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作 者:唐梦诗 袁淑娜[2] 余文刚[1,2,3] 施琦 侯天泽 吴君楠 刘子毓 TANG Mengshi;YUAN Shuna;YU Wengang;SHI Qi;HOU Tianze;WU Junnan;LIU Ziyu(College of Horticulture,Hainan University,Haikou,Hainan 570228,China;Rubber Research Institute,Chinese Academy of Tropical Agricultural Sciences/State Key Laboratory Breeding Base of Cultivation&Physiology for Tropical Crops/Danzhou Investigation&Experiment Station of Tropical Crops,Ministry of Agriculture and Rural Affairs,Haikou,Hainan 570228,China;Hainan Key Laboratory for Quality Regulation of Tropical Horticultural Plants,Haikou,Hainan 570228,China)
机构地区:[1]海南大学园艺学院,海南海口570228 [2]中国热带农业科学院橡胶研究所/热带作物栽培生理学省部共建重点实验室/农业农村部儋州热带作物科学观测实验站,海南海口570228 [3]海南省热带园艺作物品质调控重点实验室,海南海口570228
出 处:《热带作物学报》2021年第11期3369-3375,共7页Chinese Journal of Tropical Crops
基 金:国家自然科学基金项目(No.31660580);省部重点实验室开放课题(No.RRI-KLOF202003)。
摘 要:红茴砂是姜科茴香砂仁属多年生草本植物,我国仅在海南地区有自然分布,是具有很高药用价值的濒危植物。为了解红茴砂在未来气候变化下的潜在适生区及其主要环境影响因子,以期对红茴砂的保育提供科学指导,将45条红茴砂分布位点数据与20个环境因子相结合,运用最大熵生态位模型MaxEnt和ArcGIS软件模拟了当前气候和未来2050年RCP2.6和RCP8.5两种不同气候条件下红茴砂在中国的潜在分布区,并分析影响红茴砂分布的主导环境因子。结果表明:当前气候条件下,红茴砂适生区总范围在18°~32°N、27°~122°E,面积约为1.24×10^(6)km^(2),主要集中分布在海南、贵州、福建、广东、广西、云南等地;影响红茴砂地理分布的主导环境因子为最湿月降水量、最暖季度降水量、年均温度变化范围、最冷月份最低温、海拔和最热季度均温,累计贡献率达87%;在未来2050年RCP2.6和RCP8.5两种不同气候情景下,红茴砂适生区域丧失面积均达到95%以上,潜在分布区缩小到云南、四川、西藏、贵州和台湾这5个省区,新增区域主要在西藏东南部和四川中南部,同时潜在总适生区和高适生区的质心有向西北方迁移的趋势。Zingiberaceae Etlingera littoralis(J. Koenig) Giseke is a endangered perennial herb with high medicinal value,the natural distribution in China is Hainan. Predicting the potential suitable areas and key environmental factors are critical to the conservation of E. littoralis. Based on the data of 45 current distribution points of E. littoralis in global and 20 environmental factors the key environmental factors and the potential suitable areas under current and future two scenarios(2050 s RCP 2.6, 2050 s RCP 8.5) in China were dtudied using the MaxEnt and ArcGIS, and the potential distribution changes of E. littoralis in China was analyzed, using the SDM toolbox of ArcGIS software, Under the present climatic conditions, E.littoralis is mainly distributed from North latitude 18° to 32°, and East longitude from 27° to 122°, with a total suitable area about 1.24×10^(6)km^(2). The current potential distribution areas are Hainan, Guizhou, Fujian,Guangdong, Guangxi, Yunnan, Sichuan, Chongqing, Tibet, Hunan, Hubei, Taiwan. Dominant environmental factors affecting the distribution of E. littorali. were precipitation of the wettest month, precipitation of the warmest quarter,temperature annual range, mean temperature of the coldest month, altitude and mean temperature of the warmest quarter,with a cumulative contribution rate of 87%. Under future climate scenarios of RCP2.6 and RCP8.5 by the 2050 s, the loss of potential suitable areas of E. littoralis would be up to 95%, and the potential distribution areas would be limited to Yunnan, Sichuan, Tibet, Guizhou and Taiwan. The increased areas are in southeastern Tibet and south-central Sichuan.The centers of total suitable areas and most suitable areas would be moved towards northwest.
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