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Coupling groundwater and ecological models (MIKE-SHE & ECO Lab) 
Roberta-Serena Blasone (DHI)
© DHI 
•Integrated groundwater and surface water modelling 
•ECO Lab 
•Comparison of ECO Lab results with analytical solutions and laboratory experiments 
•Integrated flow, temperature and ecological modelling, Silver Creek, Idaho, USA 
•Nutrient removal in wetland environment, Odense, DK (ongoing) 
•Nuclear waste site risk assessment, SE (future) 
Agenda
1 
Integrated modelling and ECO Lab 
© DHI
© DHI
MIKE 21 
MIKE 11 
MIKE URBAN 
MIKE SHE 
LITPACK 
MIKE 21 
© DHI
Surface water and groundwater interaction 
© DHI 
MIKE SHE - MIKE 11 coupling
What is ECO Lab? 
•Process equation solver for coupled ordinary differential equations 
•Designed to describe processes of chemistry, ecology etc. 
•It calculates the rate of change of any type of state variable given any number of related variables, processes and forcing 
•Integrated with DHI’s hydrodynamic models 
ECO Lab 
Chemistry 
Physics 
Biology 
Ecology 
MIKE 21 
MIKE 11 
MIKE URBAN 
MIKE SHE 
LITPACK 
© DHI
Eco-hydrological modelling at catchment scale 
MIKE SHE/MIKE 11 
ECOLAB 
Hydrological processes 
•Water levels 
•Fluxes 
•….. 
Advection Dispersion 
•Concentration & fluxes of solutes 
•Temperature 
•….. 
Water Quality processes 
•Concentration & fluxes (nutrients, pesticides, organic & inorganic chemicals) 
Ecological and Chemical processes 
•Status indicators 
•Chemical reactions 
•Population, growth, health of species… 
© DHI
2 
Comparison of ECO Lab results with analytical solutions and laboratory experiments 
© DHI
Multi-species transport - Groundwater 
© DHI 
Nitrate -> Nitrite -> Ammonia or N PCE -> TCE -> DCE ->VD 
Sp 1. Adsorb + Decay Sp 2. Decay Sp 3. Decay 
Sun et al., 1999 
0 
0.1 
0.2 
0.3 
0.4 
0.5 
0.6 
0.7 
0.8 
0.9 
1 
0 
5 
10 
15 
20 
25 
30 
35 
40 
Relative concentration 
Distance [cm] 
Analytical solution - C1 
Analytical solution - C2 
Analytical solution - C3 
MIKE SHE + ECOLab - C1 
MIKE SHE + ECOLab - C2 
MIKE SHE + ECOLab - C3 
100 hours
Model validation – analytical solutions 
© DHI 
0 
0.1 
0.2 
0.3 
0.4 
0.5 
0.6 
0.7 
0.8 
0.9 
1 
0 
10 
20 
30 
40 
Relative concentration 
Distance [cm] 
0 
0.1 
0.2 
0.3 
0.4 
0.5 
0.6 
0.7 
0.8 
0.9 
1 
0 
10 
20 
30 
40 
Relative concentration 
Distance [cm] 
Analytical solution - C1 
Analytical solution - C2 
Analytical solution - C3 
MIKE SHE + ECOLab - C1 
MIKE SHE + ECOLab - C2 
MIKE SHE + ECOLab - C3 
50 hours 
400 hours 
Sun et al., 1999
Pesticide reactive transport – soil columns 
© DHI 
0 
0.2 
0.4 
0.6 
0.8 
1 
0 
20 
40 
60 
80 
100 
120 
Relative concentration 
days 
Tuxen et al. (2000) - Isoproturon B II 
Tuxen et al. (2000) - Bromide B II 
MIKE SHE + ECOLab - Isoproturon B II 
MIKE SHE + ECOLab - Bromide B II 
Bromide 
Isoproturon 
Tuxen et al., 2000
Model validation - Pesticides 
© DHI 
0.0 
0.2 
0.4 
0.6 
0.8 
1.0 
0 
20 
40 
60 
80 
100 
120 
Relative concentration 
days 
Tuxen et al. (2000) - MCPP B II 
Tuxen et al. (2000) - Bromide B II 
MIKE SHE + ECOLab - MCPP B II 
MIKE SHE + ECOLab - MCPP B II 
(new calibration) 
MIKE SHE + ECOLab - Bromide B II 
0 
0.2 
0.4 
0.6 
0.8 
1 
0 
20 
40 
60 
80 
100 
120 
Relative concentration 
days 
Tuxen et al (2000) - Dichlorprop B I 
Tuxen et al. (2000) - Bromide B I 
MIKE SHE + ECOLab - Dichlorprop B I 
MIKE SHE + ECOLab - Dichlorprop B I 
(new calibration) 
MIKE SHE + ECOLab - Bromide B I 
MCPP 
Dichloroprop
3 
Integrated flow, temperature and ecological modelling Silver Creek, Idaho, USA 
© DHI
Silver Creek Ecology 
© DHI 
Silver Creek is abundant in wildlife and a highly valued trout habitat 
Brown Trout and Rainbow Trout Numbers
Silver Creek, Idaho 
© DHI 
Woor River Valley
Lower Wood River Valley 
© DHI 
Semi-arid climate with low precipitation and high evaporation. 
