Skip to main content

Will Forest Carbon Credits Easier to Develop in China?

Three years after the Afforestation Carbon Sink Methodology was first drafted, it is finally undergoing revision. Although final implementation may still take time, for practitioners who are struggling to hold on in this field, it is a ray of light in the darkness.

The Bottlenecks

Although CCER trading has been increasing, offshore wind power projects have dominated this volume, leaving forestry carbon sink projects absent from this trading boom. This is a strange phenomenon because forestry carbon sinks were among the earliest approved CCER methodologies, and forestry carbon sink projects represent more than half of all CCER projects. So far, the number of forestry carbon sink projects with registered carbon credits stands at zero. Only emission reductions that have been formally registered and issued can be traded, transferred, or pledged on the national trading platform. In other words, no forestry carbon sink project has yet generated tradable carbon credits.

The obstacles arise from land eligibility and additionality demonstration. 

For land eligibility, many project owners face difficulties in providing evidence to prove that the project land was not forest prior to development. Many initiatives are retrospective projects where the afforestation has already taken place. This requires project owners to look back to the pre-afforestation period and locate historical evidence spanning three consecutive years. The challenge, however, is that early records—such as remote sensing imagery, land-use maps, forest and grassland resource surveys, operational plans, and project acceptance documentation—are not always complete. This is particularly true for projects involving small plots, marginal land, village collective land, roadside greening, mine site restoration, and urban landscaping.

Additionality is one of the aspects that consumes the most time and incurs the highest costs in terms of explanation. Project owners need to answer whether the carbon sinks generated by the project are additional to what would have occurred without the project. However, many forestry carbon sink projects were not initially designed simply to sell carbon credits, but were often driven by multiple motivations such as ecological restoration and rural greening. Proving additionality is undoubtedly troublesome for these forestry carbon sink projects.

As a result, the reality is characterized by slow approval processes, delayed market entry, and returns that remain a distant prospect.

The Revision

The most important adjustment is that eligible afforestation projects are exempted from additionality demonstration. This directly reduces one of the most uncertain parts of project development. Instead of asking every project owner to defend the counterfactual case individually, the revised methodology places more weight on project eligibility rules and baseline assumptions. The draft defines the baseline as the continuation of pre-afforestation land use and management, with baseline removals treated as zero. 

This is a meaningful simplification, but it also changes where the integrity burden lies. In this revision, the MEE appears to place substantial value on the broader co-benefits of forestry carbon sink projects, rather than treating them purely as delivered carbon removals. The document explains the reason for the exemption as follows:

To further shorten development timelines and reduce costs, it is necessary to consider that afforestation is primarily driven by public-interest objectives—such as enhancing forest ecological functions and improving biodiversity and living environments—yet entails high costs for planting and subsequent maintenance; as it is difficult to generate revenue beyond that derived from emission reductions, such projects lack financial attractiveness.

If additionality is no longer demonstrated project by project, then land eligibility, conservative accounting, and third-party verification become more important. In other words, the revision lowers the explanation burden, but it does not remove the credibility challenge.

Another important change is the expansion of land eligibility. As the remaining area of conventional forest land suitable for afforestation becomes increasingly limited, the revised methodology extends support beyond traditional forestry land such as barren hills and wasteland. It newly includes greening projects on non-forestry land, such as transport corridors, urban and rural settlements, and industrial or mining sites. This is important because many potential forestry carbon sink projects in China are not located in large, clean, continuous forestland, but in fragmented and mixed land-use settings created by urbanization, infrastructure development, and land rehabilitation. At the same time, the methodology continues to exclude economic forests in order to strictly adhere to the baseline requirement of additionality.

Other changes include clarifying the methods for proving ownership of emission reduction benefits and optimizing and simplifying accounting methodologies. In addition, the revised methodology is also intended to increase project development returns. These changes will require further adaptation in front-line implementation.

Summary

To summarize, the revision of the Afforestation Carbon Sink Methodology provides a more enabling policy framework for developing forest carbon credits in China. In the past, the forestry carbon sink sector was constrained by narrow eligibility rules and high development costs, leaving many potential forest and greening resources outside the project pipeline. If the details of this revision are effectively implemented, a large number of dormant forestlands and greening assets could be activated. 

