Next Article in Journal
Study on the Characteristics of Vacuum-Bagged Fermentation of Apo Pickle and Visualization Array Analysis of the Fermentation Process
Previous Article in Journal
Analysis of Volatile Profile and Aromatic Characteristics of Raw Pu-erh Tea during Storage Based on GC-MS and Odor Activity Value
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Assessment of Toxic Pyrrolizidine and Tropane Alkaloids in Herbal Teas and Culinary Herbs Using LC-Q-ToF/MS

by
Zinar Pinar Gumus
Central Research Test and Analysis Laboratory Application and Research Center (EGE-MATAL), Ege University, 35100 Izmir, Turkey
Foods 2023, 12(19), 3572; https://doi.org/10.3390/foods12193572
Submission received: 23 August 2023 / Revised: 20 September 2023 / Accepted: 22 September 2023 / Published: 26 September 2023
(This article belongs to the Section Food Analytical Methods)

Abstract

:
Pyrrolizidine alkaloids are secondary metabolites produced by plants as a defense against insects. These can cause acute or chronic toxicity in humans. Therefore, avoiding potential poisoning from the consumption of tea and culinary plants contaminated with pyrrolizidine alkaloids (PAs), pyrrolizidine alkaloids N-oxides (PANOs), and tropane alkaloids (TAs) is important for human health and food safety. Therefore, it is important to determine the levels of these substances with reliable and highly accurate methods. In this study, the PAs, PANOs, and TAs in herbal teas and culinary herbs sold in Turkish markets were identified and their levels were determined. Thus, the general profiles of herbal teas and culinary herbs in Turkey were revealed, and the compliance of the total amounts of PA and TA with the regulations was examined. The identification and quantification of 25 PAs and N-oxides and 2 TAs (atropine and scopolamine) in the samples was performed with a liquid chromatography-quadrupole time-of-flight tandem mass spectrometer (LC-Q-ToF/MS). At least a few of these substances were detected in all of the tested herbal teas and culinary herbs. The total contents of the black tea, green tea, mixed tea, flavored tea, chamomile tea, sage tea, linden tea, fennel tea, rosehip tea, peppermint, and thyme samples ranged from 4.6 ng g−1 to 1054.5 ng g−1. The results obtained shed light on the importance of analyzing the total dehydro PA, PANO, and TA amounts in plant-based products consumed in diets with sensitive and accurate methods, and they highlight the necessity of performing these analyses routinely in terms of food safety.

Graphical Abstract

1. Introduction

Pyrrolizidine alkaloids (PAs) are secondary plant metabolites that are naturally biosynthesized by angiosperms through defense mechanisms against herbivorous insects and pests. PAs and their N-oxides are a diverse class of secondary metabolites known as hepatotoxins in animals and humans. PAs are a class of phytotoxins that occur in an estimated 3% of flowering plants worldwide. More than 660 individual PAs and PANOs have been structurally characterized, and three plant families (Asteraceae, Boraginaceae, and Fabaceae) are among the most important sources of these toxins [1,2]. PA poisoning is caused by the consumption of herbal products containing these alkaloids for medicinal purposes or as culinary herbs. The pollution of plants with PAs, PANOs, and TAs, which are potentially harmful and toxic for humans and animals, can occur in different ways. Accidental or unintentional co-harvesting can be cited as the main source of plant contamination. Mixing the leaves of plants containing PAs with medicinal herbs or tea leaves and mixing the seeds of cereals with the seeds of plants containing PAs can be counted among other contamination pathways [3,4,5]. Beehive products (e.g., honey, royal jelly, and pollen food supplements) can naturally become contaminated with PAs through flowers, nectars, and pollen contents. It has been found that nectar from PA-diff or TA-producing plants is the main source of contamination of beehive products, and pollen from these flowers can additionally increase PA loads [6,7,8]. Animals may be fed with contaminated animal feed and plants. Thus, animal products (e.g., eggs, milk, cheese, and meat) can also be contaminated with Pas. Therefore, animal products may contain low levels of PAs [7,8,9,10]. In Hama and Strobel’s studies, it was reported that in regions with large populations of PA-producing plants, the surrounding soils and surface waters are vulnerable to PA pollution, and PAs can be transported from fields to surface waters by rain. With these studies, the importance of monitoring PAs in environmental samples has also been demonstrated [11,12].
Toxic PAs can cause liver cirrhosis and liver failure, pulmonary hypertension, cardiac hypertrophy, renal degeneration, carcinogenicity, and genotoxicity, which can be fatal [13,14,15,16,17]. Due to the nature of the plant materials, some teas may contain high amounts of PAs. In addition, teas can be contaminated with PAs from various plants (weeds) during growing and harvesting periods [18,19]. Medicinal preparations and teas can be important sources of human exposure to related pollutants as there may be poisonings and diseases caused by the consumption of medicinal preparations and teas prepared with PA-containing plants [19,20]. For livestock and human health reasons, as well as for food and feed safety, relevant PA/PANO and large PA/PANO quantities should be monitored comprehensively. Even in small amounts, they can cause toxic effects as a result of continuous exposure. Therefore, some of the European risk assessment bodies have made recommendations regarding daily intake to limit PA intake. The UK Committee on the Toxicity of Food Consumables and Environmental Chemicals and the German Federal Institute for Risk Assessment have recommended a maximum tolerable daily intake of 0.007 µg dehydro PA/kg body weight (bw). The Austrian Health and Food Safety agency does not allow any PA residues in final food products [21,22]. There is a need for regulations and standard methods for all countries for determining the allowable amounts of PAs/PANOs.
Tropane alkaloids (TAs) are an additional group of hazardous alkaloids that have been found to contaminate food and feed products. They are naturally occurring secondary metabolites of various plant families, including Brassicaceae, Solanaceae, and Erythroxylaceae. The most common alkaloids in TA-producing plants are naturally occurring (−)-hyoscyamine and (−)-scopolamine. Atropine, on the other hand, is a racemic mixture of (−)-hyoscyamine and (+)-hyoscyamine produced during the purification process of (−)-hyoscyamine. The wide distribution of TA-producing weeds in temperate and tropical regions worldwide can cause the occasional contamination of agricultural crops. It was reported by the EFSA CONTAM panel in 2013 that TAs have negative effects on human health, and they emphasized that the widespread TA-containing weeds in temperate and tropical regions may cause the accidental contamination of agricultural products as well as tea and herbal mixtures. Excessive anti-muscarinic activity in the central and autonomic nervous system are the main toxicological effects caused by atropine and scopolamine. Because of these effects on human health, the EFSA Panel has established a group acute reference dose of 0.016 μg/kg bw for the sum of the relevant TAs [23,24,25]. TAs, similar to PAs, can contaminate feeds, agricultural and animal products, and teas and herbal mixtures. Therefore, studies on TAs have investigated their presence in teas and herbal infusion matrices, as well as in honey and its products, cereal-based baby foods, other bee products, plants, cow’s milk, seeds, bread, and leafy vegetables [24,25,26,27,28,29,30,31,32]. LC-MS/MS systems or high-resolution mass systems were used in these studies.
According to the EFSA regulation, the pyrrolizidine alkaloid concentration is given as the sum of the PAs and PANOs [22]. According to the EC regulation, the maximum limit value for herbal infusions (dried products) is accepted to be 200 ug/kg. The limit value for herbal infusions of rooibos, anise, lemon balm, chamomile, thyme, mint, and lemon verbena as dried products and mixtures consisting of these dried products is only 400 ug/kg. The limit was determined to be 150 ug/kg for dried teas and flavored teas. The EC regulation suggested at least atropine and scopolamine as the tropane alkaloids to be analyzed, and their sum is given as the total TA concentration. The limit value for herbal infusions as dried products is 25 ug/kg [22,23,33,34].
Therefore, the safety management of PAs and TAs in teas and culinary herbs is necessary. Due to the worldwide widespread habit of consuming teas and other herbal infusions, if these are frequently contaminated, they can become the main source of human exposure to relevant contaminants. On the other hand, while studies on monitoring PAs in teas and culinary herbs in Turkey are very limited, according to literature reviews, no studies on TAs have been conducted [35,36,37,38].
The efficiency of PA and TA analyses depends on many factors, and they include the steps of extraction, separation, and identification. The analysis of PAs is mainly based on high performance liquid chromatography (HPLC), taking into account the physical and chemical properties of the PAs and TAs. Accurate and precise analytical methods using HPLC with mass spectrometry (MS) or tandem mass spectrometry MS/MS are commonly used in multicomponent analyses [12,39,40,41,42,43]. The use of LC-MS/MS or high-resolution mass spectrometry instruments is the dominant approach in the analysis of TAs. For the determination of TAs, SPE techniques are used prior to instrumental analysis [44,45,46,47,48,49,50].
Various purification methods such as thin layer chromatography, column chromatography, liquid-liquid extraction (LLE), and solid phase extraction (SPE) are applied to samples as pre-treatment methods. Among these, SPE is the most widely used, and it uses a strong cation exchange stationary phase based on the properties of the tertiary amine groups of PAs. To achieve the highest possible sensitivity, modern methods often rely on cleaning the samples by SPE prior to liquid chromatography-tandem mass spectrometry (LC-MS/MS) analysis. In general, the application of tandem mass spectrometry (MS/MS) results in low limits of detection (LOD), especially where multistage tandem mass spectrometry (MS3) or high resolution mass spectrometry systems are used [51,52,53,54,55,56,57,58].
In this study, the word “tea” refers to usable plant materials that are commercially called teas by the public or by the food industry, and “culinary herbs“ refers to plants used in the food industry and cooking. The main purpose of this study was to analyze the pyrrolizidine alkaloids and tropane alkaloids in different herbal teas and culinary herbs obtained from the Turkish market using a sensitive and high-accuracy LC-Q-ToF/MS system after sonification extraction with methanol. By evaluating the results obtained, the content of pyrrolizidine alkaloid was determined and its importance for human health and food safety was revealed. The distribution of PAs, PANOs, and TAs determined in Turkey is also explained by performing principal component analysis (PCA) according to the samples.

