Research Article | | Peer-Reviewed

Evaluation of CO2 Storage Potential of Some Depleted Hydrocarbon Reservoirs: Niger Delta Case Study

Received: 6 May 2026     Accepted: 18 May 2026     Published: 27 May 2026
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Abstract

Recent joint efforts led by the international financial corporation (IFC) with strong support from the Federal Government of Nigeria and various industrial and policy stakeholders has produced the Nigerian CO2 Storage Atlas, sorting prospective geological storage sites. However, the storage efficiency factors applied to the estimated resource capacity to provide low, medium and high resource estimations may not be a true representation for the underground CO2 storage space, especially for depleted hydrocarbon reservoirs, in the Nigeria rich oil province that is very porous and permeable. We therefore present assessment of CO2 storage potential of some depleted hydrocarbon reservoirs in the Niger Delta, derive specific approximate CO2 Storage efficiency factors for these reservoirs, and develop a model for determining site-specific CO2 storage efficiency factor. Comparison of results from various approaches – production-based, volumetric- based with varying CO2 storage efficiency factors obtained from the new model and previous works, and an enhanced analytical simulation tool (EASiTool) was also carried out. The newly developed model for determining site-specific CO2 storage efficiency factor can help improve the predictive capability of the volumetric method for CO2 storage potential estimates, especially for depleted oil reservoirs in the Niger Delta.

Published in Petroleum Science and Engineering (Volume 10, Issue 1)
DOI 10.11648/j.pse.20261001.15
Page(s) 51-62
Creative Commons

This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited.

Copyright

Copyright © The Author(s), 2026. Published by Science Publishing Group

Keywords

CO2 Storage Efficiency Factor, CO2 Storage Resources, Nigerian CO2 Storage Atlas, CO2 Storage Estimates, Geological Storage

1. Introduction
Carbon capture, utilization, and storage (CCUS) projects are increasing in number across the globe to ease climate change. A total of 202 carbon capture and storage (CCS) projects can be found in the United State of America (USA) and Canada, out of which twenty-one facilities are in operation, nine in construction, eighty in advanced development and ninety-two in early development. In Europe, there are four facilities in operation, six in construction and one hundred and nine are in early or advanced development. The Middle East and North Africa have three facilities in operation, three in construction and three in advanced development. South America has one facility in operation and one in early development, and Asia Pacific has twelve facilities in operation, eight in construction and thirty-four in advanced or early development . Some CCS progress, and initiatives by some countries and regions, and their potential storage capacity are as follows: the 420 Million tonnes per year by 2030 by the USA, through the additional funding from the 2021 Infrastructure Investment and Jobs Act and beneficial CCUS tax credit adjustments in the 2022 Inflation Reduction Act ; the Net Zero Industry Act was introduced by the European Union (EU), setting an annual goal of 50 Million tonnes (Mt) per year for Carbon IV Oxide (CO2) injection by 2030 and aim to increase to 300 Mt per year by 2040 ; The early deployment of CCS projects with up to 30 Mt per year target by 2030, backed by billions of Pounds in the Spring Budget of 2023 ; The United Arab Emirate’s (UAE) target of 5 Mt per year by 2030, the 44 Mt per year by 2035 set by Saudi Arabia, and Qatar committed to reducing emissions by 25% by 2030, aiming to have 7 Mt per year by 2030 .
Underground space for carbon sequestration is abundant to facilitate carbon emission reduction targets. The CO2 geological storage potential in reservoirs of sedimentary bodies, which represents the reservoir maximum capacity for CO2 storage, is much better explored and developed, with clearer characteristics and more data available in hydrocarbon reservoirs than in coal beds and deep saline aquifers 3. Hydrocarbon reservoirs have proven capacity for fluid injection, potential for layered storage, and existing well infrastructure for monitoring . Several actual and planned CO2 geological storage projects worldwide are in different locations and with different formation types, such as deep saline aquifers, depleted oil and gas fields, and basalt formations . Some projects in deep saline aquifers are; the Sleipner field project in North Sea, Norway has an estimated storage capacity of 2) Mt , the Rangely field project in Northwest Colorado , and the Gorgon liquified natural gas project in Western Australia has one hundred and twenty-nine (129) Mt storage capacity . The CO2-CRC project in Australia , the SACROC field in Texas , the Cranfield project in Natchez, USA and the In Salah CO2 Storage Project are in depleted oil and gas reservoirs.
Many previous studies, with comprehensive datasets on the geological storage potential are predominantly from geologic provinces in the USA and Canada , in onshore and offshore basins across Europe, and in Asia Pacific. Reservoir-level datasets of CO2 storage potential, such as; porosity, permeability, depth, and other critical parameters for thirty-three (33) sedimentary basins in eight regions of the U.S. have been documented by the United States Geological Survey (USGS) . There are very few technically sound studies, with comprehensive datasets on the geological storage potential in developing countries. One of the barriers in the CCS process in developing countries is availability and accessibility of data concerning potential geological CO2 storage locations. However, recently, a collective effort led by the international financial corporation (IFC) with concrete support from the Federal Government of Nigeria and numerous public and private sector stakeholders, has produced the Nigerian CO2 Storage Atlas, cataloguing prospective geological storage sites, to address the data gaps . The Atlas reported 10,700 Gigatonnes (Gt) of prospective CO2 storage resources (using the volumetric method outlined by the U.S. Department of Energy’s National Energy Technology Laboratory (DOE-NETL) , with an adjustment for net, rather than gross thickness) and showed that the most suitable locations are in the Niger Delta, specifically the saline aquifers and depleted oil and gas fields within the Miocene-age formations. However, the storage efficiency factor (EF) of 0.5% for low case, 2.0% for medium case and 5.4% high case, guided by the work of Goodman et al. , applied to the estimated resource capacity to provide low, medium and high resource estimations may not be a true representation for the underground CO2 storage space in the Niger Delta. This study therefore applies a production-based approach (proposed by the Carbon Sequestration Leadership Forum (CSLF), to estimate the CO2 Storage Resource potential for some depleted oil reservoirs in the Niger Delta, derives and proposes a storage efficiency factor to improve the predictive capability of the volumetric method. Results comparison of the predicted prospective CO2 storage resources to that of Nigerian CO2 Storage Atlas was also carried out.
2. Brief Overview of the Niger Delta, Gathered Datasets and CO2 Storage Potential Estimations for This Study
There are five sedimentary basins of Nigeria with potential to store subsurface CO2: Niger Delta (onshore and offshore), Dahomey Basin, Benue Trough, Bida Basin, and Chad Basin (see, Figure 1). The Niger Delta is one of the most productive deltaic petroleum systems, with decades of oil and gas exploration and exploitation activities, in the world. It has over 12,000 m of sediments, which is composed of three diachronous siliciclastic units: the deep-marine pro-delta Akata Group, the shallow-marine delta-front Agbada Group and the continental, delta-top Benin Group .
Figure 1. Map location of the Niger Delta .
2.1. Datasets for This Work
In the Nigerian oil and gas sector, as at 2023, there were over 200 fields, more than 1200 reservoirs and over 2500 wells with records of technical allowable rates. Details of the distribution of the reservoirs and wells in the hydrocarbon fields can be found in the website of Nigeria Upstream Petroleum Regulatory Commission (NUPRC). Geological and petrophysical information of some of these oil and gas fields can be found in some public literatures, such as and websites of the fields’ operators. Dataset of 250 reservoirs from the Niger Delta, which were obtained from different sources - well logs, well testing, seismic analysis, simulation studies, pressure buildup test, area versus depth plot obtained from mapping packages, reservoir isochores, proprietary software to estimate probabilistic in place volumes and reservoir engineering calculations where necessary, was used for this study. Some of these datasets from oil reservoirs with small pay thickness and variable gas cap sizes have been reported by .
The statistical description of the data is presented in Table 1, and relevant data information for twenty-five (25) reservoirs are also provided in Table 4 in the appendix.
Table 1. Statistical description of oil rim dataset used in this study.

