Case study:Removal of the Brosses weir on the Soanan River

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Location: 47° 32' 12.19" N, 3° 41' 29.40" E
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Project overview

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Status Complete
Project web site
Themes Habitat and biodiversity, Hydromorphology, Urban
Country France
Main contact forename Pierre
Main contact surname Gadiolet
Main contact user ID
Contact organisation Development board for the Chères and Azergues plain
Contact organisation web site
Partner organisations Rhône local office of Onema (National agency for water and aquatic environments), SMRPCA, Departmental federation for fishing and the protection of aquatic environments for the Rhône department (FDPPMA 69)
Parent multi-site project
This is a parent project
encompassing the following
projects
No
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Project summary

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The Brosses weir was completely destroyed and the rubble was removed, except for a few large rocks left in the bed, where the weir once stood. During the works, the river was temporarily diverted to avoid the fine sediment being washed away. The dissipation pool of the weir served as a sedimentation pool. A rescue fishing campaign was undertaken prior to the works to limit the impact on the fish population.

Monitoring surveys and results

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Pre-works monitoring was carried out on several compartments of the hydrosystem. The characteristics of the morphological compartment (long and cross profiles, substrate measurements, flow patterns) were identified prior to the works. The fish and riparian-vegetation compartments were also assessed by the FDPPMA 69 and the SMRPCA respectively. Finally, pre-works monitoring of the spawning redds was done by the Rhône local office of Onema. Post-works monitoring was done on the same compartments in 2011.

The removal of the Brosses weir opened 2.5 km of river and potential spawning redds for brown trout. The free movement of fish species and sediment was restored between this section of the Soanan and the Azergues River.

On the site of the former weir, the Onema local office noted, post works, more diversified flow patterns and a shift from lentic to lotic facies. These changes in facies would seem to have stimulated the populations of bullheads and juvenile brown trout, whose respective densities were multiplied by factors of ten and three one year after the works.

In 2017, following numerous floods including a particularly morphogeneous flood in 2016, it was decided to pursue monitoring on the Soanan. The flood in question reduced some of the irregularities in the long and cross profiles of the river. The slope is now similar to the steady slope observed in the rest of the river. However, regressive erosion upstream of the former weir has been observed.

Analysis of the monitoring data revealed reactivation of sediment over a distance of 120 metres upstream of the former weir and, downstream, sediment progression to the confluence with the Azergues River. The fine sediment (sand and silt) disappeared from the upstream zone, revealing gravel beds. In just one year, the natural sediment dynamics were restored in this section of the river.

Prior to the removal of the weir in 2009, no spawning activity by brown trout had been observed over a distance of 200 metres below the weir. Two spawning redds were subsequently observed in 2010, i.e. during the winter immediately following the removal, and twelve spawning redds were observed in December 2011. On the basis of the monitoring results for fish, the species commonly found in calm waters and ponds/lakes had disappeared following the removal of the weir. The number of brook lampreys fell virtually to zero due to the disappearance of the sand and silt substrates. The studied river section had returned to its initial fish-population context comprising essentially salmonids. In 2017, the trout population had returned to a certain equilibrium in that all age classes were represented. However, juveniles were under-represented due to two very hot and dry summers the previous two years.

An action programme for flood prevention (PAPI) and a river-basin contract are currently in effect in the Azergues basin. These two instruments aim to enhance the coordination of management work to control floods and restore aquatic environments by developing contacts and project development in the area.

Lessons learnt

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Catchment and subcatchment



Site

Name Soanan River
WFD water body codes FRDR571
WFD (national) typology
WFD water body name
Pre-project morphology
Reference morphology
Desired post project morphology
Heavily modified water body No
National/international site designation
Local/regional site designations
Protected species present No
Invasive species present No
Species of interest
Dominant hydrology
Dominant substrate
River corridor land use
Average bankfull channel width category 5 - 10 m
Average bankfull channel width (m) 88 m <br />0.008 km <br />800 cm <br />
Average bankfull channel depth category
Average bankfull channel depth (m)
Mean discharge category 0.1 - 1.0 m³/s
Mean annual discharge (m3/s) 0.80.8 m³/s <br />800 l/s <br />
Average channel gradient category 0.01 - 0.1
Average channel gradient 0.01
Average unit stream power (W/m2) 9.8079.807 W/m² <br />


Project background

Reach length directly affected (m) 300300 m <br />0.3 km <br />30,000 cm <br />
Project started 2010/09/01
Works started
Works completed
Project completed 2010/09/30
Total cost category 10 - 50 k€
Total cost (k€) 2727 k€ <br />27,000 € <br />
Benefit to cost ratio
Funding sources Rhône-Méditerranée-Corse water agency (60%), Rhône-Alpes region (20%), Development board for the Chères and Azergues plain (SMRPCA) (20%)

Cost for project phases

Phase cost category cost exact (k€) Lead organisation Contact forename Contact surname
Investigation and design
Stakeholder engagement and communication
Works and works supervision
Post-project management and maintenance
Monitoring



Reasons for river restoration

Mitigation of a pressure Reservoir impoundment
Hydromorphology Continuity for organisms, Continuity of sediment transport
Biology Fish: Abundance, Fish: Species composition
Physico-chemical
Other reasons for the project


Measures

Structural measures
Bank/bed modifications Weir removal
Floodplain / River corridor
Planform / Channel pattern
Other
Non-structural measures
Management interventions Rescue fishing campaign, temporary diversion of river
Social measures (incl. engagement)
Other


Monitoring

Hydromorphological quality elements

Element When monitored Type of monitoring Control site used Result
Before measures After measures Qualitative Quantitative

Biological quality elements

Element When monitored Type of monitoring Control site used Result
Before measures After measures Qualitative Quantitative

Physico-chemical quality elements

Element When monitored Type of monitoring Control site used Result
Before measures After measures Qualitative Quantitative

Any other monitoring, e.g. social, economic

Element When monitored Type of monitoring Control site used Result
Before measures After measures Qualitative Quantitative


Monitoring documents



Additional documents and videos


Additional links and references

Link Description

Supplementary Information

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All information on this page is copied from the AFB, The French Agency for Biodiversity.