Reducing greenhouse gas emissions from deforestation: No hope without forests - Environmental Audit Committee Contents


Memorandum submitted by the Royal Society for the Protection of Birds (RSPB)

INTRODUCTION

  1.  The RSPB considers that human-induced climate change poses the biggest long-term threat to global biodiversity. To avoid a catastrophe for wildlife, anthropogenic greenhouse gas emissions need to be cut hard and rapidly, with global emissions peaking within the next ten years and then declining steeply.

  2.  In any international regime to combat climate change, forests have a vital part to play. Emissions from deforestation, mainly in tropical countries, account for about one fifth of all emissions, roughly the same as the USA or China. Uptake of carbon dioxide by forests is, after the oceans, the most important natural mechanism for removing carbon dioxide from the atmosphere. By conserving and enhancing forests we can both decrease carbon dioxide emissions to, and increase removals from, the atmosphere on a huge scale.

    (i) The RSPB therefore strongly supports the initiative by Papua New Guinea and the Coalition for Rainforest Nations to build into the international, post-2012 regime a mechanism for reducing emissions from deforestation and degradation in developing countries (REDD).

    (ii) Recongising that tackling emissions from deforestation is likely to cost in excess of US$10billion per year, we consider that the mechanism should either be market-based or market-linked.

    (iii) If a REDD regime is to begin in 2013, considerable effort (and money) must be expended on building capacity in developing countries with forests. At present, far too little money is forthcoming. Despite vocal support for REDD development, particularly from the UK government, rhetoric has not been followed up by new funding. We believe there is a need to review the UK's funding plans for REDD activities, to ensure that these are commensurate with the scale of the challenge, timely, and managed in a way appropriate to the needs of recipient countries.

    (iv) REDD has now been under negotiation in the UN Climate Change Convention process for nearly three years; the negotiations are well advanced and no nation has opposed the REDD concept. There is thus a strong case for fast-tracking REDD in the international process.

  3.  Finally, the RSPB has concerns about the certification of voluntary carbon offsets from UK forestry. It would be difficult to determine carbon "additionality" in relation to such activities, ie to be confident that they would not have happened without funding from the sale of offsets.

THE ROLE OF FINANCIAL MECHANISMS

  4.  We consider that financial mechanisms have a key role to play in protecting and enhancing natural forests, depending upon where such mechnisms are located and how they are constructed. We see mechanisms established jointly by governments in the form of international regimes as the way forward, because these provide the scale of both geographical coverage and finances needed to do the job, whilst potenially providing a regulatory framework to guard against perverse outcomes. We do not see private markets as playing a significant role, although they might help in some niche areas.

  5.  Currently, the pre-eminent prospective mechanism for protecting and enhancing forests is Papua New Guinea's initiative in the UNFCCC on reducing emissions from deforestation and degradation in developing countries (REDD). Negotiations on this subject are well advanced and, since the 13th conference of parties (COP13) to the UNFCCC in Bali last year, includes not only deforestation but also enhancement of carbon stocks (potentially afforestation, reforestation and sustainable management) and probably also a compensating of rewarding countries that are not currently deforesting significantly, such as Surinam, Guyana and the Democratic Republic of Congo. The REDD regime thus has the potential to cover all aspects of tropical forestry and we therefore focus on this subject in this submission.

  6.  Currently there are three main types of financial mechanism being discussed for REDD: a market-based approach, a market linked approach and a fund. The market-based mechanism, advocated by Papua New Guinea and the Coalition for Rainforest Nations would involve nations setting a baseline, based on historic emissions, and generating credits for any reduction below the baseline which could be traded in the Kyoto market, or its successor. At the opposite extreme is a fund, proposed mainly by Brazil, into which developed countries would pay and the money would be disbursed to countries that reduced their emissions, again below a baseline. There are several market-linked proposals that would use money generated by a carbon market but would not be directly linked to it. For example, a developed country emission allowances might be auctioned and the proceeds used to pay for reducing emissions from deforestation.

