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Community Structure and Survival of Tertiary Relict Thuja sutchuenensis (Cupressaceae) in the Subtropical Daba Mountains, Southwestern China

  • Cindy Q. Tang , (CQT); (YY)

    Affiliation Institute of Ecology and Geobotany, Yunnan University, Kunming 650091, China

  • Yongchuan Yang , (CQT); (YY)

    Affiliations Key Laboratory of Three Gorges Reservoir Region’s Eco-Environment, Ministry of Education, Chongqing University, Chongqing 400045, China, National Centre for International Research of Low-carbon and Green Buildings, Chongqing University, Chongqing 400045, China

  • Masahiko Ohsawa,

    Affiliation Institute of Ecology and Geobotany, Yunnan University, Kunming 650091, China

  • Arata Momohara,

    Affiliation Graduate School of Horticulture, Chiba University, 648 Matsudo, Chiba 271–8510, Japan

  • Si-Rong Yi,

    Affiliation Institute of Medicinal Plant Cultivation of Chongqing, Nanchuan 408435, China

  • Kevin Robertson,

    Affiliation Tall Timbers Research Station and Land Conservancy, 13093 Henry Beadel Drive, Tallahassee, Florida 32312 United States of America

  • Kun Song,

    Affiliation Department of Environmental Science, East China Normal University, No. 3663 North Zhongshan Road, Shanghai 200062, China

  • Shi-Qiang Zhang,

    Affiliation Dabashan National Nature Reserve, Chengkou 405900, China

  • Long-Yuan He

    Affiliation Institute of Ecology and Geobotany, Yunnan University, Kunming 650091, China

Community Structure and Survival of Tertiary Relict Thuja sutchuenensis (Cupressaceae) in the Subtropical Daba Mountains, Southwestern China

  • Cindy Q. Tang, 
  • Yongchuan Yang, 
  • Masahiko Ohsawa, 
  • Arata Momohara, 
  • Si-Rong Yi, 
  • Kevin Robertson, 
  • Kun Song, 
  • Shi-Qiang Zhang, 
  • Long-Yuan He


A rare coniferous Tertiary relict tree species, Thuja sutchuenensis Franch, has survived in the Daba Mountains of southwestern China. It was almost eliminated by logging during the past century. We measured size and age structures and interpreted regeneration dynamics of stands of the species in a variety of topographic contexts and community associations. Forest communities containing T. sutchuenensis were of three types: (1) the Thuja community dominated by T. sutchuenensis, growing on cliffs; (2) the Thuja-Quercus-Cyclobalanopsis community dominated by T. sutchuenensis, Quercus engleriana and Cyclobalanopsis oxyodon, along with Fagus engleriana and Carpinus fargesiana, on steep slopes; (3) the Thuja-Tsuga-Quercus community dominated by T. sutchuenensis, Tsuga chinensis, and Quercus spinosa, on crest ridges. The established seedlings/saplings were found in limestone crevices, on scarred cliff-faces, cliff-edges, fallen logs, canopy gaps and forest margins. The radial growth rate was 0.5-1.1 mm per year. Its growth forms were distorted. It had strong sprouting ability after disturbances. The T. sutchuenensis population thrives on cliffs where there is little competition from other species because of harsh conditions and rockslide disturbances. It is shade-intolerant but stress-tolerant. Its regeneration has depended on natural disturbances.


Tertiary relict flora represents some of the rarest and most threatened plant species in the world. Understanding the population structure, demographics, and ecological niches of such species is essential both for their modern-day conservation and to discover the mechanisms that have influenced their biogeography and allowed them to persist for millennia.

Refugia of Tertiary relict flora exist in eastern Asia (China, Japan and Korea), southwestern Eurasia, southeastern and western North America [1, 2, 3, 4]. These regions possess a great number of genera in common, while particular species are usually endemic to only one of the four areas [5, 3, 6, 4]. Species richness of Tertiary relict flora differs greatly among refugia, with the greatest diversity occurring in East Asia and the least in southwestern Eurasia [2, 3, 4].

