Cation Exchange in Chemical Flooding: Part 1--Basic Theory Without Dispersion

1978 ◽  
Vol 18 (06) ◽  
pp. 418-434 ◽  
Author(s):  
G.A. Pope ◽  
L.W. Lake ◽  
F.G. Helfferich

Abstract The interfacial activity and mobility control of a chemical flooding process are affected by the concentrations of the cationic and anionic species that travel with the surfactant and polymer. In this paper we use equations from the literature to paper we use equations from the literature to describe the environmental composition changes resulting from cation exchange that occurs as a chemical flood traverses a reservoir. This paper presents examples of two or three exchanging cations (calcium, sodium, and magnesium) with and without mobilized oil present and with up to four fluids in a typical chemical flooding sequence (connate water, preflood, slug, and polymer drive). The results indicate how cation polymer drive). The results indicate how cation exchange and adsorption may be incorporated into a chemical flood design. The general theory from which the results are developed is based on the concept of "coherence." This theory allows any number of exchanging cations to be present and allows adsorption of surfactant, polymer, or other species and their interaction with cation exchange to be included. Introduction A key requirement for a successful chemical flood is to provide an adequate ionic environment for the surfactant, to ensure that the desired interfacial activity, phase behavior, and mobility control are maintained. Aside from the inplace and injected ionic compositions and mixing through dispersion, crossflow, etc., this environment may be affected deeply by cation exchange with clays, solubility of minerals, and adsorption on rock. The importance of cation exchange effects in chemical flooding recently has been stressed and need not be reiterated here. We describe a fundamental theoretical analysis of cation exchange and adsorption phenomena in reservoir flooding. The treatment is applicable to multicomponent systems with any kind of equilibrium relations, specifically including interactions between components, but presumes idealized behavior with respect to fluid dynamics, absence of dispersion, immiscibility of aqueous and oleic phases, and conservation of local equilibrium. The treatment is an adaptation of multicomponent chromatographic theory to practical problems of chemical and related floods. The bask problem is that the components involved in a chemical flood--water, cations, surfactant, polymer, and oil--are coupled with respect to their transport properties, and only a theory of coupled, multicomponent systems can adequately describe their dynamic behavior. At first glance, one may be inclined to assume that a mixture injected as a slug might traverse the reservoir as such, changing its composition a little by mixing with fluids ahead and behind or by loss to, or gain from, the rock over which it travels, but otherwise conserving its integrity. Multicomponent theory shows this idea is too naive. Rather, an injection sets off a set of "waves" (composition variations) that advance at different speeds and between which new compositions arise that bear little resemblance to the injected and previously present compositions, or any that could be formed from these by mixing. Moreover, the wave patterns generated by successive injections of different fluids may overlap and interfere and, thereby, modify injected compositions. Injected components thus generate their own environment through dynamic interactions. To be sure, it is not impossible, in principle, to operate under conditions ensuring that an injected active surfactant slug retains its favorable environment and thus its activity through most or all of the reservoir, but this often may prove impracticable. The task then is to design the flood so that a favorable environment is generated in-situ. This paper tries to present a theoretical basis that will paper tries to present a theoretical basis that will facilitate such design. SPEJ P. 418

1978 ◽  
Vol 18 (06) ◽  
pp. 435-444 ◽  
Author(s):  
L.W. Lake ◽  
F. Helfferich

