Nickel Based Nano Particles as Adsorbents in Water Purification Methods - A Review
K. Ravindhranath and Mylavarapu Ramamoorty
Department of Chemistry, K. L. University, Green Fields, Vaddeswaram - 522 502, Guntur Dt., Andhra Pradesh.
Corresponding Author E-mail: email@example.com
Nickel based nano particles are metallic Ni and NiO. These materials find wide utility in various fields in view of their high surface potentials, surface area, semi conducting nature, reduction and complexing tendencies. The present review is mainly aimed at the investigations made in using these nano nickel particles as adsorbents in purifying water. The synthesis of nano particles of Ni/NiO adopting the conventional physical/chemical methods, their draw backs and the progress so far made in the green synthesis of particles using plant extracts as reducing, capping and stabilizing argents, are also emphatically discussed. Further, the potential areas of research with respect to the green synthesis of the said nano particles and their applications to water purification are identified and comprehensively presented.KEYWORDS:
Review; nano particles; water treatment; phytomethods; Ni/NiO; adsorbents; pollutantsDownload this article as:
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Nickel has two manifestations of nano particles: nickel metal and nickel oxide. These two classes of nano particles possess magnetic properties, biocompatibility, catalytic activity, antimicrobial activity and sorption nature. Further, nano-NiO is a semiconductor (band gap: 3.6 to 4.9 eV) with high chemical stability and electron transfer ability (Thema et al., 2016). Hence these nano particles are finding wide applications in diverse fields such as electronics, energy appliances (Karmhag R et al, 2000), biomedicines (Mariam A.A. et al, 2014), sensors, waste water treatment and in the various organic syntheses based on reduction, hydrogenation, alkylation etc(Li X.K et al, 2005, Saxena A et al, 2007, Alonso F et al, 2008, 2009 Dhakshinamoorthy A, 2008).Investigations are also being made in using these nano particles as adsorbents in water remediation methods as detailed hereunder.
The present review is a comprehensive account of the new research trends in green methods of synthesis of Ni and NiOnano particles and their applications to the wastewater treatment.
Synthesis of Nickel Based Nanoparticles by Physical /Chemical Routes
Literature reports the synthesis of nickel nano particles using microwave assisted synthesis (Lai et al, 2006, Xu et al., 2008; Eluri and Paul, 2012), micro-emulsion synthesis (Ai et al., 2003; Chen and Wu, 2000; Khan, 2008), chemical reduction technique using suitable reducing agents like sodium borohydride (Hou et al., 2005), and hydrazine hydrate (Wu and Chen, 2003, Roselina and Azizan, 2012; Wu et al., 2012; Sudhasree et al., 2014), reversed micelles method (Harish et al., 2011), thermal decomposition of nickel (II) acetylacetonate in alkylamines (Chen et al., 2007) and sol-gel methods (Jia et al. 2008).
Various methods to fabricate NiOnano particles are reported in the literature which includes surfactant-mediated method (Wang et al., 2002), low-pressure spray pyrolysis (Lenggoro et al., 2003), precipitation-cum-calcination (Deng and Chen, 2004), simple liquid phase process (Wang et al., 2005), solvothermal method (Ghosh et al., 2006), chemical precipitation (Mahaleh et al., 2008), microwave-assisted hydrothermal method (Zhu et al., 2011), sol-gel method (Alagiri et al., 2012), thermal decomposition (Ghosh et al., 2006; Zhang et al., 2010) and other techniques (Cherrey et al., 2002; Tao and Wei, 2004; Wang and Ke, 1996).
Of all these methods, the sol-gel methods are simple and convenient. In these methods, the growth of nano particles are controlled by suitable choice of precursors, reducing agents and/or capping agents to stabilize the nano particles (NowsathRifaya et al, 2012, Pandey and Manivannan, 2015). The commonly used precursors are nickel chloride, nickel sulphate, nickel acetate, nickel nitrate, nickel carboxylate etc. and the reducing agents are sodium borohydride, sodium hydride, hydrazine hydrate, organic amine (oleyl amine), primary aliphatic amines (dodecylamine), sodium hypophosphite etc. and thecapping agents are polyvinyl pyrrolidone (PVP), sodium dodecyl sulfate, cetyltrimethylammonium bromide (CTAB) and theorganic solvents used are ether, unsaturated alkynes, ethylene glycol, diethylene glycol, triethylene glycol, polyethylene glycol, hexane, cyclohexane and octane etc(NowsathRifaya et al, 2012, Pandey and Manivannan, 2015). The reducing agents convert the nickel ions to nickel atoms and thus formed metal atoms are ‘oozed out’ from the aqueous or organic mother liquors in the atomic/molecular forms as they are insoluble. Then they start growing by aggregation called Ostwald ripening, and when they come to the nano-size, the capping agents have to arrest the further growth or otherwise, the particles pass through the colloidal stage and precipitate (Sun, Y.P et al , 2007, Pandian, C. J. et al, 2015). Here, the success or failure of the synthesis depends upon the growth conditions and much based on adopting the theoretical principles of crystal growth using homogeneous precipitations whether it is in aqueous or organic media (Vogel, 1989, Ling Bing Kong et al, 2015). When metal oxide nano particles are to be prepared, in place of reducing agents, precipitating agents are needed for precipitating the metal ions as hydroxides and/or hydrated oxide under controlled conditions besides the usual capping and stabilizing agents.
