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Article

UHPLC-ToF-MS as a High-Resolution Mass Spectrometry Tool for Veterinary Drug Quantification in Milk

1
National Institute for Agricultural and Veterinary Research (INIAV), Rua dos Lágidos, Lugar da Madalena, 4485-655 Vila do Conde, Portugal
2
Faculty of Pharmacy, University of Coimbra, Health Science Campus, Azinhaga de Santa Comba, 3000-548 Coimbra, Portugal
3
Associated Laboratory for Green Chemistry of the Network of Chemistry and Technology (REQUIMTE/LAQV) R. D. Manuel II, 55142 Porto, Portugal
4
Escola Superior Agrária, Instituto Politécnico de Viana do Castelo, Rua Escola Industrial e Comercial de Nun’Álvares, 4900-347 Viana do Castelo, Portugal
5
Centro de Investigação e Desenvolvimento em Sistemas Agroalimentares e Sustentabilidade (CISAS), Escola Superior Agrária, Instituto Politécnico de Viana do Castelo, Rua Escola Industrial e Comercial de Nun´Álvares, 4900-347 Viana do Castelo, Portugal
*
Author to whom correspondence should be addressed.
Submission received: 31 July 2023 / Revised: 15 August 2023 / Accepted: 16 August 2023 / Published: 21 August 2023

Abstract

:
Milk is one of the most widely consumed foods in the world, despite the increasing consumption of plant-based alternatives. Although rich in nutrients and believed by consumers to be free of undesirable contaminants, milk, whether of animal or plant origin, is not always free from residues of chemical substances, including veterinary medicines. For instance, in intensive livestock production, antibiotics are often used to treat animals or, illicitly, to improve their growth performance, which can lead to their presence in the final food. Additionally, the continuous use of veterinary drugs in intensive animal production can lead to their occurrence in agricultural soils and therefore are absorbed by plants as another source of entering the food chain. An effective and accurate multi-detection quantitative screening method to analyze 89 antibiotics in milk was optimized by ultra-high-performance liquid chromatography coupled with a time-of-flight detector (UHPLC-ToF-MS) and further validated in accordance with the Commission Implementing Regulation (CIR) 808/2021 and the International Council for Harmonization (ICH) guidelines on the validation of analytical procedures. Apart from the specific parameters required by CIR 808/2021, the aim was to access the lower limits of the method, limits of detection (LoD) and quantification (LoQ), regardless of the maximum residue limits (MRLs) defined in the legislation. The method was then applied in the analysis of 32 supermarket samples, resulting in four positive findings, including one plant-based sample. The antibiotics found were from the macrolides and sulphonamides families. Nevertheless, the concentrations detected were below the established maximum residue level (MRL).

1. Introduction

The importance of science and technology in improving the quality of human life is directly related to the need to consume safe and healthy food. Worldwide, several chemical agents are responsible for the contamination of food products, mainly of anthropogenic origin. Veterinary drug medicines are frequently found in residual concentrations in food originating from intensive animal production. Through an increase in the world’s population and consequent intensification of agriculture and livestock, the use of veterinary drugs in animal production began to include disease prevention and not exclusively therapeutic purposes. Illicitly, it can also be used to increase feed efficiency and, consequently, result in the promotion of growth in healthy animals [1,2]. For instance, concerning milk and its derivatives, antimicrobial residues are the most detected [3,4]. Due to its high nutritional composition being rich in water, proteins, lipids, vitamins and minerals, milk is considered one of the most complete and valuable foods. It is, therefore, crucial to guarantee its quality and safety through accurate control measures.
Several factors, such as animal breed, age, feeding quality, lactation phase or infections in the mammary gland, can result in the development of pathogenic microorganisms, which lead to the need for treatment with antibiotics. These treatments are applied as a preventive measure, and the intramammary injection of antibiotics has proven to be an effective way to treat mammary gland infections [5,6]. If the withdrawal period is not respected, the final food product will be contaminated, which can pose risks to human health [6,7] and affect the quality of dairy-fermented products [5]. The health threats to humans may include toxic effects (carcinogenic, mutagenicity, teratogenic, etc.), alterations in the microbiota responsible for gastrointestinal diseases, and allergic reactions, among others [1,4]. Additionally, one of the major threats is the development and transfer of antimicrobial-resistant bacterial strains, which can cause therapeutic failures in the case of infected individuals [8]. This is a problem that has been increasing due to several issues, including excessive and uncontrolled use of antibiotics both in humans and in animals [9,10,11], leading to an increasingly severe scenario of antimicrobial resistance [12]. In addition, the continuous use of antibiotics in animal livestock breeding and the direct and uncontrolled use of manure as organic fertilizer can cause their dissemination through the environment. In the case of antibiotics, whose absorption by animals is not total, their occurrence in the soil can cause their absorption by plants, leading to their introduction into food chains by contaminated plant-based food products [13,14,15,16,17]. Though the risk is clear, studies concerning the occurrence of antibiotics in plants are scarce, including plant-based milk products.
In this sense, monitoring the presence of antibiotic residues in milk intended for human consumption is crucial to the protection of consumers and should comply with the regulations used for that purpose. Reliable, accurate and precise analytical methodologies are therefore needed to ensure efficient control of these anthropogenic contaminants. The European Commission (EC) has determined the rules for that specific control to prevent residues in food, with substances being completely prohibited and others with defined and established maximum residue limits (MRLs) in case of allowed pharmacologically active substances in edible tissues of animal origin [18,19]. Thus, the Commission Implementing Regulation (CIR) 2021/808 [20] defines the mandatory requirements to be met for the development and validation of analytical methods for the determination of drug residues in animal matrices. For the analysis of antibiotics in a multi-detection and multi-class approach, an efficient screening method is very important to ensure the reliability, accuracy and time-effectiveness of the results [21]. Those multi-residue methods are increasingly sought and adopted in routine analyses, improving the relationship between the cost and effectiveness of analytical methodologies by maximizing the number of analyses determined in each sample in one analysis. The most frequent analytical methodologies used for the presence of drug residues in food matrices are microbiological [4], immunochemical [22] and physico-chemical [21,23,24,25]. However, to fulfill the necessary and mentioned specifications, techniques such as ultra-high-performance liquid chromatography (UHPLC) coupled with mass spectrometry detectors are the golden choice to achieve such accurate and unequivocal identification of target antibiotics [26,27]. Although triple quadrupole mass spectrometry detectors are still one of the main choices for contaminant analysis in food, in recent years, the use of high-resolution mass spectrometry (HR-MS) in the field of multi-detection of a large number of veterinary drug residues has proven to provide the necessary specificity and sensitivity, despite the number of compounds, for target and also untargeted analyses [28,29,30,31]. Another valuable characteristic of such technology is the given possibility of performing a retrospective analysis of suspected and untargeted contaminants, considering its linking to computer and data analysis systems [32]. The specific determination of antibiotics in milk has been described mainly by liquid chromatography coupled with tandem mass spectrometry in order to comply with the necessary requirements implemented by the European Commission, which reflect the very low levels of contaminants to be detected [33]. Notwithstanding, these methods are mostly aimed at a reduced number of target compounds or at one class of compounds due to the loss of the sensitivity of MS/MS detectors when a large number of analytes are analyzed in a single run, affecting parameters such as the limits of detection (LoD) and quantification (LoQ) [34,35]. A few reports using LC-ToF-MS have been applied for this purpose, highlighting the simplicity, time and cost-effectiveness of such a method [33,36,37,38], being a tool of excellence as a screening method for a high number of analytes (multi-class methods) in a short period of time, allowing to significantly reduce the analyses length, especially in routine analysis, with the added value of a preliminary quantitative assessment in positive cases.
In line with the aforementioned, the present study intends to describe an analytical methodology for the screening of 89 antibiotics from 10 classes, including penicillins, cephalosporins, macrolides, tetracyclines, quinolones, sulfonamides, pleuromutillins, sulfone (dapsone), amphenicols and diaminopyrimidines, in milk matrices. The method performed using HR-MS, namely by UHPLC-ToF-MS, was fully validated, comprising the calculation of LoD and LoQ values to further evaluate the levels of contamination in real milk samples available to consumers. The sampling profile of real samples was defined according to current consumption patterns of this type of food, which included animal milk (raw and processed) and also plant-based milk samples (soya and oat) since the increasing consumer search for healthier food products leads to an increase in such products in the market, which can be contaminated by antibiotic-contaminated soils or water.

