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國立臺灣大學生物資源暨農學院實驗林研究報告

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篇名 日本魚附林和臺灣漁業保安林
卷期 31:4
並列篇名 The Fishery Protection Forest in Japan and Taiwan
作者 陳財輝李宗宜汪大雄
頁次 265-274
關鍵字 漁業保安林(魚附林)保安林復育Fishery protection forestProtection forestRecovery
出刊日期 201712

中文摘要

日本魚附林是為了誘集和保護目的,在海岸、湖岸、河岸等處所種植林木,營造 魚類喜好棲息陰暗之處所。臺灣保安林制度,源自1901年日治時期臺灣總督府頒布府令第 十號「臺灣保安林規則」,做為保安林指定編定及林野保護取缔管理之依據,至1944年 時,總計編入484處保安林,面積達374,944 ha。2015年林務局依據森林法第22條規定,編 定為海岸保安林有防風林、潮害防備林、飛砂防止林及漁業林等4種。臺灣最早的漁業保 安林編制是屬1908年(明治41年)3月3日屏東縣琉球鄉編入之第2411及2412號漁業保安林, 其目的是維持附近海岸漁業經營。之後漁業保安林陸續增加,目前全臺漁業保安林共有 25個,面積共計4,748 ha,主要分佈於宜籣縣烏石鼻附近沿岸以及屏東縣沿海一帶。有鑑於 臺灣沿海漁業資源日益減少,漁業保安林的功能更顯重要,同時參考日本農林水產省生物 多樣性戰略下,藉著森、川、海的連結來保護里山、里海的生物多樣性,且積極推行魚附 林(同漁業保安林)的復育工作。本文從日本魚附林的觀念介紹解說森林、河川及海洋的關 係,並說明臺灣漁業保安林之分布及現況,最後以臺灣東北角王銘祥教練等軟絲復育的例 子進行說明,雖無自然河川等生態系連結,藉著人為辅助作業也可發揮魚附林功能之作法 等,期望喚起大家對於魚附林及海洋資源的重視及保護。

英文摘要

Fishery protection forests were established for the sake of providing a suitable environment for fishes by planting trees along river bank, lake side and seacoast. The protection forest system in Taiwan was traced back to the Japanese colonial periods. In 1901, based on the Order No 10「Taiwan Protection Forest Regulations」promulgated by the Taiwan Viceroy Authority, it was installed as the basis for management of protection forests. In 1944, the number of places assigned as protection forests has reached to 484 with the total area of 374,944 ha in Taiwan. In 2015, under the Forest Law, four types of protection forest such as windbreak forest, damp prevention forest, sandy conservation forest, and fishery forest were installed in coastal area. The first two protection forests assigned as fishery protection forests in Taiwan in 1908 were named No. 2411 and 2412 fishery protection forest located in Liuchiu Township in Pingtung County for the sake of nearby fishery management. At present, 25 places of fishery protection forests which majorly distribute in the coastal area along I-land and Pingtung County were available in Taiwan. Owing to the gradual decrease of fishery resources in the coastal area, the function of fishery protection forests in Taiwan becomes more important. Therefore, it is essential to enhance the recovery of fishery protection forests via integration of biodiversity protections in forest, river and ocean. In this paper, using fishery protection forest in Japan as an example, we illustrated the relationships among forests, rivers and oceans, and the status of fishery protection forests in Taiwan. Finally, through the case of recovery bigfin reef squid (Sepioteuthis lessoniana) in the norhteast area in Taiwan, It is hoped to raise public awareness of fishery protection forests and enhance protection of surrounding ocean resources.

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