Next Article in Journal
Preparation and Adsorption Performance Study of Graphene Quantum Dots@ZIF-8 Composites for Highly Efficient Removal of Volatile Organic Compounds
Previous Article in Journal
Two-Dimensional Transition Metal-Hexaaminobenzene Monolayer Single-Atom Catalyst for Electrocatalytic Carbon Dioxide Reduction
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Review

A Critical Overview of ASP and Future Perspectives of NASP in EOR of Hydrocarbon Reservoirs: Potential Application, Prospects, Challenges and Governing Mechanisms

1
Department of Petroleum Engineering, Faculty of Engineering, Soran University, Soran 44008, Kurdistan Region, Iraq
2
Research Group, Biogeochemistry & Modelling of the Earth System, Université Libre de Bruxelles, 1050 Brussels, Belgium
*
Author to whom correspondence should be addressed.
Nanomaterials 2022, 12(22), 4007; https://doi.org/10.3390/nano12224007
Submission received: 19 October 2022 / Revised: 7 November 2022 / Accepted: 8 November 2022 / Published: 14 November 2022

Abstract

:
Oil production from depleted reservoirs in EOR (Enhanced Oil Recovery) techniques has significantly increased due to its huge demands in industrial energy sectors. Chemical EOR is one of the best approaches to extract the trapped oil. However, there are gaps to be addressed and studied well for quality and cost consideration in EOR techniques. Therefore, this paper addresses for the first time a systematic overview from alkaline surfactant polymer ((ASP)) and future perspectives of nano-alkaline surfactant polymer ((NASP)), its synergy effects on oil recovery improvement, and the main screening criteria for these chemicals. The previous findings have demonstrated that the optimum salinity, choosing the best concentration, using effective nano-surfactant, polymer and alkaline type, is guaranteed an ultra-low IFT (Interfacial Tension). Core flood results proved that the maximum oil is recovered by conjugating nanoparticles with conventional chemical EOR methods (surfactant, alkaline and polymer). This work adds a new insight and suggests new recommendation into the EOR application since, for the first time, it explores the role and effect of nanotechnology in a hybrid with ASP. The study illustrates detailed experimental design of using NASP and presents an optimum micro-model setup for future design of NASP flow distribution in the porous media. The presence of nano along with other chemicals increases the capillary number as well as the stability of chemicals in the solution and strengthens the effective mechanisms on the EOR.

Graphical Abstract

1. Introduction

The United States energy information administration has forecasted that worldwide energy use will surge 28% by 2040. Hydrocarbons are regarded as the vital source of energy in the world [1]. Hydrocarbons are recovered in three stages: primary, secondary, and tertiary. Primary oil recovery or natural drive means production of oil due to a change in the production well pressure [2]. Secondary oil recovery starts when the pressure inside the well drops decreases significantly. In the secondary oil recovery reservoir, pressure increased due to fluid (water or gas) injection [3]. Tertiary recovery is used after the secondary stage to displace the trapped oil. Around 33% STOOIP (Stock Tank Oil Original in Place) recovered after primary and secondary methods [4]. After the secondary stage, high oil saturation remains in the reservoir formation [5]. Many oil companies focused on developing new technology at the beginning of 1980; in the US, oil production was expedited after using chemical flooding [6].
Chemical injection as the main EOR process mobilizes the remaining residual oil saturation by improving oil microscopic/macroscopic displacement efficiency [7,8]. Oil microscopic displacement efficiency is improved by surfactant and alkaline injection. Alkaline enhances the trapped oil mobility by adjusting the pH of in situ water [2]. On the other hand, oil macroscopic displacement efficiency is improved by polymer injection. All of the mentioned CEOR (Chemical Enhance Oil Recovery) methods aim to expedite the ultimate oil recovery.
The main limitation of CEOR method is the excessive adsorption at the rock surface. When these chemicals are introduced into the formation for oil recovery optimization, an extreme amount of surfactant and polymer is lost on the rock surface. This challenge makes the process very costly and have low efficiency in wettability alteration and IFT reduction.
Recently, nanoparticles were used as an effective chemical EOR method to reduce surfactant and polymer adsorption, to increase oil recovery by modifying wettability, and to reduce oil viscosity and water oil IFT. Recent works have suggested that using ASP in hybrid effectively improves residual oil production in the reservoir pore throats [9]. Recent advances, methods and technologies of these chemicals have not been summed up in detail. Therefore, a critical review on the role and effect of different types and concentrations of surfactant, polymer, alkaline and hybrid on oil recovery is needed
The main objective of our work is focused on the application of nano-alkaline surfactant polymer in EOR by considering the governing mechanisms of recovery and reservoir conditions. Moreover, the effect and role of hybrid nano-ASP flooding in carbonate and sandstone reservoirs are studied effectively by addressing different EOR mechanisms such as interfacial tension, wettability alteration and mobility control. Accordingly, the following questions would be addressed: (i) Could the new idea and recommendation by utilizing NASP design be successful in providing the multi-functional EOR agents? (ii) What are the advantages and disadvantages of using natural based surfactants in NASP over chemical surfactants, and which kind of surfactant is environmentally-friendly; (iii) What are the main challenges and limitations of ASP? (iv) What are the effects of different parameters on interaction between rock/fluid and fluid/fluid such as concentration and type of EOR agents, operational conditions such as salinity and temperature, and pressure of reservoir and injection conditions on the CEOR efficiencies? (v) How NASP can boost the oil recovery in real field projects? (vii) What are the main governing mechanisms of NASP in microscopic and macroscopic scales? Lastly, the authors will investigate the best scenario or method for guaranteeing the maximum oil recovery through NASP injection.

2. The Mechanisms and Role of NASP in CEOR

The EOR project is hugely controlled by mobility of fluids in the pore spaces. Favorable mobility (M) is achieved through reducing the mobility ratio to less than 1.0. Unstable displacement front occurs if M > 1.0. In this case, the large contrast in oil and water viscosity (displacing phase) fingers into oil (displaced phase) leads to premature breakthroughs at production wells, decreasing oil production. To overcome the viscous fingering issue, a polymer is used to enhance the viscosity of the displacing phase to decrease the mobility of the displaced phase (Equation (1)):
M=(Krw/Kro) × (μow)
where Krw = water relative permeability, Kro = oil relative permeability, µw = water viscosity, µo = oil viscosity. For microscopic sweeping, efficiency using AS (Alkaline Surfactant) has been utilized, in situ soap formation by alkaline flooding is not high enough to reduce IFT (Interfacial Tension) significantly [10]. The concept of using surfactant applies to washing surfaces of the oil reservoir rocks when these oils were trapped due to capillary pressure. ASP synergism is one of the successful CEORs in developing oil recovery in complex reservoir conditions. Moreover, it is cost effective in reservoirs that rely on gravity and imbibition in recovering the oil. Around 32 ASP field projects are surveyed in the literature [11]. Twenty-one field projects were reported in China followed by USA, India, Canada and Venezuela with 7, 2, 1 and 1 projects, respectively. Only one project was performed in an offshore reservoir, which was in Lagomar, Venezuela. Five-spot patterns were used in most of the ASP field projects [11]. Heavy alkylbenzene sulfonate was used in most of the projects. In these projects, pump working life and lifting system were damaged due to scale and corrosion. Due to scaling issues, weak alkali is widely used instead of strong alkali. The utilized surfactants were ORS-41HF, ORS-62, biosurfactant local Chinese surfactant product (OP10, KPS-1 and CY1), anionic surfactant (BES), (local petroleum sulfonate (YPS-3A), isobutanol, n-butanol, and isopropyl alcohol (cosurfactant). The main polymer used in an ASP slug was HPAM, 1275A, 3530S, and Pusher 700 [11]. Biopolymer (xanthan) was used only in one project [11].
Table 1 depicts a summary of previous ASP works while highlighting the role and mechanisms of each chemical alone and in hybrid for enhancing oil mobilization. To enhance the mobility and investigate the role of the injected NASP, the volumetric sweeping efficiency micromodel as a future new insight in EOR would have been a new recommendation for oil companies. A micromodel experiment (Figure 1) is a future planned model to investigate the mechanism of the fluid flow on porous media via flow visualization, fluid interactions, pore space geometry and heterogeneity effects. To carry out the test, the oil–wet glass micromodel would be saturated with oil, followed by the injection of the prepared hybrid nano-ASP solution. The micromodel is placed horizontally to avoid the gravity effect. During the tests, high resolution pictures will reveal the fluid distribution in the micromodel taken at various time intervals.
From the previous lab and experimental works, it is quite clear that, for mobilizing and improving the trapped oil effectively and efficiently, most of the EOR mechanisms such as mobility, IFT, and wettability should be controlled and activated. For this objective, the ASP synergism effect should be addressed extensively and optimum concentration of each chemical should be selected for boosting the oil recovery.

3. Natural Surfactants

Natural surfactants mostly derived from the seeds; like chemical surfactants, natural surfactants may be ionic, polymeric, nonionic or amphoteric (Table 2). The critical micelle concentration (CMC) value of synthesized natural surfactant ranges between 9–10 mM, yielding an IFT between 0.075 to 0.125 mNm−1. Natural surfactant can also reduce the contact angle efficiently besides IFT reduction. Several extraction methods are explained for synthesizing natural surfactant, but the main methods were spray dryer, soxhlet extraction, methanolic extraction, and maceration process. Different natural surfactant types versus minimum interfacial tension value are depicted in Figure 2. However, Ref. [72] explored the fact that honeycomb micro-porous structures are effective in separating water from oil, hence it may be very significant in diminishing water–oil IFT.
The previous work results (Table 2) declared that, in addition to the commercial surfactants (Table 1), natural surfactants are effective with decreasing IFT, wettability alteration and adsorption on the solid surface. Nowadays, researchers are focusing on applying this type of surfactant because of some advantages and reasonable features such as cost effectiveness, less toxicity, more stability and effectiveness at high pressure and temperature and more biodegradabilities as compared to commercial surfactants (Table 1). These kinds of surfactants can increase oil recovery by about 5–40% of OIIP.

4. Potential of NASP Synergism

To increase the potential of EOR, the optimum chemical solution is achieved at large injection volumes through injecting alkaline, polymer and surfactant (Figure 3). Oil improvement through ASP flooding has been reported previously. The principle of this method is the reaction between alkali and organic to create petroleum soaps. These petroleum soaps will interact with surfactants to reduce the IFT to minimum value (10−4 mN/m). In addition, the polymer is used to reduce the viscosity ratio of oil/water interface. Reduction of IFT and oil viscosity significantly improve vertical and displacement efficiency. ASP flooding is used for heavy oil reservoirs [25]. Recently, nanoparticle is mixed with the chemicals above to reduce the cost of these chemicals, modify the wettability, minimize oil-water IFT and boost oil recovery efficiency. Table 3 examines the types of process efficiencies for each of the methods used in the article, and predicts the amount of efficiency by NASP:
Ero   =   E do   E a   E v · S o   V p B o
where Edo is the microscopic displacement efficiency increased by using the optimum surfactant and alkaline type and concentration, Vp is the permeability variation and So is the oil saturation. Ea and Ev are displacement efficiencies of areal and vertical, developed by using the appropriate polymer.

5. NASP Prediction Technical Characteristics

The NASP synergism limits the polymer adsorption and high alkali consumption [82]. Figure 4 illustrates the main reasons for NASP interaction. The predicted technical properties of NASP EOR compared to single element flooding are summarized as follows:
The amount of surfactant is significantly lowered in NASP system;
Strong or a weak base alkali is used in the ASP synergy system;
NASP significantly increases oil recovery since it has physical and chemical (dual) effects;
It is forecasted that, when the four-element composites (N, A, S, and P) are used together, the IFT rapidly decreases to 0.001 or lower.

6. Screening the Reservoir Rock Properties

Screening criteria can determine the suitable EOR process for the target reservoir rocks and control the cost issue. Sheng [60] summarized the significant parameters of ASP process, EOR, permeability, clay contents, reservoir temperature, pressure, divalent contents, formation water salinity and oil viscosity.
Due to high anionic surfactant adsorption on carbonate, nearly all the chemical (CEOR) processes were conducted on sandstone reservoir rocks. The presence of anhydrate mineral in carbonate formations caused severe alkaline consumption [83]. On the other hand, clays in sandstone reservoirs caused surfactant adsorption. Thus, clay percentage should be lowered for effective and successful ASP flooding. The permeability is another criterion and very critical to polymer injection in the ASP project since a polymer is not able to flow through tight or low permeable reservoirs.
For alkali, the crude oil composition is a very critical point, while, for polymers, it is not significant [83]. The viscosity of oil should be >35 cP for AS projects. The oil viscosity in Chinese fields projects is from 10–70 cP. According to some authors, it is preferred to apply polymer EOR in reservoirs with viscosity of 2000 cP [84].
ASP projects are more convenient in low salinity reservoirs 10,000 ppm of total salinity [85]. The preferable reservoir temperature is 93 °C for ASP, while the average reservoir temperature for AS field projects was 27 °C, even up to 80 °C, was documented [85]. Recently, scholars have been thinking about using optimum chemicals, in particular polymers, to withstand high salinity and temperature [85].

