1. Introduction
Ochratoxins, particularly Ochratoxin A (OTA), are a group of mycotoxins produced by several fungi such as
Aspergillus ochraceus and
Penicillium verrucosum. These toxins are pervasive in agricultural commodities like maize [
1], wheat [
1], barley [
1], rice, and rice-products [
2], as well as in dried fruit [
3], coffee [
3,
4], cocoa [
3], animal feed [
1], pork [
5], and ewe’s milk [
6], representing a significant health hazard to both humans and animals [
7,
8,
9]. OTA is recognized for its extensive harmful effects across various species, affecting zootechnical performance (e.g., body weight gain, feed/gain ratio, etc.) [
1,
10], leading to reductions in average daily feed intake (ADFI) and egg weight (EW) in laying hens [
11], as well as inducing immunosuppression and inflammation [
12,
13].
On a molecular level, OTA interferes with phenylalanine in reactions catalyzed by phenylalanine-tRNA synthetase and phenylalanine-hydroxylase, while also exacerbating lipid peroxidation [
14,
15]. This dual action disrupts cellular mechanisms and promotes oxidative stress, causing organ damage, particularly in the liver and kidneys, which are the main sites of OTA accumulation and toxicity [
16,
17].
OTA’s toxicokinetics have been widely studied in various animal species, with administration typically through the oral route or via injection. This thorough investigation spans a diverse array of species, including growing pigs [
18], rabbits [
18], chickens [
18], rats [
19], monkeys [
20], dairy ewes [
6], Atlantic salmon [
21], and donkeys [
22]. There is a marked variability in sensitivity to OTA among different species, with livestock and poultry, particularly pigs, showing considerable susceptibility due to a higher affinity for serum proteins [
10,
18]. The efficient absorption and slow elimination of OTA contribute to its persistence in animals [
22], raising concerns about its accumulation in animal products and subsequent transfer to humans through consumption, thereby affecting human health.
Despite existing studies on OTA’s toxicokinetics in growing pigs [
18] and its effects on nursery pigs [
23], research on lactating sows is absent. This gap is significant considering the unique physiological and metabolic changes during lactation, which can affect the detoxification and excretion of toxins like OTA. Moreover, the potential of OTA excretion through milk presents an indirect risk to piglets.
Given these considerations, the primary objective of this study is to explore the toxicokinetics of OTA in lactating sows and to examine the potential transmission of OTA through sow’s milk.
3. Discussion
Research on the toxicokinetics of orally administered OTA has not been previously conducted in lactating sows. Thus, the primary objective of this study was to bridge the existing knowledge gap by investigating the entry rate of OTA into the body, as well as its absorption, distribution, metabolism, and elimination.
In our investigation into the toxicokinetics of OTA across various species, distinct patterns emerged concerning Tmax and T
1/2Elim [
24]. For lactating sows, Tmax occurred at 9 h, and T
1/2Elim at 78.47 h. These findings indicate a longer Tmax in lactating sows compared to poultry [
18,
25], yet shorter than that observed in growing pigs [
18]. Moreover, the T
1/2Elim in lactating sows was found to be slightly shorter than in growing pigs [
18], but significantly longer than in poultry species like broiler chickens and laying hens [
25], as detailed in
Table S1. The variability in OTA elimination half-life across species is likely due to pronounced differences in plasma protein affinity.
Regarding peak concentration (Cmax), a critical indicator of absorption and safety, we observed species-specific and administration route variations. In our study, lactating sows exhibited a Cmax of 0.92 μg/mL following a 500 μg/kg BW dose, a figure that aligns closely with that reported for growing pigs (1.74 μg/mL at 500 μg/kg BW), yet markedly lower than that observed in donkeys, as shown in
Table S1. Notably, within the same species, intravenous injection yielded a higher Cmax than oral administration, underscoring the influence of administration route, dosage, and the physiological stage of the animals. Compared with other livestock animals, our research suggests that lactating sows exhibit characteristics of high absorption and slow excretion of OTA.
After OTA is absorbed, it is distributed throughout the body via the bloodstream, reaching various tissues and organs. This distribution, reflected by the volume of distribution (Vd) values detailed in
Table S1, varies among species. In lactating sows, we observed a Vd nearly fourfold higher than in growing pigs, indicating a broader OTA distribution in these mammals. Our research reveals milk secretion as an additional route of OTA elimination in lactating sows, with peak OTA concentrations in milk occurring at 24 h post ingestion.
