C.R. Kleijn
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1
The sustainability of geothermal energy in an aquifer
A mathematical model
Geothermal energy plays a role in advancing clean energy solutions for a sustainable future, which is why we investigate the sustainability of geothermal systems in an aquifer. The geothermal system examined in this research operates using two wells, positioned 1 km apart. One well pumps cold water into the porous medium and the second well pumps warm water out of the aquifer. As warm water is extracted, the temperature of the aquifer decreases. This cooling disturbs the chemical balance of the minerals in the water, which can lead to precipitation reactions. This precipitation reduces the porosity and consequently the permeability of the aquifer. The temperature distribution is modeled using the pressure and velocity field. This showed that the aquifer had cooled to 40˝C in 6 years. According to this result, the use of a geothermal aquifer is not sustainable. The cooling within 6 years is not accurate, because the boundary conditions that were selected were not fully chosen to reflect the complexities of the system and we didn’t properly consider the heat coming from Earth’s core. Precipitation reactions lead to an increase or decrease in concentration of various minerals in the water. These reactions cause deposits of solid minerals on the grains or porous rock, causing the aquifer to clog, allowing less and less water to flow through. In this model, the amount of precipitation was very small and therefore had little effect on the water flow and the sustainability of the aquifer.
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Geothermal energy plays a role in advancing clean energy solutions for a sustainable future, which is why we investigate the sustainability of geothermal systems in an aquifer. The geothermal system examined in this research operates using two wells, positioned 1 km apart. One well pumps cold water into the porous medium and the second well pumps warm water out of the aquifer. As warm water is extracted, the temperature of the aquifer decreases. This cooling disturbs the chemical balance of the minerals in the water, which can lead to precipitation reactions. This precipitation reduces the porosity and consequently the permeability of the aquifer. The temperature distribution is modeled using the pressure and velocity field. This showed that the aquifer had cooled to 40˝C in 6 years. According to this result, the use of a geothermal aquifer is not sustainable. The cooling within 6 years is not accurate, because the boundary conditions that were selected were not fully chosen to reflect the complexities of the system and we didn’t properly consider the heat coming from Earth’s core. Precipitation reactions lead to an increase or decrease in concentration of various minerals in the water. These reactions cause deposits of solid minerals on the grains or porous rock, causing the aquifer to clog, allowing less and less water to flow through. In this model, the amount of precipitation was very small and therefore had little effect on the water flow and the sustainability of the aquifer.
The salinity profile in a coastal sea-river system is the result of balancing of salt transport due to mixing of the water by tides and the freshwater discharge from the river. When for example during times of drought freshwater discharge suddenly declines, the salinity in the river may increase significantly and threaten drinking water supplies and agriculture. The time it takes for the salinity to reach the new equilibrium may be considerable. Thorough understanding of the adaptation process is essential for taking appropriate prevention measures. However, much about this adjustment process is still unknown, in particular regarding the interaction between the river and the adjacent sea. In this study, a simplified linear model is developed to describe a well-mixed river and the adjacent sea where the water flows radially away from the mouth of the river. The unique assumptions, most notably a time-independent intrusion length, allow for a unique analytical approach using the method of eigenfunction expansion. The smallest eigenvalues are found to define a time scale of the adjustment process. The eigenfunctions provide insight about how the salinity adjustment time varies within the system. The adjustment time does not only depend on the parameters that describe the new equilibrium, but also on the initial salinity. The eigenvalue time scales corresponding to the sea and to the river can then be used to determine the time scale of the coupled system. It is found that when the sea adjusts much faster than the river, the time scale of the river is leading the adjustment. When the eigenvalue time scale of the sea is similar to or larger than the eigenvalue time scale of the river, the adjustment time is significantly increased by the sea. When salinity is increasing, the sea restricts the inflow of salt in the river, while for decreasing salinity, the sea keeps transporting salt to the river by mixing which delays the adjustment. The model is applied to analyse a sudden decrease in freshwater discharge in the Rotterdam Waterway, which is part of the Dutch Rhine-Meuse delta. Results show that the salinity response is delayed compared to freshwater discharge, indicating that the adjustment time of the river indeed plays an important role. Further research should consider a more general dispersion relation or an extra vertical dimension to better describe estuaries that are not well-mixed. Using numerical methods there are many other possibilities to extend the model. The effect of tides on the presence and dynamics of the fresh water bulge in the sea is of specific interest.
