What is REDD+?
Forests: why are they important?
Combating climate change
Forests cover a total of 4 billion hectares worldwide, equivalent to 31% of the total land area (1). Although this figure may seem high, the world’s forests are disappearing. Between 1990 and 2000 there was a net loss of 8.3 million hectares per year, and the following decade, up to 2010, there was a net loss of 6.2 million hectares per year. Although the rate of loss has slowed, it remains very high, with the vast majority occurring in tropical regions (1). Aside from the devastating effects tropical forest loss has on biodiversity and forest-dependent communities, a major consequence of deforestation and forest degradation is the release of heat-trapping carbon dioxide (CO2) into the atmosphere. Forests provide vast carbon sinks that when destroyed emit CO2 into the atmosphere, either by burning or degradation of organic matter (2). CO2 is one of the most potent greenhouse gases and the primary component of anthropogenic emissions (3). The conversion of forests to other land uses is responsible for around 10% of net global carbon emissions (4). Solving the problem of deforestation is a prerequisite for any effective response to climate change.
People and forests
Global estimates of numbers of forest-dwelling and forest-dependent peoples vary widely (5), however the World Bank states that forest resources contribute directly to the livelihoods of 90% of the 1.2 billion people living in abject poverty (6). Of these, there are an estimated 500 million forest dependent people, 200 million of whom are indigenous peoples (5). Forests support the livelihoods of local communities who depend on forests not only for food, but for fuel, fodder for livestock, medicine and shelter (5). Whether in terms of communities most directly dependent on forest resources or people at the consumer end of international supply chains, forests are vital for the well-being of humanity and play a central role in poverty alleviation initiatives (6).
As it is often the poorest that are most susceptible to the adverse effects of climate change (7), reducing deforestation provides an opportunity to simultaneously tackle the problem at its source whilst helping to promote the resilience of those most vulnerable to climate change.
Forests provide essential ecosystem services beyond carbon storage and emissions offsetting – such as health (through disease regulation), livelihoods (providing jobs and local employment), water (watershed protection, water flow regulation, rainfall generation), food, nutrient cycling and climate security. Protecting tropical forests therefore not only has a double-cooling effect, by reducing carbon emissions and maintaining high levels of evaporation from the canopy (4), but also is vital for the continued provision of essential life-sustaining services.
These services are essential for the well-being of people and the planet, however they remain undervalued and therefore cannot compete with the more immediate gains delivered from converting forests into commodities (8). Ecosystem services operate from local to global scales and are not confined within national borders; all people are therefore reliant on them and it is in our collective interest to ensure their sustained provisioning into the future.
Drivers of deforestation
Understanding the drivers of deforestation and forest degradation (hereafter ‘deforestation’) is vital in developing the policies and measures needed to effectively alter the current trends of forest loss and climate change, and to promote a positive future for biodiversity and human well-being (9).
The underlying causes of deforestation lie in the ever-increasing demand for food, fuel and forest products that result from not only a growing global population, but also from the higher incomes and resulting changing patterns of consumption of an increasing proportion of that population (10,11). This problem is exacerbated by the fact that growing demand causes an alarming increase in the price of a number of commodities, further incentivising land-use extension and encroachment into forests (12).
The causes of deforestation vary both regionally and temporally (10). They generally do not exist in isolation but operate through a complex range of interactions with one threat facilitating another (11). Over the last 50 years there has been a shift from deforestation driven by largely state-driven activities to that caused by enterprise-driven activities (5). From the 1960s to 1980s, small-scale subsistence activities were predominantly responsible as governments endorsed the colonisation of forests by facilitating access through infrastructural improvements and decreasing land prices (10). Since then however, globalisation and urbanisation have heightened the demand from distant urban and export markets, weakening the previously strong association between local demand and deforestation (13) and placing commercial enterprises at the heart of the problem (10).
