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Colorimetric Nanosensors

A special issue of Sensors (ISSN 1424-8220). This special issue belongs to the section "Chemical Sensors".

Deadline for manuscript submissions: closed (30 November 2018) | Viewed by 48342

Special Issue Editors


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Guest Editor
Universitat Politècnica de Valencia. Camino de Vera s/n, 46022 Valencia, Spain
Interests: chromo-fluorogenic sensors, electrochemical sensors, molecular probes, nanomaterials, controlled release, nanomedicine, smart materials, hybrid material

Special Issue Information

Dear Colleagues,

The development of colorimetric sensors has been a main trend in the last decades, with several groups worldwide preparing novel chemical sensing systems. They are usually cheap, versatile and can be printed on the surfaces. However, the main advantages currently include the possibility of designing naked eye systems or easily measuring colour changes using smartphones, cameras, or other image capturing systems. Few technologies are as advanced or as inexpensive as visual imaging. Traditionally, the most common approaches to colorimetric sensors was provided by (i) linking a chromophore with a receptor unit by means of a covalent bond, (ii) the use of competition assays between a dye bonded to a receptor and a certain analyte, and (iii) the use of new molecular systems that undergo guest-induced chemical reactions coupled to suitable colorimetric events. Recently, the incorporation of nanomaterials in the sensing systems has offered a full set of novel properties to be explored. This Special Issue is intended to be a timely and comprehensive issue on recent and emerging concepts and technologies in the area of chromogenic chemosensors including nanomaterials. Topics include, but are not limited to, sensors that include nanomaterials in the recognition moiety (i.e., hybrid supramolecular materials), in the signalling group (i.e., gold nanoparticles or quantum dots), or as vehicles for more complex events (i.e., aggregation processes or FRET). Furthermore, other areas such as chromogenic arrays or other emerging fields can be discussed. Research papers, short communications, and reviews are all welcome. If the author is interested in submitting a review, it would be helpful to discuss this with the Guest Editor before your submission.

Assist. Prof. Dr. Jose V. Ros-Lis
Prof. Dr. Ramón Martínez-Máñez
Guest Editors

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Keywords

  • nanoparticle
  • colour
  • sensor
  • molecular recognition
  • arrays

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Published Papers (8 papers)

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Research

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12 pages, 3519 KiB  
Article
A Simple Colorimetric and Fluorescent Sensor to Detect Organophosphate Pesticides Based on Adenosine Triphosphate-Modified Gold Nanoparticles
by Xiaoxia Li, Haixin Cui and Zhanghua Zeng
Sensors 2018, 18(12), 4302; https://doi.org/10.3390/s18124302 - 6 Dec 2018
Cited by 39 | Viewed by 6652
Abstract
A simple and dual modal (colorimetric and fluorescent) sensor for organophosphate pesticides with high sensitivity and selectivity using adenosine triphosphate (ATP)- and rhodamine B-modified gold nanoparticles (RB-AuNPs), was successfully fabricated. This detection for ethoprophos afforded colorimetric and fluorescence imaging changes visualization. The quantitative [...] Read more.
A simple and dual modal (colorimetric and fluorescent) sensor for organophosphate pesticides with high sensitivity and selectivity using adenosine triphosphate (ATP)- and rhodamine B-modified gold nanoparticles (RB-AuNPs), was successfully fabricated. This detection for ethoprophos afforded colorimetric and fluorescence imaging changes visualization. The quantitative determination was linearly proportional to the amounts of ethoprophos in the range of a micromolar scale (4.0–15.0 µM). The limit of detection for ethoprophos was as low as 37.0 nM at 3σ/k. Moreover, the extent application of this simple assay was successfully demonstrated in tap water samples with high reliability and applicability, indicating remarkable application in real samples. Full article
(This article belongs to the Special Issue Colorimetric Nanosensors)
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Figure 1

