1. Introduction
Zearalenone (ZEN), mainly produced by F. graminearum and other Fusarium species, is one of the most important mycotoxins frequently found in maize, barley, wheat, and compound feeds (poultry, pig, dairy, cattle, and pet feeds) [1,2,3,4]. A number of toxicities were revealed to be associated with ZEN, including teratogenicity, mutagenicity, nephrotoxicity, immunotoxicity, genotoxicity, and carcinogenicity [5]. It is also an estrogen analogue, which can affect the reproductive system and lead to abnormal reproductive functions [6,7,8,9]. Due to its widespread occurrence and high toxicity, the maximum regulation level of 100–3000 μg/kg has been set for ZEN in feeds and feed materials by the European Union (EU) [10]. The European Food Safety Authority (EFSA) set a tolerable daily intake (TDI) for ZEN of 0.25 μg/kg body weight (BW) per day [11].
In recent years, masked mycotoxins generated by plants during detoxification have aroused more and more attention due to their potential toxicities and the difficulties in their detection [12,13,14]. As a masked form of ZEN, zearalenone-14-glucoside (ZEN-14G) was discovered to occur in grains such as maize (16.7%), barley (17.6%), and rice bran (60%), with the levels ranging from 1.3 μg/kg to 274 μg/kg [15,16,17]. Common foods such as fiber-enriched bread (29%), oatmeal (38%), and breakfast cereals (40%) were also contaminated with ZEN-14G [18]. ZEN-14G frequently co-occurs with ZEN in wheat (42%) and various feed products (formula feed, concentrated feed, and premixed feed) (35%) at concentration ranges of 17–104 μg/kg and 0.89–15.31 μg/kg, respectively [19,20]. Although it has low toxicity, ZEN-14G could be converted to ZEN within the digestive tract of mammals, posing potential health risks to humans and/or animals [21,22,23]. Therefore, the European Commission declared that it is essential to assess the exposure of ZEN-14G apart from ZEN [24].
In recent years, comprehensive investigations on the absorption, distribution, metabolism, and excretion of ZEN have been extensively conducted in different animal species [25,26,27]. Among them, pigs were reported by Biehl et al. to have absorption ratios of approximately 80–85%, and Fleck et al. revealed that the absolute oral bioavailability was about 51.5% [25,28]. In comparison, fewer studies could be found on ZEN-14G. An in vitro study carried out by Cirlini et al. clearly indicated that ZEN-14G could pass through the cell barrier to be absorbed by a human colorectal cancer cell line (Caco-2) and further converted into ZEN [29]. Dellafiora et al. revealed that ZEN-14G could be absorbed into a human breast cancer cell line (MCF-7) and cleaved to ZEN by an estrogen-sensitive cell culture [30]. Additionally, as reported, more than 97% of ZEN-14G could be rapidly and efficiently hydrolyzed to ZEN by the colonic microbiota, and even completely cleaved after 24 h of fecal fermentation [12,31]. The investigations of Yang et al. indicated that ZEN-14G could be deglucosylated into ZEN in the liver microsomes of several animals (swine, rats, goats, cows, and chickens) and humans [32]. However, knowledge of the in vivo kinetics and transformations of ZEN-14G are still insufficient, hindering the assessment of the exposure risks to humans and animals related to this masked mycotoxin.
The development of reliable and sensitive analytical technologies is the primary requirements for investigations into the in vivo kinetics and distributions of ZEN-14G and its metabolite, ZEN. Various analytical methods have been developed to detect ZEN, including the enzyme-linked immunosorbent assay (ELISA), thin-layer chromatography (TLC), gas chromatography–mass spectrometry (GC-MS), and high-performance liquid chromatography–tandem mass spectrometry (HPLC-MS/MS) [25,33,34]. ELISA provides high sensitivity, but it only serves as a supplementary method due to its erratic accuracy and the possibility of cross-reactivity [35,36]. Although it is simple and rapid, the unsatisfactory accuracy and poor separation of TLC limit its application [37,38]. Detection by GC-MS is a frequently used method, but requires critical and time-consuming derivatization steps [39]. HPLC-MS/MS is regarded as the most promising tool because of its high selectivity and sensitivity [40,41,42]. However, the current analytical methods can barely be utilized for the simultaneous detection of ZEN and ZEN-14G in various biomatrices due to the great challenges posed by their different polarities, along with the significant matrix effects.
