| Peer-Reviewed

Inhibition Effects of Cobalt Nano Particles Against Fresh Water Algal Blooms Caused by Microcystis and Oscillatoria

Received: 17 June 2017    Accepted: 28 June 2017    Published: 28 November 2017
Views:       Downloads:
Abstract

Cyanobacterial blooms deplete nutrients, reduce water clarity, exhaust carbon di oxide and produces secondary metabolites which negatively affect aquatic organisms and water quality. Control of algal blooms using metal nano particles is one effective method for the safety of water environment. Cobalt nano particles (CoNPs) were synthesized and tested against microalgae isolated from fresh water cyanobacterial blooms by assessing the effects on growth rate, biomass concentration, photosynthetic pigments concentration and antioxidant enzyme activity. Microcystis and Oscillatoria were identified as the predominant isolates from algal blooms and treated with varying concentrations (1, 2, 3, 4 and 5 mg·L-1) of CoNPs. Steady decline in the growth rate of microalgae was observed at the end of 5 days indicating the toxicity of CoNPs on microalgal growth. At the end of cultivation period, 78% and 88% of reduction in biomass concentration of Microcystis and Oscillatoria were observed at 5 mg·L-1 of CoNPs. The chlorophyll content was reduced from 1.53 to 0.24 mg·L-1 in Microcystis and 1.63 to 0.29 mg·L-1 in Oscillatoria. There was a 69.3% and 73.2% decrease in carotenoid content of Microcystis and Oscillatoria respectively. Both protein and carbohydrate contents of the microalgae were reduced with increasing concentration of nano particles. The decrease in Super oxide dismutase (SOD) activity with increased nanoparticle concentration reveals the formation of stress in the microalgae. The increasing GSH activity proved the effect of CoNPs on the activation of antioxidative enzymes to protect the cells. This study demonstrates the efficiency of cobalt nano particles (CoNPs) on inhibition of fresh water algal blooms thereby reducing the eutrophication problem.

Published in American Journal of Applied Scientific Research (Volume 3, Issue 4)
DOI 10.11648/j.ajasr.20170304.12
Page(s) 26-32
Creative Commons

This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited.

