Hostname: page-component-cd9895bd7-dk4vv Total loading time: 0 Render date: 2024-12-24T03:41:54.082Z Has data issue: false hasContentIssue false

Modification of Halloysite Nanotubes for Enhancement of Gas-Adsorption Capacity

Published online by Cambridge University Press:  01 January 2024

Sungho Lim
Affiliation:
Department of Chemistry and Research Institute for Convergence of Basic Science, Hanyang University, Seoul 04763, Korea
Sooji Park
Affiliation:
Department of Chemistry and Research Institute for Convergence of Basic Science, Hanyang University, Seoul 04763, Korea
Daewon Sohn*
Affiliation:
Department of Chemistry and Research Institute for Convergence of Basic Science, Hanyang University, Seoul 04763, Korea
*
*E-mail address of corresponding author: [email protected]
Rights & Permissions [Opens in a new window]

Abstract

Structure control and quantitative evaluation of porous materials are essential for many industrial and consumer applications of clay minerals, and nanotubular halloysite (HNT) has been used extensively for such purposes; performance enhancements are still needed, however. The objective of the present study was to improve the gas-adsorption capacity of HNT by controlling the particle size and porosity. This was accomplished through acid treatment and particle-size fractionation by centrifugation. Various particle sizes were obtained and porosities ranged from macropores to mesopores. Natural halloysite nanotubes were modified by sulfuric acid in various concentrations to selectively remove the alumina composition of the tubes. X-ray diffraction and energy dispersive X-ray spectroscopy were used to verify the mineralogical and compositional changes. Surface modification by the acid treatment increased the inner space volume of the tubes and decreased the mass of the nanotubes because of the elimination of alumina. The gas adsorption capacity of both natural and modified halloysite nanotubes was measured quantitatively using N2 adsorption and the Brunauer-Emmett-Teller (BET) method, and the morphology was determined from transmission electron microscopy (TEM) images. The results showed that the modified halloysite nanotube was 7.47 times more efficient at gas adsorption than pristine halloysite. Moreover, the dealumination of the surface increased the inner space. Greatly increased porosity characteristics, including gas adsorption and macroporosity, were obtained through modification by acid treatment.

Type
Article
Copyright
Copyright © Clay Minerals Society 2020

Introduction

Halloysite is a natural aluminosilicate nanotube with the formula Al2Si2O5(OH)4, a kaolin mineral. This clay material has tube walls that are 20–30 layers thick, with each layer consisting of one alumina (Al-OH) sheet and one siloxane (Si-O-Si) sheet (a one-to-one ratio), thus forming multiple inorganic walls. The inner wall surface is composed of alumina units, and the outer surface area is made of siloxane units. The diameter of the lumen (hollow space or channel inside the tube) ranges from 20 to 30 nm and the outer diameter from 50 to 100 nm (Tazaki Reference Tazaki2005; Kamble et al. Reference Kamble, Ghag, Gaikawad and Panda2012; Joo et al. Reference Joo, Sim, Jeon, Lee and Sohn2013; Lvov et al. Reference Lvov, Wang, Zhang and Fakhrullin2016).

Halloysite nanotubes (HNTs) are of great interest due to their porosity as tubular structures, having specific mesoporosity (<50 nm) and macroporosity (>50 nm) characteristics (Shu et al. Reference Shu, Chen, Zhou, Li, Yu and Wang2015). These nano spaces have great potential for use in the creation of nanocomposites in clay materials.