Globally, agriculture and timber extraction are the clear driving forces behind deforestation, with commercial and subsistence activities accounting for 40% and 33% respectively, and mining, infrastructure and urban expansion cumulatively being responsible for the remainder (9). The main drivers vary between tropical regions. In Latin America, logging and agriculture play central roles, with beef, soy and sugar cane being the main agricultural commodities. Since the 2006 moratorium on the expansion of soy production in the Amazon, development of pasture for cattle has become the dominant threat in this region (10). Across Asia the majority of deforestation is driven by large-scale agricultural and timber plantations, mainly for the production of palm oil, coconut, rubber and teak (10). Conversely, Africa remains in the early phases of forest cover transition, with small-scale activities such as fuel wood collection and charcoal production still playing a central role (9).
Despite these general trends, the drivers of deforestation are dynamic and it is likely that rising demand will result in the homogenisation of threats as the activities responsible for deforestation throughout the tropics come to play an increasing role in Africa also. There is evidence of this already in the growing interest of Asian timber companies in Africa’s tropical forests (9).
What is REDD/REDD+?
Degradation and deforestation of the world’s tropical forests are cumulatively responsible for about 10% of net global carbon emissions. Therefore, tackling the destruction of tropical forests is core to any concerted effort to combat climate change (14). Traditional approaches to halting tropical forest loss have typically been unsuccessful, as can be seen from the fact that deforestation and forest degradation continue unabated.
REDD (reducing emissions from deforestation and forest degradation) incentivises a break from historic trends of increasing deforestation rates and greenhouse gases emissions. It is a framework through which developing countries are rewarded financially for any emissions reductions achieved associated with a decrease in the conversion of forests to alternate land uses (14). Having identified current and/or projected rates of deforestation and forest degradation, a country taking remedial action to effectively reduce those rates will be financially rewarded relative to the extent of their achieved emissions reductions (15).
REDD provides a unique opportunity to achieve large-scale emissions reductions at comparatively low abatement costs (16). By economically valuing the role forest ecosystems play in carbon capture and storage, it allows intact forests to compete with historically more lucrative, alternate land uses resulting in their destruction (14).
In its infancy, REDD was first and foremost focused on reducing emissions from deforestation and forest degradation. However, in 2007 the Bali Action Plan, formulated at the thirteenth session of the Conference of the Parties (COP-13) to the United Nations Framework Convention on Climate Change (UNFCCC), stated that a comprehensive approach to mitigating climate change should include “[p]olicy approaches and positive incentives on issues relating to reducing emissions from deforestation and forest degradation in developing countries; and the role of conservation, sustainable management of forests and enhancement of forest carbon stocks in developing countries” (17). A year later, this was further elaborated on as the role of conservation, sustainable management of forests and enhancement of forest carbon stocks was upgraded so as to receive the same emphasis as avoided emissions from deforestation and forest degradation (18).
Finally, in 2010, at COP-16 (19) as set out in the the Cancun Agreements, REDD became REDD-plus (REDD+), to reflect the new components. REDD+ now includes:
(a) Reducing emissions from deforestation;
(b) Reducing emissions from forest degradation;
(c) Conservation of forest carbon stocks;
(d) Sustainable management of forests;
(e) Enhancement of forest carbon stocks.
Within its remit, REDD+ has the potential to simultaneously contribute to climate change mitigation and poverty alleviation, whilst also conserving biodiversity and sustaining vital ecosystem services (20). This potential for multiple benefits raises the crucial question of to what extent the inclusion of development and conservation objectives may help or hinder the overall success of, and negotiations for, a future REDD+ framework (explicitly for climate change mitigation). Having said this, prospective co-benefits can easily transform into prospective co-detriments, making the earlier question arguably irrelevant. Aside from whether consideration of such factors will promote or hamper the success and negotiations of a REDD+ framework, they are unquestionably important for the creation of a sustainable and equitable REDD+ process.
The details of a REDD+ mechanism continue to be debated under the UNFCCC (21), and the considerable financial needs for full-scale implementation have not yet been met. A final mechanism is therefore not yet in place and operating at scale. Despite this, in recognition of the need for urgent action if reducing deforestation is going to have a meaningful effect in terms of reducing emissions and mitigating climate change, REDD+ initiatives have already been instigated outside the auspices of the UNFCCC, both independently and in anticipation of a formal REDD+ mechanism (12).
Watch our REDD+ video, An Introduction to REDD+.
