Dispersal of the non-native invasive species Crassula helmsii (Crassulaceae) may involve seeds and endozoochorous transport by birds

L. Denys, J. Packet, W. Jambon, K. Scheers
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引用次数: 17

Abstract

Reproductive abilities are essential to assess pathways of introduction, modes of dispersal, and possibilities for effective on-site remediation of invasive species, as well as to identify areas at risk and develop adequate biosafety protocols. Crassula helmsii (Kirk) Cockayne, an amphibious plant from New Zealand and Australia, was introduced in Great Britain in the early 1900s (Swale & Belcher, 1982) and now occurs throughout most of the British Isles. It was not recorded in continental Atlantic Europe until the 1980s (Margot, 1983) and it is still spreading rapidly there, especially in the Low Countries. Due to its proliferous growth and ensuing negative consequences (Robert et al., 2013), control of this highly invasive species is drawing considerable attention; efforts have so far met with little success. Dispersal of C. helmsii in Europe is believed to depend exclusively on the distribution of vegetative propagules (stem fragments or turion-like apical parts) by water, man, or animals. Overwintering also occurs in a vegetative state. As with many aquatic plants, minute fragments with a single node allow regrowth. Vaughan (1978) mentioned that the species ‘seems to set good fruit’ in Britain, but Dawson & Warman (1987) considered it likely that seeds from British plants are unviable, reporting that some were retrieved from soil samples but that these did not germinate. Germination experiments with UK material at CEH Dorset were unsuccessful (Brunet, 2002), whilst Delbart (2011) recovered only aborted seeds from three populations in southern Belgium. Recent reviews reiterate dependence on vegetative parts for dispersal, overwintering, and regrowth after management, noting uncertainty about seed viability in Europe (e.g. EPPO, 2007; Lansdown, 2012; Minchin, 2008; Willby, 2008) and current management strategies are entirely based on this presumption (Delbart et al., 2011). The rapid regrowth after sod-cutting at sites in Flanders, Belgium, where care was taken to remove even the smallest fragments, and observations of water birds grazing on stands of Crassula, led us to (re)consider (1) reproduction by means of seeds, and (2) the possibility of endozoochorous transport of vegetative propagules. Dense tufts of flowering C. helmsii were collected from the coastal dune nature reserve at D’Heye, Bredene, Belgium (51u149540N, 2u599190E) in October 2013. Plants were put into plastic bags and transferred to dark storage at 4uC for eight weeks, after which, wilted flowers with seemingly well-developed brown fruits (follicles) were removed by cutting the pedicel just below their base. Dissection of one hundred follicles yielded 30 mature seeds with a maximum of two per follicle. According to the literature, a single flower may produce two to five seeds, each c.500 mm long (EPPO, 2007). The elliptical seeds in our case were slightly smaller, 385–425 mm, and presented a characteristic rugulate surface texture (Fig. 1). 300 flowers were sown in a shallow tray with fine sand and covered with 2–3 mm of sand. Another 1000 were distributed in a similar tray but mixed with the substrate to a depth of 3–4 cm. The trays were placed in a growing chamber with 14 hours of fluorescent illumination at 18uC and 10 hours of darkness at 12uC. The substrate was kept moist by allowing demineralised water to be soaked up from below. The first seedling appeared on the twenty-fifth day in both trays. Emergence ceased completely after 43 days. Overall, 21 plants developed, 86% emerging within 32 days after sowing. The germination percentage was approximately ten times higher (18%) when seeds were at or very close to the surface than when distributed to a depth of a few centimetres; germination was epigeal. Given the small size of seeds and abundant flowering from early summer up to late autumn, we conclude that reproduction from seeds should not be dismissed as a means for site colonisation by C. helmsii or in its reestablishment after control in continental *Corresponding author: luc.denys@inbo.be
非本地入侵物种龙葵(Crassula helmsii)的传播可能涉及种子和鸟类的内源性运输
生殖能力对于评估引进途径、扩散模式和对入侵物种进行有效现场补救的可能性,以及确定有风险的地区和制定适当的生物安全协议至关重要。科凯因是一种来自新西兰和澳大利亚的水陆两栖植物,于20世纪初被引入英国(Swale & Belcher, 1982),现在分布在不列颠群岛的大部分地区。直到20世纪80年代,欧洲大西洋大陆才有该病的记录(Margot, 1983),该病仍在那里迅速传播,特别是在低地国家。由于其大量生长和随之而来的负面后果(Robert et al., 2013),对这种高度入侵物种的控制正在引起相当大的关注;到目前为止,这些努力收效甚微。据信,C. helmsii在欧洲的传播完全依赖于水、人或动物的营养繁殖体(茎片段或turion状的顶端部分)的分布。植物状态下也会越冬。与许多水生植物一样,带有单个节点的微小碎片允许再生。Vaughan(1978)提到该物种在英国“似乎结了好果子”,但Dawson & Warman(1987)认为英国植物的种子可能无法存活,他们报告说有些种子是从土壤样本中提取的,但这些种子没有发芽。在CEH Dorset用英国材料进行的发芽实验没有成功(Brunet, 2002),而Delbart(2011)只从比利时南部的三个种群中恢复了流产的种子。最近的综述重申了在管理后对营养部分的传播、越冬和再生的依赖,并指出了欧洲种子活力的不确定性(例如EPPO, 2007;Lansdown, 2012;Minchin, 2008;Willby, 2008)和当前的管理策略完全基于这一假设(Delbart et al., 2011)。在比利时的佛兰德斯,割草后的快速再生,即使是最小的碎片也被小心地去除,以及对水鸟在水草林分上吃草的观察,使我们(重新)考虑(1)通过种子繁殖的方式,(2)营养繁殖体的内源运输的可能性。2013年10月,在比利时布雷登尼D 'Heye海岸沙丘自然保护区(51u149540N, 2u599190E)采集了一丛茂密的开花海蕨(C. helmsii)。植物被装进塑料袋,在4摄氏度的低温下存放8周,之后,枯萎的花朵和看似发育良好的棕色果实(卵泡)被切掉,方法是将花梗剪掉。解剖100个卵泡得到30个成熟的种子,每个卵泡最多2个。根据文献,一朵花可以产生两到五个种子,每个种子长约500毫米(EPPO, 2007)。在我们的实验中,椭圆种子略小,为385-425 mm,呈现出典型的规则表面纹理(图1)。300朵花播种在浅盘中,用细沙覆盖,并用2-3 mm的沙子覆盖。另外1000个分布在类似的托盘中,但与基质混合至3-4厘米深。培养皿置于生长室中,18uC荧光照射14小时,12uC黑暗照射10小时。通过允许从下面吸收去矿化水,基底保持湿润。在两个托盘中,第25天出现了第一株幼苗。43天后完全停止出现。总体而言,21株植株发育,86%在播种后32天内出苗。当种子处于或非常接近地表时,其发芽率(18%)比分布在几厘米深处时高约10倍;发芽是表皮的。考虑到种子体积小,从初夏到深秋花期丰富,我们得出结论,种子繁殖不应被视为黑蝇在大陆控制后的原位定殖或重建的一种手段
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