HNTs are utilized frequently as additives to other materials (Mroczek et al. Reference Mroczek, Kalisz, Pronobis and Sołtys2011; Hong et al. Reference Hong, Liu and Choi2013). Owing to their tubular shape with a hollow inside, they can be used as carriers (Shi et al. Reference Shi, Tian, Zhang, Shen and Jia2011; Tan et al. Reference Tan, Yuan, Annabi-Bergaya, Yu, Liu, Liu and He2013; Owoseni et al. Reference Owoseni, Nyankson, Zhang, Adams, He, McPherson, Bose, Gupta and John2014; Gorrasi Reference Gorrasi2015) or nanoreactors (Ko et al. Reference Ko, Lee, Yoo, Ryu and Sohn2016). The confinement of nanomaterials in nanotube formations generates nanoscale reactions (Abdullayev et al. Reference Abdullayev, Sakakibara, Okamoto, Wei, Ariga and Lvov2011; Lazzara et al. Reference Lazzara, Cavallaro, Panchal, Fakhrullin, Stavitskaya, Vinokurov and Lvov2018). Various studies on surface modification aimed at utilizing the lumen have been reported (Yah et al. Reference Yah, Takahara and Lvov2012a, Reference Yah, Xu, Soejima, Ma, Lvov and Takahara2012b; Chao et al. Reference Chao, Liu, Wang, Zhang, Zhang, Zhang, Xiang and Chen2013; De Silva et al. Reference De Silva, Pasbakhsh, Goh, Chai and Ismail2013; Wu et al. Reference Wu, Watanabe, Ma, Fujimoto, Higuchi, Uesugi, Takeuchi, Suzuki, Jinnai and Takahara2013, Reference Wu, Liu, Qi, Zhang, Dai, Zhang, Zhang, Wu and Peng2016; Szczepanik et al. Reference Szczepanik, Słomkiewicz, Garnuszek, Rogala, Banaś, Kubala-Kukuś and Stabrawa2017). HNT nanocomposites are useful for remedying the shortcomings of base materials. The eco-friendly and biocompatible properties of HNTs are likewise important characteristics (Vergaro et al. Reference Vergaro, Abdullayev, Lvov, Zeitoun, Cingolani, Rinaldi and Leporatti2010; Liu et al. Reference Liu, Zhang, Wu, Xiong and Zhou2012; Lvov et al. Reference Lvov, Aerov and Fakhrullin2014; Massaro et al. Reference Massaro, Riela, Cavallaro, Gruttadauria, Milioto, Noto and Lazzara2014). These properties, which provide great advantages in applied research, originate from the aluminosilicate composition, which is not harmful to organisms or to the natural environment. Various studies have utilized this biocompatibility for drug-delivery systems and the controlled release of medicines (Guo et al. Reference Guo, Wang, Muhammad, Qi, Ren, Guo and Zhu2012; Xi et al. Reference Xi, Xiaojie, Rui, Jiang, Jie and Liangyin2013).

Because the lumen is the main reason for the interest in using HNTs in applied research, detailed analysis of these nano spaces is necessary. Although natural, meaning unmodified, HNTs have adequate inner space volume to put various chemicals in the tube, the gas adsorption capacity and the surface area can be increased significantly by modifying the HNTs. The alumina composition of HNTs can be removed by sulfuric acid, because sulfuric acid selectively reacts with only the alumina sheets (Abdullayev et al. Reference Abdullayev, Joshi, Wei, Zhao and Lvov2012; Zhang et al. Reference Zhang, Pan, Zhang, Liu, Ye, Xia and Chen2012).

The purpose of the present study was to chemically modify the HNTs by treatment with sulfuric acid in an effort to enhance the storage efficiency of the tubes and to quantify the gas-adsorption capacity, then to compare the lumen surface area of the sulfuric-acid-modified HNTs with that of unmodified HNTs.

EXPERIMENTAL

Materials

HNTs were obtained from Applied Minerals Inc. (New York, USA). Sodium hexametaphosphate (Junsei Co., Tokyo, Japan, 97% purity) and sulfuric acid (Daejung Co., Seoul, Korea, 98% purity) were used without further purification.

Modification of Natural HNTs

A 1.5 g portion of HNT was mixed with 50 mL of 1 M, 3 M, or 5 M sulfuric acid solution in a flask. The HNT was well dispersed in the acid solution by bath-type sonication for 20 min. An aspirator was used to remove atmospheric gases from the lumen of the tubes. As a result, the sulfuric acid solution from the flask filled the lumen of the halloysite nanotubes, and chemical reactions occurred to remove the alumina composition of the HNT. The flask was heated at 90°C for 24 h to react the sulfuric acid with the aluminum of the HNT (Abdullayev et al. Reference Abdullayev, Joshi, Wei, Zhao and Lvov2012). After reaction, the HNT modified by the 1 M, 3 M, and 5 M sulfuric acid were labeled “yHNT (x M)”, where y is the modification and x is 1, 3, or 5, depending on which sulfuric acid concentration was used. The sample was then washed with DI water 5 times, placed in a freezer for 6 h, and freeze dried for 3 days.

