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Sanderling Plan - Western Hemisphere Shorebird Reserve Network

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for commercial construction projects), and mechanized beach raking (removal of seaweed and<br />

other debris for aesthetic purposes) all alter the sand composition, prey abundance, and other<br />

attributes of the habitat, and likely impact <strong>Sanderling</strong>s and other organisms as well (e.g., nesting<br />

sea turtles). These practices are common along U.S. coasts, although their impacts on<br />

invertebrate populations and their predators (i.e., shorebirds) are largely unstudied. Fortunately,<br />

however, some habitat loss and most habitat degradation is reversible. Means of reversal can be<br />

through habitat restoration or though improved/altered management practices, e.g., timing of<br />

certain practices with relation to wildlife needs, and ensuring/requiring comparable sediment<br />

particle size in imported sediments (a habitat characteristic that influences <strong>Sanderling</strong><br />

distributions; Danufsky and Colwell 2003) (Drut and Buchanan 2000).<br />

Within the breeding range, habitat loss and degradation are also issues, albeit from less<br />

visible threats. High-arctic breeding habitat is far from most human habitation and development,<br />

however global climate change impacts are exaggerated there and may disrupt prey availability<br />

and nesting habitat of <strong>Sanderling</strong>s (see Climate Change, below).<br />

Several other types of habitat degradation occur in many parts of the nonbreeding range:<br />

Exotic invertebrates, plants, and vertebrates. The introduction of exotic marine<br />

invertebrates into coastal and interior waters may impact shorebirds prey populations. Exotic<br />

plants may alter sand roost characteristics, such as through changes in dune communities or dune<br />

dynamics, or through changes in algal communities, and/or may cause changes in foraging areas<br />

(tidal flats) or susceptibility to predation.<br />

Utility lines: Many bird species, including shorebirds, have died from in-flight collisions<br />

with utility lines (e.g., Kitchin 1949, Bevanger 1994, Brown and Drewien 1995, Janss and Ferrer<br />

1998). The placement of utility lines next to intertidal areas where shorebirds forage and roost<br />

degrades habitat quality, by incurring an added source of mortality (Kitchin 1949, Buchanan<br />

2000). Additionally, utility lines or poles adjacent to foraging areas may become perches for<br />

avian predators, potentially facilitating predation impacts (see Research and Monitoring Needs),<br />

as Peregrine Falcons favor higher perch sites with better visibility and easy access to prey<br />

(Dzialak et al. 2007).<br />

Wind turbines: <strong>Shorebird</strong> mortality has been documented at wind turbine sites in the<br />

United States and the Netherlands (Buchanan 2000). Certain regions (e.g., U.S. Pacific<br />

WHSRN – <strong>Sanderling</strong> Conservation <strong>Plan</strong>, February 2010, v1.1 39

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