Figure 1
<p>The structure of organophosphate (OP) pesticides.</p>
Full article ">Figure 2
<p>(<b>a</b>) The color changes of citrate-capped gold nanoparticles (AuNPs) (3.0 nM) added with various pesticides (10.0 μM for ethoprophos, profenofos, and chlorpyrifos; 1.0 mM for others). (<b>b</b>) The Δ<span class="html-italic">A</span><sub>520</sub> values changes of citrate-capped AuNPs (3.0 nM) added with various OPs pesticides (10.0 μM for ethoprophos, profenofos, and chlorpyrifos; 1.0 mM for others).</p>
Full article ">Figure 3
<p>(<b>a</b>) The color changes of rhodamine B (RB)-AuNPs (3.0 nM) added with various pesticides (10.0 μM for ethoprophos, profenofos, and chlorpyrifos; 1.0 mM for others). (<b>b</b>) The Δ<span class="html-italic">A</span><sub>520</sub> values changes of RB-AuNPs (3.0 nM) added with various OP pesticides (10.0 μM for ethoprophos, profenofos, and chlorpyrifos; 1.0 mM for others). (<b>c</b>) The absorption spectra changes and (<b>d</b>) corresponding fitting curve plot of RB-AuNPs (3.0 nM) in the presence of different concentrations of ethoprophos. (<b>e</b>) Selectivity studies of RB-AuNPs by measuring ROA<sub>600/520</sub> versus interference analytes with a specific concentration.</p>
Full article ">Figure 3 Cont.
<p>(<b>a</b>) The color changes of rhodamine B (RB)-AuNPs (3.0 nM) added with various pesticides (10.0 μM for ethoprophos, profenofos, and chlorpyrifos; 1.0 mM for others). (<b>b</b>) The Δ<span class="html-italic">A</span><sub>520</sub> values changes of RB-AuNPs (3.0 nM) added with various OP pesticides (10.0 μM for ethoprophos, profenofos, and chlorpyrifos; 1.0 mM for others). (<b>c</b>) The absorption spectra changes and (<b>d</b>) corresponding fitting curve plot of RB-AuNPs (3.0 nM) in the presence of different concentrations of ethoprophos. (<b>e</b>) Selectivity studies of RB-AuNPs by measuring ROA<sub>600/520</sub> versus interference analytes with a specific concentration.</p>
Full article ">Figure 4
<p>TEM images of RB-AuNPs (3.0 nM) added with various amount of ethoprophos. The scale bar is 100.0 nm.</p>
Full article ">Figure 5
<p>(<b>a</b>) The variation of fluorescence intensity and (<b>b</b>) fluorescence imaging of RB-AuNPs (3.0 nM) added with various amounts of ethoprophos (EP) (0–5.0 µM).</p>
Full article ">Figure 6
<p>The pH effect on the assay for ethoprophos (10.0 μM) based on the measurement of Δ<span class="html-italic">A</span><sub>520</sub> of RB-AuNPs.</p>
Full article ">Figure 7
<p>(<b>a</b>) The colorimetric and (<b>b</b>) absorption changes of RB-AuNPs in various amounts of ethoprophos. (<b>c</b>) The linear fitting of ROA<sub>600/520</sub> based on RB-AuNPs in the range of 4.0–10.0 μM ethoprophos.</p>
Full article ">Scheme 1
<p>The proposed mechanism of colorimetric and fluorescence detection for ethoprophos using RB-AuNPs.</p>
Full article ">
8 pages, 2249 KiB  
Article
Functionalized Silver Nano-Sensor for Colorimetric Detection of Hg2+ Ions: Facile Synthesis and Docking Studies
by Kollur Shiva Prasad, Govindaraju Shruthi and Chandan Shivamallu
Sensors 2018, 18(8), 2698; https://doi.org/10.3390/s18082698 - 16 Aug 2018
Cited by 33 | Viewed by 5062
Abstract
In the present study, we describe the facile synthesis of silver nanoparticles (AgNPs) and their nanostructures functionalized with 2-aminopyrimidine-4,6-diol (APD-AgNPs) for Hg2+ ion detection. The promising colorimetric response of APD-AgNPs to detect Hg2+ ions was visible with naked eyes and spectroscopic [...] Read more.
In the present study, we describe the facile synthesis of silver nanoparticles (AgNPs) and their nanostructures functionalized with 2-aminopyrimidine-4,6-diol (APD-AgNPs) for Hg2+ ion detection. The promising colorimetric response of APD-AgNPs to detect Hg2+ ions was visible with naked eyes and spectroscopic changes were examined by using a UV-Visible spectrophotometer. The aggregation of APD-AgNPs upon addition of Hg2+ ions was due to the chelation effect of the functionalized nanostructures and results in a color change from pale brown to deep yellow color. The probing sensitivity was observed within five minutes with a detection limit of about 0.35 µM/L. The TEM images of APD-AgNPs showed polydispersed morphologies with hexagonal, heptagonal and spherical nanostructures with an average size between 10 to 40 nm. Furthermore, the sensing behavior of APD-AgNPs towards Hg2+ ions detection was investigated using docking and interaction studies. Full article
(This article belongs to the Special Issue Colorimetric Nanosensors)
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Figure 1