2. Materials and Methods

2.1. Chemicals and Reagents

Pure water from a Milli-Q water purification system (Millipore, Bedford, MA, USA) was used. Acetonitrile and methanol of LC-MS grade were purchased from Sigma-Aldrich (St. Louis, MO, USA). Formic acid eluent additive for the mobile phase was purchased from Merck (Darmstadt, Germany).

2.2. Samples

All of the tea samples (black tea (BT), green tea (GT), mixed tea (MT), and flavored tea (FT)), herbal tea samples (chamomile (CT), sage (ST), linden (LT), fennel (FT), and rosehips (RT)), and culinary herb samples (thyme (T) and peppermint (PM)) were obtained from Turkish supermarkets in the İzmir area and stored at room temperature until analysis.

2.3. Standards and Samples Preparation

A stock solution mixture was used where each of the standard compounds in methanol were in concentrations of 1.0 µg mL−1. Working solutions were prepared from this stock solution diluted with methanol. Working solutions were stored at −20 °C until analysis.
Different extractions were compared in the study by Avula et al. In this study, the extraction procedure, which mirrored that of Avula et al., obtained the best results, and it was applied [58]. Briefly, in the extraction method based on sonication with methanol, 50 mg of solid sample was sonicated in 2.5 mL of methanol for 30 min and then centrifuged at 3000 rpm for 15 min. The clear supernatant solution was transferred to a 10 mL metered flask. The procedure was repeated three more times, and the respective supernatants were combined. The final volume was adjusted to 10 mL with methanol and mixed well. Prior to injection, a sufficient volume (approximately 2 mL) was filtered through a 0.45 µm PTFE membrane filter and analyzed with the liquid chromatography hyphenated with quadrupole time of flight mass spectrometry (LC-Q-ToF/MS) system.

2.4. Instrumentation and Conditions

Chromatographic separation was performed using an Agilent HPLC 1260 Infinity system. The mass analysis was studied using an Agilent 6550 iFunnel high resolution accurate-mass Q-TOF/MS equipped with an Agilent Dual Jet Stream ElectroSpray Ionization (Dual AJS ESI) system according to the literature [58]. The interface operating in a positive ion mode was used for the analysis of the PAs (Agilent Technologies, Santa Clara, CA, USA). The acquisition was controlled by Agilent MassHunter Acquisition Software Ver. A.09.00 and the data were processed with MassHunter Qualitative Software Ver. B.07.00. The LC and MS detailed instrument conditions are given in Supplementary SM-1 and the MS/MS spectra with the product ions are given in Supplementary SM-2.
Although intermedine, intermedine-N-oxides, lycopsamine, lycopsamine-N-oxides, indicine, and indicine-N-oxides were present in the standard mixture, quantification was performed as the sum of these PAs and PANOs. Intermedine, lycopsamine and indicine have the same chemical formula (C15H25NO5), and the calculated [M+H]+ ion value was 300.1805. In the extracted ion chromatogram (EIC) of this ion, 2 peaks were observed at retention times of 9.029 min and 9.874 min. The N-oxides value of these substances (the (C15H25NO6) [M+H]+ ion) was 316.1760 and two peaks were observed at 15.169 min and 16.859 min in the EIC. Since the product ions seen in the MS/MS spectra were the same, the total peak areas could be determined in quantification. In addition, the mass resolutions calculated according to the MS/MS spectra of the two peaks were between 3099 and 5645. There was a need to study new methods for one-by-one calculations for intermedine, intermedine-N-oxides, lycopsamine, lycopsamine-N-oxides, indicine, and indicine -N-Oxides. Thus, it could be more clearly stated which of these PAs or PANOs were in the samples. All chromatograms and mass spectra are given in Supplementary SM-3 and SM-4 for these PAs and PANOs.

2.5. Principal Component Analysis

PCA was performed using MINITAB 15 Statistical Software. Similarities and differences between the main groups and the observations are presented as score plots. The loading plots were used to explain the relationships between the variables in the score plots and cluster observations [59,60]. All analysis results of the study are given in the Supplementary Materials (SM-5).

2.6. Method Validation

The LC-Q-ToF/MS method for the determination of the dehydro PAs, PANOs, and TAs in the teas, herbal teas, and culinary herbs were validated according to the SANCO/12571/2013 guideline [61]. The applied method for the determination of the dehydro PAs, PANOs, and TAs in the teas and herbal teas was validated in terms of linearity, recovery, repeatability, matrix effects, limit of detections (LODs), and limit of quantifications (LOQs). Quantification of the dehydro PAs, PANOs, and TAs was accomplished by external calibration. The calibration curves were determined at six different concentration levels ranging from 5.0 to 500.0 ng g−1 in methanol. Figure 1 shows a representative chromatogram of all the ions of the compounds. Recovery experiments were carried out in triplicate by spiking two different concentrations (5 and 20 ng/g of each PA, PANO, and TA compound) to blank herbal tea, peppermint, thyme, and chamomile samples. The repeatability of the method was expressed as the relative standard deviation (RSD) of the PA, PANO, and TA contents. LODs and LOQs were determined by the signal/noise ratio method. The calibration curves, LODs, LOQs, and relative standard deviation (RSD) values obtained for the teas and herbal teas for each compound are shown in Table 1. It was found that the linearity of the analytical response in the studied range was good and the correlation coefficients were appropriate.
Recovery (R) was calculated for each compound using the following formula:
R = (Cfound/Cadded) × 100,
where Cfound is the determined concentration of each compound after adding a known amount of standard solution to the blank sample and Cadded is the known concentration of the compound solution added to the blank sample [62].
Table 1 provides the calibration data for the 27 reference PAs, PANOs, and TAs used in this study, and it includes the correct mass, mass error (diff), product ion, regression equation, correlation coefficient, detection limit, quantification limit, and RSD of repeatability.
According to the SANCO/12571/2013 guideline, the mean of the recovery limit values is accepted as 70–120% in the residue analysis [61]. It is seen in Table 2 that the recovery values of this study remained within these limits. In terms of the accuracy parameter, the method was valid for four different matrices (thyme, peppermint, tea, and chamomile) and all of the compounds (PAs, PANOs, and TAs).
For the estimation of the matrix effect, the calculation method in the study by Kwon et al. [63] was used. Linear calibration curves were calculated for each analyte using the peak areas for the matrix-matched standards and the solvent standards only. The matrix effect (ME) was calculated as follows: %ME = ((slope of matrix-matched calibration − slope of solvent-only calibration)/slope of solvent-only calibration) × 100 [63]. The matrix effect was investigated for four different matrices (thyme, mint, tea, and chamomile), and the results for each matrix are given in Table 2. The tables of the regression equations and the R2 values are given in the Supplementary Materials (Supplementary SM-6–SM-9) for the solvent and the matrix-matched calibration.

