圣彼得堡和列宁格勒地区特殊自然保护区内鸟类分散灌木物种的入侵

I. Kucherov
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For this purpose, distributions of these species are traced along with different forest types they invade, paying attention to species constancy and projective cover in different layers of forest communities (See Tables 2 and 4). Values of intralandscape species activeness, based upon the proper relevé sets, were also calculated for both aboriginal and adventitious plant species from different community types in each study area (See Tables 3 and 5). Lonicera nigra has never been detected as an invader before. It is presumably dispersed by robins, thrushes, and warblers, also by means of barochory and secondary hydrochory. The latter is proved by the occurrence of the oldest shrubs in riverine Norway spruce and Scots pine forests on the Littorine terrace of the Gulf of Finland within Komarovo Coast Nature Sanctuary. The results of secondary bird dispersal of this species are observed in sorrel spruce forests where the untypical low shrub layer is being formed (See Fig. 2). These plants are remote form brooks or drainage channels (See Table 2). L. nigra acts as one of the most active species in the sanctuary forest coenofloras studied (See Table 3). Nevertheless, floristic composition of these forest communities remains yet unchanged in its main features. The invasion of L. nigra in the sanctuary area was first mentioned in literature by NN Tzvelev in 2000 but it took place much earlier, as the ancestral plant specimens were likely to grow in a transplant nursery near the present-day sanctuary north-eastern border in the early XX-th century. According to Komarov Botanical Institute Herbarium (LE) data, the secondary area of L. nigra in Russia is restricted to several findings in the Karelian Isthmus. Amelanchier spicata, the June berry, listed among the most aggressive plant invaders in European Russia, is dispersed by thrushes along roads in forests and then invades sorrel and horsetail-peatmoss spruce and pine forests on southern-boreal watersheds in Lisino Reserve, often as a gap-filling species. It is less common and abundant in secondary birch and aspen forests. In contrast to Lonicera nigra, it is infrequent and never abundant in riverine forests (See Table 4), the fact probably explained by difference in prevailing bird distributor species. A. spicata is never found in feathermoss pine forests on fluvial-glacial sand as well as in dwarfshrub-peatmoss pine bog forests. The invasion of this species in the reserve area probably took place after 1984-1987 when the species was not registered in forest communities of the area according to the author’s personal observations. In 2017, the activeness of A. spicata is low in all the forest types it inhabits, being compared to that of the dominant aboriginal species (See Table 5). As follows from the correlation analysis results, no one of the discussed invaders affects the projective cover of any of the native plant species in both protected areas significantly. Speaking of Amelanchier spicata, it is in fact far less aggressive than in the more southern areas of Central and Southern Russia where the species transforms forest communities actively and affects aboriginal field- and ground-layer plants negatively, even as far as to the extinction of some of the latter, as it is well-known from the literature on the subject. We are just at the beginning of the invasion process in the forests of the Russian North-West yet. The invasion of both species studied is likely to be connected with the climate change processes. The research reveals that a neglected adventive species, persisting long within a given area, may also suddenly become an aggressive invader (the case of Lonicera nigra). The invasion of adventive shrubs into the paludified forest communities, including those of the boreal peatmoss spruce forests which served as etalons of floristic stability quite recently, is also alarming.","PeriodicalId":37153,"journal":{"name":"Vestnik Tomskogo Gosudarstvennogo Universiteta-Biologiya","volume":null,"pages":null},"PeriodicalIF":0.4000,"publicationDate":"2021-01-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":"{\"title\":\"Invasions of bird-dispersed shrub species in specially protected natural reservations of Saint-Petersburg and Leningrad Region\",\"authors\":\"I. 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引用次数: 0

