| Literature DB >> 36133546 |
Achinta Sannigrahi1, Sourav Chowdhury1,2, Indrani Nandi1,3, Dwipanjan Sanyal1, Sayantani Chall1, Krishnananda Chattopadhyay1,3.
Abstract
Although the research activities pertaining to the synthesis of fluorescent noble metal nanoclusters (NCs) and their applications in biological optics have been growing, only limited information is available in the near IR (NIR) region. However, fluorescence spectroscopy and microscopy in the NIR region offer significant advantages over UV and visible wavelengths. In this manuscript, we demonstrate bio-mineralized synthesis of stable Au-Ag bimetallic NCs with tunable NIR fluorescence using bovine serum albumin (BSA) as a protein template. We also demonstrate its application in the detection of toxic heavy metal ions Pb2+ in vitro and inside cells. The tunability of the fluorescence emission between 680 nm and 815 nm is achieved by systematically varying the ratio of Au and Ag in the composite NCs. The bimetallic NCs when interacting with Pb2+ offered a large increase in fluorescence intensity, which enabled sensitive detection of Pb2+. We determined a limit of detection (LOD) of 96 nM for the detection of Pb2+ under in vitro conditions, which is significantly less than the safe level in drinking water. Its applicability has also been demonstrated successfully in real water samples collected from local water bodies. This journal is © The Royal Society of Chemistry.Entities:
Year: 2019 PMID: 36133546 PMCID: PMC9417565 DOI: 10.1039/c9na00459a
Source DB: PubMed Journal: Nanoscale Adv ISSN: 2516-0230
Fig. 1Normalised fluorescence intensity vs. wavelength plot of Au–Ag@BSA NCs with different molar ratios of Au and Ag. This figure suggested a gradual red shift of emission spectra with increasing concentration of Ag. The red arrow indicates the composition of our interest as it showed significant intensity in the NIR region (Au : Ag = 2.3 : 2.0).
Fig. 2(a) Change in the wavelength of Au–Ag@BSA NCs as observed from fluorescence emission spectra with varying Ag concentration keeping the Au concentration fixed at 2.3 mM; (b) change in wavelength of Au–Ag@BSA NCs as observed from fluorescence emission spectra with varying Au concentration keeping the Ag concentration fixed at 2.0 mM; (c) fluorescence lifetime spectra of (Au–Ag@BSA)opt NCs where the Au : Ag molar ratio was 2.3 : 2.0; (d) changes in fluorescence lifetime with respect to the concentration of Au and Ag.
Fig. 3(a) Fluorescence intensity enhancement with increasing concentration of Pb2+; (b) increase in fluorescence lifetime with increasing concentration of Pb2+; (c) bar plots presenting the extent of fluorescence enhancement of (Au–Ag@BSA)opt NCs in the presence of different metal ions; (d) plot of fluorescence intensity against the concentration of Pb2+ showing the limit of detection (LOD).
Changes in τ1 and τ2 values of (Au–Ag@BSA)opt NCs with gradual addition of Pb2+
| [Pb2+] (μM) |
|
|
|
|
|---|---|---|---|---|
| 0 | 1.04 | 98.6 | 14.2 | 1.25 |
| 48 | 1.18 | 92.2 | 9.66 | 1.30 |
| 95 | 13.4 | 53.9 | 17.1 | 1.24 |
| 180 | 0.80 | 105.0 | 17.4 | 1.14 |
| 260 | 0.85 | 118.7 | 33.6 | 1.04 |
| 330 | 1.00 | 143.3 | 111.3 | 1.06 |
Fig. 4(a) MTT assay showing the percentage of viable cell populations in the presence of different concentrations of (Au–Ag@BSA)opt NCs; (b) bar plot presenting the extent of permeation of (Au–Ag@BSA)opt NCs at different concentrations as obtained from FACS.
Fig. 5Confocal imaging of HeLa cells: fluorescence, DIC and merged images of HeLa cells (a) without and (b) with treatment of Pb2+ ions (50 μM (Au–Ag@BSA)opt NCs for 20 min incubation); 3D surface plot of (Au–Ag@BSA)opt NC permeation, that is, the heat map in (c) absence and (d) presence of Pb2+.
Detection of Pb2+ in natural samples using the standard addition method. The term ‘Spiked’ denotes the addition of different concentration of Pb2+. “Recovery” denotes the percentage of lead detection by (Au–Ag@BSA)opt NCs with respect to the added Pb2+. RSD is the relative standard deviation
| Sample | Detected (nM) | Spiked (nM) | Found (nM) | Recovery | RSD |
|---|---|---|---|---|---|
| Tap water (Kolkata Municipal Corporation) | ND | 100 | 98.7 | 98.7 ± 0.2 | 0.38 |
| ND | 200 | 195.1 | 97.5 ± 0.5 | 1.01 | |
| ND | 300 | 305.0 | 101.6 ± 1.1 | 1.15 | |
| Neighborhood pond | ND | 100 | 96.0 | 96.0 ± 0.1 | 1.07 |
| ND | 200 | 185.0 | 92.0 ± 1.6 | 1.28 | |
| ND | 300 | 287.5 | 95.3 ± 0.8 | 0.83 | |
| Drinking water (reverse osmosis) | ND | 100 | 97.8 | 97.8 ± 0.1 | 1.21 |
| ND | 200 | 198.0 | 99.0 ± 0.6 | 1.36 | |
| ND | 300 | 307.6 | 102.5 ± 0.7 | 0.69 |