环境因素对伞形科两种植物种子萌发的影响

种子萌发模式是植物生活史策略中的一个主要特征。研究了环境因素对伞形科濒危植物明党参 (Changium smyrnioidesWolff)和非濒危植物峨参 (Anthriscussylvestris Hoffm.)种子萌发特性的影响。结果表明 ,温度是影响明党参和峨参这类冬性植物种子萌发的主要因素。两物种的种子萌发温度范围是 5～ 15℃ ,明党参种子的最适萌发温度是 10℃ ,峨参是 5℃ ,两物种在15℃时萌发率均已受抑制 ,到 18℃时几乎不萌发。两种植物种子的萌发率与温度显著负相关。两种植物种子在光照和黑暗条件下萌发率差异很小 ,均是中性种子。明党参种子在干燥条件下比峨参种子更容易失去活力 ,其种子的适宜含水量 (5 .9%～6 .4 % )比峨参 (<3.7% )高。种子质量好、萌发率高但种子产量低也是濒危植物种群更新的一个薄弱环节。     

濒危植物明党参种子散布和种子库动态研究

对伞形科濒危植物明党参（Changium smyrnioides)的种子生产、散布和种子库动态进行了研究。明党参平均每株产生完好种子132粒,86.36%来自顶生花序,不同生境中个体产生的种子千粒重有差异;其平均1.06m高的花葶在种子散布过程中易倒伏,使种子远离母株;种子散布格局为聚集型;种子库密度随时间逐渐下降。明党参种子产量和不同时期种子库密度均低于同科非濒危植物峨参（Anthriscus sylvestris),2个种的种子库均为非持续型;明党参具有低种子数、大粒种子、种子散布远离母株以减少种内竞争的K对策,在受到人类大量采挖和生境干扰后种群不容易迅速恢复;而峨参采取高种子数、小粒种子、种子近母株密集分布和产生无性系的r对策,种群受干扰后易恢复。     

珍稀濒危植物种子休眠的成因及解除方法研究进展

珍稀濒危植物为人类提供了稀缺的化工、医药、生活原料等产品，还是地质变迁、植物进化和系统发育等的见证者，是维护地球生物多样性不可或缺的重要成员之一。然而，部分珍稀濒危植物的种子因休眠作用难以萌发，这是导致它们濒临灭绝的主要原因之一。为探究珍稀濒危植物种子休眠的原因，本文综述了近年来造成珍稀濒危植物种子休眠的外因和内因，特别归纳了引起种子休眠的关键基因、miRNAs和转录因子，并从物理和化学两个层面综述了解除休眠的方法，最后讨论了未来研究的重点方向，将为濒危植物种子休眠与萌发的分子调控和其它难以打破休眠的植物苗木工程化繁育技术体系的建立奠定理论基础和科学依据。     

青藏高原东缘11种小檗属(Berberis)植物种子萌发特性

在实验室条件下研究了青藏高原东缘11种小檗属(Berberis)植物的种子萌发特性,并分析了种子萌发能力与种子大小和海拔之间的关系。结果表明,11种植物中,仅有5种植物(金花小檗、匙叶小檗、锥花小檗、鲜黄小檗和刺黄花)种子萌发率超过50%,其中金花小檗最高(86.7%);有2种植物(巴东小檗、华西小檗)种子始终没有萌发,其余4种植物种子萌发率均在10%以下;种子萌发开始时间均在10d以后,匙叶小檗种子萌发的持续时间最长(40d)。11种植物种子萌发率、萌发速率、萌发持续时间与种子大小均呈显著负相关,而萌发开始时间与种子大小之间具有显著的正相关关系。萌发率、萌发速率、萌发持续时间与海拔均有较弱的正关联,萌发开始时间与海拔有较弱的负关联。     

青阳参种子的萌发

青阳参（Cynanchum otophyllum）种子在11月成熟时有休眠习性。收获后将其种子种植在自然温室内,到第二年的春天种子才会萌发,且大多数种子在3月28至4月4日间萌发,这期间的日平均最高和最低温度分别为19．0℃和9．9℃。层积能有效地打破青阳参种子的休眠,休眠种子通过大约1周的层积便能萌发。种子在有光的条件下层积1周后转移到25／15℃的黑暗条件下萌发率可达到75．4％。青阳参种子不论在有光的条件下还是在黑暗环境中层积2～3周后转入30／20和25／15℃进行变温处理,其萌发率最低能达到66．4％,而转入20／10℃变温处理其萌发率最多只能达到20．1％,但若层积6周,即便在20／10℃变温处理的情况下其萌发率也可以达到65．3％以上。     

