
生物多样性 ›› 2025, Vol. 33 ›› Issue (8): 25037. DOI: 10.17520/biods.2025037 cstr: 32101.14.biods.2025037
吉晟男1,2, 韩佳蓉3, 任月恒1, 穆晓东2, 朱彦鹏1,*(
)
收稿日期:2025-01-24
接受日期:2025-04-12
出版日期:2025-08-20
发布日期:2025-09-17
通讯作者:
*E-mail: zhuyp@craes.org.cn
基金资助:
Shengnan Ji1,2, Jiarong Han3, Yueheng Ren1, Xiaodong Mu2, Yanpeng Zhu1,*(
)
Received:2025-01-24
Accepted:2025-04-12
Online:2025-08-20
Published:2025-09-17
Contact:
*E-mail: zhuyp@craes.org.cn
Supported by:摘要:
外来入侵植物对生态系统、生物多样性和人类社会构成了严重威胁。海南岛作为我国生物多样性最丰富的地区之一, 面临着外来入侵植物的潜在危害。为评估重点管理外来入侵物种在海南岛的潜在适生区及其入侵风险, 本研究基于农业农村部等六部委最新发布的《重点管理外来入侵物种名录》中的33种入侵植物, 利用最大熵(MaxEnt)模型与地理信息系统(GIS)技术, 对物种分布数据和环境因子进行了综合分析。结果显示, 共有25种入侵植物在海南岛具有不同程度的适生区, 其中假高粱(Sorghum halepense)、飞机草(Chromolaena odorata)、刺苋(Amaranthus spinosus)和马缨丹(Lantana camara) 4个物种的适生区面积均占海南岛总面积的50%以上, 风险等级最高。入侵热点主要集中在海南岛东北部低海拔平原和部分沿海区域, 人类活动强度、温度季节性、平均昼夜温差和最暖季降水量是影响其分布的主要因素。结合结果分析, 本研究建议加强对高风险区域和高风险物种的精准监测和综合防控, 同时将社会环境因素及生物互作机制纳入后续研究, 以进一步提升对外来入侵植物的预警能力并制定科学高效的防控策略。
吉晟男, 韩佳蓉, 任月恒, 穆晓东, 朱彦鹏 (2025) 基于MaxEnt模型预测海南岛重点管理外来入侵植物适生区及其入侵风险. 生物多样性, 33, 25037. DOI: 10.17520/biods.2025037.
Shengnan Ji, Jiarong Han, Yueheng Ren, Xiaodong Mu, Yanpeng Zhu (2025) Prediction of suitable habitats and risk assessment for key invasive alien plant species on Hainan Island based on the MaxEnt model. Biodiversity Science, 33, 25037. DOI: 10.17520/biods.2025037.
| 风险等级 Risk level | 物种 Species | 分布点数 Distribution point | 海南岛适生面积比例 Suitability area ratio on Hainan Island (AR) |
|---|---|---|---|
| 高风险 High-risk (0.5 ≤ AR < 1.0) | 假高粱 Sorghum halepense | 244 | 0.8641 |
| 飞机草 Chromolaena odorata | 2,005 | 0.7521 | |
| 刺苋 Amaranthus spinosus | 789 | 0.5449 | |
| 马缨丹 Lantana camara | 3,874 | 0.5394 | |
| 中风险 Middle-risk (0.3 ≤ AR < 0.5) | 银胶菊 Parthenium hysterophorus | 1,370 | 0.4846 |
| 藿香蓟 Ageratum conyzoides | 44 | 0.4482 | |
| 五爪金龙 Ipomoea cairica | 4,071 | 0.4230 | |
| 凤眼蓝 Eichhornia crassipes | 995 | 0.4044 | |
| 假臭草 Praxelis clematidea | 1,167 | 0.3137 | |
| 低风险 Low-risk (0.1 ≤ AR < 0.3) | 大薸 Pistia stratiotes | 715 | 0.2981 |
| 小蓬草 Erigeron canadensis | 1,315 | 0.1734 | |
| 极低风险 Minimal-risk (0 ≤ AR < 0.1) | 三叶鬼针草 Bidens pilosa | 6,145 | 0.0739 |
| 空心莲子草 Alternanthera philoxeroides | 1,370 | 0.0647 | |
| 紫茎泽兰 Ageratina adenophora | 68 | 0.0615 | |
| 光荚含羞草 Mimosa bimucronata | 52 | 0.0486 | |
| 毒莴苣 Lactuca serriola | 25 | 0.0294 | |
| 垂序商陆 Phytolacca americana | 1,051 | 0.0276 | |
| 薇甘菊 Mikania micrantha | 4,726 | 0.0178 | |
| 互花米草 Spartina alterniflora | 47 | 0.0076 | |
| 野燕麦 Avena fatua | 176 | 0.0039 | |
