Chemometrics-assisted calibration transfer strategy for determination of three agrochemicals in environmental samples: Solving signal variation and maintaining second-order advantage
Introduction
Agrochemicals are profusely used in agriculture to increase production and improve the quality of plants and crops. It is necessary to monitor and quantify the levels of their residues in environmental samples as they can accumulate in the environment and show potentially detrimental effects on mammals and plants [1]. Thiabendazole (TBZ), a systemic benzimidazole fungicide, which is commonly used as a fungicide to prevent fruits such as pears, citrus and bananas from mould, rot, blight and stain, thus keeping their freshness before waxing step during storage [2]. Indole-3-acetic acid (IAA) and 1-Naphthylacetic acid (NAA) are two of the representatives of auxins widely used as plant growth regulators in agriculture, primarily in many kinds of fruit and vegetables [3,4]. Commonly, two or even more types of agrochemicals are used simultaneously in combination to obtain synergistic effects, requiring effective and sensitive methods for determining their residue levels in fruits and environmental samples including soils and sewage waters.
Methods developed to determine these agrochemical residues are mainly based on chromatographic and luminescent techniques [[5], [6], [7], [8], [9]]. However, chromatographic techniques usually involve large amounts of organic solvents consumption and long analysis time, making it uneconomic and less competitive to some extent. By contrast, luminescent techniques, such as fluorescence spectroscopy, are generally regarded as a green strategy for its simple, cheap, non-destructive and sensitive. Nevertheless, one of the main difficulties in the use of luminescent techniques in quantitative analysis is the resolution of overlapping signals, especially for multi-component mixtures, which require prior separation processes to reach the goal. Meanwhile, some efforts have been made to increase selectivity and achieve successful resolution by using synchronous fluorescence spectrometry (SFS) for qualitative and quantitative analysis [10,11].
Luckily, the combination of suitable chemometric tools along with excitation-emission matrix fluorescence may handle these troubles with good resolution and high selectivity. So far, chemometric multivariate calibration coupled with high order analytical instruments have been successfully applied in many fields, either for quantitative or qualitative purposes [[12], [13], [14], [15], [16], [17], [18]]. In multivariate calibration, the potential interferences in the complex samples can be modeled by chemometric algorithms and pure signals of target analytes can be extracted out accurately. Therefore, quantification can be achieved successfully even in the presence of unknown components, known as the famous “second-order advantage”.
An ideal state in chemometric analysis is that the multivariate models should be made to last a long time and “second-order advantage” can be maintained because much time and effort is necessary to develop them, e.g. a sufficient number of samples should be prepared and analyzed by reference methods [19]. It is particularly useful especially for long-term process analysis and quality control in environment and food analysis. Nevertheless, the signals of instrument may be changed when original instrument is replaced by a new one, or the analytical signals may be changed by using the same instrument but changing over time due to variations in spectrographic components (e.g., aging of xenon lamp) or in experimental conditions (e.g., temperature, humidity, operator) among others. The most direct way is to recalibrate for the new measurement conditions or to expand the original model for the new situation, which are rather costly and in conflict with principle of the green analytical chemistry.
Calibration transfer strategy may provide good compromise in the costly and analytical accuracy. It applies chemometric tools to find a mathematical transformation that makes the response of samples measured on the secondary conditions corrected to that obtained on the primary conditions so that the response signals collected from two different conditions/instruments resemble each other. One of the most widely used calibration transfer strategies is piecewise direct standardization (PDS) [20], which requires the selection of a subset of calibration samples from the primary situation and measure them on the secondary situation. So far, this strategy has been widely used in combination with NIR [21,22], electrochemical [23,24], Raman [25,26], UV–Vis [27,28] and fluorescence data [[29], [30], [31]]. At the same time, there are also several recent works dealing with the joint use of chemometric multivariate calibration and calibration transfer strategy. Gu et al. [32] firstly applied PDS strategy with ATLD algorithm to compensate for the signal instability of LC-MS data acquired from one instrument with different days. Recently, Montemurro et al. [31] presented a similar strategy that combined PDS with second-order PARAFAC algorithm to overcome the matrix effect and reduce analysis time for the determination of pirimiphos-methyl in maize grains.
