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1.
种子雨研究进展   总被引:14,自引:0,他引:14  
种子雨是指在特定的时间和特定的空间从母株上散落的种子量。种子雨的组成和大小具有时空异质性。种子雨的空间异质性表现在种子雨的组成和大小因群落而异,种群间的种子雨因种群而异,种群内部的种子雨因个体而异;种子雨的时间异质性表现在不管是群落、种群还是种群内部的个体,其种子雨既具有季节动态,又具有年际变化。种子雨、种子库、幼苗库和地上植被相互联系、相互作用。种子雨的研究对更好地了解种群和群落动态等具有重要意义。应用现代的分子遗传标记技术、同位素标记法和荧光染料法等研究种子雨的散布过程和种子命运将是未来种子雨研究的热点,种子雨和种子库的结合研究及其与动植物关系的研究尚需加强。  相似文献   

2.
王树林  侯扶江 《生态学报》2023,43(11):4369-4389
成熟种子被动物采食和排泄后,沉积在粪便中的有活力的种子称为粪种子库。种子经动物消化道携带而实现传播的过程称为消化道传播,粪种子库是种子消化道传播的必经阶段和关键节点。粪种子库和种子消化道传播一直以来都是生态学家关注的热点。介绍了粪种子库的形成原因和理论基础,指出粪种子库是动-植物互作的结果;讨论了影响粪种子库结构和组成的因素,包括种子形态、动物种类和外界环境对粪种子库生态功能的调控作用;阐述了粪种子库的生态意义,主要表现为种子远距离传播、粪便物质返还以及促进植物群落更新和发展;最后指出将来关于粪种子库的研究需要重点关注的几个方面问题,以期为合理、全面认识粪种子库提供理论参考,并为深刻理解动-植物互作机制提供科学依据。  相似文献   

3.
王静  闫巧玲 《生态学杂志》2017,28(5):1716-1726
干扰在森林生态系统中普遍存在,并影响森林的更新和演替.动物传播种子是种子更新的必经阶段,其对森林干扰的响应在一定程度上能够预测未来的森林群落组成和结构变化,对于明确森林演替方向具有重要意义.本文论述了森林干扰对动物传播种子有效性(包括动物传播种子的数量和质量)影响研究的生态学意义,全面揭示了自然干扰(火干扰、林窗干扰等)和人为干扰(生境破碎化、狩猎、采伐等)对动物传播种子数量、传播距离以及传播后幼苗更新影响的研究进展,指出干扰通过影响动物种群动态,进而造成动物传播种子数量发生了改变,动物传播种子的距离对干扰的响应基本表现出轻微负相关;干扰对传播后幼苗更新的影响结果因干扰类型的不同而复杂多变,干扰迹地环境因子的变化也影响着传播后的种子萌发和幼苗更新.干扰对动物传播种子有效性影响研究中存在的问题,主要表现为火干扰迹地恢复过程、增益性的干扰(如抚育、间伐、林窗)等对种子传播有效性影响研究的匮乏,以及忽略了温带森林内的干扰对动物传播种子的影响等.今后,应开展干扰对种子传播有效性的长期研究;对于干扰多发地带的森林,应高度重视增益性干扰影响动物传播植物种子的研究.  相似文献   

4.
王宁  刘俊娥  周正朝 《生态学报》2021,41(18):7464-7474
生物土壤结皮(BSC)在陆地生态系统中具有重要的生态地位,尤其是旱地生态系统中,BSC占据了种子植物之间的广阔地面。因此,BSC的发展必然影响种子植物更新过程与植被空间格局;但其作用方式、影响程度等因相关研究涉及多气候要素、土壤类型、BSC组成物种和种子植物物种的差异及其不同组合,导致目前的研究结论存在广泛争议。研究综合论述了BSC改变地表微形态对种子传播过程的影响;BSC改变土壤特性(物理、化学、生物学)对种子萌发和幼苗存活与建植等关键环节的影响;并结合种子形态特征及种子萌发、幼苗建植的性状等,综合分析了BSC对种子传播、种子萌发与幼苗建植等更新过程的潜在影响机理;探讨了目前研究矛盾性结论产生的原因。总体来说,深入研究并全面揭示BSC对种子植物更新过程的影响,应加强学科交叉,将分子生物学、植物生理学、生物化学等微观研究,与遥感、野外生态因子过程监测、控制实验等宏观、中观研究结合,从机理到过程方面动态研究BSC对种子植物更新过程的影响,并引入水文模型、气候模型、种群动态模型等模型预测方法,研究气候变化、各类干扰频发的情景下,BSC对种子传播、萌发及幼苗建植过程的潜在影响,以期促进对BSC与种子植物间相互关系的研究,加深对干旱脆弱生态系统植被发展规律的认识。  相似文献   

