{"title":"氟原子和哌嗪环对诺氟沙星类似物生物毒性的影响:实验与理论结合研究","authors":"Chuanxi Yang, Xiaoning Wang*, Xinyan Zhao, Yongkun Wu, Jingyan Lin, Yuhan Zhao, Yiyong Xu, Kaipeng Sun, Chao Zhang, Ziheng Wan, Weihua Zhao, Yihua Xiao, Haofen Sun, Dong Chen, Wenping Dong, Tieyu Wang and Weiliang Wang*, ","doi":"10.1021/envhealth.4c0009510.1021/envhealth.4c00095","DOIUrl":null,"url":null,"abstract":"<p >To clarify the effect of the fluorine atom and piperazine ring on norfloxacin (NOR), NOR degradation products (NOR-DPs, P1–P8) were generated via UV combined with hydrogen peroxide (UV/H<sub>2</sub>O<sub>2</sub>) technology. NOR degradation did not significantly affect cytotoxicity of NOR against BV2, A549, HepG2, and Vero E6 cells. Compared with that of NOR, mutagenicity and median lethal concentration of P1–P8 in fathead minnow were increased, and bioaccumulation factor and oral median lethal dose of P1–P8 in rats were decreased. Molecular docking was used to evaluate the inhibitory effect of DNA gyrase A (gyrA) on NOR-DPs to determine the molecular-level mechanism and establish the structure–activity relationship. Results indicated that the most common amino acid residues were Ile13, Ser27, Val28, Gly31, Asp36, Arg46, Arg47, Asp157, and Gly340; hydrogen bonds and hydrophobic interactions played key roles in the inhibitory effect. Binding area (BA) decreased from 350.80 Å<sup>2</sup> (NOR) to 346.21 Å<sup>2</sup> (P1), and the absolute value of binding energy (|BE|) changed from 2.53 kcal/mol (NOR) to 2.54 kcal/mol (P1), indicating that the fluorine atom mainly affects BA. The piperazine ring clearly influenced BA and |BE|. “Yang ChuanXi Rules” were used to explain effects of molecular weight (MW), BA, |BE|, and sum of η<sub>1</sub> + η<sub>2</sub> (η<sub>1</sub>: normalization of BA, η<sub>2</sub>: normalization of |BE|) and predict biotoxicity of NOR-DPs based on half-maximum inhibitory concentration (IC<sub>50</sub>), half-minimal inhibitory concentration (MIC<sub>50</sub>), and half-minimal bactericidal concentration (MBC<sub>50</sub>) values.</p>","PeriodicalId":29795,"journal":{"name":"Environment & Health","volume":"2 12","pages":"886–901 886–901"},"PeriodicalIF":0.0000,"publicationDate":"2024-08-22","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"https://pubs.acs.org/doi/epdf/10.1021/envhealth.4c00095","citationCount":"0","resultStr":"{\"title\":\"Effect of Fluorine Atoms and Piperazine Rings on Biotoxicity of Norfloxacin Analogues: Combined Experimental and Theoretical Study\",\"authors\":\"Chuanxi Yang, Xiaoning Wang*, Xinyan Zhao, Yongkun Wu, Jingyan Lin, Yuhan Zhao, Yiyong Xu, Kaipeng Sun, Chao Zhang, Ziheng Wan, Weihua Zhao, Yihua Xiao, Haofen Sun, Dong Chen, Wenping Dong, Tieyu Wang and Weiliang Wang*, \",\"doi\":\"10.1021/envhealth.4c0009510.1021/envhealth.4c00095\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"<p >To clarify the effect of the fluorine atom and piperazine ring on norfloxacin (NOR), NOR degradation products (NOR-DPs, P1–P8) were generated via UV combined with hydrogen peroxide (UV/H<sub>2</sub>O<sub>2</sub>) technology. NOR degradation did not significantly affect cytotoxicity of NOR against BV2, A549, HepG2, and Vero E6 cells. Compared with that of NOR, mutagenicity and median lethal concentration of P1–P8 in fathead minnow were increased, and bioaccumulation factor and oral median lethal dose of P1–P8 in rats were decreased. Molecular docking was used to evaluate the inhibitory effect of DNA gyrase A (gyrA) on NOR-DPs to determine the molecular-level mechanism and establish the structure–activity relationship. Results indicated that the most common amino acid residues were Ile13, Ser27, Val28, Gly31, Asp36, Arg46, Arg47, Asp157, and Gly340; hydrogen bonds and hydrophobic interactions played key roles in the inhibitory effect. Binding area (BA) decreased from 350.80 Å<sup>2</sup> (NOR) to 346.21 Å<sup>2</sup> (P1), and the absolute value of binding energy (|BE|) changed from 2.53 kcal/mol (NOR) to 2.54 kcal/mol (P1), indicating that the fluorine atom mainly affects BA. The piperazine ring clearly influenced BA and |BE|. “Yang ChuanXi Rules” were used to explain effects of molecular weight (MW), BA, |BE|, and sum of η<sub>1</sub> + η<sub>2</sub> (η<sub>1</sub>: normalization of BA, η<sub>2</sub>: normalization of |BE|) and predict biotoxicity of NOR-DPs based on half-maximum inhibitory concentration (IC<sub>50</sub>), half-minimal inhibitory concentration (MIC<sub>50</sub>), and half-minimal bactericidal concentration (MBC<sub>50</sub>) values.