山地水鼠(Arvicola scherman)在西班牙西北部作为农作物害虫的作用:从什么时候开始?

A. Somoano
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Additionally, vegetation is covered by earth mounds because of its activity, which interferes with farming practices (Meylan 1977). It was as a result of first records of A. scherman in NW Spain when agricultural damages produced by this species were well described (García-Dory 1974, Noval 1976, 1981, Nores 1986). The first study on A. terrestris (read A. scherman) reported its presence in the Cantabrian Mountain range (Niethammer 1964). Shortly after, a study of barn owl (Tyto alba) pellets from Picos de Europa (Heim de Balsac & Beaufort1 969) verified the existence of established populations of this species in Asturias, Cantabria and Galicia. By the same methodology, A. scherman was revealed to occur in a relatively wide distribution in Asturias (Braña 1974, Nores 1989). Also in 1970s, Garzón-Heydt et al. (1971) and Gosálbez (1976) detected this species in mountains of Los Ancares (Galicia) and in southern Cantabrian Mountain range (Castilla y León) respectively. However, it could be probably that crop damages caused by A. scherman in Cantabrian mountain range had been historically well-known by farmers before the species was described (García-Dory 1974). The presence of montane water voles in the NW Iberian Peninsula goes back to the Mousterian (Middle Palaeolithic, about 39,110 years BP) as showed the dentitions of several specimens found in Cueva del Conde, an archaeo-palaeontological deposit located in Asturias (Lopez-García et al. 2011). In Upper Paleolithic, this species seemed to be present along NW coastal Spain, from Donostia to at least Oviedo (García-Ibaibarriaga et al. 2013). Nevertheless, there seems to be no information on agricultural damages caused by montane water voles until the beginning of the XVII-century. In that sense, the first reported case encountered to date which suggests crop losses arguably caused by montane water voles occurred in uplands from Villaviciosa (Asturias) between 1616 and 1622 (Fig. 1). 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引用次数: 3

