Effects of CO2 and acid gas injection on enhanced gas recovery and storage
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Abstract
Sequestration of CO2 and other associated waste gases in natural gas reservoirs is an option to mitigate greenhouse gases and enhanced gas recovery. This paper examines strategies to maximize enhanced gas recovery in a natural gas reservoir via subsurface storage of potential associated waste gases such as CO2 and H2S. Numerical simulations are performed with a compositional reservoir simulator ‘Tempest’ using experimental data initially produced by Clean Gas Technology Australia (CGTA) at Curtin University in 2009. The simulation results shows that additional gas is recovered by gas-gas displacement after injecting CO2 and acid gas (CO2–H2S) in two separate scenarios. Importantly, when pure CO2 is injected, CO2 breakthrough at the production well occurred faster than the breakthrough under mixed CO2–H2S injection.
Keywords
Gas injection CO2 breakthrough CO2 storage Enhanced gas recoveryIntroduction
Greenhouse gas injection into geological formations is often considered when attempting to mitigate atmospheric emissions and enhanced hydrocarbon recovery. Sequestrating CO2 to mitigate CO2 atmospheric emissions is available and technologically feasible because of experience gained in enhanced oil recovery (EOR) by CO2 injection. The majority of these operations are located in Canada and United States (Bachu et al. 2003). In particular, during the past decade, oil and gas producers in the Alberta basin of western Canada are increasingly being required to reduce atmospheric emissions by injecting acid gas into deep geological formations (Huerta et al. 2012).
The concept of CO2-EOR, is now considered to be matured, in Canada for conventional oil reservoirs, and has been successfully applied in Zama (Huerta et al. 2012). Additionally, there are several current and planned projects for CO2-EOR that involve the separation and geological storage of CO2. The Sleipner gas field in the North Sea (operated by Statoil) is one such pilot project where separated CO2 is injected into an underground saline aquifer for sequestration purposes. Other commercial projects are based in central Algeria in Salah (operated by BP) (Algharaib and Abu Al-Soof 2008). Similarly, similar processes are under consideration for sour reservoirs being produced in the Arabian Gulf and central Asia. In particular, producers in Iran, Arab Emirates and Kazakhstan are turning to acid gas disposal by deep injection.
However, data on these operations are only available for the CO2 injection of enhanced oil recovery and storage, mostly in the Permian basin in west Texas (Bennion and Bachu 2008). Experimental data on impure acid gas injection into natural gas reservoirs for enhanced gas recovery and storage are not yet available. While some published simulation studies attempt to investigate the CO2-EGR and storage processes, the focus of these studies is to achieve this task in depleted natural gas reservoirs. In addition, several studies are limited to considering only the economic aspects of CO2 capture and storage. However, Hussen et al. (2012), Khan et al. (2012) simulate experimental data and outline factors that are favourable to enhanced gas recovery and the storage of CO2 under supercritical CO2 injection.
This study intends to examine the effects of pure CO2 and acid gas injection into known natural gas reservoirs in Western Australia, and the displacement of native gases to better understand the mechanisms involved in enhanced gas recovery regarding geological storage.
Reservoir simulation model
Hypothetical gas reservoir model
General reservoir characteristics by layer
| Layers (1–4) | Very low | High | Medium | Low |
|---|---|---|---|---|
| Core plugs | S_A_4 | S_A_1 | S_A_2 | S_A_3 |
| Swcr | 0.120 | 0.175 | 0.145 | 0.100 |
| Sgcr | 0.05 | 0.03 | 0.04 | 0.05 |
| Porosity (%) | 0.04 | 0.17 | 0.14 | 0.09 |
| K z (md) | 4 | 370 | 100 | 6 |
| K y (md) | 6 | 390 | 115 | 8.5 |
| K x (md) | 6 | 390 | 115 | 8.5 |
| Z direction (cells) | 8 | 10 | 12 | 8 |
| Z thickness (m) | 50 | 70 | 120 | 60 |
Reservoir model parameters
| Property | Value |
|---|---|
| Reservoir type | Sandstone |
| Reservoir depth | 3,650 m |
| Area (X–Y direction) | 1,700 m X, 2,300 m Y |
| Thickness (Z direction) | 300 m |
| Grids in X direction | 32 |
| Grids in Y direction | 44 |
| Grids in Z direction | 8, 10, 12 and 8 for L1, L2, L3 and L4 |
| Relative permeability | JBN method and Darcy’s law |
| Initial reservoir temperature | 160 °C |
| Initial reservoir pressure | 406 bar |
| Well injector pressure (maximum) | 450 bar |
| Well producer pressure (minimum) | 50 bar |
| Injection rate | 1,250 × 1,000 m3/day |
| Maximum gas production rate | 9,600 × 1,000 m3/day |
Enhance gas production
Cumulative gas production and average bottom-hole
CO2 and acid gas breakthrough
Storage of gas injection
Produced fraction of different injected gas
Injection rate and production rate of the injected gas
Furthermore, CO2 and CO2–H2S storage is evaluated after breakthrough is illustrated for both scenarios in terms of the produced fraction of injected CO2 and H2S–CO2 after allowing for the initial gas reservoir conditions. After estimating the produced fraction of the injected gas for both cases, production rates of the injected gas are calculated by multiplying the produced fraction of the injected gas from each well by production rate of CO2 or H2S–CO2 (at the same time during the injection). Additionally, the total production rates of injected CO2 or H2S–CO2 are compared, after allowing for the injection rate under alternative storage scenarios. Figure 5 shows that pure CO2 injection leads to greater production rates of injected gas when compared to acid gas injection scenario. In addition, during the CO2 injection process some of the injected CO2 dissolves in the formation of water. Finally, acid gas injection because of favourable H2S solubility requires smaller volumes of injected gas to be available in the gas reservoir to mix. This will lead to delay breakthrough and results in more storage.
Results and discussion
While injected solvent and extant gases mix and contaminate production, the best strategy to employ depends on the physical properties of solvents when compare to those of methane, the natural gas in the reservoir. In this study, the physical properties of methane, H2S and CO2 are studied at different pressures and temperatures using HYSYS software. The simulation results indicate that H2S has higher viscosity and density compared to CO2 and methane. Another physical property is the solubility factor. Al-Hashami et al. (2005) claim carbon dioxide is potentially more soluble than methane. The current simulation study and other laboratory experiments (Pooladi-Darvish et al. 2009) confirm that the solubility of H2S is higher than CO2 solubility.
Furthermore, injected gas whether CO2 or/and H2S–CO2 is migrated downward due to gravity, and these forces will stabilize the displacement between the injected gas and methane initially in place because of low mobility ratio of CO2 and acid gas, respectively. Additionally, higher acid gas solubility in forming water compared to that for pure CO2 injection delays breakthrough. Any of these gases as injection considered could potentially provide favourable reservoir re-pressurization without extensive gas-gas mixing, and benefit the enhanced gas recovery (EGR) and storage process. Therefore, gas-gas mixing technically could be supervised via good reservoir management and production control measures, because these physical properties of the solvents undergo large changes as the pressure increases.
Injection sweep efficiency
Under H2S–CO2 and pure CO2 mixing in the injection stream, the potential for EGR and storage are investigated at an injection rate of 1,250 × 100 m3/day. Under CO2 injection, slightly higher methane production is recovered because CO2 is more mobile (less viscous) compared to H2S in forming water. Therefore, pure CO2 injection is expected to rise to the upper layers more quickly than impure CO2 injection. In this instance, the injected gases are expected to overrun native gases in the production wells faster. Although, this scenario will affect sweep efficiency at some time, to that stage reservoir re-pressurization will occur faster.
Conclusion
This paper develops a true gas reservoir model using the reservoir simulation software Tempest and true reservoir experimental data produced by CGTA. The simulation indicates that gas injection for enhanced gas recovery and storage is technically feasible for this particular reservoir. Even though, reservoir heterogeneity can cause increase in CO2 or/H2S–CO2 breakthrough, reservoir re-pressurization can be considered a support against the concept of breakthrough. A benefit of re-pressurization is that it can occur prior to CO2 and acid gas breakthrough. Accordingly, an optimal strategy is to benefit from the high viscosity, density and solubility of injected gases, reservoir re-pressurization by injecting gas into the lower portions of the reservoir to drive out the out natural gas from the bottom reservoir layers, while minimizing mixing and contamination in the upper parts of the reservoir.
References
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