3. Results and Discussion

The data obtained on the total PAs and TAs were evaluated and their profiles were revealed by screening and measuring the herbal teas and culinary herbs consumed in Turkey. Table 3 summarizes the levels of the total dehydro PAs and TAs obtained for the various tea/herbal tea strains and edible herbs.
According to the analysis results, one or more of the PAs and/or PANOs were found in all samples. TAs were found in only four of the herbal teas (green tea, chamomile tea, flavored tea, and rosehip tea). Echmidine, erucifoline, monocrotaline-n-oxide, and lasiocarpine were qualified and quantified in nearly all samples. When the samples were evaluated against the sum the intermedine, lycopsamine, and indicine-N-oxides, these PANOs were not found except for in the linden tea sample. The PA and TA levels and distribution are given in Table 3 and Figure 2.
Whether the total PAs exceeded the limit values was evaluated according to the EU regulations [33]. When the black, green, mixed, and flavored tea samples were examined, while the flavored teas remained below the 150 ng g−1 limit value, one sample from each of the other tea groups was above the limit value (black tea: 196.3 ng g−1, green tea: 781.6 ng g−1, and mixed tea: 596.2 ng g−1). According to the EU regulations, the limit value for chamomile, thyme, and peppermint dry products is 400 ng g−1 [33]. Only the fresh chamomile sample (1054.5 ng g−1) was well above the limit value. For the peppermint samples, three exceeded the limit value, with concentration values of 547.9, 479.1, and 480.8 ng g−1, respectively. With the exception of one of the thyme samples (435.9 ng g−1), the others remained below the limit value. The sage, linden, fennel, and rosehip teas all had concentrations below the 400 ng g−1 cutoff value for total pyrrolizidine alkaloid content. Scopolamine, one of the tropane alkaloids, was found in a mixed tea sample and in the rosehip tea in amounts of 35.1 ng g−1 and 244.5 ng g−1, respectively, while atropine was found in one flavored tea (29.3 ng g−1) and in the green tea (482.3 ng g−1) and chamomile tea (559.2 ng g−1) samples. The limit value for herbal infusions as dried products is above 25 ug/kg [34].
The black tea samples contained an average PA sum of 142.4 ng g−1. Atropine and scopolamine were not found in the black tea samples. The black tea samples all contained echminidine, lasiocarpine, and monocrotaline-N-oxide. The average concentration of the green tea samples was 434.5 ng g−1. Echminidine, lasiocarpine, monocrotaline-N-oxide, senecionine, and senecionine N-oxide were found in the samples, and 482.3 ng g−1 of atropine was found in the green tea sample. While the average was 336.3 ng g−1 in the mixed teas, echminidine and erucifoline are common PAs. Scopolamine was found in a sample at a value of 36.1 ng g−1. While echminidine and lasiocarpine are common in flavored teas, there was 29.3 ng g−1 of atropine found in one sample, and the PA average of the samples was 143.6 ng g−1. Unlike the other teas, monocrotaline was found in all chamomile tea samples, in addition to echminidine and erucifoline. While the echminidine, erucifoline, retrorsine, senecionine-N-oxide, riddelline, and atropine concentrations in the fresh chamomile were higher than in the other chamomile teas, scopolamine was found only in the fresh chamomile. The contents of the chamomile teas and the green tea were in alignment with the literature [21,64]. When the peppermint samples were examined, it was found that there was an average PA value of 308.4 ng g−1. TAs were not found in these samples. Erucifoline, lasiocarpine, senecionine, senecionine N-oxide, and seneciphylline-N-oxides were found in all samples. The total contents of the freshly analyzed chamomile and peppermint samples were higher than those of the dried chamomile and peppermint samples. Particularly because peppermint is used in salads and beverages, it is more important to control its contents for human health. Unlike the other teas, the sage and linden teas contained heliotrine, and the linden tea also contained heliotrine-N-oxide. Apart from this, there was 244.7 ng g−1 of scopolamine in the rosehip tea sample, and this type of tea is consumed quite a lot during the winter months. The fact that the numbers and types of PAs found in the herbal tea samples were different was in line with the literature [65,66,67,68,69]. The thyme samples contained the most lasiocarpine, monocrotaline-N-oxides, retrorsine, senesiphylline, and senesiphylline-line-N-oxides, with an average of 87.8 ng g−1. TAs were not found in the thyme samples. When the samples were examined in terms of the sum of their intermedin, lycopsamine, and indicin contents, which were found in most of the tea samples, they were detected in only one of the thyme samples (137.5 ng g−1). The sum of the intermedin, lycopsamine, and indicin contents could not be measured in the fennel and rosehip teas because it was below the LOQ value. When the total of the intermedin, lycopsamine, and indicin N oxides contents were examined, only one linden tea contained a value of 27.1 ng g−1. The wide PA content variations within the same species could be explained by the fact that the samples came from different plant varieties and, consequently, they were subjected to different growing, harvesting, storage, and transportation conditions.
After determining the amounts of the PAs, PANOs, and TAs in the samples, PCA analysis was performed to more clearly reveal the similarities and differences in the contents. The PCA scores and loading plots can be seen in Figure 3. First, general information was obtained by PCA using the whole dataset (Figure 3 and Figure 4). The PCA analysis for the thyme, tea, peppermint, and chamomile samples was performed for each sample group separately (Supplementary SM-10–13). The columns with zero values were not included in the analysis.
Although the overall effect of PC1 and PC2 was 35.49%, the separate classifications of the fresh chamomile and fresh mint samples is clearly seen in Figure 3. As can be seen from the PCA score plot, the fresh peppermint and dry peppermint samples were separated from the other samples and showed similar characteristics within themselves (Figure 3). The fresh chamomile sample was separated from all other samples. The grouping of fresh chamomile separately from the other teas was realized under the influence of retrorsine-N-oxide, seneciphylline, riddelline, senecivernine, and monocrotaline-N-oxides. While the peppermint samples differed from the other samples, they also showed similarity with the fresh peppermint sample. The fresh peppermint was separated by the effects of erucifoline, senecionine, lasiocarpine, seneciphylline-N-oxide, senecivernine-N-oxide, and senecionine N-oxide. It could be said that the effect of the PANOs was effective for the separation of the fresh plant samples from the other dry samples, and this may have indicated that the differences in the contents of the teas and culinary herbs may also have been due to the drying process. The differences between the fresh samples and the dry samples may also have revealed the importance of the drying process because the total PA amounts in the fresh peppermint and the fresh chamomile samples were above the limit values.
In this study—the first of its kind—conducted to determine the total PA and TA amounts for some herbal tea and edible herb samples in Turkey, it was determined that some samples were above the limit values. Therefore, the continued quality control of herbal teas, edible plants, herbs, and other foodstuffs that may be contaminated with PAs is important.

4. Conclusions

Herbal teas and culinary herbs are products that are constantly consumed in daily diets. Although these teas and culinary herbs have therapeutic benefits, they can also pose potential health risks due to the toxic substances they contain. Therefore, PAs, PANOs, and TAs should be monitored with sensitive and accurate analytical techniques in terms of human health and food safety. In order to determine their total amounts, extraction techniques should be developed quickly to be cost-effective and suitable for routine analysis, and all structures should be defined and measured by instrumental methods. In this study, it was determined that it is important to control these products as the total PA and TA contents in some of the teas and culinary herb samples were present in amounts that exceeded the legal limits, and the PAs were screened and quantified in all samples. Thus, it needs to be ensured that only products complying with legal regulations reach consumers. In addition, the importance of applying regulations for the determination of PA and TA contents in teas and culinary herbs and continuous data collection on the presence of alkaloids in these products has been demonstrated. This study also sheds light on the optimization of methods that can be applied to other food products and feeds that may be contaminated with PAs, PANOs, and TAs.

