Abstract
Spraying a tertiary blend of the insecticides (hexythiazox, imidacloprid, and thiamethoxam), on tomato fruits, is a routine in agriculture-attentive countries. A simple green sample preparation technique was developed and applied to the field samples. Specific HP-TLC and RP-HPLC methodologies are established to estimate the residual insecticides and applied to the prepared field specimens. In the planner chromatographic methodology, methanol:chloroform:glacial acetic acid:triethyl amine (8.5:1.5:0.2:0.1, v/v) is recommended as a mobile system. The other one is columnar chromatography; acetonitrile: water (20:80, v/v), pH 2.8, is recommended as a mobile system. The validation parameters were examined following the ICH rules. The means percentages and standard deviations of the accuracy of the HP-TLC method for the determined compounds were 99.66 ± 0.974, 99.41 ± 0.950, and 99.89 ± 0.983, correspondingly. The values were 99.24 ± 0.921, 99.69 ± 0.681, and 99.20 ± 0.692, correspondingly, when they were determined by the RP-HPLC method. The relative standard deviation percentages of the methods’ repeatability and intermediate precision ranged from 0.389 to 0.920. Both methods were highly specific having resolution factors of ≥ 1.78 and selectivity factors of ≥ 1.71. They were applied to the field samples perfectly.
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Introduction
Pharmaceutical care does not matter only the medicines, but it considers any chemical or natural substance that may affect human health too. One of these substance categories is insecticides, especially those related to direct contact with our natural nutrition. The most form of close, common, and frequent exposure to insecticides is the ingestion of food contaminated by these dangerous chemicals. Fresh or processed tomatoes are the most common constituent in our dining tables. Not only is the estimation of residual insecticides critical in labs of official institutions in the health sector but also inlabs on exporting-importing boundaries between countries. That may reflect the hygienic and economic impact of establishing selective methods of monitoring for a specific blend of insecticides on certain field samples.
The development of specific methods of analysis for a mixture of little definite insecticides and/or fungicides is a new trend in residual assessment for food and environmental analysis1,2,3. The authors have been working consistently since early 2017 using this strategy starting with extensive studies concerning specific insecticide residues on cucumbers4,5. And here, we are following the same concern extending our work on a different blend of the insecticides6,7 and the concerned substances [hiexythiazox (HTX), imidacloprid (IDD), and thiamethoxam (TTM)] by spectrophotometric techniques8. In this work, the authors, superiorly, present more specific techniques using separating conditions and tools. The chromatographic analysis was suggested for the assessment of the considered blend constitutions which are used uniquely in a mixture form for the protection of tomatoes, in the Middle East area, the host of this research9. Worldwide, the official inspecting institutions contribute great responsiveness to the estimation of residual insecticides on field samples. In this work, the authors offer separation techniques for the detection of the residual insecticides (HXT, IDD & TTM) on tomato samples with simple and short procedures of sampling (sample preparation and extraction).
Chemical structures and molecular weights of the proposed compounds; hexythiazox, Imidacloprid, and thiamethoxam are illustrated in the PubChem10,11,12. The organic configuration of the substance's molecules is figured out in Figure S1. Some methods have been found to determine them individually13,14,15,16. No single method has been found for analysis of the studied blend in publication except a GC method, which makes a general estimation of a huge number of insecticide residues in different parts of the tomato plant17. But the proposed methods, superiorly, are more specific since they determine only the specific blend of insecticides used for tomatoes. Also, we followed more economical sample preparation as simple tools and less complicated extraction procedures were used. The proposed RP-HPLC is more accessible in application than the published GC method due to its wide availability in general and official laboratories. As well, the advantage of HP-TLC over the published method is its simplicity and cost cut-off. The proposed methods are simpler, faster, and more economical than the published works. That makes them better selections and significantly valuable in quality control laboratories of developing countries.