Purification and Separation of Natural HNTs

Purification of the unmodified HNTs followed the method introduced by Luo et al. (Reference Luo, Song, Feng, Run, Cui, Wu, Gao and Wang2013). 25 g of HNT was suspended in 100 mL of DI water by stirring for 2 h; then 2 g of sodium hexametaphosphate (SHMP) was added gradually to enhance dispersion. The system was then stirred for an additional 24 h and left to stand at room temperature for 6 h to allow solids to settle. The supernatant was decanted and discarded to remove readily soluble impurities. The remaining solid was then separated into various size fractions by centrifugation as follows. The sediment was resuspended in water then centrifuged at 2000 rpm (431×g) for 5 min and the supernatant collected and labeled HNT-1. The sediment was again resuspended in water and centrifuged at 4000 rpm (1722×g) for 10 min and the supernatant decanted and labeled HNT-2. These steps were repeated at 6000 rpm (3875×g), 8000 rpm (6888×g), and 10,000 rpm (10,763×g) to obtain samples labeled HNT-3, HNT-4, and HNT-5, respectively. This was repeated for each HNT specimen. Each such particle-size fractionation yielded tubes with different average lengths and outer and inner diameters (Table 4).

Acid Modification of HNT

A 0.5 g portion of each mHNT-x (m = modification; x = 1–5) sample was mixed with 16.7 mL of 5 M sulfuric acid in a flask and further dispersed by vortex mixing and sonication. The suspension was then aspirated to remove dissolved gases in the HNT suspension in order to facilitate the entrance of sulfuric acid solution into the lumen, thereby enabling reaction between the sulfuric acid and the Al in the tetrahedral sheet of the HNT inner wall. The reaction was further promoted by heating the suspensions at 90°C for 24 h. They were then cooled, washed five times with DI water, and freeze-dried. The process was repeated for all HNTs.

RESULTS AND DISCUSSION

Modification of Natural HNTs

The porosities and surface areas of the HNTs were measured using N2 adsorption. The volume of adsorbed gas at standard state (STP: T = 273.15 K, 101.3 kPa) per g of sample, represented by V a, was measured by the Brunauer-Emmett-Teller (BET) method using a Belsorp-Mini II device (MicrotracBEL Corp., Osaka, Japan). Adsorption of volumetric N2 proceeded on unmodified and modified HNTs. The N2 gas-adsorption capacity of the unmodified HNT was 163.74 cm3 (STP)/g. The isotherm type was IUPAC type IV, revealing pore sizes in the mesoporous and macroporous ranges, but not in the microporous range. In the case of mHNTs (1 M), the value of V a was 471.14 cm3 (STP)/g; for mHNTs (3 M), 746.75 cm3 (STP)/g. The value of V a for mHNTs (5 M) was 837.31 cm3 (STP)/g, which is 5.11 times greater than for the natural HNTs (Table 1). All modified HNTs exhibited morphologies and plot shapes that follow the IUPAC type IV isotherms, similar to the natural HNTs.

Table 1 Adsorbed gas volume (V a), specific surface area (S BET), and total pore volume (V total) of natural HNT, mHNT (1 M), mHNT (3 M), and mHNT (5 M).

The thickness of the adsorption layer is defined as t = 0.354×V a/V m [nm]. The value of 0.354 comes from the assumption that the thickness of a single layer of N2 molecules is 0.354 nm (Lippens and De Boer Reference Lippens and De Boer1965; Kaneko Reference Kaneko1994). According to one hypothesis, adsorbed N2 molecules form an hexagonally close-packed layer on the solid surface (Schull Reference Schull1948). The linear-like graph shapes of the samples in Fig. 1b, which increase at the same rate as standard isotherms, means that they have macroporous characteristics. The graphs of the modified HNTs have a steeper slope than those for unmodified HNTs. This is because the V m values, which indicate the monolayer volume of the samples, are larger in the modified HNTs. The V a value of mHNTs (5 M) at 1.2 nm of pore thickness was 270.17 cm3 (STP)/g, which is 8.5 times larger than the V a value of the natural HNTs of 31.703 cm3 (STP)/g at 1.2 nm. The modified HNTs had a larger capacity for gas-adsorption than the natural HNTs.

Fig. 1 a N2 adsorption isotherms and b thickness plots of natural HNT, mHNT (1 M), mHNT (3 M), and mHNT (5 M).

The internal structures of the natural HNTs and the mHNTs were revealed by transmission electron microscopy (TEM, JEOL JEM-2100F, Tokyo, Japan) (Fig. 2). A clear crystal morphology with a relatively small lumen diameter in the natural HNTs was verified. In contrast, the mHNTs lost their crystallinity after dealumination, and their lumen diameter was expanded.

