Next Article in Journal
Assessment of Industrial Modules to Design a GFMA Process for Cyanide Recovery Based on a Phenomenological Model
Next Article in Special Issue
Structure Manipulation of Carbon Aerogels by Managing Solution Concentration of Precursor and Its Application for CO2 Capture
Previous Article in Journal
Rotor-Stator Mixers: From Batch to Continuous Mode of Operation—A Review
Article Menu
Issue 4 (April) cover image

Export Article

Processes 2018, 6(4), 33; doi:10.3390/pr6040033

Review
Preparation and Potential Applications of Super Paramagnetic Nano-Fe3O4
1
Hunan Provincial Key Laboratory of Shale Gas Resource Utilization and Exploration, Xiangtan 411201, China
2
College of Civil Engineering, Hunan University of Science and Technology, Xiangtan 411201, China
3
School of Science & Sport, University of the West of Scotland, Paisley PA1 2BE, UK
*
Author to whom correspondence should be addressed.
Received: 14 February 2018 / Accepted: 3 April 2018 / Published: 9 April 2018

Abstract

:
Ferroferric oxide nanoparticle (denoted as Nano-Fe3O4) has low toxicity and is biocompatible, with a small particle size and a relatively high surface area. It has a wide range of applications in many fields such as biology, chemistry, environmental science and medicine. Because of its superparamagnetic properties, easy modification and function, it has become an important material for addressing a number of specific tasks. For example, it includes targeted drug delivery nuclear magnetic resonance (NMR) imaging in biomedical applications and in environmental remediation of pollutants. Few articles describe the preparation and modification of Nano-Fe3O4 in detail. We present an evaluation of preparation methodologies, as the quality of material produced plays an important role in its successful application. For example, with modification of Nano-Fe3O4, the surface activation energy is reduced and good dispersion is obtained.
Keywords:
Nano-Fe3O4; super paramagnetic; water; environment remediation

1. Introduction

Recently, adsorption has become widely used in industrial wastewater treatment technology. In the process, many adsorbents have been synthesized and applied to the treatment of pollutants that contain metallic elements, synthetic dyes and pharmaceutical products [1,2,3,4]. However, the removal of suspended adsorbent in wastewater is still a challenge. If it can be handled properly, it allows the effective recycling of the adsorbent with a reduction in operational costs. The addition of magnetic adsorbents has been studied to help efficient removal from wastewater. The use of magnetic Nano-Fe3O4 as an effective means for separating suspended sorbents has been identified [5,6].
As society develops, the water environment and its protection is increasingly more complex and treatment demands are much more changeable. Conventional water treatment materials are not able to satisfy the long term requirements of water treatment processes. Consequently, there is considerable interest in the development of multi-performance materials. Among them, Nanoadsorption materials have been considered to be an effective and environmentally friendly high-performance water treatment material [7]. Compared with atomic or larger scale systems, nanoscale materials have excellent physical and chemical properties from its mesoscopic effect, small objects effect, quantum size and surface effect. Nano-Fe3O4 has attracted wide attention because of its small size, large surface area (BET), super magnetic properties and easy recycling. In addition, it also has the non-toxic and biocompatible characteristics. Nano-Fe3O4 has diverse applications in new biomedical biosensors [8], contrast agent in magnetic resonance imaging [9], magnetic targeting for drug delivery system [10], tissue engineering [11]. New preparation systems and methods of modification have been developed during its application. Prabha et al. [12] studied the preparation of polymer nanocomposite coated magnetic nanoparticles. Compared with the traditional preparation method, this method can increase the reactivity of the nanoferroferric oxide by changing the active groups such as the amino group and the carboxyl group on the surface to increase the surface-active sites.
The application of Nano-Fe3O4 has many advantages but it is easy to coalesce and oxidize in the water environment, resulting in limited development. A modification to the Nanomagnetic particles can prevent agglomeration, thus increasing its dispersion in water resulting in broader opportunities for application [13]. To date, superparamagnetic Nano-Fe3O4 has been applied to the preparation of magnetic fluid material such as ink. These materials in damping device, rotating seal, magnetic drug target cells, magnetic separation, magnetic card and other fields play an important role [14]. They are also being used in environmental remediation. Given the critical dependence of properties on preparation methodology, it is useful to provide an overview of the Nano-Fe3O4 in its preparation, modification and application.

2. Methods for Preparation of Nano-Fe3O4

The methods for the preparation of Nano-Fe3O4 usually consists of co-precipitation [15], hydrothermal [16], sol-gel [17], micro-emulsion [18], high temperature thermal decomposition [19], solvothermal [20] and a number of less common approaches, which aim to obtain nanometer sized magnetic adsorption material. The performance of Nano-Fe3O4 is critically dependent on its particle size and specific surface area. Fuskele et al. [21] focused on the preparation and stability of nanofluids, studied the synthesis methods of various nanoparticles and found that the particle size of ferroferric oxide has a great influence on its performance. As the particle size decreases, the specific surface area increases, the specific saturation magnetization decreases but the coercive force does not change substantially. For example, Dutta et al. [22] proposed a simple method for preparing PEGylated Fe3O4 cubic magnetic nanoparticles using iron acetylacetonate thermal decomposition methods and discussed its application in drug release and hyperthermia. The results show that Nano-Fe3O4 has good crystallinity and there are active groups such as carboxyl groups on the surface, which provide colloidal stability, low toxicity and anti-protein properties. The modified Nano-Fe3O4 has high electrostatic binding affinity with the positively charged anti-cancer drug doxorubicin hydrochloride and which provides useful pH release characteristics.

2.1. Hydrothermal Method

The hydrothermal method—also called hot solvent synthesis—refers to a chemical reaction in a sealed pressure vessel with water as a solvent and under high temperature and pressure. The nanocrystals prepared by the hydrothermal method have relatively advanced development, wide distribution range and do not require high-temperature calcination and treatment. However, because the reaction is carried out at higher temperatures and pressures, the requirements for equipment are more extreme [23,24]. Yang et al. [25] used iron acetylacetonate as the only iron source to prepare magnetite nanoparticles under simple hydrothermal conditions and chose polyacrylic acid as a stabilizer to provide good hydrophilicity. High-water-dispersed Nano-Fe3O4 with a particle size of about 50 to 100 nm was obtained. The Nano-Fe3O4 was composed of monodispersed magnetite with a size of about 6 nm and had high magnetic properties. The content of magnetite was over 70%. Wu et al. [26] used FeCl2, FeCl3 and glucose as raw materials at 160 °C in water to prepare Fe3O4@C composite nanoparticles, as shown in Figure 1. The adsorption behavior of methylene blue on Fe3O4@C was studied. The results showed that Fe3O4@C prepared by hydrothermal method could adsorb methylene blue effectively and the maximum adsorption capacity was 117 mg/g.

2.2. Coprecipitation Method

The co-precipitation method involves the mixing of Fe2+ and Fe3+ in 1:2 proportion, precipitation under alkali conditions followed by filtering, washing and drying to generate Nano-Fe3O4. Due to its simple procedure, low cost and rapid reaction co-precipitation methods have been widely used [27,28], (see Figure 2). Qin et al. [29] adopted the chemical coprecipitation method, taking NH3·H2O as the precipitant, which was added to a mixed solution of Fe2+ and Fe3+. The particle size of NanoFe3O4 could be controlled within 20 nm under appropriate experimental conditions. Meng et al. [30] used FeCl3·6H2O, FeCl2·4H2O and deionized water to prepare an iron salt solution and a ferrous salt solution. At the same time, the two solutions were mixed and heated to prepare Nano-Fe3O4 with NH3·H2O as a precipitant in the mixed solution. The results showed that the concentration of Fe2+/Fe3+ in the mixed solution had the greatest effect on the yield of Nano-Fe3O4. In addition, the temperature has an effect on the particle size, indicating that as the temperature increases, the Nano-Fe3O4 particle size increases first and then decreases.

2.3. Sol-Gel Method

The sol-gel method typically utilizes iron sulfate, metal alkoxide hydrolysis and metal oxide or metal hydroxide sol as the raw material and a clean oxide powder [31,32] is then obtained after drying, as shown in Figure 3. The Fe3O4 synthesized by the sol-gel method has high purity but the gelation process is slow, the overall period of synthesis is long, with high temperature calcination needed [33]. Zhang et al. [34] prepared Fe3O4 aerogels by sol-gel method using FeCl3·6H2O, FeCl2·4H2O and propylene oxide as precursors and gel promoters, respectively. The results show that Fe3O4 aerogel has lower density, larger specific surface area, higher saturation magnetization and its structure and magnetic properties are controlled by factors such as solution concentration, propylene oxide and Fe3+ molar ratio and calcining temperature and Fe3O4 aerosol is prepared. The gel has certain electromagnetic properties in the 2–18 GHz frequency range. Guo et al. [35] used the sol-gel method for preparation of a Nano-Fe3O4 coated with tetraethyl orthosilicate under a constant temperature of 380 °C. It showed a good particle size of 15~20 nm and uniform dispersion.

2.4. Micro-Emulsion Method

Micro-emulsion method using two kinds of mutually miscible e solvents under the action of surfactant, forms a homogeneous emulsion. The solid phase is subsequently precipitated from the emulsion and the complete process consisting of nucleation, growth, coalescence and agglomeration finally forms spherical particles in a spherical droplet, as shown in Figure 4. The microemulsion method can prevent the agglomeration of particles while synthesizing Fe3O4 but the yield of nanoparticles prepared by a single synthesis is low, the separation and purification process of particles is complicated and the water solubility is poor [36,37]. Sun et al. [38] synthesized monodisperse Fe3O4 and polyaniline core-shell nanocomposites by microemulsion polymerization. Before the polymerization of aniline, Fe3O4 nanoparticles were prepared by thermal decomposition of acetylacetone and oleic acid using benzyl alcohol as solvent. Surface modification was carried out, then sodium dodecylbenzenesulfonate was used as surfactant, ammonium persulfate was used as oxidant and microemulsion was polymerized on the surface of Fe3O4 nanoparticles to obtain aniline monomer. Studies have shown that the oleic acid-modified Fe3O4 nanoparticles have good dispersion and the particle size is about 10 nm. Lv et al. [39] used the microemulsion hydrothermal method to prepare a new type of tower-like Fe3O4 particles. Through experiments, it was found that the reaction time has important influence on the final product. The key factors, such as NaOH concentration and the formation of tower-like Fe3O4 microstructures, are very large. The relationship and the micro-scale pagoda-like Fe3O4 crystals were grown from the Fe3O4 rod structure by an etching process and lithium air cells prepared with a pagoda-type Fe3O4 air electrode had a higher specific capacity at 100 mA g−1. The specific capacity is up to 1429 mA h g−1.

2.5. Solvent Heat Method

The solvent heat method is similar to the hydrothermal method but the water is replaced by organic solvents. The solvo-thermal method can precisely regulate the morphology and properties of Fe3O4 but it requires stringent preparation conditions [40]. Jiang et al. [41] synthesized monodisperse mesoporous Fe3O4 hollow microspheres with a diameter of 220 nm and a shell thickness of 50 nm using the trisodium citrate-assisted solvothermal method. The reaction time was good for this kind of mesoporous structure. The formation method influences the final product. Through experimental studies, it has been found that the synthesized Fe3O4 hollow microspheres have superparamagnetism, high saturation magnetization at room temperature, mesopores and high dispersibility. Zeng et al. [42] used ferric chloride hexahydrate as the sole iron source and sodium dodecylbenzenesulfonate as the surfactant. A uniform hollow Fe3O4 submicron sphere with a particle size of 350–450 nm was prepared by solvothermal synthesis. And it has high saturation magnetization and very low coercivity. The results show that the addition of sodium dodecylbenzenesulfonate is beneficial to the formation of monodisperse Fe3O4 hollow particles with a narrow particle size distribution, a high specific capacitance of 294 F g−1 at 0.5 A g−1 and good cycle stability. It maintained about 90.8% of the original capacitance after 500 charge and discharge cycles.
Table 1 summarizes the particle sizes of Fe3O4 prepared by several commonly used chemical methods; the substances added during the synthesis process and the optimal synthesis conditions; by optimizing the experimental conditions. The adsorption of pollutants and chemical adsorption properties are identified and the difference in the physical and chemical properties of Fe3O4 before and after the experimental conditions were optimized are highlighted.

