Open Access Article
Minh Vuong
Phan
*ac,
Thi Kim Thoa
Tran
ac,
Quynh Nhu
Pham
a,
Manh Huy
Do
a,
Thi Hong No
Nguyen
ac,
Minh Ty
Nguyen
a,
Thanh Thao
Phan
ac and
Thi Xuan Hang
To
bc
aInstitute of Chemical Technology, Vietnam Academy of Science and Technology, Ho Chi Minh City 700000, Vietnam. E-mail: pmvuong@ict.vast.vn; Tel: +84909312860
bInstitute for Tropical Technology, Vietnam Academy of Science and Technology, Hanoi 100000, Vietnam
cGraduate University of Science and Technology, Vietnam Academy of Science and Technology, Hanoi 100000, Vietnam
First published on 3rd January 2024
The development of layered double hydroxide (LDH) nanosheets as nanocontainers has been intensively studied in recent years. Despite their potential for application on a large scale, their synthesis in an aqueous medium is rarely reported. Herein, we report a straightforward approach for the controllable synthesis of uniform MgAl-LDH nanosheets by an aqueous nucleation process followed by a hydrothermal treatment. The key to this method relies on the well-dispersed LDH nuclei that are produced by high-speed homogenization. Following the nucleation step, the coalescence of the aggregate hydroxide layers is diminished by hydraulic shear forces, leading to the disaggregation and even distribution of LDH nuclei. As a result, the oriented growth of individual crystals along the horizontal plane becomes predominant, leading to a high surface charge density of the hydroxide sheets and preventing their stacking. The electron microscope virtual proofs showed that the particles had a well-defined circular shape with a thickness of about 2–3 nm. Afterward, for the first time, LDH nanosheets were used to prepare LDH nanocontainers loaded with 2-benzothiazolythio-succinic acid (BTSA) by anion exchange. The incorporation of BTSA into the interlayer region and the emission behavior of the inhibitor were investigated. These results indicate that the prepared nanosheets can be utilized as effective nanocontainers for organic inhibitor loading and anti-corrosion application.
:
(M2+ + M3+), which typically varies in the range from 0.2 to 0.33 for pure LDHs, and (An−) represents the interlayer anion.6–8 The interlayer region can be utilized as a nanospace, wherein anions of various functions are stored and exchanged. Such a property is attributed to extensive research conducted with respect to their potential applications in such a wide range of fields as catalysts, absorbents, flame retardants, polymer additives, and anti-corrosion agents.9–13 However, the natural aggregation of the lamellar LDH sheets restricts access to the interlayer region, resulting in a decrease in ion exchange capacity, which severely limits their application and overall performance.2,14 To address this issue, the exfoliation of LDH into nanosheets was proposed.
Nanosheets, which typically range from 0.5 to 3 nm in thickness, are highly anisotropic materials.15,16 Their unique structure and performance are the attributes that drive the construction of functional blocks for a wide variety of applications.17–20 In general, LDH nanosheets are typically synthesized via two ways: delamination of pristine LDH and direct synthesis via the co-precipitation process. The former requires two important factors: (i) organic anion-intercalated molecules that can weaken the interaction between LDH sheets and (ii) polar dispersant solvents that can form hydrogen bonds with the LDH galleries, allowing a large number of solvent molecules to enter the interlayer space and thereby accelerating the delamination process.18,21–23 Recently, Lian Ma et al. have reported a method for fabricating novel nanocontainers by exfoliating MgAl-LDHs into nanosheets and then recombining them with organic inhibitors. The resulting LDH-AIA− demonstrated itself as a very good inhibitor with regard to copper electrodes.24 However, the delamination method involves a complex stage that includes the synthesis of LDH pristine and, subsequently, exfoliation. Due to the strong electrostatic interaction between the sheets, LDH was exfoliated in a formamide solution rather than an aqueous medium, which has detrimental environmental effects.25 The direct synthesis methods of LDH nanosheets relied on controlling the nucleation and growth conditions of LDH nuclei during the co-precipitation procedure.18,21,26 The key to the approaches is the use of certain reactants, such as hydrogen peroxide or formamide, which can be placed in the LDH galleries to prevent the stacking of hydroxide layers or inhibit the growth of LDH along the Z-direction.2,27,28 Ang Liu et al. reported the direct synthesis of ZnAl-LDH nanosheets by co-precipitation in a formamide/water mixture solution followed by an aging step. Then, the LDH nanosheets were applied in the fabrication of highly ordered hybrid polyvinyl butyral/LDH films, which were used as barrier coatings for steel electrodes. The results indicated that the well-oriented LDH nanosheets in the hybrid film significantly improved the corrosion protection of mild steels.20 Nevertheless, the as-prepared LDH nanosheets need to be dispersed in formamide to prevent re-stacking, which further restricts their practical application.