Parameters

Min. value

Max. value

Mean

Standard deviation

Variance

Porosity (%)

15

35

26.1

4.08

16.62

Water saturation (%)

5.0

40.0

24.6

10.80

116.63

Oil formation volume factor (rb/stb)

1.08

6.27

1.47

273.40

74748.03

Gas cap, m-factor

0.01

4.73

0.66

0.8387

0.70

Area (acres)

19.66

64593.74

856.64

5131

26327160

Average net pay (ft)

10

524

58.53

47.92

2296.18

Temperature (oF)

125

240

175.20

25.39

644.80

(Oil up to (OUT) pressure (psi)

2148

5984

3717.40

715.06

511308.79

OUT depth (ft)

4930

13017

8486.15

1584.95

2512061.73

Rsi (scf/bbl)

76

6234

925.76

593.31

352021.17

Permeability (mD)

3.36

18225

797.97

1439.87

2073213.4

OIP (MMstb)

0.9

158.4

21.3

24.9880

624.4042

2.2. Estimation of CO2 Storage Potential for Some Hydrocarbon Reservoirs
The volumetric method (see, Eq. (1)) proposed by the U.S. Department of Energy (US-DOE), which is based on the industry standard method for calculating original oil or gas in place (OOIP or OGIP) by the formation volume factor , and the production-based method (see, Eq. (2)) for CO2 storage capacity estimation proposed by the Carbon Sequestration Leadership Forum (CSLF) are the most common approaches.
MCO2(prod)=ρCO2 x ERoil/gas x A x h x ∅ x(1-Sw)(1)
MCO2(vol)=ρCO2 x [RF xOOIPBf-Viw+Vpw](2)
where, MCO2(vol), mass estimate of oil and gas reservoir CO2 storage resource, tonnes; A, drainage area of the oil or gas reservoir that is being assessed for CO2 storage, ft2; h, net oil and gas thickness of the reservoir, ft; , average effective porosity, fraction; Sw, average initial water saturation within the total area and net thickness, fraction; ρCO2, density of CO2, lb/ft3; RF, oil and gas recovery factor, fraction; ERoil/gas, CO2 storage efficiency factor, the volume of CO2 stored in an oil or gas reservoir per unit volume of original oil or gas in place (OOIP or OGIP), fraction; OOIP,.
The volumetric method requires the CO2 storage efficiency factor, which can be calculated using reservoir simulations or CO2-Enhanced Oil Recovery experience. However, where there are no reservoir simulations or CO2-enhanced oil recovery experience, The CO2 storage efficiency factor, guided by , is adopted. In the Nigeria CO2 storage atlas report, an efficiency factor of 0.5% for low case, 2.0% for medium case and 5.4% high case, was used. Unfortunately, this may not be a true representation for the underground depleted hydrocarbon space in the Niger Delta. In this work, we therefore applied the production-based method to estimate the CO2 storage potential of some depleted oil reservoirs, which is useful in site-specific calculations . Figure 2 shows the results of CO2 storage capacity, in Million tonnes (Mt). Majority of the reservoirs (over 200 reservoirs) have storage capacity less than 1.23 Mt. However, out of the two hundred and fifty (250) reservoirs evaluated, less than ten (10) reservoirs have CO2 storage capacity between 1.23 and 3.68 Mt. The total storage capacity for the two hundred and fifty (250) reservoirs is about 76 Mt.
Figure 2. CO2 storage capacity, in Million tonnes, predictions using the production-based model for the reservoirs under study.
Predictions from volumetric method (see, Equation (1)), after adopting CO2 efficiency factor of 0.5% for low case, 2.0% for medium case and 5.4% high case, as used in the Nigeria CO2 storage atlas report, were compared with that of the production-based model. Figures 3-5 show the spread of the percentages of deviations for the three cases. For CO2 efficiency factor of 0.5%, over one hundred and forty (140) reservoirs were under-predicted, with deviations less than 57% of the storage capacity predictions between the volumetric method and the production-based method, as can be seen in Figure 3. These large deviations observed can be due to uncertainties in the petrophysical properties and the generalized CO2 efficiency factor of 0.5% may match the site-specific CO2 efficiency factor for some reservoirs.
Figure 3. Ranges of percentage error for 0.5% CO2 efficiency factor volumetric-based model, when compared with that of the production-based model.
Figure 4. Ranges of percentage error for 2.0% CO2 efficiency factor volumetric-based model, when compared with that of the production-based model.
Figure 5. ranges of percentage error for 5.4% CO2 efficiency factor volumetric-based model, when compared with that of the production-based model.
Figure 4 shows the ranges of percentage error for 2.0% CO2 efficiency factor; less than one hundred (100) reservoirs have percentage error bandwidth below -68%. There was increase in the number of reservoirs with improvement in predictions of the storage capacity between the volumetric method and the production-based method. The number of reservoirs increased further, when 5% CO2 efficiency factor is applied, as can be seen in Figure 5. These analyses therefore demonstrate that the CO2 efficiency factors can be greater than 5.4% for CO2 storage resources in depleted oil reservoirs in the Niger Delta.
3. Development of Model for Estimation of Specific CO2 Storage Efficiency Factor
