Wang Mei-Na, Duan Lei, Qiao Qi, Wang Zheng-Feng, Zimmer Elizabeth A, Li Zhong-Chao, Chen Hong-Feng
Key Laboratory of Plant Resources Conservation and Sustainable Utilization, South China Botanical Garden, Chinese Academy of Sciences, Guangzhou, China.
Shenzhen Key Laboratory for Orchid Conservation and Utilization, The National Orchid Conservation Center of China and The Orchid Conservation & Research Center of Shenzhen, Shenzhen, China.
PLoS One. 2018 Jan 12;13(1):e0189034. doi: 10.1371/journal.pone.0189034. eCollection 2018.
Bretschneidera sinensis, a class-I protected wild plant in China, is a relic of the ancient Tertiary tropical flora endemic to Asia. However, little is known about its genetics and phylogeography. To elucidate the current phylogeographic patterns and infer the historical population dynamics of B. sinensis, and to make recommendations for its conservation, three non-coding regions of chloroplast DNA (trnQ-rps16, rps8-rps11, and trnT-trnL) were amplified and sequenced across 256 individuals from 23 populations of B. sinensis, spanning 10 provinces of China. We recognized 13 haplotypes, demonstrating relatively high total haplotype diversity (hT = 0.739). Almost all of the variation existed among populations (98.09%, P < 0.001), but that within populations was low (1.91%, P < 0.001). Strong genetic differentiation was detected among populations (GST = 0.855, P < 0.001) with limited estimations of seed flow (Nm = 0.09), indicating that populations were strongly isolated from one another. According to SAMOVA analysis, populations of B. sinensis in China could be divided into five geographic groups: (1) eastern Yunnan to western Guangxi; (2) Guizhou-Hunan-Hubei; (3) central Guangdong; (4) northwestern Guangdong; and (5) the Luoxiao-Nanling-Wuyi -Yangming Mountain. Network analysis showed that the most ancestral haplotypes were located in the first group, i.e., the eastern Yungui Plateau and in eastern Yunnan, which is regarded as a putative glacial refugia for B. sinensis in China. B. sinensis may have expanded its range eastward from these refugia and experienced bottleneck or founder effects in southeastern China. Populations in Liping (Guizhou Province), Longsheng (Guangxi Province), Huizhou (Guangdong Province), Chongyi (Jiangxi Province), Dong-an (Hunan Province), Pingbian (Yunnan Province) and Xinning (Hunan Province) are proposed as the priority protection units.
伯乐树是中国国家一级保护野生植物,是古老的第三纪亚洲热带植物区系的孑遗植物。然而,人们对其遗传学和系统地理学知之甚少。为了阐明伯乐树当前的系统地理格局,推断其历史种群动态,并为其保护提出建议,我们对来自中国10个省份23个种群的256个伯乐树个体的叶绿体DNA的三个非编码区(trnQ-rps16、rps8-rps11和trnT-trnL)进行了扩增和测序。我们识别出13种单倍型,显示出相对较高的总单倍型多样性(hT = 0.739)。几乎所有的变异都存在于种群间(98.09%,P < 0.001),而种群内的变异较低(1.91%,P < 0.001)。检测到种群间存在强烈的遗传分化(GST = 0.855,P < 0.001),种子流估计有限(Nm = 0.09),表明种群之间相互隔离程度很高。根据SAMOVA分析,中国的伯乐树种群可分为五个地理组:(1)云南东部至广西西部;(2)贵州-湖南-湖北;(3)广东中部;(4)广东西北部;(5)罗霄-南岭-武夷-阳明山。网络分析表明,最古老的单倍型位于第一组,即云贵高原东部和云南东部,这里被认为是中国伯乐树的一个假定冰期避难所。伯乐树可能从这些避难所向东部扩展其分布范围,并在中国东南部经历了瓶颈效应或奠基者效应。建议将贵州省黎平县、广西壮族自治区龙胜县、广东省惠州市、江西省崇义县、湖南省东安县、云南省屏边县和湖南省新宁县的种群作为优先保护单元。