7. ASP/EOR Process Challenges

Even though a chemical ASP process is the most effective chemical process for decreasing water cut and oil enhancement, tight oil produced in water emulsion creates huge problems [86]. In addition, several problems and limitations are associated with offshore ASP/EOR applications [87]. Large chemical volumes that are transported to remote sites, and less space availability, lead to difficulty in operation [86]. Extra treatment is needed for the produced fluid containing alkaline, polymer and surfactant. This tight emulsion formation leads to difficulty and limitation in the separation process [86]. Literature revealed that this chemical process works more efficiently in low salinity water reservoirs [87]. Nevertheless, the source of water injection is from the seawater; therefore, alternative chemicals may be needed. Divalent cations in the system are the main source of scaling.

7.1. Operational Difficulties

Like any CEOR injection, ASP are associated with many operational problems such as corrosion, scaling, pump failures, polymer degradation, and low injectivity [82]. In addition, this process is complex in design and needs water and oil analyzing. Moreover, due to a large volume of chemicals, the cost of this process should be analyzed effectively. Finally, this EOR flooding type is not favorable for hot reservoirs or those with saline water [82].

7.1.1. Scaling Issues during ASP Flooding

Calcium and magnesium reaction with the injected alkali leads to a scaling issue. This effect is regarded as one of the ASP limitations since this reaction leads to extreme surfactant precipitation and alkali consumption [88,89]. Several publications reported scaling issues during ASP injection into the reservoir [90,91,92,93]. Scales may originate from the alkalis and carbonate mineral’s reaction. According to the literature, silicate scale formation is a very sophisticated mechanism because the problems associated with silicate are poorly understood. In Chinese oil fields, scaling issues have been observed and reported [93].

7.1.2. Surfactant Precipitation

Divalent cationic existences in hard brines cause surfactant precipitation as illustrated in Equation (3):
2R + M2+ → MR2
where MR2 is the surfactant divalent cation, and R the anionic surfactant. Different factors like temperature, alcohol and salt concentration are responsible for anionic surfactants’ precipitation [94]. In most of the cases, the presence of oil reduces surfactant precipitation efficiently since oil competes for surfactant. Ethoxylate (EO) helps surfactant to resist divalent cations. At lower hardness, monovalent cation is formed from the reaction of multivalent cation with the anionic surfactant [94].

8. Prospects and Future Developments of ASP/CEOR

Based on this review paper, the following conclusions and recommendations can be proposed for this study:
ASP limitations could be due to alkaline since alkaline reduces polymer viscosity. Thus, a big question is: can SP work more effectively than ASP?
Due to the carbonate rock complexity, most of the nano-EOR flooding has to be performed on sandstone rocks. Further studies should be implemented for understanding the effect of oil recovery on carbonate rocks;
More sophisticated and advanced tools should be used to accurately examine the role of NASP in changing the wettability and IFT;
Due to the lack of economic data in the research papers, more economic study should be implemented to evaluate the economic performance of NASP in accelerating oil recovery;
HS and HT could limit NASP to work effectively in maximizing oil recovery. This is why a more effective nano, surfactant and polymer should be developed to limit this issue.
More research is needed to evaluate the performance of NASP in sandstone and carbonate reservoirs.

9. NASP Performance Anticipation in Changing the Wettability and IFT

After reviewing and evaluating ASP lab and field projects, it is forecasted that NASP could modify wettability and IFT effectively more than any other previous chemical methods due to the synergism effect of ASN (Alkaline Surfactant Nano), and it may stabilize the polymer solution excellently due to the NP synergism effect. Based on the above points, ultimate oil recovery could be guaranteed by implementing NASP. IFT and contact angle are the main parameters of any EOR type since it is related to the capillary number modification. Due to accuracy and ease of use, pendant drop is considered as one of the main methods to calculate IFT and contact angle. IFT study will be implemented by introducing a drop into a bulk phase under the desired P and T. For contact angle measurement, the drop is completed on a plane solid sample. Pictures captured by a digital camera connected to a computer show the shape of the drop and allow for solving the Laplace equation contact angle and IFT calculation. Figure 5 illustrates IFT and contact angle measurement by using pendant drop.

10. Core Flooding

For recovery measurement, a dynamic test will be prepared by core-flooding. Different core plugs are used with injecting best chemical, nanofluid and hybrid nanochemical solutions under the reservoir condition. For this purpose, a core sample should undergo several procedures to be prepared and aged. After aging, the brine solution is injected, followed by the injection of a hybrid Nano-ASP solution to study oil recovery from the carbonate rock. Then, the values of oil production are recorded vs. time. Finally, oil recovery is plotted vs. pore volume. This review paper forecasted that oil recovery by NASP could be more than 25% due to the improved mechanisms that have been discussed in the other sections. Figure 6 illustrates NASP core–flood procedure.

11. Future Design, Materials and Features of NASP Process

11.1. Nano-EOR

Nanoparticles are wide classes of material substances, with sizes between 1–100 nm. Nowadays, the oil and gas industry has attracted much consideration on applications of nanoparticles (NPs). NPs have become widely used due to having unique optical, magnetic and electric features. Mixing nanoparticles with other substance phases is called nanocomposites (NCs). NPs within different dispersion media can be easily transported through the porous media and reach the oil bank due to their smaller sizes, less than micron-sized rock pores. Consequently, NCs can be used to decrease ASP adsorption with the rock surface, altering the wettability of the rock, reducing the interfacial tension (IFT) and improving oil displacement and recovery (Figure 7). The surface area-to-volume ratio of nanoparticles is too large, where a small concentration of them is needed to induce EOR injection fluids. Combining nanoparticles with the natural polymers develop polymeric nanofluids, thus the resulted NPs would have a better stability, mobility of injection fluids and sweep efficiency.
Figure 7 highlights that the nanoparticles can alter the wettability and reduce oil water IFT. The mechanism of wettability alteration by nanoparticles is to build a wedge film on the oil droplet and the rock surface. The nano size particles re-arrange themselves between the rock and oil droplet, leading to oil separation and thus altering the wettability from hydrophobicity to hydrophilicity, and decreasing the excessive surfactant adsorption. Moreover, disjoining pressure is regarded as one of the nanoparticle mechanisms in EOR since it responsible for changing the oil wet surface to water wet. This mechanism is highly affected by nanoparticle type and concentration. Different nanoparticle types play different roles in the EOR mechanism process (Table 4).

11.2. Summary of Nano (NASP) EOR Flooding

Nanoparticles are very effective in changing the wettability and contact angle. Recently, nanoparticles were mixed with surfactant, polymer and SP to further improve oil recovery. The shape, size, dispersion media, nature and concentraion of nanoparticle will govern the most suitable and effective nanoparticles for achieving the best EOR mechanisms (Table 4). The main advantages of using nanoparticles are their large surface areas with spherical nanoparticles being more effective than any other nanoparticle shapes.
The main parameters that control the nanoparticle shape is the temperature, pH and time. In addition, nanoparticles play an astonishing role in improving the oil recovery since smaller nanoparticle size leads to lower IFT and contact angle (Figure 7). Furthermore, lab works hypothesized that optimum concentration should be guaranteed for any EOR application; otherwise, nanoparticles will agglomerate, leading to lower recovery efficiency. Regarding the dispersion media, our review paper finds out that different oil recovery is accomplished through dispersing nanoparticles into different dispersion media. However, Rajabi et al. used the wettability modifier: nanoparticles, surfactant and alkaline, but the highest percent of oil recovery was obtained by nano-surfactant rather than by adding alkaline [95]. The latter did not cause any positive impact on EOR. Furthermore, the oil improvement, using different kinds of nanoparticles, nano-polymers, nano-surfactants and nano-surfactant-polymers, efficiently decreases contact angles and IFT (Table 5), despite the fact that heterogeneity of sedimentary rocks could influence the quantity of oil improvement. The sedimentary rocks, especially carbonate rocks, characterized intensive lithological changes along micrometer-sized scales in both subsurface [96] and near-surface conditions [97]. This heterogeneity in enhanced oil recovery is the main cause behind the failure of oil recovery in the field scale. Therefore, the new model or design (NASP) for future experimental work should be achieved with detailed work on reservoir characteristics, including mineralogy and, of course, by detailed observations (both optical microscope and SEM).
This work systematically investigates the potential of NASP suspension for enhanced oil recovery (EOR) in carbonate and sandstone reservoirs. Using NASP (Nano/Alkaline/Surfactant/Polymer) could be proved successfully in future work due to its ability to improve displacement and sweep efficiency.
In the case of NASP, various mechanisms will be activated, and the interaction of them will be important, which we will describe separately to better understand the issue:
  • The capability of the nano-polymer suspensions for improving the oil recovery by the following mechanisms:
    • Wettability alteration was explored using contact angle measurement; increasing temperature and adding salt to polymeric solutions caused a reduction in shear viscosity, and the addition of NPs to the solutions could relatively recover the viscosity;
    • The presence of polymers in the nanofluids improved dispersion stability of NPs;
    • The nano-polymer suspensions could improve the ability of the NPs for wettability alteration and faster equilibrium states obtained than the polymer-free nanofluids.
  • The performance of the nano-surfactant solutions for improving the oil recovery by the following mechanisms:
    • The adsorption process of these substances is one of the important methods to increase the oil recovery factor from oil reservoirs by wettability alteration;
    • The results of the IFT experiments of these materials showed that surfactant nanofluid solutions could significantly reduce the IFT value between the oil and water system.
  • Alkaline can activate the following mechanisms:
    • Interfacial tension reduction;
    • Wettability alteration;
    • Control of adsorption of ions;
    • Improving the emulsion stability;
    • Inhibitor of clay swelling.
Suitable experimental design is critical for using nanoparticles with chemical EOR. This paper for the first time will investigate a detailed schematic diagram for using nanoparticles in hybrid with ASP for future perspectives.
Figure 8. Future experimental work. The figure forecasted NASP experimental work methodology. The latter is subdivided into several sections: material preparation, carbonate rock preparation and EOR static tests (IFT and contact angle) and Dunamis tests (core flooding and micromodel).
Figure 8. Future experimental work. The figure forecasted NASP experimental work methodology. The latter is subdivided into several sections: material preparation, carbonate rock preparation and EOR static tests (IFT and contact angle) and Dunamis tests (core flooding and micromodel).
Nanomaterials 12 04007 g008

12. Conclusions

  • To sum up, CEOR was applied to greatly increase the ultimate oil recovery by wettability, IFT and mobility modification. This paper will add a new insight integrating nano-alkaline, polymer and surfactant flooding for the first time by addressing the main mechanism of each one. The main conclusions of this paper are as follows:
  • ASP limitations could be due to alkaline since alkaline reduces polymer viscosity;
  • Due to nano, surfactant, polymer, and alkaline synergy effects, most of the EOR mechanisms are greatly improved, leading to higher oil recovery as compared to using each component alone;
  • The objective behind using NASP in hybrid is to modify wettability, IFT and mobility ratios, which are regarded as the main EOR mechanisms;
  • NASP type and concentration play a major role in changing wettability and reducing IFT to a minimum level;
  • For checking the mobility of chemical EOR, the micromodel is used to find the fluid flow distribution;
  • Nanoparticle type and size play a major role in changing wettability and reducing IFT to the minimum level;
  • Future recommendations by utilizing NASP will probably be a new finding to understand the details about the EOR system in both micro- and -macroscale settings;
  • This review paper highlights the fact that natural surfactants are less costly, biodegradable, available, less toxic, more stable, and environmentally friendly, and it can reduce the IFT to an ultra-low value.
  • NASP could effectively boost the oil recovery by more than 25% due to the synergism effect.

Author Contributions

Writing and preparation the original draft, N.S. and R.S.; review and editing, N.S. and A.P; Methodology and software, N.S., R.S. and A.P. All authors have read and agreed to the published version of the manuscript.