Copyright

Copyright © The Author(s), 2024. Published by Science Publishing Group

Keywords

Microalgae, Nano Particles, Algal Bloom, Microcystis, Oscillatoria

References
[1] Fogg GE. (1969). The physiology of an algal nuisance. Proc. R. Sco. London. Ser. B. 173: 175-189.
[2] Reynolds CS., Walsby AE. (1975). Water blooms. Biol. Rev. 50: 437-481.
[3] Vallentyne JR. (1974). The Algal Bowl. Lakes and Man. Department of the Environment, Fisheries and Marine Service, Ottawa, Canada. 185 p.
[4] Chorus I., Bartram J. (1999). Toxic cyanobacteria in water. E&FN Spon, London. 416 p.
[5] Lund JWG. (1965). The ecology of freshwater phytoplankton. Biol. Rev. Cambridge Philos. Soc. 40: 231-293.
[6] Paerl HW. (1988). Nuisance phytoplankton blooms in coastal, estuarine and inland waters. Limnol. Oceanogr. 33: 823-847.
[7] Round FE. (1965). The Biology of the Algae. Arnold Press. London.
[8] Sournia A. (1978). Phytoplankton manual. UNESCO, Paris.
[9] Duong TT, Le TS, Tran TTH, Nguyen TK, Ho CT, Dao TH et al., (2016). Inhibition effect of engineered silver nanoparticles to bloom forming cyanobacteria. Adv. Nat. Sci.: Nanosci. Nanotechnol. 7: 035018.
[10] Hu LB, Zhou W, Yang JD, Chen J, Yin YF, Shi ZQ. (2011) Cinnamaldehyde induces PCD-like death of via reactive oxygen species. Water Air Soil Pollut. 217(1):105-113.
[11] Angeline K, Prepas EE, Spink D, Hrudey SE. (1994). Chemical control of hepatotoxic phytoplankton blooms: implication for human health. Water Research, 29: 1845.
[12] Wiegand, C., Pflugmacher, S. (2005). Ecotoxicological effects of selected cyanobacterial secondary metabolites a short review. Toxicol. Appl. Pharmacol. 203: 201-218.
[13] Burda C, Chen X, Narayanan R, El-Sayed MA. (2005). Chemistry and properties of nanocrystals of different shapes. Chem Rev 105(4): 1025-1102.
[14] Burchardt AD, Carvalho RN, Valente A, Nativo P, Gilliland D, Garcia CP, Passarella R, Pedroni, Rossi F, Lettieri T. (2012). Effects of Silver Nanoparticles in Diatom Thalassiosira pseudonana and Cyanobacterium Synechococcus sp. Environ. Sci. Technol., 46(20): 11336-11344.
[15] Oukarroum A, Bras S, Perreault F and Popovic R. (2012). Inhibitory effects of silver nanoparticles in two green algae, Chlorella vulgaris and Dunaliella tertiolecta. 78: 80-85.
[16] Saison C, Perreault F, Daigle JC, Fortin C, Claverie J, Morin M, Popovic R. (2010) Effect of core-shell copper oxide nanoparticles on cell culture morphology and photosynthesis (photosystem II energy distribution) in the green alga. Chlamydomonas reinhardtii. Aquat Toxicol 96(2):109-114.
[17] Xia B, Chen B, Sun X, Qu K, Ma F, Du M. (2015). Interaction of TiO2 nanoparticles with the marine microalga Nitzschia closterium: Growth inhibition, oxidative stress and internalization. Sci. Total Environ. 508: 525–533.
[18] Suman, T. Y, Rajasree, S. R. R, Kirubagaran, R. (2015). Evaluation of zinc oxide nanoparticles toxicity on marine algae Chlorella vulgaris through flow cytometric, cytotoxicity and oxidative stress analysis. Ecotoxicol. Environ. Saf. 113: 23-30.
[19] Castro-Bugallo, A, Gonzalez-Fernandez, A, Guisande, C, Barreiro, A. (2014). Comparative responses to metal oxide nanoparticles in marine phytoplankton. Arch. Environ. Contam. Toxicol. 67(4): 483-493.
[20] Sadiq, I. M, Pakrashi, S, Chandrasekaran, N, Mukherjee, A. (2011). Studies on toxicity of aluminium oxide (Al2O3) nanoparticles to microalgae species: Scenedesmus sp. and Chlorella sp. J. Nanopart. Res. 13: 3287-3299.
[21] Manier, N, Bado-Nilles A, Delalain P, Aguerre-Chariol O, Pandard P. (2013). Ecotoxicity of non-aged and aged CeO2 nanomaterials towards freshwater microalgae. Environ. Pollut. 180: 63-70.