2. Materials and Methods

2.1. Reagents and Standards

All solvents and reagents used were of analytical grade or LC-MS grade for the mobile phase preparation, including ultrapure water type I. Acetonitrile, methanol, ethylenediaminetetraacetic acid disodium salt dihydrate (EDTA) and formic acid were acquired from Merck (Germany). For the preparation of the EDTA solution 0.1%, it was dissolved at 29.23 g in water until a final volume of 1 L. Mobile Phase A (formic acid 0.1%) was prepared by diluting 1 mL of formic acid in water to 1 L of the solution. Antibiotic standards, including internal standards (IS), were provided by Sigma-Aldrich (Spain) with a purity of at least 98%. The appropriate amount of each standard was weighted to prepare the individual stock solutions with concentrations of 1 mg mL−1 in methanol, except for the beta-lactams, which were prepared in water. These solutions were stored at −20 °C for 6 months and used to prepare the necessary mixtures to be used to spike the blank samples for the matrix calibration curves. Similarly, a mixed solution of IS (demeclocycline, sulfadiazine 13C6, penicillin G d7, cefadroxil d4, erythromycin 13C d3, lomefloxacin, florfenicol d3, trimethoprim d9) with a concentration of 10 µg mL−1 was prepared. The mixtures and working solutions were kept for 1 month, also at −20 °C.

2.2. Instrumentation

In addition to the current material in the laboratory, the following equipment was used: analytical balances, Toledo PC200 and AE100 (Greifensee, Switzerland); Heidolph Reax mixer (Schwabach, Germany); Selecta Mater ultrasonic water bath with a controlled temperature (Selecta, Spain); Heraeus Megafuge centrifuge (Hanau, Germany); Turbovap Zymark evaporator coupled with a nitrogen generator (Hopkinton, MA, USA); and Whatman Mini-Uniprep PVDF 0.45 μm filters (Clifton, NJ, USA).
The detection was performed with an UHPLC-ToF-MS comprising an UHPLC Nexera X2 (Shimadzu, Japan) for chromatographic separation coupled with a Triple TOFTM 5600+ (Sciex, Framingham, MA, USA). The UHPLC system consisted of a solvent degasser, a binary pump, an autosampler with a controlled temperature (10 °C), an automatic injector with a variable volume (10 µL), and an oven for the column (40 °C). The reverse-phase column used was an Acquity UPLC HSS T3 1.8 μm, 2.1 × 100 mm (Waters, Milford, MA, USA). The flow rate was 500 μL.min−1 with mobile phases (A) formic acid 0.1% (v/v) in water and (B) acetonitrile. A gradient program was selected as follows: the first 2 min was kept at 97% (A) and then until 5 min from 97% to 40% (A); 5–9 min from 40% to 0% (A); 9–10 min from 0% back to 97% (A) in a total run time of 11 min.
The ToF-MS detector was equipped with an electrospray ion source in the positive ionization mode (ESI+) and full-scan acquisition mode in a range from 100 to 900 Da. Four software programs were used, all from the Sciex brand: Analyst® TF for the acquisition; and for the identification and quantification, we used PeakView™, LibraryView™ and MultiQuant™. The criteria of identification followed were based on the CIR 808/2021 requirements: exact mass with an error below 5 ppm (∆ppm in Equation (1)) and a maximum variation in relative retention time (RRT) of 1% (∆RRT Equation (2)).
p p m = M a s s   d e t e c t e d E x a c t   m a s s E x a c t   m a s s × 10 6
R R T ( % ) = ( R R T s a m p l e R R T s t a n d a r d R R T s t a n d a r d ) × 100
Quantitatively, and to ensure a reliable identification with an added criterion, the isotope ratio difference was established to be accepted to be lower than 10%. Such a value is automatically generated by the PeakView™ software. Also, to guarantee an accurate mass resolution, the detector was automatically calibrated at every 10 injections.

2.3. Sample Preparation

The method optimized for sample extraction was adapted from a previous method [34]. In summary, to 2 mL of homogenized milk, 60 μL of the IS mixture solution was added. After 10 min of rest in the dark, a liquid–liquid extraction and protein precipitation, with 10 mL of acetonitrile plus 1 mL of 0.1 M of EDTA, was carried out using 20 min of homogenization, 10 min in an ultrasound bath and centrifugation at 3100× g for 10 min at 4 °C. The extract was then evaporated under nitrogen steam at 45 °C until 500 µL was left. Then, 200 µL of mobile phase A was added, filtered through a PVDF Mini-Uniprep TM filter (0.45 μm) and injected in the UHPLC-ToF-MS system. Each batch of samples was analyzed with a matrix calibration curve using blank milk samples fortified prior to the sample extraction, with 0.1, 0.25, 0.5, 0.75, 1 and 1.5 MRL or the VL (validation level when no MRLs are established).
For the analyses of real samples, 32 milk aliquots were acquired at Portuguese supermarkets and stored at −80 °C until analysis. The samplings were performed on animal milk, including raw (n = 1), whole (n = 2), semi-skimmed (n = 16), and skimmed (n = 7) milk samples, and plant-based milk, soya (n = 3) and oat (n = 3) milk.

2.4. Validation Procedure

According to the specifications described in the CIR 808/2021 [20], the validation parameters that should be studied for a quantitative screening method are CCβ, trueness (or recovery), precision and selectivity/specificity and the linearity of calibration curves in the 0.1 MRL to 1 MRL range. In addition, the objective of the validation was to determine the LoDs and LoQs [39] for the various antibiotics in milk. It should be noted that for compounds in which there is no established MRL, the lowest MRL value established for another antibiotic in the same family was used as the validation level (VL) in accordance with the cascade MRL’s use that can be applied to authorized substances (CIR 470/2018) [19].
Specificity and selectivity were evaluated by analyzing 30 blank samples from different origins (20 from animal origin and 10 from vegetable), and the same 30 samples spiked at the 0.5 MRL (or 0.5 VL). These spiked samples were analyzed over 3 days along with one calibration curve each day (the first and second days with an animal origin milk and the third day with soy milk), and all data obtained were used to evaluate the recovery, precision, ruggedness and the linearity of the curve. For setting the screening CCβ, samples were analyzed at the levels of 0.1 MRL, 0.25 MRL and 0.5 MRL to access the option able to fulfill the accurate identification. For the LoD and LoQ, Equations (3) and (4), respectively, were used [39].
L o D = 3.3 × σ S
L o Q = 10 × σ S
where σ represents the standard deviation associated with the 30 blank sample analyses, and S is the slope of the calibration curve.

