Resolving a nearly 90-year-old enigma: The rare Fagus chienii is conspecific with F. hayatae based on molecular and morphological evidence
Dan-Qi Lia,b,c,1, Lu Jianga,b,1, Hua Lianga,b, Da-Hai Zhud, Deng-Mei Fanb, Yi-Xuan Koub,e,f, Yi Yangb,**, Zhi-Yong Zhanga,b,e,f,*     
a. College of Forestry, Jiangxi Agricultural University, Nanchang 330045, China;
b. Laboratory of Subtropical Biodiversity, Jiangxi Agricultural University, Nanchang 330045, China;
c. Lushan Botanical Garden, Jiangxi Province and Chinese Academy of Sciences, Jiujiang 332900, China;
d. Longxi-Hongkou National Reserve, Chengdu 611830, China;
e. Key Laboratory of Ecology of Rare and Endangered Species and Environmental Protection (Guangxi Normal University), Ministry of Education, Guilin 541004, China;
f. Guangxi Key Laboratory of Landscape Resources Conservation and Sustainable Utilization in Lijiang River Basin, Guilin 541006, China
Abstract: Taxonomic uncertainties of rare species often hinder effective prioritization for conservation. One such taxonomic uncertainty is the 90-year-old enigma of Fagus chienii. F. chienii was previously only known from the type specimens collected in 1935 in Pingwu County of Sichuan Province, China, and has long been thought to be on the verge of extinction. However, morphological similarities to closely related Fagus species have led many to question the taxonomic status of F. chienii. To clarify this taxonomic uncertainty, we used the newly collected samples to reconstruct a molecular phylogeny of Chinese Fagus species against the phylogenetic backbone of the whole genus using seven nuclear genes. In addition, we examined nine morphological characters to determine whether F. chienii is morphologically distinct from its putatively closest relatives (F. hayatae, F. longipetiolata, and F. lucida). Both morphological and phylogenetic analyses indicated that F. chienii is conspecific with F. hayatae. We recommended that F. chienii should not be treated as a separate species in conservation management. However, conservation strategies such as in situ protection and ex situ germplasm preservation should be adopted to prevent the peculiar "F. chienii" population from extinction.
Keywords: Conspecific    Fagus chienii    F. hayatae    Phylogenetics    Morphology    Conservation    
1. Introduction

Accurate species delimitation and identification are essential for biodiversity conservation and sustainable use of economically important plants, especially in rare taxa that are taxonomically uncertain due to a lack of rigorous research (Thomson et al., 2018; Ding et al., 2019; Nic Lughadha et al., 2019; Cheng et al., 2021). Erroneous classification and misidentification can leave out endangered species that should otherwise be protected (Gibson et al., 2019). Conversely, management action that results from incorrect identification of species wastes resources and funding (Solow et al., 2011). For instance, Torreya grandis var. jiulongshanensis Z.Y. Li, Z.C. Tang & N. Kang (Kang and Tang, 1995) is listed as a Category Ⅱ protected plant in the Chinese List of Wild Plants (http://www.forestry.gov.cn/main/5461/20210908/162515850572900.html). However, a recent phylogenetic study clearly demonstrated that this endangered plant is a natural hybrid between Torreya jackii Chun and T. grandis Fort. ex Lindl., raising doubts about its validity as a key protected plant species (Kou et al., 2017).

Fagus L. is an economically important genus that consists of 12 members of deciduous trees (Shen, 1992; Peters, 1997; Jiang et al., 2022). China accommodates five beech species in subtropical regions between the Qinling Mountains and the Nanling Mountains: F. engleriana Seem. ex Diels (1900), F. longipetiolata Seem. (von Seemen, 1897), F. lucida Rehd. & Wils. (Rehder and Wilson, 1916), F. hayatae Palib. ex Hayata (1911) and Fagus chienii Cheng (Cheng, 1935; Zhang and Huang, 1998; Fang et al., 1999; Denk, 2003; Jiang et al., 2022). Although four of these species are widespread in subtropical China, F. chienii has an exceptionally narrow distribution and is only found in Pingwu County, northern Sichuan (Cheng, 1935). Because no specimens have been collected since its establishment based on a single collection in 1935, F. chienii is believed to be in danger of going extinct (Peters, 1997; Guo and Werger, 2010). To prevent the extinction of this rare plant, the People's Government of Sichuan Province listed F. chienii as a key protected species in 2016.

The scarcity of field collections, however, has led to the taxonomic uncertainty of F. chienii (Huang et al., 1999). Cheng (1935) provided a brief description of F. chienii and noted that it might be of hybrid origin because it shares similar involucres and scales with F. longipetiolata while resembling F. lucida in leaf blade shape and size. Chang and Huang (1988) suspected that F. chienii might be an ecotype of F. lucida, but still considered it as a mysterious finding with a disputed taxonomic rank. Furthermore, F. chienii was not recorded by the authors of Flora of China (Huang et al., 1999), possibly owing to limited information and the resultant taxonomic uncertainty. To date, the species status of F. chienii remains an enigma that needs to be resolved using newly available experimental materials.

