中国植物园保护稀有濒危植物的现状和若干对策

针对中国植物园稀有濒危植物的保护现状和存在问题进行分析，重点讨论了稀有濒危植物在植物园迁地保护的有效性问题，涉及稀有濒危植物在植物园迁地保护的生长和适应问题、稀有濒危植物在植物园重复栽培问题、稀有濒危植物在植物园迁地保护的有效种群大小问题、科学记录系统和监测中心的建立问题。就稀有濒危植物在植物园迁地保护的可持续发展提出了若干对策与建议：以植物园为基础形成保护的网络系统；加强稀有濒危植物迁地保护规划并突出重点；加强科学记录系统和监测中心的建立；多方筹措资金，加强支持强度；加强人才培训与学术交流。     

珍稀植物濒危机制及保育策略中的营养条件

首先简要论述了珍稀植物濒危的原因、濒危机制的各种理论和研究方法，包括就地保护和迁地保护两个方面的保育策略的制定与实践。然后着重从营养条件的角度对这些理论和现状进行了分析。认为濒危物种在其历史演化过程中存在的脆弱环节以及活植物迁地保护的评价标准均与营养条件密切相关，营养条件可能是某些物种濒危机制中的一个重要组成部分；营养条件方面的研究可以为保护区设立的大小提出指导性意见；珍稀植物迁地保护过程中应密切关注营养条件的影响；营养条件在一定程度上决定了对某些物种保育策略的制定；将分子生物学与植物营养学的研究方法相结合，将能成为珍稀植物濒危机制及保育策略研究中的一种有效手段。     

广西壮族自治区自然保护区建设与珍稀植物保护

广西地区自然分布有国家稀有濒危植物１２１种，是我国濒危植物资源最丰富的省份之一。本文在评价广西的自然保护区建设现状、保护区类型和结构布局以及对濒危植物资源保护情况的基础上，提出了广西的自然保护区建设和濒危植物资源有效保护的建议和对策。     

中国特有植物猪血木的濒危原因及保护对策

猪血木(Euryodendron excelsum H.T.Chang)为中国特有的山茶科单型属猪血木属的珍稀濒危植物,现仅分布于广东省阳春县八甲镇地区,且仅残存一个居群,居群内个体数量仅100余株,该物种已被列为国家二级保护植物。物种濒危原因分析是生物多样性保护的关键环节,文章从猪血木的地理分布、生活史特性、种群分布现状及生态环境因素影响等方面分析了该物种的濒危现状,猪血木种群地理分布的局限性限制了其空间拓展;种子萌发和幼苗生长对生境要求特殊和种群现状不利于其更新和发展,人为干扰对猪血木影响严重。其濒危的主要原因是人为因素引起的生境破碎化和过度砍伐所导致的个体数量下降,文章认为现存种群和生境的保护是濒危物种保护的最有效手段,针对猪血木的濒危现状和原因,提出了就地保护,促进自然种群的繁衍更新,建立猪血木繁育基地进行迁地保护和回归引种的保护策略,以期为猪血木的保护和种群恢复提供科学的理论指导,也为中国珍稀濒危物种和生物多样性的保护提供基础资料。     

苏浙皖地区珍稀濒危植物的研究

本文对苏浙皖地区分布的64种国家第一批重点保护植物种的种群现存数量、生态地理分布、稀有濒危原因、保护价值及保护措施等进行了调查和研究,为有效地抢救和保护本区的珍稀濒危植物提供了科学依据。     