Figure 1
<p>X-ray diffraction spectrum of APD-AgNPs-Hg<sup>2+</sup> complex.</p>
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<p>Absorption spectra showing (<b>a</b>) SRP bands of APD-AgNPs and (<b>b</b>) APD-AgNPs-Hg<sup>2+</sup> complex. Inset image showing colorimetric digital picture of APD-AgNPs and APD-AgNPs-Hg<sup>2+</sup> complex.</p>
Full article ">Figure 3
<p>(<b>a</b>) Electronic absorption spectra of APD-AgNPs solutions with various concentrations of Hg<sup>2+</sup> in the range of 0 to 65 µM L<sup>−1</sup> increasing in steps of 5 µM L<sup>−1</sup>; (<b>b</b>) Linear relationship between the absorbance intensity of APD-AgNPs versus Hg<sup>2+</sup> ion concentration at 538 nm.</p>
Full article ">Figure 4
<p>TEM images of (<b>a</b>) APD-AgNPs, (<b>b</b>) APD-AgNPs-Hg<sup>2+</sup> complex and (<b>c</b>) HRTEM of APD-AgNPs-Hg<sup>2+</sup> complex with SAED image (inset).</p>
Full article ">Figure 5
<p>Image showing the interaction of Hg<sup>2+</sup> with N1, N3, N4 and N9 of APD-AgNPs ring with the bond length of 3.655 Å, 3.858Å, 3.480 Å and 3.257 Å respectively, forming a APD-AgNPs-Hg<sup>2+</sup> complex.</p>
Full article ">Scheme 1
<p>Synthetic pathway of APD-AgNPs (<b>top</b>) and its Hg<sup>2+</sup> sensing property (<b>bottom</b>).</p>
Full article ">
13 pages, 3641 KiB  
Article
A Colorimetric Probe Based on Functionalized Gold Nanorods for Sensitive and Selective Detection of As(III) Ions
by Kun Ge, Jingmin Liu, Guozhen Fang, Peihua Wang, Dongdong Zhang and Shuo Wang
Sensors 2018, 18(7), 2372; https://doi.org/10.3390/s18072372 - 21 Jul 2018
Cited by 18 | Viewed by 5291
Abstract
A colorimetric probe for determination of As(III) ions in aqueous solutions on basis of localized surface plasmon resonance (LSPR) was synthesized. The dithiothreitol molecules with two end thiols covalently combined with Au Nanorods (AuNRs) with an aspect ratio of 2.9 by Au-S bond [...] Read more.
A colorimetric probe for determination of As(III) ions in aqueous solutions on basis of localized surface plasmon resonance (LSPR) was synthesized. The dithiothreitol molecules with two end thiols covalently combined with Au Nanorods (AuNRs) with an aspect ratio of 2.9 by Au-S bond to form dithiothreitol coated Au Nanorods (DTT-AuNRs), acting as colorimetric probe for the determination of As(III) ions. With the adding of As(III) ions, the AuNRs will be aggregated and leading the longitudinal SPR absorption band of DTT-AuNRs decrease due to the As(III) ions can bind with three DTT molecules through an As-S linkage. The potential factors affect the response of DTT-AuNRs to As(III) ions including the concentration of DTT, pH values of DTT-AuNRs, reaction time and NaCl concentration were optimized. Under optimum assay conditions, the DTT-AuNRs colorimetric probe has high sensitivity towards As(III) ions with low detection limit of 38 nM by rules of 3σ/k and excellent linear range of 0.13–10.01 μM. The developed colorimetric probe shows high selectivity for As(III) ions sensing and has applied to determine of As(III) in environmental water samples with quantitative spike-recoveries range from 95.2% to 100.4% with low relative standard deviation of less than 4.4% (n = 3). Full article
(This article belongs to the Special Issue Colorimetric Nanosensors)
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Figure 1

