and reduction efforts.

Avoiding dilution of emissions reduction targets is a key issue for the APAC region which is home to half of the world’s top emitting countries, including the world’s largest emitter - China.[2]

Carbon markets require sufficient scale to generate material economic and environmental benefit and transform carbon instruments into an investable and liquid asset class. Achieving sufficiency of scale requires standardisation and certainty.

China’s carbon markets at a glance

China's climate strategy centres on the "3060" targets announced by President Xi Jinping in 2020: reaching carbon peak by 2030 and achieving carbon neutrality by 2060. These goals have been formally incorporated into China's 14th Five-Year Plan (2021-2025), demonstrating the country's serious commitment to climate action. The current Five-Year Plan includes concrete environmental targets, including an 18% reduction in carbon intensity and a 13.5% decrease in energy intensity by 2025.

National ETS

China’s national emissions trading scheme (National ETS), the country’s national compliance carbon market, began trading in July 2021, and is regulated by the Ministry of Ecology and Environment (MEE). It operates in parallel with a number of pilot schemes (each a Pilot Scheme) and currently covers approximately 2,200 thermal power plants (Covered Entities). Currently only China Emissions Allowances (CEAs) may be traded on the National ETS.

On 9 September 2024, the MEE released a draft work plan proposing to expand the sectoral coverage of the National ETS to the cement, steel, and aluminium industries. The draft work plan is expected to be finalised and implemented by the end of 2024, with the first compliance deadline scheduled for 2025. The proposed expansion is expected to bring an additional 1,500 companies within the scope of the National ETS.[3]

CCER scheme

Originally launched in 2012, the CCER[4] scheme began trading in 2015 and was subsequently halted in 2017. The MEE allows entities that are subject to the National ETS to use pre-existing CCERs to offset a proportion of their annual compliance obligations under the National ETS, in an amount not exceeding 5% of the emissions allowances that they are required to surrender. The long-awaited relaunch of the CCER scheme occurred in January 2024. Following the relaunch, it is now possible for new CCERs to be traded.

Pilot schemes

Each of China’s nine pilot carbon market schemes operates independently according to their respective rules and requirements. These pilot markets have actively explored innovations in carbon market financial products and practices. They have helped to enhance efficiency and combat fragmentation in onshore carbon markets, and to promote onshore low-carbon development.

CCER scheme in more detail

Under the relaunched scheme, CCERs are traded, registered and regulated on a centralised basis. Currently, the trading of CCERs is managed by the Beijing Green Exchange, and the operation of the national registration system for voluntary greenhouse gas emissions reduction is managed by the National Centre for Climate Change Strategy Studies and International Cooperation. In time, it is expected that a single, unified institution will be established to oversee all aspects of the CCER scheme.

The methodologies for designating a project as a CCER project are set by the MEE following public consultation. Accordingly, there is a single set of standards that is used to determine CCER project status.

Third party validation and verification of CCER projects is carried out by bodies approved and accredited by the State Administration for Market Regulation (SAMR) and the MEE. Any issues relating to validation and verification are coordinated and resolved by a centralised Validation and Verification Technical Committee.

Unlike the National ETS, participation in the new CCER scheme is open to any PRC business or individual that wishes to voluntarily offset their own emissions or make a positive contribution to climate change mitigation efforts without the need to offset their own emissions.

For a project to qualify as an “emissions reduction” project under the relaunched CCER scheme, that project must either (i) reduce the volume of emissions released or (ii) remove emissions from the atmosphere according to the methodologies prescribed by the MEE. An emissions reduction project must also meet three core criteria: authenticity, uniqueness, and additionality. The MEE will arrange project inspections to ensure that these criteria are satisfied in accordance with the prescribed methodologies. Failure to comply may lead to revocation of CCER project status as well as potential civil and criminal liability.

In this article, references to ‘carbon’ and ‘emissions’ are references to carbon dioxide and equivalent greenhouse gases.

