生物多样性 ›› 2018, Vol. 26 ›› Issue (2): 138-148. DOI: 10.17520/biods.2017188
所属专题: 青藏高原生物多样性与生态安全
武晓宇1,2, 董世魁1,*(), 刘世梁1, 刘全儒3, 韩雨晖1, 张晓蕾1, 苏旭坤1, 赵海迪1, 冯憬1
收稿日期:
2017-06-26
接受日期:
2017-12-01
出版日期:
2018-02-20
发布日期:
2018-05-05
通讯作者:
董世魁
作者简介:
# 共同第一作者
基金资助:
Xiaoyu Wu1,2, Shikui Dong1,*(), Shiliang Liu1, Quanru Liu3, Yuhui Han1, Xiaolei Zhang1, Xukun Su1, Haidi Zhao1, Jing Feng1
Received:
2017-06-26
Accepted:
2017-12-01
Online:
2018-02-20
Published:
2018-05-05
Contact:
Dong Shikui
About author:
# Co-first authors
摘要:
三江源地处全球生物多样性热点之一的青藏高原腹地, 是高寒草地生物多样性的集中分布区。但过去几十年中, 人为干扰和气候变化等因素导致高寒草地严重退化, 草地生物多样性受到极大威胁。本研究利用最大熵(MaxEnt)模型模拟了三江源区40种濒危保护植物当前及未来气候变化情景下的热点分布区。根据最大熵模型估计结果统计, 目前三江源濒危保护植物的热点区面积89,438 km2, 主要分布于三江源东部和南部, 其中濒危物种大于30种的最热点地区面积485 km2, 主要分布于囊谦县、玉树市、班玛县、久治县和河南县。未来在增温增湿的气候变化情景下, 最大熵模型模拟的三江源区草地濒危保护植物的热点区将向西北部扩大, 有利于植物多样性的维持和提升。然而, 模型模拟还发现, 在囊谦县、玉树市、班玛县、久治县和河南县等县市, 均有濒危保护植物大于25种以上的热点区域未被重点保护区覆盖, 总面积为4,423 km2。这一区域被划分为可开展畜牧生产活动的一般保护区, 受到人为干扰的可能性较大, 应予以更多关注与保护。
武晓宇, 董世魁, 刘世梁, 刘全儒, 韩雨晖, 张晓蕾, 苏旭坤, 赵海迪, 冯憬 (2018) 基于MaxEnt模型的三江源区草地濒危保护植物热点区识别. 生物多样性, 26, 138-148. DOI: 10.17520/biods.2017188.
Xiaoyu Wu, Shikui Dong, Shiliang Liu, Quanru Liu, Yuhui Han, Xiaolei Zhang, Xukun Su, Haidi Zhao, Jing Feng (2018) Identifying priority areas for grassland endangered plant species in the Sanjiangyuan Nature Reserve based on the MaxEnt model. Biodiversity Science, 26, 138-148. DOI: 10.17520/biods.2017188.
