Examining the efficiency of electrochemical purification of storm wastewater at machine­building enterprises

Authors

DOI:

https://doi.org/10.15587/1729-4061.2018.150088

Keywords:

electrocoagulation, machine building, surface­drain wastewater, heavy metal contamination, current density, settling

Abstract

We have examined the composition of polluted storm water discharged from the territory of a machine­building enterprise. It was established that the territory was unevenly polluted, with the surface wastewater from the area adjacent to the production shops dominated by ions of copper, to 1.1 mg/dm3; zinc, to 2.0 mg/dm3; nickel, to 1.6 mg/dm3; chromium, to 0.93 mg/dm3, and lead, to 5.0 mg/dm3. It was found that the removal of metals’ ions during electrocoagulation treatment is significantly influenced by the following factors: a flow rate of the wastewater sent for purification; duration of wastewater settling upon electrocoagulation, and current density during electrolysis. We have defined optimal parameters for the wastewater treatment process.

Based on experimental research, we have built graphic dependences of purification effectiveness on current density and water settling time. The optimal parameters were determined for the wastewater treatment process, which ensure sufficiently high efficiency of water purification from heavy metals’ ions (to match the values for discharge standards) at an acceptable amount of electricity. It was established that the best conditions for deposition of nickel and lead are a current density of 50 A/m3 and a time of settling after electrocoagulation of 9 hours. The optimal conditions for depositing copper and zinc are 12 hours, and it is possible to lower the concentration of chromium to safe concentrations at a current density of 10 A/m3 and a time of settling of 4 hours. It was revealed that the effectiveness of purification from metals’ ions increases significantly with an increase in the current density and settling time; in addition, the efficiency of settling is 1.4‒3 times higher than the increase in current density. It is shown that prolonging the time of settling might not always compensate for the decrease in current density during electrocoagulation, which requires selecting the optimal balance of all factors. The experimental data that we acquired are necessary to calculate the technological process parameters.

By applying a method of full­factor experiment, we have constructed mathematical models of the process, which include the dependence of response (the residual concentration) on the above­enumerated factors. The proposed models could make it possible to control the process of electrocoagulation by influencing those factors on which the efficiency of purification depends

Author Biographies

Olena Maksimenko, National Technical University «Kharkiv Polytechnic Institute» Kyrpychova str., 2, Kharkiv, Ukraine, 61002

Senior Lecturer

Department of labor and environment protection

Hanna Pancheva, National Technical University «Kharkiv Polytechnic Institute» Kyrpychova str., 2, Kharkiv, Ukraine, 61002

PhD, Associate Professor

Department of labor and environment protection

Svitlana Madzhd, National Aviation University Kosmonavta Komarova ave., 1, Kyiv, Ukraine, 03058

PhD, Associate Professor

Department of Ecology

Yana Pysanko, National Aviation University Kosmonavta Komarova ave., 1, Kyiv, Ukraine, 03058

Postgraduate student

Department of Ecology

Oleksandr Briankin, National Technical University «Kharkiv Polytechnic Institute» Kyrpychova str., 2, Kharkiv, Ukraine, 61002

Postgraduate student

Department of Chemical Technique and Industrial Ecology

Tetyana Tykhomyrova, National Technical University «Kharkiv Polytechnic Institute» Kyrpychova str., 2, Kharkiv, Ukraine, 61002

PhD, Аssociate Рrofessor

Department of chemical technique and industrial ecology

Tatiana Hrebeniuk, National Technical University of Ukraine "Igor Sikorsky Kyiv Polytechnic Institute" Peremohy аve., 37, Kiev, Ukraine, 03056

