Skip to main content
Molecules logoLink to Molecules
. 2022 Dec 26;28(1):216. doi: 10.3390/molecules28010216

Identification and Quantification of 29 Active Substances by HPLC–ESI-MS/MS in Lyophilized Swine Manure Samples

Carolina Nebot 1,*, Alejandra Cardelle-Cobas 1, Ignacio García-Presedo 2, Ewelina Patyra 3, Alberto Cepeda 1, Carlos M Franco 1
Editor: Gavino Sanna
PMCID: PMC9822080  PMID: 36615410

Abstract

Veterinary drugs are frequently employed to treat and prevent diseases in food-producing animals to improve animal health and to avoid the introduction of microorganisms into the food chain. The analysis of the presence of pharmaceutical residues in animal manure could help to evaluate the legal and illegal practices during food production without harming the animals and to correctly manage manure when it is going to be applied as a fertilizer. This article describes a method for the simultaneous analysis of 29 active substances, mostly antibiotics and antiparasitic agents. Substances were extracted from lyophilized manure with a methanol:McIlvaine solution and analyzed with HPLC–ESI-MS/MS and a C18 HPLC column. The method was validated following European guidelines, the achieved trueness was between 63 and 128% (depending on the analytes), and the linearity was between 100 and 1500 µg/kg. The applicability of the method was demonstrated in 40 manure samples collected from pig farms where tetracycline was quantified in 7.5% of the samples. These results show the viability of this non-invasive method for the control of the legal and illegal administration of pharmaceuticals in food-producing animals.

Keywords: swine, drugs, feces, manure, non-invasive method, HPLC–MS/MS

1. Introduction

Food of animal origin is produced around the world, and animals involved in this type of production include cattle, sheep, goats, swine, poultry, and equines [1]. These animals, like humans, have diseases and need to be treated to avoid death which leads to economic losses for farmers, and, more importantly, to avoid the introduction of food pathogens in the food chain. Therefore, inspections and animal treatments are vital for consumers’ safety and human health. Veterinary treatments in food-producing animals are always conducted and controlled by veterinarians within the European Union, who choose the treatment [2]. Depending on the diseases and number of animals, medicines may be administrated in a variety of forms, including injections, tablets, creams, ointments, lotions, and sprays. For large groups of animals, pharmaceuticals are administrated through medicated feed or water. A wide range of drugs can be administrated to food-producing animals, including non-steroidal anti-inflammatory agents, antibiotics, and coccidiostats [1]. Drugs are metabolized and excreted through feces or urine as metabolites or in the unmetabolized form, and the percent of excretion of the unmetabolized form is variable and dependent on the drugs. For example, 66% of the initial dose of the antibiotic sulfachloropyridazine is excreted unchanged [3]. On the other hand, only 11% of the initial dose of sulfamethoxazole is excreted unchanged [4].

The analysis of the presence of active substances such as antibiotics in swine manure is relevant from two points of view. First is the food safety perspective, as it is a non-invasive way to control the legal or illegal administration of veterinary drugs to food-producing animals, as samples can be easily taken from the floor without stressing or damaging animals. Food of animal origin is controlled with different monitoring plans to ensure food safety; however, the analysis of manure is an interesting way to curtail illegal practices. On the other hand, the presence of active substances in manure needs to be controlled from an environmental point of view, as manure is employed as a natural fertilizer for farmland or grassland [5,6] and pharmaceuticals are transferred from the manure to soils and the water, thus contaminating rivers, lakes, and drinking water sources [7,8]. The concentration of antibiotics in swine manure has been shown to be between a few μg/kg and several hundred mg/kg [9,10] depending on the location of the farm, the farm size, and the treatment applied to the animals. One of the most relevant problem of the environmental presence of antibiotics is the increased development of bacteria with resistance genes. In a study conducted in the Netherlands where feces samples from pigs and cattle were analyzed, antibiotics were detected in more than 50% of the samples, and 34% of the samples contained more than one antibiotic, with those from the groups of tetracyclines and sulfonamides being most frequently detected [10].

Few articles on analytical method for the analysis of antibiotic in feces samples could be found in the literature because most research has focused on contaminated matrices such as water, soil, or food. Additionally, manure analysis could require different steps due to the complexity of the studied matrix, and reported methods include laborious extraction protocols [11] including the use of ultrasonic-assisted extraction [12,13,14,15,16], microwave-assisted extraction [17,18,19], and solid-phase extraction, which is the most popular method for matrix clean-up [20,21,22]. Regarding the detection of veterinary drugs high-performance liquid chromatography combined with tandem mass spectrometry is considered the best choice due to its high selectivity and sensitivity [11,23,24,25,26,27].

Even if a few methods have been reported in the literature for the analysis of active substances in animal feces samples, more reliable methods are required to control the presence of these substances in swine manure to avoid the introduction of antibiotics into the food chain or the environment; these methods will also help to reduce the illegal use of drugs in food-producing animals. Therefore, the objective of this work was to present an analytical tool based on HPLC–MS/MS for the identification and quantification of 31 active substances in swine manure. Table 1 compiles the compound, therapeutic class, CAS Number, molecular weight, and chemical formula of the selected pharmaceuticals.

Table 1.

Analyte name, therapeutic class, CAS Register Number (CAS), molecular weight (MW) and chemical formula of the selected pharmaceuticals.