Applications of Nickel Based Nanoparticles
Anti Microbial Activity
The microbial activities of nano particles are attributed to their shape and size, surface area, chemical nature and functional groups present on the solution–solid interface and photo-sensitivity. Antibacterial activity of nickel nanoparticles against E. coli, L. cassie, S. aureus, P. aerugenosaand B. subtilisare studied by Chevellier, 1996.Nickel nanoparticles synthesized from leaf extract of Ocimum sanctum are shown good antimicrobial activity against pathogenic Gram-negative (E. coli, K. pneumoniae, and S. typhi), Gram-positive (B. subtilis, S. epidermidis) bacteria and fungi (C. albicans, C. tropicalis, A. fumigatus, A. clavatus, and A. niger) (Pandian et al., 2015). Antimicrobial activities of nickel and nickel oxides nanoparticles are reported against urinary tract infectious bacterial pathogens by Ravikumar et al., 2012.
Antibacterial activity of Nickel (Ni) and bimetallic Cu–Ni nanoparticles are tested against the human pathogens: Staphylococcus aureus (gram-negative) and Escherichia coli (gram-positive) (Pang et al., 2009; Kumar et al., 2010; Liliana et al., 2014). Ratiram GC et al., 2015 synthesized nano Ni using Nickel nitrate as precursor, hydrazine hydrate as reducing agent and ehtylenediamine as capping agent and the nano particles so obtained are probed for their antibacterial activities against human bacterial pathogens such as Klebsiellasp, Staphylococcus aureus, Enterococcus faecalis, Escherichia coli, and Pseudomonas aeruginosa by using well diffusion method.
Khashan et al., 2016synthesized colloidal NiO nanoparticles and theirantimicrobial activity was investigated against pseudomonas aurogenisa, Escherichia coli, Staphylococcus aureus and Streptococcus pneumonia.
Mechanism of Antimicrobial Activity
By virtue of high surface area and redox potential (Ni2+/Ni) -0.14 V, the surface Ni atoms on nano Ni particles get oxidized to Ni2+ with the release of highly reactive oxygen species (ROS) when the nano particles are in contact with water. The ROS passes through the cell membranes and denature the proteins and subsequently results in cellular content leakage. Ni2+ and/or free radicals prevent or block the transport of electrons in the microbial cell and thereby cause the cell death (Pandian et al., 2015). Similar observations are reported with nano particles of Ag with regard to their antimicrobial nature (Mallikarjuna et al., 2011; Kenneth et al., 2010).
Removal of Pollutants
The nano particles of Ni or NiO are less investigated in the treatment of waste waters, in contrast to the large literature available pertaining to their applications in other fields of research viz., catalytic, anti-microbial, bio-medical, Electrochemical, sensor etc.,
Nickel oxide is considered as good adsorbent due to its chemical and magnetic properties (Roya et al., 2012, 2013). UzairaRafique et al (2012) synthesized nanoNiO using co-precipitation method and the obtained particles were probed for their adsorption nature towards Sulphate and Nitrate. It was noted that the adsorbent was effective at pH: 7 for the removal of both anions from waters.
Srivastava N K et al, 2014 prepared nanoNiO using Nickel acetate as precursor. To the ethanolic solution of precursor, oxalic acid solution was added to obtain a green gel. Then the gel was dried, grounded and calcinated at elevated temperature between 300oC to 700oC to obtain the nano particles. Thus synthesized nanoNiO was investigated for its sorption nature with respect to various physicochemical parameters such as pH, sorbent dosage, agitation time, initial Conc. of Chromium ion. The adsorbent was found to be effective.
FereshtehMotahari et al, 2015, hydrothermallysynthesized β-Ni(OH)2 using Nickel nitrate and sodium hydroxide as precursors and H2acacen as stabilizer. Then β-Ni(OH)2 was subsequently calcinated to obtain nanoNiO. The effectiveness of so prepared nanoNiO in the removal of dye Rhodamine B from polluted waters was investigated and found to be successful.
