The two most serious threats to the conservation of the Amazon's biodiversity are climate change and deforestation, both of which will be greatly stimulated by IIRSA and PPA investments. Deforestation and forest degradation are fully underway along the margins of the Amazon. IIRSA and related initiatives will lead to the further fragmentation of the Amazon, accelerate forest degradation in the Andes, and complete the conversion of the Cerrado savannas to cropland.
Without a radical change in the nature of modern development, efforts by governments, financial institutions, and civil societies to limit the degradation will be unsuccessful. Regional and global markets will continue to dominate the dynamic on the agricultural front, and standard remedies for slowing or limiting deforestation will have little chance of success. Although sustainable development has been promoted as a philosophical framework to reconcile development and conservation, it has, in practice, only ameliorated the most egregious aspects of development and has had no substantive impact on slowing the rate of tropical deforestation (Figure 7.1).
Under the best of circumstances, protected areas and indigenous reserves will be consolidated to function as biological reserves. However, it is unlikely that more than 30–40 percent of the land surface in the Amazon will be set aside for this purpose. In addition, indigenous and extractive reserves will face increased degradation unless the so-called sustainable forestry model is significantly modified or communities choose to opt out of that exploitation alternative. Outside of the protected area and indigenous reserve systems, the landscape will be subject to the inevitable forces of the market.
Policies to slow deforestation on privately held land over the past 20 years have depended on improving “governance,” but unfortunately, these have been largely—if not entirely—ineffective. The two most common approaches have been 1) to invest in land use planning studies that promote forest management, and 2) to promulgate regulations that require landholders to retain a specified amount of their land in natural habitat.88 Deforestation, however, continues at near-record levels, and Brazil's recent report that the annual rate of deforestation has fallen is probably a shortterm phenomenon caused by weak international commodity markets rather than the success of government policies to suppress land use change. Landowners routinely ignore requirements to maintain a certain percentage of a property in forest cover. Similarly, regulations that prohibit land clearing along water courses and on steep slopes to create environmental easements are either ignored or unknown. Despite limited success to improve forest management most timber originates from the agricultural frontier where forest landscapes are cleared of their timber resources before the land is converted to crops or pastures. Some analysts are hopeful that the current trend to decentralize administrative responsibility to regional and municipal governments will decrease deforestation. They believe that local governments will be more effective at convincing land holders to conserve forest, limit the use of fire, and avoid the overexploitation of terrestrial and aquatic ecosystems (Nepstad et al. 2002). Although improving local government is a laudable goal, it is unlikely that private landholders will react differently to overriding market conditions, or that local governments will be less corrupt or any more attuned to environmental issues than national governments (Fearnside 2003).
Landholders will always act to maximize their own economic benefits, and no amount of regulation will successfully alter that behavior. Landholders will also probably dominate local government and its policies. In the developed world, the right of the landowner to manage private property is considered a foundation of a free market economy and a basic element of human nature. It is unreasonable to expect Amazonian landowners, most of whom come from this cultural tradition, to believe or behave differently, regardless of legal systems that seek to control the exploitation of the natural resources in the national interest.
If markets are destined to prevail and statutory land use regulations prove ineffective, then alternative approaches for saving the Amazon must be developed and implemented that recognize the predominance of the market, or society must accept the fact that most of this forest will eventually be degraded. One approach is to recognize the predominance of markets and to manipulate them through regulatory mechanisms that have been effective in other regions of the world. Almost all markets are regulated to some degree, to avoid extreme situations that are characterized as an abuse of the marketplace. As recent history has shown, unregulated land and commodity markets will eventually lead to the complete deforestation of the Amazon, which can logically and appropriately be considered an abuse of the marketplace.
Market regulations take many forms, but the most effective are those based on financial incentives that motivate individuals to choose voluntarily what is in their shortterm economic interest. In North America, Europe, and Japan, subsidies and tax incentives guide land use and promote certain production activities. Agriculture is the most obvious example of how subsidies maintain a land use that would not otherwise be economically competitive. Countries with agricultural subsidies argue that they are necessary to ensure traditional activities, essential to their economy, and provide social welfare to an important sector of the population. This argument applies equally well for the conservation of the Amazon forest ecosystem. Brazil and the Andean countries have recognized that the conservation of the Amazon is a strategic priority. Combine this with the even greater strategic priority for economic growth to improve the social welfare of their populations, and it fully justifies the use of direct and indirect subsidies to ensure investments and activities that promote economic growth while simultaneously conserving the Amazon ecosystem.
The challenge is to find a source of revenue large enough to finance the requisite subsidies. Equally important is to identify economic models that produce goods and services while also avoiding deforestation. Fortunately, the growing recognition that ecosystem services have real market value is creating an opportunity to finance this new development paradigm. Key policy options must be elucidated and selected over the next decade to generate the revenues and to ensure a framework that delivers the right economic incentives to the individuals who live and work in the Amazon.
Below are some recommendations for policies and mechanisms that would provide a new development paradigm for the Amazon. This list is by no means exhaustive or particularly novel, but it identifies opportunities for reducing deforestation while addressing the major impediments to sustainable development in the Amazon, Cerrado, and Andes.
RAISING THE MONEY: MONETIZING ECOSYSTEM SERVICES
There is now worldwide concern over global warming and awareness that the conservation of tropical forests can partially mitigate this threat. Given this context, a framework for the transfer of funds from developed nations to developing countries with threatened tropical ecosystems can serve as one source of revenue for conservation and subsidize development that is truly sustainable. The bulk of this revenue would come from carbon credits, which will eventually be implemented under reformed rules of the United Nations Framework Convention on Climate Change (UNFCCC 2006).
Carbon credits would be earned by reducing emissions from deforestation and forest degradation (REDD according to UNFCCC terminology). For example, lowering the annual deforestation rate in the Amazon basin by 5 percent would generate approximately $650 million in the first year of a multiyear commitment; amounts would multiply dramatically as avoided emissions increased over 30-year commitment periods (see Appendix, Table A.3).
For countries with currently high levels of deforestation, reductions would be calculated on the basis of historical deforestation; other countries would negotiate a different compensation package so as not to be penalized for past (or recent) low levels of deforestation.
The issue of leakage— the displacement of existing emissions to other regions rather than actual reductions—would be managed by setting deforestation reduction targets at the national level. Consequently, shifts in land use within a country would cancel each other out or, more optimistically, add up.
Reforestation and afforestation projects need to be greatly increased in developing countries to restore ecosystem function on previously degraded landscape. Current rules within the Clean Development Mechanism (CDM) have not fostered carbon sequestration in many countries because of implementation and certification burdens. Many of these measures were imposed to address concerns that carbon credits derived from reforestation projects might perversely stimulate the drivers of deforestation. The past decade has demonstrated, however, that this is not the case, and reforestation projects in the developing world have subsequently lagged.
