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Portable solid rapid quantitative detection for Cu2+ ions: Tuning the detection range limits of fluorescent conducting polymer dots

Published online by Cambridge University Press:  27 March 2017

Shizhen Zhao
Affiliation:
Chemical Synthesis and Pollution Control, Key Laboratory of Sichuan Province, School of Chemistry and Chemical Industry, China West Normal University, Nanchong 637002, China
Siwei Yang
Affiliation:
State Key Laboratory of Functional Materials for Informatics, Shanghai Institute of Microsystem and Information Technology, Shanghai 20050, China
Xun Song
Affiliation:
Chemical Synthesis and Pollution Control, Key Laboratory of Sichuan Province, School of Chemistry and Chemical Industry, China West Normal University, Nanchong 637002, China
Gang Wang
Affiliation:
Department of Microelectronic Science and Engineering, Faculty of Science, Ningbo University, Ningbo, Zhejiang 315211, China
Yucheng Yang
Affiliation:
State Key Laboratory of Functional Materials for Informatics, Shanghai Institute of Microsystem and Information Technology, Shanghai 20050, China
Fang Liao*
Affiliation:
Chemical Synthesis and Pollution Control, Key Laboratory of Sichuan Province, School of Chemistry and Chemical Industry, China West Normal University, Nanchong 637002, China
Guqiao Ding
Affiliation:
State Key Laboratory of Functional Materials for Informatics, Shanghai Institute of Microsystem and Information Technology, Shanghai 20050, China
*
a) Address all correspondence to this author. e-mail: liaofang407@163.com

Abstract

In this work, o-phenylenediamine-m-phenylenediamine copolymer dots (omCPs) with designed surface groups are synthesized and characterized. Here, we explored a simple, rapid semiquantitative detection system for Cu2+ with a wide detection range (5–7 orders of magnitude) based on the fluorescence in the solid state of omCPs and their tunable detection limits. The construction and application of the rapid semiquantitative detection system for Cu2+ are developed and demonstrated for the practical applications. What’s more, the detection limit can be modulated easily by adjusting the surface groups of these dots through the monomer dose control before the co-polymerization. Moreover, we demonstrated that this new technological approach is suitable for the semiquantitative determination of other ions pollutants (i.e., Na+, K+, Cu2+, Pb2+, Hg2+, and NO2 −) in environmental water.

Information

Type
Articles
Copyright
Copyright © Materials Research Society 2017 
Figure 0

SCHEME 1. A schematic diagram of the structure of omCPs.

Figure 1

FIG. 1. (a) Low magnification TEM image and corresponding size distribution of omCPs. (b) High-resolution TEM image of a single omCP particle in (a). (c) FFT of a single omCP particle in (a). (d) AFM topography image of omCPs on a mica substrate in the tapping mode (Bruker Dimension Icon AFM microscope), (e) height profile analysis along the line shown in the image. High-resolution (f) C 1s and (g) N 1s XPS spectra of omCPs.

Figure 2

FIG. 2. (a) Normalized UV–vis absorption (black curve), PLE (red curve λem = 460 nm), and PL (blue curve λex = 356 nm) spectra of omCP-95 aqueous solution. (b) PL decay curves of omCP-95 aqueous solution measured at room temperature with λem = 460 nm. (c) PL spectra of omCP-95 aqueous solution at room temperature when λem is 250, 275, 300, 320, 356, 380, 400, 425, and 450 nm, respectively. (d) PLE (black curve) and PL (black curve) spectra of omCP-95 in the solid state, inset: photographs of omCP-95 aqueous solution under visible light (left) and 365 nm UV light (right). (e) Photostability (black curve) of omCP-95 under UV light (150 W Xe lamp with a center wavelength of 320 nm). F0 and F are initial (t = 0), and specific time, PL intensities, respectively. Red curve shows the pH-stability of omCP-95; F0 and F are initial (pH = 7.0), and specific pH, PL intensities, respectively. (f) The difference in the PL intensity of omCP-95 between the blank and solutions containing different metal ions (F0 and F are PL intensities in the absence and presence of these ions, respectively). The ions are Na+, K+, Mg2+, Ca2+, Zn2+, Co2+, Ni2+, Cd2+, Hg2+, Pb2+, Al3+, Fe3+, Cl−, NO3−, SO42−, and CO32− (left to right). The concentration of ions and omCP-95 is 0.5 M and 0.5 mg mL−1, respectively.