To resolve the taxonomic status of F. chienii, we reexamined the type specimens and conducted extensive field investigations in the type locality from 2019 to 2021. A local news report from Sichuan Province led us to a rediscovered population of F. chienii in Laohegou Nature Reserve in Pingwu County in 2021 (Li, 2016). We used the new collections and samples to reconstruct the molecular phylogeny of Chinese Fagus members against the phylogenetic backbone of the whole genus (Jiang et al., 2022) based on sequences of seven nuclear DNA markers. We also determined whether F. chienii is morphologically distinct from its closely relatives (F. hayatae, F. longipetiolata, and F. lucida) through statistical analyses of nine morphological characters.

2. Materials and methods 2.1. Phylogenetic analyses

Twelve species of Fagus were examined in this study, with Castanea seguinii Dode used as outgroup. To achieve good coverage, no less than four individuals from separate locations for each Chinese species were included (Fig. 1). Samples from 10 individuals of F. chienii were collected. To enlarge the intraspecific representation of F. hayatae, which was assumed to be conspecific with F. chienii, an additional 10 F. hayatae individuals were included. Seven representative loci from Jiang et al. (2022) were amplified and sequenced for F. chienii and the new F. hayatae samples, i.e., F128, F138, P4, P14, P37, P52, and P72 (Table S1). We did not use chloroplast DNA sequences in this study because chloroplast haplotypes are shared frequently within Fagus and are considered ineffective in phylogenetic reconstructions of the genus (Zhang et al., 2013). DNA extraction, PCR amplification, and DNA sequencing followed Jiang et al. (2022). The DNA sequences of additional accessions were from Jiang et al. (2022) (Table S2). Voucher information of the additional samples are shown in Table S2 and the new sequence data of each locus were deposited in GenBank under accession numbers: ON584566–ON584685.

Fig. 1 The distribution map of DNA and herbarium samples of Fagus hayatae and F. chienii in this study. Note that F. hayatae has a fragmented distribution in mainland China and Taiwan. 1, Pingwu; 2, Qinchuan; 3, Micangshan; 4, Guangwushan; 5, Xipingcun; 6, Puyuancun; 7, Tianshuxia; 8, Shennongjia; 9, Dalaoling; 10, Houhecun; 11, Hupingshan; 12, Qinliangfeng; 13, Sihaishan; 14, Lalashan; 15, Beichatianshan; 16, Tongshan. Relevant citations on the specimens are shown in Tables S2 and S3.

Raw chromatograms were manually checked and aligned using Sequencher v.5.4.6 (Gene-Codes Corporation, Ann Arbor, MI, USA), and then refined manually in MEGA 5.05. Phylogenetic analyses were performed based on the concatenated data set using maximum likelihood (ML) and Bayesian inference (BI) methods. ML analysis was carried out using RaxML v.8.2.12 (Stamatakis, 2014) software in Linux system with 1000 bootstrap replicates. BI analysis was conducted in MrBayes v.3.2.6 (Ronquist et al., 2012). The best-fitting nucleotide substitution models (HKY + I) were decided by jModeltest 2.1.7 (Darriba et al., 2012) with the Bayesian information criterion (BIC). Posterior probabilities were approximated by sampling trees using a variant of the Markov Chain Monte Carlo (MCMC) method. A total of 20, 000 trees were sampled every 1000th generation. The first 5000 generations (about 25%) were eliminated as "burn-in". Average standard deviation of split frequencies was less than 0.01. All the phylogenetic trees were visualized in FigTree v.1.4.4 and edited in Adobe Illustrator 2020 (Fig. 2). To account for incomplete lineage sorting, which can have a major influence on phylogenetic reconstruction, we used a multispecies coalescent approach in StarBEAST2 0.15.5 (Ogilvie et al., 2017, see details in Jiang et al., 2022) to infer the species tree using the seven nuclear loci.

Fig. 2 The maximum likelihood (ML) tree and Bayesian inference (BI) tree based on seven concatenated nuclear genes (4102 bp) for the phylogenetic analysis of Fagus taxa. Numbers above branches are statistical support values for ML and BI. Bold font represents Fagus chienii. Clade Ⅰ: subgen. Fagus, clade Ⅱ: subgen. Engleriana.
2.2. Morphological studies

Digital images of F. chienii and its putatively closest relatives (F. hayatae, F. longipetiolata, and F. lucida) were derived from the Chinese Virtual Herbarium (https://www.cvh.ac.cn/), the web of Plants of Taiwan (https://tai2.ntu.edu.tw), the Global Biodiversity Information Facility (https://www.gbif.org/) and JSTOR Global Plants (https://plants.jstor.org). For F. chienii, we examined twelve available specimens in total, seven of which were collected in this study from Pingwu County (the type locality); the remaining five samples were holotype and isotypes with mature fruits deposited in the Royal Botanic Gardens, Kew, South China Botanical Garden, CAS, Chinese National Herbarium, Royal Botanic Garden Edinburgh and New York Botanic Garden, respectively (Table S3). Additionally, we measured 38 specimens of F. hayatae, and 15 specimens each of F. longipetiolata and F. lucida. Specimens of the four species were selected to provide a broad geographical representation across their native ranges (Fig. 1).

