Gd-DTPA Adsorption on Chitosan/Magnetite Nanocomposites
© Pylypchuk et al. 2016
Received: 10 December 2015
Accepted: 10 March 2016
Published: 31 March 2016
The synthesis of the chitosan/magnetite nanocomposites is presented. Composites were prepared by co-precipitation of iron(II) and iron(III) salts by aqueous ammonia in the 0.1 % chitosan solution. It was shown that magnetite synthesis in the chitosan medium does not affect the magnetite crystal structure. The thermal analysis data showed 4.6 % of mass concentration of chitosan in the hybrid chitosan/magnetite composite. In the concentration range of initial Gd-DTPA solution up to 0.4 mmol/L, addition of chitosan to magnetite increases the adsorption capacity and affinity to Gd-DTPA complex. The Langmuir and Freundlich adsorption models were applied to describe adsorption processes. Nanocomposites were characterized by scanning electron microscopy (SEM), differential thermal analysis (DTA), Fourier transform infrared spectroscopy (FTIR), X-ray diffraction (XRD), and specific surface area determination (ASAP) methods.
Increasing interest in multifunctional nanomaterials for biomedical application necessitates detailed investigations of processes occurring at the nanolevel. Development of such nanomaterials brings scientists closer to realization of nanorobot concept—targeted drug delivery, cell recognition, and complex therapy and diagnostics. Creation of hybrid biopolymer/mineral nanomaterials can lead to development of novel nanocomposites that are sensitive to pH, temperature, magnetic field, and other physicochemical actions .
Nanocomposites based on magnetite (Fe3O4) are widely used for magnetic resonance imaging (MRI) and targeted drug delivery [2–5]. Promising trends of using magnetic materials with advanced surface are preparation of magnetosensitive nanocomposites with natural biopolymers (e.g., chitosan). Combination of chitosan and magnetite properties opens the way to creation of Pylypchuknew effective pH-controllable drug delivery and release systems with high biocompatibility. Chitosan-inorganic mineral composites have attracted researchers’ attention due to their good adsorption properties, high speed of adsorption kinetics, and some technical advantages to operate with them. The previous studies exhibit great potential of chitosan-inorganic mineral composites [1–6].
There are a number of articles reporting on synthesis and properties of magnetite/chitosan nanomaterials. For instance, hydrogel, chitosan (CS) cross-linked carboxymethyl-β-cyclodextrin (CM-β-CD) polymer modified Fe3O4 magnetic nanoparticles were synthesized in . Magnetic chitosan beads were synthesized by incorporating N,O-carboxymethyl chitosan-coated magnetic nanoparticles (NOCC-MNPs) into chitosan-citrate gel beads (CCGBs) for adsorbing Cu(II) ions. The maximal adsorption capacity as estimated by the Langmuir model was 294.11 mg/g . A magnetic composite material composed of nanomagnetite (NMT), heulandite (HE), and cross-linked chitosan was prepared and used as an adsorbent for methylene blue (MB) and methyl orange (MO). The adsorption of MB and MO followed the pseudo-second-order kinetics, and the maximum adsorption capacities were 45.1 and 149.2 mg/g at pH 5.5, respectively . The authors developed a novel chitosan/Al2O3/magnetic iron oxide nanoparticle composite acting as an adsorbent for removing MO, a model anionic dye, from aqueous solution. The adsorption isotherm was well described by the Langmuir model and showed a high MO adsorption capacity (1.27 mmol/g, i.e., 417 mg/g at 25 °C) .
Biofunctionalized chitosan@Fe3O4 nanoparticles were synthesized by combining Fe3O4 and CS chemically modified with PEG and lactobionic acid in one step . A novel pyridinium-diethylenetriamine magnetic chitosan (PDFMC) was prepared and used for magnetic separation of Cr(VI) from aqueous solution. The PDFMC worked well on removal of Cr(VI) in any condition of acidic, neutral, and basic solutions with the capacity (q max) of 176 mg/L (at pH 3, acidic), 124 mg/L (pH 6, near-neutral), and 86 mg/L (pH 9, basic) based on the Langmuir isotherm model . Cellulose grafted to nanomagnetites was found to be an efficient biopolymer composite for catalysis of Friedel-Crafts reaction between isatins and indoles, leading to selective synthesis of 3-hydroxy-3- indolylindolin-2-ones . As another example, magnetic nanoparticles double-coated with different concentrations of dextran sulfate or reduced dextran and chitosan solutions were formed by layer-by-layer deposition. Chitosan-coated magnetic nanoparticles have been synthesized and developed as a highly efficient nano-adsorbent for the removal of Hg2+ ions from industrial aqueous and oily samples. The results confirmed formation of narrow-dispersed nanoparticles with a mean average diameter of about 10 nm .