变量 Variable | 描述 Description |
---|---|
Bio1 | 年均温 Annual mean temperature |
Bio2 | 平均温度日较差 Mean diurnal temperature range |
Bio3 | 等温性 Isothermality |
Bio4 | 温度季度变化 Temperature seasonality |
Bio5 | 最热月最高温 Max temperature of warmest month |
Bio6 | 最冷月最低温 Min temperature of coldest month |
Bio7 | 年温度变化范围 Temperature annual range |
Bio8 | 最湿季度均温 Mean temperature of wettest quarter |
Bio9 | 最干季度均温 Mean temperature of driest quarter |
Bio10 | 最暖季度均温 Mean temperature of warmest quarter |
Bio11 | 最冷季度均温 Mean temperature of coldest quarter |
Bio12 | 年平均降水量 Annual precipitation |
Bio13 | 最湿月降水量 Precipitation of wettest month |
Bio14 | 最干月降水量 Precipitation of driest month |
Bio15 | 降水量变异系数 Precipitation seasonality (coefficient of variation) |
Bio16 | 最湿季度降水量 Precipitation of wettest quarter |
Bio17 | 最干季度降水量 Precipitation of driest quarter |
Bio18 | 最暖季度降水量 Precipitation of warmest quarter |
Bio19 | 最冷季度降水量 Precipitation of coldest quarter |
表1 19个生物气候环境因子及其描述
Table 1 19 bioclimatic variables and their descriptions
变量 Variable | 描述 Description |
---|---|
Bio1 | 年均温 Annual mean temperature |
Bio2 | 平均温度日较差 Mean diurnal temperature range |
Bio3 | 等温性 Isothermality |
Bio4 | 温度季度变化 Temperature seasonality |
Bio5 | 最热月最高温 Max temperature of warmest month |
Bio6 | 最冷月最低温 Min temperature of coldest month |
Bio7 | 年温度变化范围 Temperature annual range |
Bio8 | 最湿季度均温 Mean temperature of wettest quarter |
Bio9 | 最干季度均温 Mean temperature of driest quarter |
Bio10 | 最暖季度均温 Mean temperature of warmest quarter |
Bio11 | 最冷季度均温 Mean temperature of coldest quarter |
Bio12 | 年平均降水量 Annual precipitation |
Bio13 | 最湿月降水量 Precipitation of wettest month |
Bio14 | 最干月降水量 Precipitation of driest month |
Bio15 | 降水量变异系数 Precipitation seasonality (coefficient of variation) |
Bio16 | 最湿季度降水量 Precipitation of wettest quarter |
Bio17 | 最干季度降水量 Precipitation of driest quarter |
Bio18 | 最暖季度降水量 Precipitation of warmest quarter |
Bio19 | 最冷季度降水量 Precipitation of coldest quarter |
物种 Species | AUC值 AUC value | 物种 Species | AUC值 AUC value |
---|---|---|---|
褐紫乌头 Aconitum brunneum | 0.969 | 广布红门兰 Orchis chusua | 0.910 |
八宿雪灵芝 Arenaria baxoiensis | 0.969 | 宽叶红门兰 Orchis latifolia | 0.919 |
三刺草 Aristida triseta | 0.978 | 河北红门兰 Orchis tschiliensis | 0.995 |
华雀麦 Bromus sinensis | 0.962 | 青海固沙草 Orinus kokonorica | 0.982 |
凹舌兰 Coeloglossum viride | 0.948 | 川赤芍 Paeonia veitchii | 1.000 |
毛杓兰 Cypripedium franchetii | 0.997 | 羽叶点地梅 Pomatosace filicula | 0.833 |
黑紫披碱草 Elymus atratus | 0.867 | 小丛红景天 Rhodiola dumulosa | 0.992 |
短芒披碱草 Elymus breviaristatus | 0.884 | 喜马红景天 Rhodiola himalensis | 0.876 |
矮麻黄 Ephedra minuta | 0.930 | 圆丛红景天 Rhodiola juparensis | 0.830 |
单子麻黄 Ephedra monosperma | 0.839 | 狭叶红景天 Rhodiola kirilowii | 0.911 |
中华羊茅 Festuca sinensis | 0.915 | 四裂红景天 Rhodiola quadrifida | 0.844 |
南山龙胆 Gentiana grumii | 0.880 | 粗茎红景天 Rhodiola wallichiana | 0.844 |
