Yang Xuan*a,
Guancheng Jianga,
Yingying Lib,
Lili Yanga and
Xianmin Zhanga
aState Key Laboratory of Petroleum Resources and Prospecting, China University of Petroleum (Beijing), Beijing 102249, China. E-mail: hades_331@163.com
bCNPC Drilling Research Institute, Beijing 102206, China
First published on 2nd October 2015
Oligo (poly-L-lysine) (OPLL), utilized as a high-performance inhibitor for the hydration of shale, was synthesized with L-lysine as a monomer by the thermal copolymerization method. OPLL was characterized through Fourier-transform ion cyclotron resonance mass spectroscopy (FT-ICR-MS), nuclear magnetic resonance hydrogen spectroscopy (1H NMR), Fourier-transform infrared spectroscopy (FT-IR) and thermogravimetry (TG). The inhibition performance of OPLL was evaluated through the combination of montmorillonite (MMT) linear swelling, MMT dispersion and shale dispersion tests, and these results were compared with those for other commonly-used inhibitors in the field. The results demonstrated that OPLL possessed an outstanding inhibition effect on the hydrated dispersion of both MMT-rich and illite-rich shale that was superior to many commonly-used shale inhibitors such as KCl, 2,3-epoxypropyltrimethylammonium chloride (EPTAC) and polyoxypropylenediamine (Jeffamine D230). Along with excellent inhibition capacity, OPLL also possessed good thermal stability and a broad pH adaptability, and therefore, it can perform well under high temperatures up to 180 °C and in the pH range of 7 to 10. Based upon a combined use of X-ray diffraction (XRD) and zeta potential techniques, the inhibition mechanism was determined. The excellent performance of OPLL on shale can be attributed to the synergistic effects of the inhibition of the MMT crystalline swelling and the weakening of the diffuse double layer repulsion between clay particles. Additionally, biodegradability tests proved that OPLL is an environmentally friendly shale inhibitor that can be readily biodegraded.
To address the drilling problems associated with shale instability, various kinds of drilling fluids have been developed and utilized in the field. Oil-based drilling fluids (OBFs) generally give greater shale stability than water-based drilling fluid (WBFs) system due to the prevention of water invasion into shales through a semi-permeable membrane provided by emulsifiers.9 However, the disadvantages of OBFs such as high cost, environmental limitations, disposal problems, health and safety issues and detrimental effects on the drilling and completion of reservoir cannot be ignored.10 Consequently, designing and developing high performance WBFs as good alternatives to OBFs has been a major goal of the petroleum drilling industry.
Because the hydration of the water-sensitive clay mineral montmorillonite (MMT) is commonly considered to be the primary cause of the shale failure, for more than the past five decades various chemicals that can inhibit clay hydration have been used in WBFs as “shale hydration inhibitors” to maintain wellbore stability.
Before the 1990's, the most widely used shale inhibitor was KCl, and most of the time it was used as the main ingredient in combination with other polymer-type species, such as partially hydrolysed polyacrylamide (PHPA)11,12 and polyethylene glycol (PEG).12,13 The inhibition mechanism of KCl occurs via the exchange of sodium cations in the MMT interlayer with the weakly hydrating potassium cations.14,15 However, the high concentrations of KCl that are required can seriously harm ecosystems.16 To overcome the environmental disadvantages of KCl, alternative cation sources have been sought. Because the ammonium cation possesses a very similar hydrated volume and a similar hydration energy to the potassium cation,17 amine-based chemicals were introduced as potent inhibitors and applied in the field during the last few decades; the most effective classes of these chemicals are quaternary ammonium salts18–20 and polyether amines.21–25 Despite the partial success they achieved, quaternary ammonium salts and polyether amine still have some drawbacks, such as the toxicity of some of the high-molecular-weight quaternary amine salts26 and the relatively lower inhibition of the polyether amines. Due to these shortcomings, further efforts must be made to develop environmental friendly and high performance amine-based shale inhibitors.