The CO2 storage efficiency factor, ERoil/gas, which is the volume of CO2 stored in an oil or gas reservoir per unit volume of original oil or gas in place (OOIP or OGIP), fraction; OOIP, is essential for realistic CO2 storage resource estimate using the volumetric approach. Approximately 1.8% to 2.2% is the effective storage coefficient reported in the Carbon Sequestration Atlas for the United States and Canada , developed through Monte Carlo simulation, for the P50 level. The US-DOE used a database, known as the Average Global Database (AGD) – from two main databases (the Gas Information System or GASIS (1999) and the Tertiary Oil Recovery Information System or TORIS (1995)), containing fluid and geologic properties for over 20,000 hydrocarbon reservoirs representing a wide variety of reservoir types from all over the world. CSLF proposed that, “the effective storage coefficients should be determined through numerical simulations and/or field work” , and so no values were given. Effective storage coefficients of 2.0% to 3.3% as calculated through numerical simulations was reported by . In 2011, Goodman et. al. published efficiency factors based on documented ranges derived from oil and gas reservoirs and numerical simulations , by applying the log-odds normal distribution with Monte Carlo sampling procedure ; the overall efficiency for saline formations ranges from 0.40 to 5.5% for the three different lithologies (clastics, dolomites and limestones) over the 10 and 90 percent probability range, respectively.
At a site-specific scale, the reported the efficiency factors to be 4.62 to 14.92%, 6.57 to 14.92%, and 4.24 to 9.82%, respectively for clastics, dolomites and limestones, over the 10 and 90 percent probability range. Goodman et. al. reported 3.1 to 10%, 5.1 to 9.2%, and 3.5 to 7.3%, respectively for clastics, dolomites and limestones, according to the 10 and 90 percent probability range. So, the statement by the CSLF , as earlier shared, is behind the motivation of this section of this study.
3.1. Derivation of Specific Approximate CO2 Storage Efficiency Factor
Previous studies have shown that predictions from production-based and volumetric methods are similar (US-DOE and CSLF). Ighomuaye et al compared three methods – volumetric, production-based and correlation-based, using data from the Vermillion Basin, Gulf of Mexico (GOM), and observed that the CO2 storage capacity estimates by the production-based and correlation-based methods deviate from the estimate of the volumetric methods by 7.3% and 14.6%, respectively.
Figure 6. Distribution of the specific approximate CO2 storage efficiency factors (%) for the reservoirs under study.
So, specific approximate CO2 storage efficiency factors were therefore derived for the oil reservoirs considered in this work, when we applied Eq. (1) with the assumption that the estimates of CO2 storage potential from the production-based approach Eq. (2) is equal to that of the volumetric method. Figure 6 shows the distribution of the specific approximate CO2 storage efficiency factors for the reservoirs under study. One hundred and eighty (180) reservoirs have CO2 storage efficiency factors between 0.11 and 32.33%. Less than thirty reservoirs (30) have CO2 storage efficiency factors of 32.33 to 64.55%. From the analyses, we can also deduce that the CO2 storage efficiency factors for hydrocarbon reservoirs may not exceed 32.33%, and it has a wide spread of values. Reservoirs with very good porosity, permeability and reservoir capacity values were observe to have high CO2 storage efficiency factors.
3.2. Model Development for Approximate CO2 Storage Efficiency Factor Determination
One of the simple machine learning methods was considered for this work, which is the Multiple linear regression (MLR) technique - statistical approach. The general multiple regression equation presented by is expressed in Eq. (3).
yi= βo+β1xi1+β2xi2++βpxip(3)
where, i=n observations; yi is the dependent variable (predicted value); xi, the input variables; βo, the intercept constant; βp, the slope coefficients for each input variable.
The multiple linear regression tool available in Microsoft Excel package was used for the development of a model for approximate prediction of CO2 Storage Efficiency Factor. Important input variables were considered for the development of CO2 Storage Efficiency Factor model that will be best suited for depleted hydrocarbon reservoirs, especially oil reservoirs in the Niger Delta, namely: reservoir thickness, h, ft; reservoir permeability, K, mD; drainage area, A, ft2; porosity, , %; water saturation, Sw, %. The dataset was partitioned into test size of 30% and training data of 70% for the multilinear regression process. The fitting performance was good, with an R-squared value of 0.71.
From the multiple linear regression process, the expressions for estimating the CO2 Storage Efficiency Factor, EFCO2, is given in Eqs. (4) and (5).
EFCO2=10Z(4)
where,
Z= b1log10h++b2log10K+b3log10A+b4log10+b5log10Sw(5)
where, b1 through b8 denote the coefficients associated with the input variables. Thus, the coefficients of the developed model are presented in Table 2.
Table 2. Coefficients of the developed injection pressure model.

