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International Journal of ChemTech Research 
CODEN( USA): IJCRGG ISSN : 0974-4290 
Vol.5, No.5, pp 2303-2308, July-Sept 2013 
Nanotechnology in Waste Water Treatment: A Review 
Prachi1*, Pranjali Gautam1, Deepa Madathil1, A. N. Brijesh Nair2 
1School of Bio Sciences and Technology, 2School of Mechanical and Building 
Sciences, VIT University, Vellore, Tamilnadu, India – 632014 
*Corres.Author: prachi.11sep@gmail.com 
Abstract: Nanoparticles have a great potential to be used in waste water treatment. Its unique characteristic 
of having high surface area can be used efficiently for removing toxic metal ions, disease causing microbes, 
organic and inorganic solutes from water. Various classes of nanomaterials are also proved to be efficient for 
water treatment like metal-containing nanoparticles, carbonaceous nanomaterials, zeolites and dendrimers. 
The paper reviews recent advances on different nanomaterials (nanostructured catalytic membranes, 
nanosorbents, nanocatalysts, bioactive nanoparticles, biomimetic membrane and molecularly imprinted 
polymers (MIPs)) with their application in waste water treatment. Nanotechnology has lead to various 
efficient ways for treatment of waste water in a more precise and accurate way on both small and large scale. 
Keywords: Nanoparticles, Polymers, Nanosorbents, Nanocatalyst, Water contamination. 
Introduction 
Water contamination is one of the major problems which the world is facing today. Water contamination not 
only effect environment and human health, but it has also impacts on economic and social costs. There are 
various ways used commercially and non- commercially to fight this problem which is advancing day by day 
due to technological progress. Nanotechnology has also proved to be one of the finest and advance ways for 
waste water treatment. There are various reasons behind the success of nanotechnology and scientists are still 
working on further enhancement of its usage. Nanoparticles have very high absorbing, interacting and 
reacting capabilities due to its small size with high proportion of atoms at surface. It can even be mixed with 
aqueous suspensions and thus can behave as colloid. Nanoparticles can achieve energy conservation due to 
its small size which can ultimately lead to cost savings. Nanoparticles have great advantage of treating water 
in depths and any location which is generally left out by other conventional technologies. 
Since water treatment by using nanoparticles has high technology demand, its usage cost should be managed 
according to existing competition in market (Crane et al., 2012)1. There are various recent advances on 
different nanomaterials (nanostructured catalytic membranes, nanosorbents, nanocatalysts, bioactive 
nanoparticles, biomimetic membrane and molecularly imprinted polymers (MIPs)) for removing toxic metal 
ions, disease causing microbes, organic and inorganic solutes from water.
Deepa Madathil et al /Int.J.ChemTech Res.2013,5(5) 2304 
Nanosorbents 
Nanosorbents have very high and specific sorption capacity having wide application in water purification, 
remediation and treatment process. Commercialized nanosorbents are very few mainly from the U.S. and 
Asia but research is on going on in large numbers targeting various specific contaminants in water. Few 
advancements and applications of nanosorbents are given below. 
Table 1: Different specialization of nanosorbents 
S.No. Nanosorbent Specialization/Treatment 
1. Carbon-based nanosorbents Water containing nickel ions (Ni2+). (high specific surface area, 
excellent chemical resistance, mechanical strength, and good 
adsorption capacity) (lee et al., 2012)2 
2. CaptymerTM Contaminants (perchlorate, nitrate, bromide and uranium) branched 
macromolecules forming globular micro particles (Aquanano, n.d.)3 
3. Regenerable polymeric 
nanosorbent 
Many organic and inorganic contaminants in wastewater (Dunwell 
Group, n.d.) 4 
4. Nanoclays Hydrocarbons dyes and phosphorus (Carrado et al., 2009)5 
5. Carbo-Iron The activated carbon for sorption while the elementary iron is 
reactive and can reduce different contaminants (Helmholtz Centre 
for Environmental Research, n.d.)6 
6. Nano networks Complex three-dimensional networks caused by the ion beam 
providing better efficiency (Dongqing et al., 2010)7 
Magnetic nanosorbents also helps in treating waste water and is proved very interesting tool especially for 
organic contaminants removal (Bull Mater, 2011)8. Since most of the contaminants are not of magnetic 
nature filtration aids are needed to absorb which is generally followed by magnetic separation. The 
nanosorbents used for magnetic separation are prepared by coating magnetic nanoparticles with specific 
ligands presenting specific affinity (Apblett et al., 2001)9. Different methods like magnetic forces, cleaning 
agents, ion exchangers and many more are used to remove nanosorbents from the site of treatment to avoid 
unnecessary toxicity. Regenerated nanosorbents are always cost effective and promoted more for 
commercialization. 