孑遗植物四合木(Tetraena mongolica)迁地保护中的光合作用日变化特征与生理生态适应性

为了进一步廓清迁地保护条件下孑遗植物四合木(Tetraena mongolica)的光合生理生态适应性,在分析了瞬时光合效率的基础上,应用LI-6400光合作用测定系统测定了迁地保护试验区的四合木以及原生境伴生种白刺(Nitraria tangutorum)的光合作用日变化,并测定了其生长量。结果表明:四合木实生苗的生长南北冠幅大小依次为乌海四合木核心区实生苗(26.48cm×27.26 cm)鄂尔多斯实生苗(21.27 cm×21.75 cm)阿拉善实生苗(19.25 cm×18.27 cm)。在原生境地乌海四合木核心区种植的实生苗与阿拉善实生苗之间的生长量存在显著差异(P≤0.01),与鄂尔多斯实生苗之间的生长量存在显著差异(P≤0.05)。迁地保护条件下四合木生实生苗植株叶片光合速率Pn日变化均呈"双峰"曲线。不同试验区四合木光合作用日变化(Pn)、蒸腾速率(Tr)、气孔导度(Gs)和胞间CO2浓度(Ci)均表现出明显的分异。迁地保护四合木条件下原生境地栽培的四合木实生苗的光合速率鄂尔多斯栽培的四合木实生苗的光合速率阿拉善栽培的四合木实生苗。鉴此可以作进一步推论,孑遗濒危植物四合木从原生境地西鄂尔多斯核心区(乌海)东移进行迁地保护具有更高的生理生态适应性和生境适宜性。但完成"从种子到种子"进而实现"保存性和代表性",最终实现四合木迁地保护的"保持性和防止性",保持其遗传多样性和遗传稳定性,最终成功实现四合木的迁地保护仍有待作进一步探索和深入研究。     

广西特有植物瑶山苣苔的濒危原因及保护对策

瑶山苣苔(Dayaoshania cotinifolia W.T.Wang)是苦苣苔科多年生草本植物,为国家Ⅰ级重点保护野生植物.在2004-2006年对瑶山苣苔资源现状、生物学和生态学特性调查的基础上,探讨了瑶山苣苔的濒危原因及解濒措施.结果表明,人为原因是导致瑶山苣苔濒危的最主要原因;其次是昆虫对瑶山苣果实的捕食显著减少了种子数量;第三,瑶山苣苔同有的生物学特性限制其种群数量增加.为更好的保护瑶山苣苔,作者建议采用就地保护策略,即建立金秀老山自然保护区独木桥和青年工区两个瑶山苣苔保护点,有效地保护该种群及其分布生境;同时加强瑶山苣苔的科学研究,实施迁地保护.     

南岳珍稀濒危植物的调查研究

在南岳野生植物中,珍稀濒危植物主要是指国家级保护植物,共有13种,其中一级2种,二级11种,它们是金钱松Pseudolarix amabilis (Nelson) Rehd.,篦子三尖杉Cephalotaxus oliveri Mast.,南方红豆杉Taxus chinensis (Pilger) Rehd.var.mairei (Lemeé et Lévl.) Cheng et L.K.Fu,榉树Zelkova Schneideriana Hand.-Mazz.,樟树Cinnamomum camphora (L.) Presl,闽楠Phoebe bournei (Hemsl.) Yang,伯乐树Bretschneidera sinensis Hemsl,绒毛皂荚Gleditsia.japonica Miq.var. velutina L.C.Li,野大豆Glycine soja Sieb. et Zucc.,花榈木Ormosia henryi Prain,毛红椿Toona sinensis (A.Juss.) Roem.var.pubescens (Franch.) Hand.-Mazz.,喜树Camptotheca acuminata Decne.,以及香果树等,本文主要介绍他们的分类位置、形态特征和地理分布状况,分析了它们的区系特征,提出应该尽快建立南岳国家级野生保护植物的核心或者优先保护地段、建立珍稀濒危植物的地理信息系统、研究其生物学和生态学特性以及采取就地或迁地保护措施来保存等对策.     