In the current study, a rapid and sensitive HPLC-MS/MS method was established for the simultaneous detection of ZEN and ZEN-14G in the plasma, urine, and various tissues of rats, i.e., the liver, kidney, stomach, small intestine, large intestine, and ovary. The greatest advantage of this proposed analytical method was that identical conditions could be utilized for analyzing ZEN and ZEN-14G in all the above mentioned biomatrices to achieve high sensitivity, accuracy, and reliability. Through use of the methodological advantages, the kinetics and tissue distribution of ZEN-14G after oral administration to rats was successfully investigated.
2. Materials and Methods
2.1. Reagents and Chemicals
ZEN-14G was acquired from HPC Standards GmbH (Borsdorf, Germany). ZEN was bought from Sigma-Aldrich (Saint Louis, MO, USA). Acetonitrile and methanol are commercially available from Merck (Darmstadt, Germany). Milli-Q quality water was used for analysis (Millipore, Billerica, MA, USA). The chemical reagents used were of either HPLC or analytical grade.
2.2. Animal Trials
Sprague–Dawley rats (female, 200–250 g, 6–8 weeks) were bought from Shanghai Jihui Laboratory Animal Care Co., Ltd. (Shanghai, China). The rats were kept for a week at a relative humidity of 50–65%, a temperature of 22 ± 3 °C, and a dark/light cycle of 12 h to adapt them to the experimental environments. They were subjected to 12-hour fasting before administration of the gavage. The control group was given a normal diet without any treatment, while the experimental group, reared in independent metabolic cages, was administered ZEN-14G dissolved in an ethanol aqueous solution (25%, v/v) (4 mg/kg BW, n = 3) by gavage. No adverse effects were observed in the rats after administration by gavage. The animal experiments were conducted in accordance with the Laboratory Animal Ethics Committee of the Shanghai Academy of Agricultural Science (Shanghai, China) (SAASPZ0921015).
2.3. Sample Collection
After analysis by the developed HPLC-MS/MS method, the samples of plasma, different tissues, and urine obtained from the control group were free from ZEN or ZEN-14G, and were thus used as the blank matrices to establish and validate the analytical method (Figure 1A).
Plasma samples were individually collected from rats via the tail vein at 5, 10, 15, 30, 60, 120, 240, 480, and 1440 min after the administration of ZEN-14G by gavage (4 mg/kg BW). The supernatant was transferred into K2-ethylenediaminetetraacetic acid (EDTA) tubes (Becton Dickinson and Co., Franklin Lakes, NJ, USA) after centrifugation (800× g, 4 °C, 20 min) and kept at −20 °C. Urine was collected for the periods 0–6 h, 6–12 h, and 12–24 h after administration and stored at −20 °C. All rats were sacrificed 24 h after administration, and the liver, kidney, stomach, small intestine, large intestine, and ovary were collected. After harvesting, the tissues were rinsed with saline, individually homogenized with triple volumes of normal saline, and stored at −20 °C until analysis.
2.4. Sample Preparation
The samples of the plasma, urine, and tissue homogenates (200 μL) were ultrasonically extracted (Shanghai Ampu Experimental Technology Co., Ltd., Shanghai, China) with 1 mL of formic acid/acetonitrile (1/99, v/v) for 10 min at 40 °C, followed by vortexing (Bono Biotechnology Co., Ltd., Shanghai, China) for 5 min. After centrifugation (13,000× g, 5 min) (Eppendorf, Hamburg, Germany), the supernatant was gathered and dried at 40 °C with nitrogen (Organomation Associates, Inc., Dublin, OH, USA). The residues were redissolved in a 200 µL acetonitrile–water mixture containing 5 mmol/L ammonium acetate (30/70, v/v), filtered through a 0.22 μm nylon filter (Pall, Port Washington, NY, USA), and stored for analysis.
2.5. HPLC-MS/MS Analysis
The target analytes were separated by a Waters ACQUITY UPLC system at 40 °C using an XBridge® C18 column XP (3.0 × 100 mm, 2.5 μm) (Waters, Milford, MA, USA). A linear gradient elution program using a mobile phase consisting of (A) methanol and (B) water containing 5 mmol/L ammonium acetate was set as follows: 0–1 min, 10% A; 1–6 min, 90% A; 6–6.5 min, 90% A; 6.5–6.7 min, 10% A; 6.7–8 min, 10% A. The injection volume was 3 μL and the flow rate was 0.4 mL/min.
