Study of the hydrological processes in four small and medium-scale Mediterranean catchments by performing flood hydrograph decompositions using graphical methods

5 or 6 months, february - july 2025
Laboratory : Institut des Géosciences de l’Environnement (IGE)
Supervision : O. Fischer (ophelie.fischer univ-grenoble-alpes.fr), C. Legoût (cedric.legout univ-grenoble-alpes.fr), G. Nord (guillaume.nord univ-grenoble-alpes.fr)
Co-supervisor : C. Le Bouteiller (caroline.le-bouteiller inrae.fr)
Adress : IGE, building OSUG B
Required skills : M2 in physics or geosciences. As the internship is focused on the analysis of large datasets, it is necessary to be comfortable with at least one programming tool (R, Python, or MATLAB). A basic knowledge of hydrology is desirable.
Key words : hydrology, hydrograph decomposition, erosion, badlands

Context

Suspended sediment fluxes (organic and inorganic materials smaller than 63 micrometers) in watersheds are essential natural processes for landscape structuring, maintaining ecosystem health, and transporting nutrients within watersheds (Owens 2020). Suspended sediment (SS) constitute the dominant type of sediment generated by watersheds, representing 70% of the annual sediment export by rivers to the ocean (Vercruysse, Grabowski, et Rickson 2017). However, despite their crucial role in the river systems ecology, SS are also associated with numerous environmental and economic issues (redistribution of contaminants, degradation of the quality of riparian environments and aquatic life, threat for water quality, the food security, reservoirs siltation, damage during flash floods). Given these significant challenges, it is important to understand and prioritize the processes that control erosion dynamics and sediment transfers within watersheds during storms. However, despite decades of research, the spatial and temporal variabilities of the processes generating SS transport have not yet been fully understood (Vercruysse, Grabowski, et Rickson 2017).
Storm events are key moments during which sediments and nutrients are mobilized (Lloyd et al. 2016). During such events, the impact of precipitation tends to dislodge unconsolidated particles from slopes. These detached sediments are then either transported by overland flow to the nearest watercourse and exported out of the watershed, or deposited within the watershed before or after reaching the watercourse, where they may later be remobilized. The sediment transport rate primarily depends on discharge (Q) in the first instance, but many other factors influence sediment dynamics, which exhibit strong spatial and temporal variability (Onderka et al. 2012). Most studies examine sediment dynamics by linking suspended sediment concentration (SSC) to the total flow at the watershed’s outlet and often observe significant dispersion in the Q-SSC relationship. However, water at the watershed outlet is a mixture of water coming from different compartments (mainly overland flow and subsurface/groundwater flow), which play different roles in the sediment export processes. Overland flow actively contributes to the detachment of particles from slopes and their transport to the hydrological network (Tolorza et al. 2014), whereas subsurface/groundwater provides clear water to the hydrological network, which can dilute sediments and/or contribute to the remobilization of riverbed sediments (Bača 2008). Therefore, the total discharge at the watershed outlet is not the best variable for understanding and identifying sediment production processes in a watershed. Decoupling the overland flow and subsurface/groundwater compartments during floods should lead to a better understanding of primary erosion (i.e., detachment of soil particles from slopes) and secondary erosion processes due to the arrival of subsurface/groundwater in the river, which limits sediment deposition by sustaining flow transport capacity and can contribute to the remobilization of previously deposited particles in the hydrological network.

Water compartments at the watershed outlet during floods can be separated by performing hydrograph decompositions. Hydrograph decomposition is based on the assumption that the streamflow at the watershed outlet is the result of a mixture of a finite number of different identified water sources (Pelletier et Andréassian 2020). Many methods have been developed to decompose flood hydrographs. The oldest and most basic ones are graphical methods, and primarily rely on the difference in transfer time between water compartments (often baseflow and quick flow) ((Pelletier et Andréassian 2020), (Szilagyi et Parlange 1998)). Later, low-pass filtering methods were developed for base flow separation, assuming that baseflow produces the low-frequency components of the hydrograph ((Eckhardt 2005 , (Eckhardt 2008)). Several studies have conducted graphical hydrograph decompositions to investigate the dynamics of suspended sediment concentration in watersheds ((Bača 2008), (Walling et Webb, s. d.), (Andermann et al. 2012)). All these studies have highlighted the dilution effect of subsurface/groundwater by showing that the dispersion of the SSC/Q relation is reduced when considering only overland flow discharge. However, no such study has been conducted in small and medium-scale Mediterranean watersheds, which are known to have very high erosion rates ((Francke et al. 2014), (Klotz et al. 2023), (Nord 2016)).