3. Results and Discussion

The main objective of this work was to validate a multi-class method, by UHPLC-TOF-MS, of antibiotics in milk. Although the main purpose is to use the current method in the routine quality control of milk samples, studies of the occurrence of milk at lower concentrations than the MRLs are also considered of huge importance. The growing concerns related to the development and dissemination of antimicrobial resistance are the main driver for the need to evaluate the real levels of contamination that can be presented in food products. For that, the method developed was fully validated in accordance with the CIR 808/2021 [15]. In addition, the evaluation of the analytical thresholds of the method, LoD and LoQ, was performed with the ultimate objective of evaluating the antibiotic levels in milk samples and studying the ability to identify and quantify the target antibiotics independently of the MRLs established in the legislation. The ability to detect and quantify the target antibiotics at concentrations highly below the MRL was proven, as described in detail in the following subsections. Having assessed the applicability of the method through validation, the method was used to analyze 32 supermarket milk samples, including one of plant origin, in the screening of 89 antibiotics from 10 families: penicillins, cephalosporins, macrolides, tetracyclines, quinolones, sulfonamides, pleuromutillins, sulfone (dapsone), amphenicols and diaminopyrimidines.

3.1. Scope of the Method

Even though sample preparation and detection optimizations are easier to develop when working in single-class methods due to the similar chemical characteristics of compounds of the same family, it is consensual that multi-detection and multi-class are the most efficient approaches for monitoring veterinary drugs in food. Some authors are still using the single-family [40] method or multi-class with a limited number of compounds in the same method [29,30] to determine antibiotics in milk [41,42]. The aim of the present work was to obtain a method with a broader number of antibiotics detected than the previous one [34], benefiting from the use of HR-MS, which its sensitivity is independent of the number of compounds analyzed. Another important goal was to maintain the sample extraction as simple as possible in order to have a rapid method able to be used for a high number of samples in a short time period. Other methods available in the literature that also provide multi-class approaches do not always use simple liquid–solid extraction but resort to solid-phase extraction [24,43,44], dispersive solid-phase extraction [43], QuEChERS [45] or the automated turbulent flow cyclone clean-up system [46], resulting in more time-consuming methods with higher consumption of reagents. Previously reported studies also described the development of methods to perform the multi-detection of veterinary drugs in milk, as Stolker et al. [31] presented a method able to detect 100 drugs; however, only half of them were antibiotics. Additionally, the validation process was in accordance with the MRLs established without further studies on the limits of detection. The advantages of mass spectrometry were also stated by other multi-class studies on an LC-MS/MS method basis. This recent report described the optimization and development of 78 veterinary drugs in bovine milk through an efficient and cost-effective procedure, encompassing a broad scope of analytes with an increase in laboratory productivity of 2- to 3-fold [45]. Nonetheless, the authors stated the importance and future trends in milk analyses using HR-MS technologies towards non-target residue screening.

3.2. Validation

The validation process allows for the verification that a method is suitable to be used as a quality control tool and is an essential step in developing a method either as screening or confirmatory, qualitative or quantitative. It is important to emphasize that even though some literature presents multi-detection methods for a large number of veterinary drugs, not all provide a complete validation in accordance with the European Regulations for veterinary drug residue analysis [44,47]. The current method, with an extraction procedure based on a previous study [34], provides improvement mainly on the number of compounds analyzed. The broader scope of targeted antibiotics is due to the possibility of using HR-MS as full-scan detection technology, which allows the enhancement of the number of compounds detected without loss in sensitivity. The ionization needed to detect the target compounds was set to be performed by positive electrospray after testing both positive and negative modes. To promote the positive ionization, an acidic mobile phase was adjusted with 0.1% of formic acid, which guarantees the necessary concentration of H+ to create the positive ions.
Regarding the process of the identification of antibiotics by UHPLC-ToF-MS, it is based on two main factors described in the CIR 808/2021: the identification of the exact mass (with a maximum acceptable error of ∆ppm = 5) and the variation in the relative retention time (not exceeding 1%). Additionally, to these identification parameters, the overlap of the isotopic profile of each compound, where a maximum of a 10% difference was considered acceptable, was also performed. Such a parameter was internally defined during method validation as a qualitative criterion since there is no official one.
The quantitative screening method was validated according to CIR 2021/808 [20] and for the established MRLs of the target antibiotics. For those that do not have MRLs established, including antibiotics that are not allowed to be used in milk production (doxycycline and oxolinic acid) or are prohibited in food animal production (dapsone), VLs were defined. The optimized method was fully validated, and Table 1 presents the antibiotics and the summary of the validation parameters. The validation, although in accordance with European legislation, included the evaluation of the analytical thresholds, LoD and LoQ, and for all calculations performed, the relative areas were used as a ratio between the areas of the target antibiotics and the corresponding IS. As can be observed in Table 1, all the obtained LoD and LoQ values are below the MRL established in Regulation 37/2010 [13]. For all compounds in which the LoDs were below 0.1 MRL, the achieved screening CCβ was also set as a 0.1 MRL. However, considering the lower level of the calibration curve, 0.1 MRL, the achieved LoD and LoQ for some antibiotics were higher. For instance, amoxicillin, ampicillin and benzylpenicillin had those threshold limits between 1/10 xMRL and 1/2 xMRL. In the class of sulfonamides, sulfanilamide had the worst sensitivity response, and only 50 µg kg−1 for CCβ was acceptable, despite the MRL being 100 µg kg−1. Another example is erythromycin, for which the CCβ obtained was 0.25 MRL, meaning 10 µg kg−1 for an MRL of 40 µg kg−1. In those cases, the lower calibration level considered for the method was defined to be the LoQ calculated.
Overall, the lowest LoD and LoQ, 0.001 and 0.004 µg kg−1, respectively, were obtained for oxolinic acid from the fluoroquinolones antibiotic class and considered not allowed for milk production. On the other hand, the highest values were found for sulfanilamide, as already described, with, respectively, 9.13 and 30.45 µg kg−1. In the work by Jadhav et al. (2019) [45], the LoQ range found for 78 veterinary drugs’ minimum limits was higher than in our study (0.02 µg kg−1), though a maximum value of 25 µg kg−1 was obtained. Similar ranges were found on a validation procedure for 25 veterinary drugs, including quinolones, fluoroquinolones, tetracyclines, sulphonamides, trimethoprim and bromhexine, also using tandem mass spectrometry as a detection technology. LoDs were found between 0.2 and 10 µg kg−1, and LoQs between 2.5 and 25 µg kg−1, though a considerably lesser number of analytes was determined when compared to our study [33]. Analyses of quinolones, penicillins and cephalosporins in cow’s milk were also performed in a comparative study using LC-MS/MS and UHPLC-MS/MS techniques [35]. The limit values ranged from 0.03 to 0.5 µg kg−1 for the LoD values and from 0.1 to 1.25 µg kg−1 for the LoQ values by using LC; and, with UPLC, the range of LOD values was 0.02–0.75 µg kg−1 and was 0.1–9 µg kg−1 for the LOQ values.
Criteria of acceptance for recovery and precision are directly related to the range of concentrations and are well described in the CIR 808/2021 [20]. For recovery, the tightest range of acceptance is between 80% and 120%. The inferior limit was completely fulfilled, being the cefoperazone compound with a lower recovery of 80.7%. However, for the upper limit, four of the compounds have exceeded 120%, namely: sulfisomidine at 120.8%, cefquinome at 122%, phenoxymethylpenicillin at 128.8% and cefazolin at 129.4%. It can be assumed that the matrix effect has a major influence on the detection of those compounds. For instance, in an aforementioned study of veterinary drugs in milk samples, recoveries were within the range of 70–120% for over 90% of the compounds analyzed at and above the VLL, and tough, very low recoveries were found for amoxicillin, tetracycline, oxytetracycline, chlortetracycline and doxycycline, ranging from 19 to 59% [45]. When it comes to the precision evaluation, the criteria defined are calculated in accordance with the Horwitz equation, which leads to the maximum value acceptable for reproducibility. Two-thirds of the same value provide the criterion for repeatability. Precision is calculated as the coefficient of variation intra-day for repeatability and inter-day for reproducibility. The higher reproducibility obtained was for cefoperazone, 25%, which is the higher limit of acceptance for the range of concentrations evaluated for this compound. On the other hand, for repeatability, the higher coefficient of variation achieved was for baquiloprim, with 20.3% being 20% the limit for the range of concentrations inferior to 10 µg kg−1 (MRL is 30 µg kg−1). Essentially, the acceptance criteria established for precision through the Horwitz equation was fully achieved for all molecules.
Concerning the specificity of the method, in all 30 blank samples (20 of animal origin and 10 of plant-based origin), it was observed that no interfering peaks at the retention time of the target antibiotics were present. In addition, the same 30 samples were spiked at half of the validation level, and the identification criteria were all guaranteed, regardless of the composition of the milk sample. Overall, it can be assumed that the matrix effect does not interfere with the detection of the 89 antibiotics in those different types of beverage products.
In terms of linearity, the coefficient of determination R2 was evaluated for all compounds in the spiked matrix calibration curve, and the internal acceptance criteria of R2 > 0.95 was fulfilled. The farthest value achieved was for cefoperazone, with an R2 of 0.98.

