
生物多样性 ›› 2025, Vol. 33 ›› Issue (9): 25267. DOI: 10.17520/biods.2025267 cstr: 32101.14.biods.2025267
所属专题: 世界生物圈保护区专题
武慧1,2(
), 俞乐1,3,*(
)(
), 赵剑桥4(
), 郑诗军1(
), 刘涛1(
), 戚文超1(
), 赵强1(
), 朱丽5(
), 申小莉5(
), 马克平2,5(
)
出版日期:2025-09-20
发布日期:2025-10-31
通讯作者:
*E-mail: leyu@tsinghua.edu.cn
基金资助:
Hui Wu1,2(
), Le Yu1,3,*(
)(
), Jianqiao Zhao4(
), Shijun Zheng1(
), Tao Liu1(
), Wenchao Qi1(
), Qiang Zhao1(
), Li Zhu5(
), Xiaoli Shen5(
), Keping Ma2,5(
)
Online:2025-09-20
Published:2025-10-31
Contact:
*E-mail: leyu@tsinghua.edu.cn
Supported by:摘要:
本研究聚焦联合国教科文组织“人与生物圈计划”框架下的世界生物圈保护区网络, 系统评估其在生态代表性与保护成效方面的全球南北差异。基于全球759个生物圈保护区的空间分布格局, 结合1992-2020年生境质量数据与3类全球保护优先区图层, 分析其生态演变趋势与代表性特征。结果表明, 尽管全球范围内生境质量整体呈下降趋势, 但近10年降幅明显减缓, 且全球北方保护区的生境状况普遍优于全球南方。在空间代表性方面, 生物圈保护区对生物多样性重要区、特有鸟类区与植物多样性中心的覆盖率分别为11.91%、9.76%和9.52%, 均显著高于其占全球陆地面积的随机覆盖概率(4.83%), 但在热带山区与岛屿等关键区域仍存在明显空缺。上述差异反映出全球南方与北方在保护能力、监测支撑与制度保障等方面的结构性不均衡。面向未来, 推进一个更具代表性、公平性与适应性的全球保护体系, 将有赖于生物圈保护区在南北差异认知基础上的协同提升。
武慧, 俞乐, 赵剑桥, 郑诗军, 刘涛, 戚文超, 赵强, 朱丽, 申小莉, 马克平 (2025) 世界生物圈保护区网络生态代表性与保护成效的南北差异. 生物多样性, 33, 25267. DOI: 10.17520/biods.2025267.
Hui Wu, Le Yu, Jianqiao Zhao, Shijun Zheng, Tao Liu, Wenchao Qi, Qiang Zhao, Li Zhu, Xiaoli Shen, Keping Ma (2025) Global South-North differences in ecological representativeness and conservation performance of the World Network of Biosphere Reserves. Biodiversity Science, 33, 25267. DOI: 10.17520/biods.2025267.
图1 全球南北方生物圈保护区分布。灰点表示全球759个生物圈保护区的位置。背景色表示全球南方(红色)与全球北方(蓝色)的划分。本研究参考联合国统计司(United Nations Statistics Division, UNSD)的“发达地区”分类标准, 将被归类为发达经济体的国家(如美国、加拿大、德国、法国、英国、意大利、瑞典、澳大利亚、新西兰、日本、韩国、以色列等)归为“全球北方”, 其余国家归为“全球南方”。
Fig. 1 Global distribution of Biosphere Reserves across the Global South and Global North. Gray dots indicate the locations of 759 Biosphere Reserves worldwide. Background colors denote the Global South (red) and the Global North (blue). Following the United Nations Statistics Division (UNSD) classification of “developed regions,” countries categorized as developed economies (e.g., the United States, Canada, Germany, France, the United Kingdom, Italy, Sweden, Australia, New Zealand, Japan, the Republic of Korea, and Israel) are grouped as the “Global North”; all other countries are grouped as the “Global South”.
图2 生物圈保护区(BRs)对生物多样性重要区域(KBAs)、特有鸟类区(EBAs)和植物多样性中心(CPDs)的代表性。(a)全球生物圈保护区与生物多样性重要区域的空间分布及其叠加关系; (b1)全球生物圈保护区与特有鸟类区的空间分布及其叠加关系; (b2)生物圈保护区对全球218个特有鸟类区的覆盖率; (c1)全球生物圈保护区与植物多样性中心的空间分布及其叠加关系; (c2)生物圈保护区对全球234个植物多样性中心的覆盖率。
Fig. 2 Representativeness of Biosphere Reserves (BRs) for Key Biodiversity Areas (KBAs), Endemic Bird Areas (EBAs), and Centres of Plant Diversity (CPDs). (a) Spatial overlap between global BRs and KBAs; (b1) Spatial overlap between global BRs and EBAs; (b2) Coverage rate of BRs across 218 global EBAs; (c1) Spatial overlap between global BRs and CPDs; (c2) Coverage rate of BRs across 234 global CPDs.
图3 全球南方(红)与全球北方(蓝)生物圈保护区生境质量变化趋势与分布特征(1992-2020年)。(a)年均生境质量的变化趋势: 分1992-2000年、2001-2010年和2011-2020年3个时间段进行线性拟合, 阴影表示95%置信区间, ****表示P < 0.0001; **表示P < 0.01。(b)1992年与2020年的生境质量分布: 上方为核密度分布, 下方箱线图显示中位数、四分位数与范围, 并标注均值和中位数。
Fig. 3 Habitat quality trends and distributions for Biosphere Reserves in the Global South (red) and Global North (blue), 1992-2020. (a) Annual habitat quality trends: Linear fits are shown for three periods—1992-2000, 2001-2010, and 2011-2020; shaded areas indicate 95% confidence intervals; **** P < 0.0001; ** P < 0.01. (b) Habitat quality distributions in 1992 and 2020: Kernel density curves (top) and boxplots (bottom) showing the median, interquartile range, and range, with the mean and median annotated.
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