Objectives :

Therefore, the objective of this internship is to analyze the hydrological processes of four Mediterranean watersheds by performing graphical hydrograph decompositions over several hydrological years. The studied catchments are part of French observatories of the OZCAR network : three of them (Laval, Brusquet and Galabre) belong to the Draix-Bléone observatory (located in the Southern Alps near Digne-les-Bains, south-east of France, (Klotz et al. 2023), (Legout et al. 2021)) and the Claduègne catchment is in the OHMCV observatory (“Observatoire Hydro-Météorologique Cevennes Vivarais”, located in Ardeche in the south of France (Nord 2016). These watersheds have different sizes (0.86for Laval, 1.07 for Brusquet, 20 for Galabre, 43 for Claduègne), different land uses (Brusquet, Laval, and Galabre watersheds are minimally anthropized with vegetation cover rates of respectively 80%, 30%, and 80% ; Claduègne watershed is more anthropized with approximately 40% of forest and the rest occupied by agriculture). These watersheds are all equipped with a hydrological station where high-frequency measurements of rainfall and discharge have been conducted for several years.

This internship is linked to an ongoing PhD project, which aims to analyze the impact of groundwater input on the hydrosedimentary processes of these watersheds. As part of this PhD, hydrograph decompositions have already been carried out in the two small watersheds (Laval and Brusquet), by using a different decomposition method based on the chemical composition differences of the various water compartments. This internship will therefore allow the comparison of the results of several flood hydrograph decomposition methods based on different principles.

Method :

The different steps planned for the internship are :
• Conduct a literature review on the various graphical hydrograph decomposition methods and select the most relevant one(s) for the studied watersheds.
• Perform hydrograph decompositions during the available flood events in the data from the four hydrological stations and develop a method to estimate uncertainty in the results.
• Compare the hydrological responses during floods in the four watersheds, particularly in terms of surface runoff generation processes. Try to link the observed variations in these processes to differences in flood types, vegetation cover, size, geology, rainfall spatial variabilities and human activities between the watersheds.

The internship may also involve participating in fieldwork missions on the different watersheds as part of the regular maintenance of the hydrological stations.

Period of the internship :
Ideally February-July (6 months)

Application :
Send a CV and cover letter by email to the supervisors.

References  :

