东南亚兰科植物的物种多样性、生活习性及其传粉系统（附表）

兰科(Orchidaceae)植物广布于除两极和极端沙漠地区外的各种陆地生态系统,包括5个亚科800多属28 000多种。东南亚地区兰科植物种数约占世界的1/3,是兰科植物生物多样性热点区域之一。通过查阅文献及书籍等资料,该文系统整理了东南亚兰科植物物种种类及其扩散演化历史,并对其生活习性和传粉系统进行了归类。结果表明:(1)东南亚兰科植物8 855种,分属5亚科17族26亚族240属;(2)主要生活型为附生的有127属6 000种以上,地生97属2 000种以上,腐生13属约100种,藤本4属40余种;(3)根据整理出的东南亚79个属的兰科植物传粉系统发现,有44个属含有自动自交的物种,具报酬物的传粉系统有花粉(仅见于拟兰亚科)、芳香类物质(仅见于香荚兰亚科)和花蜜(5个亚科均有)等报酬物类型。欺骗性传粉系统广泛存在于各个亚科,包括食源性欺骗、性拟态、繁殖地拟态和信息素拟态等类型。东南亚兰科植物在物种、生活习性及传粉系统都展现出极高的多样性,对这些生物学特点的总结将为兰科植物的保育提供一定的理论基础和本底资料。     

气候变化对中国大黄花虾脊兰及其传粉者适生区的影响

大黄花虾脊兰(Calanthe sieboldii)是典型的大陆与岛屿间间断分布的兰科物种, 适宜分布气候范围狭窄, 同时依赖特殊的传粉者传粉, 包括黄胸木蜂(Xylocopa appendiculata)、赤足木蜂(X. rufipes)和中华绒木蜂(X. chinensis)等3种木蜂属(Xylocopa)昆虫。本文通过R语言Biomod2程序包建立物种分布模型(SDM), 预测了2050年和2070年时大黄花虾脊兰及其传粉者在3种代表浓度路径(RCP2.6、RCP4.5与RCP8.5)下的分布格局, 以期为该濒危植物的保育提供参考。结果表明: 降水相关变量比温度相关变量对大黄花虾脊兰分布的平均解释率更高, 两者分别为25.4%和13.9%。当前大黄花虾脊兰适生区主要集中在华中和华东地区, 未来适生区的增减主要受到气候情景的影响, 其变化范围为-59.0%到34.7%, 并可能向更高海拔的地区移动; 未来木蜂适生区将净收缩16.4%-19.7%, 且主要向西北和东北移动; 因而两者共同分布的面积占大黄花虾脊兰适生区的比例未来相比当前的90.0%可能下降0.5%-11.4%, 表明大黄花虾脊兰分布可能受到未来气候变化和传粉者分布减少的双重影响, 因此对该物种或类似特化传粉的兰科植物进行保育时应当充分考虑传粉者因素。     

中国特有兰科植物褐花杓兰的繁殖生物学特征及其与西藏杓兰的生殖隔离研究

作为被子植物中最进化的类群, 兰科植物通常依靠种内特化的传粉者而形成种间物种隔离。褐花杓兰(Cypripedium smithii)与西藏杓兰(C. tibeticum)是杓兰属大花亚组中的两个近缘种类, 二者形态特征相似, 分布区也存在明显重叠。在西藏杓兰繁殖生物学特征已知的基础上, 本文对褐花杓兰的繁殖生物学特征进行了研究, 并对褐花杓兰与西藏杓兰进行了外部形态比较。结果表明, 4个居群中普遍存在西藏杓兰和褐花杓兰间的一系列形态过渡类型, 两个物种并没有明确的形态差异。褐花杓兰与西藏杓兰杂交亲和, 传粉观察也表明褐花杓兰由熊蜂(Bombus)蜂王传粉, 具有与西藏杓兰相同的传粉系统。因此, 在自然条件下, 西藏杓兰与褐花杓兰之间可能会存在较频繁的基因流, 从而产生一系列中间过渡类型。将它们分为两个独立的物种并不是最好的选择, 建议将其合并为一个种。     