Amira M et al, 2015 studied the extraction of Pb2+ from waters using nano Ni as adsorbent. The nano Ni was prepared adopting two different routes. In one, aqueous solution of NaOH was added to the Nickel Nitrate solution and the precipitate of Ni(OH)2 obtained was filtered, washed, dried and calcinated at 400oC. In the other route, an ethanolic solution of Oxalic acid was added to the ethanolic solution of Nickel Nitrate and the resulting precipitate was filtered, washed with ethanol and acetone, dried and calcinated at 400oC. It was found that the nano Ni prepared in the second route was found to be more effective in the removal of potential pollutant, Pb2+ from polluted waters.
Mingyi Tang et al, 2014, by using nano Ni particles loaded poly(acrylamide-co-acryl acid) as a catalyst, studied the removal of potential organic pollutant, 4-nitrophenol, with NaBH4 a reducing agent. Roya Nateghi et al, 2012 investigated the removal of mono azo Orange II dye from waste waters using commercially available nanoNiO as adsorbent and found to be effective. The surface of the adsorbent diatomite was modified with nanoNiO oxide and was used in the extraction of basic red 46 (Khalighi et al., 2012). Under optimum extraction conditions, the adsorption capacity was found to be 105.61 mg/g (pH:7; temp. 25 ± 1°C, equilibration time: 1 hr; 200 rpm; initial conc. of dye: 25 ppm).
The nickel based nano particles have wide applications in view of their catalytic, magnetic and semi conducting nature. They are used as electrodes in solid oxide fuel cells, catalysts in various industrial syntheses, coloring agents for enamels and paints and in making nano wires and fibers. As these materials are magnetic in nature, they are used in making permanent magnets, magnetic fluids, magnetic recording media, and electronic parts. They are also used in plastic and textile industries and in making adhesive formulations and further, they are used in making lightweight aerospace components and also as gas sensors (Chen and Hsieh, 2002; Kurihara et al., 1995; Dooley et al., 1994; Biji and Khadar, 2001; Kodama, 1999; Li F et al., 2002; Matsumiya et al., 2002).
Green Synthesis and Applications to Water Treatment
All the above said chemical and physical methods used in the synthesis of nickel based nanoparticles are costly, involve complicated procedures and cause environmental pollution besides low productivity (Nagaraj et al., 2011). The nano particles produced by these methods have less biocompatibility and less antioxidant and microbial activities besides high cytotoxic nature. Hence, researchers are trying to develop green methods based bio-materials especially with the plant extracts (Abdul-RaheimM et al, 2016, Shakeel Ahmed et al, 2016; PalaniselvamKuppusamy et al, 2016).
Hence, eco-friendly synthetic methods based on biomaterials like plant extracts and microbes are interesting the researchers in developing simple, economical and effective methodologies for the simple fact that the plants are the limit-less sources of diverse chemical compounds which can serve as reducing, capping and stabilizing agents. The chemical compounds such as vitamins, sugar, proteins, peptides, polyphenols etc., that present in flora materials may serve this purpose by virtue of possessing different functional groups such as -OH, -HCHO, -COOH, C=O, esters, amino, amide groups etc. that can be oxidized or reduced or involved in the complex formation with the surface functional groups of the nano Ni/NiO particles (Kowshik et al., 2003; Singh et al., 2005; Nadagouda and Varma, 2006; Raveendran et al., 2006; Raj and Viswanathan, 2011).
This mode of research is interesting the researchers as the nano particles thus synthesized are bio-compatible and eco-friendly and in the event of their contamination in the water bodies, they are unlikely to be hazardous (Vaseem et al, 2013, PaskalisSahaya et al, 2014, Amira M. Mahmoud, 2015).
Synthesis of Nickel (Ni) Nanoparticles Using Plants
The nano Ni particles are easily oxidizable and to make them stable in aqueous solutions, capping agents are used. The conventional synthetic capping agents are toxic. Hence, researchers are looking towards plants whose bio-extracts contain compounds that can serve as reducing agents as well as capping agents viz. sugars, vitamins., polyphenols etc. Only few reports are Available in this Aspect of Synthesis
Chen et al, 2014, used the extracts of Medicago sativa (alfalfa) for the synthesis of Ni nano particles. The precursor used was Ni(NO3)2 and the reduction was carried out at room temperature and the obtained particles were freeze-dried for one day to obtain nano particles of Ni. Vaseem et al, 2013, found that glucose served both as reducing and capping agent, when Nickel salt solution was treated with glucose and ammonia. The aldehyde group in the glucose causes the reduction of Ni2+ to Ni and in doing so, it is oxidized to carboxylate group. Thus obtained caroxylate groups and hydroxyl groups in the glucose, are bound to the the surface of Ni nano particles and thereby, prevent the aggregation of Ni particles i.e. the nano particles are capped.