Supplementary Materials

The following supporting information can be downloaded at https://www.mdpi.com/article/10.3390/foods12193572/s1, SM-1, the LC-Q-ToF/MS method; SM-2, the MS/MS spectra for the PAs, PANOs, and TAs; SM-3, the MS EIC, MS/MS EIC, and mass spectrum of the product ions of intermedine, lycopsamine, and indicine; SM-4, the MS EIC, MS/MS EIC, and mass spectrum of the product ions of intermedine-N-oxides, lycopsamine-N-oxides, and indicine -N-oxides; SM-5, the data for the PAs and Tas in the samples; SM-6, the regression equations and R2 values of the solvent and matrix-matched calibration for the thyme matrix; SM-7, the regression equations and R2 values for the solvent and matrix-matched calibration for the tea matrix; SM-8, the regression equations and R2 values for the solvent and matrix-matched calibration for the chamomile matrix; SM-9, the regression equations and R2 values for the solvent and matrix-matched calibration for the peppermint matrix; SM-10, the scores and loading plots of the thyme samples; SM-11, the scores and loading plots of the tea samples; SM-12, the scores and loading plots of the chamomile samples; and SM-13, the scores and loading plots of the peppermint samples.

Funding

A part of this study was supported by the Ege University, Scientific Research Projects (EGE-BAP) (project no. FGA-2020-21099).

Data Availability Statement

The data can be requested from the author if needed.

Acknowledgments

The author would like to thank Altium International Laboratory Instrument Company İzmir/Turkey Technical Service for kindly providing the PhytoLab branded standard mixture solutions of the pyrrolizidine alkaloids.

Conflicts of Interest

The author declares no conflict of interest.

