Spatial Distribution Patterns of the Dominant Canopy Dipterocarp Species in a Seasonal Dry Evergreen Forest in Western Thailand Sarayudh Bunyavejchewina, James V
Total Page：16
File Type：pdf, Size：1020Kb
Forest Ecology and Management 175 (2003) 87±101 Spatial distribution patterns of the dominant canopy dipterocarp species in a seasonal dry evergreen forest in western Thailand Sarayudh Bunyavejchewina, James V. LaFrankieb, PatrickJ. Baker c,*, Mamoru Kanzakid, Peter S. Ashtone, Takuo Yamakuraf aRoyal Thai Forest Department, Silvicultural Research Division, Forest Research Of®ce, Chatuchak, Bangkok 10900, Thailand bCenter for Tropical Forest Science, Smithsonian Tropical Research Institute, 469Bukit Timah Road, Singapore 1025, Singapore cCollege of Forest Resources, University of Washington, Seattle, WA 98195, USA dGraduate School of Agriculture, Kyoto University, Kitashirakawa, Kyoto 606-8502, Japan eArnold Arboretum, Harvard University, One Eliot Street, Cambridge, MA 02138, USA fDepartment of Biology, Faculty of Science, Osaka City University, Sumiyoshi-ku, Osaka 558-8585, Japan Received 2 October 2001; accepted 31 March 2002 Abstract Population structure and spatial patterns were examined for four species of canopy dipterocarps (Anisoptera costata, Dipterocarpus alatus, Hopea odorata, Vatica cinerea) in a 50 ha plot in seasonal dry evergreen forest at the Huai Kha Khaeng Wildlife Sanctuary in western Thailand. Spatial dispersion was assessed with Morisita's index for quadrat sizes ranging from 61 m2 to 25 ha; spatial attraction and repulsion between species and size classes were measured with Iwao's index. Only Vatica had a negative exponential diameter distribution suggesting continuous recruitment. The other species had either normal (Hopea) or irregular diameter distributions with peaks in the large size classes (Anisoptera, Dipterocarpus). All four species were signi®cantly clumped at most quadrat sizes. At the local scale, saplings and poles of Hopea and Anisoptera were negatively associated with adults at quadrat sizes <1000±5000 m2, while the distributions of Dipterocarpus and Vatica saplings and poles were independent of adult trees. In general, saplings and poles were always positively associated with each other. Spatial segregation among species may imply habitat specialization. A torus-translation analysis of habitat association for each of the dipterocarp species revealed both positive and negative species-speci®c associations. At HKK, most of the dipterocarps' spatial distributions were independent of each other and there was no evidence of strong spatial segregation among species. The irregular diameter distributions, clumping at large spatial scales, and lackof positive association between juvenile and adult stems suggest that many of the dipterocarps at the 50 ha plot may have established after a large-scale catastrophic disturbance. In the absence of catastrophic disturbance, we hypothesize that the Hopea and Anisoptera populations will eventually disappear from the plot because of a lackof suitable recruitment conditions. # 2002 Elsevier Science B.V. All rights reserved. Keywords: Spatial patterns; Dipterocarps; Thailand 1. Introduction * Corresponding author. Present address: Institute of Pacific In recent decades much ecological research has Islands Forestry, Pacific Southwest Research Station, USDA Forest Service, 23 E. Kawili St., 967 20 Hilo, HI, USA. focused on identifying potential mechanisms for the E-mail address: [email protected] (P.J. Baker). maintenance of diversity in species-rich communities 0378-1127/02/$ ± see front matter # 2002 Elsevier Science B.V. All rights reserved. PII: S 0378-1127(02)00126-3 88 S. Bunyavejchewin et al. / Forest Ecology and Management 175 (2003) 87±101 (Ashton, 1998). In the study of tropical forests two a large-scale permanent forest dynamics plot in questions have received particular attention: (1) are Panama, Condit et al. (1992) found that few species tree species narrowly specialized for a certain habitat showed signs of density-dependence. In a later paper (e.g., Ashton, 1969; Hubbell, 1979)? and (2) is the (Condit et al., 1994), they suggested that the role of distribution of juvenile trees a function of the distribu- density-dependence may only be important among tion of adult trees (e.g., Janzen, 1970; Connell, 1971; those species with the highest population densities. Condit et al., 1992)? More recently, however, Wills et al. (1997), using The relationship between the local distribution of a more robust statistical techniques to reanalyze the species and topography in tropical forests has been Panama plot data, showed that density-dependence studied in many regions (Hubbell and Foster, 1986; was much more common than originally believed. As Basnet, 1992; Itoh, 1995; Yamada et al., 1997). None- with habitat specialization, most studies of