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The salinity profile in a coastal sea-river system is the result of balancing of salt transport due to mixing of the water by tides and the freshwater discharge from the river. When for example during times of drought freshwater discharge suddenly declines, the salinity in the river may increase significantly and threaten drinking water supplies and agriculture. The time it takes for the salinity to reach the new equilibrium may be considerable. Thorough understanding of the adaptation process is essential for taking appropriate prevention measures. However, much about this adjustment process is still unknown, in particular regarding the interaction between the river and the adjacent sea. In this study, a simplified linear model is developed to describe a well-mixed river and the adjacent sea where the water flows radially away from the mouth of the river. The unique assumptions, most notably a time-independent intrusion length, allow for a unique analytical approach using the method of eigenfunction expansion. The smallest eigenvalues are found to define a time scale of the adjustment process. The eigenfunctions provide insight about how the salinity adjustment time varies within the system. The adjustment time does not only depend on the parameters that describe the new equilibrium, but also on the initial salinity. The eigenvalue time scales corresponding to the sea and to the river can then be used to determine the time scale of the coupled system. It is found that when the sea adjusts much faster than the river, the time scale of the river is leading the adjustment. When the eigenvalue time scale of the sea is similar to or larger than the eigenvalue time scale of the river, the adjustment time is significantly increased by the sea. When salinity is increasing, the sea restricts the inflow of salt in the river, while for decreasing salinity, the sea keeps transporting salt to the river by mixing which delays the adjustment. The model is applied to analyse a sudden decrease in freshwater discharge in the Rotterdam Waterway, which is part of the Dutch Rhine-Meuse delta. Results show that the salinity response is delayed compared to freshwater discharge, indicating that the adjustment time of the river indeed plays an important role. Further research should consider a more general dispersion relation or an extra vertical dimension to better describe estuaries that are not well-mixed. Using numerical methods there are many other possibilities to extend the model. The effect of tides on the presence and dynamics of the fresh water bulge in the sea is of specific interest.
Hot water pumped out of the ground for purposes of geothermal energy extraction cools down after it is used in a heat exchanger. The now cold water contains minerals that undergo a shift in chemical equilibrium. This may cause the minerals to come out of solution and become sediments. When pumping the cold water back into the porous ground, these sediments can cause clogging that eventually lead to a net energy loss using this source. It will require more mechanical energy to pump up the water than we gain in geothermal energy. In this report we aim to create a simple computer program that models the creation of these sediments. The goal is to know which minerals cause clogging, and which do not.
The program approximates the underground as a 0-dimensional tank with inflow and outflow called a continuously stirred tank reactor (CSTR). We derive a set of differential equations for both the inflow and outflow and the chemical reactions that take place. The chemistry used in this model uses data from individual reactions, which gives us differential equations for the concentrations of the minerals. These chemical reactions are very dependent on the temperature in the tank. Because the inflow water may have a different temperature than the tank, we will also make a differential equation for the temperature. Using a fourth-order Runge-Kutta scheme we can numerically integrate these equations in time.
To test the program, we use six of the most common dissolution reactions in groundwater. When using the program, we can see that some concentrations change by a very insignificant amount and therefore do not contribute to the clogging. These minerals are Mg²⁺ from the dissolution of dolomite and Fe²⁺ from the dissolution of magnetite. The program works as desired, but it does lack some elements, first and foremost the reactions between acids and bases, such as HCO₃⁻ and H⁺. ...
The program approximates the underground as a 0-dimensional tank with inflow and outflow called a continuously stirred tank reactor (CSTR). We derive a set of differential equations for both the inflow and outflow and the chemical reactions that take place. The chemistry used in this model uses data from individual reactions, which gives us differential equations for the concentrations of the minerals. These chemical reactions are very dependent on the temperature in the tank. Because the inflow water may have a different temperature than the tank, we will also make a differential equation for the temperature. Using a fourth-order Runge-Kutta scheme we can numerically integrate these equations in time.
To test the program, we use six of the most common dissolution reactions in groundwater. When using the program, we can see that some concentrations change by a very insignificant amount and therefore do not contribute to the clogging. These minerals are Mg²⁺ from the dissolution of dolomite and Fe²⁺ from the dissolution of magnetite. The program works as desired, but it does lack some elements, first and foremost the reactions between acids and bases, such as HCO₃⁻ and H⁺. ...
Hot water pumped out of the ground for purposes of geothermal energy extraction cools down after it is used in a heat exchanger. The now cold water contains minerals that undergo a shift in chemical equilibrium. This may cause the minerals to come out of solution and become sediments. When pumping the cold water back into the porous ground, these sediments can cause clogging that eventually lead to a net energy loss using this source. It will require more mechanical energy to pump up the water than we gain in geothermal energy. In this report we aim to create a simple computer program that models the creation of these sediments. The goal is to know which minerals cause clogging, and which do not.