Chitosan microspheres are the most widely studied drug delivery systems for the controlled release of drugs, such as antibiotics, antihypertensive agents, anticancer agents, proteins, peptide drugs, and vaccines . In this respect, composites containing chitosan are widely used as a drug carrier for gadolinium and its biocompatible complexes (e.g., Gd-diethylenetriaminepentaacetic (DTPA), Gd-DOTA). Such substances find application as contrast agent in MRI due to paramagnetic properties of Gd3+ . The conjugates of the complexes of Gd-DTPA with low-molecular-weight chitosan are described in [16–22]. In addition, gadolinium, due to its nucleus property to capture thermal neutron with release of γ-quantum’s and Auger electrons, can be used in the neutron capture therapy (NCT) of cancer [22–31].
Unfortunately, there is no relevant information about Gd-DTPA adsorption on magnetite-chitosan composites. The main goal of this article is to obtain magnetite-chitosan nanocomposites and obtain information with respect to the Gd-DTPA adsorption on these materials.
Development of hybrid magnetic chitosan nanocomposites and peculiarities of Gd-DTPA adsorption on these nanocomposites is an important task for further development of composites for biomedical destination with a wide range of functions—targeted drug delivery, pH-controllable release, and chemo-, immuno-, and radiotherapy as well as diagnostic agents.
All reagents were of analytical grade and used without further purification. Demineralized water was used for preparation of all sample solutions (Hydrolab).
Chitosan, Sigma-Aldrich, with a molecular weight from 190,000 to 370,000 Da, degree of deacetylation not less than 75 %, and solubility of 10 mg/mL.
Gd-DTPA was prepared by dissolution of two equivalents of Gd2O3 in 0.04 M DTPA to obtain 0.04 M Gd-DTPA solution. Obtained solution was adjusted to pH = 7.26 by NaOH.
Differential Thermal Analysis
Thermal behavior of magnetite and its nanocomposites was determined by thermogravimetric analysis (TGA) using Q50 TGA instrument. TGA measurements of 4–25-mg samples were carried out at 10 °C/min heating rate in the range of 25–1000 °C under nitrogen atmosphere with a flow rate of 50 cm3/min.
Surface Area and Average Pore Diameter (ASAP) Measurements
Specific surface areas and pore volumes were determined from the low-temperature nitrogen adsorption data (automatic sorption analyzer ASAP 2020, Micromeritics, USA). Before measurements, the samples were outgassed at 60 °C.
Carbon, Hydrogen, and Nitrogen Analysis
Elemental analysis of chitosan-silica composite was carried out by using the CHN/O analyzer (Perkin Elmer, Series II CHNS/O Analyzer 2400). The analysis was made at the combustion temperature of 925 °C and the reduction temperature of 640 °C.
Surface Morphology Analysis
The surface morphology of chitosan-magnetite composite was observed by using a scanning electron microscope (SEM, LEO 1430VP, Carl Zeiss, Germany).
The Fourier Transform Infrared Spectra
The Fourier transform infrared spectra were registered using a Cary 630 ATR-FTIR instrument (Agilent Technologies) by the attenuated total internal reflection technique.
The pH of the Point of Zero Charge pHpzc
The pH of the point of zero charge pHpzc was measured using the pH drift method. The pH of the sorbent in the 0.01 M NaCl solution was adjusted between 2 and 12 by adding 0.01 M NaOH and 0.01 M HCl. To 50 cm3 of the solution, 0.2 g of the adsorbent was added, and after 24 h, the final pH was measured.
In 1 L of deionized water, 24 g of ferrous chloride (FeCl2) and 48 g of Ferric chloride solution (FeCl3) were dissolved. This solution was added dropwise to 250 mL of ammonia solution (NH4OH, 25 % in water). Black precipitate was collected and washed several times by distilled water to pH = 7.
Chitosan/Magnetite Nanocomposite Synthesis
Results and Discussion
There are many ways to obtain chitosan-magnetite nanocomposites. For instance, magnetic nanoparticles with an average crystallite size of 21.8 nm were covered in a core/shell type; magnetite/silica, magnetite/chitosan, and a double-shell magnetite/silica/chitosan were developed for attaching an antineoplastic drug . Chitosan-coated magnetite nanocomposites (Fe3O4/CS) were prepared under different external magnetic fields by the co-precipitation method . A chitosan-based hydrogel, graft-copolymerized with methylenebisacrylamide and poly(acrylic acid) (i.e., CS-co-MMB-co-PAA), was employed in the studies on the adsorption kinetics of Pb(II), Cd(II), and Cu(II) ions in aqueous solution .