3. The Modification of Nano-Fe3O4

Magnetic attraction is often present in the Nano-Fe3O4 colloidal solution, which has obvious aggregation effect because of the large BET and small diameter. At the same time, the Nano-Fe3O4 is easily oxidized in the air during the preparation process. It is of great importance to modify the surface of the Nano-Fe3O4 by using physical and chemical methods to solve the problem that agglomeration and oxidation in Nano-Fe3O4. The common surface modification methods include surface chemical reaction [49], surface polymerization reaction [50], ultrasonic chemistry-method [51], surface adsorption deposit [52] and others. According to the different classification of modified raw materials, the package materials on Nano-Fe3O4 are generally classified into 3 kinds [53] including inorganic small molecules [54], organic small molecules [55] and organic polymers [56]. The specific classification was shown in Table 2.

3.1. Modification of Small Inorganic Molecules

Currently, there are two types of materials for Nano-Fe3O4 surface modification. The first includes SiO2 and other oxides and the second is a metal such as Au, Co, Ni. There are also other inorganic materials used to modify Nano-Fe3O4, for example, the introduction of carbon to ferrosoferric oxide can increase its electrochemical performance. Han et al. [60] prepared a series of Fe3O4/C nanocomposites with nanoholes of 5 to 10 nm using a cotton assisted combustion reaction. The particle size of Fe3O4 nanoparticles is less than 10 nm and it is well embedded in the carbon matrix, making Fe3O4/C have good electrochemical performance. At a current of 0.4 A g−1, the presence of carbon favors good dispersion and minimal agglomeration of Fe3O4 nanoparticles, with higher conductivity and buffer volume change.
Coating the Nano-Fe3O4 with a layer of silicon dioxide can effectively improve its corrosion resistance and dispersion. For example, Wang et al. [61] found that Fe3O4 without silica is highly susceptible to corrosion by acidic solutions. However, the silica-coated Fe3O4 forms a shell structure that blocks the contact with the solution. To a large extent, Fe3O4 is protected, which improves its acid resistance. Mostafaei et al. [62] first synthesized Nano-Fe3O4 by chemical precipitation. It was found through analysis that its small particle size was easily modified without precipitation and the dispersion effect was poor before the surface was modified with silica. From the experimental results, it can be seen that the spherical structure did not change. Each of the microspheres covered with SiO2 has a small number of magnetic particles and has a good dispersion. The reason for this phenomenon after modification may be that the SiO2 core shell blocks the dipole interaction between Nano-Fe3O4 to make the particle distribution more uniform.
The surface of mesoporous SiO2 had Si-OH structure and its surface was easy to be modified after the Nano-Fe3O4 coated with SiO2, further grafting other active functional groups [63,64,65,66]. Xue et al. [67] used the hydrothermal method to prepare Nano-Fe3O4, compounding a magnetic shell composite microsphere by coating SiO2 on its surface. It had a unique channel structure and a large BET based on SiO2 groups in the surface. Finally, through the comparison of its performance in adsorption, they concluded that the adsorption effect for Cr ions by SiO2 on the Nano-Fe3O4 coating was poor. After introducing -NH2 groups, the attraction of negatively charged CrO42− by the positively charged -NH2 through electrostatic attraction, significantly improved the absorption of Cr ions. Scanone et al. [68] synthesized Nano-Fe3O4 by co-precipitating Fe2+ and Fe3+ in ammonia solution and then modified the surface of SiO2 with sodium silicate and passed 3-aminopropyltriethoxysilane. After the alkylsilane (APTS) treatment, the amino group was introduced onto the surface of SiO2 by grafting. Then use 5, 10, 15, 20-tetrakis (4-carboxyphenyl) porphyrin (TCPP) activated by carbondiamine (NHS/EDC) and triiron tetraoxide (MNPNH) and coated with silica. The tri-iron oxide (MNPSINH) is covalently bonded. The photodynamic activities of MNPNH-TCPP and MNPSINH-TCP in the presence of different photo-oxidation substrates and in microbial cell suspensions were compared. The main difference is that the silica coating on the surface of mnpnh-tcpp produces O2 in water. The photodynamic effect of TCPP linked to MNP is very sensitive to the decomposition of tryptophan. The last study showed that the MNPSINH-TCPP as an antibacterial material can control the proliferation of microorganisms under visible light and can maintain the sterilization state and has potential value in the medical field.
Nano-Fe3O4 BET surface area can be controlled in the presence of certain heavy metals. Sun et al. [69] studied composite Fe3O4 particles under the influence of Ag. The results of the experiment showed that after coating Ag on Fe3O4, the specific surface area had a significant increase, the same as its average pore size and total pore volume. In addition, the modification Fe3O4 by Ag provided excellent physical and chemical properties, with good stability even under high temperature and also improved its adsorption capacity in heavy metal removal application.

3.2. Modification of Small Organic Molecules

Inorganic nanomaterials have many advantages in the modification of Nano-Fe3O4 but in some systems (water phase system, oil phase system, oil and water system), their impact is limited. The modification of Nano-Fe3O4 by small organic molecule can provide good performance in both the water and oil phase systems. Modification by small organic molecules is divided into two, using either coupling agents or surfactants. The most common coupling agent is silane and surface-active agents include β-cyclodextrin [70], sodium carboxymethylcellulose [71], citric acid [71], amino acids [72,73] and other small organic molecules.
Surfactant-treated Nano-Fe3O4 often has lipophilic and hydrophilic groups forming micelles in the solution and on this basis, can achieve nanoparticle size and morphology control. The modification by surfactants can be to form a coating layer of long chain hydrocarbon on the Fe3O4, with the surface of Fe3O4 as the polar end for adsorption [74]. For example, Zhu et al. [75] modified the ferroferric oxide with oleic acid and found that the unmodified Nano-Fe3O4 was easy to reunite and the Nano-Fe3O4, which was modified by oleic acid, had large particle diameter and better dispersion. The reason for this phenomenon was that oleic acid on the Nano-Fe3O4 surface became a layer which effectively prevented the aggregation of particles. The hydrophilic group of oleic acid exposed to air turned the hydrophilic surface of Nano-Fe3O4 into a lipophilic surface. In addition, the modified Nano-Fe3O4 had more active sites on its surface. Wang et al. [70] synthesized a new cyclodextrin(-CD) polymer adsorbent-cyclodextrin/ethylenediamine/magnetic oxide graphene (CD-E-MgO) to extract Cr(VI) from aqueous solution. The adsorption mechanism was also analyzed: (a) electrostatic attraction; (b) subject-object interaction; (c) Cr (VI), (HCrO4-) icons and CD-E-MgO combined with hydrogen bonding.
Nano-Fe3O4 after being modified by a silane coupling agent, can undergo further surface modification introducing higher selectivity. Shi et al. [76] used a silane coupling agent as modification material in the process of synthesizing magnetic microspheres. The results showed that the hydroxyl group of the Nano-Fe3O4 and the hydroxyl group were dehydrated, so the coupling agent could be adsorbed on the Nano-Fe3O4 surface. In addition, the surface of the modified Nano-Fe3O4 increases the relative concentration of oxygen atoms on the silane coupling agent, so that it can better integrate with other reactive groups and enhance its surface activity. Gui et al. [77] used a coupling agent to surface-treat Nano-Fe3O4 synthesized by the co-precipitation method and found that the coupling agent bonds well to the surface of Nano-Fe3O4. In addition, studies have shown that lipophilic and hydrophilic amphiphilic Nano-Fe3O4 can be obtained on the surface of Nano-Fe3O4 treated with coupling agent and the coupling agent is chemically bound in the dehydration reaction of the coupling agent and Nano-Fe3O4 to give new surface activity.
The modification of the coupling agent can improve the surface performance of Nano-Fe3O4. Lou et al. [78] compared the properties of the Nano-Fe3O4 had coupling agent on the surface and the unmodified Nano-Fe3O4. The results showed that after modified by coupling agent, the dispersity of Nano-Fe3O4 was greatly improved and the settlement was difficult to occur with the same magnetic responsiveness. The methanol formed during the hydrolysis of coupling agent also increased the hydroxyl groups on the Nano-Fe3O4 surface which is helpful for further modification.

3.3. Modification of Organic Polymers

There are still many deficiencies in aspects of the biocompatibility and stability in the modification of inorganic nanomaterials using small organic molecule in the case of Nano-Fe3O4. Modification of Nano-Fe3O4 by an organic polymer provides a special nucleation, shell structure, which also has the surface functionality and biological activity of the polymer. The modification using an organic polymer is typically divided into two: a natural biological molecule or a synthetic polymer. The natural polymers commonly used include: glucan [79], proteins [80], starch [81] and polypeptides [82]. The synthetic polymers usually used include: polyethylene glycol [83] and polyvinyl alcohol [84,85].
After the modification of natural biomolecules, the biocompatibility of Nano-Fe3O4 can be improved with new biological activity also established. For instance, as a natural, non-toxic protein macromolecule, gelatin has two segments, which can provide Nano-Fe3O4 with micellar encapsulation and water dispersion. The synthesis of magnetic nanoparticles and the stabilizing effect on Fe3O4 nanoparticles were proposed in the polyacrylamide hydrogel gel network by Reddy et al. [86] The study found that the presence of biocompatible gelatin in magnetic hydrogel enhanced the absorption of Nano-Fe3O4 and in vitro blood compatibility by thrombus and hemolysis test to study the biocompatibility of the gel. In addition, drug release was studied under an external magnetic field. The results showed that the hydrogel prepared in this way can be used for magnetic control drug release system and had potential application value in magnetic sensor, actuator and pseudo muscle. The water dispersible Fe3O4 nanoparticles were prepared with the method of gelatin embedding by Cheng et al. [87] and the surface coated with micellar was analyzed. At the same time, because the gelatin contained a large number of active groups, the nanocomposites could be prepared by fluorescent labeling and low-toxic platinum-precursor drugs, which could be applied in anti-cancer therapies.
After the surface modification of Nano-Fe3O4, various copolymers can be introduced to give Nano-Fe3O4 a variety of better and richer properties. For example, Hu et al. [88] looked at polyethylamine (PEI). The Fe3O4 modified by PEI was significantly more dispersed than pure Fe3O4 and the modified Fe3O4 particles were more spherical. The explanation was that the made increased the repulsive effect of charges and increased the steric resistance [89]. He et al. [90] first prepared ferroferric oxide by coprecipitation method at 90 °C, then the ferroferric oxide was coated with sodium polyacrylate by solution dispersion polymerization and surface Ca2+ crosslinking. The composite materials prepared had good adsorption properties for Pb2+ and Cd2+, which had the highest adsorption rate when the dosage of adsorbent was 1.0 g/L and 1.6 g/L to 200 mg/L Pb2+ solution and 100 mg/L Cd2+ solution. Yan et al. [91] used catalytic polymerization of aniline to load polyaniline on the surface of Fe3O4 to prepare a highly efficient complex catalyst. In a simulated wastewater treatment, COD removal was highly effective. In addition, the hydrogen ions provided by polyaniline can form coordination bonds with iron ions and reduce the loss of iron into the aqueous phase.

