Adsorption behaviour and mechanisms of cadmium and nickel on rice straw biochars in single- and binary-metal systems

Adsorption mechanisms and competition between Cd2+ and Ni2+ for adsorption by rice straw biochars prepared at 400 °C (RB400) and 700 °C (RB700) were investigated in this study. Based on the Langmuir model, the maximum adsorption capacities (mg g−1) of Cd2+ and Ni2+ on RB400 and RB700 were in the ord...

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Published in	Chemosphere (Oxford) Vol. 218; pp. 308 - 318
Main Authors	Deng, Yiyi, Huang, Shuang, Laird, David A., Wang, Xiugui, Meng, Zhuowen
Format	Journal Article
Language	English
Published	England Elsevier Ltd 01.03.2019
Subjects	Adsorption binding sites Biochar Cadmium Cadmium - chemistry Cadmium - isolation & purification cation exchange Charcoal - chemistry Competition Mechanism metal ions Nickel Nickel - chemistry Nickel - isolation & purification Oryza - chemistry Plant Stems - chemistry rice straw soil sorption isotherms Water Pollutants, Chemical - chemistry Water Pollutants, Chemical - isolation & purification Competition Cadmium Nickel Biochar Mechanism
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Abstract	Adsorption mechanisms and competition between Cd2+ and Ni2+ for adsorption by rice straw biochars prepared at 400 °C (RB400) and 700 °C (RB700) were investigated in this study. Based on the Langmuir model, the maximum adsorption capacities (mg g−1) of Cd2+ and Ni2+ on RB400 and RB700 were in the order of Cd2+ (37.24 and 65.40) > Ni2+ (27.31 and 54.60) in the single-metal adsorption isotherms and Ni2+ (25.20 and 32.28) > Cd2+ (24.22 and 26.78) in the binary-metal adsorption isotherms. Cd2+ competed with Ni2+ for binding sites at initial metal concentrations >10 mg L−1 for RB400 and > 20 mg L−1 for RB700. The adsorption sites for Cd2+ and Ni2+ on the biochars largely overlapped, and the binding of Cd2+ and Ni2+ to these sites was affected by the occupation sequence of these metals. For Cd2+ and Ni2+ adsorption in the binary system, cation exchange and precipitation were the dominant adsorption mechanisms on RB400 and RB700, respectively, accounting for approximately 36% and 60% of the adsorption capacity. Competition decreased the contribution of cation exchange but increased that of precipitation and other potential mechanisms. Results from this study suggest that types and concentrations of metal ions should be taken into account when removing metal contaminants from water or soil using biochars. [Display omitted] •The adsorption sites for Cd2+ and Ni2+ on the biochars largely overlapped.•Rice straw biochars exhibited adsorption preferences for Ni2+ over Cd2+ when coexisted.•Competition occurred once the concentrations of Cd2+ and Ni2+ exceeded the threshold values.•Competition between Cd2+ and Ni2+ decreased the adsorption amounts but increased the mobility.•Competition between Cd2+ and Ni2+ decreased the contribution of cation exchange mechanism.
