Synthesis and antibacterial properties of a novel magnetic nanocomposite prepared from spent pickling liquors and polyguanidine

Magnetic nanoparticles have received much interest for their application in wastewater treatment because of their easy retrieval and reuse. However, the methods used to synthesise high saturation magnetization magnetic nanoparticles require expensive and pure precursors. In the current study, we explore the potential for using spent pickling liquor, a wastewater solution from steel factories, as the iron precursor for preparing iron oxide nanoparticles. Here, magnetic Fe3O4 nanoparticles were synthesized via the oxidation–precipitation of spent pickling liquors using a saturated solution of calcium hydroxide at room temperature. The Fe3O4 nanoparticles were then modified with antibacterial polyguanidine to form a nanocomposite. It was found that monodisperse magnetic Fe3O4 nanoparticles with a size in the range 20–30 nm and a high saturation magnetization value of 73.9 emu g−1 were synthesised. The Fe3O4 nanoparticles were successfully encapsulated with polyguanidine to form an Fe3O4/polyguanidine nanocomposite. FT-IR and TGA analysis results indicated the presence of the polymer on the Fe3O4 surface and the polymer content in the nanocomposite was about 15% (w/w). The Fe3O4/polyguanidine nanocomposite exhibited strong antibacterial activity against Escherichia coli (E. coli), demonstrating its potential for use in disinfecting wastewater.


Introduction
In recent years, magnetic materials have attracted intensive interest due to their potential applications in various elds, including biomedicine, 1,2 information storage, 3 catalysts, 4 and environmental treatment. [5][6][7][8] Magnetic nanoparticles are promising for industrial scale wastewater treatment due to their high adsorption capacity, easy separation and enhanced stability. Magnetic nanoparticles can be produced using a variety of synthesis methods and can also be modied with different agents to form nanocomposites for the aforementioned applications.
In metal processing industries, iron and steel parts are oen pickled in hydrochloric or sulfuric acid to remove the oxide layer from their surface before undergoing any further processing such as electroplating, metal nishing etc. The pickle solutions are gradually contaminated with dissolved metals through usage. As the metal concentration increases, the free acid concentration decreases and the pickling efficiency drops. To retain the high pickling efficiency, fresh concentrated acid is added from time to time to rejuvenate the bath but eventually it becomes spent and must be discarded. The waste generated by metal pickling industries is identied as an environmentally hazardous material.
Due to the high concentration of iron, spent pickling liquors (SPL) are possibly a cheap source of raw material for the production of iron materials. The conventional methods for SPL regeneration and metal recovery have been discussed in a recent detailed review. 9 Generally, the regeneration of SPL is carried out by oxidizing its dissolved iron chloride (FeCl 2 ) in a uidized bed reactor at about 800 C to form ferric oxide (Fe 2 O 3 ) and gaseous hydrochloric acid. This is a relatively expensive process and it still produces an environmental pollutant, gaseous hydrochloric acid. In addition, the Fe 2 O 3 recovered product has low economic value. Thus, it is important to develop a process that can produce a more valuable product from SPL with regard to both environmental considerations and processing cost.
For wastewater disinfection, most of the treatment methods involve chemicals and nanomaterials such as chlorine, ozone or Ag nanoparticles. These chemicals and materials possess high antibacterial activity. However, they exhibit some disadvantages: chlorine may harm the environment by forming toxic byproducts such as trihalomethanes and haloacetic acids, which are potentially carcinogenic; 10,11 ozone has no residual effects but it is sensitive to the presence of organic matters and can produce unknown toxic products; 12 Ag nanoparticles may also have negative effects on the environment and human health. 13,14 Hence, the development of safe antibacterial agents with high recovery or recycling ability has attracted considerable research interest in recent years.
In the last decade, guanidine-based polymers have attracted considerable attention as antibacterial materials due to their excellent biocide efficiency against a wide range of microorganisms. Zhang et al. have tested the antimicrobial activity of some polymeric guanidine and biguanidine salts against 10 bacterial and fungal species, and the determined MIC was not larger than 200 mg mL À1 . 15 Polyethylene hexamethylene biguanidine has been demonstrated by Wigdahl et al. to be a promising microbial candidate for anti-HIV compounds. 16 In addition, polyguanidines have good thermal stability, low corrosive activity and lower toxicity for humans than the currently used disinfectants. 17 However, the high water solubility restricts their potential application in some cases. There have been some studies reported recently about polyguanidine immobilization on different materials to form nonleaching antibacterial composites. Polyguanidine was used as a graing agent on polyamide, 18 polysulfone 19 or cellulose membranes. 20 Antibacterial experiments indicated a clearly enhanced antibiofouling performance of the modied ltration membranes. Recently, polyguanidine was also investigated for use in graphene oxide functionalization, in the presence of polyethylene glycol for dispersion improvement. The as-prepared composite material demonstrated an enhanced antibacterial activity against both Gram-negative bacteria Escherichia coli and Grampositive bacteria Staphylococcus aureus. 21 In our current study, we combine polyguanidine and Fe 3 O 4 magnetic nanoparticles to construct Fe 3 O 4 /polyguanidine nanocomposites possessing unique properties such as easy magnetic separation and anti-microbial activity that can be exploited in water purication applications. To the best of our knowledge, this antibacterial Fe 3 O 4 /polyguanidine magnetic nanocomposite has been synthesized for the rst time via the oxidation-precipitation of SPL and modication with polyguanidine. The chemical and phase structures of the product were characterized, and the magnetic properties and antibacterial activity of the sample against E. coli were evaluated.

