The Use of Adsorbent Materials of Improving the Characteristics of Polluted Soils, Part 2 the Bioaccumulation of Metals in Plants Used in Phytoremediation Processes

Authors

  • Florica Morariu Banat’s University of Agricultural Sciences and Veterinary Medicine ”King Michael I of Romania” from Timisoara, Faculty of Animal Science and Biotechnologies, 300645-Timisoara, Calea Aradului 119, Romania
  • Smaranda Mâşu National R & D Institute for Industrial Ecology, Branch of Timisoara, 300004-Timisoara, Regina Maria 1, Romania
  • Maria Popa “1 Decembrie 1918” University of Alba Iulia, Science Faculty, 510009-Alba Iulia, N. Iorga 11-13, Romania
  • Dumitru Popescu Banat’s University of Agricultural Sciences and Veterinary Medicine ”King Michael I of Romania” from Timisoara, Faculty of Animal Science and Biotechnologies, 300645-Timisoara, Calea Aradului 119, Romania
  • Gheorghe Cioban Aurel Vlaicu” University Arad, 310130-Arad, B-dul Revoluţiei, 77, Romania

Keywords:

phytoremediation, total petroleum hydrocarbon

Abstract

The study covers the advantages of phytoremediation processes of soils heavily polluted with total petroleum hydrocarbon (TPH) with the use of Linum usitatissimum (flax). To increase the potential development of technical crops on TPH soils polluted with 74.12±3.5 g·kg-1 D.M., the contaminated soils were amended with fly ash; the ratio of polluted soil: fly ash 12:1 wt./wt. and fertilized with sewage sludge. The degree of accumulation of Fe in the stems was 21-33% higher than in the control sample and 6-27% in the seeds; the accumulation of Mn in the stems was 13.5-30% higher than in the control sample and 8-17% in the seeds; the accumulation of Cu in stems was 17-6% higher than in the control sample and for seeds 20-60%; the accumulation of Zn in stems was 13-27% higher than in the control sample with 49-63% in the seeds. In the harvested plant tissues from the studied variants the content of heavy metals Cd, Cr, Pb and Ni was less than the detection limit. Monitoring bioaccumulation of heavy metals in aerial plant tissue was needed to decide the sector where the biomass harvested from TPH polluted soil covered with vegetation.

References

Cofield, N., Banks, M. K., Schwab, A. P., Evaluation of Hydrophobicity in Pah-Contaminated Soils during Phytoremediation, Environmental Pollution, 2007, 145, 60-67

Riding, M. J., Doick, K. J., Martin, F. L., Jones, K. C., Semple, K. T., Chemical Measures of Bioavailability/Bioaccessibility of PAHs in Soil, Fundamentals to application, Journal of Hazardous Materials, 2013, 261, 687-700

Page, A. L., Elseevi, A. A., Straughan, I. R., Phisical and Chemical Proprieties of Fly from Coal Fired Power Plant with Reference to Environmental Impacts, Springer Verlag Inc., New York, 1979

Haynes R. J., Reclamation and Revegetation of Fly Ash Disposal Sites–Challenges and Research Needs, Journal of Environmental Management, 2009, 90(1), 43-53

Ram, L. C., Masto, R. E., Fly Ash for Soil Amelioration: A Review on the Influence of Ash Blending with Inorganic and Organic Amendments, Earth-Science Reviews, 2014, 128, 52-74

Basu, M., Pande, M., Bhadoria, P. B. S., Mahapatra, S. C., Potential Fly-Ash Utilization in Agriculture: A Global Review, Progress in Natural Science, 2009, 19(10), 1173-1186

Mâşu, S., Burtica, G., Jurj, N. L., Albulescu, M., Aspects of Sustainable Development: Fly Ash Deposits, Biosolids, Contaminated Biomass, Studia UBB Chemia, 2012, 57(3), 249-258

Singh, R., Singh, D. P., Kumar, N., Bhargava, S. K., Barman, C., Accumulation and Translocation of Heavy Metals in Soil and Plants from Fly Ash Contaminated Area. Journal of Environmental Biology, 2010, 31(14), 421-430.

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Published

2023-09-05