Hurricane Katrina impacts the breeding bird community in a bottomland hardwood forest of the Pearl River basin, Louisiana

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Abstract

We monitored breeding bird communities and vegetation both before and after Hurricane Katrina category 2 winds severely damaged extensive bottomland hardwood forest of the Pearl River basin, south Louisiana. Many trees were felled by wind, most others were stripped of leaves and branches, and the canopy opened considerably (57%). Blackberry thickets sprouted and expanded to cover almost all of what was previously a patchily open forest understory. The bird community changed distinctively following the hurricane, driven primarily by increased density of species that prefer dense understory (regenerating) habitat. Individual species that increased significantly in density included one year-round resident, Carolina wren, and five breeding migrants, white-eyed vireo, Swainson's warbler, Kentucky warbler, hooded warbler, and yellow-breasted chat. These patterns were predictable responses to the opened canopy and increased density of understory vegetation. However, over three years following the storm, most species, especially canopy breeders, showed no distinct numerical response to the hurricane, which suggests that the initial bird community was resistant to hurricane disturbance. Only one species, Acadian flycatcher, declined significantly after the hurricane, presumably because of loss of its preferred open understory breeding and feeding habitat. Our results thus document and reinforce the important role hurricanes play along the Gulf coast in structuring forest bird communities by altering understory habitat. We expect habitat changes will continue as invasive plant species further change forest community structure, and as large storms increase in frequency in relation to global climate change. Thus, we also expect continued changes to the bird community, which may include additional future declines.

Research highlights

▶ The bird community of a coastal forest changed following hurricane disturbance. ▶ Densities of species that prefer dense understory habitat increased. ▶ Most species did not change numerically, suggesting resistance to disturbance. ▶ Only one species declined, presumably because of loss of open understory habitat. ▶ Hurricanes help structure forest bird communities along the Gulf coast.

Introduction

Hurricanes have relatively large annual impact areas and economic costs relative to most other types of natural disturbance (Dale et al., 2001). As a result of habitat disturbance, hurricanes also have strong effects on animal communities in forested ecosystems (reviewed by Michener et al., 1997). For example, in the Caribbean, frequent hurricanes are an important force structuring forest bird communities (Wunderle et al., 1992, Wunderle, 1995). The impact of hurricanes on animal communities depends on geographic location, and severity and extent of storm damage, among other factors. Post-hurricane conditions, such as drought or fire events, and the timing of storms in relation to breeding and migration also influence community response (Lynch, 1991, Waide, 1991). As with any disturbance, the response of individual species to hurricanes is not uniform (Rittenhouse et al., 2010a), and disturbance-dependent species can even benefit (Greenberg and Lanham, 2001, Tejeda-Cruz and Sutherland, 2005). In some cases, bird communities are only minimally affected or rebound quickly following hurricanes (Waide, 1991, Murphy et al., 1998, Tejeda-Cruz and Sutherland, 2005, Yaukey, 2008). Surprisingly, little recent research addresses the effects of hurricanes on forest bird communities along the northern Gulf of Mexico, where hurricanes are frequent and have strong influences on coastal forest composition and structure (Williams et al., 1999). However, following Hurricane Katrina, radar tracking of habitat use indicated that for several weeks migratory songbirds avoided the most severely impacted forests as well as high quality stopover habitat (bottomland hardwood forest) in favor of not only less disturbed, but also typically less preferred habitat (intensively managed pine), before densities among habitats returned to typical patterns (Barrow et al., 2007). Following Hurricane Rita in southwest Louisiana, arthropod abundance had increased after one year, but food availability for birds was lower in severely damaged forest than in lightly damaged forest because of reduced foraging substrate (Dobbs et al., 2009). In urban and suburban New Orleans, all of the most common bird species experienced severe declines, some for just months and others lasting for more than a year (Yaukey, 2008). At a regional scale, Rittenhouse et al. (2010a) compared community similarity before and after four hurricanes that made landfall along the Gulf and Atlantic coasts of the United States. They found that similarity of bird communities in the first year following hurricanes was lower for all species combined as well as for species nesting in the mid-story or canopy, and changes to community diversity persisted for at least five years. Nonetheless, few before–after reports document how these recent Gulf Coast hurricanes impact forest bird breeding community composition, especially in relation to plant community changes.