Figure 1
<p>The schematic mechanism of determination of As(III) by DTT-AuNRs colorimetric probe.</p>
Full article ">Figure 2
<p>(<b>a</b>) TEM image of AuNRs; (<b>b</b>) Size distribution of AuNRs and DTT-AuNRs exposed to As(III); (<b>c</b>) UV–vis absorption spectra of CTAB-coating AuNRs; (<b>d</b>) UV–vis absorption spectra of AuNRs and DTT-AuNRs.</p>
Full article ">Figure 3
<p>(<b>a</b>) UV–vis absorption spectra of DTT-AuNRs (0.8 nM) upon adding increasing concentration of As(III) ions (from 0.13 to 10.01 μM); (<b>b</b>) Effects of concentration of DTT on UV-vis spectra of AuNRs.</p>
Full article ">Figure 4
<p>Evaluation of stability of DTT-AuNRs colorimetric probe: (<b>a</b>) Effect of the pH value of NaAc-HAc buffer (10 mM); (<b>b</b>) Effect of the reaction time; (<b>c</b>) Effect of the concentration of NaCl.</p>
Full article ">Figure 5
<p>Effects of pH and buffer media on UV-vis spectra of AuNRs: (<b>a</b>) 10 mM PBS; (<b>b</b>) 10 mM Tris-HCl; (<b>c</b>) BR buffer; (<b>d</b>) 10 mM NaAc-HAc.</p>
Full article ">Figure 6
<p>Optimization of developed AuNR probe for the colorimetric detection of As(III): (<b>a</b>) Effect of the concentration of DTT; (<b>b</b>) Effect of the pH value of NaAc-HAc buffer (10 mM); (<b>c</b>) Effect of the reaction time; (<b>d</b>) Effect of the concentration of NaCl.</p>
Full article ">Figure 7
<p>Selectivity test of the developed colorimetric probe for As(III) ions (6.67 μM) over other metal ions (50 μM, except for Hg<sup>2+</sup>, 25 μM). Black bars denote the responses of individual metal ions, while red bars show the responses of As(III) (6.67 μM) in the presence of other metal ions.</p>
Full article ">Figure 8
<p>Plot of decreased longitudinal SPR absorption intensity (ΔA) against As(III) concentration over the linear range of 0.13–10.01 μM.</p>
Full article ">
15 pages, 9345 KiB  
Article
Investigation of Gasochromic Rhodium Complexes Towards Their Reactivity to CO and Integration into an Optical Gas Sensor for Fire Gas Detection
by Carolin Pannek, Karina R. Tarantik, Katrin Schmitt and Jürgen Wöllenstein
Sensors 2018, 18(7), 1994; https://doi.org/10.3390/s18071994 - 21 Jun 2018
Cited by 10 | Viewed by 4346
Abstract
The detection of the toxic gas carbon monoxide (CO) in the low ppm range is required in different applications. We present a study of the reactivity of different gasochromic rhodium complexes towards the toxic gas carbon monoxide (CO). Therefore, variations of binuclear rhodium [...] Read more.
The detection of the toxic gas carbon monoxide (CO) in the low ppm range is required in different applications. We present a study of the reactivity of different gasochromic rhodium complexes towards the toxic gas carbon monoxide (CO). Therefore, variations of binuclear rhodium complexes with different ligands were prepared. They were characterized by FTIR spectroscopy, 1H NMR spectroscopy, and differential scanning calorimetry. All complexes are spectroscopically distinguishable and temperature stable up to at least 187 °C. The gasochromic behavior of all different compounds was tested. Therefore, the compounds were dissolved in toluene and exposed to 100 ppm CO for 10 min to investigate their gas sensitivity and reaction velocity. The changes in the transmission spectra were recorded by UV/vis spectroscopy. Furthermore, a significant influence of the solvent to the color dyes’ gasochromic reaction and behavior was observed. After characterization, one complex was transferred as sensing element into an optical gas sensor. Two different measurement principles (reflection- and waveguide-based) were built up and tested towards their capability as gasochromic CO sensors. Finally, different gas-dependent measurements were carried out. Full article
(This article belongs to the Special Issue Colorimetric Nanosensors)
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Figure 1

