The opening of the dams should impact the functioning of Atlantic salmon populations migrating up the Sélune River and its tributaries. Restoring the river's ecological continuity will alter population flows by allowing amphihaline sea trout to migrate further upstream and native trout to move downstream and upstream of the dams. The trout population is monitored at a network of stations covering the entire Sélune basin using an abundance index, which is carried out every two years before 2021 and every year since then. Field campaigns comply with the fishing protocol developed by INRAE and OFB. The aim of this method is to estimate the abundance of juvenile Atlantic salmon (Salmo salar) at a station (or sector). This protocol targets juveniles of the year (aged 0+) whose abundance reflects the renewal of generations within the population (or recruitment) and survival after the embryonic development phases under gravel and the first months of life in the open environment. Field campaigns are carried out by INRAE and the Manche d'Ille-et-Vilaine Federation for Fishing and the Protection of the Aquatic Environment (FDAPPMA50 and FDAAPPMA35). This dataset provides individual biometric data on Atlantic salmon caught during PAS fishing sessions in the Sélune watershed, by station and by fishing session.

The study of riparian vegetation is based on the observation of natural plant communities spontaneously colonizing newly exposed areas following the erasure of the Vezins and La-Roche-Qui-Boit dams. The vegetation monitoring system includes two complementary approaches: i) a vegetation sampling method based on floristic surveys (composition & structure) carried out within a series of quadrats positioned along a transect ii) a monitoring of the vegetation units (UV) observed within the valley This sheet specifically concerns the monitoring of vegetation units (UV) observed within the valley, only for data from the Sélune Observatory (2021-2026). The monitoring system for Vegetation Units is based on the identification of vegetation distributed along the transect at each station in the main stream. It aims to obtain a representative view of diversity and the organization of plant formations and communities. This monitoring consists of identifying the discontinuities in terms of composition and structure of the various vegetation types that develop within the neo-valley along the transect that descends to the bank, and to report their influence. (distance in metres from the reference point at the edge of the old dam). These data can be used to establish a pro rata of the different plant formations encountered along the transect. Although this value is thus really valid only at the transect of each station, this information can potentially constitute an approximation of the heterogeneity and distribution of vegetation at the valley scale. This layer gives, for each riparian vegetation monitoring station and each campaign from 2021 to 2026, the following information: – Campaign information (id, code, date, campaign), – Station information (code, name, protocol applied, number of quadrats, code for the associated Sélune reference point and, as a result: location on the watershed, distance to sea, distance to source and water course) – Information on the transect by campaign (number and length, X, Y, LON coordinates, LAT of reference points "NGF" and end point "rive") – Information regarding the Vegetation Units (VU) identified by campaign (number, description: code, start position, end position, EUNIS3 characteristics, 4) – Origin of the data ("Observatoire Sélune," "Hors Observatoire Sélune," "Projet Séripage," or "Projet Restaure") – “Point” geometry (default) corresponding to the transect reference point – Line (alternative) geometry of the associated transect for each campaign. The study of riparian vegetation in exposed areas is based on the observation of natural plant communities colonizing newly exposed mudflats, at different time scales (intra- and interannual variations) and at nested spatial scales. The botanical inventory is carried out according to the Braun-Blanquet method. The sampling protocol is stratified in order to maximize the recorded diversity. For each study area, a transect perpendicular to the riverbed is established, where strips parallel to the watercourse are marked on the ground according to the exposure rate. This layer indicates the location of these study areas, the layout of transects and information regarding vegetation units recorded between 2021 and 2026.

The spawning grounds of the sea lamprey (Petromyzon marinus) are located within the perimeter of the Sélune Observatory. As this species is migratory, its colonisation of the Sélune river and its tributaries will probably be influenced by the removal of the Sélune dams. The spawning grounds are characterised by a depression accompanied by a sediment ejection dome immediately downstream. The stones returned to the dome are lighter, making the nests easily visible and identifiable for up to several weeks after spawning. This data is available for the years 2015, 2019, 2020, 2021, 2022, 2023, 2024, 2025 and 2026. The Sélune Observatory's activity reports (see attached links) give details of the prospecting conditions.

