Remove barrier
Contents
- 1 Remove barrier
- 1.1 General description
- 1.2 Applicability
- 1.3 Expected effect of measure on (including literature citations):
- 1.4 Temporal and spatial response
- 1.5 Pressures that can be addressed by this measure
- 1.6 Cost-efficiency
- 1.7 Case studies where this measure has been applied
- 1.8 Useful references
- 1.9 Other relevant information
Remove barrier
Remove barrier04. Longitudinal connectivity improvement
General description
At present there are many barriers in the rivers that might be eliminated due to their lack of use, obtaining with it the longitudinal continuity of the flows and the connectivity of the fluvial habitat recovery. Barriers are obstacles to the natural flows longitudinal continuity, represented by hydraulic engineering transverse structures, including large dams, weirs, and dikes. The aim of this measure is to recover the continuity of water and sediment flows, and the organism connectivity in both ways, in order to recover the principal attributes of natural functioning rivers. The elimination of these barriers will be possible only in the cases in which the property, the use or the purpose allow it, attending to the in force legislation and to the agreements that could be reached between the social implied agents.
Many of these river transverse barriers are nowadays in disuse, or its use has diminished in intensity or profitability, and the ecological functioning alteration caused is not justified any more, being necessary to check the interest of its maintenance, or the possibility of their removal.
Depending of its height, all dams suppose a more or less impassable barrier for the fish migratory species of the river, and concern the dispersion of the seeds, drift of macroinvertebrates, and transport and distribution of the sediments along the riverbed. To avoid this barrier effect, in many cases it is possible and suitable, to built fish passes, by-pass channels, fish elevators or any other system that is considered to be appropriate. But in many other cases, the most suitable and effective measure will be to proceed to reduce the height of the dam, or even the demolition of the dam, in order to restore the primitive conditions of the river.
The elimination of dams and weirs or obstacles for the pass of the waters and the aquatic organisms is a habitual practice in many countries in order to recover the ‘fluvial continuity’, which is an indicator of the Hydro-morphological quality of the running waters water bodies as Water Framework Directive proposes. In United States an increased experience on dam demolition (International Rivers Network, 2001; Bednarek, 2001; Higgs, 2002) exists, considering that these have a limited life span, and that often the environmental impacts that they generate are not justified by its use or current exploitation.
Applicability
There are publications and scientific and technical works on barrier and dam demolition where previous considerations necessary are detailed. The dam characteristics and on the effects of the its elimination in the river at short, medium and long term after its removal (American Institute of Biological Sciences, 2002). The techniques for dam demolition or to make the fluvial continuity effective can be very different, and must be designed in accordance with the peculiarities of every dam (size, type, location, etc.), the characteristics of the river and its catchment area and the aims of the demolition (restoration of the river, maintenance of recreative activities, use of river banks, etc.).
Depending on the determining conditions of each dam and fluvial section it is possible to choose for one of the next alternatives:
- To demolish the dam completely, leaving the riverbed as it was before its construction. In this case, it is necessary to use heavy machinery, hydraulic hammers, explosives, etc., that dismantle the whole structure, withdrawing later all the materials and rubbles originated with the respective works. It is recommended in the cases of small dams, land dams, or in natural spaces of high value, where one tries to reach a major level of restoration of the river, being generally the costliest option but that of more complete and ideal results (figure ).
- To break partially the dam, allowing that the water should flow across the opened gaps and that the water does not remain stored upstream. To break the main walls also will be necessary to use heavy machinery or explosives, the dam can be open it in one or in several zones, leaving in occasions in the same riverbed the ruined remains, which are avoided by the waters forming sections of major turbulence. With this option part of the structure is kept, but the connectivity of the habitats along the fluvial continuum is recovered (to see figure ). It is recommended in concrete dams or masonry of major width, where its demolition is expensive, and represents a much more economic alternative, which in some sections can be recommended in the short term, delaying its total demolition for a later period. It has been in use often in the sections where one has tried to support certain recreational activities in the shores of the former reservoir.
- To raise the hatches and to allow the water flow out emptying the reservoir, recovering the continuity of water and sediments upstream and downstream the dam, but without altering the hanging of the prey. This option does not need any type of heavy machinery or work of demolition, and can turn out to be most indicated in the cases in that the dam is having an additional uses (as a bridge and support of a road or railroad). However, for its efficiency it is necessary that the hatches are placed at the level of the current bed, and that have sufficient width to allow the water flow without causing obstructions.
Expected effect of measure on (including literature citations):
- HYMO (general and specified per HYMO element)
- physico � chemical parameters
- Biota (general and specified per Biological quality elements)
Temporal and spatial response
Pressures that can be addressed by this measure
- Colinear connected reservoir
- Embankments, levees or dikes
- Artificial barriers upstream from the site
- Artificial barriers downstream from the site
- Impoundment
Cost-efficiency
Case studies where this measure has been applied
- Fish ramp Friedrichsgüte
- Chícamo Life project. Conservation of Aphanius iberus´ genetics stocks ( Murcia ).
- Fish ramp Baumannsbrücke
- Regelsbrunner Aue
- Klein Wall
- Maxsee
- Emån - Emsfors
- Meander fish ramp Erpe BB
- Fish ramp Erpe BB
- Fish ramp Erpe Berlin
- Nansa River. Morphological and functional restoration of the Nansa River at Muñorrodero
- Narcea
- Narew river restoration project
- Töss
- Sella
- Enns - Aich
- Sweden- Restoration of the Freshwater Pearl Mussel and its habitats (LIFE04/NAT/SE/000231)
- Karlsruhe – Living Rhine floodplain near Karlsruhe (LIFE04 NAT/DE/000025)
- Conservation of Atlantic Salmon in Scotland (LIFE 04/NAT/GB/000250)