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Fast Breaking Comments

By David Hooper

ESI Special Topics, February 2006
Citing URL - http://www.esi-topics.com/fbp/2006/february06-DavidHooper.html

David Hooper answers a few questions about this month's fast breaking paper in the field of Environment/Ecology.


From •>>February 2006 - [LATE ENTRY]

Field: Environment/Ecology
Article Title: Effects of biodiversity on ecosystem functioning: A consensus of current knowledge
Authors: Hooper, DU;Chapin, FS;Ewel, JJ;Hector, A;Inchausti, P;Lavorel, S;Lawton, JH;Lodge, DM;Loreau, M;Naeem, S;Schmid, B;Setala, H;Symstad, AJ;Vandermeer, J;Wardle, DA
Journal: ECOL MONOGR
Volume: 75
Issue: 1
Page: 3-35
Year: FEB 2005
* Western Washington Univ, Dept Biol, Bellingham, WA 98225 USA.
* Western Washington Univ, Dept Biol, Bellingham, WA 98225 USA.
* Univ Alaska, Inst Arctic Biol, Fairbanks, AK 99775 USA.
* USDA, US Forest Serv, Pacific SW Res Stn, Inst Pacific Isl Forestry, Honolulu, HI 96813 USA.
* Univ Zurich, Inst Environm Sci, CH-8057 Zurich, Switzerland.
* CNRS, CEBC, F-79360 Beauvoir Sur Niort, France.
* Univ Grenoble 1, CNRS, Lab Ecol Alpine, UMR 5553, F-38041 Grenoble 9, France.
* Natl Environm Res Council, Swindon SN2 1EU, Wilts, England.
* Univ Notre Dame, Dept Sci Biol, Notre Dame, IN 46556 USA.
* Ecole Normale Super, Ecol Lab, UMR 7625, F-75230 Paris 05, France.
* Columbia Univ, Dept Ecol Evolut & Environm Biol, New York, NY 10027 USA.
* Univ Helsinki, Dept Ecol & Environm Sci, FIN-15140 Lahti, Finland.
* US Geol Survey, Mt Rushmore Natl Mem, Keystone, SD 57751 USA.
* Univ Michigan, Dept Biol, Ann Arbor, MI 48109 USA.
* Landcare Res, Lincoln, New Zealand.
* Swedish Univ Agr Sci, Dept Forest Vegetat Ecol, SE-90183 Umea, Sweden.

  June 1, 2006: This paper has also been named the Emerging Research Front in Environment/Ecology for June 2006.

ST:  Why do you think your paper is highly cited?

Our paper reviews the evidence for the extent to which altered biodiversity affects ecosystem-level processes and the mechanisms underlying such effects. I think this paper is highly cited because study of this particular question in ecology has grown incredibly quickly in the last several years, and it touches on a variety of common questions in ecology: what are the mechanisms allowing different species to coexist? How do the functional traits of organisms influence ecosystem fluxes of matter and energy?


“As a follow-up to this paper, our synthesis group put together a position statement for the Ecological Society of America
(ESA) to summarize key applications of this science for managing ecosystems.”

This field has also seen its share of controversy in the last several years, with some fairly high-profile disputes in the literature about the interpretation of several key experiments. Our goal in this paper was to thoroughly review the recent literature, bringing together the major players from different sides of the arguments to try to hammer out key points of agreement, clarify important remaining questions, and distill the most important points relevant to ecosystem management. We covered a lot of ground in that paper, so our consensus points are relevant to a wide variety of questions that are still actively under investigation.

ST:  Does it describe a new discovery or a new methodology that's useful to others?

It synthesizes findings from among many different papers and tries to put them clearly into the context of a large body of previous work. I think our synthesis will be useful scientifically by clarifying general trends (as well as exceptions to those trends) and identifying key questions for future research. I hope that the consensus nature of the work will be useful in breaking down barriers among different "scientific camps" and encouraging communication.

ST:  Could you summarize the significance of your paper in layman's terms?