Table 5 compares our findings with previous research on growing pigs, indicating a similar rate of OTA excretion in urine; however, the proportion of OTα in our fecal excretion data is relatively low. This difference may be due to methodological limitations in analyzing fecal OTA metabolites, highlighting the significance of milk as a potential route for OTA elimination in our results. It is important to note that challenges in collecting milk samples, influenced by animal welfare considerations, could contribute to these variations. Furthermore, these differences are likely to impact the observed variability in absorption rates among pigs at different physiological stages.
This study marks the first identification of OTA residues in the milk of lactating sows. This finding is significant considering that OTA residues have previously been identified in the milk of dairy cows [
26], dairy ewes [
6], and in humans [
27]. We observed that the milk-to-plasma (M/P) ratio increased from 0.06 to 0.46 within the first 24 h after ingestion (
Table 6), indicating a dynamic pattern of lactational transfer. The ratio, although generally higher than those recorded in dairy ewes (M/P 0.04 to 0.21) over longer periods [
6], aligns with human studies showing that dietary OTA contaminants can be transferred to breast milk [
27]. The average OTA concentration in human breast milk represents about a quarter of that in plasma (M/P 0.25), with a notable increase in OTA excretion during the first week post delivery (M/P 0.4) [
27].
Additionally, we must acknowledge the limitations of this study, such as significant fluctuations in OTA excretion in milk over time, necessitating that the M/P value may be viewed only as an approximate indicator of this mycotoxin’s transmission through milk.
5. Materials and Methods
5.1. Mycotoxins
The standards of OTA and OTα used for animal experiments and sample analysis in this study were obtained from Pribolab Biological Engineering Co. Ltd. (Qingdao, China), while acetonitrile (ACN) and methanol (MeOH) used for the sample analysis were all HPLC-MS grade (Fisher Chemical, Pittsburgh, PA, USA). Physiological saline and dimethyl sulfoxide (DMSO, sigma, Tokyo, Japan) used for the animal oral administration were both cell-culture grade.
5.2. Animals and Experimental Diets
The experiment was approved by the Animal Welfare and Ethics Committee of China Agricultural University. The feeding experiment was carried out at the Experimental Feeding Assessment Station of China Agricultural University.
Four healthy primiparous lactating sows of the French Large White breed, weighing 186.25 ± 10.31 kg, were selected and housed in metabolism cages, which were designed to ensure the collection all of fecal and urine samples. The blank blood, feces, urine, and milk samples were obtained 4 h before the beginning of the experimental dosing. During both the pre-experimental and the experimental phases, the sows were fed a customized lactating sow diet (
Table 7), which was confirmed to have undetectable levels of Ochratoxin A (OTA). The detected concentrations of Aflatoxin B1 (AFB1), Zearalenone (ZEN), and Deoxynivalenol (DON) were 0.85, 4.3, and 27.8 μg/kg, respectively.
5.3. Toxin Administration Route
The
Aspergillus ochraceus corn culture, containing 640 mg/kg of OTA, was the same batch sample used by Kang et al. (2023) [
22]. The amounts of culture material given orally to the sows contained a single OTA dose of 500 µg/kg BW, which equals the OTA dose previously used by Galtier et al. in their pig study [
18]. In detail, according to the OTA dose of 500 µg/kg BW, 137–152 g culture (containing OTA 87.5–97.5 mg) was accurately weighed into a plastic beaker and then dissolved and stirred in 100 mL of distilled water to form a suspension. Subsequently, this suspension was rapidly introduced into the stomachs of the lactating sows through an esophageal tube.
5.4. Collection of Plasma, Feces, Urine, and Milk
The blood samples were obtained from the anterior vena cava via indwelling needles in sows before administration (0 min) and a 5, 15, and 30 min, and 1, 2, 3, 6, 9, 12, 24, 48, 72, 88, 96, and 120 h after OTA post administration. The samples stored in heparin anticoagulation tubes were transferred to the laboratory, and then centrifuged at 3000 rpm for 15 min to obtain plasma. Moreover, the feces were collected before administration (0 h) and at 6, 12, 24, 36, 48, 60, 72, 84, 96, 108, and 120 h post administration. Urine samples were collected before administration (0 h) and at 6, 12, 18, 24, 30, 36, 42, 48, 54, 60, 66, 72, 78, 84, 90, 96, 102, 108, 114, and 120 h following administration. Milk samples were collected at 0, 6, 12, 24, 36, 48, 72, 96, and 120 h after the administration. Meanwhile, the feces weight and urine volume were recorded at each collection time. All samples were stored at −20 °C for further analysis.