Dutta and Dolui, 2011, synthesized nano Ni using naturally occurring tanic acid as reducing and stabilizing agent. Mariam et al., (2014) used leaves extract of Azadirachtaindica for the synthesis. AbhijitKar and Ajoy Kumar Ray, 2014, on pyralysis of the petals of Hibiscus rosa-sinensis soaked in Nickel chloride solution obtained 10 to 200 nm sized nano Ni particles. These particles were found to have carbon on their surface which prevented the agglomeration and responsible for stability of particles.
Muhmmad Imran Den and Aneela Rani, 2016, reviewed the literature available on chemical and green methods of synthesis of Ni and NiOnano particles and the influence of the method of preparation on the physicochemical properties of the said nano particles. Alfalfa plant extract (Huimei et al., 2014), Desmodiumgangeticum root extract (Sudhasree et al., 2014), root tuber extract of Dioscorea (Elephant Yam) (Helen and Rani , 2015) and leaf extract of Coriander (Vasudeo and Pramod, 2016) were also used for the synthesis of nano Ni.
Angajala et al., 2014, used leaf extract of AeglemarmelosCorrea (AmC) as a reducing and capping agent and NiCl2⋅6H2O as precursor in synthesizing nano Ni. It was observed that Sitosterol, naturally present in the leaves extract of sterol plant, was bound to the nano particles through its –OH groups and thereby imparting its anti-inflammatory properties to the nanoparticles. Using NiO as precursor and the Annonasquamosa leaves extract as reducing and capping agent, Mamuru et al, 2015, synthesized nano Ni at pH:7.
Synthesis of Nickel Oxide (Nio) Nanoparticles Using Plants
Mariam et al., (2014) synthesized NiO2 and Ni nanoparticles using leaf extracts of Psidiumguajava and Azadirachtaindicarespectively. Rambutan peel waste was found to serve as capping and stabilizing agent in the synthesis of NiOnanocrystals using Nicklesulphate as precursor (Yuvakkumar et al., 2014). Thema et al., 2016 synthesizednanoNiO with Agathosmabetulina natural extract.
Some investigations were made using microbes viz., bacteria, yeast, fungi, as reducing and/or stabilizing agents in the preparation of NiOnano particles. Salvadori et al, 2014 used dead biomass of filamentous fungus while Ullah et al, 2014 used Rhizopusnigricans fungus. Using the bacteria, Microbacterium sp. MRS-1, Sathyavathiet al, 2014 synthesized NiOnano particles.
All these particles prepared from these bio-means are found to have biocompatibility because the capping, reducing and stabilizing agents are derived from biomaterials such as sugars and flavonoids which are not cytotoxic.
Removal of Dyes and Pollutants Using Green Synthesized Nano Ni/Nio
Pandian C J et al, 2015 synthesized Ni nanoparticles by treating Ni(NO3)2 solution with the leaves extract of Ocimum sanctum at 60o C and the resulting particles were freeze dried for one day. Thus obtained particles were used as adsorbent in the removal of dyes viz., eosin, crystal violet and orange II and also anions, NO3- and SO42- from polluted water and found to be effective.
Comparisonwith Other Similar Inorganic Materials
Of the Ti, Al, Fe,Ni-based nano materials, it is evident that asnano Al is highly reactive and thermodynamically unstable when in contact with water or air due to its high reduction potentials, Eo = -1.677 V and hence, only the stable Al2O3 in different manifestations, are probed as adsorbents in water purification methods. The nano particles of Fe and Ni are less reactive compared to Al as their standard reduction potentials are:Eo = -0.440 and -0.236 V respectively, and further, Ni exhibits passivity for oxidation. Hence, researchers are employing zero valentnano particles as well as their oxides of Fe and Ni as adsorbents in developing the water treatment methods. Iron oxide or its oxyhydroxide have many forms viz., Fe3O4, α-Fe2O3, γ-Fe2O4 and FeOOH while Ni has only one oxide NiO. This is because of more oxidizable tendency of Iron than Nickel and is attributed to the formation of continuous and protective oxide film on Ni surface resulting the passive nature to the Ni and in fact, Ni is used as protective coating for steals. These oxide forms are endowed with strong adsorption forces of diverse nature i.e. electrostatic interactions, ion exchanging and ion-association tendencies, complex formations etc. and these are of immense use in evoking affinity between the pollutants and surface of the adsorbent, which results in the successful extraction of pollutants from wastewaters. In this aspect, iron oxide based adsorbents are extensively being probed in view of their diverse nature than Nickel oxide adsorbent, NiO and further, the iron based materials are cheap and bio-degradable. Some investigations are also devoted to control the oxidation tendencies of the nano particles of Fe and Ni by alloying them with another stable metal or by entrapping in the matrix of some templates or polymer (synthetic or natural). These zero valent Fe and Ni are used as catalysts in the oxidation of oxidizable organic and inorganic impurities in wastewaters.
