Ecological effects of biodiversity 1250786 214104387 2008-05-22T02:56:14Z 202.36.179.66 The diversity of [[species diversity|species]] and [[genetic diversity|genes]] in [[community ecology|ecological communities]] affects the functioning of these communities. These '''ecological effects of biodiversity''' in turn affect both [[climate change]] through enhanced [[greenhouse gas]]es, [[Particulate|aerosols]] and loss of land cover, and biological diversity, causing a rapid loss of [[ecosystem]]s and [[extinction]]s of [[species]] and local populations. The current rate of extinction is sometimes considered a [[extinction event|mass extinction]], with current species extinction rates on the order of 100 to 1000 times as high as in the past.<ref name="Vitousek et al. 1997">Vitousek, P.M., Mooney, H. A., and Lubchenco, J. et al. 1997.Human domination of Earth's ecosystems. Science 277: 494-499.</ref> The two main areas where the effect of biodiversity on ecosystem function have been studied are the relationship between diversity and productivity, and the relationship between diversity and community stability. More biologically diverse communities appear to be more productive (in terms of [[biomass]] production) than are less diverse communities, and they appear to be more stable in the face of perturbations. Also animals that inhabit an area may alter the surviving conditions by factors assimilated by climate. ===Definitions of diversity, productivity, and stability=== In order to understand the effects that changes in [[biodiversity]] wiill have on ecosystem functioning, it is important to define some terms. Biodiversity is not easily defined, but may be thought of as the number and/or evenness of [[gene]]s, species, and ecosystems in a [[region]]. This definition includes [[genetic diversity]], or the diversity of genes within a species, [[species diversity]], or the diversity of species within a [[habitat (ecology)|habitat]] or region, and ecosystem diversity, or the diversity of habitats within a region. Two things commonly measured in relation to changes in diversity are productivity and [[stability]]. Productivity is a measure of ecosystem function. It is generally measured by taking the total aboveground [[biomass]] of all plants in an area. Many assume that it can be used as a general indicator of ecosystem function and that total resource use and other indicators of ecosystem function are correlated with productivity. Stability is much more difficult to define, but can be generally thought of in two ways. General stability of a population is a measure that assumes stability is higher if there is less of a chance of extinction. This kind of stability is generally measured by measuring the [[statistical variability|variability]] of aggregate community properties, like total biomass, over time <ref name="Doak 1998">Doak, D.F., Bigger, D., Harding, E.K., et al. 1998. The statistical inevitability of stability-diversity relationships in community ecology. Am. Nat. 151: 264-276.</ref> The other definition of stability is a measure of resilience and resistance, where an ecosystem that returns quickly to an [[Homeostasis#Ecological homeostasis|equilibrium]] after a perturbation or resists invasion is thought of as more stable than one that doesn't.<ref name="McCann 2000">McCann, K.S. 2000. The diversity-stability debateing. Nature 405: 228-233.</ref> ===Productivity and stability as indicators of ecosystem health=== The importance of stability in community ecology is clear. An unstable ecosystem will be more likely to lose species. Thus, if there is indeed a link between diversity and stability, it is likely that losses of diversity could feedback on themselves, causing even more losses of species. Productivity, on the other hand, has a less clear importance in community ecology. In managed areas like [[farm|cropland]], and in areas where animals are grown or caught, increasing productivity increases the [[economics|economic]] success of the area and implies that the area has become more efficient, leading to possible long term resource [[sustainability]].<ref name="Fridley 2001">Fridley, J.D. 2001. The influence of species diversity on ecosystem productivity: how, where, why? Oikos 93: 514-526.</ref> It is more difficult to find the importance of productivity in natural ecosystems. This will be discussed in more detail later. ===Does biodiversity have value?=== Beyond the value biodiversity has in regulating and stabilizing ecosystem processes, there are direct economic consequences of losing diversity in certain ecosystems and in the world as a whole. Losing species means losing potential [[food]]s, [[medicine]]s, industrial products, and [[tourism]], all of which have a direct economic effect on peoples lives.<ref name="Wilson 1992">[[Edward Osborne Wilson|Wilson,E.O.]] 1992. The Diversity of Life. Harvard Univ. Press, Cambridge, Mass., U.S.A.