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Article

Quartz Crystal Nanobalance in Conjunction with Principal Component Analysis for Identification of Volatile Organic Compounds

by
Abdolreza Mirmohseni
1,* and
Kobra Rostamizadeh
1
1
Polymer Research Technology Laboratory, Department of Applied Chemistry, Faculty of Chemistry, University of Tabriz, Iran
2
Research Center for Pharmaceutical Nanotechnology, Tabriz University of Medical Science, Tabriz, Iran
*
Author to whom correspondence should be addressed.
Sensors 2006, 6(4), 324-334; https://doi.org/10.3390/s6040324
Submission received: 6 July 2005 / Accepted: 4 January 2006 / Published: 7 April 2006

Abstract

:
Quartz crystal nanobalance (QCN) sensors are considered as powerful mass-sensitive sensors to determine materials in the sub-nanogram level. In this study, a single piezoelectric quartz crystal nanobalance modified with polystyrene was employed to detect benzene, toluene, ethylbenzene and xylene (BTEX compounds). The frequency shift of the QCN sensor was found to be linear against the BTEX compound concentrations in the range about 1-45 mg l-1. The correlation coefficients for benzene, toluene, ethylbenzene, and xylene were 0.991, 0.9977, 0.9946 and 0.9971, respectively. The principal component analysis was also utilized to process the frequency response data of the single piezoelectric crystal at different times, considering to the different adsorption-desorption dynamics of BTEX compounds. Using principal component analysis, it was found that over 90% of the data variance could still be explained by use of two principal components (PC1 and PC2). Subsequently, the successful identification of benzene and toluene was possible through the principal component analysis of the transient responses of the polystyrene modified QCN sensor. The results showed that the polystyrene-modified QCN had favorable identification and quantification performances for the BTEX compounds.

Introduction

Quartz crystal nanobalance (QCN) sensors are considered as powerful mass-sensitive sensors to determine materials in the sub-nanogram level. Polymers which play a key role in a variety of fields, including chemical sensors [1], membrane-separation technology [2] and solid-phase extraction techniques [3] have gained wide theoretical and practical applications in the area of sensors as well. In the last few years, there has been an increasing amount of attention paid to the application of polymer-coated quartz crystal nanobalance (QCN) sensors [4-6]. The QCN comprises a thin vibrating AT-cut quartz wafer sandwiched between two metal excitation electrodes. When a small amount of mass is adsorbed at the quartz electrode surface, the frequency of the quartz is changed. Sauerbrey's equation is used to relate the frequency change (Δf) to the mass loading (Δm):
Δ m = [ A ( ρ q μ q ) 1 / 2 / 2 F 0 2 ] Δ F
where F0 is the fundamental resonant frequency of the unloaded quartz crystal (10 MHz), A is the electrode area (0.21 cm2), ρq is the density of quartz (2.65 g cm-3) and μq is the shear modulus of quartz (2.95*1011 dyn cm-2). With these constants, we obtain:
Δ m ( n g ) = 0.926 Δ F ( H z )
When the surface of a quartz crystal electrode is coated by a polymer capable of interaction with the environment of interest, a sensor sensitive to this component can be constructed. The performance characteristics of the QCN sensor (such as selectivity, response time and reversibility) will depend on the chemical nature and physical properties of the polymeric coating.
Polymer coated quartz crystals have been studied as sensors for various gases [7-9]. For the development of a chemical sensor, selective, sensitive and stable sensing materials have to be found. Unfortunately, the construction of an entirely selective chemical sensor is almost unrealizable, since along with the analyte, other compounds usually interfere. As a matter of fact, the major drawback of the polymer-modified QCN sensors is a lack of selectivity, since there is no discrimination between the sources of the mass changes. Using pattern recognition techniques is the key of the data processing of the signals of a non-selective sensor. In this regard, the characteristic information contents of the signal have to be recorded. Different chemometric tools could be applied for this purpose. Fuzzy clustering [10], partial least squares (PLS) [11,12], Principal Component Analysis (PCA) [13,14] and Artificial Neural Network (ANN) [14,15] have been widely used for the classification of analytes. In recent years, considerable interest has risen on the use of quartz crystals as sensors in conjunction with associated pattern recognition techniques in distinguishing various kinds of compounds.
Polystyrene is a low priced and widely available material. Besides, polystyrene is a hard and glassy polymer hence, it neither generates a significant damping nor does it show significant viscoelastic contributions to the frequency shift of the quartz even at higher coating thickness. We developed a method of a thin polystyrene-coated QCN sensor for the determination of benzene, toluene, ethylbenzene and xylene (BTEX compounds).

