Green synthesis of iron oxide (Fe<sub>3</sub>O<sub>4</sub>) nanoparticles using two selected brown seaweeds: Characterization and application for lead bioremediation

EL-KASSAS Hala Y.; ALY-ELDEEN Mohamed A.; GHARIB Samiha M.

doi:10.1007/s13131-016-0880-3

Article Contents

Article Navigation > Acta Oceanologica Sinica > 2016 > 35(8): 89-98

EL-KASSAS Hala Y., ALY-ELDEEN Mohamed A., GHARIB Samiha M.. Green synthesis of iron oxide (Fe3O4) nanoparticles using two selected brown seaweeds: Characterization and application for lead bioremediation[J]. Acta Oceanologica Sinica, 2016, 35(8): 89-98. doi: 10.1007/s13131-016-0880-3

Citation:

EL-KASSAS Hala Y., ALY-ELDEEN Mohamed A., GHARIB Samiha M.. Green synthesis of iron oxide (Fe₃O₄) nanoparticles using two selected brown seaweeds: Characterization and application for lead bioremediation[J]. Acta Oceanologica Sinica, 2016, 35(8): 89-98. doi: 10.1007/s13131-016-0880-3

Green synthesis of iron oxide (Fe₃O₄) nanoparticles using two selected brown seaweeds: Characterization and application for lead bioremediation

doi: 10.1007/s13131-016-0880-3

National Institute of Oceanography and Fisheries, Alexandria 21556, Egypt

Received Date: 2015-06-17
Rev Recd Date: 2015-08-28

Abstract

The exploitation of different plant materials for the biosynthesis of nanoparticles is considered a green technology because it does not involve any harmful chemicals. In this study, iron oxide nanoparticles (Fe₃O₄-NPs) were synthesized using a completely green biosynthetic method by reduction of ferric chloride solution using brown seaweed water extracts. The two seaweeds Padina pavonica (Linnaeus) Thivy and Sargassum acinarium (Linnaeus) Setchell 1933 were used in this study. The algae extract was used as a reductant of FeCl₃ resulting in the phytosynthesis of Fe₃O₄-NPs. The phytogenic Fe₃O₄-NPs were characterized by surface plasmon band observed close to 402 nm and 415 nm; the obtained Fe₃O₄-NPs are in the particle sizes ranged from 10 to 19.5 nm and 21.6 to 27.4 nm for P. pavonica and S. acinarium, respectively. The strong signals of iron were reported in their corresponding EDX spectra. FTIR analyses revealed that sulphated polysaccharides are the main biomolecules in the algae extracts that do dual function of reducing the FeCl₃ and stabilizing the phytogenic Fe₃O₄-NPs. The biosynthesized Fe₃O₄-NPs were entrapped in calcium alginates beads and used in Pb adsorption experiments. The biosynthesized Fe₃O₄-NPs alginate beads via P. pavonica (Linnaeus) Thivy had high capacity for bioremoval of Pb (91%) while that of S. acinarium (Linnaeus) Setchell 1933 had a capacity of (78%) after 75 min. The values of the process parameters for the maximum Pb removal efficiency by Fe₃O₄-NPs alginate beads synthesized via P. pavonica (Linnaeus) Thivy were also estimated.
- seaweeds,
- iron oxide,
- silver,
- nanoparticles

References

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[39]	Ngomsik A F, Bee A, Siaugue J M, et al. 2009. Co (Ⅱ) removal by mag-netic alginate beads containing Cyanex 272.. Journal of Haz-ardous Materials, 166(2-3):1043-1049
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Green synthesis of iron oxide (Fe₃O₄) nanoparticles using two selected brown seaweeds: Characterization and application for lead bioremediation

National Institute of Oceanography and Fisheries, Alexandria 21556, Egypt

Received Date: 2015-06-17

Rev Recd Date: 2015-08-28

Key words:

seaweeds /
iron oxide /
silver /
nanoparticles

Abstract: The exploitation of different plant materials for the biosynthesis of nanoparticles is considered a green technology because it does not involve any harmful chemicals. In this study, iron oxide nanoparticles (Fe₃O₄-NPs) were synthesized using a completely green biosynthetic method by reduction of ferric chloride solution using brown seaweed water extracts. The two seaweeds Padina pavonica (Linnaeus) Thivy and Sargassum acinarium (Linnaeus) Setchell 1933 were used in this study. The algae extract was used as a reductant of FeCl₃ resulting in the phytosynthesis of Fe₃O₄-NPs. The phytogenic Fe₃O₄-NPs were characterized by surface plasmon band observed close to 402 nm and 415 nm; the obtained Fe₃O₄-NPs are in the particle sizes ranged from 10 to 19.5 nm and 21.6 to 27.4 nm for P. pavonica and S. acinarium, respectively. The strong signals of iron were reported in their corresponding EDX spectra. FTIR analyses revealed that sulphated polysaccharides are the main biomolecules in the algae extracts that do dual function of reducing the FeCl₃ and stabilizing the phytogenic Fe₃O₄-NPs. The biosynthesized Fe₃O₄-NPs were entrapped in calcium alginates beads and used in Pb adsorption experiments. The biosynthesized Fe₃O₄-NPs alginate beads via P. pavonica (Linnaeus) Thivy had high capacity for bioremoval of Pb (91%) while that of S. acinarium (Linnaeus) Setchell 1933 had a capacity of (78%) after 75 min. The values of the process parameters for the maximum Pb removal efficiency by Fe₃O₄-NPs alginate beads synthesized via P. pavonica (Linnaeus) Thivy were also estimated.

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Reference (63)