PhD, Senior Lecturer

Department of Engineering Ecology

References

  1. Rajeshkumar, S., Liu, Y., Zhang, X., Ravikumar, B., Bai, G., Li, X. (2018). Studies on seasonal pollution of heavy metals in water, sediment, fish and oyster from the Meiliang Bay of Taihu Lake in China. Chemosphere, 191, 626–638. doi: https://doi.org/10.1016/j.chemosphere.2017.10.078
  2. Ghaderpoori, M., kamarehie, B., Jafari, A., Ghaderpoury, A., Karami, M. (2018). Heavy metals analysis and quality assessment in drinking water – Khorramabad city, Iran. Data in Brief, 16, 685–692. doi: https://doi.org/10.1016/j.dib.2017.11.078
  3. Chowdhury, S., Mazumder, M. A. J., Al-Attas, O., Husain, T. (2016). Heavy metals in drinking water: Occurrences, implications, and future needs in developing countries. Science of The Total Environment, 569-570, 476–488. doi: https://doi.org/10.1016/j.scitotenv.2016.06.166
  4. Khandegar, V., Saroha, A. K. (2013). Electrocoagulation for the treatment of textile industry effluent – A review. Journal of Environmental Management, 128, 949–963. doi: https://doi.org/10.1016/j.jenvman.2013.06.043
  5. Maksymenko, O. A., Maksymenko, O. A., Kovalenko, M. S. (2014). Saving and rational use of water at enterprises due to rainwater. Technology audit and production reserves, 3 (3 (17)), 65–68. doi: https://doi.org/10.15587/2312-8372.2014.25406
  6. Shkop, A., Tseitlin, M., Shestopalov, O. (2016). Exploring the ways to intensify the dewatering process of polydisperse suspensions. Eastern-European Journal of Enterprise Technologies, 6 (10 (84)), 35–40. doi: https://doi.org/10.15587/1729-4061.2016.86085
  7. Shkop, A., Tseitlin, M., Shestopalov, O., Raiko, V. (2017). Study of the strength of flocculated structures of polydispersed coal suspensions. Eastern-European Journal of Enterprise Technologies, 1 (10 (85)), 20–26. doi: https://doi.org/10.15587/1729-4061.2017.91031
  8. Moussa, D. T., El-Naas, M. H., Nasser, M., Al-Marri, M. J. (2017). A comprehensive review of electrocoagulation for water treatment: Potentials and challenges. Journal of Environmental Management, 186, 24–41. doi: https://doi.org/10.1016/j.jenvman.2016.10.032
  9. Akbal, F., Camcı, S. (2011). Copper, chromium and nickel removal from metal plating wastewater by electrocoagulation. Desalination, 269 (1-3), 214–222. doi: https://doi.org/10.1016/j.desal.2010.11.001
  10. Al Aji, B., Yavuz, Y., Koparal, A. S. (2012). Electrocoagulation of heavy metals containing model wastewater using monopolar iron electrodes. Separation and Purification Technology, 86, 248–254. doi: https://doi.org/10.1016/j.seppur.2011.11.011
  11. Al-Shannag, M., Al-Qodah, Z., Bani-Melhem, K., Qtaishat, M. R., Alkasrawi, M. (2015). Heavy metal ions removal from metal plating wastewater using electrocoagulation: Kinetic study and process performance. Chemical Engineering Journal, 260, 749–756. doi: https://doi.org/10.1016/j.cej.2014.09.035
  12. Gatsios, E., Hahladakis, J. N., Gidarakos, E. (2015). Optimization of electrocoagulation (EC) process for the purification of a real industrial wastewater from toxic metals. Journal of Environmental Management, 154, 117–127. doi: https://doi.org/10.1016/j.jenvman.2015.02.018
  13. Hakizimana, J. N., Gourich, B., Chafi, M., Stiriba, Y., Vial, C., Drogui, P., Naja, J. (2017). Electrocoagulation process in water treatment: A review of electrocoagulation modeling approaches. Desalination, 404, 1–21. doi: https://doi.org/10.1016/j.desal.2016.10.011

Downloads

Published

2018-12-10

How to Cite

Maksimenko, O., Pancheva, H., Madzhd, S., Pysanko, Y., Briankin, O., Tykhomyrova, T., & Hrebeniuk, T. (2018). Examining the efficiency of electrochemical purification of storm wastewater at machine­building enterprises. Eastern-European Journal of Enterprise Technologies, 6(10 (96), 21–27. https://doi.org/10.15587/1729-4061.2018.150088