AbstractList	Adsorption mechanisms and competition between Cd2+ and Ni2+ for adsorption by rice straw biochars prepared at 400 °C (RB400) and 700 °C (RB700) were investigated in this study. Based on the Langmuir model, the maximum adsorption capacities (mg g−1) of Cd2+ and Ni2+ on RB400 and RB700 were in the order of Cd2+ (37.24 and 65.40) > Ni2+ (27.31 and 54.60) in the single-metal adsorption isotherms and Ni2+ (25.20 and 32.28) > Cd2+ (24.22 and 26.78) in the binary-metal adsorption isotherms. Cd2+ competed with Ni2+ for binding sites at initial metal concentrations >10 mg L−1 for RB400 and > 20 mg L−1 for RB700. The adsorption sites for Cd2+ and Ni2+ on the biochars largely overlapped, and the binding of Cd2+ and Ni2+ to these sites was affected by the occupation sequence of these metals. For Cd2+ and Ni2+ adsorption in the binary system, cation exchange and precipitation were the dominant adsorption mechanisms on RB400 and RB700, respectively, accounting for approximately 36% and 60% of the adsorption capacity. Competition decreased the contribution of cation exchange but increased that of precipitation and other potential mechanisms. Results from this study suggest that types and concentrations of metal ions should be taken into account when removing metal contaminants from water or soil using biochars. [Display omitted] •The adsorption sites for Cd2+ and Ni2+ on the biochars largely overlapped.•Rice straw biochars exhibited adsorption preferences for Ni2+ over Cd2+ when coexisted.•Competition occurred once the concentrations of Cd2+ and Ni2+ exceeded the threshold values.•Competition between Cd2+ and Ni2+ decreased the adsorption amounts but increased the mobility.•Competition between Cd2+ and Ni2+ decreased the contribution of cation exchange mechanism. Adsorption mechanisms and competition between Cd2+ and Ni2+ for adsorption by rice straw biochars prepared at 400 °C (RB400) and 700 °C (RB700) were investigated in this study. Based on the Langmuir model, the maximum adsorption capacities (mg g-1) of Cd2+ and Ni2+ on RB400 and RB700 were in the order of Cd2+ (37.24 and 65.40) > Ni2+ (27.31 and 54.60) in the single-metal adsorption isotherms and Ni2+ (25.20 and 32.28) > Cd2+ (24.22 and 26.78) in the binary-metal adsorption isotherms. Cd2+ competed with Ni2+ for binding sites at initial metal concentrations >10 mg L-1 for RB400 and > 20 mg L-1 for RB700. The adsorption sites for Cd2+ and Ni2+ on the biochars largely overlapped, and the binding of Cd2+ and Ni2+ to these sites was affected by the occupation sequence of these metals. For Cd2+ and Ni2+ adsorption in the binary system, cation exchange and precipitation were the dominant adsorption mechanisms on RB400 and RB700, respectively, accounting for approximately 36% and 60% of the adsorption capacity. Competition decreased the contribution of cation exchange but increased that of precipitation and other potential mechanisms. Results from this study suggest that types and concentrations of metal ions should be taken into account when removing metal contaminants from water or soil using biochars.Adsorption mechanisms and competition between Cd2+ and Ni2+ for adsorption by rice straw biochars prepared at 400 °C (RB400) and 700 °C (RB700) were investigated in this study. Based on the Langmuir model, the maximum adsorption capacities (mg g-1) of Cd2+ and Ni2+ on RB400 and RB700 were in the order of Cd2+ (37.24 and 65.40) > Ni2+ (27.31 and 54.60) in the single-metal adsorption isotherms and Ni2+ (25.20 and 32.28) > Cd2+ (24.22 and 26.78) in the binary-metal adsorption isotherms. Cd2+ competed with Ni2+ for binding sites at initial metal concentrations >10 mg L-1 for RB400 and > 20 mg L-1 for RB700. The adsorption sites for Cd2+ and Ni2+ on the biochars largely overlapped, and the binding of Cd2+ and Ni2+ to these sites was affected by the occupation sequence of these metals. For Cd2+ and Ni2+ adsorption in the binary system, cation exchange and precipitation were the dominant adsorption mechanisms on RB400 and RB700, respectively, accounting for approximately 36% and 60% of the adsorption capacity. Competition decreased the contribution of cation exchange but increased that of precipitation and other potential mechanisms. Results from this study suggest that types and concentrations of metal ions should be taken into account when removing metal contaminants from water or soil using biochars. Adsorption mechanisms and competition between Cd²⁺ and Ni²⁺ for adsorption by rice straw biochars prepared at 400 °C (RB400) and 700 °C (RB700) were investigated in this study. Based on the Langmuir model, the maximum adsorption capacities (mg g⁻¹) of Cd²⁺ and Ni²⁺ on RB400 and RB700 were in the order of Cd²⁺ (37.24 and 65.40) > Ni²⁺ (27.31 and 54.60) in the single-metal adsorption isotherms