Abstract
Spontaneous water imbibition into matrix blocks can be a significant oil recovery mechanism in fractured reservoirs. Many enhanced oil recovery methods, such as injection of modified salinity brine, are proposed for improving spontaneous imbibition efficacy. Many scaling equations are developed in the literature to predict spontaneous imbibition oil recovery. However, almost none of them included the impact of the diversity in ionic composition of injected and connate brines and the blending/interaction of a low salinity imbibing brine with a higher salinity connate brine. In this research, these two issues are included to propose new scaling equations for the scaling of spontaneous imbibition oil recovery by modified salinity imbibing brines. This study uses experimental data of the spontaneous imbibition of modified salinity brines into oil-saturated rock samples with different lithologies containing an irreducible high salinity connate brine. The collected tests from the literature were performed at high temperatures and on aged altered wettability cores. The results of 110 available spontaneous imbibition laboratory experiments (85, 12 and 13 tests on chalks, dolomites and sandstones, respectively) are gathered. This research initially shows the poor ability of three selected convenient scaling equations from the literature to scale imbibition recovery by modified salinity brine. Then, our newly proposed technique to find the scaling equation for spontaneous imbibition recovery by modified salinity brine, during the abovementioned conditions in limestones (Bassir et al. in J Pet Explor Prod Technol 13(1): 79–99, 2023. https://doi.org/10.1007/s13202-022-01537-7) is used in chalks, dolomites and sandstones to develop the three new scaling equations. Finally, a new general equation to scale imbibition recovery by modified salinity brine for all four lithologies is presented. Moreover, for each of the four datasets (chalk, dolomite, sandstone and all the four lithologies), the scaled data by the new equations is matched by two mathematical expressions based on the Aronofsky et al. model and the Fries and Dreyer model. These mathematical expressions can be used to develop transfer functions in reservoir simulators for a more accurate prediction of oil recovery by spontaneous imbibition of modified salinity brine in fractured reservoirs.
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Introduction
Conventional reservoirs’ oil recovery varies from field to field, but the global oil recovery factor is at an average range of 30–35% of the initial oil in place (IOIP) (Aadnoy and Looyeh 2019). It has been estimated that about 40% of the world’s known oil reserves are held in naturally fractured reservoirs. A major portion of the oil reserves in Iran is placed in fractured carbonate formations, such as Asmari, Ilam and Sarvak formations. The biggest oil fields in Iran produced from the formations mentioned above are the Ahwaz, Marun, Aghajari, Gachsaran and Karanj fields (Saidi 1987). High-conductive, low-porosity fractures surround the low-permeability matrix blocks in these reservoirs (Gilman and Kazemi 1983; Mehran Pooladi-Darvish and Abbas Firoozabadi 2000a, b).
Spontaneous imbibition is the crucial mechanism for oil recovery from the matrix blocks located in the water-invaded zone of fractured reservoirs (Aronofsky et al. 1958; Behbahani et al. 2006; Kazemi et al. 1992; Pooladi-Darvish and Firoozabadi 2000a, b; Warren and Root 1963). At the early production times in fractured reservoirs, oil is produced from fractures only; but after a while, the matrix system feeds oil into the fracture network. Oil production from the reservoir continues depending on natural reservoir properties and active drives; however, a large amount of oil could remain at the end of primary recovery (Saidi 1987; van Golf-Racht 1982).
Many enhanced oil recovery (EOR) methods are suggested, such as gas injection (e.g., hydrocarbon gases, inert gases and carbon dioxide), thermal injection (e.g., steam, hot water and combustion) and chemical injection (e.g., nanofluids, ionic liquids, alkalines, surfactants and polymers). Most chemical EOR techniques are used for wettability alteration of reservoir rocks (Bassir and Shadizadeh 2020; Mandal 2015; Salih et al. 2016). Carbonate rocks are usually oil–wet; therefore, wettability alteration towards a relatively water-wet state can diminish the capillary barrier (Chandrasekhar and Mohanty 2013; Das et al. 2021; Standnes 2004; Standnes et al. 2002; Strand et al. 2003).
Modified salinity brine injection is an inexpensive technique that has attracted attention in the last decade. In this strategy, a brine with a lower salinity than the connate brine, with/without manipulation of ionic composition, is injected into the reservoir (Zhang et al. 2006). This technique can be applied individually or hybridly by any chemical EOR method. Recent studies have shown that manipulating the chemistry of injected brine leads to a change in the wettability behavior of the reservoir rock (Chandrasekhar and Mohanty 2013; Kazankapov 2014; Roostaei 2014).
Before the field application, the simulation of the spontaneous imbibition of modified salinity brine into the matrix blocks helps to predict the degree of oil recovery improvement by this technique. Proper scaling equations can improve the simulation accuracy of this process in fractured reservoirs (Behbahani et al. 2006). Scaling equations are dimensionless times considering many variables, including rock absolute permeability and porosity, the interfacial tension between imbibing brine and oil, the core sample’s dimensions, the fluids’ viscosities and the boundary conditions. The scaling of spontaneous imbibition recovery data is important in predicting oil recovery from matrix blocks in the water invaded zone of fractured reservoirs (Aronofsky et al. 1958; Kazemi et al. 1992; Ma et al. 1995, 1997; Rapoport 1955; Saidi 1987; van Golf-Racht 1982; Zhang et al. 1996).