Poly-L-lysine (PLL), which is a polymer comprised of lysine amino acids, has been widely utilized for biomaterial applications,27–31 owing to its attractive properties including hydrophilicity, excellent biocompatibility and biodegradability. As a primary amine-based cationic polyelectrolyte, PLL is known to have high affinity for negatively charged substrates in a wide pH range through electrostatic attraction.32 Therefore, it is reason to expect that PLL can act as novel biodegradable hydration inhibitor for shale. In most cases, the molecular weight of PLL that was prepared and researched in the field of biomaterial is higher than tens of thousands of grams per mole. However, high molecular weight has significant adverse effect on the shale inhibition performance, which is disclosed by studies on other cationic shale inhibitors.21,33
In this paper, we synthesized oligo (PLL) (OPLL) with molecular weight less than 1000 g mol−1 as a high performance, environmental friendly and low cost shale inhibitor via a simple method. The inhibition performance of OPLL on the hydrated swelling and dispersion of MMT and shale was evaluated through a variety of methods, and these results were compared with those of several commonly-used inhibitors in the oil-field. Moreover, the inhibition mechanism was analysed via combined characterizations of the OPLL–MMT composites.
| Samples | Quartz | Total clay | % by weight of the total clay | ||||
|---|---|---|---|---|---|---|---|
| Montmorillonite | Illite | Kaolin | Mixed layer illite/montmorillonite | % montmorillonite in mixed layer | |||
| Shale 1# | 47 | 26 | — | 31 | 3 | 62 | 55 |
| Shale 2# | 34 | 24 | — | 41 | 2 | 46 | 20 |
For the MMT dispersion tests at a constant MMT loading and variable pH values, the concentration of MMT was fixed at 16 wt%, and the pH value of the suspension ranged from 7–11.
The measurements were obtained using a ZNN-D6L rotational viscometer (Qingdao, China). The yield point and plastic viscosity of the MMT/inhibitor suspension was calculated from viscometer readings of 600 and 300 rpm (Φ600 and Φ300) using the following formulas:
| Yield point (YP) = Φ300 − Φ600/2 (Pa). |
| Plastic viscosity (PV) = Φ600 − Φ300 (mPa s) |
000 rpm for 20 min and then hot rolled at 80 °C for 16 h to reach the adsorption and hydration equilibrium. After being cooled to room temperature, the suspensions were centrifuged at 8000 rpm for 10 min, and the solid samples were washed with DI water to eliminate the residual OPLL solution. The washing and centrifugation processes were repeated several times until the pH value of supernatant was approximately 7. Finally, the solid composites were dried overnight at 105 °C and ground to fine powders for the use in the XRD, FT-IR and TG analyses.The FT-IR patterns of the MMT exhibited the extremely typical characteristic of smectite group. Some of the major absorption peaks were the following: stretching bands of the structural O–H (3625 cm−1), the broad stretching band of the physisorbed water (3425 cm−1), the deformation band of water (1639 cm−1), bands of Si–O stretching and Si–O–Si bending (1040 cm−1 and 1080 cm−1), deformation bands of Al–Al–OH vibrations (917 cm−1), coupled out-of-plane vibration band of Al–O and Si–O (625 cm−1) and deformation bands of Al–O–Si and Si–O–Si, located at 521 cm−1 and 465 cm−1, respectively.39 In the case of the OPLL–MMT composite, although the peaks that are attributed to the amide group in OPLL cannot be distinguished, the peak that appeared at 1457 cm−1 (CH2 stretching bands) undoubtedly suggests the adsorption of OPLL on the MMT surface. Additionally, the spectrum also possess broad and weak peaks at 3425 cm−1 and 1639 cm−1, indicating a significant decrease in the interlayer water.
The microstructure of the OPLL was characterized by the 1H NMR spectrum, which is shown in Fig. 3. The peak at 4.08 ppm in the spectrum was assigned to the α-CH proton of the α-linked lysyl units, and the near peak at 3.98 ppm originated from the α-CH proton of the terminal lysyl units.40 The three broad peaks located in the range of 1.2–1.8 ppm were attributed to the β, γ and δ-CH2 groups. The highest peak at 2.82 ppm was assigned to the ε-CH2 group next to a free amino group.34,40 Additionally, no signals that can be attributed to the α-CH proton or the ε-CH2 proton of the ε-linked lysyl units were apparently visible, indicating that the OPLL synthesized in this paper was mainly composed of α-linked units. This finding could be due to that, in the presence of phosphoric acid as catalyst, the L-lysine monomers have a strong tendency to polymerize via the amidation of the α-NH2 group rather than the ε-NH2 group.
The linear swelling behaviour of compacted MMT in aqueous media is strongly dependent on the crystalline swelling that occurs between the individual MMT layers caused by the hydration of interlayer cations and layer surfaces.41 Therefore, the stronger inhibition of OPLL on swelling of compacted MMT could be mainly due to the higher inhibition on crystalline swelling of the MMT.