濒危植物裸芸香的繁育系统及在植物园迁地保护环境下的传粉研究

迁地保护是防止濒危物种灭绝的一种重要的辅助手段。为了有效保护和管理在中国科学院武汉植物园迁地保护环境下的濒危植物裸芸香（Psilopeganum sinense）,通过定位观察、人工授粉实验等方法对裸芸香的开花生物学、繁育系统和传粉过程进行了研究。结果表明：裸芸香单花花期6～8 d,雄性先熟,单花开放进程中性表达经历了雄性功能期、两性功能期和雌性功能期。裸芸香不存在无融合生殖和风媒传粉,其繁育系统类型为兼性异交,但在无传粉昆虫时能自发自交结实。在武汉植物园内的主要传粉者与宜昌野生居群的传粉者相同,均为双翅目的灰带管蚜蝇（Eristalis cerealis）、细腹食蚜蝇（Sphaerophoria sp.）、黑带食蚜蝇（Episyrphus balteatus）和膜翅目的两种遂蜂（Halictidae）。在植物园自然状况下裸芸香的结实率为90%,不存在生殖障碍。自然自发自交及兼性异交的繁育系统显示裸芸香具有一定的适应生境片断化及环境干扰的潜力。     

杓兰属植物的开花和结实动态

作为被子植物中最进化的类群,兰科植物的开花和结实动态对制定其保护策略具有重要意义。利用20032007年的数据,对分布于四川黄龙寺自然保护区的5种杓兰的种群开花和结实动态进行了分析。结果表明所研究的所有杓兰种类均是自交亲和物种,但在自然条件下都必须依赖传粉媒介才能成功结实。尽管不同种类的杓兰植物具有不同的开花时间,但统计分析表明杓兰属植物的开花早晚与其结实率之间相关性并不显著,这可能因为不同的杓兰具有不同的传粉系统而导致的。而杓兰属植物的花期长短与结实率之间却呈显著的负相关,这可能是与杓兰属植物具有典型的欺骗性传粉系统相关的。另外,除绿花杓兰外,其他4种杓兰2003年的结实率明显高于20042007年间的结实率。而2003年一个突出的事件即是发生了SARS导致游客人数显著减少,暗示了人为活动对杓兰属植物成功结实具有比较大的影响。     

同域分布的紫堇属三种植物的繁育系统和传粉差异

为研究近缘物种之间繁育系统分化对传粉环境的适应性意义,本文针对湖北地区的3种紫堇属植物（紫堇Corydalis edulis Maxim.、尖距紫堇C.shearer S.Moore.和小花黄堇C.racemosa（Thunb.） Pers.）进行了传粉生态学研究,对比分析了它们在花部特征、分布模式、花期、交配系统、传粉系统等方面的差异。3种紫堇属植物常见伴生现象,花期有一定重叠;花色、距长、花蜜量等方面均有显著差异;尖距紫堇交配系统为自交不亲和、依靠传粉者异花授粉;而紫堇和小花黄堇交配系统为自交亲和,兼有自交和异交的混合交配系统。3个物种均由蜂类传粉,且花部性器官与传粉者的接触部位一致,但访花频率差异较大。在混合群落中,传粉者访花具有较高的忠实性,花部特征差异可能是传粉者选择性访花的原因。对于紫堇属3个物种,花部特征和交配系统的分化有助于其避免传粉过程的相互干扰,交配系统与传粉环境具有一定相关性,混合交配系统可能有利于提高植物对不同生境和气候的适应性。     

珍稀濒危植物猬实的开花特性与传粉生物学研究

对迁地保护的珍稀濒危植物猬实的开花动态、花粉活力、柱头可授性、访花昆虫种类、访花频率、花粉与胚珠比(P/O)、异交指数(OCI)进行观测.结果表明：猬实的单花期约为7 d,种群花期约为14 d,花冠展开后2~3 h,花粉活力达到最高,约为90％,3 d后花粉基本不具活力.在整个单花期,柱头一直具可授性,花冠展开后第2天可授性最强.花粉与胚珠比(P/O)为(398．1±63．7),异交指数(OCI)为3,表明猬实是以异交为主,自交亲和的繁育系统,有时需要传粉者完成传粉过程.猬实的访花昆虫有10余种,以膜翅目蜜蜂科和隧蜂科昆虫为主,另外还有少量双翅目食蚜蝇科昆虫,偶见鳞翅目的柑橘凤蝶和长喙天蛾,其中以蜜蜂科蜜蜂属昆虫传粉效率最高.迁地保护的猬实未见结籽,其原因还有待于进一步研究.     