Many authors have investigated the effective parameters on spontaneous imbibition efficiency and their configuration in the dimensionless time terms (scaling equations) (Ma et al. 1997; Mason et al. 2010; Mattax and Kyte 1962). Up to now, only Bassir et al. (2023) scaling equation has been suggested (specialized for limestones) to consider the effect of the spontaneous imbibition of a modified salinity imbibing brine into a rock containing higher salinity connate brine. This scaling equation was verified by 59 tests, which were collected from the literature (Bassir et al. 2023).
For this study, 110 spontaneous imbibition experiments by modified salinity brine available in the literature (85, 12 and 13 tests performed on chalk, dolomite and sandstone rock samples, respectively) are collected. At first, three convenient scaling equations are selected and evaluated by the gathered tests to choose the equation with a better scaling quality of data for each lithology. Then, a dimensionless term according to theoretical implications is added to the selected scaling equations to improve them for the scaling imbibition recovery of modified salinity brines. This technique proposes three new scaling equations for chalks, dolomites and sandstones. In the next step, the scaled data by the new scaling equations is matched by two mathematical expressions similar to the Aronofsky et al. model and the Fries and Dreyer model (Aronofsky et al. 1958; Fries and Dreyer 2008). Finally, a universal empirical scaling equation is also presented for all lithology (i.e., limestone (data from our past work (Bassir et al. 2023)), chalk, dolomite and sandstone). Moreover, the two aforementioned mathematical expressions matched this scaled data.
Fractured reservoirs characteristics
A fractured system consists of two particular media responsible for the fluids’ storage and conductance: matrix blocks and fracture networks, respectively (Gilman and Kazemi 1983; van Golf-Racht 1982; Warren and Root 1963). The ultimate oil recovery and spontaneous imbibition rate of each matrix block depend on the properties of each system constituent, such as oil, rock, imbibing and connate brines, in addition to their mutual properties. Moreover, the block’s shape and size and the system’s boundary condition are other influential factors controlling spontaneous imbibition oil recovery (Hatiboglu and Babadagli 2004; Kazemi et al. 1992).
There are two types of spontaneous imbibition: co-current (COCSI) and counter-current (COUCSI). In the COCSI, the flow directions of displaced and displacing phases are similar, whereas, in the COUCSI, they have contrary directions (Mirzaei-Paiaman et al. 2017; Pooladi-Darvish and Firoozabadi 2000a, b). Most laboratory spontaneous imbibition tests are executed on cylindrical cores saturated with oil and in contact with freshwater/brine in one or more outer surfaces. (Anderson 1986; Fischer et al. 2008). For representing the COUCSI and COCSI, four boundary conditions exist which are all faces open (AFO), one end open (OEO), two ends open (TEO), and two ends closed (TEC) (Fischer et al. 2008; Hatiboglu and Babadagli 2006).
Scaling equations
The oil recovery factor is the ratio of the amount of the expelled oil from the porous media (e.g., rock sample) to the IOIP. This quantity can also be expressed concerning the pore volume, but it is usual to define the oil recovery factor in terms of IOIP (in ratio or percent). When the oil production ceases, we have touched the ultimate oil recovery (\(R_{\infty }\)). The scaling purpose of scattered recovery data is to reach a universal curve of recoverable oil versus dimensionless time in a semi-log plot for all rock/fluid conditions. Recoverable oil is described as the volume of produced oil as a fraction of \(R_{\infty }\) (Bassir et al. 2023).
Mattax and Kyte (1962) used Rapoport’s equation (Rapoport 1955) to scale two tests on sandstone cores and four on alundum cores on two separate plots. They offered the following equation (Mattax and Kyte 1962):
where t, k, φ, σ, L and µw are imbibition recovery time, rock absolute permeability, rock porosity, interfacial tension (IFT) between imbibing brine and crude oil, the length of the core and the viscosity of the imbibing brine, respectively (Mattax and Kyte 1962).
Ma et al. (1997) modified Mattax and Kyte’s scaling equation. They found that poor definitions of boundary condition and viscosity are the two causes for the simultaneous scaling failure of Mattax and Kyte’s equation for recovery data in sandstone and alundum cores. The developed scaling equation by Ma et al. is as follows (Ma et al. 1997):
In Eq. (2), core length (L) and viscosity of the imbibing brine (\(\mu_{w}\)) in Mattax and Kyte’s equation are substituted by a characteristic length (\({\text{L}}_{\text{C}}\)) and the geometric mean of viscosities (\(\sqrt {\mu_{w} \mu_{{\text{o}}} } )\) of crude oil (\(\mu_{{\text{o}}}\)) and imbibing brine (\(\mu_{w}\)), respectively. The characteristic length includes the effect of various boundary conditions and is defined by (Ma et al. 1997):
where \({\text{V}}_{\text{b}}\) is the bulk volume of the matrix block, \({\text{A}}_{\text{i}}\) is the i-th surface area that is open to flow and \({\text{l}}_{{\text{A}}_{\text{i}}}\) is the length of the i-th imbibition face to the no-flow boundary. For an AFO boundary condition and a cylindrical core, the characteristic length is:
where D and L are the cylindrical core’s diameter and length (height) (Ma et al. 1997).
Mason et al. (2010) suggested a more general scaling equation to scale spontaneous imbibition tests with a broader range of viscosity ratio (0.008 < \(\frac{{\mu_{{\text{o}}} }}{{\mu_{w} }}\)<173). Their scaling equation is (Mason et al. 2010):
Table 1 summarizes all the effective parameters of crude oil/brine/rock systems of the spontaneous imbibition tests scaled by the three abovementioned scaling equations, the collected tests of our past work (Bassir et al. 2023) and this study.