The difference in dispersion states of the MMT in pure water and OPLL solution can be directly observed by TEM, as shown in Fig. 6. Apparently, the plate-like MMT particles dispersed in OPLL solution is much thicker and longer than in DI water, indicating that the dispersion of the MMT particles is inhibited by OPLL. The size of MMT particles in aqueous suspension is mainly governed by the diffuse double layer repulsion.42 If the repulsion between the diffuse double layers of two approaching MMT particles is weak enough to be overcome by kinetic energy, the diffuse portions of the double layers will begin to fuse, which results that the two particles join together forming one larger particle. The reduction of particle number undoubtedly has an adverse effect on the formation of network structure, as indicated by the decrease in the yield point of suspension. Consequently, the inhibition on hydrated dispersion of MMT particles by OPLL could be attributed to the weakening of the double-layer repulsion through electrostatic neutralization between the negative MMT surface and the positive charged OPLL. The detailed analysis will be discussed in the later section.
Electrostatic attraction between the positively charged amine groups and the negative MMT surface and ion exchange with interlayer cations are the main driving forces for the adsorption of the OPLL molecules onto the MMT particles. Only when the pH value of solution is close to or lower than the pKa value of OPLL can the protonation of amine groups occur. Therefore it can be expected that the inhibition performance of the OPLL would be strongly influenced by the pH value of solution. Fig. 7 shows the yield points and the plastic viscosities of the MMT/OPLL suspensions as a function of pH with the same MMT concentration. In the pH range between 7 and 10, the yield points and the plastic viscosities did not exhibit an obvious change. However, when the pH value increased to 11, these two values simultaneously possessed a significant increase, indicating the poor inhibition on the dispersion of the MMT particles. Therefore, it can be deduced that the pKa value of OPLL is in the range between 10 and 11. The fact that the reported pKa of ε-NH2 and α-NH2 in poly(L-lysine) is 7.6 (ref. 43) and 10.5,44 respectively, further proves that the OPLL synthesized in this paper was predominantly of the α-type. This test suggests that the OPLL can exhibit a good performance in the WBFs, where the pH range is generally fixed between 9.5 to 10.5.45
The inhibition capacity at high temperature is also of great significance for the shale inhibitor because the drilling depth in the recent decades is much deeper than ever, and therefore, the inhibitor needs to be able to overcome the negative effects brought about by high temperatures. Fig. 8 presents the yield points of the MMT/OPLL suspensions as a function of temperature with the same MMT concentration. In the temperature range between 90 °C to 180 °C, no significant change in the yield point and plastic viscosity was detected for the MMT/OPLL suspension. However, when the temperature was further increased to 210 °C, both of the two values increased sharply, indicating the serious weakening of the inhibition performance of OPLL under such a high temperature.
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| Fig. 8 Yield points and plastic viscosities of the MMT/OPLL suspensions as a function of temperature. | ||
Fig. 9 presents the TG curves of the OPLL, pristine MMT and the OPLL–MMT composite. For OPLL, within the experimental temperature range, there are two major stages in the process of thermal decomposition. The slight weight loss from 30 °C to ∼120 °C was attributed to the evaporation of the physically adsorbed water. The second stage began at approximately 250 °C, and a rapid loss of weight up to 50 wt% was observed; this effect was attributed to the thermal decomposition of the unstable functionalities, such as the primary amine and amide. Because the thermal decomposition of OPLL will not occur when the temperature is lower than 250 °C, the poorer inhibition performance on MMT dispersion at 210 °C could be due to the significantly weakened electrostatic adsorption of OPLL on the MMT surface at the high temperature.
In the case of pristine MMT, the mass loss step observed up to ∼140 °C was ascribed to the release of the free (interstitial water and surface adsorbed water) and interlayer water. The second step, starting from ∼550 °C, due to the removal of the structural water (bonded hydroxyl moieties that underwent dihydroxylation).46 The TG curve of the OPLL–MMT composite demonstrated that the amount of free and interlayer water in MMT decreases after the adsorption of the OPLL molecules, indicating the effective inhibition of the OPLL on the hydration of MMT.
Fig. 10 compares the inhibition performance of the OPLL with other commonly-used inhibitors, including KCl, Jeffamine D230 and EPTAC. Apparently, at the same concentration, the yield point of the MMT/OPLL suspension was much lower than that of any other inhibitor, indicating the higher inhibition of OPLL on the MMT hydrated dispersion.
