Investigating the binding properties between antimony(V) and dissolved organic matter (DOM) under different pH conditions during the soil sorption process using fluorescence and FTIR spectroscopy

Antimony (Sb) is listed as a priority pollutant by European Union and U.S. Environmental Protection Agency. However, reports on its environmental behavior, particularly the sorption process in soil are still limited. In this paper, Sb(V) was selected as the sorbate and the black soil as the sorbent....

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Veröffentlicht in:Ecotoxicology and environmental safety 2019-10, Vol.181, p.34-42
Hauptverfasser: Fan, Yurui, Zheng, Chunli, Huo, Aidi, Wang, Qiaorui, Shen, Zhenxing, Xue, Zhiwei, He, Chi
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container_title Ecotoxicology and environmental safety
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creator Fan, Yurui
Zheng, Chunli
Huo, Aidi
Wang, Qiaorui
Shen, Zhenxing
Xue, Zhiwei
He, Chi
description Antimony (Sb) is listed as a priority pollutant by European Union and U.S. Environmental Protection Agency. However, reports on its environmental behavior, particularly the sorption process in soil are still limited. In this paper, Sb(V) was selected as the sorbate and the black soil as the sorbent. The initial sorption rate (k2qe,cal2) was calculated to be 0.1254 mg g−1∙min−1 and the maximum sorption amount (qm) 57.33 mg g−1. Once the dissolved organic matter (DOM) was removed from the soil, the values of k2qe,cal2 and qm went down to 0.1066 mg g−1∙min−1 and 19.01 mg g−1, respectively. These results suggested that the existence of DOM significantly influenced the mass transfer rate and sorption amount of Sb(V) in soil. In order to find out the reason why DOM exerted such an influence, the binding interaction mechanism between Sb(V) and DOM was investigated under different pH values. The protein-like and humic-like substances as well as the functional groups of CO, phenol hydroxyl, C–O, C–H, C-X and sulfur/phosphorus contributed to the formation of DOM-Sb(V)-complexes under pH of 7.0, in which the humic-like substance and the functional groups containing oxygen showed higher binding affinity for Sb(V) than protein-like substance and other functional groups, respectively. The protein-like substance and some functional groups disappeared under pH of 4.0 and 10.0. Alkaline condition resulted in a bigger impact on reducing the number of functional groups than acid condition. It can be concluded that the strongest binding interaction occurred at pH of 7.0 then followed by 4.0 and 10.0. This paper might be helpful to further studying the environmental behavior of Sb(V) in soil. [Display omitted] •The existence of DOM in soil enhanced the sorption extent of Sb(V).•Fluorescence proved that protein- and humic-like substances in DOM bound with Sb(V).•FTIR indicated that DOM carried various functional groups which bound with Sb(V).•The strongest binding interaction between Sb(V) and DOM occurred at pH of 7.0
doi_str_mv 10.1016/j.ecoenv.2019.05.076
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However, reports on its environmental behavior, particularly the sorption process in soil are still limited. In this paper, Sb(V) was selected as the sorbate and the black soil as the sorbent. The initial sorption rate (k2qe,cal2) was calculated to be 0.1254 mg g−1∙min−1 and the maximum sorption amount (qm) 57.33 mg g−1. Once the dissolved organic matter (DOM) was removed from the soil, the values of k2qe,cal2 and qm went down to 0.1066 mg g−1∙min−1 and 19.01 mg g−1, respectively. These results suggested that the existence of DOM significantly influenced the mass transfer rate and sorption amount of Sb(V) in soil. In order to find out the reason why DOM exerted such an influence, the binding interaction mechanism between Sb(V) and DOM was investigated under different pH values. The protein-like and humic-like substances as well as the functional groups of CO, phenol hydroxyl, C–O, C–H, C-X and sulfur/phosphorus contributed to the formation of DOM-Sb(V)-complexes under pH of 7.0, in which the humic-like substance and the functional groups containing oxygen showed higher binding affinity for Sb(V) than protein-like substance and other functional groups, respectively. The protein-like substance and some functional groups disappeared under pH of 4.0 and 10.0. Alkaline condition resulted in a bigger impact on reducing the number of functional groups than acid condition. It can be concluded that the strongest binding interaction occurred at pH of 7.0 then followed by 4.0 and 10.0. This paper might be helpful to further studying the environmental behavior of Sb(V) in soil. [Display omitted] •The existence of DOM in soil enhanced the sorption extent of Sb(V).