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Econ. Environ. Geol. 2024; 57(4): 417-429

Published online August 30, 2024

https://doi.org/10.9719/EEG.2024.57.4.417

© THE KOREAN SOCIETY OF ECONOMIC AND ENVIRONMENTAL GEOLOGY

The Effects of Organic, Inorganic, and Microbiological Stabilizers on the Transfer of Arsenic and Heavy Metals to Rice Plant

Hui-Yeon Kim, Ga-Hyun Park, Yejin Choi, Eui-Jeong Hwang, Daeung Yoon*, Jong-Un Lee*

Department of Energy and Resources Engineering, Chonnam National University, Gwangju 61186, Korea

Correspondence to : *duyoon@jnu.ac.kr / jongun@jnu.ac.kr

Received: July 18, 2024; Revised: August 20, 2024; Accepted: August 21, 2024

This is an Open Access article distributed under the terms of the Creative Commons Attribution Non-Commercial License (http://creativecommons.org/licenses/by-nc/3.0) which permits unrestricted non-commercial use, distribution, and reproduction in any medium, provided original work is properly cited.

Abstract

To assess the effectiveness of stabilization techniques on the transfer of As and heavy metals in soil to rice plant, pot experiments were conducted using organic (biochar), inorganic (limestone-steel slag mixture), and microbiological (sulfate-reducing bacteria, SRB) stabilizers. The results showed that microbiological treatments, particularly when SRB and SO42- were co-injected, achieved higher stabilization efficiencies for Pb, Cu, and Cd in soil solution by the end of the experiments (153 days). The transfer of Pb, Zn, Cu, and Cd to the rice stems, leaves, and husks was reduced across all stabilization treatments. Notably, in husks, the stabilization efficiencies of Pb, Zn, Cu, and Cd ranged from 30% to 65% for organic stabilizers and 23% to 69% for inorganic stabilizers, surpassing those achieved with microbiological stabilizers. This study highlighted the potential of SRB as an effective alternative or supplementary stabilizer to conventional options such as limestone, steel slag, and biochar in reducing the transfer of heavy metals to crops in paddy soils.

Keywords heavy metals, rice, stabilization, paddy soil, sulfate-reducing bacteria

유기, 무기 및 미생물학적 안정화제가 비소 및 중금속의 벼 전이에 미치는 영향

김희연 · 박가현 · 최예진 · 황의정 · 윤대웅* · 이종운*

전남대학교 에너지자원공학과

요 약

안정화 공법이 토양 내 As 및 중금속의 작물 전이에 미치는 영향을 평가하기 위해 안정화제를 적용한 오염 토양에 벼를 재배하는 포트 실험을 수행하였다. 안정화제는 유기 안정화제로 바이오차, 무기 안정화제로 석회석·제강슬래그 혼합물, 미생물학적 안정화제로 황산염환원균(SRB)을 사용하였다. 토양수 분석 결과, 실험종료(153일) 시점에 미생물학적 안정화제 조건에서 Pb, Cu, Cd의 높은 안정화 효율을 보였으며, SRB와 SO42-가 함께 주입된 조건에서 더 높은 효율을 나타내었다. 안정화제 투입 조건에서 벼의 줄기, 잎, 왕겨로의 Pb, Zn, Cu, Cd의 전이가 감소하였으며, 특히 왕겨에서 Pb, Zn, Cu, Cd의 안정화 효율은 유기 안정화제가 30~65%, 무기 안정화제가 23~69%로 미생물학적 안정화제보다 높은 안정화 효율을 보였다. 이 연구는 논토양에서 작물로의 중금속 전이를 저감할 때, 널리 사용되는 안정화제인 석회석, 제강슬래그, 바이오차의 대체 또는 보조 안정화제로서 SRB가 효과적으로 적용될 수 있는 가능성을 나타낸다.

주요어 중금속, 벼, 안정화, 논토양, 황산염환원균

Article

Research Paper

Econ. Environ. Geol. 2024; 57(4): 417-429

Published online August 30, 2024 https://doi.org/10.9719/EEG.2024.57.4.417

Copyright © THE KOREAN SOCIETY OF ECONOMIC AND ENVIRONMENTAL GEOLOGY.

The Effects of Organic, Inorganic, and Microbiological Stabilizers on the Transfer of Arsenic and Heavy Metals to Rice Plant

Hui-Yeon Kim, Ga-Hyun Park, Yejin Choi, Eui-Jeong Hwang, Daeung Yoon*, Jong-Un Lee*

Department of Energy and Resources Engineering, Chonnam National University, Gwangju 61186, Korea

Correspondence to:*duyoon@jnu.ac.kr / jongun@jnu.ac.kr

Received: July 18, 2024; Revised: August 20, 2024; Accepted: August 21, 2024

This is an Open Access article distributed under the terms of the Creative Commons Attribution Non-Commercial License (http://creativecommons.org/licenses/by-nc/3.0) which permits unrestricted non-commercial use, distribution, and reproduction in any medium, provided original work is properly cited.