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| Fig. 11 Recovery percentages of the shale with a relatively high MMT content after being hot-rolled in different inhibitor solutions at 120 °C for 16 h. | ||
Above the cloud point temperature (∼50 °C), the Jeffamine solution started to phase separate. The droplets or aggregates resulting from the separation of the Jeffamine-rich phase can seal the shale surface, thereby reducing the water ingress into the shale.48
Although the traditional inhibitor KCl has a strong inhibitory effect on the swelling of MMT, it had hardly any effect on the non-swelling minerals, such as illite, according to a report by van Oort.3 Fig. 12 shows the recovery percentages of the shale with relatively high illite contents (shale 2#) after they were hot-rolled in DI water, KCl or OPLL solutions. The recovery percentage in DI water was 13 wt%, and the value was merely increased to 23 wt% by the KCl solution with up to 7 wt% concentration, which indicated the negligible inhibition of KCl on the illite-based shale. In sharp contrast, the shale recovery percentage was increased significantly to 59 wt% by the 1 wt% OPLL solution. This difference suggests that OPLL can effectively inhibit the hydrated dispersion of both the MMT-rich and illite-rich shale.
Fig. 13(a) presents the XRD patterns of the dry OPLL–MMT composites with different OPLL concentrations. The peaks were assigned to the (001) basal diffraction of the MMT. It was observed that the pristine MMT exhibited broad diffraction peak at 2θ = 8.8°, which corresponded to an average interlayer spacing of 9.74 Å, revealing a dominant dehydrated interlayer stage.50 The addition of small amounts of OPLL immediately modified the XRD patterns. For a low concentration of 0.2 wt% OPLL, the peak shifted toward the lower angle side corresponding to interlayer spacing of 13.1 Å. As the concentration of OPLL increased to above 0.6 wt%, the interlayer spacing further expanded to 13.6 Å, which is the sum of the thickness of dehydrated MMT and a single layer of OPLL molecules. This effect indicated the successful intercalation of the OPLL into the interlayer of MMT driven by cationic exchange.51
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| Fig. 13 XRD patterns of (a) dry OPLL/MMT composites and (b) wet OPLL/MMT composites with different concentration of OPLL. | ||
In addition, with an increase in OPLL dosage, the diffraction patterns exhibited a significant increase in the crystallinity as judged from the half width of the d001 signals. Higher crystallinity indicates a greater inhibition on the hydrated dispersion of the MMT quasicrystals with higher OPLL concentrations.4 For the concentrations of OPLL above 1.5 wt%, the patterns distinctly demonstrated two peaks, thus revealing a coexistence of layers with and without intercalation with the OPLL molecules. This pattern suggests that some of the layers were intercalated before the others, which may be linked to the layer charge heterogeneities that are nearly always present in natural swelling clays.52
The evolution of the XRD patterns of the wet OPLL-MMT composites with the concentration of OPLL is presented in Fig. 13(b). For pristine MMT, the XRD pattern displayed an interlayer spacing of 19.5 Å, corresponding to a dominant three-layer hydrate stage of MMT.53 With the increase in the OPLL concentration to 1.5 wt%, the interlayer spacing gradually decreased to 13.9 Å, and the further increase of concentration to 2 wt% did not obviously change the spacing. It must be noted that this value was approximately the same as that of the dry OPLL–MMT composite (13.6 Å), which may indicate that the intercalated OPLL molecules almost totally prevented any crystalline swelling resulted from the uptake of water.
Our previous studies have shown that the degree of crystalline swelling was closely correlated with the macroscopic swelling degree of the densely compacted MMT immersed in inhibitor solution,54 which is also clearly revealed in Fig. 14. This figure compares the macroscopic linear swelling height and the microscopic change in the interlayer spacing of the MMT exposed to different inhibitor solutions. It can be observed that the MMT sample, which had a lower degree of macroscopic swelling in the OPLL solution, shows a smaller interlayer spacing than what was observed with other inhibitor solutions. This finding indicated that OPLL effectively inhibited the hydrated swelling of MMT-rich shale via intercalating into the interlayer space and preventing the crystalline swelling of MMT. Additionally, it is worth mentioning that the MMT sample that was compressed under an applied stress of 15 MPa for the linear swelling test was dense enough to approximately represent impermeable shale with a high MMT content.49 Therefore, it can be concluded that inhibiting crystalline swelling of MMT is an effective way for OPLL to prevent the impermeable shale from destabilizing.