3.3. Analysis of Real Samples

After a complete validation and, consequently, limits of quantification (LOQ) and detection (LOD) were established, the analytical method was applied to a total of 32 real milk samples from different sources and types. The sampling was therefore performed on animal milk, including raw (n = 1), whole (n = 2), semi-skimmed (n = 16), and skimmed (n = 7) milk samples, and plant-based milk, namely soya (n = 3) and oat (n = 3) milk. In Table 2, data on the sample analyses for antibiotic residue determination is shown.
In most of the samples, no traces of the targeted antibiotics were observed, with only four samples (approximately 13%) presenting antibiotic residues in their composition at low concentrations. Three of the samples presented one antibiotic, with only one presenting a co-occurring antibiotic profile of two macrolides, gamithromycin and tilmicosin. The highest concentration was found in this semi-skimmed cow milk sample, at a value of 10.70 µg kg−1. Tilmicosin was also found, though it was not possible to quantify since the value obtained was between the LOD and LOQ of the validated method for this compound. Two samples of skimmed milk also presented the macrolide tildipirosin at concentrations of 3.33 and 2.89 µg kg−1. One of the samples of plant-based origin also presented one contaminant of the sulfonamide family, sulfamerazine, at a concentration level of 4.25 µg kg−1. Despite the occurrence of antibiotic residues found, it can be concluded that these samples do not pose a risk of toxicity to the consumer since all were far below the established MRLs.
Although the occurrence studies available in the literature are difficult to compare due to the geographic different origins of milk samples and the scope of the analytical methods used (in terms of antibiotics and detection limits), there are a few worth mentioning. Nearest to our collection area, Castilla-Férnandez et al. [43], in Spain, after comparing two sample extractions, collected 24 milk samples from local supermarkets and detected traces of danofloxacin in two of them, both below the MRL. Another occurrence study, performed in a city in India [45], obtained a higher rate of contaminations, despite all being at low concentrations. In 1000 milk samples analyzed for different veterinary drugs, 80% presented at least one contaminant from antibiotics (sulfonamides, tetracyclines and fluoroquinolones) and anthelmintics. Wang et al. [48] also presented a method to detect only 20 antibiotics (tetracyclines, fluoroquinolones, macrolides, beta-lactams and amphenicols) and afterwards collected 106 samples from Shanghai markets of edible animal origin tissues, including milk, which was found to reach 10.6% of the positive findings in milk. More recently, also in China [24], milk samples acquired in local markets were analyzed, and the antibiotics mostly found were tetracyclines, macrolides and trimethoprim, all below MRLs. In Brazil [49], a study of more than 1000 milk samples resulted in the detection of tilmicosin, cloxacillin and ceftiofur in three samples at concentrations higher than the MRL.
Overall, the occurrence studies that were performed and are available in the literature agree with the results achieved in this work concerning macrolides’ detection in animal milk samples. Thus, the presence of antibiotics in milk is verified as a reality scenario in different types of milk, supporting the need to implement accurate farm and industrial production measures to minimize this exposure. On a wide systematic review study on this theme of antibiotics in milk, it was observed that the highest number of published works occur in Europe (n = 105), with bovine milk being the mostly used matrix worldwide (193), followed by ovine (n = 19) and caprine (n = 14) (Sachi et al., 2019), though this is still a trim down number of occurrence studies to fully comprehend the exposure range in this widely consumed food product. The specific case of the contaminated plant-based milk samples can also provide a promising insight into the arising issue of antibiotic absorption in plant and vegetable crops from contaminated soil or water. Future work should therefore focus on a wider range of types of milk, with a representative number of samples for each category, by also adding new veterinary drugs that represent a risk to public health, namely anti-inflammatory and antiparasitic agents.

4. Conclusions

The analytical strategy presented can be considered an efficient tool in terms of the food safety control of milk by combining new technology with the required sensitivity and the efficiency of a rapid, handy and easy approach. Another feature that should be highlighted is the possibility of revisiting the results in the future for presently untargeted molecules. The use of HR-MS and the full-scan acquisition provides that possibility in the mass range of the method. The presence of antibiotic residues in milk samples also emphasizes the need to establish assessment and management strategies to minimize or eliminate such a presence in a widely consumed food product, especially by vulnerable age population groups. Though it was proven that the safety of consumers could be perceived as not being compromised, combined toxicology is still an unexplored field that ought to be of utmost concern in the field of anthropogenic contaminants in food.