Fig. 2 TEM images of: a natural HNT, b mHNT (1 M), c mHNT (3 M), d mHNT (5 M).

The crystallinities of both natural HNTs and modified HNTs were analyzed using X-ray diffraction (XRD). The diffraction patterns of natural HNTs have a monoclinic-domatic crystallographic character. The characteristic sharp peak at 12°2θ (Fig. 3) corresponding to the (001) reflection occurred due to the HNT multiwall reflection (Costanzo and Glese Reference Costanzo and Giese1985; Guimaraes et al. Reference Guimaraes, Enyashin, Seifert and Duarte2010). Modified HNTs lost the characteristic peaks in the corresponding 2θ region, however. Instead of the sharp peaks indicating alumina crystals, modified HNTs showed a broad band observed at ~20–25°2θ. This means that the aluminosilicate composition of the natural HNTs was changed to amorphous silica by acid modification.

Fig. 3 XRD traces of natural HNT and mHNT (5 M).

Energy-dispersive X-ray spectroscopy (EDS) mapping was used to track changes in elemental composition and to verify structural changes during acid modification. Comparison of unmodified and modified HNTs (Fig. 4) revealed that the unmodified HNT was composed of evenly combined and distributed Al, Si, and O, whereas EDS mapping of the mHNTs (5 M) sample revealed that most of the Al was lost but the morphology of the silica structure remained.

Fig. 4 EDS mapping images of a natural HNT and b mHNT (5 M).

Modification of Separated HNTs

The five particle-size fractions of the unmodified HNT (using the BET method) yielded similar shapes in their gas-adsorption isotherms (type IV), as would be expected because of their similar atomic compositions and morphologies. A notable difference, however, was in the value of V a, which is a reflection of characteristics such as size, mass, and porosity. The samples showed a consistent tendency of increasing V a, except for HNT-5, which was assumed to differ because of an imperfect structure in the tubes that hindered gas adsorption.

The largest value for V a was 226.43 cm3 (STP)/g, for HNT-4. This was 1.74 times larger than the smallest V a value, which was exhibited by HNT-1 (130.37 cm3 (STP)/g. Another trend was that the adsorption capacity increased consistently in the lower p/p 0 range, from HNT-1 to HNT-5 (Table 2).

Table 2 Adsorbed-gas volume (V a), specific surface area (S BET), and total pore volume (V total) of 5 groups of natural HNTs.

Compared to those of unmodified HNTs (Fig. 5a), the adsorption isotherms of the five particle-size fractions of the acid-modified HNTs revealed a consistent tendency for the V a value to decrease as the particle size became smaller (Fig. 5b). The largest V a was 1223.1 cm3 (STP)/g, for mHNT-5, which was 5.6 times larger than for HNT-5 before acid treatment (Tables 2 and 3). The results showed that the modification of halloysite nanotubes increased the gas-adsorption efficiency of the unmodified halloysite by a factor of 7.47 (1223.1/163.74) (Tables 1 and 3). Overall, acid modification of the HNT increased its porosity, gas-adsorption capacity, and macroporosity. The smallest value for V a among the mHNT samples was 638.84 cm3 (STP)/g for mHNT-1, which is 4.9 times larger than for HNT-1. Both acid activation and smaller particle size improved the gas-adsorption capacity of HNT tubular materials, therefore.

Fig. 5 Adsorption isotherms of five groups of: a natural HNT, b mHNT (5 M).

Table 3 Adsorbed gas volume (V a), specific surface area (S BET), and total pore volume (V total) of five groups of mHNTs (5 M).

The porosity distributions of the HNTs were plotted using the Barrett-Joyner-Halenda (BJH) method. Adsorbents that have type IV adsorption isotherms can be characterized by BJH adsorption-desorption plots (Luan et al. Reference Luan, He, Zhou, Cheng and Klinowski1995; Baiju et al. Reference Baiju, Shukla, Biju, Reddy and Warrier2009). Hysteresis, the difference between adsorption and desorption curves, occurs due to capillary condensation of N2 gas in the mesopores of the materials (Barrett et al. Reference Barrett, Joyner and Halenda1951). The desorption isotherm of the material and the Kelvin equation (Eq. 1) demonstrate the relationships between critical condensation pressure and pore size and were used to calculate the pore-size distribution in the BJH plots (Schull Reference Schull1948).