Compound Therapeutic Groups CAS MW Stock Solution Concentration (µg/mL) Solvent
Amoxicillin Antibiotic 26787-78-0 365.4 800 Methanol
Azithromycin Antibiotic 83905-01-5 749.03 800 Methanol
Cefuroxime Antibiotic 55268-75-2 424.38 800 Methanol
Chloramphenicol Antibiotic 56-75-7 323.13 1000 Methanol
Chlortetracycline Antibiotic 57-62-5 478.88 1000 Methanol
Ciprofloxacin Antibiotic 85721-33-1 331.34 400 Water:Methanol (3:1)
Clarithromycin Antibiotic 81103-11-9 747.96 400 Methanol
Colistin Antibiotic 1066-17-7 1155.4 800 Methanol
Danofloxacin Antibiotic 112398-08-0 357.38 800 Methanol
Decoquinate Antiparasitic Agent 18507-89-6 417.5 100 Methanol
Dexamethasone Corticosteroids 50-02-2 392.5 800 Methanol
Diclofenac Anti-Inflammatory 15307-86-5 296.15 800 Methanol
Difloxacin Antibiotic 98106-17-3 399.4 400 Methanol
Doxycycline Antibiotic 564-25-0 444.44 1000 Methanol
Enrofloxacin Antibiotic 93106-60-6 359.4 800 Methanol
Erythromycin Antibiotic 114-07-8 733.9 800 Methanol
Florfenicol Antibiotic 73231-34-2 358.2 1000 Methanol
Flumethasone Glucocorticoid 2135-17-3 410.5 800 Methanol
Griseofulvin Fungistatic Agent 126-07-8 352.8 400 Methanol
Ibuprofen Nonsteroidal Anti-inflammatory 15687-27-1 206.28 800 Methanol
Levofloxacin Antibiotic 100986-85-4 361.37 800 Methanol
Lincomycin Antibiotic 154-21-2 406.54 800 Methanol
Maduramicin Antiparasitic Agent 84878-61-5 934.2 800 Methanol
Mefenamic Acid Anti-Inflammatory 61-68-7 241.28 400 Methanol
Monesin Antiparasitic Agent 17090-79-8 670.9 800 Methanol
Narasin Antiparasitic Agent 555134-13-9 765.0 400 Methanol
Nicarbazin Antiparasitic Agent 330-95-0 426.4 800 Dimethyl Sulfoxide
Norfloxacin Antibiotic 70458-96-7 319.33 800 Methanol
Oxytetracycline Antibiotic 79-57-2 460.44 1000 Methanol
Paracetamol Nonsteroidal Anti-Inflammatory 103-90-2 151.16 800 Methanol
Propranolol Beta Blocker 525-66-6 259.34 800 Methanol
Robenidine Antiparasitic Agent 25875-51-8 334.2 Methanol
Sarafloxacin Antibiotic 98105-99-8 385.36 400 Methanol
Salinomycin Antiparasitic Agent 53003-10-4 751.0 Methanol
Spectinomycin Antibiotic 1695-77-8 332.35 400 Water:H+
Sulfachloropyridazine Antibiotic 80-32-0 284.73 50 Methanol
Sulfadiazine Antibiotic 68-35-9 250.28 50 Methanol
Sulfadimethoxine Antibiotic 122-11-2 310.33 50 Methanol
Sulfamerazine Antibiotic 127-79-7 264.31 50 Methanol
Sulfamethazine Antibiotic 57-68-1 278.33 50 Methanol
Sulfamethoxazole Antibiotic 723-46-6 253.28 50 Methanol
Sulfamethoxypyridazine Antibiotic 80-35-3 280.3 50 Methanol
Sulfapyridine Antibiotic 144.83-2 249.29 50 Methanol
Sulfaquinoxaline Antibiotic 59-40-5 300.34 50 Methanol
Sulfathiazole Antibiotic 72-14-0 255.32 50 Methanol
Tetracycline Antibiotic 60-54-8 444.43 1000 Methanol
Trimethoprim Antibiotic 738-70-5 290.32 800 Methanol
Tylosin Antibiotic 1401-69-0 916.1 800 Methanol
Amoxicillin Antibiotic 26787-78-0 365.4 800 Methanol
Azithromycin Antibiotic 83905-01-5 749.03 800 Methanol
Cefuroxime Antibiotic 55268-75-2 424.38 800 Methanol
Chloramphenicol Antibiotic 56-75-7 323.13 1000 Methanol
Chlortetracycline Antibiotic 57-62-5 478.88 1000 Methanol
Ciprofloxacin Antibiotic 85721-33-1 331.34 400 Water:Methanol (3:1)
Clarithromycin Antibiotic 81103-11-9 747.96 400 Methanol
Colistin Antibiotic 1066-17-7 1155.4 800 Methanol
Danofloxacin Antibiotic 112398-08-0 357.38 800 Methanol
Decoquinate Antiparasitic Agent 18507-89-6 417.5 100 Methanol
Dexamethasone Corticosteroids 50-02-2 392.5 800 Methanol
Diclofenac Anti-Inflammatory 15307-86-5 296.15 800 Methanol
Difloxacin Antibiotic 98106-17-3 399.4 400 Methanol
Doxycycline Antibiotic 564-25-0 444.44 1000 Methanol
Enrofloxacin Antibiotic 93106-60-6 359.4 800 Methanol
Erythromycin Antibiotic 114-07-8 733.9 800 Methanol
Florfenicol Antibiotic 73231-34-2 358.2 1000 Methanol
Flumethasone Glucocorticoid 2135-17-3 410.5 800 Methanol
Griseofulvin Fungistatic Agent 126-07-8 352.8 400 Methanol
Ibuprofen Nonsteroidal Anti-Inflammatory 15687-27-1 206.28 800 Methanol
Levofloxacin Antibiotic 100986-85-4 361.37 800 Methanol
Lincomycin Antibiotic 154-21-2 406.54 800 Methanol
Maduramicin Antiparasitic Agent 84878-61-5 934.2 800 Methanol
Mefenamic Acid Anti-Inflammatory 61-68-7 241.28 400 Methanol
Monesin Antiparasitic Agent 17090-79-8 670.9 800 Methanol
Narasin Antiparasitic Agent 555134-13-9 765.0 400 Methanol
Nicarbazin Antiparasitic Agent 330-95-0 426.4 800 Dimethyl Sulfoxide
Norfloxacin Antibiotic 70458-96-7 319.33 800 Methanol
Oxytetracycline Antibiotic 79-57-2 460.44 1000 Methanol
Paracetamol Nonsteroidal Anti-Inflammatory 103-90-2 151.16 800 Methanol
Propranolol Beta Blocker 525-66-6 259.34 800 Methanol
Robenidine Antiparasitic Agent 25875-51-8 334.2 Methanol
Sarafloxacin Antibiotic 98105-99-8 385.36 400 Methanol
Salinomycin Antiparasitic Agent 53003-10-4 751.0 Methanol
Spectinomycin Antibiotic 1695-77-8 332.35 400 Water:H+
Sulfachloropyridazine Antibiotic 80-32-0 284.73 50 Methanol
Sulfadiazine Antibiotic 68-35-9 250.28 50 Methanol
Sulfadimethoxine Antibiotic 122-11-2 310.33 50 Methanol
Sulfamerazine Antibiotic 127-79-7 264.31 50 Methanol
Sulfamethazine Antibiotic 57-68-1 278.33 50 Methanol
Sulfamethoxazole Antibiotic 723-46-6 253.28 50 Methanol
Sulfamethoxypyridazine Antibiotic 80-35-3 280.3 50 Methanol
Sulfapyridine Antibiotic 144.83-2 249.29 50 Methanol
Sulfaquinoxaline Antibiotic 59-40-5 300.34 50 Methanol
Sulfathiazole Antibiotic 72-14-0 255.32 50 Methanol
Tetracycline Antibiotic 60-54-8 444.43 1000 Methanol
Trimethoprim Antibiotic 738-70-5 290.32 800 Methanol
Tylosin Antibiotic 1401-69-0 916.1 800 Methanol

2. Results and Discussion

2.1. Optimization of the LC–MS/MS Method

The selected compounds were detected with a mass spectrometer (MS) employing electrospray ionization (ESI) in the negative or positive mode depending on the analyte. For correct analyte identification, precursor and product ions, as well as the electrospray ionization (ESI) mode, were optimized by infusing standard solutions of each compound at 1 μg/L. Even though the samples matrix was manure, it was related to food, so Regulation 2021/808 [28] was employed as a guideline for method optimization and validation. MS optimization was achieved for most compounds; even though the employed MS has very good features for most compounds, response for coccidiostats (decoquinate, maduramicin, monesin, narasin, nicarbazin, robenidine and sarafloxacin, and salinomycin), were not the same as those previously achieved with other equipment [29,30], therefore theirs detection was discarded.