Author Contributions

Conceptualization, A.F.; methodology, M.L. and A.R.M.; validation, M.L., A.R.M., A.S.V.P., S.C.B. and A.F.; formal analysis, A.F., J.B., F.R. and I.M.A.; investigation, M.L. and A.F.; writing—original draft preparation, M.L., A.R.M. and A.F.; writing—review and editing, A.F., J.B., F.R. and I.M.A.; supervision, I.M.A. and A.F. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Data Availability Statement

Data will be made available on request.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Gonzalez Ronquillo, M.; Angeles Hernandez, J.C. Antibiotic and Synthetic Growth Promoters in Animal Diets: Review of Impact and Analytical Methods. Food Control 2017, 72, 255–267. [Google Scholar] [CrossRef]
  2. Beyene, T. Veterinary Drug Residues in Food-Animal Products: Its Risk Factors and Potential Effects on Public Health. J. Vet. Sci. Technol. 2015, 7, 1–7. [Google Scholar] [CrossRef]
  3. Pereira, M.N.; Scussel, V.M. Resíduos de Antimicrobianos Em Leite Bovino: Fonte de Contaminação, Impactos e Controle. Revista de Ciências Agroveterinárias 2017, 16, 170–182. [Google Scholar] [CrossRef]
  4. Chen, J.; Ying, G.-G.; Deng, W.-J. Antibiotic Residues in Food: Extraction, Analysis, and Human Health Concerns. J. Agric. Food Chem. 2019, 67, 7569–7586. [Google Scholar] [CrossRef] [PubMed]
  5. Kurjogi, M.; Issa Mohammad, Y.H.; Alghamdi, S.; Abdelrahman, M.; Satapute, P.; Jogaiah, S. Detection and Determination of Stability of the Antibiotic Residues in Cow’s Milk. PLoS ONE 2019, 14, e0223475. [Google Scholar] [CrossRef] [PubMed]
  6. Saad, M.M.E.-D.; Ahmed, M.B.M. Necessary Usage of Antibiotics in Animals. In Antibiotic Use in Animals; InTech: London, UK, 2018. [Google Scholar]
  7. Daeseleire, E.; Van Pamel, E.; Van Poucke, C.; Croubels, S. Veterinary Drug Residues in Foods. In Chemical Contaminants and Residues in Food, 2nd ed.; Elsevier: Amsterdam, The Netherlands, 2017; pp. 117–153. ISBN 9780081006740. [Google Scholar]
  8. Nisha, A. Antibiotic Residues—A Global Health Hazard. Vet. World 2008, 2, 375. [Google Scholar] [CrossRef]
  9. Guimarães, D.O.; da Silva Momesso, L.; Pupo, M.T. Antibióticos: Importância Terapêutica e Perspectivas Para a Descoberta e Desenvolvimento de Novos Agentes. Quim. Nova 2010, 33, 667–679. [Google Scholar] [CrossRef]
  10. Chowdhury, R.; Haque, M.; Islam, K.; Khaleduzzaman, A. A Review On Antibiotics In An Animal Feed. Bangladesh J. Anim. Sci. 1970, 38, 22–32. [Google Scholar] [CrossRef]
  11. Velazquez-Meza, M.E.; Galarde-López, M.; Carrillo-Quiróz, B.; Alpuche-Aranda, C.M. Antimicrobial Resistance: One Health Approach. Vet. World 2022, 15, 743–749. [Google Scholar] [CrossRef]
  12. FAO; WHO. Joint FAO/WHO Expert Meeting in Collaboration with OIE on Foodborne Antimicrobial Resistance: Role of the Environment, Crops and Biocides; WHO: Geneva, Switzerland, 2019. [Google Scholar]
  13. Albero, B.; Tadeo, J.L.; Miguel, E.; Pérez, R.A. Rapid Determination of Antibiotic Residues in Cereals by Liquid Chromatography Triple Mass Spectrometry. Anal. Bioanal. Chem. 2019, 411, 6129–6139. [Google Scholar] [CrossRef]
  14. Hu, X.; Zhou, Q.; Luo, Y. Occurrence and Source Analysis of Typical Veterinary Antibiotics in Manure, Soil, Vegetables and Groundwater from Organic Vegetable Bases, Northern China. Environ. Pollut. 2010, 158, 2992–2998. [Google Scholar] [CrossRef] [PubMed]
  15. Yu, X.; Zhang, X.; Chen, J.; Li, Y.; Liu, X.; Feng, Y.; Sun, Y. Source, Occurrence and Risks of Twenty Antibiotics in Vegetables and Soils from Facility Agriculture through Fixed-Point Monitoring and Numerical Simulation. J. Environ. Manag. 2022, 319, 115652. [Google Scholar] [CrossRef] [PubMed]
  16. Feng, Y.; Zhang, W.J.; Liu, Y.W.; Xue, J.M.; Zhang, S.Q.; Li, Z.J. A Simple, Sensitive, and Reliable Method for the Simultaneous Determination of Multiple Antibiotics in Vegetables through SPE-HPLC-MS/MS. Molecules 2018, 23, 1953. [Google Scholar] [CrossRef] [PubMed]
  17. Zhao, F.; Yang, L.; Chen, L.; Li, S.; Sun, L. Bioaccumulation of Antibiotics in Crops under Long-Term Manure Application: Occurrence, Biomass Response and Human Exposure. Chemosphere 2019, 219, 882–895. [Google Scholar] [CrossRef] [PubMed]
  18. European Parliament; Council of the European Union. COMMISSION REGULATION (EU) No 37/2010. Off. J. Eur. Union 2010, 32, 275–346. [Google Scholar]
  19. European Commission Commission Implementing Regulation (EU) 2018/470. Off. J. Eur. Union 2018, L79, 16–18.
  20. European Commission Commission Implementing Regulation (EU) 2021/808. Off. J. Eur. Union 2021, L180, 84–109.
  21. Companyó, R.; Granados, M.; Guiteras, J.; Prat, M.D. Antibiotics in Food: Legislation and Validation of Analytical Methodologies. Anal. Bioanal. Chem. 2009, 395, 877–891. [Google Scholar] [CrossRef]
  22. Cháfer-Pericás, C.; Maquieira, Á.; Puchades, R.; Miralles, J.; Moreno, A.; Pastor-Navarro, N.; Espinós, F. Immunochemical Determination of Oxytetracycline in Fish: Comparison between Enzymatic and Time-Resolved Fluorometric Assays. Anal. Chim. Acta 2010, 662, 177–185. [Google Scholar] [CrossRef]
  23. Samanidou, V.; Nisyriou, S. Multi-residue Methods for Confirmatory Determination of Antibiotics in Milk. J. Sep. Sci. 2008, 31, 2068–2090. [Google Scholar] [CrossRef]
  24. Hu, M.; Ben, Y.; Wong, M.H.; Zheng, C. Trace Analysis of Multiclass Antibiotics in Food Products by Liquid Chromatography-Tandem Mass Spectrometry: Method Development. J. Agric. Food Chem. 2021, 69, 1656–1666. [Google Scholar] [CrossRef] [PubMed]
  25. Chan, C.L.; Wai, H.K.F.; Wu, P.; Lai, S.W.; Chan, O.S.K.; Tun, H.M. A Universal LC-MS/MS Method for Simultaneous Detection of Antibiotic Residues in Animal and Environmental Samples. Antibiotics 2022, 11, 845. [Google Scholar] [CrossRef]
  26. Lopes, R.P.; Reyes, R.C.; Romero-González, R.; Vidal, J.L.M.; Frenich, A.G. Multiresidue Determination of Veterinary Drugs in Aquaculture Fish Samples by Ultra High Performance Liquid Chromatography Coupled to Tandem Mass Spectrometry. J. Chromatogr. B 2012, 895–896, 39–47. [Google Scholar] [CrossRef] [PubMed]
  27. Quesada, S.P.; Paschoal, J.A.R.; Reyes, F.G.R. Considerations on the Aquaculture Development and on the Use of Veterinary Drugs: Special Issue for Fluoroquinolones-A Review. J. Food Sci. 2013, 78, R1321–R1333. [Google Scholar] [CrossRef] [PubMed]
  28. Tylová, T.; Flieger, M.; Olšovská, J. Determination of Antibiotics in Influents and Effluents of Wastewater-Treatment-Plants in the Czech Republic—Development and Application of the SPE and a UHPLC-ToFMS Method. Anal. Methods 2013, 5, 2110. [Google Scholar] [CrossRef]
  29. Kang, J.; Park, S.-J.; Park, H.-C.; Hossain, M.A.; Kim, M.-A.; Son, S.-W.; Lim, C.-M.; Kim, T.-W.; Cho, B.-H. Multiresidue Screening of Veterinary Drugs in Meat, Milk, Egg, and Fish Using Liquid Chromatography Coupled with Ion Trap Time-of-Flight Mass Spectrometry. Appl. Biochem. Biotechnol. 2017, 182, 635–652. [Google Scholar] [CrossRef] [PubMed]
  30. Jongedijk, E.; Fifeik, M.; Arrizabalaga-Larrañaga, A.; Polzer, J.; Blokland, M.; Sterk, S. Use of High-Resolution Mass Spectrometry for Veterinary Drug Multi-Residue Analysis. Food Control 2023, 145, 109488. [Google Scholar] [CrossRef]