Nanocatalysts 
Nanocatalysts are also widely used in water treatment as it increases the catalytic activity at the surface due 
its special characteristics of having higher surface area with shape dependent properties .It enhances the 
reactivity and degradation of contaminants. The commonly used catalytic nanoparticles are semiconductor 
materials, zero-valence metal and bimetallic nanoparticles for degradation of environmental contaminants 
such as PCBs (polychlorinated biphenyls), azo dyes, halogenated aliphatic, organochlorine pesticides, 
halogenated herbicides, and nitro aromatics (Xin et al., 2011)10. The catalytic activity has been proved on 
laboratory scale for various contaminants. Since hydrogen is used in making active catalyst in large scale by 
redox reactions, there is need in reducing its consumption and maintain hydrogen economy by directly 
making catalysts in metallic form. 
Silver (Ag) nanocatalyst, AgCCA catalyst, N-doped TiO2 and ZrO2 nanoparticles catalysts have been made 
which is highly efficient for degradation of microbial contaminants in water and are reusable as well (Shalini 
et al., 2012)11. TiO2-AGS composite is very efficient for Cr (VI) remediation in waste water due to the 
modification done in TiO2 nanoparticles leading to absorption band shift from UV light activity to natural 
light degradation. Specific interactions between hydrogen and the Pd based nanoparticles were proved (Kan 
et al., 2012)12. Waste waters with specific contaminants like traces of halogenated organic compounds 
(HOCs) can be selectively biodegraded using advanced nanocatalytic activities. The contaminants (HOCs) 
are first converted into organic compounds using nano-sized Pd catalysts which are followed by its
Deepa Madathil et al /Int.J.ChemTech Res.2013,5(5) 2305 
biodegradation in treatment plant. The nanocatalyst can be recycled back and reused due its property of 
having ferromagnetism which helps it to be easily separated. 
The reductants for the reaction can be Hydrogen or Formic acid depending on the level of contamination 
(Hildebrand et al., 2008)13.It has also been found that the nanocatalyst of silver and amidoxime fibres which 
is made by coordination interactions can be reactivated many times using simple tetrahydrofuran treatment 
and thus can be used efficiently for degradation of organic dyes (Zhi-Chuan Wua et al., 2010)14. 
Palladium incorporated ZnO nanoparticles were found to be having very high photocatytic activity for 
removal of E.coli from water which was studied through several analytical studies done using different 
concentrations of Pd in ZnO nanoparticles (Khalil et al., 2011)15. 
Nano-WO3 having photo-catalytic activity for E.coli disinfection in water showed increased activity when 
used in conjunction with 355 nm pulse laser which is synthesized by sol–gel method (Khalil et al., 2009)16. 
In situ remediation by using Palladium nanoparticles (PdNPs) as catalyst for the reduction of Cr (VI) to Cr 
(III) has been studied (Marcells et al., 2009)17.Another approach for enhancing the effect is by combining 
nanosorbents with a catalyst for the combined sorption and degradation of contaminants. Nanocatalysis has 
proved to very efficient in water treatment. 
Nanostructured catalytic membranes (NCMS) 
Nanostructured catalytic membranes are widely used for water contamination treatment. It offers several 
advantages like high uniformity of catalytic sites, capability of optimization, limiting contact time of catalyst, 
allowing sequential reactions and ease in industrial scale up. 
Several functions which include decomposition of organic pollutants, inactivation of microorganisms, anti-bio 
fouling action, and physical separation of water contaminants are performed by nanostructured TiO2 
films and membranes under UV and visible-light irradiation (Hyeok et al., 2009)18.The N-doped “nut-like” 
ZnO nanostructured material forming multifunctional membrane is very efficient in removing water 
contaminants by enhancing photo degradation activity under visible light irradiation. It also showed 
antibacterial activity and helped in producing clean water with constant high flux benefiting the water 
purification field (Hongwei et al., 2012)19. 
