| Literature DB >> 27782032 |
Alexandro Catini1, Raj Kumar2, Rosamaria Capuano3, Eugenio Martinelli4, Roberto Paolesse5, Corrado di Natale6.
Abstract
Several studies in the last two decades have demonstrated that metalloporphyrins coated quartz microbalances can be fruitfully used in many diverse applications, spanning from medical diagnosis to environmental control. This large versatility is due to the combination of the flexibility of metalloporphyrins molecular design with the independence of the quartz microbalance signal from the interaction mechanisms. The nature of the metal atom in the metalloporphyrins is often indicated as one of the most effective tools to design differently selective sensors. However, the properties of sensors are also strongly affected by the characteristics of the transducer. In this paper, the role of the metal atom is investigated studying the response, to various volatile compounds, of six quartz microbalance sensors that are based on the same porphyrin but with different metals. Results show that, since quartz microbalances (QMB) transducers can sense all the interactions between porphyrin and volatile compounds, the metal ion does not completely determine the sensor behaviour. Rather, the sensors based on the same molecular ring but with different metal ions show a non-negligible common behaviour. However, even if limited, the different metals still confer peculiar properties to the sensors and might drive the sensor array identification of the pool of tested volatile compounds.Entities:
Keywords: electronic nose; metalloporphyrins; quartz microbalance
Year: 2016 PMID: 27782032 PMCID: PMC5087428 DOI: 10.3390/s16101640
Source DB: PubMed Journal: Sensors (Basel) ISSN: 1424-8220 Impact factor: 3.576
Linear Sorption-Energy Relationship (LSER) parameters of the tested volatile organic compounds (VOCs), R is the polarizability, the dipolarity, and the hydrogen bond acidity and basicity, and is the solubility term [17].
| VOC | |||||
|---|---|---|---|---|---|
| ethanol | 0.246 | 0.420 | 0.370 | 0.480 | 1.485 |
| toluene | 0.601 | 0.520 | 0.000 | 0.140 | 3.325 |
| hexane | 0.000 | 0.000 | 0.000 | 0.000 | 2.668 |
| triethylamine | 0.101 | 0.150 | 0.000 | 0.790 | 3.040 |
| dimethysulfide | 0.404 | 0.380 | 0.000 | 0.290 | 2.238 |
| propanoic acid | 0.233 | 0.650 | 0.600 | 0.450 | 2.290 |
Figure 1Time progression of the frequency shift of the sensor functionalized with CoTPP. The sensor is constantly kept in a nitrogen flow, from t = 130 s to t = 230 s 2865 ppm of toluene are added to nitrogen flow. After removal of the toluene, the sensor signal recovers the baseline. The line with two arrows indicates the sensor response used in the successive analysis.
Figure 2Response curves of each sensor vs. the concentration of test VOCs: (a) CuTPP; (b) CoTPP, (c) ZnTPP; (d) MnTPPCl; (e) FeTPPCl; (f) SnTPPCl2. In order to accommodate the wide range of concentration, the x axis is plotted in logarithmic scale. Linear fits, drawn as a continuous line, appears curved.
Figure 3Sensors sensitivity respect to each VOC.
Figure 4Map of linear correlations of sensors data. The magnitude of correlation is given in a color scale.
Figure 5Results of the PCA of the sensors data. (a) Scores of the first four principal components; (b) Loadings of the first four principal components.
Figure 6Results of the PCA of the linearly normalized sensors data. (a) Scores of the first four principal components; (b) Loadings of the first four principal components.
Figure 7Biplot of the first two principal components of the linearly normalized sensors data.