The novelty of the work is hidden in the way the analyst prepared the pre-analysis samples "peeling off the spray-exposed surface is only the samples without interfering of the whole matrix". This way is faster and greener than the traditional QuEChERS method. Supporting the greenness and financial cut concepts of this work, the proposed sample preparation steps consume much lesser volumes of organic solvents than those used in liquid–liquid extraction and they cost lesser than the solid phase extraction. All that makes the proposed sampling and assays more recommended for local governmental inspection and guarantee.
The two main international organizations that control and regulate insecticide residue analysis18,19, describe methods of the data validation intended for proving obedience to upper residual allowance or control of the customer contact with insecticides. One of the main criteria is the matrix effect. Upon studying the European Commission validation set and comparing it to the corresponding items in ICH validation rules, we have found many similarities. Considering the European Commission statements in [C25] and [C26], Hegazy et al. used the standard addition technique in methods of validation procedures and collected field samples according to SANTE document guidelines19.
Methodology
Apparatus
CAMAG TLC scanner, High-performed TLC Alum sheets plated with 60 F254 (0.25 mm) (Merck, DE), and R201 Shang. Shen. Biot. Lim. Co. Camag-Linomat IV applicator were instrumentations in HP-TLC methodology.
1200 infinity series LC (Agilent Technologies), 1260 infinity UV–VIS detector (Agilent Technologies), and Eclipse plus C8 column (15, 4.6 and 5 µm) were instrumentations in RP-HPLC methodology.
Authentic powders
HTX, IDD, and TTM (99.10%, 99.10% and 99.30%) were supplied via Sigma, EG.
Trade powders
Macomite® (HTX; 1:10, Bch. # 1019), Imdamex® (IDD; 7: 10, Bch. # 3018721), and Pelxam® (TTM; 2.5: 10, Bch. # 1625) were supplied via producers; Nipon Sod Co., Ltd (JP), Agrsmart Ind. (Behera, EG) and Barat Insec., Ltd (IN), respectively.
Solvents
Methanol, acetonitrile, and acetone of HPLC grade were supplied from Sigma Chemie (GmbH, DE). Chloroform, glacial acetic acid, orthophosphoric acid, sod. sulfate and triethyl amine (analytical grade) were obtained from El-Nasr Pharm. Chem. Co. (EG).
Sampling
Samples of standard solutions
Standard solutions of HTX, IDD, and TTM in concentrations of (103 µg/mL) were prepared, separately, and diluted to final concentrations of (102 µg/mL) in methanol.
Macomite®, Imdamex®, and Pelxam® stock solutions (103 µg/mL) and working solutions (102 µg/mL) were prepared in methanol.
Samples for method validation
Successions of sequential concentration of HTX, IDD, and TTM solutions, in concentrations of 0.05–0.31, 0.20–2.0, and 0.1–1.0 µg/mL, correspondingly, were prepared.
Field samples
A bushel of tomatoes (≈ 10 kg) was picked up from the investigator's private land at El-Fyoum governorate, EG, during the cold weather period (≈ 20 °C). It was divided into four sets of 3 kg/set. The insecticides blend was applied on only three sets, complying with the SANTE document rules19, and the left set was treated as a control. Each set was re-divided into three replicates each of 1 kg.
Preparation of the field samples
Simply, the fruits of tomatoes were peeled carefully via a pelamatic fruit peeler then the peels were chopped, thoroughly. In a centrifuge tube, the sample of peel pieces was shaken with acetonitrile (20 mL), thoroughly, and re-shaken after the addition of sod. sulfate (5 g), then centrifuged. The quantitatively collected extract was concentrated to a few milliliters under vacuum at room temperature, then diluted with acetonitrile to get 5 mL, accurately.
Method validation
Sequential solutions of HTX (0.05–0.31 µg/mL), IDD (0.20–2.0 µg/mL), and TTM (0.1–1.0 µg/mL) were applied for achievement of HP-TLC and RP-HPLC methods linearity. The mixture solutions of them were applied to prove the precision of the methods. Limits of detection and quantitation were estimated. Both methods were applied to the trade solutions and field samples for confirmation of their applicability.