Various studies have been done regarding immobilization of metallic nanoparticles in membrane (such as 
cellulose acetate, polyvinylidene fluoride (PVDF), polysulfone, chitosan, etc.) for effective degradation and 
dechlorination of toxic contaminants which offers several advantages like high reactivity, organic 
partitioning, prevention of nanoparticles, lack of agglomeration and reduction of surface passivation (Jian et 
al., 2009)20. 
Nanocomposites films have been prepared from polyetherimide and palladium acetate and specific 
interactions between hydrogen and the Pd based nanoparticles have been studied proving the efficiency in 
water treatment. The metal nanoparticles were generated within the matrix by annealing the precursor film 
under different conditions using both in situ and ex situ method. This provides opportunities to design 
materials having tunable properties (Clémenson et al., 2010)21. 
With the advancement in nanotechnology several novel nanostructured catalytic membranes has been 
synthesized with increased permeability, selectivity, and resistance to fouling. The techniques include 
bottom-up approaches and hybrid processes for enabling its multi functionality (Volodymyr et al., 2009)22. 
Bioactive nanoparticles 
Water pollution has caused lots of infectious diseases due to various contaminating pathogens. Many of the 
microorganisms acting as pathogens are antibiotic resistance and so it’s very difficult to remove them from 
water. Recently the concept of bioactive nanoparticles has emerged which has given the alternative of new 
chlorine –free biocides (2008)23. 
Silver nanoparticles (AgNPs) can be synthesized extracellularly by bacteria Bacillus cereus which is having 
very high antibacterial potential. The silver resistant strain was exposed to different concentrations of silver
Deepa Madathil et al /Int.J.ChemTech Res.2013,5(5) 2306 
salt (AgNO3) and studied with the help of various analytical instruments like High Resolution Transmission 
Electron Micrography (HRTEM), X-ray diffraction (XRD) and Energy Dispersive spectroscopy (EDS) 
(Prakash et al., 2011)24. 
MgO nanoparticles and Cellulose acetate (CA) fibres with embedded Ag nanoparticles are very effective 
biocides against Gram-positive bacteria, Gram-negative bacteria and bacterial spores (Nora et al., 2005)25. 
Current and emerging nanotechnology approaches for the detection of microbial pathogens will aid microbial 
and pathogen detection as well as diagnostics. 
Biomimetic membrane for water treatment 
Biomimetic membranes are developed by Albuquerque-based Sandia National Laboratories and the 
University of New Mexico. It represents a new and advanced way for water purification based on its specific 
design and fabrication (2011)26. 
The invention uses self-assembly and atomic layer deposition tuned nanopores which generally gives high-flux 
desalination. The membranes remove impurities like salt and others from water with applied pressure 
powered by electrical energy. The nonporous bio mimetic design enables high salt rejection and faster water 
flow at lower driving pressures generally used is around 5.5 bars. The process basically uses reverse osmosis 
principle with doubled efficiency due to its low pressure requirement. 
Tremendous improvement was found in water purification with cost effectiveness due to this innovative 
functionalization which combines use of nano-fabrication techniques and inspiration from protein channels 
in biological membranes. Some of the molecular design principles of natural porous systems were 
transcribed into robust synthetic porous membranes. 
The technology uses pressure driven water filtration. Some of the advantages of this technique are 
advancements, reduced cost, better water flux and improved efficiency with high salt rejection (Jeffrey et al., 
2011)27. A biomimetic membrane can be prepared by vesicle fusion on a dense water-permeable support, 
such as an NF membrane. The process uses electrostatic stiching principle by maximizing attraction and 
minimizing repulsion between head groups. Biomimetic membrane should have high permeability and 
selectivity with chemical stability (Kaufman et al., 2011)28. Chemical stability can be provided using various 
synthetic biomimetic analogues like of aquaporins, carbon nanotubes etc. Many more advancements are 
expected from this technology in coming years. 