References

  1. Chmit, M.S.; Horn, G.; Dübecke, A.; Beuerle, T. Pyrrolizidine alkaloids in the food chain: Is horizontal transfer of natural products of relevance? Foods 2021, 10, 1827. [Google Scholar] [CrossRef] [PubMed]
  2. Langel, D.; Ober, D.; Pelser, P.B. The evolution of pyrrolizidine alkaloid biosynthesis and diversity in the Senecioneae. Phytochem. Rev. 2011, 10, 3–74. [Google Scholar] [CrossRef]
  3. WHO. Pyrrolizidine alkaloids. In Environmental Health Criteria for Pyrrolizidine alkaloids; World Health Organization: Geneva, Switzerland, 1988; Available online: http://www.inchem.org/documents/ehc/ehc/ehc080.htm (accessed on 15 August 2023).
  4. Schrenk, D.; Gao, L.; Lin, G.; Mahony, C.; Mulder, P.P.J.; Peijnenburg, A.; Pfuhler, S.; Rietjens, I.M.C.M.; Rutz, L.; Steinhoff, B.; et al. Pyrrolizidine alkaloids in food and phytomedicine: Occurrence, exposure, toxicity, mechanisms, and risk assessment—A review. Food Chem. Toxicol. 2020, 136, 111107. [Google Scholar] [CrossRef]
  5. Roncada, P.; Isani, G.; Peloso, M.; Dalmonte, T.; Bonan, S.; Caprai, E. Pyrrolizidine Alkaloids from Monofloral and Multifloral Italian Honey. Int. J. Environ. Res. Public Health 2023, 20, 5410. [Google Scholar] [CrossRef] [PubMed]
  6. Boppré, M.; Colegate, S.M.; Edgar, J.A. Pyrrolizidine alkaloids of Echium vulgare honey found in pure pollen. J. Agric. Food Chem. 2005, 53, 594–600. [Google Scholar] [CrossRef] [PubMed]
  7. EFSA (European Food Safety Authority). Risks for human health related to the presence of pyrrolizidine alkaloids in honey, tea, herbal infusions and food supplements. EFSA J. 2017, 15, 4908. [Google Scholar]
  8. Lucchetti, M.A.; Glauser, G.; Kilchenmann, V.; Dubecke, A.; Beckh, G.; Praz, C.; Kast, C. Pyrrolizidine alkaloids from Echium vulgare in honey originate primarily from floral nectar. J. Agric. Food Chem. 2016, 64, 5267–5273. [Google Scholar] [CrossRef]
  9. Selmar, D.; Wittke, C.; Beck-vonWolffersdorff, I.; Klier, B.; Lewerenz, L.; Kleinwächter, M.; Nowak, M. Transfer of pyrrolizidine alkaloids between living plants: A disregarded source of contaminations. Environ. Pollut. 2019, 248, 456–461. [Google Scholar] [CrossRef]
  10. Kaltner, F.; Rychlik, M.; Gareis, M.; Gottschalk, C. Occurrence and Risk Assessment of Pyrrolizidine Alkaloids in Spices and Culinary Herbs from Various Geographical Origins. Toxins 2020, 12, 155. [Google Scholar] [CrossRef]
  11. Hama, J.R.; Strobel, B.W. Occurrence of pyrrolizidine alkaloids in ragwort plants, soils and surface waters at the field scale in grassland. Sci. Total Environ. 2021, 755, 142822. [Google Scholar] [CrossRef]
  12. Hama, J.R.; Strobel, B.W. Pyrrolizidine alkaloids quantified in soil and water using UPLC-MS/MS. RSC Adv. 2019, 9, 30350–30357. [Google Scholar] [CrossRef] [PubMed]
  13. Wang, J.; Zhang, M.; Chen, L.; Qiao, Y.; Ma, S.; Sun, D.; Si, J.; Liao, Y. Determination of toxic pyrrolizidine alkaloids in traditional Chinese herbal medicines by uplc-ms/ms and accompanying risk assessment for human health. Molecules 2021, 26, 1648. [Google Scholar] [CrossRef] [PubMed]
  14. Xia, Q.; He, X.; Shi, Q.; Lin, G.; Fu, P.P. Quantitation of DNA reactive pyrrolic metabolites of senecionine—A carcinogenic pyrrolizidine alkaloid by LC/MS/MS analysis. J. Food Drug Anal. 2020, 28, 167–174. [Google Scholar] [CrossRef] [PubMed]
  15. Sharma, S.; Agrawal, R. Toxic behaviour of naturally occurring pyrrolizidine alkaloids. Int. J. Multidiscip. Curr. Res. 2015, 3, 594–597. [Google Scholar]
  16. Teschke, R.; Vongdala, N.; Quan, N.V.; Quy, T.N.; Xuan, T.D. Metabolic toxification of 1, 2-unsaturated pyrrolizidine alkaloids causes human hepatic sinusoidal obstruction syndrome: The update. Int. J. Mol. Sci. 2021, 22, 10419. [Google Scholar] [CrossRef]
  17. Casado, N.; Morante-Zarcero, S.; Sierra, I. The concerning food safety issue of pyrrolizidine alkaloids: An overview. Trends Food Sci. Technol. 2022, 120, 123–139. [Google Scholar] [CrossRef]
  18. Kwon, Y.; Koo, Y.; Jeong, Y. Determination of pyrrolizidine alkaloids in teas using liquid chromatography–tandem mass spectrometry combined with rapid-easy extraction. Foods 2021, 10, 2250. [Google Scholar] [CrossRef]
  19. Habs, M.; Binder, K.; Krauss, S.; Müller, K.; Ernst, B.; Valentini, L.; Koller, M. A balanced risk–benefit analysis to determine human risks associated with pyrrolizidine alkaloids (Pa)—The case of tea and herbal infusions. Nutrients 2017, 9, 717. [Google Scholar] [CrossRef]
  20. Letsyo, E.; Jerz, G.; Winterhalter, P.; Beuerle, T. Toxic pyrrolizidine alkaloids in herbal medicines commonly used in Ghana. J. Ethnopharmacol. 2017, 202, 154–161. [Google Scholar] [CrossRef]
  21. Bodi, D.; Ronczka, S.; Gottschalk, C.; Behr, N.; Skibba, A.; Wagner, M.; Lahrssen-Wiederholt, M.; Preiss-Weigert, A.; These, A. Determination of pyrrolizidine alkaloids in tea, herbal drugs and honey. Food Addit. Contam. Part A Chem. Anal. Control. Expo. Risk Assess. 2014, 31, 348–358. [Google Scholar] [CrossRef]
  22. EFSA Panel on Contaminants in the Food Chain (CONTAM). Scientific opinion on pyrrolizidine alkaloids in food and feed. EFSA J. 2011, 9, 2406. [Google Scholar]
  23. EFSA Panel on Contaminants in the Food Chain (CONTAM). Scientific opinion on tropane alkaloids in food and feed. EFSA J. 2013, 11, 3386. [Google Scholar]
  24. León, N.; Miralles, P.; Yusà, V.; Coscollà, C. A green analytical method for the simultaneous determination of 30 tropane and pyrrolizidine alkaloids and their N-oxides in teas and herbs for infusions by LC-Q-Orbitrap HRMS. J. Chromatogr. A 2022, 1666, 462835. [Google Scholar] [CrossRef] [PubMed]
  25. Martinello, M.; Manzinello, C.; Gallina, A.; Mutinelli, F. In-house validation and application of UHPLC-MS/MS method for the quantification of pyrrolizidine and tropane alkaloids in commercial honey bee-collected pollen, teas and herbal infusions purchased on Italian market in 2019–2020 referring to recent European Union regulations. Int. J. Food Sci. Technol. 2022, 57, 7505–7516. [Google Scholar]
  26. Marín-Sáez, J.; Romero-González, R.; Garrido Frenich, A. Reliable determination of tropane alkaloids in cereal based baby foods coupling on-line spe to mass spectrometry avoiding chromatographic step. Food Chem. 2019, 275, 746–753. [Google Scholar] [CrossRef] [PubMed]
  27. Romera-Torres, A.; Romero-González, R.; Martínez Vidal, J.L.; Garrido Frenich, A. Comprehensive tropane alkaloids analysis and retrospective screening of contaminants in honey samples using liquid chromatography-high resolution mass spectrometry (Orbitrap). Food Res. Int. 2020, 133, 109130. [Google Scholar] [CrossRef] [PubMed]
  28. Du, N.; Zhou, W.; Jin, H.; Liu, Y.; Zhou, H.; Liang, X. Characterization of tropane and cinnamamide alkaloids from Scopolia tangutica by high-performance liquid chromatography with quadrupole time-of-flight tandem mass spectrometry. J. Sep. Sci. 2019, 42, 1163–1173. [Google Scholar] [CrossRef]
  29. Klein, L.M.; Gabler, A.M.; Rychlik, M.; Gottschalk, C.; Kaltner, F. A sensitive LC–MS/MS method for isomer separation and quantitative determination of 51 pyrrolizidine alkaloids and two tropane alkaloids in cow’s milk. Anal. Bioanal. Chem. 2022, 414, 8107–8124. [Google Scholar] [CrossRef]
