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Underground Pumped Storage Hydroelectricity using abandoned works (open pits and deep mines)

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Underground

Pumped

Storage

Hydroelectricity

(UPSH) using abandoned works (open pits or deep

mines): Groundwater flow impacts

Pujades, E., Willems, T., Bodeux, S., Orban, P., Dassargues, A. (estanislao.pujades@ulg.ac.be)

AGU FALL MEETING December 14-18, 2015

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Index

 Introduction

 Motivation and objectives

 Methodology

 Problem statement and procedures

 Numerical results

 Main impacts and influence of aquifer parameters, reservoir properties and pumping-injection characteristics

 Analytical solutions

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Introduction

 Efficiency of conventional energy plants needs to be improved

 The best option to increase the efficiency consists in adjusting the produced electricity to the demand

 This is not always possible:

 Nuclear energy plants: Constant production

 Wind and solar energy plants: Production not related with the demand.

 Pumped Storage Hydroelectricity (PSH) plants can be used

 Landscape and wildlife impacts

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Introduction

 Underground Pumped Storage

Hydroelectricity (UPSH) plants can be

constructed in flat areas

 Landscape and wildlife impacts are lower, difference in the elevation between reservoirs is higher (smaller reservoirs can store more energy) and MORE AVAILABLE SITES

 Underground reservoir can be drilled or

abandoned cavities can be used (open pits or deep mines)

 Cheaper but impacts the surrounding aquifer.

 Main impacts: Modification of piezometric head and/or the chemistry of the groundwater

Natural Head Modified Head

Upper reservoir

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Objectives

 To define the main impacts caused by UPSH plants on the piezometric head.

 To evaluate the influence on the groundwater flow impacts of aquifer parameters,

underground reservoir properties, and pumping/injection characteristics.

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Methods

 Reference scenario

K is 2 m/d, S is 0.1, radius of the mine is 50m, α’ is 100d-1 , cycles are regular

 One variable is modified at each alternative scenario to determine its influence

 Aquifer parameters

 Reservoir properties

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Results (general behavior)

Time (d) Δ hea d (m)

Dynamic steady state

h

Initial head=50m depth

Max. drawdown Bottom obs. Top obs. Time (d) Time (d) Δ head (m) Max. drawdown h Initial head h

Initial head=50m depth

Dynamic steady state

Δ head (m) Oscillations magnitude Average head

 Main impact consists in oscillation of the piezometric head

 Piezometric evolution depends on depth

 Some relevant characteristics are defined to compare the impacts caused in different scenarios.

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Results (aquifer parameters)

Bottom obs. Top obs.

K=2m/d and θS=0.1 K=0.2m/d θS=0.05d K=0.2m/d θS=0.05d K=2m/d and θS=0.1 If K is reduced: Oscillations magnitude Max. Drawdown

Time to reach a dynamic steady state

If S (θS)is reduced:

Oscillations magnitude

Max. Drawdown

Time to reach a dynamic steady state (deduced analytically)

Time (d)

Δ

head

(m)

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Time (d)

Δ

head

(m)

Time (d)

Results (reservoir characteristics)

α’=1d-1 α’=100d-1 and Vol.=0.5hm3 Vol.=0.125hm3 Vol.=0.125hm3 α’=1d-1 α’=100d-1 and Vol.=0.5hm3

Bottom obs. Top obs.

If α’ is reduced:

Oscillations magnitude

Max. Drawdown

If the size is reduced:

Oscillations magnitude

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Results (pumping-injection periods)

Time (d) Δ head (m) Time (d) SceR Sce2 Sce1 Bottom obs. Top obs.

SceR (regular) 0.5d pumping (1m3/s) + 0.5d injection (1m3/s)

Sce1 (irregular) 0.5d pumping (1m3/s) + 0.25d injection (2m3/s)+0.25d no-activity

Sce2 (irregular) 0.5d pumping (1m3/s) + 0.25d no-activity +0.25d injection (2m3/s)

SceR Sce2

Oscillations magnitude increases with irregular cycles (the same volume injected in less time → more linear behavior)

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Results (analytical solutions)

 Derived from equations for large diameter well (Papadopulos-Cooper (1967) and

Boulton-Streltsova (1976)

 Time to reach the dynamic steady state

Dynamic steady state is reached when increment of F (of a continuous pumping) is constant that occurs when dF/dln(1/u) starts to decrease.

 Oscillations magnitude

, ,

4 W o ew Q s F u r r Kb    2 4 ur S Kbt W r S rew c  

 

4 0.5 to 0 Q s F T      

Increment of time equal to the duration of pumping or injections

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Conclusions

 Groundwater flow impact consists in an oscillation of the piezometric head. It drops at the beginning and recovers until reaching a dynamic steady state.

Groundwater flow impact is higher if the hydraulic diffusivity (T/S) is increased. Therefore, impact would be higher in high transmissive confined aquifers.

 The properties of the underground reservoir (walls waterproofed and size) and

characteristics of pumping-injections periods are important to estimate the flow impacts.

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E. Pujades gratefully acknowledges the financial support from the University of Liège and the EU through the Marie Curie BeIPD-COFUND postdoctoral fellowship programme (2014-2016). This research has been supported by the Public Service of Wallonia – Department of Energy and sustainable Building.

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