(1) ln p p 0 = 2 γ V L R T r m

where p is equilibrium pressure in pores with a radius r m; p 0, pressure on the planar surface; γ, the surface tension; V L, the molar volume; R, the gas constant; and T, the absolute temperature. The cumulative pore-volume graph was obtained for various pore volumes. The observed tendency (Fig. 6a) was that the pore size decreased from HNT-1 to HNT-5. Samples HNT-1 and HNT-2 were macroporous, whereas HNT-3, HNT-4, and HNT-5 were mesoporous. HNT-1 exhibited the tallest peak at d p = 70 nm, revealing obvious microporous behavior. On the other hand, sample HNT-5 was mesoporous because the porosity distribution was clearly <50 nm. Because the volume distributions of HNT-4 and HNT-5 were close to 0 with a porosity distribution >50 nm, these samples were non-macroporous tubes.

Fig. 6 BJH plots of 5 groups of: a natural HNT, b mHNT (5 M).

Plots of the BJH curves for the five groups of modified HNTs (Fig. 6b) revealed that the porosities of all natural HNTs were expanded by sulfuric acid modification. The pore sizes of samples mHNT-3, mHNT-4, and mHNT-5 (on the right side of Fig. 6b) compared to those of the natural HNTs groups were enlarged from mesopores to macropores.

Regarding pore-thickness curves of the separated HNTs7, the slopes of the curves increased with decreasing particle size (Fig. 7a). This indicates that samples separated later had larger V m values and gas-adsorption efficiencies. The gas adsorption of mHNT-5 at 1.2 nm pore thickness was 83.816 cm3 (STP)/g, which is 2.98 times greater than the corresponding value for the mHNT-1, 28.313 cm3 (STP)/g.

Fig. 7 Thickness plots of five groups of: a natural HNT, b mHNT (5 M).

The thickness plot patterns of the modified HNTs were similar to those of the unmodified HNTs (Fig. 7b). The inclination increased according to the order of separation, because the samples separated later had larger V m values and gas-adsorption efficiencies. The gas-adsorption of mHNT-5 at 1.2 nm pore thickness was 191.81 cm3 (STP)/g, which is 1.52 times greater than that of mHNT-1, which was 125.87 cm3 (STP)/g.

Transmission electron microscopy images of natural and modified HNTs (Fig. 8, Table 4) were used to determine the average lengths and outer and inner diameters of the HNTs. The TEM images were also utilized to compare the relative differences between the five difference sizes of natural HNTs. The size of the nanotubes tended to decrease with increasing centrifugal force. The nanotube groups were not clearly divided in terms of gas-adsorption capacity because the separation of HNTs was affected by various factors such as mass, hydrophilicity, and the size of each particle.

Fig. 8 TEM images of natural HNT groups: a HNT-1, b HNT-2, c HNT-3, d HNT-4, e HNT-5. TEM images of modified HNT groups: f mHNT-1, g mHNT-2, h mHNT-3, i mHNT-4, j mHNT-5.

Table 4. Average lengths and outer (O.D.) and inner (I.D.) diameters of the HNTs.

The largest contribution to separation was assumed to be the mass of the particles. Because the atomic composition of each halloysite is almost the same, as the HNT particle size decreased, the mass of the particle would be decreased proportionally. Therefore, in principle, the gas adsorption capacity of the tubes is inversely proportional to the size of the particles.

HNT-5 had nano-size debris (Fig. 8e). The hindrance of gas-adsorption for this sample was because of these light nanotube fragments that were mixed with the intact tubes.

Separated samples of modified HNTs are shown in Fig. 8f–j. They exhibited an increasing gas-adsorption tendency with separation process; the size of the nanotubes decreased according to the order of separation. Therefore, the assumption that the gas-adsorption capacity is inversely proportional to the mass or size of the particles is applied from the same perspective as with separated natural HNTs. The fragments of nanotubes are detectable in the mHNT-5 sample also (Fig. 8j). These experiments demonstrated that the porosity of halloysite nanotubes could be increased by selection of a small size and acid treatment.

