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A good understanding of how migratory animals use their habitat network is expected to provide important insights for the prediction of population dynamics at both local and regional scales. We focused on how the physical structure of a habitat network could affect fish migration between Lake Biwa and its tributary lagoons. Although the lagoons provide suitable breeding and nursery grounds for native fishes, it is a matter of concern that they can also be a hotbed of invasive exotic fishes. Here, we assessed the migration patterns of native crucian carps (Carassius spp.) and exotic largemouth bass (Micropterus salmoides) and bluegill sunfish (Lepomis macrochirus) using their carbon and nitrogen stable isotopes as migration tracers. As there were marked differences in the carbon isotope ratios of basal food webs between the main lake and its tributary lagoons, stable isotopic signatures of individual fishes collected from each lagoon enabled us to judge whether they were residents of the lagoon or recent immigrants from the main lake. The analysis revealed that native and invasive fishes showed different migration patterns across a variety of lagoons. Exotic fishes frequently immigrated from the main lake to the lagoon as the distance of the channel connecting these two habitats was short. For native crucian carps, in contrast, their migrations were unaffected by the channel distance but were promoted by narrow channels. Physical barriers of weirs and dense vegetation within the channel obstructed their migrations. Such ecological information on migration behavior will be vital to plan designs for habitat restoration to conserve native fishes.
A good understanding of how migratory animals use their habitat network is expected to provide important insights for the prediction of population dynamics at both local and regional scales. We focused on how the physical structure of a habitat network could affect fish migration between Lake Biwa and its tributary lagoons. Although the lagoons provide suitable breeding and nursery grounds for native fishes, it is a matter of concern that they can also be a hotbed of invasive exotic fishes. Here, we assessed the migration patterns of native crucian carps (Carassius spp.) and exotic largemouth bass (Micropterus salmoides) and bluegill sunfish (Lepomis macrochirus) using their carbon and nitrogen stable isotopes as migration tracers. As there were marked differences in the carbon isotope ratios of basal food webs between the main lake and its tributary lagoons, stable isotopic signatures of individual fishes collected from each lagoon enabled us to judge whether they were residents of the lagoon or recent immigrants from the main lake. The analysis revealed that native and invasive fishes showed different migration patterns across a variety of lagoons. Exotic fishes frequently immigrated from the main lake to the lagoon as the distance of the channel connecting these two habitats was short. For native crucian carps, in contrast, their migrations were unaffected by the channel distance but were promoted by narrow channels. Physical barriers of weirs and dense vegetation within the channel obstructed their migrations. Such ecological information on migration behavior will be vital to plan designs for habitat restoration to conserve native fishes.
As a part of our general effects to develop a technique to eliminate outside fish invading a dam reservoir, we examined for the appearance of fish in an artificial grass bed made of carbon fibre in the Nomura Dam reservoir of the Hiji River, Ehime Prefecture between April and November, 2005. During the experimental period, the water depth of the artificial grass bed site changed with movement by the wind of the driftwood fence attached and the dam operation in 3.2 m-11.9 m (an average of 7.9 m). Since no significant correlation was found between the movement of the artificial glass bed and the number of captured individual fishes, was little found, it was considered that there possibility that the movement of this artificial grass bed affected the amount of captured fish. A total of 10 species of 3 families in 2 orders of fishes representing 46,516 individual fish was caught during the experimental period, and most of the samples exhibited larva and juvenile stages (99.8 % of which were offspring and young fish). The number of individuals was high in early summer (7,361 fish at maximum), and no individuals appeared in the autumn to winter season. The number of collected specimens consisted of 59.9 % bluegill, Lepomis macrochirus, 34.1 % of lacustrine goby, Rhinogobius sp. OR, 5.5 % chub, Zacco platypus, 0.4 % of largemouth bass, Micropterus salmoides, and 0.1 % of other types of fish. The artificial grass bed in this study was considered to be an effective nursery ground of the early development stage of some fishes in the reservoir where a natural emergent plant belt and a natural submerged plant belt hardly developed. The artificial grass bed proved effective as a means to rid the waters of bluegill, Lepomis macrochirus. However, the issue remains regarding preventing the capture other of fishes together with them.
REVIEW Japan Abstract: The majority of published papers in ECE were relating to aquatic ecosystems and written by university and or institute members. Other fields such as terrestrial or coastal ecosystems should be more focused, and consultant and government employee should be encouraged to submit their case studies. As a philosophy and a target of ECE, interdependence between ecology and civil engineering, holistic view of environment, target for restoration, and ecological health were discussed. At investigation and planning stage, life history trait, habitat condition, disturbance, material cycle, interactions between organisms were examined. The focus should be given to the key habitat corresponding to the key lifestage such as reproduction stage. IBI, RHS and habitat evaluation by GIS were introduced and other multivariate statistical analyses were employed. I believe that evaluation of ecosystem health in a broad scale is an important theme to build effective conservation or restoration plan. At the implementation stage, I doubt the necessity to draw the detail design of engineering structures, rather I feel it produce great mischief. Design with nature or passive restoration should be the first priority. The studies on this stage were very few, probably because evaluation of engineering works was not planned before implementation, and evaluation has not been fulfilled. Thus, at monitoring and evaluation stage, Before-AfterReference -Control-Impact design were recommended, and critical lines to refine or improve management plan and engineering works should be presented before implementation.
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