In this article, references to ‘China’ and ‘PRC’ are references to the People’s Republic of China excluding the Hong Kong Special Administrative Region, the Macau Special Administrative Region, and Taiwan.

The proposed expansion of the National ETS is expected to cover both energy-related and process-related emissions from the cement, steel, and aluminium sectors. For the aluminium industry, the proposed expansion is also expected to include emissions of perfluorocarbons and hexafluoroethane. Source: https://icapcarbonaction.com/en/news/china-expand-national-ets-cement-steel-and-aluminum-2024.

China Certified Emissions Reduction.

Original CCER scheme
Relaunched CCER scheme
Example uses 2
Market structure

Decentralised. CCERs traded within various pilot schemes according to the rules of the individual schemes.

Centralised. Currently, all trading is undertaken via the Beijing Green Exchange.

Trading method

OTC or exchange based.

Currently exchange based only. Participants must register with the National GHG Voluntary Emission Reduction Trading Institution.

Units traded

CCERs issued before 14 March 2017.

CCERs issued before 14 March 2017 may only be traded and used for offset until 31 December 2024. From 1 January 2025, only new CCERs (issued under the relaunched CCER scheme) may be traded and used for offset.

Registration

Registration with the exchange responsible for the applicable pilot scheme.

Registration in the registry established by the relevant national competent authority.

Methodology

Clean Development Mechanism project methodologies.

Clean Development Mechanism project methodologies filed with the relevant national authorities.

Third party validation and verification

Undertaken in accordance with the rules of the applicable pilot scheme.

Undertaken by third parties that are registered with the relevant national authorities. 

Regulatory authority

NDRC.

MEE.

How China’s approach may help to create opportunities and address key risks

Voluntary carbon markets have an important role in helping support the transition to net zero by:

  • promoting natural resources as a valuable commodity;
  • monetising the benefits of projects that reduce emissions through the sale, purchase, and retirement of carbon credits;
  • helping to connect capital with climate change mitigation projects and opportunities; and
  • helping countries, corporates and individuals to realise their individual decarbonisation goals and commitments (provided, of course, that they do not serve to dilute decarbonisation efforts within compliance carbon markets).

Whilst voluntary carbon markets do not seek to limit the volume of emissions released into the atmosphere, they nonetheless provide a flexible mechanism for reducing and removing carbon at an accelerated rate. However, for voluntary carbon markets to be an effective (and scalable) tool to help facilitate global decarbonisation aligned with United Nations targets, it is imperative that they adhere to three core principles:

  • environmental integrity: identifying and agreeing the right benchmarks (set according to science based principles) is critical to promote fungibility and help mitigate market fragmentation risk;
  • stability: the success of any financial market is, in part, measured by its depth and liquidity. A financial market that is ‘opaque’ is inherently unstable (and therefore unsustainable) because the potential risks associated with that market are unknown and unquantifiable; and
  • accountability: proportionality and responsibility are essential components in the effective regulation of voluntary carbon markets that, at the same time, promote growth and protect market integrity.

Achieving sufficiency of scale within voluntary carbon markets requires standardisation (to reduce fragmentation, increase transparency, and increase interoperability) and certainty (e.g. robust systems, clear lines of responsibility, and comparable regulatory classification and treatment).

Article 6 of the Paris Agreement[5] (Article 6) establishes a market-based framework for bilateral trading of carbon credits between jurisdictions (under Article 6.2) and the development of a global carbon market (under Article 6.4).[6] Achieving consensus on the key principles for achieving nationally determined contributions (NDCs) under Article 6, is however proving challenging, at least in part because disagreements persist on whether applicable systems should be centralised or decentralised.

In contrast to the approach adopted in other voluntary carbon markets, China’s CCER scheme operates according to a centralised model which:

  • adopts centralised methodologies for CCER projects;
  • requires validation and verification of CCER projects by centrally accredited bodies (each applying the centralised methodologies);
  • stipulates that all trading must be carried out on a centralised basis through the national CCER trading organization (currently the Beijing Green Exchange);
  • provides for registration of all trades with a centralised registration body (whose records are definitive); and
  • imposes potential civil and criminal liability for non-compliance with applicable rules.

