长江三峡地区退化生态系统土壤微生物的初步研究*

通过对长江三峡地区4种退化生态系统类型,每一类型5个土壤样品中微生物的初步研究, 结果表明该地区土壤每克干土中真菌和细菌的数量分别为 8.62×10⁴ ～1.31×10⁵ cfu 及 1.547×10⁷～6.957×10⁷ cfu, 但不同退化生态系统类型下土壤微生物的数量有所不同,其中单位重量土壤真菌数量 (cfu/g)多少顺序为：栓皮栎林(Quercus variabilis forest)＞马尾松林( Pinus massoniana forest)＞马尾松-栓皮栎混交林( Pinus massoniana-Quercus variabilis forest)＞杉木林( Cunninghamia lanceolata forest),细菌数量顺序为：马尾松-栓皮栎混交林( Pinus massoniana-Quercus variabilis forest)＞栓皮栎林( Quercus　variabilis forest)＞马尾松林( Pinus massoniana forest)＞杉木林( Cunninghamia lanceolata forest)。真菌种类鉴定表明,青霉菌(Penicillium ssp.)、镰刀菌(Fusarium spp.)、木霉菌(Trihoderma spp.)和葡萄孢菌(Botrytis spp.)等是组成该地区土壤真菌的主要类群。     

动物分散贮食行为对植物种群更新的影响

分散贮食是许多动物取食行为策略的重要组成部分。对以植物种子为主要贮食对象的动物来说,种子内营养物质含量、种子大小以及种子内次生化合物的含量等因素都直接影响动物的贮食行为。动物偏爱贮藏个体较大的种子,大种子多被搬运并分散贮藏在远离种源的地方,而小种子则多被就地取食,以补充动物贮食过程中的能量消耗。贮食动物主要通过空间记忆、特殊路线以及贮藏点周围的直接线索等途径重新获取贮藏点内食物。在重取过程中,一些贮藏点被遗忘,其中的种子成为植物种群更新的潜在种子库。因此,分散贮食动物不仅是种子捕食者,还是种子传播者,它们对植物种子的捕食、搬运和贮藏,影响了植物种子的存活和幼苗的建成,从而在一定程度上影响植物种群的更新、分布。植物种群为了促进种子的传播,在进化过程中逐渐形成了形式多样的适应性策略,降低种子的直接被捕食率,提高种子的被贮藏率。研究动物分散贮食行为对植物种群更新的影响,将有助于理解贮食动物与植物之间的互惠关系,从而认识贮食动物种群在生态系统中的作用,为生物多样性的保护提供科学依据。     

以种子为繁殖体的植物更新模型研揪

种子植物的自然更新过程是20世纪70年代以来生态学领域研究的热点问题之一。对影响种子植物更新过程因子的研究主要涉及3个阶段,即种子生产、种子运动(主要为种子扩散的过程)和种子萌发、幼苗建成以及幼树生长到成树。一些完整的理论和实验模型被提出。反过来模型的研究促进了野外研究的进一步发展。关于种子植物更新的定性模型和定量模型陆续被提出,定量研究种子植物的更新过程将成为主要的发展方向。本文综述了近年来关于种子植物更新过程的3个较为完整的定性模型,即Chambers等的种子命运模型、Clark等的补充限制模型和Nathan等的时空模型,以及2个定量模型,即Vander和Boehning等的种子扩散模型。     

狼毒种子萌发特性与种群更新机制的研究

研究了采集于植株上的和收集于土壤种子库的狼毒(Stellera chamaejasme)种子在不同温度、光照和5种预处理(即破裂种皮、去除种皮、98％H2SO4浸种5min、0．2％KNO3浸种24h、10℃低温保存1周)条件下的萌发力。结果表明,狼毒种子萌发率较低,25℃恒温、黑暗条件下萌发率为13％,较适宜的萌发温度为30℃恒温或10～30℃变温,破裂种皮和去除种皮萌发率显著提高,25℃恒温、光暗交替条件下萌发率分别为49％和47％,浓硫酸浸种5min处理萌发率可达到32％,KON3浸种和10℃低温保存两个处理对促进狼毒种子萌发效果不明显,狼毒种子萌发对光照条件不敏感,种子硬实性是导致狼毒种子萌发率较低的主要原因,取自土壤种子库内的狼毒种子萌发率高于当年采集的种子,在自然条件下,并非每年都有狼毒种子萌发长成幼苗,种群更新时机是随机的或周期性的。     

生境破碎化对食果动物及种子传播的影响

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.     

