Suppr超能文献

三价铜高效降解五环及六环磺胺类抗生素:性能与机制研究。

Insight into efficient degradation of pentacyclic and hexacyclic sulfonamide antibiotics by synthetic trivalent copper: Performance and mechanism.

机构信息

National and Local Joint Engineering Research Center for Ecological Treatment Technology of Urban Water Pollution, College of Life and Environmental Science, Wenzhou University, Wenzhou, 325035, China.

National and Local Joint Engineering Research Center for Ecological Treatment Technology of Urban Water Pollution, College of Life and Environmental Science, Wenzhou University, Wenzhou, 325035, China.

出版信息

J Environ Manage. 2024 Nov;370:122798. doi: 10.1016/j.jenvman.2024.122798. Epub 2024 Oct 2.

Abstract

High valent metal species, including Mn(III), Fe(IV) and Cu(III), have been identified as key intermediates in the degradation of pollutants in many advanced oxidation processes. However, unlike Mn(III) and Fe(IV), the current exploration of the reaction activity and selective oxidation mechanism of Cu(III) towards pollutants with different structures is still quite limited. Herein, the copper(III) periodate was synthesized to investigate the reactivity towards six sulfonamide antibiotics (SAs) including typical two pentacyclic structures (sulfamethoxazole (SMX) and sulfathiazole (STZ)) and four hexacyclic structures (sulfadiazine (SDZ), sulfamerazine (SMR), sulfamonomethoxine (SMM) and sulfapyridine (SPD)). The results indicated that all SAs almost completely removed by Cu(III) system after 10 min with the molar ratio of approximately 3:1 (Cu(III):SAs) and Cu(III) direct oxidation played the most important role. SAs with 6-ring substituents were more readily degraded by Cu(III) than SAs with 5-ring substituents, and the presence of electron-rich group such as -CH and -S in ring substituent increased the reactivity towards Cu(III). The introduction of coexisting anions (Cl, SO and HCO) hardly affected the degradation of SAs by Cu(III) oxidation, while the addition of HA to some extent inhibited SAs degradation. The solution pH greatly affected the degradation of SAs by Cu(III) and the removal efficiencies of SAs roughly followed the rule of neutral > acidic > alkaline. The degradation mechanism of SAs with 5-ring and 6-ring substituents in Cu(III) system mainly included amino nitration, self-coupling, hydroxylation, S-N cleavage in SAs with 5-ring substituents and SO extrusion in SAs with 6-ring substituents. Although the real water matrix inhibited the degradation of SAs to varying degrees, Cu(III) still played a satisfactory performance on SAs degradation especially for electron-rich structure.

摘要

高价金属物种,包括 Mn(III)、Fe(IV) 和 Cu(III),已被确定为许多高级氧化过程中污染物降解的关键中间体。然而,与 Mn(III) 和 Fe(IV)不同,目前对 Cu(III)对不同结构污染物的反应活性和选择性氧化机制的探索仍然相当有限。在此,合成了高碘酸铜来研究其对六种磺胺类抗生素 (SAs)的反应活性,包括典型的两种五环结构 (磺胺甲恶唑 (SMX) 和磺胺噻唑 (STZ)) 和四种六环结构 (磺胺嘧啶 (SDZ)、磺胺二甲嘧啶 (SMR)、磺胺甲噁唑 (SMM) 和磺胺吡啶 (SPD))。结果表明,在 10 分钟内,Cu(III)体系几乎可以完全去除所有的 SAs,Cu(III):SAs 的摩尔比约为 3:1,Cu(III)的直接氧化起着最重要的作用。具有 6 元环取代基的 SAs比具有 5 元环取代基的 SAs更容易被 Cu(III)降解,并且在环取代基中存在富电子基团,如-CH 和 -S,会增加其对 Cu(III)的反应性。共存阴离子 (Cl、SO 和 HCO) 的引入几乎不会影响 Cu(III)氧化对 SAs 的降解,而 HA 的添加在一定程度上抑制了 SAs 的降解。溶液 pH 值对 Cu(III)降解 SAs 的影响很大,SAs 的去除效率大致遵循中性>酸性>碱性的规律。Cu(III)体系中 5 元和 6 元环取代基的 SAs 的降解机制主要包括氨基硝化、自偶联、羟化、5 元环取代基的 S-N 裂解和 6 元环取代基的 SO 挤出。尽管实际水基质会在不同程度上抑制 SAs 的降解,但 Cu(III)对 SAs 的降解仍表现出令人满意的性能,尤其是对富电子结构。

文献检索

告别复杂PubMed语法,用中文像聊天一样搜索,搜遍4000万医学文献。AI智能推荐,让科研检索更轻松。

立即免费搜索

文件翻译

保留排版,准确专业,支持PDF/Word/PPT等文件格式,支持 12+语言互译。

免费翻译文档

深度研究

AI帮你快速写综述,25分钟生成高质量综述,智能提取关键信息,辅助科研写作。

立即免费体验