SUMMARY

Sulfuric acid was used to increase the porosity of halloysite nanotubes by etching the lumen of the HNT. Modified HNTs were prepared successfully using various concentrations of sulfuric acid. The chemical compositions of modified HNTs were verified by XRD and EDX spectroscopy. This modification selectively removed alumina from the tubes, and decreased the mass of the tubes. Furthermore, the porosity and the inner space of the tubes were clearly increased. The transformation of the tubes increased significantly the gas-adsorption efficiency of the HNTs. The dealumination of the surface increased the inner space, which is very effective for storing other materials within the tubes. The size of the lumen of the modified HNTs was verified by BJH plots and thickness plots. Thus, more materials could be loaded into the HNT tubes. In addition, the separation of smaller HNTs by centrifugation provided an opportunity to maximize the gas-adsorption capacity by excluding low-efficiency groups.

ACKNOWLEDGMENTS

This work was supported by a National Research Foundation of Korea grant (NRF-2019R1F1A1056947).

Compliance with Ethical Statements

Conflict of Interest

The authors declare that they have no conflict of interest.

Footnotes

(AE: Jun Kawamata)

References

Abdullayev, E., Sakakibara, K., Okamoto, K., Wei, W., Ariga, K., & Lvov, Y. (2011). Natural tubule clay template synthesis of silver nanorods for antibacterial composite coating. ACS Applied Materials & Interfaces, 3, 40404046.CrossRefGoogle ScholarPubMed
Abdullayev, E., Joshi, A., Wei, W., Zhao, Y., & Lvov, Y. (2012). Enlargement of halloysite clay nanotube lumen by selective etching of aluminum oxide. ACS Nano, 6, 72167226.CrossRefGoogle ScholarPubMed
Baiju, K., Shukla, S., Biju, S., Reddy, M., & Warrier, K. (2009). Hydrothermal processing of dye-adsorbing one-dimensional hydrogen titanate. Materials Letters, 63, 923926.CrossRefGoogle Scholar
Barrett, E. P., Joyner, L. G., & Halenda, P. P. (1951). The determination of pore volume and area distributions in porous substances. I. Computations from nitrogen isotherms. Journal of the American Chemical Society, 73, 373380.CrossRefGoogle Scholar
Chao, C., Liu, J., Wang, J., Zhang, Y., Zhang, B., Zhang, Y., Xiang, X., & Chen, R. (2013). Surface modification of halloysite nanotubes with dopamine for enzyme immobilization. ACS Applied Materials & Interfaces, 5, 1055910564.CrossRefGoogle ScholarPubMed
Costanzo, P., & Giese, R. (1985). Dehydration of synthetic hydrated kaolinites: a model for the dehydration of halloysite (10 Å). Clays and Clay Minerals, 33, 415423.CrossRefGoogle Scholar
De Silva, R., Pasbakhsh, P., Goh, K., Chai, S.-P., & Ismail, H. (2013). Physico-chemical characterisation of chitosan/halloysite composite membranes. Polymer Testing, 32, 265271.CrossRefGoogle Scholar
Gorrasi, G. (2015). Dispersion of halloysite loaded with natural antimicrobials into pectins: characterization and controlled release analysis. Carbohydrate Polymers, 127, 4753.CrossRefGoogle ScholarPubMed
Guimaraes, L., Enyashin, A. N., Seifert, G., & Duarte, H. A. (2010). Structural, electronic, mechanical properties of single-walled halloysite nanotube models. Journal of Physical Chemistry C, 114, 1135811363.CrossRefGoogle Scholar
Guo, M., Wang, A., Muhammad, F., Qi, W., Ren, H., Guo, Y., & Zhu, G. (2012). Halloysite nanotubes, a multifunctional nanovehicle for anticancer drug delivery. Chinese Journal of Chemistry, 30, 21152120.CrossRefGoogle Scholar
Hong, C. H., Liu, Y. D., & Choi, H. J. (2013). Carbonyl iron suspension with halloysite additive and its magnetorheology. Applied Clay Science, 80, 366371.CrossRefGoogle Scholar
Joo, Y., Sim, J. H., Jeon, Y., Lee, S. U., & Sohn, D. (2013). Opening and blocking the inner-pores of halloysite. Chemical Communications, 49, 45194521.CrossRefGoogle ScholarPubMed
Kamble, R., Ghag, M., Gaikawad, S., & Panda, B. K. (2012). Halloysite nanotubes and applications: a review. Journal of Advanced Scientific Research, 3, 2529.Google Scholar
Kaneko, K. (1994). Determination of pore size and pore size distribution: 1. Adsorbents and catalysts. Journal of Membrane Science, 96, 5989.CrossRefGoogle Scholar
Ko, J., Lee, J., Yoo, B., Ryu, J., & Sohn, D. (2016). Capillarity-induced selective ex-situ synthesis of metal–organic framework inside mesoporous nanotubes. Microporous and Mesoporous Materials, 220, 1620.CrossRefGoogle Scholar
Lazzara, G., Cavallaro, G., Panchal, A., Fakhrullin, R., Stavitskaya, A., Vinokurov, V., & Lvov, Y. (2018). An assembly of organic-inorganic composites using halloysite clay nanotubes. Current Opinion in Colloid & Interface Science, 35, 4250.CrossRefGoogle Scholar
Lippens, B. C., & De Boer, J. (1965). Studies on pore systems in catalysts: V. The t method. Journal of Catalysis, 4, 319323.CrossRefGoogle Scholar