Since southern China was never covered by extensive and unified ice-sheets, owing in part to its mountainous topography [7, 8], the mountains in the region have had a relatively stable long-term environment, now referred to as Pleistocene glacial refugia, harboring many Tertiary relict plants [9, 10, 11]. Today paleoendemic and monotypic taxa thrive in the Yangtze River valley, and survive in highly fragmented areas with small population sizes in specific habitats [12, 13, 14, 15].

The genus Thuja (Cupressaceae) is represented in the fossil record dating back to the late Cretaceous. Fossil records reveal a wide distribution in the Northern Hemisphere over geological time, as in the late Cretaceous in Alaska [16], in the Paleocene in Greenland [17] and Ellesmere Island, Canada [18], in the Miocene of the Sikhote Alin Mountains of Russia [19] and from the late Miocene and the Plio-Pleistocene in Japan [20, 21], and in the Plio-Pleistocene of Peary Land, North Greenland [22]. Thuja currently comprises five extant species found disjunctly in East Asia and in North America. T. sutchuenensis Franch. (Yabai or Sichuan Thuja) is endemic to the Daba Mountains at the northern fringe of the Sichuan Basin in the Yangtze River valley of China. T. koraiensis Nakai (Korean Thuja) is found in Korea and on the boundary between Korea and northeastern China (Changbaishsan). T. standishii (Gordon) Carrière (Japanese Thuja) is native to Japan. T. occidentalis L. (northern whitecedar) and T. plicata Donn ex D. Don (western redcedar) grow in eastern and western North America, respectively [23]. Thuja disappeared from Europe and high latitudes during the ice ages of the Pleistocene [24]. The ancestral area of Thuja had been presumed to be eastern Asia [25]. Both the North Atlantic land bridge and the Bering land bridge have been considered as possible routes for the migration of ancestral populations to North America [25]. A reverse process has been proposed by Peng and Wang [26], who used multiple gene sequences to infer that Thuja could have originated in the high-latitude areas of North America in the Paleocene or earlier, with subsequent expansion into eastern Asia over the Bering land bridge. In that case, the two eastern Asia species T. standishii and T. sutchuenensis would have a sister relationship, and could have differentiated in the Oligocene or early Miocene.

The first specimens of T. sutchuenensis were collected from a single location at 1400 m asl in Chengkou County (formerly Sichuan Province, now part of Chongqing Municipality) by the French missionary P. G. Farges from 1892 to 1900 [27] and was named T. sutchuenensis Franch. in 1899 [28]. Botanical collecting trips to Chengkou by Chinese botanists later in the twentieth century failed to find T. sutchuenensis, thus it was considered extinct in the wild [29] and known only by Farges' specimens in various European herbaria [27]. It was the only conifer listed as extinct in the wild on the global red list of conifers [30]. In October 1999 it was rediscovered in Chengkou by a regional team of Chinese botanists near the location where P. G. Farges made his last collections almost 100 years earlier [31, 27]. It had been subject to extremely intensive logging, as local people used the soft, easily-worked wood for home construction, shingles, and other purposes requiring resistance to rot. Remaining specimens are limited to those left in inaccessible limestone formations, mostly on crest ridges or steep slopes at 800–2100 m elevation, and their seedlings are scarce [31, 32, 27]. It is now ranked as an endangered species on the IUCN red list [33]. However, no ecological research has been conducted on the species in its various topographic surroundings and community associations and its mechanisms of persistence have not been identified.

The objective of this paper is to present field data to answer fundamental questions about the species' ecology: (1) What are the spatial distribution patterns and population structure of T. sutchuenensis? (2) How is its population maintained within the forest community? (3) How do its regeneration dynamics compare with other species of Thuja communities? Answers to these questions should contribute to a better understanding of the current status of this Tertiary relict plant and provide insight into its demographic mechanisms and prospects for survival.