Funding

The study benefited from research funds of the Université Libre de Bruxelles (ULB)-Belgium.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Litvinenko, V. The Role of Hydrocarbons in the Global Energy Agenda: The Focus on Liquefied Natural Gas. Resources 2020, 9, 59. [Google Scholar] [CrossRef]
  2. Sheng, J. Status of Alkaline Flooding Technology. J. Pet. Eng. Technol. 2015, 5, 44–50. [Google Scholar]
  3. Simon, R. Enhanced oil recovery: Definitions, fundamentals, applications, and research frontiers. Phys. Chem. Earth 1981, 13–14, 447–460. [Google Scholar] [CrossRef]
  4. Alvarado, V.; Manrique, E. Enhanced Oil Recovery: An Update Review. Energies 2010, 3, 1529. [Google Scholar] [CrossRef]
  5. Pei, H.; Zhang, G.; Ge, J.; Jin, L. The Effect of Oil Viscosity, Permeability, and Residual Oil Saturation on the Performance of Alkaline Flooding in the Recovery of Heavy Oil. Energy Sources Part A Recovery Util. Environ. Eff. 2012, 34, 702–710. [Google Scholar] [CrossRef]
  6. Gbadamosi, A.O.; Junin, R.; Manan, M.A.; Agi, A.; Yusuff, A.S. An overview of chemical enhanced oil recovery: Recent advances and prospects. Int. Nano Lett. 2019, 9, 171–202. [Google Scholar] [CrossRef] [Green Version]
  7. Hussein, I.A.; Feng, Y.; Bai, B. Chemical EOR. J. Chem. 2013, 2013, 871542. [Google Scholar] [CrossRef]
  8. Abbas, A.H.; Ajunwa, O.M.; Mazhit, B.; Martyushev, D.A.; Bou-Hamdan, K.F.; Alsaheb, R.A.A. Evaluation of OKRA (Abelmoschus esculentus) Macromolecular Solution for Enhanced Oil Recovery in Kazakhstan Carbonate Reservoir. Energies 2022, 15, 6827. [Google Scholar] [CrossRef]
  9. Mohajeri, M.; Reza Rasaei, M.; Hekmatzadeh, M. Experimental study on using SiO2 nanoparticles along with surfactant in an EOR process in micromodel. Pet. Res. 2019, 4, 59–70. [Google Scholar] [CrossRef]
  10. Liu, S.; Zhang, D.; Yan, W.; Puerto, M.; Hirasaki, G.J.; Miller, C.A. Favorable Attributes of Alkaline-Surfactant-Polymer Flooding. SPE J. 2008, 13, 5–16. [Google Scholar] [CrossRef]
  11. Sheng, J.J. A Comprehensive Review of Alkaline-Surfactant-Polymer (ASP) Flooding. In Proceedings of the SPE Western Regional & AAPG Pacific Section Meeting 2013 Joint Technical Conference, Monterey, CA, USA, 19–25 April 2013. SPE-165358-MS. [Google Scholar]
  12. Burk, J.H. Comparison of Sodium Carbonate, Sodium Hydroxide, and Sodium Orthosilicate for EOR. SPE Reserv. Eng. 1987, 2, 9–16. [Google Scholar] [CrossRef]
  13. Hazarika, K.; Gogoi, S.B. Effect of alkali on alkali–surfactant flooding in an Upper Assam oil field. J. Pet. Explor. Prod. Technol. 2020, 10, 1591–1601. [Google Scholar] [CrossRef] [Green Version]
  14. El-Sayed, A.A.H.; Almalik, M.S. Effect of Horizontal-vertical Well Configuration On Oil Recovery By Alkaline Flooding. J. Can. Pet. Technol. 1995, 34, 19–24. [Google Scholar] [CrossRef]
  15. Rincón-García, F.; Ortiz-Moreno, H.; Marroquín, G.; Moreno-Montiel, N.; Sanchez, S.; Chacon, C.; Sánchez-Minero, F. Enhanced oil recovery by means of alkali injection. Behavior of the SARA fractions. Pet. Sci. Technol. 2019, 37, 1–10. [Google Scholar] [CrossRef]
  16. Samanta, A.; Bera, A.; Mandal, A.; Ojha, K. Comparative Studies on Enhanced Oil Recovery by Alkali-Surfactant and Polymer Flooding. J. Pet. Sci. Eng. 2012, 2, 67–74. [Google Scholar] [CrossRef] [Green Version]
  17. Cooke, C.E., Jr.; Williams, R.E.; Kolodzie, P.A. Oil Recovery by Alkaline Waterflooding. J. Pet. Technol. 1974, 26, 1365–1374. [Google Scholar] [CrossRef]
  18. Leach, R.O.; Wagner, O.R.; Wood, H.W.; Harpke, C.F. A Laboratory and Field Study of Wettability Adjustment in Water Flooding. J. Pet. Technol. 1962, 14, 206–212. [Google Scholar] [CrossRef]
  19. Raimondi, P.; Gallagher, B.J.; Ehrlich, R.; Messmer, J.H.; Bennett, G.S. Alkaline Waterflooding: Design and Implementation of a Field Pilot. J. Pet. Technol. 1977, 29, 1359–1368. [Google Scholar] [CrossRef]
  20. Emery, L.W.; Mungan, N.; Nicholson, R.W. Caustic Slug Injection in the Singleton Field. J. Pet. Technol. 1970, 22, 1569–1576. [Google Scholar] [CrossRef]
  21. Graue, D.J.; Johnson, C.E., Jr. Field Trial of Caustic Flooding Process. J. Pet. Technol. 1974, 26, 1353–1358. [Google Scholar] [CrossRef]
  22. Du, Y.; Zhang, G.; Ge, J.; Li, G.; Feng, A. Influence of Oil Viscosity on Alkaline Flooding for Enhanced Heavy Oil Recovery. J. Chem. 2013, 2013, 938237. [Google Scholar] [CrossRef]
  23. Alam, M.W.; Tiab, D. Mobility Control of Caustic Flood. Energy Sources 1988, 10, 1–19. [Google Scholar] [CrossRef]
  24. Kazempour, M.; Sundstrom, E.; Alvarado, V. Effect of Alkalinity on Oil Recovery During Polymer Floods in Sandstone. SPE Reserv. Eval. Eng. 2012, 15, 195–209. [Google Scholar] [CrossRef]
  25. Zhijian, Q.; Yigen, Z.; Xiansong, Z.; Jialin, D. A Successful ASP flooding Pilot in Gudong Oil Field. In Proceedings of the SPE/DOE Improved Oil Recovery Symposium, Tulsa, OK, USA, 19–22 April 1998. SPE-39613-MS. [Google Scholar]
  26. Strand, S.; Høgnesen, E.J.; Austad, T. Wettability alteration of carbonates—Effects of potential determining ions (Ca2+ and SO42−) and temperature. Colloids Surf. A Physicochem. Eng. Asp. 2006, 275, 1–10. [Google Scholar] [CrossRef]
  27. Mohajeri, M.; Hemmati, M.; Shekarabi, A.S. An experimental study on using a nanosurfactant in an EOR process of heavy oil in a fractured micromodel. J. Pet. Sci. Eng. 2015, 126, 162–173. [Google Scholar] [CrossRef]
  28. Gupta, R.; Mohanty, K.K.K. Temperature Effects on Surfactant-Aided Imbibition Into Fractured Carbonates. SPE J. 2010, 15, 588–597. [Google Scholar] [CrossRef]
  29. Rilian, N.A.; Sumestry, M.; Wahyuningsih. Surfactant Stimulation to Increase Reserves in Carbonate Reservoir: “A Case Study in Semoga Field”. In Proceedings of the SPE EUROPEC/EAGE Annual Conference and Exhibition, Barcelona, Spain, 14–17 June 2010. SPE-130060-MS. [Google Scholar]
  30. Alvarez, J.O.; Neog, A.; Jais, A.; Schechter, D.S. Impact of Surfactants for Wettability Alteration in Stimulation Fluids and the Potential for Surfactant EOR in Unconventional Liquid Reservoirs. In Proceedings of the SPE Unconventional Resources Conference, The Woodlands, TX, USA, 1–3 April 2014. D011S002R003. [Google Scholar]
  31. Kamal, M.S.; Hussein, I.A.; Sultan, A.S. Review on Surfactant Flooding: Phase Behavior, Retention, IFT, and Field Applications. Energy Fuels 2017, 31, 7701–7720. [Google Scholar] [CrossRef]
  32. Pal, S.; Mushtaq, M.; Banat, F.; Al Sumaiti, A.M. Review of surfactant-assisted chemical enhanced oil recovery for carbonate reservoirs: Challenges and future perspectives. Pet. Sci. 2018, 15, 77–102. [Google Scholar] [CrossRef] [Green Version]
  33. Xie, X.; Weiss, W.W.; Tong, Z.J.; Morrow, N.R. Improved Oil Recovery from Carbonate Reservoirs by Chemical Stimulation. SPE J. 2005, 10, 276–285. [Google Scholar] [CrossRef]
  34. Vijapurapu, C.S.; Rao, D.N. Compositional effects of fluids on spreading, adhesion and wettability in porous media. Colloids Surf. A Physicochem. Eng. Asp. 2004, 241, 335–342. [Google Scholar] [CrossRef]
  35. Adil, M.; Lee, K.; Mohd Zaid, H.; Ahmad, S.; Alnarabiji, M. Experimental study on electromagnetic-assisted ZnO nanofluid flooding for enhanced oil recovery (EOR). PLoS ONE 2018, 13, e0193518. [Google Scholar] [CrossRef] [PubMed]
  36. Fu, L.; Zhang, G.; Ge, J.; Liao, K.; Pei, H.; Jiang, P.; Li, X. Study on organic alkali-surfactant-polymer flooding for enhanced ordinary heavy oil recovery. Colloids Surf. A Physicochem. Eng. Asp. 2016, 508, 230–239. [Google Scholar] [CrossRef]
  37. Mohd Zaid, H.; Ahmad, S.; Yahya, N. The Effect of Zinc Oxide and Aluminum Oxide Nanoparticles on Interfacial Tension and Viscosity of Nanofluids for Enhanced Oil Recovery. Adv. Mater. Res. 2014, 1024, 56–59. [Google Scholar] [CrossRef]
  38. Onyekonwu, M.; Akaranta, O. Alkaline-Surfactant Flooding in Niger-Delta: An Experimental Approach. In Proceedings of the SPE Nigeria Annual International Conference and Exhibition, Lagos, Nigeria, 2–4 August 2016. SPE-184271-MS. [Google Scholar]
  39. Yang, J.; Jin, B.; Jiang, L.; Liu, F. An Improved Numerical Simulator for Surfactant/Polymer Flooding. In Proceedings of the SPE/IATMI Asia Pacific Oil & Gas Conference and Exhibition, Nusa Dua, Indonesia, 20–22 October 2015. SPE-176206-MS. [Google Scholar]
  40. Kamal, M.S.; Sultan, A.S.; Al-Mubaiyedh, U.A.; Hussein, I.A. Review on Polymer Flooding: Rheology, Adsorption, Stability, and Field Applications of Various Polymer Systems. Polym. Rev. 2015, 55, 491–530. [Google Scholar] [CrossRef]
  41. Chen, T.; Song, Z.; Fan, Y.; Hu, C.; Qiu, L.; Tang, J. A Pilot Test of Polymer Flooding in an Elevated-Temperature Reservoir. SPE Reserv. Eval. Eng. 1998, 1, 24–29. [Google Scholar] [CrossRef]
  42. Chen, Q.; Wang, Y.; Lu, Z.; Feng, Y. Thermoviscosifying polymer used for enhanced oil recovery: Rheological behaviors and core flooding test. Polym. Bull. 2012, 70, 391–401. [Google Scholar] [CrossRef]
  43. Cui, X.-H.; Li, Z.-Q.; Cao, X.-I.; Song, X.-W.; Zhang, X. A Novel PPG Enhanced Surfactant-Polymer System for EOR. In Proceedings of the SPE Enhanced Oil Recovery Conference, Kuala Lumpur, Malaysia, 19–21 July 2011. SPE-143506-MS. [Google Scholar]
  44. Mogbo, O. Polymer Flood Simulation in a Heavy Oil Field: Offshore Niger-Delta Experience. In Proceedings of the SPE Enhanced Oil Recovery Conference, Kuala Lumpur, Malaysia, 19–21 July 2011. [Google Scholar] [CrossRef]
  45. Gao, P.; Towler, B. Investigation of polymer and surfactant-polymer injections in South Slattery Minnelusa Reservoir, Wyoming. J. Pet. Explor. Prod. Technol. 2011, 1, 23–31. [Google Scholar] [CrossRef] [Green Version]
  46. Zubari, H.K.; Sivakumar, V.C.B. Single Well Tests to determine the Efficiency of Alkaline-Surfactant Injection in a highly Oil-Wet Limestone Reservoir. In Proceedings of the Middle East Oil Show, Sanabis, Bahrain, 5–8 April 2003. SPE-81464-MS. [Google Scholar]
  47. Vavra, E.; Puerto, M.; Biswal, S.L.; Hirasaki, G.J. A systematic approach to alkaline-surfactant-foam flooding of heavy oil: Microfluidic assessment with a novel phase-behavior viscosity map. Sci. Rep. 2020, 10, 12930. [Google Scholar] [CrossRef]