[1]	Abdul Salam H, Rajiv P, Kamaraj M, et al. 2012. Plants:green route for nanoparticle synthesis. International Research Journal of Biolo-gical Science, 1(5):85-90
[2]	Adegoke H I, AmooAdekola F, Fatoki O S, et al. 2014. Adsorption of Cr (VI) on synthetic hematite (α-Fe2O3) nanoparticles of different morphologies. Korean Journal of Chemical Engineering, 31(1):142-154
[3]	Afkhami A, Moosavi R. 2010. Adsorptive removal of Congo red, a car-cinogenic textile dye, from aqueous solutions by maghemite nanoparticles. Journal of Hazardous Materials, 174(1-3):398-403
[4]	Aleem A A. 1993. Marine Algae of Alexandria. Alexandria:Privately Published Alidokht L, Khataee A R, Reyhanitabar A, et al. 2011. Reductive re-moval of Cr(VI) by starch stabilized Fe0 nanoparticles in aqueous solution. Desalination, 270(1-3):105-110
[5]	Asmathunisha N, Kathiresan K. 2013. A review on biosynthesis of nanoparticles by marine organisms. Colloids and Surfaces B:Biointerfaces, 103:283-287
[6]	ATSDR. 2001. Agency for toxic substances and disease registry. CER-LLA Comprehensive environmental response, compensation and liability act, Priority list of hazardous substances. http://www.atsdr.cdc.gov/clist.html
[7]	Azizi S, Namvar F, Mahdavi M, et al. 2013. Biosynthesis of silver nan-oparticles using brown marine Macroalga, Sargassum Mutic-um aqueous extract. Materials, 6(12):5942-5950
[8]	Baumann H A, Morrison L, Stengel D B. 2009. Metal accumulation and toxicity measured by PAM-Chlorophyll fluorescence in seven species of marine macroalgae. Ecotoxicology and Envir-onmental Safety, 72(4):1063-1075
[9]	Bayramo.lu G, Tuzun I, Celik G, et al. 2006. Biosorption of mercury (Ⅱ), cadmium (Ⅱ) and lead (Ⅱ) ions from aqueous system by microalgae Chlamydomonas reinhardtii immobilized in algin-ate beads. International Journal of Mineral Processing, 81(1):35-43
[10]	Budavari S, O'Neil M J, Smith A, et al. 1989. The Merck Index:an En-cyclopedia of Chemicals, Drugs, and Biologicals. 11th ed. Rah-way, NJ, USA:Merck & Co, Inc
[11]	Cardwell A J, Hawker D W, Greenway M. 2002. Metal accumulation in aquatic macrophytes from southeast Queensland, Australia. Chemosphere, 48(7):653-663
[12]	Chekroun K B, Sánchez E, Baghour M. 2014. The role of algae in bioremediation of organic pollutants. International Research Journal of Public and Environmental Health, 1(2):19-32
[13]	Chen Hong, Pan Shanshan. 2005. Bioremediation potential of Spirulina:toxicity and biosorption studies of lead. Journal of Zhejiang University Science, 6B(3):171-174
[14]	Crist R H, Oberholser K, McGarrity J, et al. 1992. Interaction of metals and protons with algae. 3. Marine algae, with emphasis on lead and aluminum. Environmental Science and Technology, 26(3):496-502
[15]	Daby D. 2006. Coastal pollution and potential biomonitors of metals in Mauritius. Water, Air, and Soil Pollution, 174(1-4):63-91
[16]	Daka E R, Allen J R, Hawkins S J. 2003. Heavy metal contamination in sediment and biomonitors from sites around the Isle of Man. Marine Pollution Bulletin, 46(6):784-791
[17]	Dave P N, Chopda L V. 2014. Application of iron oxide nanomaterials for the removal of heavy metals. Journal of Nanotechnology, 2014:Article ID 398569
[18]	Dutta R K, Sahu S. 2012. Development of oxaliplatin encapsulated in magnetic nanocarriers of pectin as a potential targeted drug de-livery for cancer therapy. Results in Pharma Sciences, 2:38-45
[19]	Dwivedi S. 2012. Bioremediation of heavy metal by algae:current and future perspective. Journal of Advanced Laboratory Research in Biology, 3(3):195-199
[20]	El Maghraby D M, Fakhry E M. 2015. Lipid content and fatty acid composition of Mediterranean macro-algae as dynamic factors for biodiesel production. Oceanologia, 57(1):86-92
[21]	El-Kassas H Y, El-Taher E M. 2009. Optimization of batch process parameters by response surface methodology for mycoremedi-ation of chrome-VI by a chromium resistant strain of marine Trichoderma viride. American-Eurasian Journal of Agricultural & Environmental Sciences, 5(5):676-681
[22]	Farghali A A, Bahgat M, Enaiet Allah A, et al. 2013. Adsorption of Pb (Ⅱ) ions from aqueous solutions using copper oxide nano-structures. Beni-Suef University Journal of Basic and Applied Sciences, 2(2):61-71
[23]	Fiol N, Poch J, Villaescusa I. 2005. Grape stalks wastes encapsulated in calcium alginate beads for Cr(VI) removal from aqueous solutions. Separation Science and Technology, 40(5):1013-1028
[24]	Gole A, Dash C, Ramakrishnan V, et al. 2001. Pepsin-gold colloid con-jugates:preparation, characterization, and enzymatic activity. Langmuir, 17(5):1674-1679
[25]	Hammud H H, El-Shaar A, Khamis E, et al. 2014. Adsorption studies of Lead by Enteromorpha algae and its silicates bonded materi-al. Advances in Chemistry, 2014:Article ID 205459
[26]	Huang Jiale, Li Qingbiao, Sun Daohua, et al. 2007. Biosynthesis of sil-ver and gold nanoparticles by novel sun dried Cinnamomum camphora leaf. Nanotechnology, 18(10):105104
[27]	Ilankoon N. 2014. Use of iron oxide magnetic nanosorbents for Cr (VI) removal from aqueous solutions:A review Journal of En-gineering Research and Applications, 4(10):55-63
[28]	Jiang Mingqin, Wang Qingping, Jin Xiaoying, et al. 2009. Removal of Pb (Ⅱ) from aqueous solution using modified and unmodified kaolinite clay. Journal of Hazardous Materials, 170(1):332-339
