Abstract:A pronounced pollution of surface water bodies in the Western Bug River Basin, Ukraine, has been caused by outdated or overloaded wastewater treatment plants, agriculture, industry and coal mining. These pressures have led to a generally poor state of both chemical and microbiological variables creating health risks of various kinds. The state of surface water quality for the Western Bug and five main tributaries was assessed by measuring physical, chemical and microbiological indicators during field campaigns… Show more
“…While showing a good morphological quality (Scheifhacken et al 2011), the river is strongly polluted with inputs from agriculture, industry, urban areas and mining activities Delfs et al 2011;Ertel et al 2011;Tavares Wahren et al 2011). Two general research questions are (1) can the lessons learned from the newly formed German states be useful for improving the water quality in the Bug Area and (2) what are the consequences for the implementation of the EU Water Framework Directive as the Bug River crosses the EU border.…”
“…While showing a good morphological quality (Scheifhacken et al 2011), the river is strongly polluted with inputs from agriculture, industry, urban areas and mining activities Delfs et al 2011;Ertel et al 2011;Tavares Wahren et al 2011). Two general research questions are (1) can the lessons learned from the newly formed German states be useful for improving the water quality in the Bug Area and (2) what are the consequences for the implementation of the EU Water Framework Directive as the Bug River crosses the EU border.…”
“…Point sources such as overburdened or obsolete urban waste water treatment plants as well as industrial activities (mining, pesticide deposits) are often responsible for high pollution loads (Ertel et al 2011), but also diffuse agricultural inputs contribute to pollution (Ertel et al 2011;Malynovsky et al 2007).…”
Section: Introductionmentioning
confidence: 99%
“…In this context, the Western Bug River basin was chosen as an example for a medium sized river basin facing a crucial pollution load already in its headwaters and thereafter affecting both the Ukrainian as well as EU branches of the river basin in varying dimensions (Ertel et al 2011;Yanko 2008;Tacis 2001Tacis , 2006. The Ukrainian catchment of the Western Bug contains several important point source polluters in the vicinity of the river or its tributaries (Ertel et al 2011).…”
Section: Introductionmentioning
confidence: 99%
“…The Ukrainian catchment of the Western Bug contains several important point source polluters in the vicinity of the river or its tributaries (Ertel et al 2011). The monitoring efforts remain restricted solely to water quality problems and primarily focussed on point source polluters (Tacis 2001(Tacis , 2006.…”
Section: Introductionmentioning
confidence: 99%
“…In conjoint studies aspects of water quality problems (Ertel et al 2011), data scarcity in the modelling of climate projections , sewer systems (Blumensaat et al 2011) and soil distributions (Tavares et al 2011) are analysed. Moreover, comprehensive work is related to the methodology for dealing with regional changes (Schanze et al 2011) or capacity development within the model region (Leidel et al 2011).…”
Recently, the Ukrainian Western Bug water authorities developed a national field survey to assess the quality of river habitats. The Ukrainian government already cooperates with EU member states along transboundary rivers and also orientates itself towards the European Water Framework Directive (WFD). As a future application for EU membership is feasible, the water authorities started to implement WFD criteria into their national survey schemes including the assessment of rivers' hydromorphology. This article compares two different hydromorphological survey methods to identify similarities and differences of the classification approaches with regard to the conformity of obtained outputs with the WFD demands. The field surveys, the Ukrainian (UA-FS) and the German (LAWA-FS), were applied in parallel on 14 river sections along the Western Bug River and parts of its tributaries. Results show a wide range of conformity, but also several differences between and gaps within all methods. The UA-FS generally lacks the idea of reference condition in rivers' hydromorphology and the definition of different stream types or near-natural land uses. The UA-FS and the LAWA-FS approaches are similar with respect to their incorporated compartments and most main parameters, but differ in definition and interpretation of specific functional units and single parameters. Greatest similarities down to single parameters exist in aspects of land use, bank vegetation, currents diversity, and within-stream variation of water depths. Differences include the assessment and interpretation of lateral erosion, sinuosity, type and depth of profile, substrate diversity, as well as special structures of bank and riverbed. Overall, the LAWA-FS is more conservative in its rating than the UA-FS. Still, UA-FS can be regarded as an important improvement for a systematic and reliable monitoring of river hydromorphology in the Ukraine that will help to successfully engage with both the integrated water resources management and the WFD harmonisation process in the future.
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