Chapter 12 Conservation Biology

12 Conservation Biology — Update 2014 Nathaniel T. Wheelwright In the 14 years since Monteverde: Ecology The first step in protecting biodiversity is and Conservation of a Tropical Cloud Forest conducting thorough inventories of species. In was published (Nadkarni and Wheelwright this regard, Monteverde has been a leader 2000), vast tracts of land have been newly among neotropical sites. Documentation of the protected in the Monteverde-Arenal Bioregion, region's stunning biological diversity continues thanks to the work of the Monteverde to be expanded by the observations of visiting Conservation League, Costa Rican and biologists and ecotourists, as well as local international conservation groups, and numerous farmers and citizen scientists (e.g., Rowe and generous donors. The Children's Eternal Pringle 2005, Yanoviak et al. 2003a). A team Rainforest is now the largest private reserve in from the Monteverde Cloud Forest Reserve, led Costa Rica, with an area of 22,500 ha, more than by Yoryineth Méndez, has been conducting twice the size of the Monteverde Cloud Forest regular censuses of frogs and toads from the Reserve (see Chapter 10 Update by Peñas Blancas Valley to the Reserve to the San Burlingame). A new generation of young Luis Valley. Preliminary results indicate scientists and policy makers, many of them recovery of species that had been missing for students on courses offered by the Organization more than a decade. Another team, led by Mark for Tropical Studies, the Council on Wainwright, documented the recovery of the International Educational Exchange, and the Green-eyed Frog (Lithobates vibicaria). University of California Education Abroad However, there remains much to do in Program, has visited Monteverde's forests. Monteverde with regard to several key areas of Building upon what was known about the conservation biology highlighted by region's flora and fauna a decade and a half ago, Wheelwright (2000). As of 2014, no one has yet they and others have worked with local published a study of the impact on cloud forest organizations to connect knowledge to plant or animal communities of invasive species conservation action. or native lowland species that have expanded their range upslope (e.g., Keel-billed Toucan, Ramphastos sulfuratus; Bronzed Cowbird, Understanding the causes and consequences Molothrus aeneus). We still can only guess of rarity is also crucial for protecting which plants or animals in Monteverde are biodiversity. Jankowski and Rabenold (2007) keystone species (species whose loss would found that endemic species in neotropical have disproportionate negative effects on montane rainforests such as Monteverde tend to biodiversity; Ficus tuerkheimii and Acnistus be locally rare: there is a positive correlation arborescens, trees whose fruits are eaten by between distribution and abundance at several numerous bird species, are good candidates), spatial scales. There is also a correlation and the population genetic structure and between regions of high species richness and demographics are known for virtually no high endemism, at least for taxa such as Monteverde species (although see Soare et al. bromeliads, palms, aroids and scarab beetles, 2014). Gathering such information is critical according to Kohlmann et al. (2010), who single because it will help us prioritize conservation out premontane wet forests in the Cordillera de efforts and effect management plans that target Tilarán as among the most important particularly vulnerable or ecologically important conservation priority areas in Costa Rica populations. because of their biological diversity and Monteverde's arthropods have been well- uniqueness. catalogued (Yanoviak et al. 2003b, 2007; The main focus of conservation biology at Schonberg et al. 2004, Hanson 2014) but Monteverde since 2000 has been on the role of knowledge of most herbivorous insect species' landscape features in preserving biodiversity, host plants is lacking (see Hanson 2014). Soil particularly connectedness between habitats at fauna—bacteria, protists, fungi—remain a different spatial scales. Since the late 1970's, not mystery, although Nadkarni and colleagues only has the size of protected areas in the (Nadkarni et al. 2002, Rains et al. 2003) Monteverde-Arenal Bioregion (MAB) been continue to make progress understanding the greatly expanded, but forest regeneration has biology of soils in cloud forest canopies. also occurred throughout the region, thanks in Monitoring species that are easy to count and are large part to ecotourism, changes in local ecologically (or economically) important or that attitudes, and abandonment of pastures and indicate the health of Monteverde's communities coffee parcels (see Chapter 11 Update by and ecosystems ("indicator species") is