The spawning grounds of the sea lamprey (Petromyzon marinus) are located within the perimeter of the Sélune Observatory. As this species is migratory, its colonisation of the Sélune river and its tributaries will probably be influenced by the removal of the Sélune dams. The spawning grounds are characterised by a depression accompanied by a sediment ejection dome immediately downstream. The stones returned to the dome are lighter, making the nests easily visible and identifiable for up to several weeks after spawning. The identification and counting of sea lamprey spawning grounds is done through an internal standardized INRAE protocol. This is a visual count with GPS pointing by foot prospecting from the downstream to the upstream on the tributaries, in kayak from the upstream to the downstream on the main course of the Sélune. The resources allocated to counting spawning grounds do not cover the entire hydrographic network of the Sélune and its tributaries; geographically located spawning areas at the upstream boundary do not necessarily correspond to the colonization front. Starting in 2025, due to the time-consuming nature of this monitoring, it was decided to restrict and make permanent the prospecting shelves. Were therefore prospected: a section of the linear downstream of the dams (downstream of the Sélune, tributary of the Oir, and downstream of the tributary of the Beuvron), the linear within the old reservoirs (La Sélune), and a section of linear upstream of the dams. (The Sélune from upstream of the dams to Saint Hilaire du Harcouët as well as downstream from the tributary of the Airon). This dataset makes it possible to report on the line surveyed per campaign, the number of spawning grounds identified on each line, the length of each line, and the spawning rate related to the length of the prospected line. This data is available for the years 2015, 2019, 2020, 2021, 2022, 2023, 2024, 2025 and 2026. The Sélune Observatory's activity reports (see attached links) give details of the prospecting conditions.

The study of riparian vegetation is based on the observation of natural plant communities spontaneously colonizing newly exposed areas following the erasure of the Vezins and La-Roche-Qui-Boit dams. The vegetation monitoring system includes two complementary approaches: i) a vegetation sampling method based on floristic surveys (composition & structure) carried out within a series of quadrats positioned along a transect ii) a monitoring of the vegetation units (UV) observed within the valley This dataset specifically concerns the overall characterization observed on each quadrat in terms of strata and concerns only the Sélune Observatory (2021-2026). The sampling monitoring system is based on measurements distributed at different points in space (longitudinally and laterally). It aims to identify the diversity of flora and vegetation and describe the structure of emerging formations and plant communities within the neo-valley. Implemented annually (sub-annual only for 2021, before dismantling), this monitoring aims to identify and characterize the evolution trajectories of these vegetation over time. The vegetation sampling protocol is implemented at several stations located along the course of the Sélune and at the mouth of several tributaries located in the right-of-way of the two former reservoirs. The sample of stations is supplemented by a batch of stations positioned outside the right-of-way of the two former reservoirs, downstream and upstream, which constitute so-called "reference" stations. For each station, a transect is established perpendicular to the channel, from the bank to a reference point located at the level of the former water reservoir (i.e. 60m NGF for Vezins & 28.5m NGF for LRQB). Along this transect, 25m2 (5mx5m) quadrats are positioned according to previously set distance intervals. These quadrats (named Q1 to Q1+n) constitute the elementary unit within which abiotic (slope, texture...) and biotic (composition, structure) parameters are characterized and evaluated. The number of quadrats sampled per station varies depending on the width of the exposed bank (or transect length). It is completed by a reference quadrat, located beyond this maximum value (named Q0). The inventory of vascular flora, i.e. herbaceous and woody plant species within the quadrats, aims to be exhaustive and to identify them up to the specific or even sub-specific rank. The overall characterization mentioned mainly concerns, for each quadrat, the type of soil encountered (see attribute dictionary), the slope (see attribute dictionary), the proportions of water cover, bare soil, and litter, as well as, for each of the 6 defined strata (see attribute dictionary): the considered height limits, the maximum and average height, and the proportion of overlap (relative to the 25m2 of the quadrat). This layer gives, for each monitoring quadrat of vegetation sampling from 2021 to 2026, the following information: – Quadrat information (id, code, number and distance from its centroid to the station reference point), – Campaign information (id, code, date, campaign), – Station information (code, name, protocol applied, number of quadrats, code for the associated Sélune reference point and, as a result, positioning on the catchment area, distance to sea, distance to source and watercourse, watercourse reference altitude) – Information on the transect by campaign (number and length, X, Y, LON, LAT coordinates of the reference points “NGF” and end point “bank”) – Information concerning the strata (identified or not), soil typology, water, bare and litter coverings, as well as details for each stratum (name of stratum ‘muscinal’, “herbaceous”, “young plant shrub,” “low shrub', “high shrub” and “arborescent, the height limits of the stratum, the associated overlap, the maximum and average heights of the stratum) – “Point” geometry (default) corresponding to the transect reference point

The opening of the dams should impact the functioning of Atlantic salmon populations migrating up the Sélune River and its tributaries. Restoring the river's ecological continuity will alter population flows by allowing amphihaline sea trout to migrate further upstream and native trout to move downstream and upstream of the dams. The trout population is monitored at a network of stations covering the entire Sélune basin using an abundance index, which is carried out every two years before 2021 and every year since then. Field campaigns comply with the fishing protocol developed by INRAE and OFB. The aim of this method is to estimate the abundance of juvenile Atlantic salmon (Salmo salar) at a station (or sector). This protocol targets juveniles of the year (aged 0+) whose abundance reflects the renewal of generations within the population (or recruitment) and survival after the embryonic development phases under gravel and the first months of life in the open environment. Field campaigns are carried out by INRAE and the Manche and Ille-et-Vilaine Federations for Fishing and the Protection of the Aquatic Environment (FDAAPPMA50 and FDAAPPMA35). This dataset provides abundance data for Atlantic salmon (0+, 1+, 2+ and cumulative) as well as the salmon abundance index (PAS) by station and fishing session.