National commitments to reduce emissions from deforestation (RED) and sequester carbon (CDM) within the confines of the UNFCCC could be complemented by individual projects financed via voluntary markets with a less stringent certification process than the UNFCCC, especially when these bring strong benefits for biodiversity conservation and human welfare. Voluntary certifications could be fortified by adhering to the standards outlined in the Convention on Biological Diversity and the Millennium Development Goals.
Carbon credit compensation schemes should be designed and managed by the governments of sovereign states as part of their national strategy to reduce carbon emissions. Some countries may adopt market mechanisms, whereas others may choose to create compensation funds that are replenished from both the private and public sectors.89
In recognition of the fact that their agricultural production and hydropower depend partially on the Amazon, the Southern Cone countries of Argentina, Paraguay, and Uruguay join Brazil in making payments for ecosystem services according to the percentage of water each Mercosur nation receives from the Amazon and its degree of economic development.
A FAIR EXCHANGE: ECOSYSTEM SERVICES FOR SOCIAL SERVICES
Frontier populations rank education and health care as their two most important needs; thus, direct economic subsidies that link forest conservation to social services would create a powerful local constituency for conservation. To reduce deforestation, each nation must involve the actors responsible for deforestation and monitor the efficacy of the program on an annual basis. Although the administration of economic subsidies will vary among countries, resources and benefits must flow to local communities, regardless of the mechanism selected. Because local governments are usually responsible for providing essential social services, they are logical candidates for administering these programs (see below).
Transfer payments to local governments for carbon credits and other ecosystem services should be dedicated to improving education and health care.
Payments for ecosystem services would not be entitlements. Positive incentives in the form of increased budgets could be used to reward communities for going beyond commitments, while communities that fail to meet commitments would face budget reductions.
A similar mechanism to reduce forest fires could generate additional carbon-based revenues. A reduction in fire would benefit forest management, local health, and contribute to more robust rainfall regimes.
QUID PRO QUO
Although ecosystem services can provide an important new source of national revenue, individual nations may need additional incentives to enter into ecosystem services agreements. In particular, Brazil and the Andean nations may be resistant to participate in mechanisms that seem to limit their sovereignty over the natural resources of the Amazon. To make participation politically palatable, compensation systems related to ecosystem services could also relate to other national priorities such as commerce and international security.
Agricultural subsidies in Europe and North America are a major point of contention in world trade talks. Brazil is a leader among developing countries in contending that agricultural subsidies must be reduced if commerce in industrial goods and services is to be liberalized. Shifting subsidies from domestic agriculture to forest conservation via reduced emissions from deforestation would limit agricultural expansion in the Amazon and indirectly protect European and North American farmers.90 Brazil would open its markets to industrial goods and services, while developed countries would open their markets to food and biofuels from Brazil.
Global climate change represents a real and present threat to the planet's security—one that the collapse of the Amazon ecosystem would dramatically exacerbate.91 Although the United Nations Security Council has not traditionally addressed environmental security, an increase in climate-related natural disasters has highlighted the vulnerability of the planet. Recognizing the importance of the Amazon to global security would provide additional weight to Brazil's petition for a permanent seat on the Security Council.
In the Manaus Free Trade Zone, international companies have demonstrated a willingness to invest in an Amazonian urban center when offered tax advantages and lower tariffs. This could be used as a model for manufacturing and commercial centers in other regional cities, providing an alternative to development based solely on natural resource exploitation. Any such initiative must also include incentives for technology transfer so that these centers evolve past the initial assembly line (masquilladora) stage of development.
SUBSIDIZING ALTERNATIVE PRODUCTION SYSTEMS
The inhabitants of the Amazon need and deserve increased economic opportunity. Revenues generated by the monetization of ecosystem services could subsidize production systems that both stimulate economic growth and remain compatible with forest conservation. A number of systemic constraints to economic growth exist in the region. The most important is the insecurity of land tenure, followed by poor transportation systems, the absence of affordable credit, and a lack of reliable energy supplies. Current development models provide no adequate solutions for any of these impediments and tend to promote deforestation. The following alternative models conserve ecosystem services and could replace the existing models if markets are effectively regulated and are accompanied by subsidies to counterbalance existing market forces.
People by Air and Cargo by Water
As an alternative to highways that degrade and fragment the Amazon, the countries of the region could adopt a bimodal transportation model that uses airlines and river barges. This system could complement a limited highway network envisioned by IIRSA, but would erase the need for other projects promoted by national and state transportation ministries.92 As part of a modified IIRSA investment program, it would provide cost-effective alternatives for transporting people and commodities.
Airline and barge companies could be supported indirectly by tax abatements, as well as subsidized fuel prices and below-market interest rates for capital investments. Services to remote areas could be directly subsidized by cash payments to ensure reliable and regular services.
Air service could promote regional integration by offering cross-border flights without routing through capital cities or large regional hubs.
A greatly expanded air service would benefit the tourism industry by opening up remote areas, which would have the added benefit of reducing the environmental impact on areas with high tourist loads.
A subsidized river transport service would provide a costeffective solution for moving bulk commodities (i.e., timber, grain, minerals, and biofuels).
Land Tenure for Conservation
Reformed land tenure systems are central to stopping deforestation. People seeking land tenure are one of the principal causes of deforestation because the current titling process rewards land tenants who deforest lands and it castigates those who do not. The goal would be to maintain a forest matrix by subsidizing land use models that follow the 80:20 (forest:cultivated land) rule stipulated by the Brazilian Forest Code.93 Both governmental regulations and market-based economic incentives are needed to ensure that intensive production systems are linked to forest conservation.
Enterprises that agree to a contractually binding ratio of 80:20 in perpetuity would enjoy an expedited titling process.94
The state would distribute land by commercial transactions rather than land grants, and the terms of the mortgage would stipulate the 80:20 land use ratio.
In heavily deforested landscapes, access to low-interest credit and expedited land titles would be offered to enterprises that agree to plant trees to meet the 80:20 land use rule.
Enterprises that agree to the 80:20 land use rule would have access to low-interest loans to implement highintensity production models (see next section).
Compliance with the 80:20 land use rule would be monitored with remote sensing technology and with land registries managed by local and national governments. Failure to comply would lead to an immediate revocation of credit and the reversion of land to the state.