Hence, the aim of this work was to develop a chemometric second-order calibration strategy named self-weighted alternating normalized residue fitting (SWANRF) for simultaneous determination of IAA, NAA and TBZ in complex environmental samples by using excitation-emission matrix fluorescence. Moreover, piecewise direct standardization (PDS) method was applied to compensate for the variations in the instrument responses on two process EEM fluorescence spectrophotometers of the same manufacturer. They are produced to be alike, but due to differences in the optical fibers used and inherent, small differences in the filters e.g. due to aging/bleaching, there is a clear distinction between the spectra the two spectrometers record [29]. The applicability of the proposed strategy was first verified using one set of simulated EEM fluorescence data that contains three components of interest and one uncalibrated interference, and one set of real EEM fluorescence data produced by three agrochemicals in soil and sewage samples. Both analytical figures of merit and statistical parameters including average recoveries and root-mean-square error of prediction were calculated to investigate the quantitative results obtained from the proposed strategy and that from the complete recalibration. To the best of knowledge, it is the first time that PDS and SWANRF are combined together for transferring and resolving EEM fluorescence signals measured on two instruments. A schematization of the global chemometric analysis flow is shown in Fig. 1.
Section snippets
Trilinear component model
For the type of EEM fluorescence data, a two-way matrix with the size of I excitation wavelength points and J emission wavelength points can be acquired for each analytical sample. Given K samples containing calibration and prediction samples, a three-way data array X (I × J × K) could be obtained by stacking them along the sample dimension. According to the theory of trilinear component model, the three-way array X can be expressed as:here xijk
Simulated EEM fluorescence data
A set of EEM fluorescence data containing 23 samples with four components was simulated to evaluate the performance of the developed strategy. Both excitation and emission profiles were generated by the Gaussian equation. The first 15 samples were used as a calibration set containing only three components of interest. The remaining 8 samples, served as a prediction set, contained three components of interest and an uncalibrated interference component. The simulated fluorescence peaks of four
Simulated EEM fluorescence data
Herein, the calibration transfer has been carried out from situation A to B, which simulates a calibration transfer of signal responses from different instruments. The objective of the standardization strategy is to get satisfactory analytical results with the significant reduction of experimental efforts, cost, and time for a full recalibration. To investigate the feasibility of the proposed strategy, two kinds of simulated EEM fluorescence data sets were created and divided into four possible
Conclusion
This work presented a chemometrics-assisted calibration transfer strategy to determine three agrochemicals in environmental samples by excitation-emission matrix fluorescence detection. With the aid of prominent “second-order advantage” provided by the SWANRF method, successful resolution together with satisfactory quantification results can be achieved, regardless of highly overlapped fluorescence signals of analytes and unknown interferences. Moreover, a standardization approach named PDS was
Declaration of competing interest
The authors declare that they have no conflict of interest.
Acknowledgments
The authors gratefully acknowledge the National Natural Science Foundation of China (Grant no. 21575039 and no. 21775039) and the Foundation for Innovative Research Groups of NSFC (Grant no. 21521063) for financial supports.
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2020, Microchemical JournalCitation Excerpt :Lozano et al. carried out the simultaneous determination of isoproturon, linuron, monuron and rimsulfuron in underground, tap water, and soil samples by using EEMs combined with U-PLS/RBL [135]. Sun et al. developed a second-order calibration method assisted EEMs strategy for simultaneous quantification of thiabendazole, indole-3-acetic acid and 1-naphthylacetic acid in complex soil and sewage samples [136]. In this work, the second-order calibration method effectively addressed the headaches of overlapping peaks and unknown interference and achieved successful resolution and acceptable quantitative results.