Nine morphological characters, i.e., leaf length, leaf width, ratio of leaf length/width, leaf petiole length, leaf teeth length, number of secondary veins, cupule peduncle length, bract length, and cupule length, were measured (Fig. 3A). According to Shen (1992), these characters are key to distinguishing Chinese Fagus species. ImageJ software was applied to the examination of characters under investigation. Three well-preserved leaves and/or fruits per specimen were randomly selected for examination. Detailed measurements and voucher information are available in Table S3.

Fig. 3 Morphological analyses of Fagus chienii and related species. A, Morphometric measurements in this study. L1: leaf length, L2: leaf petiole length, L3: leaf width, L4: cupule peduncle length, L5: bract length, L6: cupule length, L7: leaf teeth length; B, Scatter plot of the first two principal components (PCs) of PCA based on seven morphological variables of Fagus chienii collected in this study (Fagus chienii), F. chienii types (F. chienii-TYPE), F. hayatae, F. longipetiolata, and F. lucida. Each dot represents a specimen; C and D, Scatter plot of the first two dimensions of PCoA. We treated the specimen of F. hayatae, F. chienii and F. chienii-TYPE as one group (C) and three separate groups (D), respectively. R2 is the proportion of sum of squares from the total in Adonis analysis. P is the significance value of R2.

The values of the nine characters were normalized by mean and standard deviation. To avoid collinearity in subsequent analyses, highly correlated characteristics were then eliminated by Pearson correlation analysis conducted in the IBM SPSS Statistics 26. Principal Component Analysis (PCA) was performed in ORIGIN 2021 to investigate the relationships among F. chienii, F. hayatae, F. longipetiolata, and F. lucida. The clustering analysis of specimen samples in the scatter plot was tested by discriminant analysis of the first two PCs.

To further test the reliability of the clustering analysis, a Principal Coordinates Analysis (PCoA) using Bray–Curtis dissimilarity index was performed and graphically visualized by Vegan package and ggplot2 package in R v.4.1.2 software (Oksanen et al., 2015). We treated the specimen of F. hayatae, F. chienii collected in this study (denoted as F. chienii in Fig. 3) and F. chienii types (F. chienii-TYPE in Fig. 3) as one group and three separate groups, respectively. The significance level of pairwise comparisons between groups was computed based on Adonis test by pairwiseAdonis package (Martinez Arbizu, 2020) according to Bonferroni adjusted P-values.

In addition, comparisons of nine morphological characters between the four beech species were conducted and their significances were evaluated by t-test using the ggsignif package in R v.4.1.2 software (RcoreTeam, 2021).

3. Results 3.1. Molecular phylogenetic relationships of Fagus chienii

The aligned data set consisted of 52 accessions, including twelve taxa of Fagus and one outgroup species, with a concatenated sequence length of 4102 bp. Within Fagus, the total aligned length of concatenated sequences of seven nuclear loci was 4007 bp, and the length of each locus ranged from 291 bp to 657 bp, with an average of 572 bp. The variable sites of each locus ranged from 23 to 48 with an average of 38 and the parsimony informative sites ranged from 22 to 39 with an average of 31 (Table S1). The phylogenetic trees inferred from ML and BI approaches based on concatenated sequences were identical in topology. The species tree (Fig. S1) based on the multi-species coalescent approach was consistent with the ML and BI trees but with relatively low resolution. Below, we only present the ML tree, with posterior probabilities from BI analyses designated (Fig. 2).

Our results showed that Fagus was monophyletic (ML bootstrap = 100/BI posterior probability = 1.00). The concatenated ML and BI trees both identified two clades, and strongly supported a sister relationship between subgen. Fagus (clade Ⅰ) and subgen. Engleriana (clade Ⅱ) (73/0.92 and 100/1.00, Fig. 2). All twelve Fagus species, except for F. chienii and F. hayatae, were recovered as monophyletic clades. F. lucida, which was assumed to be synonymous or one of the parents of F. chienii, was sister to F. longipetiolata (74/1.00), both of which were sister to a Japanese beech (Fagus crenata Blume). Notably, F. hayatae intermingled with F. chienii, forming a highly supported clade (86/1.00). In other words, F. chienii was distinct from both F. longipetiolata and F. lucida but indistinguishable from F. hayatae phylogenetically. In addition, F. chienii did not form a monophyletic clade as other species of subgen. Fagus, implying that F. chienii is not a lineage with an independent evolutionary history.

