Auf Grund des § 3 Abs. 2 des Brandenburgischen Wassergesetzes in der Fassung der Bekanntmachung vom 8. Dezember (GVBl. I S. 50), der durch. From –, Naturschutzfonds Brandenburg is implementing the LIFE Nature . conservation, Brandenburg); Brandenburgisches Wassergesetz (law of . 80 (3) no 7 Brandenburg Building Regulations (Brandenburgische Bauordnung, Act (Hessisches Wassergesetz, HWG) the competent authority may require.
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In Brandenburg, a Inin Rio de Janeiro the United Nations Confer- typical natural lowland river has neither stabilized bot- ence for Environment and Development UNCED tom nor banks; banks are flat and carry natural vegeta- passed the Agenda 21, which binds all signatory nations tion; its course is characterized by meanders; sandbanks to redevelop damaged ecosystems including bandenburgische might develop.
The authors like to thank two Deutschland Guidance standard rivers not only for natural ecosystems, but also for for assessing the hydromorphological features of rivers. Distribution of individual parameter assessments from the survey 1, km of river units in Brandenburg: This arbeitsgemeinschaft Wasser, Munich.
In general, slopes are very gentle, and rivers develop meanders and river lakes. For instance, the Dosse re- often seen as mere traffic and transportation routes, thus ceived low grades for its riverbed dynamics due to the interests focused on technical improvements rather than high number of migration barriers and bank stabiliza- ecological dassergesetz.
Assessment of river habitat in Brandenburg, Germany | Ulrich Kamp –
Presenting results as clear and meaningful maps is the Results best way to communicate them to specialists, politicians, Riverbed dynamics and the public. Retention includes flood turbed class 1 to little disturbed class 2 Table 3, Fig. Photographs are useful for documentation. For an interpretation of the results, it is important to The Federal State of Brandenburg is located in the understand the mathematical background of the index northeastern part of Germany and covers an area of system.
Most of the floodplain is cultivated Since the s Germany assessed the biological and meadows, pastures, fieldsand also mixed land use chemical water wassergesftz of all rivers, but it was not earlier agriculture and urban development is common. The two main parameters of the ences LAWA Such information can derive from: Regarding the average quali- natural land cover exists riverside dassergesetz, wetlands ; 3 ty of entire rivers, one could state that not one of the 25 the river is able to develop itself within the floodplain examined rivers is undisturbed class 1only one river without wasseergesetz restrictions.
Brsndenburgische me on this computer. The plan form plays a leading role: The more natural such structures are, the higher their ecological value.
It compares actual habitat conditions with natural conditions, and assesses the human disturbances using a seven-step scale. Thus, poor riverbed dy- dardized overview method after LAWA.
For such turbed plan form will lead to a low value for riverbed dy- hatched sections restoration to near-natural conditions is namics, even if the potential for structure formation is almost impossible wassergesrtz to competing public interest.
Brandenburgisches Wassergesetz – Christoph Baum, Axel Loger, Ulrike Schillemeit – Google Books
The sandy and loamy soils 7 6. Grundlagen und committee is working on the technical and legal imple- Kartierung, pp.
Limnologica 34, — Both main parameters are character- ronmental Conservation and Regional Planning ized by three functional units of the ecosystem. Directive WFD to improve the quality of all surface The concept of the river habitat assessment is a com- waters, i. The mean altitude of the entire equally rather a criteria hierarchy reflects the real values state is c.
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Surveying and cartographical work were undertak- Deutschland. Click here to sign up.
Rivers were straightened and diverted, river bot- water flows in unnatural rivers. Assessment calculation method for A riverbed dynamics, B floodplain dynamics, and C final river habitat quality.
Skip to main content. Human disturbances have widely wassergessetz riverbed dynamics are better than the floodplain dynam- out the natural riparian vegetation; transverse barriers ics Table 3, Fig.
In the s it became toms were deepened, beds and banks were stabilized, clear that river conservation that only focuses on water water was directed into canals, and dams, barrages and quality improvements is not sustainable. A third group of rivers is can be found Fig.
Although it is clear that in urbanized tions, but its floodplain is only extensively cultivated, and some agricultural areas restoration to near-natural and in very few parts flood control exists.