Molecularly imprinted polymers (MIPs) 
Molecularly imprinted polymers have recently emerged as one of very fine techniques for various biological, 
pharmaceutical and environmental applications. The high selectivity of the polymers is due to its synthetic 
procedure where a template molecule is linked to suitable monomer(s) having functional groups by covalent, 
semi covalent or non-covalent bonds providing subsequent specific binding sites to the MIPs. The left 
imprint after the removal of template from polymer helps in recognizing properties of the MIP and are 
generally called binding sites. 
Molecular imprinting is basically a process of free radical polymerization of a functional monomer and a 
cross linker. It works very selectively and has great potential to act as absorbents. It has been used for 
detection and treatment of water pollutants even at very low concentrations (Caro et al, 2006)29. 
Molecularly imprinted materials can be also used in combination with catalysts forming novel composite 
adsorbent or catalyst systems. The use of MIPs is advantageous over commonly used sorbents due to nature 
of being or performing selective extraction .MIP nanoparticles are encapsulated in nanofibres using 
electrospinning method that can be used for various pollution control applications including water treatment 
(Costas Kiparissides, 2010)30. 
Molecularly imprinted nanospheres (nano MIPs) are also developed for the specific adsorption of micro 
pollutants from hospital waste water by using mini-emulsion polymerization technique which is very 
complex but can run in a single reaction chamber resulting in particles with size( 50 nm-500 nm). Magnetic
Deepa Madathil et al /Int.J.ChemTech Res.2013,5(5) 2307 
core can be introduced to allow the final separation of the nano MIPs and more important of the recognized 
pollutants from waste water (Tino et al, 2009)31. 
Conclusion 
Nanotechnologies have made great improvements for handling water contamination problems and will 
clearly make further advancements in future. Nanotechnology based treatment has offered very effective, 
efficient, durable and eco friendly approaches. These methods are more cost-effective, less time and energy 
consuming with very less waste generations than conventional bulk materials based methods. However 
certain precautions are to be taken to avoid any threat to human health or environment due to the 
nanoparticles. 
The technology should be cost effective and friendly with ease in establishment and use. BCC research has 
concluded, in a report from 2011-12, that the total market for emerging nanotechnology products used in 
water treatment, including nanosorbents, will be only around €80 million in 2015. One can see that the large 
scale commercialisation of nanosorbents is to be expected only after some additional 10 years of applied 
research (Boehm, 2009)32.For the success of proper commercialization of nanotechnology based water 
treatment several technical, economical and social challenges has to be tackled properly. 
References 
1. Crane R. A., Scott T. B., (2012), Nanoscale zero-valent iron: Future prospects for an emerging water 
treatment technology. J Hazard Mater, pp 211-212. 
2. Lee X. J., Foo L. P. Y., Tan K. W., Hassell D. G., Lee L. Y., (2012), Evaluation of carbon-based 
nanosorbents synthesised by ethylene decomposition on stainless steel substrates as potential 
sequestrating materials for nickel ions in aqueous solution, Journal of Environmental Sciences, 24( 
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3. AquaNano, available at: www.captymer.com 
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15. Khalil A., Gondal M.A., Dastageer M.A., (2011), Augmented photocatalytic activity of palladium 
incorporated ZnO nanoparticles in the disinfection of Escherichia coli microorganism from water. 
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Improving Water Quality: Potentials and Risks. Nanotechnology Applications for Clean Water, pp 
233-247. 
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Clean Water, pp 39-46. 
19. Hongwei Bai, Zhaoyang liu, Darren Delai Sun, (2012), Hierarchical ZnO nanostructured membrane 
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20. Jian Xu, Leonidas Bachas, Dibakar Bhattacharyya, (2009), Synthesis of Nanostructured Bimetallic 
Particles in Poly ligand Functionalized Membranes for Remediation Applications. Nanotechnology 
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and challenges. Journal of Nanoparticle Research, 7, pp 331–342. 
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membranes-for-pressure-drivenwater-purification 
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30. Professsor Costas Kiparissides, (2010), Nanotechnology Meets Water Treatment, Dissemination 
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nanotechnology / environmental/ applications/ nan039b. 