3.2. Morphological analyses

After Pearson correlation analysis, we excluded leaf length and cupule peduncle length from further morphological analysis. The results of PCA and PCoA were determined by the remaining seven variables (leaf teeth length, ratio of length/width, number of secondary veins, leaf petiole length, leaf width, cupule length, bract length). Both PCA and PCoA clearly showed that three distinct groups, i.e., F. chienii plus F. hayatae, F. longipetiolata, and F. lucida, were identified by the scatter plots of the first two axes. In the PCA (Fig. 3B), the first two axes explained 74.9% of the variance, with 54.1% for PC1 and 20.8% for PC2, respectively. In PCoA, irrespective of whether the specimen of F. hayatae, F. chienii or F. chienii-TYPE were treated as one group or not, the first two principal coordinates accounted for 92.3% of the variance, with 87.2% for PCoA1 and 5.1% PCoA2, respectively. The proportion of sum of squares from the total was significantly high (R2 = 0.7691, P = 0.001 when F. hayatae, F. chienii and F. chienii-TYPE treated as one group and R2 = 0.7996, P = 0.001 when F. hayatae, F. chienii and F. chienii-TYPE as three separate groups, Fig. 3C, D). When F. hayatae, F. chienii and F. chienii-TYPE were pairwise compared, only F. hayatae and F. chienii-TYPE showed a significant difference in Adonis analysis (Table 1).

Table 1 Pairwise comparisons of Fagus chienii collected in this study (Fagus chienii), F. chienii types (F. chienii-TYPE), F. hayatae, F. longipetiolata, and F. lucida based on seven morphological characters in Adonis analysis using pairwise Adonis package.
Pairs R2 P-value P-adjusted
Fagus hayatae vs. F. chienii-TYPE 0.2175 0.030 0.0375*
F. hayatae vs. F. chienii 0.0636 0.246 0.2460
F. hayatae vs. F. longipetiolata 0.8253 0.001 0.0014**
F. hayatae vs. F. lucida 0.6619 0.001 0.0014**
F. chienii-TYPE vs. F. chienii 0.2780 0.056 0.0622
F. chienii-TYPE vs. F. longipetiolata 0.7668 0.001 0.0014**
F. chienii-TYPE vs. F. lucida 0.5673 0.001 0.0014**
F. chienii vs. F. longipetiolata 0.8346 0.001 0.0014**
F. chienii vs. F. lucida 0.6516 0.001 0.0014**
F. longipetiolata vs. F. lucida 0.5623 0.001 0.0014**
F. hayatae & F. chienii vs. F. longipetiolata 0.7852 0.001 0.0010**
F. hayatae & F. chienii vs. F. lucida 0.5769 0.001 0.0010**

T-test analyses of all nine morphological characters (P < 0.01) showed that there was no significant difference between F. chienii and F. hayatae (Fig. 4). Furthermore, significant differences between F. chienii/F. hayatae and F. lucida were detected in terms of leaf petiole length, cupule peduncle length, bracts length, teeth length, and number of secondary veins. Conspicuous divergences between F. chienii/F. hayatae and F. longipetiolata were observed in all the characters except for the ratio of leaf length/width. All the original measurements of morphological traits are presented in Table S4.

Fig. 4 Comparisons of nine morphological characters between Fagus chienii, F. hayatae, F. longpetiolata, and F. lucida. The boxes represent the interquartile and the vertical lines represent the range excluding the extreme values (black dots). Different lowercase letters on the top of the vertical lines indicate significant differences (P < 0.01) between Fagus species.
4. Discussion 4.1. Taxonomic status of Fagus chienii

Recently, Jiang et al. (2022) reconstructed a robust phylogenetic tree of Fagus in which all eleven species were well recognized except for F. chienii, due to a lack of experimental materials at that time. In this study, although only seven of 28 nuclear single/low-copy genes of Jiang et al. (2022) were adopted, our phylogenetic trees are essentially congruent with that of Jiang et al. (2022), suggesting the seven nuclear genes are effective in phylogenetic reconstruction and species identification of Fagus. However, F. chienii and F. hayatae are nested together in our newly reconstructed tree (Fig. 2). The PCA, PCoA and the t-test of morphological characters consistently indicate that there is little differentiation between the two species (Figs. 3 and 4). Note that although Adonis analysis showed a significant difference between F. hayatae and F. chienii types, it did not show significant differences between F. hayatae and F. chienii we collected or between F. chienii we collected and F. chienii types. This pattern is reasonable because the fragmented distribution of F. hayatae may result in high genetic as well as morphological differentiation within the species (Zhang et al., 2013; Ying et al., 2016; Gao et al., 2020; Li et al., 2021). In this study, we included the holotype and isotype specimens (red dots in Fig. 3B, D) specifically, a practice that may avoid the bias introduced by potential misidentification of the new F. chienii collections. In addition, the location of F. chienii is adjacent to the populations of F. hayatae at the border of Shanxi and Sichuan Provinces (Fig. 1); thus, it is possible that F. chienii represents the westernmost population of F. hayatae. Recently, Liang et al. (2022) have reached a similar conclusion concerning the taxonomic status of F. chienii based on genetic differentiation among beech species. However, they recommended that F. chienii should be treated as a synonym of Fagus pashanica (i.e., mainland F. hayatae populations), which were synonymized to F. hayatae in Flora Reipublicae Popularis Sinicae (Zhang and Huang, 1998). Because intraspecific structure does not warrant a species split (Meikle, 1957; Aranda et al., 2014; Feng et al., 2021) and no further information, such as morphological difference and reproductive isolation between F. hayatae (sensu stricto) and F. pashanica, is available in Liang et al. (2022), it is premature to treat F. chienii as a synonym of F. pashanica. Taken together, F. chienii is highly likely to be conspecific with F. hayatae rather than an independent species, resolving a nearly 90-year-old enigma in the taxonomy of Fagus.

