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Key words: dispersal, seed bank, seed germination, seed predation.
INTRODUCTION a persistent soil-stored seed bank, although empirical data are lacking. Measuring the fate of seeds between seed production Species with event driven recruitment have a pulse and seedling establishment is critical in understanding of germination following fire, but species lacking fire mechanisms of recruitment limitation in many terres-related germination cues may be expected to recruit trial ecosystems, including grassy woodlands (Yates & seedlings between fire events. Recruitment of shrub Hobbs 1997; Clarke 2000). Seed dynamics encom-seedlings in grassy woodlands has rarely been pass seed production, dispersal in space and time, and observed (Campbell 1999; Clarke 2000; Clarke & losses through predation, decay and germination Davison 2001; Knox & Clarke 2006) and seed sowing (Harper 1977). In fire-prone communities the accu-experiments have demonstrated that recruitment is mulation of a persistent seed bank is important for seed-limited rather than safe-site limited (Clarke & post-fire recruitment and compensation of adult mor-Davison 2001; Knox & Clarke 2006). Grassy woodtality in both obligate seeding and resprouting species land species in the families Epacridaceae and (Tyler 1995; Keith 1996). Resprouting is the most Fabaceae also have innate seed dormancy, implying common response to fire in temperate grassy wood-that recruitment of seedlings may be event-driven and lands (Knox & Clarke 2004) and resprouters tend to that diaspores should accumulate in the soil if plants produce fewer seeds per season than species killed by are fecund in most years. Accumulation of these seed fire (Keeley 1977; Carpenter & Recher 1979; Bell banks is however, also dependent upon seed losses 2001; Pausas et al. 2004). Nevertheless, resprouting through dispersal to unsafe sites by seed removal species with innate seed dormancy should accumulate pathogen loss, and seed predation (Clarke & Davison 2001). In particular, predators can impose top-down effects on plant populations by limiting the number of
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关键词:扩散,种子库,种子发芽,种子采食。
引言持续土壤种子库储存,虽然缺乏经验数据。测量种子命运的物种之间的种子生产与事件驱动招募具有脉冲和幼苗建立是至关重要的理解萌发下列火灾,但火灾机制缺乏物种招募限制在许多特莱斯有关萌发线索可以预期招聘审判生态系统,包括草地林地(耶茨及幼苗之间的消防活动。招募灌木霍布斯1997 ;克拉克2000年) 。种子动态encom苗在草地林地很少通过种子生产,分散在空间和时间,并观察(坎贝尔1999 ;克拉克2000 ;克拉克和损失通过捕食,腐烂和发芽戴维森2001 ;诺克斯和克拉克2006年)和种子播种(哈珀1977年) 。在火灾易发的社区后, Accu -实验表明,模拟招聘是一个持续的种子库是非常重要的种子有限的,而不是安全现场有限公司(克拉克及火灾后的招募和补偿成人铁道部-戴维森2001 ;诺克斯&克拉克2006年) 。草地woodtality有义务在播种和resprouting土地种物种中的家庭Epacridaceae和(泰勒1995年;基思1996年) 。 Resprouting是最豆科也有天生的种子休眠,这意味着共同应对火灾温带草地木招聘幼苗可事件驱动和土地(诺克斯与克拉克2004年)和resprouters往往是散布体应在土壤中积累,如果植物生产种子每赛季少多物种死亡的丰饶在大多数年份。积累的这些种子火警( Keeley 1977 ;木匠Recher 1979 ;贝尔银行,但也取决于种子损失2001 ; Pausas等。 2004年) 。然而,通过分散resprouting不安全网站的种子去除种先天种子休眠应该积累病原体损失,种子捕食(克拉克和戴维森2001年) 。特别是,天敌可以判处自上而下对植物种群的数量限制的.
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第1个回答  2009-02-28
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第2个回答  2009-02-28
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