Hostname: page-component-586b7cd67f-2brh9 Total loading time: 0 Render date: 2024-11-25T18:13:59.677Z Has data issue: false hasContentIssue false
  • English
  • Français

Long-term effects of biochar on rice production and stabilisation of cadmium and arsenic levels in contaminated paddy soils

Published online by Cambridge University Press:  29 November 2018

Peng CHEN ,
Hong-Yan WANG ,
Rui-Lun ZHENG ,
Bo ZHANG  and
Guo-Xin SUN
Peng CHEN
Affiliation:
State Key Laboratory of Urban and Regional Ecology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China. Email: [email protected] University of Chinese Academy of Sciences, Beijing 100049, China.
Hong-Yan WANG
Affiliation:
State Key Laboratory of Urban and Regional Ecology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China. Email: [email protected]
Rui-Lun ZHENG
Affiliation:
Research & Development Center for Grasses and Environment, Beijing Academy of Agriculture and Forestry Sciences, Beijing 100097, China.
Bo ZHANG
Affiliation:
Institute of Biological and Environmental Sciences, University of Aberdeen, Aberdeen AB24 3UU, UK.
Guo-Xin SUN*
Affiliation:
State Key Laboratory of Urban and Regional Ecology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China. Email: [email protected]
*
*Corresponding author
Get access Rights & Permissions [Opens in a new window]

Abstract

Heavy metal contamination in the paddy soils of China is a serious concern because of its health risk through transfer in food chains. A field experiment was conducted in 2014–2015 to investigate the long-term effects of different biochar amendments on cadmium (Cd) and arsenic (As) immobilisation in a contaminated paddy field in southern China. Two types of biochar, a rice-straw-derived biochar (RB) and a coconut-by-product-derived biochar (CB), were amended separately to determine their impacts on rice yield and their efficacy in reducing Cd and As in rice. The two-year field experiment showed that biochar amendments significantly improved the rice yields and that CB is superior to RB, especially in the first growth season. Using a large amount of biochar amendment (22.5tha–1) significantly increased soil pH and total organic carbon, and concomitantly decreased the Cd content in rice grains over the four growth seasons, regardless of biochar type and application rate. Arsenic levels in rice were similar to the control, and results from this study suggest that there was a sustainable effect of biochar on Cd sequestration in soil and reduction of Cd accumulation in rice for at least two years. Biochar amendment in soil could be considered as a sustainable, reliable and cost-effective option to remediate heavy metal contamination in paddy fields for long periods.

Keywords

dissolved organic matterimmobilisationpH valueremediationtotal organic carbon
Type
Articles
Information
Earth and Environmental Science Transactions of The Royal Society of Edinburgh , Volume 109 , Issue 3-4: Earth Surface Processes and Environmental Sustainability in China , September 2018 , pp. 415 - 420
Copyright
Copyright © The Royal Society of Edinburgh 2018 

Access options

Get access to the full version of this content by using one of the access options below. (Log in options will check for institutional or personal access. Content may require purchase if you do not have access.)

