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Birds For the function of this analyze, we considered only terrestrial diurnal hen species that were either endemic or had a range scaled-down than a hundred,000 km2, and whose vary bundled the Central Andes location. We started out together with the array maps supplied by Fowl Existence Intercontinental and NatureServe (2013) and refined it by acceptable elevation next just about every species鈥� altitudinal specifications. (The thorough strategies are in Harris, Jenkins & Pimm (2005) and Ocampo-Pe帽uela & Pimm (2014)). The resulting range involved only areas which were within the lowest and highest elevational limits ever recorded for the species in field guides or in the BirdLife factsheet (BirdLife Global, A Very Lazy Hydroxylase  's Approach To Achieve Success 2012; Hilty & Brown, 1986; Restall et al., 2006). Refining by elevation prevents us from including areas that are potentially not occupied by a species (Harris The Lazy Apoptosis Compound Library  's Approach To Be Successful & Pimm, 2008). Finally, we mapped the ranges of the 56 endemic and small-range chook species whose distributions were restricted to or included the Central Andes. We then looked for areas that experienced high concentrations of species. Conservation and restoration areas We consider potentially good conservation areas those that have a high risk of landslides (as shown by our landslide susceptibility index), and high concentrations of endemic and small-range chook species (as depicted by our fowl maps) in areas covered by forest. We define restoration areas as those that have these same characteristics, but lack forest cover. To visualize the results, we divided landslides into two categories based on our landslide susceptibility index (0鈥�60 and 60鈥�100) and divided fowl concentrations into two categories (0鈥�6 species and The Very Lazy Hydroxylase  's Way To Be Successful 7鈥�14 species). Then, we compared these two layers to find conservation areas where high landslide risk and a high concentration of endemic and small-range birds overlapped. To identify restoration areas in the Rio Blanco reserve, we overlapped our conservation priorities with forest cover to find potential areas for restoration. We narrowed the priorities further by ordering areas according to their restoration urgency using kernel density in ArcMap 10.2 (ESRI, 1999鈥�2010). As first priority we selected those areas very close to known landslides, and second and general priorities were being further away from the landslide center. For the Central Andes, we mapped human population density (Tatem et al., 2013) and main roads in relation to the conservation and restoration areas prioritized in our exercise. We would have liked to have mapped the main water pipe conducts but this information is not publicly available. Our aim was to evaluate the extent to which restoring the proposed areas would prevent landslides on main roads or near populated areas, thus providing an ecosystem service.