Matches in SemOpenAlex for { <https://semopenalex.org/work/W2767231491> ?p ?o ?g. }
- W2767231491 abstract "Vegetation clearing results in the loss of species from landscapes. Indeed, the area of remaining native vegetation is an important determinant of species richness in human-modified mosaics. Of interest to ecologists and landscape managers is the effect of areamthat is, how the number of species a landscape supports changes with the amount of native vegetation, as revealed by the shape and functional form of the species-area relationship. Understanding this is vital for guiding conservation interventions such as setting limits to vegetation clearing or establishing revegetation targets. Crucially though, it is not only vegetation area that affects patterns of species richness at the landscape levelmso do environmental attributes such as soil properties and topography. Complicating the matter is the fact that these attributes tend to be correlated with landscape-level vegetation area, because humans preferentially remove vegetation from landscapes suited to land uses such as agriculture. However, this interplay between vegetation area, other landscape attributes, and biased patterns of vegetation loss/retention is infrequently considered in landscape-level species-area analyses. If unaccounted for, these confounding factors may result in erroneous interpretations of the effect of area, leading to suboptimal management actions. The aim of this thesis was to examine how attributes of landscapes affect the relationship between species richness and vegetation area. Through four specific research questions, I explored in detail the hypothesis that attributes of human-modified landscapes that bias vegetation clearing also interact with vegetation area to produce landscape-specific area effects on species richness. First, I quantified correlates of vegetation clearing/retention in two regions of the southern hemisphere, and reviewed the literature to determine how often, and in what ways, biased clearing patterns are accounted for in studies relating vegetation area to an ecological response. I demonstrated that soil properties and range in elevation are reliably associated with the amount of remaining native vegetation across ~18,000 100 km2 landscapes in Australia and South Africa. Importantly though, I found that clearing biases were explicitly acknowledged in only 15 of the 118 reviewed studies. If the area of native vegetation in landscapes is a legacy of biased clearing, confounding factors like soil properties should be accounted for in analyses of area effects. Second, I explored the extent to which the effect of native vegetation area on species richness differed in 100 km2 landscapes categorised by attributes such as soil fertility, range in elevation or matrix land use. Using a case study of south-east Australian birds, I found that the shape of the species-area relationship varied substantially depending on whether landscapes were, for example, more- or less-topographically variable, or had higher or lower soil fertility. While threshold models depicting a point of sudden change in the effect of area emerged consistently, the amount of vegetation corresponding with observed thresholds differed considerably among landscape types. Therefore, aggregating and analysing species-area data from different landscape types is likely to misrepresent how species richness is affected by vegetation area. This will be exacerbated by clearing biases, because heavily cleared landscapes tend to be characterised by very different attributes to high cover landscapes. Third, I compared the effect of vegetation area on bird species richness at three scales of analysis (landscapes of 25 km2, 100 km2, 400 km2) for two regions of south-east Australia. When data for the entire study extent were analysed, a remarkable degree of scale-invariance was observedmnamely, a threshold relationship with a change-point at approximately 30% vegetation cover. However, when data were analysed for two regional subsets of the overall dataset, the effect of vegetation area, and the factors moderating this relationship, were scale-dependent. Given this finding, observed thresholds can only reliably be used to guide landscape management at the scale and in the region where the relationship was observed. Finally, I evaluated the implications of accounting for clearing biases when using species-area relationships to guide conservation, focussing on a region of Australia undergoing rapid landscape transformation. I found that using observed thresholds from species-area models that do and do not account for landscape attributes yielded different outcomes for landscape-scale species richness conservation, given a scenario of future vegetation loss. Specifically, the number and location of landscapes that could be prioritised for conservation actions varied considerably depending on the species-area model used. This research demonstrates that the effect of area on species richness differs substantially as a function of the attributes of landscapes. Crucially, clearing biases underpinned by these same attributes can confound analyses of the species-area relationship. Accounting for landscape attributes will allow for a more rigorous understanding of how species richness varies among landscapes with different amounts of native vegetation. A robust appreciation of the effect of area will provide more certainty around how much vegetation needs to be managed (i.e. protected, revegetated), and where this should occur among multiple landscapes, to avert the loss of, or enhance, landscape-scale species richness." @default.
- W2767231491 created "2017-11-17" @default.
- W2767231491 creator A5004754276 @default.
- W2767231491 date "2017-06-21" @default.
- W2767231491 modified "2023-09-27" @default.
- W2767231491 title "Implications of vegetation clearing biases for the interpretation of landscape-scale species-area relationships" @default.