5.5. Standard Solutions
Obtained from Pribolab (Qingdao, China), the stock solution of 1 mg/mL OTA and OTα was subsequently diluted with 50% acetonitrile to generate diverse concentrations of OTA and OTα working standard solutions (0.0125, 0.025, 0.05, 0.125, 0.25, 0.5, 1, 2.5, and 5 micrograms per milliliter). For the preparation of calibration samples, blank plasma, urine, and milk samples, each with a volume of 90 μL, were utilized. To these, adding 10 μL of the diverse concentrations of the working solutions yielded spiked samples at nine different concentration levels, ranging from 1.25 to 500 μg/L. Similarly, in the case of fecal samples, 1 g of blank material was employed, along with the addition of 100 μL of different concentrations of the working standard solution, leading to nine spiked sample concentration levels in the identical range. These spiked plasma, urine, milk, and fecal samples were then processed and analyzed using established treatment and detection methods specific to each sample type.
5.6. Sample Pretreatment
For plasma, urine, and milk, after thawing, a 1 mL sample was transferred to a 10 mL centrifuge tube, and 300 μL of 0.2 M sodium sulfate solution, 400 μL of 0.2 M acetate buffer (pH 5.5), and 300 μL of the enzyme solution were added. After thorough vortex mixing, the mixture was incubated at 37 °C in a water bath overnight (17 h). Then, 4 mL of acetonitrile/water (80/20, v/v) was added. Among them, the enzyme solution was prepared by dissolving 50 mg of the H-1 type β-glucuronidase (3,023,000 units/g) in 10 mL of 0.2 M acetic acid buffer (pH 5.5).
For feces, after drying and homogenization, 2 g was placed in a 50 mL stoppered plastic centrifuge tube, and 20 mL of acetonitrile/water (80/20, v/v) was added.
On this basis, the mixture was vortexed for 2 min, sonicated for 1 h, and centrifuged at a speed of 8000 rpm/min for 7 min. Then, 1 mL of supernatant was taken from the centrifuged feces, urine, plasma, and milk, respectively, it was filtered using a 0.22 μm filter membrane for further analysis.
5.7. UPLC-MS/MS Method Validation
During method validation, linearity, sensitivity, and recovery were assessed individually for plasma, urine, feces, and milk samples. Calibration curves were generated using four separate blank matrices, encompassing plasma, urine, feces, and milk, across 9 concentration levels ranging from 1.25 to 500 μg/L. Sensitivity was evaluated by determining the limit of detection (LOD) and limit of quantification (LOQ), with the LOD achieving a signal-to-noise (S/N) ratio of ≥3, and the LOQ reaching a S/N ratio of ≥10. To assess the method’s accuracy in different matrices, recovery efficiency was evaluated by comparing the peak area of two OTA and OTα concentrations (20 and 100 μg/L) in the spiked samples to the OTA and OTα peak area in the corresponding standard working solutions.
5.8. Detecting OTA and OTα in Plasma, Feces, Urine, and Milk Using UPLC-MS/MS
UPLC was performed on a Waters Acquity (Milford, MA, USA) system. Chromatographic separation was achieved on an ACQUITY UPLC BEH C18 (100 mm × 2.1 mm, 1.7 μm) column (Waters, Milford, MA, USA). The flow rate was 0.3 mL/min and the injection volume was 2 μL. The mobile phase was consisted of 0.1% formic acid in water (A) and methanol (B). A linear gradient elution program was applied as follows: 0–2 min 5% B; 2–3 min 35% B; 3–6 min 65% B; 6–10 min 65% B; 10–12 min 95% B; and 12–13.5 min 5% B (total run 15 min). Mass spectrometry analysis was carried out using an A 5500 triple-quadrupole tandem mass spectrometer (AB Sciex, Framingham, MA, USA) equipped with an electrospray interface (ESI) operating in positive mode for OTA. The ESI conditions were as follows: ion spray voltage (IS) at 5.5 kv; curtain gas (CUR) at 20 psi; nebulizer gas (GS1) at 55 psi; and ion source temperature at 450 °C. The mass spectrometry conditions are presented in
Table S2.
5.9. Statistical Analysis
Statistical analysis was performed based on the standardized concentrations of OTA and OTα in plasma, urine, feces, and milk. Plasma toxicokinetic parameters of OTA and OTα were calculated using the non-compartmental modeling in WinNonlin 5.2.1 software (Certara, Inc., Princeton, NJ, USA). Then, the average OTA and OTα concentrations in plasma and milk at different times were used to chart the plasma and milk concentration–time profiles. The mean excretions of OTA and OTα in feces and urine at different times were used to plot the OTA and OTα excretion–time profiles. The figures were charted using GraphPad Prism version 9.4.1 (GraphPad Software, Inc., San Diego, CA, USA). Data are shown as mean ± SEM.