*****
Deepa Madathil et al /Int.J.ChemTech Res.2013,5(5) 2309 
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Ww0

  • 1. International Journal of ChemTech Research CODEN( USA): IJCRGG ISSN : 0974-4290 Vol.5, No.5, pp 2303-2308, July-Sept 2013 Nanotechnology in Waste Water Treatment: A Review Prachi1*, Pranjali Gautam1, Deepa Madathil1, A. N. Brijesh Nair2 1School of Bio Sciences and Technology, 2School of Mechanical and Building Sciences, VIT University, Vellore, Tamilnadu, India – 632014 *Corres.Author: prachi.11sep@gmail.com Abstract: Nanoparticles have a great potential to be used in waste water treatment. Its unique characteristic of having high surface area can be used efficiently for removing toxic metal ions, disease causing microbes, organic and inorganic solutes from water. Various classes of nanomaterials are also proved to be efficient for water treatment like metal-containing nanoparticles, carbonaceous nanomaterials, zeolites and dendrimers. The paper reviews recent advances on different nanomaterials (nanostructured catalytic membranes, nanosorbents, nanocatalysts, bioactive nanoparticles, biomimetic membrane and molecularly imprinted polymers (MIPs)) with their application in waste water treatment. Nanotechnology has lead to various efficient ways for treatment of waste water in a more precise and accurate way on both small and large scale. Keywords: Nanoparticles, Polymers, Nanosorbents, Nanocatalyst, Water contamination. Introduction Water contamination is one of the major problems which the world is facing today. Water contamination not only effect environment and human health, but it has also impacts on economic and social costs. There are various ways used commercially and non- commercially to fight this problem which is advancing day by day due to technological progress. Nanotechnology has also proved to be one of the finest and advance ways for waste water treatment. There are various reasons behind the success of nanotechnology and scientists are still working on further enhancement of its usage. Nanoparticles have very high absorbing, interacting and reacting capabilities due to its small size with high proportion of atoms at surface. It can even be mixed with aqueous suspensions and thus can behave as colloid. Nanoparticles can achieve energy conservation due to its small size which can ultimately lead to cost savings. Nanoparticles have great advantage of treating water in depths and any location which is generally left out by other conventional technologies. Since water treatment by using nanoparticles has high technology demand, its usage cost should be managed according to existing competition in market (Crane et al., 2012)1. There are various recent advances on different nanomaterials (nanostructured catalytic membranes, nanosorbents, nanocatalysts, bioactive nanoparticles, biomimetic membrane and molecularly imprinted polymers (MIPs)) for removing toxic metal ions, disease causing microbes, organic and inorganic solutes from water.
  • 2. Deepa Madathil et al /Int.J.ChemTech Res.2013,5(5) 2304 Nanosorbents Nanosorbents have very high and specific sorption capacity having wide application in water purification, remediation and treatment process. Commercialized nanosorbents are very few mainly from the U.S. and Asia but research is on going on in large numbers targeting various specific contaminants in water. Few advancements and applications of nanosorbents are given below. Table 1: Different specialization of nanosorbents S.No. Nanosorbent Specialization/Treatment 1. Carbon-based nanosorbents Water containing nickel ions (Ni2+). (high specific surface area, excellent chemical resistance, mechanical strength, and good adsorption capacity) (lee et al., 2012)2 2. CaptymerTM Contaminants (perchlorate, nitrate, bromide and uranium) branched macromolecules forming globular micro particles (Aquanano, n.d.)3 3. Regenerable polymeric nanosorbent Many organic and inorganic contaminants in wastewater (Dunwell Group, n.d.) 4 4. Nanoclays Hydrocarbons dyes and phosphorus (Carrado et al., 2009)5 5. Carbo-Iron The activated carbon for sorption while the elementary iron is reactive and can reduce different contaminants (Helmholtz Centre for Environmental Research, n.d.)6 6. Nano networks Complex three-dimensional networks caused by the ion beam providing better efficiency (Dongqing et al., 2010)7 Magnetic nanosorbents also helps in treating waste water and is proved very interesting tool especially for organic contaminants removal (Bull Mater, 2011)8. Since most of the contaminants are not of magnetic nature filtration aids are needed to absorb which is generally followed by magnetic separation. The nanosorbents used for magnetic separation are prepared by coating magnetic