b1

b2

b3

b4

b5

-2.17

5.95

-2.36

-9.61

3.37

Figure 7 shows the relationship between the percentage error and the predicted CO2 storage efficiency factor. The percentage error bandwidth falls in the range of -52% and +37-66%, with an absolute average error of 37.03%.
Figure 7. Percentage error and the predicted CO2 storage efficiency factor.
Though the parameters considered in the development of the model were reservoir rock properties from less than 300 reservoirs in the Niger Delta, Eq. (3) can be a useful tool for estimating CO2 Storage Efficiency Factor to be used in the volumetric method for estimation of the CO2 storage potential of depleted oil reservoirs in the Niger Delta. Where the model predicts CO2 storage efficiency factor above 32.33%, probabilistic estimation can be adopted with values between 0.11 and 32.33%; this is the range of values of the CO2 storage efficiency factors for over one hundred and eighty (180) reservoirs, as earlier shown.
The standard errors from the MLR analysis show high values for the logarithmic values of the porosity and permeability, as presented in Figure 8. So, reservoirs or storage media whose logarithmic values of the percentages of the porosities and permeabilities values are far from the mean values of 1.4125 and 2.6413, respectively, may result in over- or under-estimation of the CO2 Storage Efficiency Factor, thereby affecting the predictive accuracy of the volumetric method in this region.
Figure 8. Standard error plot for the input variables in the MLR.
4. Predicted Results Comparison from Various Methods for Some Reservoirs
We compared the predictions from production-based, volumetric method with CO2 efficiency factors (0.5, 2, and 5.4%) from and the newly developed model, and an enhanced analytical simulation tool (EASiTool) by developed to predict pressure impact on CO2 injectivity and reservoir-storage capacity of geological formations. For the EASiTool method, we consider one injection well with maximum injection pressure of 10% greater than the initial reservoir pressure. Information obtained from the EASiTool method include: CO2 Storage Volume estimates, CO2 injection rate and CO2 plume radius. However, for this work, we only reported the CO2 Storage Volume estimates. The results from the various methods are summarized in Table 3 and Figure 9.
Table 3. Predicted results from various approaches.

Res.

