鼠类对山杏(Prunus armeniaca)种子扩散及存活作用研究

虽然有关鼠类搬运森林种子的证据已很清楚,但这些被移走种子的存活情况却知之甚少.提出了一个新的标记和跟踪种子的方法--标签法,即将种子拴一带有编码的细长金属片,研究了北京东灵山地区山杏(Prunus armeniaca)种子的扩散距离和存活率.于1998年6月19～20日,7月3日和10月23日共在24个样点释放1440粒山杏种子.几乎所有释放的种子在10d内被鼠类取走.夏天释放的种子比秋天释放的种子消失的速度快.大多数种子的扩散距离在20m以内,小于鼠类的活动距离.鼠类吃掉种子的速度很快,但当种子变得稀少时,种子存活率有所提高.山杏种子6、7月份的每日存活率小于其它月份的每日存活率.     

鼠类对山杏（Prunus armeniaca）种子扩散及存活作用研究

虽然有关鼠类搬运森林种子的证据已很清楚,但这些初移走种子的存活情况却知之甚少。提出了一个新的标记和跟踪种子的方法－－标签法,即将种子拴一带有编码的细长金属片,研究了北京东灵山地区山杏（Prunus armeniaca）种子的扩散距离和存活率。于1998年6月19－20日,7月3日和10月23日共在24个样点释放1440粒山杏种子。几科所有释放的种子在10d内被鼠类取走,夏天释放的种子比秋天释放的种子消失的速度快。大多数种子的扩散距离在20m以内,小于鼠类的活动距离,鼠类吃掉种子的速度很快,但当种子变得稀少时,种子存活率有所提高。山杏种子6、7月份的每日存活率小于其它月份的每日存活率。     

不同干扰强度生境中啮齿动物对苦槠种子的取食和扩散

在浙江省千岛湖地区,选择了受人类活动干扰较轻、中度和严重的3个生境,采用金属片标记法研究了啮齿动物对苦槠种子的取食和扩散.结果表明:在研究点捕获的取食种子的啮齿动物为针毛鼠( Niviventer fulvescens),尽管捕获的数量少,但种子被取食和扩散的速率很快,3个样地内的种子均在2d内被取食或扩散完毕;中等干扰强度的生境中,被就地取食的种子最多,占鉴别种子总数的37.8%.种子扩散距离大多<5m,最大扩散距离为24.76m,3个样地种子扩散均符合负指数分布,且样地间没有显著差异;饱满种子与虫蛀种子被就地取食与搬运后取食的命运没有显著差异,但饱满种子的最大扩散距离均显著大于虫蛀种子(P<0.05),除中等干扰样地中饱满种子与虫蛀种子平均扩散距离没有显著差异外,其余2个样地中饱满种子的平均扩散距离均显著大于虫蛀种子,显示啮齿动物对饱满种子与虫蛀种子有一定的区分能力.     

鼠类扩散种子的几种标签标记法的比较

以四川省都江堰市亚热带常绿阔叶林内的优势鼠种——小泡巨鼠为实验动物,通过半自然状态围栏控制实验,检验了几种种子标签法对鼠类扩散植物种子的影响。结果表明:鱼线和细钢丝两种标记线在跟踪扩散种子命运上都是很有效的,但考虑到鱼线有时会被实验鼠咬断,细钢丝是更值得推广应用的一种标记线。3种标记牌(大塑料牌、小塑料牌和金属牌)在跟踪扩散种子命运上没有显著差异,但由于较大的尺寸和较强的可见度,大塑料牌更适合作为标签应用于野外种子扩散标记。     

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。     

食物丰富度对鼠类鉴别和扩散虫蛀短柄枹栎种子的影响

时空因素和种子特征对森林鼠类扩散植物种子有着非常重要的影响。为了解食物丰富度对鼠类鉴别和扩散虫蛀种子的影响,于2012年春季(4—5月,食物匮乏季节)和2012年秋季(9—11月,食物丰盛季节),采用塑料片标记法,在秦岭南坡的佛坪国家级自然保护区内调查了森林鼠类对完好的和虫蛀的短柄枹栎Quercus glandulifera种子的扩散差异。结果显示:1)森林鼠类可以较为准确地区分完好种子和虫蛀种子。完好种子的扩散速度较快,而虫蛀种子在原地的存留时间相对较长。2)食物丰富度会对鼠类鉴别和扩散虫蛀种子产生一定的影响,但是这种影响并不显著,鼠类在春、秋季均倾向于优先取食或贮藏完好种子。3)完好种子在秋季被鼠类贮藏的比例(20%)显著高于春季(12.5%),说明种子在食物丰盛季节能够获得更大的利益。     