Other scaling equations in the literature cannot be used in this study, because some of them need relative permeability and capillary pressure data that were not available (Behbahani and Blunt 2005; Li and Horne 2005, 2006; Mirzaei-Paiaman et al. 2017; Schmid and Geiger 2012, 2013; Standnes and Andersen 2017; Zhou et al. 2002) and some others are developed for the COCSI conditions that are not within the scope of this study (Cai et al. 2012, 2010; Mirzaei-Paiaman et al. 2017; Mirzaei‐Paiaman and Masihi 2014). Therefore, the scaling equations of Mattax and Kyte, Ma et al. and Mason et al. are selected as the base equations to improve due to the relative similarity of their tests conditions to the experimental data collected for this study.
Mechanisms of oil recovery improvement by modified salinity imbibing brine
The oil reservoirs usually have a pH level in the acidic range because of the presence of acidic components in the crude oil. In this situation, the charge of the rock surface in carbonate rocks becomes positive; whereas in sandstone rocks, it is negative (Madsen and Ida 1998; Skauge et al. 1999). During a carbonate rock sample aging in the laboratory, organic acids adsorption from the negatively charged head (RCOO−) on the rock surface with a positive charge becomes the critical mechanism of carbonate rocks’ wettability alteration from a water-wet state to a mixed-/oil-wet state (Fathi et al. 2011a; Fathi et al. 2010a, b).
Wettability alteration by multi-ion exchange with electrical double-layer expansion is believed to be the primary mechanism of oil recovery improvement by modified salinity brine (Shirazi et al. 2020). There are two layers around any charged particle: diffused and stern layers filled with a low- and high-density concentration of ions, respectively (Ligthelm et al. 2009). Due to reducing the imbibing brine salinity, the rock surface’s electrical double-layer will be enlarged, and the multi-ion exchange will be boosted. Multivalent ions such as magnesium (\({\text{Mg}}^{2+}\)), calcium (\({\text{Ca}}^{2+}\)) and sulfate (\({\text{SO}}_{4}^{2-}\)) are considered potential determining ions (PDIs) in the research area of modified salinity brine. These ions are the major contributors to the multi-ion exchange, so that \({\text{Mg}}^{2+}\) and \({\text{Ca}}^{2+}\) have operative roles while \({\text{SO}}_{4}^{2-}\) has a catalyst role (Fathi et al. 2010a, b).
\({\text{Mg}}^{2+}\) and \({\text{Ca}}^{2+}\) ions can adsorb carboxylic acids (with a negative charge) and separate them from the rock’s surface; in this situation, a surface with a positive charge can behave as an obstacle. Mixing a low salinity imbibing brine with a high salinity connate brine will enlarge the electrical double-layer and create a proper condition for separating the crude oil acidic components from the rock’s surface. Meanwhile, \({\text{SO}}_{4}^{2-}\) ion can decrease the rock surface’s positive charge and boost the process of wettability alteration by \({\text{Mg}}^{2+}\) and \({\text{Ca}}^{2+}\) ions (Fathi et al. 2010a, b).
Aside from imbibing brine salinity, some research focuses on the impact of connate brine salinity on oil recovery. Mechanisms of the effect of the connate brine on the oil recovery are analogous to that of imbibing brine (i.e., lowering the salinity). Moreover, the PDIs participation in the connate brine has a positive effect on the oil recovery in the modified salinity brine imbibition (Mohammadkhani et al. 2018; Sharma and Filoco 2000; Shehata and Nasr-El-Din 2017).
It is shown that PDIs behave the same in chalk rocks as in limestone rocks, with the difference being that the reactivity in chalks is higher than in limestones (Shariatpanahi et al. 2010). Moreover, investigations have shown that the abovementioned chemical reactions for wettability alteration by modified salinity brine in dolomite rocks are not different from the other carbonates (Shariatpanahi et al. 2016).
Oil recovery improvement mechanisms in sandstones are similar to those of carbonates but have differences. Contrary to carbonates, anionic groups of crude oil’s organic acid (e.g., carboxylate) adsorb on the sandstones’ mineral surfaces with a negative charge via calcium bridges instead of sodium bridges or van der Waals forces. Consequently, decreasing salinity can enhance the electrostatic repulsive forces between carboxylate groups and mineral surfaces and unravel calcium bridges to make the rock surface wettability more water-wet (Yang et al. 2016). Moreover, investigations have demonstrated that reservoir sandstone cores saturated by connate brine comprising divalent cations (Ca2+ and Mg2+) show more oil recovery than the cores saturated by monovalent cations (Na+) (Shehata and Nasr-El-Din 2017).
Some other mechanisms are suggested, such as microdispersion formation and mineral dissolution, but they are not widely accepted as the principal mechanism of improving oil recovery by modified salinity brine imbibition (Mahani et al. 2015; Mahzari et al. 2019). Consequently, the multi-ion exchange is generally believed to be the critical mechanism of the oil recovery enhancement during modified salinity brine imbibition, as is considered in our investigations.
Literature analysis and novelties of this work
From Table 1, the following limitations in the literature scaling equations can be shown. This research tries to resolve these limitations.
-
1.
