SPE 169578 CO2 Injection for Enhanced Gas Recovery

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SPE 169578-MS CO 2 Injection for Enhanced Gas Recovery Sumeer Kalra, Xingru Wu, University of Oklahoma Copyright 2014, Society of Petroleum Engineers This paper was prepared for presentation at the SPE Western North American and Rocky Mountain Joint Regional Meeting held in Denver, Colorado, USA, 1618 April 2014. This paper was selected for presentation by an SPE program committee following review of information contained in an abstract submitted by the author(s). Contents of the paper have not been reviewed by the Society of Petroleum Engineers and are subject to correction by the author(s). The material does not necessarily reflect any position of the Society of Petroleum Engineers, its officers, or members. Electronic reproduction, distribution, or storage of any part of this paper without the written consent of the Society of Petroleum Engineers is prohibited. Permission to reproduce in print is restricted to an abstract of not more than 300 words; illustrations may not be copied. The abstract must contain conspicuous acknowledgment of SPE copyright. Abstract Literature shows that there is a significant amount of natural gas available for enhanced recovery in the depleted reservoirs; at the same time, the depleted gas reservoirs are a proven storage facility for Carbon Dioxide (CO 2 ) storage in terms of reservoir integrity. Conceptually, injecting CO 2 into a depleted gas reservoir will not only potentially rejuvenalize the gas production, but will also store the greenhouse gas in a proven subsurface formation. Study on CO 2 phase behavior in subsurface conditions shows that CO 2 most likely will be in super-critical state which exhibits liquid-like density and gas-like viscosity. These properties are favorable in displacing natural gas reservoirs in volumetric and pore scale sweep efficiency. Using numerical reservoir simulation on a synthetic case with multiple scenarios, this paper identifies the most amenable characteristics of a reservoir for enhancing gas production by injecting CO 2 and analyzes the parameters influencing this secondary recovery process. In the paper, reservoir depth, depletion pressure ratio, aquifer activity, inclination angle, reservoir heterogeneity with various permeability arrangement, injection rate, and producer bottomhole pressure will be studied on the synthetic model. Furthermore, this paper will quantify the amount of natural gas which can be produced and CO 2 that can be stored in an ideal case using economic matrix. From this study, the ideal candidates for enhanced gas recovery by CO 2 injection will be proposed based on simulation results, thus one can screen the available gas reservoirs for CO 2 storage purpose and can quickly quantify the additional gas production from the secondary recovery. Introduction World energy demands are only met by the utilization of fossil fuels but the byproducts of combustion are a major cause of concern. Carbon Dioxide (CO 2 ) sequestration can help in the mitigation of global warming concerns caused by CO 2 emission (Agarwal et al. 2011). CO 2 sequestration is a process of capturing CO 2 and permanently sequestrating it into a reservoir. Major candidates for CO 2 sequestration are deep saline aquifers, depleted oil/gas reservoirs and coal seams. The subsurface storage of CO 2 mechanisms, techniques, and pilot projects have been well documented in literature (Clemens and Wit 2002, Gallo et al. 2002, Oldenburg and Benson 2002, Oldenburg 2003, Jikich et al. 2003). For depleted gas reservoirs, some reservoirs had to be abandoned at high pressures because of a variety of reasons such as formation subsidence, water invasion, and non-economic production rates. In gas reservoir development, high abandoned pressure indicates that there is still a large quantity of natural gas available for further development by pushing the subsurface and technical limits. A technique to repressurize the reservoir is to inject CO 2 to displace the remaining oil/gas present in the formation. As the pressure buildup, cumulative production is increased and also the depleted reservoir can act as an ideal carbon sink for long-term storage. In summary, injecting CO 2 in a depleted gas reservoir will not only potentially rejuvenalize the gas production by pressure buildup but will also store the greenhouse gas in a proven subsurface formation. There are four primary reasons that a depleted gas reservoir be a good candidate for CO 2 storage. First of all, the gas reservoir is a container with a proven integrity. One big concern of CO 2 subsurface storage is that it potentially leaks out to aquifer and surface (Maldal and Tappel 2004, Michael et al. 2010, Klusman 2003, Divison et al. 2010). For a depleted gas reservoir, its integrity has been tested by the original natural gas in geological time scale. Secondly, CO 2 can efficiently displace the remaining natural gas because of gravity segregation. Therefore, natural gas is produced from an upper part of the reservoir and CO 2 is injected at bottom part of the formation for better sweep efficiency and avoiding gas mixing to a better extent.

