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Comparing Bioavailability of Cadmium and Arsenic in Agricultural Soil Under Varied pH Condition

  • Oh, Se Jin (Department of Biological Environment, Kangwon National University) ;
  • Kim, Sung Chul (Department of Bioenvironmental Chemistry, Chungnam National University) ;
  • Ok, Yong Sik (Department of Biological Environment, Kangwon National University) ;
  • Oh, Seung Min (Department of Biological Environment, Kangwon National University) ;
  • Lee, Bup Yeol (Department of Biological Environment, Kangwon National University) ;
  • Lee, Sang Hwan (Technology Research Center, Korea Mine Reclamation Corporation) ;
  • Yang, Jae E. (Department of Biological Environment, Kangwon National University)
  • Received : 2015.01.13
  • Accepted : 2015.02.18
  • Published : 2015.02.28

Abstract

Bioavailability of cadmium (Cd) and arsenic (As) can be different depending on soil pH. For this reason, main purpose of this research was to compare bioavailability of Cd and As in agricultural field under varied soil pH and different extractants. Bioavailable fraction of Cd and As in soil was extracted with $CaCl_2$, $NaNO_3$, DTPA, EDTA, and low molecular weight organic acids (LMWOAs). Soil samples and cultivated crops were collected at the range of soil pH 4.5-8.5 and correlation analysis was conducted between bioavailable fraction of Cd and As in soil and total concentration of Cd and As in crops. Results showed that concentration of Cd and As in acidic soil was ranged $0.002-0.462mg\;kg^{-1}$ and $0.041-4.903mg\;kg^{-1}$ respectively. In alkaline condition, concentration of Cd and As were ranged $0.006-0.351mg\;kg^{-1}$ and $0.039-2.807mg\;kg^{-1}$ respectively. Comparing bioavailable fraction of Cd and As in acidic and alkaline soil condition, higher concentration was measured in acidic condition. Similarly, higher average concentration of Cd and Asin crops was observed in acidic condition (0.398 and $0.751mg\;kg^{-1}$ respectively) than alkaline condition (0.248 and $0.264mg\;kg^{-1}$). Among different extractants, LMWOAs method showed higher correlation ($r^2=0.545$) for Cd in acidic condition indicating that LMWOAs method could be applied for evaluating bioavailability of Cd in acidic soil. However, no high correlation was observed for As in both acidic and alkaline condition. Overall, bioavailable fraction of Cd and As can be higher in acidic condition of soil than alkaline condition resulting higher uptake of Cd and As from soil to crops. Therefore, efficient best management practice (BMPs) for Cd and As in acidic soil should be conducted for minimizing uptake of Cd and As into crops.