nanoparticles with specific ligands presenting specific affinity (Apblett et al., 2001)9. Different methods like magnetic forces, cleaning agents, ion exchangers and many more are used to remove nanosorbents from the site of treatment to avoid unnecessary toxicity. Regenerated nanosorbents are always cost effective and promoted more for commercialization. Nanocatalysts Nanocatalysts are also widely used in water treatment as it increases the catalytic activity at the surface due its special characteristics of having higher surface area with shape dependent properties .It enhances the reactivity and degradation of contaminants. The commonly used catalytic nanoparticles are semiconductor materials, zero-valence metal and bimetallic nanoparticles for degradation of environmental contaminants such as PCBs (polychlorinated biphenyls), azo dyes, halogenated aliphatic, organochlorine pesticides, halogenated herbicides, and nitro aromatics (Xin et al., 2011)10. The catalytic activity has been proved on laboratory scale for various contaminants. Since hydrogen is used in making active catalyst in large scale by redox reactions, there is need in reducing its consumption and maintain hydrogen economy by directly making catalysts in metallic form. Silver (Ag) nanocatalyst, AgCCA catalyst, N-doped TiO2 and ZrO2 nanoparticles catalysts have been made which is highly efficient for degradation of microbial contaminants in water and are reusable as well (Shalini et al., 2012)11. TiO2-AGS composite is very efficient for Cr (VI) remediation in waste water due to the modification done in TiO2 nanoparticles leading to absorption band shift from UV light activity to natural light degradation. Specific interactions between hydrogen and the Pd based nanoparticles were proved (Kan et al., 2012)12. Waste waters with specific contaminants like traces of halogenated organic compounds (HOCs) can be selectively biodegraded using advanced nanocatalytic activities. The contaminants (HOCs) are first converted into organic compounds using nano-sized Pd catalysts which are followed by its
  • 3. Deepa Madathil et al /Int.J.ChemTech Res.2013,5(5) 2305 biodegradation in treatment plant. The nanocatalyst can be recycled back and reused due its property of having ferromagnetism which helps it to be easily separated. The reductants for the reaction can be Hydrogen or Formic acid depending on the level of contamination (Hildebrand et al., 2008)13.It has also been found that the nanocatalyst of silver and amidoxime fibres which is made by coordination interactions can be reactivated many times using simple tetrahydrofuran treatment and thus can be used efficiently for degradation of organic dyes (Zhi-Chuan Wua et al., 2010)14. Palladium incorporated ZnO nanoparticles were found to be having very high photocatytic activity for removal of E.coli from water which was studied through several analytical studies done using different concentrations of Pd in ZnO nanoparticles (Khalil et al., 2011)15. Nano-WO3 having photo-catalytic activity for E.coli disinfection in water showed increased activity when used in conjunction with 355 nm pulse laser which is synthesized by sol–gel method (Khalil et al., 2009)16. In situ remediation by using Palladium nanoparticles (PdNPs) as catalyst for the reduction of Cr (VI) to Cr (III) has been studied (Marcells et al., 2009)17.Another approach for enhancing the effect is by combining nanosorbents with a catalyst for the combined sorption and degradation of contaminants. Nanocatalysis has proved to very efficient in water treatment. Nanostructured catalytic membranes (NCMS) Nanostructured catalytic membranes are widely used for water contamination treatment. It offers several advantages like high uniformity of catalytic sites, capability of optimization, limiting contact time of catalyst, allowing sequential reactions and ease in industrial scale up. Several functions which include decomposition of organic pollutants, inactivation of microorganisms, anti-bio fouling action, and physical separation of water contaminants are performed by nanostructured TiO2 films and membranes under UV and visible-light irradiation (Hyeok et al., 2009)18.The N-doped “nut-like” ZnO nanostructured material forming multifunctional membrane is very efficient in removing water contaminants by enhancing photo degradation activity under visible light irradiation. It also showed antibacterial activity and helped in producing clean water with constant high flux benefiting the water purification field (Hongwei et al., 2012)19. Various studies have been done regarding immobilization of metallic nanoparticles in membrane (such as cellulose acetate, polyvinylidene fluoride (PVDF), polysulfone, chitosan, etc.) for effective degradation and