5.
草地退化是全球干旱和半干旱草地生态系统的共同特征,由于土壤种子库在植被恢复和生物多样性维持等方面的重要作用,已成为研究热点。作为重要的脆弱生态系统,松嫩碱化草甸在人类活动和全球变化影响下发生了明显退化。松嫩碱化草甸土壤种子库研究始于20世纪90年代,主要集中在对虎尾草群落、星星草群落、碱蓬群落、羊草群落等不同演替阶段土壤种子库物种种类、密度、季节变化研究;该地区土壤种子库的物种数目随着恢复演替由初级向高级阶段而呈现逐渐增加的趋势,但物种数目均相对较少,且多以1年生为主。另外对种子雨和某些物种种子散布动态也有零星报道,主要是从群落水平进行的研究,种子雨的空间异质性表现在其组成和大小因群落而异。今后需要加强对松嫩碱化草甸土壤种子库格局与关键生境要素的耦合特征、种子库分布格局的形成机制等研究,研究方法上,引入稳定同位素标记和分子遗传学等研究方法和手段,开展持久种子库的长期定位监测研究,为盐碱地植被恢复提供理论依据。  相似文献   

6.
不同空间尺度下的肉果植物扩散过程和机理   总被引:5,自引:2,他引:3  
肉果植物扩散的生态学过程在最近得到生态学者们的广泛关注,其扩散过程包括果实搬运、果实消耗、种子雨、种子取食、种子库动态、萌发和幼苗定居等。许多过程涉及到果食性动物和肉果植物之间的互惠的协同进化关系。对最近15a关于肉果植物扩散的研究论文进行了综述,探讨在生境、微生境、景观和区域等常用的空间尺度上,肉果植物扩散和定居过程的格局与机理。  相似文献   

7.
重庆四面山常绿阔叶林建群种种子雨、种子库研究   总被引:3,自引:2,他引:1  
对重庆四面山常绿阔叶林建群种种子雨、种子库的研究表明,建群种早期和晚期的种子雨无活力;种子偏早或偏晚成熟及大籽粒的树种,其种子雨被取食的比例大;种子雨、有活力种子雨、种子库三者的数量变化不一致;有活力种子雨量较大的栲、石栎、小叶青冈、扁刺栲、香桂等,其种子库密度在早期以近几何级数的方式增长,元江栲、银木荷种子库小,存在时间短,翌年无一年生萌发苗;种子库数量动态、消减率动态决定于种子被取食的强度、种子衰老的速度以及种子对病菌、逆境的抗性和种子萌发的整齐性.  相似文献   

8.
重庆四面山常绿阔叶林建群种种子雨、种子库研究   总被引:29,自引:2,他引:27  
对重庆四面山常绿阔叶林建种种种子雨、种子库的研究表明,建群种早期和晚期的种子雨无活力;种子偏早或偏晚成熟及大籽粒的树种,其种子雨被取食的比例大;种子雨、有活力种子雨、种子库三者的数量变化不一致;有活力种子雨量较大的栲、石栎、小叶青冈、扁刺栲、香桂等,其种子库密度在早期以近几何级数的方式增长,元江栲、银木荷种子库小,存在时间短,翌年无一生年萌发苗;种子库数量动态、消减率动态决定于种子被取食的强度、  相似文献   

9.
种子生态学: 种子在群落中的作用   总被引:1,自引:0,他引:1       下载免费PDF全文
种子是指由胚珠发育而成的繁殖器官。在生态学研究中,其涵义要比植物学上种子的概念宽泛有时也指果实。作为种子植物生活史的一个重要阶段,种子从其发生、发育到成熟、传播、萌发以至成苗都与周围的环境紧密联系着。因而种子生态学是研究种子与其环境相互关系的科学。种子生态学的研究内容主要包括:种子发育与成熟的环境调节(生殖分配和结实格局)、种子性状、种子捕食、种子传播(包括种子雨)、种子库、种子休眠、种子萌发、幼苗建成和种群更新等,其中种子传播、土壤种子库、种子休眠与萌发是研究的核心内容。  相似文献   