spatial theless, the relative importance of habitat specializa- association among tropical forest species have been tion in structuring species-rich forest communities either in aseasonal or neotropical forests. No such remains unclear. Some studies, particularly in the studies exist for the seasonal forests of tropical south- aseasonal evergreen forests of southeast Asia, have east Asia. suggested that tree species may be habitat specialists An important factor that must be taken into con- for particular edaphic or topographic conditions (Ash- sideration is the relative increase in disturbance inten- ton, 1964, 1976; Ashton and Hall, 1992; Richards, sity with increasing seasonality in tropical Asia. The 1996; Yamada et al., 1997). Other studies have not occurrence of catastrophic drought, ®re, and cyclones found strong evidence of habitat specialization. For increases with increasing distance from the equator example, Hubbell and Foster (1986) found that the (Whitmore, 1984). Spatial patterns of tree species may majority of species in a semi-evergreen neotropical provide indirect evidence of the relative in¯uence of forest were habitat generalists with respect to topo- large- and small-scale disturbances in structuring for- graphy. However, studies in Asian forests have been est communities (Duncan and Stewart, 1991). mostly restricted to aseasonal forests; the relationship Trees of the family Dipterocarpaceae dominate between spatial distribution and topography in seaso- forests across much of south and southeast Asia nal forests in continental Asia has not yet been studied. (Wyatt-Smith, 1963; Champion and Seth, 1968; The spatial distribution of tropical tree populations Ashton, 1982; Whitmore, 1984). Dipterocarps are has been a major source of interest among tropical typically canopy trees or emergents and reach con- ecologists because of its potential role in explaining siderable dimensions throughout forests of the region. the coexistence of tree species in species-rich forests. Consequently, they are both ecologically and econom- Janzen (1970) and Connell (1971) ®rst proposed that ically important. Developing a better understanding of the probability of mortality and survival of juveniles how dipterocarp populations are maintained within a may be a function of the density of conspeci®c adults forest is critical to advancing forest management and in the surrounding area. The intensity of predation by silviculture in the seasonal tropics. insects and other herbivores (Janzen, 1970; Burkey, In this study, we examine patterns of spatial asso- 1994) and the probability of infection by fungal ciation and habitat specialization within and among pathogens (Augspurger, 1983; Augspurger and Kelly, four dominant dipterocarp species in a 50 ha perma- 1984) are expected to be higher where accumulations nent forest dynamics plot located in seasonal dry of seeds or seedlings are denser, and lower where evergreen forest in western Thailand. Speci®cally, seeds and seedlings are sparse. Given the dispersal we test the following hypotheses: limitations of most tropical forest tree species, seed and seedling density is typically highest directly below 1. Spatial dispersion of each species is random with the crown of a mother tree and decreases exponentially respect to size class; that is, saplings and poles are with increasing distance from the mother tree. Yet, as neither positively or negatively associated with with habitat specialization, the extent to which den- adult trees. sity-dependence in¯uences community diversity pat- 2. Spatial dispersion of each dipterocarp species is terns remains uncertain. For example, in an analysis of independent of all other dipterocarp species. S. Bunyavejchewin et al. / Forest Ecology and Management 175 (2003) 87±101 89 3. Spatial dispersion of each dipterocarp species is Province, western Thailand (Fig. 1). The sanctuary random with respect to habitat. encompasses approximately 2780 km2. Three main forest types, seasonal dry evergreen forest, deciduous We evaluate the spatial patterns of each species dipterocarp forest and dry mixed deciduous forest, within the context of the current stand structure and form a mosaic across most of the sanctuary, with a few consider the processes that may have created these high altitude sites (<5% of the total sanctuary area) patterns and their role in forest development in the occupied by lower montane forest. Rainfall is highly seasonal tropics of southeast Asia. seasonal with a 4±6-month dry period (<100 mm per month) from November to April. Mean annual rainfall 2. Study area and methods is approximately 1425 mm (1983±1995 average). The study plot is located in the interior of the 2.1. Study area sanctuary in a stand of seasonal dry evergreen forest with no record of logging or other forest management The study area is located in the Huai Kha Khaeng