Various magnetic films of chitosan and the synthesized magnetite nanopowders containing different concentrations of the latter were prepared by the ultrasonication route .
The use of the biopolymer chitosan as a template for the preparation of magnetite and magnetite/silver core/shell nanoparticle systems, following a two-step procedure of magnetite nanoparticles in situ precipitation and subsequent silver ion reduction, is discussed in .
A magnetic nanoparticle drug carrier for the controlled drug release that responds to the change in external temperature or pH was described in , with characteristics of longer circulation time and reduced side effects. The novel nanocarrier is characterized by a functionalized magnetite (Fe3O4) core that is conjugated with drug via acid-labile hydrazone bond and encapsulated by the thermosensitive smart polymer, chitosan-g-poly(N-isopropylacrylamide-co-N,N-dimethylacrylamide) [chitosan-g-poly(NIPAAm-co-DMAAm)]. The polyelectrolyte complex (PEC) effect between hyaluronic acid (HA) and chitosan was explored to recover HA from the fermentation broth. Chitosan was conjugated with the magnetic nanoparticles by the co-precipitation method to facilitate its recovery . Chitosan/magnetite nanocomposite was synthesized induced by magnetic field via in situ hybridization under ambient conditions. The saturated magnetization (Ms) of nanomagnetite in chitosan was 50.54 emu/g, which is as high as 54 % of bulk magnetite .
In this work, we used a method based on co-precipitation of Fe2+/Fe3+ salts by aqueous ammonia in 0.1 % chitosan solution.
It is well known that chitosan is soluble in water in acidic media (pH = 2–6). At this pH, chitosan swells and its chains undergo deploying due to electrostatic repulsion of positively charged –NH3 + groups.
Iron salts, after mixing with chitosan solution, surrounding the chitosan molecule form complexes with its amino groups . The addition of ammonia affects the charge of chitosan molecule, resulting in shrinkage of chitosan and precipitation of Fe3O4, and leads to the formation of chitosan-magnetite aggregates. The scheme of synthesis is presented in Fig. 1.
Chitosan/magnetite nanocomposite (Fig. 2c, d) has similar but not identical surface with some differences. Chitosan/magnetite nanocomposite has a rough and irregular surface, which is common for hybrid materials. Compared to unmodified magnetite (Fig. 2a, b), composite particles surface and pores between them look like filled by polymer species. Filling of magnetite particle aggregates with polymer causes decrease in the specific surface area of composite (101 m2/g). The influence of chitosan addition to magnetite on the specific surface area of composite is discussed further.
Specific Surface Area Determination
The isotherm plots were used to calculate the specific surface area and the average pore diameter of the magnetite and chitosan/magnetite nanocomposite.
The BET and the Langmuir surface areas of Fe3O4 and Chitosan/Fe3O4 composites
BET surface area
Langmuir surface area
For magnetite, the contribution of cylindrical pores calculated by the SCV/SCR method gives 62 %, contribution of pores between particles is 22 %, and slit-like pores 15.9 %. For chitosan/magnetite nanocomposite, contribution of cylindrical pores is equal to 56.3 %, contribution of pores between particles is 38.47 %, and slit-like pores 5.2 %. Changes in pore distribution can be caused by polymer filling in the cylindrical pores and redistribution in favor of the pores between particles.
In the FTIR spectrum of chitosan/magnetite, the broad adsorption band from 3600 to 3100 cm−1 corresponds to the stretching vibrations O–H of hydroxyl groups. The bands at 2919 and 2846 cm−1 were attributed to the asymmetric and symmetric CH2 stretch vibrations of chitosan, respectively. The AB at 1657 cm−1 can be coupled with water molecules. The band at 1561 cm−1 corresponds to the deformation vibrations of -NH2; 1415 and 1310 сm−1 for C–H bending vibrations, 1310 сm−1 for asymmetric С–О–С stretching vibrations, and 1080 сm−1 for С–О stretching vibration of СН–ОН were observed. Magnetite adsorption bands can be observed at 581 cm−1.
The low temperature weight loss from 25 up to 190 °C (endothermic peak) in the magnetite and hybrid composite corresponds to evaporation of physically adsorbed water. Chitosan started to undergo thermal destruction at 190 °C. The temperature range from 227 to 286 °C (exothermic process) could be assigned to chitosan oxidation (oxidation of –NH2 and –CH2OH groups).
Decomposition of the polymer chain in magnetite/chitosan starts from 190 °C and practically is over at 410–420 °C. In the temperature range from 289 to 775 °C, we can observe descending endothermic curve which can be explained by chitosan destruction (decarboxylation of oxidized –CH2OH groups, macromolecule chain breaks, release of nitrogen oxides from oxidized amino groups, etc.). In the case of chitosan/magnetite, the onset of the chitosan decomposition shifted to the temperatures of up to 20 °C.