  30. Kowalczyk, E.; Kwiatek, K. Scopolamine and atropine in feeds–determination with liquid chromatography mass spectrometry. Food Addit. Contam. Part A 2022, 39, 977–989. [Google Scholar] [CrossRef]
  31. Veršilovskis, A.; Mulder, P.P.J.; Pereboom-de Fauw, D.P.K.H.; de Stoppelaar, J.; de Nijs, M. Simultaneous quantification of ergot and tropane alkaloids in bread in the Netherlands by LC-MS/MS. Food Addit. Contam. Part B Surveill. 2020, 13, 215–223. [Google Scholar] [CrossRef]
  32. González-Gómez, L.; Morante-Zarcero, S.; Pereira, J.A.M.; Câmara, J.S.; Sierra, I. Improved Analytical Approach for Determination of Tropane Alkaloids in Leafy Vegetables Based on µ-QuEChERS Combined with HPLC-MS/MS. Toxins 2022, 14, 650. [Google Scholar] [CrossRef] [PubMed]
  33. Commission Regulations (EU) 2020/2040. Commission regulations of 11 December 2020 amending Regulation (EC) No 1881/2006 as regards maximum levels of pyrrolizidine alkaloids in certain foodstuffs. Off. J. Eur. Union 2020, L420/2, 2–5. [Google Scholar]
  34. Commission Regulations (EU) 2021/1408. Commission regulations of 27 August 2021 amending Regulation (EC) No 1881/2006 as regards maximum levels of tropane alkaloids in certain foodstuffs. Off. J. Eur. Union 2021, L304/1, 1–4. [Google Scholar]
  35. Korkmaz, S.D.; Küplülü, Ö. Denizli ilinde üretilen kekiklerde (Origanum onites) pirolizidin alkaloidlerinin LC-MS Q-TOF yöntemi ile belirlenmesi. Vet. Hekim. Der. Derg. 2022, 93, 115–123. [Google Scholar] [CrossRef]
  36. Kurucu, S.; Kartal, M.; Choudhary, M.I.; Topçu, G. Pyrrolizidine Alkaloids from Symphytum sylvaticum Boiss. subsp. sepulcrale. (Boiss. & Bal.) Greuter & Burdetvar. sepulcrale and Symphytum aintabicum Hub.-Mor. & Wickens. Turk. J. Chem. 2002, 26, 195–200. [Google Scholar]
  37. Tosun, F.; Tamer, U. Determination of pyrrolizidine alkaloids in the seeds of Heliotropium europaeum by GC-MS. J. Fac. Pharm. Ankara 2004, 33, 7–9. [Google Scholar]
  38. Nemli, Y.; Kaynar, A.; Kayadan, A.; Er, T.; Kaya, İ. First Report of Pyrrolozidine Alkaloid Contents of Cuscuta campestris. Turk. J. Weed Sci. 2015, 18, 23–25. [Google Scholar]
  39. Keuth, O.; Humpf, H.U.; Fürst, P. Determination of pyrrolizidine alkaloids in tea and honey with automated SPE clean-up and ultra-performance liquid chromatography/tandem mass spectrometry. Food Addit. Contam. Part A Chem. Anal. Control. Expo. Risk Assess. 2022, 39, 149–157. [Google Scholar] [CrossRef]
  40. Mudge, E.M.; Jones, A.M.; Brown, P.N. Quantification of pyrrolizidine alkaloids in North American plants and honey by LC-MS: Single laboratory validation. Food Addit. Contam. Part A 2015, 32, 2068–2074. [Google Scholar] [CrossRef]
  41. Prada, F.; Stashenko, E.; Martinez, J.R. LC/MS study of the diversity and distribution of pyrrolizidine alkaloids in Crotalaria species growing in Colombia. J. Sep. Sci. 2020, 43, 4322–4337. [Google Scholar] [CrossRef]
  42. Zhang, Y.; Yang, F.-F.; Chen, H.; Qi, Y.-D.; Si, J.-Y.; Wu, Q.; Liao, Y.-H. Analysis of pyrrolizidine alkaloids in Eupatorium fortunei Turcz. and their in vitro neurotoxicity. Food Chem. Toxicol. 2021, 151, 151–160. [Google Scholar] [CrossRef] [PubMed]
  43. Chmit, M.S.; Wahrig, B.; Beuerle, T. Quantitative and qualitative analysis of pyrrolizidine alkaloids in liqueurs elixirs and herbal juices. Fitoterapia 2019, 136, 172–178. [Google Scholar] [CrossRef] [PubMed]
  44. Cao, Y.; Colegate, S.M.; Edgar, J.A. Safety assessment of food and herbal products containing hepatotoxic pyrrolizidine alkaloids: Interlaboratory consistency and the importance of N-oxide determination. Phytochem. Anal. 2008, 19, 526–533. [Google Scholar] [CrossRef]
  45. Valese, A.C.; Molognoni, L.; de Sá Ploêncio, L.A.; de Lima, F.G.; Gonzaga, L.V.; Górniak, S.L.; Daguer, H.; Barreto, F.; Oliveira Costa, A.C. A fast and simple LC-ESI-MS/MS method for detecting pyrrolizidine alkaloids in honey with full validation and measurement uncertainty. Food Control. 2016, 67, 183–191. [Google Scholar] [CrossRef]
  46. Cramer, L.; Schiebel, H.M.; Ernst, L.; Beuerle, T. Pyrrolizidine alkaloids in the food chain: Development, validation, and application of a new HPLC-ESI-MS/MS sum parameter method. J. Agric. Food Chem. 2013, 61, 11382–11391. [Google Scholar] [CrossRef]
  47. Dzuman, Z.; Jonatova, P.; Stranska-Zachariasova, M.; Prusova, N.; Brabenec, O.; Novakova, A.; Fenclova, M.; Hajslova, J. Development of a new LC-MS method for accurate and sensitive determination of 33 pyrrolizidine and 21 tropane alkaloids in plant-based food matrices. Anal. Bioanal. Chem. 2020, 412, 7155–7167. [Google Scholar] [CrossRef] [PubMed]
  48. Gonçalves, C.; Cubero-Leon, E.; Stroka, J. Determination of tropane alkaloids in cereals, tea and herbal infusions: Exploiting proficiency testing data as a basis to derive interlaboratory performance characteristics of an improved LC-MS/MS method. Food Chem. 2020, 331, 127260. [Google Scholar] [CrossRef] [PubMed]
  49. Martinello, M.; Borin, A.; Stella, R.; Bovo, D.; Biancotto, G.; Gallina, A.; Mutinelli, F. Development and validation of a QuEChERS method coupled to liquid chromatography and high resolution mass spectrometry to determine pyrrolizidine and tropane alkaloids in honey. Food Chem. 2017, 234, 295–302. [Google Scholar] [CrossRef]
  50. Romera-Torres, A.; Romero-González, R.; Martínez Vidal, J.L.; Frenich, A.G. Study of the occurrence of tropane alkaloids in animal feed using LC-HRMS. Anal. Methods 2018, 10, 3340–3346. [Google Scholar] [CrossRef]
  51. Al-Subaie, S.F.; Alowaifeer, A.M.; Mohamed, M.E. Pyrrolizidine Alkaloid Extraction and Analysis: Recent Updates. Foods 2022, 11, 3873. [Google Scholar] [CrossRef]
  52. Mädge, I.; Cramer, L.; Rahaus, I.; Jerz, G.; Winterhalter, P.; Beuerle, T. Pyrrolizidine alkaloids in herbal teas for infants, pregnant or lactating women. Food Chem. 2015, 187, 491–498. [Google Scholar] [CrossRef] [PubMed]
  53. Dübecke, A.; Beckh, G.; Lüllmann, C. Pyrrolizidine alkaloids in honey and bee pollen. Food Addit. Contam. Part A Chem. Anal. Control. Expo. Risk Assess. 2011, 28, 348–358. [Google Scholar] [CrossRef]
  54. Chung, S.W.C.; Lam, C.H. Development of an analytical method for analyzing pyrrolizidine alkaloids in different groups of food by UPLC-MS/MS. J. Agric. Food Chem. 2018, 66, 3009–3018. [Google Scholar] [CrossRef] [PubMed]
  55. Sagi, S.; Avula, B.; Wang, Y.H.; Khan, I.A. Quantification and characterization of alkaloids from roots of Rauwolfia serpentina using ultra-high performance liquid chromatography-photo diode array-mass spectrometry. Anal. Bioanal. Chem. 2016, 408, 177–190. [Google Scholar] [CrossRef] [PubMed]
  56. Dzuman, Z.; Zachariasova, M.; Veprikova, Z.; Godula, M.; Hajslova, J. Multi-analyte high performance liquid chromatography coupled to high resolution tandem mass spectrometry method for control of pesticide residues, mycotoxins, and pyrrolizidine alkaloids. Anal. Chim. Acta 2015, 863, 29–40. [Google Scholar] [CrossRef] [PubMed]
  57. Kaltner, F.; Stiglbauer, B.; Rychlik, M.; Gareis, M.; Gottschalk, C. Development of a sensitive analytical method for determining 44 pyrrolizidine alkaloids in teas and herbal teas via LC-ESI-MS/MS. Anal. Bioanal. Chem. 2019, 411, 7233–7249. [Google Scholar] [CrossRef]