Transcript of SPE 169578 CO2 Injection for Enhanced Gas Recovery

SPE 169578-MS

CO2 Injection for Enhanced Gas Recovery Sumeer Kalra, Xingru Wu, University of Oklahoma

Copyright 2014, Society of Petroleum Engineers This paper was prepared for presentation at the SPE Western North American and Rocky Mountain Joint Regional Meeting held in Denver, Colorado, USA, 16–18 April 2014. This paper was selected for presentation by an SPE program committee following review of information contained in an abstract submitted by the author(s). Contents of the paper have not been reviewed by the Society of Petroleum Engineers and are subject to correction by the author(s). The material does not necessar ily reflect any position of the Society of Petroleum Engineers, its officers, or members. Electronic reproduction, distribution, or storage of any part of this paper without the written consent of the Society of Petroleum Engineers is prohi bited. Permission to reproduce in print is restricted to an abstract of not more than 300 words; illustrations may not be copied. The abstract must contain conspicuous acknowledgment of SPE copyright.

Abstract Literature shows that there is a significant amount of natural gas available for enhanced recovery in the depleted reservoirs; at

the same time, the depleted gas reservoirs are a proven storage facility for Carbon Dioxide (CO2) storage in terms of reservoir

integrity. Conceptually, injecting CO2 into a depleted gas reservoir will not only potentially rejuvenalize the gas production,

but will also store the greenhouse gas in a proven subsurface formation.

Study on CO2 phase behavior in subsurface conditions shows that CO2 most likely will be in super-critical state which

exhibits liquid-like density and gas-like viscosity. These properties are favorable in displacing natural gas reservoirs in

volumetric and pore scale sweep efficiency. Using numerical reservoir simulation on a synthetic case with multiple scenarios,

this paper identifies the most amenable characteristics of a reservoir for enhancing gas production by injecting CO2 and

analyzes the parameters influencing this secondary recovery process. In the paper, reservoir depth, depletion pressure ratio,

aquifer activity, inclination angle, reservoir heterogeneity with various permeability arrangement, injection rate, and producer

bottomhole pressure will be studied on the synthetic model. Furthermore, this paper will quantify the amount of natural gas

which can be produced and CO2 that can be stored in an ideal case using economic matrix.

From this study, the ideal candidates for enhanced gas recovery by CO2 injection will be proposed based on simulation

results, thus one can screen the available gas reservoirs for CO2 storage purpose and can quickly quantify the additional gas

production from the secondary recovery.

Introduction World energy demands are only met by the utilization of fossil fuels but the byproducts of combustion are a major cause of

concern. Carbon Dioxide (CO2) sequestration can help in the mitigation of global warming concerns caused by CO2 emission

(Agarwal et al. 2011). CO2 sequestration is a process of capturing CO2 and permanently sequestrating it into a reservoir.

Major candidates for CO2 sequestration are deep saline aquifers, depleted oil/gas reservoirs and coal seams. The subsurface

storage of CO2 mechanisms, techniques, and pilot projects have been well documented in literature (Clemens and Wit 2002,

Gallo et al. 2002, Oldenburg and Benson 2002, Oldenburg 2003, Jikich et al. 2003).

For depleted gas reservoirs, some reservoirs had to be abandoned at high pressures because of a variety of reasons such as

formation subsidence, water invasion, and non-economic production rates. In gas reservoir development, high abandoned

pressure indicates that there is still a large quantity of natural gas available for further development by pushing the subsurface

and technical limits. A technique to repressurize the reservoir is to inject CO2 to displace the remaining oil/gas present in the

formation. As the pressure buildup, cumulative production is increased and also the depleted reservoir can act as an ideal

carbon sink for long-term storage. In summary, injecting CO2 in a depleted gas reservoir will not only potentially

rejuvenalize the gas production by pressure buildup but will also store the greenhouse gas in a proven subsurface formation.

There are four primary reasons that a depleted gas reservoir be a good candidate for CO2 storage. First of all, the gas reservoir

is a container with a proven integrity. One big concern of CO2 subsurface storage is that it potentially leaks out to aquifer and

surface (Maldal and Tappel 2004, Michael et al. 2010, Klusman 2003, Divison et al. 2010). For a depleted gas reservoir, its

integrity has been tested by the original natural gas in geological time scale. Secondly, CO2 can efficiently displace the

remaining natural gas because of gravity segregation. Therefore, natural gas is produced from an upper part of the reservoir

and CO2 is injected at bottom part of the formation for better sweep efficiency and avoiding gas mixing to a better extent.

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Thirdly, the cost of sequestration and storage of CO2 can be offset by income from additional gas production; verse versa, the

gas production cost will be mitigated via taxes of using CO2. Fourthly, the industry can capitalize on existing wells (previous

producer or injector) rather than drilling new wells, which potentially makes the project more economically viable. Therefore,

we consider depleted gas reservoirs as the target for CO2 storage as well as enhanced gas production.

However, a good candidate does not guarantee a viable engineering project as there are many uncertainties in subsurface

conditions. What are the ideal characteristics for enhancing gas production by injecting CO2 in the formation is the problem

that this paper focuses on. We used numerical simulator as the tool to study some key parameters controlling the subsurface

flow. Our simulation work is based on a synthetic case with an aim to study the generic relationship between CO2 storage and

natural gas recovery with different reservoir descriptions. The purpose is to define the typical characteristics of the formation

for CO2 storage with the highest possible natural gas recovery. We present our results using several dimensionless variables

so that the conclusions drawn from this study can be applied to other reservoirs without scaling issue.