The MS/MS acquisition was realized by a Triple-Quad™ 5500 mass spectrometer equipped with an electrospray ionization (ESI) interface operating in both negative (ESI−) and positive (ESI+) modes (AB SCIEX, Foster City, CA, USA). The analysis was conducted with the following parameters: ion spray voltage, 4.5–5.5 kV; source temperature, 450 °C; curtain gas pressure, 35 psi; nebulizer gas, 50 psi; turbo gas pressure, 50 psi. ZEN and ZEN-14G were quantitatively analyzed by multiple reaction monitoring (MRM) (Table 1). Data were processed and analyzed with MultiQuant 3.0.2 software (AB SCIEX, Foster City, CA, USA).
2.6. Method Validation
The newly developed method was validated by examining the selectivity, the lower limit of detection (LLOD), the lower limit of quantification (LLOQ), linearity, recovery, precision, and stability according to the FDA guidelines [43]. The blank matrices, the matrices spiked with ZEN and ZEN-14G (20 μg/L), and the real collected samples after administration of ZEN-14G by gavage were investigated to illustrate the selectivity of the developed method. Standard solutions with concentrations of 0.1, 0.2, 0.5, 1, 2, 5, 10, 20, 50, 100, and 200 μg/L for ZEN and ZEN-14G were prepared in the blank matrices of the plasma, liver, kidney, stomach, small intestine, large intestine, ovary, urine and acetonitrile–water containing 5 mmol/L ammonium acetate (30/70, v/v). The responses of MS (peak areas) to the concentrations of the analytes were plotted to construct the calibration curves (1/x weighted). The ratio of the slope of the matrix-matched calibration curve to that of pure solvent was calculated to illustrate the matrix effect (signal suppression/enhancement, SSE). The sensitivity was expressed as the LLOD and LLOQ. The LLOQ was defined as the lowest concentration of the calibration curve that acquired a signal-to-noise ratio (S/N) value of 10, with the precision within 20%, and an accuracy of 80–120%. The LLOD was obtained by dividing the LLOQ by 3.
Samples of blank plasma, urine, and various tissues spiked with ZEN and ZEN-14G at the LLOQ, and low (5 μg/L), intermediate (20 μg/L), and high (50 μg/L) levels were used for the recovery, precision, and stability tests (n = 5). Equation (1) was used to calculate the recovery through a comparison of the detected concentrations with the ideal (spiked) levels of each analyte [44]. The relative standard deviation (RSD) measured within one day and on five consecutive days represented the intra-day and inter-day precision, respectively. Plasma, urine, and various tissue samples containing ZEN and ZEN-14G at the LLOQ and low, intermediate, and high concentrations were determined to assess the short-term (room temperature, 8 h), long-term (−20 °C, 20 days), and freeze–thaw (three cycles) stability.
Recovery = Concentration measured/Concentration spiked × 100%(1)
2.7. Statistical Analysis
Toxicokinetic data were processed by the non-compartmental method with WinNonlin 8.1 software (Pharsight Co., Mountain View, CA, USA). SPSS 27 software (SPSS Inc., Chicago, IL, USA) was applied for statistical analyses of the data.
3. Results and Discussion
3.1. Optimization of the HPLC Conditions
The HPLC conditions were carefully optimized according to our previously described protocols [20]. The results revealed that a methanol–water mixture containing 5 mmol/L ammonium acetate resulted in the highest ionization efficiency and good peak shapes for both analytes (Supplemental Figures S1 and S2).
3.2. Optimization of Sample Preparation
3.2.1. Sample Extraction
Three candidate extraction solvents, i.e., methanol, acetone, and acetonitrile, were compared in spiked plasma (50 μg/L). The extraction recovery (RE) was determined by Equation (2) [45]. As shown in Figure 2A, when methanol and acetone were utilized, the recovery of ZEN-14G was above 85%, but ZEN achieved relatively lower recovery levels (only 79.1 ± 2.1% for methanol and 78.3 ± 3.6% for acetone). The highest RE values (ZEN: 91.7 ± 5.8%; ZEN-14G: 90.9 ± 7.0%) were found for acetonitrile. Studies have reported that an acidic medium would break the chemical bonds between the analyte and other molecules to benefit their transfer to the organic solvent, contributing to an improved extraction efficiency [46,47]. Then the extraction effects of acetonitrile containing different contents of formic acid (0.25, 0.5, 0.75, 1, 2, 3, and 4%) were investigated. The highest RE values were achieved when acetonitrile containing 1% formic acid was chosen as the extraction solution (Figure 2B).