基于标本和分布信息评估中国虾脊兰属 植物的濒危状况

兰科植物是生物多样性保护的旗舰类群之一, 但如何客观准确地评估兰科植物的濒危状况, 一直是生物多样性保护中急需解决的问题。本文以中国虾脊兰属(Calanthe)植物为例, 探讨了基于馆藏标本和野外分布信息进行兰科植物红色名录濒危等级评估的利弊。我们的研究表明, 馆藏标本能够比较客观地反映物种地理分布信息和相应的野外居群状况, 但对于物种分布的历史变化和受威胁因素反映不足; 而野外工作对于物种的实际分布状况和受威胁因素等的反映比较客观, 但能发现的物种和居群数量有限, 部分极小种群物种在短时间野外工作中很难发现。我们的研究认为, 有2种虾脊兰属植物应被评估为野外灭绝(EW), 16种应被评估为极度濒危(CR)。可见, 中国虾脊兰属植物濒危的状况远比前人的评估结果要严重得多。     

芳香石豆兰的繁殖生态学

芳香石豆兰(Bulbophyllum ambrosia)是分布于我国南方石灰岩山热带季节性雨林中的一种常见附生兰科植物, 附着生长于岩石或树干上, 野外监测发现其自然不结实。对芳香石豆兰繁殖生态学的研究表明, 不同于石豆兰属其他具有蝇类传粉综合征的种类, 其花具有香味和花蜜, 中华蜜蜂(Apis cerana cerana)是芳香石豆兰唯一的有效传粉者, 具有较高的访问频率, 自然种群中有较高的花粉块移出率和柱头花粉块沉降率, 在中华蜜蜂的传粉过程中, 芳香石豆兰铰链结构的唇瓣起着重要作用。人工授粉试验表明, 芳香石豆兰自交授粉不结实, 异交授粉结实率达90%以上, 芳香石豆兰为自交不亲和的繁育系统。芳香石豆兰具有较强的克隆生长能力, 同一个体花期内有大量的花同时开放, 其传粉者中华蜜蜂平均单次访花(4.29 ± 0.40)朵( n= 66), 造成了严重的同株异花传粉。芳香石豆兰附生于石灰岩山顶岩石或树干上, 种群密度较低, 使得不同个体之间花粉交流困难, 自交不亲和的特性导致了芳香石豆兰自然不结实。本研究结果为开展芳香石豆兰的有效保护提供了依据。     

山莨菪(茄科)的传粉生物学

茄科的多数种类具有自交不亲和的特点, 主要通过异花传粉结实; 但是, 一些物种或者物种内的部分种群或者个体却高度自交亲合, 转变为自交的繁育系统。该科植物山莨菪(Anisodus tanguticus)主要分布在青藏高原, 开花较早, 比其他晚开花的植物种类更加缺少有效的异花传粉昆虫。我们选择了位于不同海拔高度的2个种群进行比较研究, 主要目的是检验该物种的繁育系统是否在极端环境下由于传粉者的缺乏而发生了部分改变。研究发现,山莨菪的花不完全雌性先熟, 柱头和花药间的平均距离随着花开放时间的延长而不断缩小, 但两者在多数花的单花花期结束时并没有发生接触。因此, 山莨菪花主要表现为适应异花传粉的雌雄异位特征。然而, 少数花 (4.9％)的柱头和花药发生接触, 为“自动自交”的传粉解除了空间隔离。2个种群的多数个体存在自交不亲和机制, 应具有异花传粉的繁育系统; 但是部分个体具有明显的自交亲和能力, 为自交提供了生理基础。高海拔种群的传粉昆虫主要是厕蝇(Fannia sp.), 它们在不同植株间的活动能够保证异花传粉结实; 同时该种群的部分个体存在“自动自交”。低海拔种群的主要访花昆虫是蚂蚁, 它们在花内的活动导致花粉在同一朵花内传递, 而引起“协助自交”; 而异花传粉昆虫厕蝇的访花频率则较高海拔种群低。两个种群的结实均由于异花传粉者不足而受到传粉限制。因此两种不同类型的自交机制为该早期开花植物异花访花昆虫的不足提供了一定程度上的繁殖补偿。     

珍稀濒危植物迁地保护策略中植物营养问题的探讨

营养缺乏、过量或不平衡都会直接导致植物生长繁殖障碍甚至死亡,通过改良土壤或补充矿质元素来解决这些问题是植物营养学研究的主要内容。这一学科的研究范围已经从传统人工生态系统发展到自然生态系统中。但总的来说,这一学科还没有真正渗透到珍稀濒危物种的迁地保护领域中来。中国各植物园目前正在开展大规模的珍稀濒危植物迁地保护工作,但人们都只重视了物种的引入,却忽视了它们在迁地保护过程中业已存在和可预见的生长繁殖障碍,对迁地保护植物的研究很少涉及其生长繁殖所需的营养条件。针对这一现状,本文提出了目前应开展的几项工作:(1)明确优先开展植物营养学研究的物种范围;(2)物种原产地土壤与植物化学元素背景值的分析;(3)迁地保护物种营养状况动态监测与营养诊断。该研究思路的提出,无论是从植物营养学与植物保育学的学科交叉角度,还是从珍稀濒危物种迁地保护保育策略的理论探索与解决实际问题的角度,都具有十分重要的意义。     

