首页> 外文期刊>Knowledge and Management of Aquatic Ecosystems >CAN AUSTROPOTAMOBIUS ITALICUS MERIDIONALIS BE USED AS A MONITORING INSTRUMENT IN CENTRAL ITALY? PRELIMINARY OBSERVATIONS
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CAN AUSTROPOTAMOBIUS ITALICUS MERIDIONALIS BE USED AS A MONITORING INSTRUMENT IN CENTRAL ITALY? PRELIMINARY OBSERVATIONS

机译:可以在意大利中部使用子午夜澳大利亚子午线监视工具吗?初步观察

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Attributing the term bioindicator to a species complex such as Austropotamobius pallipes is complicated, considering that the meaning given to a bioindicator can vary according to the geographic position, and that A. pallipes species complex has been divided into 2 species and 5 subspecies, the possibility of using A. i. meridionalis as a bioindicator in watercourses of Central Italy was evaluated. To this end, we analysed the structure and abundance of a number of crayfish populations and then compared them to the water quality of the corresponding watercourses, using E.B.I. (Extended Biotic Index). This index provides information on water quality through an analysis of the macrobenthos community. The watercourses are assigned to various classes (from I to V, increasing the degrees of alteration). This study was carried out in several watercourses near Rome. The abundance of crayfish was found to be greatest in those tracts that are assessed as class I, where the populations seem well structured with individuals of various sizes and the sex ratio is approximately 1:1. In contrast, in class II we found a reduced presence of specimens, mostly in bad conditions. No crayfish specimens were observed in watercourses designated as class III. In light of these preliminary results, it does not seem possible to consider A. i. meridionalis as a bioindicator, given that one of the typical characteristics of a biological indicator (wide distribution) is not met. Though these results illustrate the possibility of using A. i. meridionalis populations as an excellent monitoring instrument in Central Italy.
机译:鉴于将生物指示剂的含义根据地理位置而定,并且将生物指示剂分为两种和5个亚种,因此将术语生物指示剂赋予物种复合物(例如南洋猿)很复杂。使用A.对意大利中部水道中作为生物指示剂的子午线进行了评估。为此,我们使用E.B.I.分析了许多小龙虾种群的结构和丰富度,然后将它们与相应河道的水质进行了比较。 (扩展的生物指数)。该指数通过对大型底栖动物群落的分析来提供有关水质的信息。河道分为不同的等级(从I到V,增加了变更的程度)。这项研究是在罗马附近的几个水道中进行的。发现小龙虾的丰度在被评估为I类的那些区域中最大,那里的种群似乎结构合理,大小不一的个体,性别比约为1:1。相反,在II类中,我们发现减少了标本的存在,主要是在恶劣条件下。在指定为III类的水道中未观察到小龙虾标本。根据这些初步结果,似乎不可能考虑A。子午线作为生物指示剂,因为没有满足生物指示剂的典型特征之一(广泛分布)。尽管这些结果说明了使用A. i。的可能性。子午线人口是意大利中部的优秀监测工具。

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