Liu, M., Zhang, Y., Wu, C., Xiong, S., & Zhou, C. (2012). Chitosan/halloysite nanotubes bionanocomposites: structure, mechanical properties and biocompatibility. International Journal of Biological Macromolecules, 51, 566575.CrossRefGoogle ScholarPubMed
Luan, Z., He, H., Zhou, W., Cheng, C.-F., & Klinowski, J. (1995). Effect of structural aluminium on the mesoporous structure of MCM-41. Journal of the Chemical Society, Faraday Transactions, 91, 29552959.CrossRefGoogle Scholar
Luo, Z., Song, H., Feng, X., Run, M., Cui, H., Wu, L., Gao, J., & Wang, Z. (2013). Liquid crystalline phase behavior and sol–gel transition in aqueous halloysite nanotube dispersions. Langmuir, 29, 1235812366.CrossRefGoogle ScholarPubMed
Lvov, Y., Aerov, A., & Fakhrullin, R. (2014). Clay nanotube encapsulation for functional biocomposites. Advances in Colloid and Interface Science, 207, 189198.CrossRefGoogle ScholarPubMed
Lvov, Y., Wang, W., Zhang, L., & Fakhrullin, R. (2016). Halloysite clay nanotubes for loading and sustained release of functional compounds. Advanced Materials, 28, 12271250.CrossRefGoogle ScholarPubMed
Massaro, M., Riela, S., Cavallaro, G., Gruttadauria, M., Milioto, S., Noto, R., & Lazzara, G. (2014). Eco-friendly functionalization of natural halloysite clay nanotube with ionic liquids by microwave irradiation for Suzuki coupling reaction. Journal of Organometallic Chemistry, 749, 410415.CrossRefGoogle Scholar
Mroczek, K., Kalisz, S., Pronobis, M., & Sołtys, J. (2011). The effect of halloysite additive on operation of boilers firing agricultural biomass. Fuel Processing Technology, 92, 845855.CrossRefGoogle Scholar
Owoseni, O., Nyankson, E., Zhang, Y., Adams, S. J., He, J., McPherson, G. L., Bose, A., Gupta, R. B., & John, V. T. (2014). Release of surfactant cargo from interfacially-active halloysite clay nanotubes for oil spill remediation. Langmuir, 30, 1353313541.CrossRefGoogle ScholarPubMed
Schull, C. (1948). The determination of pore size distribution from gas adsorption data. Journal of the American Chemical Society, 70, 14051410.CrossRefGoogle Scholar
Shi, Y.-F., Tian, Z., Zhang, Y., Shen, H.-B., & Jia, N.-Q. (2011). Functionalized halloysite nanotube-based carrier for intracellular delivery of antisense oligonucleotides. Nanoscale Research Letters, 6, 608.CrossRefGoogle ScholarPubMed
Shu, Z., Chen, Y., Zhou, J., Li, T., Yu, D., & Wang, Y. (2015). Nanoporous-walled silica and alumina nanotubes derived from halloysite: controllable preparation and their dye adsorption applications. Applied Clay Science, 112, 1724.CrossRefGoogle Scholar
Szczepanik, B., Słomkiewicz, P., Garnuszek, M., Rogala, P., Banaś, D., Kubala-Kukuś, A., & Stabrawa, I. (2017). Effect of temperature on halloysite acid treatment for efficient chloroaniline removal from aqueous solutions. Clays and Clay Minerals, 65, 155167.CrossRefGoogle Scholar
Tan, D., Yuan, P., Annabi-Bergaya, F., Yu, H., Liu, D., Liu, H., & He, H. (2013). Natural halloysite nanotubes as mesoporous carriers for the loading of ibuprofen. Microporous and Mesoporous Materials, 179, 8998.CrossRefGoogle Scholar
Tazaki, K. (2005). Microbial formation of a halloysite-like mineral. Clays and Clay Minerals, 53, 224233.CrossRefGoogle Scholar
Vergaro, V., Abdullayev, E., Lvov, Y. M., Zeitoun, A., Cingolani, R., Rinaldi, R., & Leporatti, S. (2010). Cytocompatibility and uptake of halloysite clay nanotubes. Biomacromolecules, 11, 820826.CrossRefGoogle ScholarPubMed
Wu, H., Watanabe, H., Ma, W., Fujimoto, A., Higuchi, T., Uesugi, K., Takeuchi, A., Suzuki, Y., Jinnai, H., & Takahara, A. (2013). Robust liquid marbles stabilized with surface-modified halloysite nanotubes. Langmuir, 29, 1497114975.CrossRefGoogle ScholarPubMed
Wu, X., Liu, C., Qi, H., Zhang, X., Dai, J., Zhang, Q., Zhang, L., Wu, Y., & Peng, X. (2016). Synthesis and adsorption properties of halloysite/carbon nanocomposites and halloysite-derived carbon nanotubes. Applied Clay Science, 119, 284293.CrossRefGoogle Scholar
Xi, L., Xiaojie, J., Rui, X., Jiang, M., Jie, W., & Liangyin, C. (2013). Halloysite nanotube composited thermo-responsive hydrogel system for controlled-release. Chinese Journal of Chemical Engineering, 21, 991998.Google Scholar
Yah, W. O., Takahara, A., & Lvov, Y. M. (2012a). Selective modification of halloysite lumen with octadecylphosphonic acid: new inorganic tubular micelle. Journal of the American Chemical Society, 134, 18531859.CrossRefGoogle ScholarPubMed
Yah, W. O., Xu, H., Soejima, H., Ma, W., Lvov, Y., & Takahara, A. (2012b). Biomimetic dopamine derivative for selective polymer modification of halloysite nanotube lumen. Journal of the American Chemical Society, 134, 1213412137.CrossRefGoogle ScholarPubMed
Zhang, A.-B., Pan, L., Zhang, H.-Y., Liu, S.-T., Ye, Y., Xia, M.-S., & Chen, X.-G. (2012). Effects of acid treatment on the physico-chemical and pore characteristics of halloysite. Colloids and Surfaces A: Physicochemical and Engineering Aspects, 396, 182188.CrossRefGoogle Scholar
Figure 0