Abstract

To assess the effectiveness of stabilization techniques on the transfer of As and heavy metals in soil to rice plant, pot experiments were conducted using organic (biochar), inorganic (limestone-steel slag mixture), and microbiological (sulfate-reducing bacteria, SRB) stabilizers. The results showed that microbiological treatments, particularly when SRB and SO42- were co-injected, achieved higher stabilization efficiencies for Pb, Cu, and Cd in soil solution by the end of the experiments (153 days). The transfer of Pb, Zn, Cu, and Cd to the rice stems, leaves, and husks was reduced across all stabilization treatments. Notably, in husks, the stabilization efficiencies of Pb, Zn, Cu, and Cd ranged from 30% to 65% for organic stabilizers and 23% to 69% for inorganic stabilizers, surpassing those achieved with microbiological stabilizers. This study highlighted the potential of SRB as an effective alternative or supplementary stabilizer to conventional options such as limestone, steel slag, and biochar in reducing the transfer of heavy metals to crops in paddy soils.

Keywords heavy metals, rice, stabilization, paddy soil, sulfate-reducing bacteria

유기, 무기 및 미생물학적 안정화제가 비소 및 중금속의 벼 전이에 미치는 영향

김희연 · 박가현 · 최예진 · 황의정 · 윤대웅* · 이종운*

전남대학교 에너지자원공학과

Received: July 18, 2024; Revised: August 20, 2024; Accepted: August 21, 2024

요 약

안정화 공법이 토양 내 As 및 중금속의 작물 전이에 미치는 영향을 평가하기 위해 안정화제를 적용한 오염 토양에 벼를 재배하는 포트 실험을 수행하였다. 안정화제는 유기 안정화제로 바이오차, 무기 안정화제로 석회석·제강슬래그 혼합물, 미생물학적 안정화제로 황산염환원균(SRB)을 사용하였다. 토양수 분석 결과, 실험종료(153일) 시점에 미생물학적 안정화제 조건에서 Pb, Cu, Cd의 높은 안정화 효율을 보였으며, SRB와 SO42-가 함께 주입된 조건에서 더 높은 효율을 나타내었다. 안정화제 투입 조건에서 벼의 줄기, 잎, 왕겨로의 Pb, Zn, Cu, Cd의 전이가 감소하였으며, 특히 왕겨에서 Pb, Zn, Cu, Cd의 안정화 효율은 유기 안정화제가 30~65%, 무기 안정화제가 23~69%로 미생물학적 안정화제보다 높은 안정화 효율을 보였다. 이 연구는 논토양에서 작물로의 중금속 전이를 저감할 때, 널리 사용되는 안정화제인 석회석, 제강슬래그, 바이오차의 대체 또는 보조 안정화제로서 SRB가 효과적으로 적용될 수 있는 가능성을 나타낸다.

주요어 중금속, 벼, 안정화, 논토양, 황산염환원균

    Fig 1.

    Figure 1.Pot experiments cultivating rice with organic, inorganic, and microbiological stabilizers after 141 days.
    Economic and Environmental Geology 2024; 57: 417-429https://doi.org/10.9719/EEG.2024.57.4.417

    Fig 2.

    Figure 2.Variations in (i) Fe and (ii) Mn concentrations in soil solutions over time for (a) organic, (b) inorganic, and (c) microbiological stabilizers. Each error bar represents the standard deviations of replicates.
    Economic and Environmental Geology 2024; 57: 417-429https://doi.org/10.9719/EEG.2024.57.4.417

    Fig 3.

    Figure 3.Variations in (i) As, (ii) Pb, (iii) Zn, (iv) Cu, and (v) Cd concentrations in soil solutions over time for (a) organic, (b) inorganic, and (c) microbiological stabilizers. Each error bar represents the standard deviation of replicates.
    Economic and Environmental Geology 2024; 57: 417-429https://doi.org/10.9719/EEG.2024.57.4.417

    Fig 4.

    Figure 4.Length of (a) roots and (b) above ground parts of rice samples with different stabilization treatments. Each error bar represents the standard deviation of replicates.
    Economic and Environmental Geology 2024; 57: 417-429https://doi.org/10.9719/EEG.2024.57.4.417

    Fig 5.

    Figure 5.Effects of organic, inorganic, and microbiological stabilizers on the transfer of As, Pb, Zn, Cu, and Cd to (a) stems, (b) leaves, and (c) husks of rice after 153 days of planting.
    Economic and Environmental Geology 2024; 57: 417-429https://doi.org/10.9719/EEG.2024.57.4.417

    Fig 6.

    Figure 6.Biological absorption coefficient (BAC) of (a) As, (b) Pb, (c) Zn, (d) Cu, and (e) Cd in rice stems, leaves, and husks with different stabilization treatments.
    Economic and Environmental Geology 2024; 57: 417-429https://doi.org/10.9719/EEG.2024.57.4.417

    Table 1 . Chemical properties of limestone and steel slag used in this study.

    StabilizersConcentrations (%)
    CaOSiO2Al2O3MgOFe2O3K2OSO3Na2OTiO2SrOP2O5PbORb2O
    Limestone76.90.2-0.4-----0.02---
    Steel slag37.530.46.14.53.71.40.90.40.40.140.090.020.01

    KSEEG
    Feb 28, 2025 Vol.58 No.1, pp. 1~97

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