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Efficiency of Fe-zeolite and Fe-bentonite on co-stabilization of As, Cd and Pb in Contaminated Soil

Received: 13 September 2018     Accepted: 15 January 2019     Published: 28 May 2020
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Abstract

Lead (Pb), Cadmium (Cd) and Arsenic (As) have been known as a malicious environment and their toxic effects for plants, animals and humans has been demonstrated. This metals in soil have a different behaviours. The normal concentrations of Cd, As and Pb in agricultural soil were 1.1, 20 and 67 mg.kg-1 respectively. In situ immobilization of Lead and Cadmium (by zeolite and bentonite) and Arsenic (by iron) in soil is well recognized. However, studies on soils that are simultaneously contaminated with lead, cadmium and arsenic are fewer, and assessment of the sorbents effectiveness on co-stabilization of As, Cd and Pb is also necessary. In this study, local bentonite and zeolite were converted to Fe-zeolite and Fe-bentonite. A Pb-, Cd- and As-contaminated soil has been treated with modified bentonite and zeolite separately in 1 and 6 wt% rate. After one month of incubation in at 80% of field capacity moisture, Sunflower (Helianthus annuus. L) plant was transplanted into each pot. The result showed that Fe-zeolite and Fe-bentonite decreased concentration of Pb and Cd extractable with DTPA-TEA; however, Fe-bentonite in the soil reduced water-soluble arsenate, but Fe-zeolite increased it. Finally application of Fe-bentonite can be an effective approach to co-stabilize Pb, Cd and As, in contaminated soils.

Published in International Journal of Environmental Monitoring and Analysis (Volume 8, Issue 3)
DOI 10.11648/j.ijema.20200803.11
Page(s) 45-49
Creative Commons

This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited.

