共 65 条
Inhibitory effects of rice residues amendment on Cd phytoavailability: A matter of Cd-organic matter interactions?
被引:41
作者:
Tang, Wenli
[1
]
Zhong, Huan
[1
,2
]
Xiao, Lin
[1
]
Tan, Qiaoguo
[3
]
Zeng, Qilong
[4
,5
]
Wei, Zhongbo
[1
]
机构:
[1] Nanjing Univ, Sch Environm, State Key Lab Pollut Control & Resource Reuse, Nanjing, Jiangsu, Peoples R China
[2] Trent Univ, Environm & Life Sci Program EnLS, Peterborough, ON, Canada
[3] Xiamen Univ, Coll Environm & Ecol, Key Lab Coastal & Wetland Ecosyst, Minist Educ, Xiamen, Fujian, Peoples R China
[4] Inst Bot, Nanjing, Jiangsu, Peoples R China
[5] Chinese Acad Sci, Nanjing, Jiangsu, Peoples R China
来源:
基金:
中国国家自然科学基金;
关键词:
Organic matter;
Cadmium;
Soil;
Bioavailability;
Straw return;
ORYZA-SATIVA L;
CONTAMINATED SOIL;
HEAVY-METALS;
WHEAT-STRAW;
PADDY SOIL;
CADMIUM;
COPPER;
CU;
MANAGEMENT;
ZN;
D O I:
10.1016/j.chemosphere.2017.07.152
中图分类号:
X [环境科学、安全科学];
学科分类号:
08 ;
0830 ;
摘要:
Incorporating crop residues into soils, a most common way of organic input into farmland soils, is being encouraged in many parts of the world, while its potential impacts on Cd phytoavailability are not well understood. Here, a Cd-contaminated soil was amended with rice residues (RR, i.e., straw + root mixture) or not (Control) and incubated for 81 days under laboratory-controlled conditions. During the incubation, key soil parameters (e.g., dissolved organic carbon and pH), Cd geochemical fractionation (by BCR sequential extraction), and CaCl2 extracted Cd in soils (by 0.01 M CaCl2 extraction) were quantified to explain the effects of RR amendment on Cd phytoavailability (assessed by 7 day-cultivation of rice seedling in soils). Besides, hydroponic experiments were designed to explore the effects of D-RR-OM (dissolved-RR-organic matter) on the uptake of Cd by rice seedlings (quantified by uptake constant rate, k(u), using stable isotope tracing technique). Our results demonstrated that RR amendment reduced Cd phytoavailability by 17-92% compared with Control during incubation, which might be explained by the interactions between Cd and RR-OM (RR-organic matter) in soil or porewater: (1) Cd immobilization due to its association with solid-RR-OM in soils, (2) Cd mobilization by D-RR-OM, and (3) Cd complexation with D-RR-OM in porewater, and thus reduced k(u) of Cd. Our results suggested that dynamics of RR-OM (e.g., dissolution, decomposition and transformation) in soils, and thus interactions between Cd and solid/dissolved-RR-OM may control Cd phytoavailability under RR amendment. Information gained in this study would further our understanding about Cd phytoavailability in farming soils. (C) 2017 Elsevier Ltd. All rights reserved.
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页码:227 / 234
页数:8
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