References

5. References

Abumaizar, R. J. & Smith, E. H. 1999. Heavy metal contaminants removal by soil washing. Journal of Hazardous Materials 70, 71–86.Google Scholar
Antoniadis, V. & Alloway, B. J. 2002. The role of dissolved organic carbon in the mobility of Cd, Ni and Zn in sewage sludge-amended soils. Environmental Pollution 117, 515–521.Google Scholar
Beesley, L. & Marmiroli, M. 2011. The immobilisation and retention of soluble arsenic, cadmium and zinc by biochar. Environmental Pollution 159, 474–480.Google Scholar
Bian, R. J., Chen, D., Liu, X. Y., Cui, L. Q., Li, L. Q., Pan, G. X., Xie, D., Zheng, J. W., Zhang, X. H., Zheng, J. F. & Chang, A. 2013. Biochar soil amendment as a solution to prevent Cd-tainted rice from China: results from a cross-site field experiment. Ecological Engineering 58, 378–383.Google Scholar
Bian, R. J., Joseph, S., Cui, L. Q., Pan, G. X., Li, L. Q., Liu, X. Y., Zhang, A. F., Rutlidge, H., Wong, S. W., Chia, C., Marjo, C., Gong, B., Munroe, P. & Donne, S. 2014. A three-year experiment confirms continuous immobilization of cadmium and lead in contaminated paddy field with biochar amendment. Journal of Hazardous Materials 272, 121–128.Google Scholar
Chen, Z., Zhu, Y. G., Liu, W. J. & Meharg, A. A. 2005. Direct evidence showing the effect of root surface iron plaque on arsenite and arsenate uptake into rice (Oryza sativa) roots. New Phytologist 165, 91–97.Google Scholar
Chung, N. T., Jintrawet, A. & Promburom, P. 2015. Impacts of seasonal climate variability on rice production in the central highlands of Vietnam. Agriculture and Agricultural Science Procedia 5, 83–88.Google Scholar
Cornu, J. Y., Schneider, A., Jezequel, K. & Denaix, L. 2011. Modelling the complexation of Cd in soil solution at different temperatures using the UV-absorbance of dissolved organic matter. Geoderma 162, 65–70.Google Scholar
Cui, L. Q., Li, L. Q., Zhang, A. F., Pan, G. X., Bao, D. D. & Chang, A. 2011. Biochar amendment greatly reduces rice Cd uptake in a contaminated paddy soil: A two-year field experiment. BioResources 6, 2605–2618.Google Scholar
GB/T 12496.7-1999. Test methods of wooden activated carbon – determination of pH. Issued by The State Bureau of Quality and Technical Supervision, Beijing, China.Google Scholar
GB15618-1995. Environmental Quality Standard for Soils. Issued by State Environmental Protection Administration of China, 1995. Beijing: Standards Press of China. [In Chinese.]Google Scholar
GB2762-2012. Maximum Levels of Contaminants in Food. Chinese Food Standards Agency. Issued by Ministry of Health of the People's Republic of China.Google Scholar
Houben, D., Evrard, L. & Sonnet, P. 2013. Mobility, bioavailability and pH-dependent leaching of cadmium, zinc and lead in a contaminated soil amended with biochar. Chemosphere 92, 1450–1457.Google Scholar
Hu, Y., Li, J. H., Zhu, Y. G., Huang, Y. Z., Hu, H. Q. & Christie, P. 2005. Sequestration of As by iron plaque on the roots of three rice (Oryza sativa L.) cultivars in a low-P soil with or without P fertilizer. Environmental Geochemistry and Health 27, 169–176.10.1007/s10653-005-0132-5Google Scholar
Huang, H., Zhu, Y. G., Chen, Z., Yin, X. X. & Sun, G. X. 2012. Arsenic mobilization and speciation during iron plaque decomposition in a paddy soil. Journal of Soils and Sediments 12, 402–410.Google Scholar
Huang, M., Yang, L., Qin, H. D., Jiang, L. G. & Zou, Y. B. 2013. Quantifying the effect of biochar amendment on soil quality and crop productivity in Chinese rice paddies. Field Crops Research 154, 172–177.Google Scholar
Jain, A. & Loeppert, R. H. 2000. Effect of competing anions on the adsorption of arsenate and arsenite by ferrihydrite. Journal of Environmental Quality 29, 1422–1430.Google Scholar
Khan, S., Reid, B. J., Li, G. & Zhu, Y. G. 2014. Application of biochar to soil reduces cancer risk via rice consumption: A case study in Miaoqian village, Longyan, China. Environment International 68, 154–161.Google Scholar
Kumar, S., Sangwan, P., Dhankhar, R., Mor, V. & Bidra, S. 2013. Utilization of rice husk and their ash: a review. Research Journal of Chemical and Environmental Sciences 1, 126–129.Google Scholar
