NE Resilience Report - Conservation Gateway
NE Resilience Report - Conservation Gateway
NE Resilience Report - Conservation Gateway
You also want an ePaper? Increase the reach of your titles
YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.
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