Physical Properties of CO2 and CH4 Knowledge of thermodynamic properties of Carbon Dioxide (CO2) and Methane (CH4) are important as these properties are

responsible to optimize compression, monitor transportation and model mobility of gas in the reservoir conditions. Some key

parameters of Methane and Carbon Dioxide are listed in Table 1. Likely, CO2 at deep reservoir conditions behave as a super

critical fluid which has viscosity of a gas and density of a liquid. The higher density of CO2 means that it will migrate

downward in the reservoir as relative to CH4. Figure 1 describes the density comparison of CH4 and CO2 changes with depth.

Methane density is calculated using Jacobsen and Stewart equation (Angus et al. 1976) and CO2 density is estimated by an

equation developed by Chapela and Rowlinson (Younglove and Ely 1987). The figure clearly signifies that CO2 is highly

denser than CH4 throughout the reservoir pressure range. CO2 will tend to migrate in the downward direction relative to CH4.

Figure 2 shows the viscosity comparison of CO2 and CH4 with respect to formation depth. The mobility ratio of CH4

displacement by CO2 will be very favorable rendered by the highly viscous property of CO2. Figure 3 shows the comparison

of solubilities of CH4 and CO2 in formation brine. Solubility of CO2 is modeled using correlations developed by Chang,

Coats and Nolen (Chang et al. 1996) and CH4 solubility in aqueous phase is modeled using correlation developed by Duan

and Mao (Duan and Mao 2006). The solubility curve shows that CH4 solubility in brine water is negligible as compared with

the solubility of CO2. In these correlations, the solubilities of CO2 and CH4 are a function of temperature, pressure and

salinity. The comparison of solubility at salinity range from 1,000 ppm to 300,000 ppm in Figure 3 indicates that the

solubility decreases with an increase in salinity because of the presence of dissolved solids in the formation water, also

termed as a salting out effect (Bachu et al. 2003).

All above calculations are done considering normal temperature gradient of 0.015°F/ft and hydrostatic pressure gradient of

0.433 Psi/ft. Due to these properties, there are fewer tendencies to finger and intermix between the gases (Oldenburg et al.

2001). From these properties, it can be inferred that the properties of CO2 and CH4 with limited inter mixing, makes depleted

gas reservoirs an ideal candidate for CO2 injection for enhanced gas recovery and storage. Furthermore, from these figures,

we can see that shallow reservoirs below depths of 4,000 ft will provide less storage capacity and can be ignored for carbon

storage and enhanced gas recovery. The density and viscosity contrast between CO2 and CH4 is very high beyond 4,000 ft;

making these reservoirs a suitable candidates for enhanced gas recovery and carbon storage.

Base Case Description A depleted gas reservoir is modeled for this study using a commercial simulator CMG-GEM developed by Computer

Modelling Group Ltd. for general purpose of compositional simulation. The original reservoir pressure was assumed to be

7,000 Psia and after years of production it has depleted to 4,350 Psia which is the initial reservoir pressure for our study. The

reservoir temperature is a constant 200 °F during injection and production. We use 99.9% CH4 and a trace of CO2 to

represent the original gas composition in the reservoir. When we analyze the results, CH4 recovery will be used to represent

the natural gas recovery. Key parameters in the model of reservoir and well properties for the base case are outlined inTable

2. Figure 4 illustrate the relative permeability curve used in the simulation study and Figure 5 depicts the simulation model

for the base case with an injector and a producer well. The reservoir top layer is at a depth of 9,700 ft with 300 ft payzone

thickness and a positive dip of 15°. Water-Gas contact (DWGC) is defined at 9,700 ft signifying the presence of aquifer zone

( =1.0).

Initially, the reservoir is saturated with natural gas and 10% residual water saturation. Injector well has perforations at the

lower most grid block and producer well perforations are in the top layer because of the density contrast to delay CO2

breakthrough during natural gas production. For all simulation modeling, natural gas production is stopped at a time when

mole fraction of CO2 in the producing stream reaches a set value of 50%. For the injector, the injection will stop when

injection bottomhole pressure reaches the original reservoir pressure. For the base case, the reservoir has a uniform

permeability of 100 mD.

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Figure 6 demonstrates the importance of CO2 injection. Three scenarios were simulated: No injection (reservoir blowdown

till the reservoir pressure reaches 2000 psia); No Production case, and using CO2 injection simultaneously with natural gas

production. It shows that the natural gas recovery factor increases from 46.3% to 94.8 % and also the percent hydrocarbon

pore volume (%HCPV) of CO2 injected is increased from 95.8% to 166.6%. The simulated results clearly justify the

importance of CO2 injection to potentially rejuvenalize the gas production and also allow higher quantity of CO2 storage into

the subsurface formation.