食果动物传播种子的跟踪技术

研究食果动物传播种子的主要问题之一是难以跟踪种子命运和估计种子域。到目前为止,已有不少方法用于研究食果动物与种子扩散和种子命运的关系,如直接观察法、同位素标记法、金属标记法、磁铁标记法、荧光染料法、微粒体标记法、线标法和遗传技术等。近年来,一些研究将数字编号用于种子标记,并已成为发展的主流。本文综述了以往跟踪种子命运和估计种子域的一些重要方法,并讨论了它们各自的优缺点及其应用。     

黄檗的更新特点及食果实鸟类对其种子的传播

在帽儿山实验林场和哈尔滨实验林场 ,黄檗母树下没有幼苗分布 ,不能进行天然更新 ,需要靠食果实鸟类等将果实和种子传播至远离母树的其他林下。捕食黄檗果实的食果实鸟类有 9种。其中 6种是食果肉鸟类 ,吞入果实后 ,消化果肉 ,而种子完整地随粪便排出而得以传播。其余 3种是食种子鸟类 ,没有传播作用。果实在鸟类消化道内的滞留时间达 2 0～ 30min ,具有很长的潜在传播距离。将鸟类消化后的种子与完整果实和人为去果肉种子进行萌发对比实验 ,消化后种子的累计萌发率与其余二者之间均没有显著性差异 ,说明食果实鸟类的消化 (道 )过程对种子萌发没有明显影响 ,同时证明果肉对种子萌发率没有显著影响 ,果肉中不含萌发抑制物质。黄檗提供多种鸟类以食物 ,而鸟类也同时以多种肉质果植物为食物。因此食果实鸟类和肉质果植物 (包括黄檗 )之间形成了松散的互利共生关系     

动物与植物种子更新的关系I.对象,方法及意义

大多数植物靠种子库来更新。种子从离开母体到建成幼苗的过程中始终受动物活动的影响。动物对种子既有取食消耗的不利一面,又有将其扩散到适于发芽的安全地点的有利一面,二者处于一种利弊权衡状态。研究动物与植物种子更新的关系,有助于揭示种群动态的机制,理解动物和植物之间协同进化的规律,了解生态系统演替及其组分之间的关系,认识取食种子的动物在生态系统中的作用,进而为生态系统维持和生物多样性保护提供科学依据及有效     

模拟动物取食子叶对辽东栎种子萌发和幼苗早期生长的影响

在实验室人工气候箱和玻璃温室盆播条件下,研究了不同程度子叶切除处理(切除1/4、1/2和3/4子叶,以不切除子叶为对照)对辽东栎(Quercus wutaishanica)种子萌发和幼苗早期生长的影响。结果表明:在人工气候箱培养条件下,子叶切除处理后种子的萌发率均高于对照,其中切除1/4子叶处理与对照间差异显著;子叶切除处理加快了种子萌发进程,即萌发速率系数减小,各处理及其与对照间差异不显著;萌发指数在切除1/4子叶处理显著大于对照,其他切除处理与对照间无显著差异;子叶切除处理对活力指数无显著影响。在玻璃温室盆播条件下,尽管不同程度子叶切除处理种子的萌发率无显著提高,但子叶切除后,种子的萌发进程加快,萌发指数增大;活力指数在切除1/4子叶处理略高于对照,而切除1/2和3/4子叶处理均大幅减小。切除子叶处理的幼苗株高、基径、主根长、侧根数、最大侧根长、叶片数、单株叶面积和总干质量等生长参数均不同程度的减小,其中株高在各处理及其与对照间均差异显著,其他生长参数在2个重度子叶切除处理(切除1/2和3/4子叶)均显著小于对照;幼苗根冠比受子叶切除处理的影响较小,各处理及与对照间均差异不显著;切除子叶处理增大了幼苗的比叶面积、比枝长和比根长,其中比叶面积在切除1/2子叶处理显著大于对照,比枝长在各切除处理均显著大于对照,切除1/2子叶和切除3/4子叶处理幼苗的比根长显著大于切除1/4子叶处理和对照幼苗。     