The distinction between F. chienii and F. lucida, according to Flora Reipublicae Popularis Sinicae, is that the former has longer cupule bracts that are slightly recurved, and the latter has tuberculate cupule bracts that are closely appressed to the cupule (see Fig. 5G, H, I) (Zhang and Huang, 1998). However, there are no discernible differences in the two species' leaf length (6–9 cm in F. chienii vs. 6–11 cm in F. lucida) or leaf width (3–4.5 cm vs. 3.5–6.5 cm), and the leaf blades of both are ovate to elliptic-ovate. Based on the similarities in leaf blade shape and size, Zhang and Huang (1998) suggested that F. chienii might be conspecific with F. lucida. Indeed, our results show that there are no significant differences between F. chienii and F. lucida in leaf length (5.4–8.5 cm in F. chienii vs. 6.5–10 cm in F. lucida), leaf width (2.6–4 cm vs. 3–5 cm), ratio of leaf length/width (1.9–2.3 vs. 1.8–2.3) or cupule length (0.7–1.3 cm vs. 0.5–1.3 cm) (Figs. 4 and 5). However, we found significant divergences between the two species in the length of leaf petiole (0.3–1 cm in F. chienii/F. hayatae vs. 0.7–1.9 cm in F. lucida), teeth (0.3–1 mm vs. 0.8–1.9 mm), cupule peduncle (0.5–1.8 cm vs. 0.3–0.9 cm) and bracts (0.1–4 mm vs. 0.5–0.8 mm), and the number of secondary veins (7–11 vs. 10–13) (Figs. 4 and 5). Therefore, our results disagree with the suggestion of Zhang and Huang (1998) and provide more accurate criteria for discriminating F. chienii/F. hayatae from F. lucida.

Fig. 5 Specimens of Fagus chienii, F. hayatae, F. lucida and F. longipetiolata. A, B, holotype and isotype of F. chienii from Royal Botanic Gardens, Kew and Chinese National Herbarium, respectively; C, Specimen of F. hayatae we collected from Guangwushan, Sichuan; D, Specimen of F. chienii we collected from Pingwu County; E, holotype of F. longipetiolata; F, Specimen of F. lucida we collected from Xianheping, Guizhou; G, H, I, J, Fruit characters of F. chienii, F. hayatae, F. lucida, and F. longipetiolata, respectively; K, Fruiting branch, photographed by D. Li. The holotype specimens of F. hayatae and F. lucida are not shown because there are no fruits or inflorescences on them.

In addition, our results also reject the hypothesis that F. chienii is a hybrid between F. lucida and F. longipetiolata (Cheng, 1935), because F. chienii is neither clustered with its putative parental progenitors in phylogenetic tree (Fig. 2) nor intermediate between F. lucida and F. longipetiolata in PCA, PCoA plots as well as box and whisker plots (Figs. 3 and 4).

4.2. Conservation implications

Without a stable taxonomy, it is difficult to implement management strategies that will adequately conserve diversity (Garnett and Christidis, 2017; Sun et al., 2017; Thomson et al., 2018). Because no additional individuals of "F. chienii" had been found since its first discovery, some researchers believed that this species was extremely endangered or on the edge of extinction (Peters, 1997; Guo and Werger, 2010). Accordingly, the People's Government of Sichuan Province listed "F. chienii" as a key protected wild plant in 2016 and great efforts have been invested to protect this rare species. In this study, however, we demonstrated that "F. chienii" is conspecific with F. hayatae and should be synonymized to the latter. Therefore, it is unnecessary to treat "F. chienii" as a separate species in conservation management.

However, F. hayatae is a second-class protected plant in the Chinese List of Wild Plants under State Protection (http://www.forestry.gov.cn/main/5461/20210908/162515850572900.html) and is also an endangered species in the IUCN Red List of Threatened Species (International Union for Conservation of Nature and Natural Resources, 2022). It is thus essential to protect the "F. chienii" population because it belongs to F. hayatae. Furthermore, given that "F. chienii" is located at the northwestern edge of F. hayatae range, this population may be of peculiar conservation values because elevated genetic drift and reduced gene flow in association with local adaptation in the periphery are likely to result in the formation of distinct ecotypes (Hampe and Bairlein, 2000). Furthermore, peripheral populations are always more prone to extinction and genetically less diverse than those from the center (Hampe and Petit, 2005). This situation could be worse for "F. chienii" (F. hayatae) in Pingwu County because it was overexploited from the 1960s–1990s for its high-quality timber. Although the conservation value of the "F. chienii" population needs to be further evaluated by sophistical population genomic approaches (Garner et al., 2016; Zhang et al., 2021) and reciprocal transplant experiments (Ågren and Schemske, 2012; Lortie and Hierro, 2021), we recommend that effective conservation measures such as in situ protection and ex situ germplasm preservation should be prioritized by the local government and the germplasm bank of wild species to prevent this peculiar population from extinction (Frankham, 2010; Rawat and Agarwal, 2015; Heywood, 2017).