啮齿动物对印度栲种子扩散的效率

从2007 年11 月到2009 年11 月,在西双版纳热带雨林中选取三棵母树,在每棵树下每年释放标记印度栲种子200 粒(三年共计1 800 粒),并追踪其命运。通过调查啮齿动物搬运和分散贮藏印度栲种子的比例,以及
查贮藏种子的微生境、贮藏点大小和扩散距离,分析贮藏种子的存活情况,进而评估啮齿动物对印度栲种子扩散的效率。结果表明,啮齿动物搬运了69.3% 的印度栲种子,被搬运的种子中18% 被分散贮藏。所有被分散贮藏的种子均被埋于落叶下或埋于土壤表层,并且大部分贮藏点仅含一粒种子。种子的扩散距离从0.5 m 到43.8 m,平均距离为7.1 m,扩散距离在年间没有显著差异。2007 年(种子密度低,啮齿动物密度高) 没有种能最终存活到实验结束,而2008 和2009 年(种子密度高,啮齿动物密度低)分别有0.3% 和1.5% 的种子存活。研究表明,啮齿动物是印度栲有效的种子扩散者,但其扩散效率很大程度上取决于森林中种子的密度和啮齿动物的丰富度。     

济源太行山区鼠类对三种林木种子的扩散和贮藏

对取食种子的动物而言,种子的选择、扩散以及随后的处理是一个复杂的过程。为了解济源太行山区鼠类对不同种林木种子的选择和扩散策略的差异,于2011 年9 月10 日至11 月8 日,选取山杏、桃和栓皮栎3 种林木种子,将种子标记后,释放于次生林中,以5 d 间隔,调查并记录种子命运。结果表明: (1)大林姬鼠和岩松鼠是该地区主要的种子取食者和扩散者; (2)3 种种子的扩散速率明显不同,栓皮栎种子扩散速率最快(中位存留时间8. 6 d),其次为山杏种子(中位存留时间20. 9 d),桃种子扩散速率最慢(中位存留时间37. 5 d); (3)鼠类倾向于取食栓皮栎种子(55.0%) , 埋藏山杏种子(62. 0% ),但忽略桃种子(原地存留率99. 0% );(4)88. 6%的山杏和78. 8% 的栓皮栎种子被贮藏在灌丛下方、树干基部周围和石块旁边等生境中,而仅有4 3% 的山杏和9.1% 的栓皮栎种子被贮藏于裸地中;(5)鼠类将山杏种子搬运到更远(3. 4 ± 2. 1 m,mean± SE,n =63)处贮藏;而栓皮栎种子的搬运距离则相对较近(2. 5 ± 2. 4 m,n = 57)。结果显示:鼠类对不同种植物种子具有明显的取食、贮藏偏好和不同的贮藏策略。     

啮齿动物对秦岭松栎混交林建群种种子扩散格局的影响

森林群落中的啮齿动物对林木种子存在着一定的取食偏好性,这种偏好性会使啮齿动物形成不同的捕食和贮藏策略,从而导致林木种子形成不同的扩散格局。以秦岭中段松栎混交林建群种锐齿槲栎、油松、华山松为研究对象,采用塑料标签标记种子方法,研究啮齿动物对种子传播和扩散格局的影响。结果表明:(1)种子特征是影响啮齿动物对其进行扩散的重要因子,油松种子以其质量小、种皮薄等特点吸引啮齿动物大量捕食,其原地取食率达到83.33%,显著高于华山松和锐齿槲栎种子。(2)锐齿槲栎和华山松种子大部分被搬运一定距离后再被取食和埋藏,其中,扩散距离在1 m以内、1—3 m和5—8 m的锐齿槲栎种子分别占59.12%、18.23%和13.26%,最远扩散距离达12 m处;华山松种子扩散距离主要介于在1—3 m(37.85%)和3—5 m(23.73%),在距离5—8 m(13.56%)、8—10 m(11.86%)和大于10 m(11.30%)区间也有一定的分布,最大扩散距离为12 m。(3)啮齿动物倾向于将锐齿槲栎种子搬运至松林内取食,而将华山松种子搬运至栎林内埋藏,说明不同林分类型及其环境因素对林木种子扩散后的分布格局具有重要影响。(4)3种类型种子被啮齿动物捕食的比例以油松最大(96.90%),锐齿槲栎次之(73.57%),华山松最小(50%);次年调查时,未被捕食的种子大部分已经被取食,仅有极少数锐齿槲栎种子萌发成幼苗(1.67%)。啮齿动物的捕食和贮藏行为对林木种子扩散及其成功更新都至关重要。     