•Fluorescence proved that protein- and humic-like substances in DOM bound with Sb(V).•FTIR indicated that DOM carried various functional groups which bound with Sb(V).•The strongest binding interaction between Sb(V) and DOM occurred at pH of 7.0</description><identifier>ISSN: 0147-6513</identifier><identifier>EISSN: 1090-2414</identifier><identifier>DOI: 10.1016/j.ecoenv.2019.05.076</identifier><identifier>PMID: 31158721</identifier><language>eng</language><publisher>Netherlands: Elsevier Inc</publisher><subject>Antimony(V) ; Binding interaction ; Dissolved organic matter ; Sorption</subject><ispartof>Ecotoxicology and environmental safety, 2019-10, Vol.181, p.34-42</ispartof><rights>2019 Elsevier Inc.</rights><rights>Copyright © 2019 Elsevier Inc. 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However, reports on its environmental behavior, particularly the sorption process in soil are still limited. In this paper, Sb(V) was selected as the sorbate and the black soil as the sorbent. The initial sorption rate (k2qe,cal2) was calculated to be 0.1254 mg g−1∙min−1 and the maximum sorption amount (qm) 57.33 mg g−1. Once the dissolved organic matter (DOM) was removed from the soil, the values of k2qe,cal2 and qm went down to 0.1066 mg g−1∙min−1 and 19.01 mg g−1, respectively. These results suggested that the existence of DOM significantly influenced the mass transfer rate and sorption amount of Sb(V) in soil. In order to find out the reason why DOM exerted such an influence, the binding interaction mechanism between Sb(V) and DOM was investigated under different pH values. The protein-like and humic-like substances as well as the functional groups of CO, phenol hydroxyl, C–O, C–H, C-X and sulfur/phosphorus contributed to the formation of DOM-Sb(V)-complexes under pH of 7.0, in which the humic-like substance and the functional groups containing oxygen showed higher binding affinity for Sb(V) than protein-like substance and other functional groups, respectively. The protein-like substance and some functional groups disappeared under pH of 4.0 and 10.0. Alkaline condition resulted in a bigger impact on reducing the number of functional groups than acid condition. It can be concluded that the strongest binding interaction occurred at pH of 7.0 then followed by 4.0 and 10.0. This paper might be helpful to further studying the environmental behavior of Sb(V) in soil. [Display omitted] •The existence of DOM in soil enhanced the sorption extent of Sb(V).•Fluorescence proved that protein- and humic-like substances in DOM bound with Sb(V).•FTIR indicated that DOM carried various functional groups which bound with Sb(V).•The strongest binding interaction between Sb(V) and DOM occurred at pH of 7.0</description><subject>Antimony(V)</subject><subject>Binding interaction</subject><subject>Dissolved organic matter</subject><subject>Sorption</subject><issn>0147-6513</issn><issn>1090-2414</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2019</creationdate><recordtype>article</recordtype><recordid>eNp9UcFu1DAQtRCILoU_QMjH7SHBTuLEviChltKViiqhwtVK7PHiVdYOtrNov68_VodtOXKxR5o38968h9B7SkpKaPtxV4Ly4A5lRagoCStJ175AK0oEKaqGNi_RitCmK1pG6zP0JsYdIaQmjL1GZzWljHcVXaGHjTtATHbbJ-u2OP0CPFinl3oKfoKQLEQ8QPoD4HDvkt17d1z_vMi1xtrG6McDaOzDtndW4X2fEgS8vrr7doFnp3OtrTEQwCU83WDl8_JkvYtYz-GZMno75idMS2chVhAjnuPSN-PsA0QFTsFf0uv7zXccJ1Ap-Kj8dHyLXpl-jPDu6T9HP66_3F_eFLd3XzeXn28LVQuRit50AEQISgauOac1U0rzhpuWa0YaI5hgQ6e77JEybcdEYzoBnHSc8bZSUJ-j9WlvFvh7zq7Jvc26xrF34Ocoq6pmpO2y-RnanKAqa4wBjJyC3ffhKCmRS3xyJ0_xySU-SZjM8eWxD08M87AH_W_oOa8M-HQCQL7zYCHIqOzijLYhGyK1t_9neAQNgLIS</recordid><startdate>20191015</startdate><enddate>20191015</enddate><creator>Fan, Yurui</creator><creator>Zheng, Chunli</creator><creator>Huo, Aidi</creator><creator>Wang, Qiaorui</creator><creator>Shen, Zhenxing</creator><creator>Xue, Zhiwei</creator><creator>He, Chi</creator><general>Elsevier Inc</general><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7X8</scope></search><sort><creationdate>20191015</creationdate><title>Investigating