Even though direct synthesis in an aqueous medium is an attractive route due to the limited use of toxic chemicals and the potential for large-scale synthesis, systematic studies in this direction are still rare. Li et al. reported the successful synthesis of LDH nanosheets by the use of excess amounts of lactate in the fast co-precipitation.29 Subsequently, LDH precursors were sonicated and allowed to stand overnight. This made them disaggregated, producing LDH nanosheets. However, the LDH precursors were not separated from their mother liquor before ultrasonic treatment. This promotes the disorderly growth of LDH nuclei, which affects the final particle size and distribution of LDH particles. Much recently, Quin et al. have reported the use of large molecules such as styrene-maleic anhydride (SMA) copolymers, which adhere to the surface of hydroxide layers and weaken the interaction among hydroxide sheets.30 This caused LDH sheets to grow laterally without stacking during the subsequent aging step. However, the controlled lateral size of the nanosheets was not discussed. To the best of our knowledge, the effect of the LDH nuclei dispersion on the tunable particle size of LDH nanosheets is not fully understood. Moreover, the use of LDH nanosheets to construct organic inhibitor-loaded nanocontainers via anion exchange has not been reported previously.
In this study, we propose a straightforward technique for the controllable synthesis of LDH nanosheets in an aqueous medium. This novel approach involved using a high-speed homogenizer to generate evenly dispersed LDH nuclei, which facilitated the growth of nanosheets with uniform particle sizes. In addition, the particle size of LDH nanosheets can be easily manipulated by adjusting the hydrothermal temperatures. Without the use of any organic solvents or hazardous chemicals or the need to operate under N2 pressure, this approach is simpler and more effective than the current techniques. Then, for the first time, anion exchange was performed on the as-prepared LDH nanosheets to construct a nanocontainer loaded with organic inhibitor anions (BTSA). The anion exchange capacity of the LDH nanosheets and the release behaviors of LDH-BTSA nanocontainers were investigated by various analytic techniques. Finally, the inhibitor efficiency of LDH-BTSA in a NaCl solution was investigated using polarization curves and impedance techniques.
The S45C carbon steel electrodes with a surface area of 1.13 cm2 were used to prepare the working electrode. For all experiments, the electrode surface was polished with SiC abrasive paper (Fujistar-Japan) from 300 to 1200 grades, rinsed with ethanol, and dried before testing. The surface compositions of electrodes after polishing were 3.14 wt% C, 0.98 wt% O, 0.08 wt% Si, 0.78 wt% Mn, 1.28 wt% S, 0.05 wt% P, 0.18 wt% Cr, 0.09 wt% Ni and the rest is Fe.
000 rpm for 15 minutes to obtain a homogeneous suspension (so-called LDH precursors) denoted as LDH-Cl-H. The obtained suspension was transferred into a 500 mL autoclave and heated to 125 °C at a stirring speed of 250 rpm for 24 h. After cooling to room temperature, the LDH nanosheets were collected by centrifugation at 15
000 rpm and signed as LDH-Cl. A part of the nanosheets were vacuum dried at 80 °C for 12 h in order to determine their characteristics, while the rest were re-dispersed into DI water for loading the inhibitor. To precisely tailor the particle size of LDH nanosheets, the hydrothermal temperature was adjusted at 80, 100, 125, and 150 °C.