放牧对小叶锦鸡儿种子产量的影响

锡林河流域草地灌木化表现为小叶锦鸡儿（Caragana microphylla）种群的扩张。为了研究放牧与小叶锦鸡儿种群扩张的关系, 从小叶锦鸡儿的种子产量和萌发入手, 分析放牧对小叶锦鸡儿生殖的直接影响（即放牧的直接影响）以及不同放牧处理下昆虫种群对小叶锦鸡儿生殖造成的影响（即放牧的间接影响）。通过比较不同处理下小叶锦鸡儿果荚的数量、种子产量以及昆虫对种子的取食, 发现放牧产生的直接影响和间接影响性质不同, 放牧的直接影响是不利于小叶锦鸡儿的繁殖,而其间接影响却对小叶锦鸡儿的繁殖有利, 且这两种影响在很大程度上会互相抵消。根据所得的研究结果可知在停止放牧之后的一段时间内, 小叶锦鸡儿种群扩张的可能性会增加, 因此在草地生态系统管理中应该注意这个问题。     

Latitude, seed predation and seed mass

Aim We set out to test the hypothesis that rates of pre‐ and post‐dispersal seed predation would be higher towards the tropics, across a broad range of species from around the world. We also aimed to quantify the slope and predictive power of the relationship between seed mass and latitude both within and across species. Methods Seed mass, pre‐dispersal seed predation and post‐dispersal seed removal data were compiled from the literature. Wherever possible, these data were combined with information regarding the latitude at which the data were collected. Analyses were performed using both cross‐species and phylogenetic regressions. Results Contrary to expectations, we found no significant relationship between seed predation and latitude (log₁₀ proportion of seeds surviving predispersal seed predation vs. latitude, P = 0.63; R² = 0.02; n = 122 species: log₁₀ proportion of seeds remaining after postdispersal seed removal vs. latitude, P = 0.54; R² = 0.02; n = 205 species). These relationships remained non‐significant after variation because of seed mass was accounted for. We also found a very substantial (R² = 0.21) relationship between seed mass and latitude across 2706 species, with seed mass being significantly higher towards the tropics. Within‐species seed mass decline with latitude was significant, but only about two‐sevenths, as rapid as the cross‐species decline with latitude. Results of phylogenetic analyses were very similar to cross‐species analyses. We also demonstrated a positive relationship between seed mass and development time across ten species from dry sclerophyll woodland in Sydney (P < 0.001; R² = 0.77; Standardized Major Axis slope = 0.14). These data lend support to the hypothesis that growing period might affect the maximum attainable seed mass in a given environment. Main conclusions There was no evidence that seed predation is higher towards the tropics. The strong relationship between seed mass and latitude shown here had been observed in previous studies, but had not previously been quantified at a global scale. There was a tenfold reduction in mean seed mass for every c. 23° moved towards the poles, despite a wide range of seed mass within each latitude.     

Postdispersal seed predation and seed viability in forest soils: implications for the regeneration of tree species in Ethiopian church forests

Almost all dry Afromontane forests of Northern Ethiopia have been converted to agricultural, grazing or scrub lands except for small fragments left around churches (‘Church forests’). Species regeneration in these forests is limited. We investigated (i) how intense postdispersal seed predation was in church forest, and if this seed predation varied with species and/or habitat, and (ii) for how long tree seeds maintained their viability while buried in forest soil. In the seed predation experiment, we monitored seeds of six tree species in four habitats for a period of 14 weeks (the peak seeding season). In the seed viability experiment, we assessed seed viability of five species in four habitats after being buried 6, 12, or 18 months. Ninety‐two percent of the tree seeds were predated within 3.5 months. Predation was mainly dependent on species whereas habitat had a weaker effect. Seed viability decreased sharply with burial time in soil for all species except for Juniperus. To minimize seed availability limitation for regeneration of such species in the forest, the standing vegetation needs to be persistently managed and conserved for a continuous seed rain supply. Additional seed sowing, and seed and seedling protection (by e.g. animal exclosures) may increase successful regeneration of important species in these forests.     

