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Fish stocks of Lake Vesijaervi: from nuisance to flourishing fishery in 15 years

机译:维西耶尔维湖的鱼类种群:15年间从滋扰到繁荣的渔业

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摘要

Original goals of the biomanipulation project of Lake Vesijarvi, southern Finland, were to eliminate blooms of cyanobacteria and re-establish a sustainable fishery (Keto & Sammalkorpi 1988). From 1989-93, blooms of cyanobacteria were eliminated with mass removal of 1018 metric tons coarse fish, mainly roach (52 %), Rutilus rutilus (L.) and smelt (27 %), Osmerus eperlanus (L.), from the Enonselka basin (2600 ha, Horppila & Peltonen 1994, Horppila et al. 1996, 1998). Fishing with seine and fyke nets to remove 60-86 metric tons of coarse fish annually from 1994-96 prevented new increase of roach stock (Peltonen et al. 1999a). Additionally, large-scale stockings of predatory fish, especially pikeperch, Sander lucioperca (L.), were done in 1987-91 to increase predation on coarse fish and to improve the value of fish catches (Kairesalo et al. 1999). Stocked pikeperch established a population in Lake Vesijarvi and the first strong natural year-class hatched in 1992 (Peltonen et al. 1999b). An attempt to increase the predation on cyprinids in Lake Vesijarvi by stocking pikeperch (Keto & Sammalkorpi 1988) was not successful, because the most important prey fishes of pikeperch in Lake Vesijarvi are perch, Perca fluviatilis L., and smelt (Peltonen et al. 1996). Only big pikeperch ( > 1kg) can feed on adult ( > 12cm) roach living in pelagial of the lake. Effective subsistence fishing with 35-45 mm (bar length) gillnets, together with small recruitment size, kept numbers of big pikeperch and size of spawning stock very low (Kairesalo et al. 1999). To improve pikeperch catches and natural recruitment, fishery region of Lake Vesijarvi forbade fishing with gillnets of mesh sizes 22-49 mm (bar length) in the Enonselka basin from the beginning of 1997 (Suoraniemi et al. 2000). A new three-year period of intensive stocking of pikeperch fingerlings occurred in 1997-99. Half of stocked fingerlings were bigger than usual to determine if survival of stocked pikeperch can be im- proved by stocking fingerlings of size equal to natural ones (Ruuhijarvi & Salminen 2004). The objective of this study is to evaluate how management of fish stocks and fishery of Lake Vesijarvi from 1997-2003 has succeeded in fullfilling original goals of the restoration project. Successful biomanipulation from 1989—1993 and management to present date offer a unique long-term time series to assess how biomanipulated lakes react and how they should be managed after mass removal of coarse fish.
机译:芬兰南部维西耶尔维湖的生物操作项目的最初目标是消除蓝藻的繁殖并恢复可持续的渔业(Keto&Sammalkorpi 1988)。从1989-93年开始,通过从Enonselka大量去除1018公吨粗鱼,主要是蟑螂(52%),Rutilus rut​​ilus(L.)和冶炼(27%),Osmerus eperlanus(L.),消除了蓝藻的花开。盆地(2600公顷,Horppila&Peltonen 1994,Horppila et al。1996,1998)。从1994年至96年,每年使用围网和鱼叉网捕鱼以清除60至86吨粗鱼,从而阻止了蟑螂种群的新增加(Peltonen等,1999a)。此外,1987-91年进行了大规模的捕食性鱼类放养,特别是长鳍鲈,Sander lucioperca(L.),以增加对粗养鱼的捕食并提高渔获物的价值(Kairesalo等人,1999)。放养的鲈鱼在维西耶尔维湖建立了种群,并在1992年孵化出第一个自然年级强的种群(Peltonen等,1999b)。试图通过放养长鳍鲈来增加维西耶尔维湖的鲤鱼捕食的尝试(Keto&Sammalkorpi 1988)是不成功的,因为维西耶尔维湖中最重要的鲈鱼的猎物是鲈鱼,Perca fluviatilis L. 1996)。只有大鲈鱼(> 1kg)才能以生活在湖中的成年(> 12cm)蟑螂为食。使用35-45毫米(杆长)刺网进行有效的自给性捕捞,再加上较小的征募规模,使大型梭鲈的数量和产卵种群的数量保持在非常低的水平(Kairesalo等,1999)。为了改善鲈鱼的捕捞和自然捕捞,从1997年初开始,维西耶尔维湖湖渔业区禁止在Enonselka盆地使用网眼尺寸为22-49 mm(条长)的刺网捕鱼(Suoraniemi等,2000)。在1997-99年,开始了为期三年的密集放养鲈鱼鱼种的新时期。放养的鱼种有一半比平时大,可以确定放养大小等于自然鱼种的鱼种是否可以提高放养的鲈鱼的生存能力(Ruuhijarvi&Salminen 2004)。这项研究的目的是评估从1997年至2003年的Vesijarvi湖鱼类种群和渔业管理如何成功地实现了恢复项目的最初目标。从1989年至1993年成功进行生物操作以及目前的管理工作,提供了一个独特的长期时间序列,用于评估生物操作的湖泊如何反应以及大规模去除粗鱼后应如何管理。

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