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     

Fate of the soil seed bank of giant ragweed and its significance in preventing and controlling its invasion in grasslands

Giant ragweed (Ambrosia trifida, L. henceforth referred to as GR), an annual non‐native invasive weed, may cause health problems and can reduce agricultural productivity. Chemical control of GR in grasslands may have irreversible side effects on herbs and livestock. In an attempt to propose a solution to the harmful effects of GR on grasslands, this study explores the fate of its soil seed bank (SSB) and considers the physical control of its SSB reduction. By studying GR distributed in grasslands of the Yili Valley, Xinjiang, China, we measured the spatial and temporal changes in seed density, seed germination, dormancy, and death. We analyzed seed germination, dormancy, and death following different storage periods. The study analyzed population characteristics over time, including seed fate, and examined physical control methods for reducing the SSB density. The SSB of GR occurs in the upper 0–15 cm of soil in grasslands. Seed density in the SSB decreased by 68.1% to 82.01% from the reproductive growth period to the senescence period. More than 98.7% of the seeds were rotten, eaten, germinated, dispersed, or died within one year after being produced. The seed germination rate of the SSB decreased with the number of years after invasion. When stored for 0.5 or 3.5 years, seed germination rates fell by 40%, during which time seed death rate increased by almost 40%. When GR was completely eradicated for two consecutive years, the SSB and population densities decreased by >99%. The vast majority of GR seeds germinated or died within one year; the germination rate decreased significantly if the seeds were stored dry at room temperature for a long time. Newly produced seeds are the main source of seeds in the SSB. Therefore, thoroughly eradicating GR plants for several years before the seeds can mature provides an effective control method in grasslands.     

Seed Dispersal by Monkeys and the Fate of Dispersed Seeds in a Peruvian Rain Forest1

Primary seed dispersal by two species of monkeys and the effects of rodents and dung beetles on the fate of dispersed seeds are described for a rain forest in southeastern Perú. During the six-month study period (June–November 1992) spider monkeys (Ateles paniscus) dispersed the seeds of 71 plant species, whereas howler monkeys (Alouatta seniculus) dispersed seeds of 14 species. Spider and howler monkeys also differed greatly in their ranging behavior and defecation patterns, and as a consequence, produced different seed rain patterns. Monkey defecations were visited by 27 species of dung beetles (Scarabaeidae). Dung beetles buried 41 percent of the seeds in the dung, but the number of seeds buried varied greatly, according to seed size. Removal rates of unburied seeds by rodents varied between 63–97 percent after 30 d for 8 plant species. The presence of fecal material increased the percentage of seeds removed by seed predators, but this effect became insignificant with time. Although seed predators found some seeds buried in dung balls (mimicking burial by dung beetles), depth of burial significantly affected the fate of these seeds. Less than 35 percent of Brosimum lactescens seeds buried inside dung balls at a depth of 1 cm remained undiscovered by rodents, whereas at least 75 percent of the seeds escaped rodent detection at a depth of 3 cm and 96 percent escaped at 5 cm. Both dung beetles and rodents greatly affected the fate of seeds dispersed by monkeys. It is thus important to consider postdispersal factors affecting the fate of seeds when assessing the effectiveness of frugivores as seed dispersers.     

啮齿动物及凋落物存留对天山野果林野生樱桃李种子命运的影响

2010年9月至2013年4月通过设置人工土壤种子库,研究了野生樱桃李土壤种子库的动态及啮齿动物和凋落物覆盖对种子库中种子命运的影响.结果表明: 在有取食动物扰动下,48.3%的种子萌发输出为幼苗,50%的种子被动物搬运或当场取食,4%的种子腐烂.在排除了取食动物干扰的条件下,樱桃李种子形成了短期持久的土壤种子库,3年后依然有部分种子萌发并输出为幼苗.凋落物覆盖和对照处理中,被搬运和当场取食种子的比例均显著低于清除凋落物的裸地.地表凋落物存留能减少动物搬运、取食,但不足以导致新生幼苗的大量出现,而啮齿类动物的搬运或取食是影响野生樱桃李种子命运和种子库动态的主要因素.
     

Primary Seed Dispersal by Red Howler Monkeys and the Effect of Defecation Patterns on the Fate of Dispersed Seeds1

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.     

