Strategy and mechanisms of sulfamethoxazole removal from aqueous systems by single and combined Shewanella oneidensis MR-1 and nanoscale zero-valent iron-enriched biochar

被引:13
作者
Li, Yuanyuan [1 ,2 ]
Zhu, Yuen [1 ,2 ]
Yan, Xiurong [1 ,2 ]
Zhang, Guixiang [3 ]
Yan, Guanyu [1 ,2 ]
Li, Hua [1 ,2 ]
机构
[1] Shanxi Univ, Coll Environm & Resource Sci, Taiyuan 030006, Shanxi, Peoples R China
[2] Shanxi Lab Yellow River, Taiyuan 030006, Shanxi, Peoples R China
[3] Taiyuan Univ Sci & Technol, Sch Environm & Resources, Taiyuan 030024, Shanxi, Peoples R China
关键词
Sulfamethoxazole; Aqueous system; Removal strategy; Nanoscale zero-valent iron-enriched biochar; Dissimilatory iron-reducing bacteria; GROUNDWATER REMEDIATION; WATER; DECHLORINATION; SULFONAMIDES; ADSORPTION; TOXICITY; NZVI; ZVI;
D O I
10.1016/j.scitotenv.2023.163676
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Sulfamethoxazole (SMX, a sulfonamide antibiotic) is ubiquitously present in various aqueous systems, which can accelerate the spread of antibiotic resistance genes, induce genetic mutations, and even disrupt the ecological equilibrium. Considering the potential eco-environmental risk of SMX, this study explored an effective technology using Shewanella oneidensis MR-1 (MR-1) and nanoscale zero-valent iron-enriched biochar (nZVI-HBC) to remove SMX from aqueous systems with different pollution levels (1-30 mg center dot L-1). SMX removal by nZVI-HBC and nZVIHBC + MR-1 (55-100 %) under optimal conditions (iron/HBC ratio of 1:5, 4 g center dot L-1 nZVI-HBC, and 10 % v/v MR-1) was more effective than its removal by MR-1 and biochar (HBC) (8-35 %). This was due to the catalytic degradation of SMX in the nZVI-HBC and nZVI-HBC + MR-1 reaction systems because of accelerated electron transfer during oxidation of nZVI and reduction of Fe(III) to Fe(II). When SMX concentration was lower than 10 mg center dot L-1, nZVIHBC + MR-1 effectively removed SMX (removal rate of approximately 100 %) when compared to nZVI-HBC (removal rate of 56-79 %). In addition to oxidation degradation of SMX by nZVI in the nZVI-HBC + MR-1 reaction system, MR1-driven dissimilatory iron reduction accelerated electron transfer to SMX, thereby enhancing reductive degradation of SMX. However, a considerable decline in SMX removal from the nZVI-HBC + MR-1 system (42 %) was observed when SMX concentrations ranged 15-30 mg center dot L-1, which was due to the toxicity of accumulated degradation products of SMX. A high interaction probability between SMX and nZVI-HBC promoted the catalytic degradation of SMX in the nZVI-HBC reaction system. The results of this study provide promising strategies and insights for enhancing antibiotic removal from aqueous systems with different pollution levels.
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页数:12
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