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Sulfadiazine dissipation as a function of soil bacterial diversity

机译:磺胺嗪散热作为土壤细菌多样性的函数

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Antibiotic residues in the environment are concerning since results in dispersion of resistance genes. Their degradation is often closely related to microbial metabolism. However, the impacts of soil bacterial community on sulfadiazine (SDZ) dissipation remains unclear, mainly in tropical soils. Our main goals were to evaluate effects of long-term swine manure application on soil bacterial structure as well as effects of soil microbial diversity depletion on SDZ dissipation, using "extinction dilution approach" and C-14-SDZ. Manure application affected several soil attributes, such as pH, organic carbon (OC), and macronutrient contents as well as bacterial community structure and diversity. Even minor bacterial diversity depletion impacted SDZ mineralization and non-extractible residue (NER) formation rates, but NER recovered along 42 d likely due to soil diversity recovery. However, this period may be enough to spread resistance genes into the environment. Surprisingly, the non-manured natural soil (NS-S1) showed faster SDZ dissipation rate (DT90 = 2.0 versus 21 d) and had a great number of bacterial families involved in major SDZ dissipation pathways (mineralization and mainly NER), such as Isosphaeraceae, Ktedonobacteraceae, Acidobacteriaceae_(Subgroup_1), Micromonosporaceae, and Sphingobacteriaceae. This result is unique and contrasts our hypothesis that long-term manured soils would present adaptive advantages and, consequently, have higher SDZ dissipation rates. The literature suggests instantaneous chemical degradation of SDZ in acidic soils responsible to the fast formation of NER. Our results show that if chemical degradation happens, it is soon followed by microbial metabolism (biodegradation) performed by a pool of bacteria and the newly formed metabolites should favors NER formation since SDZ presented low sorption. It also showed that SDZ mineralization is a low redundancy function. (C) 2020 Elsevier Ltd. All rights reserved.
机译:环境中的抗生素残留是关于抗性基因分散的结果。它们的降解通常与微生物代谢密切相关。然而,土壤细菌群落对磺胺嗪(SDZ)耗散的影响仍不清楚,主要是在热带土壤中。我们的主要目标是评估长期猪粪施肥对土壤细菌结构的影响以及土壤微生物多样性消耗对SDZ耗散的影响,采用“消光稀释方法”和C-14-SDZ。粪便应用影响了几种土壤属性,例如pH,有机碳(OC)和Macronutrient含量以及细菌群落结构和多样性。甚至轻微的细菌多样性耗竭均受到SDZ矿化和不可萃取的残余物(NER)形成速率,但是沿42d恢复,可能由于土壤多样性恢复而恢复。然而,该时期可能足以将抗性基因传播到环境中。令人惊讶的是,未调味的天然土壤(NS-S1)显示出更快的SDZ耗散率(DT90 = 2.0与21d),并且具有大量参与主要SDZ耗散途径(矿化和主要是NER)的细菌系列,例如磷酸盐,ktedonobacteraceae,acidobacteriaceae_(亚类_1),microomonosporaceae和鞘癌肌肌。这一结果是独特的,并对比我们的假设使得长期调味的土壤将呈现适应性的优势,因此具有更高的SDZ耗散率。该文献表明SDZ在酸性土壤中瞬时化学降解,其酸性污垢负责Ner快速形成。我们的研究结果表明,如果发生化学降解,则很快就是通过细菌池进行的微生物代谢(生物降解),并且新形成的代谢物应该有利于SDZ呈现低吸附剂。它还表明,SDZ矿化是一个低冗余函数。 (c)2020 elestvier有限公司保留所有权利。

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