Co-evolution of seed size and seed predation

Using the evolutionarily stable strategy (ESS) approach in a model for the co-evolution of seed size and seed predation, I show that seed size variation within individual plants is favoured if there is a trade-off in the predator's attack rate for different seed sizes. A single seed size is not evolutionarily stable because a predator that is optimally adapted to one particular seed size cannot prevent invasion by plants with a different seed size. The model generates the following predictions. The ESS consists of a continuous range of seed sizes. Small seeds tend to be attacked more frequently than big seeds. Plants with many resources and plants with low (frequency-independent) juvenile mortality have more variable seeds than plants with few resources and a high juvenile mortality. Seed size variation is higher in fluctuating populations regulated by seed predation alone than in stable populations (partially) regulated by seedling competition. Predator searching behaviour does not directly affect the ESS seed size range, but may have an indirect effect by affecting population stability or the significance of seedling competition as a population regulating mechanism. Moreover, seed size distributions are found to be more skewed in favour of small seeds if predation is spatially non-uniform than if predation is more even. Application of the model to systems of several co-evolving plant and predator species is discussed.     

昆虫种子捕食与蒙古栎种子产量和种子大小的关系

为了了解昆虫种子捕食者在栎类种群更新中的作用,于2006年秋季,在黑龙江省伊春市带岭区东方红林场研究了昆虫对蒙古栎Quercus mongolica在参园和东山两个种群的种子蛀食情况及其与蒙古栎种子产量和种子大小的关系。结果表明：(1)在参园和东山两个林分内,蒙古栎种子雨动态非常相似,种子雨成分中完好种子的平均密度仅为3.2±4.1个/m²（参园）和1.7±2.8个/m²（东山）,分别仅占种子产量的4.0％和3.2％,而虫蛀种子和败育种子的比例均在38%以上,以虫蛀种子的比例最高,分别为58.2％和57.7％;(2)柞栎象Curculio arakawai是蛀食蒙古栎种子的主要昆虫种类,在虫蛀种子中所占比例高达96.8％（参园）和97.1％（东山）,且象甲蛀食种子中所含虫卵数与种子大小有关,即种子越大,所含象甲的虫卵数就较多。本研究的结果说明2006年蒙古栎成熟种子多遭遇虫蛀,导致完好种子的数量极低,因而可能成为限制蒙古栎种群更新的重要因素。     

Predispersal seed predation on five Piper species in tropical rainforest

Absolute number of seeds lost to predispersal seed predators and proportion of total seeds lost per infructescence were compared among five Costa Rican Piper species of different annual fecundities. Mean seed number and mean seed size in the five species were negatively correlated. The impact of predation on these species was inversely related to the number of seeds they produced. The two early successional species had very high fecundities, a combination of many seeds per infructescence, many infructescences per plant, and, in one species, year-round reproduction. Although seed predators destroyed as many or more seeds of these early successional species than they did of the less fecund, late successional species, this loss accounted for a relatively minor proportion (9 and 12%) of the seeds of the early successional species. In contrast, late successional species produced fewer, larger seeds in a smaller number of infructescences and were not continually in fruit. One of these species, which produced intermediate numbers of intermediately sized seeds, lost 30% of the seeds in each infructescence on average. Seed predators destroyed a larger proportion (65 and 76%) of the seeds per infructescence in the two species with fewest seeds per infructescence. High levels of insect damage in these late successional species caused many of their infructescences to abort prematurely. Taken together these factors resulted in annual fecundities several orders of magnitude smaller in shade-tolerant Piper species than the annual fecundities of shade-intolerant, early successional species. Seedlings of the two early successional species were common in large gaps and other sunny clearings and seedlings of the species with 30% seed loss were occasional, whereas no seedlings were seen of the two species with the highest proportional seed loss, suggesting that seed predation on the latter species may limit seedling recruitment.     