dechlorination of toxic contaminants which offers several advantages like high reactivity, organic partitioning, prevention of nanoparticles, lack of agglomeration and reduction of surface passivation (Jian et al., 2009)20. Nanocomposites films have been prepared from polyetherimide and palladium acetate and specific interactions between hydrogen and the Pd based nanoparticles have been studied proving the efficiency in water treatment. The metal nanoparticles were generated within the matrix by annealing the precursor film under different conditions using both in situ and ex situ method. This provides opportunities to design materials having tunable properties (Clémenson et al., 2010)21. With the advancement in nanotechnology several novel nanostructured catalytic membranes has been synthesized with increased permeability, selectivity, and resistance to fouling. The techniques include bottom-up approaches and hybrid processes for enabling its multi functionality (Volodymyr et al., 2009)22. Bioactive nanoparticles Water pollution has caused lots of infectious diseases due to various contaminating pathogens. Many of the microorganisms acting as pathogens are antibiotic resistance and so it’s very difficult to remove them from water. Recently the concept of bioactive nanoparticles has emerged which has given the alternative of new chlorine –free biocides (2008)23. Silver nanoparticles (AgNPs) can be synthesized extracellularly by bacteria Bacillus cereus which is having very high antibacterial potential. The silver resistant strain was exposed to different concentrations of silver
  • 4. Deepa Madathil et al /Int.J.ChemTech Res.2013,5(5) 2306 salt (AgNO3) and studied with the help of various analytical instruments like High Resolution Transmission Electron Micrography (HRTEM), X-ray diffraction (XRD) and Energy Dispersive spectroscopy (EDS) (Prakash et al., 2011)24. MgO nanoparticles and Cellulose acetate (CA) fibres with embedded Ag nanoparticles are very effective biocides against Gram-positive bacteria, Gram-negative bacteria and bacterial spores (Nora et al., 2005)25. Current and emerging nanotechnology approaches for the detection of microbial pathogens will aid microbial and pathogen detection as well as diagnostics. Biomimetic membrane for water treatment Biomimetic membranes are developed by Albuquerque-based Sandia National Laboratories and the University of New Mexico. It represents a new and advanced way for water purification based on its specific design and fabrication (2011)26. The invention uses self-assembly and atomic layer deposition tuned nanopores which generally gives high-flux desalination. The membranes remove impurities like salt and others from water with applied pressure powered by electrical energy. The nonporous bio mimetic design enables high salt rejection and faster water flow at lower driving pressures generally used is around 5.5 bars. The process basically uses reverse osmosis principle with doubled efficiency due to its low pressure requirement. Tremendous improvement was found in water purification with cost effectiveness due to this innovative functionalization which combines use of nano-fabrication techniques and inspiration from protein channels in biological membranes. Some of the molecular design principles of natural porous systems were transcribed into robust synthetic porous membranes. The technology uses pressure driven water filtration. Some of the advantages of this technique are advancements, reduced cost, better water flux and improved efficiency with high salt rejection (Jeffrey et al., 2011)27. A biomimetic membrane can be prepared by vesicle fusion on a dense water-permeable support, such as an NF membrane. The process uses electrostatic stiching principle by maximizing attraction and minimizing repulsion between head groups. Biomimetic membrane should have high permeability and selectivity with chemical stability (Kaufman et al., 2011)28. Chemical stability can be provided using various synthetic biomimetic analogues like of aquaporins, carbon nanotubes etc. Many more advancements are expected from this technology in coming years. Molecularly imprinted polymers (MIPs) Molecularly imprinted polymers have recently emerged as one of very fine techniques for various biological, pharmaceutical and environmental applications. The high selectivity of the polymers is due to its synthetic procedure where a template molecule is linked to suitable monomer(s) having functional groups by covalent, semi covalent or non-covalent bonds providing subsequent specific binding sites to the MIPs. The left imprint after the removal of template from polymer helps in recognizing properties of the MIP and are generally called binding sites. Molecular imprinting is