孑遗植物四合木(Tetraenamongolica)迁地保护中的光合作用日变化特征与生理生态适应性

为了进一步廓清迁地保护条件下孑遗植物四合木（Tetraena mongolica）的光合生理生态适应性,在分析了瞬时光合效率的基础上,应用LI-6400光合作用测定系统测定了迁地保护试验区的四合木以及原生境伴生种白刺（Nitraria tangutorum）的光合作用日变化,并测定了其生长量。结果表明：四合木实生苗的生长南北冠幅大小依次为乌海四合木核心区实生苗（26.48 cm×27.26 cm）>鄂尔多斯实生苗（21.27 cm×21.75 cm）>阿拉善实生苗（19.25 cm×18.27 cm）。在原生境地乌海四合木核心区种植的实生苗与阿拉善实生苗之间的生长量存在显著差异（P≤0.01）,与鄂尔多斯实生苗之间的生长量存在显著差异（P≤0.05）。迁地保护条件下四合木生实生苗植株叶片光合速率Pn日变化均呈“双峰”曲线。不同试验区四合木光合作用日变化（Pn）、蒸腾速率（Tr）、气孔导度（Gs）和胞间 CO2浓度（Ci）均表现出明显的分异。迁地保护四合木条件下原生境地栽培的四合木实生苗的光合速率>鄂尔多斯栽培的四合木实生苗的光合速率>阿拉善栽培的四合木实生苗。鉴此可以作进一步推论,孑遗濒危植物四合木从原生境地西鄂尔多斯核心区（乌海）东移进行迁地保护具有更高的生理生态适应性和生境适宜性。但完成“从种子到种子”进而实现“保存性和代表性”,最终实现四合木迁地保护的“保持性和防止性”,保持其遗传多样性和遗传稳定性,最终成功实现四合木的迁地保护仍有待作进一步探索和深入研究。     

珍稀濒危植物评价分级专家系统研究

开列珍稀濒危植物的清单并划分其保护序列，是生物多样性保护的一项最基本的工作。本文通过对珍稀濒危植物评价分级指标的研究，以评价指标体系为基础，并引入专家系统方法，建立了珍稀濒危植物评价分级专家系统。该系统模拟人类专家的思维过程，将有助于把珍稀濒危植物优先保护级别的划分，由定性划分提高到定量定性相结合的水平。     

Resolving whether botanic gardens are on the road to conservation or a pathway for plant invasions

A global conservation goal is to understand the pathways through which invasive species are introduced into new regions. Botanic gardens are a pathway for the introduction of invasive non‐native plants, but a quantitative assessment of the risks they pose has not been performed. I analyzed data on the living collections of over 3000 botanic gardens worldwide to quantify the temporal trend in the representation of non‐native species; the relative composition of threatened, ornamental, or invasive non‐native plant species; and the frequency with which botanic gardens implement procedures to address invasive species. While almost all of the world's worst invasive non‐native plants occurred in one or more living collections (99%), less than one‐quarter of red‐listed threatened species were cultivated (23%). Even when cultivated, individual threatened species occurred in few living collections (7.3), while non‐native species were on average grown in 6 times as many botanic gardens (44.3). As a result, a botanic garden could, on average, cultivate four times as many invasive non‐native species (20) as red‐listed threatened species (5). Although the risk posed by a single living collection is small, the probability of invasion increases with the number of botanic gardens within a region. Thus, while both the size of living collections and the proportion of non‐native species cultivated have declined during the 20th century, this reduction in risk is offset by the 10‐fold increase in the number of botanic gardens established worldwide. Unfortunately, botanic gardens rarely implement regional codes of conduct to prevent plant invasions, few have an invasive species policy, and there is limited monitoring of garden escapes. This lack of preparedness is of particular concern given the rapid increase in living collections worldwide since 1950, particularly in South America and Asia, and highlights past patterns of introduction will be a poor guide to determining future invasion risks.     

The Role of Botanic Gardens in the Science and Practice of Ecological Restoration

Abstract: Many of the skills and resources associated with botanic gardens and arboreta, including plant taxonomy, horticulture, and seed bank management, are fundamental to ecological restoration efforts, yet few of the world's botanic gardens are involved in the science or practice of restoration. Thus, we examined the potential role of botanic gardens in these emerging fields. We believe a reorientation of certain existing institutional strengths, such as plant‐based research and knowledge transfer, would enable many more botanic gardens worldwide to provide effective science‐based support to restoration efforts. We recommend botanic gardens widen research to include ecosystems as well as species, increase involvement in practical restoration projects and training practitioners, and serve as information hubs for data archiving and exchange.     