Sensitivity Analysis on the Base Model Reservoir Heterogeneity: Reservoir heterogeneity is probably the most important parameter to be considered for numerical

simulation studies because reservoir permeability defines the path for the fluid to flow. For the base case, we considered ideal

situation with uniform permeability of 100 mD. The study evaluated the effects of reservoir heterogeneity in the displacement

process. The method used to quantify reservoir heterogeneity is the Dykstra-Parsons Coefficient (DPC), as elaborated in

Appendix A. The Dykstra-Parsons Coefficient relates standard deviation of permeability profile to the median permeability.

CO2 mixing with the in-situ gas in the reservoir can potentially degrade the gas price. Therefore, it is important to capture the

mixing physics using the numerical simulation. Recovery efficiency depends on how much CO2 “mixes” with the in-situ gas

in the reservoir. In reservoir simulation, physical dispersion is commonly approached by numerical dispersion.

As considering reservoir heterogeneity, the permeability variation within the reservoir applying the Dykstra-Parsons

Coefficient of 0.5 can be observed in Figure 7. The effect of dispersion can be observed in Figure 8 where the profile of mole

fraction of CO2 mixing in the reservoir is described with varying Dykstra-Parson Coefficient. The CO2 mole fraction profile

is observed when 46% HCPV of CO2 is injected into the reservoir. It shows that with zero DPC, no mixing takes place and

CO2 profile is very smooth. With increasing diffusivity, bigger mixing zones are observed and CO2 is displaced all over the

reservoir. Bigger mixing zones leads to early CO2 breakthrough in the producer and results in lower natural gas recovery as

observed in Figure 9. Given that the uniform permeability for analysis also provides best case scenario of the reservoir which

is usually not observed during operations, it is very important to take into account the effect of reservoir heterogeneity in

defining the operational parameters for CO2 sequestration and enhanced gas recovery.

For all the following simulation analysis, we assumed reservoir heterogeneity with Dykstra-Parsons Coefficient of 0.5. Also,

the maximum injection bottomhole pressure is kept constant at 7,000 Psia and minimum production bottomhole pressure is

constant at 1,000 Psia.

Depletion Pressure Ratio: Depletion pressure ratio is defined as the ratio of initial reservoir pressure when EGR starts to the

original reservoir pressure. Depletion pressure provides broader understanding of the present reservoir conditions instead of

analyzing results considering only current reservoir pressure. It will help in the decision making for the time frame in a

reservoir development to be considered for CO2 injection and allow the production from the reservoir through secondary

recovery. Three cases with initial reservoir pressures of 4,500, 3,000 and 2,000 Psia are considered for the study leading to

depletion pressure ratios of 0.65, 0.43 and 0.30. The results shown in Figure 10 indicates that CO2 injection should be started

as late as possible if no other detrimental factors are involved. For example, in the case of active or strong aquifer, starting the

CO2 injection late may indicate that a large quantity of natural gas will be trapped by the water invasion.

Location of Injection Well: As stated before, existing wells (previous producer or injector) are usually considered for CO2

injection rather than drilling new wells. Therefore, the location of injection well is an important parameter in planning for

CO2 injection in a field. A case study was run by changing the location of injection well and moving it towards the producer

well in the reservoir. Three injection well locations were simulated in the cells 1, 20, and 40 in the X-direction. Figure 11

shows the recovery factor of natural gas and %HCPV of CO2 injected in all the three cases. The result shows that perforating

an injection well closer to the producer will lead to a significantly less natural gas recovery and CO2 storage. With early

production well shut-in, the reservoir pressure will build up at a higher rate as compared to an injector well at a farther

location and less amount of CO2 will be sequestered in the reservoir. So, considering all candidate injection wells in a

reservoir, decision can be made to select the well which is very far from the current producer well.

Arrangement of Permeability Layers and Anisotropy: In order to model a very heterogeneous reservoir, we considered 5

layers of permeability throughout the payzone thickness of 300 ft. The reservoir grid block is modified to (100, 1, 5) (NX,

NY, NZ) with each layer in the vertical direction has a different mean permeability and permeability of each grid block in

that layer is calculated using 0.5 Dykstra-Parsons Coefficient. The schematic of different permeability arrangements used for

the simulation study are drawn in Figure 12. Figure 13 shows the natural gas recovery and CO2 storage for different

permeability arrangements when the operational limits are reached. From the simulated results, it can be inferred that the

injection and production well should be perforated in relatively lower mean permeability zones. In case of permeability

arrangement (K3-K5-K1-K2-K4), natural gas recovery is the highest and also more CO2 stored. In this case, the injection

well is perforated in a mean permeability of 5 mD and production well in mean permeability of 1 mD. Perforating the

producer well in a lower permeability zone will delay CO2 breakthrough into the producer well to reach 50% and will allow

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more time for the reservoir pressure to reach the injection well pressure and thus higher CO2 can be injected into the

subsurface formation.