4.3. Taxonomic treatment

Fagus hayatae Palib. ex Hayata Journ. Coll. Sci. Univ. Tokyo 30: 286.1911 — Type: China, Taiwan: Taoyuan, Chatienshan, alt. 1700 m, 5 Feb. 1906, N. Konishi (holotype TAI-T00127!; isotype unseen).

=F. chienii Cheng, Contr. Biol. Lab. Sci. Soc. China 14: 70.1935. Syn. Nov. — Type: China, Sichuan: Pingwu County, alt. 1300m, 17 Aug. 1931, W.C. Cheng 2903 (holotype K-000832761!; isotypes E-00098603!, HUH (A)-00033870!, IBSC-0001170!, NAS-00070338!, NAS-00070339!, NY-00248568!, PE-00022177!, PE-00022178!, PE-00022179!, PE-00022180!, PE-00022181!, PE-00022182!).

=F. hayatae var. zhejiangensis M.C.Liu & M.H.Wu ex Y.T.Chang & C.C.Huang, Acta Phytotax. Sin. 26: 115.1988 — Type: China, Zhejiang, Yongjia County, Sihai-shan, 7 Oct. 1980, M.H. Wu 619 (holotype FJSI-015724!; isotype unseen).

=F. pashanica C.C. Yang, Acta Phytotax. Sin. 16: 100, pl. 1.1978. — Type: China, Sichuan, Nanjiang County, 13 Aug. 1975, C.C. Yang 75011 (holotype unseen; isotypes CDBI-0172185!, IBSC-0001171!, IBSC-0001172!, NAS-00070342!, PE-00022195!).

Description. Trees up to 20 m tall. Winter buds to 1.5 cm. Leaf petiole 0.3–1 cm long; leaf blade ovate, 3.8–8.4 cm long, 2.1–4 cm broad, base broadly cuneate to acuminate; midvein flexuous toward apex; secondary veins (5) 7–11 on each side of midvein, ending in teeth; teeth 0.3–1 mm long. Peduncle 0.5–1.8 (−2) cm, pilose. Cupule 6–13 mm long; bracts linear, recurved, pilose, 0.1–4 mm long. Nut as long as cupule, with very small wings near apex.

Phenology. It starts to flower from April to May; its fruits are mature from October to November.

Distribution and habitat. It is currently known in Taiwan (Taipei, Taoyuan, Hsinchu, Yilan), Zhejiang (Yongjia, Lin'an), Hunan (Shimen), Hubei (Yichang, Xingshan, Baokang, Xuan'en), Chongqing (Chengkou), Sichuan (Nanjiang, Qingchuan, Wangcang, Pingwu) and Shaanxi (Pingli, Xixiang) and grows in forests at elevations between 1000 and 2000 m.

Acknowledgements

We are grateful to Ming Yang (Laohegou Nature Reserve, Pingwu County, Sichuan, China) for his assistance in the field collection. This study was supported by grants from the National Natural Science Foundation of China (No. 31770236), the Guangxi Key Research and Development Projects (Guike AB21220057), and Training Program for Academic and Technical Leaders (leading talents) in Major Disciplines of Jiangxi Province (grant to Zhiyong Zhang, 20213BCJ22006).

Author contributions

Z.Z., Y.Y. and D.L. conceived and designed the work. D.L., H.L. and D.Z. collected and identified material. D.L., L.J., Y.Y., D.F. and Y.K. carried out the laboratory work and performed analyses. L.J. designed primers. D.L. drafted the manuscript and figures. Z.Z. and Y.Y revised the manuscript. All authors have read, commented and approved the final manuscript.

Declaration of competing interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Appendix A. Supplementary data

Supplementary data to this article can be found online at https://doi.org/10.1016/j.pld.2023.01.003.