[22] Manzo, S, Miglietta M. L, Rametta G, Buono S, Francia, G. D. (2013). Toxic effects of ZnO nanoparticles towards marine algae Dunaliella tertiolecta. Sci. Total Environ. 445-446: 371-6.
[23] Anderson, R. A. (2005). Algal Culturing Techniques. Elsevier Inc., Amsterdam.
[24] Stanier, R. Y., Kunisawa, R., Mandel, M. and Cohen-Bazire, G. (1971). Purification and properties of unicellular blue-green algae (Order Chroococcales). Bacteriological Reviews, 35: 171-205.
[25] Becker EW. (1994). Microalgae: Biotechnology and Microbiology. Cambridge University Press, New York.
[26] Whyte JC. (1987). Biochemical composition and energy content of six species of phytoplankton used in mariculture of bivalves. Aquaculture. 60:231-241.
[27] Lowry, O. H., Rosebrough, N. J., Farr, A. L. and Randall, RJ. (1951). Protein Measurement with the Folin Phenol Reagent. The Journal of Biological Chemistry, 193: 265-275.
[28] Gerhardt, P., Murray, R. G. E., Wood, W. A. and Krieg, N. R. (1994) Methods for General and Molecular Bacteriology. ASM, Washington DC.
[29] Leyva, A., Quintana, A., Sanchez, M., Rodriguez, E. N., Cremata, J. and Sanchez, J. C. (2008). Rapid and sensitive anthrone-sulfuric acid assay in microplate format to quantify carbohydrate in biopharmaceutical products: Method development and validation. Biologicals, 36: 134-141.
[30] Paoletti F, Mocali A. (1990). Determination of superoxide dismutase activity by purely chemical system based on NAD (P) H oxidation. Methods Enzymol. 186: 209-20.
[31] Anderson ME. (1985). Determination of glutathione and glutathione disulfide in biological samples. Methods Enzymol. 113:548-555.
[32] Humbert JF, Barbe V, Latifi A, Gugger M, Calteau A, Coursin T, Lajus A, Castelli V, Oztas S, Samson G, Longin C, Medigue C, de Marsac NT. (2013). A tribute to disorder in the genome of the bloom-forming freshwater cyanobacterium Microcystis aeruginosa. PLoS ONE 8: 70747.
[33] Yoshida M, Yoshida T, Kashima A, Takashima Y, Hosoda N, Nagasaki K, Hiroishi S (2008). Ecological dynamics of the toxic bloom-forming cyanobacterium Microcystis aeruginosa and its cyanophages in freshwater. Appl Environ Microbiol 74(10):3269-3273.
[34] Park H M, Kim KH, Lee HH, Kim JS and Hwang S J (2010). Selective inhibitory potential of silver nanoparticles on the harmful cyanobacterium Microcystis aeruginosa. Biotechnol Lett. 32: 423-428.
[35] Wang Z, Li J, Zhao J, Xing B. (2011). Toxicity and internalization of CuO nanoparticles to prokaryotic alga Microcystis aeruginosa as affected by dissolved organic matter. Environ Sci Technol 45(14):6032-6040.
[36] Sankar, R., Prasath, B. B., Nandakumar, R. et al. (2014). Growth inhibition of bloom forming cyanobacterium Microcystis aeruginosa by green route fabricated copper oxide nanoparticles. Environ Sci Pollut Res Int 21: 14232-14240.
[37] Zhang W, Xiong B, Chen L, Lin K, Cui X, Bi H, Guo M, Wang W. (2013). Toxicity assessment of Chlorella vulgaris and Chlorella protothecoides following exposure to Pb (II). Environ Toxicol Pharmacol. 36(1):51-57.
[38] Pinto E., Sigaud-kutner T., Leitao M. A., Okamoto O. K., Morse D., Colepicolo P. (2003). Heavy metal-induced oxidative stress in algae. J. Phycol. 39: 1008-1018.
[39] Abd El-Baky, H. H., El Baz, F. K. and El-Baroty, G. S. (2004). Production of antioxidant by the green alga Dunaliella salina. Int. J. Agri. Biol. 6: 49-57.
[40] Mittler, R., Vanderauwera, S., Gollery, M. and Van Breusegem, F. (2004). The reactive oxygen gene network of plants. Trends Plant Sci. 9: 490-498.
[41] Noctor, G., L. Gomez, H. Vanacker, and C. Foyer. (2002). Interactions between biosynthesis, compartmentation and transport in the control of glutathione homeostasis and signaling. J. Exp. Bot. 53: 1283-1304.
Cite This Article
  • APA Style

