| Literature DB >> 35161589 |
José C Campelo1, Juan V Capella1, Rafael Ors1, Miguel Peris2, Alberto Bonastre1.
Abstract
The in-line determination of chemical parameters in water is of capital importance for environmental reasons. It must be carried out frequently and at a multitude of points; thus, the ideal method is to utilize automated monitoring systems, which use sensors based on many transducers, such as Ion Selective Electrodes (ISE). These devices have multiple advantages, but their management via traditional methods (i.e., manual sampling and measurements) is rather complex. Wireless Sensor Networks have been used in these environments, but there is no standard way to take advantage of the benefits of new Internet of Things (IoT) environments. To deal with this, an IoT-based generic architecture for chemical parameter monitoring systems is proposed and applied to the development of an intelligent potassium sensing system, and this is described in detail in this paper. This sensing system provides fast and simple deployment, interference rejection, increased reliability, and easy application development. Therefore, in this paper, we propose a method that takes advantage of Cloud services by applying them to the development of a potassium smart sensing system, which is integrated into an IoT environment for use in water monitoring applications. The results obtained are in good agreement (correlation coefficient = 0.9942) with those of reference methods.Entities:
Keywords: Internet of Things; cloud services; in-line monitoring; ion-selective electrode; potassium determination; smart sensor; water analysis
Mesh:
Substances:
Year: 2022 PMID: 35161589 PMCID: PMC8839428 DOI: 10.3390/s22030842
Source DB: PubMed Journal: Sensors (Basel) ISSN: 1424-8220 Impact factor: 3.576
Figure 1IoT services used in Analytical Chemistry and the relationships between them.
Figure 2Potassium monitoring system.
Main features of the three Ion Selective Electrodes (ISEs) used.
| ISE | Membrane Preparation | Calibration | Correlation with Official | Nernstian Slope | Limit of Detection | Response | Drift |
|---|---|---|---|---|---|---|---|
| K+ | tetrahydrofuran solution of 4% benzo-15-crown-5 crown ether, 28% polyvinyl chloride, and 68% orto-nitrophenylphenylether (plasticizer). Inner electrode solution: 0.01 M KCl | KCl standard solutions | 0.9947 in the range 0.5–20.0 mg L−1 | 55 ± 4 | 0.4 | <10 | <0.5 |
| Na+ | 4% ionophore, 65% dioctylphthalate, 30% polyvinyl chloride (PVC), and 1% potassium tetrakis( | NaCl standard solutions | 0.9972 in the range 1.0–200.0 mg L−1 | 55 ± 5 | 0.5 | <10 | <0.4 |
| NH4+ | 400 mg of a mixture of 31% carboxylated polyvinylchloride, 4% nonactin, and 65% bis-(2-ethyl)hexyl sebacate in 5 mL of tetrahydrofurane (THF). | NH4Cl standard solutions | 0.9937 in the range 0.1–5.0 mg L−1 | 54 ± 5 | 0.02 | <5 | <0.4 |
a The official methods used are inductively coupled plasma–atomic emission spectrometry (ICP-AES) for Na+ and K+ and UV-V spectrophotometry for NH4+.
Figure 3FIWARE architecture.
Design of the experiment.
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Results of the linear regression.
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| −0.00038936 | −0.15672332 | 0.96977118 | 0.16375884 | |
| Regression standard error | 0.00015719 | 0.01283918 | 0.00191162 | 0.01755759 |
Linear regression parameters.
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| 0.99953069 |
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| 85,902.0567 |
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| 999.530693 |
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| 0.06227814 |
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| 121 |
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| 0.46930663 |
Results obtained in the in-line monitoring of K+ in a small-size dam.
| Sampling Point | [K+] mg L−1 (In-Line) a | [K+] mg L−1 (Reference Method) b |
|---|---|---|
| 1 | 2.3 | 2.4 |
| 2 | 4.0 | 4.2 |
| 3 | 2.1 | 2.1 |
| 4 | 3.5 | 3.4 |
| 5 | 3.9 | 3.8 |
| 6 | 5.1 | 4.9 |
| 7 | 4.7 | 4.7 |
| 8 | 4.8 | 4.7 |
a measured by the ISEs deployed at different points of the dam surface. b obtained off-line by inductively coupled plasma–atomic emission spectrometry (ICP-AES).