  31. Stolker, A.A.M.; Rutgers, P.; Oosterink, E.; Lasaroms, J.J.P.; Peters, R.J.B.; van Rhijn, J.A.; Nielen, M.W.F. Comprehensive Screening and Quantification of Veterinary Drugs in Milk Using UPLC–ToF-MS. Anal. Bioanal. Chem. 2008, 391, 2309–2322. [Google Scholar] [CrossRef]
  32. Zhu, C.; Lai, G.; Jin, Y.; Xu, D.; Chen, J.; Jiang, X.; Wang, S.; Liu, G.; Xu, N.; Shen, R.; et al. Suspect Screening and Untargeted Analysis of Veterinary Drugs in Food by LC-HRMS: Application of Background Exclusion-Dependent Acquisition for Retrospective Analysis of Unknown Xenobiotics. J. Pharm. Biomed. Anal. 2022, 210, 114583. [Google Scholar] [CrossRef]
  33. Martins, M.T.; Barreto, F.; Hoff, R.B.; Jank, L.; Arsand, J.B.; Motta, T.M.C.; Schapoval, E.E.S. Multiclass and Multi-Residue Determination of Antibiotics in Bovine Milk by Liquid Chromatography–Tandem Mass Spectrometry: Combining Efficiency of Milk Control and Simplicity of Routine Analysis. Int. Dairy J. 2016, 59, 44–51. [Google Scholar] [CrossRef]
  34. Freitas, A.; Barbosa, J.; Ramos, F. Development and Validation of a Multi-Residue and Multiclass Ultra-High-Pressure Liquid Chromatography-Tandem Mass Spectrometry Screening of Antibiotics in Milk. Int. Dairy. J. 2013, 33, 38–43. [Google Scholar] [CrossRef]
  35. Junza, A.; Amatya, R.; Barrón, D.; Barbosa, J. Comparative Study of the LC–MS/MS and UPLC–MS/MS for the Multi-Residue Analysis of Quinolones, Penicillins and Cephalosporins in Cow Milk, and Validation According to the Regulation 2002/657/EC. J. Chromatogr. B 2011, 879, 2601–2610. [Google Scholar] [CrossRef] [PubMed]
  36. Kaufmann, A.; Butcher, P.; Maden, K.; Walker, S.; Widmer, M. Development of an Improved High Resolution Mass Spectrometry Based Multi-Residue Method for Veterinary Drugs in Various Food Matrices. Anal. Chim. Acta 2011, 700, 86–94. [Google Scholar] [CrossRef] [PubMed]
  37. Kaufmann, A.; Butcher, P.; Maden, K.; Widmer, M. Quantitative Multiresidue Method for about 100 Veterinary Drugs in Different Meat Matrices by Sub 2-Μm Particulate High-Performance Liquid Chromatography Coupled to Time of Flight Mass Spectrometry. J. Chromatogr. A 2008, 1194, 66–79. [Google Scholar] [CrossRef] [PubMed]
  38. Ortelli, D.; Cognard, E.; Jan, P.; Edder, P. Comprehensive Fast Multiresidue Screening of 150 Veterinary Drugs in Milk by Ultra-Performance Liquid Chromatography Coupled to Time of Flight Mass Spectrometry. J. Chromatogr. B 2009, 877, 2363–2374. [Google Scholar] [CrossRef] [PubMed]
  39. European Medicines Agency. ICH Guideline Q2(R2) on Validation of Analytical Procedures; Food and Drug Administration: Silver Spring, MD, USA, 2022.
  40. Yan, Y.; Zhang, H.; Ai, L.; Kang, W.; Lian, K.; Wang, J. Determination of Gamithromycin Residues in Eggs, Milk and Edible Tissue of Food-Producing Animals by Solid Phase Extraction Combined with Ultrahigh-Performance Liquid Chromatography-Tandem Mass Spectrometry. J. Chromatogr. B 2021, 1171, 122637. [Google Scholar] [CrossRef] [PubMed]
  41. Wang, K.; Lin, K.; Huang, X.; Chen, M. A Simple and Fast Extraction Method for the Determination of Multiclass Antibiotics in Eggs Using LC-MS/MS. J. Agric. Food Chem. 2017, 65, 5064–5073. [Google Scholar] [CrossRef]
  42. Li, J.; Ren, X.; Diao, Y.; Chen, Y.; Wang, Q.; Jin, W.; Zhou, P.; Fan, Q.; Zhang, Y.; Liu, H. Multiclass Analysis of 25 Veterinary Drugs in Milk by Ultra-High Performance Liquid Chromatography-Tandem Mass Spectrometry. Food Chem. 2018, 257, 259–264. [Google Scholar] [CrossRef]
  43. Castilla-Fernández, D.; Moreno-González, D.; Beneito-Cambra, M.; Molina-Díaz, A. Critical Assessment of Two Sample Treatment Methods for Multiresidue Determination of Veterinary Drugs in Milk by UHPLC-MS/MS. Anal. Bioanal. Chem. 2019, 411, 1433–1442. [Google Scholar] [CrossRef]
  44. Wang, J.; Leung, D.; Chow, W.; Chang, J.; Wong, J.W. Target Screening of 105 Veterinary Drug Residues in Milk Using UHPLC/ESI Q-Orbitrap Multiplexing Data Independent Acquisition. Anal. Bioanal. Chem. 2018, 410, 5373–5389. [Google Scholar] [CrossRef]
  45. Jadhav, M.R.; Pudale, A.; Raut, P.; Utture, S.; Ahammed Shabeer, T.P.; Banerjee, K. A Unified Approach for High-Throughput Quantitative Analysis of the Residues of Multi-Class Veterinary Drugs and Pesticides in Bovine Milk Using LC-MS/MS and GC–MS/MS. Food Chem. 2019, 272, 292–305. [Google Scholar] [CrossRef]
  46. Zhu, W.; Yang, J.; Wang, Z.; Wang, C.; Liu, Y.; Zhang, L. Rapid Determination of 88 Veterinary Drug Residues in Milk Using Automated TurborFlow Online Clean-up Mode Coupled to Liquid Chromatography-Tandem Mass Spectrometry. Talanta 2016, 148, 401–411. [Google Scholar] [CrossRef]
  47. Kim, Y.R.; Park, S.Y.; Lee, T.H.; Kim, J.Y.; Choi, J.-D.; Moon, G. Multi-Class, Multi-Residue Analysis of 59 Veterinary Drugs in Livestock Products for Screening and Quantification Using Liquid Chromatography-Tandem Mass Spectrometry. Korean J. Environ. Agric. 2022, 41, 288–309. [Google Scholar] [CrossRef]
  48. Wang, H.; Ren, L.; Yu, X.; Hu, J.; Chen, Y.; He, G.; Jiang, Q. Antibiotic Residues in Meat, Milk and Aquatic Products in Shanghai and Human Exposure Assessment. Food Control 2017, 80, 217–225. [Google Scholar] [CrossRef]
  49. Jank, L.; Martins, M.T.; Arsand, J.B.; Motta, T.M.C.; Feijó, T.C.; dos Santos Castilhos, T.; Hoff, R.B.; Barreto, F.; Pizzolato, T.M. Liquid Chromatography–Tandem Mass Spectrometry Multiclass Method for 46 Antibiotics Residues in Milk and Meat: Development and Validation. Food Anal. Methods 2017, 10, 2152–2164. [Google Scholar] [CrossRef]
Table 1. Validation parameters of the target antibiotics.
Table 1. Validation parameters of the target antibiotics.
AntibioticMolecular
Formula
Mass (Da)[M+H]+ (m/z)Max. ∆ppmRT (min)MRL or (*)VL
(µg kg−1)
CCβ
(µg L−1)
LoD
(µg L−1)
LoQ
(µg L−1)
Recovery (%)PrecisionLinearity (R2)
Intra-Day (%)Inter-Day (%)
Acetyltylosin, 3-O-C48H79NO18957.52971958.536750.965.365012.50.030.10105.65.58.10.9995
AmoxicillinC16H19N3O5S365.10454366.111821.493.6420.671.2284.315.520.60.9978
AmpicillinC16H19N3O4S349.10963350.116900.604.2420.311.0496.110.615.90.9967
BacitracinC66H103N17O16S1421.74894711.882260.764.75100251.414.27111.86.411.60.9968
BaquiloprimC17H20N6308.17494309.18200−4.543.3307.50.090.28106.520.328.80.9951
BenzylpenicillinC16H18N2O4S334.09873335.10601−0.244.4420.531.7683.18.913.40.9953
CefacetrileC13H13N3O6S339.05251340.05978−3.704.912512.52.428.0685.811.317.00.9988
CefaloniumC20H18N4O5S2458.07186459.079270.814.320100.080.23103.910.6313.60.9990
CefapirinC17H17N3O6S2423.05588424.063160.794.06060.060.21114.57.010.40.9958
CefazolinC14H14N8O4S3454.03002455.037293.774.65050.060.18129.413.019.40.9973
CefoperazonC25H27N9O8S2645.14240646.14968−0.724.95050.872.8880.714.725.00.9800
CefquinomeC23H24N6O5S2528.12496529.13224−3.933.92020.381.28122.013.016.50.9925
CeftiofurC19H17N5O7S3523.02901524.036292.595.2100100.0030.01096.28.913.30.9906
CephalexinC16H17N3O4S347.09398348.101250.654.2100100.943.15117.810.215.30.9842
ChlortetracyclinC22H23ClN2O8478.11429479.12157−0.104.6100100.070.24101.010.716.10.9865
Cinoxacin (a)C12H10N2O5262.05897263.06625−0.305.030*30.010.0292.111.717.50.9984