essential. Stuckey et al.). As a direct result, population Populations of vocal animals such as frogs, declines in numerous species have been insects, mammals and birds can be monitored reversed. For example, there was little or no using new technologies such as real-time change in the number of bats (individuals and bioacoustics monitoring (Aide et al. 2013). species) captured per unit time per net length Three-wattled Bellbirds (Procnias over a 27-year period (LaVal 2004). Twenty- tricarunculata) and Resplendent Quetzals four new bat species, most of them from the (Pharomachrus moccino) are two obvious lowlands, colonized the area over the same time, species to begin with. For monitoring plant presumably in response to warming climates and responses to environmental changes, much could a 19% increase in forest area between 1973 and be learned by recording the annual timing and 1998 (based on aerial photographs; LaVal 2004). magnitude of flowering and fruiting of a Agricultural windbreaks, increasingly planted in taxonomically diverse set of common, easily open pastures throughout the zone, have had recognized tree species (Wheelwright 1986); numerous beneficial effects for biodiversity. For transects could be set up along readily accessible one thing, they provide habitat for forest tree roads in Monteverde with observations made by species and facilitate forest regeneration within "citizen scientists" and entered into on-going agricultural areas: 91 tree species representing phenological databases (c.f. U.S. National primary and secondary forests occur in Phenology Network). These studies need to be Monteverde windbreaks, with tree seedling designed and implemented quickly, with the densities highest in windbreaks connected to goal of pursuing them over the long-term. forest patches (Harvey 2000a). Dispersal of the seeds of trees and shrubs was greater in windbreaks planted on dairy farms than in essentially, from the Continental Divide to sea nearby pastures, with 199 species recorded in level—and across international boundaries. seed traps during a single year; the presence of Climate change has surged to the fore as the remnant forest trees in pastures increased the central concern in conservation biology. Making number of tree species (Harvey 2000b). One headlines in the popular press in ways that encouraging discovery is that, in addition to tropical deforestation and the extinction crisis attracting seed dispersers, relict pasture trees can never succeeded in doing, fears about climate serve as "regeneration foci"—increasing change have awoken the public to take action to ecological connectedness on a temporal scale— mitigate the worst effects of global warming on by ameliorating soil microclimates and crop production, rising sea levels, disease supporting diverse canopy seed banks in their outbreaks, etc. It was apparent in 2000 that decomposing epiphyte masses (Nadkarni and Monteverde had already begun to feel the effects Haber 2009). of climate change. In future decades, the flora O'Donnell and colleagues have studied the and fauna of cloud forests throughout Latin effect of forest fragmentation in Monteverde on America will suffer from climate changes more army ants (Formicidae: Ecitoninae) and the birds than those of lowland habitats. Montane that facultatively take advantage of them to flush landscapes support distinctly high beta diversity insect prey. In one study, they found that, (the accumulation of increasing diversity as one compared to forest fragments, continuous forest moves between sites; Jankowski et al. 2009). supported greater bird species richness, larger Moreover, refuges to escape the rises in flocks and great total body mass of birds temperature and alterations in rainfall and attending army ant swarms (Kumar and seasonality that are already upon us are limited O'Donnell 2007). In another study, on mountaintops, and they diminish even further microsatellites were used to reconstruct as species are forced upslope. At least half of the genotypes and determine population genetic 77 cloud forest bird species included in the structure and found "isolation by landscape modeling study of Gasner et al. (2010) are resistance": forest clearing impedes dispersal predicted to decline in the next century, with and gene flow between colonies of the keystone eight species restricted to Central America ant species Eciton burchellii (Soare et al. 2014). projected to become locally extinct. Species that The increase in road-building and traffic in are particularly threatened include the Mountain Monteverde over the last several decades is Robin (Turdus plebejus)—one of the likely to have created new barriers to gene flow commonest and most important seed dispersers for numerous species (including,

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