Abstract

Hydrotechnical activities on the Slupia river above the town of Slupsk (northern Poland) were performed against floods in the valley. The results based on the data on fauna and flora gathered before (in 2003, T +0 ) and after (in T +2 , T +6 and T +11 ) the reclamation showed that the river canalization and oxbow lake dredging can significantly disturb the ecology of water bodies adjacent to the river. Observations of the oxbow lake (OLS5), showed the decrease in the number of macrophyte phytocenoses from 11 before the dredging to 6 very valuable Potametea phytocenoses , after wards. The development of common pleustonic phytocenoses of Lemnetea minoris and the massive development of green algae resulted from the bottom sediment removal. In the case of population, Stratiotes aloides was rebuilt after elimination during dredging already in T +2 . Before hydrotechnical works, the oxbow lake was characterized by 12 invertebrate taxa inhabiting S.aloides , whereas only 9 were found first period after the dredging, 15 taxa in second period and 23 in a recent study. During both observation periods, dominated by Chironomidae larvae (T +0 ), Trichoptera larvae (T +2 and T +6 ) and again Chironomidae larvae (T +11 ). The hydrotechnical activities significantly altered in the first period the structure of fauna and flora inhabiting the water body. Such radical interference in natural values of oxbow lakes is un-suitable for the preservation of ecosystems due to the significant decrease in their biodiversity. Achieved on a similar or higher level of macrophytes diversity and epiphytic invertebrates was noticeable ten years after the dredging of a water body.

Highlights

  • Oxbow lakes belong to those important aquatic ecosystems in floodplains which due to lentic character create suitable habitats for a significant number of macrophytes and invertebrates communities preferring stagnant water

  • Aquatic vegetation was studied twice, both before reclamation works in the period from April to July of 2003 (T+0) and after wards in the same months in 2005 (T+2), 2009 (T+6) and 2014 (T+11)

  • The dredged oxbow lake was characterized by 11 plant communities in T+0 (Tab. 1) and represented by 3 classes: Lemnetea minoris, Potametea and Phragmitetea

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Summary

Introduction

Oxbow lakes belong to those important aquatic ecosystems in floodplains which due to lentic character create suitable habitats for a significant number of macrophytes and invertebrates communities preferring stagnant water. Natural processes of succession in such water bodies lead to changes in the structure of fauna and flora. Immersed or floating macrophytes play a important role in intensively eutrophicated water body where anaerobic conditions at the bottom disable the existence of zoobenthos [6]. They become “a second bottom” inhabited willingly by oxybionts [7, 8]. Another important role of floating aquatic plants is delivery of food for aquatic fauna [9]

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