CiprofloxacinC17H18FN3O3331.13322332.140500.954.4100100.080.28108.011.016.40.9996
Clindamycin (a)C18H33ClN2O5S424.17987425.187450.715.9100*100.150.44106.45.08.60.9995
CloxacillinC19H18ClN3O5S435.06557436.072850.655.93030.030.1199.14.14.70.9992
DanofloxacinC19H20FN3O3357.14887358.156151.344.43030.130.42116.610.315.50.9989
Dapsone (b)C12H12N2O2S248.06195249.06923−0.994.810*2.50.471.58109.17.110.70.9975
DesacetylcephapirinC15H15N3O5S2381.04531382.052750.102.76060.361.09108.68.111.70.9984
DicloxacillinC19H17Cl2N3O5S469.02660470.03387−0.816.23030.130.43107.75.17.60.9986
DifloxacinC21H19F2N3O3399.13944400.146480.804.7307.50.040.13104.25.67.70.9998
Doxycycline (c)C22H24N2O8444.15327445.160541.004.94*20.280.95117.613.420.10.9875
Enoxacin (a)C15H17FN4O3320.12847321.135751.704.330*30.020.08107.07.910.40.9982
EnrofloxacinC19H22FN3O3359.16452360.171800.104.5100100.170.56114.411.917.80.9992
epi-ChlortetracyclinC22H23ClN2O8478.11429479.12157−0.364.4100100.170.58118.211.016.60.9988
epi-OxytetracyclinC22H24N2O9460.14818461.155460.383.9100100.260.8695.28.512.80.9996
epi-TetracyclinC22H24N2O8444.15327445.16054−0.154.3100100.140.48112.78.212.30.9954
ErythromycinC37H67NO13733.46124734.468520.905.240101.755.82110.37.511.30.9988
FlorfenicolC12H14Cl2FNO4S357.00046358.007413.944.55051.775.35103.49.312.20.9981
Florfenicol amineC10H14FNO3S247.06784248.07521−2.891.355012.50.170.52103.45.59.30.9995
FlumequineC14H12FNO3261.08012262.087400.775.75050.010.05107.55.37.90.9998
GamithromycinC40H76N2O12776.53982777.54708−0.104.85012.50.050.14102.86.38.40.9996
JosamycinC42H69NO15827.46672828.474021.035.65012.50.020.05106.44.58.60.9990
LincomycinC18H34N2O6S406.21375407.221451.354.115012.50.070.21106.66.08.70.9991
MarbofloxacinC17H19FN4O4362.13903363.146311.514.3757.50.140.47101.35.68.50.9997
NafcillinC21H22N2O5S414.12494415.132220.846.03030.070.22105.45.17.70.9994
Nalidixic acid (a)C12H12N2O3232.08479233.092070.295.630*30.010.04106.35.67.20.9996
NeospiramycinC36H62N2O11698.43536699.442970.474.72001000.110.34113.712.419.90.9930
Norfloxacin (a)C16H18FN3O3319.13322320.140500.964.330*30.020.06114.99.414.20.9984
NovobiocinC31H36N2O11698.43536699.44199−0.287.05012.50.461.40110.18.412.10.9969
Ofloxacin (a)C18H20FN3O4361.14378362.151060.594.330*30.010.04110.88.813.10.9994
OleandomycinC35H61NO12687.41938688.426400.355.15012.50.110.33105.56.68.60.9996
Ormetoprim (a)C14H18N4O2274.14298275.150250.974.450*50.130.45103.24.33.40.9981
OxacillinC19H19N3O5S401.10454402.111820.845.83030.180.61111.28.011.90.9985
Oxolinic acid (c)C13H11NO5261.06372262.071000.965.23030.0010.004107.98.412.70.9974
OxytetracyclineC22H24N2O9460.14818461.155460.514.1100100.090.29106.06.29.30.9994
PhenoxymethylpenicillinC16H18N2O5S350.09364351.100840.775.7420.080.24128.812.620.90.9876
PirlimycinC17H31ClN2O5S410.16422411.171640.464.7100100.290.89106.25.07.70.9998
RifaximinC43H51N3O11785.35236786.359241.256.560150.631.91107.117.125.60.9962
RoxithromycinC41H76N2O15836.52457837.532460.685.55050.050.15107.64.48.90.9994
Sarafloxacin (a)C20H17F2N3O3385.12380386.13107−0.224.730*30.090.30104.94.56.80.9999
SpiramycinC43H74N2O14842.51401843.52128−0.374.6200200.270.90119.210.112.20.9911
SulfabenzamideC13H12N2O3S276.05686277.06438−0.475.2100100.110.3395.97.916.80.9952
SulfacetamideC8H10N2O3S214.04121215.04849−0.853.5100107.2224.06108.412.919.30.9976
SulfachloropyridazineC10H9ClN4O2S284.01348285.02075−0.264.9100100.110.36112.413.019.60.9947
SulfaclozineC10H9ClN4O2S284.01348285.020750.275.3100100.140.4899.03.14.70.9999
SulfadiazineC10H10N4O2S250.05245251.059720.804.0100100.391.3081.68.112.10.9895
SulfadimethoxineC12H14N4O4S310.07358311.080851.585.3100100.040.14104.94.16.10.9973
SulfadimidinC12H14N4O2S278.08375279.091020.964.6100101.023.39107.75.78.60.9945
SulfadoxineC12H14N4O4S310.07358311.080850.755.0100100.040.15114.013.319.90.9992
SulfaguanidinC7H10N4O2S214.05245215.059720.781.2100101.103.6598.16.09.00.9967
SulfamerazineC11H12N4O2S264.06809265.075661.214.3100250.160.4898.45.98.70.9995
SulfamethizolC9H10N4O2S2270.02452271.031800.614.6100101.234.10107.76.610.40.9991
SulfamethoxazoleC10H11N3O3S253.05211254.059390.675.0100100.200.66105.712.118.20.9968
SulfamethoxypyridazineC11H12N4O3S280.06301281.070290.964.6100100.591.98100.02.23.30.9996
SulfamonomethoxineC11H12N4O3S280.06301281.070290.764.8100100.842.8199.53.34.90.9996
SulfamoxolC11H13N3O3S267.06776268.075040.824.5100100.612.03102.93.24.80.9986
SulfanilamideC6H8N2O2S172.03065173.03793−0.851.4100509.1330.45109.27.210.80.9927
SulfapyridinC11H11N3O2S249.05720250.064470.784.2100100.240.81102.38.312.50.9951
SulfaquinoxalineC14H12N4O2S300.06810301.075370.875.3100100.431.42104.14.87.20.9940
SulfasalazineC18H14N4O5S398.06849399.075770.835.5100100.110.36101.23.75.50.9995
SulfathiazoleC9H9N3O2S2255.01362256.020900.904.2100100.180.59101.96.610.00.9994
SulfisomidineC12H14N4O2S278.08375279.091020.623.9100102.829.40120.811.317.00.9966
SulfisoxazoleC11H13N3O3S267.06776268.075040.695.1100100.090.29112.212.719.00.9965
TetracyclineC22H24N2O8444.15327445.160540.884.5100100.421.4097.73.45.10.9959
ThiamphenicolC12H15Cl2NO5S355.00480356.01230−1.404.55051.183.58106.58.312.50.9989
Tiamulin (a)C28H47NO4S493.32258494.329860.475.450*50.070.24103.34.26.20.9998
TildipirosinC41H71N3O8733.52412734.531920.944.05050.010.02110.88.015.20.9986
TilmicosinC46H80N2O13868.56604869.57332−0.864.950250.230.8499.510.213.50.9986
TrimethoprimC14H18N4O3290.13789291.145171.574.35050.170.57108.74.710.10.9998
TulathromycinC41H79N3O12805.56638806.573440.204.35050.050.16115.68.415.10.9962
Tylosin AC46H77NO17915.51915916.52643−0.365.35050.020.07117.89.113.60.9984
TylvylosinC53H87NO191041.58723348.202941.705.55050.030.08105.15.48.80.9998
Valnemulin (a)C31H52N2O5S564.35970565.36697−0.895.650*50.010.03118.69.414.10.9998
Virginiamycin M1C28H35N3O7525.24750526.254971.105.85050.842.55103.96.48.70.9999
Virginiamycin S1C43H49N7O10823.35409824.361360.566.45050.070.23106.14.77.70.9986
(a) No MRL defined; (b) prohibited; (c) not allowed for milk production.
Table 2. Antibiotics detected in raw milk samples.
Table 2. Antibiotics detected in raw milk samples.
OriginMilk SourceTypes of MilkDetected
Compounds
Antibiotic GroupConcentration
(µg kg−1)
AnimalCowRaw---
AnimalCowSemi-skimmed milkGamithromycin
Tilmicosin
Macrolides10.70
<LOQ
AnimalCowSemi-skimmed milk---
AnimalCowSemi-skimmed milk---
AnimalCowSemi-skimmed milk---
AnimalCowSemi-skimmed milk---
AnimalCowSemi-skimmed milk---
AnimalCowSemi-skimmed milk---
AnimalCowSemi-skimmed milk---
AnimalCowSemi-skimmed milk---
AnimalCowSemi-skimmed milk---
AnimalCowSemi-skimmed milk---
AnimalCowSemi-skimmed milk---
AnimalCowSemi-skimmed milk---
AnimalCowSemi-skimmed milk---
AnimalCowSemi-skimmed milk
(Fresh milk)
---
AnimalCowSkimmed milkTildipirosinMacrolides3.33
AnimalCowSkimmed milk---
AnimalCowSkimmed milk---
AnimalCowSkimmed milkTildipirosinMacrolides2.89
AnimalCowSkimmed milk---
AnimalCowSkimmed milk---
AnimalCowSkimmed milk---
AnimalCowWhole milk---
AnimalCowWhole milk---
AnimalGrazing cowSemi-skimmed milk---
Plant-basedOats----
Plant-basedOats----
Plant-basedOats----
Plant-basedSoya---
Plant-basedSoya-SulfamerazinSulfonamides4.25
Plant-basedSoya----
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MDPI and ACS Style