Table 1 Adsorbed gas volume (Va), specific surface area (SBET), and total pore volume (Vtotal) of natural HNT, mHNT (1 M), mHNT (3 M), and mHNT (5 M).

Figure 1

Fig. 1 a N2 adsorption isotherms and b thickness plots of natural HNT, mHNT (1 M), mHNT (3 M), and mHNT (5 M).

Figure 2

Fig. 2 TEM images of: a natural HNT, b mHNT (1 M), c mHNT (3 M), d mHNT (5 M).

Figure 3

Fig. 3 XRD traces of natural HNT and mHNT (5 M).

Figure 4

Fig. 4 EDS mapping images of a natural HNT and b mHNT (5 M).

Figure 5

Table 2 Adsorbed-gas volume (Va), specific surface area (SBET), and total pore volume (Vtotal) of 5 groups of natural HNTs.

Figure 6

Fig. 5 Adsorption isotherms of five groups of: a natural HNT, b mHNT (5 M).

Figure 7

Table 3 Adsorbed gas volume (Va), specific surface area (SBET), and total pore volume (Vtotal) of five groups of mHNTs (5 M).

Figure 8

Fig. 6 BJH plots of 5 groups of: a natural HNT, b mHNT (5 M).

Figure 9

Fig. 7 Thickness plots of five groups of: a natural HNT, b mHNT (5 M).

Figure 10

Fig. 8 TEM images of natural HNT groups: a HNT-1, b HNT-2, c HNT-3, d HNT-4, e HNT-5. TEM images of modified HNT groups: f mHNT-1, g mHNT-2, h mHNT-3, i mHNT-4, j mHNT-5.

Figure 11

Table 4. Average lengths and outer (O.D.) and inner (I.D.) diameters of the HNTs.