- W2767231491 cites W136159158 @default.
- W2767231491 cites W1487654381 @default.
- W2767231491 cites W14932847 @default.
- W2767231491 cites W1494793062 @default.
- W2767231491 cites W1496425362 @default.
- W2767231491 cites W1497165213 @default.
- W2767231491 cites W1501534531 @default.
- W2767231491 cites W1513912195 @default.
- W2767231491 cites W1518897246 @default.
- W2767231491 cites W1520907354 @default.
- W2767231491 cites W1523676411 @default.
- W2767231491 cites W1542847053 @default.
- W2767231491 cites W1564462405 @default.
- W2767231491 cites W1567459460 @default.
- W2767231491 cites W1584343945 @default.
- W2767231491 cites W1588676708 @default.
- W2767231491 cites W1590962353 @default.
- W2767231491 cites W1607415717 @default.
- W2767231491 cites W1608598779 @default.
- W2767231491 cites W1766029576 @default.
- W2767231491 cites W1803843921 @default.
- W2767231491 cites W1834602081 @default.
- W2767231491 cites W1861062512 @default.
- W2767231491 cites W1867783020 @default.
- W2767231491 cites W1875284268 @default.
- W2767231491 cites W1893187722 @default.
- W2767231491 cites W1905358649 @default.
- W2767231491 cites W1908593855 @default.
- W2767231491 cites W1910907980 @default.
- W2767231491 cites W1923840614 @default.
- W2767231491 cites W1936774573 @default.
- W2767231491 cites W1964434544 @default.
- W2767231491 cites W1966305178 @default.
- W2767231491 cites W1968121043 @default.
- W2767231491 cites W196819306 @default.
- W2767231491 cites W1968326106 @default.
- W2767231491 cites W1968354271 @default.
- W2767231491 cites W1969818747 @default.
- W2767231491 cites W1970210694 @default.
- W2767231491 cites W1970771558 @default.
- W2767231491 cites W1971046564 @default.
- W2767231491 cites W1971944189 @default.
- W2767231491 cites W1974364027 @default.
- W2767231491 cites W1975003732 @default.
- W2767231491 cites W1975171092 @default.
- W2767231491 cites W1975258901 @default.
- W2767231491 cites W1977702346 @default.
- W2767231491 cites W1978428146 @default.
- W2767231491 cites W1979198660 @default.
- W2767231491 cites W1980363808 @default.
- W2767231491 cites W1981213426 @default.
- W2767231491 cites W1981757710 @default.
- W2767231491 cites W1981974728 @default.
- W2767231491 cites W1983105640 @default.
- W2767231491 cites W1984875690 @default.
- W2767231491 cites W1984957345 @default.
- W2767231491 cites W1985817723 @default.
- W2767231491 cites W1987311970 @default.
- W2767231491 cites W1989169985 @default.
- W2767231491 cites W1989343681 @default.
- W2767231491 cites W1989758149 @default.
- W2767231491 cites W1990704551 @default.
- W2767231491 cites W1992061543 @default.
- W2767231491 cites W1992290591 @default.
- W2767231491 cites W1995394073 @default.
- W2767231491 cites W1995484832 @default.
- W2767231491 cites W2000779440 @default.
- W2767231491 cites W2001312631 @default.
- W2767231491 cites W2001691516 @default.
- W2767231491 cites W2002780996 @default.
- W2767231491 cites W2003962351 @default.
- W2767231491 cites W2005190585 @default.
- W2767231491 cites W2005326702 @default.
- W2767231491 cites W2006457769 @default.
- W2767231491 cites W2007769867 @default.
- W2767231491 cites W2008735241 @default.
- W2767231491 cites W2012693665 @default.
- W2767231491 cites W2013815516 @default.
- W2767231491 cites W2014050038 @default.
- W2767231491 cites W2014101946 @default.
- W2767231491 cites W2014990349 @default.
- W2767231491 cites W2017802607 @default.
- W2767231491 cites W2018204894 @default.
- W2767231491 cites W2019767912 @default.
- W2767231491 cites W2021763655 @default.
- W2767231491 cites W2021863013 @default.
- W2767231491 cites W2022008036 @default.
- W2767231491 cites W2023851381 @default.
- W2767231491 cites W2024034535 @default.
- W2767231491 cites W2025603472 @default.
- W2767231491 cites W2025606984 @default.
- W2767231491 cites W2026126909 @default.
- W2767231491 cites W2026742653 @default.
- W2767231491 cites W2029532743 @default.