The amounts of BTSA intercalated to an LDH interlayer and the released fraction of BTSA in a NaCl solution were analyzed by V-630 UV-vis spectroscopy (Japan). The standard curve was performed at different concentrations: 1, 5, 10, 20, and 50 mg L−1 of BTSA in ethanol at 280 nm. For determining the content of BTSA, 10 mg LDH-BTSA was dissolved in 1 mL of 3 M HNO3 with a sonicator for 5 minutes to ensure the dissolution of the nanocontainer. The resulting solution is filled to 10 mL with absolute ethanol in a volumetric flask and quantitated by UV spectroscopy. The fraction releases of BTSA in a NaCl solution were determined as follows: 300 mg of the nanocontainers were dispersed in 100 mL of different concentrations (0.05, 0.1, and 0.5 M) of NaCl solution at a stirring rate of 300 rpm. At the time of the survey, 1 mL of release solution was collected by a 0.45 μm filter, up to 10 mL in a volumetric flask with ethanol, and also quantitated using a UV spectrometer.
The inhibitory effect of LDH nanocontainers was analyzed by electrochemical measurements performed using a VSP potentiostat from Biologic (France). The setup consisted of a three-electrode cell with an Ag/AgCl electrode as the reference electrode, a platinum grid as the counter electrode, and a bare steel rod as the working electrode. Polarization curves were obtained after immersing the steel rod in 0.1 M NaCl solution for 2 h, with and without LDH at a concentration of 3 g L−1, using a fixed scan rate of 1 mV s−1 starting from the open circuit potential. Electrochemical impedance spectroscopy was conducted with a sinus amplitude voltage fixed at 5 mV, ranging from 100 kHz to 10 mHz. The impedance data were collected after 2, 4, 8, and 24 h of immersion. The parameters of impedance diagrams were extracted using Z-fit functions of the EC-Lab (v11.43) software. For comparison, 0.005 M Na2(BTSA) solution in NaCl 0.1 M was also used for testing. The electrode surfaces and their compositions were also observed using a JEOL JSM-IT200 associated with an EDS detector (Japan).
The morphologies of the LDH nanosheets obtained from the hydrothermal treatment at 125 °C are displayed in Fig. 2. The FE-SEM images (Fig. 2A and B) revealed that LDH has uniform particles, centered around 143.7 nm and well distributed in the range of 100–200 nm (as shown in Fig. 2F). The TEM image (Fig. 2C) demonstrated that the LDH nanosheets have the morphology of circular nanoplates with a very faint contrast, which is consistent with the ultrathin LDH sheet-like particles. In conjunction with the height profile of LDH nanosheets, the AFM results (Fig. 2D) indicated that the thickness of the nanosheets can reach 1.42 nm, but mostly sheets with a thickness of 2–3 nm were observed (Fig. 2E). Thicker plates (brighter particles on the AFM image) were observed, which may be due to the accumulation of numerous LDH platelets after sample drying, as also confirmed by FE-SEM observation (see Fig. 2B). In addition, the LDH suspension exhibited the Tyndall effect when the laser beam was incident from the side (the insert image of Fig. 2C). This indicated that the LDH nanosheets were dispersed uniformly.
In order to further tailor the particle size of the LDH nanosheets, the hydrothermal treatment temperatures were varied. Fig. 3A depicts the particle hydrodynamic size distribution of nanosheet samples. According to the DLS results, all of the LDH-Cl samples exhibited a narrow distribution and a low PI index of about 0.1–0.2 (Table S1†), indicating homogeneous dispersion in water. The average diameter of LDH-Cl increased from 77.4 to 115.4, 168.4, and 212.5, corresponding with the increase in temperature from 80 to 100, 125, and 150 °C, respectively. Compared to the LDH-Cl sample hydrothermally treated at 125 °C, the other samples showed the same morphology of a circular nanoplate (Fig. S1†). The hydrodynamic size measured by the DLS method is in good agreement with the particle size that was observed from the FE-SEM analysis. Additionally, the extremely high zeta potential, greater than +60 mV (Table S1†), indicated that the final homogeneous suspensions were stable.