Economic Growth and Job Creation
Intensive production needs to predominate on landscapes that have been converted to agriculture, livestock, or tree plantations. 95 This production must ensure long-term sustainability and be diversified to ensure economic stability in fluctuating international commodity markets. Subsidized credit, transportation, and energy are paramount and should be considered as legitimate components of Amazonian production models; however, producers must provide commercially attractive goods and services that are competitive in real markets.
A diversified tourist industry could focus on ecotourism, but it would also include sport fishing, cultural tourism, adventure leisure activities (water skiing and scuba diving), and luxury cruise lines.
The tourist industry should be democratized by involving local communities as shareholders in new enterprises. Subsidized credit can be given to enterprises that enlist local communities as shareholders.
Fish farming should be promoted as the primary production system in the Amazon.96 Water is the region's most abundant and valuable resource and should form the foundation for its economic growth. Fish farming is the most efficient method of converting vegetable matter to animal protein and can be organized into small units managed by families.97 It can also be a key component in a production chain that links the granaries of Mato Grosso and Santa Cruz with overseas markets.98
Tree plantations in previously deforested regions will sequester carbon while also creating an economic resource over the medium term. Subsidies in the form of low-interest loans, technical support, and direct payments can be used to reforest landscapes.
Mineral and hydrocarbon exploitation will continue to be important sources of revenue for national economies. 99 Royalty revenues from these activities should be used to secure additional resources from deforestation avoidance initiatives; for example, hydrocarbons are often produced within protected areas, so a portion of the royalties could be used to finance the management of the protected area. This would link fossil fuel production to positive actions that will reduce greenhouse gas emissions.
Nonresource-dependent economic models need to be created to diversify the region's economy; the example of Manaus as a free trade zone that developed a high-tech industry should be duplicated in other Amazonian urban centers.
Innovation in Energy
Economic growth requires energy. The remoteness of the Amazon increases the cost of traditional fossil fuels, creating both challenges and opportunities. Clean energy should be the paradigm for production systems that are subsidized by ecosystem services payments, and the Amazon can create opportunities for strategic partnerships in the research, development, and commercialization of alternative energy.
Solar power will be the most competitive option for most remote localities with moderate energy needs; investments in this technology could be subsidized by ecosystem service payments.
Tax abatements, tariff preferences, and direct subsidies should be provided to multinational corporations that establish solar panel manufacturing facilities in Amazonian urban centers.
Because water is the Amazon's most important natural resource, hydroelectric power will be an important component of the energy model. The potential for hydroelectric power in the Amazon is enormous, but facilities should not be constructed on the major tributaries of the Amazon (e.g., Madeira and Xingu) in order to limit the impact of dams on aquatic ecosystems.
Biofuel crops, including African oil palm to produce biodiesel and elephant grass to produce cellulosic alcohol, will probably be the most successful agricultural enterprise in the Amazon. Locally produced biodiesel could provide an economically competitive source of fuel for the barge industry.
Although the cultivation of biofuel crops probably poses the largest single future threat to the Amazon, this threat can be mitigated by requiring the 80:20 land use model and—most importantly—subsidizing biofuel production on previously deforested, degraded landscapes.
Propane and butane (i.e., liquefied petroleum gas—LPG) are usually abundant in natural gas fields and provide an energy-rich, clean, and portable fuel source. Although LPG is separated out at refineries and sold as subsidized fuel to urban populations, small gas plants can be built in the Amazon, and LPG can become one of several energy options.
Fossil fuels for the airline industry will have to be subsidized to support the people-by-air cargo-by-water transportation model; however, technological innovation should eventually allow for the conversion of vegetable oils to produce kerosene and aviation fuel.
HARNESSING THE POWER OF LOCAL GOVERNMENT
Statutory regulations have been ineffective because they have been isolated from market mechanisms. Similarly, economic incentives will be insufficient to change the development dynamic in the Amazon if they are implemented in a lax regulatory environment. Subsidies are easily abused, and strong institutions are required to ensure that market forces operate as intended. Thus, all the subsidies and market mechanisms proposed here are linked to regulatory requirements, particularly the 80:20 land use rule that offers one of the few realistic options to limit deforestation. Most laws and regulations are initiated at the national level, but municipal and regional governments have an important and growing role in enforcement. The conservation of the Amazon will depend on a large extent on the capacity of local governments to fulfill their role as public institutions.
Land title registries must be a priority investment across the Amazon region. Questionable land tenure is a source of violence and corruption in frontier areas. Local governments must create and maintain rural and urban land registers as the foundation for long-term growth and good government. Land tenure would be the basis for local taxes, and access to credit would be granted on the basis of the patrimonial value of land.
Independent watchdog agencies must be established to monitor deforestation, and municipal governments will need remote sensing and geographic information system (GIS) capacity to enforce bans on deforestation and fires. In Brazil, this capacity exists at the national level and has recently been decentralized in Mato Grosso100; however, no such coordinated effort exists in any of the Andean countries.
Regional universities will need an infusion of investment to support revitalized educational and health systems. Resources channeled to state universities should be linked to governance reforms and support expanded research programs linked to extension and focusing on rural development.101
University-based research will help subsidize and improve intensive production systems, particularly to discover novel uses for the biological and genetic resources of the Amazon and Andes.
DESIGNING CONSERVATION LA NDSCAP ES
In addition to conserving large blocks of the Amazon within an expanded protected area system, it will also be necessary to design and implement “conservation corridors” in strategic areas where transportation corridors are considered requisite for the physical and economic integration of the region. A conservation corridor is a landscape that is designed to promote biodiversity conservation. It consists of protected areas strategically situated within a matrix of different land use types so that species can move and exchange genetic resources. As IIRSA highways are constructed and deforestation belts expand over time, and as global warming brings about shifts in the environmental gradients that control species distribution, the importance of habitat connectivity will become ever more important.
Large blocks of forest must be conserved to minimize the impact of edge effects and to provide sufficient area for the survival of rare species.
The western Amazon should receive special consideration because it is the most biologically diverse region and has enjoyed the most stable climate over millennia.
Although much of the landscape outside of protected areas will eventually become “production forests,” these should be established with timber harvest cycles of approximately 100 years to maintain the essential characteristics of forest wilderness.
Incentives must be developed for communities to conserve forest landscapes adjacent to highways so that wildlife can migrate across these barriers.102
The connectivity between the piedmont and the montane ecosystems of the Tropical Andes Hotspot must be maintained (or restored) to ensure that lowland species can migrate into the foothills in response to climate change.
River Corridors should be another priority because they incorporate moist valley bottoms that will be resilient to future drought, and they protect both terrestrial and aquatic ecosystems. The southern Amazon tributaries (e.g., Xingu, Madeira) will also function as latitudinal corridors.
