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Costa Rica's Ecosystems: Setting the Stage
Maarten Kappelle
We should preserve every scrap of biodiversity as priceless while we learn to use it and come to understand what it means to humanity.
— Edward O. Wilson, Professor Emeritus, Harvard University
No other area of equal size anywhere in America possesses so rich and varied flora, and none in North America is at all comparable in these respects. It is improbable that in any part of the Earth there can be found an equal area of greater botanical interest. ... In few countries of the world, I believe, would it be possible to travel so much and find only pleasant and ever varied scenes, and be received everywhere with simple and sincere hospitality.
— Paul C. Standley, in Flora of Costa Rica, October 12, 1937
Ecosystem Discovery, Exploitation, Conservation, and Sustainability
Some twenty years after Christopher Columbus visited in 1502 the coast of today's Puerto Limón on his fourth and final voyage to the New World, the Spanish conquistador Gil González D'Ávila, while on a royal expedition sailing from Panama to Nicaragua, named the country Costa Rica, or Rich Coast. He did so because of the golden objects that were used by pre-Columbian indigenous tribes for body decoration and rank distinction, including necklaces, nose plugs, ear plugs, bracelets, and bells (Quilter and Hoopes 2003). However, ultimately it was not the golden treasures that justified the name of Costa Rica, but rather its biological richess: its huge variety of life, piled up in a small corner of the world (Gómez and Savage 1983). Ever since foreign naturalists like Anders Sandoe Ørsted, William More Gabb, Karl Sapper, Karl Hoffmann, Alexander von Frantzius, Karl Wercklé, and Henri François Pittier visited the country and were astonished by its rich flora and fauna, Costa Rica and its ecosystems have been considered by specialists and laymen a true Valhalla of biotic diversity in all its senses (Pittier 1908, Gómez and Savage 1983, Hartshorn 1983, Gómez 1986).
However, over the past 150 years Costa Rica's lush ecosystems have become more and more threatened, pricipally as a result of land conversion for cattle ranching, coffee growing, and large-scale banana production (Hall 1985). Particularly since World War II when the interest in precious hardwoods increased and construction of highways flourished (Merker et al. 1943), accelerated deforestation became the prime driver of biodiversity loss in the country (Sader and Joyce 1988). During the past few decades forest conversion together with other stress factors — such as climate change, overfishing, the introduction of aggressive invasive alien species, the construction of large infrastructure features such as roads and dams, sedimentation, environmental pollution, urban sprawl, and coastal encroachment — have begun to put ever-increasing pressures on the fragile cornucopia of Costa Rica's ecological systems, impoverishing and reshaping them in already fragmented landscapes and seascapes.
While during the second half of the twentieth century Costa Rica lost almost half of its forest cover, since the early 1970s to date (2015) the country has been able to save millions of hectares in 169 protected areas, ranging from absolute reserves and national parks to forest reserves and protective zones (Gámez and Ugalde 1988, Boza 1992, Wallace 1992, SINAC 2009, Obando 2011). Together, Costa Rica's protected areas cover 26.2% of the country's territory today. The development of the national park system initially occurred simultaneously with massive deforestation in unprotected areas, a phenomenon now known as the "Grand Contradiction" (Evans 1999).
The first wildlife area that received formal protection was created in 1945. It concerned the montane oak forest zone just south of Cartago, along both sides of the Inter-American Highway (Kappelle 1996). From 1969 to the late 1970s this and other early protected areas, including the Reserva Natural Absoluta Cabo Blanco and the Volcán Turrialba and Volcán Irazú national parks, were formally administered by the Departamento de Parques Nacionales. Then in 1977, protected area management passed on to the Servicio de Parques Nacionales (SPN), which was formally created as a specialized unit under direction of the Ministerio de Agricultura y Ganadería (MAG). Key protected areas like the now famous Cahuita, Chirripó, Corcovado, Santa Rosa, and Tortuguero national parks were created during that decade, as the environmental movement became stronger and focused hard on safeguarding the country's last remaining wild places (Gámez and Ugalde 1988, Wallace 1992, Boza 1993).
At the end of the next decade, in 1988, SPN was incorporated into the new Ministerio de Recursos Naturales, Energía y Minas (MIRENEM). Then, in 1995, new responsibilities were added while MIRENEM was restructured. It became the Ministerio del Ambiente y Energía (MINAE). In that same year, SPN was merged with both the Dirección General Forestal (DGF) and the Dirección General de Vida Silvestre (DGVS) into the innovative Sistema Nacional de Áreas de Conservación (SINAC), a subdivision of the young MINAE (Evans 1999). During the second administration of President Oscar Arias Sánchez (2006 to 2010) the telecommunications sector was added to MINAE, to become the Ministerio del Ambiente, Energía y Telecomunicaciones (MINAET). In 2013 MINAET became again MINAE, as the telecommunication department was moved to another ministry. As of 2014, MINAE is also referred to as the Ministerio del Ambiente, Energía, Aguas y Mares, recognizing the growing importance of the freshwater and marine resources for the country.
SINAC was foremost created to serve as a facilitating mechanism necessary to administer all protected areas in an integrated manner at regional level (SINAC 2009). In total, eleven Áreas de Conservación (ACs) were established as part of SINAC, covering the full territory of the country. Costa Rica's 1998 biodiversity law (Ley de Biodiversidad) legally formalized and strengthened this organizational structure and its holistic, decentralized, and inclusive approach.
Thanks to extraordinary efforts in the past, Costa Rica has now been able to devote nearly a third of its territory to the conservation into perpetuity of its rich biological diversity, spread over eleven conservation areas (for a more detailed historical account, see Wallace 1992, García 1997, Evans 1999, and Gámez 2003). Therefore, today Costa Rica serves as a successful model of biodiversity research and conservation. It is a country in which many innovative ideas were first conceptualized, tested, and implemented (Fournier 1991, Wallace 1992, Evans 1999). These ideas range from all-taxa biodiversity inventories (ATBI) (Janzen and Gámez 1997) and biological prospecting meant to discover wild species with medicinal properties (Tamayo et al. 2004) to avant-garde bar-coding of plant and insect specimens in ex situ collections (Gámez 1999); from an out-of-the-box means of linking debt reduction with environmental protection measures through Debt-for-Nature Swaps proposed by Tom Lovejoy in 1984 (Thapa 1998) to revolutionary Payments for Environmental Services (PES; Pagiola 2008, and see Arriagada et al. 2012); and from ecosystem-based sustainable...
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