</ref> For more information, see the [[biodiversity#Economic role of biodiversity|economic role of biodiversity]]. ==Effects of diversity on community productivity== ===How species diversity may influence productivity=== * '''Complementarity''' Plant species coexistence is thought to be the result of [[ecological niche|niche]] partitioning, or differences in resource requirements among species. By complementarity, a more diverse plant community should be able to use resources more completely, and thus be more productive.<ref name = "Fridley 2001"/><ref name = "Tilman et al. 1997a">Tilman, D., Knops, J., Wedin, D. et al. 1997a. The influence of functional diversity and composition on ecosystem processes. Science 277: 1300-1302.</ref> Also called niche differentiation, this mechanism is a central principle in the [[functional group]] approach, which breaks species diversity down into functional components. <ref name = "Tilman et al. 1997b">Tilman, D., Lehman, C.L. and Thomson, K.T. 1997b. Plant diversity and ecosystem productivity: theoretical considerations. Proc. Natl. Acad. Sci. USA 94: 1857-1861.</ref><ref name ="Tilman 1999">Tilman, D. 1999. The ecological consequences of changes in biodiversity: a search for general principles. Ecology 80: 1455-1474.</ref> * '''Facilitation ''' [[Facilitation]] is a mechanism whereby certain species help or allow other species to grow by modifying the environment in a way that is favorable to a co-occurring species.<ref name = "Vandermeer 1989">Vandermeer, J. H. 1989. The ecology of intercropping. Cambridge Univ. Press., Cambridge, England.</ref> Plants can interact through an intermediary like nitrogen, water, temperature, space, or interactions with weeds or herbivores among others. Some examples of facilitation include large desert perennials acting as nurse plants, aiding the establishment of young neighbors of other species by alleviating water and temperature stress,<ref name = "Turner et al. 1966">Turner, R.M., Alcorn, S.M., Olin, G. and Booth, J.A. 1966. The influence of shade, soil, and water on saguaro seedling establishment.Bot. Gaz. 127: 95-102.</ref> and nutrient enrichment by nitrogen-fixers such as legumes. * '''The Sampling Effect ''' The sampling effect of diversity can be thought of as having a greater chance of including a species of greatest inherent productivity in a plot that is more diverse. This provides for a composition effect on productivity, rather than diversity being a direct cause. However, the sampling effect may in fact be a compilation of different effects. The sampling effect can be separated into the greater likelihood of selecting a species that is 1) adapted well to particular site conditions, or 2) of a greater inherent productivity. Additionally, one can add to the sampling effect a greater likelihood of including 3) a pair of species that highly complement each other, or 4) a certain species with a large facilitative effect on other members of the community. ===Review of data=== Field experiments to test the degree to which diversity affects community productivity have found many things, but many long term studies in [[grassland]] ecosystems have found that diversity does indeed enhance the productivity of ecosystems. <ref name ="Tilman et al. 1996">Tilman, D., Wedin, D, and Knops, J. 1996. Productivity and sustainability influenced by biodiversity in grassland ecosystems. Nature 379: 718-720.</ref><ref name ="Naeem et al 1994">Naeem, S., Thompson, L.J., Lawler, S.P, et al. 1994. Declining biodiversity can alter the performance of ecosystems. Nature 368: 734-737.</ref> <ref name ="Hooper and Vitousek 1997"> Hooper, D. and Vitousek, P. 1997. The effect of plant composition and diversity on ecosystem processes. Science 277: 1302-1305.</ref> Evidence of the relationship has also been found in grassland microcosms. However, these different studies have come to different conclusions as to whether the cause was due more to diversity or to species composition. Recent mathematical models have highlighted the importance of ecological context in unraveling this problem. Some models have indicated the importance of [[disturbance]] rates and spatial [[heterogeneous|heterogeneity]] of the environment,<ref name ="Cardinale et al. 2000">Cardinale B.J., Nelson K., Palmer M.A. 2000. Linking species diversity to the functioning of ecosystems: on the importance of environmental context. Oikos 91: 175-183.</ref> others have indicated that the time since disturbance and the habitatÂ’s carrying capacity can cause differing relationships.<ref name ="Aarssen et al. 2003">Aarssen, L.W., Laird, R.A., and Pither J. 2003. Is the productivity of vegetation plots higher or lower when there are more species? Variable predictions from interaction of the "sampling effect" and "competitive dominance effect" on the habitat templet. Oikos 102: 427-432.