Materials and Methods

Study area

The study was conducted in the Dabashan Nature Reserve of Chengkou County and the Xuebaoshan Nature Reserve of Kaixian County in the Daba Mountains on the borders of Chongqing Municipality and Sichuan, Hubei and Shaanxi provinces (31°35′52′′–31°41′50′′N, 108° 34′52′′–′ 8°50′34′′E) (Fig 1). During the past century, logging and agricultural development greatly altered the composition and structure of the region's vegetation and landscape. A wide variety of forest types once intermingled at varying spatial scales. Today, the most common vegetation land cover types are even-aged plantations (e.g. Cunninghamia lanceolata), early successional plant communities (dominated by Populus adenopoda or Betula utilis), and particularly coppice forests used for firewood and shrublands regenerated after the abandonment of agricultural fields, comprise the most common vegetation. Embedded within these secondary communities are some remnant forests on the limestone cliffs (inclination: 75°‒90°), steep slopes (inclination: 30°‒75°), and crest ridges (rounded tops of cliffs and slopes), some including stands of T. sutchuenensis. The steep slopes and crest ridges are partially covered by soils composed of moist and fertile mountain yellow-brown earth. The soil layer is relatively thin and rich in organic matter (2.3–3% of total dry weight), with a thick humus layer (c. 20 cm) and pH of 6.2–7 [27]. The limestone landscape with steep precipices and cliffs is one of the most pronounced topographic features of the Sichuan Basin. The cliffs are especially landslide-prone, being composed of limestone, clay shale, and volcanoclastic and siliceous rock. The rock crevices on the cliffs result from tectonic instability and landslide-prone formations of various rock strata. The main triggering factors of landslides are active faults and rainstorms, especially during May to October [34, 35]. On average, in the range of our study sites there are four landslides per year of various intensities, including cliff rockslides and debris flows [34]. Slope hazard (landslide and collapse) are common in the study area. This is one of the most geologically active regions in China. According to our field observations, the intensity of rockslides or landslides is highest on cliffs, medium on steep slopes, and medium-low on crest ridges. A subtropical monsoon (humid and warm) climate prevails, with a mean annual precipitation of 1114 mm, of which 78% occurs in May–October. The mean relative humidity is c. 73% year-round. Mean annual temperature is 14°C, with 2.7°C in January (coldest month), 24.2°C in July (hottest month).

Fig 1. Study sites on the Daba Mountains, southwestern China.

The study plots represent the natural distribution range of T. sutchuenensis.

Data collection and analysis

Given that T. sutchuenensis is an endangered species, we obtained permission from the Dabashan and Xuebaoshan National Nature Reserves to conduct the botanical and vegetational survey. In August 2014, we sought out all populations of T. sutchuenensis in areas where they were known by botanists and local people to exist. We interviewed local villagers to obtain the information on their use of this species. Based locations of populations, we established 25 plots (sizes ranging from 10 × 10 m to 10 × 50 m according to size of the community patch containing Thuja) representing the natural distribution range of T. sutchuenensis in Chengkou and Kaixian counties (Fig 1). Plots were designated as occurring on cliffs, steep slopes, or crest ridges, as described above. We identified all the vascular plant species and recorded diameter at breast height (DBH at 1.3 m tall) and height for all woody plants in each plot. For trees in inaccessible locations such as steep cliff faces, DBH and height were estimated. Young individuals of woody plants 15 cm–60 cm high were counted as established seedlings, and those from 60 cm–1.3 m were counted as saplings. Increment core samples of T. sutchuenensis were taken at DBH from 31 main stems among the 25 plots in order to estimate size-age relationships. Tree ages were determined using the WinDendro tree-ring image analysis software (version 2003a; Regent Instruments, Sainte-Foy, Quebec, Canada). Analysis of correlation between age and DBH was conducted using DeltaGraph Pro 3.5 software (DeltaPoint, Inc., USA). Plant communities were classified using a floristic similarity dendrogram with Euclidean and Ward’s clustering, using the relative basal area of woody species as the input value (PCORD software [36]). Communities were considered distinct at the 50% floristic similarity threshold. Dominance was determined using a dominance analysis according to relative basal area of each species [37]. The communities were named according to the genera of the first three dominant species. We considered a species to be a major one if it was dominant in at least one community. The Gleason richness index (dGI = S/LnA, S: number of species, A: plot area) [38] was employed to compare species richness among various plots. Differences in species richness among different plant communities were tested using the Tukey–Kramer test for unequal sample sizes. Statistical analyses were performed using STATISTICA software package (StatSoft, USA). Size class and age class distributions of T. sutchuenensis and its associated major species in various topographic habitats were used to interpret regeneration dynamics.


