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一种用于识别环境中氟喹诺酮类抗生素(FQs)残留的快速检测技术。

A prompt technique to identify fluoroquinolone antibiotics (FQs) residue in the environments.

作者信息

Niloy Nahin Mostofa, Parvin Fahmida, Tareq Shafi M

机构信息

Hydrobiogeochemistry and Pollution Control Laboratory, Department of Environmental Sciences, Jahangirnagar University, Dhaka 1342, Bangladesh.

Centre for Coastal Biogeochemistry, School of Environment, Science and Engineering, Southern Cross University, Lismore, New South Wales, Australia.

出版信息

MethodsX. 2025 Mar 26;14:103287. doi: 10.1016/j.mex.2025.103287. eCollection 2025 Jun.

DOI:10.1016/j.mex.2025.103287
PMID:40236802
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC11999577/
Abstract

The widely used fluoroquinolone (FQ) antibiotics have become emerging contaminants due to their unconstrained usage. A prompt, straightforward, précised, and advanced technique named fluorescence spectroscopy was applied to characterize and semi-quantify FQs. However, excitation wavelengths on the comparable ranges of FQs and ubiquitous humic substance (HS) complicate their identification in the mixture. This study develops a simple spectral technique that affirms the individual identification of FQs and HS in the natural environment. The following characteristics and methods can demonstrate the traces of FQs in the environment-•Presence of fluorophore at Excitation/Emission = 225-230/285-295 nm wavelength in excitation-emission matrix (EEM) and parallel factor analysis (PARAFAC) models.•FQs and HS have fluorophores at excitation wavelengths of 275 nm and 325 nm in PARAFAC analysis. Unlike HS, the notable spectral presence in <350 nm emission during 275 nm excitation in FQs ensures their distinct identification in the mixture.•FQ affirming component intensity at Excitation/Emission = 225-230/285-295 nm and the intensity <350 nm emission during 275 nm excitation are considered in conjunction to quantify the amount of least FQ in any environmental sample.

摘要

由于氟喹诺酮(FQ)类抗生素的无节制使用,这类广泛应用的抗生素已成为新出现的污染物。一种名为荧光光谱法的快速、直接、精确且先进的技术被用于对FQ进行表征和半定量分析。然而,FQ和普遍存在的腐殖质(HS)在可比波长范围内的激发波长使得在混合物中对它们进行识别变得复杂。本研究开发了一种简单的光谱技术,可在自然环境中对FQ和HS进行单独识别。以下特征和方法可证明环境中FQ的踪迹:

  • 在激发-发射矩阵(EEM)和平行因子分析(PARAFAC)模型中,激发/发射波长为225 - 230/285 - 295 nm处存在荧光团。

  • 在PARAFAC分析中,FQ和HS在激发波长275 nm和325 nm处有荧光团。与HS不同,FQ在275 nm激发时,在<350 nm发射处有显著的光谱存在,这确保了它们在混合物中的独特识别。

  • 结合考虑在激发/发射 = 225 - 230/285 - 295 nm处确认FQ的组分强度以及在275 nm激发时<350 nm发射的强度,以量化任何环境样品中最少FQ的含量。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e3f1/11999577/7b144b8eed8f/gr5.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e3f1/11999577/a87c154be3d3/ga1.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e3f1/11999577/5c0f10ffb03a/gr1.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e3f1/11999577/19c6acece120/gr2.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e3f1/11999577/6d56f382bfc1/gr3.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e3f1/11999577/ef5d92ef33da/gr4.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e3f1/11999577/7b144b8eed8f/gr5.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e3f1/11999577/a87c154be3d3/ga1.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e3f1/11999577/5c0f10ffb03a/gr1.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e3f1/11999577/19c6acece120/gr2.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e3f1/11999577/6d56f382bfc1/gr3.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e3f1/11999577/ef5d92ef33da/gr4.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/e3f1/11999577/7b144b8eed8f/gr5.jpg

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本文引用的文献

1
Interaction of Antibiotics and Humic Substances: Environmental Consequences and Remediation Prospects.抗生素与腐殖质相互作用:环境后果与修复前景。
Molecules. 2022 Nov 10;27(22):7754. doi: 10.3390/molecules27227754.
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氟喹诺酮类药物相关性残疾的治疗:病理生物化学意义。
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