生物多样性 ›› 2024, Vol. 32 ›› Issue (3): 23324. DOI: 10.17520/biods.2023324 cstr: 32101.14.biods.2023324
陶斯琦1, 杨飞龄2,3, 华朝朗4,*(), 武瑞东2,3
收稿日期:
2023-09-06
接受日期:
2023-12-08
出版日期:
2024-03-20
发布日期:
2024-03-06
通讯作者:
*E-mail: huacl@163.com
基金资助:
Siqi Tao1, Feiling Yang2,3, Chaolang Hua4,*(), Ruidong Wu2,3
Received:
2023-09-06
Accepted:
2023-12-08
Online:
2024-03-20
Published:
2024-03-06
Contact:
*E-mail: huacl@163.com
摘要:
植被保护优先性评估是保护规划制定和保护资源配置的重要基础。目前, 评估植被保护优先性的因子较为单一, 结合多因子系统性评估植被保护优先性的研究还很有限。本研究综合考虑植被受威胁状况和保护价值, 评估了云南省104类自然群系的保护优先性。首先, 根据IUCN生态系统红色名录评估框架评估群系受威胁状态; 然后, 选取濒危保护物种丰富度、冠层高度和碳储量3个指标, 加权计算各群系的生态系统质量以表征其保护价值; 最后, 通过综合受威胁状态与保护价值评估云南省自然植被的保护优先性, 并进一步划分为4个植被保护类型。研究结果表明: (1)在云南省104类群系中, 66.3%的群系受威胁等级为易危/濒危/极危(VU/EN/CR), 受到不同程度的威胁, 群系的分布范围受限是导致其受威胁的关键因素。(2) 45.2%的群系评估为高和极高保护价值, 38.5%的群系评估为中等保护价值, 植被质量整体较高。(3)综合评估建议: 保护价值高或极高且受威胁的31类群系进行优先保护; 保护价值中等但受威胁的26类群系进行次优先保护; 保护价值极高或高但未受威胁的16类群系进行预先保护; 其他群系进行一般保护。(4)云南省已建自然保护区对优先、次优先和预先保护植被的覆盖率分别为19.5%、9.7%和16.9%, 还存在一定的保护空缺。本研究构建的综合受威胁状态和保护价值的植被保护优先性评估方法, 能够为区域尺度生态系统水平的保护规划与行动提供科学支持。
陶斯琦, 杨飞龄, 华朝朗, 武瑞东 (2024) 通过综合受威胁状态和保护价值评估云南省自然植被的保护优先性. 生物多样性, 32, 23324. DOI: 10.17520/biods.2023324.
Siqi Tao, Feiling Yang, Chaolang Hua, Ruidong Wu (2024) Priority assessment for natural vegetation conservation in Yunnan Province by integrating threatened status and conservation value. Biodiversity Science, 32, 23324. DOI: 10.17520/biods.2023324.
图1 结合土地利用类型的自然植被面积变化估算方法示意图(以随机选择的云南省思茅松林的部分斑块为例)。(a)中华人民共和国植被图(1 : 1,000,000)中思茅松林(部分斑块)自然植被面积; (b) 2000年思茅松斑块分布区的土地利用类型; (c) 2000年剔除耕地和人造地表后的思茅松林斑块面积; (d) 2020年的土地利用类型; (e) 2020年剔除耕地和人造地表后的思茅松林斑块面积。
Fig. 1 Schematic diagram of the method for estimating the loss of natural vegetation area based on land use types data (taking randomly selected Pinus kesiya var. langbianensis forest patches in Yunnan Province as an example). (a) The partial patches area of the P. kesiya var. langbianensis forest distributed in the Vegetation Map of the People’s Republic of China (1:1,000,000); (b) Land use types in the distribution area of the P. kesiya var. langbianensis forest patches in 2000; (c) The partial patches area of the P. kesiya var. langbianensis forest in 2000 after excluding cultivated land and artificial land; (d) The land use data in 2020; (e) The partial patches area of the P. kesiya var. langbianensis forest in 2020 after excluding cultivated land and artificial land.
图3 IUCN生态系统红色名录标准A、标准B及综合两个标准的评估结果。CR: 极危; EN: 濒危; VU: 易危; NT: 近危; LC: 无危。
Fig. 3 The evaluation results of the IUCN Red List of Ecosystems criterion A and B, as well the integrating A and B criteria. CR, Critically Endangered; EN, Endangered; VU, Vulnerable; NT, Near Threatened; LC, Least Concern.