RE = A/B × 100%(2)
where A represents the peak area of the analyte in the plasma spiked before extraction, and B represents the peak area of the analyte in the plasma spiked after extraction.3.2.2. Re-Dissolution of the Samples
Re-dissolution is a basic operation in the pretreatment of samples because its efficiency directly affects the recovery. To optimize the re-dissolution effects of the analytes, the efficiency of solutions with different percentages were compared, including: (1) an acetonitrile–water mixture containing 5 mmol/L ammonium acetate (10/90, v/v), (2) an acetonitrile–water mixture containing 5 mmol/L ammonium acetate (20/80, v/v), (3) an acetonitrile–water mixture containing 5 mmol/L ammonium acetate (30/70, v/v), (4) an acetonitrile–water mixture containing 5 mmol/L ammonium acetate (40/60, v/v), and (5) an acetonitrile–water mixture containing 5 mmol/L ammonium acetate (50/50, v/v). As shown in Table S1, with an increase in the proportion of acetonitrile, the recovery of ZEN increased sharply and then decreased slowly, while ZEN-14G always showed a steady trend. Satisfactory recovery rates were obtained for the two analytes when the acetonitrile–water mixture containing 5 mmol/L ammonium acetate in water (30/70, v/v) was chosen. This might be related to the fact that both analytes, which had different properties, had relatively good solubility in this re-dissolving solution.
3.3. Validation of the Method
The analytical performance of HPLC-MS/MS was evaluated by the selectivity, linearity, sensitivity, precision, and stability parameters. The method was selective for both ZEN and ZEN-14G in the plasma, different tissues, and urine, since no interference peaks appeared during the retention time in blank samples, also indicating that no ZEN or ZEN-14G existed in the regular rat feed (Figure 1). The SSE values for ZEN and ZEN-14G were 31–79% and 70–87%, respectively. The matrix-matched calibration curves were constructed to compensate for the matrix effects to accurately quantify the two analytes. Satisfactory linear relationships of the two target analytes were observed, with the coefficients of determination (R2) greater than 0.99. The LLOD and LLOQ obtained were 0.03–0.3 μg/L and 0.1–1.0 μg/L, respectively (Table 2), which were obviously lower than those in plasma reported by Catteuw et al. (ZEN, 7.4 μg/L) [48] and Catteuw et al. (ZEN-14G, 1.7 μg/L) [49], but higher than those in plasma reported by Sun et al. (ZEN, 0.1 μg/L; ZEN-14G, 0.03 μg/L) [24]. To date, there have been few studies on the simultaneous detection of ZEN and ZEN-14G in the plasma, different tissues, and urine of rats. The LLOQ values in this approach were obviously lower than or comparable with those in several tissues and urine reported (0.6–0.8 μg/L) by Veršilovskis et al. [50], proving that the sensitivity of the established method was sufficient for measuring both analytes in different biological matrices. Acceptable recovery rates of ZEN (80.7 ± 3.0–112.3 ± 3.1%) and ZEN-14G (85.0 ± 4.9–109.3 ± 2.4%) were obtained with the RSD values of intra-day and inter-day precision being in the range of 0.9–14.6% and 0.6–16.5%, respectively (Table 3). After a detailed study of the stability under different conditions, ZEN and ZEN-14G were fully verified to be stable (81.7 ± 1.7–104.1 ± 3.9%) in the plasma, different tissues, and urine of rats (Table S2). These satisfactory parameters proved that the developed method was selective, accurate, sensitive, and stable, and could be used for studies of the kinetics and distribution of ZEN and ZEN-14G in rats.
To better understand the strengths and weaknesses of the developed HPLC-MS/MS method, we further compared it with previously reported methods of determining ZEN and ZEN-14G. In comparison with the rapid detection methods, namely immunoassays or aptasensors [51,52], the current method exhibited comparable sensitivity and accuracy, and could be applied for the simultaneous determination of two compounds with different polarities in a variety of matrices. The method of ultra-high performance liquid chromatography coupled with quadrupole time-of-flight tandem mass spectrometry (UHPLC-Q-TOF/MS) previously developed in our lab was also tested and showed high selectivity for the targets in different matrices (Figures S3–S8), but the sensitivity with the screening detection limits (SDLs) ranging from 50 μg/L to 200 μg/L seemed relatively lower (Table S3) [53]. A parallel analysis was carried out using the current method and a series of previously established LC-MS/MS methods for the analysis of ZEN and its glucoside in the plasma [54], liver [50], and urine [55] (Table S4). Accurate results were obtained independent of the matrix tested, proving it to be a promising tool for studies of the kinetics and distribution of ZEN and ZEN-14G in rats.