Average porosity (%)

Res. Net height (ft)

Water Sat.%

Perm., (mD)

Res. Area (Acre)

Prospective CO2 Storage Volume (Million tonnes)

Prod. Based

Site specific EF%

EASiTool

EF, New model

EF, 0.5%

EF, 2%

EF, 5.4%

1

23.0

80

17.0

422

30.5

0.0895

0.01828

0.0052

0.0283

0.0012

0.0050

0.0136

2

35.0

27

15.0

845

59.4

0.0512

0.01047

0.00044

0.0459

0.0012

0.0051

0.0140

3

19.0

18

37.0

215

179.0

0.0618

0.01264

0.00031

0.0143

0.0010

0.0041

0.0113

4

19.0

12

36.0

218

292.7

0.0732

0.01496

0.00143

0.0118

0.0011

0.0046

0.0125

5

25.0

32

25.0

395

94.1

0.0206

0.00422

0.00151

0.0195

0.0015

0.0061

0.0165

6

22.0

61

13.0

452

34.3

0.1951

0.03987

0.00101

0.0310

0.0010

0.0043

0.0117

Figure 9. Comparison of predicted results from various approaches
For the six (6) reservoirs used for the comparison, all approaches under-predicted the CO2 storage potential when referenced to results from the production-based method. All methods under-predicted the CO2 storage potential for reservoirs designated as 1, 3, 4 and 6. However, results from the new model, for specific approximate CO2 Storage Efficiency Factor, have the best predictions for reservoirs designated as 2 and 5; the percentage errors were less than -20%. Predictions from the EASiTool match excellently well with that of the 0.5% efficiency factor approach for all reservoirs.
5. Conclusion
There are many depleted hydrocarbon reservoirs in the Niger Delta with CO2 storage potential. The production-based method applied to estimate the CO2 storage potential of some depleted oil reservoirs under study gives a total storage capacity of about 76 Million tonnes. Predictions from the volumetric method with CO2 efficiency factor of 0.5% for low case, 2.0% for medium case and 5.4% for high case, show large deviations from the production-based method. Majority of the reservoirs under study have CO2 storage efficiency factors between 0.11 and 32.33%. The relationship between the percentage error and the predicted CO2 storage efficiency factor, from the newly developed model, falls in the range of -52% and +37-66%, with an absolute average error of 37.03%. Under-predictions of storage capacity were observed from the volumetric method with CO2 efficiency factors (0.5, 2, and 5.4%) from and the newly developed model, and an enhanced analytical simulation tool (EASiTool) by , when compared to that of the production-based approach, for the six (6) reservoirs used in the analyses. However, results from the new model, for specific approximate CO2 storage efficiency factor, have the best predictions. The findings in this work will primarily best applied to depleted oil reservoirs in the Niger Delta, and may not be directly applicable to the region's massive saline aquifer potential, which often holds the largest volume of storage capacity in CCS projects.
Abbreviations

AGD

Average Global Database

CCS

Carbon Capture, and Storage

CCUS

Carbon Capture, Utilization, and Storage

CSLF

Carbon Sequestration Leadership Forum

CO2

Carbon IV Oxide

DOE-NETL

U.S. Department of Energy’s National Energy Technology Laboratory

EASiTool

Enhanced Analytical Simulation Tool

EFCO2

CO2 Storage Efficiency Factor

EU

European Union

GOM

Gulf of Mexico

IFC

International Financial Corporation

Mt

Million Tonnes

NUPRC

Nigeria Upstream Petroleum Regulatory Commission

OGIP

Original Gas in Place

OOIP

Original Oil in Place

ODT

Oil Down to

OUT

Oil Up to

TORIS

Tertiary Oil Recovery Information System

UAE

United Arab Emirate

USA

United State of America

USGS

United States Geological Survey

US-DOE

U.S. Department of Energy

Author Contributions
Aniefiok Livinus: Conceptualization, Resources, Supervision, Writing – review & editing
Raymond Mkpouto Obot: Data curation, Formal Analysis, Writing – original draft
Antigha Eyo: Data curation, Writing – review & editing
Itoro Udofort Koffi: Data curation, Writing – review & editing
Victor E. Etuk: Writing – review & editing
Data Availability Statement
The full datasets used and/or analysed during the current study available from the corresponding author on reasonable request.
Conflicts of Interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Appendix

