生物多样性 ›› 2017, Vol. 25 ›› Issue (5): 453-463. DOI: 10.17520/biods.2016134
谭剑波1,2, 李爱农1,*(), 雷光斌1, 陈国科3, 马克平3
收稿日期:
2016-05-15
接受日期:
2017-02-27
出版日期:
2017-05-20
发布日期:
2017-06-06
通讯作者:
李爱农
基金资助:
Jianbo Tan1,2, Ainong Li1,*(), Guangbin Lei1, Guoke Chen3, Keping Ma3
Received:
2016-05-15
Accepted:
2017-02-27
Online:
2017-05-20
Published:
2017-06-06
Contact:
Li Ainong
摘要:
生态系统红色名录作为物种红色名录的重要补充, 是基于生态系统水平上的生物多样性评估, 对于重要生物的生境保护至关重要。当前, 世界自然保护联盟(IUCN)将IUCN生态系统红色名录评估方法作为生态系统受威胁状况评估的正式标准, 广泛应用于全球生态系统的评估, 在生物多样性保护和生态系统管理中发挥着重要作用。随着IUCN生态系统红色名录评估体系的修订和推广, 其评估标准日趋完善, 但生态系统制图、生态系统崩溃的概念以及实际操作层面仍面临挑战。本文回顾了生态系统红色名录的发展过程, 归纳了IUCN生态系统红色名录评估方案中生境范围退化(标准A)、生境限制分布(标准B)、非生物环境退化(标准C)、生物过程退化(标准D)以及威胁定量分析(标准E)这5个指标的含义和评估过程, 并围绕IUCN生态系统红色名录实际评估中面临的挑战, 论述了利用遥感和生态模型可能提供的解决方案。文中指出, 明确生态系统分类体系以及生态系统崩溃等基本概念对生态系统红色名录评估至关重要; 尺度效应是评估过程的重要影响因素; 多尺度评估是丰富生态系统红色名录空间信息的潜在方法; 耦合遥感和生态模型等手段共同参与评估, 是未来研究IUCN生态系统红色名录的重要方法。
谭剑波, 李爱农, 雷光斌, 陈国科, 马克平 (2017) IUCN生态系统红色名录研究进展. 生物多样性, 25, 453-463. DOI: 10.17520/biods.2016134.
Jianbo Tan, Ainong Li, Guangbin Lei, Guoke Chen, Keping Ma (2017) Research advances and challenges in the IUCN Red List of Ecosystems. Biodiversity Science, 25, 453-463. DOI: 10.17520/biods.2016134.
图1 绝对变化量模型和绝对变化率模型预测结果对比(改编自Rodríguez et al, 2015)
Fig. 1 Results derived from proportional rate of decline versus absolute rate of decline (adapted from Rodríguez et al, 2015)
图2 生境限制分布(标准B)示意图。生境范围(EOO)为28,249 km2, 生境所占网格数目(AOO)为88(改编自Keith et al, 2013)。
Fig. 2 The diagram of habitat restricted distribution (Criterion B). Extent of Occurrence (EOO) is 28,249 km2 and Area of Occupancy (AOO) is 88 (adapted from Keith et al, 2013).
图3 IUCN生态系统受威胁状况评估流程(改编自Rodríguez et al, 2015)
Fig. 3 The steps followed for the application of IUCN of Ecosystems Categories and Criteria (adapted from Rodríguez et al, 2015)
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