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Co-planting can phytoextract similar amounts of cadmium and zinc to mono-cropping from contaminated soils
Authors:Cheng-ai Jiang  Qi-Tang Wu  Thibault Sterckeman  Christophe Schwartz  Catherine Sirguey  Stéphanie Ouvrard  Jérôme Perriguey  Jean-Louis Morel
Institution:1. College of Natural Resources and Environment, Key Laboratory of Ecological Agriculture and Rural Environment of Ministry of Agriculture and Guangdong Province, South China Agricultural University, 510642 Guangzhou, China;2. Laboratoire Sols et Environnement, Nancy Université – INRA, 54505 Vandoeuvre-Les-Nancy, France;1. School of Energy and Environmental Engineering, University of Science and Technology Beijing, Beijing 100083, China;2. Beijing Key Laboratory on Resource-oriented Treatment of Industrial Pollutants, Beijing 100083, China;1. Department of Ecology, College of Natural Resources and Environment, South China Agricultural University, Wushan Road, Tianhe District, Guangzhou, 510642, People’s Republic of China;2. Guangdong Provincial Key Laboratory of Eco-Circular Agriculture, Guangzhou, 510642, People’s Republic of China;3. Guangdong Engineering Research Center for Modern Eco-agriculture and Circular Agriculture, Guangzhou 510642, People’s Republic of China;4. Guangdong Laboratory for Lingnan Modern Agriculture, Guangzhou, 510642, People’s Republic of China;5. USDA Forest Service, Center for Bottomland Hardwoods Research, 775 Stone Blvd., Thompson Hall, Room 309, Mississippi State, MS 39762, United States
Abstract:Co-planting crops normally decreases the main crop yield due to the reduced soil surface area occupied by the main crop. However, in our previous experiments, co-planting Sedum alfredii, a shade-requiring, Cd and Zn-hyperaccumulating plant, with corn increased the biomass and metal phytoextraction of S. alfredii. This experiment was conducted to verify if co-planting another hyperaccumulator, Thlaspi caerulescens, with ryegrass (Lolium perenne) in a pot-trial could obtain a similar result. The soil was separated by two permeable nets with a 2 mm interface soil layer to obtain a shared rhizosphere zone. Soluble metal concentrations in the soil in different rooting zones were measured using 0.01 mol L?1 CaCl2 extraction. The results showed that the growth of T. caerulescens was significantly promoted by co-planting, with a growth increase of about 2-fold compared with monoculture growth. The total uptake of Cd and Zn by T. caerulescens was not decreased by co-planting, and resulted in similar phytoextraction rates for Cd (about 26.6% of the soil total Cd) and Zn (about 2.4% of the soil total Zn) when compared with monoculture, though the T. caerulescens population was decreased by 50% because of co-planting. Analysis of soil samples showed that T. caerulescens substantially reduced the concentrations of 0.01 mol L?1 CaCl2 extractable Cd and Zn throughout the soil, even in the interface area and the ryegrass rooting area. The ryegrass roots did not mobilize more metals for the co-planted T. caerulescens. Based on these results, existing grass on contaminated land could be partly left while planting metal hyperaccumulators for phytoremediation in order to reduce runoff from the contaminated soil. However a field scale trial would be required for these results to be verified.
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