3.4. Structure of Nano-Fe3O4 Composite Materials

There were four basic sub-structures for ferroferric oxide modified by inorganic or organic substances. These include: core-shell [92], shell-core [93], diffuse [94] and sandwich [95] and are shown in Figure 5a–d. Figure 5a is the core-shell structure, with Nano-Fe3O4 as centrally, surrounded by a polymer shell. The Nano-Fe3O4 is completely embedded in the polymer. Figure 5b is the shell-core structure, in which the polymer acts as the core and Nano-Fe3O4 surrounds as the shell. This kind of composite microsphere is combined with Nano-Fe3O4 by complexation or electrostatic adsorption. Figure 5c is the diffuse structure, with the Nano-Fe3O4 evenly distributed within the polymer. Figure 5d is the sandwich structure and inner and outer layers of the complex are organic polymers, while the middle layer is Nano-Fe3O4. These microspheres are usually coated with organic polymers in the shell-core structure microspheres [96,97]. In addition, magnetic complexes after modification are found to have super paramagnetism, which was faster and easier to separate from the reaction system under the action of magnetic field. Moreover, magnetic compounds can be rapidly dispersed in the reaction system after removing the external magnetic field, which can assist in the recycling of materials and reduce its application costs [98,99].
The magnetic properties of these four different structures varies. The core-shell structure has a number of advantages over the other three structures. It is easier to modify the magnetic complex of the core-shell structure and introduce additional functional groups such as hydroxyl, mercapto and carboxyl group [100,101]. Compared with the diffuse structure and the shell-core structure, the environmental stability and thermal stability of the core-shell structure magnetic complex were improved. At the same time, this structure can prevent Nano-Fe3O4 from contacting with air and other substances, which can avoid its core being oxidized and corroded [102]. Compared with the sandwich structure, the core-shell structure magnetic complex was easier to prepare and the surface modification of Nano-Fe3O4 can be completed by a one-step method [103], which produced a superparamagnetic product and easier to be separated. For example, Kalska et al. [104] prepared nuclear shell nanoparticles with different magnetic core diameters and different thickness, who used Ag, Au and Cu as spacer metal. The influence of the thickness and composition of the particles in the structure were studied, together with the Cu, Au and Ag on the structure of core crystal magnetite. The results showed that the existence of the precious metal shell and the dipole interaction between the magnetic particles made the magnetic complex separation better. The presence of Cu, Ag and Au in magnetic particles leaded to the addition of superfine magnetic fields, which made them superparamagnetic.

4. Applications of Nano-Fe3O4

4.1. Biomedical Sciences

The Nano-Fe3O4 had more selective and catalytic activity than general materials because of its characteristics of small particle size, BET and surface activity center [105]. At the same time, the modified Nano-Fe3O4 can be used as an anti-tumor drug carrier, which had good specificity and targeting in the field of external magnetic field [106]. The Fe3O4 nanoparticles modified by sodium oleate were expected to do drug carrier for osteosarcoma chemotherapy. It could be combined with anticancer drugs targeting tumor body parts through the magnetic field and the basic physiology of the human body with added benefit of low toxicity [107]. For example, Isiamian et al. [108] studied the enhanced radio sensitivity of breast cancer cells with the combination of 2-deoxy-d-glucose and doxorubicin plus superparamagnetic Fe3O4 nanoparticles. At the same time, it was also found that doxorubicin and 2-deoxy-d-glucose combined with targeted magnetic Fe3O4 nanoparticles can promote breast cancer radiotherapy by improving the localization of chemotherapy, increasing the cytotoxicity of tumor cells and reducing the single therapeutic dose.
With good biocompatibility and magnetic effect, Nano-Fe3O4 had a wide application in the treatment of tumors and magnetic resonance imaging [109]. Zhang et al. [110] studied the application of Nanoferroferric oxide in rats’ hydrocrania CT imaging, which could be used as a photographic developer. They also analyzed the Nano-Fe3O4 distribution in rat various organs and found that there was no accumulation in different organs. This phenomenon showed that the Nano-Fe3O4 had biocompatibility.

4.2. Removal of Heavy Metals from Aqueous Systems

Modified Nano-Fe3O4 surfaces reacts with heavy metal ions and have been studied in the removal for treatment of aqueous systems. For example, Cui et al. [111] synthesized a new magnetic nanocomposite material (MgHAP/Fe3O4) by adding Fe3O4 into magnesium hydroxyapatite (MgHAP), which can remove the Cu2+ from the aqueous solution. The adsorption of Cu2+ by MgHAP/Fe3O4 was mainly by chemical adsorption, with the sharing or exchange of electrons between adsorbent and Cu2+, in which the valence state is important. Because of this chemical interaction, the combination of MgHAP/Fe3O4 and Cu2+ had stable chemical and physical properties. In addition, Mg2+ and Cu2+ in MgHAP had the same charge and similar ionic radius, promoting their exchange in hydroxyapatite. After adsorption, the properties of the material were very stable, which would not cause secondary pollution to the environment, making it advantageous for water treatment.
The modified Nano-Fe3O4 can also reduce the reactivity of heavy metals and produce stable hydroxide and iron oxide precipitation on its surface. Tian et al. [112] modified the Nano-Fe3O4 by using a kaolin with better functional properties after comparing various modifiers. Based on this, the pH was studied in the process of removing heavy metal chromium. At higher concentrations, the kaolin-modified Nano-Fe3O4 forms hydroxides of iron and chromium on the surface, so that the particles are in a stable state and passivated and their surface almost loses reactivity. Chang et al. [113] used coprecipitation to wrap the γ-polyglutamic acid (γ-PGA) on the Nano-Fe3O4 surface successfully. The results showed that the γ-PGA/Fe3O4 particle size was smaller than that of the Nano-Fe3O4, which also had larger surface area. The removal rate of Cr3+, Cu2+ and Pb2+ by γ-PGA/Fe3O4 in the deionized water was more than 99%, which was because of the larger specific surface area of the γ-PGA/Fe3O4 mNPs. The experimental results showed that γ-PGA/Fe3O4 was better performance than Fe3O4 and γ-PGA/Fe3O4 in heavy metal removal. The adsorption of heavy metal ions got through the membrane by means of γ-PGA and the unabsorbed ions removal activity was reduced through the membrane.
The heavy metal ions could react with the function group on the modified Nano-Fe3O4 surface. For instance, Jin et al. [114] analyzed the process of adsorption of heavy metals by the Nano-Fe3O4 surface loaded amino functional group. The study found that the Nano-Fe3O4 coated with a single silicon dioxide had a low adsorption capacity of heavy metals and when its surface is modified with amino functional group, faster and more effective removal of heavy metal ions occurred. As a result of the interaction between lewis acid-alkali, amino groups can strengthen the introduction of SiO2 for heavy metal ions, such as Hg2+, Pb2+ and Ag+. The reason of this phenomenon maybe is the amino changed the silica shell with Nano-Fe3O4 nuclear structure, increasing the BET and pore size. Shen et al. [115] investigated the fungi and ferroferric oxide compound material. Using a kind of rice root mildew derived biomaterial to modify Fe3O4 and analyzed adsorption mechanism. They concluded that the rhizopus oryzae surface functional groups can readily react with metals, promoting enhanced adsorption of metals from water.
The removal activity of modified Nano-Fe3O4 for heavy metals is strongly pH dependent. For example, Zhao et al. [116] successfully synthesized Fe3O4-MnO2 magnetic nanoplates using a simple hydrothermal method to remove divalent heavy metals in water. The modification of amorphous MnO2 can significantly increase the specific surface area of Fe3O4-MnO2 and reduce the zero-charge point, thus ensuring good adsorption capacity for metal cations. Experiments show that the acid-alkaline environment affects the surface charge of Nano-Fe3O4 during the adsorption of divalent heavy metal by Nano-Fe3O4. The reason is that at low pH, H+ ions easily combine with the hydroxyl groups on the surface of Nano-Fe3O4, which increases the positive charges and groups on the surface and the negatively charged divalent heavy metal ion complexes are electrostatically attracted to the surface of Nano-Fe3O4. At the same time, the ability to adsorb divalent heavy metals is increased. Kilianová et al. [117] reported a simple and cheap synthesis of ultra-fine Nano-Fe3O4 with narrow particle size distribution and its application in the field of arsenic removal in a water environment. The study showed that the mesoporous arrangement of nanoparticles in their system enhanced the adsorption capacity, which was due to the strong magnetic interaction between nanoparticles. As (V) would be removed totally when the pH value was in the acid range. At this time, the Zeta potential of Nano-Fe3O4 adsorbent was 7.6; pH value was 5–7.6; Fe/As was approximately 20/1 and the balance of arsenic removal was 45 mg/g.
Table 3 lists the modification of Fe3O4 by surface chemical physical methods for different substances. After modification, Fe3O4 can increase the adsorption efficiency of heavy metal ions and the mechanism of removal of metal ions also differs between them. The three main mechanisms are electrostatic adsorption, surface reaction and chemical ligand exchange.

4.3. Electrochemical Sensor and Energy Storage

Complex Nano-Fe3O4 had shown excellent charge-discharge cycling stability [123]. For example, composite material combined by Nano-Fe3O4 and Graphene after modification had good electrochemical sense performance. The modified graphene can enhance its stability and conductivity and Fe3O4 has a reversible capacity synergistic effect [124]. Peng et al. [125] synthesized a novel multifunctional magnetic biomolecule with Fe3O4 as the core, and heme protein and polydopamine as shells, using a one-pot chemical polymerization method. The results showed that the synthesized biomacromolecules not only possess the magnetic properties of Fe3O4 but also maintain the native structure of the heme protein under the action of an external magnetic field. Polydopamine and Au nanoparticles have good biocompatibility and conductivity. At the same time, due to the presence of Au nanoparticles, the exchange of electrons between the hemoprotein and the electrode is enhanced. Zheng et al. [126] synthesized magnetic Fe3O4 nanoparticles using chemical co-precipitation method and mixed Fe3O4 nanoparticles with chitosan to form a matrix of immobilized hemoglobin to prepare a hydrogen peroxide biosensor. In the pH range of 4–10, the potential of the Fe(III)/Fe(II) couples changes linearly with increasing pH, indicating that electron transfer is accompanied by transport of single protons in the electrochemical reaction. At the same time, it also has a certain effect on the storage of electrical energy.
After secondary modification, the dispersion of the composite particles was better and graphene had a stronger protective effect on granules, which was of great practical significance. Zhu et al. [127] studied a lab prepared Nano-Fe3O4 compound rich in amino and carboxyl groups on the rheophore. After testing the content of the alpha fetoprotein antibody absorbed by amino and electrostatic forces, they concluded that alpha fetoprotein immune sensor had high sensitivity and stability. In addition, the adsorption capacity of nanometer compound to the antibody was increased compared with the traditional method.

4.4. Chemical Catalysis

Cai et al. [128] found that when Ag was loaded on the surface of Fe3O4, the effect on the catalytic reduction of nitrophenol was greater than in its absence and that this effect increased with the increase in Ag concentration. Zou et al. [129] used PdCl2, SnCl2·2H2O as precursors to prepare different Fe3O4 catalysts with different Fe3O4 content. They found, using cyclic voltammetry and timing current tests, that the catalyst had a good electrocatalytic activity for ethanol oxidation and the charge transfer resistance had a strong relationship with the Pd/Sn content.
Coupling agents were used to connect the heavy metal bridge on the Nano-Fe3O4 surface, effectively inhibiting the agglomeration of Fe3O4 and enhance its stability. Gu et al. [130] prepared Au/Fe3O4 by ultrasound in the presence of 3-aminopropyl triethoxysilane, which had high catalytic activity and did not agglomerate because of the action of the amino containing 3-aminopropyl triethoxysilane. Its rate constant can reach 0.2256 min−1 in the catalytic reduction of 4-nitrophenol. After nine cyclic reactions, the catalytic conversion rate was still very high. Gao et al. [131] utilized Nano-Fe3O4 as a filler for polytetrafluoroethylene and the linear expansion coefficient of composite material was greatly reduced. When the mass fraction of Fe3O4 was 15%, the linear expansion coefficient decreased by 40.1 × 10−6/°C compared with the single polytetrafluoroethylene.

