植物生态学报 ›› 2025, Vol. 49 ›› Issue (10): 1612-1625.DOI: 10.17521/cjpe.2024.0387
李利平1, 余堃1, 陈芳淼1, 陈强1, 景雨航1,3, 牛振国1,3, 胡辰璐1,3, 覃海宁2,3, 黄慧萍1,3, 田亦陈1,3,*(
)
收稿日期:2024-11-06
接受日期:2025-04-03
出版日期:2025-10-20
发布日期:2025-06-04
通讯作者:
*田亦陈(tianyc@aircas.ac.cn)基金资助:
LI Li-Ping1, YU Kun1, CHEN Fang-Miao1, CHEN Qiang1, JING Yu-Hang1,3, NIU Zhen-Guo1,3, HU Chen-Lu1,3, QIN Hai-Ning2,3, HUANG Hui-Ping1,3, TIAN Yi-Chen1,3,*(
)
Received:2024-11-06
Accepted:2025-04-03
Online:2025-10-20
Published:2025-06-04
Supported by:摘要:
世界自然保护联盟(IUCN)红色名录是进行生物多样性保育的依据之一, 由红色名录评估结果数据计算的红色名录指数(RLI)是评估全球/国家/区域/某生物类群的物种整体生存状况的指标。红色名录指数计算的数据源可以是国家的红色名录评估结果数据, 也可以是IUCN全球红色名录评估结果数据; 中国已完成基于国家高等植物评估结果数据的红色名录指数计算, 而基于IUCN全球红色名录评估结果数据的红色名录指数尚未有报道。该研究基于IUCN评估方法框架, 考虑物种的分布区, 计算了基于IUCN全球红色名录评估结果数据的中国高等植物红色名录指数, 并与生物多样性指标联盟(BIP)仅采用苏铁类代表植物来计算国家红色名录指数的结果进行了比较。研究发现, 采用等步长法, 基于IUCN红色名录评估结果数据、合并IUCN和中国特有种评估结果数据、仅采用苏铁类评估结果数据3种数据源得到的中国高等植物红色名录指数分别为0.946 7、0.908 2和0.540 1, 仅采用苏铁类评估结果数据的方法低估了中国高等植物红色名录指数, 存在类群偏差, 所以用尽可能多的可靠数据进行该指数的计算更为合理。该研究在红色名录指数的计算方面进行了探索, 考虑了物种分布区。研究结果可以与其他国家的相关数据进行对比, 也可以为中国生物多样性相关的国际履约提供基础数据。
李利平, 余堃, 陈芳淼, 陈强, 景雨航, 牛振国, 胡辰璐, 覃海宁, 黄慧萍, 田亦陈. 基于IUCN全球评估数据的中国高等植物红色名录指数. 植物生态学报, 2025, 49(10): 1612-1625. DOI: 10.17521/cjpe.2024.0387
LI Li-Ping, YU Kun, CHEN Fang-Miao, CHEN Qiang, JING Yu-Hang, NIU Zhen-Guo, HU Chen-Lu, QIN Hai-Ning, HUANG Hui-Ping, TIAN Yi-Chen. Red List Index of Chinese higher plants based on IUCN global assessment data. Chinese Journal of Plant Ecology, 2025, 49(10): 1612-1625. DOI: 10.17521/cjpe.2024.0387
| 总物种数 Total species | 已评估 Assessed species | 占比 Percentage (%) | 受威胁物种数 Threatened species | |
|---|---|---|---|---|
| 苔藓类 Mosses | 21 925 | 327 | 1.5 | 181 |
| 蕨类 Ferns and Allies | 11 800 | 821 | 7.0 | 321 |
| 裸子植物 Gymnosperm | 1 113 | 1 059 | 95.1 | 451 |
| 被子植物 Angiosperm | 369 000 | 68 704 | 18.6 | 26 367 |
| 绿藻类 Green algae | 13 960 | 17 | 0.1 | 0 |
| 红藻类 Red algae | 7 523 | 78 | 1.0 | 9 |
| 总计 Total | 425 321 | 71 006 | 17.0 | 27 329 |
表1 IUCN全球植物评估情况(截至2024年6月27日)
Table 1 Numbers of plant species by IUCN global assessment as of June 27th, 2024
| 总物种数 Total species | 已评估 Assessed species | 占比 Percentage (%) | 受威胁物种数 Threatened species | |
|---|---|---|---|---|
| 苔藓类 Mosses | 21 925 | 327 | 1.5 | 181 |
| 蕨类 Ferns and Allies | 11 800 | 821 | 7.0 | 321 |
| 裸子植物 Gymnosperm | 1 113 | 1 059 | 95.1 | 451 |
| 被子植物 Angiosperm | 369 000 | 68 704 | 18.6 | 26 367 |
| 绿藻类 Green algae | 13 960 | 17 | 0.1 | 0 |
| 红藻类 Red algae | 7 523 | 78 | 1.0 | 9 |
| 总计 Total | 425 321 | 71 006 | 17.0 | 27 329 |
图1 IUCN评估数据库中受威胁植物累积数量(1998-2024, 截止到2024年6月27日)。数据来源: https://www.iucnredlist.org/resources/summary-statistics。
Fig. 1 Accumulated numbers of threatened plant species in IUCN global assessment database: CR (Critically Endangered), EN (Engdangered), VU (Vulnerable), and Total threatened species (1998-2004, as of June 27th, 2024). Data source: https://www.iucnredlist.org/resources/summary-statistics.