REDD+ Negotiations under the UNFCCC: The Story so Far
The details of a REDD+ mechanism continue to be debated under the UNFCCC (21), and the considerable financial needs for full-scale implementation have not yet been met. A final mechanism is therefore not yet in place and operating at scale. The following section provides a chronological summary of what has happened so far within the UNFCCC REDD+ negotiations.
The Kyoto Protocol
Although REDD was formalised as an idea at the thirteenth Session of the Conference of the Parties (COP-13) to the United Nations Framework Convention on Climate Change (UNFCCC) in Bali, 2007, and in its current form, is considered a success of COP-16 in Cancun (2010), its roots extend back to the adoption of the Kyoto Protocol in 1997. Within the context of emissions limitation and reduction commitments in Article 2, the Kyoto Protocol refers to the protection and enhancement of sinks and reservoirs of greenhouse gases, sustainable forest management practices and afforestation and reforestation activities (22). The inclusion of the above practices was restricted, as it was only afforestation and reforestation activities that were considered eligible for generating credits under the Clean Development Mechanism.
Despite the inclusion of deforestation as an important land use issue, confusion existed over the role of Land Use, Land Use Change and Forestry (LULUCF) activities in countries’ commitments under Kyoto and there was a significant lack of information and technology to guide the measurement, reporting and verification of such activities (22).
COP-7, Marrakesh, 2001
At COP-7 in 2001 it was decided, as part of the Marrakesh Accords, that only afforestation and reforestation qualified as LULUCF activities capable of generating carbon credits under the Clean Development Mechanism of the Kyoto Protocol (Decision 17/CP.17) (23). Reducing deforestation or forest degradation was excluded from the decision due to concerns of leakage (22). The concern was that reducing emissions from deforestation and forest degradation was unlikely to achieve a net reduction in emissions due to the fact that whilst reduced in one area, the same pressures may present themselves elsewhere, as the emissions producing activity is merely relocated (22). Other concerns originally raised over REDD included issues to do with: permanence, the idea that carbon is only ever temporarily stored and at some point is always re-released into the atmosphere; additionality, the notion that identifying any improvements in emissions reductions is complicated by complexities of predicting what eventualities would have occurred in the absence of the REDD project; and measurement, difficulties in accurately ascertaining the levels of carbon stored in soils and trees (15).
Read Decision 17/CP.7 from the Marrakesh Accords here
COP-11, Montreal, 2005
The notion of avoided deforestation as an important climate change mitigation mechanism then did not re-enter the negotiations until COP-11 in Montreal, 2005.
Throughout 2005, there had been increasing attention paid to the individual roles of countries at different developmental stages in efforts to combat climate change. The European Commission laid the foundations for a climate change strategy with measures targeting both industrialised and developing countries. Given the respective contributions of countries to global greenhouse gas emissions, the decreasing share attributable to developed countries within the EU along with the growing role of developing countries in emissions generation, in February 2005, the European Commission adopted a communication entitled “Winning the battle against global climate change” (SEC(2005)180) (COM/2005/0035) recognising the need to broaden country participation in order to achieve the global action required. Despite their growing share of emissions, developing countries expressed concerns that imposing reduction targets could hamper their economic development. Meanwhile, some developed countries, such as the U.S., argued that exclusion of developing countries from commitments not only undermined the environmental effectiveness of an agreement but also jeopardised their own industry’s competitiveness. From either viewpoint, the benefits of positive incentives that would permit developing countries to participate in emissions reduction efforts whilst maintaining progress towards their wider development goals were clear. As well as appreciating the varying capacities of countries on the basis of ‘common but differentiated responsibilities and respective capabilities’, the communication also highlighted the importance of including more policy areas, in particular emphasising the need for a fresh approach to halting deforestation (24).