For the chromatographic separation of the analytes, three HPLC columns were tested; ACQUITY UPLC BEH C18 from Waters (Milford, USA), Intensity Solo 2 C18 from Bruker (Bremen, Germany), and Synergi Polar 5 um from Phenomenex (California, USA). Based on previously developed methods, the mobile phase was selected to be a combination of a gradient mode of water acidified with 0.1% of formic acid (mobile phase A) and acetonitrile acidified with 0.1% of formic acid (mobile phase B). The three tested columns were C18-packed, but their integration with the same analytes was different. The peak shape of mefenamic acid had a more gaussian shape with the Bruker and Phenomenex columns than with the Waters columns, and the opposite was observed for sulfamethizole. Regarding retention time (Rt), compounds eluted fastest with the Phenomenex column because it is shorter than the others. The difference in Rt varied from 0.5 min for danofloxacin to 2.9 min for mefenamic acid. Based on resolution, better peak shapes, peak high, and back pressure, the Intensity Solo HPLC column from Bruker was chosen as the most versatile column. Figure 1 shows the total ion chromatograms (TICs) of the three tested columns. As unsatisfactory chromatograms were obtained for amoxicillin, azithromycin, cefuroxime, colistin, flumethasone, griseofulvin, spectinomycin and sulfamethizole, these pharmaceuticals were not included in the final analysis. The other two columns, C18 from Waters and Phenomenex, showed similar chromatography for the discarded pharmaceuticals, but it is important to note that both of them permit the correct identification of more than 10 different compounds, as previously reported by other researchers [29,30,31,32,33]. Other columns available in the market and employed for antimicrobial detection in manure and feces samples include Nucleosil C18 HD [34] and Kinetex C18 [35]. The chromatographic performance of the HPLC method used in this study was initially investigated with a standard solution containing all selected pharmaceuticals at 100 ng/mL in mobile phase A. Replicate injections of various volumes (3, 5, 10, 15 and 20 µL) were performed to investigate repeatability and to avoid the introduction of a high volume of the sample matrix in order to obtain a good limit of detection for the selected drugs. The best results were achieved with 15 µL of injection. The reliable confirmation of the analytes was achieved with Rt and two MRM transitions from one parent and two product ions [28]. Table 2 compiles the Rt, MRM transition, and collision energy values of each analyte.

Figure 1.

Figure 1

Total ion chromatograms (TICs) of the selected pharmaceuticals separated on different HPLC columns.

Table 2.

Matrix effects, RSD matrix effects (RSDME), precision under repeatability (RSDr) and reproducibility (RSDR) conditions, trueness, and correlation coefficient (R2) achieved at different concentrations for each pharmaceutical.

Compound Concentration Matrix Effects RSDME (%) RSDr RSDR Trueness a b R2
(µg/kg) (%) (n = 6) (%) (n = 18) (%) (n = 18)
Chloramphenicol 200 0.9 7.5 13 11 118 3300.7 70.4 0.971
400 29 5 110
600 9 7 117
Chlortetracycline 200 1.3 15.8 20 13 141 22,883.9 3167.6 0.981
400 27 13 110
600 11 12 117
Ciprofloxacin 200 1.0 10.5 12 14 98 53,985.2 5468.9 0.986
400 21 14 113
600 3 14 107
Clarithromycin 200 0.5 13.0 21 5 107 68,053.0 906.3 0.966
400 41 7 111
600 8 16 136
Danafloxacin 200 0.6 8.1 7 18 99 16,787.8 4841.5 0.978
400 19 12 104
600 5 11 106
Dexamethasone 200 0.0 11.3 21 11 100 82.1 100.9 0.972
400 13 6 119
600 16 11 97
Diclofenac 200 0.4 2.9 10 12 110 49,795.8 3404.6 0.998
400 26 11 102
600 10 9 102
Difloxacin 200 0.3 3.0 9 18 113 30,438.3 2226.7 0.977
400 20 11 109
600 5 15 102
Doxycycline 200 2.8 8.4 11 16 95 1,294,454.7 14660.6 0.998
400 18 6 103
600 6 17 108
Enrofloxacin 200 1.2 9.0 18 10 90 236,205.7 7664.0 0.982
400 12 8 117
600 14 9 92
Florfenicol 200 0.9 9.0 18 10 111 2720.1 37.8 0.975
400 24 9 118
600 13 6 139
Levofloxacin 200 0.5 14.4 13 16 102 93,029.5 3682.9 0.971
400 23 5 102
600 3 14 98
Lincomycin 200 5.5 2.1 34 16 70 178,170.3 43379.3 0.977
400 28 15 66
600 20 10 74
Mefenamic Acid 200 2.3 19.1 24 16 118 273,977.7 13018.5 0.994
400 38 12 82
600 8 14 95
Norfloxacin 200 0.5 1.1 12 8 101 210,771.6 2414.2 0.969
400 22 9 110
600 4 9 114
Oxytetracycline 200 0.5 1.1 8 20 124 183,941.1 2705.8 0.977
400 24 13 84
600 13 10 109
Propranolol 200 0.4 3.8 13 20 118 77,055.7 1916.3 0.991
400 21 17 118
600 10 7 126
Sarafloxacin 200 0.7 3.6 7 18 109 96,223.4 4575.7 0.98
400 19 10 111
600 6 15 96
Sulfachloropyridine 200 1.0 3.7 10 22 113 239,127.4 5107.6 0.984
400 25 13 123
600 6 11 144
Sulfadimethoxine 200 0.8 3.6 6 15 117 480,417.2 13543.4 0.975
400 23 11 113
600 5 11 115
Sulfamerazine 200 1.8 3.6 5 22 117 67,678.2 4582.8 0.979
400 24 12 108
600 3 11 116
Sulfamethazine 200 1.5 2.5 6 25 132 645,449.5 13561.1 0.974
400 23 13 122
600 4 12 125
Sulfamethoxazole 200 0.9 5.5 12 22 111 185,586.8 5934.0 0.974
400 28 18 106
600 8 9 128
Sulfamethoxypyridazine 200 1.6 3.6 6 23 117 153,709.0 11111.6 0.976
400 22 12 110
600 3 12 115
Sulfapyridine 200 1.2 4.9 5 22 111 90,339.4 8788.6 0.983
400 27 13 112
600 5 11 123
Sulfaquinoxaline 200 0.8 4.6 6 21 115 216,109.5 4361.8 0.985
400 34 14 118
600 5 13 137
Sulfathiazole 200 0.5 5.4 6 21 116 70,093.4 6651.6 0.97
400 25 18 117
600 18 4 125
Tetracycline 200 0.1 5.2 7 18 107 16,481.5 1369.9 0.997
400 28 6 109
600 5 17 115
Trimethoprim 200 0.3 5.2 8 19 111 58,128.0 6639.5 0.975
400 27 12 119
600 5 11 121

2.2. Extraction Procedure

The analysis of pharmaceuticals in animal feces and manure can be difficult because it requires a complex matrix with a high level of organic matter. The primary objective of this research was to present a non-invasive analytical tool for organization related to food safety to control the administration of active substance in swine production The presented method was also aimed to be simple, inexpensive, and easy to apply in the laboratory, with reproducible results. Previously, pressurized liquid extraction enabled the extraction of toltrazuril, an antiparasitic, and its metabolites from manure collected from a piglet near Copenhagen [36]. The same technique was employed by Hansen et al. (2011) [37], who identified 10 hormones in pig manure, and by Wang et al. (2020), who extracted 33 antibiotics and 37 pesticides from livestock and poultry excrement samples [38]. Argüeso-Mata and collaborators (2021) combined two different extraction processes, dispersive solid-phase extraction and compact solid-phase extraction, to extract 21 analytes from different groups of antimicrobials such as macrolides, tetracyclines, β-lactams, sulfonamides and fluoroquinolones [39]. Approaches with QuEChERS [40] and normal solid-phase extraction with cartridges have also been reported [41]. The optimized method of extraction presented in this study does not require any material related to solid-phase extraction or pressurized liquid extraction as it employs a solvent of extraction mixture of methanol and a McIlvaine buffer. The use of this buffer combined with an organic solvent or followed by solid-phase extraction previously showed satisfactory results for the extraction of veterinary drugs from value matrices including baby food [42], feed [43] and soil [44]. One remarkable extraction protocol was described by Melekhina et al. (2021), who identified 63 veterinary drugs from various classes (sulfonamides, amphenicols, nitroimidazoles, β-lactams, macrolides, lincosamides, tetracyclines, quinolones and pleuromutilins) in chicken meat [45]. However, the protocol requires a purification step with hypercrosslinked polystyrene. This is the main advantage of the method presented here, as it only needs 10 mL of an extraction solvent. Before extraction, samples needed to be lyophilized to reduce the water content and to achieve a lower limit of detection. A total of 27 active ingredients in swine manure were satisfactorily extracted with the final extraction protocol, which was a combination of simple and short consecutive steps: a mixture of manure and the extraction solvent, sonication, agitation, centrifugation, and filtration, followed by a chromatographic method based on HPLC–MS/MS; this method enabled the correct identification and quantification of the studied compounds. Figure 2 shows MRM transition of each pharmaceutical of a matrix-matched sample spiked with pharmaceuticals at 400 µg/kg

Figure 2.