Topographic features that would offer refuge to lowland species migrating in response to global change should be identified as priority areas for protection; this highlights the importance of the hills, ridges, and valleys of the Brazilian and Guayana Shield regions.
Text Box 7
Protected Areas: Enough Is Enough—or Not Nearly Enough?
The 1990s witnessed the creation of many protected areas throughout the Amazon, with the goal to designate approximately 20 percent of the total surface of each country as some type of protected area, with different levels of natural resource use (IUCN 1994). At the same time, indigenous peoples began to gain the titles for their traditional lands, acquiring about 20 percent of the region, which many conservationists hope will function as surrogate protected areas.
Brazil is still actively expanding its protected area system under a range of categories with flexible development options. Slightly more than 70 percent of Amapá and almost half the area of Pará, Acre, and Roraima states have been incorporated into some form of conservation unit, including indigenous areas and productive forest reserves. Peru has likewise set aside almost half (45 percent) of its Madre de Dios Province, and Colombia has essentially ceded almost all of its lowland Amazon region to indigenous groups (see Figure 5.3 and Tables A.5 to A.7). However, the basin-wide total is still a long way from 50 percent, and even if 50 percent is eventually set aside, the eventual deforestation and degradation of the remaining half is far from an attractive proposition
Many people, particularly in the private sector and the prodevelopment ministries, believe that “enough is enough” and fear that more protected areas will make large regions unavailable for mining, hydrocarbons, and timber. However, conservationists argue that what has been set aside is “not nearly enough,” particularly because parallel efforts to slow forest degradation and deforestation have failed (see Figure 2.1).
These apparently opposed positions will eventually be resolved via democratic processes. It is hoped that both groups will realize that there can be common ground: that a protected area may have multiple uses, that mining and hydrocarbon production do not necessarily have to lead to widespread deforestation, and that logging might be truly sustainable. One hopes, too, that people will see conservation as an investment in the planet's future. Once the natural ecosystem is permanently altered, there is no turning back. If a mistake is to be made, it would only seem prudent to err on the side of caution and be generous with future generations when deciding “how much is enough?”
The Amazon Wilderness Area is facing inexorable changes resulting from economic development and environmental degradation, processes that have already transformed the Cerrado into a vast agroindustrial estate. The tropical forests of the Andes have been subject to a long history of degradation, but in the past this settlement has been characterized by isolation, with small circumscribed regions linked to a single urban area in the highlands; IIRSA proposed to integrate the isolated regions of the Andean piedmont and link them with national, regional, and global markets. IIRSA, the PPA, and other public and private initiatives will amplify the impacts of human migration, agricultural expansion, timber extraction, mining, hydrocarbon production, and climate change. The existing paradigm of sustainable development has failed to arrest deforestation and forest degradation. Unfortunately, traditional development is largely incompatible with conservation because it cannot produce the economic incentives to promote the long-term preservation of natural forest habitat. Efforts to use community-based initiatives to slow deforestation have failed—and will continue to fail—because the ever-expanding Amazon frontier is populated with individuals who make decisions on the basis of their economic interests for the short term. Even the most amenable production systems, such as the current model of sustainable forestry, will lead to the eventual degradation of forest ecosystems and conversion to tree plantations.
The traditional solution of creating protected areas will likely be an integral but insufficient solution because it will encompass only 20–30 percent of the landscape, and these protected areas will become increasingly isolated in a matrix of degraded forest and anthropogenic landscapes. Indigenous lands and extractive reserves offer an important complement to protected areas, but these may be co-opted into the current forest management model unless communities have a more attractive economic alternative. Even if indigenous lands are preserved intact and the protected area system is expanded, they will not exceed 50 percent of the total land surface of the Amazon, even in the most optimistic scenario. That explicitly leaves the remaining 50 percent exposed to the forces of international commodity markets and the search for personal wealth that characterizes modern society.
The Amazon requires a new development paradigm unique to its special characteristics and global importance. This new paradigm must ensure its inhabitants a dignified level of prosperity while making important contributions to the economies of the nations that are custodians of the Amazon. If the Amazon forest is a global asset worth preserving, then it is only reasonable that the custodians be paid for their efforts.
AndersenL. E. 1997A Cost-benefit Analysis of Deforestation in the Brazilian AmazonTexto para Discussão, no. 455Río de JanieroIPEA, Instituto de Pesquisas Econoimicas AplicadaGoogle Scholar
Banco do Brasil 2007PROEX – Programa de Financiamento às Exportações.Online. Available: http://www.bb.com.br/appbb/portal/gov/ep/srv/fed/AdmRecPROEXFin.jspGoogle Scholar
BarthemR. B. M.Goulding 1997The Catfish Connection: Ecology, Migration, and Conservation of Amazon PredatorsNew YorkColumbia University PressGoogle Scholar
BerryM. C. 1975The Alaska Pipeline: The Politics of Oil and Native Land ClaimsBloomington, INIndiana University PressGoogle Scholar
