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Evolution of wild and feral vines from the Ega river gallery forest (Basque country and Navarra, Spain) from 1995 to 2015

机译:1995年至2015年,埃加河画廊森林(巴斯克人和西班牙纳瓦拉)野生藤蔓和野生藤蔓的演变

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Aims: The present paper is focused on wild and feral grapevines from the Ega River gallery forest (Alder grove), one of the most important tributaries of the Ebro River. Since this area was preliminary prospected in 1995, it was our intention to assess the evolution of the ecosystem during this time.Methods and results: Ampelographic description of wild grapevines shows that all male plants had flowers with fully developed stamens and no gynoecium. No hermaphrodite individuals were detected. No virus infection and symptoms caused by Phylloxera on roots were detected. The Erineum strain of Colomerus vitis constitutes the main phytophagous arthropod. Damages caused by powdery and downy mildew were not lethal for the vines. Around 73% of the wild grapevine individuals found in 1995 had disappeared due to human impacts. The number of rootstocks and producer hybrids (French hybrids) had increased in this period by about 30%. Microvinification of wild berries yielded a wine with very high color intensity and total polyphenol index with a low pH.Conclusion: The wild grapevine population described has suffered a dramatic regression in the 20-year period between prospections, together with a significant increase of feral accessions thus endangering the endurance of the ecosystem and remaining wild grapevine.Significance and impact of the study?: Wild grapevines are a valuable genetic resource for the genetic improvement of cultivated vines. However, our study shows that human impacts and increasing pressure of feral accessions are threatening wild grapevine populations. IntroductionThe only Eurasian wild grapevine, Vitis vinifera L. subsp. sylvestris (Gmelin) Hegi, is considered an endangered subspecies in Europe (Di Vecchi-Staraz et al., 2009; Bodor et al., 2010). This is due to diverse anthropic impacts on natural habitats, like the exploitation of river-banks, public works, the infestation of downy and powdery mildew as well as the introduction of invasive vines, such as American rootstocks and producer hybrids used as a cultural method to prevent phylloxera infestation from the 19th century (Issler, 1938; Arnold, 2002; Ocete et al., 2007; Iriarte-Chiapusso et al., 2013).During the COST Action FA-1003 East-West Collaboration for Grapevine Diversity Exploration and Mobilization of Adaptive Traits for Breeding, developed between 2011 and 2014 (http://www.cost.eu/COST_Actions/fa/FA1003), the objectives were to increase the knowledge on wild grapevine populations by studying its ampelography, genetic pool, sanitary status, and enological characteristics. One of the main targets was to find some vines with potential resistance to pest and diseases, mainly to downy and powdery mildew.However, current viticulture is affected by an alarming genetic erosion process (This et al., 2001; González-Moreno et al., 2004; Esquinas-Alcázar, 2005; Gago et al., 2009) in the framework of climatic warming and markets globalization (Mira de Ordu?a, 2010; Mozell and Thach, 2014). In modern vineyards there are only a small number of clones with sanitary passport of the cultivars allowed within each Guarantee of Origin, so the genetic pool is declining alarmingly. Global warming will result in loss of acidity and color and together