Figure 2

Figure 2

MRM chromatograms of pig feces sample fortified 29 veterinary drugs at the concentration level 400 μg/kg.

2.3. Method Validation

The entire procedure of extraction and HPLC–MS/MS analysis was validated with matrix-matched calibration samples. Validation parameters evaluated included linearity, precision under repeatability and reproducibility conditions, accuracy, sensitivity, specificity, and matrix effects. The results are shown in Table 2.

On each day of validation, a calibration curve was built with eight matrix-matched lyophilized manure samples spiked with all selected analytes at concentrations from 0 to 1500 µg/kg. The coefficient of determination (R2) obtained for each compound on each day was 0.97 or higher, indicating good linearity. Precision under repeatability (n = 6, one day) and reproducibility conditions (n = 18, three days) showed a relative standard deviation (RSD%) of less than 20% for most compounds; out of 27, lincomycin showed the highest RSD of 34%, 30%, and 20% at 200, 400 and 600 µg/kg, respectively.

Accuracy, as defined in Regulation 808/2021, was evaluated with six replicate samples showing a close agreement between the spiked level and accepted true reference value; employing the calibration curve build on that day showed that the accuracy was between 80 and 120%. Additionally, the specificity of the method was tested by processing and analyzing 20 replicate samples with different drugs at the same concentration (400 µg/kg) and without drugs.

The potential effect of the matrix on the drug concentration calculation was also evaluated by comparing the response of the instrument to the compounds dissolved in a solvent to the response to a matrix-matched sample. In these manure samples, the matrix was complex and had a high level of interference from inorganics such as Ca, Mg, and other minerals that could form chelates; tetracyclines and other organic compounds compete with the selected pharmaceuticals in terms of extraction efficiency. These interferences not only could reduce the recoveries but also they could amplify or lower the signal response.

Matrix effects were calculated, as indicated in Regulation 2021/808, by dividing the signal of a matrix-matched sample by the signal of a standard solution at the same concentration. A result below 100% indicated ion suppression, and a result above 100% indicated ion enhancement.

The matrix effect is the effect that a matrix can have on a drug concentration calculation. It was evaluated in this study by comparing the response of the instrument to the compounds dissolved in a solvent to the response to a matrix-matched sample. In this case, feces were found to affect pharmaceutical concentration by interfering with the extraction and reducing its efficiency. The feces matrix could also interfere with the signal response by amplifying or lowering it and consequently increasing or reducing the calculated concentration. The matrix factor (MF) for each drug was calculated as the peak area of a matrix-matched standard against the peak area of a standard solution. The results are summarized in Table 2. In general, MF values were around one except for mefenamic acid, diclofenac, and lincomycin, which had values of 1.6, 1.7, and 1.4, respectively. The RSD of the MF, calculated as the mean of the MF obtained for the concentration range from LOD to 2000 ng/g, was below 20% in all cases, which is a satisfactory value according to Regulation 2021/808.

2.4. Application to Feces Samples

Pharmaceuticals were only detected in 4 manure samples out of 40, representing 7.5% of the analyzed samples. The compounds that were detected were doxycycline and oxytetracycline. The detection of doxycycline and oxytetracycline was an unexpected result since the animals were not treated with these substances and their concentration in the lyophilized samples did not exceed 7 mg/kg, which could indicate animal treatment at the previous stage of production. Since the treatments at the piglet weaning phase were unknown, the proposed explanation is plausible.

It is also important to highlight that even though some animals were treated with Florken and Pulmoval, no florfenicol residues were detected in the feces. Even though two samples were collected for each batch of pigs, florfenicol treatment was conducted just after the collection of the first sample and one month before the collection of the second sample. Therefore, residues of florfenicol in the animals were slowly eliminated after the treatment. For the specific case of pigs and florfenicol, the withdrawal period is 15 days.

Likewise, it should be noted that fecal analysis is a non-invasive method that allows for the detection of the illegal and legal administration of drugs to food -producing animals. The analysis of this type of sample is not a common practice for food-producing animals even though it can be used to obtain satisfactory results with a low limit of detection when lyophilization is applied to samples. Most publications on the drug analysis of animal feces, such as the work carried out by Sengeløv et al. (2003), Holzel et al. (2013), Joy et al. (2013), and Pu et al. (2018) [46,47,48,49], have focused on the environmental point of view and the impact of applying manure as a fertilizer, especially on the development of bacteria with resistance genes. Considering the results obtained within this research project and all the benefits observed for animals and farmers, the analysis of drugs in fecal samples for the detection of legal or illegal practices during animal production should be more common and standardized since it allows for control without harming animals.

3. Materials and Methods

3.1. Chemicals and Reagents

Amoxicillin, azithromycin, cefuroxime, chloramphenicol, chlortetracycline, ciprofloxacin, clarithromycin, colistin, danafloxacin, decoquinate, dexamethasone, diclofenac, difloxacin, doxycycline, enrofloxacin, erythromycin, florfenicol, flumethasone, griseofulvin, ibuprofen, levofloxacin, lincomycin, maduramicin, mefenamic acid, monesin, narasin, nicarbazin, norfloxacin, oxytetracycline, paracetamol, propranolol, robenidine, sarafloxacin, salinomycin, spectinomycin, sulfachloropyridine, sulfadiazine, sulfadimethoxine, sulfamerazine, sulfamethasone, sulfamethoxazole, sulfamethoxypyridazine, sulfapyridine, sulfaquinoxaline, sulfathiazole, tetracycline, trimethoprim, and tylosin with a purity above 98% were bought from Sigma-Aldrich (St. Louis, MO, USA). Anhydrous citric acid, trichloroacetic acid (TCA), ethylenediaminetetraacetic acid disodium salt (EDTA), and disodium hydrogen phosphate dehydrate were also purchased from Sigma-Aldrich (St. Louis, MO, USA). Acetonitrile (ACN), methanol (MeOH) (HPLC grade ≥ 99%), and formic acid (purity > 99% for analysis) were obtained from Acros Organics (Geel, Belgium). Purified water, with a resistivity higher than 18.0 MU, was prepared in the laboratory with a Milli-Q system from Millipore (Burlington, MA, USA).

3.2. Preparation of Reagents and Standard Solutions

Water, ACN, or MeOH were employed as solvents to prepare the standard solutions of the selected pharmaceuticals. First, an accurately weighed (±0.1 mg) amount of pharmaceutical, 10 or 20 mg measured with an analytical balance (Ohaus, Greifensee, Switzerland), was transferred into a 25 mL amber volumetric flask. The final concentration of each stock solution depended on each pharmaceutical’s solubility. The different stock solutions were mixed to obtain a 5 µg/mL working standard solution of each pharmaceutical. All solutions were stored at −20 °C for a minimum period of one month.

Mobile phases A and B were prepared by adding 500 μL of formic acid to ~400 mL of Milli-Q water (mobile phase A) or acetonitrile (mobile phase B), respectively. The volume was finally set to 500 mL with the corresponding solvent to achieve a final formic acid concentration of 0.1% in each case.