  58. Avula, B.; Sagi, S.; Wang, Y.H.; Zweigenbaum, J.; Wang, M.; Khan, I.A. Characterization and screening of pyrrolizidine alkaloids and N-oxides from botanicals and dietary supplements using UHPLC-high resolution mass spectrometry. Food Chem. 2015, 178, 136–148. [Google Scholar] [CrossRef]
  59. Gumus, Z.P.; Ertas, H.; Yasar, E.; Gumus, O. Classification of olive oils using chromatography, principal component analysis and artificial neural network modelling. J. Food Meas. Charact. 2018, 12, 1325–1333. [Google Scholar] [CrossRef]
  60. Dunford, N.T.; Gumus, Z.P.; Gur, C.S. Chemical Composition and Antioxidant Properties of Pecan Shell Water Extracts. Antioxidants 2022, 11, 1127. [Google Scholar] [CrossRef]
  61. SANCO/12571/2013 Rev. 0. Guidance Document on Analytical Quality Control and Validation Procedures for Pesticides Residues Analysis in Food and Feed. 2013. Available online: https://www.eurl-pesticides.eu/library/docs/allcrl/AqcGuidance_Sanco_2013_12571.pdf (accessed on 2 September 2023).
  62. Soylak, M.; Uzcan, F.; Goktas, O.; Gumus, Z.P. Fe3O4-SiO2-MIL-53 (Fe) nanocomposite for magnetic dispersive micro-solid phase extraction of cadmium (II) at trace levels prior to HR-CS-FAAS detection. Food Chem. 2023, 429, 136855. [Google Scholar] [CrossRef]
  63. Kwon, H.; Lehotay, S.J.; Geis-Asteggiante, L. Variability of matrix effects in liquid and gas chromatography–mass spectrometry analysis of pesticide residues after QuEChERS sample preparation of different food crops. J. Chromatogr. A 2012, 1270, 235–245. [Google Scholar] [CrossRef]
  64. Chen, L.; Zhang, Q.; Yi, Z.; Chen, Y.; Xiao, W.; Su, D.; Shi, W. Risk Assessment of (Herbal) Teas Containing Pyrrolizidine Alkaloids (PAs) Based on Margin of Exposure Approach and Relative Potency (REP) Factors. Foods 2022, 11, 2946. [Google Scholar] [CrossRef] [PubMed]
  65. Mathon, C.; Edder, P.; Bieri, S.; Christen, P. Survey of pyrrolizidine alkaloids in teas and herbal teas on the Swiss market using HPLC-MS/MS. Anal. Bioanal. Chem. 2014, 406, 7345–7354. [Google Scholar] [CrossRef] [PubMed]
  66. Shimshoni, J.A.; Duebecke, A.; Mulder, P.P.J.; Cuneah, O.; Barel, S. Pyrrolizidine and tropane alkaloids in teas and the herbal teas peppermint, rooibos and chamomile in the Israeli market. Food Addit. Contam. Part A Chem. Anal. Control. Expo. Risk Assess. 2015, 32, 2058–2067. [Google Scholar] [CrossRef]
  67. Kowalczyk, E.; Kwiatek, K. Application of the sum parameter method for the determination of pyrrolizidine alkaloids in teas. Food Addit. Contam. Part A Chem. Anal. Control. Expo. Risk Assess. 2020, 37, 622–633. [Google Scholar] [CrossRef] [PubMed]
  68. Zhu, L.; Ruan, J.Q.; Li, N.; Fu, P.P.; Ye, Y.; Lin, G. A novel ultra-performance liquid chromatography hyphenated with quadrupole time of flight mass spectrometry method for rapid estimation of total toxic retronecine-type of pyrrolizidine alkaloids in herbs without requiring corresponding standards. Food Chem. 2016, 194, 1320–1328. [Google Scholar] [CrossRef] [PubMed]
  69. Schulz, M.; Meins, J.; Diemert, S.; Zagermann-Muncke, P.; Goebel, R.; Schrenk, D.; Schubert-Zsilavecz, M.; Abdel-Tawab, M. Detection of pyrrolizidine alkaloids in German licensed herbal medicinal teas. Phytomedicine 2015, 22, 648–656. [Google Scholar] [CrossRef]
Figure 1. Extracted ion chromatogram of all the PA and TA standards. 1: Echimidine; 2: Erucifoline; 3: Europine; 4: Europine N-oxide; 5: Heliotrine; 6: Heliotrine N-oxide; 7: Jacobine; 8: Jacobine N-oxide; 9: Lasiocarpine; 10: Lasiocarpine N-oxide; 11: Monocrotaline; 12: Monocrotaline N-oxide; 13: Retrorsine; 14: Retrorsine N-oxide; 15: Senecionine; 16: Senecionine N-oxide; 17: Seneciphylline; 18: Seneciphylline N-oxide; 19: Senecivernine; 20: Senecivernine N-oxide; 21: Riddelline; 22: Riddelline N-oxide; 23: Senkirkine; 24: Trichodesmine; 25: Integerrimine; 26: Atropine; 27: Scopolamine; 28: Intermedine + Lycopsamine + Indicine; and 29: Intermedine-N-oxides + Lycopsamine-N-oxides + Indicine-N-oxides. Extracted ions of PAs and TAs are shown in different colors.
Figure 1. Extracted ion chromatogram of all the PA and TA standards. 1: Echimidine; 2: Erucifoline; 3: Europine; 4: Europine N-oxide; 5: Heliotrine; 6: Heliotrine N-oxide; 7: Jacobine; 8: Jacobine N-oxide; 9: Lasiocarpine; 10: Lasiocarpine N-oxide; 11: Monocrotaline; 12: Monocrotaline N-oxide; 13: Retrorsine; 14: Retrorsine N-oxide; 15: Senecionine; 16: Senecionine N-oxide; 17: Seneciphylline; 18: Seneciphylline N-oxide; 19: Senecivernine; 20: Senecivernine N-oxide; 21: Riddelline; 22: Riddelline N-oxide; 23: Senkirkine; 24: Trichodesmine; 25: Integerrimine; 26: Atropine; 27: Scopolamine; 28: Intermedine + Lycopsamine + Indicine; and 29: Intermedine-N-oxides + Lycopsamine-N-oxides + Indicine-N-oxides. Extracted ions of PAs and TAs are shown in different colors.
Foods 12 03572 g001
Figure 2. Distribution of the samples regarding their PA, PANO, and TA contents based on the 21 PAs and the 2 TAs.
Figure 2. Distribution of the samples regarding their PA, PANO, and TA contents based on the 21 PAs and the 2 TAs.
Foods 12 03572 g002
Figure 3. Score plot of the PCA results for all samples.
Figure 3. Score plot of the PCA results for all samples.
Foods 12 03572 g003
Figure 4. Loading plot of the PCA results for all samples.
Figure 4. Loading plot of the PCA results for all samples.
Foods 12 03572 g004
Table 1. Retention time, accurate mass data, mass error, calibration data, LOD, LOQ, and repeatability for the 25 PAs and PANOs and the two TA standards determined using LC-Q-ToF-MS.
Table 1. Retention time, accurate mass data, mass error, calibration data, LOD, LOQ, and repeatability for the 25 PAs and PANOs and the two TA standards determined using LC-Q-ToF-MS.
#Compound NameRT a (min)FormulaMass[M+H]+ Calculated[M+H]+ ExperimentalProduct IonMass Error (Diff) (ppm)Regression EquationR2LOD a
(ng g−1)
LOQ a
(ng g−1)
Repeatability
RSD%
1Echimidine43.88 ± 0.02C20H31NO7397.2101398.2173398.2175120.08080.50y = 113,975x − 188,6910.99960.163 ± 0.0040.550 ± 0.0104.11
2Erucifoline31.65 ± 0.02C18H23NO6349.1525350.1604350.1595120.0807−2.57y = 98,243x − 438,6080.99970.424 ± 0.0041.417 ± 0.0093.49
3Europine8.73 ± 0.02C16H27NO6329.1838330.1911330.1919138.09132.42y = 75,299x + 40,5880.99980.520 ± 0.0031.730 ± 0.0121.06
4Europine N-oxide10.58 ± 0.01C16H27NO7345.1788346.186346.1857172.0973−0.87y = 75,711x + 39,7110.99990.782 ± 0.0052.609 ± 0.0151.32
5Heliotrine26.07 ± 0.02C16H27NO5313.1889314.1962314.1964138.09160.64y = 92,882x − 259,5520.99940.793 ± 0.0082.646 ± 0.0253.92
6Heliotrine N-oxide30.48 ± 0.01C16H27NO6329.1838330.1911330.1911172.09710.00y = 116,893x − 192,3700.99950.363 ± 0.0071.207 ± 0.0263.24
7Jacobine10.58 ± 0.01C18H25NO6351.1682352.1760352.1751120.0807−2.56y = 83,888x − 206,7100.99940.867 ± 0.0082.890 ± 0.0240.39
8Jacobine N-oxide14.08 ± 0.01C18H25NO7367.1631368.1709368.1702296.1490−1.90y = 49,715x + 220,5600.99920.750 ± 0.0032.501 ± 0.0080.44
9Lasiocarpine49.62 ± 0.01C21H33NO7411.2257412.233412.2325120.0809−1.21y = 228,585x − 70,1550.99970.141 ± 0.0020.472 ± 0.0044.18
10Lasiocarpine N-oxide52.10 ± 0.01C21H33NO8427.2206428.2279428.228254.13850.23y = 180,097x + 785,8640.99920.105 ± 0.0060.357 ± 0.0152.89