不同种子预处理对10种沙拐枣植物萌发的影响

为了确定沙拐枣植物种子的萌发特性及最优播前预处理方法,在实验室条件下,对10种沙拐枣植物的种子进行了磨砺、硫酸和热水浸泡、冷藏、种子浸出液处理,然后进行发芽实验研究。萌发实验的结果表明,10种沙拐枣植物对于不同的种子预处理,均表现出相似的萌发反应。磨砺、硫酸浸泡和冷藏处理对种子萌发有明显地促进作用。与对照相比,种子浸出液处理对种子的发芽率、发芽速度均具有明显地抑制作用,并能增强种子的休眠。冷藏处理具有打破有活力的种子休眠、促进种子萌发的作用,但它与热水浸泡处理一样,对有活力种子表现出一定的致死作用。沙拐枣植物的萌发模式在不同种子预处理问均表现出明显的差异性。机械磨擦和硫酸处理能够促进种子的萌发率及发芽势。泡果沙拐枣(Callingonum junceum)在本项实验中表现出很强的萌发能力。     

莎草科4种植物种子休眠与萌发特性的研究

以嵩草、黑穗苔草、藨草和苔草4种莎草科植物种子为材料,研究了硫酸、植物生长调节剂及低温层积处理对其休眠与萌发特性的影响,以揭示其休眠机制及其破除方法,为指导生产提供理论依据。结果表明:(1)4种参试植物种子均存在不同程度的生理休眠,其中嵩草为浅度生理休眠,黑穗苔草为中度生理休眠,藨草和苔草为深度生理休眠。(2)浓硫酸浸种可显著提高嵩草、黑穗苔草种子的萌发,随浸种时间增加,种子萌发率先增加后降低,最大值分别达86%、77%,但浓硫酸处理对藨草和苔草的种子萌发无显著促进作用。(3)赤霉素(GA3)、氟啶酮(FL,脱落酸抑制剂)和KNO3单独处理可显著提高嵩草种子萌发,但对其他3种植物种子无显著作用;而硫酸处理后再用赤霉素或氟啶酮处理,则显著促进黑穗苔草种子的萌发率。(4)低温层积对种子萌发的影响因种与层积时间而异,层积2个月可显著提高嵩草种子萌发,层积4个月可显著提高嵩草和藨草种子萌发;层积6个月可显著提高嵩草、黑穗苔草、藨草和苔草4种植物种子萌发,其最终萌发率分别为90%、73%、17%、7%。     

新疆短命植物小拟南芥(Arabidopsis pumila)种子萌发特性及其生态适应性

通过显微结构及不同处理条件下种子萌发率的观察,对早春短命植物小拟南芥(Arabidopsis pumila)种子萌发特性及影响因素进行了研究,并对其生态适应性进行了讨论。结果表明:(1)温度和光照变化对自然生境和温室收获种子的萌发率影响均不显著,说明此种群在前期萌发阶段对光、温不敏感;(2)自然生境中采收的小拟南芥种子萌发率显著低于温室收获种子,说明环境条件的变化对短命植物种子的发育具有重要作用,可显著改变种子的萌发行为;(3)赤霉素使自然生境收获种子胚活性增强从而对萌发有较大促进作用,可使萌发率增加50%以上;(4)对种皮进行各种机械损伤处理使得种皮松弛或透气,可以显著提高自然生境种子的萌发率(超过70%);(5)盐和干旱胁迫对种子萌发均具有明显的抑制作用,但复水后部分被抑制种子可重新萌发,显示盐和干旱胁迫可导致种子产生浅度休眠。结合小拟南芥自然生存环境及本研究的结果,显示其种子萌发特性与生境具有高度适应性。     

画眉草种子萌发对策及生态适应性

研究了画眉草种子在不同贮藏条件以及光照、温度和降雨等环境因素下的萌发对策.结果表明,画眉草新种子具有较强的内在休眠;4个月的干藏和冷藏处理对解除种子休眠作用不明显,但较长时间的贮藏（干藏1年）则能促进种子成熟.画眉草种子在光照和黑暗条件下都能萌发,但较强的光照更有利于种子萌发.种子萌发适宜温度是28 ℃,温度升高和降低都会导致画眉草种子萌发率下降;变温条件下（16～28 ℃）种子萌发率高于恒温28 ℃条件,但两个处理间的萌发率没有显著差异.种子萌发降雨阈值是10 mm,种子萌发率和萌发持续时间均随降雨量的增加而增加.画眉草种子具有迅速萌发和推迟萌发时间超过1年以上两种萌发对策.根据种子形态特征和萌发策略,推断画眉草具有持久土壤种子库.     

盐生植物种子的休眠、休眠解除及萌发的特点

本文讨论了盐生植物种子的休眠、休眠解除及萌发的特点 ,主要内容有 :( 1 )盐生植物种子的休眠类型 ;( 2 )打破盐生植物种子休眠的必要条件 ;( 3)盐生种子萌发与土壤盐度的关系。并讨论了盐度抑制盐生植物种子的机理。最后 ,作者提出了将来研究盐生植物种子萌发需要解决的几个重点问题以及研究盐生植物种子休眠和萌发问题的意义     

Modelling biological invasions: species traits,species interactions,and habitat heterogeneity

In this paper we explore the integration of different factors to understand, predict and control ecological invasions, through a general cellular automaton model especially developed. The model includes life history traits of several species in a modular structure interacting multiple cellular automata. We performed simulations using field values corresponding to the exotic Gleditsia triacanthos and native co-dominant trees in a montane area. Presence of G. triacanthos juvenile bank was a determinant condition for invasion success. Main parameters influencing invasion velocity were mean seed dispersal distance and minimum reproductive age. Seed production had a small influence on the invasion velocity. Velocities predicted by the model agreed well with estimations from field data. Values of population density predicted matched field values closely. The modular structure of the model, the explicit interaction between the invader and the native species, and the simplicity of parameters and transition rules are novel features of the model.     