  48. Liu, Q.; Dong, M.; Yue, X.; Hou, J. Synergy of alkali and surfactant in emulsification of heavy oil in brine. Colloids Surf. A: Physicochem. Eng. Asp. 2006, 273, 219–228. [Google Scholar] [CrossRef]
  49. Sheng, J.J. Chapter 8—Alkaline-Surfactant Flooding. In Enhanced Oil Recovery Field Case Studies; Sheng, J.J., Ed.; Gulf Professional Publishing: Boston, MA, USA, 2013; pp. 179–188. [Google Scholar] [CrossRef]
  50. Pei, H.; Zhang, G.; Ge, J.; Tang, M.; Zheng, Y. Comparative Effectiveness of Alkaline Flooding and Alkaline–Surfactant Flooding for Improved Heavy-Oil Recovery. Energy Fuels 2012, 26, 2911–2919. [Google Scholar] [CrossRef]
  51. Bryan, J.; Kantzas, A. Potential for Alkali-Surfactant Flooding in Heavy Oil Reservoirs Through Oil-in-Water Emulsification. J. Can. Pet. Technol. 2009, 48, 37–46. [Google Scholar] [CrossRef]
  52. Sheng, J. Alkaline-Polymer Flooding. In Enhanced oil Recovery Field Case Studies; Gulf Professional Publishing: Boston, MA, USA, 2013; pp. 169–178. [Google Scholar] [CrossRef]
  53. Pitts, M.J.; Wyatt, K.; Surkalo, H. Alkaline-Polymer Flooding of the David Pool, Lloydminster Alberta. In Proceedings of the SPE/DOE Symposium on Improved Oil Recovery, Tulsa, OK, USA, 17–21 April 2004. SPE-89386-MS. [Google Scholar]
  54. Pitts, M.J.; Dowling, P.; Wyatt, K.; Surkalo, H.; Adams, K.C. Alkaline-Surfactant-Polymer Flood of the Tanner Field. In Proceedings of the SPE/DOE Symposium on Improved Oil Recovery, Tulsa, OK, USA, 22–26 April 2006. SPE-100004-MS. [Google Scholar]
  55. Chen, Z.; Zhao, X.; Wang, Z.; Fu, M. A comparative study of inorganic alkaline/polymer flooding and organic alkaline/polymer flooding for enhanced heavy oil recovery. Colloids Surf. A Physicochem. Eng. Asp. 2015, 469, 150–157. [Google Scholar] [CrossRef]
  56. Doll, T.E. An Update of the Polymer-Augmented Alkaline Flood at the Isenhour Unit, Sublette County, Wyoming. SPE Reserv. Eng. 1988, 3, 604–608. [Google Scholar] [CrossRef]
  57. Wu, Y.; Dong, M.; Shirif, E. Study of Alkaline/Polymer Flooding for Heavy-Oil Recovery Using Channeled Sandpacks. SPE Reserv. Eval. Eng. 2011, 14, 310–319. [Google Scholar] [CrossRef]
  58. Yang, D.-H.; Wang, J.-Q.; Jing, L.-X.; Feng, Q.-X.; Ma, X.-P. Case Study of Alkali—Polymer Flooding with Treated Produced Water. In Proceedings of the SPE EOR Conference at Oil & Gas West Asia, Muscat, Oman, 11–13 April 2010. SPE-129554-MS. [Google Scholar]
  59. Zhang, J.; Wang, K.; He, F.; Zhang, F. Ultimate Evaluation of the Alkali/Polymer Combination Flooding Pilot Test in XingLongTai Oil Field. In Proceedings of the SPE Asia Pacific Improved Oil Recovery Conference, Kuala Lumpur, Malaysia, 25–26 October 1999. SPE-57291-MS. [Google Scholar]
  60. Adams, W.T.; Schievelbein, V.H. Surfactant Flooding Carbonate Reservoirs. SPE Reserv. Eng. 1987, 2, 619–626. [Google Scholar] [CrossRef]
  61. Sun, C.; Guo, H.; Li, Y.; Song, K. Recent Advances of Surfactant-Polymer (SP) Flooding Enhanced Oil Recovery Field Tests in China. Geofluids 2020, 2020, 1–16. [Google Scholar] [CrossRef]
  62. Sharma, T.; Kumar, G.S.; Sangwai, J.S. Comparative effectiveness of production performance of Pickering emulsion stabilized by nanoparticle–surfactant–polymerover surfactant–polymer (SP) flooding for enhanced oil recoveryfor Brownfield reservoir. J. Pet. Sci. Eng. 2015, 129, 221–232. [Google Scholar] [CrossRef]
  63. Ge, M.-R.; Miao, S.-J.; Liu, J.-F.; Gang, H.-Z.; Yang, S.-Z.; Mu, B.-Z. Laboratory studies on a novel salt-tolerant and alkali-free flooding system composed of a biopolymer and a bio-based surfactant for oil recovery. J. Pet. Sci. Eng. 2021, 196, 107736. [Google Scholar] [CrossRef]
  64. Cheraghian, G. An Experimental Study of Surfactant Polymer for Enhanced Heavy Oil Recovery Using a Glass Micromodel by Adding Nanoclay. Pet. Sci. Technol. 2015, 33, 1410–1417. [Google Scholar] [CrossRef]
  65. Liu, W.; Luo, L.; Liao, G.; Zuo, L.; Wei, Y.; Jiang, W. Experimental study on the mechanism of enhancing oil recovery by polymer-surfactant binary flooding. Shiyou Kantan Yu Kaifa/Pet. Explor. Dev. 2017, 44, 600–607. [Google Scholar] [CrossRef]
  66. Olsen, D.K.; Hicks, M.D.; Hurd, B.G.; Sinnokrot, A.A.; Sweigart, C.N. Design of a Novel Flooding System for an Oil-Wet Central Texas Carbonate Reservoir. In Proceedings of the SPE/DOE Enhanced Oil Recovery Symposium, Tulsa, OK, USA, 22–25 April 1990. SPE-20224-MS. [Google Scholar]
  67. Manji, K.H.; Stasiuk, B.W. Design Considerations For Dome’s David Alkali/Polymer Flood. J. Can. Pet. Technol. 1988, 27, 49–54. [Google Scholar] [CrossRef]
  68. Vargo, J.; Turner, J.; Bob, V.; Pitts, M.J.; Wyatt, K.; Surkalo, H.; Patterson, D. Alkaline-Surfactant-Polymer Flooding of the Cambridge Minnelusa Field. SPE Reserv. Eval. Eng. 2000, 3, 552–558. [Google Scholar] [CrossRef]
  69. Dang, C.T.; Nguyen, N.T.; Chen, Z.; Nguyen, H.X.; Bae, W.; Phung, T.H. A Comprehensive Evaluation of the Performances of Alkaline/Surfactant/Polymer in Conventional and Unconventional Reservoirs. In Proceedings of the SPE Asia Pacific Oil and Gas Conference and Exhibition, Perth, Australia, 22–24 October 2012. SPE-160444-MS. [Google Scholar]
  70. Feng, R.-S.; Guo, Y.-J.; Zhang, X.-M.; Hu, J.; Li, H.-B. Alkali/Surfactant/Polymer Flooding in the Daqing Oilfield Class II Reservoirs Using Associating Polymer. J. Chem. 2013, 2013, 275943. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  71. Bealessio, B.A.; Blánquez Alonso, N.A.; Mendes, N.J.; Sande, A.V.; Hascakir, B. A review of enhanced oil recovery (EOR) methods applied in Kazakhstan. Petroleum 2021, 7, 1–9. [Google Scholar] [CrossRef]
  72. Bormashenko, E.; Balter, S.; Bormashenko, Y.; Aurbach, D. Honeycomb structures obtained with breath figures self-assembly allow water/oil separation. Colloids Surf. A Physicochem. Eng. Asp. 2012, 415, 394–398. [Google Scholar] [CrossRef]
  73. Saha, R.; Uppaluri, R.; Tiwari, P. Impact of Natural Surfactant (Reetha), Polymer (Xanthan Gum), and Silica Nanoparticles To Enhance Heavy Crude Oil Recovery. Energy Fuels 2019, 33, 4225–4236. [Google Scholar] [CrossRef]
  74. Ahmadi, M.A.; Arabsahebi, Y.; Shadizadeh, S.R.; Shokrollahzadeh Behbahani, S. Preliminary evaluation of mulberry leaf-derived surfactant on interfacial tension in an oil-aqueous system: EOR application. Fuel 2014, 117, 749–755. [Google Scholar] [CrossRef]
  75. Shadizadeh, S.; Kharrat, R. Experimental Investigation of Matricaria chamomilla Extract Effect on Oil-Water Interfacial Tension: Usable for Chemical Enhanced Oil Recovery. Pet. Sci. Technol. 2015, 33, 901–907. [Google Scholar] [CrossRef]
  76. Jalali, A.; Mohsenatabar Firozjaii, A.; Shadizadeh, S.R. Experimental investigation on new derived natural surfactant: Wettability alteration, IFT reduction, and core flooding in oil wet carbonate reservoir. Energy Sources Part A Recovery Util. Environ. Eff. 2019, 1–11. [Google Scholar] [CrossRef]
  77. Saxena, N.; Saxena, A.; Mandal, A. Synthesis, characterization and enhanced oil recovery potential analysis through simulation of a natural anionic surfactant. J. Mol. Liq. 2019, 282, 545–556. [Google Scholar] [CrossRef]
  78. Deymeh, H.; Shadizadeh, S.R.; Motafakkerfard, R. Experimental investigation of Seidlitzia rosmarinus effect on oil–water interfacial tension: Usable for chemical enhanced oil recovery. Sci. Iran. 2012, 19, 1661–1664. [Google Scholar] [CrossRef] [Green Version]
  79. Kumar, S.; Kumar, A.; Mandal, A. Characterizations of Surfactant Synthesized from Jatropha Oil and its Application in Enhanced Oil Recovery. AIChE J. 2017, 63, 2731–2741. [Google Scholar] [CrossRef]
  80. Rahmati, M.; Mashayekhi, M.; Songolzadeh, R.; Daryasafar, A. Effect of Natural Leaf-derived Surfactants on Wettability Alteration and Interfacial Tension Reduction in Water-oil System: EOR Application. J. Jpn. Pet. Inst. 2015, 58, 245–251. [Google Scholar] [CrossRef] [Green Version]
  81. Khorram Ghahfarokhi, A.; Dadashi, A.; Daryasafar, A.; Moghadasi, J. Feasibility study of new natural leaf-derived surfactants on the IFT in an oil–aqueous system: Experimental investigation. J. Pet. Explor. Prod. Technol. 2015, 5, 375–382. [Google Scholar] [CrossRef] [Green Version]
  82. Olajire, A.A. Review of ASP EOR (alkaline surfactant polymer enhanced oil recovery) technology in the petroleum industry: Prospects and challenges. Energy 2014, 77, 963–982. [Google Scholar] [CrossRef]
  83. Taber, J.J. Technical Screening Guides for the Enhanced Recovery of Oil. In Proceedings of the SPE Annual Technical Conference and Exhibition, San Francisco, CA, USA, 5–8 October 1983. SPE-12069-MS. [Google Scholar]
  84. Moe Soe Let, K.P.; Manichand, R.N.; Seright, R.S. Polymer Flooding a ~500-cp Oil. In Proceedings of the SPE Improved Oil Recovery Symposium, Tulsa, OK, USA, 14–18 April 2012. SPE-154567-MS. [Google Scholar]
  85. Vermolen, E.C.; van Haasterecht, M.J.; Masalmeh, S.K.; Faber, M.J.; Boersma, D.M.; Gruenenfelder, M. Pushing the Envelope for Polymer Flooding Towards High-temperature and High-salinity Reservoirs with Polyacrylamide Based Ter-polymers. In Proceedings of the SPE Middle East Oil and Gas Show and Conference, Manama, Bahrain, 25–28 September 2011. SPE-141497-MS. [Google Scholar]
  86. French, T. Evaluation of the Sho-Vel-Tum Alkali-Surfactant-Polymer (ASP) Oil Recovery Project-Stephens County, OK; National Petroleum Technology Office (NPTO): Tulsa, OK, USA, 1999.
  87. Raney, K.; Ayirala, S.; Chin, R.; Verbeek, P. Surface and Subsurface Requirements for Successful Implementation of Offshore Chemical Enhanced Oil Recovery. SPE Prod. Oper. 2012, 27, 294–305. [Google Scholar] [CrossRef]
  88. He, L.; Gang, C.; Guochen, S. Technical Breakthrough in PCPs’ Scaling Issue of ASP Flooding in Daqing Oilfield. In Proceedings of the SPE Annual Technical Conference and Exhibition, Anaheim, CA, USA, 11–14 November 2007. [Google Scholar]
  89. Arensdorf, J.; Hoster, D.; McDougall, D.; Yuan, M. Static and dynamic testing of silicate scale inhibitors. In Proceedings of the International Oil and Gas Conference and Exhibition in China, Beijing, China, 8–10 June 2010. [Google Scholar]
  90. Song, R.; Xu, D.; Zuo, X.; Ma, Z.; Qing, H.; Liu, Y. A case study of ASP multi-well groups. In Proceedings of the SPE EOR Conference at Oil & Gas West Asia, Muscat, Oman, 11–13 April 2010. [Google Scholar]