In the above study, the permeability is assumed to be isotropic. We also performed sensitivity study on reservoir permeability

contrast between the vertical permeability and the horizontal permeability. Simulation results show that as long as the vertical

equilibrium is satisfied, the natural gas recovery and CO2 storage would be about the same for different permeability

anisotropic contrasts. This is because vertical equilibrium is achieved very quickly and will not affect the production or

injection profile.

Injection Rate: Simulation study was carried out by varying injection rate and keeping other parameters constant. In this

case, four rates of injection are simulated as shown in Figure 14. The figure shows that natural gas recovery does not vary

much by changing the injection rate. But, with increasing the injection rate, the pore volume of CO2 injected into the

reservoir decreases. This happens because the maximum injection bottomhole pressure limitation is kept constant, and with

very high injection rates, the reservoir pressure reaches quickly the maximum pressure i.e. the injection pressure and will

allow less time for CO2 injection.

Production Rate: For this case, simulation study was carried out by varying production rates as shown in Figure 17. The

figure indicates that the recovery of natural gas is not sensitive to the production rate, and about 92% is achieved with all

production rates but the time to achieve the same recovery significantly increases by reducing the production rate. Similarly

the amount of CO2 storage remains relative constant.

Activity of Aquifer: Energy from aquifer is very important in natural gas development. Strong aquifer can sustain high

production rate; however, aquifer invasion also traps a large quantity of gas which cannot be produced, and some producers

close to the aquifer might be watered out. For simulation study, three cases are modeled by varying the aquifer zone

comparative to the reservoir drainage area. It can be observed in Figure 16 that by increasing the presence of aquifer in the

reservoir from no aquifer zone to 30% reservoir being covered by aquifer, we achieve higher natural gas recovery. Also,

effect of well location within or outside the aquifer has an impact of natural gas recovery and CO2 sequestered. By moving

the well away from aquifer, natural gas recovery is reduced. But this may also be an effect of the lesser distance between the

injector and producer well.

Analysis Using Dimensionless Numbers Dimensionless analysis is very important for the purpose of scaling the results from a reservoir to quantify other reservoirs.

Utilization of dimensionless variables will reduce the number of varying parameters in the study and avoid unit conversions.

More importantly, dimensionless analysis for the governing equations of fluid flow in a reservoir can provide insight into the

relative importance of driving forces such as viscous force, gravity force, and capillary force on the displacement

mechanisms. Independent dimensionless groups that control immiscible flow in porous media were derived by Shook, Li and

Lake (Shook et al. 1992) using inspectional analysis of the governing equations and boundary and initial conditions. These

dimensionless groups provided the guidelines for selecting the variables that influence the hydrocarbon recovery process in

EGR by CO2 injection.

Buoyancy Number ( ): In a fluid flow system, buoyancy number is defined as the ratio of gravity force to the viscous

force. Mathematically, the buoyancy number can be expressed as follows.

…………………………………………………………………………………………………… (1)

Buoyancy number typically ranges from 0.01 to 10. In the higher value range of , the flow is mainly controlled by

gravitational forces. This indicates that the flow rate is low and will allow CO2 to drop to the bottom of reservoir. At lower

value range, the flow is controlled by viscous forces indicating a higher rate and providing less time for CO2 to segregate to

the bottom of reservoir.

Effective Aspect Ratio ( ): The effective aspect ratio is defined as a characteristic ratio of time for fluid to cross the

reservoir in the horizontal direction to that in the vertical direction. The effective aspect ratio is defined as follow.

…………………………………………………………………………………………………… (2)

If is large, saturation or pressure variations in the vertical direction are much less than those in the horizontal direction.

The effective aspect ratio is mainly used for identifying whether the assumption of vertical equilibrium (VE) for a particular

reservoir is valid or not.

Dip Angle Group ( ): Dip angle group accounts for the geometry of a reservoir. The group considers geometrical effects,

and it does not involve any fluid properties.

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…………………………………………………………………………………………………… (3)

Simulation studies were carried out to relative quantify natural gas recovery factor using above dimensionless variables.

Table 3 provides the input parameters for the simulation model. Dimensionless variables were analyzed so that the above

simulation results of sensitivity analysis can be scaled up to be applied for several types of reservoir.

Natural gas recovery was observed with respect to buoyancy number ( ) with varying effective aspect ratio ( ) with

results shown in Figure 17. It is observed that with decreasing , natural gas recovery is also decreasing, as the fluid

movement along vertical direction is more stringent with decreasing effective aspect ratio. A significantly less variation is

being observed in the buoyancy number, which in our study is a function of reservoir dip angle keeping other parameters as

constant. Buoyancy number decreases with increasing dip angle. So, it can be stated that Buoyancy number ( ) is

insensitive to changes in the reservoir parameters. With higher buoyancy number, natural gas recovery is diminishing, which

is due to the increasing gravity effects. Also, as by the understanding of buoyancy number, it is inversely proportional to the

flux velocity (relative to production rate).