Forest community structure

The dendrogram analysis resulted in classification of the 25 plots into three plant communities corresponding to the three topographic positions (Fig 2A): 1) the Thuja community, dominated by coniferous T. sutchuenensis on cliffs; 2) the Thuja-Quercus-Cyclobalanopsis community, dominated by T. sutchuenensis, evergreen sclerophyllous broad-leaved Quercus engleriana and subtropical evergreen broad-leaved Cyclobalanopsis oxyodon along with some deciduous broad-leaved trees such as Fagus engleriana and Carpinus fargesiana on steep slopes; 3) the Thuja-Tsuga-Quercus community, dominated by T. sutchuenensis and another conifer Tsuga chinensis, and evergreen sclerophyllous broad-leaved Quercus spinosa on the crest ridges. The relative basal area (RBA) of T. sutchuenensis decreased with decreasing intensity of natural disturbance (rockslide), i.e. from the cliffs to the steep slopes to the crest ridges (Fig 2B). T. sutchuenensis accounted for 78% of total basal area on the cliffs, 42% on the steep slopes, and 36% on the crest ridges, while Tsuga accounted for only 0.1% on the cliffs, 1.4% on the steep slopes, and 31% on the crest ridges. A few other minor conifers, including Torreya fargesii, Taxus wallichiana var. chinensis, Pinus tabuliformis var. henryi, and Cephalotaxus fortunei, grew in all three habitats. Evergreen sclerophyllous broad-leaved Quercus engleriana are absent from the crest ridges. Deciduous Fagus engleriana existed only on the steep slopes. In total, there were 118 woody species (70 on cliffs, 94 on steep slopes, and 18 on crest ridges) and 37 herbaceous species in the study sites. The major woody species (RBA ≥ 0.5%) composition of each community type is shown in Table 1. The community on the steep slopes had significantly higher Gleason richness (3.73 ± 1.4) than those on the crest ridges (2.27 ± 0.18) and the cliffs (2.78 ± 1.4). A composite representation of the distribution pattern of T. sutchuenensis and associated major species is shown in a schematic diagram (Fig 3). The height of T. sutchuenensis reached 16 m, but few exceeded 10 m in all three habitats (Fig 4). The cliffs support the greatest number of Thuja seedlings/saplings (15 cm < height < 1.3 m) in the study area (Fig 4).

Fig 2. Floristic similarity dendrogram and forest characteristics (A).

Relative basal area (%) distribution of species (height ≥ 1.3 m) (B). The evergreen broad-leaved species include the subtropical evergreen broad-leaved species and the evergreen sclerophyllous species of Quercus.

Fig 3. Schematic diagram of the composite representation of distribution patterns of T. sutchuenensis.

The Thuja-Tsuga-Quercus community on the crest ridge (a) and (b). The red circled area is shown in (a)-Thuja sutchuenensis. A T. sutchuenensis on the cliff (c). The Thuja-Quercus-Cyclobalanopsis community on the steep slope (d) and (e). QUSP: Quercus spinosa; QUEN: Quercus engleriana.