No scaling equation includes the effect of the imbibition of a modified salinity imbibing brine into a chalk/dolomite/sandstone rock containing higher salinity connate brine. Our recent work proposes a new scaling equation for such conditions only in limestones (Bassir et al. 2023).
-
2.
All literature scaling equations are justified by spontaneous imbibition experiments at room temperature and no initial aging conditions toward an oil-wet state (far from reservoir conditions).
-
3.
Due to the specific properties of each lithology, such as tortuosity, mineral type and grain packing and sorting, scaling equations should be defined separately for each lithology.
-
4.
The properties of the connate brine are not included explicitly in the literature scaling equations. Mixing of imbibing and connate brines may cause memorable interactions that must be checked.
-
5.
Most of the developed scaling equations in the literature are for a water-wet situation and an unchanged wettability during the test. During modified salinity brine injection, it is generally accepted that a wettability alteration to a more water-wet state occurs and is crucial. The duration of all the collected experiments in this study is extended sufficiently until no oil is produced from the core samples. Consequently, the wettability alteration becomes complete as the leading cause of improved recovery.
Data and methods
Data acquisition
In this section, all the 110 literature spontaneous imbibition experimental data that are collected and used in our study are discussed. This research will consider spontaneous imbibition experimental tests with a boundary condition of AFO representing a cylindrical core (matrix block) immersed in the imbibing brine. The data analysis shows that some required parameters are not reported in the corresponding references. The viscosity of crude oil and brine and the IFT between crude oil and imbibing brine are among those nonreported data. Therefore, these parameters are produced. For this purpose, the most accepted correlations in literature defined based on experimental data (Abooali et al. 2019; Glaso 1980; Numbere et al. 1977) with an acceptable error range are used. These correlations (Abooali et al.’s correlation for IFT, Glaso’s correlation for oil viscosity and Numbere et al.’s correlation for brine viscosity) are explained in detail in Appendix A.
To select proper correlations for computing the non-reported properties, operative ranges of the published correlations were compared to the gathered data. The correlations with a good matching to the collected data properties were chosen. This comparison is shown in Table 7 (Appendix A). Some other critical non-reported data, such as crude oil total acid number (TAN) and core dimensions, cannot be estimated. This data is achieved by communication with the papers’ authors. A plot digitizer software digitizes the published oil recovery curves to find the exact oil recovery data values (i.e., time and oil recovery percent (%IOIP)).
For chalks, 85 experimental data from ten references published between 2006 and 2014 are gathered (Fathi et al. 2010a, b; Fathi et al. 2011a, 2011b; Fathi et al. 2010a, b; Kazankapov 2014; Puntervold et al. 2009; Strand et al. 2008; Zhang and Austad 2006; Zhang et al. 2006, 2007). For dolomites, 12 test data from three references published between 2012 and 2020 are collected (Mehraban et al. 2020; Romanuka et al. 2012; Shariatpanahi et al. 2016). For sandstones, 13 experimental data from four references published between 2016 and 2020 are gathered (Al-Saedi et al. 2020, 2019; Shehata and Nasr-El-Din 2017; Yang et al. 2016). In these experiments, a modified salinity brine is imbibed spontaneously into an oil-saturated rock sample containing a higher salinity connate brine.
In Table 2, all the data used to find new scaling equations for chalk, dolomite and sandstone samples are shown, respectively. Iw and Iwi denote imbibing and connate brines ionic strengths, respectively (this data is shown in Sect. "Methods").
Some of the literature experimental data not included explicitly in the new scaling equations are shown in Table 3. This table show the range of the data to which new scaling equations apply. All these parameters are reported directly in the references. Details are shown in Appendix B. It is remarkable that in the articles in which the TAN is not mentioned, the IFT value is noted instead. This data can clarify the range of the applicability of our newly proposed scaling equations. Moreover, the effect of these parameters is applied to the new scaling equations; for example, temperature and °API affect viscosities and the brines salinities are reflected in their viscosities and ionic strengths. The five reported ions (Sodium, Chlorine, Magnesium, Calcium and Sulfate) include the brine's bulk of salts. The concentration of other ions (such as potassium, strontium, barium, bicarbonate, etc.,) is less than 1% of the total salinity of each brine and, therefore, can be neglected because very few studies report the significant effect of these minor ions on the oil recovery improvement process by modified salinity brine in the literature.
In all experiments, the rock samples’ initial wettability can be considered oil-/mixed-wet due to the aging process before the tests start. Because the vital mechanism of the modified salinity brine effect for recovery improvement is believed to be wettability alteration, the wettability of all the rock samples assumed to be changed to a less oil-wet state during the tests (Fathi et al. 2010a, b, 2011a, 2010a; Puntervold et al. 2007, 2009; Shariatpanahi et al. 2016).
All the collected literature experiments are performed at atmospheric pressure; hence, the crude oils are all “dead oil” which is the weak point of the data far from the reservoir conditions with typically live oil. Our investigations show no spontaneous imbibition tests in the literature used modified salinity brine and live oil. This topic must be addressed in the future in this research area, both in experimental and scaling studies.
Methods
In the first stage of this research, Mattax and Kyte’s, Ma et al.’s and Mason et al.’s scaling equations (as shown in Sect. “Scaling equations”) are used to scale the literature experimental data of spontaneous imbibition by modified salinity brine in three lithologies rock samples (i.e., chalk, dolomite and sandstone). This analysis shows the scaling strength of each equation and chooses the equation with the lowest error that can be used as the base equation for developing a new scaling equation for each lithology.