  7.  For us, a key factor is the choice of a financial instrument is whether it is likely to deliver money on the scale necessary to address the drivers of deforestation worldwide. Stern estimated that tropical deforestation could begin to be addressed at a cost of US$10 billion per year, although many consider this figure to be conservative. To deliver finance on this scale, we some no option but to employ either a market-based or a market linked mechanism. We do not envisage a voluntary fund delivering anywhere near this amount of money.

THE ENVIRONMENTAL AND SOCIAL RISKS AND BENEFITS OF USING FINANCIAL MECHANISMS

  8.  There are potential environmental and social risks associated with all of the mechanisms mentioned above and any agreement should contain safeguards for biodiversity and both indigenous and local people.

  9.  In market-based approaches the most commonly perceived risk, expressed by many indigenous peoples groups, is that entrepreneurs will purchase their forest from under the local people and then try to throw them out, as has happened so often in the past. This is a reasonable fear, although not one that would necessarily occur due to implementation of an international REDD regime. The type of market-based system envisaged by most governments would involve trading between states, as in the Kyoto Protocol's emissions trading scheme, rather than trading between private commercial entities. Whether there was domestic market would be entirely up to individual governments. For example, Papua New Guinea is a main proponent of a market based approach but has said that it might take the revenues from an international market and put them in a trust fund; which would fund local communities to conserve their forests in perpetuity. A state-based trading scheme does not therefore necessarily presuppose any particular domestic mechanism, which could comprise a fund, a trading scheme, straightforward regulation or a combination of these. The EU, for example, is a participant in the Kyoto Protocol's cap and trade scheme but it has chosen to achieve some emission reductions via the EU emissions trading scheme, some by regulation and much by various different forms of mechanisms in member states.

  10.  International funds offer the prospect of fairly and equitably delivering money to where it is needed but, in practice, have a very poor record of doing so. Also, governments have a poor record of giving substantial sums of money to voluntary funds, certainly not US$10billion per year for many years into the future. A hybrid approach, such as a fund using money raised by auctioning emission allowances might get around this problem but the difficulty in establishing a fair and equitable distribution system would remain to be solved.

THE USE OF LAND USE CHANGE CREDITS IN CARBON MARKETS AND IN MEETING EMISSION TARGETS

  11.  A clear potential difficulty of any market-based approach to REDD is that it may lead to the market in emission reduction allowances from developed countries being flooded with cheap, offsetting forestry credits. This would not only have the effect of reducing the amount by which developed countries reduce their emissions at home (and hence put at risk their timely transition to a low carbon economy) but it would not serve REDD well either. To displace lucrative drivers of deforestation, such as conversion to oil palm plantations, a high carbon price of at least $20 or $30 per tonne carbon dioxide is required, more with a biofuels boom.

  12.  There are several ways of avoiding this difficulty. The simplest is for developed countries to take on substantial emission reduction targets of which a proportion could be met using REDD credits. For example, if developed countries were to take on 40% emission reduction targets by 2020 from 1990 levels, in line with climate science (as expressed in the IPCC's fourth assessment report) then 5 or 10% of this target might be achieved using REDD credits. This type of arrangement might be formalised in several different ways, as outlined by Papua New Guinea and some NGOs, notably Greenpeace and the Centre for Clean Air Policy.

  13.  Fund-based options, including market-linked ones, generally avoid this difficult although they can present different problems, as outlined above.

THE WORLD BANK'S FOREST CARBON PARTNERSHIP FUND

  14.  We see the FCPF as filling a potentially useful role in building developing country's capacity to implement a REDD regime, in advance of a REDD regime coming into force in 2013. In setting up the fund, the Bank consulted widely with both developing countries and NGOs, including the RSPB, although we suspect that they might not have done so as thoroughly had the German Presidency of the G8 insisted on it.