Li, H. Y., Ye, X. X., Geng, Z. G., Zhou, H. J., Guo, X. S., Zhang, Y. X., Zhao, H. J. & Wang, G. Z. 2016. The influence of biochar type on long-term stabilization for Cd and Cu in contaminated paddy soil. Journal of Hazardous Materials 304, 40–48.Google Scholar
Li, T. Q., Liang, C. F., Han, X. & Yang, X. E. 2013. Mobilization of cadmium by dissolved organic matter in the rhizosphere of hyperaccumulator Sedum alfredii. Chemosphere 91, 970–976.Google Scholar
Liu, W. J., Zhu, Y. G. & Smith, F. A. 2004. Do phosphorus nutrition and iron plaque alter arsenate (As) uptake by rice seedlings in hydroponic culture? New Phytologist 162, 481–488.Google Scholar
Makino, T., Kamiya, T., Takano, H., Itou, T., Sekiya, N., Sasaki, K., Maejima, Y. & Sugahara, K. 2007. Remediation of cadmium-contaminated paddy soils by washing with calcium chloride: verification of on-site washing. Environmental Pollution 147, 112–119.Google Scholar
Sun, G. X., Van deWiele, T., Alava, P., Tack, F., Du Laing, G. 2012. Arsenic in cooked rice: Effect of chemical, enzymatic and microbial processes on bioaccessibility and speciation in the human gastrointestinal tract. Environmental Pollution 162, 241–246.Google Scholar
Utomo, W. H., Kusuma, Z. & Nugroho, W. H. 2011. Soil fertility status, nutrient uptake, and maize (Zea mays L.) yield following biochar and cattle manure application on sandy soils of Lombok, Indonesia. Journal of Tropical Agriculture 49, 47–52.Google Scholar
Waltham, C. A. & Eick, M. J. 2002. Kinetics of arsenic adsorption on goethite in the presence of sorbed silicic acid. Soil Science Society of America Journal 66, 818–825.Google Scholar
Wang, H. Y., Wen, S. L., Chen, P., Zhang, L., Cen, K. & Sun, G. X. 2016. Mitigation of cadmium and arsenic in rice grain by applying different silicon fertilizers in contaminated fields. Environmental Science and Pollution Research 23, 3781–3788.Google Scholar
Wang, X. J., Chen, X. P., Yang, J., Wang, Z. S. & Sun, G. X. 2009. Effect of microbial mediated iron plaque reduction on arsenic mobility in paddy soil. Journal of Environmental Science 21, 1562–1568.Google Scholar
Williams, P. N., Lei, M., Sun, G. X., Huang, Q., Lu, Y., Deacon, C., Meharg, A. A., Zhu, Y. G. 2009. Occurrence and partitioning of cadmium, arsenic and lead in mine impacted paddy rice: Hunan, China. Environmental Sci & Technology 43(3), 637–642.Google Scholar
Wilson, S. C., Lockwood, P. V., Ashley, P. M. & Tighe, M. 2010. The chemistry and behaviour of antimony in the soil environment with comparisons to arsenic: a critical review. Environmental Pollution 158, 1169–1181.Google Scholar
Yuan, J. H., Xu, R. K. & Zhang, H. 2011. The forms of alkalis in the biochar produced from crop residues at different temperatures. Bioresource Technology 102, 3488–3497.Google Scholar
Zhang, A. F., Bian, R. J., Pan, G. X., Cui, L. Q., Hussain, Q., Li, L. Q., Zheng, J. W., Zheng, J. F., Zhang, X. H., Han, X. J. & Yu, X. Y. 2012. Effects of biochar amendment on soil quality, crop yield and greenhouse gas emission in a Chinese rice paddy: A field study of 2 consecutive rice growing cycles. Field Crops Research 127, 153–160.Google Scholar
Zheng, R. L., Cai, C., Liang, J. H., Huang, Q., Chen, Z., Huang, Y. Z., Arp, H. P. H. & Sun, G. X. 2012. The effects of biochars from rice residue on the formation of iron plaque and the accumulation of Cd, Zn, Pb, As in rice (Oryza sativa L.) seedlings. Chemosphere 89, 856–862.Google Scholar
Zheng, R. L., Chen, Z., Cai, C., Wang, X. H., Huang, Y. Z., Xiao, B. & Sun, G. X. 2013. Effect of biochars from rice husk, bran and straw on heavy metal uptake by pot-grown wheat seedling in a historically contaminated soil. BioResources 8, 5965–5982.Google Scholar
Zheng, R. L., Chen, Z., Cai, C., Tie, B. Q., Liu, X. L., Reid, B. J., Huang, Q., Lei, M., Sun, G. X. & Baltrėnaitė, E. 2015. Mitigating heavy metal accumulation into rice (Oryza sativa L.) using biochar amendment – a field experiment in Hunan, China. Environmental Science and Pollution Research 22, 11097–108.Google Scholar
Zhu, Y. G., Duan, G. L., Chen, B. D., Peng, X. H., Chen, Z. & Sun, G. X. 2014. Mineral weathering and element cycling in soil-microorganism-plant system. Science China Earth Sciences 57, 888–896.Google Scholar