Experimental

Reagents and materials

Benzene, toluene, ethylbenzene and xylene (BTEX) were all purchased from Merck (Germany) and used without any further purification. Polystyrene was supplied by Tabriz Petrochemical Co.

Instrumentation

Ten megahertz AT-cut quartz crystals with gold electrodes on both sides were purchased from International Crystal Manufacturer (ICM, Oklahoma, USA). A home-made QCN apparatus was used for frequency measurements as shown in Figure 1. The oscillator circuit used was based on that designed based on Bruckenstein and Shay system which was modified by A. Mirmohseni and G.G. Wallace [16-18]. However, some modification of the original design was also carried out to improve the mass sensitivity and stability.

Procedures

All measurements were carried out in a glass cell with an internal volume of 38 ml. Hamilton microliter syringes (Hamilton Bonaduz AG Switzerland) were used for analyte injection and dispensing polymer solution cast on the gold electrode of the quartz crystal. A certain volume of analyte was injected into the cell and the frequency shift of crystal was recorded. The concentration of injected analyte in the cell was calculated in mg l−1 using its density, purity percent and volume [19]. The difference between the highest and the lowest value was used to plot calibration curve for each analyte. A flow of air was purged through the cell to desorb analyte and recover the electrode. All measurements were carried out at room temperature (25 °C).

Polymer coating

A solution casting method was used to cast the polymer film on the top of the quartz crystal electrode. The gold coated quartz electrode was coated using a 3 μl solution of polystyrene in chloroform (various concentrations). The film thickness varied corresponding to the polymer solution concentration. In order to regenerate the electrode, the polymeric coating was dissolved in chloroform and dried by acetone.

Data processing

The principal component analysis (PCA) method is widely used to classify compounds and mixtures. PCA contains an orthogonalization procedure such as singular-value decomposition (SVD) that decomposes the primary data matrix by projecting the multi-dimensional dataset onto new coordinates base formed by the orthogonal directions with data maximum variance. The data matrix consists of a number of experiments, each consisting of a number of variables. The eigenvectors of the data matrix are called principal components and they are uncorrelated among them. Sensor signals can be expressed as the linear combination of eigenvectors. Generally, the k-th principal component, PCk, is a linear combination of the n response vectors Xn,j for the analyte under study, where n is the number of the variables, j indicates different samples and the coefficients (an,k) are called loading (Eq. 3).
P C k = n = 1 n a n , k X n , j
The magnitude of each eigenvector is expressed by its own eigenvalue, which gives a measure of the variance related to that principal component. The variance is related to the quantity of information which is supplied by the component. By elimination of the less important eigenvectors, it is possible to achieve fewer vectors without any considerable information loss. So, during data processing, the results are transformed in a plane or in a space of the first two or three eigenvectors. The coordinates of the data in the new base are called their score. The scores plot is usually used for the classification of the data clusters. In this study, the input data of the primary matrix are the normalized and standardized response of the QCN sensor at various time windows.
PCA calculations used a singular-value decomposition algorithm and were performed with the MATLAB software version 6.5. The operating system was Microsoft Windows XP.

Results and discussion

Sensors have to fulfill many requirements such as selectivity, sensitivity and reversibility in the working range. For this mean, construction of a QCN sensor having a good character to analysis BTEX compounds was investigated.

Development and amount of coating material

First, the optimum amount of polystyrene that have to be coated on the QCN surface was investigated. The coating thickness depends on the polymer concentration. The thickness of coating was estimated by the difference between the frequencies of the bare crystal, and the coated crystal after solvent evaporation.
The QCN was coated with 3 μl of diverse concentration of polystyrene solutions. The QCN-coated with different amounts of polystyrene were exposed to 15 mg L-1 toluene. Figure 2 shows the responses of the QCN coated with different amounts of polystyrene. The QCN crystal with a thicker polystyrene coating exhibited a larger frequency response for the same concentration of toluene (15 mg l-1) below 0.5%w/v, but above 0.5%w/v the response tended to level off. This behavior implies that there is a limit of the adsorption of gas molecules in a small area of adsorbent. On the other hand, the response time obtained for the crystal having different thickness of polystyrene showed that the QCN crystal with a thicker coating exhibit a high response time for the same concentration of toluene (Figure 3). Besides, too much coating would disturb the resonance stability and occasionally leads to a failure in the quartz crystal oscillation. Based on these results, we decided that the QCN in all subsequent experiments should be modified using 3 μl of 0.5%w/v polystyrene solution (with approximately 104 nm thickness). So, it had a significant response and its response time was less than 16 min.