Shell strength and primate seed predation of nontoxic species in eastern and southern Africa

The large African primates that eat fruit destroy the seeds of a number of fruiting species. This paper addresses several questions about seed-eating: What is the nature of the dietary niche provided by the nonpoisonous seeds of eastern and southern Africa? How well are these seeds mechanically protected? What other means of reducing seed predation are employed by the plants? and is the niche ecologically stable? Measurements of seed shell strength on 37 species from 17 families reveal a range of values, from <100-kg (numerous species) to over 2000-kg (palm nuts) breaking load. Primates crack open with their teeth seed shells from species exhibiting test strengths less than 600 kg. Variation in shell strength appears to increase dramatically for average species strengths above 100 kg. Plant species are not characterized by specific shell strengths but instead, display envelopes of shell strength overlapping broadly with other species. Taking this into account, adult male baboons (Papio spp.) appear to be dentally capable of preying upon most of the seed species of eastern and southern Africa. The possibility for predation of nonpoisonous seeds exists primarily because the plants periodically produce large crops in synchrony and the hard-shelled seeds are effectively dispersed, sometimes explosively but more often by means of edible fruits. The concomitant primate seed predation is a facultative specialization, of little apparent threat to the community of plants that support it.     

The role of pre- and post-dispersal seed predation in determining total seed loss

Most seed predation studies focus on either pre- or post-dispersal predation and may therefore underestimate the role of predation in regulating plant populations. We therefore estimated total seed predation of an invasive tree, mesquite (Leguminoseae: Prosopis spp.), by examining the entire seed pool from tree to seed bank. The spatio-temporal dynamics of total seed predation was examined by sampling across its Australian distribution and through time. The main predator was a host-specialist multivoltine beetle, Algarobius prosopis L. (Bruchidae), previously introduced as a biocontrol agent. Seed predation exceeded 20% in all seed stages (in pods on and off the tree, and seeds within woody endocarps (capsules) and free seeds on and in the ground) but was consistently highest in capsules on the ground (up to 90%). Pre-dispersal predation contributed little. Total seed predation rates were primarily determined by predation rates on the most persistent seed stage, in this case fallen pods if only pods are considered and seeds in capsules for the total seed pool. This pattern was consistent across the surveyed taxa, regions, years and seasonally. Predation rate was relatively unaffected by seed density, potentially because densities were always low (<150 seeds m⁻²). Average total seed predation within a region reached 55%, but we conclude that any population regulation of mesquite by seed predation will principally be through reduced seed bank persistence. Our results highlight the need to consider the entire seed pool, especially the often cryptic and overlooked long-lived stages, when determining seed loss to predation and its likely population consequences.     

Spatiotemporal variation in predispersal seed predation intensity

The effect of predispersal seed predation by Bruchus atomarius (Bruchidae, Coleoptera) on individual performance and population dynamics of the perennial forest herb, Lathyrus vernus (Leguminosae), was investigated in 11 permanent plots over 4 years. Seed predation and parameters describing intra-specific neighbour distance, plant size, inflorescence size, flowering phenology and current and previous herbivore damage were measured on all plants. In addition, demographic information from all plots was analysed using transition matrix population models in order to estimate the influence of seed predation on population growth rates. Predispersal seed predation rates differed significantly among years. Plot averages ranged from 0 to 83.7%. However, most of the variation occurred among individuals. Within individuals there was no consistency in predation rates among years. Exposure to herbivory, plant size and flowering phenology did not affect predation rates but individuals with larger inflorescences suffered from significantly higher predation. Seed predation in L. vernus was not influenced by neighbour distances of individual plants but it was positively correlated with the average density of seeds within plots, suggesting that seed predation is density dependent at the patch level. The reduction in population growth rate due to seed predation ranged from 0 to 7.6%. The sensitivity of population growth rate to reductions in seed production varied considerably among years and plots. This variation was mainly due to differences in the reproductive value of seeds and seedlings. The intensity of seed predation over the range found was not correlated with changes in population growth rate. The results of this study suggest that the influence of external factors, like seed predation, on population growth rate largely depends on the demographic transition rates in the investigated population.