Leite, M.; Marques, A.R.; Vila Pouca, A.S.; Barros, S.C.; Barbosa, J.; Ramos, F.; Afonso, I.M.; Freitas, A. UHPLC-ToF-MS as a High-Resolution Mass Spectrometry Tool for Veterinary Drug Quantification in Milk. Separations 2023, 10, 457. https://0-doi-org.brum.beds.ac.uk/10.3390/separations10080457

AMA Style

Leite M, Marques AR, Vila Pouca AS, Barros SC, Barbosa J, Ramos F, Afonso IM, Freitas A. UHPLC-ToF-MS as a High-Resolution Mass Spectrometry Tool for Veterinary Drug Quantification in Milk. Separations. 2023; 10(8):457. https://0-doi-org.brum.beds.ac.uk/10.3390/separations10080457

Chicago/Turabian Style

Leite, Marta, Ana Rita Marques, Ana Sofia Vila Pouca, Silvia Cruz Barros, Jorge Barbosa, Fernando Ramos, Isabel Maria Afonso, and Andreia Freitas. 2023. "UHPLC-ToF-MS as a High-Resolution Mass Spectrometry Tool for Veterinary Drug Quantification in Milk" Separations 10, no. 8: 457. https://0-doi-org.brum.beds.ac.uk/10.3390/separations10080457

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