As shown in Tables 8, 9, 10 (Appendix B), each of the collected tests has a specific \(R_{\infty }\) and \({\text{t}}_{\text{end}}\). Hence, the oil recovery at each time step is normalized relative to its \(R_{\infty }\); by this method, the normalized oil recovery of each experiment varies between zero and one. The normalized recovery data are plotted versus a horizontal semi-log plot axis of dimensionless time. For each lithology, all scaled recovery data by the three scaling equations are drawn on similar log cycles for a fair comparison among the scaling quality of different equations. Moreover, the arithmetic mean of the data scatter is used to better compare the scaling accuracy of the scaling equations. The data scatter at specific y-axis values (i.e., 0, 0.1, 0.2, 0.3, 0.4, 0.5, 0.6, 0.7, 0.8, 0.9 and 1) are determined and averaged arithmetically to calculate this mean value.
According to the mechanisms described in Sect. “Mechanisms of oil recovery improvement by modified salinity imbibing brine” and the methodology explained in our recent work (Bassir et al. 2023), both imbibing and connate brines ionic strengths (Iw and Iwi, respectively) are used to develop a new scaling equation for the scaling of spontaneous imbibition by modified salinity imbibing brine in limestone rocks. Here, we repeat the same method for the literature experimental data on chalks, dolomites, and sandstones. After that, the data of all four lithologies is used to develop a general scaling equation that can be applied regardless of lithology.
The ionic strength (I) concept is introduced by Hückel and Debye (1923):
where z and c are each ion’s charge number and molar concentration (mol/L), respectively (Hückel and Debye 1923). Based on Eq. (6), due to the charge number exponent, the impact of the divalent ions (such as Mg2+ and SO42−) is four times that of monovalent ions (such as Na+ and Cl−). The ionic strength has the advantage of independence from the temperature. We applied their ionic strengths to make a dimensionless parameter to add to the base scaling equations for considering the impact of both imbibing and connate brines’ PDIs. The ratio of imbibing to connate brines ionic strengths (\(\frac{{\text{I}}_{\text{w}}}{{\text{I}}_{\text{wi}}}\)) is the simplest dimensionless form that can be assumed. If the imbibing and connate brines have a similar ionic composition, the effect of this ratio will be eliminated (becomes one).
Literature studies (Bassir et al. 2023) show that the oil recovery and \(\frac{{\text{I}}_{\text{w}}}{{\text{I}}_{\text{wi}}}\) term do not have a distinctive direct/inverse relationship. An empirical exponent is allocated to the \(\frac{{\text{I}}_{\text{w}}}{{\text{I}}_{\text{wi}}}\) ratio to finalize this complex issue. Based on this survey, the general form of the new scaling equations is:
where N is the suggested empirical exponent. N can be positive or negative to demonstrate the direct/inverse relationship between the spontaneous imbibition oil recovery of the modified salinity brine and \(\frac{{\text{I}}_{\text{w}}}{{\text{I}}_{\text{wi}}}\) term for each lithology. To find the empirical exponents, a reasonable extensive arbitrary interval for N is tested and the final exponents for each lithology are selected by gradually narrowing the interval. This trial and error method examines negative to positive values. The empirical exponent with the lowest arithmetic mean of the data scatter is selected as the best one for each lithology.
Another point is that for a tall oil-wet block in a fractured reservoir that is immersed in imbibing brine, in addition to the capillary force, gravity force affects the oil recovery. In this study, we focus on the spontaneous imbibition oil recovery due to increased oil-imbibing brine capillary force as a result of wettability alteration to a more water-wet state caused by modified salinity brine and the oil recovery due to gravity force is neglected. The collected literature data in this study agrees with this assumption because the core samples’ heights (as shown in Table 3) are short enough to ignore the effect of gravitational forces.
In general, scaling equations can be used to derive transfer functions that can be included in reservoir simulators. For this purpose, a mathematical expression with minimum matching parameters is needed. This study uses two models to fit the scaled data by our new scaling equations. The first model is similar to Aronofsky et al. model (Aronofsky et al. 1958) that links oil recovery and time with an exponential function as follows:
where λ is the constant of oil production decline applied as the matching parameter (Behbahani and Blunt 2005; Ma et al. 1997).
The second model suggested by Fries and Dreyer (2008) links oil recovery and time by applying Lambert’s W-function (Abouzar Mirzaei-Paiaman 2015; Abouzar Mirzaei-Paiaman et al. 2011; Standnes 2010) as follows:
where ‘a’ is a tuning parameter. Equation (10) can compute Lambert’s W-function for \(- {\text{e}}^{ - 1} \le x \le 0\) with a maximum error of 0.1% (Fries and Dreyer 2008):
where ‘x’ is any value between − e−1 and zero, and e is the Euler’s number (2.71828). Using a trial and error technique and the root of mean square error (RMSE), these two models fitted to the scaled data of each lithology.
The stages of finding the matching parameters are similar to the arithmetic mean of the data scatter, with the difference that achieving the least value for the RMSE is favored here. RMSE can be calculated by:
where \({\text{x}}_{{\text{actual}}_{\text{i}}} \, \text{and }{\text{x}}_{{\text{predicted}}_{\text{i}}}\) are the actual and predicted values by model for each data point, respectively. Two mathematical expressions are developed based on the abovementioned models for each of the four new scaling equations (i.e., chalk, dolomite, sandstone and all lithology).