Figure 3

FIG. 3. (a) PL spectra of the omCP-95 aqueous solution with different concentrations of Cu2+ (2 × 10−13 to 2 × 10−11 M) with λem = 460 nm at 25 °C and pH = 7. The concentration of omCP-95 was 0.5 mg mL−1. Inset: linear fitting of the Stern–Volmer plot of the PL intensity at 460 nm for different Cu2+ concentrations (2 × 10−13 to 3 × 10−12 M). (b) PL intensity of omCP-95 and omCP-NS in a 460 nm aqueous solution in a different time after Cu(NO3)2 was added (the concentration of Cu2+ was 1 × 10−12 M). F0 and F are initial (t = 0), and specific time, PL intensities, respectively. Inset: partial enlarged plot of omCP-95. (c) The lifetime of omCP-95 plotted against the concentration of Cu2+, where τ0 and τ are the fluorescent lifetimes in the absence and presence of Cu2+, respectively. (d) The PL spectra of omCP-95 (black curve), omCP-95 and Cu2+ (concentration of Cu2+ was 2 × 10−11 M, red curve), and mixture of omCP-95, Cu2+, and EDTA (concentration of Cu2+ was 2 × 10−11 M, concentration of EDTA was 1 × 10−9 M, blue curve). (e) Photographs of omCP-95, omCP-80, omCP-65, omCP-50, omCP-35, omCP-25, omCP-20, and omCP-05 aqueous solution with different concentrations of Cu2+ (concentrations of Cu2+ were 5 × 10−13, 5 × 10−12, 5 × 10−11, 5 × 10−10, 2 × 10−9, and 2 × 10−8 M) 365 nm UV light. The concentrations of omCP-95, omCP-80, omCP-65, omCP-50, omCP-35, omCP-25, omCP-20, and omCP-05 are all 0.5 mg mL−1. (f) A diagram of the detection limit (red) and linearity range (blue) of omCP-95, omCP-80, omCP-65, omCP-50, omCP-35, omCP-25, and omCP-20.

Figure 4

TABLE I. PL performances of omCP-95, omCP-80, omCP-65, omCP-50, omCP-35, omCP-25, omCP-20, omCP-05, and omCP-NS.

Figure 5

FIG. 4. High-resolution N 1s spectrum of (a) omCP-80, (b) omCP-65, (c) omCP-50, (d) omCP-35, (e) omCP-25, and (f) omCP-20.

Figure 6

FIG. 5. (a) A scheme of detection progress of the semiquantitative detection system for Cu2+ based on the fluorescence in the solid state of omCPs and their tunable detection limits. First, the water sample was dropped on the test papers for 10 s with different detection limits. Then, the water sample was removed. Finally, the dry test papers were put under UV light and show the concentration range of Cu2+. (b) Photographs of test papers loaded with omCP-95, omCP-80, omCP-65, omCP-50, omCP-35, omCP-25, and omCP-20 with different concentrations of Cu2+ (concentrations of Cu2+ were 2 × 10−13, 2 × 10−12, 2 × 10−11, 2 × 10−10, 2 × 10−9, 2 × 10−8, and 2 × 10−7 M, respectively) and 365 nm UV light. (c) and (d) Practical application of the semiquantitative detection system for Cu2+ of river water. (e) A map of the Jialing River in Nanchong, China and the concentrations of Cu2+ in different place were showed. (f) A map of the Suzhou River in Shanghai, China and the concentrations of Cu2+ in different place were showed.

Figure 7

FIG. 6. (a) Diagram of the detection limit (red) and linearity range (blue) of oECP, oBCP, oTCP, oCCP, and oRCP. (b) Diagram of the solid simultaneous detection system for Na+, K+, Cu2+, Pb2+, Hg2+, and NO2−. Digital photos of the solid simultaneous detection system under (c) visible light and (d) 365 nm UV light.

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