Research into the biosorption process of heavy metal ions by the sediments from stations of biological iron removal

Authors

  • Alexander Kvartenko National University of Water and Environmental Engineering Soborna str., 11, Rivne, Ukraine, 33028, Ukraine https://orcid.org/0000-0001-5634-1128
  • Valery Orlov National University of Water and Environmental Engineering Soborna str., 11, Rivne, Ukraine, 33028, Ukraine
  • Oksana Pletuk National University of Water and Environmental Engineering Soborna str., 11, Rivne, Ukraine, 33028, Ukraine https://orcid.org/0000-0003-2295-4238

DOI:

https://doi.org/10.15587/1729-4061.2017.106961

Keywords:

biominerals, biosorption of ions of heavy metals, matrices of iron bacteria, sediment of iron-removal station

Abstract

 

The article considers the possibility of using the sediments from stations of biological iron removal for the biosorption of heavy metal ions (IHMs) from both natural groundwaters and washing waters of enterprises with galvanic cycles. The processes of extracting Zn2+ ions (up to 50 mg/dm3), Cu2+ (up to 16 mg/dm3), Ni2+ (up to 1.3 mg/dm3), Cr6+ (up to 2.0 mg/dm3) on the bacterial structures of iron bacteria consortia and the optimal parameters of passing this process are determined (for washing waters pH=8.5–9.0). The influence of constant magnetic field with intensity of 20–60 mT, as well as the influence of different kinds of sediments from stations of biological iron removal on the efficiency of the process of removing IHM have been investigated. A significant percentage of the removal of IHM using calcined precipitate (98 % for Cu2+, 97 % for Zn2+, 85 % for Ni2+) is due to the exoeffect that occurs at a wide temperature range of 200–400 ºС. In this case, there is a smooth decrease in the mass of the sediment, indicating the combustion of the organic component and the crystallization of the amorphous phase. As a result, goethite (a-FeOOH) and lepidocrocyte (g-FeOOH) are converted into hematite (a-Fe2O3) and magnetite (g-Fe2O3), which have magnetic properties. When using as a reagent a fresh sediment, active involvement in the process of adsorption of heavy metal ions is carried out by biominerals, cells and polymer matrices of iron bacteria that have a crystalline structure and a large specific surface. At the same time, the effectiveness of removing IHMs was, respectively: for Cu2+ 93 %; for Zn2+ 92 %; for Ni2+ 70 %.

The efficiency of one-, two- and three-stage water purification schemes have been investigated. It was established that using the three-stage scheme with hydromechanical mixers and water alkalinization to pH 9.0, the efficiency of IHM removal was: for Cu2+ up to 96 %; For Zn2+ up to 99 %; for Ni2+ up to 85 %. The X-ray spectral microanalysis of the sediment of the surface of the Gallioella bacterium case revealed the accumulation of IHM in the structure. The process of adsorption of IHM on the bacterial structures of consortia of iron bacteria due to their electrostatic bonding with both anionic surface of cell wall and with organic polymers isolated by cells of iron bacteria is substantiated.

Author Biographies

Alexander Kvartenko, National University of Water and Environmental Engineering Soborna str., 11, Rivne, Ukraine, 33028

PhD, Associate Professor

Department of water supply, water sewerage and drilling

Valery Orlov, National University of Water and Environmental Engineering Soborna str., 11, Rivne, Ukraine, 33028

Doctor of Technical Sciences, Professor

Department of water supply, water sewerage and drilling

Oksana Pletuk, National University of Water and Environmental Engineering Soborna str., 11, Rivne, Ukraine, 33028