Chemicals
Samples of chloride pickling liquors (pH 0.1-0.2, total iron 151.2 g L À1 , trace amounts of other heavy metals, e.g. Mn 26.7 mg L À1 , Cr 16.9 mg L À1 and Cu 9.3 mg L À1 ) were collected from Hoa Phat Steel Factory, Vietnam. Calcium hydroxide (Ca(OH) 2 ) of reagent grade was received from Xilong Scientic Co., China. Polyguanidine (Biopag-D) was ordered from Fito-Line Co., Russia. All chemicals were used as received without further purication.

Preparation of magnetic nanocomposites
Fe 3 O 4 nanoparticles were synthesized via an oxidation-precipitation process using spent pickling liquors according to our recent work. 22 Briey, 4.5 mL SPL was added drop-wise into a beaker containing 600 mL of saturated Ca(OH) 2 solution at room temperature. The solution was stirred vigorously in air for about 45 min. The black precipitate of the Fe 3 O 4 was separated using an external magnet, and was then washed with distilled water until the pH reached 7.
For the preparation of the Fe 3 O 4 /polyguanidine nanocomposite, 2 g puried Fe 3 O 4 nanoparticles was added into 20 mL aqueous polyguanidine solution, 25% (w/w). The mixture was sonicated for 5 min and then stirred mildly for 6 h. The black precipitate was collected using a magnet, and was subsequently rinsed with distilled water and ethanol before being dried at 40 C in a vacuum oven.

Characterisation
A eld emission scanning electron microscope (FE-SEM, HITA-CHI S-4800) equipped with an energy dispersive X-ray spectroscope (EDX) was used to examine the morphology and elemental composition of Fe 3 O 4 and the Fe 3 O 4 /polyguanidine nanocomposite. X-ray diffraction (XRD) patterns of the synthesized samples were taken with a Siemens/Bruker D5005 X-ray powder diffractometer over a 2q range from 10 to 70 , using Cu K a radiation (l ¼ 0.154 nm) with a step size of 0.03. Fourier transform infrared (FT-IR) spectra were recorded on a Thermo Scien-tic Nicolet iS10 FT-IR Spectrometer with Diamond ATR. Thermogravimetric analysis (TGA) was performed with a NETZSCH TG 209 F1 Libra instrument, from 25 C to 600 C in air (heating rate 10 C min À1 ). The magnetic properties of the samples were studied using a vibrating sample magnetometer (VSM, DMS 800, Quantum Design, Inc.). Saturation magnetization (M s ) and coercive eld (H c ) were measured at room temperature with the magnetic eld ranging from À10 to 10 kOe.

Antibacterial tests
The disk diffusion method was used to evaluate the antibacterial activity of Fe 3 O 4 and the Fe 3 O 4 /polyguanidine nanocomposite against E. coli (ATCC 8739). Mueller-Hinton agar was used as the growth medium. Briey, 8 mm sterile disks impregnated with the magnetic nanoparticles (0.5, 1.7 and 5.0 mg mL À1 ) were placed on an E. coli cultured agar plate. Aer being incubated for 24 h at 37 C, the diameter of the inhibition zone was determined.

The inuence of synthesis conditions on the magnetic properties
The direct oxidation-precipitation of the SPL in the saturated Ca(OH) 2 solution produced magnetic nanoparticles. In the current study, we investigated the inuence of synthesis conditions, including the speed of stirring and the volume of the precursor solution, on the morphology and magnetic properties of the nanoparticles. It was found that the magnetic properties of the material changed strongly with the variation of stirring speed and precursor concentration. The sample reached the highest M s value of 74 emu g À1 at the stirring speed and precursor concentration of 400 rpm and 1.25 g L À1 , respectively (Table 1). This sample was used for our further studies.
For the antibacterial tests, the surface of the sample was modied with polyguanidine to improve its antibacterial activity. Fig. 1 shows the FE-SEM images of the sample before and aer modication with the polymer. As shown in Fig. 1a, the iron oxide nanoparticles are fairly monodisperse and have a spherical shape with an average size of about 30 nm. A similar morphology was obtained for the nanocomposite (Fig. 1b).  24 indicates that the nanoparticles synthesized from the spent pickling liquors in our work are single phase. Aer encapsulating with polyguanidine to form the nanocomposite, no signication change in the phase structure was identied.
The chemical composition of both samples was determined using energy-dispersive X-ray spectroscopy (EDX). The EDX spectra of the nanoparticles synthesized from the spent pickling liquor demonstrate the presence of carbon (5.15% atomic), as well as Fe and O, indicating a little impurity of the product ( Fig. 3a and Table 2). EDX data of the nanocomposite conrm the presence of polyguanidine by showing the coexistence of Fe, O, C, N and Cl in the spectrum ( Fig. 3b and Table 2). From the EDX results, the polyguanidine content in the Fe 3 O 4 /polyguanidine is determined to be approximately 18% (w/w), which is similar to that determined using TGA (see the next section).