Sensor response

Typical QCN sensor responses over the measuring time for toluene, with a concentration of 15 mg l-1, are illustrated in Figure 4. The negative frequency shifts arise from the analyte exposure. A plateau is reached after a period of time, indicating a maximum adsorption onto the QCN surface.
After turning back to the purge cycle, the frequency goes back to a value approximating the basic line. k is considered as a value for reversibility of the sensor response [19],
k = t 90 , desorp t 90 , sorp
where t90 is the Δf-value at 90% after starting the adsorption or desorption process. For an ideal fast reversible response, k must be 1. Table 1 shows the reversibility of the polystyrene-coated QCN sensor at two different concentrations of analytes. It can be concluded that the polystyrene shows a good reversibility with all analytes. This implies that the polystyrene-coated QCN crystal sensor can be repeatedly reused for the detection of examined organic vapors.
Figure 5 shows the frequency change Δf as a function of time for different concentrations of toluene, indicating that Δf increases monotonically with increasing gas concentration. This result strongly suggests that it is possible to prepare the gas sensor using a polystyrene-coated QCN for BTEX compounds. The frequency shifts used for plotting the calibration curves corresponded to the difference between the highest and the lowest values observed. Plots of the frequency shifts as a function of BTEX compounds concentration are shown in Figure 6. As shown in Figure 6, in the range of about 1-45 mg l-1 there was a good linear relationship. The value of 0.9975, 0.9977, 0.9946 and 0.9971 was calculated for correlation coefficients of benzene, toluene, ethylbenzene and xylene, respectively.
The determination of the minimal concentration level of analytes that could be registered with the designed QCN sensor has been carried out. The frequency stability of an oscillator consists in its capacity to maintain the frequency of the output signal constant with time. The study showed that the base-line noise of the applied system was 1 Hz. The frequency-change limit necessary to detect an analyte is set at a signal-to-noise ratio of 3, three times the base line noise. Thus, the lower limit detection (LLD) of the QCN for BTEX was 1 mg l-1.
The sensitivity of each polymer towards each BTEX gas is expressed as the slope of the calibration curve. The bar graph (Figure 7) illustrates the sensivity of the QCN sensors towards the examined analytes. As expected the sensors showed different sensitivities to the BTEX gases.
The sensor coated with polystyrene was alternatively exposed four times to the presence of BTEX compounds at the concentrations of 9.0 mg l-1. The relative standard deviations (RSDs) for BTEX compounds were 10.54%, 5.84%, 10.66% and 10.30%, respectively.

Identification of gases using principal component analysis

In this study, we concentrated on finding a gas sensor that also possesses an excellent selectivity for BTEX compounds. There is generally no applied rule to find selective sensing materials for the development of QCN sensors. To establish the ability of the polystyrene-coated QCN to discriminate between the BTEX gases a principal component analysis (PCA) was carried out. It can be seen from Figure 8 that the shape of the transient responses of sensor is different from gas to gas. So, in order to distinguish gases using principal component pattern recognition analysis, we focused our attention to the different shape of each transient response.
The input variable used is the frequency of the crystal at every 20 s for 20 min after gas injection in the cell. All compounds were exposed to the cell at least twice and for four different concentrations including 15.2, 18.3, 21.3 and 24.4. To account for the different response magnitudes from the different concentrations, the responses were normalized and standardized to give a response vector of unity in each case, and subjected to PCA.
The results of the principal component analysis indicated that most of the information close to 90% is provided by PC1 and PC2. Figure 9 is the plot of the PCA data for different concentrations of BTEX compounds. It is clear that an easy discrimination of the toluene and benzene was possible because they were specimen data clustered in two different regions, independent of their concentrations. In the case of ethylbenzene and xylene it is impossible to discrimination them. This result is because of the similar response profile of the polystyrene-coated QCN towards xylene and ethylbenzene (Figure 8).

Conclusions

A sensor was constructed based on a quartz crystal nanobalance modified with a thin layer of polystyrene to detect BTEX compounds in atmospheric media. Frequency shifts versus concentration of analytes exhibited satisfactory linear correlation within the range about 1-45 mg l−1. The results showed that the sensor is sensitive enough to detect analytes. Principal component analysis was performed using frequency response of the sensor every 20 second as input data. The results showed that benzene and toluene were specimen data clustered in two different regions, independent of their concentrations. Subsequently, they could successfully recognized by the polystyrene-coated QCN sensor. The result meaned that the polystyrene modified QCN can be utilized to determine BTEX compounds in atmospheric media.

Acknowledgments

We are most grateful the continuing financial support of this research project by the University of Tabriz.