The program approximates the underground as a 0-dimensional tank with inflow and outflow called a continuously stirred tank reactor (CSTR). We derive a set of differential equations for both the inflow and outflow and the chemical reactions that take place. The chemistry used in this model uses data from individual reactions, which gives us differential equations for the concentrations of the minerals. These chemical reactions are very dependent on the temperature in the tank. Because the inflow water may have a different temperature than the tank, we will also make a differential equation for the temperature. Using a fourth-order Runge-Kutta scheme we can numerically integrate these equations in time.
To test the program, we use six of the most common dissolution reactions in groundwater. When using the program, we can see that some concentrations change by a very insignificant amount and therefore do not contribute to the clogging. These minerals are Mg²⁺ from the dissolution of dolomite and Fe²⁺ from the dissolution of magnetite. The program works as desired, but it does lack some elements, first and foremost the reactions between acids and bases, such as HCO₃⁻ and H⁺.
The program approximates the underground as a 0-dimensional tank with inflow and outflow called a continuously stirred tank reactor (CSTR). We derive a set of differential equations for both the inflow and outflow and the chemical reactions that take place. The chemistry used in this model uses data from individual reactions, which gives us differential equations for the concentrations of the minerals. These chemical reactions are very dependent on the temperature in the tank. Because the inflow water may have a different temperature than the tank, we will also make a differential equation for the temperature. Using a fourth-order Runge-Kutta scheme we can numerically integrate these equations in time.
To test the program, we use six of the most common dissolution reactions in groundwater. When using the program, we can see that some concentrations change by a very insignificant amount and therefore do not contribute to the clogging. These minerals are Mg²⁺ from the dissolution of dolomite and Fe²⁺ from the dissolution of magnetite. The program works as desired, but it does lack some elements, first and foremost the reactions between acids and bases, such as HCO₃⁻ and H⁺.
Oil-in-water emulsions are very common in industrial processes, and understanding the fac- tors governing emulsification and de-emulsification is crucial. A mechanism through which de-emulsification commonly takes place is coalescence, being the act of two dispersed-phase droplets coming together to create a single larger droplet. Due to density differences, it is common for dispersed phase droplets to form a creaming layer at the top of the emulsion, in- creasing the likelihood of coalescence and therefore de-emulsification. The goal of this thesis is to use the lattice Boltzmann method to simulate the rising of a dispersed phase oil droplet towards a creaming layer due to buoyancy effects and to quantify the effect of the viscosities of both phases on the velocity with which aforementioned droplet rises. This is done using the Shan-Chen psuedopotential method. After introducing gravity into the simulation the the droplet is allowed to reach a terminal velocity vt. This is done for independently varying viscosities for both the dispersed phase and continuous phase (νd and νc respectively). A weakly inverse relation was found between vt and νc. An estimation for the terminal velocity of a droplet rising due to creaming behavior is found by cancelling drag force found from Stokes’ law against the buoyancy force. Found results were not in agreement with said estimation. Different explanations for this discrepancy are varying droplet diameters, varying droplet densities, droplet deformation and high velocity fluctuations. The terminal velocities were also compared to the ratio between the viscosity of both phases, but no correlation was found.
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Oil-in-water emulsions are very common in industrial processes, and understanding the fac- tors governing emulsification and de-emulsification is crucial. A mechanism through which de-emulsification commonly takes place is coalescence, being the act of two dispersed-phase droplets coming together to create a single larger droplet. Due to density differences, it is common for dispersed phase droplets to form a creaming layer at the top of the emulsion, in- creasing the likelihood of coalescence and therefore de-emulsification. The goal of this thesis is to use the lattice Boltzmann method to simulate the rising of a dispersed phase oil droplet towards a creaming layer due to buoyancy effects and to quantify the effect of the viscosities of both phases on the velocity with which aforementioned droplet rises. This is done using the Shan-Chen psuedopotential method. After introducing gravity into the simulation the the droplet is allowed to reach a terminal velocity vt. This is done for independently varying viscosities for both the dispersed phase and continuous phase (νd and νc respectively). A weakly inverse relation was found between vt and νc. An estimation for the terminal velocity of a droplet rising due to creaming behavior is found by cancelling drag force found from Stokes’ law against the buoyancy force. Found results were not in agreement with said estimation. Different explanations for this discrepancy are varying droplet diameters, varying droplet densities, droplet deformation and high velocity fluctuations. The terminal velocities were also compared to the ratio between the viscosity of both phases, but no correlation was found.