Ex situ collections and their potential for the restoration of extinct plants

The alarming current and predicted species extinction rates have galvanized conservationists in their efforts to avoid future biodiversity losses, but for species extinct in the wild, few options exist. We posed the questions, can these species be restored, and, if so, what role can ex situ plant collections (i.e., botanic gardens, germplasm banks, herbaria) play in the recovery of plant genetic diversity? We reviewed the relevant literature to assess the feasibility of recovering lost plant genetic diversity with using ex situ material and the probability of survival of subsequent translocations. Thirteen attempts to recover species extinct in the wild were found, most of which used material preserved in botanic gardens (12) and seed banks (2). One case of a locally extirpated population was recovered from herbarium material. Eight (60%) of these cases were successful or partially successful translocations of the focal species or population; the other 5 failed or it was too early to determine the outcome. Limiting factors of the use of ex situ source material for the restoration of plant genetic diversity in the wild include the scarcity of source material, low viability and reduced longevity of the material, low genetic variation, lack of evolution (especially for material stored in germplasm banks and herbaria), and socioeconomic factors. However, modern collecting practices present opportunities for plant conservation, such as improved collecting protocols and improved cultivation and storage conditions. Our findings suggest that all types of ex situ collections may contribute effectively to plant species conservation if their use is informed by a thorough understanding of the aforementioned problems. We conclude that the recovery of plant species currently classified as extinct in the wild is not 100% successful, and the possibility of successful reintroduction should not be used to justify insufficient in situ conservation.     

Conservation of the Toromiro Tree: Case Study in the Management of a Plant Extinct in the Wild

Abstract: We reviewed the history and conservation of Sophora toromiro , a species that has been extinct in the wild since 1960 but has survived as scattered individuals in botanic gardens and private collections. The short-term conservation of S. toromiro is dependent on the management of surviving ex situ stocks. This is being achieved through international collaboration by a working group established to coordinate the conservation management of the species. Molecular evidence indicates that the species retains greater genetic variability than expected. The greatest amount of genetic variability was located in specimens outside botanic garden collections. No unmodified natural habitat survives on Rapa Nui ( Easter Island); so opportunities to establish a viable wild population are limited. Evidence from past reintroductions indicates that the best short-term opportunity for the species is through conventional horticultural management in botanic gardens and traditional farm plots on Rapa Nui. Some extinct-in-the-wild taxa (sensu World Conservation Union 1994), such as the Toromiro, retain genetic variability, and appropriate reintroduction sites exist. These taxa represent valid priorities for conservation management.     

Urban Plants as Genetic Reservoirs or Threats to the Integrity of Bushland Plant Populations

Abstract:  Remnant plants in urban fringes and native plants in gardens have the potential to contribute to the conservation of threatened plants by increasing genetic diversity, effective size of populations, and levels of genetic connectedness. But they also pose a threat through the disruption of locally adapted gene pools. At Hyams Beach, New South Wales, Australia, four bushland stands of the rare shrub, Grevillea macleayana McGillivray, surround an urban area containing remnant and cultivated specimens of this species. Numbers of inflorescences per plant, fruits per plant, and visits by pollinators were similar for plants in urban gardens and bushland. Urban plants represented a substantial but complex genetic resource, displaying more genetic diversity than bushland plants judged by H_e , numbers of alleles per locus, and number of private alleles. Of 27 private alleles in urban plants, 17 occurred in a set of 19 exotic plants. Excluding the exotic plants, all five stands displayed a moderate differentiation ( F_ST = 0.14 ± 0.02), although the urban remnants clustered with two of the bushland stands. These patterns may be explained by high levels of selfing and inbreeding in this species and by long-distance dispersal (several seeds in the urban stand were fathered by plants in other stands). Genetic leakage (gene flow) from exotic plants to 321 seeds on surrounding remnant or bushland plants has not occurred. Our results demonstrate the conservation value of this group of urban plants, which are viable, productive, genetically diverse, and interconnected with bushland plants. Gene flow has apparently not yet led to genetic contamination of bushland populations, but high levels of inbreeding would make this a rare event and difficult to detect. Remnant plants in urban gardens could successfully contribute to recovery plans for endangered and vulnerable species.     