That year also saw the formation of the Coalition for Rainforest Nations. Led by Papua New Guinea, the Coalition came together as a collaboration aiming to reconcile forest stewardship with economic development (22) and highlight and remedy the exclusion of reducing emissions from deforestation from carbon markets under the Kyoto Protocol. COP-11 saw the Coalition act through the governments of Papua New Guinea and Costa Rica in requesting that “Reducing emissions from deforestation [RED] in developing countries and approaches to stimulate action” be included in the agenda. It was proposed that, in generating credits from RED activities, developing countries could gain access to carbon markets that would incentivise the protection of forests by making their worth greater in their carbon value than from industries requiring their destruction (25). The issue received extensive support and Parties generally agreed on the issue’s importance in the context of climate change mitigation (26). Governments subsequently agreed to a two-year work programme (27) and agreed to initiate consideration of the issue at the twenty-fourth SBSTA (Subsidiary Body for Scientific and Technological Advice) session in Bonn, May 2006. This would involve both consideration of the Parties’ views and recommendations on RED-related issues with a specific focus on scientific, technical and methodological issues (28).
COP-13, Bali, 2007
In 2007, given that forest degradation plays a more threatening role than deforestation in central Africa, a group of countries within the Commission des Forets d’Afrique Centrale (COMIFAC) proposed that emissions reductions from forest degradation be included also (29). Previously, RED had omitted inclusion of degradation due to a number of technological challenges associated with the accurate measuring and reporting of emissions reductions from reduced degradation (19).
A key milestone was subsequently achieved at COP-13. The two previous years, following COP-11 in Montreal, had seen extensive discussion and deliberation by the SBSTA on policy, scientific, technical and methodological issues, culminating in a decision at COP-13 in Bali, 2007. The Bali Action Plan, under Decision 1/CP.13, outlined a commitment of the Parties to address enhanced action on climate change mitigation, including the consideration of “Policy approaches and positive incentives on issues relating to reducing emissions from deforestation and forest degradation in developing countries; and the role of conservation, sustainable management of forests and forest carbon stocks in developing countries” (17). The Bali Action Plan also established a subsidiary body to conduct the process, the Ad Hoc Working Group on Long-term Cooperative Action under the Convention (AWG-LCA). The AWG-LCA was to conduct a comprehensive process to enable full, effective and sustained implementation of the Convention through long-term cooperative action (30), with the aim of completing its work in 2009 and presenting its outcomes at COP-15 (17).
A further decision (Decision 2/CP.13): ‘Reducing emissions from deforestation in developing countries: approaches to stimulate action’ was adopted (17). Whilst the Decision itself in referring explicitly to deforestation maintains the limited scope of RED, it also importantly acknowledges that “forest degradation also leads to emissions, and needs to be addressed when reducing emissions from deforestation” and affirms “the urgent need to take meaningful action to reduce emissions from deforestation and forest degradation in developing countries” (REDD) (17).
This decision provided a mandate for several elements and actions by Parties relating to RED, including: i) strengthening and support of current efforts; ii) capacity-building, technical assistance and technological transfer to support methodological and technical needs of developing countries; iii) identifying and undertaking activities to address the drivers of deforestation, enhance forest carbon stocks via the sustainable management of forests, and; iv) mobilise resources to support the above (20).
Read the Bali Action Plan/Decision 1/CP.13 and Decision 2/CP.13 in full here
COP-14, Poznań, 2008
At COP-14 in Poznań, the SBSTA reported on the outcomes of its programme of work on methodological issues associated with REDD policy approaches and incentives (20). In its report, in response to pressure from some developing countries, the role of conservation, sustainable management of forests and enhancement of forest carbon stocks countries was upgraded so as to receive equal emphasis as deforestation and forest degradation (20). This saw the early progression of REDD to REDD+ (22) and recognised that conservation, the sustainable management of forests and the enhancement of forest carbon stocks play as equally an important role in emissions reductions through protecting carbon stocks, as preventing deforestation and forest degradation.
The aim of expanding the scope of REDD to REDD+ was to prevent the development of a mechanism that would reward only historically high emitters in favour of one that could incentivise regions with low deforestation rates to keep them as such. The “+”improved the potential of REDD to achieve co-benefits such as poverty alleviation, improved governance, biodiversity conservation and protection of ecosystem services (31).
