Reconciliation ecology
Reconciliation ecology
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Reconciliation ecology

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Reconciliation ecology

Reconciliation ecology is the branch of ecology which studies ways to encourage biodiversity in the human-dominated ecosystems of the anthropocene era. Michael Rosenzweig first articulated the concept in his book Win-Win Ecology, based on the theory that there is not enough area for all of earth's biodiversity to be saved within designated nature preserves. Therefore, humans should increase biodiversity in human-dominated landscapes. By managing for biodiversity in ways that do not decrease human utility of the system, it is a "win-win" situation for both human use and native biodiversity. The science is based in the ecological foundation of human land-use trends and species-area relationships. It has many benefits beyond protection of biodiversity, and there are numerous examples of it around the globe. Aspects of reconciliation ecology can already be found in management legislation, but there are challenges in both public acceptance and ecological success of reconciliation attempts.

Traditional conservation is based on "reservation and restoration"; reservation meaning setting pristine lands aside for the sole purpose of maintaining biodiversity, and restoration meaning returning human impacted ecosystems to their natural state. However, reconciliation ecologists argue that there is too great a proportion of land already impacted by humans for these techniques to succeed.

While it is difficult to measure exactly how much land has been transformed by human use, estimates range from 39 to 50%. This includes agricultural land, pastureland, urban areas, and heavily harvested forest systems. An estimated 50% of arable land is already under cultivation. Land transformation has increased rapidly over the last fifty years, and is likely to continue to increase. Beyond direct transformation of land area, humans have impacted the global biogeochemical cycles, leading to human caused change in even the most remote areas. These include addition of nutrients such nitrogen and phosphorus, acid rain, ocean acidification, redistribution of water resources, and increased carbon dioxide in the atmosphere. Humans have also changed species compositions of many landscapes that they do not dominate directly by introducing new species or harvesting native species. This new assemblage of species has been compared to previous mass extinctions and speciation events caused by formation of land bridges and colliding of continents.

The need for reconciliation ecology was derived from patterns of species distribution and diversity. The most relevant of these patterns is the species-area curve which states that a larger geographic area will contain higher species diversity. This relationship has been supported by so large a body of research that some scholars consider it to be an ecological law.

There are two main reasons for the relationship between number of species and area, both of which can be used as an argument for conservation of larger areas. The habitat heterogeneity hypothesis claims that a larger geographic area will have a greater variety of habitat types, and therefore more species adapted to each unique habitat type. Setting aside a small area will not encompass enough habitat variety to contain a large variety of species. The equilibrium hypothesis draws from the theory of island biogeography as described by MacArthur and Wilson. Large areas have large populations, which are less likely to go extinct through stochastic processes. The theory assumes that speciation rates are constant with area, and a lower extinction rate coupled with higher speciation leads to more species.

The species-area relationship has often been applied to conservation, often quantitatively. The simplest and most commonly used formula was first published by Frank W. Preston. The number of species present in a given area increases in relationship to that area with the relationship S = cAz where S is the number of species, A is the area, and c and z are constants which vary with the system under study. This equation has frequently been used for designing reserve size and placement (see SLOSS debate). The most common version of the equation used in reserve design is the formula for inter-island diversity, which has a z-value between 0.25 and 0.55, meaning protecting 5% of the available habitat will preserve 40% of the species present. However, inter-provincial species area relationships have z-values closer to 1, meaning protecting 5% of habitat will only protect 5% of species diversity.

Taken together, proponents of reconciliation ecology see the species-area relationship and human domination of a large percentage of the earth's area as a sign that we will not be able to set aside enough land to protect all of life's biodiversity. There can be negative effects of setting land aside because it means the remaining land is used more intensely. For example, less land is required for crop production when high levels of inorganic fertilizer is applied, but these chemicals will affect nearby land set aside for natural ecosystems. The direct benefits of land transformation for the growing world population often make it ethically difficult to justify the tradeoff between biodiversity and human use. Reconciled ecosystems are ones in which humans dominate, but natural biodiversity is encouraged to persist within the human landscape. Ideally, this creates a more sustainable socio-ecological system and does not necessitate a trade off between biodiversity and human use.

How can understanding of species' natural history aid their effective conservation in human-dominated ecosystems? Humans often conduct activities that allow for the incorporation of other species, whether as a by-product or as a result of a focus on nature. Traditional natural history can only inform how best to do this to a certain degree, because landscapes have been changed so dramatically. However, there is much more to learn through direct study of species' ecology in human-dominated ecosystems, through what is known as focused natural history. Rosenzweig cites four examples: shrikes (Laniidae) thrived in altered landscapes when wooden fence post perches allowed them easy access to pouncing on prey, but inhospitable steel fence posts contributed to their decline. Replacing steel fence posts with wood fence posts reverses the shrikes' decline and allows humans to determine the reasons for the distribution and abundance of shrikes. Additionally, the cirl bunting (Emberiza cirlus) thrived on farms when fields alternated between harvests and hay, but declined where farmers began to plant winter grain crops, natterjack toads (Bufo calamatus) declined when reductions in sheep grazing ceased to alter ponds to their preferred shape and depth, and longleaf pine (Pinus palustris) declined in the Southeastern United States when lack of wildfires prevented its return after timbering. Thus, applying focused natural history in human-dominated landscapes can contribute to conservation efforts.

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