</ref> Each ecological context should yield not only a different relationship, but a different contribution to the relationship due to diversity and to composition. ===Implications for ecology/future research=== In order to correctly identify the consequences of diversity on productivity and other ecosystem processes, many things must happen. First, it is imperative that scientists stop looking for a single relationship. It is obvious now from the models, the data, and the theory that there is no one overarching effect of diversity on productivity. Scientists must try to quantify the differences between composition effect and diversity effects, as many experiments never quantify the final realized species diversity (instead only counting numbers of species of seeds planted) and confound a sampling effect for facilitators (a compositional factor) with diversity effects. Relative amounts of [[overyielding]] (or how much more a species grows when grown with other species than it does in monoculture) should be used rather than absolute amounts as relative overyielding can give clues as to the mechanism by which diversity is influencing productivity, however if experimental protocols are incomplete, one may be able to indicate the existence of a complementary or facilitative effect in the experiment, but not be able to recognize its cause. Experimenters should know what the goal of their experiment is, that is, whether it is meant to inform natural or managed ecosystems, as the sampling effect may only be a real effect of diversity in natural ecosystems (managed ecosystems are composed to maximize complementarity and facilitation regardless of species number). By knowing this, they should be able to choose spatial and temporal scales that are appropriate for their experiment. Lastly, to resolve the diversity-function debate, it is advisable that experiments be done with large amounts of spatial and resource heterogeneity and environmental fluctuation over time, as these types of experiments should be able to demonstrate the diversity-function relationship more easily.<ref name = "Fridley 2001"/> ==Effects of diversity on community stability== ===How species diversity may influence community stability=== * '''Averaging Effect''' If all species have differential responses to changes in the ecosystem over time, then the averaging of these responses will cause a more temporally stable ecosystem if more species are in the ecosystem.<ref name ="Doak 1998"/>. This effect is a [[statistics|statistical]] effect due to summing [[randomness|random]] [[variable]]s. * '''Negative Covariance Effect''' If some species do better when other species are not doing well, then when there are more species in the ecosystem, their overall [[variance]] will be lower than if there were fewer species in the system. This lower variance indicates higher stability. <ref name ="Tilman et al. 1998"> Tilman, D., Lehman, C.L. and Bristow, C.E. 1998. Diversity-stability relationships: statistical inevitability or ecological consequence. Am. Nat. 151: 264-276.</ref> This effect is a consequence of [[competition]] as highly competitive species will negatively [[covariance|covary]]. * '''Insurance Effect''' If an ecosystem contains more species then it will have a greater likelihood of having [[redundancy (engineering)|redundant]] stabilizing species, and it will have a greater number of species that respond differently to perturbations. This will enhance an ecosystem's ability to [[wiktionary:Buffer|buffer]] perturbations.<ref name ="Naeem and Li 1997">Naeem, S. and Li, S. 1997. Biodiversity enhances ecosystem reliability. Nature 390: 507-509.</ref> * '''Resistance to Invasion''' Diverse communities may use resources more completely than simple communities because of a diversity effect for complementarity. Thus [[bioinvader|invaders]] may have reduced success in diverse ecosystems, or there may be a reduced likelihood that an invading species will introduce a new property or process to a diverse ecosystem.<ref name ="Elton 1958">Elton, C.S. 1958. The ecology of invasions by animals and plants. John Wiley, New York, New York, USA.</ref> <ref name ="Tilman 1999"/> <ref name ="Chapin et al. 1997">Chapin, F.S., III, Walker, B.H., Hobbs, R.J. et al. 1997. Biotic control over the functioning of ecosystems. Science 277: 500-504.</ref> * '''Resistance to Disease''' A decreased number of competing plant species may allow the abundances of other species to increase, facilitating the spread of diseases of those species. <ref name ="Elton 1958"/> <ref name = "Chapin et al. 1997"/> <ref name = "Mitchell et al. 2002">Mitchell, C.E., Tilman, D. and Groth, J.V., Effects of grassland plant species diversity, abundance, and composition on foliar fungal disease. Ecology 83: 1713-1726.</ref> ===Review of temporal stability data=== Models have predicted that [[empirical]] relationships between [[time|temporal]] variation of community productivity and species diversity are indeed real, and that they almost have to be. Some temporal stability data can be almost completely explained by the averaging effect by constructing null models to test the data against.