    Anusha L., Chingangbam Sushmita Devi, Sibi G. (2017). Inhibition Effects of Cobalt Nano Particles Against Fresh Water Algal Blooms Caused by Microcystis and Oscillatoria. American Journal of Applied Scientific Research, 3(4), 26-32. https://doi.org/10.11648/j.ajasr.20170304.12

    Copy | Download

    ACS Style

    Anusha L.; Chingangbam Sushmita Devi; Sibi G. Inhibition Effects of Cobalt Nano Particles Against Fresh Water Algal Blooms Caused by Microcystis and Oscillatoria. Am. J. Appl. Sci. Res. 2017, 3(4), 26-32. doi: 10.11648/j.ajasr.20170304.12

    Copy | Download

    AMA Style

    Anusha L., Chingangbam Sushmita Devi, Sibi G. Inhibition Effects of Cobalt Nano Particles Against Fresh Water Algal Blooms Caused by Microcystis and Oscillatoria. Am J Appl Sci Res. 2017;3(4):26-32. doi: 10.11648/j.ajasr.20170304.12

    Copy | Download

  • @article{10.11648/j.ajasr.20170304.12,
      author = {Anusha L. and Chingangbam Sushmita Devi and Sibi G.},
      title = {Inhibition Effects of Cobalt Nano Particles Against Fresh Water Algal Blooms Caused by Microcystis and Oscillatoria},
      journal = {American Journal of Applied Scientific Research},
      volume = {3},
      number = {4},
      pages = {26-32},
      doi = {10.11648/j.ajasr.20170304.12},
      url = {https://doi.org/10.11648/j.ajasr.20170304.12},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.ajasr.20170304.12},
      abstract = {Cyanobacterial blooms deplete nutrients, reduce water clarity, exhaust carbon di oxide and produces secondary metabolites which negatively affect aquatic organisms and water quality. Control of algal blooms using metal nano particles is one effective method for the safety of water environment. Cobalt nano particles (CoNPs) were synthesized and tested against microalgae isolated from fresh water cyanobacterial blooms by assessing the effects on growth rate, biomass concentration, photosynthetic pigments concentration and antioxidant enzyme activity. Microcystis and Oscillatoria were identified as the predominant isolates from algal blooms and treated with varying concentrations (1, 2, 3, 4 and 5 mg·L-1) of CoNPs. Steady decline in the growth rate of microalgae was observed at the end of 5 days indicating the toxicity of CoNPs on microalgal growth. At the end of cultivation period, 78% and 88% of reduction in biomass concentration of Microcystis and Oscillatoria were observed at 5 mg·L-1 of CoNPs. The chlorophyll content was reduced from 1.53 to 0.24 mg·L-1 in Microcystis and 1.63 to 0.29 mg·L-1 in Oscillatoria. There was a 69.3% and 73.2% decrease in carotenoid content of Microcystis and Oscillatoria respectively. Both protein and carbohydrate contents of the microalgae were reduced with increasing concentration of nano particles. The decrease in Super oxide dismutase (SOD) activity with increased nanoparticle concentration reveals the formation of stress in the microalgae. The increasing GSH activity proved the effect of CoNPs on the activation of antioxidative enzymes to protect the cells. This study demonstrates the efficiency of cobalt nano particles (CoNPs) on inhibition of fresh water algal blooms thereby reducing the eutrophication problem.},
     year = {2017}
    }
    

    Copy | Download

  • TY  - JOUR
    T1  - Inhibition Effects of Cobalt Nano Particles Against Fresh Water Algal Blooms Caused by Microcystis and Oscillatoria
    AU  - Anusha L.
    AU  - Chingangbam Sushmita Devi
    AU  - Sibi G.
    Y1  - 2017/11/28
    PY  - 2017
    N1  - https://doi.org/10.11648/j.ajasr.20170304.12
    DO  - 10.11648/j.ajasr.20170304.12
    T2  - American Journal of Applied Scientific Research
    JF  - American Journal of Applied Scientific Research
    JO  - American Journal of Applied Scientific Research
    SP  - 26
    EP  - 32
    PB  - Science Publishing Group
    SN  - 2471-9730
    UR  - https://doi.org/10.11648/j.ajasr.20170304.12
    AB  - Cyanobacterial blooms deplete nutrients, reduce water clarity, exhaust carbon di oxide and produces secondary metabolites which negatively affect aquatic organisms and water quality. Control of algal blooms using metal nano particles is one effective method for the safety of water environment. Cobalt nano particles (CoNPs) were synthesized and tested against microalgae isolated from fresh water cyanobacterial blooms by assessing the effects on growth rate, biomass concentration, photosynthetic pigments concentration and antioxidant enzyme activity. Microcystis and Oscillatoria were identified as the predominant isolates from algal blooms and treated with varying concentrations (1, 2, 3, 4 and 5 mg·L-1) of CoNPs. Steady decline in the growth rate of microalgae was observed at the end of 5 days indicating the toxicity of CoNPs on microalgal growth. At the end of cultivation period, 78% and 88% of reduction in biomass concentration of Microcystis and Oscillatoria were observed at 5 mg·L-1 of CoNPs. The chlorophyll content was reduced from 1.53 to 0.24 mg·L-1 in Microcystis and 1.63 to 0.29 mg·L-1 in Oscillatoria. There was a 69.3% and 73.2% decrease in carotenoid content of Microcystis and Oscillatoria respectively. Both protein and carbohydrate contents of the microalgae were reduced with increasing concentration of nano particles. The decrease in Super oxide dismutase (SOD) activity with increased nanoparticle concentration reveals the formation of stress in the microalgae. The increasing GSH activity proved the effect of CoNPs on the activation of antioxidative enzymes to protect the cells. This study demonstrates the efficiency of cobalt nano particles (CoNPs) on inhibition of fresh water algal blooms thereby reducing the eutrophication problem.
    VL  - 3
    IS  - 4
    ER  - 

    Copy | Download

Author Information
  • Department of Biotechnology, Bangalore City College, Bengaluru, India

  • Department of Microbiology, Bangalore City College, Bengaluru, India

  • Department of Biotechnology, Indian Academy Degree College-Autonomous, Bengaluru, India

  • Sections