References
Ågren, J., Schemske, D.W., 2012. Reciprocal transplants demonstrate strong adaptive differentiation of the model organism Arabidopsis thaliana in its native range. New Phytol., 194: 1112-1122. DOI:10.1111/j.1469-8137.2012.04112.x
Aranda, S.C., Gradstein, S.R., Patiño, J., et al., 2014. Phylogeny, classification and species delimitation in the liverwort genus Odontoschisma (Cephaloziaceae). Taxon, 63: 1008-1025. DOI:10.12705/635.12
Chang, Y.T., Huang, C.C., 1988. Note on fagaceae (Ⅱ). Acta Phytotaxon. Sin., 26: 111-119. http://www.plantsystematics.com/CN/Y1988/V26/I2/111.
Cheng, J., Li, M., Yuan, T., et al., 2021. A dataset on wild Rhododendron and geographical distribution information in China. Biodivers. Sci., 29: 1175-1180. DOI:10.24899/do.202109001
Cheng, W.C., 1935. New ligneous plants from China. Contr. Biol. Lab. Sci. Soc. China, 10: 70-71.
Darriba, D., Taboada, G.L., Doallo, R., et al., 2012. jModelTest 2: more models, new heuristics and parallel computing. Nat. Methods, 9: 772. DOI:10.1038/nmeth.2109
Denk, T., 2003. Phylogeny of Fagus L. (Fagaceae) based on morphological data. Plant Syst. Evol., 240: 55-81. DOI:10.1007/s00606-003-0018-x
Diels, L., 1900. Die Flora von Central-China. Bot. Jahrbücher, 29: 285-287.
Ding, X., Xiao, J.H., Li, L., et al., 2019. Congruent species delimitation of two controversial gold-thread nanmu tree species based on morphological and restriction site-associated DNA sequencing data. J. Syst. Evol., 57: 234-246. DOI:10.1111/jse.12433
Fang, J.Y., Guo, Q.H., Liu, G.H., 1999. Distribution patterns of Chinese beech (Fagus L.) species in relation to topography. J. Integr. Plant Biol., 41: 766-774. https://www.jipb.net/EN/Y1999/V41/I7/.
Feng, X.Y., Wang, X.H., Chiang, Y.C., et al., 2021. Species delimitation with distinct methods based on molecular data to elucidate species boundaries in the Cycas taiwaniana complex (Cycadaceae). Taxon, 70: 477-491. DOI:10.1002/tax.12457
Frankham, R., 2010. Challenges and opportunities of genetic approaches to biological conservation. Biol. Conserv., 143: 1919-1927. DOI:10.1016/j.biocon.2010.05.011
Gao, J., Liu, Z.L., Zhao, W., et al., 2020. Combined genotype and phenotype analyses reveal patterns of genomic adaptation to local environments in the subtropical oak Quercus acutissima. J. Syst. Evol., 59: 541-556. DOI:10.5061/dryad.q2bvq83fv
Garner, B.A., Hand, B.K., Amish, S.J., et al., 2016. Genomics in conservation: case studies and bridging the gap between data and application. Trends Ecol. Evol., 31: 81-83. DOI:10.1016/j.tree.2015.10.009
Garnett, S.T., Christidis, L., 2017. Taxonomy anarchy hampers conservation. Nature, 546: 25-27. DOI:10.1038/546025a
Gibson, K.J., Streich, M.K., Topping, T.S., et al., 2019. Utility of citizen science data: a case study in land-based shark fishing. PLoS One, 14: e0226782. DOI:10.1371/journal.pone.0226782
Guo, K., Werger, M.J.A., 2010. Effect of prevailing monsoons on the distribution of beeches in continental East Asia. For. Ecol. Manag., 259: 2197-2203. DOI:10.1016/j.foreco.2009.11.034
Hampe, A., Bairlein, F., 2000. Modified dispersal-related traits in disjunct populations of bird-dispersed Frangula alnus (Rhamnaceae): a result of its Quaternary distribution shifts?. Ecography, 23: 603-613. DOI:10.1111/j.1600-0587.2000.tb00179.x
Hampe, A., Petit, R.J., 2005. Conserving biodiversity under climate change: the rear edge matters. Ecol. Lett., 8: 461-467. DOI:10.1111/j.1461-0248.2005.00739.x
Hayata, B., 1911. Materials for a Flora of Formosa. J. Coll. Sci. Univ. Tokyo, 30: 286-287. DOI:10.5962/bhl.title.10783
Heywood, V.H., 2017. The future of plant conservation and the role of botanic gardens. Plant Divers., 39: 309-313. DOI:10.1016/j.pld.2017.12.002
Huang, C.C., Zhang, Y.T., Bartholomew, B., 1999. Fagaceae. In: Wu, Z.Y., Raven, P.H., Hong, D.Y. (Eds.), Flora of China, Cycadaceae through Fagaceae, 4. Science Press, Beijing, pp. 314–315. Missouri Botanical Garden Press, St. Louis.
International Union for Conservation of Nature and Natural Resources (IUCN), 2022. The IUCN Red List of Threatened Species, Version 15.1.
Jiang, L., Bao, Q., He, W., et al., 2022. Phylogeny and biogeography of Fagus (Fagaceae) based on 28 nuclear single/low-copy loci. J. Syst. Evol., 60: 759-772. DOI:10.1016/j.pld.2017.12.002
Kang, N., Tang, Z.X., 1995. Studies on the taxonomy of the genus Torreya. Bull. Bot. Res. 15, 349-362. (in Chinese with English abstract). http://bbr.nefu.edu.cn/EN/Y1995/V15/I3/349.