OIIP EXP

Av. Np

Poro%

Water Sat%

Avg H, ft

ODT ftss

ODT psi

Boi v/v

Res. T, oF

API

Perm, mD

A, Acres

8.90

2.50

23.00

17.00

80.00

10510.00

4576.00

1.77

218.00

34.97

423.00

30.53

25.37

0.36

35.00

15.00

27.00

6602.00

2883.00

1.19

144.00

22.30

845.33

59.48

5.67

0.21

19.00

37.00

18.00

9142.00

3974.00

1.77

196.00

45.38

215.28

179.06

3.90

1.29

19.00

36.00

12.00

9998.00

4340.00

1.96

212.00

45.38

218.25

292.78

0.90

0.27

25.00

25.00

32.00

8566.00

3751.00

1.97

182.00

39.19

395.28

94.17

6.50

1.05

22.00

13.00

61.00

9199.00

4200.00

1.59

190.00

40.85

452.51

34.35

112.70

0.60

27.00

24.00

40.00

6590.00

2880.00

1.14

125.00

17.76

452.80

42.91

95.00

1.74

28.00

21.00

20.00

6657.00

2910.00

1.14

126.00

18.55

511.21

82.41

14.80

0.09

26.00

30.00

31.00

8082.00

3530.00

1.24

155.00

28.93

382.71

65.34

15.00

0.18

26.00

42.00

8.00

8083.00

3530.00

1.20

155.00

26.60

323.45

297.68

24.10

3.31

31.00

11.00

26.00

8330.00

3640.00

1.26

160.00

29.48

822.84

62.37

68.50

4.97

28.00

21.00

42.00

8820.00

3926.00

1.50

168.00

36.15

511.21

51.86

5.40

3.43

29.00

20.00

50.00

7669.00

3365.00

1.17

142.00

23.65

552.14

33.61

7.10

0.25

27.00

26.00

22.00

7454.00

3248.00

1.35

174.00

25.72

435.04

95.27

5.10

0.31

27.00

26.00

25.00

7454.00

3248.00

1.24

174.00

25.72

435.04

76.96

41.40

0.32

23.00

16.00

110.00

7972.00

3474.00

1.33

182.00

29.30

436.02

16.50

17.10

0.82

26.00

20.00

24.00

8776.00

3824.00

1.51

184.00

36.15

468.72

90.40

39.90

2.57

24.00

20.00

100.00

8945.00

3898.00

1.58

201.00

34.97

415.69

22.60

4.10

2.62

22.00

19.00

88.00

9858.00

4278.00

1.68

220.00

35.96

374.31

27.02

4.60

1.10

22.00

19.00

27.00

9858.00

4278.00

1.68

220.00

35.96

374.31

88.07

16.20

3.51

26.00

10.00

90.00

10908.00

4734.00

1.53

221.00

30.77

662.87

21.64

2.20

1.91

26.00

10.00

30.00

10099.00

4420.00

1.71

220.00

35.36

662.87

72.49

References
[1] Adeoti, L., Ojo, A. A., Olatinsu, O. B., Fasakin, O. O. and Adesanya, O. Y. (2015). Comparative analysis of hydrocarbon potential in shaly sand reservoirs using archie and simandoux models: a case study of “x” field, Niger delta, Nigeria. Ife Journal of Science 17(1): 15-28.
[2] Bachu, S., Bonijoly, D., Bradshaw, J., Burruss, R., Holloway, S., Christensen, N. P., Mathiassen, O. M., (2007). CO2 storage capacity estimation: methodology and gaps. Int. J. Greenhouse Gas Control 1, 430–443.
[3] Bowker, K. A., Shuler, P. J., (1991). Carbon dioxide injection and resultant alteration of the Weber Sandstone, Rangely Field, Colorado. Am. Assoc. Pet. Geol. Bull. 75, 1489–1499.
[4] Budinis, S., Fajardy, M., Greenfield, C., (2023). Carbon Capture, Utilisation and Storage. The IEA. URL.
[5] Chudi, O., Lewis, H., Stow, D., and Buckman, J. (2016). Reservoir Quality Prediction of Deep-Water Oligocene Sandstones from the West Niger Delta by Integrating Petrological, Petrophysical and Basin Modeling. Geological Society of London Special Publications 435: 245-264.
[6] Cantucci B, Buttinelli M, Procesi M, Sciarra A, Anselmi M (2016). Algorithms for CO2 Storage Capacity Estimation: Review and Case Study. In: Vishal V, et al. (Eds.), Geologic Carbon Sequestration. Springer Cham, pp: 21-44.
[7] CSLF - Carbon Sequestration Leadership Forum, (2007). Estimation of CO2 storage capacity in geological media, June 2007.
[8] Daniels, J., (2022). Ambition Must Now Translate to Urgent, Broad, and Large-Scale Action if we Are to Maintain a Livable Climate [WWW Document]. Global CSS Institute. URL.
[9] Devore, J. L., (2004). Probability and Statistic for Engineering and the Sciences, 6th ed. Brooks/Cole-Thomson Learning, Belmont, CA.
[10] DOE-NETL (U.S. Department of Energy – National Energy Technology Labora tory – Office of Fossil Energy), (2006). Carbon Sequestration Atlas of the United States and Canada.
[11] DOE-NETL (U.S. Department of Energy – National Energy Technology Laboratory – Office of Fossil Energy), (2008). Carbon Sequestration Atlas of the United States and Canada, 2nd ed.
[12] Farajzadeh, R., Eftekhari, A. A., Dafnomilis, G., Lake, L. W., Bruining, J., (2020). On the sustainability of CO2 storage through CO2–Enhanced oil recovery. Appl. Energy 261, 114467.
[13] Ganjdanesh, R. and Hosseini, S. A. (2017). Geologic Carbon Storage Capacity Estimation Using Enhanced Analytical Simulation Tool (EASiTool). Energy Procedia 114 (2017) 4690–4696;
[14] Global CCS Institute. Global Status of CCS 2023. GCCSI. 2023.
[15] Goodman, A., Hakala, A., Bromhal, G., Deel, D., Rodosta, T., Frailey, S., Small, M., Allen, D., Romanov, V., Fazio, J., Huerta, N., Mclntyre, D., Kutchko, B., and Guthrie, G. (2011). U.S. DOE Methodology for the Development of Geologic Storage Potential for Carbon Dioxide at the National and Regional Scale. International Journal of Greenhouse Gas Control 5(4): 952 - 965.
[16] Greenfield, C., Budunis S., Fajardy, M., (2024). CO2 Transport and Storage - Energy System.