Copyright

Copyright © The Author(s), 2020. Published by Science Publishing Group

Keywords

Fe-Bentonite, Fe-Zeolite, Lead, Cadmium, Arsenic

References
[1] Sparks D L (2003) Environmental Soil Chemistry. Academic Press, San Diego, CA.
[2] Kabata-Pendias A, Pendias H (1984) Trace Elements in Soils and Plants. CRC Press, Boca Raton, FL, pp. 143–157.
[3] Yanshan C, Du X, Weng L, Willem H, Riemsdijk V (2010) Assessment of In Situ Immobilization of Lead (Pb) and Arsenic (As) in Contaminated Soils with Phosphate and Iron: Solubility and Bioaccessibility. J Water Air Soil Pollut. 213: 95–104.
[4] Kim J Y, Davis A (2003) Stabilization of available arsenic in highly contaminated mine tailings using iron. Environ Sci Tec. 37: 189 195.
[5] Miretzky P, Fernandez-Cirelli A (2008) Phosphates for Pb immobilization in soils: A review. Environ Chem Lett. 6: 121–133.
[6] Yang L, Donahoe R J, Redwine J C (2007) In situ chemical fixation of arsenic contaminated soils: An experimental study. Sci. Total Environ. 387: 28–41.
[7] Neupane G, R Donahoe J (2013) Calcium–phosphate treatment of contaminated soil for arsenic immobilization, Appl. Geochem. 28: 145–154.
[8] Kumpiene J, Fitts JP, Mench M (2012) Arsenic fractionation in mine spoils 10 years after aided phytostabilization. Environ Pollut 166: 82–88.
[9] Vodyanitskii Yu, N (2010) The role of iron in the fixation of heavy metals and metalloids in Soils: a review of publications. Eurasian Soil Science 43: 519–532.
[10] Alvarez-Ayuso E, Otones V, Murciego A, Garcia-Sanchez A (2013) Evaluation of different amendments to stabilize antimony in mining polluted soils, Chemosphere 90: 2233–2239.
[11] Hamidpour M, Afyuni M, Kalbasi M, Khoshgoftarmanes A H, Inglezakis V J (2010) Mobility and plant-availability of Cd (II) and Pb (II) adsorbed on zeolite and bentonite. Appl Clay Sci. 48: 342-348.
[12] Mahar A, Wang P, Ronghua L I, Zhang Z (2015) "Immobilization of Lead and Cadmium in Contaminated Soil Using Amendments: A Review." Pedosphere 25: 555-568.
[13] Keller C, Marchetti M, Rossi L, Lugon-Moulin N (2005) Reduction of cadmium availability to tobacco (Nicotiana tabacum) plants using soil amendments in low cadmium contaminated agricultural soils: a pot experiment. Plant Soil 27: 669–84.
[14] Sun Y, Li Y, Liang X, Wang L (2015) In situ stabilization remediation of cadmium (Cd) and lead (Pb) co-contaminated paddy soil using bentonite. Appl Clay Sci.105–106: 200-206.
[15] Kim K R, Lee B T, Kim K W (2011) Arsenic stabilization in mine tailings using nano-sized magnetite and zero valent iron with the enhancement of mobility by surface coating. J. Geochemical Exploration. 113: 124-129.
[16] Martin T A, Ruby M V (2003) In situ remediation of arsenic in contaminated soils. Remediation J. 14: 21–32.
[17] Sarkar B, Naidu R, Rahman M M, Megharaj M, Xi Y (2012) Organoclays reduce arsenic bioavailability and bioaccessibility in contaminated soils, Journal of Soils and Sediments. 12: 704-712.
[18] Malekian R, Abedi-Koupai J, Eslamian S S (2011) Influences of clinoptilolite and surfactant-modified clinoptilolite zeolite on nitrate leaching and plant growth, Journal of Hazardous Materials. 185: 970-976.
[19] Sarkar, B., Xi, Y., Megharaj, M., Krishnamurti, G. S., Rajarathnam, D., Naidu, R. (2010) Remediation of hexavalent chromium through adsorption by bentonite based Arquad® 2HT-75 organoclays, Journal of hazardous materials. 183, 87-97.
[20] Sarkar B, Xi Y, Megharaj M, Krishnamurti G S, Naidu R (2010) Synthesis and characterisation of novel organopalygorskites for removal of p-nitrophenol from aqueous solution: Isothermal studies, Journal of colloid and interface science. 350: 295-304.
[21] Sarkar B, Megharaj M, Xi Y, Naidu R (2011) Structural characterisation of Arquad 2HT-75 organobentonites: Surface charge characteristics and environmental application, Journal of hazardous materials. 195: 155-161.
[22] Sarkar B, Megharaj M, Xi Y, Naidu R (2011) Orange II adsorption on palygorskites modified with alkyl trimethylammonium and dialkyl dimethylammonium bromidean isothermal and kinetic study, Applied Clay Science. 51: 370-374.
[23] Sarkar B, Megharaj M, Xi Y, Naidu R (2012) Surface charge characteristics of organo-palygorskites and adsorption of p-nitrophenol in flow-through reactor system. Chemical Engineering Journal. 185: 35-43.
[24] Westerman R L (1990) Soil testing and plant analysis. Soil Science Society of America, Inc.
[25] Macedo-Miranda M, Olguín M (2007) Arsenic sorption by modified clinoptilolite–heulandite rich tuffs. J. Incl. Phenom. Macro. 59: 131-142.
[26] Karak T, AbollinO, Bhattacharyya P, Das K K, Paul R K (2011) Fractionation and speciation of arsenic in three tea gardens soil profiles and distribution of As in different parts of tea plant (Camellia sinensis L.), Chemosphere 85: 948–960.
[27] Lindsay W L, Norvell W A (1978) Development of DTPA soil test for zinc, iron manganese, and copper, Soil. Sci. Soc. Am. J. 42: 421–428.
[28] Harborne J B (1998) Phytochemical methods A Guide to modern techniques of plant analysis. Springer.
[29] Usman A R A, Kuzyakov Y, Lorenz K, Stahr K (2006) Remediation of a soil contaminated with heavy metals by immobilizing compounds. J. Plant Nutr Soil Sci. 169: 205–212.
[30] Mench M, Vangroensveld J, Lepp N M, Edwards R (1998) Physico-chemical aspects and efficiency of trace element immobilization by soil amendments, in Vangroensveld, J., Cummingham, S. D. (eds.): Metal-contaminated soils. Springer, Berlin, pp. 151–182.
[31] Robins R G (1981) The solubility of metal arsenates. Metall Trans. 12 : 103-109.
[32] Sherman D M, Randall S R (2003) Surface complexation of arsenic (V) to iron (III) (hydr)oxides: structural mechanism from ab initio molecular geometries and EXAFS spectroscopy. Geochim Cosmochim Ac. 67-22: 4223–4230.
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  • APA Style

    Sajad Shahmoradi, Majid Afyuni Mohmmad, A. Hajabbasi. (2020). Efficiency of Fe-zeolite and Fe-bentonite on co-stabilization of As, Cd and Pb in Contaminated Soil. International Journal of Environmental Monitoring and Analysis, 8(3), 45-49. https://doi.org/10.11648/j.ijema.20200803.11

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    ACS Style

    Sajad Shahmoradi; Majid Afyuni Mohmmad; A. Hajabbasi. Efficiency of Fe-zeolite and Fe-bentonite on co-stabilization of As, Cd and Pb in Contaminated Soil. Int. J. Environ. Monit. Anal. 2020, 8(3), 45-49. doi: 10.11648/j.ijema.20200803.11