Figure 1
<p>(<b>a</b>) Sketch of the measuring principle. The color change of the sensitive probe can be detected by the reflected light of a blue LED on the surface of the color dye. To avoid interfering light, an optical barrier is mounted between the LED and the detector; (<b>b</b>) Picture of the realized measurement system. The measuring board is fixed towards the sensitive probe.</p>
Full article ">Figure 2
<p>(<b>a</b>) Sketch of the gasochromic sensor, consisting of a planar optical waveguide, covered with the colorimetric film. The light of an LED is coupled into one end of the waveguide, and travels through it under TIR before it is focused onto a photo detector. The gas reaction leads to changes in the detector signal. Top view of the sensor element consisting of the measurement channel, a reference channel, two photo detectors, and one LED; (<b>b</b>) Picture of the waveguide-based measurement system realized by R2R processing [<a href="#B13-sensors-18-01994" class="html-bibr">13</a>].</p>
Full article ">Figure 3
<p>Chemical structure of the gasochromic binuclear rhodium complex [Rh<sub>2</sub>{(XC<sub>6</sub>H<sub>3</sub>)P(XC<sub>6</sub>H<sub>4</sub>)}<sub>n</sub>(OCR)<sub>2</sub>]∙<b>A<sub>2</sub></b> with different ligands (see <a href="#sensors-18-01994-t001" class="html-table">Table 1</a>).</p>
Full article ">Figure 4
<p>Principal reaction scheme of the rhodium complex with CO. The reaction induces a two stages ligand exchange of <b>A</b> with CO. Left: [Rh<sub>2</sub>{(XC<sub>6</sub>H<sub>3</sub>)P(XC<sub>6</sub>H<sub>4</sub>)}<sub>n</sub>(OCR)<sub>2</sub>]∙<b>(A)<sub>2</sub></b>, Middle: [Rh<sub>2</sub>{(XC<sub>6</sub>H<sub>3</sub>)P(XC<sub>6</sub>H<sub>4</sub>)}<sub>n</sub>(OCR)<sub>2</sub>]∙<b>(A,CO),</b> Right: [Rh<sub>2</sub>{(XC<sub>6</sub>H<sub>3</sub>)P(XC<sub>6</sub>H<sub>4</sub>)}<sub>n</sub>(OCR)<sub>2</sub>]∙<b>(CO)<sub>2</sub></b>.</p>
Full article ">Figure 5
<p>Color changes of the rhodium complexes <b>1∙(A)<sub>2</sub></b>–<b>5∙(A)<sub>2</sub></b> dissolved in toluene, during the exposure to 100 ppm CO (40% r.H.) for 10 min.</p>
Full article ">Figure 6
<p>Difference of the transmission change (ΔT/%) of the investigated Rh compounds before and after exposure to 100 ppm for 10 min.</p>
Full article ">Figure 7
<p>Difference of the transmission change (ΔT/%) of <b>1∙(A)<sub>2</sub></b> dissolved in ethanol, propane-1,2-diole, toluene, and chloroform, before and after exposure to 100 ppm for 10 min.</p>
Full article ">Figure 8
<p>Color change of <b>1∙(A)<sub>2</sub></b> adsorbed on silica gel before (left) and after exposure to 50–1000 ppm CO in synthetic air at 50% r.H. Each picture was taken after 30 s of CO exposure. After CO exposure, the color change is reversible, and the silica reaches its original color again.</p>
Full article ">Figure 9
<p>Colorimetric reaction of <b>1∙(A)<sub>2</sub></b> adsorbed on silica gel to 100 ppm CO with 40% r.H. at room temperature.</p>
Full article ">Figure 10
<p>Calculated Langmuir isotherm for gasochromic CO reaction of the color dye. The reaction leads to signal changes up to 28.53%.</p>
Full article ">Figure 11
<p>Temperature dependence of the maximum signal shift of <b>2∙(A)<sub>2</sub></b> at different reaction temperatures between 10 °C and 50 °C. The colored silica was exposed to 300 ppm CO.</p>
Full article ">Figure 12
<p>Temperature dependence of the maximum signal shift of <b>2∙(A)<sub>2</sub></b> at different reaction temperatures between 10 °C and 50 °C. The colored silica was exposed to 300 ppm CO.</p>
Full article ">Figure 13
<p>CO-dependent reaction of the waveguide-based sensor to 200 ppm CO and different background humidity. The signals are divided into the measurement and reference channel, as well as the calculated sensor signal. The measurement was carried out under ambient conditions.</p>
Full article ">Figure 14
<p>CO-dependent sensor reaction to 200 ppm and 100 ppm CO, as well as to different steps, recorded at room temperature with 40% r.H. The sensor shows sufficient repeatability over time. The measurement was performed using the sensor system shown in <a href="#sensors-18-01994-f002" class="html-fig">Figure 2</a>b.</p>
Full article ">
6 pages, 907 KiB  
Article
Improving Color Accuracy of Colorimetric Sensors
by Eric Kirchner, Pim Koeckhoven and Keshav Sivakumar
Sensors 2018, 18(4), 1252; https://doi.org/10.3390/s18041252 - 18 Apr 2018