Fig 4. The height-class frequency distribution in different topographic habitats.

Bars in the height-class of 0–1.3 m indicate the seedlings/samplings of T. sutchuenensis.

Table 1. Floristic composition for woody species (relative basal area [RBA] ≥ 0.5% in at least one plant community).

Lists of woody species (RBA > 0.01%) occurring in each community type, including their DBH- and height-class frequency distributions, are shown in S1 Table.

Regeneration dynamics

Size class distributions of the five major species (Fig 5) can be categorized by inverse-J, sporadic, or unimodal types of DBH-size frequency distribution. On the cliffs (Thuja community), the DBH of T. sutchuenensis ranged from 0.5–40 cm and showed the inverse-J type distribution, suggesting that regeneration is active with continual recruitment of seedlings/saplings. Only a few individuals of Quercus engleriana, Cyclobalanopsis oxyodon, Quercus spinosa and Tsuga chinensis were present, almost all in small size classes. On the steep slopes (Thuja-Quercus-Cyclobalanopsis community), Thuja reached 35 cm DBH and showed the unimodal distribution type, suggesting that recent conditions have not been conducive to regeneration. Quercus engleriana, Cyclobalanopsis oxyodon and Quercus spinosa displayed the sporadic distribution type, suggesting periodic regeneration, and Tsuga had very few individuals. On the crest ridges (Thuja-Tsuga-Quercus community), Thuja ranged from 3–25 cm DBH and showed a distribution intermediate between the cliff and slope populations, with Quercus spinosa fitting the sporadic type, while Tsuga and Cyclobalanopsis were of the unimodal type.

Fig 5. DBH-class frequency distribution for five major species in various topographic habitats.

Empty bars indicate the seedlings/saplings.

Population age structure

Age and diameter at breast height at 1.3 m (DBH) for T. sutchuenensis were fairly strongly correlated (y = 7.1x + 9.03, R2 = 0.84, n = 31). The correlation was statistically significant (p < 0.001). The growth rate of T. sutchuenensis was very low. The average radial growth rate per year was 1.1 mm below age 20 years, 0.75 mm from 20–40 years old, 0.5 mm from 40‒90 years old, and it varied between 0.8‒0.5 mm above 90 years. The age structure of T. sutchuenensis in each topographic habitat is shown in Fig 6. On the cliffs, the age structure suggests continual recruitment with a pattern similar to its DBH-size frequency distribution. On the cliff, nearly 26% of individuals were under 20 years old, indicating better regeneration than in the other two types of topographic habitats, on the steep slopes (7%) or on the crest ridges (19%). The oldest tree (c. 293 years) was located on a cliff. Many older trees with greater DBHs were logged during the past century, based on our observations of logged stumps and our interviews with local villagers.

Fig 6. The age structure of the T. sutchuenensis population in different topographical habitats.

Data include individuals ≥ 1.3 m in height and established seedlings/saplings (15 cm< H < 1.3 m).

Regeneration modes

Substantial numbers of seedlings/saplings of T. sutchuenensis were growing on the cliffs (Table 2, see also Figs 4, 5 and 6), but regeneration was generally poor as a whole for all the populations in the three topographic habitats. Most seedlings/saplings were found in rock crevices (Fig 7A and 7B), cliff-faces scarred from rockslides, and cliff-edges where the micro-sites were dry. Some seedlings/saplings were found on fallen logs, canopy gaps, and forest margins by slopes and crest ridges. The stems of T. sutchuenensis showed evidence of variable disturbances of intensity. Some stems showed human disturbance in the form of cutting, and several adult trees had limbs cut off. However, we saw no evidence of fire disturbance. The growth forms varied; most of the stems were twisted (Fig 7C and 7D). Roots were well developed and widely spread on the outcrops, sometimes reaching over 10 m (Fig 7E). After sustaining damage from natural disturbances (i.e. rockslides or landslides) or cutting, T. sutchuenensis was able to resprout. The ratio of resprouts to main stems was roughly 15: 1. For example, many individuals on the cliffs had 2–18 resprouts after they were damaged by rockfall, and a main stem of Thuja with 140 cm DBH was cut in the 1970s, and now there are 20 resprouts ranging 2–35 cm DBH (Fig 7F).