干旱胁迫下白刺花种子大小与萌发对策

种子大小与种子萌发及其与环境因子的关系是植物种子萌发对策研究中的重要科学问题之一。采用PEG模拟干旱法研究不同干旱胁迫强度(0,5%,10%,15%,20%)下,白刺花(Sophora davidii)种子萌发进程、种子大小与种子萌发及种子命运的关系。结果表明:不同干旱胁迫下,白刺花种子具有相似的萌发进程,但中度干旱处理(10%PEG)萌发率显著高于零干旱(0%PEG)和重度干旱处理(P0.05),重度干旱处理(20%PEG)种子萌发开始时间晚于零干旱和中度干旱处理;种子大小与种子萌发开始时间的关系表现为零干旱处理下呈极显著负线性关系,中度干旱处理(5%PEG,10%PEG)下无相关关系,重度干旱处理(15%PEG,20%PEG)下呈负二次曲线关系;种子大小对种子命运的影响表现为零干旱处理有利于大、小种子萌发和小种子休眠,中度干旱处理(10%PEG)增加中等种子萌发、大种子休眠和小种子死亡风险,重度干旱处理(15%PEG,20%PEG)增加大种子死亡风险、中等种子和小种子休眠。综合分析表明,白刺花种子大小与萌发行为及种子命运的关系具有较强的环境依赖性,即种子萌发行为表现为顺境下种子越大萌发越快,逆境下小种子和大种子较中等种子萌发更快;种子命运表现为顺境增加种子死亡的风险,中度干扰有利于种子萌发,逆境则有利于种子休眠。     

Postdispersal Seed Fate of Tropical Montane Trees in an Agricultural Landscape, Southern Costa Rica

Variation in postdispersal seed fate is an important factor driving patterns of forest regeneration. Because most previous studies have not tracked final seed fate and have commonly equated seed removal with predation without considering the possibility of secondary dispersal, little is known about individual seed mortality factors in successional and degraded habitats. This study tracked the postdispersal fate of large-seeded tropical montane trees in abandoned pasture, young secondary forests, and small forest fragments during two consecutive years in an agricultural landscape in southern Costa Rica. The incidence of secondary dispersal by animals, scatterhoarding in particular, and the effects of seed burial on germination were measured. Overall, seeds survived through germination more often in secondary forests with high levels of mortality occurring in abandoned pastures and forest fragments. The majority of seed mortality was caused by rodent predation in forest fragments, insects and fungal pathogens in secondary forests, and a combination of desiccation, insects, and fungal pathogens in pastures. Seeds were frequently secondarily dispersed in larger forest fragments, whereas they were only rarely moved in pastures and secondary forests. Burial tended to improve germination in pastures and was important for an often scatterhoarded species, Otoba novogranatensis, in all habitats. The results of this study suggest that: (1) seed mortality factors differ in response to the type of habitat degradation; (2) large-seeded species have high potential for survival when dispersed to young secondary forests; and (3) seed removal is not a reliable proxy for seed predation, particularly in less degraded forest fragments.     

Linking frugivore activity to early recruitment of a bird dispersed tree,Eugenia umbelliflora (Myrtaceae) in the Atlantic rainforest

Seed dispersal by animals is a complex process involving several distinct stages: fruit removal by frugivores, seed delivery in different microhabitats, seed germination, seedling establishment, and adult recruitment. Nevertheless, studies conducted until now have provided scarce information concerning the sequence of stages in a plant's life cycle in its entirety. The main objective of this study was to evaluate the immediate consequences of frugivore activity for Eugenia umbelliflora (Myrtaceae) early recruitment by measuring the relative importance of each fruit‐eating bird species on the establishment of new seedlings in scrub and low restinga vegetation in the Atlantic rainforest, Brazil. We conducted focal tree observations on E. umbelliflora trees recording birds' feeding behaviour and post‐feeding movements. We also recorded the fate of dispersed seeds in scrub and low restinga vegetation. We recorded 17 bird species interacting with fruits in 55 h of observation. Only 30% of the handled fruits were successfully removed. From 108 post flight movements of exit from the fruiting trees, 30.6% were to scrub and 69.4% to low restinga forest. Proportion of seed germination was higher in low restinga than in the scrub vegetation. Incorporating the probabilities of seeds' removal, deposition, and germination in both sites, we found that the relative importance of each frugivorous bird as seed dispersers varies largely among species. Turdus amaurochalinus and Turdus rufiventris were the best dispersers, together representing almost 12% probability of seed germination following removal. Our results show the importance of assessing the overall consequence of seed dispersal within the framework of disperser effectiveness, providing a more comprehensive and realistic evaluation of the relative importance of different seed dispersers on plant population dynamics.     