3.4. Kinetics and Tissue Distribution
For the in vivo study of the kinetics and tissue distribution, different solvents, i.e., ethanol/water (10/90, v/v), ethanol/water (20/70, v/v), ethanol/water (25/75, v/v), ethanol/water (30/70, v/v), and ethanol/water (40/60, v/v), were compared for the solubility of ZEN-14G for administration to rats by gavage. When the percentage of ethanol was no less than 25%, satisfactory solubility (>99%) was achieved, and therefore ethanol/water (25/75, v/v) was selected (Table S5).
After administration by gavage, ZEN-14G could be absorbed and converted into its prototype, ZEN, resulting in additional health risks to humans or animals. Both ZEN and ZEN-14G exhibited similar metabolic trends and reached peak concentrations of 4.4 ± 1.2 µg/L and 2.8 ± 0.2 µg/L in 10 min, respectively (Table 4). After that, ZEN and ZEN-14G rapidly decreased (Figure 3). The low plasma concentrations of ZEN-14G might be due to its poor absorption (oral bioavailability <10%) [24]. The elimination half-life of ZEN-14G was consistent with that acquired by Sun et al. [24] but was lower than that for ZEN obtained by Lu et al., attributed to the higher polarity of the glycoside’s structure [56].
The tissue distribution of ZEN-14G and its metabolite, ZEN, is shown in Figure 4. ZEN-14G was still detectable in the stomach, small intestine, and large intestine 24 h after administration by gavage, and this could be hydrolyzed into ZEN in the digestive tract by the intestinal flora during digestion [57,58]. Compared with investigations into ZEN-14G in the digestive tract for a short time (55 min) [50], our results suggested that ZEN-14G may be continuously and slowly converted to low levels of ZEN that are absorbed into the plasma and subsequently distributed to various tissues. Relatively higher amounts of ZEN were quantified in all tested tissues. The ranked order was as follows: small intestine > large intestine > liver > stomach > ovary > kidney. The highest concentration detected in the small intestine was 1004.9 ± 155.0 µg/L.
Both ZEN-14G and its metabolite, ZEN, were detected in the urine (Figure 5). The amounts of urinary ZEN-14G were low and showed a decreasing trend at concentration levels from 43.9 ± 11.1 μg/L to 7.6 ± 3.0 μg/L within 24 h. These results were consistent with our data in plasma showing that ZEN-14G could be absorbed directly into the plasma in small amounts. Compared with ZEN-14G, ZEN maintained relatively higher levels ranging from 301.4 ± 36.7 μg/L to 4801.5 ± 424.8 μg/L, with the highest concentration detected at 6–12 h, indicating that ZEN-14G was slowly and continuously cleaved to ZEN, followed by sustainable absorption and excretion (Figure 6). Although ZEN-14G is less toxic than ZEN, the cumulative health risks related ZEN-14G cannot be neglected.
4. Conclusions
An effective HPLC-MS/MS method was established for the analysis of ZEN-14G and its metabolite, ZEN, in the plasma, various tissues, and urine of rats. After careful validation, the developed method was proved to be selective, accurate, sensitive, and stable, and was subsequently applied to explore the kinetics and tissue distribution after the administration of ZEN-14G by gavage to rats. ZEN-14G could be partially absorbed into the plasma and partially converted into ZEN, followed by sustained absorption and excretion. After 24 h, ZEN-14G could still be detected in the digestive tract and urine, while its metabolite, ZEN, could be found in all biosamples at high concentrations, verifying the cumulative health risks to humans and animals. Therefore, it is recommended to include masked mycotoxins in monitoring and control programs of agricultural practices and food safety authorities, with the established method as a powerful tool.
Investigation, methodology, writing—original draft, writing—review and editing, Y.C.; investigation, methodology, writing—review and editing, Z.Z. (Zhiqi Zhang); data curation, F.D.; software, Z.M.; methodology, validation, K.F.; funding acquisition, methodology, supervision, writing—review and editing, Z.H.; validation, writing—review and editing, supervision, project administration, Z.L.; funding acquisition, methodology, supervision, Z.Z. (Zhihui Zhao). All authors have read and agreed to the published version of the manuscript.