10.
食果动物与依赖其传播种子的植物间在进化过程中形成互惠关系,生境破碎化往往干扰种子传播过程,继而破坏这种关系.生境破碎化通常降低食果动物的多样性,但亦有相反的情况出现.食果动物对生境破碎化的适应能力不同,泛性森林动物和广食性动物具有较强的适应性.生境破碎化对依赖动物传播的植物影响有差异,多数植物受到负面影响,但也有一些植物不受影响,甚至受益.动物在破碎生境中对种子传播的有效性是种子搬运量、传播距离、种子萌发及种群建立等环节的综合效果.破碎化生境中种子的搬运量与动物的觅食行为和食物选择有关;种子传播距离受食物资源可获得性的改变和生境斑块异质性的影响;种子萌发和更新种群建立成功与否决定于是否存在有效的种子传播者.生境破碎化如何影响种子传播以及动植物相互关系,尤其是异质斑块的空间分布如何影响食果动物的传播有效性、破碎化生境下动植物互惠共生关系如何建立,生境破碎化导致的植物入侵对本地植物种子传播的影响是未来需要深入研究的问题.  相似文献   

11.
Seed persistence is the survival of seeds in the environment once they have reached maturity. Seed persistence allows a species, population or genotype to survive long after the death of parent plants, thus distributing genetic diversity through time. The ability to predict seed persistence accurately is critical to inform long‐term weed management and flora rehabilitation programs, as well as to allow a greater understanding of plant community dynamics. Indeed, each of the 420000 seed‐bearing plant species has a unique set of seed characteristics that determine its propensity to develop a persistent soil seed bank. The duration of seed persistence varies among species and populations, and depends on the physical and physiological characteristics of seeds and how they are affected by the biotic and abiotic environment. An integrated understanding of the ecophysiological mechanisms of seed persistence is essential if we are to improve our ability to predict how long seeds can survive in soils, both now and under future climatic conditions. In this review we present an holistic overview of the seed, species, climate, soil, and other site factors that contribute mechanistically to seed persistence, incorporating physiological, biochemical and ecological perspectives. We focus on current knowledge of the seed and species traits that influence seed longevity under ex situ controlled storage conditions, and explore how this inherent longevity is moderated by changeable biotic and abiotic conditions in situ, both before and after seeds are dispersed. We argue that the persistence of a given seed population in any environment depends on its resistance to exiting the seed bank via germination or death, and on its exposure to environmental conditions that are conducive to those fates. By synthesising knowledge of how the environment affects seeds to determine when and how they leave the soil seed bank into a resistance–exposure model, we provide a new framework for developing experimental and modelling approaches to predict how long seeds will persist in a range of environments.  相似文献   

12.
Abstract. Plants possessing generalized dispersal syndromes are likely to be more invasive than those relying on specialist dispersal agents. To address this issue on a local and regional scale, avian seed dispersal of the invasive alien Chinese tallow tree (Sapium sebiferum (L.) Roxb.) was assessed in forests and spoil areas of South Carolina and along forest edges in Louisiana during the 1997–99 fruiting seasons. Tallow trees in these floristically distinct habitats had a few common and many casual visitors, and considerable species overlap among habitats was found. However, bird species differed in the importance of dispersing and dropping seeds among habitats. Important dispersal agents common to forests and spoil areas of South Carolina included Northern Flicker, American Robin and Red‐winged Blackbird, whereas Red‐bellied Woodpecker and European Starling were important in the former and latter habitat, respectively. In Louisiana, Red‐bellied Woodpecker, American Robin, Northern Cardinal and Eastern Bluebird dispersed many seeds. Nearly all species foraging on seeds were winter residents. Estimated numbers of seeds dispersed and dropped were higher in spoil areas of South Carolina than in Louisiana because of higher numbers of individuals per visit, higher seed consumption and seed dropping rates, and longer foraging durations. Within South Carolina, more seeds were dispersed and dropped in spoil areas than in forests because of higher numbers of birds per visit. These findings show that among habitats, tallow tree attracts diverse but variable coteries of dispersal agents that are qualitatively similar in seed usage patterns. We suggest that its generalized dispersal syndrome contributes to effective seed dispersal by many bird species throughout its range. Effects of differential avian use among locales may include changes in local bird communities, and differing tallow tree demographics and invasion patterns.  相似文献   

