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NE Resilience Report - Conservation Gateway

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We hypothesized that sites with a large variety of landforms and long elevation gradients will retain more<br />

species throughout a changing climate by offering ample microclimates and thus more options for<br />

rearrangement. However, we found that in areas with very little topographic diversity, we needed a finerscale<br />

indicator of subtle micro topographic features, to distinguish between otherwise similar landscapes.<br />

We chose wetland density as a surrogate for micro-topography in flat landscapes after experimenting with<br />

several rugosity measures. Our final measure of landscape complexity was based on landform variety,<br />

elevation range and, in flats, wetland density. Below we describe how we measured each of these<br />

landscape elements.<br />

Landform Variety: To be explicit about the number of microclimatic settings created by an area’s surface<br />

features we created a landform model that delineated local environments with distinct combinations of<br />

moisture, radiant energy, deposition, and erosion. The model, based on Ruhe and Walker’s (1968) fivepart<br />

hillslope model of soil formation, and Conacher and Darymple’s (1977) nine-unit land surface model,<br />

categorizes various combinations of slope, land position, aspect, and moisture accumulation (Figure 3.1<br />

and 3.2). The methods to develop the model were based on Fels and Matson (1997) and are described in<br />

Anderson (1999) and in Appendix II. The major divisions are based on relative land position and slope<br />

(Figure 3.3) with side slopes further subdivided by aspect, and flats further subdivided by flow<br />

accumulation. The landform model can distinguish an unlimited number of landform units, but we used a<br />

simple 11 unit model that captures the major differences in settings and combines some landform types<br />

that typically occur as pairs (e.g. cliff/steep slope, cove/slope bottom) so they did not skew the results.<br />

The types include the following (Figure 3.1-3.3):<br />

Cliff/steep slope<br />

Summit/ridgetop<br />

<strong>NE</strong> sideslope<br />

SE sideslope<br />

Cove/slope bottom,<br />

Low hill<br />

Low hilltop flat<br />

Valley/toeslope<br />

Dry flat<br />

Wet flat<br />

Water/lake/river<br />

To calculate the landform variety metric we tabulated the number of landforms within a 100-acre circle<br />

around every 30-meter cell in the region using a focal variety analysis on the 11 landform types. Scores<br />

for each cell ranged from 1 to 11 (Map 3.1, Figure 3.4 a. & b.) with a mean of 6.05 and a standard<br />

deviation of 1.85.<br />

With respect to climate change, our assumption was that separate landform settings will retain their<br />

distinct processes despite a changing climate. For example, a hot dry eroding upper slope will continue to<br />

offer a climatic environment different from a cool moist accumulating toe slope.<br />

16 Resilient Sites for Terrestrial <strong>Conservation</strong> in the Northeast and Mid-Atlantic Region<br />

The Nature Conservancy • Eastern <strong>Conservation</strong> Science • Eastern Division • 99 Bedford St • Boston, MA 02111

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