西南手参 Gymnadenia orchidis | 0.942 | 短颖鹅观草 Roegneria breviglumis | 0.906 |
落地金钱 Habenaria aitchisonii | 0.981 | 短柄鹅观草 Roegneria brevipes | 0.953 |
裂瓣角盘兰 Herminium alaschanicum | 0.984 | 青海鹅观草 Roegneria kokonorica | 0.980 |
角盘兰 Herminium monorchis | 0.981 | 云状雪兔子 Saussurea aster | 0.818 |
沼兰 Malaxis monophyllos | 0.983 | 苞叶雪莲 Saussurea obvallata | 0.927 |
红花绿绒蒿 Meconopsis punicea | 0.921 | 红叶雪兔子 Saussurea paxiana | 0.855 |
颈果草 Metaeritrichium microuloides | 0.873 | 羌塘雪兔子 Saussurea wellbyi | 0.916 |
羌活 Notopterygium incisum | 0.940 | 华福花 Sinadoxa corydalifolia | 0.993 |
表2 MaxEnt模型模拟三江源自然保护区濒危植物当前分布的模型预测准确性(AUC值)
Table 2 The AUC value of predicted distribution of endangered plant species in Sanjiangyuan Nature Reserve based on MaxEnt model
物种 Species | AUC值 AUC value | 物种 Species | AUC值 AUC value |
---|---|---|---|
褐紫乌头 Aconitum brunneum | 0.969 | 广布红门兰 Orchis chusua | 0.910 |
八宿雪灵芝 Arenaria baxoiensis | 0.969 | 宽叶红门兰 Orchis latifolia | 0.919 |
三刺草 Aristida triseta | 0.978 | 河北红门兰 Orchis tschiliensis | 0.995 |
华雀麦 Bromus sinensis | 0.962 | 青海固沙草 Orinus kokonorica | 0.982 |
凹舌兰 Coeloglossum viride | 0.948 | 川赤芍 Paeonia veitchii | 1.000 |
毛杓兰 Cypripedium franchetii | 0.997 | 羽叶点地梅 Pomatosace filicula | 0.833 |
黑紫披碱草 Elymus atratus | 0.867 | 小丛红景天 Rhodiola dumulosa | 0.992 |
短芒披碱草 Elymus breviaristatus | 0.884 | 喜马红景天 Rhodiola himalensis | 0.876 |
矮麻黄 Ephedra minuta | 0.930 | 圆丛红景天 Rhodiola juparensis | 0.830 |
单子麻黄 Ephedra monosperma | 0.839 | 狭叶红景天 Rhodiola kirilowii | 0.911 |
中华羊茅 Festuca sinensis | 0.915 | 四裂红景天 Rhodiola quadrifida | 0.844 |
南山龙胆 Gentiana grumii | 0.880 | 粗茎红景天 Rhodiola wallichiana | 0.844 |
西南手参 Gymnadenia orchidis | 0.942 | 短颖鹅观草 Roegneria breviglumis | 0.906 |
落地金钱 Habenaria aitchisonii | 0.981 | 短柄鹅观草 Roegneria brevipes | 0.953 |
裂瓣角盘兰 Herminium alaschanicum | 0.984 | 青海鹅观草 Roegneria kokonorica | 0.980 |
角盘兰 Herminium monorchis | 0.981 | 云状雪兔子 Saussurea aster | 0.818 |
沼兰 Malaxis monophyllos | 0.983 | 苞叶雪莲 Saussurea obvallata | 0.927 |
红花绿绒蒿 Meconopsis punicea | 0.921 | 红叶雪兔子 Saussurea paxiana | 0.855 |
颈果草 Metaeritrichium microuloides | 0.873 | 羌塘雪兔子 Saussurea wellbyi | 0.916 |
羌活 Notopterygium incisum | 0.940 | 华福花 Sinadoxa corydalifolia | 0.993 |
图2 基于MaxEnt模型的三江源自然保护区草地濒危植物当前分布概率图。物种存在概率为0-1, 暖色为物种存在概率高的区域, 最高为红色, 依次下降为橙色、黄色、绿色、青色、淡青色, 深蓝色为最低。
Fig. 2 The probability graph of current distribution of the grassland endangered plant species in Sanjiangyuan Nature Reserve based on MaxEnt models. The species existing probability range from 0 to 1. Warmer colors show areas with higher predicted probability, red is the highest, followed by orange, yellow, green, cyan, light cyan and dark blue.
图4 气候变化RCP2.6情景下2070年三江源自然保护区草地濒危保护植物多样性热点分布图
Fig. 4 The distribution map of the grassland endangered plant species hotspots in Sanjiangyuan Nature Reserve under RCP2.6 of climate change in 2070
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