Time, love and species

Physiological and behavioral phenomena of many animals are restricted to certain times of the day. Many organisms show daily rhythms in their mating. The daily fluctuation in mating activity of a few insects is controlled by an endogenous clock. The fruitfly, Drosophila, is the most suitable material to characterize the genetic basis of circadian rhythms of mating because some mutants with defective core oscillator mechanism, feedback loops, have been isolated. D. melanogaster wild-type display a robust circadian rhythm in the mating activity, and the rhythms are abolished in period or timeless null mutant flies (per(01) and tim(01)), the rhythms are generated by females but not males. Disconnected (disco) mutants which have a severe defect in the optic lobe and are missing lateral neurons show arrhythmicity in mating activities. Thus, the lateral neurons seem to be essential for the circadian rhythm in mating activity of Drosophila. Furthermore, an anti-phasic relation in circadian rhythms of the mating activity was detected between D. melanogaster and their sibling species D. simulans. The Queensland fruit flies or wild gypsy moth also show species-specific mating rhythm, suggesting that species-specific circadian rhythms in mating activity of insect appear to cause a reproductive isolation.     

Hybridization, species collapse, and species reemergence after disturbance to premating mechanisms of reproductive isolation

There are now a number of well-studied cases in which hybridization between closely related sympatric species has increased, sometimes resulting in the replacement of species pairs by hybrid swarms. Many of these cases have been linked to anthropogenic environmental change, but the mechanisms leading from environmental change to species collapse, and the long-term effects of hybridization on species pairs, remain poorly understood. We used an individual-based stochastic simulation model to explore the conditions under which disturbances that weaken premating barriers to reproduction patterns between sympatric species might lead to increased hybridization and to species collapse. Disturbances often resulted in bouts of hybridization, but in many cases strong reproductive isolation spontaneously reemerged. This was sometimes true even after hybrid swarms had replaced parental species. The reemergence of species pairs was most likely when disturbances were of short duration. Counterintuitively, incipient species pairs were more likely to reemerge after strong but temporary disturbances than after weaker disturbances of the same duration. Even temporary bouts of hybridization often led to substantial homogenization of species pairs. This suggests that ecosystem managers may be able to refill ecological niches, but in general will not be able to resurrect lost species after species collapse.     

Integration, individuality and species concepts

Integration (interaction among parts of an entity) is suggested to be necessary for individuality (contra, Metaphysics and the Origin of Species). A synchronic species is an integrated individual that can evolve as a unified whole; a diachronic lineage is a non-integrated historical entity that cannot evolve. Synchronic species and diachronic lineages are consequently suggested to be ontologically distinct entities, rather than alternative perspectives of the same underlying entity (contra Baum (1998), Syst. Biol. 47, 641–653; de Queiroz (1995), Endless Forms: Species and Speciation, pp. 57–75; Genes, Categories and Species). Species concepts usually refer to either one or the other entity; for instance, the Biological Species Concept refers to synchronic species, whereas the Cladistic Species Concept refers to diachronic lineages. The debate over species concepts has often failed to recognise this distinction, resulting in invalid comparisons between definitions that attempt to delineate fundamentally different entities. This revised version was published online in July 2006 with corrections to the Cover Date.     

Patterns of species ranges, speciation, and extinction

The exact nature of the relationship among species range sizes, speciation, and extinction events is not well understood. The factors that promote larger ranges, such as broad niche widths and high dispersal abilities, could increase the likelihood of encountering new habitats but also prevent local adaptation due to high gene flow. Similarly, low dispersal abilities or narrower niche widths could cause populations to be isolated, but such populations may lack advantageous mutations due to low population sizes. Here we present a large-scale, spatially explicit, individual-based model addressing the relationships between species ranges, speciation, and extinction. We followed the evolutionary dynamics of hundreds of thousands of diploid individuals for 200,000 generations. Individuals adapted to multiple resources and formed ecological species in a multidimensional trait space. These species varied in niche widths, and we observed the coexistence of generalists and specialists on a few resources. Our model shows that species ranges correlate with dispersal abilities but do not change with the strength of fitness trade-offs; however, high dispersal abilities and low resource utilization costs, which favored broad niche widths, have a strong negative effect on speciation rates. An unexpected result of our model is the strong effect of underlying resource distributions on speciation: in highly fragmented landscapes, speciation rates are reduced.