Journal of Soils and Sediments

, Volume 9, Issue 2, pp 103–110

Iron oxidation in different types of groundwater of Western Siberia

  • Leonid V. Serikov
  • Elena A. Tropina
  • Liudmila N. Shiyan
  • Fritz H. Frimmel
  • George Metreveli
  • Markus Delay
INTERCOMP• RESEARCH ARTICLE

DOI: 10.1007/s11368-009-0069-x

Cite this article as:
Serikov, L.V., Tropina, E.A., Shiyan, L.N. et al. J Soils Sediments (2009) 9: 103. doi:10.1007/s11368-009-0069-x

Abstract

Background, aim, and scope

The groundwaters of Western Siberia contain high concentrations of iron, manganese, silicon, ammonium, and, in several cases, hydrogen sulfide, carbonic acids, and dissolved organic substances. Generally, the groundwaters of Western Siberia can be divided into two major types: one type with a relatively low concentration of humic substances and high hardness (water of A type) and a second type with a relatively low hardness and high concentration of humic substances (water of B type). For drinking water production, the waters of A type are mostly treated in the classical way by aeration followed by sand bed filtration. The waters of B type often show problems when treated for iron removal. A part of iron practically does not form the flocs or particles suitable for filtration or sedimentation. The aim of this work was to determine the oxidizability of Fe(II), to characterize the iron colloids, and to investigate the complexation of the iron ions with humic substances and the coagulation of the iron colloids in the presence of dissolved organic matter.

Materials and methods

Water samples of the A and B types were taken from bore holes in Western Siberia (A type: in Tomsk and Tomsk region, B type: in Beliy Yar and Kargasok). Depth of sampling was about 200 m below surface. The oxidation of the groundwater samples by air oxygen and ozone was done in a bubble reactor consisting of a glass cylinder with a gas-inlet tube. To produce ozone, a compact ozone generator developed by Tomsk Polytechnic University was used. For the characterization of the colloids in the water of B type, the particle size distribution and the zeta potential were measured. To investigate the formation of complexes between iron and humic substances in the water of B type, size exclusion chromatography was used. The coagulation behavior of iron in the presence of dissolved organic substances was investigated at different pH values. The agglomerates were detected by measuring the optical density using a UV-Vis spectrometer.

Results

Ozone showed, as expected, a faster oxidation of Fe(II) than air oxygen. The rate constants for Fe(II) oxidation were not much different for the waters of A and B types when the same oxidation process was used. However, the removal of iron after oxidation and filtration was higher in the water of A type than in the water of B type. No evidence for the formation of soluble complexes between iron and humic substances were found. In the water of A type, the coagulation process started at pH = 4.5 and accelerated with increasing pH value. In the water of B type, the coagulation of colloids occurred only at pH = 11 and higher.

Discussion

The oxidation experiments indicated no major effect of dissolved organic carbon concentration on the kinetics of Fe(II) oxidation. In contrast to this, the humic substances showed a significant influence on the aggregation behavior of the iron hydroxide colloids. Due to the sorption of humic substances on the iron hydroxide colloids, they were highly stable in the pH range between 4.5 and 10. The particle size measurements confirmed the presence of small colloids in the water of B type. In contrast to this, the iron hydroxide colloids aggregated rapidly at pH = 11.

Conclusions

The results showed a great influence of humic substances on the iron removal from groundwaters of Western Siberia with high organic content. The sorption of humic substances on the iron colloids does not obviously allow their coagulation and formation of flocs suitable for filtration or sedimentation.

Recommendations and perspectives

By treatment of groundwaters containing high amounts of humic substances, some problems with the removal of iron are likely to occur. To increase the effectiveness of iron removal, the surface coating and pH-dependent charge effects should be taken into account by the selection and optimization of water treatment processes. The iron colloids coated by humic substances should be separated from the water phase by membrane filtration or by flocculation followed by filtration through different solid materials.

Keywords

Aggregation Colloids Groundwater Humic substances Iron oxidation Iron removal Western Siberia Zeta potential 

Copyright information

© Springer-Verlag 2009

Authors and Affiliations

  • Leonid V. Serikov
    • 1
  • Elena A. Tropina
    • 1
  • Liudmila N. Shiyan
    • 1
  • Fritz H. Frimmel
    • 2
  • George Metreveli
    • 2
  • Markus Delay
    • 2
  1. 1.Tomsk Polytechnic UniversityTomskRussia
  2. 2.Chair of Water ChemistryUniversity of Karlsruhe (TH) Engler-Bunte-InstituteKarlsruheGermany