A New Class of Renewable Surfactants for Chemical Enhanced Oil Recovery Hadi ShamsiJazeyi*, Anton Kaiser*, Jonathan J. Wylde, Amir Mahmoudkhani, and Dirk Leinweber, Clariant Oil Services Abstract With the ever-growing demand for more environmentally acceptable oilfield chemicals, classic oilfield chemistries are becoming obsolete and new chemical systems are required. Future oil production will be dominated by unconventional oil production with increased amounts of chemicals needed to further improve oil recovery with higher production rates. In addition, environmentally acceptable chemistries will be of increased significance and the use of natural product based chemicals will further ensure a more sustainable oil production. To achieve the future requirements of environmentally acceptable surfactants for chemical enhanced oil recovery, chemistries with low toxicity and high biodegradability are needed. Renewable based fatty acid amides represent such a class of bio-based surfactants that are environmentally acceptable and show superior performance in enhanced oil recovery applications. The following paper describes the chemical design of renewable based fatty acid amide surfactants and their use in EOR applications. Extensive phase behavior studies, salinity scans, IFT measurements and surface tension measurements were performed to present the high efficiency and potential of these products for alkaline surfactant polymer-, alkaline surfactant- and surfactant flooding on different crude oils. Furthermore, the biodegradation and aqua-toxicity of the renewable based fatty acid amide surfactants will be discussed in detail. This new class of bio-based surfactants represents an environmentally acceptable option to the broadly used internal olefin sulfonates with superior performance. The non-ionic character of the renewable based fatty acid amide molecule results in much less ability to adsorb on rock surfaces which allows a potential re-injection of the produced water to decrease chemical consumption. Additionally, the viscoelastic behavior of this new class of surfactants will improve the sweep efficiency during a flooding process. Overall, these multifunctional natural-based surfactants will drastically increase oil recovery rates when applied. Keywords: Biodegradability, Enhanced Oil Recovery, Environment, Renewable, Surfactant Introduction There is an increasing worldwide demand for crude oil with only short-lived fluctuations caused, typically by historical oversupply [1]. This means the production of crude oil needs to increase at a similar pace in order to meet the energy demands around the globe. One way to increase production is to change to higher efficiency oil and gas production technologies. Such methods should be able to recover a greater percentage of the STOOIP (Stock Tank Oil Originally in Place) in an economically viable way. Enhanced Oil Recovery (EOR) is a common name for a series of technologies that can significantly increase the production of oil and gas from a given reservoir. EOR is also known as tertiary oil recovery due to the fact that it is usually done after primary step (recovery of oil due to the natural pressure of the reservoir) and second step (flooding the reservoir with water) [2]. Chemical EOR (CEOR) is a name given to a series of methods involving surfactants, polymers, and sometimes alkaline substances in order to increase the oil production [2]. CEOR is a very promising technique that has repeatedly shown the ability to recover almost all the STOOIP both in lab and field trials. However, there are challenges ahead of widespread application of CEOR, the most important of which are cost of chemicals and environmental aspects of chemicals [3, 4, 5]. The use of environmental-acceptable chemicals in CEOR applications can promote the application of these methods, because increased production will not lead to any additional chemical induced risk to the environment. In the past few decades, there has been some effort to design biodegradable surfactants from natural sources. One of the earliest cases is a patent published in 1992 that discloses processes for making surfactants from fatty acids or their derivatives in combination with Nalkylglucamines, the latter made by reductive amination of glucose with methylamine [6]. Later, the surface properties of such fatty acid amide surfactants was studied [7, 8]. Also, application of surfactants from natural sources have been studied in many different areas [912]. In this paper, application of a new class of surfactants for CEOR is introduced. These fatty acid amide surfactants are mostly synthesized using abundant natural resources, are biodegradable, lower interfacial tension, and show low adsorption to reservoir rock surfaces. This class of fatty acid amide surfactants can be considered as a breakthrough in environmentally friendly application of CEOR for increase in crude oil recovery. Materials and Methods Eagle-Ford condensate oil was used as oil phase to determine interfacial properties of the surfactant. Silica and Kaolinite were provided by Evonik and Sigma-Aldrich, respectively. Iceland Spar (by Ward Scientific) was crushed and powdered and grain size <40 micron was used as a substrate for adsorption experiments, which will be referred to as Powdered Iceland Spar. The salinity scan tests were done by changing the concentration of NaCl in each sample, while the concentration of fatty acid amide and C-20/24 IOS (internal olefin sulfonate) was kept constant. For each sample, the final concentration of fatty acid amide and C-20/24 IOS was 0.5 wt% per initial aqueous phase. 