CONCEPTUAL ECOLOGICAL MODEL
FOR MANAGEMENT OF
BREEDING SHRUBLAND BIRDS
IN THE MID-ATLANTIC REGION
Technical Report NPS/NER/NRR--2006/043
Bruce Peterjohn
USGS Patuxent Wildlife Research Center
Laurel, MD 20708
June 2006
U.S. Department of the Interior
National Park Service
Northeast Region
Philadelphia, Pennsylvania
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Introduction
While grassland
birds have become the focus of increased conservation activities, the
status of birds occupying shrubland habitats has received relatively
little attention (Hunter et al. 2001). Yet, in eastern North America,
shrubland birds exhibited consistent population declines during the
past 40 years, based on data from the North American Breeding Bird Survey
(Pardieck and Sauer 2001). These population declines primarily reflect
large-scale changes in land use patterns during the previous century
(Lorimer 2001). Large areas of marginal farmland were abandoned and
underwent secondary succession during the first half of the twentieth
century, producing abundant successional habitats favored by shrubland
birds. As these habitats matured, combined with strict fire-suppression
policies (Hunter et al. 2001), shrublands succeeded into mature forests,
and shrubland bird communities were replaced by woodland birds (Irland
1982; Askins 1993). For example, while nearly 29% of New England forests
were classified as sapling stage in 1950, only 8% remained at that stage
in the 1980s (Askins 1993). The trend towards forest maturation and
loss of shrubland habitats continues, yet concerted conservation activities
have not been directed to benefit declining shrubland bird populations.
The National Park Service (NPS) could contribute to shrubland bird conservation
in the Mid- Atlantic Region. The NPS maintains a number of historic
sites and former battlefields managed for their cultural significance
but also support wildlife populations. Many of these cultural
parks maintain open landscapes, recreating land use patterns existing
at the times of the historical events. While these open landscapes are
frequently managed grasslands, some parks also support successional
habitats that could be managed to benefit shrubland birds.
In 2005, the NPS initiated a project exploring the potential of cultural
parks to support significant breeding grassland and shrubland
bird communities. This project involved parks within three NPS Inventory
and Monitoring Program (I&M) networks, Mid-Atlantic, National Capital,
and Eastern Rivers and Mountains. Five parks were selected for the initial
focus of this study, all of which maintain open landscapes for interpreting
historic events. Most parks were selected because they contain the most
extensive grassland habitats within their networks, although some also
support shrubby successional habitats. The five parks included in this
study are Antietam National Battlefield, Fort Necessity National Battlefield,
Gettysburg National Battlefield, Manassas National Battlefield, and
Monocacy National Battlefield.
This conceptual ecological model is one product of this project. The
information presented below allows NPS network coordinators to understand
which factors should be considered when making decisions concerning
shrubland management within their networks. This model provides park
resource managers with information on shrubland ecology in the Mid-Atlantic
Region, the ecological requirements of shrubland birds likely to occur
in their parks, and management issues influencing whether significant
breeding populations can occupy shrublands created and maintained in
the parks. Resource managers can then make informed decisions concerning
their ability to create and maintain shrubland habitats. The emphasis
of this conceptual model is restricted to management of breeding shrubland
birds. Additional species occur during migration and winter, and habitat
requirements of shrubland birds during nonbreeding seasons may differ
from those described for the breeding season.
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