4.5. Others

The use of Nano-Fe3O4 has great practical value in other applications (as shown in Table 4). In addition, to the water environment, a number of studies had shown that Nano-Fe3O4 can effectively remove heavy metals from sewage and also remove organic, inorganic compounds, dyes, algae [132] and other environmental pollutants in water. Ito et al. [133] studied the effect of ZrFe2(OH)8 as adsorbent on phosphorus removal in wastewater. According to the study, ZrFe2(OH)8 was a good phosphate adsorbent. More than 90% of the phosphate can be removed within 5 min. It can effectively prevent the eutrophication of polluted water and is straight forward to recycle. Phenol was widely used in rubber, pesticides, dyes, plastics and other fields but its toxicity led to significant environmental pollution and subsequent restriction. Nano-Fe3O4 shows good adsorption for phenol, for example, Jiang et al. [134] in studies of fungal degradation, compared Nano-Fe3O4 immobilized cells to isolated fungal cells without nucleus, free floating cells and calcium alginate immobilized cells without nanoparticles. The results showed that the immobilized dedoxycycline strain had better biodegradability than the free cells and the Nano-Fe3O4 immobilized cells had the highest rate of removal of phenol. In addition, when the initial phenol concentration was higher than 900 mg L−1, the Nano-Fe3O4 immobilized cells could degrade over 99.9 percent of phenol in 80 h and had good stability in the saline environment. On the contrary, the free cells removal rate of phenol was 34.5% and immobilized cells without Nano-Fe3O4 was 81.3%.
Due to having a magnetic property, some materials are likely to combine with it and enhance their functions. They often show a combination performance other than individual. For example, in order to short settling time of flocs in coagulation-flocculation, with the help of external magnetic fields, the coagulation by magnetic coagulant consisting of Nano-Fe3O4 and conventional coagulants (e.g., polyaluminum chloride [143], chitosan [144,145], polyacrylamide [146] et al.) is easy to achieve the purpose. In fact, it is far more than the effect in settling speed enhancement because the presence of Nano-Fe3O4 is likely to enhance original functions of coagulant in charge neutralization, netting adsorption-bridging [147]. Therefore, Nano-Fe3O4 is helpful in improving performance of coagulation. Magnetic separation is a green technology and its development is more tempting. Research on the magnetic coagulant is, however, quite deficient. How to ensure its stability and effectiveness is an important problem. In on another part, the Nano-Fe3O4 has also received wide attention. A typical example is the metal-organic frameworks (MOFs) being powder materials means that they have a small Nanosize, which means they are often difficult to separate from liquid phase. With the help of Nano-Fe3O4, this difficulty can be overcome. The hybridized materials of Nano-Fe3O4 and MOFs were able to show more special functions than their individual [148]. Overall, the composite material of Nano-Fe3O4 and other functional materials may be a better solution in overcoming their shortcomings or obtaining their expected functions.

5. Conclusions

Because Nano-Fe3O4 has the excellent chemical properties, it has been an important research focus in recent years. It is different from general magnetic materials due to unique features which include simple preparation and lower requirements for equipment compared with the traditional adsorbents. Although Nano-Fe3O4 has been widely applied in many fields, some problems still need to be addressed. For example, its dispersion and stability. Through modification, iron oxide has multidimensional functional properties such as oxidation, adsorption, catalysis, magnetic separation. If the Nano-Fe3O4 was applied to different fields, the morphology, structure and surface properties are the main factors controlling their successful application. Further research on their modification is still needed. Finding a more convenient and more economical way to prepare and modify good Nano-Fe3O4 should be addressed to fully exploit their potential in the diverse fields of application.

Acknowledgments

This work is financially supported by National Natural Science Foundation of China (No. 51408215), National Natural Science Foundation of Hunan Province of China (No. 2018JJ2128), China Postdoctoral Science Foundation funded project (No. 2017M622578), Research Foundation of Hunan University of Science and Technology (Nos. E51508 and KJ1808) and Hunan Province graduate research and innovation projects in China (CX2017B638).