摘要

61山地水鼠Arvicola scherman (Shaw, 1801)主要栖息于欧洲主要山区的草甸、草地和果园(Giraudoux et al. 1997, FichetCalvet et al. 2000) (Kryštufek et al. 2015,参考文献)。该物种生活在地下广泛的洞穴系统中(Airoldi 1976),消耗植物的后生和后生部分(Airoldi 1976, Kopp 1993)。由于其相对较高的能量需求,每个人每天应该摄入相当于其体重的食物(qu2013.09)。因此,可能会对草地、果园(苹果、樱桃、李子和梨树)(Meylan 1977, Somoano et al. 2016)和一年生作物(Braña 2001)造成重大损害,但也可能对猕猴桃树和草青贮物造成损害(Somoano 2017)。此外,植被因其活动而被土丘覆盖,这干扰了耕作方式(Meylan 1977)。这是由于在西班牙西北部首次记录到该物种造成的农业危害得到了很好的描述(García-Dory 1974, Noval 1976, 1981, Nores 1986)。第一个关于A. terrestris(阅读A. scherman)的研究报告了它在坎塔布连山脉的存在(Niethammer 1964)。不久之后,对来自Picos de Europa (Heim de Balsac & Beaufort1 969)的仓鸮(Tyto alba)颗粒的研究证实了该物种在阿斯图里亚斯,坎塔布里亚和加利西亚的既定种群的存在。通过同样的方法,发现a . scherman在阿斯图里亚斯的分布相对广泛(Braña 1974, Nores 1989)。同样在20世纪70年代,Garzón-Heydt et al.(1971)和Gosálbez(1976)分别在Los Ancares(加利西亚)山脉和Cantabrian山脉南部(Castilla y León)发现了该物种。然而,可能在该物种被描述之前,坎塔布连山脉的农民就已经知道了A. scherman对作物造成的损害(García-Dory 1974)。根据在Cueva del Conde(位于阿斯图里亚斯的考古古生物沉积物)发现的几个标本的牙列,伊比利亚半岛西北部山地水田鼠的存在可以追溯到莫斯特纪(旧石器时代中期,约39,110年前)(Lopez-García et al. 2011)。在旧石器时代晚期,这个物种似乎出现在西班牙西北沿海,从多诺斯蒂亚到至少奥维耶多(García-Ibaibarriaga et al. 2013)。然而,直到十七世纪初,似乎没有关于山地水鼠对农业造成损害的资料。从这个意义上说,迄今为止遇到的第一个报告病例表明,在1616年至1622年之间,可能是山区水鼠造成的作物损失发生在Villaviciosa(阿斯图里亚斯)的高地上(图1)。作者Gaspar de Villarroel(1738)提到,过量的老鼠砍伐了果树和作物,给农民带来了负面后果。值得注意的是,保护措施远非采用人口控制措施,而是在神职人员的指导下完成的,维护了老鼠作为上帝动物的权利。自史前以来,该地理区域的农业活动发展将推动草甸取代落叶林(Díaz-Maroto 2009),而大多数天然草地仅限于高地地区。山地水鼠(Arvicola scherman)在西班牙西北部作为作物害虫的作用:从什么时候开始?
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The role of the montane water vole (Arvicola scherman) as a crop pest in NW Spain: since when?
61 The montane water vole, Arvicola scherman (Shaw, 1801), mainly inhabits meadows, grasslands and fruit orchards (Giraudoux et al. 1997, FichetCalvet et al. 2000) of the main mountainous areas of Europe (Kryštufek et al. 2015 and reference therein). This species lives underground in extensive burrow systems (Airoldi 1976), consuming both epigeic and hipogeic parts of plants (Airoldi 1976, Kopp 1993). Due to its relatively high energy demand, each individual should daily ingest the equivalent of its body mass in food (Quéré 2009). As a consequence, important damage to grasslands, fruit orchards (apple, cherry, plum and pear trees) (Meylan 1977, Somoano et al. 2016) and annual crops (Braña 2001) can occur, but also damages to kiwi trees and grass silages may be observed (Somoano 2017). Additionally, vegetation is covered by earth mounds because of its activity, which interferes with farming practices (Meylan 1977). It was as a result of first records of A. scherman in NW Spain when agricultural damages produced by this species were well described (García-Dory 1974, Noval 1976, 1981, Nores 1986). The first study on A. terrestris (read A. scherman) reported its presence in the Cantabrian Mountain range (Niethammer 1964). Shortly after, a study of barn owl (Tyto alba) pellets from Picos de Europa (Heim de Balsac & Beaufort1 969) verified the existence of established populations of this species in Asturias, Cantabria and Galicia. By the same methodology, A. scherman was revealed to occur in a relatively wide distribution in Asturias (Braña 1974, Nores 1989). Also in 1970s, Garzón-Heydt et al. (1971) and Gosálbez (1976) detected this species in mountains of Los Ancares (Galicia) and in southern Cantabrian Mountain range (Castilla y León) respectively. However, it could be probably that crop damages caused by A. scherman in Cantabrian mountain range had been historically well-known by farmers before the species was described (García-Dory 1974). The presence of montane water voles in the NW Iberian Peninsula goes back to the Mousterian (Middle Palaeolithic, about 39,110 years BP) as showed the dentitions of several specimens found in Cueva del Conde, an archaeo-palaeontological deposit located in Asturias (Lopez-García et al. 2011). In Upper Paleolithic, this species seemed to be present along NW coastal Spain, from Donostia to at least Oviedo (García-Ibaibarriaga et al. 2013). Nevertheless, there seems to be no information on agricultural damages caused by montane water voles until the beginning of the XVII-century. In that sense, the first reported case encountered to date which suggests crop losses arguably caused by montane water voles occurred in uplands from Villaviciosa (Asturias) between 1616 and 1622 (Fig. 1). The author, Gaspar de Villarroel (1738), mentioned an overabundance of mice that cut down the fruit trees and crops, with negative consequences for farmers. It is worth noting that, far from applying demographic control practices, protective measures were accomplished under the guidelines of clergy, upholding mice rights as animals of God. The agricultural activity developed since prehistory in this geographic area would have propelled the substitution of deciduous forests by meadows (Díaz-Maroto 2009), whereas most natural grasslands were restricted to elevated areas The role of the montane water vole (Arvicola scherman) as a crop pest in NW Spain: since when?
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