Fig 7. A sapling of T. sutchuenensis in a crevice on the cliff (a).

A seedling of T. sutchuenensis in a crevice on the cliff (b). The deformed structure of T. sutchuenensis on the cliffs (c) and (d). A root of T. sutchuenensis over rocks (e). T. sutchuenensis resprouting after cutting (f).

Table 2. Number of seedlings/saplings (15 cm < height < 1.3 m) of Thuja sutchuenensis in various micro-sites.


Growth rates and growth forms

Our results show T. sutchuenensis to have a slow radial growth rate (0.5–1.1 mm/year) in the topographic context studied, as compared with the other Tertiary relict Metasequoia glyptostroboides in its natural habitats in Lichuan, south-central China (0.34–7.81 mm/year, [13]) of Cupressaceae. Individuals of T. sutchuenensis in existing populations are generally small in stature, but they can grow to be very old. While the oldest tree found (293 years old) was 40 cm DBH, interviews with local villagers and our observations of logged stumps reveal that some stems logged in the 20th century were up to 140 cm DBH, suggesting that they were over 1000 years old. The distinctive traits of stunted and morphologically deformed crowns, slow growth, and exceptional longevity parallel those of T. occidentalis on exposed cliff edges and faces of the Niagara Escarpment of southern Ontario [39, 40]. On the cliffs of the Niagara Escarpment, the high probability of survival is thought to be linked to slow use of limited resources compensating for slow growth [40]. Cliff-dwelling trees of T. occidentalis almost without exception have lower growth rates than trees growing in more favorable environments [40]. Biotic interactions on cliffs are low because individuals are widely spaced, competition for light is low or nonexistent, and the root systems of neighboring plants are often completely separated by rock formations [41]. Given the potentially extreme longevity of this species under perennially harsh conditions, it seems that survival is dependent on establishment through the accident of finding safe sites with adequate rooting volume, followed by the lack of any fatal disturbance in that location [42].

Spatial distribution and regeneration

The altitudinal distribution range of T. sutchuenensis falls within the subtropical evergreen broad-leaved forest zone and mixed evergreen, deciduous broad-leaved and coniferous forest zone (altitudinal range (800) 1100–2100 m) (Table 1). In contrast, the other four species of Thuja grow in the cool temperate and cold temperate forest zones. The distribution, ecological characteristics and major associated species of T. sutchuenensis as compared with the other four species of Thuja are summarized in Table 3. The spatial distribution patterns of Thuja sutchuenensis found in this study result from the interactions among natural disturbances, life history traits and stress-tolerance. Marginal habitats formed under conditions of disturbance support distinctive flora and rare species because of differing competitive abilities and tolerance limits among species [57]. The cliffs with high intensity rockslides are solely dominated by T. sutchuenensis. In contrast, the slopes and crest ridges are dominated by three species capable of forming dense canopies. The size-structures of T. sutchuenensis and its major associated species, including Quercus engleriana, Cyclobalanopsis oxyodon, Tsuga chinensis and Quercus spinosa in the three topographic communities, suggest trade-offs in environmental requirements among those species (Fig 5). Species with narrow regeneration niches often require special sites [58]. Seedlings/saplings of T. sutchuenensis growing in crevices, on scarred cliff-faces and cliff-edges, on fallen logs, in canopy gaps and forest margins by steep slopes and crest ridges, show that the species' regeneration depends on disturbances which create or maintain these exposed, low-competition conditions (Table 2). Its seeds are minute (1.13g per 1,000 seeds) [59] and can take advantage of wind-dispersal to fall into rock crevices on the cliffs, unlike the big acorns of Quercus and Cyclobalanopsis. Tsuga chinensis is shade-tolerant but susceptible to drought [60], and so unable to become established on the exposed cliffs. Resprouting can also be a strategy in maintaining population stability and continuity, especially in habitats where disturbances that do not kill the whole plant frequently occur. T. sutchuenensis resprouts vigorously after disturbances that damage stems and branches, suggesting adaptation to such disturbances. Quercus engleriana, Quercus spinosa and Cyclobalanopsis oxyodon also showed resprouting abilities (the mean ratio of resprouts to main stems is 9:1) after disturbances on the cliffs, but we did not find many resprouts for these four species on the slopes and crest ridges. This indicates less frequent natural disturbance on the slopes and crest ridges. T. sutchuenensis has relatively strong recruitment on the cliffs compared to the slopes and the crest ridges. This also suggests its strong tolerance of xeric sites. The species appears to be the stress-tolerant type as classified by Grime [61].