The study was conducted in accordance with the Declaration of Helsinki, and approved by the Laboratory Animal Ethics Committee at the Shanghai Academy of Agricultural Science of China (protocol code: SAASPZ0921015; date of approval: 2022).
Not applicable.
The data presented in this study are available in this article and the
The authors declare no conflict of interest.
Footnotes
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Figure 1. MRM chromatograms of zearalenone (ZEN) and zearalenone-14-glucoside (ZEN-14G) in blank plasma, small intestine, and urine samples (A); plasma, small intestine, and urine samples spiked with ZEN and ZEN-14G at the level of 20 μg/L (B); and the plasma samples gathered at 10 min, small intestine samples gathered at 24 h, and urine samples gathered at 6 h after the administration of ZEN-14G by gavage (4 mg/kg body weight) in rats (C).
Figure 2. The extraction efficiencies of zearalenone (ZEN) and zearalenone-14-glucoside (ZEN-14G) by three candidate solvents (A) and acetonitrile containing different contents of formic acid (0.25–4%, v/v) (B) were compared. The concentration is 50 μg/L. Acceptable recovery rates are between 70% and 120%.
Figure 3. The plasma concentration vs. time profiles after the administration of zearalenone-14-glucoside (ZEN-14G) by gavage to rats (dose of 4 mg/kg body weight, n = 3).
Figure 4. Tissue distribution of zearalenone-14-glucoside (ZEN-14G) and its metabolite, zearalenone (ZEN), in rats (dose of 4 mg/kg body weight, n = 3).
Figure 5. The concentrations of zearalenone-14-glucoside (ZEN-14G) and zearalenone (ZEN) in urine collected 6–24 h after oral administration to rats (dose of 4 mg/kg body weight, n = 3).
Figure 6. The supposed biotransformation characteristics in the plasma, tissue distribution, and urinary excretion after the administration of ZEN-14G by gavage to rats.
MS/MS parameters of the masked mycotoxin zearalenone-14-glucoside (ZEN-14G) and its metabolite, zearalenone (ZEN).
Mycotoxin | Retention Time (min) | Precursor Ion (m/z) | Products Ion (m/z) | Collision Energy |
Ionization Mode |
---|---|---|---|---|---|
ZEN-14G | 5.90 | 481.2 | 319.2 * | 12 | ESI+ |
283.1 | 20 | ||||
ZEN | 6.78 | 316.9 | 174.9 * | −35 | ESI− |
131.0 | −40 |
“*” Primary product ions.
Linearity, lower limit of detection (LLOD), lower limit of quantification (LLOQ), and matrix effect (SSE) of zearalenone (ZEN) and zearalenone-14-glucoside (ZEN-14G).
Matrix | Mycotoxin | Linear Range |
Slope | Intercept | R 2 | LLOD |
LLOQ |
SSE |
---|---|---|---|---|---|---|---|---|
Solvent | ZEN | 0.1–200 | 76,190 | 11,438 | 0.999 | / | / | / |
ZEN-14G | 0.1–200 | 8063 | 639 | 0.999 | / | / | / | |
Plasma | ZEN | 0.5–200 | 57,817 | 22,503 | 0.999 | 0.2 | 0.5 | 76 |
ZEN-14G | 0.5–200 | 6322 | 2427 | 0.999 | 0.2 | 0.5 | 79 | |
Liver | ZEN | 1–200 | 43,990 | 43,727 | 0.999 | 0.3 | 1 | 58 |
ZEN-14G | 1–200 | 6792 | 8478 | 0.998 | 0.3 | 1 | 84 | |
Kidney | ZEN | 0.1–200 | 60,238 | 11,066 | 0.999 | 0.03 | 0.1 | 79 |
ZEN-14G | 0.1–200 | 6828 | 1006 | 0.999 | 0.03 | 0.1 | 85 | |
Stomach | ZEN | 0.2–200 | 39,823 | 52,550 | 0.999 | 0.06 | 0.2 | 52 |
ZEN-14G | 0.5–200 | 6567 | 1994 | 0.999 | 0.2 | 0.5 | 82 | |
Small intestine | ZEN | 0.5–200 | 23,466 | 48,872 | 0.999 | 0.2 | 0.5 | 31 |
ZEN-14G | 1–200 | 5674 | 13,574 | 0.999 | 0.3 | 1 | 70 | |
Large intestine | ZEN | 0.5–200 | 23,850 | 55,944 | 0.999 | 0.2 | 0.5 | 31 |
ZEN-14G | 0.1–200 | 6111 | 8753 | 0.996 | 0.03 | 0.1 | 76 | |
Ovary | ZEN | 0.5–200 | 60,129 | 48,669 | 0.999 | 0.2 | 0.5 | 79 |
ZEN-14G | 0.5–200 | 7009 | 2030 | 0.999 | 0.2 | 0.5 | 87 | |
Urine | ZEN | 0.2–200 | 52,337 | 8821 | 0.999 | 0.06 | 0.2 | 69 |
ZEN-14G | 0.1–200 | 6865 | 906 | 0.999 | 0.03 | 0.1 | 85 |
Recovery rates, and intra- and inter-day precision of zearalenone (ZEN) and zearalenone- 14-glucoside (ZEN-14G) (n = 5).