类别 Category | 无危/近危 LC/NT | 易危 VU | 濒危 EN | 极危 CR |
---|---|---|---|---|
群系数量 No. of formations (%) | 35 (33.7) | 16 (15.4) | 23 (22.1) | 30 (28.8) |
植被面积 Vegetation area (km2) (%) | 173,322.9 (84.3) | 21,608.7 (10.5) | 9,138.5 (4.5) | 1,407.9 (0.7) |
表1 不同受威胁等级群系的数量、占地面积及其占比
Table 1 The number, area and their ratio of formations under different threatened degrees
类别 Category | 无危/近危 LC/NT | 易危 VU | 濒危 EN | 极危 CR |
---|---|---|---|---|
群系数量 No. of formations (%) | 35 (33.7) | 16 (15.4) | 23 (22.1) | 30 (28.8) |
植被面积 Vegetation area (km2) (%) | 173,322.9 (84.3) | 21,608.7 (10.5) | 9,138.5 (4.5) | 1,407.9 (0.7) |
图4 云南省植被受威胁等级分布。CR: 极危; EN: 濒危; VU: 易危; NT: 近危; LC: 无危。
Fig. 4 Spatial distribution of threatened level of vegetation in Yunnan Province. CR, Critically Endangered; EN, Endangered; VU, Vulnerable; NT, Near Threatened; LC, Least Concern.
图5 用于评估植被保护价值的三个指标及植被保护价值的空间分布。(a)冠层高度; (b)濒危保护物种丰富度; (c)碳储量; (d)保护价值。
Fig. 5 The spatial distribution of three indicators to evaluating the conservation value of vegetation and vegetation conservation value. (a) Canopy height; (b) Endangered species richness; (c) Carbon storage; (d) Conservation value.
类别 Category | 极高保护价值 EHCV | 高保护价值 HCV | 中等保护价值 MCV | 低保护价值 LCV |
---|---|---|---|---|
群系数量 No. of formations (%) | 12 (11.5) | 35 (33.7) | 40 (38.5) | 17 (16.3) |
植被面积 Vegetation area (km2) (%) | 1,742.4 (0.9) | 51,513.9 (25.1) | 144,391.6 (70.3) | 7,644.2 (3.7) |
表2 不同保护价值等级的群系数量、面积及其占比
Table 2 The number, area and ratio of formations under different conservation value degrees
类别 Category | 极高保护价值 EHCV | 高保护价值 HCV | 中等保护价值 MCV | 低保护价值 LCV |
---|---|---|---|---|
群系数量 No. of formations (%) | 12 (11.5) | 35 (33.7) | 40 (38.5) | 17 (16.3) |
植被面积 Vegetation area (km2) (%) | 1,742.4 (0.9) | 51,513.9 (25.1) | 144,391.6 (70.3) | 7,644.2 (3.7) |
植被类型 Vegetation type | 组合类型 Combination type | 群系数量 No. of formations | 总面积 Total area (km2) (%) |
---|---|---|---|
优先保护 Priority conservation | EHCV-CR | 8 | 6,183.1 (3.0) |
EHCV-EN | 2 | ||
EHCV-VU | 1 | ||
HCV-CR | 6 | ||
HCV-EN | 7 | ||
HCV-VU | 7 | ||
次优先保护 Secondary conservation | MCV-CR | 9 | 21,006.4 (10.2) |
MCV-EN | 10 | ||
MCV-VU | 7 | ||
预先保护 Proactive conservation | EHCV-NT/LC | 1 | 47,073.3 (22.9) |
HCV-NT/LC | 15 | ||
一般保护 General conservation | MCV-NT/LC | 14 | 131,029.4 (63.9) |
LCV-CR | 7 | ||
LCV-EN | 4 | ||
LCV-VU | 1 | ||
LCV-NT/LC | 5 |
表3 各保护类型植被的数量、占地面积及占比
Table 3 The number, area and ratio of different vegetation conservation type
植被类型 Vegetation type | 组合类型 Combination type | 群系数量 No. of formations | 总面积 Total area (km2) (%) |
---|---|---|---|
优先保护 Priority conservation | EHCV-CR | 8 | 6,183.1 (3.0) |
EHCV-EN | 2 | ||
EHCV-VU | 1 | ||
HCV-CR | 6 | ||
HCV-EN | 7 | ||
HCV-VU | 7 | ||
次优先保护 Secondary conservation | MCV-CR | 9 | 21,006.4 (10.2) |
MCV-EN | 10 | ||
MCV-VU | 7 | ||
预先保护 Proactive conservation | EHCV-NT/LC | 1 | 47,073.3 (22.9) |
HCV-NT/LC | 15 | ||
一般保护 General conservation | MCV-NT/LC | 14 | 131,029.4 (63.9) |
LCV-CR | 7 | ||
LCV-EN | 4 | ||
LCV-VU | 1 | ||
LCV-NT/LC | 5 |
图7 云南省优先、次优先、预先保护植被与自然保护区空间分布
Fig. 7 Spatial distribution of priority/secondary/proactive conservation vegetation and nature reserves in Yunnan Province
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