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Exemplarily selected results of the PCR – DGGE analysis covering 768km of the upstream section of the German (lane numbers 1, 2, 3, 4, 6) Austrian (lane numbers 7 –15) and Slovakian (16 – 21) River Danube JDS 2001 sampling stations (from km2580 to km1812). Lanes 5,13,16 are tributaries (see below for details). Lane 41 is given as an “outgroup” band pattern of the given upstream sequences, representing a downstream location at km1533. Given DGGE band patterns of the analysed sampling locations are a result of the encountered bacterial 328 

Exemplarily selected results of the PCR – DGGE analysis covering 768km of the upstream section of the German (lane numbers 1, 2, 3, 4, 6) Austrian (lane numbers 7 –15) and Slovakian (16 – 21) River Danube JDS 2001 sampling stations (from km2580 to km1812). Lanes 5,13,16 are tributaries (see below for details). Lane 41 is given as an “outgroup” band pattern of the given upstream sequences, representing a downstream location at km1533. Given DGGE band patterns of the analysed sampling locations are a result of the encountered bacterial 328 

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Context 1
... methodical details are given in Winter et al. (2006) Results During the JDS 2001, all 98 filtrations of 50ml to 150ml of River Danube water followed by DNA extraction and PCR -DGGE analysis resulted in complex and well focused 16S rRNA gene DGGE band patterns (c.f. Fig.1). Apparent bacterial richness (i.e. ...
Context 2
... to the number of observable DGGE bands. 1, 2, 3, 4, 6) Austrian (lane numbers 7 -15) and Slovakian (16 -21) River Danube JDS 2001 sampling stations (from km2580 to km1812). Lanes 5,13,16 are tributaries (see below for details). ...
Context 3
... bacterioplankton including taxa of Cyanobacteria, α-, β-, γ-Proteobacteria, Cytophaga - Flavobacterium -Bacteroides group and Actinobacteria. Analysis of the longitudinal development of the DGGE profiles in the River Danube during the JDS 2001 indicated that the bacterial community developed gradually over the studied distance of over 2500km (see Fig. 1 bands 1-24 as selected example of the gradual development of the upstream sections km2580 to km1812). The similarity of the bacterial communities related to the first sampling station decreased with increasing distance and the Jaccard dissimilarity index ranged from approximately 0,25 (2412 km) to 0,65 (12 km). However, the gradual ...

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Fecal microbial pollution is a major problem throughout the Danube River Basin, posing a threat to various types of water use, including drinking water production from river bank filtrates, water supply for agricultural and industrial use, and the role of the river as a recreational space. Fecal microbial pollution is introduced into the river by point sources, such as discharges of treated or untreated sewage from human sources or livestock, and by nonpoint sources, such as urban and agricultural runoff. In addition, fecal input from wildlife may be of importance in specific regions. Despite huge efforts to improve wastewater management in the past decade, in many sections, the river and its tributaries exhibit very high levels of fecal microbial pollution. To assess microbiological water quality, indicators of fecal pollution are used as surrogates for the potential presence of intestinal pathogens. However, the standard indicators cannot provide any reliable information regarding the origin of fecal pollution, nor can their concentration levels be directly related to human health risks for many types of exposure and situations.