  91. Li, Y.; Wang, F.; Wu, J.; Yang, Z.; Chen, G.; Zong, L.; Peng, S. Current status and prospects of ASP flooding in Daqing Oil Fields. In Proceedings of the SPE Symposium on Improved Oil Recovery, Tulsa, OK, USA, 20–23 April 2008. [Google Scholar]
  92. Chang, H.L.; Zhang, Z.Q.; Wang, Q.M.; Xu, Z.S.; Guo, Z.D.; Sun, H.Q.; Cao, X.L.; Qiao, Q. Advances in Polymer Flooding and Alkaline/Surfactant/Polymer Processes as Developed and Applied in the People’s Republic of China. J. Pet. Technol. 2006, 58, 84–89. [Google Scholar] [CrossRef]
  93. Pu, H. An update and perspective on field-scale chemical floods in Daqing oilfield, China. In Proceedings of the SPE Middle East Oil and Gas Show and Conference, Exhibition, Bahrain, 15–18 March 2009. [Google Scholar]
  94. Green, D.W.; Willhite, G.P. Enhanced Oil Recovery; Henry, L., Ed.; Doherty Memorial Fund of AIME, Society of Petroleum Engineers: Richardson, TX, USA, 1998; Volume 6. [Google Scholar]
  95. Rezaei, A.; Riazi, M.; Escrochi, M.; Elhaei, R. Integrating surfactant, alkali and nano-fluid flooding for enhanced oil recovery: A mechanistic experimental study of novel chemical combinations. J. Mol. Liquids 2020, 308, 113106. [Google Scholar] [CrossRef]
  96. Rajabi, M.; Moradi, R.; Mehrizadeh, M. Experimental investigation of chemical solutions effects on wettability alteration and interfacial tension reduction using nano-alkaline–surfactant fluid: An EOR application in carbonate reservoirs. J. Pet. Explor. Prod. Technol. 2021, 11, 1925–1941. [Google Scholar] [CrossRef]
  97. Salih, N.M.; Kamal, I.M.; Préat, A. Classical observations and stable isotopes for identification the diagenesis of Jeribe formation at Jambour oil Fields-Kurdistan Region-Iraq. Pet. Sci. Technol. 2019, 37, 1548–1556. [Google Scholar] [CrossRef]
  98. Salih, N.; Mansurbeg, H.; Kolo, K.; Gerdes, A.; Préat, A. In situ U-Pb dating of hydrothermal diagenesis in tectonically controlled fracturing in the Upper Cretaceous Bekhme Formation, Kurdistan Region-Iraq. Int. Geol. Rev. 2020, 62, 2261–2279. [Google Scholar] [CrossRef]
  99. Hendraningrat, L.; Torsæter, O. Metal oxide-based nanoparticles: Revealing their potential to enhance oil recovery in different wettability systems. Appl. Nanosci. 2014, 5, 181–199. [Google Scholar] [CrossRef] [Green Version]
  100. Abhishek, R.; Hamouda, A.A.; Murzin, I. Adsorption of silica nanoparticles and its synergistic effect on fluid/rock interactions during low salinity flooding in sandstones. Colloids Surf. A Physicochem. Eng. Asp. 2018, 555, 397–406. [Google Scholar] [CrossRef]
  101. Li, K.; Wang, D.; Jiang, S. Review on enhanced oil recovery by nanofluids. Oil Gas Sci. Technol. 2018, 73, 37. [Google Scholar] [CrossRef] [Green Version]
  102. Moradi, B.; Pourafshary, P.; Jalali Farahani, F.; Mohammadi, M.; Emadi, M.A. Application of SiO2 Nano Particles to Improve the Performance of Water Alternating Gas EOR Process. In Proceedings of the SPE Oil & Gas India Conference and Exhibition, Mumbai, India, 24–26 November 2015. [Google Scholar] [CrossRef]
  103. Luo, D.; Wang, F.; Zhu, J.; Cao, F.; Liu, Y.; Li, X.; Willson, R.; Yang, Z.; Chu, C.-W.; Ren, Z. Nanofluid of graphene-based amphiphilic Janus nanosheets for tertiary or enhanced oil recovery: High performance at low concentration. Proc. Natl. Acad. Sci. USA 2016, 113, 201608135. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  104. Sun, X.; Zhang, Y.; Chen, G.; Tailin, L.; Ren, D.; Ma, J.; Sheng, Y.; Karwani, S. Wettability of Hybrid Nanofluid-Treated Sandstone/Heavy Oil/Brine Systems: Implications for Enhanced Heavy Oil Recovery Potential. Energy Fuels 2018, 32, 11118–11135. [Google Scholar] [CrossRef]
  105. Roustaei, A.; Moghadasi, J.; Iran, A.; Bagherzadeh, H.; Shahrabadi, A. An Experimental Investigation of Polysilicon Nanoparticles’ Recovery Efficiencies through Changes in Interfacial Tension and Wettability Alteration. In Proceedings of the SPE International Oilfield Nanotechnology Conference and Exhibition, Noordwijk, The Netherlands, 12–14 June 2012. SPE-156976-MS. [Google Scholar]
  106. Dahkaee, K.P.; Sadeghi, M.T.; Fakhroueian, Z.; Esmaeilzadeh, P. Effect of NiO/SiO2 nanofluids on the ultra interfacial tension reduction between heavy oil and aqueous solution and their use for wettability alteration of carbonate rocks. J. Pet. Sci. Eng. 2019, 176, 11–26. [Google Scholar] [CrossRef]
  107. Onyekonwu, M.O.; Ogolo, N. Investigating the Use of Nanoparticles in Enhancing Oil Recovery. In Proceedings of the Nigeria Annual International Conference and Exhibition, Lagos, Nigeria, 6–8 August 2010; Volume 2. [Google Scholar] [CrossRef]
  108. Li, Y.; Zhu, K.; Zydney, A.L. Effect of ionic strength on membrane fouling during ultrafiltration of plasmid DNA. Sep. Purif. Technol. 2017, 176, 287–293. [Google Scholar] [CrossRef]
  109. Bayat, A.; Junin, R.; Samsuri, A.; Piroozian, A.; Hokmabadi, M. Impact of Metal Oxide Nanoparticles on Enhanced Oil Recovery from Limestone Media at Several Temperatures. Energy Fuels 2014, 28, 6255–6266. [Google Scholar] [CrossRef]
  110. Mohammadi, M.; Moghadasi, J.; Naseri, S. An Experimental Investigation of Wettability Alteration in Carbonate Reservoir Using#3-Al2O3 Nanoparticles. Iran. J. Oil Gas Sci. Technol. 2014, 3, 18–26. [Google Scholar]
  111. Naik, S.; You, Z.; Bedrikovetsky, P. Rate enhancement in unconventional gas reservoirs by wettability alteration. J. Nat. Gas Sci. Eng. 2015, 26, 1573–1584. [Google Scholar] [CrossRef]
  112. Ogolo, N.; Olafuyi, O.A.; Onyekonwu, M.O. Enhanced Oil Recovery Using Nanoparticles. In Proceedings of the SPE Saudi Arabia Section Technical Symposium and Exhibition, Al-Khobar, Saudi Arabia, 8–11 April 2012. [Google Scholar] [CrossRef] [Green Version]
  113. Azarshin, S.; Moghadasi, J.; Arab Aboosadi, Z. Surface functionalization of silica nanoparticles to improve the performance of water flooding in oil wet reservoirs. Energy Explor. Exploit. 2017, 35, 014459871771628. [Google Scholar] [CrossRef] [Green Version]
  114. Nazari Moghaddam, R.; Bahramian, A.; Fakhroueian, Z.; Arya, S. A Comparative Study of Using Nanoparticles for Enhanced Oil Recovery: Wettability Alteration of Carbonate Rocks. Energy Fuels 2015, 29, 150223100050005. [Google Scholar] [CrossRef]
  115. Roustaei, A.; Saffarzadeh, S.; Mohammadi, M. An evaluation of modified silica nanoparticles’ efficiency in enhancing oil recovery of light and intermediate oil reservoirs. Egypt. J. Pet. 2013, 22, 427–433. [Google Scholar] [CrossRef] [Green Version]
  116. El-Diasty, A.I.; Aly, A.M. Understanding the Mechanism of Nanoparticles Applications in Enhanced Oil Recovery. In Proceedings of the SPE North Africa Technical Conference and Exhibition, Cairo, Egypt, 14–16 September 2015. D021S009R004. [Google Scholar]
  117. Ju, B.; Fan, T. Experimental study and mathematical model of nanoparticle transport in porous media. Powder Technol. 2009, 192, 195–202. [Google Scholar] [CrossRef]
  118. Kazemzadeh, Y.; Sharifi, M.; Riazi, M.; Rezvani, H.; Tabaei, M. Potential effects of metal oxide/SiO2 nanocomposites in EOR processes at different pressures. Colloids Surf. A Physicochem. Eng. Asp. 2018, 559, 372–384. [Google Scholar] [CrossRef]
  119. Hendraningrat, L.; Engeset, B.; Suwarno, S.; Torsæter, O. Improved Oil Recovery by Nanofluids Flooding: An Experimental Study. In Proceedings of the SPE Kuwait International Petroleum Conference and Exhibition, Kuwait City, Kuwait, 10–12 December 2012. SPE-163335-MS. [Google Scholar]
  120. Ehtesabi, H.; Ahadian, M.; Taghikhani, V. Enhanced Heavy Oil Recovery Using TiO 2 Nanoparticles: Investigation of Deposition during Transport in Core Plug. Energy Fuels 2015, 29, 1–8. [Google Scholar] [CrossRef]
  121. Zhang, H.; Nikolov, A.; Wasan, D. Enhanced Oil Recovery (EOR) Using Nanoparticle Dispersions: Underlying Mechanism and Imbibition Experiments. Energy Fuels 2014, 28, 3002–3009. [Google Scholar] [CrossRef]
  122. Ehtesabi, H.; Ahadian, M.M.; Taghikhani, V.; Ghazanfari, M.H. Enhanced Heavy Oil Recovery in Sandstone Cores Using TiO2 Nanofluids. Energy Fuels 2014, 28, 423–430. [Google Scholar] [CrossRef]
  123. Maghzi, A.; Mohammadi, S.; Ghazanfari, M.H.; Kharrat, R.; Masihi, M. Monitoring wettability alteration by silica nanoparticles during water flooding to heavy oils in five-spot systems: A pore-level investigation. Exp. Therm. Fluid Sci. 2012, 40, 168–176. [Google Scholar] [CrossRef]
  124. Hu, Z.; Azmi, S.M.; Raza, G.; Glover, P.W.J.; Wen, D. Nanoparticle-Assisted Water-Flooding in Berea Sandstones. Energy Fuels 2016, 30, 2791–2804. [Google Scholar] [CrossRef]
  125. Nwidee, L.; Al-Anssari, S.; Barifcani, A.; Sarmadivaleh, M.; Lebedev, M.; Iglauer, S. Nanoparticles Influence on Wetting Behaviour of Fractured Limestone Formation. J. Pet. Sci. Eng. 2016, 149, 782–788. [Google Scholar] [CrossRef] [Green Version]
  126. Joonaki, E.; Ghanaatian, S. The Application of Nanofluids for Enhanced Oil Recovery: Effects on Interfacial Tension and Coreflooding Process. Pet. Sci. Technol. 2014, 32, 2599–2607. [Google Scholar] [CrossRef]
  127. Jiang, R.; Li, K.; Horne, R. A Mechanism Study of Wettability and Interfacial Tension for EOR Using Silica Nanoparticles. In Proceedings of the SPE Annual Technical Conference and Exhibition, San Antonio, CA, USA, 9–11 October 2017. D031S046R003. [Google Scholar]
  128. Mohd, S.; Moslan, M.; Rosli, W.; Wan Sulaiman, W.R.; Ismail, A.; Jaafar, M.Z. Applications of Aluminium Oxide and Zirconium Oxide Nanoparticles in Altering Dolomite Rock Wettability using Different Dispersing Medium. Chem. Eng. Trans. 2017, 56, 1339–1344. [Google Scholar] [CrossRef]
  129. Cheraghian, G.; Sajad, K.; Nassar, N.; Alexander, S.; Barron, A. Silica Nanoparticle Enhancement in the Efficiency of Surfactant Flooding of Heavy Oil in a Glass Micromodel. Ind. Eng. Chem. Res. 2017, 56, 8528–8534. [Google Scholar] [CrossRef] [Green Version]
  130. Karimi, A.; Fakhroueian, Z.; Bahramian, A.; Pour Khiabani, N.; Darabad, J.B.; Azin, R.; Arya, S. Wettability Alteration in Carbonates using Zirconium Oxide Nanofluids: EOR Implications. Energy Fuels 2012, 26, 1028–1036. [Google Scholar] [CrossRef]