Approximately 60% of the lower valley is cultivatated, of which 80% is irrigated.
Flow Model (MIKE SHE-MIKE 11) 
© DHI 
300 m cell size 
Other model components 
•Irrigation: surface and groundwater abstractions 
•Drainage: agricultural runoff 
Objectives 
•Integrated eco-hydrological model 
•Quantify changes in ecological status 
•Development of land management scenarios 
Scenarios 
•Reduction in GW abstraction 10%, 20%, 30% 
•Change of crops 
•Natural and past climate scenarios
Flow Calibration 
© DHI 
Picabo St @ Silver Creek 
Stanton Crossing St @ Big Wood River
Groundwater Levels 
© DHI
Stream Temperature model 
© DHI
Temperature Calibration 
© DHI 
0 
5 
10 
15 
20 
25 
1/09 2/09 3/09 4/09 5/09 6/09 7/09 8/09 9/09 10/09 11/09 
Temperature (°C) 
observed 
simulated
Temperature simulations 
© DHI
Bioenergetic model 
© DHI 
Ecological indicator 
Model parameters 
EI = Min (1, AGSX / AGNS) 
Model equations
Temperature and ecological indicator 
© DHI 
Ecological indicator 
Surface water temperature
Temperature and ecological indicator 
© DHI 
Ecological indicator 
Surface water temperature
4 
Nutrient removal in wetland environment, Odense, DK (ongoing) 
© DHI
Brynemade, Odense River 
© DHI 
25 m 
12 m 
6m
Brynemade, Odense River 
© DHI
Flooding behaviour 
© DHI
Groundwater level results 
© DHI
Water balance 
© DHI
Brynemade, Odense River 
© DHI 
To do next: 
•calculate the N contribute of the different sources to the river 
•model the N transformation processes 
•model how the biota reacts to the N in the environment 
•investigating potential changes to wetland design and characteristics in order to increase the nutrient retention capacity 
Integrated GW + SW modelling 
ECO Lab
5 
Nuclear waste site risk assessment, SE (future) 
© DHI
Nuclear waste site risk assessment 
© DHI 
•Fate of radioactive contaminants in groundwater and surface water 
•Surface water biota affected by radioactive contaminants
Thank you 
© DHI
© DHI 
•Butts et al (2012). MIKE SHE-ECO Lab – An integrated catchment scale eco- hydrological modelling tool, XIX International Conference on Water Resources CMWR 2012, University of Illinois at Urbana-Champaign, June 2012 
•Loinaz et al (2014). Modeling ecohydrological impacts of land management and water use in the Silver Creek basin, Idaho, J. Geophys. Res. Biogeosci., 119, 487–507, doi:10.1002/2012JG002133 
•Loinaz et al (2013). Integrated flow and temperature modeling at the catchment scale, 495, 238–251, doi:10.1016/j.bbr.2011.03.031 
•Von Christierson et al., Modelling nutrient removal from a restored lowland wetland using an integrated dynamic surface water-groundwater flow and transport modelling tool (in preparation) 
References

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Coupling groundwater and ecological models (MIKE-SHE & ECO Lab) - Roberta-Serena Blasone (DHI)

  • 1. Coupling groundwater and ecological models (MIKE-SHE & ECO Lab) Roberta-Serena Blasone (DHI)
  • 2. © DHI •Integrated groundwater and surface water modelling •ECO Lab •Comparison of ECO Lab results with analytical solutions and laboratory experiments •Integrated flow, temperature and ecological modelling, Silver Creek, Idaho, USA •Nutrient removal in wetland environment, Odense, DK (ongoing) •Nuclear waste site risk assessment, SE (future) Agenda
  • 3. 1 Integrated modelling and ECO Lab © DHI
  • 5. MIKE 21 MIKE 11 MIKE URBAN MIKE SHE LITPACK MIKE 21 © DHI
  • 6. Surface water and groundwater interaction © DHI MIKE SHE - MIKE 11 coupling
  • 7. What is ECO Lab? •Process equation solver for coupled ordinary differential equations •Designed to describe processes of chemistry, ecology etc. •It calculates the rate of change of any type of state variable given any number of related variables, processes and forcing •Integrated with DHI’s hydrodynamic models ECO Lab Chemistry Physics Biology Ecology MIKE 21 MIKE 11 MIKE URBAN MIKE SHE LITPACK © DHI
  • 8. Eco-hydrological modelling at catchment scale MIKE SHE/MIKE 11 ECOLAB Hydrological processes •Water levels •Fluxes •….. Advection Dispersion •Concentration & fluxes of solutes •Temperature •….. Water Quality processes •Concentration & fluxes (nutrients, pesticides, organic & inorganic chemicals) Ecological and Chemical processes •Status indicators •Chemical reactions •Population, growth, health of species… © DHI