References

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Figure 1. Schematic diagram of the experimental set-up for QCN sensor. 1. PC, 2. Frequency counter, 3. Electronic circuit, 4. Quartz crystal electrode, 5. Syringe, 6. Desorbing gas.
Figure 1. Schematic diagram of the experimental set-up for QCN sensor. 1. PC, 2. Frequency counter, 3. Electronic circuit, 4. Quartz crystal electrode, 5. Syringe, 6. Desorbing gas.
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Figure 2. The effect of polymer concentration of casting solution (polymer thickness) on frequency changes of polystyrene-modified quartz crystal electrode exposed to 15 mg l−1 toluene.
Figure 2. The effect of polymer concentration of casting solution (polymer thickness) on frequency changes of polystyrene-modified quartz crystal electrode exposed to 15 mg l−1 toluene.
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Figure 3. The effect of polymer concentration of casting solution (polymer thickness) on response time of polystyrene-modified quartz crystal electrode exposed to 15 mg l−1 toluene.
Figure 3. The effect of polymer concentration of casting solution (polymer thickness) on response time of polystyrene-modified quartz crystal electrode exposed to 15 mg l−1 toluene.
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Figure 4. Typical frequency changes of the polystyrene-modified quartz crystal electrode exposed to 15 mg l−1 toluene in air: (a) sample injection; (b) sample desorption by purging air through the cell. Polymer cast from a 0.5% (w/v) of polystyrene/chloroform solution.
Figure 4. Typical frequency changes of the polystyrene-modified quartz crystal electrode exposed to 15 mg l−1 toluene in air: (a) sample injection; (b) sample desorption by purging air through the cell. Polymer cast from a 0.5% (w/v) of polystyrene/chloroform solution.
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Figure 5. Frequency changes of polystyrene-modified quartz crystal electrode as a function of time exposed to various concentrations of toluene: (a) 0.91 mg l−1, (b) 9.07 mg l−1, (c) 18.14 mg l−1, (d) 27.21 mg l−1, (e) 36.28 mg l−1, (f) 45.35 mg l−1. Polymer cast from a 0.5% (w/v) of polystyrene / chloroform solution.
Figure 5. Frequency changes of polystyrene-modified quartz crystal electrode as a function of time exposed to various concentrations of toluene: (a) 0.91 mg l−1, (b) 9.07 mg l−1, (c) 18.14 mg l−1, (d) 27.21 mg l−1, (e) 36.28 mg l−1, (f) 45.35 mg l−1. Polymer cast from a 0.5% (w/v) of polystyrene / chloroform solution.
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Figure 6. Calibration curves for determination of benzene (▪), toluene (●), ethylbenzene (▲) and xylene (×) using polystyrene-coated quartz crystal electrode. Polymer cast from a 0.5% (w/v) of polystyrene / chloroform solution.
Figure 6. Calibration curves for determination of benzene (▪), toluene (●), ethylbenzene (▲) and xylene (×) using polystyrene-coated quartz crystal electrode. Polymer cast from a 0.5% (w/v) of polystyrene / chloroform solution.
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Figure 7. Sensivity of polystyrene-coated QCN towards BTEX compounds.
Figure 7. Sensivity of polystyrene-coated QCN towards BTEX compounds.
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Figure 8. Transient frequency responses of polystyrene-coated QCN sensor on detecting BTEX compounds. a) benzene, b) toluene, c) ethylbenzene, d) xylene.
Figure 8. Transient frequency responses of polystyrene-coated QCN sensor on detecting BTEX compounds. a) benzene, b) toluene, c) ethylbenzene, d) xylene.
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Figure 9. Identification of benzene (▪), toluene (Δ), ethylbenzene (▲), xylene (○) using PCA.
Figure 9. Identification of benzene (▪), toluene (Δ), ethylbenzene (▲), xylene (○) using PCA.
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Table 1. Reversibility of polystyrene-coated QCN toward analytes.
Table 1. Reversibility of polystyrene-coated QCN toward analytes.
k (15 mg l-1)k (21 mg l-1)
Benzene0.99940.9984
Toluene0.99639.9943
Ethylbenzene0.99940.9985
Xylene0.99880.99807

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Mirmohseni, A.; Rostamizadeh, K. Quartz Crystal Nanobalance in Conjunction with Principal Component Analysis for Identification of Volatile Organic Compounds. Sensors 2006, 6, 324-334. https://doi.org/10.3390/s6040324

AMA Style

Mirmohseni A, Rostamizadeh K. Quartz Crystal Nanobalance in Conjunction with Principal Component Analysis for Identification of Volatile Organic Compounds. Sensors. 2006; 6(4):324-334. https://doi.org/10.3390/s6040324

Chicago/Turabian Style

Mirmohseni, Abdolreza, and Kobra Rostamizadeh. 2006. "Quartz Crystal Nanobalance in Conjunction with Principal Component Analysis for Identification of Volatile Organic Compounds" Sensors 6, no. 4: 324-334. https://doi.org/10.3390/s6040324

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