The importance of using sustainable use protected areas for functional connectivity

被引:44
作者
Crouzeilles, Renato [1 ,3 ]
Lorini, Maria Lucia [1 ,2 ]
Viveiros Grelle, Carlos Eduardo [3 ]
机构
[1] Univ Fed Rio de Janeiro, Dept Ecol, Programa Posgrad Ecol, BR-21941590 Rio De Janeiro, RJ, Brazil
[2] Univ Fed Rio de Janeiro, Dept Bot, Lab Gestao Biodiversidade, BR-21941971 Rio De Janeiro, RJ, Brazil
[3] Univ Fed Rio de Janeiro, Dept Ecol, Lab Vertebrados, BR-21941590 Rio De Janeiro, RJ, Brazil
关键词
Brazilian Atlantic Forest; Integral Index of Connectivity; Morphological spatial pattern analysis; Protected areas; Spatial graphs; LANDSCAPE CONNECTIVITY; HABITAT PATCHES; ATLANTIC FOREST; NETWORK ANALYSIS; CONSERVATION; AVAILABILITY; MANAGEMENT; CHECKLIST; INDEXES; GUIDE;
D O I
10.1016/j.biocon.2012.10.023
中图分类号
X176 [生物多样性保护];
学科分类号
090705 ;
摘要
Functional connectivity, which represents the animal movement responses to landscape elements, should be considered when configuring protected areas. Each habitat patch has a different contribution to functional connectivity. Functional connectivity can be accessed through the Integral Index of Connectivity (IIC), which considers the habitat patch size, the amount of flux arriving to that patch, and the topological position of the patch within the habitat patch network. These four measures can be used as distinct criteria of functional connectivity to prioritise habitat patches. We analyzed how the spatial patterns of habitat patches varied according to these criteria. For each criterion, we ranked all habitat patches within five levels of importance, and identified whether priority habitat patches are protected. We found a positive relationship between the level of importance and the presence of core areas and corridors. Stepping stones presented the opposite relationship. For each criterion, only the highest levels of importance presented more core areas than connector areas (corridors and stepping stones). In the higher level of importance, core areas are mostly under strictly protected areas (IUCN categories I-IV), while connector areas are under the less restrictive category of sustainable use protected areas (SUAs, IUCN category V). Brazilian decision makers must consider the opportunity to protect connector areas under restrictive SUM categories, such as Private Natural Heritage Reserve (IUCN category IV). Combine IIC and spatial patterns of habitat patches proved to be helpful to identify priority habitat patches for conservation and to indicate which class/category of protected areas should be established. (C) 2012 Elsevier Ltd. All rights reserved.
引用
收藏
页码:450 / 457
页数:8
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