Coming to Ti, the most stable state is +4 and compounds with -1, 0, +2 and +3 are easily converted to the tetravalent state when the compounds are in contract with air, water or in presence of oxidation environment (Lee J D, 2010). Hence, methodologies of water treatment are confined to TiO2, aversatile adsorbent.
Thus the nano particles of Al, Ti, Fe and Ni-based materials that are used as adsorbents in water/waste water treatments, comprise of : Al2O3; TiO2, zero-valent Fe and its various oxides/oxyhydroxides, zero-valent Ni and its only oxide: NiO. These materials are being investigated with respect to green methods of syntheses and their water remediation methods as thenano particles derived by using plant extracts has a changed surface morphology than the conventionally prepared nano particles and it is attributed to the adsorption of some bio-compactable compounds present in the natural extracts (Vaseem et al, 2013). One investigation made by AbhijitKar and Ajoy Kumar Ray, 2014, using petals of Hibiscus rosa-sinensis plant as ‘template’ is interesting to quote here. In this investigation, the advantage of the naturally existing minute pores in the petals is exploited in synthesizing uniform-nano Ni. These novel concepts are to be investigated in conjunction with water treatment methods in exploring or indentifying such hidden advantages bestowed on us by the nature. The surface characteristics of nano materials based on inorganic materials can be tailor-made to our specific needs and requirements in adsorptive removal of pollutants from waters.
Conclusions and Future Perspectives
The review reflects that the investigations pertaining to the plant and microbial mediated routes of synthesizing nano particles of Ni and NiO are limited. The particles synthesized by these routes are endowed with biocompatibility, stability and enhanced sorption nature. Further, only few investigations are reported using these nano particles as adsorbents in wastewater treatment.
The Following Are the Identified Areas of Research
Synthesis of Nano Ni and NiO
Plant extracts containing compounds that serve as reducing and capping agents in stabilizing the nano particles of Ni and NiO are to be identified in the available flora.
Plant materials having uniform micropores may serves as template or substrate and they may help in the production of the same size nano particles of Ni/NiO, as has been investigated by AbhijitKar and Ajoy Kumar Ray (2014), with regard to the synthesis of nano Ni using Hibiscus flower petals as bio-template.
By suitably tailor making the conditions of synthesis, isotropic/ anisotropic Ni/NiOnano particles of definite shape and size can be fabricated and thereby, enhancing surface potentials which may be exploited for binding the pollutants to the surface.
Microbial mediated synthesis of nano Ni and NiO are less investigated and this is another vital aspect for research
Surface morphological studies are to be under-taken in understanding the mechanisms of formation of nano particles of Ni/NiO.
Nano Ni/Nio as Adsorbent in Wastewater Treatment
Nano Ni exhibits sorption nature mainly via reduction (redox potential for Ni2+/Ni is -0.24V) while nanoNiO via complex formation. There are only few reports available in literature pertaining to the removal of some dyes, organic pollutants, Pb2+, Chromate, Nitrate and Sulphates as has been reviewed above. It is quite surprising. Hence methodologies are to be developed in the purification of waste waters especially for the removal of toxic cations and anions and organic pollutants using bio-synthesized nano particles because the surface of the bio-synthesized particles are supposed to be energized for conducive sorption via complex formation or reduction or both.
By doping the nano-oxides with rare earth elements, the catalytic activity for the reduction or oxidation of organic pollutants in wastewaters may be enhanced. This is a significant aspect of pollution-control research.
Nano-particles when used as compact beds in continuous extraction methods, cause great pressure head loss. This can be avoided by using open columns or films or beads or pellets doped with the nano particles of Ni/NiO. Thus by immobilizing the nano particles of Ni/NiO on a certain polymeric subtract (synthetic or natural), the sorption potentialities of nano particles can be explored without compromising for the slow rate of filtration and thereby the pollutants can be effectively removed. These studies need to be explored. Further, regeneration studies of the active surface of the adsorbent after exhausted are to be investigated.
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