COP-15, Copenhagen, 2009
The Copenhagen Accord (Decision 2/CP.15) explicitly recognised the crucial role of both REDD and the emissions removals provided by forests and agreed on the need to incentivise related activities through the establishment of a REDD+ mechanism that would aid in mobilizing financial resources from developed countries. It was stated that “scaled up, new and additional, predictable and adequate funding as well as improved access” would be provided to developing countries for improved mitigation including for REDD+. To this end, developed countries committed to providing resources approaching USD 30 billion for adaptation and mitigation for 2010-2012 (of ‘fast-start finance’) and jointly mobilising USD 100 billion by 2020 for transparent, meaningful mitigation actions in developing countries. This funding was expected to come from public and private and bilateral and multilateral sources (32).
Furthermore, discussions included a decision (Decision 4/CP.15) requesting Parties to identify the drivers of deforestation and forest degradation resulting in emissions along with means to address them, activities that reduce emissions, increase removals and stabilise carbon stocks, and to use the most recent IPCC (International Panel on Climate Change) guidelines to estimate and monitor forest-related greenhouse gas emissions and removals and changes in forest cover (32). Prior to the development of the Copenhagen Accord, negotiators, within the AWG-LCA, worked on a more detailed REDD+ agenda in the hope it would guide Parties undertaking REDD+ discussions (33). This decision text identified a number of safeguards as a means of preventing negative social or environmental outcomes of REDD+ activities and also highlighted the need for robust measurement, reporting and verification of changes in emissions resulting from REDD+ activities (34). Despite considerable progress and consensus on these issues, no formal agreement on REDD+ was reached.
Read the full Copenhagen accord (Decision 2/CP.15) here
Read Decision 4/CP.15 in full here
COP-16, Cancun, 2010
Following the formulation of a decision on REDD+ in Copenhagen, COP-16 in Cancun saw its adoption with only minor modification. The Cancun Agreements (Decision 1/CP.16) affirmed that “in the context of the provision of adequate and predictable support to developing country Parties, Parties should collectively aim to slow, halt and reverse forest cover and carbon loss” (18). Parties established a technology mechanism to facilitate in the advancement and transfer of technology to support adaptation and mitigation actions, including the full range of REDD+ activities, in developing countries.
The Cancun Agreements (Paragraph 73 of Decision 1/CP.16) also decided on a phased approach to REDD+ implementation adopting with the following steps: i) the development of national strategies or action plans, policies and measures, and capacity building; ii) the implementation of national policies, measures, strategies or action plans for further capacity building, technology development and transfer, and results-based demonstration activities, evolving into; iii) results-based actions to be fully measured, reported and verified.
The same Decision identified the systems and information needed to partake in REDD+ activities by requesting that developing country Parties support REDD+ activities, according to their respective capabilities, through developing: i) a national strategy or action plan; ii) a national forest reference emission level and/or forest reference level; iii) a robust and transparent national forest monitoring system for REDD+ activities, and; iv) a system for providing information on how REDD+ safeguards (to avoid negative social and environmental outcomes) are being addressed and adhered to (18).
Finally the Agreements (Paragraph 72 of Decision 1/CP.16) highlighted the need to address related issues by requesting that Parties, when developing their national action plans or strategies for REDD+, address “the drivers of deforestation and forest degradation, land tenure issues, forest governance issues, gender considerations and the safeguards” whilst ensuring effective and full participation of the relevant stakeholders including indigenous peoples and local communities (18).
The Green Climate Fund (GCF) was established in Cancun and it was decided that it would be designated as ‘an operating entity of the financial mechanism of the Convention’ (Paragraph 102 of Decision 1/CP.16). Despite significant ground gained, a major gap remained in that there was no progress relating to what mechanisms would provide the funding for REDD+ and decisions on market-based funding mechanisms were left to be decided at COP-17 in Durban, 2011 (35).
Read the full Cancun Agreements/Decision 1/CP.16 here
COP-17, Durban, 2011
Outcomes for REDD+ from COP-17 at Durban related to financing options, safeguards and reference levels (36).