A McIlvaine buffer solution was prepared by mixing citric acid (615.4 mL at 0.1 M) with disodium hydrogen phosphate (385 mL at 0.2 M). NaOH or HCl was used to adjust the pH. Once the pH was 4, EDTA (37.2 g) was added to a 1 L McIlvaine buffer solution and stored at 8 °C for one month. The final extraction solution was a mixture of methanol and McIlvaine–EDTA (70:30), which was prepared for each day of extraction.

3.3. Equipment

Swine manure samples were analyzed with the following equipment: an RSLAB-9 rotatory shaker (Rogo Sampaic, Wissous, France); a Minishaker model MS2 vortex mixer (IKA, Staufen, Germany); an Eppendorf model 5910 R centrifuge (Eppendorf, Hamburg, Germany); an Intensity Solo 2 C18 90 Å HPLC column, 8 µm, 2.1 × 100 mm (Bruker, Bremen, Germany); an Acquity UPLC BEH C18 130 Å HPLC column, 1.7 µm (Waters, Milford, MA, USA); and a Synergi™ Polar-RP 100 Å HPLC column, 5 µm, 2.1 × 50 mm (Phenomenex, Torrance, CA, USA). After extraction, pharmaceuticals were analyzed on with Elute UHPLC system and a triple quadrupole EVOQ LC-TQ mass spectrometer, both from Bruker (Bremen, Germany). The whole system was controlled with tqControl version 2.0.0 from Bruker (Bremen, Germany), and HPLC without MS was controlled with EDM version 1.2 (1.2.34.0) from Bruker (Bremen, Germany).

3.4. Swine Manure Samples Extraction

Samples were lyophilized and stored in a freezer before drug extraction. Two grams of lyophilized swine manure was accurately weighed into a 50 mL falcon tube. Each batch of samples (n = 20) was simultaneously extracted with 8 matrix-matched control samples; these lyophilized samples were spiked with pharmaceuticals in doses of 0, 100, 200, 400, 600, 800, 1000 and 1500 µg/kg. Then, 10 mL of an extraction solvent (MeOH:McIlvaine–EDTA; 70:30, v/v) was added to each tube, and samples were vortexed for 10 s, shaken in a rotatory shaker for 30 min at room temperature, and centrifuged at 4500 rpm for 15 min at 8 °C. The final extracts were filtered through a syringe filter (Acrodisc Waters, MA, USA) and transferred to an HPLC amber vial.

Before enacting the final extraction protocol, which yielded the best recoveries and signal responses for most compounds, various conditions related to the extraction method were investigated. The tested conditions included the extraction efficiency of ACN, MeOH, and water at different percentages and in different combinations. QuEChERS extraction with the use of a mixture of water and an organic solvent (ACN or MeOH) combined with NaCl and MgSO4 was also tested. Other investigated parameters were: (I) sample weight, (II) extraction solvent volume, (III) rotation time, (IV) centrifugation time and temperature, and (V) the evaporation of different sample extracts for concentration. The different conditions were tested on three replicated lyophilized samples spiked with pharmaceuticals at a dose of 600 µg/kg and on a blank sample (analyte-free). Results were evaluated with a standard calibration curve of a mixture of pharmaceuticals at 0, 10, 25, 50, 100 and 250 ng/mL.

3.5. LC–MS/MS Conditions

The mobile phase were mixed in a gradient mode of mobile phases A and B. The flow rate was set to 0.300 mL/min with the following gradient program: 0.0–1.0 min for 100% solvent A, 1.0–6.0 min for 10% solvent A, 6.0–6.5 min for 0% solvent A, 6.5–7.5 min for 0% solvent A, 7.5–9.0 min for 100% solvent A, and 9.0–15.0 min for 100% solvent A. The temperature of the column was maintained at 42 °C during the whole run, the sample injection volume was 15 µL, and the samples were maintained at 8 °C during the sequence analysis. For the detection of most compounds with MS analysis, the positive electrospray (ESI+) mode was employed (Table 3), except for the cases of chloramphenicol and florfenicol, where the negative ESI mode was used. Drugs were determined with two multiple reaction monitoring (MRM) runs and their Rt values. In the positive and negative modes, the electrospray voltage was 4800 V and 4500 V, respectively. During analysis, the cone temperature (300 °C), cone flow (20 psi), probe temperature (500 °C), nebulizer flow (30 psi), and exhaust gas flow (50 psi) were maintained at constant values.

Table 3.

Retention time (Rt) and multiple reaction monitoring (MRM) runs 1 and 2 employed for pharmaceutical identification.

Compound Rt (min) RSD of Rt (%) MRM 1 MRM 2
Chloramphenicol 4.82 0.5 (−) 323.0 > 152.0 [14.0 V] (−) 323.0 > 194.1 [9.0 V]
Chlortetracycline 4.43 0.2 (+) 479.0 > 462.0 [15.0 V] (+) 479.0 > 444.0 [22.0 V]
Ciprofloxacin 4.00 0.4 (+) 332.2 > 314.1 [16.0 V] (+) 332.2 > 231.0 [32.0 V]
Clarithromycin 5.17 0.3 (+) 749.0 > 158.0 [25.0 V] (+) 749.0 > 116.0 [50.0 V]
Danafloxacin 4.07 0.3 (+) 358.0 > 340.0 [25.0 V] (+) 358.0 > 255.0 [35.0 V]
Dexamethasone 5.34 0.2 (+) 393.0 > 373.0 [7.0 V] (+) 393.0 > 354.6 [10.0 V]
Diclofenac 6.29 0.2 (+) 296.0 > 215.0 [15.0 V] (+) 296.0 > 151.0 [60.0 V]
Difloxacin 4.23 0.2 (+) 386.0 > 299.0 [25.0 V] (+) 386.0 > 299.0 [25.0 V]
Doxycycline 4.52 1.7 (+) 445.0 > 428.0 [15.0 V] (+) 445.0 > 154.0 [30.0 V]
Enrofloxacin 4.11 3.9 (+) 360.0 > 342.1 [17.0 V] (+) 360.0 > 286.0 [31.0 V]
Florfenicol 4.66 1.1 (−) 358.0 > 185.0 [15.0 V] (−) 358.0 > 338.0 [5.0 V]
Levofloxacin 3.98 1.1 (+) 362.0 > 261.0 [30.0 V] (+) 362.0 > 179.0 [40.0 V]
Lincomycin 3.73 0.6 (+) 407.3 > 126.2 [22.0 V] (+) 407.3 > 359.2 [12.0 V]
Mefenamic Acid 6.61 0.2 (+) 242.0 > 223.8 [15.0 V] (+) 242.0 > 209.0 [27.0 V]
Norfloxacin 3.96 0.3 (+) 320.0 > 302.0 [15.0 V] (+) 320.0 > 276.0 [15.0 V]
Oxytetracycline 3.96 0.4 (+) 461.0 > 426.0 [20.0 V] (+) 461.0 > 443.0 [10.0 V]
Paracetamol 3.58 2.9 (+) 152.3 > 110.0 [23.0 V] (+) 152.3 > 92.7 [23.0 V]
Propranolol 4.67 1.4 (+) 260.0 > 116.0 [20.0 V] (+) 260.0 > 154.5 [20.0 V]
Sarafloxacin 4.27 0.2 (+) 400.0 > 299.0 [30.0 V] (+) 400.0 > 382.0 [30.0 V]
Sulfachloropyridine 4.52 0.2 (+) 285.0 > 156.0 [11.0 V] (+) 285.0 > 108.0 [18.0 V]
Sulfadiazine 3.74 1.6 (+) 251.1 > 156.0 [12.0 V] (+) 251.1 > 108.0 [19.0 V]
Sulfadimethoxine 4.97 0.2 (+) 311.0 > 156.0 [20.0 V] (+) 311.0 > 108.0 [18.0 V]
Sulfamerazine 4.05 1.3 (+) 265.0 > 156.0 [16.0 V] (+) 265.0 > 172.0 [16.0 V]
Sulfamethazine 4.25 0.6 (+) 279.0 > 186.0 [15.0 V] (+) 279.0 > 156.0 [15.0 V]
Sulfamethoxazole 4.64 0.2 (+) 254.0 > 156.0 [11.0 V] (+) 254.0 > 92.0 [18.0 V]
Sulfamethoxypyridazine 4.27 0.2 (+) 281.0 > 156.0 [13.0 V] (+) 281.0 > 92.0 [24.0 V]
Sulfapyridine 3.93 4.1 (+) 250.0 > 156.0 [13.0 V] (+) 250.0 > 92.0 [23.0 V]
Sulfaquinoxaline 4.98 0.2 (+) 301.0 > 156.0 [15.0 V] (+) 301.0 > 92.0 [25.0 V]
Sulfathiazole 3.86 3.1 (+) 256.0 > 156.0 [12.0 V] (+) 256.0 > 92.0 [22.0 V]
Tetracycline 4.08 5.9 (+) 445.4 > 410.0 [20.0 V] (+) 445.4 > 427.0 [15.0 V]
Trimethoprim 3.88 0.4 (+) 291.0 > 123.0 [20.0 V] (+) 291.0 > 230.0 [24.0 V]