  • 9. 2 Comparison of ECO Lab results with analytical solutions and laboratory experiments © DHI
  • 10. Multi-species transport - Groundwater © DHI Nitrate -> Nitrite -> Ammonia or N PCE -> TCE -> DCE ->VD Sp 1. Adsorb + Decay Sp 2. Decay Sp 3. Decay Sun et al., 1999 0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1 0 5 10 15 20 25 30 35 40 Relative concentration Distance [cm] Analytical solution - C1 Analytical solution - C2 Analytical solution - C3 MIKE SHE + ECOLab - C1 MIKE SHE + ECOLab - C2 MIKE SHE + ECOLab - C3 100 hours
  • 11. Model validation – analytical solutions © DHI 0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1 0 10 20 30 40 Relative concentration Distance [cm] 0 0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1 0 10 20 30 40 Relative concentration Distance [cm] Analytical solution - C1 Analytical solution - C2 Analytical solution - C3 MIKE SHE + ECOLab - C1 MIKE SHE + ECOLab - C2 MIKE SHE + ECOLab - C3 50 hours 400 hours Sun et al., 1999
  • 12. Pesticide reactive transport – soil columns © DHI 0 0.2 0.4 0.6 0.8 1 0 20 40 60 80 100 120 Relative concentration days Tuxen et al. (2000) - Isoproturon B II Tuxen et al. (2000) - Bromide B II MIKE SHE + ECOLab - Isoproturon B II MIKE SHE + ECOLab - Bromide B II Bromide Isoproturon Tuxen et al., 2000
  • 13. Model validation - Pesticides © DHI 0.0 0.2 0.4 0.6 0.8 1.0 0 20 40 60 80 100 120 Relative concentration days Tuxen et al. (2000) - MCPP B II Tuxen et al. (2000) - Bromide B II MIKE SHE + ECOLab - MCPP B II MIKE SHE + ECOLab - MCPP B II (new calibration) MIKE SHE + ECOLab - Bromide B II 0 0.2 0.4 0.6 0.8 1 0 20 40 60 80 100 120 Relative concentration days Tuxen et al (2000) - Dichlorprop B I Tuxen et al. (2000) - Bromide B I MIKE SHE + ECOLab - Dichlorprop B I MIKE SHE + ECOLab - Dichlorprop B I (new calibration) MIKE SHE + ECOLab - Bromide B I MCPP Dichloroprop
  • 14. 3 Integrated flow, temperature and ecological modelling Silver Creek, Idaho, USA © DHI
  • 15. Silver Creek Ecology © DHI Silver Creek is abundant in wildlife and a highly valued trout habitat Brown Trout and Rainbow Trout Numbers
  • 16. Silver Creek, Idaho © DHI Woor River Valley
  • 17. Lower Wood River Valley © DHI Semi-arid climate with low precipitation and high evaporation. Approximately 60% of the lower valley is cultivatated, of which 80% is irrigated.
  • 18. Flow Model (MIKE SHE-MIKE 11) © DHI 300 m cell size Other model components •Irrigation: surface and groundwater abstractions •Drainage: agricultural runoff Objectives •Integrated eco-hydrological model •Quantify changes in ecological status •Development of land management scenarios Scenarios •Reduction in GW abstraction 10%, 20%, 30% •Change of crops •Natural and past climate scenarios
  • 19. Flow Calibration © DHI Picabo St @ Silver Creek Stanton Crossing St @ Big Wood River
  • 22. Temperature Calibration © DHI 0 5 10 15 20 25 1/09 2/09 3/09 4/09 5/09 6/09 7/09 8/09 9/09 10/09 11/09 Temperature (°C) observed simulated
  • 24. Bioenergetic model © DHI Ecological indicator Model parameters EI = Min (1, AGSX / AGNS) Model equations
  • 25. Temperature and ecological indicator © DHI Ecological indicator Surface water temperature
  • 26. Temperature and ecological indicator © DHI Ecological indicator Surface water temperature
  • 27. 4 Nutrient removal in wetland environment, Odense, DK (ongoing) © DHI
  • 28. Brynemade, Odense River © DHI 25 m 12 m 6m
  • 33. Brynemade, Odense River © DHI To do next: •calculate the N contribute of the different sources to the river •model the N transformation processes •model how the biota reacts to the N in the environment •investigating potential changes to wetland design and characteristics in order to increase the nutrient retention capacity Integrated GW + SW modelling ECO Lab
  • 34. 5 Nuclear waste site risk assessment, SE (future) © DHI
  • 35. Nuclear waste site risk assessment © DHI •Fate of radioactive contaminants in groundwater and surface water •Surface water biota affected by radioactive contaminants
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