With regards to financing, in Decision 2/CP.17, it was agreed that results-based financing for developing country Parties may come from a variety of sources, including public, private, bilateral and multilateral. Notably, within this decision it was considered that market-based approaches could be developed as a means to support results-based actions (37). The decision, however, failed to clarify a number of issues. It neglected to identify the specific meaning of market-based approaches, whether sub-national activities could be supported by markets, or whether bilateral or non-convention developed mechanisms would be recognised by the UNFCCC. It also failed to specify whether any market-based mechanism would relate to those under the UNFCCC and future commitments under a second commitment phase of the Kyoto Protocol or a new legally binding agreement post-Kyoto (36). The Decision invited Parties to submit their views on ways to finance results-based activities in order for the AWG-LCA to consider these at the next SBSTA meeting (37).
Relating to safeguards, discussions focused on the reporting of how they are being respected and addressed - that is, the kind of information to be submitted, when and to whom (38). Specifically, Decision 12/CP.17 provided guidance on systems for providing information on how safeguards are addressed and respected. The decision agreed that systems providing information on how safeguards are addressed and respected should, respective of national circumstances, capabilities, sovereignty and legislation, provide transparent and consistent information, be implemented at the national level and build upon existing systems (37). It was also agreed that developing country Parties should periodically report on how social and environmental safeguards are being addressed and respected within their National Communications (37). Despite some progress in this area, there was little guidance on the level of detail required within reporting and discussions concluded with the understanding they would be further elaborated upon at COP-18.
The same decision included guidance on reference levels and/or reference emission levels. These form the benchmarks against which to measure forest-related emissions per year and are thus essential to environmental integrity when assessing future performance (36, 38). This provided a strong basis for a robust measurement, reporting and verification (MRV) scheme, essential for the development of REDD+ (39). It was decided that reference levels should be consistent with each country’s greenhouse gas inventories, referring to anthropogenic forest-related greenhouse gas emissions by sources and removals by sinks (37). The decision provides guidance on a transparent, flexible approach, in which reference levels are periodically reviewed in conjunction with any advances in methodologies and in which sub-national reference levels can be elaborated as an interim measure whilst transitioning to a national level (37).
Read the full decision on the outcome of the work of the AWG-LCA/Decision 2/CP.17 here
Read the full decision (Decision 12/CP.17) on safeguards and reference levels here
COP-18, Doha, 2012
The main areas of debate on REDD+ at COP-18 were measurement, reporting and verification (MRV) and REDD+ financing (40).
Technical issues regarding MRV were addressed under the Subsidiary Body for Scientific and Technological Advice (SBSTA). These included: (i) how to design national forest monitoring systems; (ii) how to create an appropriate MRV framework for result-based payments; (iii) how to link this in with reference levels; (iv) the need for additional guidance on designing REDD+ safeguards and (v) the drivers of deforestation. The SBSTA did not complete its work on these matters but aimed to finish by its 39th session at the 19th COP in December 2013.
The main stumbling block of the session turned out to be the issue of verification (41). Some Parties pushed for verification based on the process of international consultation and analysis (ICA) used for nationally appropriate mitigation actions (NAMAs), while others backed independent third-party verification by experts from both developed and developing countries. With no compromise reached, the issue was suspended and discussions set to resume at the next SBSTA meeting in June 2013 (42).
The second major issue concerning REDD+ discussed at the conference was how to raise finance for REDD+ activities. This was discussed under the Ad Hoc Working Group on Long-term Cooperative Action (AWG-LCA), with debate raised over (i) the creation of a new REDD+ institution; (ii) incentives for non-carbon benefits; (iii) the creation of a fund for joint adaptation/mitigation actions; and (iv) the issue of sub-national approaches for result-based payments. However, the failure to reach consensus on the issue of verification had knock-on effects for decisions on results-based finance (42). As a result the COP decided to develop a work programme on results-based finance in 2013, co-chaired by representatives each from one developed and one developing country Party (Decision 1/CP.18, paragraph 25-26). It was further agreed that draft decisions on improving the effectiveness of REDD+ finance would be developed through a series of workshops on the four topics mentioned above, for adoption at COP 19 (Decision 1/CP.18, paragraph 28-29).
Read the full text of the decisions adopted by the COP, including Decision 1/CP.18 here.