Matrix | Mycotoxin | Spiked Level |
Recovery |
Precision (RSD, %) | |
---|---|---|---|---|---|
Intra-Day | Inter-Day | ||||
Plasma | ZEN | LLOQ | 86.4 ± 2.8 | 7.3 | 10.0 |
5 | 92.1 ± 2.3 | 2.6 | 3.0 | ||
20 | 91.1 ± 3.0 | 2.9 | 3.5 | ||
50 | 94.2 ± 3.4 | 6.0 | 5.4 | ||
ZEN-14G | LLOQ | 103.0 ± 3.5 | 6.7 | 10.4 | |
5 | 102.5 ± 1.1 | 6.0 | 4.1 | ||
20 | 97.6 ± 3.4 | 2.5 | 3.5 | ||
50 | 95.9 ± 1.8 | 3.8 | 3.2 | ||
Liver | ZEN | LLOQ | 93.9 ± 8.0 | 14.6 | 13.2 |
5 | 93.9 ± 4.0 | 3.4 | 5.7 | ||
20 | 109.7 ± 2.9 | 3.1 | 6.4 | ||
50 | 104.3 ± 2.6 | 3.7 | 3.2 | ||
ZEN-14G | LLOQ | 102.2 ± 4.5 | 7.4 | 7.2 | |
5 | 96.3 ± 3.0 | 2.6 | 3.3 | ||
20 | 103.6 ± 1.8 | 4.2 | 2.8 | ||
50 | 108.7 ± 2.4 | 6.9 | 5.9 | ||
Kidney | ZEN | LLOQ | 80.7 ± 3.0 | 14.0 | 15.8 |
5 | 101.5 ± 0.8 | 4.9 | 5.5 | ||
20 | 106.2 ± 3.5 | 4.8 | 4.5 | ||
50 | 108.3 ± 3.9 | 4.9 | 2.3 | ||
ZEN-14G | LLOQ | 85.0 ± 4.9 | 13.0 | 13.0 | |
5 | 108.7 ± 1.6 | 2.7 | 2.3 | ||
20 | 107.8 ± 2.0 | 3.7 | 2.4 | ||
50 | 107.9 ± 1.4 | 6.3 | 3.5 | ||
Stomach | ZEN | LLOQ | 90.4 ± 6.2 | 13.6 | 11.1 |
5 | 95.6 ± 3.6 | 3.0 | 4.4 | ||
20 | 99.3 ± 1.1 | 4.4 | 1.6 | ||
50 | 93.8 ± 2.7 | 8.8 | 1.9 | ||
ZEN-14G | LLOQ | 94.9 ± 5.9 | 9.8 | 13.3 | |
5 | 104.9 ± 0.9 | 6.6 | 2.5 | ||
20 | 100.4 ± 3.5 | 4.2 | 4.1 | ||
50 | 100.8 ± 4.1 | 5.9 | 3.0 | ||
Small intestine | ZEN | LLOQ | 88.8 ± 3.3 | 4.1 | 11.0 |
5 | 95.0 ± 1.9 | 2.0 | 4.8 | ||
20 | 94.2 ± 4.2 | 2.9 | 12.3 | ||
50 | 100.2 ± 3.1 | 3.3 | 7.5 | ||
ZEN-14G | LLOQ | 99.6 ± 4.1 | 5.1 | 6.2 | |
5 | 100.6 ± 2.2 | 3.4 | 7.5 | ||
20 | 98.2 ± 3.6 | 3.2 | 9.0 | ||
50 | 100.7 ± 1.0 | 3.3 | 4.9 | ||
Large intestine | ZEN | LLOQ | 86.9 ± 4.5 | 8.5 | 12.8 |
5 | 103.5 ± 3.0 | 2.4 | 2.9 | ||
20 | 112.3 ± 3.1 | 4.3 | 7.3 | ||
50 | 98.1 ± 8.6 | 3.9 | 3.9 | ||
ZEN-14G | LLOQ | 95.6 ± 3.6 | 11.3 | 5.3 | |
5 | 109.3 ± 2.4 | 3.3 | 1.7 | ||
20 | 100.4 ± 4.7 | 6.4 | 6.3 | ||
50 | 102.7 ± 5.3 | 3.5 | 4.3 | ||
Ovary | ZEN | LLOQ | 92.7 ± 10.3 | 11.8 | 16.5 |
5 | 95.0 ± 3.3 | 3.1 | 5.6 | ||
20 | 94.0 ± 1.4 | 2.8 | 3.1 | ||
50 | 103.9 ± 1.7 | 2.4 | 3.1 | ||
ZEN-14G | LLOQ | 95.5 ± 0.5 | 13.2 | 10.4 | |
5 | 101.3 ± 3.1 | 2.8 | 3.9 | ||
20 | 100.6 ± 4.9 | 3.7 | 4.3 | ||
50 | 99.2 ± 3.4 | 0.9 | 0.6 | ||
Urine | ZEN | LLOQ | 89.5 ± 7.7 | 5.7 | 7.8 |
5 | 105.2 ± 0.8 | 9.6 | 10.1 | ||
20 | 98.9 ± 0.9 | 7.0 | 7.0 | ||
50 | 103.0 ± 6.2 | 4.5 | 14.1 | ||
ZEN-14G | LLOQ | 92.8 ± 3.2 | 10.2 | 9.7 | |
5 | 95.4 ± 7.0 | 10.1 | 8.5 | ||
20 | 102.4 ± 3.4 | 11.3 | 7.9 | ||
50 | 102.3 ± 3.2 | 4.6 | 3.9 |
