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This project has received funding from the European Union's Horizon 2020 research and innovation programme under the Marie Sklodowska-Curie grant agreement Nº 722028 (ENIGMA ITN). Closing the conceptual gap between the hyporheic zone and the river corridor Álvaro Pardo-Álvarez 1 , Jan Fleckenstein 2 , Oliver S. Schilling 3 , Nico Trauth 2 , Daniel Hunkeler 1 and Philip Brunner 1 1 Centre for Hydrogeology and Geothermics, University of Neuchâtel, Neuchâtel, Switzerland ([email protected]); 2 Centre for Environmental Research - UFZ, Leipzig, Germany; 3 Deparment of Geology and Geological Engineering, Laval University, Quebec City, Canada Computational Methods in Water Resources (CMWR) Session 36: Posters session Saint-Malo, France, 05.06.2018 1. INTRODUCTION Despite numerous modelling studies on hyporheic exchange have advanced our understanding of general mechanisms, they are often focused on local-scale processes with highly simplified boundary conditions (BC). This may lead to a misrepresentation of the hyporheic exchanges and biogeochemical turnover capacity in river corridors. To close this conceptual gap, we aim to provide and integrate field and modelling approaches to quantify exchange fluxes and processes between the hyporheic and stream system across different spatial and temporal scales. Brunner et al. (2017) 8. REFERENCES [1] Brunner, P., R. Therrien, P. Renard, C. T. Simmons, and H.-J. H. Franssen (2017), Advances in understanding river-groundwater interactions, Rev. Geophys., 55, doi:10.1002/ 2017RG000556. [2] Schilling, O. et al. (2017), Advancing Physically-Based Flow Simulations of Alluvial Systems Through Atmospheric Noble Gases andthe Novel 37Ar Tracer Method, Water Resour. Res. [3] Trauth, N., and J. H. Fleckenstein (2017), Single discharge events increase reactive efficiency of the hyporheic zone, Water Resour. Res., 53, 779–798, doi:10.1002/2016WR019488. [4] Partington, D.,P. Brunner, C. T. Simmons, R. Therrien,A. D. Werner, G. C. Dandy, and H. R. Maier (2011), A hydraulic mixing-cell method to quantify the groundwater component of streamflow within spatially distributed fully integrated surface water-groundwater flow models, Environ. Model. Soft., 26(7), 886–898. [5] Brunner, P., and C. T. Simmons (2012), HydroGeoSphere: A fully integrated, physically based hydrological model, Ground Water, 50(2), 170–176, doi:10.1111/j.1745-6584.2011.00882.x. [6] OpenFOAM® is licensed under the GNU General Public Licence (GPL) - www .openfoam.com [7] Doherty, J. E. (2015). Calibration and uncertainty analysis for complex environmental models. PEST: Complete theory and what it means for modelling the real world. Brisbane, Australia: Watermark Numerical Computing. 7. OUTLOOK We expect that simulation results will provide a more realistic representation of exchange flows and reactions between the stream channel, hyporheic zone and the underlying aquifer than by using steady hydraulic boundaries. 2. STUDY SITE Lowest part of the Upper Emme valley [A=0.9 km 2 ], Emmental, Switzerland Extremely dynamic pre-alpine alluvial catchment Q m_an : 4.4 m 3 /s (higher during snowmelt) Dense continuous monitored measurement network 8 GW abstraction wells (45% of Bern’s drinking water) 4 SW gauging stations (10 min interval) +30 piezometers (10-15 min interval) K aq = 550 m/d, n aq =0.1 K rb = 2.4 m/d, n rb =0.41 Schilling et al., 2017 3. OBJECTIVES 1. Exploring realistic hydraulic boundary conditions for CFD modelling 2. Using a highly advanced modelling framework to explore the superposition of different spatial and temporal scales for both synthetic and highly instrumented field based environments (Emme- catchment) 3. Integrating innovative field observations (tracer and UAV data) in this modelling process 6. FIELD DATA High-resolution state-of-the-art LIDAR- UAV characterization of the streambed (pre and post-flood event) Novel tracer methods ( 37 Ar) in addition to 222 Rn, 3 H/ 3 He and atmospheric novel gases for appropriate model parametrization Hydraulic –and also UAV– field data Brunner et al. (2017) 4. STREAM FLOW SIMULATIONS Computational Fluid Dynamics (CFD) code: Solver: two-phase (air-water) algorithm interFoam based on the volume of fluid (VOF) method Transient flow simulation (Trauth et al., 2017) Local hydraulic head distribution at the streambed Velocities (U) Hydraulic heads Q=10 m 3 /s Q=10 m 3 /s Trauth et al., 2017 5. GROUNDWATER MODELLING Fully coupled surface-subsurface flow and reactive transport model: Sequentially coupling: transient streambed pressures obtained from CFD modelling used as BC Simulate both exchange flow and biogeochemical turnover in the hyporheic sediments Hydraulic Mixing Cell (HMC) flow tracking tool for mixing ratios simulation throughout the entire domain (Partington et al., 2011) Parameter estimation: Schilling et al., 2017 Partington et al., 2011

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Page 1: Closing the conceptual gap between the hyporheic zone and ... · = 2.4 m/d, n rb =0.41 Schilling et al., 2017 3. OBJECTIVES 1. Exploring realistic hydraulic boundary conditions for

This project has received funding from the European Union's Horizon 2020 research and innovationprogramme under the Marie Sklodowska-Curie grant agreement Nº 722028 (ENIGMA ITN).