Seed dynamics of resprouting shrubs in grassy woodlands: Seed rain,predators and seed loss constrain recruitment potential

Abstract Measuring the fate of seeds between seed production and seedling establishment is critical in understanding mechanisms of recruitment limitation of plants. We examined seed fates to better understand the recruitment dynamics of four resprouting shrubs from two families (Fabaceae and Epacridaceae) in temperate grassy woodlands. We tested whether: (i) pre‐dispersal seed predation affected seed rain; (ii) post‐dispersal seed predation limited seed bank accumulation; (iii) the size of the seed bank was related to seed size; and (iv) viable seeds accumulated in the soil after seed rain. There was a distinct difference in seed production per plant between plant families with the legumes producing significantly more seeds per individual than the epacrids. Seed viability ranged from 43% to 81% and all viable had seed or fruit coat dormancy broken by heat or scarification. Pre‐dispersal predation by Lepidopteran larvae removed a large proportion of seed from the legume seed rain but not the epacrids. Four species of ants (Notoncus ectatomoides, Pheidole sp., Rhytidoponera tasmaniensis and Iridomyrmex purpureus) were major post‐dispersal seed removers. Overall, a greater percentage of Hardenbergia (38%) and Pultenaea (59%) seeds were removed than the fleshy fruits of Lissanthe (14%) or Melichrus (0%). Seed bank sizes were small (<15 seeds m^?2) relative to the seed rain and no significant accumulation of seed in the soil was detected. Lack of accumulation was attributed to seed predation as seed decay was considered unlikely and no seed germination was observed in our study sites. Our study suggests that seed predation is a key factor contributing to seed‐limited recruitment in grassy woodland shrubs by reducing the number of seeds stored in the soil.     

Seed output and the seed bank in Vallisneria americana (Hydrocharitaceae)

Seed banks and sexual reproduction are known to be significant in colonization and re-establishment of some aquatic macrophyte communities. For highly clonal aquatic macrophytes, however, there is a lack of information on seed production and seed fate as compared with annual sexual species. The seed bank for three populations of Vallisneria americana in the Huron-Erie corridor of the Great Lakes was sampled and quantified in the spring of 1994, and related to seed production in the previous season at these sites. Seed deposition rates during 1994 were also assessed. Sites varied in the proportion of plants flowering and in their tertiary sex ratios, but did not differ in seed numbers produced per unit area. The size of the seed bank was not significantly related to the previous season's seed output, and estimates of seed deposition in the following year tended to be approximately tenfold greater than seed densities found in the seed bank. The stages between seed production and subsequent seed germination are generally very dynamic, with dispersal, mortality, and predation as likely regulating factors. The potential for seedling establishment in V. americana needs to be assessed more fully before the role of seeds in population processes can be determined.     

Small mammal controls on the climate‐driven range shift of woody plant species

Climate change is resulting in shifts in species’ ranges as species inhabit new climatically suitable areas. A key factor affecting range‐shifts is the interaction with predators. Small mammals, being primary seed predators and dispersers in forest ecosystems, may play a major role in determining which plant species will successfully expand and the rate at which range‐shifts will occur. Plants dispersing seeds beyond the species’ current range limits will encounter seed predators to which these seeds are novel; however, empirical studies of seed predator–novel seed interactions are lacking. The aims of our study were to: 1) quantify seed selection by small mammals presented with ‘novel’ seeds; 2) quantify the post‐selection fate of ‘novel’ seeds; and 3) identify seed traits that affect seed selection and post‐selection seed fate. We designed a field experiment exposing small mammal communities to novel seeds produced by plants expected to shift their ranges in response to climate change. We matched novel seeds with reference ‘familiar’ seeds and studied key steps defining interactions between small mammals and novel seeds. We found that the probability of selection of a novel seed varied among species and was, at times, higher than the selection probability of familiar seeds. Key traits that affected seed selection and the distance a seed was dispersed for caching were shell hardness and seed mass. We also found that 33% of dispersed seeds were cached in optimal germination sites (e.g. within fallen logs and buried under the leaf litter mat). Through seed emergence trials we found that emergence was higher for larger seeds, suggesting that the role of small mammals may be modulated by emergence rates. Our results suggest that the interaction between small mammals and novel seeds may have cascading effects on climate‐induced plant range shifts and community composition.