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首页> 外文期刊>International association of theoretical and applied limnoloy >An investigation of macrophyte and macroinvertebrate communities in lowland sites on the rivers of Milltown (Muckno Mill) lake catchment, Co. Monaghan, Ireland
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An investigation of macrophyte and macroinvertebrate communities in lowland sites on the rivers of Milltown (Muckno Mill) lake catchment, Co. Monaghan, Ireland

机译:爱尔兰莫纳汉公司米尔敦(Muckno Mill)湖流域河流低地上的大型植物和大型无脊椎动物群落的调查

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摘要

The requirements of the Water Framework Directive (CEC 2000) have precipitated many national (Kelly-Quinn et al. 2005) and pan-European (Brabec & Szosz-kiewicz 2006) studies on the interactions between biological elements and physical and chemical water quality parameters. Kelly-Quinn et al. (2005) in a study with all sites of "high" ecological status, found that hardness and slope explained most of the variance in the 4 biological communities surveyed (macrophytes, macroinvertebrates, phytobenthos, fish). Ferreol et al. (2008) identified geographical position as a variable that influences macroinvertebrate species composition, as did Murphy & Davy-Bowker (2005) who also highlighted altitude. For macrophyte communities, Grasmuck et al. (1995) highlighted geology, while the STAR macrophyte project highlighted sampling period and shading (Brabec & Szoszkiewicz 2006). Macrophytes and macroinvertebrates are both used extensively to assess water quality, and when used together can provide a larger picture of water quality in a catchment (Caffrey 1987). Both communities, however, may be responding to different pressures (Kelly 1997). Both the macrophyte and macroinvertebrate water quality indices suggest that much of the Milltown Lake catchment is affected by eutrophication, but these indices disagree on which sites are most or least impacted (Wynne & Linnane 2007). In line with current research, our study employs appropriate multivariate statistics to explain variation in the sample communities. Because the study is restricted to one small catchment (34 km~2), variables such as hardness, altitude, geology, and geographical position will lack gradient when compared to the pan-European or national scales in those projects. Analyses were carried out to ascertain if the variance caused by water quality parameters associated with localised, anthropogenic factors could be more evident.
机译:《水框架指令》(CEC 2000)的要求催生了许多关于生物元素与物理和化学水质参数之间相互作用的国家(Kelly-Quinn等,2005)和泛欧洲(Brabec和Szosz-kiewicz 2006)的研究。 。 Kelly-Quinn等。 (2005年)在对所有处于“高”生态状态的地点进行的研究中,发现硬度和坡度解释了所调查的4个生物群落(宏观植物,大型无脊椎动物,植物底栖动物,鱼类)的大部分差异。 Ferreol等。 (2008)认为地理位置是影响大型无脊椎动物物种组成的变量,Murphy&Davy-Bowker(2005)也指出海拔高度。对于大型植物群落,Grasmuck等人。 (1995年)强调了地质学,而STAR大型植物项目强调了采样期和阴影(Brabec&Szoszkiewicz 2006)。大型植物和大型无脊椎动物都被广泛用于评估水质,当一起使用时,可以提供流域中更大的水质图景(Caffrey 1987)。但是,两个社区可能都在应对不同的压力(Kelly 1997)。大型植物和大型无脊椎动物的水质指数均表明,密尔敦湖流域的大部分地区都受到富营养化的影响,但这些指数在哪些地方受到的影响最大或最小(见Wynne&Linnane 2007)不一致。与当前的研究一致,我们的研究采用适当的多元统计数据来解释样本社区的变异。由于这项研究仅限于一个小流域(34 km〜2),因此与这些项目中的泛欧洲或国家规模相比,诸如硬度,海拔,地质和地理位置等变量将缺乏梯度。进行分析以确定由与局部人为因素相关的水质参数引起的方差是否更明显。

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