Abstract In this paper, we extend some of the results of Part 1 by discussing aspects of the effects of Part 1 by discussing aspects of the effects of dispersion, two-cation exchange, and adsorption on a chemical flood:we show that when chemical slug sizes are small and dispersion is moderate, the inclusion of dispersion in the calculation can modify results that are calculated by methods which assume no dispersion;we describe a new phenomenon in which dispersion itself can initiate cation exchange; andfinally, we describe an asymptotic concentration profile toward which dispersive, self-sharpening fronts tend. Introduction One of the most important factors affecting the interfacial activity, phase behavior, and mobility control of a chemical flood is the ionic environment in which the chemical slug passes through the reservoir. Factors affecting this environment are the in-place and injected-fluid compositions and dispersive mixing. Equally important, but perhaps not so obvious, is the role that cation exchange can play in determining the chemical slug's environment. The importance of surfactant and polymer adsorption to the practicality and economics of the chemical flood process long has been recognized. This is because adsorption directly affects the quantity and rate at which surfactant and polymer can be propagated through the reservoir. The interfacial activity and, to a lesser extent, the mobility of the surfactant and polymer are as strongly affected by their ionic environment, particularly the divalent ion concentration, as by particularly the divalent ion concentration, as by their own concentration levels for some ranges. Concern about this sensitivity has led to formulations that include cosurfactants to increase salinity tolerance in the chemical slug, and to preflooding schemes that lower reservoir salinity to acceptable levels. Since cation exchange profoundly affects the flowing phase ionic environment, it must play a central role in the design and implementation of a chemical flood. Toward this goal, this paper tries to illustrate some consequences of cation exchange and polymer/surfactant adsorption in porous media, polymer/surfactant adsorption in porous media, including the effect of fluid-dynamic dispersion. This paper is a companion to Part 1, dealing with cation exchange in nondispersing systems. We, therefore, use some conventions and definitions from that paper. ASSUMPTIONS The assumptions used here are similar to those in Part 1, except thatfluid-dynamic dispersion is not neglected,all material-balance relations are restricted to single-phase flow (there is no oil in the system), andthe system can have no more than five components: calcium (C1 - meq/ml) - a divalent cationic component; sodium (C2 - meq/ml) - a monovalent cationic component; chloride or total salinity (C3 - meq/ml) - a nonadsorbing anionic component; surfactant (C4 - meq/mi) - an adsorbing component; and polymer (C5 - ppm) - a nonionic adsorbing component. Note that all concentrations for C1 through C4 (including the stationary phase concentrations) are in milliequivalents per milliliters of pore volume. The foregoing assumptions restrict somewhat the usefulness of the following results when predicting the behavior of real systems. Nevertheless, these results effectively illustrate the combined influence of dispersion, cation exchange, and polymer/ surfactant adsorption on a chemical flood's environment. SPEJ P. 435


2020 ◽  
Vol 18 ◽  
pp. 00009
Author(s):  
Viktor Glupov ◽  
Vyacheslav Martemyanov ◽  
Vadim Kryukov

Stable and dynamic interactions among plants, herbivorous insects, parasites and associated microbes are formed in natural habitats. The study of these interactions in multicomponent models is required to develop integrated methods for the management of insect pest populations. In this work, we summarize our studies on the influence of different factors, such as hygrothermal conditions, host development, host microbiota, plant quality, and concomitant infections, on interactions between insects and their parasites, such as fungi, bacteria, viruses and parasitoids. Some approaches for developing complex products for biocontrol are also discussed. For example, the use of natural compounds with immunosuppressive effects may enhance the efficacy of microbial agents toward pest insects.


1977 ◽  
Vol 29 (10) ◽  
pp. 1336-1338 ◽  
Author(s):  
H.J. Hill ◽  
F.G. Helfferich ◽  
L.W. Lake ◽  
J. Reisberg ◽  
G.A. Pope

REAKTOR ◽  
2021 ◽  
Vol 21 (2) ◽  
pp. 65-73
Author(s):  
Agam Duma Kalista Wibowo ◽  
Pina Tiani ◽  
Lisa Aditya ◽  
Aniek Sri Handayani ◽  
Marcelinus Christwardana

Surfactants for enhanced oil recovery are generally made from non-renewable petroleum sulfonates and their prices are relatively expensive, so it is necessary to synthesis the bio-based surfactants that are renewable and ecofriendly. The surfactant solution can reduce the interfacial tension (IFT) between oil and water while vinyl acetate monomer has an ability to increase the viscosity as a mobility control. Therefore, polymeric surfactant has both combination properties in reducing the oil/water IFT and increasing the viscosity of the aqueous solution simultaneously. Based on the study, the Critical Micelle Concentration (CMC) of Polymeric Surfactant was at 0.5% concentration with an IFT of 7.72x10-2 mN/m. The best mole ratio of methyl ester sulfonate to vinyl acetate for polymeric surfactant synthesis was 1:0.5 with an IFT of 6.7x10-3 mN/m. Characterization of the product using FTIR and HNMR has proven the creation of polymeric surfactant. Based on the wettability alteration study, it confirmed that the product has an ability to alter from the initial oil-wet to water-wet quartz surface. In conclusion, the polymeric surfactant has ultralow IFT and could be an alternative surfactant for chemical flooding because the IFT value met with the required standard for chemical flooding ranges from 10-2 to 10-3 mN/m.Keywords: Enhanced Oil recovery, Interfacial Tension, Methyl Ester Sulfonate, Polymeric surfactant, vinyl acetate