3.6. Validation

Validation was conducted following different guidelines, particularly Regulation 2021/808 and Regulation 2002/657. Evaluated aspects of the method included signal/noise ratio (S/N), the RSD of the Rt, linearity, matrix effects, recovery, precision under repeatability (RSDr), and reproducibility (RSDR). To validate this method, analyte-free lyophilized swine manure samples were spiked with the selected drugs at doses of 0, 100, 200, 400, 600, 800, 1000 and 1500 µg/kg. For each concentration, six replicates were employed, and the experiment was repeated on three different days. The validation parameters of accuracy, matrix effect, precision, sensitivity, and linear dynamic range were determined for the 31 target analytes.

3.7. Swine Manure Collection

Swine manure samples were collected by the veterinarian involved in the project. Once collected, the samples were kept in a sterilized container, stored in a portable fridge, and sent to the laboratory for analysis. Once in the laboratory, samples were subject to lyophilization and stored at −20 °C until analysis, which was conducted within three months after collection. The sample collection and method were conducted as part of a project entitled “Reducción de la adición de antibióticos en la dieta de animales de porcino en ciclo industrial”, in which the main objective was to design a production system based on feeding and management in order to promote good animal health in the last 3 months of animals’ lives (fattening phase) by applying different strategies related to the systems of animal production, with the final objective of not administrating antimicrobials in the final stage of animal production.

4. Conclusions

The present article describes the validation and application of an HPLC–MS/MS method for the identification and quantification of 29 drugs in swine manure. The method was satisfactorily employed for the control of the administration of antimicrobials to pigs in the three last months of food production. A total of 40 samples were analyzed, and only four samples showed the presence of antimicrobials in the group of tetracyclines. The results indicated that the presented method could be satisfactorily applied during swine production without harming or stressing the animals, and antimicrobials detected in samples when the animals are treated with antibiotics. Additionally, the method is quick and inexpensive, as a low amount of organic solvents is used and the amount of generated residues is low compared with other reported methods employing SPE.

Acknowledgments

The authors would like to thank Rosa E. Gavilán and Gabriel Míguez-Suárez for their help and contribution in the development of this research. The authors are grateful to COPORC, pig farmers, and veterinarians for their support because without them this work would not have been possible.

Author Contributions

C.N. and E.P., methodology; I.G.-P., sample collection; A.C.-C. and A.C., writing—review and editing; C.M.F., project administration and funding acquisition. All anthers contributed to manuscript development. All authors have read and agreed to the published version of the manuscript.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Conflicts of Interest

The authors declare that there is no conflict of interest regarding the publication of this article.

Sample Availability

Samples of the compounds are not available from the authors.

Funding Statement

This research received financial support through the research project entitled “Reducción de la adición de antibióticos en la dieta de animales de porcino en ciclo industrial” financed by FEADER (The European Agricultural Fund for Rural Development) within the framework of the operating groups of the European Association for Innovation and with the reference number FEADER 2018/001.

