Chai Sen-Xin, Ma Li-Ping, Ma Zhong-Wu, Lei Yu-Tian, Ye Ya-Qiong, Wang Bo, Xiao Yuan-Ming, Yang Ying, Zhou Guo-Ying
College of Life Sciences, Qinghai Normal University, Xining, 810016, China.
CAS Key Laboratory of Tibetan Medicine Research, Northwest Institute of Plateau Biology, Xining, 810008, China.
Sci Rep. 2025 Mar 24;15(1):10055. doi: 10.1038/s41598-025-95016-8.
Amid the ongoing trend of global warming, the distribution of habitable areas for Rhododendron is facing significant risks. To investigate the possible spatial distribution of Rhododendron on the Qinghai-Xizang Plateau in light of future global warming scenarios, we employed the Maximum entropy model (MaxEnt model) to map its suitable habitat using geographic distribution data and environmental factors projected for 2050s and 2070s, considering three representative concentration pathway (RCP) scenarios, while identifying the key factors influencing their distribution. The results show that: [1] The area under curve (AUC) values of the five Rhododendron were all greater than 0.98, indicated that the model prediction effect was excellent; [2] Isothermality is the most important environmental factor affecting the distribution of Rhododendron (excluding Rhododendron przewalskii). The most important environmental factor for Rhododendron przewalskii is altitude (alt: 51%), with an optimum range of 2700-3300 m, and Rhododendron trichostomum are affected by altitude (alt 18%), with an optimum range of 3200-3900 m. Rhododendron przewalskii (bio12: 21%) and Rhododendron trichostomum(bio12: 19%) are also affected by annual precipitation, and Rhododendron laudandum(bio12: 6%) is less affected by annual precipitation, The optimal amount of precipitation is 400-500 mm as well as 500-800 mm. Rhododendron przewalskii and Rhododendron trichostomum are suitable for survival in high altitude, semi-arid areas [3]. The suitable areas for survival for Rhododendron przewalskii, Rhododendron trichostomum, Rhododendron hypenanthum, and Rhododendron nyingchiense is expanding, while the suitable areas for survival for Rhododendron laudandum is shrinking [4]. The optimal zone for Rhododendron przewalskii is primarily found in the eastern section of the Qinghai-Xizang Plateau, while suitable areas for survival for the other four Rhododendron species are predominantly located in the southern region of the same plateau. Therefore, these regions will be designated as the primary conservation zones for in-situ preservation. The results of the study provide a basis for the in situ conservation of Rhododendron in response to global warming, relocation conservation, and the construction of nature reserve communities and ecological corridors.
在全球变暖的持续趋势下,杜鹃花适宜栖息地的分布正面临重大风险。为了根据未来全球变暖情景研究杜鹃花在青藏高原可能的空间分布,我们采用最大熵模型(MaxEnt模型),利用2050年代和2070年代预测的地理分布数据和环境因素,考虑三种代表性浓度路径(RCP)情景,绘制其适宜栖息地,同时确定影响其分布的关键因素。结果表明:[1] 五种杜鹃花的曲线下面积(AUC)值均大于0.98,表明模型预测效果良好;[2] 等温性是影响杜鹃花分布的最重要环境因素(不包括普氏杜鹃)。普氏杜鹃最重要的环境因素是海拔(alt:51%),最佳范围为2700 - 3300米,毛喉杜鹃受海拔影响(alt 18%),最佳范围为3200 - 3900米。普氏杜鹃(bio12:21%)和毛喉杜鹃(bio12:19%)也受年降水量影响,而大钟杜鹃(bio12:6%)受年降水量影响较小,最佳降水量为400 - 500毫米以及500 - 800毫米。普氏杜鹃和毛喉杜鹃适合在高海拔、半干旱地区生存 [3]。普氏杜鹃、毛喉杜鹃、淡黄杜鹃和林芝杜鹃的适宜生存区域正在扩大,而大钟杜鹃的适宜生存区域正在缩小 [4]。普氏杜鹃的最佳区域主要位于青藏高原东部,而其他四种杜鹃花的适宜生存区域主要位于同一高原的南部。因此,这些区域将被指定为原地保护的主要保护区。研究结果为应对全球变暖的杜鹃花原地保护、迁地保护以及自然保护区群落和生态廊道建设提供了依据。