Twin particles and their love-hate relationship
An experimental study on shape-dependent particle pair interactions in confined Stokes flow
Master thesis
(2021)
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Robert Leliveld, H.B. Eral, J.T. Padding, C.R. Kleijn, R.N. Georgiev, N. Nagalingam
This thesis describes a study into pairwise particle interactions within a Hele-Shaw geometry, using stop-flow lithography. By exposing a photoreactive mixture to a strong UV-pulse, a hydrogel is formed. The shape of this hydrogel is controlled by masking part of the light beam. This process takes place while the Hele-Shaw channel is placed on the stage of a microscope, which allows these hydrogel particles to be viewed and tracked. Improvements were made to increase the accuracy and precision of the experimental set-up. No- tably, the initially present mismatch of intra-pair particle thickness was greatly reduced by changing the method of particle pair production. By tracking these pairs of particles, information is obtained regarding their motions and velocity relative to one another. Experiments were performed for a selection of particle shapes and compared to numerical simulations of identical geometries. Simulations predicted that attractive and repulsive velocities should be noticed depending on the separation distance and shape of the particles. Qualitatively, the experiments agree to a certain extent with the simulations. It was demonstrated that the pairwise interactions are indeed dependent on their shape. Furthermore, the magnitude of these interactions qualitatively matched with the experimental data. Quantitatively, the experimental data did not agree with the simulations, but strong evidence was presented to indicate that the UV-light hitting the sample was not uniformly distributed. This results in a discrepancy in particle thickness between the pair, which skews the experimental data. Novel insights were gained on the applicability of the current literature model on hydrogel particle propagation. In contrast to the current model, it was experimentally demonstrated that the shape and (in-plane) size of the particle affects its thickness.
...
This thesis describes a study into pairwise particle interactions within a Hele-Shaw geometry, using stop-flow lithography. By exposing a photoreactive mixture to a strong UV-pulse, a hydrogel is formed. The shape of this hydrogel is controlled by masking part of the light beam. This process takes place while the Hele-Shaw channel is placed on the stage of a microscope, which allows these hydrogel particles to be viewed and tracked. Improvements were made to increase the accuracy and precision of the experimental set-up. No- tably, the initially present mismatch of intra-pair particle thickness was greatly reduced by changing the method of particle pair production. By tracking these pairs of particles, information is obtained regarding their motions and velocity relative to one another. Experiments were performed for a selection of particle shapes and compared to numerical simulations of identical geometries. Simulations predicted that attractive and repulsive velocities should be noticed depending on the separation distance and shape of the particles. Qualitatively, the experiments agree to a certain extent with the simulations. It was demonstrated that the pairwise interactions are indeed dependent on their shape. Furthermore, the magnitude of these interactions qualitatively matched with the experimental data. Quantitatively, the experimental data did not agree with the simulations, but strong evidence was presented to indicate that the UV-light hitting the sample was not uniformly distributed. This results in a discrepancy in particle thickness between the pair, which skews the experimental data. Novel insights were gained on the applicability of the current literature model on hydrogel particle propagation. In contrast to the current model, it was experimentally demonstrated that the shape and (in-plane) size of the particle affects its thickness.
Crowd modelling is essential to the understanding of pedestrian logistics and prevention of crowd disasters. Agent-based approaches can realistically predict crowd behaviour. The social force model as proposed by Helbing and Mólnar in 1995[1] is a widely used agent-based approach. This is a physical model for psychological behaviour that relies strongly on its various parameter values. To investigate the underlying thought of the social force model the physical consequences of the effects and parameters are reviewed in this thesis. Next to this, an adjustment onHelbing andMólnar’s model is made by treating agents as particleswith a hard kernel, requiring a walkover- and ghost-prevention functionality. In addition, it is suggested to set the agent interaction magnitude to U0 ®¯ Æ 21 m2/s2. Subsequently, the adjusted model is validated to empirical research done by Seyfried et al.[2] and to simulations done by Helbing andMólnar[1]. For validation a cluster analysis method is developed to give a quantitative measure of the number of lanes.
...
Crowd modelling is essential to the understanding of pedestrian logistics and prevention of crowd disasters. Agent-based approaches can realistically predict crowd behaviour. The social force model as proposed by Helbing and Mólnar in 1995[1] is a widely used agent-based approach. This is a physical model for psychological behaviour that relies strongly on its various parameter values. To investigate the underlying thought of the social force model the physical consequences of the effects and parameters are reviewed in this thesis. Next to this, an adjustment onHelbing andMólnar’s model is made by treating agents as particleswith a hard kernel, requiring a walkover- and ghost-prevention functionality. In addition, it is suggested to set the agent interaction magnitude to U0 ®¯ Æ 21 m2/s2. Subsequently, the adjusted model is validated to empirical research done by Seyfried et al.[2] and to simulations done by Helbing andMólnar[1]. For validation a cluster analysis method is developed to give a quantitative measure of the number of lanes.