the binding properties between antimony(V) and dissolved organic matter (DOM) under different pH conditions during the soil sorption process using fluorescence and FTIR spectroscopy</title><author>Fan, Yurui ; Zheng, Chunli ; Huo, Aidi ; Wang, Qiaorui ; Shen, Zhenxing ; Xue, Zhiwei ; He, Chi</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c399t-af7ee09910b8d88135ccd848f68d504f9595b7d7305cf67594f79e80785862ce3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2019</creationdate><topic>Antimony(V)</topic><topic>Binding interaction</topic><topic>Dissolved organic matter</topic><topic>Sorption</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Fan, Yurui</creatorcontrib><creatorcontrib>Zheng, Chunli</creatorcontrib><creatorcontrib>Huo, Aidi</creatorcontrib><creatorcontrib>Wang, Qiaorui</creatorcontrib><creatorcontrib>Shen, Zhenxing</creatorcontrib><creatorcontrib>Xue, Zhiwei</creatorcontrib><creatorcontrib>He, Chi</creatorcontrib><collection>PubMed</collection><collection>CrossRef</collection><collection>MEDLINE - Academic</collection><jtitle>Ecotoxicology and environmental safety</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Fan, Yurui</au><au>Zheng, Chunli</au><au>Huo, Aidi</au><au>Wang, Qiaorui</au><au>Shen, Zhenxing</au><au>Xue, Zhiwei</au><au>He, Chi</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Investigating the binding properties between antimony(V) and dissolved organic matter (DOM) under different pH conditions during the soil sorption process using fluorescence and FTIR spectroscopy</atitle><jtitle>Ecotoxicology and environmental safety</jtitle><addtitle>Ecotoxicol Environ Saf</addtitle><date>2019-10-15</date><risdate>2019</risdate><volume>181</volume><spage>34</spage><epage>42</epage><pages>34-42</pages><issn>0147-6513</issn><eissn>1090-2414</eissn><abstract>Antimony (Sb) is listed as a priority pollutant by European Union and U.S. Environmental Protection Agency. However, reports on its environmental behavior, particularly the sorption process in soil are still limited. In this paper, Sb(V) was selected as the sorbate and the black soil as the sorbent. The initial sorption rate (k2qe,cal2) was calculated to be 0.1254 mg g−1∙min−1 and the maximum sorption amount (qm) 57.33 mg g−1. Once the dissolved organic matter (DOM) was removed from the soil, the values of k2qe,cal2 and qm went down to 0.1066 mg g−1∙min−1 and 19.01 mg g−1, respectively. These results suggested that the existence of DOM significantly influenced the mass transfer rate and sorption amount of Sb(V) in soil. In order to find out the reason why DOM exerted such an influence, the binding interaction mechanism between Sb(V) and DOM was investigated under different pH values. The protein-like and humic-like substances as well as the functional groups of CO, phenol hydroxyl, C–O, C–H, C-X and sulfur/phosphorus contributed to the formation of DOM-Sb(V)-complexes under pH of 7.0, in which the humic-like substance and the functional groups containing oxygen showed higher binding affinity for Sb(V) than protein-like substance and other functional groups, respectively. The protein-like substance and some functional groups disappeared under pH of 4.0 and 10.0. Alkaline condition resulted in a bigger impact on reducing the number of functional groups than acid condition. It can be concluded that the strongest binding interaction occurred at pH of 7.0 then followed by 4.0 and 10.0. This paper might be helpful to further studying the environmental behavior of Sb(V) in soil. [Display omitted] •The existence of DOM in soil enhanced the sorption extent of Sb(V).•Fluorescence proved that protein- and humic-like substances in DOM bound with Sb(V).•FTIR indicated that DOM carried various functional groups which bound with Sb(V).•The strongest binding interaction between Sb(V) and DOM occurred at pH of 7.0</abstract><cop>Netherlands</cop><pub>Elsevier Inc</pub><pmid>31158721</pmid><doi>10.1016/j.ecoenv.2019.05.076</doi><tpages>9</tpages></addata></record>
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subjects Antimony(V)
Binding interaction
Dissolved organic matter
Sorption
title Investigating the binding properties between antimony(V) and dissolved organic matter (DOM) under different pH conditions during the soil sorption process using fluorescence and FTIR spectroscopy
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