Cited by 9 | Viewed by 6908
Abstract
Accurate measurements of reflectance and color require spectrophotometers with prices often exceeding $3000. Recently, new “color instruments” became available with much lower prices, thanks to the availability of inexpensive colorimetric sensors. We investigated the Node+ChromaPro and the Color Muse, launched in 2015 and [...] Read more.
Accurate measurements of reflectance and color require spectrophotometers with prices often exceeding $3000. Recently, new “color instruments” became available with much lower prices, thanks to the availability of inexpensive colorimetric sensors. We investigated the Node+ChromaPro and the Color Muse, launched in 2015 and 2016 by Variable Inc. Both instruments are colorimeters, combining a colorimetric sensor with LED lighting. We investigated color accuracy compared to a high-end spectrophotometer from BYK Gardner. With different sets of samples we find for the Node an average value of dECMC (1:1) = 1.50, and a maximum of 7.86, when comparing with the 45° geometry of the spectrophotometer. Utilizing measurement data on the Spectral Power Distributions of the LEDs, we developed three methods to improve color accuracy as compared to the spectrophotometer data. We used these methods on different sets of samples with various degrees of gloss, both for training the models underlying the methods and for independent tests of model accuracy. Average color accuracy of the Node+ChromaPro improves from dECMC (1:1) = 1.82 to 1.16 with respect to spectrophotometer data. The percentage of samples with dECMC (1:1) < 1.0 increases from 30.9% (uncorrected) to 64%. With the improved color accuracy, these sensors become useful for many more applications. Full article
(This article belongs to the Special Issue Colorimetric Nanosensors)
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Figure 1
<p>Two low-cost color measurement devices: (<b>a</b>) Node+ChromaPro; (<b>b</b>) Color Muse.</p>
Full article ">Figure 2
<p>Spectral Power Distribution as measured for (<b>a</b>) Node+ChromaPro and (<b>b</b>) Color Muse. In both cases, best fit functions are shown for underlying LEDs.</p>
Full article ">
14 pages, 4029 KiB  
Article
A Miniaturized Colorimeter with a Novel Design and High Precision for Photometric Detection
by Jun-Chao Yan, Yan Chen, Yu Pang, Jan Slavik, Yun-Fei Zhao, Xiao-Ming Wu, Yi Yang, Si-Fan Yang and Tian-Ling Ren
Sensors 2018, 18(3), 818; https://doi.org/10.3390/s18030818 - 8 Mar 2018
Cited by 11 | Viewed by 7068
Abstract
Water quality detection plays an increasingly important role in environmental protection. In this work, a novel colorimeter based on the Beer-Lambert law was designed for chemical element detection in water with high precision and miniaturized structure. As an example, the colorimeter can detect [...] Read more.
Water quality detection plays an increasingly important role in environmental protection. In this work, a novel colorimeter based on the Beer-Lambert law was designed for chemical element detection in water with high precision and miniaturized structure. As an example, the colorimeter can detect phosphorus, which was accomplished in this article to evaluate the performance. Simultaneously, a modified algorithm was applied to extend the linear measurable range. The colorimeter encompassed a near infrared laser source, a microflow cell based on microfluidic technology and a light-sensitive detector, then Micro-Electro-Mechanical System (MEMS) processing technology was used to form a stable integrated structure. Experiments were performed based on the ammonium molybdate spectrophotometric method, including the preparation of phosphorus standard solution, reducing agent, chromogenic agent and color reaction. The device can obtain a wide linear response range (0.05 mg/L up to 7.60 mg/L), a wide reliable measuring range up to 10.16 mg/L after using a novel algorithm, and a low limit of detection (0.02 mg/L). The size of flow cell in this design is 18 mm × 2.0 mm × 800 ?m, obtaining a low reagent consumption of 0.004 mg ascorbic acid and 0.011 mg ammonium molybdate per determination. Achieving these advantages of miniaturized volume, high precision and low cost, the design can also be used in automated in situ detection. Full article
(This article belongs to the Special Issue Colorimetric Nanosensors)
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Figure 1