Very low values of buoyancy number indicates viscous dominated flow regimes, so the gas displacement is dependent

significantly upon residual phase saturation and relative permeability (Shook et al. 1992). Figure 18 indicates the results of

natural gas recovery with respect to effective aspect ratio ( ) with varying dip angle group ( ). As explained earlier,

natural gas recovery increases with increasing effective aspect ratio. Natural gas recovery increases very rapidly with change

in effective aspect ratio ( < 10) as with higher , fluid movement along vertical direction is less restrictive and not much

effect on natural gas recovery can be observed. Natural gas recovery is further increased by higher dip angle group which is

directly proportional to the reservoir dip angle. Dip angle group analysis is very critical before considering vertical

equilibrium (VE). In reservoirs with consideration of vertical equilibrium, effective aspect ratio is neglected. This

implies that we are considering natural gas recovery factor, saturation profiles and mixing zones to be independent of the

changes in effective aspect ratio. This assumption could lead to major errors in the study and production profile can vary

significantly than as expected. With higher effective aspect ratio, natural gas recovery will increases but it stabilizes after a

certain range, indicating the establishment of vertical equilibrium. The calculations of dip angle group and effective aspect

ratio are shown in Table 3.

Tornado Study based on Sensitivity Analysis Several reservoir parameters and well characteristics were analyzed during this sensitivity study in the paper and

implementing dimensionless variables. A tornado study was applied on the results to have an understanding of very critical

parameters while planning CO2 injection for enhanced gas recovery and sequestrating large volumes of CO2 into the

reservoir. Impact of all the parameters was analyzed to see their effect of natural gas recovery as well as %HCPV of CO2

injection. It can be observed in Figure 19 that effective aspect ratio has the highest positive impact on natural gas recovery.

So, higher aspect ratio leads to higher production. Also, the location of injection well has the highest negative impact on

natural gas recovery indicating that closer the injection well to the producer, less recovery would be achieved. Parameters

increasing towards left have inverse proportional relationship with natural gas recovery. It can be observed that depletion

pressure ratio has very minimal impact on natural gas recovery but as it can also be seen in Figure 20 that depletion pressure

ratio is the most dominating parameters for %HCPV of CO2 injection. Lower the depletion pressure ratio, higher volume of

CO2 can be sequestrated in the reservoir. This study provides clear understanding of the important parameters to be

considered while designing CO2 injection planning for enhanced gas recovery in depleted gas reservoirs.

Conclusion Based on above analysis, the following conclusions can be drawn:

1) The results in the study are represented with dimensionless group governing the displacement of the fluid. These

simulation results can be scaled up for generic reservoirs using these dimensionless groups and the effect of

interaction between parameters on gas recovery can be better analyzed.

2) Physical property study of CO2 and CH4 indicates that the minimum formation depth is of 4,000 ft for enhanced gas

recovery and carbon storage.

3) Injecting CO2 into depleted natural gas reservoir will enhance gas recovery; the recovery factors are highly affected

by the reservoir heterogeneity and anisotropy. For the scenario of no thief zone, an additional 60% or more of gas in

the depleted reservoir can be recovered. However, highly heterogeneous reservoir will lead to lower natural gas

recovery and will further reduce the percentage hydrocarbon pore volume of CO2 being sequestered because of

higher mixing zones in the formation.

4) Strong aquifer can sustain high production rate; however, aquifer invasion also traps a large quantity of gas which

cannot be produced. So, aquifer connectivity with the reservoir should be carefully studied before considering CO2

injection.

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5) Gas reservoirs must be depleted as much as possible before being considered for CO2 injection as lower depletion

pressure ratios provided higher natural gas recovery and also more carbon storage.

6) If the reservoir is relative homogeneous, the injector should be as far as possible away from the producer for high

natural gas recovery and more storage of CO2

7) Perforations of producer well should be in lower permeability zone as it will delay CO2 breakthrough into the

production well to reach 50% and will allow more time for the reservoir pressure to reach the injection well pressure

and thus higher CO2 can be injected into the subsurface formation.

Nomenclature

= density difference between the displacing fluids and displaced fluid,

= reservoir dip angle, degree

= end-point mobility of the gas phase

= mean

= standard deviation

= variance

= density,

CDF = cumulative distribution function

DPC = Dykstra-Parsons Coefficient

DWGC = water-gas contact depth,

EGR = enhanced gas recovery

g = gravitational acceleration,

H = reservoir thickness,

HCPV = hydrocarbon pore volume

= reservoir permeability,

= horizontal permeability,

= vertical permeability,

L = reservoir length in the flow direction,

= dip angle group

= buoyancy number

= effective aspect ratio

= water saturation, %

= gas saturation, %

SCF = standard cubic feet

STB = stock tank barrel

= total flux velocity,

= gas compressibility factor

References Agarwal, R., Chusak, L.and Zhang, Z. 2011. Economics of carbon dioxide sequestration and mitigation versus a suite of

alternative renewable energy sources for electricity generation in US. International Journal of Energy Economics and Policy

1 (4): 78-94.

