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The current configuration of protected areas in the Cape Floristic Region, South Africa - reservation bias and representation of biodiversity patterns and processes

机译:南非开普植物区的保护区当前配置-保留偏见以及生物多样性模式和过程的代表

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The formulation of a strategic plan for the conservation of terrestrial biodiversity in the Cape Floristic Region (CFR; 87,892 km(2)) requires an objective and spatially explicit assessment of the representativeness of major habitat categories (surrogates for biodiversity) currently under protection. A GIS layer of statutory and non-statutory conservation areas was used, along with layers of many biological and physical features, to explore the configuration of conserved areas relative to key biological and physical indicators. Three analyses were performed. (1) Recursive partitioning, a classification-tree analysis technique, was used to contrast features of protected areas with non-protected areas. (2) The conservation status of 16 primary and 88 secondary Broad Habitat Units (BHUs; derived on the basis of topography, geology, homogeneous climatic zones, and floristic composition) was assessed in terms of prescribed conservation targets. (3) The extent to which protected areas are able to sustain ecological and evolutionary processes was explored by assessing the extent of spatial components of these processes for all conservation areas. About 20% of the CFR is protected in some form of conservation area, mostly concentrated on sandstone substrates, and areas with high altitude and steep slopes. The reservation bias towards upland areas has seriously constrained representation of biodiversity pattern and processes. Most of the habitat diversity is poorly represented in the current conservation area system with only 9% of the remaining primary BHUs in the lowlands conserved. However, almost 50% of the Mountain Fynbos Complex is conserved (largely exceeding its conservation target). Spatial components of the ecological processes identified are poorly captured by the conservation area network although faunal and floral migration is possible in the uplands due to the strong spatial connectivity of the protected network.
机译:制定佛得角海角陆地生物多样性保护战略计划(CFR; 87,892 km(2))需要对目前受保护的主要生境类别(生物多样性替代物)的代表性进行客观和空间明确的评估。地理信息系统的法定保护区和非法定保护区以及许多具有生物和物理特征的层都用于探索相对于关键生物和物理指标的保护区配置。进行了三个分析。 (1)递归分区,一种分类树分析技术,用于对比保护区和非保护区的特征。 (2)根据规定的保护目标,评估了16个主要生境单元和88个次要生境单元(BHU)的保护状况,这些单位是根据地形,地质,均质气候区和植物区系得出的。 (3)通过评估所有保护区这些过程的空间成分程度,探索了保护区能够维持生态和进化过程的程度。在某种形式的保护区中,大约有20%的病死率受到保护,大部分集中在砂岩基质上以及高海拔和陡坡的地区。对高地地区的保留偏见严重限制了生物多样性模式和过程的表示。在目前的保护区系统中,大多数栖息地的多样性表现不佳,仅保留了低地中剩余的9%的主要BHU。但是,几乎只有50%的Fynbos山综合体得到了保护(大大超出了其保护目标)。尽管保护区网络在空间上具有很强的连通性,但在高地上动物和花卉的迁移是可能的,但保护区网络很难很好地识别生态过程的空间成分。

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