Footnotes

Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

References

  • 1.Radostits O.M., Gay C., Hinchcliff K.W., Constable P.D., editors. Veterinary Medicine E-Book: A Textbook of the Diseases of Cattle, Horses, Sheep, Pigs and Goats. Elsevier Health Sciences; Amsterdam, The Netherlands: 2006. [Google Scholar]
  • 2.Coyne L.A., Latham S.M., Williams N.J., Dawson S., Donald I.J., Pearson R.B., Smith R.F., Pinchbeck G.L. Understanding the culture of antimicrobial prescribing in agriculture: A qualitative study of UK pig veterinary surgeons. J. Antimicrob. Chemother. 2016;71:3300–3312. doi: 10.1093/jac/dkw300. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 3.Qui J., Zhao T., Liu Q., He J., Él D., Wu G., Li Y., Jiang C., Xu Z. Residual veterinary antibiotics in pig excreta after oral admin-istration of sulfonamides. Environ. Geochem. Health. 2016;38:549–556. doi: 10.1007/s10653-015-9740-x. [DOI] [PubMed] [Google Scholar]
  • 4.Nouws J.F.M., Vree T.B., Degen M., Mevius D. Pharmacokinetics of a sulphamethoxazole/trimethoprim formulation in pigs after intravenous administration. Vet. Q. 1991;13:148–154. doi: 10.1080/01652176.1991.9694300. [DOI] [PubMed] [Google Scholar]
  • 5.Díaz-Cruz M.S., Barceló D. Trace organic chemicals contamination in ground water recharge. Chemosphere. 2008;72:333–342. doi: 10.1016/j.chemosphere.2008.02.031. [DOI] [PubMed] [Google Scholar]
  • 6.Baquero F., Martinez J.L., Cantón R. Antibiotics and antibiotic resistance in water environments. Curr. Opin. Biotechnol. 2008;19:260–265. doi: 10.1016/j.copbio.2008.05.006. [DOI] [PubMed] [Google Scholar]
  • 7.Watkinson A.J., Murby E.J., Kolpin D.W., Costanzo S.D. The occurrence of antibiotics in an urban watershed: From wastewater to drinking water. Sci. Total. Environ. 2009;407:2711–2723. doi: 10.1016/j.scitotenv.2008.11.059. [DOI] [PubMed] [Google Scholar]
  • 8.Rodil R., Quintana J.B., Concha-Graña E., López-Mahía P., Muniategui S., Prada-Rodríguez D. Emerging pollutants in sewage, surface and drinking water in Galicia (NW Spain) Chemosphere. 2012;86:1040–1049. doi: 10.1016/j.chemosphere.2011.11.053. [DOI] [PubMed] [Google Scholar]
  • 9.Guo X.Y., Hao L.J., Qiu P.Z., Chen R., Xu J., Kong X.J., Shan Z.J., Wang N. Pollution characteristics of 23 veterinary antibiotics in livestock manure and manure-amended soils in Jiangsu province, China. J. Environ. Sci. Health Part B. 2016;51:383–392. doi: 10.1080/03601234.2016.1142743. [DOI] [PubMed] [Google Scholar]
  • 10.Berendsen B.J., Wegh R.S., Memelink J., Zuidema T., Stolker L.A. The analysis of animal faeces as a tool to monitor antibiotic usage. Talanta. 2015;132:258–268. doi: 10.1016/j.talanta.2014.09.022. [DOI] [PubMed] [Google Scholar]
  • 11.Janusch F., Scherz G., Mohring S.A., Hamscher G. Determination of fluoroquinolones in chicken faeces–A new liquid–liquid extraction method combined with LC–MS/MS. Environ. Toxicol. Pharmacol. 2014;38:792–799. doi: 10.1016/j.etap.2014.09.011. [DOI] [PubMed] [Google Scholar]
  • 12.Zhao L., Dong Y.H., Wang H. Residues of veterinary antibiotics in manures from feedlot livestock in eight provinces of China. Sci. Total. Environ. 2010;408:1069–1075. doi: 10.1016/j.scitotenv.2009.11.014. [DOI] [PubMed] [Google Scholar]
  • 13.Martínez-Carballo E., González-Barreiro C., Scharf S., Gans O. Environmental monitoring study of selected veterinary antibiotics in animal manure and soils in Austria. Environ. Pollut. 2007;148:570–579. doi: 10.1016/j.envpol.2006.11.035. [DOI] [PubMed] [Google Scholar]
  • 14.Karcı A., Balcıoğlu I.A. Investigation of the tetracycline, sulfonamide, and fluoroquinolone antimicrobial com-pounds in animal manure and agricultural soils in Turkey. Sci. Total Environ. 2009;407:4652–4664. doi: 10.1016/j.scitotenv.2009.04.047. [DOI] [PubMed] [Google Scholar]
  • 15.Zhou X., Chen C., Yue L., Sun Y., Ding H., Liu Y. Excretion of enrofloxacin in pigs and its effect on ecological environment. Environ. Toxicol. Pharmacol. 2008;26:272–277. doi: 10.1016/j.etap.2008.04.004. [DOI] [PubMed] [Google Scholar]
  • 16.Turiel E., Martín-Esteban A., Tadeo J.L. Multiresidue analysis of quinolones and fluoroquinolones in soil by ultrasonic-assisted extraction in small columns and HPLC-UV. Anal. Chim. Acta. 2006;562:30–35. doi: 10.1016/j.aca.2006.01.054. [DOI] [Google Scholar]
  • 17.Christian T., Schneider R.J., Färber H.A., Skutlarek D., Meyer M.T., Goldbach H.E. Determination of Antibiotic Residues in Manure, Soil, and Surface Waters. Acta Hydrochim. Hydrobiol. 2003;31:36–44. doi: 10.1002/aheh.200390014. [DOI] [Google Scholar]
  • 18.Morales-Muñoz S., Luque-García J.L., de Castro M.L. Continuous microwave-assisted extraction coupled with derivatization and fluorimetric monitoring for the determination of fluoroquinolone antibacterial agents from soil samples. J. Chromatogr. A. 2004;1059:25–31. doi: 10.1016/j.chroma.2004.09.086. [DOI] [PubMed] [Google Scholar]
  • 19.Sunderland J., Lovering A.M., Tobin C.M., MacGowan A.P., Roe J.M., Delsol A.A. A reverse-phase HPLC assay for the simultaneous determination of enrofloxacin and ciprofloxacin in pig faeces. Int. J. Antimicrob. Agents. 2004;23:390–393. doi: 10.1016/j.ijantimicag.2003.07.014. [DOI] [PubMed] [Google Scholar]
  • 20.Bin Ho Y., Zakaria M.P., Latif P.A., Saari N. Occurrence of veterinary antibiotics and progesterone in broiler manure and agricultural soil in Malaysia. Sci. Total Environ. 2014;488–489:261–267. doi: 10.1016/j.scitotenv.2014.04.109. [DOI] [PubMed] [Google Scholar]
  • 21.Rossi R., Saluti G., Moretti S., Diamanti I., Giusepponi D., Galarini R. Multiclass methods for the analysis of antibiotic residues in milk by liquid chromatography coupled to mass spectrometry: A review. Food Addit. Contam. Part A. 2018;35:241–257. doi: 10.1080/19440049.2017.1393107. [DOI] [PubMed] [Google Scholar]
  • 22.Moyo B., Tavengwa N.T. Critical review of solid phase extraction for multiresidue clean-up and pre-concentration of antibiotics from livestock and poultry manure. Food Addit. Contam. Part A. 2021;39:229–241. doi: 10.1080/19440049.2021.1989497. [DOI] [PubMed] [Google Scholar]
  • 23.Moretti S., Giorgio S., Roberta G. Residue determination in honey. Honey Anal. 2017;1:325–365. [Google Scholar]
  • 24.Jansen L.J., van de Schans M.G., de Boer D., Bongers I.E., Schmitt H., Hoeksma P., Berendsen B.J. A new extraction procedure to abate the burden of non-extractable antibiotic residues in manure. Chemosphere. 2019;224:544–553. doi: 10.1016/j.chemosphere.2019.02.166. [DOI] [PubMed] [Google Scholar]
  • 25.Shelver W.L., Chakrabarty S., Young J.M., Byrd C.J., Smith D.J. Evaluation of rapid and standard tandem mass spectrometric methods to analyse veterinary drugs and their metabolites in antemortem bodily fluids from food animals. Food Addit. Contam. Part A. 2022;39:462–474. doi: 10.1080/19440049.2021.2006801. [DOI] [PubMed] [Google Scholar]
  • 26.Popova I.E., Bair D.A., Tate K.W., Parikh S.J. Sorption, Leaching, and Surface Runoff of Beef Cattle Veterinary Pharmaceuticals under Simulated Irrigated Pasture Conditions. J. Environ. Qual. 2013;42:1167–1175. doi: 10.2134/jeq2013.01.0012. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 27.Schlüsener M.P., Bester K., Spiteller M. Determination of antibiotics such as macrolides, ionophores and tiamulin in liquid manure by HPLC–MS/MS. Anal. Bioanal. Chem. 2003;375:942–947. doi: 10.1007/s00216-003-1838-9. [DOI] [PubMed] [Google Scholar]