Angus, S., Armstrong, B.and de Reuck, K. M. 1976. International Thermodynamic Tables of the Fluid State - 3 Carbon

Dioxide. Pergamon, New York, Pergamon Press, Oxford (Reprint).

Bachu, S., Michael, K.and Adams, J. 2003. Effects of In Situ Conditions on Aquifer Capacity for CO2 Sequestration in

Solution. Paper presented at the Proceedings of Second National Conference on Carbon Sequestration.

Chang, Y., Coats, B.and Nolen, J. 1996. A Compositional Model for CO2 Floods Including CO2 Solubility in Water. Paper

SPE 35164 presented at the 1996 Permian Basin Oil and Gas Recovery Conference.

Chase, M. W., Jr. 1998. NIST-JANAF Themochemical Tables, Fourth Edition, Vol. Monograph 9 (Reprint).

Clemens, T.and Wit, K. 2002. CO2 enhanced gas recovery studied for an example gas reservoir. Paper SPE 77348-MS

presented at the SPE Annual Technical Conference and Exhibition.

Divison, A. E. M., Grobe, M., Pashin, J. C.and Dodge, R. L. 2010. Carbon Dioxide Sequestration in Geological Media: State

of the Science, AAPG Studies in Geology 59, Vol. 59, AAPG (Reprint).

SPE 169578-MS 7

Duan, Z.and Mao, S. 2006. A thermodynamic model for calculating methane solubility, density and gas phase composition of

methane-bearing aqueous fluids from 273 to 523K and from 1 to 2000bar. Geochimica et Cosmochimica Acta 70 (13): 3369-

3386.

Gallo, Y., Couillens, P.and Manai, T. 2002. CO2 Sequestration in Depleted Oil or Gas Reservoirs. Paper SPE 74104-MS

presented at the SPE International Conference on Health, Safety and Environment in Oil and Gas Exploration and

Production.

Jikich, S., Smith, D., Sams, W.and Bromhal, G. 2003. Enhanced Gas Recovery (EGR) with carbon dioxide sequestration: A

simulation study of effects of injection strategy and operational parameters. Paper SPE 84813-MS presented at the SPE

Eastern Regional Meeting.

Klusman, R. W. 2003. Evaluation of leakage potential from a carbon dioxide EOR/sequestration project. Energy Conversion

and Management 44 (12): 1921-1940.

Maldal, T.and Tappel, I. 2004. CO2 underground storage for Snøhvit gas field development. Energy 29 (9): 1403-1411.

Michael, K., Golab, A., Shulakova, V., Ennis-King, J., Allinson, G., Sharma, S.and Aiken, T. 2010. Geological storage of

CO2 in saline aquifers—A review of the experience from existing storage operations. International Journal of Greenhouse

Gas Control 4 (4): 659-667.

Oldenburg, C.and Benson, S. 2002. CO2 Injection for Enhanced Gas Production and Carbon Sequestration. Paper SPE

74367-MS presented at the SPE International Petroleum Conference and Exhibition, Mexico.

Oldenburg, C., Pruess, K.and Benson, S. M. 2001. Process modeling of CO2 injection into natural gas reservoirs for carbon

sequestration and enhanced gas recovery. Energy & Fuels 15 (2): 293-298.

Oldenburg, C. M. 2003. Carbon dioxide as cushion gas for natural gas storage. Energy & Fuels 17 (1): 240-246.

Shook, M., Li, D.and Lake, L. W. 1992. Scaling immiscible flow through permeable media by inspectional analysis. In Situ;

(United States) 16:4: 311-350.

Younglove, B.and Ely, J. F. 1987. Thermophysical Properties of Fluids: II. Methane, Ethane, Propane, Isobutane, and

Normal Butane, American Chemical Society and the American Institute of Physics for the National Bureau of Standards

(Reprint).

Appendix I: Estimation of Permeabilities for Each Grid Block from Dykstra-Parsons Coefficient

Permeability is usually characterized as log normal distribution in nature. The log-normal distribution has the probability

density function (PDF) as follows:

√ …………………………………………………………………………………………………… (4)

Where and are mean and standard deviation of the variable’s logarithm.

The cumulative distribution function (CDF) is:

[ (

√ )] ………………………………………………………………………………………………… (5)

From this distribution, the median permeability is:

…………………………………………………………………………………………………… (6)

So above equation can be written as:

[ (

√ )] ………………………………………………………………………………………….……… (7)

Define

…………………………………………………………………………………………………… (8)

Dykstra-Parsons coefficient is defined as:

8 SPE 169578-MS

…………………………………………………………………………………………………… (9)

Where is the median of the distribution, and is the permeability at which 84.1% of the distribution has a great

permeability. The permeability, corresponds to . From which we can solve the

By substituting Equation (8) into equation (7), an expression can be derived for the relationship between the permeability

variation and the standard derivation.