  • Andermann, Christoff, Alain Crave, Richard Gloaguen, Philippe Davy, et Stéphane Bonnet. 2012. « Connecting Source and Transport : Suspended Sediments in the Nepal Himalayas ». Earth and Planetary Science Letters 351‑352 (octobre):158‑70. https://doi.org/10.1016/j.epsl.2012.06.059.
  • Bača, Peter. 2008. « Hysteresis Effect in Suspended Sediment Concentration in the Rybárik Basin, Slovakia / Effet d’hystérèse Dans La Concentration Des Sédiments En Suspension Dans Le Bassin Versant de Rybárik (Slovaquie) ». Hydrological Sciences Journal 53 (1) : 224‑35. https://doi.org/10.1623/hysj.53.1.224.
  • Eckhardt, K. 2005. « How to Construct Recursive Digital Filters for Baseflow Separation ». Hydrological Processes 19 (2) : 507‑15. https://doi.org/10.1002/hyp.5675.
  • Eckhardt, K. 2008. « A Comparison of Baseflow Indices, Which Were Calculated with Seven Different Baseflow Separation Methods ». Journal of Hydrology 352 (1‑2) : 168‑73. https://doi.org/10.1016/j.jhydrol.2008.01.005.
  • Francke, Till, Sandra Werb, Erik Sommerer, et José Andrés López-Tarazón. 2014. « Analysis of Runoff, Sediment Dynamics and Sediment Yield of Subcatchments in the Highly Erodible Isábena Catchment, Central Pyrenees ». Journal of Soils and Sediments 14 (12) : 1909‑20. https://doi.org/10.1007/s11368-014-0990-5.
  • Klotz, Sebastien, Caroline Le Bouteiller, Nicolle Mathys, Firmin Fontaine, Xavier Ravanat, Jean-Emmanuel Olivier, Frédéric Liébault, et al. 2023. « A High-Frequency, Long-Term Data Set of Hydrology and Sediment Yield : The Alpine Badland Catchments of Draix-Bléone Observatory ». Earth System Science Data 15 (10) : 4371‑88. https://doi.org/10.5194/essd-15-4371-2023.
  • Legout Cédric, Guilhem Freche, Romain Biron, Michel Esteves, Oldrich Navratil, Guillaume Nord, Magdalena Uber, et al. 2021. « A Critical Zone Observatory Dedicated to Suspended Sediment Transport : The Meso‐scale Galabre Catchment (Southern French Alps) ». Hydrological Processes 35 (3) : e14084. https://doi.org/10.1002/hyp.14084.
  • Lloyd, C.E.M., J.E. Freer, P.J. Johnes, et A.L. Collins. 2016. « Using Hysteresis Analysis of High-Resolution Water Quality Monitoring Data, Including Uncertainty, to Infer Controls on Nutrient and Sediment Transfer in Catchments ». Science of The Total Environment 543 (février):388‑404. https://doi.org/10.1016/j.scitotenv.2015.11.028.
  • Nord, Guillaume. 2016. « Auzon Data Paper ». ASCII. Mistrals. https://doi.org/10.6096/MISTRALS-HYMEX.1438.
  • Onderka, Milan, Andreas Krein, Sebastian Wrede, Núria Martínez-Carreras, et Lucien Hoffmann. 2012. « Dynamics of Storm-Driven Suspended Sediments in a Headwater Catchment Described by Multivariable Modeling ». Journal of Soils and Sediments 12 (4) : 620‑35. https://doi.org/10.1007/s11368-012-0480-6.
  • Owens, Philip N. 2020. « Soil Erosion and Sediment Dynamics in the Anthropocene : A Review of Human Impacts during a Period of Rapid Global Environmental Change ». Journal of Soils and Sediments 20 (12) : 4115‑43. https://doi.org/10.1007/s11368-020-02815-9.
  • Pelletier, Antoine, et Vazken Andréassian. 2020. « Hydrograph Separation : An Impartial Parametrisation for an Imperfect Method ». Hydrology and Earth System Sciences 24 (3) : 1171‑87. https://doi.org/10.5194/hess-24-1171-2020.
  • Szilagyi, Jozsef, et Marc B. Parlange. 1998. « Baseflow Separation Based on Analytical Solutions of the Boussinesq Equation ». Journal of Hydrology 204 (1‑4) : 251‑60. https://doi.org/10.1016/S0022-1694(97)00132-7.
  • Tolorza, Violeta, Sébastien Carretier, Christoff Andermann, Francisco Ortega-Culaciati, Luisa Pinto, et María Mardones. 2014. « Contrasting Mountain and Piedmont Dynamics of Sediment Discharge Associated with Groundwater Storage Variation in the Biobío River ». Journal of Geophysical Research : Earth Surface 119 (12) : 2730‑53. https://doi.org/10.1002/2014JF003105.
  • Vercruysse, Kim, Robert C. Grabowski, et R.J. Rickson. 2017. « Suspended Sediment Transport Dynamics in Rivers : Multi-Scale Drivers of Temporal Variation ». Earth-Science Reviews 166 (mars):38‑52. https://doi.org/10.1016/j.earscirev.2016.12.016.
  • Walling, E, et B W Webb. s. d. « Sediment Availability and the Prediction of Storm-Period Sediment Yields ».

Mis à jour le 10 octobre 2024