Difference between revisions of "Regelsbrunner Aue"

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(Introduction)
(Introduction)
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==Introduction==
 
==Introduction==
The goal of the ‘Danube Restoration Project’ is to gradually restore hydrological connectivity and
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<p>"The goal of the ‘Danube Restoration Project’ is to gradually restore hydrological connectivity and
ecological integrity between the river and its floodplain in a segment of the Austrian Danube <ref>Schiemer,
+
ecological integrity between the river and its floodplain in a segment of the Austrian Danube. In order to test the effectiveness and success of this large-scale pilot project, a long-term evaluation program has been implemented, which includes abiotic, biotic and functional components. The biotic ‘functional describers’ include macrophytes, molluscs, odonates, amphibians, fish and benthic invertebrates. In the present analysis, the first four of these groups are focused upon, because sampling strategies for fish and benthic invertebrates are not compatible with the other groups." (Tockner et al., 1999 <ref>K. TOCKNERa,*, F. SCHIEMERb, C. BAUMGARTNERb, G. KUMc, E. WEIGANDb,
1995</ref> <ref>Tockner and Schiemer, 1997</ref>. In order to test the effectiveness and success of this large-scale pilot
+
I. ZWEIMU8 LLERb AND J.V. WARDa 1999.THE DANUBE RESTORATION PROJECT: SPECIES DIVERSITY PATTERNS ACROSS CONNECTIVITY GRADIENTS IN THE FLOODPLAIN SYSTEM. REGULATED RIVERS: RESEARCH & MANAGEMENT)
project, a long-term evaluation program has been implemented, which includes abiotic, biotic and
+
K. TOCKNERa,*, F. SCHIEMERb, C. BAUMGARTNERb, G. KUMc, E. WEIGANDb,
functional components <ref>Hein et al., 1999</ref> <ref>Schiemer et al., in press </ref>. The biotic ‘functional describers’
+
I. ZWEIMU8 LLERb AND J.V. WARDa
(sensu Castella et al., 1984) include macrophytes, molluscs, odonates, amphibians, fish and benthic
+
invertebrates. In the present analysis, the first four of these groups are focused upon, because sampling
+
strategies for fish and benthic invertebrates are not compatible with the other groups.
+
  
 
==References==
 
==References==
 
<references />
 
<references />

Revision as of 15:35, 8 May 2009

Regelsbrunner Aue


Factsheet: Regelsbrunner Aue

General
Country AT
River Name Danube
Site Name Regelsbrunner Aue
River Characterisation
{{{rivertypes}}}
River typology
Location (Lat Lon) 48.11, 16.69
Altitude mid-altitude: 200 - 800 m
Catchment area very large: > 10000 km2
Geology Calcareous
National code/
River type name
AU

Biological quality elements
{{{bqe}}}
Ecosystem Services
{{{egands}}}
EU Directives
{{{eedandp}}}
Pressures
Morphological alterations
Presence of downstream artificial barriers on the catchment scale
Artificial barriers upstream from the site
Artificial barriers downstream from the site
Channelisation/Cross section alteration
Measures
Working with physical form and function of river and floodplains
Reconnect and restore historic aquatic habitats
Changes in system operation
Change operational regime of weirs and locks
Other
Project size 570 ha
Approximate costs 0
Synergy -
Status Realised
Period of realization 1999
Evaluation 1


Introduction

"The goal of the ‘Danube Restoration Project’ is to gradually restore hydrological connectivity and ecological integrity between the river and its floodplain in a segment of the Austrian Danube. In order to test the effectiveness and success of this large-scale pilot project, a long-term evaluation program has been implemented, which includes abiotic, biotic and functional components. The biotic ‘functional describers’ include macrophytes, molluscs, odonates, amphibians, fish and benthic invertebrates. In the present analysis, the first four of these groups are focused upon, because sampling strategies for fish and benthic invertebrates are not compatible with the other groups." (Tockner et al., 1999 [1]


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