Results and discussion
Evaluation of the selected literature scaling equations
Figure 1a, b and c illustrate the scaling quality of Mattax and Kyte’s, Ma et al.’s and Mason et al.’s scaling equations, respectively, to scale the literature 85 collected imbibition experimental data in chalk rock samples.
The same analysis is repeated for experimental recovery data for dolomite (12 tests) and sandstone (13 tests) rock samples, shown in Figs. 2 and 3, respectively.
As the recovery data becomes closer to each other, the scaling equation has more accuracy. However, as shown in Figs. 1, 2 and 3, the scaling quality of all the three scaling equations is poor and the scaling equations cannot converge recovery data points on a universal curve.
For each lithology, the arithmetic mean of data scatter is calculated and the scaling equation with the lowest arithmetic mean of data scatter is chosen for the next step of our study. Table 4 shows the process of comparing the scaling ability of various scaling equations for each lithology. Mattax and Kyte’s scaling equation is chosen for chalk and dolomite rocks, and Mason et al.’s scaling equation is selected for sandstone rocks to be used for scaling equations development.
New scaling equations specific for each lithology
Using Eq. (7) and the selected literature scaling equation for each lithology, the final form of the scaling equations for chalks, dolomites and sandstones, respectively, are as follows:
As shown in Fig. 4, for chalks, an exponent of (− 1.5) with an arithmetic mean of data scatter of 1.349 log cycles, 24.7% less than Mattax and Kyte’s scaling Eq. (1.791 log cycles), is achieved. For dolomites, an exponent of (+ 0.80) with an arithmetic mean of data scatter of 0.643 log cycles, 49.4% less than Mattax and Kyte’s scaling Eq. (1.271 log cycles), is attained. An exponent of (+ 1.5) with an arithmetic mean of data scatter of 1.203 log cycles, 33.5% less than Mason et al.’s scaling Eq. (1.809 log cycles)] is achieved for sandstones. Because of the sharp increasing trend of the arithmetic mean of data scatter for the values below and above each gained empirical exponent, the acquired powers seem unique.
Our new scaling equations for chalk, dolomite and sandstone lithologies are presented in Eqs. (15), (16) and (17), respectively.
The negative value of N for chalk’s empirical exponent shows an inverse relationship between the \(\frac{{\text{I}}_{\text{w}}}{{\text{I}}_{\text{wi}}}\) term and spontaneous imbibition oil recovery in chalks, whereas in dolomites and sandstones, this relationship is direct because their empirical exponents are positive values. The different exponent sign of chalk compared to the other lithologies may be due to its unique porosity–permeability relationship. As shown in Table 2, the porosity ranges of chalk, dolomite and sandstone are 0.44–0.50, 0.18–0.20 and 0.17–0.22, respectively, whereas their permeability ranges are 1.5–3.5, 27.7–235 and 1.7–164 mD, respectively. These data show an unusual relationship between porosity and absolute permeability in chalks. Due to the vuggy structure of chalk rocks, their porosity is very high whereas their permeability is unexpectedly very low. This discrepancy might explain the different behavior of chalk compared to the other lithologies. More investigations are needed to clarify this disparity precisely.
The scaled data using the proposed scaling equations for each lithology is shown in Fig. 5.
Matching data
The best fitted models to the scaled tests data for each lithology using corresponding scaling equations (tD) into Eqs. (8) and (9) are as follows:
For chalks and sandstones, the Fries and Dreyer model and for dolomites, the Aronofsky et al. model have a better fit, as shown in Fig. 6. Equations (19), (20) and (23) can be used to develop a transfer function for the simulation of improved oil recovery by modified salinity brine in fractured chalk, dolomite and sandstone reservoirs, respectively (Abouzar Mirzaei-Paiaman et al. 2011; Tavassoli et al. 2005a, b).
Development of a universal scaling equation
All the scaling equations and mathematical models proposed in the recent work (Bassir et al. 2023) and this study are shown in Table 5.
As seen in Table 5, new scaling equations and models for each lithology are not precisely the same (i.e., base literature scaling equation and model and their matching parameters). This variation proves the initial assumption of this research that the literature data must be categorized based on rock lithology. This key point must be considered in the following studies regarding scaling the spontaneous imbibition data. Each lithology has specific features (e.g., tortuosity, grains packing and sorting, etc.,); therefore, the data in every study should be classified based on the rock lithology. Even carbonate categories (i.e., limestones, chalks and dolomites) have different scaling equations and mathematical models. Even though limestones and chalks are mainly composed of calcite, the difference in their grains’ sorting and packing may cause a difference in their behavior and the related scaling equations and mathematical models.
All scaled oil recovery data are plotted on a log scale of 0.00001 to 100,000 for a clear comparison. The scaled recovery curves by Mattax and Kyte, Ma et al., Mason et al., limestone, chalk, dolomite and sandstone’s scaling equations for all 169 tests (110 tests from this study and 59 tests from our past work (Bassir et al. 2023)) are shown in Fig. 7a–g, respectively.
The arithmetic mean of data scatter for Mattax and Kyte’s, Ma et al.’s and Mason et al.’s scaling equations are 3.041, 2.911 and 2.837 log cycles, respectively. Due to the lowest value of the arithmetic mean of data scatter compared to the other scaling equations, we select Mason et al.’s scaling equation as the base equation to find a universal scaling equation for all lithologies. The new general scaling equation form is:
An evaluation of the scaling ability of four scaling equations for each dataset compared to the best case (among three literature scaling equations) is shown in Table 6.