  131. Khademolhosseini, R.; Jafari, A.; Mousavi, S.M.; Manteghian, M. Investigation of synergistic effects between silica nanoparticles, biosurfactant and salinity in simultaneous flooding for enhanced oil recovery. RSC Adv. 2019, 9, 20281–20294. [Google Scholar] [CrossRef] [Green Version]
  132. Nwidee, L.N.; Al-Anssari, S.; Barifcani, A.; Sarmadivaleh, M.; Iglauer, S. Nanofluids for Enhanced Oil Recovery Processes: Wettability Alteration Using Zirconium Oxide. In Proceedings of the Offshore Technology Conference Asia, Kuala Lumpur, Malaysia, 22–25 March 2016. D011S002R003. [Google Scholar]
  133. Haeri, F.; Rao, D.N. Precise Wettability Characterization of Carbonate Rocks To Evaluate Oil Recovery Using Surfactant-Based Nanofluids. Energy Fuels 2019, 33, 8289–8301. [Google Scholar] [CrossRef]
  134. Giraldo, J.; Benjumea, P.; Lopera, S.; Cortés, F.B.; Ruiz, M.A. Wettability Alteration of Sandstone Cores by Alumina-Based Nanofluids. Energy Fuels 2013, 27, 3659–3665. [Google Scholar] [CrossRef]
  135. Esmaeilzadeh, P.; Hosseinpour, N.; Bahramian, A.; Fakhroueian, Z.; Arya, S. Effect of ZrO2 nanoparticles on the interfacial behavior of surfactant solutions at air–water and n-heptane–water interfaces. Fluid Phase Equilibria 2014, 361, 289–295. [Google Scholar] [CrossRef]
  136. Suleimanov, B.; Ismayilov, F.; Veliyev, E. Nanofluid for enhanced oil recovery. J. Pet. Sci. Eng. 2011, 78, 431–437. [Google Scholar] [CrossRef]
  137. Rezk, M.Y.; Allam, N.K. Unveiling the Synergistic Effect of ZnO Nanoparticles and Surfactant Colloids for Enhanced Oil Recovery. Colloid Interface Sci. Commun. 2019, 29, 33–39. [Google Scholar] [CrossRef]
  138. Zhou, Y.; Wu, X.; Zhong, X.; Sun, W.; Pu, H.; Zhao, J.X. Surfactant-Augmented Functional Silica Nanoparticle Based Nanofluid for Enhanced Oil Recovery at High Temperature and Salinity. ACS Appl. Mater. Interfaces 2019, 11, 45763–45775. [Google Scholar] [CrossRef] [PubMed]
  139. Choi, S.; Son, H.; Kim, H.; Kim, J.W. Nanofluid Enhanced Oil Recovery Using Hydrophobically Associative Zwitterionic Polymer-Coated Silica Nanoparticles. Energy Fuels 2017, 31, 7777–7782. [Google Scholar] [CrossRef]
  140. Qi, L.; Song, C.; Wang, T.; Li, Q.; Hirasaki, G.J.; Verduzco, R. Polymer-Coated Nanoparticles for Reversible Emulsification and Recovery of Heavy Oil. Langmuir 2018, 34, 6522–6528. [Google Scholar] [CrossRef]
  141. Cheraghian, G. Effect of Nanoclay on Heavy Oil Recovery During Polymer Flooding. Pet. Sci. Technol. 2015, 33, 999. [Google Scholar] [CrossRef]
  142. Sharma, T.; Sangwai, J.S. Silica nanofluids in polyacrylamide with and without surfactant: Viscosity, surface tension, and interfacial tension with liquid paraffin. J. Pet. Sci. Eng. 2017, 152, 575–585. [Google Scholar] [CrossRef]
  143. Saha, R.; Uppaluri, R.V.S.; Tiwari, P. Silica Nanoparticle Assisted Polymer Flooding of Heavy Crude Oil: Emulsification, Rheology, and Wettability Alteration Characteristics. Ind. Eng. Chem. Res. 2018, 57, 6364–6376. [Google Scholar] [CrossRef]
  144. Hendraningrat, L.; Li, S.; Torsæter, O. A coreflood investigation of nanofluid enhanced oil recovery. J. Pet. Sci. Eng. 2013, 11, 128–138. [Google Scholar] [CrossRef]
Figure 1. Future micromodel set up using NASP.
Figure 1. Future micromodel set up using NASP.
Nanomaterials 12 04007 g001
Figure 2. Summary of experimental data for different kinds of natural surfactant.
Figure 2. Summary of experimental data for different kinds of natural surfactant.
Nanomaterials 12 04007 g002
Figure 3. ASP chemical flooding sequence for enhancing oil recovery. ASP EOR injection is shown in sequence at the beginning, the preflush is injected then followed by oil bank; after that, nano-alkaline-surfactant is injected to decrease the IFT followed by a polymer to control the mobility via increasing the viscosity; finally, water drive is used to push the solutions.
Figure 3. ASP chemical flooding sequence for enhancing oil recovery. ASP EOR injection is shown in sequence at the beginning, the preflush is injected then followed by oil bank; after that, nano-alkaline-surfactant is injected to decrease the IFT followed by a polymer to control the mobility via increasing the viscosity; finally, water drive is used to push the solutions.
Nanomaterials 12 04007 g003
Figure 4. NASP interaction improved mechanisms.
Figure 4. NASP interaction improved mechanisms.
Nanomaterials 12 04007 g004
Figure 5. IFT and contact angle measurement by using pendant drop (oil drop).
Figure 5. IFT and contact angle measurement by using pendant drop (oil drop).
Nanomaterials 12 04007 g005
Figure 6. Core–flood procedure.
Figure 6. Core–flood procedure.
Nanomaterials 12 04007 g006
Figure 7. IFT reduction and wettability alteration by nanoparticles.
Figure 7. IFT reduction and wettability alteration by nanoparticles.
Nanomaterials 12 04007 g007
Table 1. Summary of previous experimental and field ASP works alone and in synergy.
Table 1. Summary of previous experimental and field ASP works alone and in synergy.
CEOR
Type
Ref.Chemical NameConc.Porosity
%
Permeability
(md)
Lithology
Alkaline[12]Na2CO31.0NA.405–608Sandstone
NaOH1.0
Na4Si040.5
[13]Na2CO30.852570Sandstone
[2]NaOH0.5NA.1580Sandstone
[14]NaOH0.533.596000Sandstone
[15]NaOH0.2NANACarbonate
[2]Na2CO3NA35.53200Sandstone
[16]NaOH0.538.7NASandstone
[17]NaOH0.2NANASandstone
[18]NaOHNA15119Sandstone
[19]NaOH4.8520.625Sandstone
[20]NaOH0.1516NASandstone
[21]NaOH0.230495–320Sandstone
[22]NaOH0.5NA2110Sandstone
[23]NaOH1.0NANAsandstone
[24]NaOH2.019.793.64Sandstone
Sandstone
Na2CO32.019.6176.25
[25]Na2C031.20353850Sandstone
Surfactant[26]Cationic C12TABNA45–502–5Carbonate
[27]SDS100052.2250Carbonate
[25]OPIO and CY1NA353850Sandstone
[28]Anionic surfactantNA29.0619.72Carbonate
[29]Nonionic surfactantsNANA20.89Carbonate
[30]Anionic surfactantNA3–5NACarbonate
[31]nonionic ethoxy alcohol3000–40003–5NACarbonate
[32]Anionic (GAC) surfactantsNANANACarbonate
[33]Nonionic (POA)75015.456Carbonate
[34]Nonionic ethoxy alcohol50–3500NANACarbonate
[16]SDS100038.6212Sandstone
[35]SDBS25037284Sandstone
[36]SLPS100038NASandstone
[37]SDS 3000NANAGlass bed
[38]XD1000NANASandstone
[39]SDBS200025NASandstone
[13]SDSNA23–2950–94Sandstone
Polymer[12]PAM3200NA405 to 608Sandstone
Xanthan gum1540NA405 to 608Sandstone
[36](HPAM)100037.53780Sandstone
[40](Gum Arabic/Poly acridNANANASandstone
[41]HPAM110021.6420Sandstone
[42]TVP2000NANASandstone
[43]HPAM1800NANASandstone
[44]PAM500>39100–60Sandstone
[16]PHPAM150037.3218Sandstone
[45]HPAM120015.223.34Sandstone
Alkaline Surfactant[46]Xylene + NaOH5000 + 10,000NANACarbonate
[47]IOS + Na2CO3(200–10,000) + 5000372400Micromodel
[48]Na2CO3 + alkyl ether sulfates1500 + 50NANANA
[38]Na2CO3 + XD10,000 + 1000NANASandstone
Na2CO3 + SDS10,000 + 10,000NANASandstone
[49](IOS) + NaOH + Na4Si04NANANASandstone
[50]NaOH + SLPS3000 + 30044.72131Sandstone
NaOH + SLPS8000 + 100043.501994
NaOH + SLPS10,000 + 100044.212016
[13]SDS + Na2CO31000 + 85002570Sandstone
[51]Na2CO3 + sodium alkane sulfonate(1000–15,000) + 100041–45790–19,220Sandstone
Alkaline polymer[52]Na2CO3 + anionic PAMNA15.521Sandstone
[53]Na2CO3 + Pusher 1000E8000 + 600291400Sandstone
[54]NaOH + Alcoflood 1275A10,000 + 100020200Sandstone
[55]NaOH + HPAM10,000 + 100038.922350Sandstone
Ethylenediamine + HPAM10,000 + 100039.412230
Na2CO3 + HPAM10,000 + 100040.332420
[56]Na2CO3 + anionic PAMNA15.521Carbonate
[57](NaOH + Na2CO3) + HPAM(4000 + 2000) + 25034.434800Sandstone
[57]HPAM + (NaOH + Na2CO3)1000 + (1000 + 2000)35.256400Sandstone
[52]Na2CO3 + Alcoflood 117510,000 + 800291400Sandstone
[58]Na2CO3 + PAM10,000 + 150031840.9Sandstone
[25]Na2C03 + OP-101200 + 10,000353850Sandstone
[59]Na2CO3 + HPAM20,000 + 100027.62063Carbonate
Surfactant polymer[60]alkyl ether sulfates + Witco petroleum sulfonate1000 + 1000125.9Carbonate
[61]Amphoteric + PAM2500 + 140029.13442Sandstone
[62]PAM + SDS1000 + 22002166Sandstone
[16]SDS + PHPAM1000 + 200036.81224Sandstone
[63]bio-surfactant and biopolymer1001 + 500017400Sandstone
[61]PS + PAM2000 + 200021115Sandstone
[39]SDBS + HPAM2000 + 200025NASandstone
[64]PAM + SDS2800 + 1000NANAGlass micromodel
PAM + SDS2800 + 2000
PAM + SDS2800 + 3000
[61](Amphoteric +anionic) + PAM1200 + 150015110Sandstone
[36]HPAM + SDS1000 + 1000381410Sandstone
[45]anionic surfactant + HPAM1200 + 120015.223.34Sandstone
[43]SLPS + HPAM4000 + 1800NA1500Sandstone
[65]KPS + HPAM3000 + 11514.75.08Sandstone
[43]SLPS + (HPAM)4000 + 1800NA1500Sandstone
Alkaline surfactant polymer (ASP)[60]NaOH + SDS + PHPAM5000 + 1000 + 2500NANASandstone
NaOH + SDS + PHPAM5000 + 2000 + 2500
NaOH + SDS + PHPAM5000 + 3000 + 2500
[66]Amphoteric Petrostep B-100 + Pusher 700E + Na2CO34000 + 1200 + 20,0008–431–600Carbonate
[67]Na2CO3 + SDS+ PAM10,000 + 1000 + 800NANASandstone
[16]NaOH + SDS + PHPAM5000 + 1000 + 150038.7NASandstone
NaOH + SDS + PHPAM7000 + 1000 + 1500
NaOH + SDS + PHPAM10,000 + 1000 + 1500
[16]NaOH + SDS + PHPAM5000 + 1000 + 150038.7NASandstone
NaOH + SDS + PHPAM5000 + 1000 + 2000
NaOH + SDS + PHPAM5000 + 1000 + 2500
[68]Na2CO3 + Petrostep B-100 + Alcoflood1175A12500 + 1000 + 147518845Carbonate
[69]Diethylene glycol butyl ether + alcoflood-2545 + NaBO23000 + 10,000 + 10,00017.7239Sandstone
[70]HAPAM + NaOH + heavy alkylbenzene sulfonate1000 + 1200 + 3000NA252Sandstone
[71]Na2CO3 + (anionic BES and lignosulfonate PS) + PAM12,000 + 3000 + 1700NANASandstone
CEOR
Type
Ref.Work TypeOil Improvement %Remark
Alkaline[12]Experimental17.2Na2CO3 is more effective for oil increment
9.42
8.91
[13]Experimental4.4Due to soap formation, Interfacial tension between oleic and aqueous phase reduced
[2]Experimental12.4Low salinity leads to O/W emulsions if the salinity is above 0.7 W/O emulsions happen
[14]Experimental13.33IFT reduction due to soap formation improves oil recovery
[15]ExperimentalNAAlkaline flooding is more applicable for medium crude oil as compared to light crude oil due to a higher ratio of soap formation in medium crude oil
[2]Experimental14Alkaline is also applicable and can accelerate oil recovery in horizontal wells
[16]Experimental13.88Strong base (NaOH) alkaline injection enhanced oil recovery