FT-IR analysis
FT-IR analysis provides direct evidence for the formation of Fe 3 O 4 and the Fe 3 O 4 /polyguanidine nanocomposite (Fig. 4). The FT-IR spectrum of the sole Fe 3 O 4 nanoparticles (curve a) shows the characteristic absorption band at 576 cm À1 , which is attributed to the stretching vibration of the Fe-O bond of    This journal is © The Royal Society of Chemistry 2018 25,26 Broad bands at around 3449 and 1634 cm À1 can also be seen, and these should be attributed respectively to the stretching and bending vibrations of the -OH groups on the surface of the nanoparticles.
In the spectrum of the Fe 3 O 4 /polyguanidine nanocomposite (curve b), in addition to the absorption peak at 574 cm À1 (which is due to the Fe-O stretching vibrations of the Fe 3 O 4 nanoparticles), one can observe the characteristic absorption peaks of polyguanidine at around 3183.7 and 1466 cm À1 , which could be related to the valence and bending vibrations of the amine group, respectively. The C-N stretching vibration band at 1355 cm À1 can also be observed, which is due to the existence of the secondary amine from polyguanidine. The peaks at around 2930 and 2865 cm À1 were assigned to the valence asymmetric and symmetric oscillations of the CH 2 groups, respectively. The absorption peak at around 1639 cm À1 was very intensive, which was probably due to the overlap of the peak at 1634 cm À1 of Fe 3 O 4 with the absorption peak of the C]N stretching vibration from polyguanidine. The broad peak at around 3449 cm À1 of Fe 3 O 4 was also displaced to 3408 cm À1 because of the overlap with the peak of the N-H vibration from polyguanidine. 27

TGA analysis
The amount of polyguanidine on the Fe 3 O 4 surface was determined using thermal analysis TGA. As shown in Fig. 5, the Fe 3 O 4 nanoparticles exhibit very good thermal stability below 600 C with insignicant weight loss in the TGA curve. On the other hand, the TGA curve of the nanocomposite indicates a low weight loss of about 5% starting from room temperature and continuing up to 200 C due to dehydration, followed by a more obvious loss of weight starting at 250 and continuing up to 400 C, which is related to the decomposition of polyguanidine. 15 The amount of polyguanidine in the nanocomposite is about 15%.

Magnetic properties
The magnetization hysteresis curves of Fe 3 O 4 and the Fe 3 O 4 / polyguanidine nanocomposite were obtained using VSM magnetometry under a magnetic eld ranging from À10 to 10 kOe at room temperature, and are shown in Fig. 6. These curves display the high saturation magnetization of both the pure and composite nanoparticles, with no coercivity or remanence, indicating that the samples are super-paramagnetic. As can be

Antibacterial activity
In this work, the antibacterial activity of the as-prepared Fe 3 O 4 and Fe 3 O 4 /polyguanidine nanocomposite at different concentrations of 5.0, 1.7 and 0.5 mg mL À1 was tested against E. coli using the agar diffusion method. Pure polyguanidine (Biopag-D) was also tested under similar conditions for comparison. The inhibition zones were determined and are shown in Table 3 and Fig. 7. It can be seen that sole polyguanidine with a concentration of 5.0 mg mL À1 presented an inhibition zone of 14 mm in diameter, which is almost the same as that reported by Grigor'eva et al. 27 On the other hand, the Fe 3 O 4 nanoparticles exhibited no antibacterial activity. The synthesized Fe 3 O 4 /polyguanidine nanocomposite had a relatively high antibacterial effect, presenting an inhibition zone of about 10 mm when the concentration was 5.0 mg mL À1 . With a low content of polyguanidine in the nanocomposite (about 15%), the obtained results indicate a higher antibacterial efficiency of the Fe 3 O 4 / polyguanidine nanocomposite material than that of sole polyguanidine.

Conclusion
In this study, a simple synthesis procedure was developed to prepare a novel magnetic Fe 3 O 4 /nanocomposite, using spent pickling liquors (SPL) and antibacterial polyguanidine. The analytical results from FE-SEM, EDX and FT-IR measurements indicated that a magnetite (Fe 3 O 4 )/polyguanidine nanocomposite with a size of about 30 nm and a saturation magnetization value of 62.1 emu g À1 was successfully synthesized via oxidation-precipitation in a calcium hydroxide solution of SPL under normal atmospheric pressure and room temperature. The amount of polyguanidine on the surface of the Fe 3 O 4 nanoparticles was about 15% (w/w). This Fe 3 O 4 /polyguanidine nanocomposite exhibits a high antibacterial activity against Escherichia coli, and we believe that the obtained nanocomposite has the potential to be used in disinfection and biomedical applications. In our next work, the antibacterial activity of the Fe 3 O 4 /polyguanidine nanocomposite against various types of microorganism (including bacteria, viruses and fungi) will be investigated.

Conflicts of interest
There are no conicts to declare.