</p>\",\"PeriodicalId\":29795,\"journal\":{\"name\":\"Environment & Health\",\"volume\":\"2 12\",\"pages\":\"886–901 886–901\"},\"PeriodicalIF\":0.0000,\"publicationDate\":\"2024-08-22\",\"publicationTypes\":\"Journal Article\",\"fieldsOfStudy\":null,\"isOpenAccess\":false,\"openAccessPdf\":\"https://pubs.acs.org/doi/epdf/10.1021/envhealth.4c00095\",\"citationCount\":\"0\",\"resultStr\":null,\"platform\":\"Semanticscholar\",\"paperid\":null,\"PeriodicalName\":\"Environment & Health\",\"FirstCategoryId\":\"1085\",\"ListUrlMain\":\"https://pubs.acs.org/doi/10.1021/envhealth.4c00095\",\"RegionNum\":0,\"RegionCategory\":null,\"ArticlePicture\":[],\"TitleCN\":null,\"AbstractTextCN\":null,\"PMCID\":null,\"EPubDate\":\"\",\"PubModel\":\"\",\"JCR\":\"\",\"JCRName\":\"\",\"Score\":null,\"Total\":0}","platform":"Semanticscholar","paperid":null,"PeriodicalName":"Environment & Health","FirstCategoryId":"1085","ListUrlMain":"https://pubs.acs.org/doi/10.1021/envhealth.4c00095","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
Effect of Fluorine Atoms and Piperazine Rings on Biotoxicity of Norfloxacin Analogues: Combined Experimental and Theoretical Study
To clarify the effect of the fluorine atom and piperazine ring on norfloxacin (NOR), NOR degradation products (NOR-DPs, P1–P8) were generated via UV combined with hydrogen peroxide (UV/H2O2) technology. NOR degradation did not significantly affect cytotoxicity of NOR against BV2, A549, HepG2, and Vero E6 cells. Compared with that of NOR, mutagenicity and median lethal concentration of P1–P8 in fathead minnow were increased, and bioaccumulation factor and oral median lethal dose of P1–P8 in rats were decreased. Molecular docking was used to evaluate the inhibitory effect of DNA gyrase A (gyrA) on NOR-DPs to determine the molecular-level mechanism and establish the structure–activity relationship. Results indicated that the most common amino acid residues were Ile13, Ser27, Val28, Gly31, Asp36, Arg46, Arg47, Asp157, and Gly340; hydrogen bonds and hydrophobic interactions played key roles in the inhibitory effect. Binding area (BA) decreased from 350.80 Å2 (NOR) to 346.21 Å2 (P1), and the absolute value of binding energy (|BE|) changed from 2.53 kcal/mol (NOR) to 2.54 kcal/mol (P1), indicating that the fluorine atom mainly affects BA. The piperazine ring clearly influenced BA and |BE|. “Yang ChuanXi Rules” were used to explain effects of molecular weight (MW), BA, |BE|, and sum of η1 + η2 (η1: normalization of BA, η2: normalization of |BE|) and predict biotoxicity of NOR-DPs based on half-maximum inhibitory concentration (IC50), half-minimal inhibitory concentration (MIC50), and half-minimal bactericidal concentration (MBC50) values.
期刊介绍:
Environment & Health a peer-reviewed open access journal is committed to exploring the relationship between the environment and human health.As a premier journal for multidisciplinary research Environment & Health reports the health consequences for individuals and communities of changing and hazardous environmental factors. In supporting the UN Sustainable Development Goals the journal aims to help formulate policies to create a healthier world.Topics of interest include but are not limited to:Air water and soil pollutionExposomicsEnvironmental epidemiologyInnovative analytical methodology and instrumentation (multi-omics non-target analysis effect-directed analysis high-throughput screening etc.)Environmental toxicology (endocrine disrupting effect neurotoxicity alternative toxicology computational toxicology epigenetic toxicology etc.)Environmental microbiology pathogen and environmental transmission mechanisms of diseasesEnvironmental modeling bioinformatics and artificial intelligenceEmerging contaminants (including plastics engineered nanomaterials etc.)Climate change and related health effectHealth impacts of energy evolution and carbon neutralizationFood and drinking water safetyOccupational exposure and medicineInnovations in environmental technologies for better healthPolicies and international relations concerned with environmental health