Closing the conceptual gap between the hyporheic zone and the river corridor

Álvaro Pardo-Álvarez1, Jan Fleckenstein2, Oliver S. Schilling3, Nico Trauth2, Daniel Hunkeler1 and Philip Brunner1

1Centre for Hydrogeology and Geothermics, University of Neuchâtel, Neuchâtel, Switzerland ([email protected]); 2Centre for Environmental Research - UFZ, Leipzig, Germany; 3Deparment of Geology and Geological Engineering, Laval University, Quebec City, Canada

Computational Methods in Water Resources (CMWR)Session 36: Posters session

Saint-Malo, France, 05.06.2018

1. INTRODUCTION

Despite numerous modelling studies on hyporheic exchange have advanced our understanding of generalmechanisms, they are often focused on local-scale processes with highly simplified boundary conditions (BC).This may lead to a misrepresentation of the hyporheic exchanges and biogeochemical turnover capacity in rivercorridors.

To close this conceptual gap, we aim to provide and integrate field and modelling approaches to quantifyexchange fluxes and processes between the hyporheic and stream system across different spatial and temporalscales.

Bru

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7)

8. REFERENCES

[1] Brunner, P., R. Therrien, P. Renard, C. T. Simmons, and H.-J. H. Franssen (2017), Advances inunderstanding river-groundwater interactions, Rev. Geophys., 55, doi:10.1002/ 2017RG000556.

[2] Schilling, O. et al. (2017), Advancing Physically-Based Flow Simulations of Alluvial SystemsThrough Atmospheric Noble Gases and the Novel 37Ar Tracer Method, Water Resour. Res.

[3] Trauth, N., and J. H. Fleckenstein (2017), Single discharge events increase reactive efficiency ofthe hyporheic zone, Water Resour. Res., 53, 779–798, doi:10.1002/2016WR019488.

[4] Partington, D., P. Brunner, C. T. Simmons, R. Therrien, A. D. Werner, G. C. Dandy, and H. R. Maier(2011), A hydraulic mixing-cell method to quantify the groundwater component of streamflowwithin spatially distributed fully integrated surface water-groundwater flow models, Environ.Model. Soft., 26(7), 886–898.

[5] Brunner, P., and C. T. Simmons (2012), HydroGeoSphere: A fully integrated, physically basedhydrological model, Ground Water, 50(2), 170–176, doi:10.1111/j.1745-6584.2011.00882.x.

[6] OpenFOAM® is licensed under the GNU General Public Licence (GPL) - www.openfoam.com

[7] Doherty, J. E. (2015). Calibration and uncertainty analysis for complex environmental models.PEST: Complete theory and what it means for modelling the real world. Brisbane, Australia:Watermark Numerical Computing.

7. OUTLOOK

We expect that simulation results will provide a more realistic representationof exchange flows and reactions between the stream channel, hyporheiczone and the underlying aquifer than by using steady hydraulic boundaries.

2. STUDY SITE

Lowest part of the Upper Emme valley [A=0.9 km2], Emmental, Switzerland

• Extremely dynamic pre-alpine alluvial catchment• Qm_an: 4.4 m3/s (higher during snowmelt)• Dense continuous monitored measurement network

• 8 GW abstraction wells (45% of Bern’s drinking water)• 4 SW gauging stations (10 min interval)• +30 piezometers (10-15 min interval)

• Kaq= 550 m/d, naq=0.1• Krb= 2.4 m/d, nrb=0.41

Schilling et al., 2017

3. OBJECTIVES

1. Exploring realistic hydraulic boundary conditions for CFD modelling

2. Using a highly advanced modelling framework to explore thesuperposition of different spatial and temporal scales for bothsynthetic and highly instrumented field based environments (Emme-catchment)

3. Integrating innovative field observations (tracer and UAV data) in thismodelling process

6. FIELD DATA

• High-resolution state-of-the-art LIDAR-UAV characterization of the streambed(pre and post-flood event)

• Novel tracer methods (37Ar) in additionto 222Rn, 3H/3He and atmosphericnovel gases for appropriate modelparametrization

• Hydraulic –and also UAV– field dataB

run

ner

et

al.

(20

17

)

4. STREAM FLOW SIMULATIONS

Computational Fluid Dynamics (CFD) code:

• Solver: two-phase (air-water) algorithm interFoam based on the volume of fluid(VOF) method

• Transient flow simulation (Trauth et al., 2017)

• Local hydraulic head distribution at the streambed

Velocities (U)

Hydraulic heads

Q=10 m3/s

Q=10 m3/s

Tra

uth

et a

l., 2

01

7

5. GROUNDWATER MODELLING

Fully coupled surface-subsurface flow andreactive transport model:

• Sequentially coupling: transient streambedpressures obtained from CFD modelling used asBC

• Simulate both exchange flow and biogeochemicalturnover in the hyporheic sediments

• Hydraulic Mixing Cell (HMC) flow tracking tool formixing ratios simulation throughout the entiredomain (Partington et al., 2011)

• Parameter estimation:

Schilling et al., 2017

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ing

ton

et a

l., 2

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1