Longitudinal monitoring of neutral and adaptive genomic diversity in a reintroduction

Restoration programs in the form of ex-situ breeding combined with reintroductions are becoming critical to counteract demographic declines and species losses. Such programs are increasingly using genetic management to improve conservation outcomes. However, the lack of long-term monitoring of genetic indicators following reintroduction prevents assessments of the trajectory and persistence of reintroduced populations. We carried out an extensive monitoring program in the wild for a threatened small-bodied fish (southern pygmy perch, Nannoperca australis) to assess the long-term genomic effects of its captive breeding and reintroduction. The species was rescued prior to its extirpation from the terminal lakes of Australia's Murray-Darling Basin, and then used for genetically informed captive breeding and reintroductions. Subsequent annual or biannual monitoring of abundance, fitness, and occupancy over a period of 11 years, combined with postreintroduction genetic sampling, revealed survival and recruitment of reintroduced fish. Genomic analyses based on data from the original wild rescued, captive born, and reintroduced cohorts revealed low inbreeding and strong maintenance of neutral and candidate adaptive genomic diversity across multiple generations. An increasing trend in the effective population size of the reintroduced population was consistent with field monitoring data in demonstrating successful re-establishment of the species. This provides a rare empirical example that the adaptive potential of a locally extinct population can be maintained during genetically informed ex-situ conservation breeding and reintroduction into the wild. Strategies to improve biodiversity restoration via ex-situ conservation should include genetic-based captive breeding and longitudinal monitoring of standing genomic variation in reintroduced populations.     

Endangered Cacti in the Chihuahuan Desert: I. Distribution Patterns

We mapped the geographical distributions of 93 endangered species of cacti from the Chihuahuan Desert Region. We divided the region into grids of 30 minutes latitude by 30 minutes longitude and calculated species frequencies for each grid. The grids with the highest species richness values are aggregated in areas of moderate elevation, particularly towards the southeastern and, to a lesser extent, the eastern margins of the Chihuahuan Desert Region, in northern San Luis Potosí and the southern portions of Coahuila, Nuevo León, and Tamaulipas. This vast area constitutes the most important nucleus of cactus species concentration in the continent. Species richness decreases toward the western segment of the Chihuahuan Desert Region and from the Cuatro Ciénegas region to the north and northwest. Another important area is the Queretaroan-Hidalgoan Arid Zone, where several grids containing an important assemblage of endangered species occur. Climatic factors, such as minimum temperatures and mean annual precipitation, explain the current distribution patterns of these plants, and the recent Pleistocene climatic episodes appear to have played a determinant role in the existence of areas of high species concentration and in the proliferation of narrow endemics. Special actions are urgently needed to conserve the endangered Cactaceae of this region. We propose that a carefully selected network of small areas would be an appropriate approach for the conservation of these plants. But species richness cannot be taken as the sole criterion in the determination of protected areas. Additional criteria, such as degree of endemicity, degree of threat to species and areas, habitat diversity, and biogeographic congruence with other plant and animal groups, should be analyzed before these areas are selected. Propagation in botanical gardens using scientific criteria and commercial propagation would be additional methods of conservation.     

Applying the zoo model to conservation of threatened exceptional plant species

Maintaining a living plant collection is the most common method of ex situ conservation for plant species that cannot be seed banked (i.e., exceptional species). Viability of living collections, and their value for future conservation efforts, can be limited without coordinated efforts to track and manage individuals across institutions. Using a pedigree-focused approach, the zoological community has established an inter-institutional infrastructure to support long-term viability of captive animal populations. We assessed the ability of this coordinated metacollection infrastructure to support the conservation of 4 plant species curated in living collections at multiple botanic gardens around the world. Limitations in current practices include the inability to compile, share, and analyze plant collections data at the individual level, as well as difficulty in tracking original provenance of ex situ material. The coordinated metacollection framework used by zoos can be adopted by the botanical community to improve conservation outcomes by minimizing the loss of genetic diversity in collections. We suggest actions to improve ex situ conservation of exceptional plant species, including developing a central database to aggregate data and track unique individuals of priority threatened species among institutions and adapting a pedigree-based population management tool that incorporates life-history aspects unique to plants. If approached collaboratively across regional, national, and global scales, these actions could transform ex situ conservation of threatened plant species.