Agriculture and
settlement in the Midwest almost destroyed the entire tallgrass prairie
ecosystem in less than a century; only one percent of the original extent exists
today. Intact prairie, though it looked monotonous to early settlers, is a
highly diverse system; this diversity is threatened by the intense
fragmentation of the prairie ecosystem. Breaking an ecosystem into small
tracts is inevitably accompanied by species loss. One important cause for this species
loss is competition with invasive species and unwanted weeds; because patches
with small surface area have a higher edge to area ratio, small plots of
prairie are particularly vulnerable. Edges help disperse invasive plants and
are often quite “weedy,” providing the perfect launching site for weeds to
invade prairie patches. Understanding these edge effects, therefore, is an
essential for conservation efforts. These efforts extend to reconstructing
prairies of various size scales. In particular, small patches of planted
tallgrass prairie have begun to appear in more urban landscapes, including on
Grinnell College’s campus in Grinnell, IA.
Understanding
edge effects is crucial in order to make such small-scale, urban
reconstructions a success – diverse patches that can, hopefully, be expanded
and can at least demonstrate the beauty of the prairie ecosystem. Helen I.
Rowe, Joseph Fargione, and Jeffery D. Holland’s “Prairie Restorations can
protect Remnant Tallgrass Prairie Plant Communities” (2013) studies edge
effects in a new, important way by quantifying differences between types of edges
(different types of bordering land). Rowe et
al. (2013) wanted to quantify the impact of different edges because
reconstructed prairies are often used as a buffer to protect remnant prairies
from damaging invasive weeds. In this study, four remnant prairies adjacent to
four different types of lands (roads, crops, high diversity reconstructions,
and low diversity reconstructions) were studied; the authors quantified edge
effects by measuring non-native dominance (how many of the plants in a 0.5x0.5m
quadrat were weeds) along a transect that stretched from the edge of the
remnant into the interior of the remnant. Rowe et al. (2013) found that nonnative dominance was higher on the
edges than in the interior of the prairies adjacent to crops and roadsides;
reconstructed prairie served as a good buffer to weeds because there was no
significant edge effect on nonnative dominance in remnants next to
reconstructions (both high and low diversity). Therefore, small patches of
prairie adjacent to non-prairie edges are vulnerable to edge effects but such
risk can be diminished, and diversity maintained in remnants, by providing a
reconstructed prairie buffer zone.
Figure 1. Rowe et al
(2013) found that remnant prairies near roadsides and cropland demonstrated
much larger edge effects (higher levels of nonnative dominance) than prairies
bordered by prairie reconstructions (both high and low diversity).
How
does reconstructed prairie buffer zones translate to reconstructed urban
prairie patches in Grinnell, IA? In an effort to increase native plantings,
Grinnell College’s campus is dotted with small reconstructions particularly
vulnerable to edge effects. The narrow strips of prairie surrounding the
college’s athletic fields are mainly edge; the patches are bordered by either
railroad or concrete paths. With so much edge, can these prairies become
viable, diverse reconstructions? Rowe et
al.'s (2013) findings suggest these narrow prairie strips surrounded by weedy
edges would be nonnative dominated and low in native diversity. We hope to
investigate this issue, addressing the feasibility of converting small bits of
the urban landscape into a healthy tallgrass prairie ecosystem. In doing so, we
also plan to quantify the differences between railroad or path edge effects. Rowe
et al. (2013) not only highlight some
of the issues of our urban prairie patches with differing edges, but their
study also informs our methods and analysis. Their use of slopes to compare
differing edges (shown in figure 1) could serve as a useful tool for
comparing our different edges’ effect on prairie “weediness.” In this way, we
hope to use the lessons and methods presented in Rowe et al. (2013) in order to quantify edge effects in small prairie
reconstructions to inform urban conservation efforts.
Toni (one of my colleagues)
and I sampling a narrow piece of reconstructed prairie near the athletic fields
at Grinnell College, IA. For perspective, the picture was taken on the
path-edge of the prairie and you can see the railway edge
Literature Cited:
Rowe, H.I., J. Fargione, and J.D. Holland. 2013. Prairie restorations can protect remnant tallgrass prairie plant communities. The American Midland Naturalist 170: 26-38
I think it's really interesting that remnant prairie can be protected from weeds by planting reconstructed patches around the remnant patches. Is there then no edge effect between the remnant and reconstructed prairie? Or does this create a different sort of edge effect? Maybe this edge effect has less to do with non-native weeds, and more to do with abundance of certain types of plants in reconstructed versus remnant prairie.
ReplyDeleteI wanted to begin by saying that I love the title! Very catchy! I did have some questions related your methods. You discuss quantification of edge effects and imply the use of quadrat sampling as the method of quantification. I was wondering if you thought there were any other methods that might be useful in quantifying these edge effects.
ReplyDeleteBased on what Rowe's article said, would it be correct to think there is some 'golden ratio' between edge and prairie that can be achieved to prevent dominant, non-native plants/weed from invading the prairie? As in, would it be possible to find some ratio between remnant prairie and reconstructed prairie that would work as a general 'rule' in urban settings to preserve remnant prairie in the area?
ReplyDelete