20 g of aqueous solution was contacted with 5 g of condensate oil, which resulted in W/O weight ratio of 4:1. The phase behavior experiments were done at a constant reservoir temperature of 60°C. The pictures were also taken in a constant temperature oven fixed at 60°C. The interfacial tensions were calculated based on Chun Huh relation [13] and the observations from the phase behavior experiment on the amount of oil and water that was solubilized in the micro-emulsion phase. Therefore, the interfacial tension values reported were an approximation of actual values, valid for 60°C. If three phases were formed after equilibrium, the interfacial tension between the micro-emulsion and oil was reported since that is what matters most in oil recovery. The surface tension measurements were done using a pendent drop method tensiometer at room temperature in different salinities. 0.5 wt% of fatty acid amide was used for these measurements in the absence of any other surfactant. In order to measure surfactant adsorption on different minerals, accurate concentration measurement is essential. The difference between the concentration of surfactant before and after contacting the mineral (silica, kaolinite, or powdered Iceland spar) is related to the adsorption of surfactant if precipitation is prohibited. The concentration of fatty acid amide was measured using High Performance Liquid Chromatography (HPLC) with a Gel Permeation Column (GPC). The calibration curve was measured between 0.4 to 1.0 wt% concentrations. The initial concentration of fatty acid amide before contacting different minerals was 1 wt%. Results and Discussions The experiments in this paper are designed to investigate the interfacial properties, biodegradation, and aqua-toxicity of the fatty acid amide surfactant. The interfacial properties are meant to study the feasibility of using fatty acid amide surfactants in CEOR applications. In addition, studying the biodegradation and aqua-toxicity of the fatty acid amide assures us about the environmental impacts of using this surfactant for CEOR applications. Figure 1 shows the salinity scan experiment with fatty acid amide (0.5 wt% C-20/24 IOS is added) in the presence of Eagle Ford condensate oil at 60°C. Micro-emulsion middle phase is seen in a wide range of salinities (5 to 8 % NaCl) using this surfactant system. Observance of a micro-emulsion middle phase (Winsor type III) in this figure is a strong indication of feasibility of using this surfactant for CEOR. This also can be seen as an indication of ultra-low interfacial tension made by using this surfactant system. The ultra-low interfacial tension is a necessary aim that a surfactant needs to provide to increase the capillary number and in order for a CEOR project to be successful. 2 3 4 5 6 7 8 9 % NaCl Figure 1) Salinity scan for 0.5 wt% fatty acid amide and 0.5 wt% C-20/24 IOS at 60°C. Three different phases are observed as Winsor type I, III, and II, which are shown with the red box in the picture. The interfacial properties of a surfactant are very important in its application for CEOR. An ultra-low interfacial tension is one of the most important properties that assure a successful CEOR project. If a surfactant leads to ultra-low interfacial tension between oil and water, this means that capillary force cannot maintain the oil inside the pores of the rocks as long as such low interfacial tension is maintained. A low surface tension, resulted from using surfactant, can also be important in many different types of EOR, including WAG, SAGD, etc. Table 1 contains more information about the interfacial properties of the fatty acid amide. The interfacial tension between the 0.5 wt% fatty acid amide and 0.5 wt% aqueous solutions of C20/24 IOS and Eagle Ford condensate oil has been calculated based on ChunHuh relationship. The surface tension measurements are reported for 0.5 wt% of fatty acid amide and air at room temperature. Based on the data provided in Table 1, it can be observed that the fatty acid amide has very distinct interfacial and surface properties. The ultra-low interfacial tension and low surface tension resulting from the use of the fatty acid amide promise great potential for its use in CEOR applications. In addition to the interfacial and surface properties of a surfactant, another factor in its economic use for CEOR project is the adsorption on the rocks. If a surfactant highly adsorbs on the reservoir rock, a great portion of it will be lost without contributing to the recovery of oil. Figure 2 shows the adsorption measurement for the fatty acid amide on silica, Kaolinite, and Iceland Spar at different conditions. Table 1) the interfacial properties of the fatty acid amide. NaCl Interfacial Tension Salinity Without Surfactant (wt %) (mN/m) 2 