Impacts of picnic areas on bird assemblages and nest predation activity within Australian eucalypt forests
Introduction
The development of day-use recreation areas (“picnic areas”) is a frequent part of conservation area management. However, their effects on wildlife have seldom been tested. In south east Qld, Australia, picnicking is the most common form of outdoor recreation, and a 1997 survey found that 65% of residents had picnicked outdoors each an average of seven times during the previous year (Queensland Government, 1998). Furthermore, there has been an overwhelming preference for picnicking in natural or near-natural areas (Queensland Government, 1998). Conservation managers and land use planners therefore often feel obliged to establish picnic areas within multiple-use forests and conservation reserves. Picnic areas may be relatively small, and thus assumed to have little ecological impact. There are, however, very few published studies which document their direct and indirect effects on wildlife (Cole and Landres, 1995).
Studies which have compared forest campgrounds, which have many similarities to picnic areas, to forest interiors have reported a range of effects of campgrounds on birds (Cole and Landres, 1995). Blakesley and Reese (1998) found seven bird species positively associated with campgrounds, and another seven species associated with non-campground sites (most of which nested on the ground or in shrubs or small trees). Foin et al. (1977) reported both positive and negative direct and secondary effects on birds and mammals in Yosemite campgrounds. However, these studies did not survey immediately adjacent to the campground edges, and the occurrence and extent of any edge effects into the forests were not quantitatively studied.
Beside the direct effects of human presence and recreational activities on wildlife distributions (van der Zande et al., 1984), there are two important mechanisms by which picnic areas may be expected to impact upon biota and ecological processes within adjacent forest. First, such areas cause increased availability of, or access to, certain resources, and provide novel resources for some species. Intentional and unintentional supplementary feeding of wildlife may lead to population increases or decreases (Green and Giese, 2004). Within Australian eucalypt forests, bird species which commonly benefit from these added resources, due to their relatively aggressive and inquisitive natures and generalist dietary preferences, include grey and pied butcherbirds (Cracticus torquatus and Cracticus nigrogularis), Australian magpie (Gymnorhina tibicen) and the pied currawong (Strepera graculina). These four larger artamid (family Artamidae) species are in many ways ecologically similar to corvids, and are well known as predators of birds’ eggs, nestlings and small vertebrates in general (Blakers et al., 1984, Major et al., 1996, Bayly and Blumstein, 2001). Other potential nest predators which may benefit from supplemental food resources within picnic areas are the brushtail possum (Trichosurus vulpecula), native and introduced species of Rattus and Varanid lizards.
Second, development of picnic areas leads to the creation of edge habitat. External edges of eastern Australian eucalypt forests cause strong edge effects on avifauna, including elevated abundances within a distinctive suite of larger, more aggressive birds, and the establishment of noisy miner (Manorina melanocephala) populations (Loyn, 1987, Catterall et al., 1991). Noisy miners are sedentary, colonial birds which flourish both in cleared, grassy areas which contain scattered eucalypts, and along eucalypt forest edges (Loyn, 1987, Sewell and Catterall, 1998, Piper and Catterall, 2003). They are intensely interspecifically aggressive, and cause large local reductions in the richness and abundance of smaller bodied birds (Dow, 1977, Piper and Catterall, 2003), as well as interfering with or depredating avian nests (Major et al., 1996, Piper and Catterall, 2004). Furthermore, eucalypt forest edges may have elevated levels of bird nest predation compared with forest interiors (Piper and Catterall, 2004), similar to the pattern reported from many parts of Europe and North America (Paton, 1994, Andrén, 1995). However, the effects of smaller scale edge-creation within these forests are not known.
The creation of all but the smallest, most carefully designed picnic areas is therefore likely to result in ecological changes within surrounding forests. However, we are not aware of any previously published Australian studies assessing the impacts of picnic areas on avian distributions or ecology. The aims of the present study are to assess the effects on birds of picnic areas within subtropical eucalypt forests. Two aspects of avian ecology are investigated: species composition and nest predation pressure. We compare assemblage structure and predation levels at artificial nests within forest transects at the edges of picnic areas with similar measurements from matched transects far from the edge, and others located similarly to the picnic edge with respect to all factors other than the picnic areas. We compare the effects of these edges with known effects of external edges, and consider implications for the management of remnant forests.
Section snippets
Study area and field sites
We carried out our study within large (>500 ha) remnants of subtropical eucalypt forest within the Brisbane region (centred at approximately 27°30′S, 153°E), in south east Qld, Australia. The study region covers around 4000 km2, and had a human population of approximately 1.4 million at the time of the study (Queensland Government, 2005). This area is topographically varied, including coastal plains and subcoastal ranges. Although other forest types, including rainforests and melaleuca forests,
Bird assemblages
Thirteen bird species were recorded using the picnic areas (Table 1). The most frequently recorded species were the noisy miner, which occurred at seven of the eight picnic areas, and the Australian magpie, which occurred at five. Parrots (five species) and three species of artamid (butcherbirds and magpies) were also prominent within picnic areas. The grey fantail was the only smaller bodied bird recorded using a picnic area (a single record).
We recorded 616 individuals and 38 species during
Changes to bird assemblages associated with picnic area edges
Within Australian eucalypt forests, picnic areas often attract a variety of wildlife, which make use of the novel structural and food resources provided. These resources may include open space, food, water and nesting materials. The species which typically take the most advantage of these resources are relatively large and strong generalist (i.e. omnivorous) predators. Examples include monitor lizards, brushtail possums and some bird species of the Corvidae (crows and ravens) and Artamidae
Acknowledgements
We thank the Brisbane City Council, in particular Mick Lawson, and the Queensland Department of Natural Resources, Mines and Energy, for allowing us permission to work in forests under their management. Fieldwork was carried out under Griffith University ethics permit AES/12/02/r/aec. We thank members of the Wildlife Ecology Discussion Group at Griffith University, and two anonymous reviewers, for their useful comments on the draft manuscript.
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