Author Contributions

Guocheng Zhu led the academic direction and developed the manuscript. Hao Zhan and Yongning Bian have collected materials and written the paper under academic direction. Qian Yuan translated the paper into English. Andrew Hursthouse further checked English style and language throughout the paper, and also gave some suggestions. Bozhi Ren gave us some suggestions on editing this manuscript.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Salem, I.A.; Salem, M.A.; El-Ghobashy, M.A. The dual role of ZnO nanoparticles for efficient capture of heavy metals and Acid blue 92 from water. J. Mol. Liquids 2017, 248, 527–538. [Google Scholar] [CrossRef]
  2. Iannazzo, D.; Pistone, A.; Ziccarelli, I.; Espro, C.; Galvaqno, S.; Giofré, S.V.; Romeo, R.; Cicero, N.; Bua, G.D.; Lanza, G.; et al. Removal of heavy metal ions from wastewaters using dendrimer-functionalized multi-walled carbon nanotubes. Environ. Sci. Pollut. Res. 2017, 24, 14735–14747. [Google Scholar] [CrossRef] [PubMed]
  3. Chaudhary, S.; Sharma, J.; Kaith, B.S.; Yadav, S.; Sharma, A.K.; Aayushi, G. Gum xanthan-psyllium-clpoly(acrylic acid-co-itaconic acid) based adsorbent for effective removal of cationic and anionic dyes: Adsorption isotherms, kinetics and thermodynamic studies. Ecotoxicol. Environ. Saf. 2018, 149, 150–158. [Google Scholar] [CrossRef] [PubMed]
  4. Islam, M.T.; Hernandez, C.; Ahsan, M.A.; Pardo, A.; Wang, H.; Noveron, J.C. Sulfonated resorcinol-formaldehyde microspheres as high-capacity regenerable adsorbent for the removal of organic dyes from water. J. Environ. Chem. Eng. 2017, 5, 5270–5279. [Google Scholar] [CrossRef]
  5. Kim, Y.S.; Kim, Y.H. Application of ferro-cobalt magnetic fluid for oil sealing. J. Magn. Magn. Mater. 2003, 267, 105–110. [Google Scholar] [CrossRef]
  6. Beydoun, D.; Amal, R.; Low, G.K.C.; McEvor, S. Novel Photocatalyst: Titania-Coated Magnetite. Activity and Photodissolution. J. Phys. Chem. B 2000, 104, 4387–4396. [Google Scholar] [CrossRef]
  7. Lu, F.; Astruc, D. Nanomaterials for removal of toxic elements from water. Coord. Chem. Rev. 2018, 356, 147–164. [Google Scholar] [CrossRef]
  8. Chen, M.; Hou, C.; Huo, D.; Fa, H.; Zhao, Y.; Shen, C. A sensitive electrochemical DNA biosensor based on three-dimensional nitrogen-doped graphene and Fe3O4 nanoparticles. Sens. Actuators B Chem. 2017, 239, 421–429. [Google Scholar] [CrossRef]
  9. Cao, J.; Wang, Y.; Yu, J.; Xia, J.; Zhang, C.; Yin, D.; Häfeli, U.O. Preparation and radiolabeling of surface-modified magnetic nanoparticles with rhenium-188 for magnetic targeted radiotherapy. J. Magn. Magn. Mater. 2004, 277, 165–174. [Google Scholar] [CrossRef]
  10. Huang, Y.S.; Lu, Y.J.; Chen, J.P. Magnetic graphene oxide as a carrier for targeted delivery of chemotherapy drugs in cancer therapy. J. Magn. Magn. Mater. 2017, 427, 34–40. [Google Scholar] [CrossRef]
  11. Pistone, A.; Iannazzo, D.; Panseri, S.; Montesi, M.; Tampieri, A.; Galvaqno, S. Hydroxyapatite-magnetite-MWCNT nanocomposite as a biocompatible multifunctional drug delivery system for bone tissue engineering. Nanotechnology 2014, 25, 425701. [Google Scholar] [CrossRef] [PubMed]
  12. Prabha, G.; Raj, V. Preparation and characterization of polymer nanocomposites coated magnetic nanoparticles for drug delivery applications. J. Magn. Magn. Mater. 2016, 408, 26–34. [Google Scholar] [CrossRef]
  13. Ji, F.; Ceng, K.; Zhang, K.; Li, J.; Zhang, J. Synthesis and Properties of PEG Modifiers of Fe3O4 Magnetic Nanoparticles. Acta Polym. Sin. 2016, 1704–1709. [Google Scholar] [CrossRef]
  14. Gupta, J.; Prakash, A.; Jaiswal, M.K.; Agarrwal, A.; Bahadur, D. Superparamagnetic iron oxide-reduced graphene oxide nanohybrid-a vehicle for targeted drug delivery and hyperthermia treatment of cancer. J. Magn. Magn. Mater. 2018, 448, 332–338. [Google Scholar] [CrossRef]
  15. Butter, K.; Kassapidou, K.; Vroege, G.J.; Philipse, A.P. Preparation and properties of colloidal iron dispersions. J. Colloid Interface Sci. 2005, 287, 485–495. [Google Scholar] [CrossRef] [PubMed]
  16. Giri, S.; Samanta, S.; Maji, S.; Ganguli, S.; Bhaumik, A. Magnetic properties of α-Fe2O3 nanoparticle synthesized by a new hydrothermal method. J. Magn. Magn. Mater. 2005, 285, 296–302. [Google Scholar] [CrossRef]
  17. Eken, A.E.; Ozenbas, M. Characterization of nanostructured magnetite thin films produced by sol-gel processing. J. Sol-Gel Sci. Technol. 2009, 50, 321–327. [Google Scholar] [CrossRef]
  18. Liang, X.; Jia, X.; Cao, L.; Sun, J.; Yang, Y. Microemulsion Synthesis and Characterization of Nano-Fe3O4 Particles and Fe3O4 Nanocrystalline. J. Dispers. Sci. Technol. 2010, 31, 1043–1049. [Google Scholar] [CrossRef]
  19. Zhu, H.; Han, T.; Zhang, J.; Zhou, Z.; Yang, S. The Synthesis and Application of Water Soluble Fe3O4 Nanoparticles. Guangzhou Chem. Ind. 2014, 42, 88–89. [Google Scholar]
  20. Niu, W.; Shen, Y.; Xu, J.; Ma, L.; Zhao, Y.; Shen, M. Solvothermal Synthesis of Fe3O4 Nanospheres and Study on the Catalytic Degradation of Xylenol Orange. Chin. J. Inorg. Chem. 2013, 29, 2110–2118. [Google Scholar]
  21. Fuskele, V.; Sarviya, R.M. Recent developments in Nanoparticles Synthesis, Preparation and Stability of Nanofluids. Mater. Today Proc. 2017, 4, 4049–4060. [Google Scholar] [CrossRef]
  22. Dutta, B.; Shetake, N.G.; Gawali, S.L.; Barick, B.K.; Barick, K.C.; Babu, P.D.; Pandey, B.N.; Priyadarsini, K.I.; Hassan, P.A. PEG mediated shape-selective synthesis of cubic Fe3O4 nanoparticles for cancer therapeutics. J. Alloys Compd. 2018, 737, 347–355. [Google Scholar] [CrossRef]
  23. Nadimpalli, N.K.V.; Bandyopadhyaya, R.; Runkana, V. Thermodynamic analysis of hydrothermal synthesis of nanoparticles. Fluid Phase Equilib. 2018, 456, 33–45. [Google Scholar] [CrossRef]
  24. Ge, S.; Shi, X.; Sun, K.; Li, C.; Baker, J.R., Jr.; Banaszak Holl, M.M.; Orr, B.G. A Facile Hydrothermal Synthesis of Iron Oxide Nanoparticles with Tunable Magnetic Properties. J. Phys. Chem. C Nanomater. Interfaces 2009, 113, 13593–13599. [Google Scholar] [CrossRef] [PubMed]
  25. Yang, X.; Jiang, W.; Liu, L.; Chen, B.; Wu, S.; Sun, D.; Li, F. One-step hydrothermal synthesis of highly water-soluble secondary structural Fe3O4 nanoparticles. J. Magn. Magn. Mater. 2012, 324, 2249–2257. [Google Scholar] [CrossRef]
  26. Wu, R.; Liu, J.H.; Zhao, L.; Zhang, X.; Xie, J.; Yu, B.; Ma, X.; Yang, S.T.; Wang, H.; Liu, Y. Hydrothermal preparation of magnetic Fe3O4@C nanoparticles for dye adsorption. J. Environ. Chem. Eng. 2014, 2, 907–913. [Google Scholar] [CrossRef]
  27. Xia, T.; Xu, X.; Wang, J.; Xu, C.; Meng, F.; Shi, Z.; Lian, J.; Bassat, J. Facile complex-coprecipitation synthesis of mesoporous Fe3O4 nanocages and their high lithium storage capacity as anode material for lithium-ion batteries. Electrochim. Acta 2015, 160, 114–122. [Google Scholar] [CrossRef]
  28. Wu, J.H.; Ko, S.P.; Liu, H.L.; Kim, S.; Ju, J.S.; Kim, Y.K. Sub 5 nm magnetite nanoparticles: Synthesis, microstructure, and magnetic properties. Mater. Lett. 2007, 61, 3124–3129. [Google Scholar] [CrossRef]
  29. Qin, R.; Jiang, W.; Liu, H.; Li, F. Preparation and Characterization of Nanometer Magnetite. Mater. Rev. 2003, 17, 66–68. [Google Scholar]
  30. Meng, H.; Zhang, Z.; Zhao, F.; Qiu, T.; Yang, J. Orthogonal optimization design for preparation of Fe3O4 nanoparticles via chemical coprecipitation. Appl. Surf. Sci. 2013, 280, 679–685. [Google Scholar] [CrossRef]
  31. Lemine, O.M.; Omri, K.; Zhang, B.; Mir, L.; Sajieddine, M.; Alyamani, A.; Bououdina, M. Sol-gel synthesis of 8 nm magnetite (Fe3O4) nanoparticles and their magnetic properties. Superlattices Microstruct. 2012, 52, 793–799. [Google Scholar] [CrossRef]
  32. Chen, G.; Yang, S.; Wang, D.; Zhao, L.; Zhou, T.; Jiang, J. Review of the Preparation of Fe3O4 Based on Sol-gel Method. Guangdong Chem. Ind. 2017, 44, 41–42. [Google Scholar]
  33. Cai, W.; Wan, J. Facile synthesis of superparamagnetic magnetite nanoparticles in liquid polyols. J. Colloid Interface Sci. 2007, 305, 366–370. [Google Scholar] [CrossRef] [PubMed]
  34. Zhang, Y.; Chai, C.P.; Luo, Y.J.; Wang, L.; Li, G.P. Synthesis, structure and electromagnetic properties of mesoporous Fe3O4 aerogels by sol–gel method. Mater. Sci. Eng. B 2014, 188, 13–19. [Google Scholar] [CrossRef]
  35. Guo, Y.; Xiao, Z. Preparation of magnetic Fe3O4/SiO2 Nano-composite Particles by the Methods of Sol-Gel. J. Jilin Inst. Archit. Civ. Eng. 2011, 28, 78–80. [Google Scholar]
  36. Lu, T.; Wang, J.; Yin, J.; Wang, A.; Wang, X.; Zhang, T. Surfactant effects on the microstructures of Fe3O4 nanoparticles synthesized by microemulsion method. Colloids Surf. A Physicochem. Eng. Asp. 2013, 436, 675–683. [Google Scholar] [CrossRef]
  37. Hao, J.J.; Chen, H.L.; Ren, C.L.; Yan, N.; Geng, H.J.; Chen, X.G. Synthesis of superparamagnetic Fe3O4 nanocrystals in reverse microemulsion at room temperature. Mater. Res. Innov. 2010, 14, 324–326. [Google Scholar] [CrossRef]
  38. Sun, L.; Zhan, L.; Shi, Y.; Chu, L.; Ge, G.; He, Z. Microemulsion synthesis and electromagnetic wave absorption properties of monodispersed Fe3O4/polyaniline core–shell nanocomposites. Synth. Met. 2014, 187, 102–107. [Google Scholar] [CrossRef]
  39. Lv, H.; Jiang, R.; Li, Y.; Zhang, X.; Wang, J. Microemulsion-mediated hydrothermal growth of pagoda-like Fe3O4 microstructures and their application in a lithium–air battery. Ceram. Int. 2015, 41, 8843–8848. [Google Scholar] [CrossRef]
  40. Abdullaeva, Z.; Kelgenbaeva, Z.; Nagaoka, S.; Matsuda, M.; Masayuki, T.; Koinuma, M.; Nishiyama, T. Solvothermal Synthesis of Surface-Modified Graphene/C and Au-Fe3O4 Nanomaterials for Antibacterial Applications. Mater. Today Proc. 2017, 4, 7044–7052. [Google Scholar] [CrossRef]
  41. Jiang, X.; Wang, F.; Cai, F.; Zhang, X. Trisodium citrate-assisted synthesis of highly water-dispersible and superparamagnetic mesoporous Fe3O4 hollow microspheres via solvothermal process. J. Alloys Compd. 2015, 636, 34–39. [Google Scholar] [CrossRef]
  42. Zeng, X.; Yang, B.; Li, X.; Li, R.; Yu, R. Solvothermal synthesis of hollow Fe3O4 sub-micron spheres and their enhanced electrochemical properties for supercapacitors. Mater. Des. 2016, 101, 35–43. [Google Scholar] [CrossRef]
  43. Ghasemi, E.; Heydari, A.; Sillanpää, M. Superparamagnetic Fe3O4@EDTA nanoparticles as an efficient adsorbent for simultaneous removal of Ag(I), Hg(II), Mn(II), Zn(II), Pb(II) and Cd(II) from water and soil environmental samples. Microchem. J. 2017, 131, 51–56. [Google Scholar] [CrossRef]
  44. Ding, C.; Pan, G.; Zhang, M. Study on preparation of starch-coated Fe3O4 and its phosphate removal properties. Chin. J. Environ. Eng. 2011, 5, 2167–2172. [Google Scholar]
  45. Zhou, Q.; Wang, X.; Liu, J.; Zhang, L. Phosphorus removal from wastewater using nano-particulates of hydrated ferric oxide doped activated carbon fiber prepared by Sol–Gel method. Chem. Eng. J. 2012, 200–202, 619–626. [Google Scholar] [CrossRef]
