Abstract

BackgroundThe species–area relationship is one of the best documented patterns in community ecology. Factors influencing species–area relationship are still not well understood. Since the proposal of the equilibrium theory of island biogeography, many studies have tested the effects of area and isolation, estimating effects of disturbance and patch age were scarce and should also be important bearing.MethodsWe investigated summer waterbird species richness in 38 post-mining subsidence lakes in Huainan and Fuyang, Anhui, China, May 25–June 12, 2016. We examined the effects of lake area, isolation (distance to natural water bodies), aquaculture disturbance, lake age and lake state (still sinking or not sinking) on summer waterbird species richness with multivariable linear regression method and model selection method.ResultsOur results from multivariable linear regression and model selection were consistent, which showed that species richness was positively related with lake area and negatively related with isolation. Aquaculture disturbance negatively influenced species richness. Highest species richness were found in lakes under intermediate intensity of aquaculture activities with area less than 100 ha and lakes under low intensity of aquaculture activities with area greater than 100 ha. Lake age and lake state had no significant effects on species richness.ConclusionsSpecies richness was most related with lake area, aquaculture disturbance, and isolation, with lake area had a positive effect, while aquaculture activities and isolation had a negative effect. What’s more, aquaculture activities significantly changed the slope of species–area relationship and might impede us finding a relationship between species richness and lake age.

Highlights

  • The species–area relationship is one of the best documented patterns in community ecology

  • The most common waterbird species were Little Grebe (Tachybaptus ruficollis, 310 individuals in 37 lakes), Common Moorhen (Gallinula chloropus, 307 individuals in disturbance (0.249 vs. 0.135), as a result, species richness of lakes under low aquaculture disturbance was higher than lakes under intermediate aquaculture disturbance when lake size exceeded 100 ha

  • Summer waterbird species richness in 38 post-mining subsidence lakes was positively related with lake area and negatively related with isolation

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Summary

Introduction

The species–area relationship is one of the best documented patterns in community ecology. One of the best documented patterns in community ecology is that species richness increases with area sampled, or the species–area relationship (Williamson 1988; Durrett and Levin 1996). A remarkable point in these studies was that researchers usually assumed that all niches on islands had been occupied and maximum species richness had being reached (Bush and Whittaker 1991; Hubbell 1997) This assumption was not verified in all systems. Patch availability in fragmented landscapes or insular islands could vary as a consequence of time since patch or island formation (Valente et al 2014) In such circumstances, the successful colonization by new species depended on another factor in addition to area and isolation: the patch or island age (Horsák et al 2012). Few previous studies have investigated patchy inland systems (Krauss et al 2009), which have been limited to short time scales

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