| Prepared sample | Hydrothermal temperature (°C) | Zeta potential (mV) | Z-Average (nm) | PI value |
|---|---|---|---|---|
| LDH-Cl-F | — | +14.8 | 1819.8 | 0.638 |
| LDH-Cl-H | — | +45.1 | 363.8 | 0.349 |
| LDH-Cl-F | 125 | +35.2 | 245.9 | 0.531 |
| LDH-Cl-H | 125 | +73.9 | 168.4 | 0.180 |
The growth of LDH nanosheet crystallites was also determined by XRD analysis (Fig. 3D). The characteristic peak at 2θ: 11.279°, 22.643°, and 34.454° corresponding to the (003), (006), and (009) planes are collectively described at (00l) reflections, which is typical for the layered structure of LDH.36,37 The XRD patterns of the gel-like precipitated samples exhibited broad peaks for LDH-Cl-H and LDH-Cl-F. This suggested that poorly crystalline LDH phases were formed via the co-precipitation process and were unaffected by homogenization. Following hydrothermal treatment, the characteristic reflections of the (00l) and (110) peaks (at 2θ 61.509°) for LDH-Cl-F increased significantly, indicating the formation of well-crystallized LDHs and the stacking of hydroxide sheets. In contrast, the XRD result of LDH-Cl revealed a slight increase in the reflections of the (00l) peaks, but a significant increase in the reflections of the (110) peak, indicating that the growth of LDH sheets along the horizontal plane has more advantages than the growth along the c-axis. It could be explained by the high-energy surfaces of the edge sides, which promoted a higher growth rate than low-energy surfaces of the basal plane, leading to a circular shape of LDHs, as observed by the electronic microscope images (Fig. 2(A)–(C)).34 In addition, the oriented growth of individual crystals leads to the high surface charge, which can be indicated through the high zeta potential (+73.9 mV) and is sufficient to stabilize nanoparticles by electrostatic stabilization. Thus, this characteristic can contribute to preventing the stacking of hydroxide layers on each other during synthesis.
According to these findings, we hypothesized that the key to this approach relies on the well-dispersed LDH nuclei. After the nucleation stage, the amorphous phase of hydroxide layers, which consists of LDH nuclei clusters, was separated from their mother liquor and re-dispersed in water (LDH-Cl-F). Then, the weak interactions between aggregated hydroxide layers can be easily broken under the impact of hydraulic shear forces, leading to evenly dispersed LDH nuclei. The segregated LDH nuclei promoted the growth of individual crystals through the Ostwald ripening, in which the growth in the horizontal plane becomes predominant due to the high-energy surfaces at the edge sides. As a result, the LDH nanosheets are able to resist aggregation by Brownian motion and preserve the stability of the final colloidal suspension. These findings were supported by AFM results (Fig. 2D and E), which indicated that the diameter of LDH sheets (∼100 nm) is significantly greater than their thickness (∼2–3 nm). It should be noted that the thickness of MgAl hydroxide layer has been investigated in previous research at about 0.477 nm,7,38 and the basal spacing of LDH-Cl was determined from XRD results to be 0.784 nm. This implies that the prepared nanosheets consist of only a few brucite layers, which revealed the successful synthesis of ultrathin LDHs by a direct synthesis method.
The presence of BTSA in the structure of the nanocontainers was confirmed using the FTIR spectrum (Fig. 4B). A broad range between 3000 and 3750 cm−1 is observed, characterized by the prolonged OH group of hydroxide layer and water blending between 1600 and 1650 cm−1 (O–H blending) present on all of the samples.7,42 LDH-Cl exhibited a well-defined peak at a frequency of 1368 cm−1, which can be attributed to the presence of Cl− anions in the LDH structure.39 The weak absorption bands located at 2926 cm−1 and 1120 cm−1 may correspond to the C–O and C–H stretching of the lactate anion present in LDH-Cl. Additionally, the strong peak at 446 cm−1 and the wide peak at 670 cm−1 are assigned to the oscillation of Mg–OH and Al–OH of the hydroxide layer.43 As regards the pure BTSA, the peaks at about 2929 cm−1 and 756 cm−1 can be assigned to the CH group in the aromatic ring structure. Moreover, the strong peaks at 1719 cm−1 and 1423 cm−1 can be attributed to the C
O and O–H stretching of the –COOH group.44 A comparison between LDH-BTSA and pure BTSA spectra revealed the disappearance of the typical peaks of the COOH group at a frequency of 1719 cm−1, and the emergence of new peaks at around 1574 cm−1 and 1402 cm−1, which can be attributed to the asymmetric and symmetric vibrations of the COO– groups.44,45 The band characteristics of metal–O at 447 cm−1 and 674 cm−1 also remained in the spectrum of LDH-BTSA. Furthermore, the significant change in the intensity and peak position could be indicating the interaction between the organic inhibitor intercalated and the hydroxide layer of LDH.46 The combined XRD and FTIR results clearly show the successful intercalation of organic inhibitor anions to the interlayer of LDHs.
The thermal properties of LDH and BTSA were also determined by the TGA method and the resulting curves are displayed in Fig. S3.† LDH-Cl and LDH-BTSA show the same amount of water loss (absorbed and interlayer water) of approximately 10 wt% at temperatures below 200 °C. It can be seen that the pure BTSA exhibited significant degradation at about 180–280 °C, while the degradation of BTSA in LDH-BTSA was observed at 380–500 °C. This can be attributed to the lamellar structure's barrier effect, which slowed the diffusion of volatile compounds.47 Compared to the weight loss results between the two types of LDH, the BTSA content in the interlayer region of the nanocontainer was calculated to be about 36.6%.
To study the effect of anion exchange time on the nanocontainer structure, XRD analysis was performed on the sample obtained at different times of reactions (Fig. 5B). The results indicate that after one hour of reaction, the typical peak at 2θ = 5.372° due to the diffraction of the (003) plane appeared. Furthermore, at different times, the positions of the diffraction angles at the (00l) plane do not change significantly, confirming the stability of the LDH structure during the anion exchange reaction. Although it can be difficult to draw definitive conclusions about the relationship between intensity and amount in XRD, we observed that the area ratio between the diffraction peaks at (003) and (006) increased with the anion exchange time. In particular, the area of the (003) diffraction peak increased, while the (006) diffraction peak decreased. In conjunction with UV analysis results, this suggested that the increasing number of organic ingredients intercalated into the basal spacing can influence the crystallographic structure of LDHs.
In comparison with pristine LDH-Cl, the morphology of LDH-BTSA (as depicted in Fig. 6) maintained uniform particle size with a circular nanoplate shape and did not exhibit significant changes during 24 h of anion exchange. This indicated that the reaction mechanism is topotactic transformation,40 by the fact that the lateral size and distribution of the nanoplates are crucial factors in taking full advantage of the material. The disorderly growth results in high aggregation, which is the major drawback for the application of LDHs, because it impedes access to the most active sites on the surface of the crystallites, affects the diffusion of anionic species in the interlayer, and reduces the anionic exchange rate.2,14 Thus, controlling the size distribution of the nanocontainers is important to enhance the performance of the materials.
The element content in the LDH-BTSA product and precursor was determined by EDS analysis and compared in Table 2. The atomic ratios of Mg/Al are close in both cases of LDH (1.99 vs. 2.02) and similar to the molar theoretical use at synthesis (2.00). The presence of BTSA in the component of the reaction mixture does not influence the Mg/Al atomic ratio of LDH, and this can be assumed that the anion exchange reaction occurs without any further reaction, which was confirmed in XRD analysis. The S content in the LDH-BTSA is 7.56 wt%, while the S content of pristine BTSA determined by EDS is 20.13 wt%. Based on the parameters, the BTSA content in LDH-BTSA was calculated to be 37.56 wt%. This results in good agreement with the TGA and UV analyses. The small distinctions between the results obtained from different methods were insignificant and could be attributed to the specific characteristics of each method. In addition, the absence of chloride anions in the composition of LDH-BTSA indicated the complete replacement of these anions, suggesting the successful accomplishment of the anion exchange process after 24 h of reaction.