and Ni²⁺ (25.20 and 32.28) > Cd²⁺ (24.22 and 26.78) in the binary-metal adsorption isotherms. Cd²⁺ competed with Ni²⁺ for binding sites at initial metal concentrations >10 mg L⁻¹ for RB400 and > 20 mg L⁻¹ for RB700. The adsorption sites for Cd²⁺ and Ni²⁺ on the biochars largely overlapped, and the binding of Cd²⁺ and Ni²⁺ to these sites was affected by the occupation sequence of these metals. For Cd²⁺ and Ni²⁺ adsorption in the binary system, cation exchange and precipitation were the dominant adsorption mechanisms on RB400 and RB700, respectively, accounting for approximately 36% and 60% of the adsorption capacity. Competition decreased the contribution of cation exchange but increased that of precipitation and other potential mechanisms. Results from this study suggest that types and concentrations of metal ions should be taken into account when removing metal contaminants from water or soil using biochars. Adsorption mechanisms and competition between Cd and Ni for adsorption by rice straw biochars prepared at 400 °C (RB400) and 700 °C (RB700) were investigated in this study. Based on the Langmuir model, the maximum adsorption capacities (mg g ) of Cd and Ni on RB400 and RB700 were in the order of Cd (37.24 and 65.40) > Ni (27.31 and 54.60) in the single-metal adsorption isotherms and Ni (25.20 and 32.28) > Cd (24.22 and 26.78) in the binary-metal adsorption isotherms. Cd competed with Ni for binding sites at initial metal concentrations >10 mg L for RB400 and > 20 mg L for RB700. The adsorption sites for Cd and Ni on the biochars largely overlapped, and the binding of Cd and Ni to these sites was affected by the occupation sequence of these metals. For Cd and Ni adsorption in the binary system, cation exchange and precipitation were the dominant adsorption mechanisms on RB400 and RB700, respectively, accounting for approximately 36% and 60% of the adsorption capacity. Competition decreased the contribution of cation exchange but increased that of precipitation and other potential mechanisms. Results from this study suggest that types and concentrations of metal ions should be taken into account when removing metal contaminants from water or soil using biochars.
Author	Deng, Yiyi Laird, David A. Meng, Zhuowen Wang, Xiugui Huang, Shuang
Author_xml	– sequence: 1 givenname: Yiyi orcidid: 0000-0001-5395-4842 surname: Deng fullname: Deng, Yiyi email: dyy7076@whu.edu.cn organization: State Key Laboratory of Water Resources and Hydropower Engineering Sciences, Wuhan University, Wuhan, 430072, China – sequence: 2 givenname: Shuang orcidid: 0000-0002-0071-6055 surname: Huang fullname: Huang, Shuang email: hsh5527@whu.edu.cn organization: State Key Laboratory of Water Resources and Hydropower Engineering Sciences, Wuhan University, Wuhan, 430072, China – sequence: 3 givenname: David A. surname: Laird fullname: Laird, David A. organization: Department of Agronomy, Iowa State University, Ames, IA, 50011, USA – sequence: 4 givenname: Xiugui surname: Wang fullname: Wang, Xiugui organization: State Key Laboratory of Water Resources and Hydropower Engineering Sciences, Wuhan University, Wuhan, 430072, China – sequence: 5 givenname: Zhuowen surname: Meng fullname: Meng, Zhuowen organization: State Key Laboratory of Water Resources and Hydropower Engineering Sciences, Wuhan University, Wuhan, 430072, China
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Keywords	Competition Cadmium Nickel Biochar Mechanism
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Snippet	Adsorption mechanisms and competition between Cd2+ and Ni2+ for adsorption by rice straw biochars prepared at 400 °C (RB400) and 700 °C (RB700) were... Adsorption mechanisms and competition between Cd and Ni for adsorption by rice straw biochars prepared at 400 °C (RB400) and 700 °C (RB700) were investigated... Adsorption mechanisms and competition between Cd²⁺ and Ni²⁺ for adsorption by rice straw biochars prepared at 400 °C (RB400) and 700 °C (RB700) were...
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SubjectTerms	Adsorption binding sites Biochar Cadmium Cadmium - chemistry Cadmium - isolation & purification cation exchange Charcoal - chemistry Competition Mechanism metal ions Nickel Nickel - chemistry Nickel - isolation & purification Oryza - chemistry Plant Stems - chemistry rice straw soil sorption isotherms Water Pollutants, Chemical - chemistry Water Pollutants, Chemical - isolation & purification
Title	Adsorption behaviour and mechanisms of cadmium and nickel on rice straw biochars in single- and binary-metal systems
URI	https://dx.doi.org/10.1016/j.chemosphere.2018.11.081 https://www.ncbi.nlm.nih.gov/pubmed/30476762 https://www.proquest.com/docview/2138647331 https://www.proquest.com/docview/2189522007
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