with globalization and open borders will increase the risk of introducing new pests and diseases, which might spread easily in vineyards with low genetic diversity. Due to those facts, Eurasian wild grapevine constitutes a useful phytogenetic resource to be used in breeding of cultivars and rootstocks for those new requirements, previously mentioned (Jones et al., 2005; Ocete et al., 2007; Popescu et al., 2013). On the other hand, this liana had important uses in the past (Ocete et al., 2011c) and nowadays it constitutes a relic element of river-bank forests, colluvial positions and coastal cliffs (Arnold, 2002).According to that idea, our attention was focused on Ega River, a tributary of Ebro River, situated in Northern Spain, because it conserves an extensive riparian vegetation with some disseminated population sites of wild grapevine, as it was shown in a preliminary prospection carried out by Ocete and Pérez (1995). The source of this river is located in álava province (Basque Country) south of the Cantabrian Mountain-Range, its length is 113 km, the average flow is 13.76 m3/s, draining an area of 1,497 km2 (fig. 1). Other plant populations within the Ebro River basin have been described previously (Martínez De Toda and Sancha, 1999; Ocete et al., 2003; Ocete et al., 2011b)SaveView full sizeExpand inlineCollapse inline Figure 1. Localization of Ega River. The aim of the present paper was to compare the number of wild vines registered in 1995 with those sampled in 2014 and to denounce the lack of a specific legislation for the conservation of this endangered taxon in the Iberian Peninsula. Also, to complete the description of the characteristics of their habitats according to associated plant communities,
机译:目的:本文重点研究埃加河最重要的支流之一埃加河画廊森林(奥尔德格罗夫)的野生和野生葡萄树。自1995年对该地区进行初步勘探以来,我们打算评估这段时间中的生态系统的演变。方法和结果:对野生葡萄树进行的传记记录显示,所有雄性植物的花都具有完全发育的雄蕊,没有雌蕊。没有检测到雌雄同体个体。未检测到根部有疫菌引起的病毒感染和症状。葡萄球菌的Erineum菌株是主要的植物吞噬节肢动物。由白粉病和霜霉病引起的损害对葡萄树没有致死性。 1995年发现的野生葡萄个体中约有73%由于人类影响而消失了。在此期间,砧木和生产者杂种(法国杂种)的数量增加了约30%。对野生浆果的微酿造产生了一种具有极高的颜色强度和低pH值的总多酚指数的葡萄酒。结论:所描述的野生葡萄种群在两次勘探之间的20年间经历了显着的退化,同时野生品种的数量也显着增加。研究的意义和影响?:野生葡萄藤是栽培葡萄遗传改良的宝贵遗传资源。但是,我们的研究表明,人类的影响和野生登录物的压力不断增加,正在威胁野生葡萄种群。简介唯一的欧亚野生葡萄Vitis vinifera L. subsp。樟子松(Gmelin)Hegi,在欧洲被认为是濒临灭绝的亚种(Di Vecchi-Staraz等,2009; Bodor等,2010)。这是由于人类对自然栖息地的各种影响,例如对河岸的开采,公共工程,霜霉病和白粉病的侵袭以及入侵性藤蔓的引入,例如美国砧木和作为生产方法的杂交种COST行动FA-1003东西方合作促进葡萄多样性的探索和发展,以防止19世纪以来的根腐病侵袭(Issler,1938; Arnold,2002; Ocete等,2007; Iriarte-Chiapusso等,2013)。动员适应性育种特性,于2011年至2014年期间进行(http://www.cost.eu/COST_Actions/fa/FA1003),其目标是通过研究其葡萄柚图谱,遗传库,卫生状况来增加对野生葡萄种群的了解。状况和生态特征。主要目标之一是找到一些对病虫害具有潜在抵抗力的藤本植物,主要​​是对霜霉病和白粉病的抵抗力。然而,目前的葡萄栽培受到令人震惊的遗传侵蚀过程的影响(This et al。,2001;González-Morenoet al。 (2004年;Esquinas-Alcázar,2005年; Gago等人,2009年),以气候变暖和市场全球化为框架(Mira de Ordu?a,2010年; Mozell和Thach,2014年)。在现代葡萄园中,每个原产地保证中只有少数几个带有栽培品种卫生护照的克隆,因此,基因库的下降令人震惊。全球变暖将导致酸度和颜色的损失,并且随着全球化和边界的开放将增加引入新的病虫害的风险,这些病虫害很容易在遗传多样性低的葡萄园中传播。由于这些事实,欧亚野生葡萄树构成了有用的植物遗传资源,可用于满足这些新要求的品种和砧木的育种,如前所述(Jones等,2005; Ocete等,2007; Popescu等,2013)。 )。另一方面,这种藤本植物在过去有重要用途(Ocete等人,2011c),如今已成为河岸森林,河流位置和沿海悬崖的遗迹元素(Arnold,2002)。我们的注意力集中在西班牙北部埃布罗河的支流埃加河上,因为它保护着广泛的河岸植被,并散布着一些野生的葡萄树种群,这是由Ocete和Pérez进行的初步勘探显示的( 1995)。这条河的源头位于坎塔布连山脉范围以南的阿拉瓦省(巴斯克地区),其长度为113公里,平均流量为13.76立方米/秒,排水面积为1,497平方公里(图1)。先前已经描述了埃布罗河流域内的其他植物种群(MartínezDe Toda和Sancha,1999; Ocete等人,2003; Ocete等人,2011b)SaveView full sizeExpand inlineCollapse inline图1. Ega River的本地化。本文的目的是将1995年注册的野生藤蔓数量与2014年抽样的野生藤蔓进行比较,并谴责缺乏保护伊比利亚半岛这一濒临灭绝的分类单元的具体立法。另外,为了根据相关的植物群落完整描述其栖息地的特征,

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