[17] Hosseininoosheri, P., Hosseini, S. A., Nunez-Lopez, V., Lake, L. W., (2018). Impact of field development strategies on CO2 trapping mechanisms in a CO2–EOR field: a case study in the permian basin (SACROC unit). Int. J. Greenhouse Gas Control 72, 92–104.
[18] Ighomuaye E., Dudun A., Boukadi F., and Osumanu J. (2024). Comparative Study of CO2 Storage Capacity Estimation in Depleted Oil & Gas Reservoir: A Case Study in Vermillion Basin Gulf of Mexico. Pet Petro Chem Eng J 2024, 8(1): 000379.
[19] IEA Greenhouse Gas R&D Programme (IEA GHG). Development of Storage Coefficients for CO2 Storage in Deep Saline Formations., 2009/13, October 2009.
[20] International Financial corporation (IFC) – World Bank Group, Nigerian CO2 Storage Atlas, March 2025,
[21] Jonas, T. M., Chou, S. I., Vasicek, S. L., (1990). Evaluation of a CO2 foam field trial: rangely weber sand unit. In: All Days. SPE.
[22] Kalam, S., Olayiwola, T., Al-Rubaii, M. M., Amaechi, B. I., Jamal, M. S., Awotunde, A. A., (2021). Carbon dioxide sequestration in underground formations: review of experimental, modeling, and field studies. J. Petrol. Explor. Prod. 11, 303–325.
[23] Kongsjorden, H., Kårstad, O., Torp, T. A., (1998). Saline aquifer storage of carbon dioxide in the Sleipner project. Waste Manag. 17, 303–308.
[24] Mustafar, I. B. and Razali, R. (2011). A Study on Prediction of Output in Oilfield Using Multiple Linear Regression. International Journal of Applied Science and Technology, 1(4): 107-113.
[25] NETL. Carbon Storage Atlas 5th Edition, Atlas V. (United States, 2015).
[26] Obah B., Livinus A., Ezugwu C. (2012) Simplified Models for Forecasting Oil Production Niger Delta Oil Rim Reservoirs Case. Petroleum Technology Development Journal 2(2): 1-12.
[27] Okpogo, E., Abbey, C., and Atueyi, I. (2018). Reservoir Characterization and Volumetric Estimation of Orok Field, Niger Delta Hydrocarbon Province. Egyptian Journal of Petroleum 27(4): 1087-1094.
[28] Omeke J., Livinus A., Uche I. N., Obah B., Ekeoma, E. (2010). A Proposed Cone Breakthrough Time for Horizontal Wells in Thin Oil Rim Reservoirs. Paper SPE 140743 presented at the 43rd SPE Nigeria Annual International Conference and Exhibition, Tinapa - Calabar, Nigeria, July 2010.
[29] Omoboriowo, A. O., Chiaghanam, O. I., Chiadikobi, K. C., Oluwajana, O. A., Soronnadi-Ononiwu C. G., Ideozu, R. U., (2012). Reservoir Characterization of KONGA Field, Onshore Niger Delta, Southern Nigeria. International Journal of Science and Emerging Technologies J 534 Sci. Emerging Tech Vol-3 No 1 IJSET, E-SSN: 2048-8688.
[30] Ringrose, P. S., Mathieson, A. S., Wright, I. W., Selama, F., Hansen, O., Bissell, R., Saoula, N., Midgley, J. (2013). "The In Salah CO2 Storage Project: Lessons Learned and Knowledge Transfer". Energy Procedia. 37: 6226–6236. Bibcode: 2013EnPro.37.6226R.
[31] Sengul, M., (2006). CO2 sequestration-a safe transition technology. Paper presented at the SPE International Health, Safety & Environment Conference, Abu Dhabi, UAE, April 2006.
[32] Sharma, S., Cook, P., Berly, T., Lees, M., (2009). The CO2CRC Otway project: overcoming challenges from planning to execution of Australia’s first CCS project. Energy Procedia 1, 1965–1972.
[33] Simon, F., 2023. EU sets World's First Target for Underground CO2 Storage Capacity.
[34] Tomḉic, L., Karoviḉ-Mariḉiḉ, V., Daniloviḉ, D., Crnogorac, M., (2018). Criteria for CO2 storage in geological formations. Podzemni Radovi 61–74.
[35] Tugwell K. W. and Livinus A. Predictive Models for Oil in Place for Oil Rim Reservoirs in the Niger Delta Using Machine Learning Approach. Pet Petro Chem Eng J 2023, 7(3): 000361.
[36] Tuttle, M. L. W., Brownfield, M. E., and Charpentier, R. R., (1999). The Niger Delta Petroleum System. USGS Science for a changing world: Open File Report 99-50, 65 p.
[37] Umar, B. A., Gholami, R., Nayak, P., Shah, A. A., and Adamu, H. (2020). Regional and Field Assessments of Potentials for Geological Storage of CO2: A Case Study of the Niger Delta Basin, Nigeria. Journal of Natural Gas Science and Engineering 77: 103-195.
[38] Ukpong S. E., Livinus A. (2023) Application of a Simulation Approach to Develop Erosional Velocity Correlation for Wells in Oil Rim Reservoirs in the Niger Delta. SPE Nigeria Annual International Conference and Exhibition, Lagos, Nigeria, July 2023.
[39] USGS. National assessment of geologic carbon dioxide storage resources: data. Report No. 774, 24 (Reston, VA, 2013).
[40] Weaver, L. K., Anderson, K. F., (1966). Cranfield Field, Cranfield Unit, Basal Tuscaloosa Reservoir, Adams and Franklin Counties, Mississippi.
[41] Yang, B., Shao, C., Hu, X., Ngata, M. R., Aminu, M. D., (2023). Advances in carbon dioxide storage projects: assessment and perspectives. Energy Fuel 37, 1757–1776.
Cite This Article
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    Livinus, A., Obot, R. M., Eyo, A., Koffi, I. U., Etuk, V. E. (2026). Evaluation of CO2 Storage Potential of Some Depleted Hydrocarbon Reservoirs: Niger Delta Case Study. Petroleum Science and Engineering, 10(1), 51-62. https://doi.org/10.11648/j.pse.20261001.15