  46. Wang, T.; Gao, Y.; Jin, X.; Chen, Z. Simultaneous removal of Pb (II) and Cr(III) from wastewater by magnetite nanoparticles. Chin. J. Environ. Eng. 2013, 7, 3476–3482. [Google Scholar]
  47. Yan, L.; Li, S.; Yu, H.; Shan, R.; Du, B.; Liu, T. Facile solvothermal synthesis of Fe3O4/bentonite for efficient removal of heavy metals from aqueous solution. Powder Technol. 2016, 301, 632–640. [Google Scholar] [CrossRef]
  48. Zarei, S.; Niad, M.; Raanaei, H. The removal of mercury ion pollution by using Fe3O4-nanocellulose: Synthesis, characterizations and DFT studies. J. Hazard. Mater. 2018, 344, 258–273. [Google Scholar] [CrossRef] [PubMed]
  49. Khanjanzadeh, H.; Behrooz, R.; Bahramifar, N.; Gindl-Altmutter, W.; Bacher, M.; Edler, M.; Griesser, T. Surface chemical functionalization of cellulose nanocrystals by 3-aminopropyltriethoxysilane. Int. J. Biol. Macromol. 2018, 106, 1288–1296. [Google Scholar] [CrossRef] [PubMed]
  50. Yang, P.; Moloney, M.G.; Zhang, F.; Ji, W. Surface Hydrophobic Modification of Polymers with Fluorodiazomethanes. Mater. Lett. 2018, 210, 295–297. [Google Scholar] [CrossRef]
  51. Qi, D.; Zhang, H.; Tang, J.; Deng, C.; Zhang, X. Facile Synthesis of Mercaptophenylboronic Acid-Functionalized Core−Shell Structure Fe3O4@[email protected] Magnetic Microspheres for Selective Enrichment of Glycopeptides and Glycoproteins. J. Phys. Chem. C 2010, 114, 9221–9226. [Google Scholar] [CrossRef]
  52. Yu, X.; Tian, X.; Wang, S. Adsorption of Ni, Pd, Pt, Cu, Ag and Au on the Fe3O4 (111) surface. Surf. Sci. 2014, 628, 141–147. [Google Scholar] [CrossRef]
  53. Laurent, S.; Forge, D.; Port, M.; Roch, A.; Robic, C.; Elst, LV.; Muller, R.N. Magnetic iron oxide nanoparticles: Synthesis, stabilization, vectorization, physicochemical characterizations, and biological applications. Chem. Rev. 2008, 108, 2064–2110. [Google Scholar] [CrossRef] [PubMed]
  54. Li, H.; Zhang, Y.; Wang, S.; Wu, Q.; Liu, C. Study on nanomagnets supported TiO2 photocatalysts prepared by a sol-gel process in reverse microemulsion combining with solvent-thermal technique. J. Hazard. Mater. 2009, 169, 1045–1053. [Google Scholar] [CrossRef] [PubMed]
  55. Liu, T.Y.; Hu, S.H.; Liu, K.H.; Liu, D.M.; Chen, S.Y. Study on controlled drug permeation of magnetic-sensitive ferrogels: Effect of Fe3O4 and PVA. J. Control. Release 2008, 126, 228–236. [Google Scholar] [CrossRef] [PubMed]
  56. Abu-Much, R.; Meridor, U.; Frydman, A.; Gedanken, A. Formation of a three-dimensional microstructure of Fe3O4-poly(vinyl alcohol) composite by evaporating the hydrosol under a magnetic field. J. Phys. Chem. B 2006, 110, 8194–8203. [Google Scholar] [CrossRef] [PubMed]
  57. Luo, S.; Liu, Y.; Rao, H.; Wang, Y.; Wang, X. Fluorescence and magnetic nanocomposite Fe3O4@SiO2@Au MNPs as peroxidase mimetics for glucose detection. Anal. Biochem. 2017, 538, 26–33. [Google Scholar] [CrossRef] [PubMed]
  58. Ga, Y.; Zhu, G.; Ma, T. Progress in Fe3O4 magnetic nanoparticles and its application in biomedical fields. Chem. Ind. Eng. Prog. 2017, 36, 973–980. [Google Scholar]
  59. Jiao, L.; He, X.; Wang, L.; Zhang, L.; Ma, Y. Preparation of Fe3O4 and Their Modification. Guangdong Chem. Ind. 2016, 43, 127–128. [Google Scholar]
  60. Han, C.J.; Sheng, N.; Zhu, C.; Akiyama, T. Cotton-assisted combustion synthesis of Fe3O4/C composites as excellent anode materials for lithium-ion batteries. Mater. Today Proc. 2017, 5, 187–195. [Google Scholar]
  61. Wang, P.; Wang, X.; Yu, S.; Zou, Y.; Wang, J.; Chen, Z.; Alharbi, N.S.; Ahmed, A.; Hayat, T.; Chen, Y.; et al. Silica coated Fe3O4 magnetic nanospheres for high removal of organic pollutants from wastewater. Chem. Eng. J. 2016, 306, 280–288. [Google Scholar] [CrossRef]
  62. Mostafaei, M.; Hosseini, S.N.; Khatami, M.; Javidanbardan, A.; Sepahy, A.A.; Asadi, E. Isolation of recombinant Hepatitis B surface antigen with antibody-conjugated superparamagnetic Fe3O4/SiO2 core-shell nanoparticles. Protein Expr. Purif. 2018, 145, 1–6. [Google Scholar] [CrossRef] [PubMed]
  63. Nie, L.; Yang, H.; Jiang, P. The Research Progress of Magnetic Fe3O4/Mesoporous Silica Composite Microspheres. Chin. J. Biomed. Eng. 2017, 36, 348–353. [Google Scholar]
  64. Gao, F.; Botella, P.; Corma, A.; Blesa, J.; Dong, L. Monodispersed Mesoporous Silica Nanoparticles with Very Large Pores for Enhanced Adsorption and Release of DNA. J. Phys. Chem. B 2009, 113, 1796–1804. [Google Scholar] [CrossRef] [PubMed]
  65. Wang, Y.; Li, B.; Zhang, L.; Peng, L.; Wang, L.; Zhang, J. Multifunctional magnetic mesoporous silica nanocomposites with improved sensing performance and effective removal ability toward Hg(II). Langmuir 2012, 28, 1657–1662. [Google Scholar] [CrossRef] [PubMed]
  66. Chen, H.; Xu, X.; Yao, N.; Deng, C.; Yang, P.; Zhang, X. Facile synthesis of C8-functionalized magnetic silica microspheres for enrichment of low-concentration peptides for direct MALDI-TOF MS analysis. Proteomics 2008, 8, 2778–2784. [Google Scholar] [CrossRef] [PubMed]
  67. Xue, J.; Xu, S.; Zhu, Q.; Qiang, L.; Ma, J. Preparation and Adsorption Properties of Amino Modified Magnetic Mesoporous Microsphere Fe3O4@SiO2@mSiO2. Chin. J. Inorg. Chem. 2016, 32, 1503–1511. [Google Scholar]
  68. Scanone, A.C.; Gsponer, N.S.; Alvarez, M.G.; Durantini, E.N. Photodynamic properties and photoinactivation of microorganisms mediated by 5,10,15,20-tetrakis(4-carboxyphenyl)porphyrin covalently linked to silica-coated magnetite nanoparticles. J. Photochem. Photobiol. A Chem. 2017, 346, 452–461. [Google Scholar] [CrossRef]
  69. Sun, Q.; Huang, Y.; Wang, J.; Guan, Z.; Li, M.; Zhou, J.; Wang, Y. Experimental study on mercury removal efficiencies of magnetic Fe3O4-Ag composite nanoparticles. Chem. Ind. Eng. Prog. 2017, 36, 1101–1106. [Google Scholar]
  70. Wang, H.; Liu, Y.G.; Zeng, G.M.; Hu, X.; Hu, X.; Li, T.; Li, H.; Wang, Y.; Jiang, L. Grafting of β-cyclodextrin to magnetic graphene oxide via ethylenediamine and application for Cr(VI) removal. Carbohydr. Polym. 2014, 113, 166–173. [Google Scholar] [CrossRef] [PubMed]
  71. Mallick, N.; Asfer, M.; Anwar, M.; Kumar, A.; Samim, M.; Talegaonkar, S.; Ahmad, F.J. Rhodamine-loaded, cross-linked, carboxymethyl cellulose sodium-coated super-paramagnetic iron oxide nanoparticles: Development and in vitro localization study for magnetic drug-targeting applications. Colloids Surf. A Physicochem. Eng. Asp. 2015, 481, 51–62. [Google Scholar] [CrossRef]
  72. Li, L.; Mak, K.Y.; Leung, C.W.; Chan, W.K.; Zhong, W.; Pong, P.W.T. Effect of synthesis conditions on the properties of citric-acid coated iron oxide nanoparticles. Microelectron. Eng. 2013, 110, 329–334. [Google Scholar] [CrossRef]
  73. Ebrahiminezhad, A.; Ghasemi, Y.; Rasoul-Amini, S.; Barar, J.; Davaran, S. Preparation of novel magnetic fluorescent nanoparticles using amino acids. Colloids Surf. B Biointerfaces 2013, 102, 534–539. [Google Scholar] [CrossRef] [PubMed]
  74. Ren, H.; Zhuang, H.; Liu, Y. Surface Modification of Fe3O4 Nanoparticles. Chem. Res. 2003, 14, 11–13. [Google Scholar]
  75. Zhu, C.; Song, J.; Qiu, L.; Zhang, Q. Preparation of magnetic Fe3O4 nano-particles modified with oleic acid at low-temperature and washed with distilled water. Chem. Ind. Eng. Prog. 2011, 30, 1552–1555. [Google Scholar]
  76. Shi, W.; Yang, J.; Wang, T.; Jin, Y. Magnetic Fe3O4 particles surface organic modification. Acta Phys.-Chim. Sin. 2001, 17, 507–510. [Google Scholar]
  77. Gui, S.; Shen, X.; Lin, B. Surface organic modification of Fe3O4 nanoparticles by silane-coupling agents. Rare Metals 2006, 25, 426–430. [Google Scholar] [CrossRef]
  78. Lou, M.; Wang, D.; Huang, W.; Zhao, H. The preparation and characterization of the MNPs mondified by silane-coupling agents. Shanghai J. Biomed. Eng. 2004, 25, 14–19. [Google Scholar]
  79. Portet, D.; Denizot, B.; Rump, E.; Lejeune, J.J.; Jallet, P. Nonpolymeric Coatings of Iron Oxide Colloids for Biological Use as Magnetic Resonance Imaging Contrast Agents. J. Colloid Interface Sci. 2001, 238, 37–42. [Google Scholar] [CrossRef] [PubMed]
  80. Berry, C.C.; Wells, S.; Charles, S.; Curtis, A.S.G. Dextran and albumin derivatised iron oxide nanoparticles: Influence on fibroblasts in vitro. Biomaterials 2003, 24, 4551–4557. [Google Scholar] [CrossRef]
  81. Kim, D.H.; Lee, S.H.; Im, K.H.; Kim, K.M.; Shim, I.B.; Lee, M.H.; Lee, Y.K. Surface-modified magnetite nanoparticles for hyperthermia: Preparation, characterization, and cytotoxicity studies. Curr. Appl. Phys. 2006, 6, e242–e246. [Google Scholar] [CrossRef]
  82. Lewin, M.; Carlesso, N.; Tung, C.H.; Tang, X.W.; Cory, D.; Scadden, D.T.; Weisslder, R. Tat peptide-derivatized magnetic nanoparticles allow in vivo tracking and recovery of progenitor cells. Nat. Biotechnol. 2000, 18, 410–414. [Google Scholar] [CrossRef] [PubMed]
  83. Martina, M.S.; Nicolas, V.; Wilhelm, C.; Ménager, C.; Barratt, G.; Lesieur, S. The in vitro kinetics of the interactions between PEG-ylated magnetic-fluid-loaded liposomes and macrophages. Biomaterials 2007, 28, 4143–4153. [Google Scholar] [CrossRef] [PubMed]
  84. Uner, B.; Ramasubramanian, M.K.; Zauscher, S.; Kadla, J.F. Adhesion interactions between poly (vinyl alcohol) and iron-oxide surfaces: The effect of acetylation. J. Appl. Polym. Sci. 2006, 99, 3528–3534. [Google Scholar] [CrossRef]
  85. Godovsky, D.Y.; Varfolomeev, A.V.; Efremova, G.D.; Moskvina, M.A. Magnetic properties of polyvinyl alcohol-based composites containing iron oxide nanoparticles. Adv. Funct. Mater. 1999, 9, 87–93. [Google Scholar] [CrossRef]
  86. Reddy, N.N.; Varaprasad, K.; Ravindra, S.; Reddy, G.V.S.; Reddy, K.M.S.; Reddy, K.M.M.; Raju, K.M. Evaluation of blood compatibility and drug release studies of gelatin based magnetic hydrogel nanocomposites. Colloids Surf. A Physicochem. Eng. Asp. 2011, 385, 20–27. [Google Scholar] [CrossRef]
  87. Cheng, Z.; Dai, Y.; Kang, X.; Li, C.; Huang, S.; Lian, H.; Hou, Z.; Ma, P.; Lin, J. Gelatin-encapsulated iron oxide nanoparticles for platinum (IV) prodrug delivery, enzyme-stimulated release and MRI. Biomaterials 2014, 35, 6359–6368. [Google Scholar] [CrossRef] [PubMed]
  88. Hu, X.; Tang, W.; He, S.; Yang, L.; Zhang, W.; Xiu, R. Preparation of Fe3O4/polyethyleneimine and its application for phosphate adsorption. Acta Sci. Circumst. 2017, 37, 4129–4138. [Google Scholar]
  89. Zhang, W.; Shen, H.; Xia, J.; Zhang, X.; He, X. Absorption Properties of Aqueous Ferrofluid Modified by Polyelthylenemine. Nanotechnol. Precis. Eng. 2007, 5, 125–128. [Google Scholar]
  90. He, S.; Zhang, F.; Cheng, S.; Wang, W. Preparation and Pb2+/Cd2+ adsorption of encapsulated Fe3O4/sodium polyacrylate magnetic crosslinking polymer. CIESC J. 2016, 67, 4290–4299. [Google Scholar]
  91. Yan, M.; Zhang, Q.; Xie, H.; Kong, J.; Qu, H. Load of PANI on nano-Fe3O4 and synergy catalytic degradation of dyes. China Environ. Sci. 2017, 37, 1394–1400. [Google Scholar]
  92. Cendrowski, K.; Sikora, P.; Zielinska, B.; Horszczaruk, E.; Mijowska, E. Chemical and thermal stability of core-shelled magnetite nanoparticles and solid silica. Appl. Surf. Sci. 2017, 407, 391–397. [Google Scholar] [CrossRef]