Results and discussion
HP-TLC methodology optimization
Many mobile systems were eluted to succeed in the complete separation resolution for the ternary mixture. Elusion of methanol:chloroform (2:8, v/v) and hexane:methanol (8:2, v/v) binary solvent mixture gave lousy separation. A tertiary solvent mixture of methanol:chloroform:acetic acid (8:2:0.2 v/v) gave better break and tailed peaks. The replacement of acetic acid with triethyl amine in the last mixture gave perfect peaks' break. The mobile system, methanol:glacial acetic acid:chloroform:triethyl amine (8.5:0.2:1.5:0.1) is selected as the method's mobile phase.
Numerous detection wavelengths were selected; detection at 220 nm gave maximum sensitivity. To minimize solvent volatility and increase homogeneity, the elusion jar was saturated with the developing system for 30 min. Scored Rf values were found at 0.15, 0.35, and 0.60, correspondingly to, HTX, IDD, and TTM, as shown in Fig. 1.
RP-HPLC methodology optimization
Several criteria were employed to attain a superlative separation for the ternary mixture as well as detection λ wavelength and flow rate, using the C8 column. Mixtures of methanol:water in ratios 700:300 and 500:500 and methanol:0.2% acetic acid solution in ratio 800:200 were eluted but the uncompleted separation was obtained. The mixture of acetonitrile:water in a ratio of 200:800 improved the separation slightly. Adjustment of the mixture pH 2.8 with orthophosphoric acid resulted in great improvement of the peaks' resolution and well-formed peaks with no tailing. Detection of peaks at 230 nm gave a maximum sensitivity and frequently the lowest LOQ and LOD. Many flow rates were tuned; 1 mL min−1 produced a better resolution in a fast run. Values of 2.129, 4.167, and 7.001 min were the retention times of TTM, IDD, and HTX, respectively, as illustrated in Fig. 2. Table 1 showed the regression equation and linearity parameters for both methods.
Methodology validity
The validity of both methods is verified by the following ICH rules20.
Linearity, accuracy, precision, LOD, LOQ, and specificity
After plotting the calibration curves and calculating regression equations for the concerning compounds, each method's linearity for determining the compound mixture was approved. The recovery % of blind authentic insecticide samples had been assessed and ranges of the concentration had been determined to prove accuracy. The means percentages and standard deviations of the accuracy of the HP-TLC method for the determined compounds were 99.66 ± 0.974, 99.41 ± 0.950, and 99.89 ± 0.983, correspondingly. The values were 99.24 ± 0.921, 99.69 ± 0.681, and 99.20 ± 0.692, respectively, when they were determined by the RP-HPLC method. The precision of the methods was proved by calculating the repeatability and intermediate precision values. The relative standard deviation percentages of the methods’ repeatability and intermediate precision ranged from 0.389 to 0.920. Values of the limit of detection (LOD) and limit of quantitation (LOQ) were calculated for both methods by dividing the standard deviation of the residual concentration over the slope of the calibration line of every compound in the detection ranges. LOD values of the HP-TLC and RP-HPLC methods for the concerned drugs were (0.33, 0.65, 0.09) and (0.03, 0.06, 0.01), respectively. LOQ values of them for the drugs were (0.98, 1.96, 0.28) and (0.09, 0.19, 0.04), correspondingly.
All validity parameters were illustrated in Table 1. Methods specificity was proved via the determination of R% for each compound as illustrated in the table.
Methods robustness
Minor changes in the mobile system content and/or saturation time were tested in the HP-TLC methodology. Also, changes in the volume of orthophosphoric acid and/or flow rates were tested for the RP-HPLC methodology. Robustness (%RSD) values ranged from 0.296 to 0.608 for both methods. No remarked effects on the retention times values, the symmetry, and the area of the peaks, Table 1.