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    Livinus, A.; Obot, R. M.; Eyo, A.; Koffi, I. U.; Etuk, V. E. Evaluation of CO2 Storage Potential of Some Depleted Hydrocarbon Reservoirs: Niger Delta Case Study. Pet. Sci. Eng. 2026, 10(1), 51-62. doi: 10.11648/j.pse.20261001.15

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    AMA Style

    Livinus A, Obot RM, Eyo A, Koffi IU, Etuk VE. Evaluation of CO2 Storage Potential of Some Depleted Hydrocarbon Reservoirs: Niger Delta Case Study. Pet Sci Eng. 2026;10(1):51-62. doi: 10.11648/j.pse.20261001.15

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  • @article{10.11648/j.pse.20261001.15,
      author = {Aniefiok Livinus and Raymond Mkpouto Obot and Antigha Eyo and Itoro Udofort Koffi and Victor E. Etuk},
      title = {Evaluation of CO2 Storage Potential of Some Depleted Hydrocarbon Reservoirs: Niger Delta Case Study},
      journal = {Petroleum Science and Engineering},
      volume = {10},
      number = {1},
      pages = {51-62},
      doi = {10.11648/j.pse.20261001.15},
      url = {https://doi.org/10.11648/j.pse.20261001.15},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.pse.20261001.15},
      abstract = {Recent joint efforts led by the international financial corporation (IFC) with strong support from the Federal Government of Nigeria and various industrial and policy stakeholders has produced the Nigerian CO2 Storage Atlas, sorting prospective geological storage sites. However, the storage efficiency factors applied to the estimated resource capacity to provide low, medium and high resource estimations may not be a true representation for the underground CO2 storage space, especially for depleted hydrocarbon reservoirs, in the Nigeria rich oil province that is very porous and permeable. We therefore present assessment of CO2 storage potential of some depleted hydrocarbon reservoirs in the Niger Delta, derive specific approximate CO2 Storage efficiency factors for these reservoirs, and develop a model for determining site-specific CO2 storage efficiency factor. Comparison of results from various approaches – production-based, volumetric- based with varying CO2 storage efficiency factors obtained from the new model and previous works, and an enhanced analytical simulation tool (EASiTool) was also carried out. The newly developed model for determining site-specific CO2 storage efficiency factor can help improve the predictive capability of the volumetric method for CO2 storage potential estimates, especially for depleted oil reservoirs in the Niger Delta.},
     year = {2026}
    }
    

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  • TY  - JOUR
    T1  - Evaluation of CO2 Storage Potential of Some Depleted Hydrocarbon Reservoirs: Niger Delta Case Study
    AU  - Aniefiok Livinus
    AU  - Raymond Mkpouto Obot
    AU  - Antigha Eyo
    AU  - Itoro Udofort Koffi
    AU  - Victor E. Etuk
    Y1  - 2026/05/27
    PY  - 2026
    N1  - https://doi.org/10.11648/j.pse.20261001.15
    DO  - 10.11648/j.pse.20261001.15
    T2  - Petroleum Science and Engineering
    JF  - Petroleum Science and Engineering
    JO  - Petroleum Science and Engineering
    SP  - 51
    EP  - 62
    PB  - Science Publishing Group
    SN  - 2640-4516
    UR  - https://doi.org/10.11648/j.pse.20261001.15
    AB  - Recent joint efforts led by the international financial corporation (IFC) with strong support from the Federal Government of Nigeria and various industrial and policy stakeholders has produced the Nigerian CO2 Storage Atlas, sorting prospective geological storage sites. However, the storage efficiency factors applied to the estimated resource capacity to provide low, medium and high resource estimations may not be a true representation for the underground CO2 storage space, especially for depleted hydrocarbon reservoirs, in the Nigeria rich oil province that is very porous and permeable. We therefore present assessment of CO2 storage potential of some depleted hydrocarbon reservoirs in the Niger Delta, derive specific approximate CO2 Storage efficiency factors for these reservoirs, and develop a model for determining site-specific CO2 storage efficiency factor. Comparison of results from various approaches – production-based, volumetric- based with varying CO2 storage efficiency factors obtained from the new model and previous works, and an enhanced analytical simulation tool (EASiTool) was also carried out. The newly developed model for determining site-specific CO2 storage efficiency factor can help improve the predictive capability of the volumetric method for CO2 storage potential estimates, especially for depleted oil reservoirs in the Niger Delta.
    VL  - 10
    IS  - 1
    ER  - 

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