…………………………………………………………………………………………..……… (10)

Or the standard derivation can be calculated from the Dykstra-Parsons Coefficient,

………………………………………………………………………………………..………… (11)

And the variance of the permeability distribution is:

[ ] ……………………………………………………………………………………………..…… (12)

For this study, sgsim (sequential gaussian simulation) moldeing in sGEMS software was utilized for generating permeability

for each grid block. Defining the number of grid block and their dimensions, sgsim provides random number distribution

based on cumulative distribution function (CDF) for each grid block, which is characterized through simple kriging system.

Using mean permeability and standard deviation, permeability can be generated for each grid block defining the reservoir.

Figure 7 provides an example of permeability distribution along the grid block using sgsim with mean permeability of 100

mD and standard deviation of 0.50.

Figures

Figure 1: Density comparison of CO2 and CH4 with formation depth

Figure 2: Viscosity comparison of CO2 and CH4 with formation depth

SPE 169578-MS 9

Figure 3: Solubility of CO2 and CH4 with varying formation depth and salinity

Figure 4: Relative permeability curves used in the base case simulation.

Figure 5: 2D gridblocks model for the base case

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Figure 6: Importance of CO2 injection in enhancing natural gas recovery before limits for production and injection reaches

Figure 7: Permeability distribution along x-axis with mean permeability of 100 mD

Figure 8: CO2 concentration in reservoir injected with varying reservoir heterogeneity at 46 %HCPV CO2

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Figure 9: Effect of reservoir heterogenity with varying Dykstra-Parsons Coefficient (DPC)

Figure 10: Depletion pressure impact on the natural gas recovery and CO2 storage.

Figure 11: Injection well location effect on the natural gas recovery

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Figure 12: Arrangement of permeability layers for simulation study

Figure 13: Permeability arrangment impact on natural gas recovery

Figure 14: Effect of injection rate on natural gas recovery and CO2 storage

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Figure 15: Natural gas recovery with changing production rate

Figure 16: Effect of aquifer on the recovery of natural gas recovery and CO2 storage

Figure 17: Effect on % natural gas recovery with buoyancy number, NG at varying effective aspect ratio, RL (dimensionless

analysis)

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Figure 18: Effect on % natural gas recovery with effective aspect ratio, RL varying dip angle group Nϴ (dimensionless analysis)

Figure 19: Sensitivity study of affecting parameters on natural gas recovery

Figure 20: Sensitivity study of affecting parameters on CO2 storage volume

SPE 169578-MS 15

Tables Table 1: Critical properties of CO2 and CH4 and their properties at reservoir depth of 10,000 ft and 200°F

Physical Property CH4 CO2 Unit Reference

Critical

Parameters

Temperature 116.6 88.0 °F (Chase 1998)

Pressure 667 1075 psia

Density 16.4 57.1

(Angus et al. 1976,

Younglove and Ely 1987)

Viscosity 0.022 0.256 cP

Solubility

(Salinity: 1 mol/kg) 24.4 182 SCF/STB

(Chang et al. 1996)

(Duan and Mao 2006)

Table 2: Reservoir description for base case simulation model

Reservoir Properties

Length 7,500 ft

Width 75 ft

Thickness 300 ft

Reservoir Grid (NX, NY, NZ) (100, 1, 10)

Dip 15° degree

Initial Pressure 4,350 psia

Reference depth 10,000 Ft.

Initial Temperature 200 oF

1

Reservoir Permeability 100 mD

Reservoir Porosity 20 %

Initial Water Saturation 0.1

Well Properties

Injection Rate 4.5 MMSCF/Day

Maximum Injection Bottomhole Pressure Limitation 7,000 psia

Production Rate 3.0 MMSCF/Day

Minimum Production Bottomhole Pressure Limitation 1,000 psia

Simulation Time 10 years

Table 3: Input parameters for dimensionless analysis

Reservoir Parameters

Parameter Field Units SI values

Horizontal Permeabity 100 mD 9.87E-14 m2

Vertical Permeability 100 mD 9.87E-14 m2

Reservoir Thickness 300 ft 91.5 m

Lateral Well Spacing 7,500 ft 2,286 m

CO2 Density 57.1 914 kg/m3

CH4 Density 16.4 263 kg/m

3

CO2 Viscosity 0.26 cP 2.56E-04 Pa.s

CH4 Viscosity 0.02 cP 2.17E-05 Pa.s

End point-Gas relative permeability 0.74

Dimensiosless Variables

Dip

Angle

Dip Angle Group

(Eq. 3)

Effective Aspect Ratio

(Eq. 2)

5° 2.20 1 25.0

15° 6.70 0.1 7.90

30° 14.4 0.01 2.50

45° 25.0 0.001 1.77

60° 43.3 0.005 0.79

0.0001 0.25

16 SPE 169578-MS