摘要

该研究涉及最近在圣彼得堡和列宁格勒地区特别保护的自然保护区入侵的鸟类分散灌木。基于2014-2018年广泛的植物群落学研究数据,给出了该地区5个部分自然保护区和自然保护区鸟类分散木本物种清查结果(见图1)(见表1)。在所列的外来灌丛物种中,根据其在天然林群落中的稳定性和丰度选择了两种最具攻击性的入侵物种。这些是科马罗夫斯基(科马罗沃海岸)自然保护区的黑忍冬,以及利辛斯基(利西诺)部分自然保护区的细叶青龙。为此,我们将这些物种的分布随其入侵的不同森林类型进行追踪,关注物种的稳定性和不同森林群落层的投影覆盖(见表2和表4)。(见表3和表5)。黑忍冬在此之前从未被发现是一种外来入侵植物。据推测,它是由知更鸟、画眉和莺传播的,也通过鸣叫和次级水鸟传播。在科马罗沃海岸自然保护区的芬兰湾滨海阶地上,最古老的挪威云杉和苏格兰松林灌木的出现证明了这一点。在正在形成非典型低灌木层的酸云杉林中观察到该物种的次生鸟类传播结果(见图2)。这些植物远离溪流或排水通道(见表2)。黑桫椤是所研究的保护区森林群落中最活跃的物种之一(见表3)。然而,这些森林群落的区系组成基本保持不变。NN Tzvelev于2000年首次在文献中提到了黑桫树对保护区的入侵,但它发生的时间要早得多,因为祖先的植物标本可能在20世纪初在今天的保护区东北边界附近的移植苗圃中生长。根据科马罗夫植物研究所植物标本馆(LE)的资料,黑桫椤在俄罗斯的次要分布区域仅限于卡累利阿地峡的几个发现。六月浆果Amelanchier spicata被列为俄罗斯欧洲地区最具侵略性的植物入侵者之一,它被画眉鸟散布在森林中的道路上,然后侵入利西诺保护区南北方流域的酢叶草、马尾草木云杉林和松林,通常是作为一种填补空白的物种。它在次生林桦树和白杨林中不太常见和丰富。与黑忍冬不同,黑忍冬在河流森林中不常见,数量也不丰富(见表4),这一事实可能是由主要鸟类分布物种的差异所解释的。在河流-冰川沙上的羽苔松林以及矮灌木-泥炭松林中从未发现过刺草。根据作者的个人观察,该物种在保护区的入侵可能发生在1984-1987年之后,当时该物种尚未在该地区的森林群落中登记。2017年,与优势本土物种相比,spicata在其所栖息的所有森林类型中的活跃度都较低(见表5)。从相关分析结果可以看出,上述两种入侵物种均未对两个保护区的任何本土植物的投影覆盖产生显著影响。说到spicata,它实际上远没有在俄罗斯中部和南部的南部地区那么具有侵略性,在那里,该物种积极地改变森林群落,对原始的田野和地面植物产生负面影响,甚至导致后者的一些灭绝,这一点从有关该主题的文献中众所周知。我们刚刚开始入侵俄罗斯西北部的森林。这两种物种的入侵很可能与气候变化过程有关。研究表明,一个被忽视的外来物种,在一个给定的区域内长期存在,也可能突然成为一个具有侵略性的入侵者(如黑色忍冬)。外来灌丛入侵的混浊森林群落,包括最近作为植物区系稳定性标杆的北方泥炭云杉林的群落,也令人担忧。
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Invasions of bird-dispersed shrub species in specially protected natural reservations of Saint-Petersburg and Leningrad Region
The research deals with recent invasions of bird-dispersed shrubs in specially protected natural reservations of St.Petersburg and Leningrad Region. The results of bird-dispersed woody species inventory in 5 partial nature reserves and nature sanctuaries of the area (See Fig. 1), based upon the extensive phytocoenological research data of 2014-2018, are given (See Table 1). Out of the adventive shrub species listed, the two most aggressive invaders were chosen according to their constancy and abundance in natural forest communities. These are Lonicera nigra in Komarovskiy Bereg [Komarovo Coast] Nature Sanctuary and Amelanchier spicata in Lisinskiy [Lisino] Partial Nature Reserve. For this purpose, distributions of these species are traced along with different forest types they invade, paying attention to species constancy and projective cover in different layers of forest communities (See Tables 2 and 4). Values of intralandscape species activeness, based upon the proper relevé sets, were also calculated for both aboriginal and adventitious plant species from different community types in each study area (See Tables 3 and 5). Lonicera nigra has never been detected as an invader before. It is presumably dispersed by robins, thrushes, and warblers, also by means of barochory and secondary hydrochory. The latter is proved by the occurrence of the oldest shrubs in riverine Norway spruce and Scots pine forests on the Littorine terrace of the Gulf of Finland within Komarovo Coast Nature Sanctuary. The results of secondary bird dispersal of this species are observed in sorrel spruce forests where the untypical low shrub layer is being formed (See Fig. 2). These plants are remote form brooks or drainage channels (See Table 2). L. nigra acts as one of the most active species in the sanctuary forest coenofloras studied (See Table 3). Nevertheless, floristic composition of these forest communities remains yet unchanged in its main features. The invasion of L. nigra in the sanctuary area was first mentioned in literature by NN Tzvelev in 2000 but it took place much earlier, as the ancestral plant specimens were likely to grow in a transplant nursery near the present-day sanctuary north-eastern border in the early XX-th century. According to Komarov Botanical Institute Herbarium (LE) data, the secondary area of L. nigra in Russia is restricted to several findings in the Karelian Isthmus. Amelanchier spicata, the June berry, listed among the most aggressive plant invaders in European Russia, is dispersed by thrushes along roads in forests and then invades sorrel and horsetail-peatmoss spruce and pine forests on southern-boreal watersheds in Lisino Reserve, often as a gap-filling species. It is less common and abundant in secondary birch and aspen forests. In contrast to Lonicera nigra, it is infrequent and never abundant in riverine forests (See Table 4), the fact probably explained by difference in prevailing bird distributor species. A. spicata is never found in feathermoss pine forests on fluvial-glacial sand as well as in dwarfshrub-peatmoss pine bog forests. The invasion of this species in the reserve area probably took place after 1984-1987 when the species was not registered in forest communities of the area according to the author’s personal observations. In 2017, the activeness of A. spicata is low in all the forest types it inhabits, being compared to that of the dominant aboriginal species (See Table 5). As follows from the correlation analysis results, no one of the discussed invaders affects the projective cover of any of the native plant species in both protected areas significantly. Speaking of Amelanchier spicata, it is in fact far less aggressive than in the more southern areas of Central and Southern Russia where the species transforms forest communities actively and affects aboriginal field- and ground-layer plants negatively, even as far as to the extinction of some of the latter, as it is well-known from the literature on the subject. We are just at the beginning of the invasion process in the forests of the Russian North-West yet. The invasion of both species studied is likely to be connected with the climate change processes. The research reveals that a neglected adventive species, persisting long within a given area, may also suddenly become an aggressive invader (the case of Lonicera nigra). The invasion of adventive shrubs into the paludified forest communities, including those of the boreal peatmoss spruce forests which served as etalons of floristic stability quite recently, is also alarming.
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