Figure 1
<p>The structure design of the colorimeter.</p>
Full article ">Figure 2
<p>The photograph of (<b>a</b>) laser light source and (<b>b</b>) photodetector. (<b>c</b>) The spectral response curves for different photodetectors, and (<b>d</b>) corresponding current response to the light intensity.</p>
Full article ">Figure 3
<p>The fabrication process of the device. (<b>a</b>) Coating on the wafer. (<b>b</b>) Graphic mold after exposure and development process. (<b>c</b>) Using polydimethylsiloxane (PDMS) to mold the flow channel. (<b>d</b>) Dicing a complete model according to the designed line frames. (<b>e</b>) Bonding the flow channel with PDMS at the ratio of 4:1, using the polymethyl methacrylate (PMMA) to increase the stability of the device. (<b>f</b>,<b>g</b>) Bonding the flow channel with detector and light source module designed previously. (<b>h</b>) Punching to get through the flow channel. (<b>i</b>) Photograph after the integrated design.</p>
Full article ">Figure 4
<p>(<b>a</b>) The schematics of the experimental setup for photometric detection. (<b>b</b>) Solutions to be tested after chromogenic reaction. (<b>c</b>) The circulating validation of micro flow cell. (<b>d</b>) shows the inlet connected with a peristaltic pump and tested with applied voltages.</p>
Full article ">Figure 5
<p>The results of test data statistics and analysis. (<b>a</b>) The exponential relation of I-c between the output current and the corresponding sample concentrations. (<b>b</b>) The relationship between the obtained absorbance and concentration. (<b>c</b>) A linear relationship between absorbance and concentration of reference.</p>
Full article ">Figure 6
<p>(<b>a</b>) A three-dimensional diagram showing the relationship between the output current and the concentration, and the relationship between the sensitivity and the concentration, both of which are exponential. (<b>b</b>) The detection limits calculated under different concentrations. The maximum value is 0.019 mg/L considering the worst condition in the point of 1.2 mg/L.</p>
Full article ">Figure 7
<p>Data recording and analysis of different test process. The current value changes to a steady value for different solution exchange.</p>
Full article ">Figure 8
<p>The results of phosphorus determination in standard water and seawater.</p>
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<p>(<b>a</b>) A complete record of tracking analysis. From left records refer to blank measurements followed of phosphorus standard solution with concentration ranging from 0.00 to 8.00 mg/L, then followed of five river water samples (a, b, c, d, e). (<b>b</b>) Data record for five sample solutions. (<b>c</b>) The linear relationship between absorbance and concentration of standard solutions in the assay. (<b>d</b>) The concentrations of a, b, c, d, e found by our design and analytical method in laboratory.</p>
Full article ">