(BOA) Board on Agriculture, Committee on Sustainable Agriculture & the Environment in the Humid Tropics, National Research Council 1993Sustainable Agriculture and the Environment in the Humid TropicsWashington, DCNational Academy PressGoogle Scholar
Bolivia Forestal 2007Preliminar: Exportaciones forestales del 2006 superan los 170 Millones de $US.Cámara Forestal81Online. Available: http://www.cfb.org.bo/NoticiasBF/8.01/boletin.notaBF03.htm. June 1, 2007Google Scholar
Brito-CarreirasJ. M. J. M.Cardoso-Pereira M. L.Campagnolo Y. E.Shimabukuro 2005A land cover map for the Brazilian Legal Amazon using SPOT-4 VEGETATION data and machine learning algorithmsAnais XII Simpósio Brasileiro de Sensoriamento Remoto. April 16–21. Goiânia, Brasil. INPE. pp. 457–464. Online. Available: http://marte.dpi.inpe.br/col/ltid.inpe.br/sbsr/2004/11.19.14.07/doc/457.pdf. May 1, 2007Google Scholar
CadmanJ. D. 2000The Environmental Aspects of Six Hydro Reservoirs in the Amazon Basin.Submission to the World Commission on Dams, no. ENV061. Online. Available: http://www.dams.org/kbase/submissions/showsub.php?rec=ENV061. January, 13, 2007Google Scholar
CamposM. M.Francis F.Merry 2005Stronger by Association: Improving the Understanding of How Forest-Resource Based SME Associations can Benefit the PoorLondonInstituto de Pesquiza Ambiental da Amazônia & The International Institute for Environment and DevelopmentGoogle Scholar
ChinaView 2006CNPC to purchase EnCana's oil business in Ecudaor.Online. Available: http://news.xinhuanet.com/english/2005-09/15/content_3497826.htm. March 14, 2007Google Scholar
ChurchillS. P. D.Griffin M.LewisIII 1995Moss diversity of the tropical Andes.In ChurchillS. P. H.Balslev E.Forero J. L.Luteyn (Eds.)Biodiversity and Conservation of Neotropical Montane Forestspp335346 Bronx, NYNew York Botanical GardenGoogle Scholar
CochraneT. A. T. J.Killeen O.Rosale 2007Agua, Gas y Agroindustria: La Gestion Sostenible de la Riego Agrícola en Santa Cruz, BoliviaLa Paz, BoliviaConservation InternationalGoogle Scholar
ColinvauxP. A. 1993Pleistocene biogeography and diversity in tropical forests of South America.In GoldblattP. (Ed.)Biological Relationships between Africa and South Americapp473499New Haven, CTYale University PressGoogle Scholar
ColliG. R. 2005As origens e a diversificação da herpetofauna do Cerrado.In ScariotA. J. C.Souza-Silva J. M.Felfili (Eds.)Cerrado: Ecologia, Biodiversidade e Conservaçãopp247264BrasíliaMinistério do Meio AmbienteGoogle Scholar
CowellA. 1990The Killing of Chico MendesEpisode 4. The Decade of Destruction: A Unique Chronicle of the Destruction of the Amazonian Rainforest. PBS Frontline Documentary Series. VideotapeGoogle Scholar
DalyD. C. D. J.Mitchell 2000Lowland vegetation of tropical South America: An overview.In LentzD. (Ed.)Imperfect Balance: Landscape Transformations in the pre-Columbian Americaspp391454New YorkColumbia University PressGoogle Scholar
DauberE. 2003Modelo de Simulación para Evaluar las Posibilidades de Cosecha en el Primer y Segundo Ciclo de Corta en Bosques Tropicales de BoliviaDocumento Técnico 128/2003Santa Cruz, BoliviaProyecto BOLFORGoogle Scholar
EmmonsL. H. 1997Neotropical Rainforest Mammals: A Field Guide2d edChicagoChicago University PressGoogle Scholar
EspinozaG. B.Richards 2002Fundamentals of Environmental Impact AssessmentWashington, DCInter-American Development Bank (IDB) & Inter-American Association of Sanitary and Environmental Engineering (AIDIS)Google Scholar
FabeyM. 1997Free-Trade-Zone Status Turns Amazon Port into Boom Town.Global Logistics & Supply Chain StrategiesOnline. Available: http://www.glscs.com/archives/2.97.FTZ.htm?adcode=90. October 13, 2006Google Scholar
FearnsideP. M. 2005bIndigenous peoples as providers of environmental services in Amazonia: Warning signs from Mato Grosso.In HallA. (Ed.)Global Impact, Local Action: New Environmental Policy in Latin Americapp187198LondonUniversity of London School of Advanced Studies, Institute for the Study of the AmericasGoogle Scholar
FearnsideP. M. Graça 2006BR-319: Brazil's Manaus-Porto Velho highway and the potential impact of a migration corridor to Central Amazonia, Instituto Nacional de Pesquisas da Amazônia-INPA, Manaus, Amazonas, Brazil.Ecological Society of AmericaMérida mexicoGoogle Scholar
FoglemanV. M. 1990Guide to the National Environmental Policy Act. Interpretations, Applications, and ComplianceNew YorkQuorum BooksGoogle Scholar
GlaserB. W. I.Woods (Eds.)2004Amazonian Dark Earths: Explorations in Space and TimeBerlinSpringer-VerlagGoogle Scholar
Global Mapping International 2006World Language Mapping SystemCDROM, Colorado Springs, COGlobal Mapping InternationalGoogle Scholar
GoeschlT. D. C.Igliori 2004Property Rights, Conservation and Development: An Analysis of Extractive Reserves in the Brazilian Amazon, Natural Resources Management(FEEM) Fondazione Eni Enrico Mattei. Working Paper no. 60.04. Online. Available: http://www.feem.it/Feem/Pub/Publications/WPapers/default.htmGoogle Scholar
Gomez-RomeroE. T.Tamariz-Ortiz 1998Uso de la tierra y patrones de deforestacion en la zona de Iquitos.In KalliolaR. S.Flores-Paitan (Eds.)Geoecologia y Desarrollo AmazonicoSulkavaFinnreklama OyGoogle Scholar
GouldingM. 1980The Fishes and the Forest: Explorations in the Amazonian Natural HistoryBerkeleyUniversity of California PressGoogle Scholar
GouldingM. E. G.Ferreira 1996Pescarias Amazônicas, Porteção de Habitas e Fazendas nas Várzeas:Uma Visão Ecológica e EconômicaRelatório Banco Mundial. Brasília: BIRDGoogle Scholar
GouldingM. R.Barthem E.Ferreira 2003The Smithsonian Atlas of the AmazonWashington, DCSmithsonian Institution PressGoogle Scholar
GroganJ. E. P.Barreto A.Veríssimo 2002Mahogany in the Brazilian Amazon: Ecology and perspectives on managementBelém, Brazil(IMAZON) Amazon Institute of People and the EnvironmentGoogle Scholar
HaggettP. A. D.Cliff A.Frey 1977Locational Analysis in Human GeographyNew YorkWileyGoogle Scholar
HallA. 2004Extractive Reserves: Building Natural Assets in the Brazilian Amazon.Working Paper Series, no. 74Amherst, MA(PERI) Political Economy Research InstituteGoogle Scholar
HanaiM. 1998Formal and garimpo mining and the environment in Brazil.In WarhurstA. (Ed.)Mining and the Environment: Case Studies from the Americaspp181197OttowaInternational Development Research CenterOnline. Available: http://reseau.crdi.ca/en/ev-31006-201-1-DO_TOPIC.htmlGoogle Scholar
HarperG. J. M. K.Steininger Y.Talero M.Sanabria T. J.Killeen L. A.Solorzano 2007Deforestation Assessments Across the Andes.Online. Available: http://science.conservation.org/portal/server.pt?open=512&objID=755&&PageID=128505&mode=2&in_hi_userid=124186&cached=true. May 1, 2007Google Scholar
HechtS. B. A.Cockburn 1989The Fate of the Forest: Developers, Destroyers, and Defenders of the AmazonLondonVersoGoogle Scholar
HezelF. X. 2001The New Shape of Old Island CulturesHonoluluUniversity of Hawaii PressGoogle Scholar
(IBGE) Instituto Brasileiro de Geografia e Estadística 2006Síntese de Indicadores Sociais 2006.Online. Available: http://www.ibge.gov.br/home/estatistica/populacao/condicaodevida/indicadoresminimos/sinteseindicsociais2006/default.shtm. May 5, 2007Google Scholar
(IDB) Inter-American Development Bank 2006Building a New Continent: A Regional Approach to Strengthening South American InfrastructureWashingtonIDBOnline. Available: http://www.iadb.org/publications/Reports.cfm?language=en&parid=4. May, 15, 2007Google Scholar
(IPCC) Intergovernmental Panel on Climate Change 2007Climate Change 2007: The Physical Science Basis, Summary for PolicymakersContribution of Working Group I to the Fourth Assessment Report of the Intergovenmental Panel on Climate ChangeGenevaIPCCOnline. Available: http://www.ipcc.ch/SPM2feb07.pdf. April 1, 2007Google Scholar
IUCN Commission on National Parks & Protected Areas & World Conservation Monitoring Centre 1994Guidelines for Protected Area Management CategoriesGland, SwitzerlandIUCNGoogle Scholar
KabatP. M.Claussen P. A.Dirmeyer J. H. C.Gash L.Bravo de Guenni M.Meybeck R. A.PielkeSr. C. J.Vorosmarty R. W. A.Hutjes S.Lutkemeier (Eds.)2004Vegetation, Water, Humans and the Climate: A New Perspective on an Interactive SystemBerlinSpringer VerlagGoogle Scholar
KaimowitzD. A.Angelsen 1998Economic Models of Tropical Deforestation: A ReviewBogorCenter for International Forestry ResearchGoogle Scholar
KalliolaR. S.Flores-Paitan 1998Geoecologia y desarolla Amazonico: Estudio integrado en la zona de Iquitos, PeruAnnales Universitatis Turkuensis, Ser A IITurku, FinlandTurku UniversityGoogle Scholar
KaltnerF. J. G. F. P.Azevedo I. A.Campos A. O. F.Mundim 2005Liquid Biofuels for Transportation in Brazil: Potential and Implications for Sustainable Agriculture and Energy in the 21st CenturySubmitted report by Fundação Brasileira para o Desenvolvimento Sustentável. Commissioned by The German Technical Cooperation. (GTZ) Online. Available: http://www.fbds.org.br/IMG/pdf/doc-116.pdf. April 2007Google Scholar
KilleenT. J. S. G.Beck E.Garcia 1993Guía de Arboles de BoliviaLa Paz, BoliviaHerbario Nacional de Bolivia & Missouri Botanical GardenGoogle Scholar
KilleenT. J. M.Douglas T.Consiglio P. M.Jørgensen 2007aWet spots and dry spots in the Andean Hotspot, the link between regional climate variability and biodiversity.Journal of BiogeopgraphyIn pressGoogle Scholar
KilleenT. J. V.Calderon L.Soria B.Quezada M. K.Steininger G.Harper L. A.Solórzano C. J.Tucker 2007bThirty Years of Land-Cover Change in Bolivia.AMBIOIn pressGoogle Scholar
LehmannJ. D. C.Kern B.Glaser W. I.Woods 2003Amazonian Dark Earths: Origin, Properties, ManagementDordrecht, The NetherlandsKluwerGoogle Scholar
LugoA. E. 2002Homoegeocene in Puerto Rico.In ZarinD. J. J. R R.Alavalapati F. E.Putz M.Schmink (Eds.)Working Forests in the Neotropics: Conservation through Sustainable Managementpp266276New YorkColumbia University PressGoogle Scholar
MacArthurR. H. E. O.Wilson 1967The Theory of Island BiogeographyPrinceton, NJPrinceton University PressGoogle Scholar
MachadoR. M. B.Ramos-Neto M. B.Harris R.Lourival L. M. S.Aguiar 2004Análise de lacunas de proteção da biodiversidade no Cerrado.InAnais IV Congresso Brasileiro de Unidades de Conservaçãopp2938Curitiba, BrasilBrasil Fundação O Boticário de Proteção à NaturezaGoogle Scholar
MachadoR. B. M. B. R.Neto J. M. C.Silva R. B.Cavalcanti 2007Cerrado deforestation and its effects on biodiversity conservation.In KlinkC. A. R. B.Cavalcanti R.Defries (Eds.)Cerrado Land-Use and Conservation: Balancing Human and Ecological NeedsApplied Advances in Biodiversity Science, no. 8Washington, DCCenter for Applied Biodiversity Science, Conservation International (CI)(In press)Google Scholar
MalhiY. J.Wright 2005Late twentieth-century patterns and trends in the climate of tropical forest regions.In MalhiY. O. L.Phillips (Eds.)Tropical Forests & Global Atmospheric Changepp316OxfordOxford University PressGoogle Scholar
MannC. 20051491: New Revelations of the Americas before ColumbusNew YorkKnopfGoogle Scholar
MargulisS. 2004Causes of Deforestation in the Brazilian AmazonBrasiliaWorld BankGoogle Scholar
MaslinM. 2005The longevity and resilience of the Amazon rainforest.In MahliY. O. L.Phillips (Eds.)Tropical Forests & Global Atmospheric Changepp167183OxfordOxford University PressGoogle Scholar
MayleF. E. M. E.Bush 2005Amazonian ecosystems and atmospheric change since the last gl;acial maximum.In MalhiY. O. L.Phillips (Eds.)Tropical Forests & Global Atmospheric Changepp183191OxfordOxford University PressGoogle Scholar
MertesL. A. K. E. M. L.Novo D. L.Daniel Y. E.Shimabukuro J. E.Richey T.Krug 1996Classification of Rios Solimoes-Amazonas wetlands through application of spectral mixture analysis to landsat thematic mapper data.VIII Simposio Brasileiro de Sensoriamento RemotoSalvador, BrazilGoogle Scholar
MoriS. A. G. T.Prance 1990Lecythidaceae - part II: The zygomorphic-flowered New World genera (Couroupita, Corythophora, Bertholletia, Couratari, Eschweilera, & Lecythis).Flora Neotropica Monographno. 21Bronx, NYNew York Botanical GardenGoogle Scholar
NairU. S. D. K.Ray R. O.Lawton R. M.Welch R. A.PielkeSr. J.Calvo The impact of deforestation on orographic cloud formation in a complex tropical environment.In BruijnzeelL. A. J.Juvik F. N.Scatena L. S.Hamilton P.Bubb (Eds.)Mountains in the Mist: Science for Conserving and Managing Tropical Montane Cloud ForestsHonoluluUniversity of Hawaii PressIn PressGoogle Scholar
OrtizE. 2005Conservation Biology of Brazil-nut Rich ForestsWashingtonSmithsonian InstitutionGoogle Scholar
PachecoP. 1998Estilos de Desarrollo, deforestación y Degradación de Los Bosques en Las Tierras Bajas de BoliviaLa PazCIFOR, CEDLA, Fundacion TIERRAGoogle Scholar
PartidárioM. R. 1999Strategic environmental assessment: Principles and potential.In PettsJ. Handbook on Environmental Impact Assessmentpp6073LondonBlackwellGoogle Scholar
PartidárioM. R. R.Clark 2000Perspectives on Strategic Environmental AssessmentBoca Raton, FLCRC PressGoogle Scholar
PattonJ. L. M. N. F.da Silva 1998Rivers, refuges, and ridges: The geography of speciation of Amazonian mammals.In HowardD. J. S. H.Berlocher Endless Forms: Species and Speciationpp202213OxfordOxford University PressGoogle Scholar
PearceD. W. 1994Economic Value BiodiversityLondonJames & Jame, EarthscanGoogle Scholar
PenningtonT. 1997The Genus Inga – BotanyLondonRoyal Botanic Gardens, KewGoogle Scholar
PenningtonR. T. M.Lavin D. E.Prado C. A.Pendry S. K.Pell 2005Climate change and speciation in Neotropical seasonally forest plants.In MalhiY. O. L.Phillips Tropical Forests & Global Atmospheric Changepp191198OxfordOxford University PressGoogle Scholar
PowersM. 2002Illegal loggers invade primordial indigenous natives.Environment News ServiceOnline. Available: http://www.ensnewswire.com/ens/aug2002/2002-08-09-01.asp. August 9, 2002Google Scholar
PranceG. T. 1972ChrysobalanaceaeFlora Neotropica Monograph, no. 9New YorkPublished for Organization for Flora Neotropica by HafnerGoogle Scholar
PranceG. T. 1989Chrysobalanaceae: SupplementFlora Neotropica. Monograph, no. 9SNew YorkOrganizaiton for Flora NeotropicaGoogle Scholar
(PROMPEX) Peruvian Export Promotion Agency 2006Boletines Sectoriales de Exportación: Enero – Marzo 2006.Online.Available: http://www.prompex.gob.pe/Prompex/Portal/Sector/DefaultSector.aspx?.menuId=3Google Scholar
PutzF. E. M. A.Pinard T. S.Fredericksen M.Peña-Claros 2004Forest science and the BOLFOR experience: Lessons learned about natural forest management in Bolivia.In ZarinD. J. J. R. R.Alavalapati F. E.Putz M.Schmink Working Forests in the Neotropics: Conservation through Sustainable Managementpp6496New YorkColumbia University PressGoogle Scholar
RatterJ. A. S.Bridgewater J. F.Ribeiro 2006Biodiversity patterns of the woody vegetation of the Brazilian Cerrados.In PenningtonR. T. G.Lewis J. A.Ratter Neotropical Savannas and Dry Forests: Plant Diversity, Biogeography and ConservationBoca Raton, FLCRC PressGoogle Scholar
RedwoodIII.J. 2002World Bank Approaches to the Brazilian Amazon: The Bumpy Road toward Sustainable Development.Latin America and Caribbean Region Sustainable Development Working Paper, no. 13. Washington: The World BankOnline. Available:http://wbln0018.worldbank.org/.../b8234d558447e77e85256ccd005dbbc5/$FILE/redwood%Google Scholar
ReidW. V. S. A.Laird R.Gamez A.Sittenfeld D. H.Janzen M. A.Gollin C.Juma 1993A new lease on life.In ReidW. V. S. A.Laird C. A.Meyer R.Gamez A.Sittenfeld D. H.Janzen M. A.Gollin C.Juma Biodiversity Prospecting: Guidelines for Using Genetic and Biochemical Resources Sustainably and Equitablypp152WashingtonWorld Resources InstituteGoogle Scholar
Reuters 2007South American Heads Meet in Brazil.January 7. Online. Available at http://www.reuters.com/news/video/videoStory?videoId=30147Google Scholar
RicardoF. A.Rolla 2006Mineração em Unidades de Conservação na Amazônia BrasileiraSão PauloInstituto SocioambientalGoogle Scholar
RiceD. C. A.Sugal S. M.Ratay G. A. B.da Fonseca 2001Sustainable Forest Management: A Review of Conventional WisdomAdvances in Applied Biodiversity Science, no. 3Washington DCCenter for Applied Biodiversity Science at Conservation InternationalGoogle Scholar
RosenfeldA. B. D. L.Gordon M.Guerin-McManus 1997Reinventing the Well Approaches to Minimizing the Environmental and Social Impact of Oil Development in the TropicsWashington, DCConservation InternationalGoogle Scholar
RosenthalJ. P. 1997Equitable sharing of biodiversity benefits: Agreements on genetic resources.InInvesting In Biological Diversity: Proceedings of the Cairns Conferencepp253274ParisOrganisation for Economic Cooperation and Development (OECD)Google Scholar
RuffinoM. L. 2001Strategies for Managing Biodiversity in Amazonian FisheriesManaus, BrazilThe Brazilian Environmental and Renewable Natural Resources Institute (IBAMA)Online. Available: http://www.unep.org/bpsp/HTML%20files/TS-Fisheries2.htmlGoogle Scholar
RylandsA. B. M.Fonseca R.Machado R.Cavalcanti 2005Brazil.In SpaldingM. S.Chape M.Jenkins The State of the World's Protected AreasCambridgeUnited Nations Environment Programme (UNEP) and World Conservation Monitoring Centre (WCMC)Google Scholar
SchaeferS. 2000Fishes of Inundated Tropical Savannas: Diversity and Endemism in the Serrania Huanchaca of Eastern BoliviaFinal report sponsored by The American Museum Center for Biodiversity and Conservation. Online. Available: http://184.108.40.206/scholar?hl=en&lr=&q=cache:h-ivoaIKpAJ:research.amnh.org/ichthyology/bolivia.pdf+Schaefer+Fishes+Tropical+inundatedGoogle Scholar
SchwartzmanS. 1985Banking on disaster.Multinational Monitor67Online. Available: http://www.multinationalmonitor.org/hyper/issues/1985/0615/schwartzman.htmlGoogle Scholar
SmithD. N. T. J.Killeen 1998A comparison of the structure and composition of montane and lowland tropical forest in the Serranía Pilón Lajas, Beni, Bolivia.In DallmeierF. J. A.Comiskey Forest Biodiversity in North, Central and South America and the Caribbean: Research and MonitoringMan and the Biosphere Series, no. 22pp681700Carnforth, UKUNESCO, The Parthenon Publishing GroupGoogle Scholar
StebbinsG. L. 1950Variation and evolution in plantsNew YorkColumbia University PressGoogle Scholar
StewardJ. H. 1948Handbook of South American Indians. Vol. 3. The Forest TribesWashington, DCBureau of American Ethnography & The Smithsonian InstitutionGoogle Scholar
StotzD. F. J. W.Fitzpatrick T. A.ParkerIII D. K.Moskovits 1996Neotropical Birds: Ecology and ConservationChicagoUniversity of Chicago PressGoogle Scholar
TierneyP. 2000Darkness in El Dorado: How Scientists and Journalists Devastated the AmazonNew YorkWW Norton and CompanyGoogle Scholar
TreeceD. 1988Brutality and Brazil: The Human Cost of Cheap Steel.Multinational Monitor92Online. Available: http://multinationalmonitor.org/hyper/issues/1988/02/mm0288_08.html#nameGoogle Scholar