图3 物种占有面积(EOO)划定方法举例。A, 竹叶花椒, 分布数据源为点类型。B, 节节麦, 分布数据源为面类型。
Fig. 3 Examples for the partition of Extent of Occurrence (EOO) in China and outside China. A, Zanthoxylum armatum, with point source data. B, Aegilops tauschii, with polygon source data.
| 级别 Status | 等步长法 Equal steps method | 灭绝风险法 Extinction risk method |
|---|---|---|
| 灭绝 Extinct (EX) | 5 | 1 |
| 野外灭绝 Extinct in the wild (EW) | 5 | 1 |
| 极危 Critically endangered (CR) | 4 | 0.5 |
| 濒危 Endangered (EN) | 3 | 0.05 |
| 易危 Vulnerable (VU) | 2 | 0.005 |
| 近危 Near threatened (NT) | 1 | 0.000 5 |
| 无危 Least concern (LC) | 0 | 0 |
表2 红色名录指数计算物种受威胁等级权重赋值
Table 2 IUCN Red List status and weights for two methods of Red List Index calculation
| 级别 Status | 等步长法 Equal steps method | 灭绝风险法 Extinction risk method |
|---|---|---|
| 灭绝 Extinct (EX) | 5 | 1 |
| 野外灭绝 Extinct in the wild (EW) | 5 | 1 |
| 极危 Critically endangered (CR) | 4 | 0.5 |
| 濒危 Endangered (EN) | 3 | 0.05 |
| 易危 Vulnerable (VU) | 2 | 0.005 |
| 近危 Near threatened (NT) | 1 | 0.000 5 |
| 无危 Least concern (LC) | 0 | 0 |
| 等级 Status | 科 Family | 属 Genus | 种 Species |
|---|---|---|---|
| 灭绝 Extinct (EX) | 6 | 6 | 6 |
| 极危 Critically endangered (CR) | 46 | 75 | 150 |
| 濒危 Endangered (EN) | 69 | 165 | 370 |
| 易危 Vulnerable (VU) | 75 | 163 | 331 |
| 近危 Near threatened (NT) | 43 | 74 | 135 |
| 无危 Least concern (LC) | 212 | 896 | 2 873 |
| 数据缺乏 Data deficient (DD) | 47 | 99 | 294 |
| 评估物种总计 Total assessed species | 241 | 1 104 | 4 159 |
| 受威胁种总计 Total threatened species | 110 | 309 | 851 |
表3 IUCN数据库中中国分布的物种评估级别统计表
Table 3 Numbers of family, genus, and species distributed in China by status in IUCN assessment database
| 等级 Status | 科 Family | 属 Genus | 种 Species |
|---|---|---|---|
| 灭绝 Extinct (EX) | 6 | 6 | 6 |
| 极危 Critically endangered (CR) | 46 | 75 | 150 |
| 濒危 Endangered (EN) | 69 | 165 | 370 |
| 易危 Vulnerable (VU) | 75 | 163 | 331 |
| 近危 Near threatened (NT) | 43 | 74 | 135 |
| 无危 Least concern (LC) | 212 | 896 | 2 873 |
| 数据缺乏 Data deficient (DD) | 47 | 99 | 294 |
| 评估物种总计 Total assessed species | 241 | 1 104 | 4 159 |
| 受威胁种总计 Total threatened species | 110 | 309 | 851 |
| 方法和物种数 Methods and species numbers | IUCN评估物种 IUCN assessed species | IUCN评估物种&中国特有种 IUCN assessed species & Chinese endemic species | 仅苏铁类 Solely Cycas |
|---|---|---|---|
| 等步长法 Equal steps method | 0.946 7 | 0.908 2 | 0.540 1 |
| 灭绝风险法 Extinction risk method | 0.987 7 | 0.985 4 | 0.871 6 |
| 物种数 Species number | 2 212 | 18 298 | 18 |
表4 基于全球评估数据的中国高等植物红色名录指数
Table 4 Red List Index of Chinese higher plants based on IUCN global assessment data (gRLI)
| 方法和物种数 Methods and species numbers | IUCN评估物种 IUCN assessed species | IUCN评估物种&中国特有种 IUCN assessed species & Chinese endemic species | 仅苏铁类 Solely Cycas |
|---|---|---|---|
| 等步长法 Equal steps method | 0.946 7 | 0.908 2 | 0.540 1 |
| 灭绝风险法 Extinction risk method | 0.987 7 | 0.985 4 | 0.871 6 |
| 物种数 Species number | 2 212 | 18 298 | 18 |
图4 4种代表性苏铁类植物的分布点、占有面积(EOO)及其在中国境内和境外的分割情况。图中右下角的饼图表示EOO在中国和中国以外区域的面积占比。
Fig. 4 Species distribution point, Extent of Occurrence (EOO) and the partition of EOO. The pie charts show the percentages of species EOO inside vs. outside of China, respectively.
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