The weight loss at the 190–800 °C temperature range for magnetite/chitosan composite was 4.6 % .
Comparison of the chitosan/magnetite and magnetite element composition
EDAX of material surface
Adsorption of Gd-DTPA
Adsorption of Gd-DTPA ions on the surface of nanocomposite was calculated by the formula q e = (С 0 − С eq)V/m, where C and C eq are the initial and equilibrium concentration of ions in solution, respectively, mg/mL; V is the volume of solution (cm3); and m is the mass of adsorbent (g).
Therefore, the surface charging is a pH dependent. From the literature, it is well known that the pzc will vary with the particle concentration, the ionic strength of the medium. The magnetite surface is positively charged up to pH ≈ 6.8. Therefore, at decreased pH, the negatively charged Gd-DTPA complexes can be adsorbed. At higher pH, their repulsion from the negative sites at the magnetite surface reduces the adsorbed amount.
The Langmuir and Freundlich isotherm models were applied to obtain data of Gd-DTPA adsorption mechanism on nanocomposite surface.
The Langmuir model is based on the assumption that maximum adsorption occurs when saturated monolayer of solute molecules is present on the adsorbent surface and the energy of adsorption is constant and there is no migration of adsorbate molecules in the surface plane .
The essential characteristic of Langmuir isotherm can be expressed by the R L parameter, which determines the favorable conditions for isotherm. If R L < 1, the process is favorable, if R L = 1, linear, and if R L > 1, unfavorable. As we can see, the adsorption process of Gd-DTPA on the chitosan/magnetite composite surface is favorable .
Langmuir and Freundlich parameters for adsorption of Gd-DTPA complex on the magnetite and chitosan-magnetite composite
q e exp, mmol/g
In the concentration range from 0.4 to 1.2 mmol/L, the adsorption capacity of composite is not much more higher than for pure magnetite. In the concentration range of the initial solution up to 0.4 mmol/L, addition of chitosan increased the adsorption capacity and affinity to Gd-DTPA complex. This parameter is very important for loading of Gd-DTPA micro quantities for possible use in medicine.
Unfortunately, there is no relevant information about Gd-DTPA adsorption on magnetite-chitosan composites. Adsorption capacities of the obtained magnetite-chitosan composites can be compared with other magnetite-based composites. For example, composite adsorbent prepared by entrapping cross-linked chitosan and nanomagnetite on the heulandite surface was used to remove Cu(II) and As(V) in aqueous solution. The composite gave the maximum equilibrium uptake of Cu(II) and As(V) of 17.2 (0.26875 mmol/g) and 5.9 mg/g (0.07878 mmol/g) in the initial concentration ranges of 16–656 and 17–336 mg/L, respectively . In , chitosan/magnetite nanocomposite beads were prepared by a simple and effective process. The maximum adsorption capacities for Pb(II) and Ni(II), which occurred at pH 6 at room temperature, were as high as 63.33 (0.30564 mmol/g) and 52.55 mg/g (0.8952 mmol/g), respectively, according to the Langmuir isotherm model .
A comparison of the results obtained in this article (0.6 mmol of Gd-DTPA per gram of composite) with other authors leads to the conclusion about the prospects of the obtained nanocomposites for adsorption of Gd-DTPA complexes.
The synthesis of chitosan/magnetite nanocomposites was made. It was shown that the magnetite synthesis in the chitosan medium does not affect magnetite crystal structure. The TGA data showed 4.6 % of mass concentration of chitosan in hybrid chitosan/magnetite. Despite low chitosan content, the adsorption properties of hybrid chitosan/magnetite composite with respect to Gd-DTPA increased in the micro quantity region to those of magnetite. In general, increase of Gd-DTPA adsorption in chitosan/magnetite composite, compared to unmodified magnetite, can be explained by the advent of chitosan. Interaction between chitosan and Gd-DTPA molecule can be connected with organic nature of these molecules coupled with electrostatic interaction. Good correlation with the Freundlich adsorption model can be explained by hybrid (organo-inorganic) nature of adsorbent.
The authors are thankful to Prof. Vladimir M. Gun’ko, Chuiko Institute of Surface Chemistry of the National Academy of Sciences of Ukraine, for his kind assistance with the calculation of the pore size distribution.
This research was funded by the International Visegrad Fund (Visegrad/V4EaP Scholarship No 51500518).
Publication based on the research was provided by the grant support of the State Fund for Fundamental Research (project No. 61/100-2015).
Open AccessThis article is distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made.
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