TrollC. 1968The Cordilleras of the Tropical Americas: Aspects of Climatic, Phytogeographical and Agrarian EcologyBonnFerd DümmlersGoogle Scholar
(UNFCCC) United Nations Framework Convention on Climate Change 2006Background Paper for the Workshop on Reducing Emissions from Deforestation in Developing Countries30 August – 1 September 2006. Rome, Italy. Online. Available: http://unfccc.int/methods_and_science/lulucf/items/3757.phpGoogle Scholar
VeigaM. M. 1997Mercury in Artisanal Gold Mining in Latin America: Facts, Fantasies and Solutions.UNIDO -Expert Group Meeting: Introducing new technologies for abatement of global mercury pollution deriving from artisanal gold miningVienna. July 1–3. Online. Available: http://www.facome.uqam.ca/. November 5, 2006Google Scholar
WanderlyI. F. R. L.Fonseca P. G.Pereira P.do A. C.Prado A.de A. B.Oliveira F. P.Barbosa F.Panciera 2007Implicações da Iniciativa de Integração da Infraestrutura Regional Sulamericana e projetos correlacionados na política de conservação no Brasil.InPolítica Ambiental, no. 3BrasíliaConservation InternationalOnline. Available: http://www.conservacao.org/publicacoes/index.php?t=5Google Scholar
WarhurstA. 1998Mining and the Environment: Case Studies from the AmericasOttowaInternational Development Research CenterGoogle Scholar
World Bank 1991Environmental Assessment SourcebookVol. 1Policies, Procedures, and Cross-sectoral Issues. World Bank Technical Paper Number 139Washington, DCWorld BankGoogle Scholar
World Bank 2003aA Common Framework: Converging Requirements of Multilateral Financial Institutions No. 1, Environmental Impact Assessment (EIA)WashingtonWorld BankOnline. Available: http://www1.worldbank.org/harmonization/romehlf/Background/MFI%20Final%20Jan17%202003-Eng.pdf. May 15, 2007Google Scholar
World Bank 2006Finding Sustainable Ways to Extract Forest Products in the Amazon.Pilot Program Extractive Reserves ProjectOnline. Available: http://web.worldbank.org/WBSITE/EXTERNAL/COUNTRIES/LACEXT/BRAZILEXTN/0,,contentMDK:20754543~pagePK:141137~piPK:141127~theSitePK:322341,00.html. June 1, 2007Google Scholar
Tables A.1 through A.4 provide simple models that estimate the value of the carbon stored in Amazonian forests (Table A.1), the value of the carbon released each year via deforestation (Table A.2), the potential value of a 5 percent reduction in deforestation in the eight countries of the greater Amazon Wilderness Area compared against the documented baseline deforestation rates (Table A.3), and the potential value of a 5 percent reduction in deforestation for four Andean countries when compared to a Business as Usual Scenario (Table A.4). Tables A.5 through A.7 provide statistics on protected areas and indigenous lands.
 88 The Forest Code of Brazil establishes this value at 80 percent in the Amazon and 20 percent in the Cerrado.
 89 Brazil has proposed that transfer payments be made as part of development assistance programs, whereas the Alliance for Rainforest Nations has proposed that market-based systems be used to govern the transfers.
 90 Subsidies in Europe and North America fluctuate between $50 to $75 billion annually. The proposed payments for carbon sequestration services represent only 1 percent of this total.
 91 The U.S. military recently recognized global climate change as an important national security threat (MAB 2007).
 92 All of the Andean countries have different versions of a piedmont highway that would transect various national parks, whereas Brazil plans a second Transamazonian highway (BR-210), known as Perimetral Norte, that would parallel the Amazon river approximately 8 degrees north of the equator.
 93 Even the most optimistic land use change scenarios predict that at least 20 percent of the Amazon will be converted to intensive or semi-intensive production systems over the next century, with pessimistic scenarios forecasting up to 50 percent deforestation. Thus, a land use model in which 20 percent of the landscape is deforested but linked to the conservation of 80 percent would result in reduced deforestation.
 94 Ten percent of the Amazon is equivalent to about 25,000 km2. At an average productivity of $500 per hectare (based on low soybean yields and low prices in Bolivia), this would generate $1.2 billion in annual revenues for the region. The potential from biofuels will be several times higher than this figure.
 95 In some parts of the humid tropics, only 5 percent of deforested lands are under production, while the other 95 percent is left as secondary forest fallow.
 96 Fish farming, or aquaculture, is now the fastest growing form of food production in the world. Since 1990, it has increased at a rate of 10 percent per year. If this trend continues, within a decade, more seafood will come from farms than from the wild.
 97 Yields of 3,682 kg/ha have been obtained in fisheries of commercial Colossoma macropomum (tambaqui), a frugivorous species that is fed a commercial diet in stocked ponds; 10,000 ha of ponds would produce 35,000 metric tons of fish per year, matching the total wild harvest of all species in Loreto, Peru in 1994 (Peralta & Teichert-Coddington 1989).
 98 This production model would need to incorporate guidelines to avoid or minimize potentially negative environmental impacts, such as the conversion of wetlands, the introduction of exotic species, and the pollution of fresh water from the inappropriate treatment of wastewater and effluents from fish ponds.
 99 Neither mines nor hydrocarbon concessions should have trouble meeting the 80:20 rule if local populations collaborate by not invading concessions.
 100 The System for Environmental Licensing in Rural Properties uses remote sensing technology provided by the national space agency (INPE) to monitor deforestation in approximately real time and compares that information with land tenure data acquired through a licensing program.
 101 Brazil has adopted a relatively efficient governance structure for its public university, but Andean countries cling to an outdated, highly politicized model in which students and faculty choose university authorities via an electoral process. This model tends to reward teaching while penalizing research and extension.