注意植物迁地保护中的遗传风险

稀有濒危植物迁地保护的长期目标之一就是要保护物种的遗传多样性和进化潜力。介绍了稀有濒危植物在植物园迁地保护过程中存在的一系列遗传风险。由于引种或取样的不足,容易导致被保存的物种缺乏足够的遗传代表性;盲目的引种、不合理的定植以及材料的来源不清则会导致稀有濒危植物的遗传混杂、近交衰退或杂交衰退;人为选择和生长环境的改变也容易造成濒危物种对迁地保护的遗传适应。在实际的迁地保护工作中,这些遗传风险往往被忽视。植物迁地保护中遗传风险将严重影响稀有濒危物种的回归和恢复。植物园应当重视濒危植物的遗传管理,以降低或避免迁地保护中的遗传风险。Abstract: Conserving genetic diversity of rare and endangered species and their evolutionary potential is one of the long-term goals of ex-situ conservation. Some potential genetic risks in ex-situ conservation in botanical gardens are presented. The preserved species may lack genetic representativity because of poor sampling. Inappropriate plantations, inadequate records and unclear kinships jeopardize endangered species to genetic confusion, inbreeding depression or outbreeding depression. Artificial selection and habitat conversion also potentially result endangered plants in adapting to ex-situ conservation, which had been usually overlooked. All the genetic risks can decrease the success of reintroduction and recovery. Therefore, appropriate genetic management should be carried out in botanical gardens to decrease or avoid genetic risks in ex-situ conservation.     

木兰科植物及其珍稀濒危种类的迁地保护

应用迁地保护的原理和方法,在华南植物园引种保存木兰植物１１属１２５种,其中中国１１３种,国外１２种,属哗啦诉珍稀濒危植物有２９种,从而建立了具有相当规模的木兰物种质基因库。     

森林遗传资源保护研究进展

森林遗传资源的保护事关现代及后代的利益,已引起全球的极大关注,自70年代以来,就地保护与迁地保护作为主要的战略在森林遗传资源保护实践中使用。一般来说森林遗传资源的就地保护可以通过建立自然保护区来实现。迁地保护主要包括种子库、田间基因库、种子园及细胞或组织培养等技术。就地保护和迁地保护应当相互补充,两者结合使用是保存森林遗传多样性的有效方法。对森林遗传资源保护战略的选择以及因贸易而濒危的热带材用树及其保护问题也作了简要评述。     

Is there a future for the Cactaceae genera Copiapoa,Eriosyce and Eulychnia? A status report of a prickly situation

Many of Chile’s iconic cactus species are threatened by human activities and global change. In order to safeguard them from extinction, both in situ and ex situ conservation actions are urgently needed. In this paper, an overview is given of the in situ and ex situ conservation status of the mainly Chilean cactus genera Copiapoa, Eriosyce and Eulychnia, including a worldwide survey of living ex situ collections of the species of these genera. From our results, we can conclude that although the threats to Chile’s remarkable biodiversity are now recognized as an environmental problem, and efforts are underway to protect the threatened endemic flora, many of the most threatened species are currently not protected in situ. Although a higher percentage of living accessions of Copiapoa, Eriosyce and Eulychnia in ex situ collections are of known wild origin compared to results of previous studies on other plant groups, the number of available accessions is insufficient to adequately preserve the genetic diversity of the threatened species. Prospects to upscale both in situ and ex situ conservation of the studied genera are discussed.     

On the horns of a dilemma: molecular approaches refine ex situ conservation in crisis

Seven years into this new millennium, species and habitat loss continue at an accelerated rate. While there have been individual examples of conservation success, the trend towards catastrophic loss of biological diversity persists. If we are to be successful in saving even a handful of critically endangered species, it is clear that they will need to be intensively managed using a variety of in situ and ex situ approaches. The highest profile ex situ conservation strategy is captive breeding. Although its relative role in an overall conservation management plan varies, captive breeding may present the only viable option for propagating the future of a species once rendered extinct in the wild. The study of Iyengar et al. in this issue of Molecular Ecology on one such species, the scimitar-horned oryx (Oryx dammah), represents an important contribution to ex situ conservation, demonstrating how critical insights into demographic history and population genetic structure obtained using molecular approaches may significantly contribute to captive breeding and reintroduction strategies.     