Keywords

References

  1. Chen, Y., Z. Shen, and X. Li. 2004. The use of vetiver grass (Vetiveria zizanioides) in the phytoremediation of soils contaminated with heavy metals. Appl. Geochem. 19(10):1553-1565. https://doi.org/10.1016/j.apgeochem.2004.02.003
  2. Chojnacka, K., A. Chojnacki, H. Gorecka, and H. Gorecki. 2005. Bioavailability of Heavy Metals from Polluted Soils to Plants. Sci. Total Environ. 337:175-182. https://doi.org/10.1016/j.scitotenv.2004.06.009
  3. Feng, M.H., X.Q. Shan, S. Zhang, and B. Wen. 2005. A Comparison of the rhizosphere-based method with DTPA, EDTA, $CaCl_2$, and $NaNO_3$ extraction methods for prediction of bioavailability of metals in soil to barley. Environ. Pollut. 137(2):231-240. https://doi.org/10.1016/j.envpol.2005.02.003
  4. Jung, G.B., W.I. Kim, K.H. Moon, and I.S. Ryu. 2000. Comparisons of simple extraction methods and availability for heavy metals in paddy soils. Korean J. Environ. Agric. 19(4):314-318.
  5. Jung, G.B,, W.I. Kim, J.S. Lee, J.D. Shin, J.H. Kim, and S.G. Yun. 2005. Availability of Heavy Metals in Soils with Different Characteristics and Controversial Points for Analytical Methods of Soil Contamination in Korea. Korea J. Environ. Agric.. 24(2):106-116. https://doi.org/10.5338/KJEA.2005.24.2.106
  6. Kim, J.Y., J.H. Lee, A. Kunhikrishnan, D.W. Kang, M.J. Kim, J.H. Yoo, D.H. Kim, Y.J. Lee, and W.I. Kim. 2012a. Transfer factor of heavy metals from agricultural soil to agricultural products. Korean J. Environ. Agric. 31(4):300-307. https://doi.org/10.5338/KJEA.2012.31.4.300
  7. Kim, K.R., K.H. Kim, G. Owens, and R. Naidu. 2007. Assessment techniques of heavy metal bioavailability in soil: A critical review. Korean J. Soil Sci. Fert. 40(4):311-325.
  8. Kim, K.R., G. Owens, and R. Naidu. 2009. Heavy metal distribution, bioaccessibility and phytoavailability in long-term contaminated soils from Lake Macquarie, Australia. Aust. J. Soil Res. 47(2):166-176. https://doi.org/10.1071/SR08054
  9. Kim, M.S., N. Koo, J.G. Kim, J.E. Yang, J.S. Lee, and G.I. Bak. 2012. Effects of soil amendments on the early growth and heavy metal accumulation of Brassica campestris ssp. Chinensis Jusl. in heavy metal-contaminated soil. korean J. Soil Sci. Fert. 45(6):961-967. https://doi.org/10.7745/KJSSF.2012.45.6.961
  10. Kim, M.S., H. Min, J.G. Kim, N. Koo, J.S. Park, and G.I. Bak. 2014. Effects of various amendments on heavy metal stabilization in acid and alkali soils. Korean J. Environ. Agric. 33(1):1-8. https://doi.org/10.5338/KJEA.2014.33.1.1
  11. Kim, S.C., J.E. Yang, D.K. Kim, Y.W. Cheong, J. Skousen, and Y.S. Jung. 2012b. Screening of extraction methods for Cd and As bioavailability prediction in rhizospheric soil using multivariate analyses. Environ. Earth Sci. 66:327-335. https://doi.org/10.1007/s12665-011-1242-2
  12. Koo, N. 2011. Availability-base assessment of trace elements and arsenic stabilization in mine soils. PhD thesis. Korea University.
  13. Lee, J.H., J.Y. Kim, W.R. Go, E.J. Jeong, K. Anitha, G.B. Jung, D.H. Kim, and W.I. Kim. 2012. Current Research Trends for Heavy Metals of Agricultural Soils and Crop Uptake in Korea. Korea J. Environ. Agric. 31(1):75-95. https://doi.org/10.5338/KJEA.2012.31.1.75
  14. Lee, P.K., M.J. Kang, S.W. Park, and S.J. Youm. 2003. The effects of pH control on the leaching behavior of heavy metals within tailings and contaminated soils: seobo and cheongyang tungsten mine areas. Korean J. Econ. Environ. Geol. 36(6):469-480.
  15. Ministry of Environment (ME). 2012. The Korean standard method of environmental pollutions for soil pollution. Ministry of environment, Korea.
  16. Oh, S.J., S.C. Kim, R.Y. Kim, Y.S. Ok, H.S. Yun, S.M. Oh, J.S. Lee, and J.E. Yang. 2012. Change of bioavailability in heavy metal contaminated soil by chemical amendment. Korean J. Soil Sci. Fert. 45(6):973-982. https://doi.org/10.7745/KJSSF.2012.45.6.973
  17. Ok, Y.S., R.A. Usman, S.S. Lee, A.M. Azeem, B.S. Choi, Y. Hashimoto, and J.E. Yang. 2011. Effects of Rapeseed Residue on Lead and Cadmium Availability and Uptake by Rice Plants in Heavy Metal Contaminated Paddy Soil. Chemosphere. 85:677-682. https://doi.org/10.1016/j.chemosphere.2011.06.073
  18. Park, S.W., J.S. Yang, S.W. Ryu, D.Y. Kim, J.D. Shin, W.I. Kim, J.H. Choi, and S.L. Kim. 2009. Uptake and translocation of heavy metals to rice plant on paddy soils in "Top-rice" cultivation areas. Korean J. Environ. Agic. 28(2):131-138. https://doi.org/10.5338/KJEA.2009.28.2.131
  19. Pueyo, M., J.F. Lopez-Sanchez, and G. Rauret. 2004. Assessment of $CaCl_2,\;NaNO_3\;and\;NH_4NO_3$ extraction procedures for the study of Cd, Cu, Pb and Zn extractability in contaminated soils. Anal. Chim. Acta. 504:217-226. https://doi.org/10.1016/j.aca.2003.10.047
  20. Seo, B.H., G.H. Lim, K.H. Kim, J.E. Kim, J.H. Hur, W.I. Kim, and K.R. Kim. 2013. Comparison of single extractions for evaluation of heavy metal phytoavailability in soil. Korean J. Environ. Agric. 32(3):171-178. https://doi.org/10.5338/KJEA.2013.32.3.171
  21. Song, C.H. 2011. Relationship between heavy metal content according to extraction method and physicochemical soil properties. MS thesis. Korea University.
  22. Tessier, A., P.G. Campbell, and M. Bisson. 1979. Sequential extraction procedures for the specification of particulate trace metals. Anal. Chem. 5:844-855.
  23. Yang, J.E., J.G. Skousen, Y.S. Ok, K.R. Yoo, and H.J. Kim. 2006. Reclamation of abandoned coal mine wastes using lime cake by-products in Korea. Mine Water Environ. 25:227-232. https://doi.org/10.1007/s10230-006-0137-z