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Spatial Variations of the Activity of 137 Cs and the Contents of Heavy Metals and Petroleum Products in the Polluted Soils of the City of Elektrostal

  • DEGRADATION, REHABILITATION, AND CONSERVATION OF SOILS
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  • Published: 15 June 2022
  • Volume 55 , pages 840–848, ( 2022 )

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international food research journal

  • D. N. Lipatov 1 ,
  • V. A. Varachenkov 1 ,
  • D. V. Manakhov 1 ,
  • M. M. Karpukhin 1 &
  • S. V. Mamikhin 1  

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The levels of specific activity of 137 Cs and the contents of mobile forms (1 M ammonium acetate extraction) of heavy metals (Zn, Cu, Ni, Co, Cr, Pb) and petroleum products were studied in the upper soil horizon of urban landscapes of the city of Elektrostal under conditions of local radioactive and chemical contamination were studied. In the soils within a short radius (0–100 m) around the heavy engineering plant, the specific activity of 137 Cs and the contents of mobile forms of Pb, Cu, and Zn were increased. The lognormal distribution law of 137 Cs was found in the upper (0–10 cm) soil layer; five years after the radiation accident, the specific activity of 137 Cs varied from 6 to 4238 Bq/kg. The coefficients of variation increased with an increase in the degree of soil contamination in the following sequence: Co < Ni < petroleum products < Cr < 137 Cs < Zn < Pb < Cu ranging from 50 to 435%. Statistically significant direct correlation was found between the specific activity of 137 Cs and the contents of mobile forms of Pb, Cu, and Zn in the upper horizon of urban soils, and this fact indicated the spatial conjugacy of local spots of radioactive and polymetallic contamination in the studied area. It was shown that the specific activity of 137 Cs, as well as the content of heavy metals and petroleum products in the upper layer (0–10 cm) of the soils disturbed in the course of decontamination, earthwork and reclamation is reduced.

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Activity Concentration of Natural Radionuclides and Total Heavy Metals Content in Soils of Urban Agglomeration

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INTRODUCTION

Contaminants migrate and accumulate in urban ecosystems under the impact of both natural and technogenic factors. The processes of technogenic migration of 137 Cs are most pronounced in radioactively contaminated territories. It was found in urboecological studies that the intensity of sedimentation of aerosol particles containing radionuclides and heavy metals is determined by the types of the surfaces of roofs, walls, roads, lawns, and parks and by their position within the urban wind field [ 12 , 26 ]. Traffic in the cities results in significant transport of dust and associated contaminants and radionuclides [ 15 , 24 ]. During decontamination measures in the areas of Chernobyl radioactive trace, not only the decrease in the level of contamination but also the possibility of secondary radioactive contamination because of the transportation of contaminated soil particles by wind or water, or anthropogenic transfer of transferring of ground were observed [ 5 , 6 ]. Rainstorm runoff and hydrological transport of dissolved and colloidal forms of 137 Cs can result in the accumulation of this radionuclide in meso- and microdepressions, where sedimentation takes place [ 10 , 16 ]. Different spatial distribution patterns of 137 Cs in soils of particular urban landscapes were found in the city of Ozersk near the nuclear fuel cycle works [ 17 ]. Natural character of 137 Cs migration in soils of Moscow forest-parks and a decrease in its specific activity in industrial areas have been revealed [ 10 ]. Determination of the mean level and parameters of spatial variations of 137 Cs in soils is one of primary tasks of radioecological monitoring of cities, including both unpolluted (background) and contaminated territories.

Emissions and discharges from numerous sources of contamination can cause the accumulation of a wide range of toxicants in urban soils: heavy metals (HMs), oil products (OPs), polycyclic aromatic hydrocarbons (PAHs), and other chemical substances. Soil contamination by several groups of toxicants is often observed in urban landscapes [ 20 , 23 ] because of the common contamination source or close pathways of the migration of different contaminants. A comprehensive analysis of contamination of urban soils by radionuclides and heavy metals has been performed in some studies [ 21 , 25 ]. The determination of possible spatial interrelationships between radioactive and chemical contaminations in urban soils is an important problem in urban ecology.

A radiation accident took place in the Elektrostal heavy engineering works (EHEW) in April 2013: a capacious source of 137 Cs entered the smelt furnace, and emission of radioactive aerosols from the aerating duct into the urban environment took place. The activity of molten source was estimated at about 1000–7000 Ci [ 14 ]. The area of contamination in the territory of the plant reached 7500 m 2 . However, radioactive aerosols affected a much larger area around the EHEW, including Krasnaya and Pervomaiskaya streets, and reached Lenin Prospect.

Geochemical evaluation of contamination of the upper soil horizon in the city of Elektrostal was carried out in 1989–1991. This survey indicated the anomalies of concentrations of wolfram, nickel, molybdenum, chromium, and other heavy metals related to accumulation of alloying constituent and impurities of non-ferrous metals in the emissions of steelmaking works [ 19 ].

The aim of our work was to determine the levels of specific activity of 137 Cs, concentrations of mobile forms of heavy metals (Zn, Cu, Ni, Co, Cr, and Pb) and oil products in the upper soil horizons in different urban landscapes of the city of Elektrostal under the conditions of local radioactive and chemical contamination.

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Lipatov, D.N., Varachenkov, V.A., Manakhov, D.V. et al. Spatial Variations of the Activity of 137 Cs and the Contents of Heavy Metals and Petroleum Products in the Polluted Soils of the City of Elektrostal. Eurasian Soil Sc. 55 , 840–848 (2022). https://doi.org/10.1134/S1064229322060072

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Received : 21 October 2021

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Published : 15 June 2022

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DOI : https://doi.org/10.1134/S1064229322060072

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