13.
Large animal species, which provide important ecological functions such as dispersal of seeds or top–down control of seed predators, are very vulnerable in fragmented forests, being unable to survive in small fragments, and facing increasing hunting pressure. The loss of large animals affects two main ecological processes crucial for the tree reproductive cycle: seed dispersal of large seeds (e.g. provided by tapirs) and control of seed predator population (e.g. provided by large cats). The changes in both processes are expected to increase seed mortality since seeds are not dispersed away from conspecifics (causing increased pre‐dispersal mortality due to negative density dependent effects) and/or face increased predation after a dispersal event (post‐dispersal mortality). Although an extensive body of empirical knowledge exists on seed predation, the link between seed loss and adult tree community composition and structure is not well established, as well as the temporal scale seed changes affect adults. Using an individual‐based forest model (FORMIND), we evaluate the long‐term consequences of increased pre and post‐dispersal seed mortality on the future forest biomass retention of a Brazilian northeastern Atlantic forest. Our results show that forest biomass is significantly affected after 80–93% pre‐dispersal loss of large seeds, or post‐dispersal predation densities of 20–25 predators per parent tree. Large‐seeded tree species are at increased risk of local extinction causing up to 26.2% loss of forest biomass when both pre and post‐dispersal processes are combined. However, these changes can last up to 100 years after the occurrence of defaunation. In summary we conclude that large animal loss has the potential to reduce future forest biomass and tree species‐richness by impacting seed survival, and should be considered in the planning of biodiversity friendly landscapes as well as in calculations of the global carbon budget.  相似文献   

14.
Symbiotic nitrogen (N)‐fixing plants have important effects on the biogeochemical processes of the sites they inhabit, but their ability to reach these sites is determined by the dispersal of their seeds. Differences in seed size and dispersal vectors of N‐fixing and non‐fixing plants could influence the spatial and temporal distributions of N fixers, and thus could have important impacts on biogeochemical cycling. Using seed mass, dispersal vector, and biome data retrieved from online public databases, we ask if there are systematic differences in seed mass and dispersal vectors between N‐fixing and non‐fixing plants. We demonstrate that rhizobial N fixers tend to have larger seeds that are more likely to be biotically dispersed than seeds of non‐fixers, whereas actinorhizal N‐fixing trees tend to have small, abiotically dispersed seeds. We then synthesize existing evidence from the literature to draw links between these dispersal traits and the spatio–temporal patterns of N fixers, as well as their biogeochemical effects on terrestrial ecosystems. Using this literature, we argue that the spatio–temporal distributions of N fixers are influenced by their seed dispersal characteristics, and that these distribution patterns have important effects on the total amount of N fixed at a site and the timing of N inputs during processes such as succession.  相似文献   

15.
Ellen Andresen 《Biotropica》2002,34(2):261-272
The effectiveness of a seed disperser depends on the quantity and quality of dispersal. The quality of dispersal depends in large part on factors that affect the post–dispersal fate of seeds, and yet this aspect of dispersal quality is rarely assessed. In the particular case of seed dispersal through endozoochory, the defecation pattern produced has the potential of affecting the fate of dispersed seeds and consequently, dispersal quality and effectiveness. In this study, I assessed the effects of dung presence and dung/seed densities on seed predation by rodents and secondary dispersal by dung beetles. In particular, I compared seed fates in clumped defecation patterns, as those produced by howler monkeys, with seed fates in scattered defecation patterns, as those produced by other frugivores. I also determined the prevalence of red howler monkeys (Alouatta seniculus) as seed dispersers at the plant community level in Central Amazonia by determining the number of species they dispersed in a 25–month period. I found that dung presence and amount affected rodent and dung beetle behavior. Seed predation rates were higher when dung was present, and when it was in higher densities. The same number of seeds was buried by dung beedes, in dumped versus scattered defecation patterns, but more seeds were buried when they were inside large dung–piles versus small piles. Seed density had no effect on rodent or dung beetle behavior. Results indicate that caution should be taken when categorizing an animal as a high or low quality seed disperser before carefully examining the factors that affect the fate of dispersed seeds. Red howler monkeys dispersed the seeds of 137 species during the study period, which is the highest yet reported number for an Alouatta species, and should thus be considered highly prevalent seed dispersers at the plant community level in Central Amazonian terra firme rain forests.  相似文献   

