| Literature DB >> 36234450 |
Jie Huang1, Tianxiang Zhou1, Wenshi Zhao1,2, Min Zhang1, Zhibo Zhang1, Wangsheng Lai1, Naveen Reddy Kadasala3, Huilian Liu1, Yang Liu1.
Abstract
As a typical representative of endocrine-disrupting chemicals (EDCs), bisphenol A (BPA) is a common persistent organic pollutant in the environment that can induce various diseases even at low concentrations. Herein, the magnetic Fe3O4-Au@Ag@(Au@Ag) nanocomposites (CSSN NCs) have been prepared by self-assembly method and applied for ultra-sensitive surface-enhanced resonance Raman scattering (SERRS) detection of BPA. A simple and rapid coupling reaction of Pauly's reagents and BPA not only solved the problem of poor affinity between BPA and noble metals, but also provided the SERRS activity of BPA azo products. The distribution of hot spots and the influence of incremental introduction of noble metals on the performance of SERRS were analyzed by a finite-difference time-domain (FDTD) algorithm. The abundance of hot spots generated by core-shell-satellite structure and outstanding SERRS performance of Au@Ag nanocrystals were responsible for excellent SERRS sensitivity of CSSN NCs in the results. The limit of detection (LOD) of CSSN NCs for BPA azo products was as low as 10-10 M. In addition, the saturation magnetization (Ms) value of CSSN NCs was 53.6 emu·g-1, which could be rapidly enriched and collected under the condition of external magnetic field. These magnetic core-shell-satellite NCs provide inspiration idea for the tailored design of ultra-sensitive SERRS substrates, and thus exhibit limitless application prospects in terms of pollutant detection, environmental monitoring, and food safety.Entities:
Keywords: FDTD; bisphenol A; core–shell–satellite nanocomposites; coupling reaction; magnetic; surface-enhanced resonance Raman scattering
Year: 2022 PMID: 36234450 PMCID: PMC9565892 DOI: 10.3390/nano12193322
Source DB: PubMed Journal: Nanomaterials (Basel) ISSN: 2079-4991 Impact factor: 5.719
Scheme 1Scheme of synthetic process of CSSN NCs and SERRS detection protocol for BPA on CSSN SERRS substrates.
Figure 1XRD pattern of Fe3O4 hollow spheres, FA, FA@Ag, and CSSN NCs.
Figure 2TEM images of Fe3O4 hollow spheres (a) and FA NCs (b). Dark-field TEM images and EDS elemental mapping results (O, Fe, Au and Ag) of FA@Ag NCs (c). TEM image of FA@Ag@PEI-DTC NCs (d). Dark-field TEM images (e) and EDS line scanning spectra of CSSN NCs (f).
Figure 3High-resolution XPS spectra of Fe3O4 hollow spheres, FA, FA@Ag, and CSSN NCs: Ag 3d (a) and Au 4f (b).
Figure 4SERRS spectra after azo reaction of BPA azo products (10−4 M) on FA, FA@Ag, and CSSN NCs.
Figure 5Electric field distribution of FA@Ag (a) and CSSN NCs (b) obtained by FDTD theoretical algorithm and the diagrammatic sketch of hot spots on CSSN NCs (c).
Figure 6SERRS spectra of BPA azo products (from 10−10 to 10−4 M) adsorbed on CSSN NCs (a). The relationship between the SERRS intensity and concentrations of BPA azo products (b).
Comparison of the SERS sensitivity of different SERS substrates to BPA.
| SERS Substrates | LOD (M) | References |
|---|---|---|
| MoS2/ZnO | 10−9 | [ |
| Au/MBA/PEG/BADGE | 3 × 10−9 | [ |
| Self-assembled graphitic substrates | 10−6 | [ |
| Ag-thiolated β-cyclodextrin | 10−7 | [ |
| MIPs@Ag NPs | 5 × 10−8 | [ |
| Ag@MIP | 10−9 | [ |
| CSSN | 10−10 | this work |