The Removal of Terasil Navy Blue Dye from Al-Kut Textile Wastewater Using Membrance Technologies

  • Authors

    • Hatem Asal Gzar
    • Zahraa khalid shhaieb
    2018-11-28
    https://doi.org/10.14419/ijet.v7i4.20.26418
  • Dyeing removal, Terasil Blue dye, NF and UF membrane, wastewater.

  • Abstract

    The current work was devoted to study the operating feasibility using membranes which were manufactured locally, two membrance types were tested nanofiltration (NF) and ultrafiltration (UF) membrane to treat the effluent of Al-kut textile industry. Based on the usage rate in Iraq textile industries, terasil navy blue (TNB) is one of the common disperse dyes discharged in effluent wastewater. Therefore this type of dyes was selected to experience in this study. Parameters such as effects of TNB concentration, feed temperature and operating pressure and its effect on permeate flux noticed and the TNB rejection were investigated. The results show that when using NF system at pressure of 10 bar and when the temperature increased from 25ºC to 37ºC, it was found that an increase in permeate flux from 46.97 to 50 LMH.  However, in UF system permeate flux was increased from 41.32 to 45.04 LMH.  While dye removal was decline in NF membrane from 96.00 to 95.14 and for UF from 79.50 to 78.67 when the temperature raised from 25ºC to 37ºC.The pressure state positive effects on dye removal for both membranes, it show that NF membrane is better in treatment than UF membrane.

     


     

  • References

    1. [1] Allegre, C., Mouline, P., Maisseu, M., & Charbit, F., 2006). Treatment and reuse of reactive dyeing effluents. J. Memb. Science. 269: 15-17.

      [2] Patnaik P., (1996). A Comprehensive Guide to the Hazardous Properties of Chemical Substances. 1st edition. New York: John Wiley & Sons, Inc.

      [3] Kim TH, Lee Y, Yang J, Park C., (2004) Decolorization of dye solutions by a membrane bioreactor (MBR) using whit-rot Fungi. Desalination, 168: 287-293.

      [4] G. Eremektar, H. Selcuk & S. Meric, (2007). Investigation of the Relation between COD Fractions and the Toxicity in a Textile Finishing Industry Wastewater: Effect of Preozonation, Journal of Desalination, 211: 314-320.

      [5] Kestioglu, K. & Yalili, M., (2006). Treatability of Textile Industry Wastewater with High COD Content by Chemical Precipitation and Adsorption, Ekoloji Journal, 15(59): 27-31.

      [6] Pinnau, I., Freeman, B. D., (2000). In Formation and Modification of Polymeric Membranes, Symposium Series 744; American Chemical Society: Washington D.C., pp 1 -22.

      [7] Hassani, A. H., Mirzayee, R., Nasseri, S., Borghei, M., Gholami, M., & Torabifar, B., (2008). Nanofiltration process on dye removal from simulated textile wastewater. International journal of environmental science & technology, 5(3): 401-408.â€

      [8] Woerner, D. L. (2003). "Membrane technology in textile operation. Koch membrane systems". Wilmington, MA.

      [9] Al-Aseeri, M., Bu-Ali, Q., Haji, S., & Al-Bastaki, N. (2007). Removal of Acid Red and sodium chloride mixtures from aqueous solutions using nanofiltration. Desalination, 206(1-3), 407-413.â€

      [10] Akbari, A., Remigy, J. C., & Aptel, P. (2002). Treatment of textile dye effluent using a polyamide-based nanofiltration membrane. Chemical Engineering and Processing: Process Intensification, 41(7), 601-609.â€

      [11] Koyuncu, I. (2002). Reactive dye removal in dye/salt mixtures by nanofiltration membranes containing vinylsulphone dyes: effects of feed concentration and cross flow velocity. Desalination, 143(3), 243-253.â€

      [12] Cadotte, J. E., Petersen, R. J., Larson, R. E., & Erickson, E. E. (1980). A new thin-film composite seawater reverse osmosis membrane. Desalination, 32, 25-31.â€

      [13] Gholami, M., Nasseri, S., Alizadehfard, M., & Mesdaghinia, A., (2003). Textile dye Removal by Membrane Technology and Biological Oxidation. Water quality research journal of Canada, 38(2): 379-391.

      [14] Tang, C., & Chen, V. (2002). Nanofiltration of textile wastewater for water reuse. Desalination, 143(1), 11-20.â€

      [15] Nilsson, M. Lipnizki, F., Trägårdh, G., & Östergren, K., (2008). Performance, Energy and Cost Evaluation of a Nanofiltration Plant Operated at Elevated Temperatures. Separation and Purification Technology, 60(1): 36–45.

      [16] Lopes, C. N., Petrus, J. C. C., & Riella, H. G., (2005). Color and COD retention by nanofiltration membranes. Desalination, 172(1): 77-83.

      [17] Peng, Y., Ge, J., Li, Z., & Wang, S. (2015). Effects of anti-scaling and cleaning chemicals on membrane scale in direct contact membrane distillation process for RO brine concentrate. Separation and Purification Technology, 154: 22-26.â€

      [18] Lee, S., Cho, J., & Elimelech, M. (2005). Combined influence of natural organic matter (NOM) and colloidal particles on nanofiltration membrane fouling. Journal of Membrane Science, 262(1-2), 27-41.

      [19] â€Alhadidi, A., Kemperman, A. J. B., Blankert, B., Schippers, J. C., Wessling, M., & Van der Meer, W. G. J. (2011). Silt density index and modified fouling index relation, and effect of pressure, temperature and membrane resistance. Desalination, 273(1): 48-56.

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  • How to Cite

    Asal Gzar, H., & khalid shhaieb, Z. (2018). The Removal of Terasil Navy Blue Dye from Al-Kut Textile Wastewater Using Membrance Technologies. International Journal of Engineering & Technology, 7(4.20), 557-562. https://doi.org/10.14419/ijet.v7i4.20.26418

    Received date: 2019-01-22

    Accepted date: 2019-01-22

    Published date: 2018-11-28