Matrix habitat and species richness in tropical forest remnants
Introduction
Deforestation has led to striking fragmentation of natural landscapes throughout the world (Whitmore, 1997, INPE, 1998). Fragmented landscapes are composed of a patchwork of habitats of differing quality for fauna. With the exception of islands in hydroelectric reservoirs, human-fragmented landscapes maintain some degree of terrestrial connectivity via the matrix of modified habitats surrounding fragments. It has become increasingly apparent that understanding how species are affected by fragmentation requires information on their responses to all components of the landscape, i.e. forest patches, remaining continuous forest, and the intervening matrix (Harris, 1984, Laurance, 1990, Laurance, 1991, Laurance, 1994, Malcolm, 1991, Fahrig & Merriam, 1994, Aberg et al., 1995, Lidicker. 1995, Flather & Sauer, 1996, Tocher et al., 1997).
The matrix is likely to be important in the evolution of fragment dynamics for several reasons. First, the matrix will often act as a selective filter (not an absolute barrier) for the movements of species across the landscape. The type of vegetation in the matrix will determine the pore size of the filter for movements of individuals. Tall second-growth forest, for example, would be analogous to a filter with large pores allowing more faunal movement because of its structural similarity to primary forest, while a pasture would have small pores that impede much movement (Malcolm, 1991). If this filter analogy is correct, one would expect a gradual increase in species richness, at least of those associated with primary habitat, from fine-pored (i.e. pasture) to larger-pored (i.e. second-growth) habitats. Forest species would be expected to vary in their pore-size requirements, with species that tolerate smaller pores being better able to persist in forest remnants (Laurance, 1990, Laurance, 1991, Laurance, 1994).
Second, the matrix may exert a strong influence on within-remnant community dynamics (Janzen, 1986, Laurance, 1990, Malcolm, 1991). For example, species associated with the matrix may invade forest remnants, altering the species composition of some taxonomic groups (Hutchings, 1991, Brown & Hutchings, 1997, Laurance, 1994, Tocher et al., 1997). Finally, different matrix types may influence fragment edge effects. Edge-related gradients in physical and biotic variables are likely to be less pronounced when the matrix is structurally similar to the original habitat, and this may reduce the ecological impacts of edge effects (Laurance & Yensen, 1991, Mesquita et al., 1999).
To investigate the importance of the matrix habitat in explaining species richness in forest fragments, we use results from long-term surveys of four taxonomically diverse groups (ants, small mammals, frogs, and birds) from the Biological Dynamics of Forest Fragments Project (BDFFP) in central Amazonia. To our knowledge, this is the first test of matrix effects using such a large and taxonomically diverse assemblage of species.
Section snippets
BDFFP history and study sites
The BDFFP, located 70 km north of Manaus, Brazil (Fig. 1), was initiated in 1979. A large area north of Manaus was designated for development in the 1970s as part of a program to establish cattle ranches in the region as an economically viable solution for human settlement. With government incentives, large (5000–10,000 ha) ranches were carved out of primary rainforest (Lovejoy et al., 1986, Bierregaard et al., 1992). With cooperation from the ranchers, BDFFP researchers were able to design a
Results
On average, the four taxonomic groups responded quite differently to fragmentation (Table 1). As expected, species richness of birds and ants declined in forest fragments, but richness of small mammals and frogs actually increased. Birds and ants lost a large number of the original species complement in continuous forest, whereas few if any species were lost among small mammals and frogs. Some frog and small mammal species were mainly associated with matrix habitats and occasionally invaded
Discussion
Our results suggest that the matrix of modified habitats surrounding fragments is likely to have pervasive effects on vertebrate communities in forest fragments. First, many new species not originally present in continuous forest have “invaded” our experimental landscape and are now commonly encountered in the matrix, a situation also observed in other tropical areas (Janzen, 1986, Moutinho, 1998, Lawton et al., 1998, Vasconcelos & Cherrett, 1998). These species probably originated from the
Acknowledgements
The BDFFP is a bi-national investigation operated by the National Institute For Amazonian Research (INPA) in Manaus, Brazil, and the Smithsonian Institution in Washington, DC. Financial and logistical assistance from the following are greatly appreciated: INPA, Smithsonian Institution, USAID-Brazil, MacArthur Foundation, A.W. Mellon Fund, Citibank, Gauntlett Foundation, PEW Charitable Trust, Pilot Program for Protection of the Brazilian Rain Forest (G-7), Summit Foundation, and World Wildlife
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Present address: Conservation International, 2501 M Street NW, Suite 200, Washington, DC 20037, USA.
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Present address: Counselor to the Secretary for Biodiversity and Conservation, Smithsonian Institution, Washington, DC 20560, USA.
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Present address: Department of Biology, University of North Carolina, Charlotte, NC 28223-0001, USA.
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Present address: Faculty of Forestry, University of Toronto, Toronto, ON, Canada M5S 3B3.
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Present address: Department of Biological Sciences, Southeastern Louisiana University, Hammond, LA 70402-0814, USA.
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Present address: Otago Conservancy, PO Box 5244, 77 Stuart St., Dunedin, New Zealand.