  93. Li, C.L.; Chang, C.J.; Chen, J.K. Fabrication of sandwich structured devices encapsulating core/shell SiO2/Fe3O4 nanoparticle microspheres as media for magneto-responsive transmittance. Sens. Actuators B Chem. 2015, 210, 46–55. [Google Scholar] [CrossRef]
  94. Feng, W.; Zhou, X.; Nie, W.; Chen, L.; Qiu, K.; Zhang, Y.; He, C. Au/[email protected] Fe3O4 nanocomposites for MR/CT dual-modal imaging guided-photothermal therapy: An in vitro study. ACS Appl. Mater. Interfaces 2015, 7, 4354–4367. [Google Scholar] [CrossRef] [PubMed]
  95. Pan, M.; Sun, Y.; Zheng, J.; Yang, W. Boronic acid-functionalized core-shell-shell magnetic composite microspheres for the selective enrichment of glycoprotein. ACS Appl. Mater. Interfaces 2013, 5, 8351–8358. [Google Scholar] [CrossRef] [PubMed]
  96. Snoussi, Y.; Bastide, S.; Abderrabba, M.; Chehimi, M. Sonochemical synthesis of Fe3O4@NH2-mesoporous [email protected]/Pd: A core/double shell nanocomposite for catalytic applications. Ultrason. Sonochem. 2018, 41, 551–561. [Google Scholar] [CrossRef] [PubMed]
  97. Sun, C.; Sun, K.; Tang, K. Extended Stöber method to synthesize core-shell magnetic composite catalyst Fe3O4@C-Pd for Suzuki coupling reactions. Mater. Chem. Phys. 2018, 207, 181–185. [Google Scholar] [CrossRef]
  98. Baskakov, A.O.; Solov Eva, A.Y.; Ioni, Y.V.; Starchikov, S.S.; Lyubutin, I.S.; Khodos, I.I.; Avilov, A.S.; Gubin, S.P. Magnetic and interface properties of the core-shell Fe3O4/Au nanocomposites. Appl. Surf. Sci. 2017, 422, 638–644. [Google Scholar] [CrossRef]
  99. Peng, Z.; Fang, X.; Yan, G.; Gao, M.; Zhang, X. Highly efficient enrichment of low-abundance intact proteins by core-shell structured Fe3O4[email protected] composites. Talanta 2017, 174, 845–852. [Google Scholar]
  100. Kandibanda, S.R.; Gundeboina, N.; Das, S.; Sunkara, M. Synthesis, characterisation, cellular uptake and cytotoxicity of functionalised magnetic ruthenium(II) polypyridine complex core-shell nanocomposite. J. Photochem. Photobiol. B Biol. 2018, 178, 270–276. [Google Scholar] [CrossRef] [PubMed]
  101. Meng, C.; Zhikun, W.; Qiang, L.; Chunling, L.; Shuangqing, S.; Song, H. Preparation of amino-functionalized Fe3O4@mSiO2 core-shell magnetic nanoparticles and their application for aqueous Fe3+ removal. J. Hazard. Mater. 2018, 341, 198–206. [Google Scholar] [CrossRef] [PubMed]
  102. Khashan, S.; Dagher, S.; Tit, N.; Alazzam, A.; Obaidat, I. Novel method for synthesis of Fe3O4@TiO2 core/shell nanoparticles. Surf. Coat. Technol. 2017, 322, 92–98. [Google Scholar] [CrossRef]
  103. Murata, J.; Ueno, Y.; Yodogawa, K.; Sugiura, T. Polymer/CeO2–Fe3O4 multicomponent core–shell particles for high-efficiency magnetic-field-assisted polishing processes. Int. J. Mach. Tools Manuf. 2016, 101, 28–34. [Google Scholar] [CrossRef]
  104. Kalska-Szostko, B.; Wykowska, U.; Satuła, D. Magnetic nanoparticles of core-shell structure. Colloids Surf. A Physicochem. Eng. Asp. 2015, 481, 527–536. [Google Scholar] [CrossRef]
  105. Zhang, M.; Chen, H.; Yang, X.; Lu, L.; Wang, X. The Development and Prospect of Nanometer Materials. Missiles Space Veh. 2000, 3, 11–16. [Google Scholar]
  106. Ramasamy, T.; Ruttala, H.B.; Gupta, B.; Poudel, B.K.; Choi, H.G.; Yong, C.S.; Kim, J.O. Smart chemistry-based nanosized drug delivery systems for systemic applications: A comprehensive review. J. Control. Release 2017, 258, 226–253. [Google Scholar] [CrossRef] [PubMed]
  107. Gong, J.; Tu, Z.; Duan, H.; Zhou, S. Study on the Histocompatibility and Tissue Distribution of Fe3O4 Nanoparticles. Chin. J. Tissue Eng. Res. 2016, 20, 7872–7877. [Google Scholar]
  108. Isiamian, J.P.; Hatamian, M.; Aval, N.A.; Rashidi, M.R.; Mesbahi, A.; Mohammadzadeh, M.; Jafarabadi, M.A. Targeted superparamagnetic nanoparticles coated with 2-deoxy-d-gloucose and doxorubicin more sensitize breast cancer cells to ionizing radiation. Breast 2017, 33, 97–103. [Google Scholar]
  109. Fakhri, A.; Tahami, S.; Nejad, P.A. Preparation and characterization of Fe3O4-Ag2O quantum dots decorated cellulose nanofibers as a carrier of anticancer drugs for skin cancer. J. Photochem. Photobiol. B Biol. 2017, 175, 83–88. [Google Scholar] [CrossRef] [PubMed]
  110. Zhang, L.; Lin, G.; Fan, X.; Wang, H.; Wang, J.; Gao, Y.; Xie, B.; Chen, Y.; Song, Z. Superparamagnetic Fe3O4 Nanoparticles in the Application of Water Model of Magnetic Resonance Imaging and CT Imaging in Rat Brain. Guangdong Trace Elem. Sci. 2017, 24, 10–16. [Google Scholar]
  111. Cui, L.; Hu, L.; Guo, X.; Zhang, Y.; Wang, Y.; Wei, Q.; Du, B. Kinetic, isotherm and thermodynamic investigations of Cu2+ adsorption onto magnesium hydroxyapatite/ferroferric oxide nano-composites with easy magnetic separation assistance. J. Mol. Liquids 2014, 198, 157–163. [Google Scholar] [CrossRef]
  112. Tian, X.; Wang, W.; Tian, N.; Zhou, C.; Yang, C.; Komarneni, S. Cr(VI) reduction and immobilization by novel carbonaceous modified magnetic Fe3O4/halloysite nanohybrid. J. Hazard. Mater. 2016, 309, 151–156. [Google Scholar] [CrossRef] [PubMed]
  113. Chang, J.; Zhong, Z.; Xu, H.; Yao, Z.; Chen, R. Fabrication of Poly(γ-glutamic acid)-coated Fe3O4 Magnetic Nanoparticles and Their Application in Heavy Metal Removal. Chin. J. Chem. Eng. 2013, 21, 1244–1250. [Google Scholar] [CrossRef]
  114. Jin, S.; Park, B.C.; Ham, W.S.; Pan, L.; Kim, K.Y. Effect of the magnetic core size of amino-functionalized Fe3O4-mesoporous SiO2 core-shell nanoparticles on the removal of heavy metal ions. Colloids Surf. A Physicochem. Eng. Asp. 2017, 513, 133–140. [Google Scholar] [CrossRef]
  115. Shen, S.; Wen, G.; Zheng, Y. Preparation of Rhizopus oryzae-Fe3O4 Composites and Their Cu2+ Adsorption Experiments. Anhui Agric. Sci. Bull. 2016, 22, 15–16. [Google Scholar]
  116. Zhao, J.; Liu, J.; Li, N.; Wang, W.; Nan, J.; Zhao, Z.; Cui, F. Highly efficient removal of bivalent heavy metals from aqueous systems by magnetic porous Fe3O4-MnO2: Adsorption behavior and process study. Chem. Eng. J. 2016, 304, 737–746. [Google Scholar] [CrossRef]
  117. Kilianová, M.; Prucek, R.; Filip, J.; Kolařík, J.; Kvítek, L.; Panáček, A.; Tuček, J.; Zbořil, R. Remarkable efficiency of ultrafine superparamagnetic iron(III) oxide nanoparticles toward arsenate removal from aqueous environment. Chemosphere 2013, 93, 2690–2697. [Google Scholar] [CrossRef] [PubMed]
  118. Chen, Z.; Li, Y. Preparation of magnetic ferriferous oxide and its application in purification of heavy metal ions in waste water. Inorg. Chem. Ind. 2015, 47, 20–22. [Google Scholar]
  119. Luo, X.; Wang, C.; Luo, S.; Dong, R.; Tu, X.; Zeng, G. Adsorption of As (III) and As (V) from water using magnetite Fe3O4-reduced graphite oxide-MnO2 nanocomposites. Chem. Eng. J. 2012, 187, 45–52. [Google Scholar] [CrossRef]
  120. Zhou, L.; Deng, H.; Wan, J.; Shi, J.; Su, T. A solvothermal method to produce RGO-Fe3O4 hybrid composite for fast chromium removal from aqueous solution. Appl. Surf. Sci. 2013, 283, 1024–1031. [Google Scholar] [CrossRef]
  121. Gupta, P.L.; Jung, H.; Tiwari, D.; Kong, S.H.; Lee, S.M. Insight into the mechanism of Cd(II) and Pb(II) removal by sustainable magnetic biosorbent precursor to Chlorella vulgaris. J. Taiwan Inst. Chem. Eng. 2017, 71, 206–213. [Google Scholar]
  122. Yi, X.; He, J.; Guo, Y.; Han, Z.; Yang, M.; Jin, J.; Gu, J.; Ou, M.; Xu, X. Encapsulating Fe3O4 into calcium alginate coated chitosan hydrochloride hydrogel beads for removal of Cu (II) and U (VI) from aqueous solutions. Ecotoxicol. Environ. Saf. 2018, 147, 699–707. [Google Scholar] [CrossRef] [PubMed]
  123. Ge, K.; Zhang, X.; Zhang, Y.; Liu, J.; Bi, H. Preparation and Capacitance Properties of Fe3O4-ODA/GO/PANI Nanocomposites. J. Mater. Sci. Eng. 2017, 35, 475–479. [Google Scholar]
  124. Guan, G.; Zou, M.; Feng, Q.; Lin, J.; Huang, Z.; Yan, G. Synthesis of Fe3O4/RGO composites and their electrochemical performance. J. Fuel Chem. Technol. 2017, 45, 362–369. [Google Scholar]
  125. Peng, H.; Liang, R.; Zhang, L.; Qiu, J.D. General preparation of novel core-shell heme protein-Au-polydopamine-Fe3O4 magnetic bionanoparticles for direct electrochemistry. J. Electroanal. Chem. 2013, 700, 70–76. [Google Scholar] [CrossRef]
  126. Zheng, N.; Zhou, X.; Yang, W.; Li, X.; Yuan, Z. Direct electrochemistry and electrocatalysis of hemoglobin immobilized in a magnetic nanoparticles-chitosan film. Talanta 2009, 79, 780–786. [Google Scholar] [CrossRef] [PubMed]
  127. Zhu, Y.; Tan, S.; Tang, R. AFP immunosensor based on Fe3O4-ferrocene nanocomposites study. Chin. J. Anal. Lab. 2017, 36, 477–480. [Google Scholar]
  128. Cai, K.; Zhang, Y.; Xu, Y.; Ma, F.; Zhang, L.; Zhou, H. One-pot Synthesis of Silver/Fe3O4 Particles and Its Catalytic Performances for the Reduction of 4-Nitrophenol. Ind. Saf. Environ. Prot. 2017, 43, 21–23. [Google Scholar]
  129. Zou, T.; Yi, Q.; Zhang, Y.; Xiang, B.; Zhou, X. Preparation of PdSn/Fe3O4-C Catalysts and Their Electro-catalytic Activities for The Oxidation of Ethyl Alcohol. Chin. J. Synth. Chem. 2017, 25, 480–486. [Google Scholar]
  130. Gu, Y.; Liu, G.; Zou, C.; Zhang, Z.; Liu, J.; Sun, M.; Cheng, G.; Yu, L. Ultrasonic Synthesis and Application in Catalytic 4-Nitrophenols Reduction of Au/Fe3O4. Chin. J. Inorg. Chem. 2017, 33, 787–795. [Google Scholar]
  131. Gao, X. Effect of nano Fe3O4 on properties of PTFE-based high temperature resistant sealing material. China Synth. Resin Plast. 2016, 33, 38–40. [Google Scholar]
  132. Gao, Z.; Peng, X.; Zhang, H.; Luan, Z.; Fan, B. Montmorillonite-Cu(II)/Fe(III) oxides magnetic material for removal of cyanobacterial Microcystis aeruginosa and its regeneration. Desalination 2009, 247, 337–345. [Google Scholar] [CrossRef]
  133. Ito, D.; Nishimura, K.; Miura, O. Removal and recycle of phosphate from treated water of sewage plants with zirconium ferrite adsorbent by high gradient magnetic separation. J. Phys. Conf. Ser. 2009, 156, 012033. [Google Scholar] [CrossRef]
  134. Jiang, Y.; Deng, T.; Shang, Y.; Yang, K.; Wang, H. Biodegradation of phenol by entrapped cell of Debaryomyces sp. with nano-Fe3O4 under hypersaline conditions. Int. Biodeterior. Biodegrad. 2017, 123, 37–45. [Google Scholar] [CrossRef]
  135. Fang, Q.; Lin, J.; Zhan, Y.; Yang, M.; Zheng, W. Synthesis of Hydroxyapatite/Magnetite/Zeolite Composite for Congo Red Removal from Aqueous Solution. Environ. Sci. 2014, 35, 2992–3001. [Google Scholar]
  136. Yuan, J.; Mao, M.; Cao, Y.; Wang, J. Preparation and properties of Fe3O4 nanoparticles/natural rubber composites. New Chem. Mater. 2015, 43, 33–36. [Google Scholar]
  137. Liu, H.; Li, X.; Wei, B.; Xu, F. Synthesis of super-paramagnetic Fe3O4 nanoparticles and its Fenton-like properties. Chin. J. Environ. Eng. 2017, 11, 3525–3531. [Google Scholar]
  138. Guo, B.; Ouyang, J.; Yang, H. Adsorption Performance to Methylene Blue by Nano-Fe3O4Assembled in Lumen of Halloysite Nanotubes. J. Chin. Ceram. Soc. 2016, 44, 1655–1661. [Google Scholar]