Table 3. General characteristics of Thuja sutchuenensis as compared with the other four species of Thuja.

The life history characteristics of T. sutchuenensis are similar to those of living fossil plants of the Yangtze River valley that are found in unstable and harsh habitats where natural disturbances occur frequently, and there is little competition from other species,as exemplified by Ginkgo biloba in the limestone habitat of the Dalou Mountains [14], Metasequoia glyptostroboides in wet lower mountain slopes and stream valleys in the border region of Hubei and Hunan provinces and Chongqing Municipality [13], Davidia involucrata on scree slopes or valley slopes and in valley bottoms, where the soil often contains much gravel, on Mt. Emei, Sichuan [12], and Cathaya argyrophylla on the steep topography of Mt. Jinfo [62].

Implications for Conservation

Efforts to conserve T. sutchuenensis will focus on the individuals in their natural habitats. Cliffs, forest margins, canopy gaps and roadsides in the study sites provide micro-habitats favorable to the regeneration of this light-demanding species. Saplings on roadsides, being especially vulnerable, should be saved where practicable. A genetic study showed that T. sutchuenensis populations have a relatively high level of within-population genetic diversity despite the small number of individuals [63]. Conservation measures should also be directly towards large numbers of seedlings in situ, which will require management and cooperation from local communities. In situ efforts to conserve remaining habitats need to be combined with ex situ research on seed propagation, with a view to establishing a new generation of plants both in cultivation and in the wild [63]. According to Jin [64], T. sutchuenensis can establish roots from cutting shoots, indicating that this species is able to be propagated by clonal reproduction. Cuttage breeding may provide the most effective artificial propagation for the species.

Demand for use of this species far outweighs current conservation efforts to replenish the supply. For a long time, T. sutchuenensis has been a preferred wood for the construction of houses, fences, and pigpens by local people because of its resistance to rotting. It is used in arts or crafts such as root carving and bonsai because of its flexibility. Better management and effective conservation are needed to ensure the recruitment and continuing survival of this rare and endangered Tertiary relict species in its natural habitats.

Supporting Information

S1 Table. Woody species (RBA > 0.01%) occurring in each community type, and their DBH- and height-class frequency distributions.


Author Contributions

Analyzed the data: CQT. Wrote the paper: CQT. Conceived and designed this study: CQT YY. Arranged and conducted field work: YY. Contributed discussion to improve the manuscript: YY AM KR. Conducted field work: CQT MO AM. Contributed ideas and discussion to improve the manuscript: MO. Collected literature on Thuja fossil records: AM. Identified plant species in the field: SRY. Helped literature collection: KR. Helped in editing the manuscript: KR. Conducted tree ring analysis for Thuja specimens: KS. Assisted in field work: SZ. Created the maps of the study sites: LYH.


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