16.
动物对松属植物种子的传播作用研究进展   总被引:3,自引:0,他引:3  
鲁长虎 《生态学杂志》2006,25(5):557-562
松属植物约110种,根据种子传播方式可分为风传播松和动物传播松。风传播松占绝大多数,种子多具有适应风力的翅。动物传播松大约23种,都具有大、可食用、无翅或短翅的种子,无法借助风力传播。动物传播松的分布生境多为贫瘠的山地,而且多位于高海拔地区。目前已知9种松树的动物传播种类,其余14种可推测为动物传播。动物传播者包括鸦科鸟类和啮齿类动物,动物将获得的种子分散贮藏,未被重取的种子可能萌发,完成传播。动物传播是定向传播,微生境多适合种子萌发。啮齿类的传播距离可达数10 m,而鸦科鸟类的传播距离可达数公里。动物传播的松树会出现树丛和多树干现象,一般由同一贮点内贮藏的多粒种子萌发造成的。动物贮藏的种子大部分被重取,称传播后取食。一些具有大种子的风传播松在种子落地后,啮齿类和鸟类会再次埋藏而形成二次传播,可看做是一个单独的传播类型,即风-动物传播松。动物传播者与依赖传播松树之间可看作是互利共生关系。  相似文献   

17.
18.
植物的繁殖体总是面临来自各类生物(如昆虫、脊椎动物、真菌)的捕食风险。因动物捕食引起的种子死亡率影响植物的适合度、种群动态、群落结构和物种多样性的保持。种子被捕食的时间和强度成为植物生活史中发芽速度、地下种子库等特征的主要选择压力,而种子大小、生境类型等因素也影响动物对植物种子的捕食。捕食者饱和现象被认为是植物和种子捕食者之间的高度协同进化作用的结果,是限制动物破坏种子、提高被扩散种子存活率的一种选择压力。大部分群落中的大多数植物种子被动物扩散。种子扩散影响种子密度、种子被捕食率、病原体攻击率、种子与母树的距离、种子到达的生境类型以及建成的植株将与何种植物竞争,从而影响种子和幼苗的存活,最终影响母树及后代植物的适合度。种子被动物扩散后的分布一般遵循负指数分布曲线,大多数种子并没有扩散到离母树很远的地方。捕食风险、生境类型、植被盖度均影响动物对种子的扩散。植物结实的季节和果实损耗的过程也体现了其对扩散机会的适应。许多动物有贮藏植物种子的行为。动物贮藏植物繁殖体的行为,一方面调节食物的时空分布,提高了贮食动物在食物缺乏期的生存概率;另一方面也为种子萌发提供了适宜条件,促进了植物的扩散。于是,植物与贮食动物形成了一种协同进化关系,这种关系可能是自然界互惠关系(mutualism)的一种。影响幼苗存活和建成的因子包括种子贮蒇点的微生境、湿度、坡向、坡度、林冠盖度等。许多果食性动物吃掉果肉后,再将完好的种子反刍或排泄出来。种子经动物消化道处理后,发芽率常有所提高。  相似文献   

19.
Seed dispersal is a central process in plant ecology with consequences for species composition and habitat structure. Some bird species are known to disperse the seeds they ingest, whereas others, termed ‘seed predators’, digest them and apparently play no part in dispersal, but it is not clear if these are discrete strategies or simply the ends of a continuum. We assessed dispersal effectiveness by combining analysis of faecal samples and bird density. The droppings of seed dispersers contained more entire seeds than those of typical seed predators, but over a quarter of the droppings of seed predators contained whole seeds. This effect was further magnified when bird density was taken into account, and was driven largely by one frequent interaction: the Chaffinch Fringilla coelebs, a typical seed predator and the most abundant bird species in the area and dispersed seeds of Leycesteria formosa, a non‐native plant with berry‐like fruits. These results suggest the existence of a continuum between seed predators and seed dispersers.  相似文献   

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