Bonn Climate Change Conference, June 2013
A number of important steps were taken for REDD+ at the inter-sessional meetings of the UNFCCC in Bonn. The conference included the 38th sessions of both subsidiary bodies: the Subsidiary Body on Implementation (SBI) and the Subsidiary Body on Scientific and Technological Advice (SBSTA).
Negotiations under the SBI were stalled when objections over procedural issues were raised by a number of Parties. This lack of progress however allowed for an unexpected amount of time to be afforded to negotiations under SBSTA, resulting in three draft decisions for REDD+ to be proposed for adoption at COP19 in Warsaw. These decisions relate to addressing the drivers of deforestation and forest degradation; modalities for national forest monitoring systems; and the timing and frequency of presentations of summary information on how safeguards are being addressed and respected (43).
The draft decision on drivers represents an important step forward after COP18 in Doha failed to produce any meaningful outcomes on this. However, although the draft decision on drivers significantly includes language that encourages the private sector to take action to reduce drivers, overall the text remains weak in that it does not incorporate any suggestion of concrete actions to address drivers, nor reference the importance of tackling the root causes of forest loss for the success of REDD+ (44).
The draft decision on safeguards states that Parties should provide a periodical summary of information on how the safeguards are being addressed and respected in the implementation of REDD+ activities. This summary is, on a voluntary basis, to be uploaded to the REDD+ Web Platform, which was created at COP18 in Doha, 2012 (45).
The third draft decision on modalities for national forest monitoring systems (NFMS) establishes that the development of Parties’ NFMS for the monitoring and reporting of REDD+ should be guided by the most recent guidelines of the Intergovernmental Panel on Climate Change (IPCC) as well as that they should provide transparent and consistent data and information that are suitable for the measurement, reporting and verification (MRV) of REDD+ activities. The decision also supports subnational monitoring and reporting as an interim measure, stating that NFMS should build on existing systems and be flexible enough to incorporate any improvements over time (46).
Progress was made in other areas, including through the agreement of elements for possible draft decisions on modalities for MRV and procedures for the technical assessment of proposed forest reference emission levels/reference levels (RELs/RLs). Elements for a possible draft decision on modalities for MRV include that data from the MRV of emissions reductions should be transparent, consistent and reported against established reference levels, and should be provided through biennial update reports, with some flexibility for least developed countries and small island developing countries. Bracketed text also states that this information will be subject to a process of international consultation and analysis (ICA), which will involve a review by experts from both developed and developing country Parties. Hopes have been expressed that this progress could see a decision on verification made in Warsaw, a contentious issue which was left unresolved at COP18 in Doha.
Regarding REDD+ financing, the issue of market-based versus non-market-based sources of finance were discussed without any concrete outcomes. However, should the above draft decisions be adopted at Warsaw alongside a decision on verification, some of the major obstacles to verification and therefore results-based payments and REDD+ implementation could be solved (41).
Two emerging topics and their relation to climate change were also discussed at Bonn: agricultural activities and high-carbon ecosystems. As a main driver of deforestation internationally, the inclusion of agricultural activities on the UNFCCC conference agenda is of interest for future progress on REDD+. The Parties agreed to define the scope and role of agriculture in mitigating and adapting to climate change. A technical workshop on the issue is being prepared and will be held at COP19 with the aim of producing a draft text for future negotiations.
Deforestation rates of tropical peatlands and mangroves are among the highest of all tropical forest ecosystems globally. The question of high-carbon ecosystems, such as mangroves and peatlands, is therefore gaining traction within the UNFCCC. Expert-provided technical information is being collated in order to formulate international level policies for the protection of such ecosystems. These recommendations will be discussed in Warsaw.
Read the full draft conclusions of the SBSTA 38 on methodological guidance for REDD+ here.
Read Addendum 1, recommendation of the SBSTA, Draft Decision -/CP.19, Modalities for national forest monitoring systems here.
Read Addendum 2, recommendation of the SBSTA, Draft Decision -/CP.19, The timing and the frequency of the summary of information on how all the safeguards referred to in decision 1/CP.16, appendix I, are being addressed and respected here.
Read Addendum 3, recommendations of the SBSTA, Draft Decision -/CP.19, Addressing the drivers of deforestation and forest degradation here.
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