As can be shown from Table 6, limestone’s new scaling equation [that is found based on Mason et al.’s scaling equation (Bassir et al. 2023)] has the highest scaling quality for scaling all the 169 test data compared to the other new scaling equations. This fact aligns with choosing Mason et al.’s scaling equation to improve the scaling dataset of all lithologies. A trial and error survey selects an exponent of (+ 0.39) with the arithmetic mean of data scatter of 2.277 log cycles, 19.7% less than Mason et al.’s scaling Eq. (2.837 log cycles). Our new proposed universal scaling equation for all lithologies is as follows:
The best fitted models to all the 169 scaled tests data by using Eq. (25) in Eqs. (8) and (9) are:
As shown in Fig. 8, the Fries and Dreyer model (2008) has a lower error than the Aronofsky et al. model for fitting spontaneous imbibition oil recovery by modified salinity brine scaled by our universal scaling equation (Eq. (25)). Equation (27) can be used to develop a transfer function to predict oil recovery by the modified salinity brine in fractured reservoirs (Abouzar Mirzaei-Paiaman et al. 2011; Tavassoli et al. 2005a, b).
Recommendations for future research
For interested researchers in this research area, there is a long research road to develop scaling equations applicable to different reservoir conditions, i.e., for various EOR techniques and lithologies at reservoir conditions:
-
1.
Many spontaneous imbibition experiments are published for water-based EOR schemes, such as surfactants (Hou et al. 2015; Santanna et al. 2014; Standnes 2004; Standnes and Austad 2000; Standnes et al. 2002) and hybrid techniques such as modified salinity brine and surfactants (Das et al. 2021; Eslahati et al. 2020; Khaleel et al. 2019; Mohammadi et al. 2019; Shi et al. 2021; Udoh and Vinogradov 2019), modified salinity brine and nanoparticles (Nowrouzi et al. 2019a; Shirazi et al. 2019) and carbonated modified salinity brine (Amarasinghe et al. 2019; Ghandi et al. 2019; Nowrouzi et al. 2019b, 2020a, b; Nowrouzi et al. 2020a, b). Nevertheless, few scaling equations have been developed to scale these numerous tests (Keykhosravi and Simjoo 2020). Eager researchers can collect and organize the data of each EOR technique and develop proper scaling equations for each lithology.
-
2.
For researchers interested in experimental works, it should be emphasized that many spontaneous imbibition tests with boundary conditions other than the AFO for each water-based EOR method are required.
-
3.
Many tests with the AFO boundary condition are needed to scale hybrid EOR techniques such as carbonated modified salinity brine, modified salinity brine and nanoparticles, modified salinity brine and surfactants.
-
4.
Applying live oil in experimental studies of spontaneous imbibition of modified salinity brine must get more attention among researchers. Scaling such data may produces more applicable scaling equations for the reservoir conditions.
-
5.
Considering gravity force to the spontaneous imbibition scaling equations can promote their applicability in reservoir conditions. This improvement requires much more spontaneous imbibition tests on high cores. This point must be attended to in the future by interested researchers in both experimental and scaling studies.
-
6.
The wettability alteration is the principal mechanism of most of the EOR processes. Therefore, it is recommended that the researchers report the initial and final relative permeability and capillary pressure data in their resources. These data can be applicable in the scaling equations development.
The purpose of this road may be to achieve a general scaling equation with a particular term developed for each lithology and EOR strategy.
Conclusions
The following conclusions could be derived from this study:
-
1.
This study presents three new empirical scaling equations to scale literature experimental recovery data of the modified salinity brine spontaneous imbibition into chalk, dolomite and sandstone rock samples. Moreover, a universal scaling equation is proposed that applies to all the lithologies (i.e., limestone, chalk, dolomite and sandstone).
-
2.
The proposed universal scaling equation for all lithology types (169 tests) reduced the arithmetic mean of data scatter of the scaled data by 19.7% less than Mason et al.’s equation (From 2.837 to 2.277 log cycles).
-
3.
For each lithology, a specific scaling equation is proposed. The differences in the configuration and the sign/value of matching parameters of these equations verified our basic assumption of the necessity of the classification of spontaneous imbibition experimental data based on rock lithology in the scaling studies.
-
4.
The suggested scaling equation for chalks (85 tests) reduced the arithmetic mean of data scatter of the scaled data by 24.7% less than Mattax and Kyte’s equation (From 1.791 to 1.349 log cycles).
-
5.
The proposed scaling equation for dolomites (12 tests) declined the arithmetic mean of data scatter of the scaled data by 49.4% less than Mattax and Kyte’s equation (From 1.271 to 0.643 log cycles).
-
6.
The suggested scaling equation for sandstones (13 tests) decreased the arithmetic mean of data scatter of the scaled data by 33.5% less than Mason et al.’s equation (From 1.809 to 1.203 log cycles).
-
7.
Four mathematical expressions (based on the Aronofsky et al. and the Fries and Dreyer models) are developed to fit the scaled imbibition recovery data by new scaling equations. These models can derive proper transfer functions for oil recovery simulation by modified salinity brine imbibition into various rocks.
-
8.