The study of riparian vegetation is based on the observation of natural plant communities spontaneously colonizing newly exposed areas following the erasure of the Vezins and La-Roche-Qui-Boit dams. The vegetation monitoring system includes two complementary approaches: i) a vegetation sampling method based on floristic surveys (composition & structure) carried out within a series of quadrats positioned along a transect ii) a monitoring of the vegetation units (UV) observed within the valley This dataset specifically concerns the overall characterization observed on each quadrat in terms of strata and concerns only the Sélune Observatory (2021-2026). The sampling monitoring system is based on measurements distributed at different points in space (longitudinally and laterally). It aims to identify the diversity of flora and vegetation and describe the structure of emerging formations and plant communities within the neo-valley. Implemented annually (sub-annual only for 2021, before dismantling), this monitoring aims to identify and characterize the evolution trajectories of these vegetation over time. The vegetation sampling protocol is implemented at several stations located along the course of the Sélune and at the mouth of several tributaries located in the right-of-way of the two former reservoirs. The sample of stations is supplemented by a batch of stations positioned outside the right-of-way of the two former reservoirs, downstream and upstream, which constitute so-called "reference" stations. For each station, a transect is established perpendicular to the channel, from the bank to a reference point located at the level of the former water reservoir (i.e. 60m NGF for Vezins & 28.5m NGF for LRQB). Along this transect, 25m2 (5mx5m) quadrats are positioned according to previously set distance intervals. These quadrats (named Q1 to Q1+n) constitute the elementary unit within which abiotic (slope, texture...) and biotic (composition, structure) parameters are characterized and evaluated. The number of quadrats sampled per station varies depending on the width of the exposed bank (or transect length). It is completed by a reference quadrat, located beyond this maximum value (named Q0). The inventory of vascular flora, i.e. herbaceous and woody plant species within the quadrats, aims to be exhaustive and to identify them up to the specific or even sub-specific rank. The characterization of cover by plant species on a quadrat allows to present, for each quadrat, all the species identified in the field (taxonomic determination and proportion (%) of cover on the quadrat and for the stratum considered). This layer gives, for each quadrat of each riparian vegetation monitoring station and each campaign of the Sélune Observatory from 2021 to 2026, the following information: – Quadrat information (id, code, number and distance from its centroid to the station reference point), – Campaign information (id, code, date, campaign), – Station information (code, name, protocol applied, number of quadrats, code for the associated Sélune reference point and, as a result, positioning on the catchment area, distance to sea, distance to source and watercourse, watercourse reference altitude) – Information on the transect by campaign (number and length, X, Y, LON, LAT coordinates of the reference points “NGF” and end point “bank”) – Information concerning the identified taxa: taxonomic determination, scientific name, and vernacular, identification stratum and overlap on this stratum – Information regarding the identification stratum: its wording "muscinal", "herbaceous", "young plant shrub", "low shrub", "high shrub" and "arborescent" as well as the height markers – “Point” geometry (default) corresponding to the transect reference point