基于灰色关联分析方法评价13种野生兜兰的迁地保护适应性

由于过度收集和对原生境地的破坏,我国野生兜兰已濒临灭绝,对其进行迁地保护十分必要。通过对引种的13种40份野生兜兰资源进行迁地栽培,并观测兜兰种质在迁移地的各种生长性状指标等,本研究利用灰色关联分析方法评价13种兜兰的迁地适应性,分析影响其迁地保护的关键因素。结果表明:(1)带叶兜兰、同色兜兰、长瓣兜兰、文山兜兰适应性较强,与理想种的关联度均在0.8以上;巨瓣兜兰、白花兜兰、小叶兜兰、紫纹兜兰、紫毛兜兰、硬叶兜兰适应性一般,与理想种的关联度在0.7~0.8之间;麻栗坡兜兰、杏黄兜兰、红旗兜兰适应性较差,与理想种的关联度均在0.6以下;(2)不同兜兰种类、同一种类不同产地兜兰种质的迁地生长适应性不同,来源地和栽培温度可能是影响其迁地保护的关键因子。     

Gap analyses of priority wild relatives of food crop in current ex situ and in situ conservation in Indonesia

Conservation programmes are always limited by available resources. Careful planning is therefore required to increase the efficiency of conservation and gap analysis can be used for this purpose. This method was used to assess the representativeness of current ex situ and in situ conservation actions of 234 priority crop wild relatives (CWR) in Indonesia. This analysis also included species distribution modelling, the creation of an ecogeographical land characterization map, and a complementarity analysis to identify priorities area for in situ conservation and for further collecting of ex situ conservation programmes. The results show that both current ex situ and in situ conservation actions are insufficient. Sixty-six percent of priority CWRs have no recorded ex situ collections. Eighty CWRs with ex situ collections are still under-represented in the national genebanks and 65 CWRs have no presence records within the existing protected area network although 60 are predicted to exist in several protected areas according to their potential distribution models. The complementarity analysis shows that a minimum of 61 complementary grid areas (complementary based on grid cells) are required to conserve all priority taxa and 40 complementary protected areas (complementary based on existing protected areas) are required to conserve those with known populations within the existing in situ protected area network. The top ten of complementary protected areas are proposed as the initial areas for the development of CWR genetic reserves network in Indonesia. It is recommended to enhanced coordination between ex situ and in situ conservation stakeholders for sustaining the long term conservation of CWR in Indonesia. Implementation of the research recommendations will provide for the first time an effective conservation planning of Indonesia’s CWR diversity and will significantly enhance the country’s food and nutritional security.

     

Near Situ Conservation for Wild Plant Species with Extremely Small Populations

Minimum Viable Population (MVP) is the endangered species faced with extinction need prior conservation. A new method of “near situ conservation” has being particularly raised by the Forestry Department of Yunnan Province for conserving Plant Species with Extremely Small Population (PSESP) in China. In accordance with the practices and results of near situ conservation for PSESP and after our study on comparison for growth and adaptation of some state emphasized plant species between near situ and ex situ conservation in recent years, the authors hold that near situ conservation for the plant species faced with extremely high risk of extinction in the wild is more efficient than that of their ex situ conservation. We therefore suggest that the system of near situ conservation need to be constructed as soon as possible, and the high risk extinction mechanism for PSESP need to be urgently studied for selecting the effective conservation methods and adopting scientific measures. Meanwhile, for near situ conservation practices of PSESP, the principles of similarities of climates, habitats and communities must be followed for reducing the investment and raising the conservation effectiveness.     

Seed banking of endangered plants: are we conserving the right species to address climate change?

The increasing awareness of the effects of climate change on plant distributions in situ has made the appropriate application of ex situ techniques more crucial. These ex situ conservation techniques need to be targeted to priority species identified at risk from climate change. The present paper assesses the sensitivity of plant species to climate change in Belgium and explores the current conservation status of those species potentially vulnerable to climate change. We then checked whether these species were included in ex situ collections. The whole Belgian flora has been assessed (a total of 1,396 native plant species). We evaluated whether each of these species occurs in a “climate change-vulnerable” habitat, having therefore a higher probability to be impacted by climate change. The assessment revealed that there are at least 415 native plant species (30% of the Belgian native flora) that appear to be vulnerable to climate change during the next decades. Results also showed that about one-third of the species currently included in the red list may have their situation made potentially worse due to climate change. In addition, depending on the region, between 45 and 67% of the species that are currently not threatened in Belgium are likely to become so due to climate change. It also appeared that only 32% of these climate change-vulnerable species are currently held ex situ. We conclude that there is a need to identify gaps in existing ex situ collections as an urgent priority and ensure that species potentially vulnerable to climate change are conserved ex situ.