The sign of empirical exponents of ionic strengths ratio (\(\frac{{I}_{w}}{{I}_{wi}}\)) in new scaling equations shows that in dolomites and sandstones, a direct relationship is governed between the ratio of imbibing to connate brines ionic strengths (\(\frac{{I}_{w}}{{I}_{wi}}\)) and the spontaneous imbibition oil recovery of modified salinity brine. Only for chalks, this relationship seems to be inverse; this discrepancy might be related to their specific porosity–permeability relationship.
-
9.
Literature scaling equations (Mattax and Kyte’s, Ma et al.’s and Mason et al.’s) could not scale the collected literature data of spontaneous imbibition of modified salinity brines. These scaling equations are for the scaling of imbibition recovery in water-wet rocks. However, Mattax and Kyte’s scaling equation shows a better scaling ability of oil recovery by modified salinity brine in chalks and dolomites. In contrast, Mason et al.’s equation shows its best scaling performance for sandstones.
-
10.
The mathematical expression based on the Aronofsky et al. model has a better fitting to scaled dolomites recovery data with lower RMSE, whereas the mathematical terms based on the Fries and Dreyer model have a better fitting to scaled chalks and sandstones recovery data with lower RMSE.
Abbreviations
- °API:
-
Degrees API (American Petroleum Institute)
- A :
-
Surface area (cm2)
- a :
-
A matching parameter in Lambert’s W-function
- AFO:
-
All faces open
- c :
-
Molar concentration (mol/L)
- C S :
-
Salt concentration (ppm)
- COCSI:
-
Co-current spontaneous imbibition
- COUCSI:
-
Counter-current spontaneous imbibition
- D :
-
Core diameter (cm)
- e :
-
Euler’s number
- I :
-
Ionic strength (mol/L)
- IFT:
-
Interfacial tension (mN/m)
- IOIP:
-
Initial oil in place (cm3)
- k :
-
Rock permeability (mD)
- L :
-
Core length (cm)
- l A :
-
Distance from the imbibition face to the corresponding no-flow boundary (cm)
- L c :
-
Characteristic length (cm)
- N :
-
The empirical exponent in the new scaling equations
- n :
-
Total number of cases (in Sigma function)
- OEO:
-
One end open
- P :
-
Pressure (psia)
- P s :
-
Saturation pressure (psia)
- PDI:
-
Potential determining ions
- R :
-
Oil production (Fraction of IOIP)
- R ∞ :
-
Ultimate oil recovery (Fraction of IOIP)
- RMSE:
-
Root of mean square error
- T :
-
Temperature (°C)
- t :
-
Time (Days)
- t D :
-
Dimensionless time
- t D-New :
-
New dimensionless time
- t end :
-
Total time of recovery (Days)
- TAN:
-
Total acid number (mgKOH/g-oil)
- tanh:
-
Hyperbolic tangent
- TEC:
-
Two ends closed
- TEO:
-
Two ends open
- V b :
-
Bulk volume (cm3)
- W :
-
Lambert’s W-function
- x :
-
An arbitrary value between − e−1 and zero
- x actual :
-
Actual value of each data point
- x predicted :
-
The predicted value of each data point
- z :
-
Charge number
- γ :
-
Specific gravity
- λ :
-
Oil production decline constant
- µ :
-
Viscosity (cp)
- σ :
-
Interfacial tension (mN/m)
- φ :
-
Rock porosity (Fraction)
- i :
-
i-th case (in Sigma function)
- MFMR:
-
Mason, Fischer, Morrow and Ruth
- MK:
-
Mattax and Kyte
- MMZ:
-
Ma, Morrow and Zhang
- o:
-
Oil
- od:
-
Dead oil
- pw:
-
Pure water
- w :
-
Imbibing brine
- wi :
-
Connate brine
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Appendices
Appendix A: Applied correlations in this research
Abooali et al. (2019) correlation for IFT
where σ, T, P, TAN and CS are in mN/m, Kelvin (K), atmosphere (atm), milligrams of potassium hydroxide (KOH) per gram of crude oil (mgKOH/g) and ppm, respectively. Moreover, \(\gamma_{{\text{o}}}\) is the specific gravity of the crude oil (Abooali et al. 2019).
Glaso (1980) correlation for oil viscosity
where dead oil viscosity (µod) and temperature (T) are in centipoises (cp) and degrees Fahrenheit (℉), respectively (Glaso 1980).
Numbere et al. (1977) correlation for brine viscosity
where pure water viscosity (µpw), brine salt concentration (\({\text{C}}_{\text{S}}\)) and the temperature (T) are in centipoises, weight percent (wt%) and degrees Fahrenheit (℉).
The µpw at any pressure (P) and temperature can be computed by Equation (A-3) (Numbere et al. 1977):
where \({\text{P}}_{\text{s}}\) is saturation pressure in psia.
µpw at Ps and any temperature can be calculated by Equation (A-4) (Numbere et al. 1977):
Ps can be predicted by the equation (A-5) (Numbere et al. 1977):
See Table 7.
Appendix B: Important properties of the literature experiments that are not included explicitly in the scaling equations
See Tables
8,
9,
10,
11,
12,
13.
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Bassir, S.M., Shokrollahzadeh Behbahani, H., Shahbazi, K. et al. Spontaneous imbibition of modified salinity brine into different lithologies: an improvement of comprehensive scaling used for fractured reservoir simulation. J Petrol Explor Prod Technol 14, 1455–1489 (2024). https://doi.org/10.1007/s13202-024-01756-0
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DOI: https://doi.org/10.1007/s13202-024-01756-0