The potential benefits of a centralised system include avoiding market fragmentation and reducing the risk of double counting. Care is however required in the implementation of a centralised model to ensure that market growth and ambition are not adversely impacted by the streamlining of market infrastructure, or the methodologies that determine project eligibility.

At COP29, the parties are tasked with resolution of the issues that have, so far, hampered progress with regards to the implementation of Article 6 mechanisms. Whilst many countries have initially (and understandably) focused on domestic emissions reduction to achieve their NDCs and mitigate the adverse impact of carbon cost equalisation measures[7] on domestic exports, many jurisdictions will have the need to source carbon credits from non-domestic projects to a greater or lesser extent.

China is an example of a jurisdiction that has the geographic and technological capacity to develop high-integrity projects that reduce/remove carbon emissions. Accordingly, the relaunch of China’s CCER scheme is potentially significant for facilitating low-carbon transition in jurisdictions other than China pursuant to Article 6. For this to be possible, China must adduce evidence that CCERs qualify as “internationally transferred mitigation outcomes” (ITMOs) either for bilateral trading under Article 6.2 or for trading within a global carbon market to be established under Article 6.4.

Alignment of standards and systems within voluntary carbon markets (or at the least, comparability and compatibility) ultimately underpins the success of Article 6 (e.g., avoiding double-counting by making corresponding adjustments between the carbon credit producing country and the carbon credit receiving country). Unlike CCERs, ITMOs are not currently traded within a single, centralised market, according to standardised systems or methodologies. Instead, intergovernmental cooperation agreements or memorandums of understanding set out the requirements for eligibility, authentication, registration, and monitoring of ITMO projects, and the transfer and surrender of ITMOs. As the ITMO market grows and matures, the case for standardisation (to promote integrity, efficiency, scale, and liquidity) similarly gains momentum.

In the nascent stage of Article 6 implementation, flexibility and innovation are of paramount importance. We must however have regard to the lessons learnt in domestic voluntary carbon markets to realise the decarbonisation potential of Article 6 mechanisms.

The Paris Agreement is a legally binding international treaty on climate change. It was adopted by 196 parties at the United National Climate Change Conference (COP21) in Paris, France, on 12 December 2015, and entered into force on 4 November 2016.

Article 6 also provides opportunities for countries to cooperate towards the achievement of their nationally determined contributions without relying on carbon markets (under Article 6.8).

Examples include Europe’s Carbon Border Adjustment Mechanism.

Reference

  • [1]

    In this article, references to ‘carbon’ and ‘emissions’ are references to carbon dioxide and equivalent greenhouse gases.

  • [2]

    In this article, references to ‘China’ and ‘PRC’ are references to the People’s Republic of China excluding the Hong Kong Special Administrative Region, the Macau Special Administrative Region, and Taiwan.

  • [3]

    The proposed expansion of the National ETS is expected to cover both energy-related and process-related emissions from the cement, steel, and aluminium sectors. For the aluminium industry, the proposed expansion is also expected to include emissions of perfluorocarbons and hexafluoroethane. Source: https://icapcarbonaction.com/en/news/china-expand-national-ets-cement-steel-and-aluminum-2024.

  • [4]

    China Certified Emissions Reduction.

  • [5]

    The Paris Agreement is a legally binding international treaty on climate change. It was adopted by 196 parties at the United National Climate Change Conference (COP21) in Paris, France, on 12 December 2015, and entered into force on 4 November 2016.

  • [6]

    Article 6 also provides opportunities for countries to cooperate towards the achievement of their nationally determined contributions without relying on carbon markets (under Article 6.8).

  • [7]

    Examples include Europe’s Carbon Border Adjustment Mechanism.

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