| Samples | Content (wt%) | Molar ratio | BTSA (wt%) | ||||
|---|---|---|---|---|---|---|---|
| Mg | Al | S | Cl | Mg : Al |
BTSA : Al |
||
| LDH-Cl | 20.78 ± 0.16 | 11.59 ± 0.14 | — | 11.47 ± 0.14 | 1.99 | — | — |
| LDH-BTSA | 14.73 ± 0.28 | 8.08 ± 0.23 | 7.56 ± 0.21 | — | 2.02 | 0.787 | 37.56 |
| LDH-BTSA released | 16.34 ± 0.19 | 9.00 ± 0.15 | 5.01 ± 0.06 | 2.07 ± 0.06 | 2.01 | 0.468 | 22.27 |
After 24 h of release in the NaCl solution, the LDH was collected for characterization by XRD (Fig. 7C) and FTIR (Fig. 7D) to study the structure of the nanocontainer after exposure to the corrosive medium. The position of diffraction peaks was similar except for the shift on the (003) plane. The released LDH-BTSA shows a decrease in the basal spacing (from 1.6438 nm to 1.5071 nm). This effect can be explained by the structural arrangement of the anion intercalated in the layer structure. It should be noted that the dimension of the chloride anion is less than that of the BTSA anion. This can cause a decrease in basal spacing after the release of BTSA. Furthermore, a significant decrease in the diffraction peak intensity at the (003) plane was observed. This can be explained by the reduced amount of BTSA in the layer structure of LDHs. Fig. 7D shows the FTIR comparison results of the LDH-BTSA before and after release in NaCl. After exposure to the sodium chloride solution, no significant changes were observed on the FTIR spectrum, suggesting that BTSA is still stored in the nanocontainer and an equilibrium of anion exchange was reached.46
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| Fig. 8 Polarization curve of steel electrodes after 2 hours of immersion in a 0.1 M NaCl solution without inhibitor and containing 3 g L−1 of LDH-Cl, LDH-BTSA, and 0.005 M Na2BTSA. | ||
The BTSA solution showed the lowest corrosion current density at 0.598 μA cm−2, whereas the blank solution had the highest value of 19.202 μA cm−2. This is probably due to the action of BTSA molecules, which adsorbed onto the oxide layers formed on the metal surface, leading to a reduction in the current density. The presence of BTSA in the LDH structure resulted in a corrosion current density of 1.866 μA cm−2, significantly lower than that of the sample with LDH-Cl at 12.987 μA cm−2. The inhibition efficiencies of LDH-Cl and LDH-BTSA were 32.4% and 90.3%. This significant increase could be explained by the effect of the nanocontainer, which can release organic inhibitors into the corrosive medium. Additionally, the reaction between the organic inhibitor and ferrous ions released from the electrode surface can result in forming barrier films by insoluble products on the substrate surface, which can also contribute to reducing the corrosion rate.47,51,52
The inhibition effect of the LDH with the organic inhibitor anion was also investigated by EIS measurements. Nyquist plots and Bode plots of steel electrodes after 2, 4, 8, and 24 h of immersion in 0.1 M NaCl solution are displayed in Fig. 9. In addition, the fitting parameters consisting of Rs, Rp, and Rf represented solution resistance, polarization resistance, and film resistance obtained from the impedance plots of electrodes are also presented in Table S4.† The polarization resistance (Rp) is the main parameter used to estimate the efficiency of inhibitors. The blank and LDH-Cl solutions exhibited a one-time constant; meanwhile, BTSA and LDH-BTSA solutions showed a two-time constant. This revealed the presence of protective films on the steel surface.47,51
The electrolyte resistance of testing samples is slightly changed, which could be caused by the presence of different components in the 0.1 M NaCl solution. Without inhibitors, the lowest impedance value was obtained during the test. After 2 h of exposure, the blank solution obtained Rp of 1300 Ω cm2 and showed a decreasing trend with the continuous immersion for 24 h. This indicates the degradation of the electrode surface and corresponds to the increased corrosion rate. At the beginning of the test, the LDH-Cl shows an Rp value 1571 Ω cm2, higher than that of the blank solution, which can be explained by the deposition of lamellar structures on the steel surface to form barriers at the defect sites of the electrode. However, Rp not only insignificantly increases in the case of continuous immersion but also reduces to a low value at the end of the test. This is attributed to the low thickness and porous structure of the precipitated layer by the LDH.53 In other words, LDH-Cl is limited to performing an anion exchange reaction with chloride anions. Thus, they present limited inhibitive behavior.