| 落葵薯 Anredera cordifolia | 1,176 | 0.0018 | |
| 苏门白酒草 Erigeron sumatrensis | 2,882 | 0.0008 | |
| 水盾草 Cabomba caroliniana | 23 | 0.0000 | |
| 加拿大一枝黄花 Solidago canadensis | 149 | 0.0000 | |
| 豚草 Ambrosia artemisiifolia | 137 | 0.0000 |
表1 海南岛25种重点管理外来入侵植物适生区面积比例及风险分级
Table 1 Proportion of suitable habitat area and risk classification for 25 key invasive alien plant species on Hainan Island
| 风险等级 Risk level | 物种 Species | 分布点数 Distribution point | 海南岛适生面积比例 Suitability area ratio on Hainan Island (AR) |
|---|---|---|---|
| 高风险 High-risk (0.5 ≤ AR < 1.0) | 假高粱 Sorghum halepense | 244 | 0.8641 |
| 飞机草 Chromolaena odorata | 2,005 | 0.7521 | |
| 刺苋 Amaranthus spinosus | 789 | 0.5449 | |
| 马缨丹 Lantana camara | 3,874 | 0.5394 | |
| 中风险 Middle-risk (0.3 ≤ AR < 0.5) | 银胶菊 Parthenium hysterophorus | 1,370 | 0.4846 |
| 藿香蓟 Ageratum conyzoides | 44 | 0.4482 | |
| 五爪金龙 Ipomoea cairica | 4,071 | 0.4230 | |
| 凤眼蓝 Eichhornia crassipes | 995 | 0.4044 | |
| 假臭草 Praxelis clematidea | 1,167 | 0.3137 | |
| 低风险 Low-risk (0.1 ≤ AR < 0.3) | 大薸 Pistia stratiotes | 715 | 0.2981 |
| 小蓬草 Erigeron canadensis | 1,315 | 0.1734 | |
| 极低风险 Minimal-risk (0 ≤ AR < 0.1) | 三叶鬼针草 Bidens pilosa | 6,145 | 0.0739 |
| 空心莲子草 Alternanthera philoxeroides | 1,370 | 0.0647 | |
| 紫茎泽兰 Ageratina adenophora | 68 | 0.0615 | |
| 光荚含羞草 Mimosa bimucronata | 52 | 0.0486 | |
| 毒莴苣 Lactuca serriola | 25 | 0.0294 | |
| 垂序商陆 Phytolacca americana | 1,051 | 0.0276 | |
| 薇甘菊 Mikania micrantha | 4,726 | 0.0178 | |
| 互花米草 Spartina alterniflora | 47 | 0.0076 | |
| 野燕麦 Avena fatua | 176 | 0.0039 | |
| 落葵薯 Anredera cordifolia | 1,176 | 0.0018 | |
| 苏门白酒草 Erigeron sumatrensis | 2,882 | 0.0008 | |
| 水盾草 Cabomba caroliniana | 23 | 0.0000 | |
| 加拿大一枝黄花 Solidago canadensis | 149 | 0.0000 | |
| 豚草 Ambrosia artemisiifolia | 137 | 0.0000 |
图3 环境变量对海南岛重点管理外来入侵植物潜在适生区的平均贡献率(只展示排名前10的环境变量)。BUA: 建设用地面积; ELE: 海拔; Sq1: 营养供应; Bio2: 平均昼夜温差; Bio4: 温度季节性; Bio7: 年温度变化范围; Bio14: 最干月降水量; Bio16: 最湿季降水量; Bio18: 最暖季降水量; Bio19: 最冷季降水量。
Fig. 3 Mean percentage contribution of environmental variables to potential suitable habitats of key invasive alien plant species on Hainan Island (only the top 10 contributing environmental variables shown). BUA, Built-up area; ELE, Elevation; Sq1, Nutrient availability; Bio2, Mean diurnal range; Bio4, Temperature seasonality; Bio7, Temperature annual range; Bio14, Precipitation of driest month; Bio16, Precipitation of wettest quarter; Bio18, Precipitation of warmest quarter; Bio19, Precipitation of coldest quarter.
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