Review

Jump to: Research

23 pages, 3239 KiB  
Review
Overview of the Evolution of Silica-Based Chromo-Fluorogenic Nanosensors
by Luis Pla, Beatriz Lozano-Torres, Ramón Martínez-Máñez, Félix Sancenón and Jose V. Ros-Lis
Sensors 2019, 19(23), 5138; https://doi.org/10.3390/s19235138 - 23 Nov 2019
Cited by 13 | Viewed by 3863
Abstract
This review includes examples of silica-based, chromo-fluorogenic nanosensors with the aim of illustrating the evolution of the discipline in recent decades through relevant research developed in our group. Examples have been grouped according to the sensing strategies. A clear evolution from simply functionalized [...] Read more.
This review includes examples of silica-based, chromo-fluorogenic nanosensors with the aim of illustrating the evolution of the discipline in recent decades through relevant research developed in our group. Examples have been grouped according to the sensing strategies. A clear evolution from simply functionalized materials to new protocols involving molecular gates and the use of highly selective biomolecules such as antibodies and oligonucleotides is reported. Some final examples related to the evolution of chromogenic arrays and the possible use of nanoparticles to communicate with other nanoparticles or cells are also included. A total of 64 articles have been summarized, highlighting different sensing mechanisms. Full article
(This article belongs to the Special Issue Colorimetric Nanosensors)
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<p>Timeline of the first examples developed by the authors in the different categories of the review.</p>
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<p>Scheme of the mesoporous silica materials S1 and S2 functionalized with pyrylium moieties anchored in the inner surface of the pores for the detection of medium chain primary amines.</p>
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<p>Scheme of the silica-based material functionalized with thiols and amines for the detection of CO<sub>2</sub> through control of mass transfer of the dye from the solution to the material surface. In the absence of CO<sub>2</sub> (<b>a</b>) squaraine dye can access to the surface and react with the grafted thiols. However, in the presence of CO<sub>2</sub> (<b>b</b>) squaraine-thiol reaction is inhibited.</p>
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<p>The scheme of a two-step protocol for the detection of anionic surfactants (SDS) with a silica inorganic support functionalized with imidazolium cations (acting as binding sites) and treatment with methylene blue.</p>
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<p>Mesoporous silica functionalized with binding sites and loaded with dyes for the selective detection of citrate and borate anions using a displacement assay.</p>
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<p>Silica nanoparticles functionalized with terpyridine (cation binding units) and sulforhodamine B (reporter) for the fluorescent recognition of anions.</p>
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<p>Mesoporous silica nanoparticles capped with polyamines for the selective chromo-fluorogenic detection of ADP and ATP.</p>
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<p>Scheme of a nanogated material capped with a fragment of the 16S ribosomal RNA subunit selective to <span class="html-italic">Mycoplasma fermentans</span>. Rhodamine B release was observed in the presence of genomic <span class="html-italic">Mycoplasma fermentans</span> DNA.</p>
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<p>Scheme of antibody-capped, mesoporous silica nanoparticles for TATP detection.</p>
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<p>Left: scheme of the MSNs-capped system for the detection of nerve agents.</p>
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<p>Scheme of the MSNs-capped system for the detection of NO<sub>2</sub>.</p>
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35 pages, 2270 KiB  
Review
Novel Spectroscopic and Electrochemical Sensors and Nanoprobes for the Characterization of Food and Biological Antioxidants
by Reşat Apak, Sema Demirci Çekiç, Ayşem Üzer, Saliha Esin Çelik, Mustafa Bener, Burcu Bekdeşer, Ziya Can, Şener Sağlam, Ayşe Nur Önem and Erol Erçağ
Sensors 2018, 18(1), 186; https://doi.org/10.3390/s18010186 - 11 Jan 2018
Cited by 26 | Viewed by 7016
Abstract
Since an unbalanced excess of reactive oxygen/nitrogen species (ROS/RNS) causes various diseases, determination of antioxidants that can counter oxidative stress is important in food and biological analyses. Optical/electrochemical nanosensors have attracted attention in antioxidant activity (AOA) assessment because of their increased sensitivity and [...] Read more.
Since an unbalanced excess of reactive oxygen/nitrogen species (ROS/RNS) causes various diseases, determination of antioxidants that can counter oxidative stress is important in food and biological analyses. Optical/electrochemical nanosensors have attracted attention in antioxidant activity (AOA) assessment because of their increased sensitivity and selectivity. Optical sensors offer advantages such as low cost, flexibility, remote control, speed, miniaturization and on-site/in situ analysis. Electrochemical sensors using noble metal nanoparticles on modified electrodes better catalyze bioelectrochemical reactions. We summarize the design principles of colorimetric sensors and nanoprobes for food antioxidants (including electron-transfer based and ROS/RNS scavenging assays) and important milestones contributed by our laboratory. We present novel sensors and nanoprobes together with their mechanisms and analytical performances. Our colorimetric sensors for AOA measurement made use of cupric-neocuproine and ferric-phenanthroline complexes immobilized on a Nafion membrane. We recently designed an optical oxidant/antioxidant sensor using N,N-dimethyl-p-phenylene diamine (DMPD) as probe, from which ROS produced colored DMPD-quinone cationic radicals electrostatically retained on a Nafion membrane. The attenuation of initial color by antioxidants enabled indirect AOA estimation. The surface plasmon resonance absorption of silver nanoparticles as a result of enlargement of citrate-reduced seed particles by antioxidant addition enabled a linear response of AOA. We determined biothiols with Ellman reagent?derivatized gold nanoparticles. Full article
(This article belongs to the Special Issue Colorimetric Nanosensors)
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<p>The CUPRAC reaction of Cu(II)-neocuproine complex with antioxidants, producing the yellow-orange colored Cu(I)-neocuproine chelate (λ<sub>max</sub> = 450 nm).</p>
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<p>Schematic diagram of CUPRAC antioxidant sensors: the measurement of the analytical signal (<b>a</b>) for absorptimetric sensor and (<b>b</b>) for reflectometric sensor.</p>
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<p>Electrochemical sensing of oxidative DNA damage and its restoration by antioxidants (immobilization method on the working electrode was adsorption on GCE).</p>
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<p>Scheme of the fluorescent turn-on sensing strategy for antioxidants.</p>
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<p>Schematic presentation of SOD biosensors based on PEDOT and CNT.</p>
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<p>Cyt <span class="html-italic">c</span> sensor in determining superoxide scavenging activity of antioxidant (Cyt <span class="html-italic">c</span>: Cytchrome <span class="html-italic">c</span>; AOX: Antioxidant; HX: Hypoxanthine; XOD: Xanthine oxidase).</p>
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<p>Schematic diagram of catalytic properties of AuNPs in decomposing H<sub>2</sub>O<sub>2</sub> and scavenging superoxide anion radical.</p>
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