11Monocrotaline3.60 ± 0.02C16H23NO6325.1525326.1598326.1593121.0885−1.53y = 84,062x + 247,3970.99980.306 ± 0.0061.022 ± 0.0162.07
12Monocrotaline N-oxide7.71 ± 0.02C16H23NO7341.1475342.1547342.1546137.0834−0.29y = 49,678x − 16,0300.99990.490 ± 0.0041.640 ± 0.0151.49
13Retrorsine22.92 ± 0.01C18H25NO6351.1682352.1755352.1754120.0808−0.28y = 66,827x − 38,3980.99960.665 ± 0.0062.211 ± 0.0304.18
14Retrorsine N-oxide25.06 ± 0.01C18H25NO7367.1631368.1704368.1698118.0649−1.63y = 43,255x + 203,7520.99970.778 ± 0.0092.593 ± 0.0312.86
15Senecionine 35.20 ± 0.01C18H25NO5335.1733336.1805336.1814120.08082.68y = 86,527x − 112,9010.99980.564 ± 0.0101.882 ± 0.0333.05
16Senecionine N-oxide38.41 ± 0.02C18H25NO6351.1682352.1755352.1762118.06501.99y = 14,0271x − 217,9100.99970.230 ± 0.0040.771 ± 0.0154.45
17Seneciphylline27.48 ± 0.01C18H23NO5333.1576334.1649334.1648120.0807−0.30y = 130,884x − 275,8780.99950.394 ± 0.0101.318 ± 0.0321.32
18Seneciphylline N-oxide31.65 ± 0.01C18H23NO6349.1525350.1598350.1598120.08070.00y = 103,691x − 152,0940.99970.382 ± 0.0071.270 ± 0.0231.15
19Senecivernine33.51 ± 0.02C18H25NO5335.1733336.1811336.1803120.0808−2.38y = 157,349x + 277,9370.99980.552 ± 0.0101.838 ± 0.0324.75
20Senecivernine N-oxide36.44 ± 0.01C18H25NO6351.1682352.1760352.1760118.06510.00y = 142,711x + 375,7420.99970.415 ± 0.0061.387 ± 0.0153.19
21Riddelline6.42 ± 0.01C18H23NO6349.1525350.1598350.1600120.08070.57y = 75,303x + 122,6940.99980.342 ± 0.0061.144 ± 0.0191.98
22Riddelline N-oxide10.53 ± 0.02C18H23NO7365.1475366.1547366.1545119.0728−0.55y = 56,263x + 372,7240.99950.824 ± 0.0062.743 ± 0.0250.62
23Senkirkine42.02 ± 0.01C19H27NO6365.1838366.1911366.1911168.10250.00y = 200,533x + 439,8940.99980.767 ± 0.0082.558 ± 0.0232.49
24Trichodesmine20.67 ± 0.02C18H27NO6353.1838354.1911354.1912222.14950.28y = 121,840x + 173,8310.99970.845 ± 0.0042.817 ± 0.0151.69
25Integerrimine34.61 ± 0.01C18H25NO5335.1733336.1805336.1803120.0807−0.59y = 100,282x + 203,9260.99960.462 ± 0.0051.538 ± 0.0163.21
26Atropine34.64 ± 0.01C17H23NO3289.1678290.1756290.1747124.1120−3.10y = 136,867x + 284,7580.99940.160 ± 0.0050.540 ± 0.0173.89
27Scopolamine16.13 ± 0.02C17H21NO4303.1471304.1549304.1538138.0912−3.62y = 66,561x − 284,5240.99900.181 ± 0.0050.599 ± 0.0181.27
28 bIntermedine
Lycopsamine
Indicine
9.03 ± 0.01
9.07 ± 0.01
C15H25NO5299.1733300.1811300.180794.0648−1.33y = 200,383x − 216,6720.99910.681 ± 0.007
0.723 ± 0.008
2.267 ± 0.024
2.411 ± 0.025
2.30
2.28
29 bIntermedine-N-oxides
Lycopsamine-N-oxides
Indicine-N-oxides
15.17 ± 0.01
16.86 ± 0.01
C15H25NO6315.1681316.1760316.1759172.0972−0.32y = 141,661x + 113,4420.99980.754 ± 0.011
0.840 ± 0.008
2.518 ± 0.037
2.800 ± 0.027
1.12
1.43
a, mean ± SD; b, peaks 28 and 29 represent the sum of intermedin, lycopsamine, and indicine and the N-oxides, respectively.
Table 2. Recovery and matrix effect for the 27 reference PAs, PANOs, and TAs used in this study for thyme, tea, peppermint, and chamomile (n = 3).
Table 2. Recovery and matrix effect for the 27 reference PAs, PANOs, and TAs used in this study for thyme, tea, peppermint, and chamomile (n = 3).
Compound NameR (%)
Thyme
5 ng g−1
R (%)
Tea
5 ng g−1
R (%)
Peppermint
5 ng g−1
R (%)
Chamomile
5 ng g−1
R (%)
Thyme
20 ng g−1
R (%)
Tea
20 ng g−1
R (%)
Peppermint
20 ng g−1
R (%)
Chamomile
20 ng g−1
ME
%
Thyme
ME
%
Tea
ME
%
Peppermint
ME
%
Chamomile
Echimidine92 ± 2101 ± 3101 ± 294 ± 2103 ± 199 ± 299 ± 2103 ± 114.12.3−5.65.5
Erucifoline94 ± 391 ± 2102 ± 2105 ± 194 ± 399 ± 296 ± 1100 ± 2−4.0−6.7−1.1−0.6
Europine102 ± 2101 ± 2102 ± 1101 ± 290 ± 290 ± 189 ± 293 ± 18.711.9−2.01.7
Europine N-oxide104 ± 1106 ± 2103 ± 299 ± 299 ± 296 ± 292 ± 295 ± 1−3.93.2−1.88.6
Heliotrine106 ± 2100 ± 2103 ± 1109 ± 2101 ± 195 ± 297 ± 294 ± 3−2.23.8−1.11.3
Heliotrine N-oxide97 ± 297 ± 2103 ± 1103 ± 2102 ± 1103 ± 195 ± 196 ± 3−9.5−10.0−7.2−3.7
Jacobine97 ± 190 ± 190 ± 299 ± 291 ± 279 ± 299 ± 295 ± 2−11.8−1.2−3.1−2.1
Jacobine N-oxide95 ± 3104 ± 2113 ± 2103 ± 189 ± 199 ± 2101 ± 197 ± 22.8−10.52.1−1.9
Lasiocarpine103 ± 1105 ± 2104 ± 2104 ± 297 ± 2103 ± 1100 ± 296 ± 2−1.9−8.4−5.9−2.0
Lasiocarpine N-oxide101 ± 299 ± 194 ± 1101 ± 2103 ± 2102 ± 2100 ± 2104 ± 210.6−3.0−2.97.1
Monocrotaline100 ± 298 ± 2101 ± 288 ± 2104 ± 294 ± 296 ± 288 ± 24.1−16.2−0.8−0.9
Monocrotaline N-oxide98 ± 2101 ± 287 ± 293 ± 199 ± 197 ± 297 ± 291 ± 2−1.7−12.82.2−2.4
Retrorsine93 ± 186 ± 289 ± 294 ± 298 ± 295 ± 299 ± 195 ± 3−1.7−12.00.5−0.9
Retrorsine N-oxide99 ± 289 ± 288 ± 295 ± 298 ± 299 ± 298 ± 397 ± 29.8−15.62.94.3
Senecionine92 ± 297 ± 276 ± 292 ± 399 ± 298 ± 297 ± 2101 ± 14.910.6−1.52.0
Senecionine N-oxide99 ± 2101 ± 2103 ± 2104 ± 2102 ± 287 ± 2102 ± 299 ± 23.6−11.9−4.41.4
Seneciphylline96 ± 394 ± 2103 ± 297 ± 195 ± 287 ± 296 ± 298 ± 3−14.8−16.1−1.80.9
Seneciphylline N-oxide100 ± 199 ± 197 ± 296 ± 2100 ± 394 ± 294 ± 296 ± 24.6−7.6−3.6−3.4
Senecivernine98 ± 399 ± 297 ± 197 ± 2102 ± 277 ± 189 ± 199 ± 2−12.9−16.8−8.3−12.8
Senecivernine N-oxide99 ± 298 ± 289 ± 297 ± 3101 ± 2100 ± 295 ± 299 ± 21.6−13.3−4.6−7.6
Riddelline99 ± 195 ± 2102 ± 2104 ± 295 ± 278 ± 293 ± 393 ± 1−2.4−12.5−1.61.1
Riddelline N-oxide98 ± 299 ± 3103 ± 283 ± 191 ± 175 ± 281 ± 289 ± 2−5.4−14.83.12.9
Senkirkine85 ± 290 ± 289 ± 296 ± 292 ± 281 ± 299 ± 2102 ± 24.7−8.5−1.91.3
Trichodesmine100 ± 295 ± 299 ± 298 ± 2102 ± 186 ± 390 ± 296 ± 21.4−12.1−2.3−6.1
Integerrimine99 ± 298 ± 398 ± 293 ± 290 ± 291 ± 489 ± 289 ± 211.64.81.113.1
Atropine88 ± 280 ± 283 ± 286 ± 2100 ± 279 ± 291 ± 3100 ± 2−4.6−11.1210.46.4
Scopolamine90 ± 280 ± 279 ± 287 ± 186 ± 283 ± 288 ± 294 ± 12.5−4.20.84.4
Intermedine
Lycopsamine
Indicine
101 ± 294 ±3100 ± 2100 ± 1102 ± 198 ± 295 ± 399 ± 3−10.39.73.5−7.0
Intermedine-N-oxides
Lycopsamine-N-oxides
Indicine-N-oxides
97 ± 195 ± 3103 ± 1102 ± 298 ± 299 ± 398 ± 1100 ± 2−12.0−9.4−6.4−5.6
Table 3. PA and TA levels in analyzed the tea and culinary herb samples.
Table 3. PA and TA levels in analyzed the tea and culinary herb samples.
SampleNumber of SamplesMean of the PAsConcentration Range of the PAs (ng g−1)Mean of the TAsConcentration Range of the TAs
(ng g−1)
Number of PAs + TAs
Black tea4142.495.2–196.3<LOQ<LOQ8
Green tea2434.587.4–781.6241.1<LOQ−482.37
Mixed tea2336.376.3–596.317.5<LOQ−35.16
Flavored tea2143.6107.4–179.814.6<LOQ−29.35
Chamomile tea5421.131.5–1054.5111.8<LOQ−559.210
Peppermint Tea8308.473.6–547.9<LOQ<LOQ10
Thyme1587.84.6–435.9<LOQ<LOQ6
Sage tea2144.930.8–259.1<LOQ<LOQ8
Linden tea2160.921.1–300.8<LOQ<LOQ8
Fennel tea1-35.7-<LOQ4
Rosehip tea1-68.6-244.78
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Gumus, Z.P. Assessment of Toxic Pyrrolizidine and Tropane Alkaloids in Herbal Teas and Culinary Herbs Using LC-Q-ToF/MS. Foods 2023, 12, 3572. https://doi.org/10.3390/foods12193572

AMA Style

Gumus ZP. Assessment of Toxic Pyrrolizidine and Tropane Alkaloids in Herbal Teas and Culinary Herbs Using LC-Q-ToF/MS. Foods. 2023; 12(19):3572. https://doi.org/10.3390/foods12193572

Chicago/Turabian Style

Gumus, Zinar Pinar. 2023. "Assessment of Toxic Pyrrolizidine and Tropane Alkaloids in Herbal Teas and Culinary Herbs Using LC-Q-ToF/MS" Foods 12, no. 19: 3572. https://doi.org/10.3390/foods12193572

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop