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1.
International Research Journal
of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 06 | Jun 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 2094 Carbon Nanotubes Membranes: Application in Water Treatment Shyamal Kumar Roy1, Suman Ghosh2, Aveek Chattopadhyaya3 Madhumita Chakrabortyt4 1,2,3,4 Department of Electrical Engineering, Guru Nanak Institute of Technology, West Bengal, India ---------------------------------------------------------------------***--------------------------------------------------------------------- Abstract - This article serves as an explanation to the application of Carbon Nanotubes(CNTs)inwaterpurification. The article is concerned with identifying the role that nanotechnology plays in water treatment and the specifics of watertransportinCNT basedmembranes. Thearticleanalyzes the fabrication of CNT membranes and their effectiveness in water permeability, water desalination and other forms of water purifi- cation. Functionalized membranes were also analyzed by breaking down the process whereby PEG is added to carboxylic CNTs in a reaction catalyzed bysulphuricacid, with such structure being found to have increased mechanical properties. A comparisonbetweenCNTbasedmembranesand otherconventionalmembranesusedinwater purificationwere formed.Thiscomparisonwasmadebyconsideringtheefficiencyof the membranesinwaterpermeability,saltrejection,aswellasthe overallphysicalandmechanical properties of the membranes. CNTbasedmembranes werefoundtoperform better than the conventional membranes in most categories, makingthemthe most costeffectiveandusefulamongthemembraneswithroom forfurtherimprovement. Key Words: Carbon nanotubes, Membranes, SWNT, PEG, CVD, Filtration 1. INTRODUCTION In the modern world, nanomaterials are manufacturedandused for a variety of different purpose. Each purpose that a nanomaterial can serve depends on the structure and physical propertiesthatthematerialmaypossessasaresultofexistingin the nanoscale. An importantpurposefornanomaterialsthathas emergedinthepastfewyearsiswaterpurification. Thisisafield thatisarequirementconsideringthedepletionoftheavailabilityof safedrinkingwateracrosstheworld. Duetotheriseinsealevel andevaporationcausedbyglobal warmingandclimatechange, fresh water sources are facing rapid salination and increased forms of pollution. Without effective water purification technology,thisisresultingina largernumberofpeoplegetting less access to potable water, especially in less economically developed countries where is most needed. Nanotechnology is being tested anddeveloped in order to alleviate this problem. A wide range of nanomaterials that perform useful tasks such as adsorption, ultrafiltration, reverse osmosis, ion exchange and electrolysis have been developed. However, their cost of production and energy they require make them difficult to implement at a large scale and make them available to low income areas. Also some processes such as the adsorption techniques fail to desalinate water, and therefore cannot deal with the issue. Some of these processes, such as the membrane technologies,seemto beperformingthetaskofdesalinationwith increasing promise. Although they have not yet been made commercially viable, they utilize deionization in order to properlyreducethe salt content in water. Scientists are looking to incorporate carbon nanotubes (CNTs) into the membrane technologies, using them as robust pores for water decontamination proper- ties. Since CNTs have self-cleaning properties,itmakesthemmoreusefulandsuitableforseparating and rejecting salt ions and permitting water to flow through the interiorofthe nanotubes. ThefunctionalityoftheseCNTswillbe examined, and their effectiveness will be compared to other conventional membranes. [2] 2. NANOTECHNOLOGY FOR WATER TREATMENT In recent times, the general use of nanomaterials in water purificationhasrisenasnanotech- nologycontinuestogrowand develop.Thesenanomaterialsareeffectiveinthedesalination of water, as well as in other forms of water purification. Other nanomaterials, in particular nanoscale metals, have the properties of reactivity, adsorption, as well as hydrophilicand hydrophobicinteractionswhichcanbeusedtocontainandremove impurities from drinking water. An example of this is the structure of silver nanoparticles which have the properties of killingbacteria,virusesandfungithatresideinbodiesofwater. Thismakesiteasierofothernanomaterialswithadsorptionand filtering properties to collect the dead pollu- tantsandremove them from the body of water without the fear of them reproducing and multiplying. Other nanomaterials such as titanium nanoparticles have the ability to induce reduction reactions that transform the structure of harmful bacteria and viruses into inactive and non-toxic substances. Since bacteria, virusesandfungileadtothespreadofwater-bornediseasessuchas cholera and bilharzia, rendering these species inert could save countless lives in poverty-stricken areas. In relation to water desalination, most nanomaterials have been found to have increased surface porosity. This property improves salt rejection, and some metal nanoparticles play a large part in removing inorganic materials from the surface of waterbodies. Other nanomaterials that play an important role in the desalination of water include graphene and CNTs. These materials haveenhanced adsorption capabilities that areuseful in the desalination process. There are, however, limitations to using nanomate- rials in water desalination. These limitations nanomaterials also become unusable after the initial run, requiringthemanufacture offreshparticles,whichisalongand costlyprocess.Thecostoftheactualnanomaterialsthemselves
2.
International Research Journal
of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 06 | Jun 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 2095 also proves to be a serious limitation in their use in water purification. Most of the nanomaterials used are heavy expensive metals such as gold, silver and titanium due to their inert properties. Processing them into nanomaterials is also an expensive process because of their high tensile strength and melting points. Developing the most cost-effective method of manufacturing these nanomaterials and using them to desalinate water inthe leastexpensivewayisthegoalofmany scientistsinvolvedinwaterpurification. [2]. 3. CARBON NANOTUBES IN WATER PURIFICATION TherearetwotypesofCNTmembranesforwaterpurification SingleWalledNanotube Membranes SWNT and Multi Walled Nanotube Membranes W N T. We can classify the water pollutants in three different types: Organicpollutantssuchas Industrial waste, pesticides, chlorinated compounds, pharmaceuticals, Inorganic pollu- tants such as soil erosion, metals, nitrates, phosphatesandMicroorganismssuchasanimal excrement and sewage. [6] 3.1. Water transport in CNT membranes Thebehaviorofwaterflowingthroughdifferentconfigurationsof CNTs has been studied to understand how these configurations influenceontheflowofwater. Thesechangeonthe configuration oftheCNTstructureproducesasignificantchangeonthediffusion coefficientathighandlowtemperatureswhenthedistortionison theZaxis,Ontheotherhandifthe distortionisatXYplaneoritis causedforalocaldefectthediffusioncoefficientchangescannot be ignored. [3] Fig. -1: Distorsion of CNT in Z an XY axis [3] 3.2. Fabrication of CNTMembranes The preferred process is CVD because of the quality of nanotubes that can be obtained. 4.1 Swnt Membranes VerticalalignedCNTweresynthesizedusingwaterassistedCVD. The microstructure of the CNT was characterized using SEM images. The inner structure, inner diameter andwall numberof theCNTswerestatisticallymeasured,andtheporesoftheopen- ended membrane were observed from transmission electron microscopy(TEM)imagesrecordedusingaJEOLJEM-3000Fhigh- resolution transmission electron microscopeatanacceleration voltageof 300 kV. The following results were obtained.[5] Fig. -3: Performance of the outer wall membrane. [5] Fig. -2: CVD fabrication process [1] 4. CNT MEMBRANES TECHNOLOGY
3.
International Research Journal
of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 06 | Jun 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 2096 Fig. -4: Characteristics of the CNT membranes. [5] 4.2. Functionalized CNT Membranes TofunctionalizecarboxylicCNTs(COOH-CNT)withPEG,10gof PEGweremeltedina roundbottomflaskonahotplateat90C and 1 g of COOH-CNTs was then added. The mixture was allowedtostirabout10min,followedbyadditionoffewdropsof sulfuricacid(H2SO4)asacatalyst.Then,thereactionproceeded for 5 h under nitrogen atmosphere followed by cooling at ambient temperature. The resulting mixture was repeatedly washed andprecipitatedwithpetroleumetheruntilnomorePEG could be observed in the super- natant solution. After that, the precipitated PEG-CNTs were decanted with acetone as a final washingstepbeforedryingovernightundervacuumat85C. The obtainedresultsreveal thattheconcentrationofPEG-CNTsinthe castingsolutiondecreasedthetensilestrength andthemodulus of the membranes until a specific loading (0–0.25 wt% PEG- CNTs)but after this loading the mechanical properties were increaseddramatically.[4] Fig. -5: Preparation of PEG funtionalized CNT.[4] Fig. -6: Different types of membranes synthesized.[4] Fig. -7: Tensile Strength and Young Modulus. [4]
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International Research Journal
of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 06 | Jun 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 2097 Fig. 9 Filtration Resistances. [4] 5.COMPARISONOFCNTMEMBRANESWITHOTHER MEM- BRANES MembranetechnologiesachievedusingCNTs hasbeenfoundto perform moreefficientlyin theprocessofwaterdesalinationas compared to other conventional membranes such as re- verse osmosis (RO), nanofiltration (NF), ultrafiltration (UF) and microfiltration(MF).This isbecauseofanumberofreasonsthat have been well-researched by scientists specializing in the manufacture of membranes for water purification. The first reasonisthatCNTsare hollow and hydrophobic, allowing polar water molecules to flow easier within them. The other membranes do not havethe hydrophobic interior, while others are hydrophobic toa lesserextentascomparedtoCNTs.Secondly, CNTshavebetterwaterpermeabilitythanthe othermembranes, namely the RO membranes which have the highest level of permeability among the other membranes. The water permeability among armchair CNTs was found to befour times higherthaninROmembranes. CNTsalsohaveahigherlevelofsalt rejection among the membranes. However, the NF membrane performssimilarlytotheCNTsinthis section. ACNTmembrane withanincreasedporediametercouldtheoreticallyretainmore solute particles that make up a salt, and it is possible to manufacture.Suchanalteration intheporediameterofaCNT membraneresultsina%removalofsaltsdissolved,aratethatis much higher than that of RO membranes. While CNTs and RO membranecurrentlyyieldthesameratesofsaltrejection,theCNT membranescanbemodifiedtoyieldahigherrateatareasonable costofproduction.Asidefromthedifferencesintheefficiencyof the membranes inthe processof water desalination, there arealso numerous physical differences between CNTbasedmembranes andtheotherconventionalmembranes.Intermsofmaterialsused toproducethemembranes,CNTsaremadeoutofcarbonarranged intubularform, whileROandNFmembranesaremanufactured from organic polymers such as polyamide, UF membranes are made from polysulfone and acrylic, and MF membranes are manufacturedusingpolypropeneandpolyurethane.Intermsof thickness,CNTsareusually2 6 um thick, which is within the nanoscale. The thickest membranes are the UF membranes whichrangefrom150 300um,whilethethinnestmembranesare theROmembraneswith athicknessof0.1 0.2um.Intermsofself- cleaning capability, the CNTs have fullcapabilitywhiletheother membranes require functionalization. [2] 6. CONCLUSIONS 1. For SWNT Membranes higher water permeability, purified water volume and flow velocity were obtained with smaller pore sizes. 2. For a PEG-CNT loading from 0.25% properties such as tensile strength, flux recovery ratio and filtration resistances start growing. 3. This enhanced in flow properties are a big step towards the improvement of membranes efficiency, however the theoretical valuesarestillfarfrombeingreached. Moreresearchinthisfieldand new fabrication techniques and improvements on the current techniques will be a key factor on the development of this technology. REFERENCES [1] OlgicaBakajin,AleksandrNoy,FrancescoFornasiero,CostasP. Grigoropoulos, Jason K. Holt,JungBinIn,Sangil Kim,and HyungGyuPark.Chapter11-nanofluidiccarbonnanotube membranes: Applications for water purification and desalination. In Anita Street, Richard Sustich, Jeremiah Duncan, and Nora Savage, editors, Nanotechnology Applications for CleanWater (SecondEdition),Microand Nano Technologies, pages 173 – 188. William Andrew Publishing, Oxford, second edition edition, 2014. [2] RaselDas,Md.EaqubAli,SharifahBeeAbdHamid,Seeram Ramakrishna, and Zaira Za- man Chowdhury. Carbon nanotube membranes for water purification: A bright future in water desalination. Desalination, 336(Supplement C):97 – 109,2014. [3] Jiamei Feng, Peirong Chen, Dongqin Zheng, and Weirong Zhong. Transport diffusion in deformed carbon nanotubes. Physica A: Statistical Mechanics and its Applications, 493:155 – 161, 2018. Fig. -8: Flux Recovery ratio.[4]
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International Research Journal
of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 09 Issue: 06 | Jun 2022 www.irjet.net p-ISSN: 2395-0072 © 2022, IRJET | Impact Factor value: 7.529 | ISO 9001:2008 Certified Journal | Page 2098 [4] Arsalan Khalid, Ahmed Abdel-Karim, Muataz Ali Atieh, SaqibJaved,andGordon McKay.PEG-CNTsnanocomposite PSUmembranesforwastewatertreatmentbymem- brane bioreactor. Separation and Purification Technology, 190:165–176, jan 2018. [5] Byeongho Lee, Youngbin Baek, Minwoo Lee, Dae Hong Jeong, Hong H. Lee, Jeyong Yoon,andYongHyupKim. A carbonnanotubewallmembraneforwatertreatment. [6] Neeta Pandey, S. K. Shukla, and N. B. Singh. Water purification by polymer nanocom- posites: an overview. Nanocomposites, 3(2):47–66, apr 2017.
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