Systems suitability
Peak asymmetry was measured and other parameters, like selectivity factor (α) and resolution (Rs), were calculated to evaluate the methods' system suitability. Perfect results were attained and shown in Table 2. Both methods had resolution factors of ≥ 1.78 and selectivity factors of ≥ 1.71.
Methods applicability to commercial formulations
Acceptable recovery percentages were attained upon the application of the methods to the trade sample, Maccomite® Powder, Imidamex®, and Pelexam®. The method of HP-TLC gives R%; of 99.66, 99.24 and 99.41, respectively, whereas the RP-HPLC method gives R%; of 99.69, 99.89 and 99.20, respectively (Table 3).
Matrix effect and application to field sample
Analysis of the field samples showed adequate values of the insecticide residues that follow the acclaimed quantity for human health and plant yield (20:22), results were listed in Table S1. The proposed technique of the field sample preparation offered in this research was related to using just the superficial part of the sprayed tomatoes. So, only the peel pieces were introduced in field sampling. A claim of the standard addition to examining the matrix effect was done and the results were illustrated in Table 4.
Statistical analysis
A comparative statistical analysis of the outcomes attained by the proposed methods for the analysis of the pure samples of HTX, IDD, and TTM and those attained by the published methods17 was carried out. It showed that there were insignificant differences between them, Table 5. Student’s t-test ranged from 0.02 to 1.51 and the values of the F-test varied from 1.18 to 2.09. But the suggested methods had significant specificity; they determined only the insecticides which were applied to the tomato fruits, definitely. Whereas, the published GC method determined 186 insecticides.
Greenness and economical efficacy of the samples preparation
The unique technique through which the analyst followed in the crop sample preparation affected greatly the volume used in the sprayed insecticides. The analyst peeled only the sprayed parts of the tomato fruits and then used them in extraction procedures instead of using the whole fruits. That had a great factor in diminishing the hazardous effect of the organic solvent waste on the environment and spending money on purchasing excessive amounts of extraction materials.
Conclusion
The proposed methodologies, HP-TLC and RP-HPLC, can determine the insecticides' residues in the pure forms and the commercial formulations, accurately. Also, they can be applied to natural specimens. The suggested HP-TLC method has the advantage of low-cost and simple procedures. Whereas, with RP-HPLC one has the privilege of high sensitivity and speediness. Generally, the whole procedures starting from the preparation of the samples to the final process of the determination obey the current international greenness trend.
Conclusively, the developed chromatographic methods can be used for monitoring residual insecticides on tomatoes without the interference of the matrix effect and analyzing commercial formulations without the interference of excipients by green and economic procedures. Statement of Guideline Tomato fruits were cultivated and collected regarding local guidelines of the Egyptian Ministry of Agriculture and Land Reclamation21.
Data availability
All data generated or analyzed during this study are included in this published article (and its supplementary information files).
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Acknowledgements
The authors are thankful to the Egyptian Ministry of Higher Education and Scientific Research, the funder of this research, for its generous financial support. Also, they appreciated Dr. Khaled Asker, a professor in Agriculture Faculty, at Beni Suef University, for his valuable advice.
Funding
Open access funding provided by The Science, Technology & Innovation Funding Authority (STDF) in cooperation with The Egyptian Knowledge Bank (EKB).
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A.H., corresponding author and project supervisor, wrote the main manuscript text, prepared the figures and tables, transcribed the files related to the article submission, and submitted the article. Whereas, H.M., boss of the project, supervised the whole work and put the main frame of the work. M.E. performed the practical part of the work and prepared the primitive data and outcomes. N.A. suggested the main idea and was the main project’s coordinator. Lastly, R.A. revised the whole manuscript and was one of the main work supervisors.
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Hegazy, A.M., Mahmoud, H.M., Elsayed, M.A. et al. Applying novel economic simple green sample preparation procedures on natural and industrial specimens for chromatographic determination of insecticidal residues. Sci Rep 13, 7209 (2023). https://doi.org/10.1038/s41598-023-33421-7
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DOI: https://doi.org/10.1038/s41598-023-33421-7
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