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Relationship between stonefly assemblages and riparian environment: case study in mountain stream in Japan

机译:Stonfly集中与河岸环境的关系:日本山区溪流案例研究

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Stream width, instream litter, and substrate conditions differ depending on the location along the stream and the season. Leaves in the upper stream riparian forest fall directly into the stream, become litter, and are broken down according to stream flow (VANNOTE et al. 1980, SWEENEY 1992, CHERGUI & PATTEE 1993, JOINSON & COVICH 1997). Input of detritus from riparian forest is essential for the conservation or restoration of many of the food webs in streams (WALLACE et al. 1997). Ben-thic invertebrate assemblages also differ depending on the lo-cation along the stream and the season. Abundance of shred-ding invertebrates decreases and that of scrapers and grazers increases according to stream flow (VANNOTE et al. 1980, MIN-SHALL et al. 1985, REED et al. 1994). The quantity and quality of riparian vegetation along streams affects instream alkalinity (KRUEGER & WATERS 1983), and the quality of nutrients in streams derived from riparian land influences larval growth (FIANCE 1978, MALLEY 1980, HAWKINS et al. 1982, RODGERS 1984). Water quality and assemblage of benthic invertebrate would be affected by surrounding land use. An understanding of variation in riparian landscapes may lead to a better interpretation of aquatic insect life cycles (REED et al. 1994, RICHARDS et al. 1996). Among typical aquatic insect groups of temperate regions (stoneflies, mayflies, and caddisflies), stoneflies tend to occu-py the cooler bodies of freshwater such as those in mountain-ous regions in western Japan. Additionally, most of the stone-flies are shredders or predators that are more abundant in the upper reaches. When the existence of stoneflies is strongly re-lated with the riparian landscape, stonefly assemblages might be different, depending on the surrounding land use, even in the upper reaches.
机译:流宽度,仪器垃圾和基板条件根据流沿流和季节的位置而不同。叶子在上游河岸森林秋天直接进入流,成为垃圾,并且根据流流细分(VANNOTE等,1980,1992年斯文,CHERGUI&PATTEE 1993,JOINSON&1997 COVICH)。来自河岸森林的碎屑的输入对于溪流中的许多食物网是必不可少的(华莱士等人1997)。本in-thic无脊椎动物组合也有所不同,这取决于沿着溪流和季节的焊接。丰富的碎片无脊椎动物减少,刮板和格拉塞尔的碎片流量(Vannote等人,Min-Call等,Min-Chat等1985,Reed等,1994)。沿着溪流的河流植被的数量和质量影响仪器碱度(Krueger&Waters 1983),以及来自河岸土地的猪群的质量影响幼虫增长(1978年,Malley 1980,Hawkins等,1982,Rodgers 1984)。底栖无脊椎动物的水质和组装将受到周围土地使用的影响。理解河岸景观的变化可能导致水生昆虫生命周期更好地解释(Reed等,1994,Richards等,1996)。在温带地区(石蝇,蝼蛄,和caddisflies)的典型的水生昆虫群,石蝇往往且发生-PY这种淡水冷却器机构那些在日本西部山区的OU地区。此外,大多数石头苍蝇都是粉碎剂或捕食者在上游更丰富。当用河岸景观而强烈重新定向石头花时,Theelfly组装可能是不同的,这取决于周围的土地使用,即使在上游。

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