Evolutionary Ecology Group, Department of Biology, University of Antwerp, Middelheimcampus, Groenenborgerlaan 171, BE-2020, Antwerp, Belgium.
Conserv Biol. 2012 Apr;26(2):284-93. doi: 10.1111/j.1523-1739.2011.01816.x. Epub 2012 Jan 23.
Despite extensive research on the effects of habitat fragmentation, the ecological mechanisms underlying colonization and extinction processes are poorly known, but knowledge of these mechanisms is essential to understanding the distribution and persistence of populations in fragmented habitats. We examined these mechanisms through multiseason occupancy models that elucidated patch-occupancy dynamics of Middle Spotted Woodpeckers (Dendrocopos medius) in northwestern Spain. The number of occupied patches was relatively stable from 2000 to 2010 (15-24% of 101 patches occupied every year) because extinction was balanced by recolonization. Larger and higher quality patches (i.e., higher density of oaks >37 cm dbh [diameter at breast height]) were more likely to be occupied. Habitat quality (i.e., density of large oaks) explained more variation in patch colonization and extinction than did patch size and connectivity, which were both weakly associated with probabilities of turnover. Patches of higher quality were more likely to be colonized than patches of lower quality. Populations in high-quality patches were less likely to become extinct. In addition, extinction in a patch was strongly associated with local population size but not with patch size, which means the latter may not be a good surrogate of population size in assessments of extinction probability. Our results suggest that habitat quality may be a primary driver of patch-occupancy dynamics and may increase the accuracy of models of population survival. We encourage comparisons of competing models that assess occupancy, colonization, and extinction probabilities in a single analytical framework (e.g., dynamic occupancy models) so as to shed light on the association of habitat quality and patch geometry with colonization and extinction processes in different settings and species.
尽管对生境破碎化的影响进行了广泛的研究,但对定居和灭绝过程的生态机制知之甚少,但了解这些机制对于理解在破碎化生境中种群的分布和持久性至关重要。我们通过多季节占有模型来研究这些机制,该模型阐明了西班牙西北部中部斑点啄木鸟(Dendrocopos medius)在斑块中的占有动态。从 2000 年到 2010 年,被占领的斑块数量相对稳定(每年有 101 个斑块中的 15-24%被占领),因为灭绝被再定居所平衡。较大和质量较高的斑块(即,>37 厘米胸径的橡树密度较高)更有可能被占领。栖息地质量(即,大橡树的密度)比斑块大小和连通性更能解释斑块的定居和灭绝的变化,而斑块大小和连通性与周转率的概率相关性较弱。高质量的斑块比低质量的斑块更有可能被占领。高质量斑块中的种群灭绝的可能性较小。此外,斑块中的灭绝与当地种群大小密切相关,但与斑块大小无关,这意味着后者在评估灭绝概率时可能不是种群大小的良好替代指标。我们的研究结果表明,栖息地质量可能是斑块占有动态的主要驱动因素,并可能提高种群生存模型的准确性。我们鼓励在单个分析框架(例如,动态占有模型)中比较竞争模型,以阐明不同环境和物种中栖息地质量和斑块几何形状与定居和灭绝过程的关系。