  15.  However, we have a number of reservations about the FCPF. The first is that the sums of money available are small in relationship to the scale of the task. When split amongst the many countries that could be eligiable for REDD, there will be only a few million US dollars available for each country spread over a period of four years, far too little to build capacity adequately in the largere countries such as Brazil, Indonesia or the Democratic Republic of Congo and arguably not even enough for small countries. We are encouraged that the amount of funding looks as though it may increase by a factor of four (to about $1 billion) but even that is barely sufficient.

  16.  We are also concerned that much of the money available from the Bank may be in to form of concessional loans. Whilst such loans may be suitable for the activities that the Bank usually funds, and we can understand concerns by developed countries about giving money to emerging economies, loans are poorly suited to capacity building.

  17.  We are also concerned about the overall modus operandi of the Bank and, indeed, the UK's faith in it to deliver environmental objectives. The Bank is set up as, and operates as a bank. It has considerable experience in making loans, with a good return to its investors countries, and has generally good, or at least well developed, relationships with finance ministries Worldwide. Like all banks, however, it is less good at giving money away and has poor or non-existent relationships with environment and forestry ministries. As a consequence, many such ministries in developing countries dislike and distrust the Bank. A number of major forested countries have expressed to us a clear preference for direct bilateral assistance from the UK where, in contrast, DfID has a good record of forest-related assistance.

THE ROLE OF TECHNOLOGIES IN THE VERIFICATION OF LAND USE CHANGE CREDITS

  18.  It is generally agreed in the UNFCCC negotiating group on REDD that remote sensing has a key role to play in assessing deforestation, where forest has been clear cut, although it is universally recognised that remote sensing must be accompanied by "ground-truthing", ie ground-based measurement.

  19.  Since Bali, however, degradation has been included in the REDD discussions and, at present, remote sensing is probably not adeaquate for assessing degradation which would depend considerably on ground-based measurement. There is the prospect of assessing degradation remotely but, for the near future, accompanied by a significant amount of measurement on the ground. It should be stressed that the difficulties associated with ground measurements are often overexagerated and that once a system is established it is not onerous to maintain it.

THE CONGO BASIN FOREST FUND

  20.  Whilst we welcome the Government's introduction of a special fund for the Congo Basin, the amount of money in it is inadequate (£40 million over three years). The Congo Basin countries are a special case amongst the rainforest nations, in that most of them are not deforesting significantly at present, many of them are very poor with weak governance and, consequently, need significant amounts of capacity building if they are to successfully implement REDD. Indeed, it is questionable whether many of the nations would be in a position to implement REDD as early as 2013. A reliable means therefore needs to be found for building capacity over the medium term.

  21.  With some of the northern South American countries, such as Guyana and Surinam, many of the Congo Basin countries are not deforesting significantly at present, although there has been significant degradation in some. They thus pose a difficulty for a REDD regime in that a system that pays for reducing emissions from deforestation might encourage nations with low deforestation rates to increase them in order to be paid for stopping again. A means of avoiding this perverse incentive might be simply to artificially skew the baselines of such countries to indicate a fairly high deforestation rate, even when there is not. If done in an open and transparent way, this approach might well work but other solutions are still being sought.

THE INTERACTION OF CARBON FINANCE MECHANISMS WITH THE TIMBER TRADE

  22.  Since the major climate change meeting in Bali last year, REDD now includes not just deforestation but also enhancement of carbon stocks and hence afforestation (plantations) and reforestation (restoration of natural forest). Therefore, assuming that REDD is market-based or market-linked, there will inevitably be and interaction with the timber trade—because REDD will cover all, or nearly all, tropical timber production.

  23.  If successful, a REDD regime should increasingly slow and, eventually halt, the extraction of timber from natural forests, and hence any trade in it. However, Timber could still be produced from plantations. In many parts of the World, especially South East Asia, natural forests are destroyed not so much for the value of their timber but as part of the business model for oil palm production. The trees are cut and sold to provide "upfront" cash for establishing oil palm plantations whilst millions of hectares that are already clearcut or degraded remain unused. The situation is often similar, if more complex, in Latin America where soya production often displaces cattle ranching which displaces forest. The relative costs of different activities are evident in such processes: soy is lucrative, cattle ranching less so and, at present, natural forests are almost worthless. An effective REDD process would value forests at a higher level that the activities that currently destroy them.