  • 28.Commission Implementing Regulation (EU) 2021/808 of 22 March 2021 on the performance of analytical methods for residues of pharmacologically active substances used in food-producing animals and on the interpretation of results as well as on the methods to be used for sampling and repealing Decisions 2002/657/EC and 98/179/EC. Off. J. Eur. Union. 2021;180:84–109. [Google Scholar]
  • 29.Nebot C., Iglesias A., Regal P., Miranda J.M., Fente C., Cepeda A. A sensitive and validated HPLC–MS/MS method for simultaneous determination of seven coccidiostats in bovine whole milk. Food Control. 2012;27:29–36. doi: 10.1016/j.foodcont.2012.02.012. [DOI] [Google Scholar]
  • 30.Gavilán R.E., Nebot C., Patyra E., Miranda J.M., Franco C.M., Cepeda A. Simultaneous analysis of coccidiostats and sulphonamides in non-target feed by HPLC-MS/MS and validation following the Commission Decision 2002/657/EC. Food Addit. Contam. Part A. 2018;35:1093–1106. doi: 10.1080/19440049.2018.1466061. [DOI] [PubMed] [Google Scholar]
  • 31.Patyra E., Nebot C., Gavilán R.E., Cepeda A., Kwiatek K. Development and validation of multi-residue and multi-class method for antibacterial substances analysis in non-target feed by liquid chromatography—Tandem mass spectrometry. Food Addit. Contam. Part A. 2018;35:467–478. doi: 10.1080/19440049.2017.1414961. [DOI] [PubMed] [Google Scholar]
  • 32.Zhang X., Li R., Zhang P., Wu X., Hua H., Yang L., Lu J., Rong Y. Rapid determination of 25 drug residues in aquatic products by ultra performance liquid chroma-tography-quadrupole/electrostatic field orbitrap high resolution mass spectrometry. Se Pu Chin. J. Chromatogr. 2018;36:114–124. doi: 10.3724/SP.J.1123.2017.10010. [DOI] [PubMed] [Google Scholar]
  • 33.Gómez-Canela C., Pueyo V., Barata C., Lacorte S., Marcé-Recasens R.M. Development of predicted environmental concentrations to prioritize the occurrence of pharmaceuticals in rivers from Catalonia. Sci. Total Environ. 2019;666:57–67. doi: 10.1016/j.scitotenv.2019.02.078. [DOI] [PubMed] [Google Scholar]
  • 34.Haller M.Y., Müller S.R., McArdell C.S., Alder A.C., Suter M.J.-F. Quantification of veterinary antibiotics (sulfonamides and trimethoprim) in animal manure by liquid chromatography–mass spectrometry. J. Chromatogr. A. 2002;952:111–120. doi: 10.1016/S0021-9673(02)00083-3. [DOI] [PubMed] [Google Scholar]
  • 35.Van den Meersche T., Van Pamel E., Van Poucke C., Herman L., Heyndrickx M., Rasschaert G., Daeseleire E. Development, validation and application of an ultra high performance liquid chromato-graphic-tandem mass spectrometric method for the simultaneous detection and quantification of five different classes of vet-erinary antibiotics in swine manure. J. Chromatogr. A. 2016;1429:248–257. doi: 10.1016/j.chroma.2015.12.046. [DOI] [PubMed] [Google Scholar]
  • 36.Olsen J., Björklund E., Krogh K.A., Hansen M. Development of an analytical methodology for the determination of the antiparasitic drug toltrazuril and its two metabolites in surface water, soil and animal manure. Anal. Chim. Acta. 2012;755:69–76. doi: 10.1016/j.aca.2012.10.015. [DOI] [PubMed] [Google Scholar]
  • 37.Hansen M., Krogh K.A., Halling-Sørensen B., Björklund E. Determination of ten steroid hormones in animal waste manure and agricultural soil using inverse and integrated clean-up pressurized liquid extraction and gas chromatography-tandem mass spectrometry. Anal. Methods. 2011;3:1087–1095. doi: 10.1039/c1ay00007a. [DOI] [Google Scholar]
  • 38.Wang J., Xu J., Ji X., Wu H., Yang H., Zhang H., Zhang X., Li Z., Ni X., Qian M. Determination of veterinary drug/pesticide residues in livestock and poultry excrement using selective accelerated solvent extraction and magnetic material purification combined with ultra-high-performance liquid chromatog-raphy–tandem mass spectrometry. J. Chromatogr. A. 2020;1617:460808. doi: 10.1016/j.chroma.2019.460808. [DOI] [PubMed] [Google Scholar]
  • 39.Argüeso-Mata M., Bolado S., Jiménez J.J., López-Serna R. Determination of antibiotics and other veterinary drugs in the solid phase of pig manure. Chemosphere. 2021;275:130039. doi: 10.1016/j.chemosphere.2021.130039. [DOI] [PubMed] [Google Scholar]
  • 40.Guo C., Wang M., Xiao H., Huai B., Wang F., Pan G., Liao X., Liu Y. Development of a modified QuEChERS method for the determination of veterinary antibiotics in swine manure by liquid chromatography tandem mass spectrometry. J. Chromatogr. B. 2016;1027:110–118. doi: 10.1016/j.jchromb.2016.05.034. [DOI] [PubMed] [Google Scholar]
  • 41.Zhi S., Zhou J., Liu H., Wu H., Zhang Z., Ding Y., Zhang K. Simultaneous extraction and determination of 45 veterinary antibiotics in swine manure by liquid chroma-tography-tandem mass spectrometry. J. Chromatogr. B. 2020;1154:122286. doi: 10.1016/j.jchromb.2020.122286. [DOI] [PubMed] [Google Scholar]
  • 42.Nebot C., Guarddon M., Seco F., Iglesias A., Miranda J.M., Franco C.M., Cepeda A. Monitoring the presence of residues of tetracyclines in baby food samples by HPLC-MS/MS. Food Control. 2014;46:495–501. doi: 10.1016/j.foodcont.2014.05.042. [DOI] [Google Scholar]
  • 43.Boscher A., Guignard C., Pellet T., Hoffmann L., Bohn T. Development of a multi-class method for the quantifi-cation of veterinary drug residues in feedingstuffs by liquid chromatography-tandem mass spectrometry. J. Chroma-Tography A. 2010;1217:6394–6404. doi: 10.1016/j.chroma.2010.08.024. [DOI] [PubMed] [Google Scholar]
  • 44.Łukaszewicz P., Białk-Bielińska A., Dołżonek J., Kumirska J., Caban M., Stepnowski P. A new approach for the extraction of tetracyclines from soil matrices: Application of the microwave-extraction technique. Anal. Bioanal. Chem. 2018;410:1697–1707. doi: 10.1007/s00216-017-0815-7. [DOI] [PubMed] [Google Scholar]
  • 45.Melekhin A.O., Tolmacheva V.V., Shubina E.G., Dmitrienko S.G., Apyari V.V., Grudev A.I. Using Hyper-crosslinked Polystyrene for the Multicomponent Solid-Phase Extraction of Residues of 63 Veterinary Preparations in Their Determination in Chicken Meat by High-Performance Liquid Chromatography–Tandem Mass Spectrometry. J. Anal. Chem. 2021;76:946–959. doi: 10.1134/S1061934821060046. [DOI] [Google Scholar]
  • 46.Sengeløv G., Agersø Y., Halling-Sørensen B., Baloda S.B., Andersen J.S., Jensen L.B. Bacterial antibiotic resistance levels in Danish farmland as a result of treatment with pig manure slurry. Environ. Int. 2003;28:587–595. doi: 10.1016/S0160-4120(02)00084-3. [DOI] [PubMed] [Google Scholar]
  • 47.Hölzel C.S., Müller C., Harms K.S., Mikolajewski S., Schäfer S., Schwaiger K., Bauer J. Heavy metals in liquid pig manure in light of bacterial antimicrobial resistance. Environ. Res. 2012;113:21–27. doi: 10.1016/j.envres.2012.01.002. [DOI] [PubMed] [Google Scholar]
  • 48.Joy S.R., Bartelt-Hunt S.L., Snow D.D., Gilley J.E., Woodbury B.L., Parker D.B., Marx D.B., Li X. Fate and Transport of Antimicrobials and Antimicrobial Resistance Genes in Soil and Runoff Following Land Application of Swine Manure Slurry. Environ. Sci. Technol. 2013;47:12081–12088. doi: 10.1021/es4026358. [DOI] [PubMed] [Google Scholar]
  • 49.Pu C., Liu H., Ding G., Sun Y., Yu X., Chen J., Ren J., Gong X. Impact of direct application of biogas slurry and residue in fields: In situ analysis of antibiotic resistance genes from pig manure to fields. J. Hazard. Mater. 2018;344:441–449. doi: 10.1016/j.jhazmat.2017.10.031. [DOI] [PubMed] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Data Availability Statement

Not applicable.


Articles from Molecules are provided here courtesy of Multidisciplinary Digital Publishing Institute (MDPI)

RESOURCES