basically a process of free radical polymerization of a functional monomer and a cross linker. It works very selectively and has great potential to act as absorbents. It has been used for detection and treatment of water pollutants even at very low concentrations (Caro et al, 2006)29. Molecularly imprinted materials can be also used in combination with catalysts forming novel composite adsorbent or catalyst systems. The use of MIPs is advantageous over commonly used sorbents due to nature of being or performing selective extraction .MIP nanoparticles are encapsulated in nanofibres using electrospinning method that can be used for various pollution control applications including water treatment (Costas Kiparissides, 2010)30. Molecularly imprinted nanospheres (nano MIPs) are also developed for the specific adsorption of micro pollutants from hospital waste water by using mini-emulsion polymerization technique which is very complex but can run in a single reaction chamber resulting in particles with size( 50 nm-500 nm). Magnetic
  • 5. Deepa Madathil et al /Int.J.ChemTech Res.2013,5(5) 2307 core can be introduced to allow the final separation of the nano MIPs and more important of the recognized pollutants from waste water (Tino et al, 2009)31. Conclusion Nanotechnologies have made great improvements for handling water contamination problems and will clearly make further advancements in future. Nanotechnology based treatment has offered very effective, efficient, durable and eco friendly approaches. These methods are more cost-effective, less time and energy consuming with very less waste generations than conventional bulk materials based methods. However certain precautions are to be taken to avoid any threat to human health or environment due to the nanoparticles. The technology should be cost effective and friendly with ease in establishment and use. BCC research has concluded, in a report from 2011-12, that the total market for emerging nanotechnology products used in water treatment, including nanosorbents, will be only around €80 million in 2015. One can see that the large scale commercialisation of nanosorbents is to be expected only after some additional 10 years of applied research (Boehm, 2009)32.For the success of proper commercialization of nanotechnology based water treatment several technical, economical and social challenges has to be tackled properly. References 1. Crane R. A., Scott T. B., (2012), Nanoscale zero-valent iron: Future prospects for an emerging water treatment technology. J Hazard Mater, pp 211-212. 2. Lee X. J., Foo L. P. Y., Tan K. W., Hassell D. G., Lee L. Y., (2012), Evaluation of carbon-based nanosorbents synthesised by ethylene decomposition on stainless steel substrates as potential sequestrating materials for nickel ions in aqueous solution, Journal of Environmental Sciences, 24( 9), pp 1559–1568. 3. AquaNano, available at: www.captymer.com 4. Dunwell Group, available at: http://www.dunwellgroup.com/productsservices/dnl/vsep/ Download /NanoSorbents.pdf 5. Carrado K. A. and Komadel P, (2009), available at: http://elements.geoscienceworld.org /cgi /conten t/, 5(2), pp 111‐116. 6. Helmholtz Centre for Environmental Research– UFZ, available at: http://www.ufz.de/ index.php?en=7038 7. Dongqing Caia, Hong Zhanga, Yi Tanga, Paul K. Chub, Zengliang Yua, Zhengyan Wua, (2010), Nano-networks have better adsorption capability than nano-rods. Nano Communication Networks, 1(4), pp 257–263. 8. Bull Mater. Sci, (2011),Using speciation diagrams to improve synthesis of magnetic nanosorbents for environmental applications, 34(7), pp 1357–1361. 9. Apblett A.W., Al-Fadul S. M., Chehbouni M and Trad T., (2001), Proc. 8th Int. Environ. Petroleum Consortium 10. Xin Zhaoa,b, Lu Lva,b, Bingcai Pana,b, Weiming Zhanga,b, Shujuan Zhanga, Quanxing Zhanga,b., (2011), Polymer-supported nanocomposites for environmental application: A review, Chemical Engineering Journal, 170( 2–3), pp 381–394. 11. Shalini Chaturvedi A., Pragnesh N., Dave A., Shah N. K.,(2012), Applications of nano-catalyst in new era. Journal of Saudi Chemical Society, 16(3), pp 307–325. 12. Kan Zhang Q., Christian Kemp K., Vimlesh Chandra, (2012), Homogeneous anchoring of TiO2 nanoparticles on graphene sheets for waste water treatment, pp 790-784. 13. Hildebrand H., Mackenzie K., Kopinke F-D., (2008), Novel nano-catalysts for wastewater treatment. Global NEST Journal,10(1), pp 47-53. 14. Zhi-Chuan Wua, Yong Zhanga, Ting-Xian Taoa, Lifeng Zhangb, Hao Fongb, (2010), Silver nanoparticles on amidoxime fibers for photo-catalytic degradation of organic dyes in waste water. Applied Surface Science, 257(3), pp 1092–1097.
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  • 7. Deepa Madathil et al /Int.J.ChemTech Res.2013,5(5) 2309 .