The study of riparian vegetation is based on the observation of natural plant communities that spontaneously colonize areas newly exposed following the removal of the Vezins and La-Roche-Qui-Boit dams. The vegetation monitoring program comprises two complementary approaches: i) a vegetation sampling method based on floristic surveys (composition and structure) conducted within a series of plots positioned along a transect ii) monitoring of Vegetation Units (VUs) observed within the valley i) Sampling monitoring: The sampling monitoring system is based on measurements distributed at different points in space (longitudinally and laterally). It aims to identify the diversity of flora and vegetation and describe the structure of emerging formations and plant communities within the neo-valley. Implemented annually (sub-annual only for 2021, before dismantling), this monitoring aims to identify and characterize the evolution trajectories of these vegetation over time. The vegetation sampling protocol is implemented at several stations located along the course of the Sélune and at the mouth of several tributaries located in the right-of-way of the two former reservoirs. The sample of stations is supplemented by a batch of stations positioned outside the right-of-way of the two former reservoirs, downstream and upstream, which constitute so-called "reference" stations. For each station, a transect is established perpendicular to the channel, from the bank to a reference point located at the level of the former water reservoir (i.e. 60m NGF for Vezins & 28.5m NGF for LRQB). Along this transect, 25m2 (5mx5m) quadrats are positioned according to previously set distance intervals. These quadrats (named Q1 to Q1+n) constitute the elementary unit within which abiotic (slope, texture...) and biotic (composition, structure) parameters are characterized and evaluated. The number of quadrats sampled per station varies depending on the width of the exposed bank (or transect length). It is completed by a reference quadrat, located beyond this maximum value (named Q0). The inventory of vascular flora, i.e. herbaceous and woody plant species (excluding bryophytes) within quadrats aims at exhaustiveness and identification up to specific or even sub-specific rank. ii) Monitoring of Vegetation Units: The monitoring system for Vegetation Units is based on the identification of vegetation distributed along the transect at each station in the main stream. It aims to obtain a representative view of diversity and the organization of plant formations and communities. This monitoring consists of identifying the discontinuities in terms of composition and structure of the various vegetation types that develop within the neo-valley along the transect that descends to the bank, and to report their influence. (distance in metres from the reference point at the edge of the old dam). These data can be used to establish a pro rata of the different plant formations encountered along the transect. Although this value is thus really valid only at the transect of each station, this information can potentially constitute an approximation of the heterogeneity and distribution of vegetation at the valley scale. This layer gives, for each riparian vegetation monitoring station and each campaign from 2021 to 2026, the following information: – Campaign information (id, code, date, campaign), – Station information (code, name, protocol applied, number of quadrats, code for the associated Sélune reference point and, as a result: location on the catchment area, distance to sea, distance to source and watercourse) – Information on the transect by campaign (number and length, X, Y, LON coordinates, LAT of reference points "NGF" and end point "rive") – Information regarding the Vegetation Units (VU) identified by campaign (number, description: code, start position, end position, EUNIS3 characteristics, 4) – Origin of the data ("Observatoire Sélune," "Hors Observatoire Sélune," "Projet Séripage," or "Projet Restaure") – “Point” geometry (default) corresponding to the transect reference point – Line (alternative) geometry of the associated transect for each campaign.

As part of the Biomonitoring project and the Sélune observatory , pilot stations have been set up along the main course of the Sélune, distributed from upstream to downstream of the hydroelectric dams. Three stations are located in the former reservoirs of the dams, while the other two, known as the reference stations, are outside the area of influence of the former dams (one downstream and the other upstream). At these stations, aquatic biocenoses (including benthic macroinvertebrates, biofilms, macrophytes, etc.) are monitored. 2 sampling campaigns (spring and autumn) for benthic macroinvertebrates (bmi) have been carried out since September 2014. During each campaign, 2 sampling protocols are implemented: - in accordance with standard NF T90-333, which enables the calculation of the IBG-DCE and I2M2 (‘SURBER’) - via artificial substrates immersed for 1 month (‘SUBART’), in order to focus on measuring the ‘effect of dams’. The protocol is described in: Piscart C., Moreteau, J.C., Beisel J.N. (2006). Monitoring changes in freshwater macroinvertebrate communities along a salinity gradient using artificial substrates. Environmental Monitoring and Assessment 116: 529-542. This layer details the benthic macroinvertebrate taxa and their abundance obtained after analysis (according to standard NF T90-388). These data are distributed by campaign and by sector. Taxa presenting all the morphological criteria clearly visible and characteristic allowing the exactitude of their determination and an irreproachable state of conservation are integrated into the reference collection of the Sélune Observatory. This collection can be consulted on request (see contact point). Taxon determination is based on version v17 of the TAXREF reference. The dataset is currently under embargo.

The opening of the dams should impact the functioning of Atlantic salmon populations migrating up the Sélune and its tributaries. Restoring the river's ecological continuity will alter population flows by allowing Atlantic salmon to migrate further upstream and downstream of the dams. The Atlantic salmon population is monitored at a network of stations covering the entire Sélune basin using an abundance index, which was carried out every two years before 2021 and annually since then. Field campaigns comply with the fishing protocol developed by INRAE and OFB. The aim of this method is to estimate the abundance of juvenile Atlantic salmon (Salmo salar) at a station (or sector). This protocol targets juveniles of the year (aged 0+) whose abundance reflects the renewal of generations within the population (or recruitment) and survival after the embryonic development phases under gravel and the first months of life in the open environment. Field campaigns are carried out by INRAE and the Manche d'Ille-et-Vilaine Federation for Fishing and the Protection of the Aquatic Environment (FDAPPMA50 and FDAPPMA35). This dataset provides the locations of these study sectors for IAS fishing sessions in the Sélune watershed by fishing session.