Engineer

Department of water supply, water sewerage and drilling

References

  1. Haferburg, G., Kothe, E. (2011). Biogeosciences in Heavy Metal-Contaminated Soils. Bio-Geo Interactions in Metal-Contaminated Soils, 17–34. doi: 10.1007/978-3-642-23327-2_2
  2. Fylypchuk, V. L. (2004). Ochyshchennia bahatokomponentnykh metalovmishchuiuchykh stichnykh vod promyslovykh pidpryiemstv. Rivne: UDUVHP, 232.
  3. Dolina, L. F. (2008). Sovremennaya tekhnika i tekhnologiya dlya ochistki stochnyh vod ot soley tyazhelyh metallov. Dnepropetrovsk: Kontinent, 254.
  4. Zapotoczny, S., Jurkiewicz, A., Tylko, G., Anielska, T., Turnau, K. (2007). Accumulation of copper by Acremonium pinkertoniae, a fungus isolated from industrial wastes. Microbiological Research, 162 (3), 219–228. doi: 10.1016/j.micres.2006.03.008
  5. Kochergin, A. S., Andreev, S. Yu., Grishin, B. M., Bakunov, M. V. (2010). Novaya tekhnologiya i princip raboty lokal'nyh ochistnyh sooruzheniy cekhov gal'vanopokrytiy. Izvestiya vyssh. ucheb. zavedeniy. Stroitel'stvo, 1, 68–74.
  6. Comte, S., Guibaud, G., Baudu, M. (2008). Biosorption properties of extracellular polymeric substances (EPS) towards Cd, Cu and Pb for different pH values. Journal of Hazardous Materials, 151 (1), 185–193. doi: 10.1016/j.jhazmat.2007.05.070
  7. Ahluwalia, S. S., Goyal, D. (2007). Microbial and plant derived biomass for removal of heavy metals from wastewater. Bioresource Technology, 98 (12), 2243–2257. doi: 10.1016/j.biortech.2005.12.006
  8. Hennebel, T., De Gusseme, B., Boon, N., Verstraete, W. (2009). Biogenic metals in advanced water treatment. Trends in Biotechnology, 27 (2), 90–98. doi: 10.1016/j.tibtech.2008.11.002
  9. Sahabi, D. M., Takeda, M., Suzuki, I., Koizumi, J. (2010). Comparison of Arsenate, Lead, and Cadmium Adsorption onto Aged Biofilter Media. Journal of Environmental Engineering, 136 (5), 493–500. doi: 10.1061/(asce)ee.1943-7870.0000184
  10. Fujikawa, Y., Sugahara, M., Hamasaki, T., Yoneda, D., Minami, A., Sugimoto, Y., Iwasaki, H. (2010). Biological filtration using iron bacteria for simultaneous removal of arsenic, iron, manganese and ammonia: Application to waterworks facilities in Japan and developing countries. Journal of Human Environmental Studies, 9, 261–276.
  11. Bukreeva, V. Yu., Grabovich, M. Yu., Eprincev, A. T., Dubinina, G. A. (2009). Sorbciya kolloidnyh soedineniy oksidov zheleza i marganca s pomoshch'yu zhelezobakteriy na peschanyh zagruzkah ochistnyh sooruzheniy vodopod’emnyh stanciy. Sorbcionnye i hromatograficheskie processy, 9 (4), 506–514.
  12. Orlov, V. O. (2008). Znezaliznennia pidzemnykh vod sproshchenoiu aeratsieiu ta filtruvanniam. Rivne: NUVHP, 158.
  13. Kvartenko, O. M. (2016). Vykorystannia osadiv stantsii biolohichnoho znezaliznennia dlia osadzhennia ioniv vazhkykh metaliv iz zvorotnykh stokiv halvanichnoho vyrobnytstva. Ekolohiia. Liudyna. Suspilstvo. Kyiv, 93–95.
  14. Angelova, R., Slavov, L., Iliev, M., Mitova, M., Blagoev, B., Nedkov, I., Groudeva, V. (2015). Biogenic iron oxides from labor atory cultivated Leptothrix sp. for application in the bionanotechnology. Annuaire de l’Université de Sofia “St. Kliment Ohridski”. First National Conference of Biotechnology, 100, 231–238.

Downloads

Published

2017-08-22

How to Cite

Kvartenko, A., Orlov, V., & Pletuk, O. (2017). Research into the biosorption process of heavy metal ions by the sediments from stations of biological iron removal. Eastern-European Journal of Enterprise Technologies, 4(10 (88), 37–43. https://doi.org/10.15587/1729-4061.2017.106961