41.31±0.32 5 43.12±0.49 10 46.29±0.52 kaolinite Powdered Iceland Spar a) 9 14 8 12 7 6 5 4 3 Surface Tension Surface Tension Without With Surfactant (mN/m) Surfactant(mN/m) 72.10±0.04 25.90±0.12 73.58±0.08 26.06±0.08 73.22±0.09 26.26±0.09 silica Adsorption (mg/g) Adsorption (mg/g) silica 10 Interfacial Tension With Surfactant (mN/m) 12.51 0.0053 7.34 kaolinite Powdered Iceland Spar b) 10 8 6 4 2 2 1 0 0 0 20 40 60 Temperature (C) 80 100 0 2 4 6 8 10 NaCl Salinity (%NaCl) Figure 2) Adsorption of fatty acid amide as a function of temperature and salinity on different rocks/minerals. As it was explained before, it is important to use environmentally-acceptable chemicals for increasing oil and gas production, especially in CEOR. Figure 3 and Table 2 represent data on bio-degradation and aqua-toxicity of fatty acid amide. It can be seen in Figure 3 that the fatty acid amide shows a continuously increasing marine bio-degradation and would biodegrade totally with time in an marine environment. Table 2 provides the algae EC50 aqua-toxicity data of the fatty acid amide surfactant. It is reported that about 335 mg/l represents the EC50 value of the fatty acid amide, consequently the fatty acid amide is not consider as aqua-toxic at all. Figure 3) OECD 306 biodegradation of the fatty acid amide. OECD 306 Biodegradation 60 50 40 30 Fatty acid amide 20 10 0 (%) (%) (%) (%) Day 7 Day 14 Day 21 Day 28 Table 2) Aquatic toxicity of the fatty acid amide. Aquatic Toxicity Test Result (mg/l) Fatty Acid Amide 72 hr Algae EC50 335.40 Conclusions In this work, the potential application of a renewable surfactant (fatty acid amide) from natural sources for enhanced oil recovery is studied. The surfactant shows a clear microemulsion phase in a salinity range, which indicates its potential to help increase the recovery of oil from depleted reservoirs. The ultra-low interfacial tension was calculated based on the formation of clear micro-emulsion middle phase. The surface tension of the surfactant was also measured in different salinities. In addition to the interfacial properties, the adsorption of this surfactant on silica, kaolinite, and Iceland spar at different conditions was studied. These minerals represent some of the common reservoir rock surfaces in the oil fields. The effect of salinity and temperature on adsorption was measured. Overall, the adsorption of the fatty acid amide on these mineral surfaces is extraordinary low, which makes its potential use for oil recovery applications economical. Finally, the data for marine biodegradability and aqua-toxicity of the Glucamide is presented. All in all, the fatty acid amide is an example for a class of surfactants that not only can help recover more oil, but also do not harm the environment due to their ultralow aquatoxicity and high biodegradability. References [1] J.C.B. Cooper, Price elasticity of demand for crude oil: estimates for 23 countries, OPEC Energy Review, 27 (2003), 1-8. [2] G.J. Hirasaki; C.A. Miller; M. Puerto, Recent Advances in Surfactant EOR, SPE Journal, 16 (2011), 889-907. [3] H. ShamsiJazeyi; G.J. Hirasaki; R. Verduzco, Sacrificial Agent for Reducing Adsorption of Anionic Surfactants, SPE-164061-MS, (2014). [4] H. ShamsiJazeyi; G.J. Hirasaki; R. Verduzco, Reducing adsorption of anionic surfactant for enhanced oil recovery: Part II. Applied aspects, Colloids and Surfaces A: Physicochemical and Engineering Aspects, 453 (2014), 168-175. [5] M.A. Lewis, Chronic and sublethal toxicities of surfactants to aquatic animals: A review and risk assessment, Water Research, 25 (1991), 101-113. [6] D. S. Connor; J. J. Scheibel; R. G. Severson; Preparation of polyhydroxy fatty acid amides in the presence of solvents, WO1992006073 A1, Application Patent, (1992). [7] P.S. Piispanen; M. Persson; P. Claesson; T. Norin, Surface properties of surfactants derived from natural products. Part 1: Syntheses and structure/property relationships— Solubility and emulsification, Journal of Surfactants and Detergents, 7 (2004), 147-159. [8] P.S. Piispanen; M. Persson; P. Claesson; T. Norin, Surface properties of surfactants derived from natural products. Part 2: Structure/property relationships—Foaming, dispersion, and wetting, , Journal of Surfactants and Detergents, 7 (2004), 161-167. [9] R. Skoeld; C. Townsley; Surfactant compositions with anti-microbial effect, WO1996028458 A1, Application Patent, (1996). [10] S. Klein; water insoluble quaternary ammonium compounds having long chain alkyl or alkenyl group(s) water soluble quaternary ammonium compounds nonionic amphoteric and/or zwitterionic solubility promoter translucent clear, US6572846 B2, Grant, (2003). [11] A. Fischer; R. Vybiral; Linear glucamide detergents - useful as accelerating emulsifiers in the emulsion polymerisation of vinyl] chloride, DE4237434 A1, Patent Application, (1994). [12] G. Crass; H. Ahrens; Fatty acid glucamide compounds are useful as emulsifying agents for the production of polymer dispersions in emulsion polymerization, DE19934836 C1, Grant, (2000). [13] C. Huh, Interfacial tensions and solubilizing ability of a microemulsion phase that coexists with oil and brine, Journal of Colloid and Interface Science, 71 (1979), 408-426.
© Copyright 2024