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    AMA Style

    Sajad Shahmoradi, Majid Afyuni Mohmmad, A. Hajabbasi. Efficiency of Fe-zeolite and Fe-bentonite on co-stabilization of As, Cd and Pb in Contaminated Soil. Int J Environ Monit Anal. 2020;8(3):45-49. doi: 10.11648/j.ijema.20200803.11

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  • @article{10.11648/j.ijema.20200803.11,
      author = {Sajad Shahmoradi and Majid Afyuni Mohmmad and A. Hajabbasi},
      title = {Efficiency of Fe-zeolite and Fe-bentonite on co-stabilization of As, Cd and Pb in Contaminated Soil},
      journal = {International Journal of Environmental Monitoring and Analysis},
      volume = {8},
      number = {3},
      pages = {45-49},
      doi = {10.11648/j.ijema.20200803.11},
      url = {https://doi.org/10.11648/j.ijema.20200803.11},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.ijema.20200803.11},
      abstract = {Lead (Pb), Cadmium (Cd) and Arsenic (As) have been known as a malicious environment and their toxic effects for plants, animals and humans has been demonstrated. This metals in soil have a different behaviours. The normal concentrations of Cd, As and Pb in agricultural soil were 1.1, 20 and 67 mg.kg-1 respectively. In situ immobilization of Lead and Cadmium (by zeolite and bentonite) and Arsenic (by iron) in soil is well recognized. However, studies on soils that are simultaneously contaminated with lead, cadmium and arsenic are fewer, and assessment of the sorbents effectiveness on co-stabilization of As, Cd and Pb is also necessary. In this study, local bentonite and zeolite were converted to Fe-zeolite and Fe-bentonite. A Pb-, Cd- and As-contaminated soil has been treated with modified bentonite and zeolite separately in 1 and 6 wt% rate. After one month of incubation in at 80% of field capacity moisture, Sunflower (Helianthus annuus. L) plant was transplanted into each pot. The result showed that Fe-zeolite and Fe-bentonite decreased concentration of Pb and Cd extractable with DTPA-TEA; however, Fe-bentonite in the soil reduced water-soluble arsenate, but Fe-zeolite increased it. Finally application of Fe-bentonite can be an effective approach to co-stabilize Pb, Cd and As, in contaminated soils.},
     year = {2020}
    }
    

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  • TY  - JOUR
    T1  - Efficiency of Fe-zeolite and Fe-bentonite on co-stabilization of As, Cd and Pb in Contaminated Soil
    AU  - Sajad Shahmoradi
    AU  - Majid Afyuni Mohmmad
    AU  - A. Hajabbasi
    Y1  - 2020/05/28
    PY  - 2020
    N1  - https://doi.org/10.11648/j.ijema.20200803.11
    DO  - 10.11648/j.ijema.20200803.11
    T2  - International Journal of Environmental Monitoring and Analysis
    JF  - International Journal of Environmental Monitoring and Analysis
    JO  - International Journal of Environmental Monitoring and Analysis
    SP  - 45
    EP  - 49
    PB  - Science Publishing Group
    SN  - 2328-7667
    UR  - https://doi.org/10.11648/j.ijema.20200803.11
    AB  - Lead (Pb), Cadmium (Cd) and Arsenic (As) have been known as a malicious environment and their toxic effects for plants, animals and humans has been demonstrated. This metals in soil have a different behaviours. The normal concentrations of Cd, As and Pb in agricultural soil were 1.1, 20 and 67 mg.kg-1 respectively. In situ immobilization of Lead and Cadmium (by zeolite and bentonite) and Arsenic (by iron) in soil is well recognized. However, studies on soils that are simultaneously contaminated with lead, cadmium and arsenic are fewer, and assessment of the sorbents effectiveness on co-stabilization of As, Cd and Pb is also necessary. In this study, local bentonite and zeolite were converted to Fe-zeolite and Fe-bentonite. A Pb-, Cd- and As-contaminated soil has been treated with modified bentonite and zeolite separately in 1 and 6 wt% rate. After one month of incubation in at 80% of field capacity moisture, Sunflower (Helianthus annuus. L) plant was transplanted into each pot. The result showed that Fe-zeolite and Fe-bentonite decreased concentration of Pb and Cd extractable with DTPA-TEA; however, Fe-bentonite in the soil reduced water-soluble arsenate, but Fe-zeolite increased it. Finally application of Fe-bentonite can be an effective approach to co-stabilize Pb, Cd and As, in contaminated soils.
    VL  - 8
    IS  - 3
    ER  - 

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Author Information
  • Soil Science Department, Isfahan University of Technology, Esfahan City, Iran

  • Soil Science Department, Isfahan University of Technology, Esfahan City, Iran

  • Soil Science Department, Isfahan University of Technology, Esfahan City, Iran

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