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Japanese vs French Artificial Reefs: High Technology vs Design to Enhance Ecological Services

机译:日本与法国的人工鱼礁:高科技与设计相结合,以增强生态服务

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摘要

Artificial reefs (ARs) worldwide are mostly used for fish production or recreational purposes. In Japan, fishermen have known this concept since the Middle Ages. Historically, fishermen used artisanal structures hand-made with traditional and natural materials to improve coastal fisheries. Nowadays, high technology assemblages optimize the operational effectiveness of artificial reefs. In France, artificial reefs are not used at the same scale as in Japan (200:1) and have been deployed since 1968 with the main objective of enhancing coastal artisanal fishing. More than half of the ARs in France have been constructed over the last 15 years. With the deployment in 2007 / 2008 of more than 400 ARs within a 200 ha zone of the Bay of Marseille (Mediterranean, France), RECIF PRADO represents the largest AR system in the French Mediterranean Sea (27 300m~2). Over the last few years, in France, it has been public policy to promote the research and deployment of small ARs for environmental restoration. Generally, the enhancement of species or ecological functions is targeted with the aim of offsetting environmental degradation. For example, the earliest benthic larval stages, fish recruitment and algal assemblages could benefit from AR-based systems. As an illustration, we may consider the example of the increase in the recruitment of juveniles on artificial reefs at Marseille from 2011 to the end of 2015, using artificial and biological systems. Artificial systems consisted of floating ropes arranged on the top of the ARs. Biological systems involved the transplantation on ARs of living specimens of Cystoseira zosteroides C. Agardh (Phaeophyceae, Fucales), an ecosystem engineer species currently in decline in the Mediterranean Sea. A four-year in situ monitoring survey was carried out on and around these systems through censuses of fish juveniles and the study of the fate of C. zosteroides transplants using SCUBA diving. The recruitment of fish juveniles was multiplied by 4 to10 on both systems, compared to non-equipped ARs. The fish family most concerned was the Labridae. Cystoseira zosteroides transplants survived, grew and produced fertile receptacles. The efficacy of the artificial system decreased over time because of the fouling that altered the habitat availability for the juveniles. In contrast, the biological system remained effective and even increased in efficacy over time, due to the recruitment on the ARs of offspring born of the transplanted C. zosteroides. During 2014, ten different species of juveniles of fishes were observed on the AR equipped with biological systems. Improved efficacy of ARs in terms of fish stock is therefore possible through the addition of special systems designed to increase the fish recruitment. Biological systems would appear to be preferable to artificial ones, especially since they are more in phase with sustainable management as they are long-lasting and do not require maintenance.
机译:全世界的人工鱼礁(ARs)主要用于鱼类生产或娱乐目的。在日本,自中世纪以来,渔民就已经知道了这一概念。从历史上看,渔民使用手工制作的手工材料,这些手工材料是用传统和天然材料制成的,以改善沿海渔业。如今,高科技组合可优化人工鱼礁的运行效率。在法国,人工鱼礁的使用比例与日本(200:1)不同,自1968年以来就开始使用,目的是加强沿海手工捕鱼。在过去的15年中,法国一半以上的AR已建成。 RECIF PRADO于2007/2008年在马赛湾(法国地中海)200公顷区域内部署了400多个AR,代表了法国地中海最大的AR系统(27 300m〜2)。在过去的几年中,在法国,促进用于环境恢复的小型AR的研究和部署已成为公共政策。通常,针对物种或生态功能的增强以抵消环境退化为目标。例如,最早的底栖幼体阶段,鱼类募集和藻类组合可受益于基于AR的系统。作为示例,我们可以考虑使用人工和生物系统从2011年到2015年底在马赛增加对人工鱼礁的捕捞的例子。人工系统由布置在AR顶部的浮绳组成。生物系统涉及将Cystoseira zosteroides C. Agardh(藻科,富卡勒斯)的活体标本移植到ARs上,该物种目前在地中海沿岸衰退。通过对鱼类幼体的普查以及对使用SCUBA潜水进行的C.zosteroids移植的命运的研究,对这些系统及其周围进行了为期四年的现场监测。与未配备装备的AR相比,在这两个系统上鱼苗的招募都乘以4到10。最关心的鱼类是唇形科。 Cystoseira zosteroides移植存活,生长并产生了可育的容器。人工系统的功效随着时间的流逝而降低,这是因为结垢改变了少年的栖息地。相比之下,由于移植的类固醇类固醇的出生后代在AR上募集了生物系统,因此随着时间的推移,该生物系统仍然保持有效,甚至功效增强。 2014年,在配备生物系统的AR上观察到十种不同的鱼类幼鱼。因此,通过增加专门用于增加鱼类数量的特殊系统,可以提高ARs在鱼类种群方面的功效。生物系统似乎比人工系统更可取,尤其是因为它们与生命周期长并且不需要维护,因此与可持续管理更加协调。

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  • 来源
    《うみ》 |2016年第4期|112-112|共1页
  • 作者单位

    Aix-Marseille University, Mediterranean Institute of Oceanography (MIO), Universite de Toulon, CNRS/INSU, IRD, France;

    Aix-Marseille University, Mediterranean Institute of Oceanography (MIO), Universite de Toulon, CNRS/INSU, IRD, France;

    Aix-Marseille University, Mediterranean Institute of Oceanography (MIO), Universite de Toulon, CNRS/INSU, IRD, France;

    IFREMER, Centre Manche-Mer du Nord, Departement Ressources Biologiques et Environnement Unite Halieutique, France;

    Aix-Marseille University, Mediterranean Institute of Oceanography (MIO), Universite de Toulon, CNRS/INSU, IRD, France;

    Aix-Marseille University, Mediterranean Institute of Oceanography (MIO), Universite de Toulon, CNRS/INSU, IRD, France;

    Aix-Marseille University, Mediterranean Institute of Oceanography (MIO), Universite de Toulon, CNRS/INSU, IRD, France;

    National Fisheries University, Department of Fishery Science and Technology, Japan;

    Aix-Marseille University, Mediterranean Institute of Oceanography (MIO), Universite de Toulon, CNRS/INSU, IRD, France;

    Aix-Marseille University, Mediterranean Institute of Oceanography (MIO), Universite de Toulon, CNRS/INSU, IRD, France;

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