Kinetic parameters after the administration of zearalenone-14-glucoside (ZEN-14G) by gavage to rats (dose of 4 mg/kg body weight, n = 3).
Parameter | Unit | ZEN-14G |
---|---|---|
AUCZEN-14G | h·µg/L | 3.0 ± 0.4 |
AUCZEN | h·µg/L | 1.3 ± 0.2 |
Cmax | µg/L | 4.4 ± 1.2 |
Tmax | h | 0.17 ± 0.0 |
T1/2 | h | 0.8 ± 0.3 |
AUCZEN-14G, area under the curve of ZEN-14G; AUCZEN, area under the curve of ZEN; Cmax, maximum concentration; Tmax, time required to reach the maximum concentration; T1/2, half-life of elimination.
Supplementary Materials
The following supporting information can be downloaded at:
References
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Abstract
A reliable high-performance liquid chromatography-tandem mass spectrometry (HPLC-MS/MS) method was established for the simultaneous detection of zearalenone-14-glucoside (ZEN-14G) and its metabolite, zearalenone (ZEN), in the plasma, urine, and various tissues of rats. The performance of the developed method was validated by determining the selectivity, linearity (R2 > 0.99), sensitivity (lower limit of quantification, 0.1–1 μg/L), recovery (80.7 ± 3.0–112.3 ± 3.1%), precision (0.6–16.5%), and stability (81.7 ± 1.7–104.1 ± 3.9%). Through use of the methodological advances, the subsequent kinetics and distribution after administration of ZEN-14G by gavage were thoroughly investigated. ZEN-14G and ZEN exhibited similar trends in the plasma, and reached their peak concentrations at 10 min and then rapidly decreased. ZEN-14G could be quantified in the stomach, small intestine, and large intestine 24 h after administration, while ZEN was detectable in all tested tissues. Interestingly, ZEN-14G (7.6 ± 3.0 μg/L) and ZEN (977.5 ± 98.0 μg/L) were also detected in the urine 24 h after administration, indicating that ZEN-14G was prone to be slowly and continuously hydrolyzed into ZEN to be absorbed into the plasma and distributed to various tissues, thus leading to a cumulative exposure. Continuous attention should be paid to the co-exposure of ZEN and ZEN-14G, which might pose additional health risks to humans and animals.
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Details
1 School of Life Science and Engineering, Lanzhou University of Technology, Lanzhou 730050, China;
2 Institute for Agro-food Standards and Testing Technology, Shanghai Academy of Agricultural Sciences, Shanghai 201403, China;
3 School of Life Science and Engineering, Lanzhou University of Technology, Lanzhou 730050, China;