Kou, Y.X., Xiao, K., Lai, X.R., et al., 2017. Natural hybridization between Torreya jackii and T. grandis (Taxaceae) in southeast China. J. Syst. Evol., 55: 25-33. DOI:10.1111/jse.12217
Li, Y.J., Zhang, Y.Y., Liao, P.C., et al., 2021. Genetic, geographic, and climatic factors jointly shape leaf morphology of an alpine oak, Quercus aquifolioides Rehder & E.H. Wilson. Ann. For. Sci., 78: 64. DOI:10.1007/s13595-021-01077-w
Li, Y.X., 2016. Rare and endangred Fagus chienii reappears in forests. Green Tianfu, 9: 17.
Liang, Y., Yang, X.X., Zhang, X.Y., et al., 2022. Species delimitation and distribution of Fagus in China based on genomic sequence variation. Sci. Sin. Vitae, 52: 1292-1300. DOI:10.1360/ssv-2022-0137
Lortie, C., Hierro, J.L., 2021. A synthesis of local adaptation to climate through reciprocal common gardens. J. Ecol., 110: 1015-1021. DOI:10.1111/1365-2745.13664
Martinez Arbizu, P., 2020. PairwiseAdonis: pairwise multilevel comparison using adonis. R package version 0.4.
Meikle, R.D., 1957. What is the subspecies?. Taxon, 6: 102-105. DOI:10.2307/1217753
Nic Lughadha, E.M., Graziele Staggemeier, V., Vasconcelos, T.N.C., et al., 2019. Harnessing the potential of integrated systematics for conservation of taxonomically complex, megadiverse plant groups. Conserv. Biol., 33: 511-522. DOI:10.1111/cobi.13289
Ogilvie, M., Bouckaert, R.R., Drummond, A.J., 2017. StarBEAST2 brings faster species tree inference and accurate estimates of subsitiution rates. Mol. Biol. Evol., 34: 2101-2114. DOI:10.1093/molbev/msx126
Oksanen, J., Blanchet, F.G., Kindt, R., et al., 2015. Vegan: community ecology package. R Package Version 2.2-1.
Peters, R., 1997. Beech Forests. Geobotany. Kluwer Academic Publishers, Dordrecht, pp. 30–36.
Rawat, U.S., Agarwal, N.K., 2015. Biodiversity: concept, threats and conservation. Environ. Conserv. J., 16: 19-28. DOI:10.36953/ECJ.2015.16303
RCoreTeam, 2021. R: A Language and Environment for Statistical Computing. R Foundation for Statistical Computing, Vienna, Austria.
Rehder, A., Wilson, E.H., 1916. Fagaceae. Plantae Wilsonianae: an enumeration of the woody plants collected in western China for the Arnold arboretum of Harvard university during the years 1907, 1908, and 1910. In: Sargent, C.S. (Ed.). The University press, Cambridge, pp. 191–192. https://doi.org/10.5962/bhl.title.191. vol. 3.
Ronquist, F., Teslenko, M., van der Mark, P., et al., 2012. MrBayes 3.2: efficient Bayesian phylogenetic inference and model choice across a large model space. Syst. Biol., 61: 539-542. DOI:10.1093/sysbio/sys029
Shen, C.F., 1992. A Monograph of the Genus Fagus Tourn. Ex L. (Fagaceae). PhD Dissertation. The City Univ. of New York, New York.
Solow, A., Smith, W., Burgman, M., et al., 2011. Uncertain sightings and the extinction of the ivory-billed woodpecker. Conserv. Biol., 26: 180-184. DOI:10.1111/j.1523-1739.2011.01743.x
Stamatakis, A., 2014. RAxML version 8: a tool for phylogenetic analysis and post-analysis of large phylogenies. Bioinformatics, 30: 1312-1313. DOI:10.1093/bioinformatics/btu033
Sun, H., Deng, T., Chen, Y.S., et al., 2017. Current research and development trends in floristic geography. Biodivers. Sci., 25: 111-122. https://www.biodiversity-science.net/CN/Y2017/V25/I2/111.
Thomson, S.A., Pyle, R.L., Ahyong, S.T., et al., 2018. Taxonomy based on science is necessary for global conservation. PLoS Biology, 16: e2005075. DOI:10.1371/journal.pbio.2005075
von Seemen, O., 1897. 13 neue Arten Fagaceen aus dem Herbar des Königlichen botanischen Museums zu Berlin. Bot. Jahrbücher, 23: 56.
Ying, L.X., Zhang, T.T., Chiu, C.A., et al., 2016. The phylogeography of Fagus hayatae (Fagaceae): genetic isolation among populations. Ecol. Evol., 6: 2805-2816. DOI:10.1002/ece3.2042
Zhang, X.J., Liu, X.F., Liu, D.T., et al., 2021. Genetic diversity and structure of Rhododendron meddianum, a plant species with extremely small populations. Plant Divers., 43: 472-479. DOI:10.1016/j.pld.2021.05.005
Zhang, Y.T., Huang, C.C., 1998. Flora Reipublicae Popularis Sinicae, 22. Science Press, Beijing, pp. 3–8 (in Chinese).
Zhang, Z.Y., Wu, R., Wang, Q., et al., 2013. Comparative phylogeography of two sympatric beeches in subtropical China: species-specific geographic mosaic of lineages. Ecol. Evol., 3: 4461-4472. DOI:10.1002/ece3.829