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Landscapes Forest and Global Change - ESA - Escola Superior ...

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K. L. Martin & P.C. Goebel 2010. Impact of hemlock decline on successional pathways <strong>and</strong> ecosystem function<br />

148<br />

move westward in Pennsylvania (Figure 1). HWA feeds on the parenchyma cells of xylem rays,<br />

which causes the death of branches <strong>and</strong> leads to mortality in T. canadensis (McClure 1991).<br />

There is no evidence that T. canadensis or T. caroliniana Engelm., a species endemic to the<br />

southern Appalachians, have any resistance to HWA. Thus complete mortality occurs in 4-15<br />

years (McClure 1991; Orwig <strong>and</strong> Foster 1998). Evans <strong>and</strong> Gregorie (2007) estimate HWA to<br />

spread at a mean rate of 12 km yr -1 , but both the spread <strong>and</strong> effects are accelerated in southern,<br />

warmer portions of the range (Ford <strong>and</strong> Vose 2007).<br />

On-going T. canadensis mortality is undoubtedly altering forest dynamics including species<br />

composition, diversity, <strong>and</strong> nutrient <strong>and</strong> energy exchanges. T. canadensis forms a foundation<br />

that supports unique species assemblages, including cold-water fishes, birds, <strong>and</strong><br />

macroinvertebrates (Ellison et al. 2005). Across the T. canadensis range, pollen records<br />

following an historic population decline 5,000 ybp provide useful insight into species likely to<br />

respond to hemlock mortality, including Betula, Acer <strong>and</strong> Quercus species (Heard <strong>and</strong> Valente<br />

2009). However, communities that develop following T. canadensis mortality may be regionspecific,<br />

thus creating greater dissimilarity across portions of the l<strong>and</strong>scape once dominated by<br />

hemlock (Ellison et al. 2005; Orwig et al. 2008). Much of the current underst<strong>and</strong>ing of the<br />

impact of T. canadensis mortality is centered in the Northern Hardwoods forest province. Yet, a<br />

large portion of the T. canadensis range lies within the Central Hardwoods forest, a province<br />

extending from West Virginia to Alabama <strong>and</strong> west to Missouri <strong>and</strong> Wisconsin (Fralish 2000).<br />

We are working to clarify the contemporary impact of this introduced disturbance across the<br />

central Appalachians. The objective of our on-going study is to quantify changes in plant<br />

community structure <strong>and</strong> ecosystem function in headwater stream riparian forests of the central<br />

Appalachian Mountains. For the broader study, we are using a chronosequence of time since<br />

HWA invasion to examine the following questions:<br />

1. How will or does T. canadensis mortality impact headwater streams at local scales, moving<br />

from the stream bank upslope<br />

2. How much variation can we expect in these changes both across the central Appalachians<br />

3. How do our results compare to underst<strong>and</strong>ing from the northeastern U.S. <strong>and</strong> southern<br />

Appalachian Mountains<br />

4. What can we predict in terms of forest composition <strong>and</strong> function over time as T. canadensis<br />

mortality progresses <strong>and</strong> forests transition to an alternate ecosystem<br />

Before HWA arrives, we are quantifying the vegetation <strong>and</strong> environmental relationships in T.<br />

canadensis dominated ravines important for natural heritage <strong>and</strong> recreation on the unglaciated<br />

Allegheny Plateau of southeastern Ohio. Therefore, in this paper we focus on our first question:<br />

How will or does T. canadensis mortality impact headwater streams at local scales, moving<br />

from the stream bank upslope According to the projected rate of spread (12 km -1 year, Evans<br />

<strong>and</strong> Gregorie 2007) <strong>and</strong> the current USDA <strong>Forest</strong> Service map of HWA invasion (Figure 1),<br />

Ohio may be invaded within the next few years.<br />

2. Methodology<br />

For the broader study, areas have been identified in the central Appalachian region, including<br />

sites within the Allegheny Mountains of Virginia <strong>and</strong> West Virginia, <strong>and</strong> the Allegheny Plateau<br />

region of eastern Ohio. Using the United States Department of Agriculture (USDA) <strong>Forest</strong><br />

Service HWA distribution map <strong>and</strong> information available from local l<strong>and</strong> managers, we have<br />

identified <strong>and</strong> acquired research permits for study areas in the states of:<br />

<strong>Forest</strong> <strong>L<strong>and</strong>scapes</strong> <strong>and</strong> <strong>Global</strong> <strong>Change</strong>-New Frontiers in Management, Conservation <strong>and</strong> Restoration. Proceedings of the IUFRO L<strong>and</strong>scape Ecology<br />

Working Group International Conference, September 21-27, 2010, Bragança, Portugal. J.C. Azevedo, M. Feliciano, J. Castro & M.A. Pinto (eds.)<br />

2010, Instituto Politécnico de Bragança, Bragança, Portugal.

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