2018 ◽  
Vol 40 (2) ◽  
pp. 85-90
Author(s):  
Yani Faozani Alli ◽  
Edward ML Tobing ◽  
Usman Usman

The formation of microemulsion in the injection of surfactant at chemical flooding is crucial for the effectiveness of injection. Microemulsion can be obtained either by mixing the surfactant and oil at the surface or injecting surfactant into the reservoir to form in situ microemulsion. Its translucent homogeneous mixtures of oil and water in the presence of surfactant is believed to displace the remaining oil in the reservoir. Previously, we showed the effect of microemulsion-based surfactant formulation to reduce the interfacial tension (IFT) of oil and water to the ultralow level that suffi cient enough to overcome the capillary pressure in the pore throat and mobilize the residual oil. However, the effectiveness of microemulsion flooding to enhance the oil recovery in the targeted representative core has not been investigated.In this article, the performance of microemulsion-based surfactant formulation to improve the oil recovery in the reservoir condition was investigated in the laboratory scale through the core flooding experiment. Microemulsion-based formulation consist of 2% surfactant A and 0.85% of alkaline sodium carbonate (Na2CO3) were prepared by mixing with synthetic soften brine (SSB) in the presence of various concentration of polymer for improving the mobility control. The viscosity of surfactant-polymer in the presence of alkaline (ASP) and polymer drive that used for chemical injection slug were measured. The tertiary oil recovery experiment was carried out using core flooding apparatus to study the ability of microemulsion-based formulation to recover the oil production. The results showed that polymer at 2200 ppm in the ASP mixtures can generate 12.16 cP solution which is twice higher than the oil viscosity to prevent the fi ngering occurrence. Whereas single polymer drive at 1300 ppm was able to produce 15.15 cP polymer solution due to the absence of alkaline. Core flooding experiment result with design injection of 0.15 PV ASP followed by 1.5 PV polymer showed that the additional oil recovery after waterflood can be obtained as high as 93.41% of remaining oil saturation after waterflood (Sor), or 57.71% of initial oil saturation (Soi). Those results conclude that the microemulsion-based surfactant flooding is the most effective mechanism to achieve the optimum oil recovery in the targeted reservoir.


2018 ◽  
Vol 193 ◽  
pp. 03045 ◽  
Author(s):  
Marat Asamatdinov ◽  
Andrey Medvedev ◽  
Alexey Zhukov ◽  
Ervand Zarmanyan ◽  
Alexey Poserenin

Clay-gypsum of each deposit are ecologically safe natural materials. They differ from others in their mineralogical and phase composition, they have different properties. Such a spread of properties of natural clay-gypsum, including after their heat treatment, makes it difficult to process them and, ultimately, use. The factor of "unpredictability of the obtained results" is one of the reasons why this type of natural composites are practically not used in modern construction. The paper presents the results of studies of the properties of model compositions of a clay-gypsum binder. The theoretical basis of the research is the methodology for the creation of new building materials, developed at the MSUCE. According to the proposed provisions, the properties of composite (or multicomponent) systems can be evaluated using the concept of a model body, in our case a "model material", manufactured with observance of certain technological parameters. According to the results of the first stage, the optimum temperature for calcination of an artificial clay-gypsum binder (which was 230-250°C) was established, and a graphical interpretation of the results was carried out using triple diagrams. By results of researches it is established, that the majority of natural structures in the natural state, or after modification can be used as a basis for reception of interior plaster mixes.


1991 ◽  
Vol 238 ◽  
Author(s):  
William D. Hopfe ◽  
J. E. Morral

ABSTRACTThe stability of phases in materials can be related to reactions occurring at their interfaces, for example fiber/matrix reactions in composites. The reaction can be modelled in a simple way, even for multicomponent systems, when it is diffusion controlled and when no intermediate phases form. In the current work a model is proposed that assumes local equilibrium at the interface and small concentration differences in each phase. The physical properties required for the model are the “square root diffusivity” for each phase and the applicable phase diagram. The model is applied to predicting concentration profiles and interface velocities for the reaction of a B2 aluminide containing Ni-34at%Cr-12at%Al with various Ni-rich, gamma solid solutions containing Cr and Al. The example shows how varying the gamma composition can alter the aluminide stability with respect to dissolution or growth. In addition, a simplified form of the model is given for extrapolating experimental interface velocity data.


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