The sample testing in the presence of 0.005 M BTSA anion shows the highest Rp value at 14
190 Ω cm2. Nevertheless, the Rp value showed a significant decrease trend during the increasing time of immersion. In contrast, the samples of LDH-BTSA are associated with different processes. After 2 h of immersion, the LDH-BTSA solution exhibited a high Rp value of 6905 Ω cm2, suggesting that the intercalated BTSA is highly effective. The Rp value continuously increased to 9703 Ω cm2 and 11
271 Ω cm2, corresponding to 4 and 8 h of exposure. This is attributed to the large number of BTSA anions released from the nanocontainer to the corrosive medium, and as a result, the corrosion rate was reduced. This phenomenon indicates the effect of nanocontainers loaded with organic inhibitors with the advantage of the controlled release of organic inhibitors for maintaining the stability of inhibitor efficiency over time. As the immersion time increased to 24 h, the Rp value decreased but remained at a high value of about 3270 Ω cm2. This can be attributed to the inhibitor molecules being consumed on the metal surface. After 24 h of immersion, the Bode plots showed that the phase angle of LDH-BTSA showed a minimum value of −56°, which was shifted to a higher frequency than that of the other samples. In addition, the two-time constant was exhibited, which revealed the formation of barrier films on the steel surface, which can be used to explain the anodic behavior of the inhibitor.47,51,54 The Rf value is attributed to the film resistance deposition on the steel electrode surface. With the increasing immersion time, Rf values of the samples with BTSA show a more declining trend than that of the samples with LDH-BTSA. This indicates that the barrier films former by LDH-BTSA are more stable than free BTSA. After 24 h, Rf was determined to be about 94.3 Ω cm2 and 135.8 Ω cm2 corresponding to samples of BTSA and LDH-BTSA. The higher Rf value of LDH-BTSA could be explained by the large numbers of nanocontainers deposited on the steel surface.
| Samples | Element content (wt%) | |||||||
|---|---|---|---|---|---|---|---|---|
| Fe | O | C | Mg | Al | S | N | ||
| Blank | Surface | 69.28 | 28.49 | 2.23 | — | — | — | — |
| Particles (1) | 56.10 | 40.08 | 3.82 | — | — | — | — | |
| LDH-BTSA | Surface | 43.34 | 24.41 | 14.49 | 8.35 | 4.15 | 2.45 | 1.79 |
| Particles (2) | 17.05 | 39.57 | 23.34 | 7.29 | 3.52 | 5.84 | 2.69 | |
In addition to LDH-BTSA, the substrate's surface was covered by the lamellar structure of LDH, and the corrosion products as iron oxide crystals disappeared (Fig. S4(C) and (D)†). This indicated the efficiency of the anti-corrosion properties of LDH-BTSA. Some elements, such as the fingerprint of the nanocontainer as Mg, Al, and S, were also detected, which further confirms the deposition of the nanocontainers on the surface of the electrode. The element content of Fe, Mg, Al, and S was 43.34%, 8.35%, 4.15%, and 2.45%, respectively. Besides the presence of LDH covering the electrode surface, other components are observed in this case (see Fig. 9D). The EDS analysis revealed that the detected particles had lower contents of Fe, Mg, and Al of about 17.05%, 7.29% and 3.52%, respectively, but a higher content of S element of 5.84% compared to the surface. It should be noted that the organic molecules released can adsorb onto metal surfaces and form coordination bonds based on the lone pair electrons of nitrogen and sulfur atoms in BTSA molecules.19,55 Thus, we postulated the presence of complex products, which formed from the reaction between BTSA released and ferrous ions, leading to the formation of insoluble products on the steel surface.
The findings from SEM/EDS analysis supported the results of the study on the corrosion inhibition efficiency of LDH-BTSA, as observed in the electrochemical measurements. The release of BTSA and its interaction with the steel surfaces resulted in the formation of insoluble species, which combined with the deposition of a lamellar structure of LDH onto the steel substrates. This formed a barrier that effectively blocked the invasion of aggressive Cl− anions, resulting in high levels of protection.
Footnote |
| † Electronic supplementary information (ESI) available. See DOI: https://doi.org/10.1039/d3na00570d |
| This journal is © The Royal Society of Chemistry 2024 |