For all three of the cationic inhibitors, including OPLL, the zeta potential did not reverse to a positive value, indicating the adsorption amount was lower than the CEC of MMT. The adsorption of the low molecular weight cationic polymer below the CEC is mainly due to the electrostatic interactions, and the adsorption above the CEC is due to additional hydrophobic interactions between the adsorbing molecular chains.55 Because OPLL does not possess long hydrophobic alkyl chains, the adsorption on the MMT cannot result in the inverse of zeta potential, which may re-stabilize the diffuse double layers. The zeta potential values of the MMT in different inhibitor solutions was extremely consistent with the inhibition effects on MMT hydrated dispersion. Crystalline swelling is a process that occurs within the individual layers; whereas in contrast, double-layer swelling is a process that occurs between the colloidal particles,42 which is the main reason behind the stable dispersion of the MMT in aqueous media. The comparison of Fig. 9 and 14 showed that the inhibitor that can neutralize the negative charge on the MMT surface to the greatest extent had the best inhibition on MMT dispersion, and this can be attributed to the decrease of the surface charge potential and the resulting extreme weakness of the double-layer repulsion. As previously mentioned, for more permeable shale, the double-layer repulsion associated with the charged external surfaces of the clay particles exposed in the opposing walls of shale pores is considered to be the dominant factor causing dispersion.49 Therefore, the ability to effectively weaken the double-layer repulsion between clay particles undoubtedly ensures the high inhibition performance of OPLL on permeable shale, no matter the main clay mineral in the shale is MMT or non-swelling type, such as illite and kaolin.
According to the opinion of Wilson and Wilson,49 generally, the hydrated dispersion of shale may be influenced by both the crystalline swelling and the double-layer repulsion of clay. Thus it is reasonable to speculate that the high inhibition performance of OPLL on shale is owning to its outstanding ability to inhibit crystalline swelling of MMT and weaken double-layer repulsive interaction between clay particles. The probable mechanism of shale inhibition by OPLL is shown in Fig. 16.
000 tons per year) are annually produced worldwide almost always by microbial fermentation.56 In china, the average price of feed grade L-lysine (98%) is only about $1400/ton; therefore, OPLL is expected to be economically viable for use in drilling industry.
Biodegradability and non-toxicity are of great importance to drilling fluid additive because of the tightening of environmental regulations. BOD/CODCr constitutes a good measure of the biodegradability of chemicals. Fig. 17 shows the changes in the BOD/CODCr ratio of OPLL over time. According to the general principle for determining biodegradability,57 organic matter with a ratio of BOD/CODCr > 0.6 on the 28th day can be deemed to be easily biodegradable. From Fig. 17, it can be observed that the BOD/CODCr value of OPLL within 5 days has already reached a value of 0.65, indicating that OPLL can be thoroughly biodegradable after a short period of time and therefore beneficial in protecting the environment. Additionally, as reported in the literature,58 polylysine and its derivatives with similar structures are non-toxic. Therefore, due to the high biodegradability and non-toxicity, OPLL can be applied as a promising environmental friendly shale inhibitor in WBFs that could be used in both onshore and offshore drilling.
The MMT linear swelling and dispersion tests exhibited high inhibition of OPLL on hydration of MMT, superior than many commonly-used inhibitors in the field. Additionally, FT-IR and TG characterizations on the OPLL–MMT composite demonstrated that the amount of free and interlayer water in the MMT significantly decreased after the adsorption of OPLL, further indicating the effective inhibition of the OPLL with respect to MMT hydration. The results of shale dispersion tests suggested that the OPLL could efficiently inhibit the hydrated dispersion of not only the MMT-rich but also the illite-rich shale. This finding represents a significant advantage over the traditional inhibitor KCl, which possesses an extremely limited inhibitory effect on illite-rich shale. In addition to strong inhibition performance, the OPLL also possesses good thermal stability, broad pH adaptability and favorable biodegradability, which ensures that OPLL can be utilized as a promising environmental friendly shale inhibitor in water-based drilling fluid.
The inhibition mechanism of OPLL was determined based on the combined use of XRD and zeta potential techniques. The results of the XRD analysis demonstrated that OPLL can intercalate into the interlayer of MMT, and therefore prevent crystalline swelling to a great extent. Zeta potential analysis demonstrated that OPLL can effectively neutralize the negative charge on the MMT surface and thereby significantly weaken the double-layer repulsion between MMT particles. Therefore, it can be concluded that the excellent inhibitive performance of OPLL on shale can be attributed to the synergistic effects of the inhibition of the MMT crystalline swelling and the weakening of the double-layer repulsion between clay particles.
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