If you ask to a western botanist: “Which is the world’s most endangered plant species?” he will probably answer the Florida torreya (Torreya taxifolia Arn.), the Wollemi pine (Wollemia nobilis W. G. Jones, K. D. Hill & J. M. Allen), or perhaps the Nebrodi fir (Abies nebrodensis Mattei), if the interviewed is of european origin. In contrast, if you make the same question to a Chinese (or at least to somebody familiar with the Chinese flora) you may get a quite different reply. Much less known than these emblematic trees, a large handful of Chinese plant taxa is currently in a more critical situation, with just a very few individuals surviving (He, 2009; Lopez-pujol & zhang, 2009). A rare cypress (Cupressus chengiana S. Y. Hu var. jiangeensis (N. zhao) Silba1) is arguably the most threatened gymnosperm on earth because only one individual tree occurs in Longmen (“Dragon’s Gate”) Mountains, in northern Sichuan. The baishanzu fir (Abies beshanzuensis M. H. Wu var. beshanzuensis1) from zhejiang, is not in a much wealthier situation, with only three representatives alive. Moreover, China has also the dubious honour of harbouring some of the surely world’s most endangered angiosperms, such as Carpinus putoensis W. C. Cheng (one fenced, old individual is remaining in the wild in putuo Island, in the east China Sea), Gleditsia japonica Miq. var. velutina L. Chu Li1 and Sinopora hongkongensis (N. H. Xia, Y. F. Deng & K. L.Yip) J. Li, N. H. Xia & H. W. Li (with two individuals each one), or Acer yangbiense Y. S. Chen & Q. e. Yang (with four representatives). These few conspicuous examples of rare plants, however, may represent just the iceberg’s tip of a flora facing a situation of extreme risk: of the approximately 4200 angiosperm taxa assessed in the first issue of the China Species Red List (which represents just 14% of the angiosperm flora of China), as many as 651 were listed as CR (“critically endangered”) following the 2001 IuCN criteria (Xie & Wang, 2007), that is, in the verge of extinction. The disproportionate number of extremely threatened plants in China may have resulted from the combination of natural and human-induced factors (Lopez-pujol & zhang, 2009). The existence of numerous refuge areas during the Quaternary glacial periods in China (Qian & Ricklefs, 2000; Lopezpujol, 2008; Lopez-pujol & Ren, 2010) yielded a large number of narrow endemics through survival of relict (pre-Quaternary) lineages as well as by differentiation and speciation in these favourable pockets, most of them located in the southern mountainous regions (Fig. 1). The huge destruction and deterioration of ecosystems, largely reported in China during recent decades (e.g. Lopez-pujol et al., 2006; He, 2009), must have decimated many of these “naturally rare” species, in some cases driving them to the brink of extinction (such as the abovementioned examples) or
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