[29]	Kang Y S, Risbud S, Rabolt J F, et al. 1996. Synthesis and characteriza-tion of nanometer-size Fe₃O₄ and γ-Fe2O3 particles. Chemistry of Materials, 8(9):2209-2211
[30]	Khuri A I, Cornell J A. 1987. Response Surfaces:Design and Analysis. New York:Marcel Dekker
[31]	Kulkarni N, Muddapur U. 2014. Biosynthesis of metal nanoparticles:a review. Journal of Nanotechnology, 2014:Article ID 510246
[32]	Kumar J I N, Oommen C, Kumar R N. 2009. Biosorption of heavy metals from aqueous solution by green marine macroalgae from Okha Port, Gulf of Kutch, India. American-Eurasian Journal of Agricultural & Environmental Sciences, 6(3):317-323
[33]	Laurent S, Forge D, Port M, et al. 2008. Magnetic iron oxide nano-particles:synthesis, stabilization, vectorization, physicochem-ical characterizations, and biological applications. Chemical Reviews, 108(6):2064-2110
[34]	Li Xiaoqin, Elliott D W, Zhang Weixian. 2006. Zero-valent iron nano-particles for abatement of environmental pollutants:Materials and Engineering Aspects. Critical Reviews in Solid State and Materials Sciences, 31(4):111-122
[35]	Mahdavi M, Namvar F, Ahmad M B, et al. 2013. Green biosynthesis and characterization of magnetic iron oxide (Fe₃O₄) nano-particles using seaweed (Sargassum muticum) aqueous extract. Molecules, 18(5):5954-5964
[36]	Mohapatra M, Anand S. 2007. Studies on sorption of Cd (Ⅱ) on Tata chromite mine overburden. Journal of Hazardous Materials, 148(3):553-559
[37]	Montgomery D C. 1991. Design and Analysis of Experiments. 3rd ed. New York:Wiley
[38]	Mubarak Ali D, Divya C, Gunasekaran M, et al. 2011. Biosynthesis and characterization of silicon-germanium oxide nanocompos-ite by Diatom. Digest Journal of Nanomaterials and Biostruc-tures, 6(1):117-120
[39]	Ngomsik A F, Bee A, Siaugue J M, et al. 2009. Co (Ⅱ) removal by mag-netic alginate beads containing Cyanex 272.. Journal of Haz-ardous Materials, 166(2-3):1043-1049
[40]	Ofer R, Yerachmiel A, Shmuel Y. 2003. Marine macroalgae as biosorbents for cadmium and nickel in water. Water Environ-ment Research, 75(3):246-253
[41]	Oh J K, Park J M. 2011. Iron oxide-based superparamagnetic poly-meric nanomaterials:design, preparation, and biomedical ap-plication. Progress in Polymer Science, 36(1):168-189
[42]	Perelo L W. 2010. Review:In situ and bioremediation of organic pol-lutants in aquatic sediments. Journal of Hazardous Materials, 177(1-3):81-89
[43]	Philp J C, Atlas R M. 2005. Bioremediation of contaminated soils and aquifers. In:Atlas R M, Philp J C, eds. Bioremediation:Applied Microbial Solutions for Real-World Environmental Cleanup. Washington, DC:ASM Press, 139-236
[44]	Qu Shengchun, Yang Haibin, Ren Dawei, et al. 1999. Magnetite nano-particles prepared by precipitation from partially reduced fer-ric chloride aqueous solutions. Journal of Colloid and Interface Science, 215(1):190-192
[45]	Rai P K. 2008. Heavy metal pollution in aquatic ecosystems and its phytoremediation using wetland plants:An ecosustainable ap-proach. International Journal of Phytoremediation, 10(2):133-160
[46]	Rai P K. 2010. Phytoremediation of heavy metals in a tropical im-poundment of industrial region. Environmental Monitoring and Assessment, 165(1-4):529-537
[47]	Rajesh S, Patric Raja D, Rathi J M, et al. 2012. Biosynthesis of silver nanoparticles using Ulva fasciata (Delile) ethyl acetate extract and its activity against Xanthomonas campestris pv. malvacear-
[48]	um. Journal of Biopesticides, 5(Suppl):119-128
[49]	Rawat I, Kumar R R, Mutanda T, et al. 2011. Dual role of microalgae:Phycoremediation of domestic wastewater and biomass pro-duction for sustainable biofuels production. Applied Energy, 88(10):3411-3424
[50]	Ribeiro R F L, Magalh.es S M S, Barbosa F A R, et al. 2010. Evaluation of the potential of microalgae Microcystis novacekii in the re-moval of Pb²⁺ from an aqueous medium. Journal of Hazardous Materials, 179(1-3):947-953
[51]	Salgado S G, Nieto M A Q, Simón M M B. 2006. Optimisation of sample treatment for arsenic speciation in alga samples by fo-cussed sonication and ultrafiltration. Talanta, 68(5):1522-1527
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Green synthesis of iron oxide (Fe₃O₄) nanoparticles using two selected brown seaweeds: Characterization and application for lead bioremediation

doi: 10.1007/s13131-016-0880-3

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Green synthesis of iron oxide (Fe₃O₄) nanoparticles using two selected brown seaweeds: Characterization and application for lead bioremediation

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Green synthesis of iron oxide (Fe3O4) nanoparticles using two selected brown seaweeds: Characterization and application for lead bioremediation

doi: 10.1007/s13131-016-0880-3

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Green synthesis of iron oxide (Fe3O4) nanoparticles using two selected brown seaweeds: Characterization and application for lead bioremediation

doi: 10.1007/s13131-016-0880-3

National Institute of Oceanography and Fisheries, Alexandria 21556, Egypt

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Green synthesis of iron oxide (Fe₃O₄) nanoparticles using two selected brown seaweeds: Characterization and application for lead bioremediation

Green synthesis of iron oxide (Fe₃O₄) nanoparticles using two selected brown seaweeds: Characterization and application for lead bioremediation