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Fate of bacterial community, antibiotic resistance genes and gentamicin residues in soil after three-year amendment using gentamicin fermentation waste

文献类型: 外文期刊

作者: Liu, Yuanwang 1 ; Cheng, Dengmiao 3 ; Xue, Jianming 4 ; Feng, Yao 2 ; Wakelin, Steve A. 5 ; Weaver, Louise 6 ; Shehata, Ebrahim 2 ; Li, Zhaojun 2 ;

作者机构: 1.Yanshan Univ, Sch Environm & Chem Engn, Hebei Key Lab Appl Chem, Hebei Key Lab Heavy Met Deep Remediat Water & Res, Qinhuangdao 066004, Hebei, Peoples R China

2.Chinese Acad Agr Sci, China New Zealand Joint Lab Soil Mol Ecol, Key Lab Plant Nutr & Fertilizer, Inst Agr Resources & Reg Planning,Minist Agr, Beijing 100081, Peoples R China

3.Dongguan Univ Technol, Res Ctr Ecoenvironm Engn, Dongguan 523808, Peoples R China

4.Nanjing Forestry Univ, Coll Biol & Environm, Nanjing 210037, Peoples R China

5.Scion, Private Bag, Christchurch 29237, New Zealand

6.Inst Environm Sci & Res Ltd, Christchurch 8041, New Zealand

7.Shandong Acad Agr Sci, Inst Anim Sci & Vet Med, Jinan 250100, Peoples R China

关键词: Gentamicin; Antibiotic resistance gene; Gentamicin fermentation wastes; Bacterial composition; Mobile genetic element

期刊名称:CHEMOSPHERE ( 影响因子:7.086; 五年影响因子:6.956 )

ISSN: 0045-6535

年卷期: 2022 年 291 卷

页码:

收录情况: SCI

摘要: Over a three-year field trial, the impacts of composted and raw gentamicin fermentation waste (GFW) appli-cation to land on residual soil gentamicin levels, physicochemical properties, bacterial community composition, and antibiotic resistance genes (ARGs) were assessed. In the saline-alkali soil tested, GFW application decreased electrical conductivity (EC) and pH. Importantly, there was no measurable long-term accumulation of gentamicin as a result of GFW addition. Changes in the abundance of Bacillus was primarily associated with degradation of gentamicin in soil, whereas wider (i.e. more general) shifts in bacterial communities over the treatments was linked to alteration of soil physicochemical properties, particularly pH, total nitrogen, dissolved organic carbon, EC, NO3--N and NH4+-N. Compared with other treatments, soils receiving composted GFW harbored more types of ARGs and significantly higher (P < 0.05) abundances of mobile genes elements (MGEs) (especially IncQ andInt1) and aminoglycoside ARGs (especially aminoglycoside phosphotransferases genes, APH). Finally, the abundances of ARGs in soils receiving raw and composted GFW were 59.60% and 50.26% higher than that in soils only receiving chemical fertilizer, respectively. Specifically, the abundances of APH, especially strB, were significantly higher than other kinds of ARGs (P < 0.05). The results of linear regression and partial least squares path model showed that MGEs, including plasmids, integrons, and transposons, along with soil properties (EC and NH4+-N) were the main factors associated with change in ARGs. Furthermore, different MGEs were involved in different transfer mechanisms of specific ARGs. Our findings demonstrated the potential risks of using raw and composted GFW as fertilizer, and suggest potential solutions to this problem.

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