We studied the response of a bottomland hardwood bird community to Hurricane Katrina, which passed directly over our study site in the Pearl River basin with category 2 wind speeds (Fig. 1). We compared habitat and avian communities in the Pearl River before and after the hurricane. We expected that the severe habitat changes caused by the hurricane (Chambers et al., 2007) would lead to (1) increased density of avian species that prefer dense understory habitat created by loss of canopy cover, and (2) decreased density of avian species that prefer open understory, closed canopy forest. Because the hurricane occurred in the middle of the autumn migration period, we also expected the hurricane to have strongest negative effects on resident species, which would have been more exposed to the short-term habitat changes such as defoliation.

Section snippets

Study area

We surveyed forest habitat structure and bird communities non-continuously beginning in 1996 and continuing through 2008 within the 14,750 ha Bogue Chitto National Wildlife Refuge of the Pearl River basin of Louisiana (30°27′13″N, 89°44′56″W). Surveys were conducted during 5 years before (1996–1999, 2003) and 3 years following Hurricane Katrina (2006–2008). The Pearl River basin contains one of the few large intact bottomland hardwood forests in the region, with large areas protected by state

Results

Canopy cover changed little over the survey period preceding the hurricane, but then decreased by an average 57% in the 3 years following Hurricane Katrina (T5 = 5.79, P = 0.002; Fig. 2a). Although Hurricane Katrina caused widespread and extensive windthrow disturbance, basal area decreased by only 17% (T22 = 0.84, P = 0.415, Fig. 2b). Thus, much of the canopy cover decrease can be attributed to shearing of large branches, and not just windthrow. The open canopy led to a 15-fold increase in blackberry (

Habitat change

The changes in habitat described here are consistent with other recent reports (Chambers et al., 2007, Chapman et al., 2008, Ramsey et al., 2009). The hurricane severely decreased forest canopy cover in our study area; however, despite substantial recovery of canopy cover in the following months, the understory became extremely dense, with density continuing to increase with each year (David Brown, personal observation, June 2008). In the Pearl River basin, Hurricane Katrina had particularly

Acknowledgements

We are grateful for the hard work of various field technicians including Kate Fournier, Nathan Hodgkins, Isaac Kremsky, Bryan Sigel, and Shannon Tanner. We also thank employees of the United States Fish and Wildlife Service (USFWS) for assistance with trail clearing. Support for this research was provided by the National Science Foundation (DEB 0089541) and USFWS. Two anonymous reviewers provided constructive comments that significantly improved the quality of the manuscript.

References (37)

  • V.H. Dale et al.

    Climate change and forest disturbances

    Bioscience

    (2001)
  • R.C. Dobbs et al.

    Short-term effects of hurricane disturbance on food availability for migrant songbirds during autumn stopover

    Wetlands

    (2009)
  • S. Faulkner et al.

    Impacts of Hurricane Katrina on floodplain forests of the Pearl River

  • C.H. Greeenberg et al.

    A comparison of bird communities in burned and salvage-logged, clearcut, and forested Florida sand pine scrub

    Wilson Bull.

    (1995)
  • T.M. Haggerty et al.

    Carolina Wren (Thryothorus ludovicianus)

  • P.B. Hamel et al.

    A Land Manager's Guide to Point Counts of Birds in the Southeast

    (1996)
  • R.L. Hutto et al.

    The effects of postfire salvage logging on cavity-nesting birds

    Condor

    (2006)
  • J. Jones et al.

    Territory and nest site selection of cerulean warblers in eastern Ontario

    Auk

    (2001)
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