  139. Zhou, L.; Jin, J.; Liu, Z.; Liang, X.; Shang, C. Adsorption of acid dyes from aqueous solutions by the ethylenediamine-modified magnetic chitosan nanoparticles. J. Hazard. Mater. 2011, 185, 1045–1052. [Google Scholar] [CrossRef] [PubMed]
  140. Ai, L.; Zhang, C.; Chen, Z. Removal of methylene blue from aqueous solution by a solvothermal-synthesized graphene/magnetite composite. J. Hazard. Mater. 2011, 192, 1515–1524. [Google Scholar] [CrossRef] [PubMed]
  141. Ghosh, S.; Badruddoza, A.Z.M.; Hidajat, K.; Uddin, M.S. Adsorptive removal of emerging contaminants from water using superparamagnetic Fe3O4 nanoparticles bearing aminated β-cyclodextrin. J. Environ. Chem. Eng. 2013, 1, 122–130. [Google Scholar] [CrossRef]
  142. Mohan, D.; Sarswat, A.; Singh, V.K.; Alexandre-Franco, M.; Pittman, C.U., Jr. Development of magnetic activated carbon from almond shells for trinitrophenol removal from water. Chem. Eng. J. 2011, 172, 1111–1125. [Google Scholar] [CrossRef]
  143. Zhang, M.; Xiao, F.; Xu, X.Z.; Wang, D.S. Novel ferromagnetic nanoparticle composited PACls and their coagulation characteristics. Water Res. 2012, 46, 127–135. [Google Scholar] [CrossRef] [PubMed]
  144. Liu, B.; Chen, X.; Zheng, H.; Wang, Y.; Sun, Y.; Zhao, C.; Zhang, S. Rapid and efficient removal of heavy metal and cationic dye by carboxylate-rich magnetic chitosan flocculants: Role of ionic groups. Carbohydr. Polym. 2018, 181, 327–336. [Google Scholar] [CrossRef] [PubMed]
  145. Xu, B.; Zheng, H.; Wang, Y.; An, Y.; Luo, K.; Zhao, C.; Xiang, W. Poly (2-acrylamido-2-methylpropane sulfonic acid) grafted magnetic chitosan microspheres: Preparation, characterization and dye adsorption. Int. J. Biol. Macromol. 2018, 112, 648–655. [Google Scholar] [CrossRef] [PubMed]
  146. Zhou, Z.; Shan, A.; Zhao, Y. Synthesis of a novel magnetic polyacrylamide coagulant and its application in wastewater purification. Water Sci. Technol. 2017, 75, 581–586. [Google Scholar] [CrossRef] [PubMed]
  147. Liu, D.; Wang, P.; Wei, G.; Dong, W.; Hui, F. Removal of algal blooms from freshwater by the coagulation–magnetic separation method. Environ. Sci. Pollut. Res. 2013, 20, 60–65. [Google Scholar] [CrossRef] [PubMed]
  148. Lu, A.H.; Salabas, E.L.; Schüth, F. Magnetic nanoparticles: Synthesis, protection, functionalization, and application. Angew. Chem. Int. Ed. 2007, 46, 1222–1244. [Google Scholar] [CrossRef] [PubMed]
Figure 1. Scheme of the hydrothermal preparation process of Fe3O4@C composite particles and its adsorption on dyes.
Figure 1. Scheme of the hydrothermal preparation process of Fe3O4@C composite particles and its adsorption on dyes.
Processes 06 00033 g001
Figure 2. Scheme of co-precipitation synthesis of Nano-Fe3O4.
Figure 2. Scheme of co-precipitation synthesis of Nano-Fe3O4.
Processes 06 00033 g002
Figure 3. Scheme of sol-gel synthesis of Nano-Fe3O4.
Figure 3. Scheme of sol-gel synthesis of Nano-Fe3O4.
Processes 06 00033 g003
Figure 4. Scheme of Micro-emulsion synthesis of Nano-Fe3O4.
Figure 4. Scheme of Micro-emulsion synthesis of Nano-Fe3O4.
Processes 06 00033 g004
Figure 5. Four different structures of magnetic polymer composite microspheres: (a) Core-shell structure; (b) Shell-core structure; (c) Diffusion structure; (d) Sandwich structure.
Figure 5. Four different structures of magnetic polymer composite microspheres: (a) Core-shell structure; (b) Shell-core structure; (c) Diffusion structure; (d) Sandwich structure.
Processes 06 00033 g005
Table 1. Optimization of Experimental Conditions in the Synthesis of Nano-Fe3O4 and Its Effect.
Table 1. Optimization of Experimental Conditions in the Synthesis of Nano-Fe3O4 and Its Effect.
Preparation MethodsParticle SizeAdditiveOptimum RatioPollutantsAdsorption MannerOptimization EffectReferences
Coprecipitation method35 nmEthylenediaminetetraacetic acid15 mol FeCl3·6 H2O, 7.5 mol FeCl2·4 H2O,150 mL deionized waterAg(I), Hg(II), Mn(II), Zn(II), Pb(II) and Cd(II)Chemical adsorption and physical adsorptionThe Fe3O4 modified by ethylenediaminetetraacetic acid had reactive functional groups such as carboxyl groups and amino groups on its surface and could undergo chemical ligand exchange with heavy metal ions in water.[43]
Coprecipitation method60 nmSoluble starchReaction time = 2 h, pH = 3, equilibrium concentration = 1.0 mg/LPPhysical adsorptionThe Fe3O4 modified by starch has good dispersion, shown a monolayer disperse. The starch coats on the surface of Fe3O4 nanoparticle through steric hindrance and charge repulsion overcome the van der Waals force and magnetic attraction force.[44]
Sol-gel method-Activated carbon fiberpH = 2.0–6.0 at room temperaturePChemical adsorptionAfter modification through activated carbon fiber, the Fe3O4 had a significant increase in surface area and total pore volume. The modified Fe3O4 was positively charged and negatively charged by the electrostatic adsorption of phosphate ions. The ion exchange reaction occurred between phosphate and hydroxide.[45]
Coprecipitation methodAround 25 nm-pH = 6.0 at 25 °C, 4.0 g/L Fe3O4Pb and Cr ionsSingle phase adsorption Pb ion, multiphase adsorption for Cr ionThe prepared Fe3O4 particle had a larger BET. Under the van der Waals force and magnetic attraction, it had the link structure of the polygon, which increased the three-dimensional space between the particles. It had a spinel structure and high crystallization degree.[46]
Solvent heat method-BentoniteHeating for 8 h at 200 °CPb2+, Cd2+ and Cu2+ ionsChemical adsorptionThe composites composed of Fe3O4 and bentonite had reactive functional groups such as hydroxyl and carboxyl groups on the surface, which exhibited better adsorption of heavy metal ions. The specific surface area and total pore volume of composites were larger than those of pure Fe3O4, with higher magnetization saturation and lower remanence.[47]
Coprecipitation and Sol-gel method1–100 nmCellulose4.0 g FeCl2·4H2O, 8.0 g FeCl3·6H2O, 150 mL deionized water, Reaction temperature = 60 °C stirring time = 60 minMercury ionChemical adsorptionCellulose slender nanostructures were more likely to adsorb mercury ions. Cellulose-modified Fe3O4 has a reactive functional group such as CH2 on its surface and interacts with mercury ions.[48]
Table 2. Modification of Nano-Fe3O4 by different substances.
Table 2. Modification of Nano-Fe3O4 by different substances.
TypeMaterialsAdvantagesReferences
Inorganic small molecules(1) SiO2 and other oxides;
(2) Au, Co, Ni and other inorganic metals
The modification of SiO2 and other oxides can shield the dipole interaction between the magnetic nanoparticles to prevent the particles from agglomerating and facilitate further functionalization of the particle surface. At the same time, it had a good biocompatibility, hydrophilicity and stability. Encapsulation of inorganic metals can synthesize composite particles of core-shell structure, giving the magnetic nanoparticles rich and excellent physical properties.[57]
Organic small molecules(1) Ethanol, organic carboxyl, sulfur and silane coupling agent oil-soluble substances;
(2) Sodium oleate, sodium carboxymethylcellulose, β-cyclodextrin, citric acid, amino acids
Particle oil-soluble conversion to water-solubility was achieved by the interaction between the modifier and the stabilizer and the ligand exchange reaction resulting in water-soluble, oil-soluble and amphiphilic nanoparticles. Surfactant modification could control nanoparticle size and shape and changed surface properties of nanoparticle. Modification of silane coupling agents introduces reactive groups on the surface of nanoparticles to provide chemical selectivity for their further functionalization.[58]
Organic polymers(1) Glucose, starch, protein, peptides and other natural polymers;
(2) Polyethylene glycol, polyvinyl alcohol and other synthetic polymers
Natural biomolecules had a good biodegradability and biocompatibility, greatly improving the biocompatibility of magnetic particles and giving them special biological activity. Synthetic polymer modification could give the material a variety of different properties to meet the actual requirement. Biomacromolecules had excellent bioactivity and were a synthetic polymer-rich chemical-selective organic combination.[59]
Table 3. Methods for the modification of Nano-Fe3O4 and mechanism for the removal of heavy metals.
Table 3. Methods for the modification of Nano-Fe3O4 and mechanism for the removal of heavy metals.
Heavy MetalMethodsRemoval MechanismReferences
PbWith different amounts of glycerolSurface coordination, chemical adsorption.[118]
AsWith manganese dioxide and graphene oxideManganese dioxide can oxidize arsenic into pentavalent arsenic and graphene oxide can increase adsorption ability. [119]
CrWith Reduced graphene oxideElectrostatic adsorption and acid groups adsorption.[120]
HgWith cellulose The complex of mercury ion and cellulose on the surface of Fe3O4.[48]
Pb and CrWith micrococcusWeak electrostatic forces between cadmium ions (II) and carboxyl groups or hydroxyl groups; chemical bonding of lead (II) ions and amino groups.[121]
U and CuWith calcium alginate containing-chitosan hydrogel beadsChemical interaction of NH3-groups in Chitosan with -COOH groups in calcium alginate. Physical pore adsorption and electrostatic adsorption. [122]
Table 4. The application of modified Nano-Fe3O4 in treatment of other environmental pollutants.
Table 4. The application of modified Nano-Fe3O4 in treatment of other environmental pollutants.
PollutantsMethods for Modification of Nano-Fe3O4Removal PrinciplesReferences
Congo redWith hydroxyapatite and zeolite The interaction of the dye and Nano-Fe3O4 through Surface coordination, hydrogen bonding, Lewis acid base reaction.[135]
Natural rubberWith silane coupling agentThe Fe3O4 has high binding energy after modification and it was much easier to bond with rubber.[136]
Rhodamine BWith Fenton reaction in the presence of H2O2The surface of Fe3O4 formed complexes and hydroxyl radicals, resulting of degradation of dye.[137]
Methylene blueWith natural eloise under vacuum impregnation and high temperature pyrolysisA large number of hydroxyl groups on the surface of rocky oxidized methylene blue.[138]
Acid orangeWith ChitosanInteracting of ions of dye with the protonated amino ions of chitosan [139]
Methylene blueWith Graphene The positive charged oxygen-containing groups in Graphene attracted a negatively charged methylene blue.[140]
Bisphenol AWith amine-containing β-cyclodextrinHybrid effects of electrostatic, hydrophobic and van der Waals.[141]
Organics 2,4,6-trinitrophenolWith activated carbon Porous physical adsorption on the surface of activated carbon; Electrostatic adsorption and hydrogen bonding; Surface reaction; In the presence of dissolved oxygen, the phenols on the surface of activated carbon are gathered.[142]

© 2018 by the authors. Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (http://creativecommons.org/licenses/by/4.0/).
Processes EISSN 2227-9717 Published by MDPI AG, Basel, Switzerland RSS E-Mail Table of Contents Alert
Back to Top