<ref name = "Doak 1998"/><ref name = "Tilman et al. 1996">Tilman, D., Wedin, D, and Knops, J. 1996. Productivity and sustainability influenced by biodiversity in grassland ecosystems. Nature 379: 718-720.</ref> Competition, which causes negative covariances, only serves to strengthen these relationships. ===Review of resistance/resilience stability data=== This area is more contentious than the area of temporal stability, mostly because some have tried generalizing the findings of the temporal stability models and theory to stability in general. While the relationship between temporal variations in productivity and diversity has a mathematical cause, which will allow the relationship to be seen much more often than not, it is not the case with resistance/resilience stability. Some experimenters have seen a [[correlation]] between diversity and reduced invasibility, though many have also seen the opposite. <ref name = "Dukes 2001">Dukes, J.S. 2001. Biodiversity and invisibility in grassland microcosms. [[Oecologia]] 126: 563-568.</ref> The correlation between diversity and disease is also tenuous, though theory and data do seem to support it.<ref name ="Mitchell et al. 2002"/> ===Implications for ecology/future research=== In order to more fully understand the effects of diversity on the temporal stability of ecosystems it is necessary to recognize that they are bound to occur. By constructing null models to test the data against (as in Doak et al. 1998<ref name = "Doak 1998"/>) it becomes possible to find situations and ecological contexts where ecosystems become more or less stable than they should be. Finding these contexts would allow for mechanistic studies into why these ecosystems are more stable, which may allow for applications in [[conservation ethic|conservation]] management. More importantly more complete experiments into whether diverse ecosystems actually resist invasion and disease better than their less diverse equivalents as invasion and disease are two important factors that lead to species extinctions in the present day. ==Theory and preliminary effects from examining food webs== One major problem with both the diversity-productivity and diversity-stability debates discussed up to this point is that both focus on interactions at just a single [[trophic level]]. That is, they are concerned with only one level of the [[food web]], namely plants. Other research, unconcerned with the effects of diversity, has demonstrated strong top-down forcing of ecosystems (see [[keystone species]]). There is very little actual data available regarding the effects of different food webs, but theory helps us in this area. First, if a food web in an ecosystem has a lot of weak [[interaction]]s between different species, then it should have more stable populations and the community as a whole should be more stable.<ref name ="McCann 2000">McCann, K.S. 2000. The diversity-stability debate. Nature 405: 228-233.</ref> If upper levels of the web are more diverse, then there will be less [[biomass]] in the lower levels and if lower levels are more diverse they will better be able to resist [[consumption (economics)|consumption]] and be more stable in the face of consumption. Also, top-down forcing should be reduced in less diverse ecosystems because of the bias for species in higher trophic levels to go extinct first.<ref name ="Duffy 2002">Duffy, J.E. 2002. Biodiversity and ecosystem function: the consumer connection. Oikos99: 201-219</ref> Lastly, it has recently been shown that [[predator|consumers]] can dramatically change the biodiversity-productivity-stability relationships that are implied by plants alone.<ref name ="Worm and Duffy 2003">Worm, B. and Duffy, J.E. 2003.Biodiversity, productivity and stability in real food webs. Trends in Ecology and Evolution 18: 628-632.</ref> Thus, it will be important in the future to incorporate food web theory into the future study of the effects of biodiversity. In addition this complexity will need to be addressed when designing biodiversity management plans. ==Conclusions== It is imperative that we come to a realization that there is no single overarching effect of diversity on either productivity or stability. The realized effects will depend heavily on environmental context and the time scale over which the effects are studied. However, it has become obvious that biodiversity is indeed important for both managed and natural ecosystems, though the relative contributions of diversity and composition remain unclear. It is therefore necessary for legislators to understand the basic science in order to maintain diversity at its current levels. If current human growth and resource management patterns do not change, it is likely that we will lose many important species, and the ecosystems of the world may never recover. ==References== <references/> ==See also== *[[Biodiversity]] *[[Ecosystem services]] [[Category:Biodiversity]]