[17]ExperimentalNAHigher oil recovery due to in situ. Emulsion formation
[18]Experimental2additional oil guaranteed by changing the wettability
[19]Field6–8the amount of IFT reduction determines the success of alkali job
[20]Field2Changing in rock surface wettability directly affects oil recovery
[21]Field5 to 7Formation of the emulsion by alkaline improves volumetric sweep efficiency
[22]Experimental12.9The oil displacement experiment proved that oil recovery is enhanced by using alkaline injection
[23]Experimental<1Orthosilicate was very successful at stopping water channeling and increasing oil recovery
[24]Experimental2.52
3.67
NaOH is more effective than Na2CO3
[25]Field9.13Ultra-low IFT after alkaline flooding
Surfactant[26]Experimental20changing rock surface wettability due to the sulfate that is present in the injection fluid
[27]Experimental9Oil recovery affected by the type and concentration of the surfactant used in the formation
[25]Field11.64Higher amount of IFT reduction leads to more oil recovery
[28]Experimental30Optimum surfactant concentration is related with brine salinity
[29]FieldNA.About 58,000 bbl of oil is produced after using Nonionic surfactants over only three months
[30]ExperimentalNAThe performance of anionic surfactants was more effective than nonionic surfactants
[31]Experimental15.0to optimize surfactant performance injection rate, conc. and volume are the important parameters
[32]ExperimentalNAIFT significantly diminished
[33]Experimental10.4Nonionic surfactant outperformed cationic surfactant
[34]ExperimentalNAsurfactants decreased IFT and changed the contact angle
[16]Experimental17.96IFT decreased marginally
[35]Experimental2.1Due to surfactant degradation, the oil recovery was low
[36]Experimental4Increase in capillary number yields more oil recovery
[37]ExperimentalNAIFT reduced from 19.59 to 2.82 mN/m
[38]Experimental11.5At lower concentration, a novel XD yielded a good oil recovery that can be compared with SDS
[39]Experimental4.6Compared to SP flooding, oil recovery by using surfactant flooding was reduced
[13]Experimental7.1Adsorption phenomena indicated that SDS was a suitable choice for sandstone formation
Polymer[12]Experimental11
10.5
Polymer type selection is critical
[36]Experimental10.7Increasing the viscosity of water by HPAM improves vertical sweep efficiency
[40]Experimental5.2Core flood test indicates that this type of polymer is less effective than other polymer types due to less oil improvement
[41]Field9.8Higher molecular weight improves thermal stability
[42]Experimental13.5Temperature affects polymer performance
[43]Experimental6.3PPG is more effective in higher and lower permeability zones compared to conventional polymer (HPAM)
13.4
[44]Field7Earlier injection of polymer is more profitable
[16]Experimental16.12High viscosity of polymer leads to an increase in macroscopic displacement
[45]Experimental8.80From the results, it can be indicated that polymer is used mostly to reach to the unrecoverable oil zones
Alkaline surfactant[46]Field10–15Alkaline-surfactant flooding offers a potential scheme to recover part of the high residual oil that was not recovered by waterfront
[47]ExperimentalNAEmulsification of heavy oil by AS was effective
[48]ExperimentalNAFor mobilizing heavy oil, AS flooding is a very suitable choice
[38]Experimental14.58In situ soap by alkali and surfactant reduces IFT significantly
10.42
[49]FieldNAAlkaline is not able to mobilize oil alone, when surfactant added IFT reaches minimum value and oil easily mobilized
[50]Experimental12.10Surfactant and soap (in situ) surfactant formation efficiently reduces IFT
15.80
18.63
[13]Experimental18As shown in adsorption phenomena, alkali plays a major role in reducing surfactant adsorption
[51]Experimental10.5Surfactant reduces the alkaline consumption
Alkaline polymer[52]FieldNAAP synergy effect was efficient for improving EOR mechanisms
[53]Field21.1AP was sufficient to improve oil recovery
[54]Field17Binary system of A and K performance is more significant than using each of the chemicals alone
[55]Experimental21.02In AP flooding, alkaline selection plays a critical role in oil recovery improvement
25.21
18.12
[56]Field26.4Soap formation by Na2CO3 and viscosity improvement by anionic polymer yielded higher recovery
[57]Experimental18.58Conc. of polymer influences oil recovery
27.60
[57]Experimental16.56Conc. of Alkaline influences oil recovery
27.39
[52]Field21.167% OOIP was recovered by AP
[58]Experimental22.8Polymer solution should be injected at a good speed
[25]Field18.12alkali cannot to the oil region without polymer
[59]Experimental1.98Mobility control improved
Surfactant Polymer (SP)[60]Experimental12.0Using two surfactants was more effective
[61]Field16.3Using surfactant with polymer yield extra oil recovery
[62]Experimental17.25Temperature and initial oil saturation affects oil recovery
[16]Experimental20.99Better mobility control is obtained by using polymer with surfactant
[63]Experimental15.94The binary system demonstrated high interfacial activity with IFT min below 0.01 mN/m
[61]Field13.8Synergism of polymer and surfactant further improves oil recovery
[39]Experimental20Oil recovery after using dual chemicals (S and P) was higher than the total oil that is produced by using S and P alone
[64]Experimental41CMC of SDS is 0.21 means that higher concentrations of CMC have a marginally effect on oil recovery
41.4
42
[61]Field14.5Polymer and surfactant synergism developed by choosing the optimum conc. of each
[36]Experimental13.7Without polymer injection surfactant cannot go through unsweep zones
[45]Experimental11.29Anionic surfactant for sandstone reservoir is very effective
[43]Experimental13.6Polymer and surfactant synergistic yields higher oil displacement
[65]Experimental23.96Polymer controls mobility control and surfactant reduces IFT
[43]Experimental22.4SLPS improves displacement efficiency and (HPAM + PPG) improves sweep efficiency
Alkaline surfactant Polymer (ASP)[60]Experimental23.69Increase in surfactant conc. leads to oil recovery enhancement
27.18
28.72
[66]Experimental45An alkaline surfactant polymer formulation was substantially better in recovering oil than surfactant or polymer surfactant
[67]Experimental7.4A, S and P synergism yielded higher oil recovery. Alkaline reduces surfactant adsorption. Surfactant reduces alkaline consumption and polymer increases the viscosity of water. These three functions play a great role in recovery enhancement
[16]Experimental23.69Effect of different alkaline concentration in ASP slug yields different oil recovery, indicating that optimum concentration of alkaline should be guaranteed
24.08
24.91
[16]Experimental23.69Optimum concentration of polymer is required during ASP injection for higher oil recovery
23.5
24.2
[68]Field28.1ASP synergy effect makes the process efficient
[69]Field10–28Pore scale displacement efficiency improved due to synergy of three chemicals
[70]Field>25NaOH and heavy alkylbenzene sulfonate reduces IFT dramatically and polymer pushes the heavy oil
[71]Experimental15.5Present the co-surfactant in the ASP slug is critical in releasing the trapped oil in the porous part of the reservoir rock
Different kind of ASP flooding in different reservoir characteristics, close up percentage of oil improvement. From this table, it is obvious that ASP is one of the promising EOR applications due to its dual efficiency effect, alkaline and surfactant microscopic efficiency, and polymer progresses volumetric sweep. Reservoir fluid and rock property play a vital role for ASP selection, and, for achieving highest oil recovery, suitable ASP type and concentration should be used. For sandstone formation, the convenient surfactant type was used in ASP is SDS. CTAB is mostly used for carbonate due to its surface charge. Lith = Lithology; P. = Porosity; Pb. = Permeability; Sst = Sandstone Carbo. = Carbonate; Qz = Quartz; SDS = sodium dodecyl sulfate; GAC = Guerbet alkoxy carboxylate; POA = polyoxyethylene alcohol; PAM = Polyacrylamide: HPAM = hydrolized polyacrylamide; C12TAB = Dodecyltrimethylammonium (bromide); SDBS = Sodium Dodecylbenzene Sulfonate Surfactant; KPS = Potassium persulfate; XD = xylitoldehydrogenase; TVP = thermo-viscosifying polymer; IOS = internal olefin sulfonate; PS = Pulmonary surfactant; SLPS = surfactant like peptides.
Table 2. Summary of natural surfactant types and their properties.
Table 2. Summary of natural surfactant types and their properties.
Ref.NameCMCTypeIFT
From-to
mN/m
Contact Angle
From-To
Oil Recovery
Improvement %
Properties
[73]Reetha Extract2.3Natural non-ionic18.6 to 7.02NA6.8Applicability of new surfactant and increase oil recovery from 18.5 to 25.3
[74]Mulberry leaves extract2.6Natural cationic44 to 17.962.5° to 42.57Suitable for carbonate rock
[75]Matricaria chamomilla extract0.05Natural Nonionic30.63 to 12.53NANAGood IFT reduction ability
[76]Cordia Myxa plant0.06Natural33 to 16.24NA27Good adsorption
[77]Mahua oilNANA10−2NA20Applicable for sandstone reservoir
[78]Seidlitzia rosmarinus extract0.08Cationic32 to 9NANAThe reduced IFT is not as low for EOR application
[79]Jatropha oil-basedNANonionic0.917NA25Good surface activity
[80]Henna extract0.02Cationic43.9 to 3.0566 to 377Good wetting ability
[81]Olive leaf extract1.95Natural cationic36.5 to 14NANAGood adsorption
[81]Spistan leaf Extract2.1Natural cationic36.5 to 20.15NANAgood associative and interfacial properties
[81]Prosopi leaf Extract2.3Natural cationic36.5 to 15.1NANAGood adsorption
Table 3. NASP oil recovery efficiency prediction and efficiency of ASP alone and in synergy.
Table 3. NASP oil recovery efficiency prediction and efficiency of ASP alone and in synergy.
CEOR TypeOil Recovery %Basic Principle
Nano5–23Improvement in sweep and displacement
Alkaline2–5Improvement in displacement
Polymer2–10Improvement in sweep
Surfactant5–15Improvement in displacement
SP5–20Improvement in sweep and displacement
AP5–18Improvement in sweep and displacement
ASP5–25Improvement in sweep and displacement
Nano-polymer4–20Improvement in sweep and displacement