Humans are influencing biodiversity in ecosystems worldwide because of a variety of well-characterized global changes such as changes in atmospheric composition (e.g., elevated CO2 and other greenhouse gases), climatic changes resulting from those atmospheric changes, increasing amounts and mobility of key plant nutrients (e.g., nitrogen), changes in land use (and therefore amount of habitat), and enhanced invasions of species. All of these changes are adversely affecting biodiversity. The key question is whether declines in biodiversity will adversely affect the way ecosystems work, in terms, for example, of total plant growth, the availability of nutrients, and trophic relations—who eats who and how much.

Ecosystem processes and the resulting ecosystem services that benefit humanity are greatly influenced by the characteristics of the species present in that ecosystem. Declining biodiversity could influence these processes because key species or functional groups—sets of species with similar effects on processes—are lost from the ecosystem. For example, having more species of plants, each of which can get nutrients from different layers of the soil, or which together create a denser canopy to absorb sunlight, could lead to greater overall rates of plant production at the ecosystem scale.

Theory suggests that this should be the case, and experimental evidence at least partially supports the theory. However, other than a few key examples (e.g., plants with mutualistic associations with bacteria that enable them to use atmospheric nitrogen), we still don’t know exactly which species and how many species partition resources in this way in many ecosystems. It’s also possible that higher diversity affects processes not because of resource partitioning, but because one or two species are fast growing or very effective at taking up nutrients. Higher diversity just means a greater probability of having at least one such effective species included in the ecosystem. Our review suggests that both mechanisms can occur and that future research should attempt to more clearly delineate the different ecological conditions under which each mechanism operates.

Species diversity could influence not just overall process rates, as just discussed, but also the stability of ecosystem processes in response to disturbances (both natural and man-made), damage by pests or diseases, or year-to-year variation in climate. Again, theory, observational studies, and some experimental studies lend support to this prediction. However, understanding the underlying mechanisms is more difficult. Having more species may be important to stability because different species often have different environmental preferences. So, if conditions change such that they are less optimal for one species, other species are around to compensate. Some studies have found, however, that changes in which species are present have a larger effect on process stability than compensation among many species. One of the main points of our paper is that just knowing how many species are present is less powerful than knowing which species are present, because it is the functional traits of those species—not something special about diversity itself—that influence ecosystem processes.

ST:  How did you become involved in this research, and were there successes or failures along the way?

I started working on questions of how biodiversity affects ecosystem functioning in graduate school. I used grasslands in California as an experimental system to investigate how changing plant diversity affects ecosystem productivity and nutrient cycling. Mine happened to be one of the earlier experiments using experimental communities to investigate these questions. A couple of years after I finished my thesis, a committee from the Ecological Society of America (ESA) published a synthesis of results from several early experiments in this field. This synthesis ended up being quite controversial. Some ecologists perceived that report as too biased toward finding diversity effects and felt it did not account for other mechanisms that had been proposed to explain the results.

Following this controversy, I was asked by ESA to co-chair a committee that included representatives from all sides of the debate. We were charged with coming to consensus about key points, whether that meant agreeing on interpretations of various experiments or "agreeing to disagree." If the latter, we were to clearly outline the scientific arguments underlying any disagreements as a way to stimulate further research. The consensus process was time-consuming and often frustrating, but ultimately rewarding. It really forced everybody to communicate clearly about theoretical assumptions, important details of experimental design, alternative mechanisms that could explain observed patterns, and even semantic differences that could lead to differences in interpretation. I happened to have had some experience in consensus building as an intern in environmental and public policy conflict mediation for a year or so after finishing my undergraduate degree. I wasn’t sure that I would ever directly use that experience in my scientific work, but it sure came in handy! Overall, I think we were successful in helping to clarify past results and point out important avenues for future research.

ST:  If applicable, what are the social or political implications of your research?

As a follow-up to this paper, our synthesis group put together a position statement for the Ecological Society of America to summarize key applications of this science for managing ecosystems. The position statement is written for nonscientists, including policy makers, and can be found at the ESA Web site.End

David Hooper
Associate Professor
Department of Biology
Western Washington University
Bellingham, WA, USA


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ESI Special Topics, February 2006
Citing URL - http://www.esi-topics.com/fbp/2006/february06-DavidHooper.html

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