Abstract
The chapter begins by suggesting that sustainable management has rarely been achieved in forests in the developing world not because the technologies for sustainable forest management are not viable, nor because resource managers do not recognize or understand the concept of sustainability. Rather, failure can be attributed to the fact that much of what happens in forests is determined by decisions made far from the forests sector, and to the fact that many of the actors in the forest sector (or nearby) are operating under perverse incentives.
Attempts to quantify the non-marketed ecosystem values of forests have encountered major methodological problems, while the impacts of macroeconomic policies on forests vary considerably from one place to another, and there has been little fieldwork on this subject in specific locations. These constraints, added to the observation made in Chapter 6 that development assistance financing has not been adequate to value sustainable management highly in the eyes of the agents of forest change, illustrate the difficulty of implementing sustainable forest management in the recent past.
Climate change, and increasing global awareness of the fragility of natural ecosystems is the potential game-changer here, and the remainder of the chapter explores the issues surrounding the reduced emissions from deforestation and forest degradation (REDD) mechanism which could finance sustainability via carbon emission trading from reduced deforestation, and an alternative approach based on public/private sector financing of forest ecosystems which does not rely on a specific trading mechanism, but does nevertheless apply value to retained forest carbon, among other assets.
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Notes
- 1.
Rapid expansion of soya growing in Brazil, or oil palm plantation in Southeast Asia (both discussed in Chapter 5) are examples.
- 2.
A number of climate scientists – notably James Hansen of NASA – have argued that even this figure will be inadequate to provide reasonable amelioration of some of the worst potential consequences of climate change, and that reductions in GHG concentrations down to the range of 330–380 ppm will need to be attained to achieve this.
- 3.
A gigatonne is equal to one billion tonnes.
- 4.
Peat is formed when plant material in marsh or swamp areas is subjected to limited decay under anaerobic conditions from a limited decay process when plant material in marsh or swamp areas.
- 5.
The FAO Trade and Markets website has index figures for oil seed prices that show prices rose by a factor of 3 from 1998–2000 (the index base period) to 2007, before falling back to 2 in 2008, in response to the international financial situation.
- 6.
There is also the question of who receives the value of logs which would have been harvested from the forest site prior to conversion to the competing commodity: we discuss this issue in the case study below.
- 7.
Fairhurst, Thomas, pers comm. February 2009.
- 8.
In Indonesia in recent years, adherence to rules of use for land in various forest categories has improved, and some provisions have been tightened. However, there have also been significant changes in the boundaries of the various forest categories, with allocations of forest land to the Conversion Forest category (and thence to licensing for other non-forest uses by Kabupaten governments) in particular growing considerably, at the expense of the Production Forest and Limited Production Forest Categories.
- 9.
What carbon prices may do on world markets in the immediate term is anyone’s guess, as the economic crisis continues to influence all markets, and some governments put green investments on hold. However, even in the midst of this, prices (which reached figures of more than € 40 per tonne of CO2 equivalent in 2008) seem to be holding at around 8 € per tonne of CO2 equivalent: this is about double the carbon dioxide price used above.
- 10.
World Bank, 2005 Development Policy Lending and Forest Outcomes, Report No. 33537-GLB.
- 11.
Apart from being restricted essentially to forestry options based on reforestation and afforestation, rather than avoided natural forest reforestation, the CDM has been criticized for a complicated verification and implementation framework, and it has not been widely utilized ion many developing countries since its inception.
- 12.
Unless it can be argued that the country has chosen to revert not merely to previous higher levels, but to even higher levels than would have occurred under a business-as-usual scenario without REDD. That would be an abrogation of that nation’s understanding with the REDD partners; it could happen, but then, it could happen at any point under any form of agreement. There is an element of faith in the REDD process: it assumes that nations which participate in the process will see the benefits – economic, social and environmental – from being in the programme.
- 13.
The Prince’s Rainforests Project was established by the Prince of Wales in 2007, with the aims of encouraging consensus on how the rate of tropical deforestation might be slowed, and to design a mechanism by which rainforest nations could be compensated for reducing deforestation.
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Douglas, J., Simula, M. (2011). Financing Forests Sustainability from Ecosystem Values. In: The Future of the World's Forests. World Forests, vol 7. Springer, Dordrecht. https://doi.org/10.1007/978-90-481-9582-4_7
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