EU FOREST LAW ENFORCEMENT, GOVERNANCE AND TRADE (FLEGT) ACTION PLAN

  24.  We support the EU initiatives on illegal logging and both we and our BirdLife Partners in developing countries have participated actively in them. However, they are limited in their scope because of inadequate funding and so, whilst they have both helped to prevent illegal logging and helped local communities, they have made limited inroads on the problem as a whole.

  25.  To be successful, REDD would have to halt illegal logging as a necessary step on the way to halting emissions from deforestation.

CARBON OFFSETS IN UK FORESTS

  26.  The RSPB has concerns about the certification of voluntary carbon offsets from UK forestry. It would be difficult to determine carbon `additionality' in relation to such activities, ie to be confident that they would not have happened without funding from the sale of offsets. The RSPB considers that a key climate change issue in the UK is reducing emissions from society at source, rather than afforestation in the UK, to mitigate a small proportion of the UK's greenhouse gas emissions.

  27.  The UK's importation of timber and wood products from environmentally unsustainable managed sources outside the UK, including high conservation value boreal and rainforests, is of great concern. This is for reasons of irreparable biodiversity loss and damage, as well as the climate change impacts of such forest loss and degradation.

  28.  The RSPB welcomed the UK Government and devolved administrations' initiative at the 2002 World Summit on Sustainable Development on timber procurement, forest conservation and certification. We have concerns about the quality and robustness of the subsequent definition of environmental "sustainability" of timber that has been developed. Using "CPET" guidance, for the UK, country and local government procurement. This concern also includes the impact on the environmental quality of UK woodland management, and its credibility of proposals for simplified statements of sustainability under CPET "Category B" for timber/wood product specifiers and procurers. Meeting the UK Forestry Standard must be a minimum requirement for CPET Category B compliance, backed up by robust auditing by Forestry Commission and Forest Service Northern Ireland.

  29.  The devolved forestry policies of the UK must continue to promote sustainable multi-benefit forest management, including through EU co-financed land management grants. All new woodland planting must be appropriately located, designed and managed to enhance, not damage, important biodiversity, such as wetland sites, semi-natural grassland, wader areas, peatland, heather moorland and coastal dune systems. Existing woodlands—native woods and forestry plantations—must also be managed to protect and enhance priority biodiversity.

  30.  The RSPB supports the removal of recent forestry plantations from restorable important semi-natural habitats, such as blanket and raised peat bogs and lowland heathland. This is to meet the UK's and devolved administrations' country, UK, EU and International biodiversity commitments for wildlife species, habitats and designated nature conservation sites.

  31.  It is imperative that rigorous standards and guidance for UK forestry are developed, to ensure that the carbon offsets industry and carbon customers have the proper level of quality assurance for both carbon and sustainability. RSPB would expect the development of any standards and their certification to be open, and inclusive—reflecting environmental as well as economic and social interests. This could build on the existing mandatory UK Forestry Standard and the voluntary UK Woodland Assurance Standard (which meets international sustainable forest management criteria).

  32.  Carbon standards for UK land management must be based on robust science, ensure genuinely additional carbon benefits, ensure that any future banked carbon is safeguarded, be transparent and independently verified by accredited auditors, be consistent with sustainable forest management policy and practice, meet biodiversity policy and practice needs.

  33.  The RSPB does not accept that so called "compensatory" planting in the UK is an appropriate mechanism to increase the UK's woodland area for climate change mitigation reasons. Targeted grants for high quality woodland expansion and management in the UK should be strategically employed, assisting with climate change adaptation for native woods, instead of a project-based "compensatory" planting approach.

  34.  We would welcome the introduction of forest management measures in the UK to reduce unnecessary green house gas emissions from UK forest operations, and help improve sequestration and storage, when consistent with the principles of sustainable multiple benefit forestry including biodiversity conservation.

October 2008





 
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