The revision may also diversify the types of participants in the sector. Traditionally, forestry carbon sink project owners have mainly been large state-owned forest farms or leading forestry enterprises. After the methodology is revised, local urban investment companies, ecological restoration firms, and even village cooperatives may find new opportunities to enter the market.

If you are involved in afforestation projects in China or elsewhere, feel free to leave a comment and share your field experience, policy observations, or views on the opportunities for developing carbon assets.

Reference

[1]https://www.mee.gov.cn/xxgk2018/xxgk/xxgk06/202606/t20260626_1160307.html

[2]https://m.bjx.com.cn/mnews/20260629/1501907.shtml

[3]https://mp.weixin.qq.com/s/oLSxhWZyf9Fx4V9Rdnl39w







Comments

Popular posts from this blog

China’s Carbon Removal Transition: Insights from the 3rd Edition of the State of CDR Report

The 2026 edition of The State of Carbon Dioxide Removal offers a useful moment to reassess China’s role in the global carbon dioxide removal (CDR) landscape. The picture is more nuanced than a simple story of leadership or lagging behind. China is already central to current global CDR, but mostly through conventional, land-based removals. Its next challenge is to move from large-scale forestry-based removals toward a more diversified, durable and policy-supported CDR portfolio. 1 | China is already a major CDR actor — but mainly through conventional CDR China is one of the world’s largest emitters, but it is also one of the largest contributors to current global CDR. This reflects the structure of today’s CDR system: global removals are still overwhelmingly dominated by conventional methods, especially afforestation and reforestation. In this sense, China’s CDR position is not marginal. Bookkeeping models suggest that China contributes more than 500 MtCO₂ per year through afforestatio...

Glossary

  Carbon dioxide removal is becoming an important part of climate policy, carbon markets, and net-zero discussions. This glossary is a simple guide to the key concepts behind carbon dioxide removal. It is designed for readers who want to understand the basic vocabulary before reading reports, policy documents, or market updates on CDR. This page will be updated regularly as new terms, technologies, and policy discussions emerge. Core Concepts Carbon Dioxide Removal (CDR) Human activities that remove CO₂ from the atmosphere and store it durably in geological, terrestrial, ocean reservoirs, or products. Emissions Reductions Actions that reduce new greenhouse gas emissions released into the atmosphere. CDR does not replace emissions reductions; it complements them. Net Zero CO₂ Emissions A state in which CO₂ emissions are balanced by CO₂ removals, so net CO₂ emissions equal zero. Gross CO₂ Emiss...

碳移除术语

Core Concepts|核心概念 Carbon Dioxide Removal (CDR) | 二氧化碳移除 / 碳移除 从大气中移除 CO₂,并将其较长期储存在地质、陆地、海洋储库或产品中的人类活动。 Emissions Reductions | 减排 减少新增温室气体排放,是实现气候目标的首要手段。CDR 不能替代减排,而是与减排共同发挥作用。 Net Zero CO₂ Emissions | CO₂ 净零排放 CO₂ 排放量与 CO₂ 移除量相互抵消后的净排放为零。也就是说,仍可能存在排放,但需要有相应的移除量来平衡。 Gross CO₂ Emissions | CO₂ 总排放 在扣除碳移除之前,人类活动释放到大气中的 CO₂ 总量。 Gross CO₂ Removals | CO₂ 总移除 在与排放量相抵消之前,从大气中移除的 CO₂ 总量。 Residual Emissions | 残余排放 即使经过深度减排后仍难以完全消除的排放。实现净零时,这部分排放通常需要通过碳移除来抵消。 Paris Temperature Goal | 巴黎温控目标 《巴黎协定》中将全球升温控制在远低于 2°C,并努力限制在 1.5°C 的长期气候目标。 Conventional CDR | 传统碳移除 已经较成熟、部署规模较大的碳移除方法,通常与森林、土地、土壤和木制品有关。 Novel CDR | 新型碳移除 目前部署规模较小、技术成熟度较低,但通常具有较长储存时间的新兴碳移除方法,例如 BECCS、DACCS、生物炭和增强风化。 CDR Gap | 碳移除缺口 各国承诺的碳移除规模与符合巴黎温控目标情景所需碳移除规模之间的差距。 Durability | 碳储存持久性 碳被储存后在较长时间内不重新释放回大气的能力。储存越持久,碳移除的气候效果越可靠。 Additionali...