Nano-surfactant5–20Improvement in sweep and displacement
NSP8–22Improvement in sweep and displacement
NASP>25 (predicted by our study)Improvement in sweep and displacement
Table 4. Role of different nanoparticles in EOR mechanisms.
Table 4. Role of different nanoparticles in EOR mechanisms.
NanoparticleNano-Composites EOR Mechanisms
SnO2, ZrO2, Carbon nanoparticlesCTAB + Al2O3Wettability alteration by disjoining pressure
SiO2NiO + SiO2Change wettability of oil by disjoining pressure
ZnOSDS + ZrO2Decreasing the contact to water wet by disjoining pressure
Al2O3SiO2 + PAMWettability alteration by disjoining pressure
Fe, SiO2, GO, TiO2ZrO2, NiOReduce interfacial tension
Al2O3, CuO, Fe2O3SDS + Al2O3Reduce the viscosity of crude
MgOCuO/TiO2 + PAMOptimized permeability
Table 5. Summary of nano, nano-surfactant, nano-polymer and nano-SP flooding. It is concluded that a combination of nanoparticle and nanocomposites with conventional CEOR methods improves the synergism effect. As shown in the summary table, nanoparticles are used to support alkaline and surfactant in IFT reduction and wettability modifications (microscopic improvement). In addition, it is used to lower surfactant costs through controlling surfactant adsorption on the rock surface. In the case of polymers, nanoparticles improve the mobility of the polymeric solution, resulting in better oil sweep efficiency and reducing breakthrough time (macroscopic improvement). Lith = Lithology; Sst = Sandstone; Carbo. = Carbonate; Qz = Quartz.
Table 5. Summary of nano, nano-surfactant, nano-polymer and nano-SP flooding. It is concluded that a combination of nanoparticle and nanocomposites with conventional CEOR methods improves the synergism effect. As shown in the summary table, nanoparticles are used to support alkaline and surfactant in IFT reduction and wettability modifications (microscopic improvement). In addition, it is used to lower surfactant costs through controlling surfactant adsorption on the rock surface. In the case of polymers, nanoparticles improve the mobility of the polymeric solution, resulting in better oil sweep efficiency and reducing breakthrough time (macroscopic improvement). Lith = Lithology; Sst = Sandstone; Carbo. = Carbonate; Qz = Quartz.
Ref.Nano TypeLith.Contact AngleIFTOil Improvement %Remark
BeforeAfterBeforeAfter
[98]SiO2Qz13138.8219.217.52Different nanoparticles’ type and size have different performances
TiO213121.6419.2NA11
Al2O313128.619.212.88
[99]SiO2Sst5130.52120.310.1Due to NP adsorption, the wettability altered from oil to water wet
[100]SiO2SstNA.NANA.NA.4.29Wedge film creation by nanoparticles
[101]SiO2Sst1221613.6210.6923.5Increase in capillary number due to SIO2
[102]graphene nanosheetsSstNA.NA.NA.NA.6.7–15.2Size of nanoparticle plays a great role in EOR
[103]SiO2/TiO2Sst15423NA.NA.NA.Spherical shape of nanoparticle improves uniformity
Al2O3/TiO215424
[104]HLPSst135.59526.31.7532.2NPS yields higher oil recovery without creating any damage to the formation
NWP135.58226.32.5528.57
[105]NiO/SiO2 NCsCarb.17432281.84NANiO/SiO2 Nanocomposite responsible for altering the wettability in carbonate rock reservoir
[106]LHPNSst35<10NA.NA.1.92Capillary number improvement leads to oil enhancement
NWPN35029.23
HLPN35NA.29.01
[107]SiO2Sst124017.5728Sweep efficiency improved by IFT reduction
[108]TiO2Carb.55.361.917.512.56.6Temperature affects oil recovery
SiO254.857.716.711.12.9
[109]γ-Al2O3Carb.119.840NA.NA.11.25γ-Al2O3 plays the main role in altering the wettability from oil to water wet
[110]Al2O3Sst53.6828.6NA.NA.NA.As a result of nanoparticle deposition, rock surface altered to water wet
TiO253.6821.6
SiO253.6838.8
[111]Al2O3SstNA.NA.NA.NA.12.5For guaranteeing optimum oil recovery design, engineers should select the effective nanoparticle type and size
MgO1.7
Ni2O32
ZnO3.3
Fe2O39.2
[112]SiO2Micrm.134.454.5237.522.110Amine-functionalized silica nanoparticles are more effective than typical nanoparticles
134.423.7137.51328
[113]SiO2Carb.140.268.5NA.NA.7.7Disjoining pressure of SiO2 was the main mechanism to remove the oil from the surface
[114]SiO2Sst135.56626.51.9525.43SiO2 is more effective for light oil reservoir
13010128.37.314.55
[115]SiO2SstNA.NA.NA.NA.5–35Arrangement of silicon nanoparticle improves IFT
[116]LHPNSst872828721Wettability is altered when polysilicon is adsorbed on the sandstone pore wall
[117]TiO2/SiO2 NCsCarb.138483913.226Trapped oil is mobilized by the nanocomposite
[118]LHPSstNA.NA.14.79.32Nanofluid was more effective for secondary recovery
[119]TiO2SstNA.NA.231814Low concentration of TiO2 improved the oil recovery
[117]Fe2O3/SiO2 NCSst138523917.531Nanocomposite was able to alter wettability of the rock surface dramatically
[120]SiO2Sst741.2161.433SiO2 can desorb the oil from the rock
[121]TiO2Sst12590NA.NA.31Higher disjoining pressure as a result of using higher concentration
[122]SiO2Micrm.1000NA.NA.8.7 (0.1 wt%)Contact angle and IFT are dependent on the weight % of nanoparticle
26 (0.3 wt%)
[123]TiO2Sst18847.544.59.5–13.3Decrease in capillary force
[124]ZrO2 and NiOCarb.15244NA.NA.NA.Additional IFT reduction after using nanoparticle
[125]Al2O3Sst1319238.52.2520.2Dispersant agent (propanol) was used for the first time and was effective in IFT reduction
Fe2O3132.510138.52.7517.3
SiO21348238.51.4522.5
[126]SiO2Carb.NA.NA.NA.NA.8.7By using nanoparticles, rheological properties of the displacing phase improved
Nano-Surfactant
[127]SDS + Al2O3Carb.92759.882.75NAAnionic surfactant is less effective than cationic surfactant for carbonate reservoir
SDS + ZrO292849.882.78
[128]NaCl + CAPB + SiO2Carb.156.2°75.1°39.631.1012.2Decrease of IFT from 39.63 to 1.10 mN/m leads to oil improvement
[129]SDS + SiO2Micrm.7311NANA13Extra heavy oil recovery as compared to SDS alone
[130]3.22 ZrO2 + 0.50 g of CTABCarb.18032NANA10Positive outcome is observed by surfactant and nanoparticle synergism
[131]rhamnolipid BS-spherical + silicaCarb.1128NA1.8526.1Spherical shape nanoparticle is more effective than other shape nanoparticle due to uniformity
rhamnolipid BS-sponge + silica12017NA1.9425.1
[132]ZrO2 + SDSCarb.15244NANA8From the tests, it was obvious that ZrO2 is very effective in changing the wettability from oil wet limestone to water wet
[133]SiO2 + ALFOTERRACarb.16714623.27.210Using nano was effective in additional oil recovery in ambient and HPHT conditions
[134]Anionic surfactant + Al2O3Carb.1420NA.NA.NAAt relatively low concentrations, Al2O3 can improve anionic surfactant to alter the oil wet to water wet more effectively
[129]A2O3/SiO2 + SDS, CTABCarb.7311NANA15Small size and high surface area of nanoparticles were very effective
[127]CTAB + Al2O3Carb.70528.461.65NASmaller particle size of Al2O3 leads to higher surface energy, resulting in bigger repulsion force
CTAB + ZrO270608.461.85
[135]SDS + ZrO2Carb.NANA4810NAAt and below CMS nanoparticles have a great role in IFT reduction
[136]non-ferrous metal + anionic surfactantSst231931.49.212–17Nanoparticles decrease surfactant adsorption
[27]ZrO2 + SDSCarb.10130163.125Cationic surfactant was more effective at altering the wettability
ZrO2 + CTAB1011618.45.432.5
[64]Cationic anionic + silicaNA5946454345Nanoparticle size 5–75 was effective at reducing the IFT
[137]SDS + ZnOSstNANA32.57.119Sodium dodecyl sulphate gives better stability of ZnO
[35]ZnO + SDBSSst44.4542.4710.8610.28.5–10.2Decreasing in NP size leads to contact angle reduction
[138]SiO2 + Soloterra964Sst43.4103.213.780.7817.23Nanosurfactant was a suitable EOR agent
[127]TX-100 + Al2O3Carb.85629.132.55NA.For carbonate, nonionic surfactant is more effective in altering the wettability as compared to ionic surfactant
TX-100 + ZrO285719.132.64NA.
Nano-Polymer
[139]SiO2 + 2-Poly(MPC)SstNA.NA.47355.2Using copolymer with nano silica yielded higher oil recovery
[140]Silica + DMAEMASst8562.227149.9Nanoparticles reduce polymer adsorption
[141]Nanoclay + HPAMSstNA.NA.NA.NA.5Improvement in viscosity after using Nanoclay/HPAM
[142]SiO2 + PAMSstNA.NA.2710.224.7Due to disjoining pressure, oil wet is changed to water wet
[143]SiO2 + Xanthan gumSst862017.86.47.81More oil is produced from unswept areas leading to improving residual oil recovery
[144]SiO2 + PVPSst542219.27.90–6.1Oil recovery increases with increasing the concentration of nanoparticles due to improved adsorption ratio
[98]Al2O3 + PVPSst5421NA.NA.7–24IFT and contact angle improved synergistically, in a nanocomposite form as compared to individual nanoparticle
Nano-SP
[62]SiO2+ PAM + SDSSstNA.NA.NA.0.1317.49Pressure drop increased to 0.38 MPa
[62]Clay + PAM + SDSSstNA.NA.NA.0.23818.28Higher viscosity as compared to conventional SP
[64]Nanoclay + 2800 PAM + 0.2 SDSMicrm.NA.NA.NA.NA.6.8The injection of nano to SP leads to a more uniform flow pattern in a micromodel, which yields a more stable front
Nanoclay + 3000 PAM + 0.2 SDS8
LHPN = lipophobic and hydrophilic polysilicon nanoparticle; HLPN = hydrophobic and lipophilic polysilicon nanoparticle; NWPN = neutral wet polysilicon nanoparticle; TX-100 = Triton X-100; PVP = Povidone: Polyvinylpyrrolidone; DMAEMA = Dimethylamino-ethyl methacrylate; CTAB = Cetyl trimethylammonium bromide; CAPB = Cocamidopropyl betaine. MPC = methacryloyloxyethyl phosphorylcholine.
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Sarbast, R.; Salih, N.; Préat, A. A Critical Overview of ASP and Future Perspectives of NASP in EOR of Hydrocarbon Reservoirs: Potential Application, Prospects, Challenges and Governing Mechanisms. Nanomaterials 2022, 12, 4007. https://doi.org/10.3390/nano12224007

AMA Style

Sarbast R, Salih N, Préat A. A Critical Overview of ASP and Future Perspectives of NASP in EOR of Hydrocarbon Reservoirs: Potential Application, Prospects, Challenges and Governing Mechanisms. Nanomaterials. 2022; 12(22):4007. https://doi.org/10.3390/nano12224007

Chicago/Turabian Style

Sarbast, Rasan, Namam Salih, and Alain Préat. 2022. "A Critical Overview of ASP and Future Perspectives of NASP in EOR of Hydrocarbon Reservoirs: Potential Application, Prospects, Challenges and Governing Mechanisms" Nanomaterials 12, no. 22: 4007. https://doi.org/10.3390/nano12224007

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop