Simultaneous Determination of 61 Veterinary Drug Residues in Animal Derived Food by Clean-Up LPAS Combined with LC-MS/MS

Abstract

A rapid analytical method was established for the simultaneous determination of 61 veterinary drug residues, covering 13 different drug categories, in five animal-derived food matrices (pork, pork liver, chicken, egg, and beef). The method integrated Low-Pressure Automated Solid-phase extraction (LPAS) as a clean-up procedure with liquid chromatography-tandem mass spectrometry (LC-MS/MS) for detection. The samples were extracted using 8 mL of acetonitrile:water (90:10, containing 0.2% formic acid), followed by purification with LPAS, and were directly analyzed using LC-MS/MS without an evaporation step. The experimental conditions, including LC-MS/MS parameters, extraction solvents and volumes, as well as the clean-up procedure for all 61 veterinary drugs, were systematically optimized. Method validation parameters, such as accuracy, precision, limits of detection (LOD), limits of quantitation (LOQ), linearity, and matrix effects, were thoroughly evaluated to ensure the reliability and robustness of the developed method. The results demonstrated good linearity for all analytes in the concentration range of 0.5 μg/L - 50 μg/L, with correlation coefficients (R2) ≥ 0.995. Recoveries at three spiked levels (5 μg/kg, 10 μg/kg and 50 μg/kg) in the 5 tested matrices ranged between 70.9% and 119.0%, with relative standard deviations (RSD) of 0.1% - 10.9%. The method showed low detection and quantitation limits, with LODs ranging from 0.03 μg/kg to 1.5 μg/kg and LOQs from 0.1 μg/kg to 5.0 μg/kg. When applied to analyze 731 real samples, 13 drug categories were detected in a total of 64 instances, among which 12 categories of restricted drugs were identified 57 times, and two types of prohibited drugs were found seven times; no other veterinary drugs were detected. These findings suggest that thesimplified LPAS clean-up procedure is superior to the conventional QuEChERS (Quick, Easy, Cheap, Effective, Rugged, and Safe) method, making it highly suitable for batch analysis and monitoring of multiple veterinary drug residues in animal-derived foods.

Share and Cite:

Zeng, Y. , Yang, Q. , Li, X. , Zheng, Y. , Zhang, Y. , Chen, J. and Zhou, X. (2025) Simultaneous Determination of 61 Veterinary Drug Residues in Animal Derived Food by Clean-Up LPAS Combined with LC-MS/MS. American Journal of Analytical Chemistry, 16, 43-67. doi: 10.4236/ajac.2025.164004.

1. Introduction

Veterinary drugs, which are essential for preventing and treating animal diseases, are used not only to prevent, treat, and diagnose diseases but also to regulate physiological functions in animals, including antibiotics, antiparasitic drugs, antifungal drugs, bronchodilators and more [1]-[3]. Owing to the perceived benefits of veterinary drugs, some breeders employ them irrationally, driven by the desire to enhance economic returns or due to insufficient awareness of the potential hazards associated with these drugs [4] [5]. However, these veterinary drugs remain in animals and enter the human body through the food chain and further exacerbates risks to human health [6]-[8]. The harm of veterinary drug residues to human health is multifaceted. Residues of antibiotic veterinary drugs may induce drug resistance in humans, thereby diminishing the efficacy of antibiotics in treating infections, which can lead to therapeutic failures and increased medical costs [9]. Additionally, certain veterinary drug residues may also trigger allergic reactions, causing symptoms such as rashes, itching, and breathing difficulties, and endangering life in severe cases. Long-term consumption of animal-derived foods containing veterinary drug residues may also have adverse effects on the human immune system, nervous system, and endocrine system, increasing the risk of chronic diseases such as cancer and cardiovascular diseases [10] [11]. Moreover, veterinary drug residues can also pollute the ecological environment, affect the quality of soil, water, and air, and disrupt the ecological balance [12]. Therefore, China, EU, USA, and others have set the maximum residue limits (MRL) [13]-[15] of veterinary drugs in animal derived food and they initiate legal procedures in any excessive cases; to meet the monitoring objectives and regulatory requirements, it is of great necessity to provide accurate test results and develop effective and reliable veterinary drug residue testing methods.

Veterinary drugs are mainly composed of involatile polar or low-polar compounds. Gas chromatography (GC) or gas chromatography-tandem mass spectrometry (GC-MS/MS) is not suitable for testing such components [2]. The liquid chromatography (LC) also has limitations in detecting veterinary drugs and their metabolites, as well as in classifying certain veterinary drugs, due to its relatively low sensitivity and selectivity. In recent years, the methods have been largely superseded by chromatography-tandem mass spectrometry techniques, which offer enhanced selectivity and improved detection efficiency [16]-[18]. The advancements in test equipment have significantly increased the capacity for simultaneous detection of veterinary drugs. For instance, the method established by Zhao et al. [19] enabled the analysis of 80 veterinary drugs. Similarly, Yin et al. [20] established a method for the detection of 210 veterinary drugs in pork, while Alcantara-Duran et al. [6] reported a method for the analysis of 77 veterinary drugs in chicken. However, these methods are mostly based on analysis on one and the same matrix in the pretreatment method of QuEChERS, and have limitations in analyzing multiple matrices. Li et al. developed a screening method for 204 veterinary drugs [21], while Desmarchelier et al. established a qualitative LC-MS/MS method for the detection of 154 veterinary drugs [22]. Although these methods enable the detection of multiple matrices, they are incapable of performing quantitative analysis. This limitation is particularly significant given that veterinary drug residues in food typically exist at concentrations in the low microgram or even nanogram range [16], which presents a major challenge for residue testing in animal-derived food products.

The matrices of livestock and poultry products are complex due to the presence of substantial amounts of lipids, proteins, and other macromolecular substances [23]-[25], resulting in false positives or false negatives test results. Consequently, sample preparation is still a challenging process for testing drug residues in animal derived foods. In this study, the sample pretreatment methods were improved and the instrumental analysis conditions were optimized to address the deficiencies of existing technologies. As a result, an efficient, accurate, and sensitive method for detecting veterinary drug residues in animal-derived foods was established. By enabling the simultaneous detection of multiple veterinary drug residues, the developed method enhances detection efficiency and reduces analytical costs, providing strong technical support for the quality and safety supervision of animal-derived foods. Clean-up LPAS columns made of novel high-polymer materials were used to rapidly filter and decontaminate multiple animal derived food. In conjunction with LC-MS/MS, a high-throughput test method was established that enables the simultaneous, rapid, accurate, and efficient detection of 61 veterinary drugs across 13 categories, including 21 sulfonamides, 10 quinolones, 9 β-receptor agonists, 4 tetracyclines, 4 amphenicols, 3 macrolides, 2 sedatives, 2 lincosamide antibiotics, 2 penicillin and 1 each of nitroimidazole, polyether anticoccidials, corticosteroid and antiviral agents. The method was verified with satisfactory results obtained and successfully applied in testing 731 real samples to investigate the safety conditions of veterinary drug residues in livestock and poultry products.

2. Experiments

2.1. Drugs and Reagents

1290-6470 LC-MS (Agilent, USA), TGL-16 High-speed Refrigerated Centrifuge (Sichuan Shuke Instrument Co., Ltd., China), KNS-2500 Multi-Tube Vortex Mixer (Krownus Scientific Experimental Instrument Co., Ltd., China), KH-500B Ultrasonic Cleaner (Kunshan Hechao Ultrasonic Instruments Co., Ltd., China), UPT-II-100L ULUPURE-series Ultrapure Water Machine (ULUPURE, China), Milli-Q Ultrapure Water Machine (Millipore, USA).

Carbinol (chromatographically pure, Fisher Chemical), acetonitrile (chromatographically pure, Fisher Chemical), formic acid (chromatographically pure, Fisher Chemical), ammonium acetate (chromatographically pure, Tianjin Kemiou Chemical Reagent Co., Ltd.), ammonium formate (GR (guarantee reagent)), clean-up column-LPAS (Beijing Knorth Technology Co., Ltd., China), and pure water used in this experiment were produced by the ultrapure water machines in the laboratory. All standard substances are standard solid substances with a purity of over 95% and were purchased from Dr. Ehrenstorfer GmbH. The names, CAS No. and groups of all standard substances are given in Table 1.

Table 1. Name of each target compound and the MS/MS acquisition conditions.

NO.

veterinary drug (Types)

CAS number

Quantitative ion (M/z) &Collision

Energy (V)

Qualitative ion (M/z) & Collision

Energy (V)

Fragment (V)

Retention time (min)

Polarity

1

Florfenicol amine (Am)

76639-93-5

248.1/230 (5)

248.1/130 (21)

100

0.650

Positive

2

Amoxicillin (Pe)

26787-78-0

366/349 (4)

366/114 (20)

90

1.400

Positive

3

Sulfaguanidine (Su)

57-67-0

215/156 (10)

215/108 (20)

100

1.424

Positive

4

Sulfacetamid (Su)

144-80-9

215.1/156.1 (5)

215.1/92 (20)

70

1.430

Positive

5

Benzonitrile (β-R)

54239-37-1

220.1/202.1 (5)

220.1/160.1 (13)

100

1.540

Positive

6

Terbutalinee (β-R)

23031-25-6

226.1/152.1 (12)

226.1/125 (24)

92

1.910

Positive

7

Salbutamole (β-R)

18559-94-9

240/148 (15)

240/222.1 (5)

80

2.060

Positive

8

Metronidazole (N)

443-48-1

172.1/128 (12)

172.1/82 (26)

90

2.061

Positive

9

Sulfadiazine (Su)

68-35-9

251/156 (20)

251/108 (25)

100

2.139

Positive

10

Sulfathiazole (Su)

72-14-0

256/156 (20)

256/108 (25)

100

2.966

Positive

11

Sulfapyridine (Su)

144-83-2

250.1/156 (10)

250.1/184 (15)

110

3.470

Positive

12

Sulfamerazine (Su)

127-79-7

265/156 (20)

265/172 (20)

100

4.090

Positive

13

Fenoterole (β-R)

13392-18-2

304.1/135.2 (15)

304.1/286.2 (8)

120

4.570

Positive

14

Sulfameter (Su)

651-06-9

281/156 (15)

281/108 (25)

130

4.885

Positive

15

Lincomycin (L)

154-21-2

407.2/126 (30)

407.2/359 (15)

150

4.928

Positive

16

Sulfamoxole (Su)

729-99-7

268/156 (13)

268/113 (16)

110

4.990

Positive

17

Sulfamethizole (Su)

144-82-1

271/156 (20)

271/108 (26)

100

5.030

Positive

18

Sulfamethazine (Su)

57-68-1

279.1/186.1 (15)

279.1/156.1 (16)

120

5.120

Positive

19

Trimethoprim (Pe)

738-70-5

291.1/230.1 (25)

291.1/123 (25)

120

5.137

Positive

20

Sulfamethoxypyridazine (Su)

80-35-3

281.1/156 (15)

281.1/108 (25)

105

5.289

Positive

21

Fleroxacin (Q)

79660-72-3

370.1/326 (15)

370.1/269 (25)

130

5.300

Positive

22

Sulfachloropyridazine (Su)

80-32-0

285/156 (20)

285/108 (25)

100

5.447

Positive

23

Ofloxacin (Q)

82419-36-1

362/318.1 (15)

362/261.1 (26)

130

5.470

Positive

24

Pefloxacin (Q)

70458-92-3

334.1/316.2 (20)

334.1/290.2 (16)

130

5.504

Positive

25

Sulfameththoxazole (Su)

723-46-6

254.1/108 (25)

254.1/156 (10)

100

5.540

Positive

26

Tetracycline (T)

60-54-8

445.2/410 (19)

445.2/427.1 (12)

125

5.550

Positive

27

Sulfamonomethoxine (Su)

1220-83-3

281.1/156.1 (15)

281.1/108.1 (26)

100

5.565

Positive

28

Norfloxacin (Q)

70458-96-7

320/302.1 (20)

320/276.1 (15)

130

5.586

Positive

29

Amantadine(Aa)

768-94-5

152.2/135 (18)

152.2/93 (30)

100

5.588

Positive

30

Ractopamine hydrochloridee (β-R)

97825-25-7

302/121 (22)

302/164.1 (10)

110

5.634

Positive

31

Clorprenalinee (β-R)

3811-25-4

214.1/154 (13)

214.1/196.1 (5)

80

5.666

Positive

32

Oxytetracycline (T)

79-57-2

461.2/426 (21)

461.2/443.1 (13)

125

5.670

Positive

33

Ciprofloxacin (Q)

85721-33-1

332.1/314.1 (20)

332.1/231 (42)

135

5.690

Positive

34

Enrofloxacin (Q)

93106-60-6

360/316.2 (20)

360/245 (30)

125

5.750

Positive

35

Sulfadoxine (Su)

2447-57-6

311/156 (20)

311/108 (25)

130

5.750

Positive

36

Danofloxacin mesylate (Q)

119478-55-6

358.1/340.1 (25)

358.1/255 (46)

140

5.780

Positive

37

Sulfisoxazole (Su)

127-69-5

268/156 (10)

268/108 (10)

100

5.808

Positive

38

Lomefloxacin (Q)

98079-51-7

352.1/265.1 (20)

352.1/308.1 (10)

130

5.822

Positive

39

Benzenemethanole (β-R)

37148-27-9

277.1/203 (12)

277.1/259.1 (5)

100

5.848

Positive

40

Sulfabenzamide (Su)

127-71-9

277.1/156 (10)

277.1/108 (25)

80

5.980

Positive

41

Sarafloxacin (Q)

98105-99-8

386.1/342.1 (18)

386.1//299 (35)

132

6.010

Positive

42

Tulobuterole (β-R)

41570-61-0

228.1/154 (13)

228.1/172 (5)

100

6.190

Positive

43

Sulfaphenazole (Su)

526-08-9

315/158 (30)

315/222 (20)

130

6.260

Positive

44

Chlorotetracycline (T)

57-62-5

479.1/444 (19)

479.1/462 (16)

130

6.473

Positive

45

Sulfadimethoxine (Su)

122-11-2

311/156 (20)

311/108 (26)

130

6.490

Positive

46

Sulfaquinoxaline (Su)

59-40-5

301.1/156 (11)

301.1/108 (22)

110

6.640

Positive

47

Oxolinic acid (Q)

14698-29-4

262.1/216 (30)

262.1/160 (40)

90

6.720

Positive

48

Doxycycline (T)

6543-77-7

445.1/428 (15)

445.1/321 (33)

130

6.920

Positive

49

Tilmicosin (M)

108050-54-0

869.6/174 (50)

869.6/696.4 (45)

260

7.090

Positive

50

Clindamycin (L)

18323-44-9

426/126 (30)

426/378 (20)

120

7.140

Positive

51

sulfanitran (Su)

122-16-7

336/294 (10)

336/156 (10)

110

7.374

Positive

52

Tylosin (M)

1401-69-0

917/174 (42)

917/101 (54)

240

7.770

Positive

53

Erythromycin (M)

114-07-8

734.5/158.1 (30)

734.5/576.3 (14)

170

7.800

Positive

54

Dexamethasone (Co)

1950/2/2

393.1/373.1 (5)

393.1/355 (10)

100

8.100

Positive

55

Chlorpromazine hydrochloride (Se)

69-09-0

319.2/86 (15)

319.2/246 (20)

120

8.120

Positive

56

Penbutolole (β-R)

36507-48-9

292.1/236 (12)

292.1/201 (20)

110

8.140

Positive

57

Diazapam (Se)

439-14-5

285.1/193 (32)

285.1/153.9 (25)

170

8.460

Positive

58

Thiamphenicol (Am)

15318-45-3

354/185 (20)

354/290 (6)

120

4.535

Negative

59

Florfenicol (Am)

73231-34-2

356/336 (5)

356/185 (15)

120

5.610

Negative

60

Chloramphenicol (Am)

56-75-7

321/257 (10)

321/152 (15)

117

6.330

Negative

61

Nicarbazin (Po )

587-90-6

301/137 (15)

301/107 (45)

70

8.760

Negative

62

Amantadine-D15

33830-10-3

167.2/150 (18)

/

100

5.511

Positive

63

Norfloxacin-D5

1015856-57-1

325.1/307.2 (17)

/

130

5.588

Positive

64

Ciprofloxacin-D8

1130050-35-9

340.2/322.2 (20)

/

135

5.670

Positive

65

Enrofloxacin-D5

1173021-92-5

365.2/321.2 (18)

/

120

5.750

Positive

66

Sulfadoxine-D3

1262770-70-6

314/156 (20)

/

130

5.750

Positive

67

Tulobuterol-D9

1325559-14-5

237.1/155 (13)

/

100

6.160

Positive

68

Sulfadimethoxine-D6

73068-02-7

317/156 (20)

/

130

6.460

Positive

69

Chlorpromazine-d6 hydrochloride

1228182-46-4

325.2/92.2 (15)

/

100

8.118

Positive

70

Chloramphenicol-D5

202480-68-0

326/157 (15)

/

117

6.310

Negative

71

Nicarbazin-d8

1156508-87-0

309/141 (15)

/

70

8.740

Negative

Note: In Table 1, * marks quantitative ions, 62 - 71 are internal standard substance, () means drug classification: (Am), Amide alcohols; (Pe), Penicillins; (Su), Sulfonamides (β-R), β-Receptor agonists; (N), Nitroimidazoles; (L), Lincosamide antibiotics; (Q), Quinolones; (Co), corticosteroid; (T), Tetracyclines;(An), Antiviral agents; (M), Macrolides; (Se), Sedatives; (Po), Polyether anticoccidials.

2.2. Preparation of Standard Solutions

Standards at 10 mg in each target group were accurately weighed and placed in 10 mL brown volumetric flasks, sufficiently dissolved with methanol to a constant volume, and then transferred to brown standard sample bottles after uniform mixing to prepare single standard stock solutions at a concentration of 1 mg/mL and stored at −20˚C. Amoxicillin was dissolved in acetonitrile: water (1:1) to a constant volume; quinolones were dissolved in an appropriate amount of sodium hydroxide solution at a concentration of 0.03 mol/L and then dissolved in methanol to a constant volume. A mixed standard solution with a concentration of 10 μg/mL containing all the diluted single standard methanol was prepared, and a series of working curves with seven concentrations of 0.5 μg/L, 1.0 μg/L, 2.0 μg/L, 5.0 μg/L, 10.0 μg/L, 20.0 μg/L, and 50.0 μg/L were prepared after diluting the mixed standard solution with ultra-pure water or blank matrices.

2.3. Instruments

2.3.1. Instruments Information

1290-6470 LC-MS (Agilent, USA), TGL-16 High-speed Refrigerated Centrifuge (Sichuan Shuke Instrument Co., Ltd., China), KNS-2500 Multi-Tube Vortex Mixer (Krownus Scientific Experimental Instrument Co., Ltd., China), KH-500B Ultrasonic Cleaner (Kunshan Hechao Ultrasonic Instruments Co., Ltd., China), UPT-II-100L ULUPURE-series Ultrapure Water Machine (ULUPURE, China), Milli-Q Ultrapure Water Machine (Millipore, USA).

2.3.2. LC-MS/MS Instrument Conditions

In the test, detection was performed using Agilent 1290-6470 HPLC-MS/MS combined with Agilent Zorbax SB-C18 and 50 mm × 0.30 mm × 1.8 µm chromatographic columns, with the following specific conditions: sample volume 2.0 µL; mobile phase A is methanol and B is 5 mmol/L ammonium acetate solution containing 0.1% formic acid; gradient elution program: 0 min - 2 min; 10% A; 2 min - 7 min; 10% - 80% A; 7 min - 7.5 min, 80% A; 7.5 min - 8 min, 80% - 95% A; 8 min - 9 min, 95% A; 9 min - 9.5 min, 95% - 10% A; 9.5 min - 14 min, 10% A; column temperature: 35˚C; flow rate: 0.3 mL/min; electrospray ionisation (ESI) source, positive and negative ion modes; drying gas temperature: 325˚C; capillary drying gas flow: 7 L/min; nebulizer pressure: 35 psi; sheath gas flow: 12 L/min; sheath gas heater: 300˚C; the chromatographic conditions for dynamic multiple reaction monitoring (dMRM) detection, internal standard rations and each target veterinary drug of interest are shown in Table 1.

2.4. Sample Preparation

The collection, preparation and storage of pork, pig liver, chicken, egg and beef samples were carried out according to the methods of sample preparation and storage of animal and poultry products according to [26]. The above samples, which were accurately weighed at 2.00 ± 0.05 g, were instilled with 100 µL of internal standard mixture solution at a concentration of 0.2 µg/mL, mixed by vortexing, and then placed in a 50 mL centrifuge tube and left in the dark for 20 min. Then the samples were instilled with 8mL acetonitrile/water solution (90:10) containing 0.2% formic acid, under vortex shaking for 2 min at the speed of 2000 r/min and ultrasonic extraction after 20 min of ice water bath, and then centrifuged at 4˚C for 5 min at the speed of 5000 r/min. 2 mL of supernatant was injected into the clean-up LPAS column at the rate of 1 drop per second, a 0.22 µm organic filter head was installed at the lower end of the column to collect the filtrate into the sample bottle for analysis by LC-MS/MS, with the specific operation as shown in Figure 1.

Figure 1. Sample pretreatment main process.

2.5. Method Validation

Method validation includes accuracy, precision, LOD, LOQ, linear range and matrix effect. Linearity was evaluated using the correlation coefficient (R2) of the matrix-matched calibration curve of each veterinary drug. Accuracy and precision were obtained in the recovery tests at the three addition levels (low, medium and high: 5 μg/kg, 10 μg/kg, and 50 μg/kg) (n = 3). In accordance with the standards set up in (EU) 2021/808 [27], the LOQ is defined so that the accuracy and precision of the quantitative results are at the lowest peak levels in the acceptable range. Therefore, in the experiment, 0.25 times MRL standard solutions were added to blank matrix samples (n = 10) (reference value 0.05 mg/kg for MRL-free pesticides). The LOD of each matrix was calculated using the following formula [4].

LOD = 3.3 × (SDMRL * 0.25/S)

LOQ = 10 × (SDMRL * 0.25/S)

ME was calculated from the ratios of the slopes of the matrix-matched calibration curves to the solvent calibration curves [27] [28].

3. Results and Discussions

3.1. Instrument Condition Optimization

To optimise the LC conditions, mobile phases, gradient elution programmes and other key LC parameters were repeatedly adjusted. Comparisons were conducted between methanol and acetonitrile as organic phases, and between aqueous solutions of 0.1% formic acid and 5 mmol/L ammonium acetate containing 0.1% formic acid as aqueous phases, and the mobile phase gradients were constantly adjusted to ensure that each parameter could peak normally. It was observed that when the organic phase was acetonitrile, tetracyclines and certain quinolones exhibited significant peak tailing or fronting, along with reduced signal responses. It was observed that when acetonitrile was used as the organic phase, tetracyclines and certain quinolones exhibited significant peak tailing or fronting, along with reduced response values. Similarly, when using only 0.1% formic acid aqueous solution as the aqueous phase, compounds such as chloramphenicol, thiamphenicol florfenicol, and nicarbazin exhibited either no signal or extremely low responses in negative ion monitoring mode. After several experiments, it was found that the response of the target objects was significantly enhanced after adding 5 mmol/L ammonium acetate solution. Considering peak patterns, test sensitivity and isomeric separation of each target compound, methanol combined with 5 mmol/L ammonium acetate aqueous solution containing 0.1% formic acid was ultimately selected as the optimal mobile phase. After further optimization of the gradient elution conditions, the gradient described in section 2.3.1 was finally confirmed to be suitable to simultaneous determination and satisfactory separation of the 61 veterinary drug residues.

Under optimized chromatographic conditions, the parent ions of target compounds were identified through full-scan mode (MS2Scan) using single standard solution (2 mg/L). Multiple fragment voltages (Fragment/V) were systematically set, and the ion with a mass-to-charge ratio (m/z) corresponding to the molecular weight of each compound was selected as the precursor ion by comparing the molecular weights obtained from individual standard solutions, and the fragment voltage that yielded below the maximum ion response was determined as optimal. Then the product ion scan was performed, with the collision energy (CE) optimized, the characteristic daughter ions and their optimal CE values were discovered simultaneously to ensure that each parameter, except for internal standards, possessed at least two characteristic ion pairs. Ultimately, the optimized parameters were applied in dynamic multiple reaction monitoring (dMRM) analysis. And the detailed retention times, MRM ion pairs, monitoring modes, and optimal CE values for all 61 veterinary drug residues are summarized in Table 1, with the total MRM ion diagrams shown in Figure 2(a), Figure 2(b).

(a)

(b)

Figure 2. Total MRM ion diagram of 61 veterinary drugs and 10 internal standards (10 μg/L): (a). Positive Polarity; (b). Negative Polarity.

3.2. Optimization of Extraction Reagents

Common extraction agents used in the pretreatment of samples for veterinary drug residue analysis typically include solutions of acetonitrile, acidified acetonitrile, ethyl acetate, phosphate buffer [29]. Animal-derived food matrices genarally contain substantial amounts of lipids, proteins, and other macro-molecular components. Acetonitrile demonstrates favorable characteristics as an extraction solvent due to its ability to minimize lipid co-extraction and facilitate albumin precipitation through protein denaturation [30]. However, its strong dehydration capacity may induce rapid drying and aggregation of samples with low moisture content, thereby compromising extraction efficiency. To address this limitation, extraction efficiency of pure acetonitrile and acetonitril with various proportions of water (10%, 20%, 30%, and 40%, v/v) were compared. As illustrated in Figure 3, acetonitrile containing 10% water (v/v) exhibited the highest extraction efficiency, with 47 target objects demonstrating recoveries within the range of 60-120%. This might be because an appropriate amount of water can improve the dispersibility of the sample, preventing the sample from caking due to excessive dehydration, thereby enhancing the extraction efficiency of veterinary drugs. However, when the water content is too high, it may lead to an increased distribution of veterinary drugs in the aqueous phase, thus reducing the extraction rate in the acetonitrile phase.

Figure 3. Recovery of veterinary drugs with different water contents in the extraction agent.

To improve the extraction efficiency of each target object, different extraction solvents, including pure acetonitrile and acetonitrile solutions containing 0.1%, 0.2%, 0.5%, and 1% formic acid (FA), were systematically compared. As shown in Figure 4, acetonitrile containing 0.2% FA provided optimal extraction performance, with 54 veterinary drugs achieving satisfactory recoveries ranging from 60% to 120%. The addition of formic acid adjusted the pH of the solution, promoting the ionization of veterinary drugs, making them more soluble in acetonitrile and thus enhancing the extraction efficiency. However, when the formic acid content was too high, it might affect the stability of some veterinary drugs, leading to a decline in the recovery rate. Therefore, after comprehensive consideration, the acetonitrile solution containing 0.2% formic acid was chosen as the optimal extraction reagent.

Figure 4. Recovery of veterinary drugs with different acid content in the extraction agent. Note: A: acetonitrile; B: 0.1% FA in Acetonitrile; C: 0.2% FA in Acetonitrile; D: 0.5% FA in Acetonitrile; E: 1% FA in Acetonitrile.

3.3. Optimization of Extraction Volumes

After selecting the optimal extraction solvent composition, the dosage of extraction solvent was also optimized. Generally, small extraction volumes resulted in high concentrations of matrix components, which ultimately complicated subsequent purification steps and increased matrix interference. However, extracting in excessive volumes can pose several issues. During the clean-up and detection procedures, it significantly escalates experimental costs. This not only diminishes the recovery rates but also results in the waste of reagents and raises environmental concerns. To systematically investigate the effect of extraction solvent volume on analyte recovery and matrix interference, 35 analytes were randomly selected and extracted using four extraction volumes (4 mL, 6 mL, 8 mL and 10 mL). As shown in Figure 5, as the extraction volume increased, the matrix effect was gradually reduced and the overall recovery rate decreased. When the extraction volume was 10 mL, recoveries for 26 analytes dropped to the range of 60% - 80%, with the recovery of metronidazole notably falling below 60%. This reduction was likely caused by excessive dilution of the analytes. Since the extraction volume is too large, the concentration of the target substances in the extraction liquid is relatively reduced. This leads to an increase in losses during the subsequent purification and detection processes, thereby affecting the recovery rate. When the extraction volume was 8 mL, 30 analytes showed recoveries within the range of 70% - 120%. However, smaller extraction volumes of 6 mL and 4 mL led to excessively high recoveries (>120%) for 8 and 25 analytes, respectively, indicating significant co-extraction of interfering matrix substances due to higher matrix concentrations. This phenomenon could negatively impact detection accuracy. This could be due to the fact that when the extraction volume is too small, the matrix concentration is too high, causing some target substances to be coxtracted with impurities during the extraction process, resulting in a high recovery rate. However, in this case, there may also be high matrix interference, affecting the accuracy of the detection. After comprehensively considering the matrix effect and recovery rate, it was finally determined that 8 mL of acetonitrile/water (90:10) solution containing 0.2% formic acid was used as the extraction volume in this experiment. This choice not only ensures the extraction effect but also minimizes the use of reagents, reduces experimental costs, and is also conducive to reducing environmental pollution, which is in line with the concept of green chemistry.

Figure 5. Effects of the different extraction volumes on the extraction effect. Note: The names of corresponding veterinary drugs matching No. in the Figure are available in Table 1.

3.4. Optimization of Clean-Up Processes

Solid phase extraction (SPE) is widely used in the detection of veterinary drug residues in animal derived foods due to its high purification efficiency and reliable recovery rates. However, SPE also presents certain inherent disadvantages. Different analyte classes require the specialized adsorbents such as MAX, MCX, HLB, C18, PSA, and GCB, whose separation mechanisms typically involve silica-based adsorption or ion exchange processes. The conventional SPE procedure includes multiple complex steps such as cartridge activation, equilibration, sample loading, washing, analyte elution, nitrogen evaporation, and redissolution. These extensive operations result in increased analytical time, reagent consumption, and operational costs. Additionally, repeated extraction and solvent evaporation steps demand skilled operators and specialized equipment, thus limiting SPE’s suitability for high-throughput applications.

The emergence of QuEChERS methodology addressed these constraints through streamlined liquid-liquid extraction coupled with dispersive SPE (d-SPE), which turns out to be a simpler and more efficient solution for simultaneously detecting multiple veterinary drugs [4] [16]. This method combines liquid-liquid extraction (LLE) with dispersive solid-phase extraction (d-SPE), enabling rapid separation of analytes from matrix interferences through a simple centrifugation step. Common adsorbents utilized in d-SPE include GCB, C18, PSA, and silica gel [31] [32]. Despite being advantageous over traditional SPE in terms of operational simplicity, speed, and cost-effectiveness, QuEChERS purification often exhibits higher matrix effects, reduced recoveries for certain analytes, and elevated costs associated with disposable purification tubes. Consequently, d-SPE is predominantly employed for qualitative screening of large sample sets rather than precise quantitative analyses. Thus, in addition to effective extraction, efficient removal of matrix interferences remains a critical challenge in achieving rapid and accurate quantitative detection of veterinary drugs.

Based on d-SPE and SPE, needle-cylinder clean-up columns were adopted in the test. The needle-cylinder clean-up columns are pre-filled with LPAS (lipid and protein adsorbent) prepared by the chemical bond modification technique, which can absorb interfering substances of lipid and protein better than C18, PSA and GCB, and is more suitable determination of multiple veterinary drug residues in animal derived food. The clean-up procedures of stripping, vortex clean-up, secondary centrifugation and secondary transfer of the supernatant have been eliminated compared with the traditional QuEChERS method, and the clean-up is completed by extracting the supernatant into clean-up tubes, gently pressing the tubes and transferring it to LPAS cartridges at the rate of 1 drop per second, it is easier and faster (specific procedures are shown in Figure 1).

The experiment compared the reagent consumption, time efficiency, waste liquid generation, etc. of two commonly used pretreatment methods with the LPAS syringe type purification (Table 2). As can be seen from Table 2, the LPAS syringe-type purification reduces the consumption of solution reagents, vessels, and reagents compared with SPE and QuEChERS. The amount of waste liquid generated is 6.0 mL, which is only one-fourth of that of SPE, showing a significant advantage in reducing pollution emissions. Additionally, the LPAS syringe-type purification method simplifies the operational procedure, with the single-sample detection time not exceeding 30 minutes. This is only one-fourth of the time required for SPE and half of that for QuEChERS. Therefore, compared with SPE, LPAS has obvious advantages in the purification steps. It can process larger batches of samples in a short time and is friendly to both the health of testers and the environment.

Table 2. Comparison of consumption among three pretreatment methods.

Items

SPE [33]

QuEChERS [34]

LPAS

Purification materials

Solid-phase extraction cartridges, such as HLB, C18, PCA, PCX, etc. 1 piece for each category of drugs

QuEChERS purification tube (containing adsorbents such as neutral aluminum oxide (NA), primary secondary amine (PSA), octadecylsilyl (C18), and polar enhanced polymer (PEP), etc.) 1 piece

1 piece of LPAS filtration type cartridge (containing adsorbents such as lipid and protein adsorbent)

Organic reagent usage amount

15 mL of Methanol

11.5 mL of Acetonitrile

8 mL of Acetonitrile

Inorganic reagent usage amount

18 mL of EDTA buffer

4 g of sodium sulfate

None

Amount of waste liquid (in liquid state)

Approximately 20.0 mL

Approximately 10.0 mL

Approximately 5.0 mL

Consumption of vessels

Many (such as stoppered measuring cylinders, conical flasks, beakers, etc. for preparing lots of solutions)

Less (1 for each of 15 mL, 10 mL, and 5 mL centrifuge tubes are used)

Few (only 1 15 mL centrifuge tube is used)

Average processing time per sample

Approximately 200 min

Approximately 60 min

Approximately 30 min

In the test, commercially available clean-up columns were selected because their fillers are fixed and therefore the clean-up effect is dependent on the volume of clean-up liquid added. In the test, 1 mL, 1.5 mL, 2 mL and 2.5 mL of pork supernatant (the addition amount was 10 μg/kg) samples were extracted and filter liquid was collected through clean-up columns; it was found that when the volume of liquid to be cleaned up was 2 mL, there was the best clean-up effect with less interference from blank matrix impurities and the best recoveries of the 61 veterinary drugs, therefore 2 mL of sample liquid was selected for filtration clean-up in the method. At the same time, a comparison of speeds through the cartridges was made and there was the best clean-up effect when the clean-up speed was 1 drop per second.

In the experiment, 21 sulfonamides were added to pork at an addition of 10 μg/kg (n = 3). The recovery effects of these 21 sulfonamides after purification by SPE, QuEChERS, and LPAS were compared respectively. The results are presented in Figure 6.

Figure 6 shows that for the pork samples purified by SPE, the average recovery rate of sulfonamides was 88.8% with a relative standard deviation (RSD) of 3.3%. When purified by QuEChERS, the average recovery rate was 87.6% with an RSD of 8.2%. After purification by LPAS, the average recovery rate was 92.4% with an RSD of 5.0%. Both the accuracy and precision of these results met the requirements specified in (EU) 2021/808 [27]. The average recovery rates of 3 purification methods all fell within the range of 75% - 110%, and the RSDs ranged from 0.5% to 10.3%. After purification with LPAS and SPE, the precision of sulfonamide recovery was relatively high, with average RSDs both within 5%. Although the recovery performance of SPE was slightly better than that of QuEChERS and LPAS, it had several drawbacks. These included long pretreatment times, high consumption of reagents and consumables, and the limitation of being able to process only one type of drug at a time, making it an unadvisable choice. Although QuEChERS could purify a relatively wide variety of drugs, the recovery data for sulfonamides were relatively scattered. The average RSD was 8.2%, and the RSDs of three sulfonamides exceeded 10%, indicating relatively low precision. This highlights the advantages of LPAS. In addition to its simple operation and low reagent and consumable consumption, LPAS can achieve good recovery and repeatability.

Figure 6. Effects of different purification on the recovery of sulfonamides in pork.

3.5. Method Validation

3.5.1. Accuracy and Precision

Different animal derived foods have different substances and different interferences with veterinary drug residue testing; to eliminate the interfering factors, the 5 types of animal derived food: pork, pig liver, chicken, egg and beef, which are widely consumed by the residents in daily life and tend to be positive, were selected as samples, adding recovery experiments were conducted by adding low, medium and high (5 μg/kg, 10 μg/kg and 50 μg/kg) levels to their blank samples (n = 3), their average recovery and RSD were calculated to verify the applicability, accuracy and precision of the method. The results have shown (Table 3) that at the low, medium and high addition levels, the total recoveries of the 61 veterinary drugs were in the range of 70.9% - 119.0%, and their RSDs were in the range of 0.1% - 10.9%. The high levels of accuracy and precision achieved demonstrate that this method is fully capable of meeting the detection requirements for 61 veterinary drug residues in various animal-derived foods, providing a reliable technical means for veterinary drug residue detection.

Table 3. Average recoveries and RSDs of 61veterinary drugs in the five matrices (n = 3).

Add levels

(μg/kg)

Average Recoveries (%)

RSD (%)

pork

pig liver

chicken

egg

beef

pork

pig liver

chicken

egg

beef

5

71.4 - 116.7

71.3 - 119.0

71.3 - 117

71.6 - 113

70.9 - 107.1

1.1 - 9.9

0.5 - 9.5

0.1 - 9.0

0.5 - 10.2

0.3 - 10.8

10

73.9 - 113.2

71.9 - 114.2

71.8 - 112.6

70.9 - 113

70.9 - 113.6

0.4 - 10.9

0.7 - 10.3

0.5 - 9.9

0.1 - 10.7

0.9 - 10.7

50

73.5 - 108.1

71.2 - 112.6

73.1 - 111.5

72.0 - 111.5

72.6 - 113.4

0.1 - 6.9

0.6 - 9.5

0.5 - 9.6

0.2 - 9.8

0.6 - 10.1

3.5.2. LOD, LOQ and Linear Range

Calibration working curves were drawn with the response value of the target compounds as the vertical coordinate and quality concentration as the horizontal coordinate. The results showed that the 61 veterinary drugs had strong linearity in the range of 0.5 μg/L - 50 μg/L with correlation coefficients (R2) > 0.995. The total LODs of the 61 veterinary drugs in 5 animal derived food were in the range of 0.03 μg/kg - 1.5 μg/kg, and their LOQs were in the range of 0.1 μg/kg - 5.0 μg/kg, which were much lower than the MRLs set by a majority of countries; therefore, it could meet the demand for the detection of multiple veterinary drugs in multiple livestock and poultry products. As β-receptor agonists are hardly used in livestock and poultry breeding, and many countries have not yet set the MRLs of such drugs in livestock and poultry products, no LOD or LOQ was investigated in chicken and eggs in the study.

3.5.3. Matrix Effects

Matrix effects (ME) refer to phenomena where other interfering substances present in matrices lead to varying degrees of signal enhancement or attenuation of analytes [28]. Matrix effects are widespread in instrumental analysis, such as GC, GC-MS/MS, LC-MS/MS, etc. [35], and affect the accuracy and precision of the determination results. When LC-MS/MS was used to analyse complex samples, such as pig liver and egg, especially in the ESI mode, matrix effects were particularly evident and directly affected quantitative accuracy, unless such matrix effects were minimised or compensated [24].

Matrix effects were obtained by comparing the slope ratio of the calibration curve prepared by matrix blank solutions (k1) and that of the reagent calibration curve (k2) (ME = k1/k2). Assuming that matrix enhancement occurs when ME > 1, that matrix attenuation occurs when ME < 1, and that no matrix effect occurs when ME = 1. Comparisons were made between the matrix effects of the 61 veterinary drugs in the 5 types of animal derived food of pork, pig liver, chicken, egg and beef in the test with the results as shown in Table 4.

It is known from Table 4 that the ME of 55 veterinary drugs in pork matrix, 38 types in chicken matrix and 37 types in beef matrix were in the range of 0.8 - 1.2, those of 26 veterinary drugs in pig liver were less than 0.8 and those of 4 types

Table 4. The MRLs, MEs, LODs and LOQs of 61 veterinary drugs in 5 matrices.

were greater than 1.2, those of 28 veterinary drugs in eggs were below 0.8 and those of 2 types were greater than 1.2. This might be caused by the fact that pig liver and eggs contain a huge amount of protein, lipid etc., more complex components resulted in more severe matrix interferences. In order to effectively compensate for matrix effects, the test was calibrated with blank matrices to ensure that the detection data can truly reflect the actual situation of veterinary drug residues in animal-derived foods.

3.6. Real Sample Testing

The method established in the test was used to detect 731 animal derived samples randomly selected from the market, slaughterhouses and plants in the years 2024-2025, including: 272 pork samples, 85 pig liver samples, 140 chicken samples, 172 egg samples, and 62 beef samples. The results showed (Table 5) that 13 veterinary drugs were detected 64 times in 61 veterinary drugs; 12 restricted veterinary drugs were detected 57 times, which were below the limits of China, USA and EU, and were determined as qualified samples; 2 prohibited veterinary drugs were detected 7 times and were determined as unqualified samples, no other veterinary drugs were detected, and the total percentage is 99.3%.

Table 5. The real samples detected results.

Samples & quantity

Detected

drugs

Detected times

Results (μg/kg)

MRLs (μg/kg) CHN/CAC

Samples & quantity

Detected

drugs

Detected times

Results (μg/kg)

MRLs (μg/kg) CHN/CAC

pork (272)

Doxycycline

4

6.89 - 40.9

100/

pig liver (85)

Doxycycline

1

44.6

300/

Tetracycline

2

7.18 - 30.3

200/200

egg (172)

Ciprofloxacin

2

2.11 - 56.3

CND/-

Oxytetracycline

2

6.22 - 23.8

200/200

Enrofloxacin

3

1.38 - 3.31

CND/-

Chlorotetracycline

1

26.0

200/200

Ofloxacin

1

1.65

/

Sulfadimethoxine

6

0.55 - 4.40

100/-

Fleroxacin

2

1.30 - 1.48

/

Sulfaquinoxaline

4

0.72 - 5.50

100/-

Pefloxacin

2

2.56 - 3.26

/

Metronidazole

2

0.21 - 0.42

CND/-

CND

beef (62)

Doxycycline

1

46.0

100/

chicken (140)

Ciprofloxacin

10

1.99 - 9.33

100/-

Oxytetracycline

1

25.8

200/200

Enrofloxacin

8

1.26 - 2.05

100/-

Chlorotetracycline

1

42.7

200/200

Ofloxacin

1

1.93

/

Sulfadimethoxine

1

1.86

100/-

Norfloxacin

9

3.19 - 10.1

/

The veterinary drugs with the highest detection rate were the quinolones (ciprofloxacin, enrofloxacin, etc.), with 38 times; tetracyclines (doxycycline, tetracycline, etc.) were second to the quinolones with 13 times; sulfonamides (sulfadimethoxine, sulfaquinoxaline, etc.) were in the third place with 11 times. The results showed that the veterinary drugs are most commonly used in the treatment of livestock and poultry diseases.

It is worth noting that ciprofloxacin and enrofloxacin were detected twice and 3 times with the detection value ranges of 2.11 μg/kg - 56.3 μg/kg and 1.38 μg/kg - 3.31 μg/kg in egg samples respectively, but the two veterinary drugs are stipulated as prohibited drugs during egg production periods in GB 31650-2019 [36] and by CAC and EU [8] [14]; Metronidazole was detected twice in pork samples, and it is prohibited in animal derived food as stipulated in GB 31650-2019 [32] and by CAC and EU [8] [14], so the 7 samples were unqualified. These results suggest that although, overall, the safety of animal-derived food is relatively high, there are still some farmers who use prohibited veterinary drugs in violation of regulations. It is necessary to strengthen the supervision of veterinary drug use as well as publicity and education to ensure the quality and safety of animal-derived foods. Through the testing of actual samples, the detection method established in this study can accurately detect veterinary drug residues in animal-derived foods, providing strong technical support for food safety supervision.

4. Conclusions

In this study, a novel clean-up LPAS column was used to rapidly filter and purify a wide range of animal foods food matrices, achieving efficient decontamination. Coupled with LC-MS/MS, a high throughput detection method was established which can simultaneously detect 61 veterinary drug residues across 13 categories in various animal-foods. Compared with the traditional QuEChERS, the process of salt stripping, liquid transfer, secondary centrifugation and other steps were reduced, which is simpler and faster.

In the experiment, the conditions of LC-MS/MS, extraction reagents, extraction volumes and clean up process of 61 kinds of veterinary drugs were optimized. The performance of the method including accuracy, precision, detection limit, quantitative limit, linear range and 5 matrix effects were verified. The results show that 61 kinds of veterinary drugs get good recovery rates in 5 kinds of animal foods ranged from 70.9% to 119.0%, RSD ranged from 0.1% to 10.9%; had a good linear relationship: R2 ≥ 0.995; the total LODs ranged from 0.03 μg/kg to 1.5 μg/kg, and the LOQs ranged from 0.1 μg/kg to 5.0 μg/kg; far below the MRLs set by most countries. There are 50.8% of the veterinary drugs ME in the 5 samples: ranged 0.8 - 1.2 can be acceptable. This approach has been triumphantly utilized for the detection of 731 samples related to livestock and poultry.

The test results indicate that quinolone, tetracycline, and sulfonamide are the most frequently used veterinary drugs in the treatment of livestock and poultry diseases. Meanwhile, they also reflect the problem that some livestock and poultry products are sold during the withdrawal period after being treated with prohibited drugs. This finding provides important data support for food safety supervision departments, which is conducive to strengthening the supervision of the quality and safety of animal products and safeguarding the health of consumers.

In conclusion, the clean-up LPAS combined with LC-MS/MS detection method established in this study enables the rapid, accurate, and efficient detection of multiple veterinary drug residues in animal-derived foods. It has the advantages of simple operation, low cost, and environmental friendliness. It provides strong technical support for the quality and safety supervision of animal-derived foods and has broad application prospects.

Although this study has successfully established a method for detecting multiple veterinary drug residues in animal-derived foods based on Clean-up LPAS combined with LC-MS/MS technology and achieved satisfactory results, there are still some deficiencies that need to be further improved and refined in future research. This study mainly focuses on the detection of 61 veterinary drugs in 13 categories. However, there is a wide variety of veterinary drugs, and new varieties of veterinary drugs are constantly emerging on the market. To more comprehensively ensure the safety of animal-derived foods, future research can further expand the types of veterinary drugs to be detected, covering more new veterinary drugs and metabolites. This requires further optimization and verification of the detection method to ensure that the newly included veterinary drugs can be accurately detected within the existing detection system, improving the comprehensiveness and accuracy of detection.

In addition, in practical applications, animal-derived foods in different regions may have different veterinary drug use situations and matrix characteristics. Although this study has analyzed common samples such as pork, pig liver, chicken, eggs, and beef, for animal-derived foods with other special matrices, such as mutton, duck meat, dairy products, etc., for samples from different regions and with different matrices, the detection method needs to be optimized and adjusted accordingly to ensure the accuracy and reliability of the method. In the future, multi-center and large sample studies can also be carried out to collect animal-derived food samples from different regions, conduct more extensive verification and evaluation of the detection method, and provide a basis for establishing universal veterinary drug residue detection standards.

Future research should also focus on the integration of veterinary drug residue detection technology and the food safety supervision system. By establishing a complete veterinary drug residue monitoring network, real-time monitoring and early warning of the whole chain of animal-derived foods from breeding, processing to sales can be realized: strengthen cooperation with relevant departments, apply detection technology to actual supervision work, provide a scientific basis for formulating reasonable veterinary drug use policies and food safety standards, and thus better ensure public food safety.

Authors’ Contributions

Data curation, Yu Zhang, and Qiaohui Yang; Formal analysis, Xiaxue Li; Yunhua Zheng, Funding acquisition, Xiaxue Li and Yan Zeng; Investigation, Qiaohui Yang; Methodology, Qiaohui Yang and Yan Zeng; Resources, Jie Chen; Supervision, Jie Chen and Yan Zeng; Validation, Qiaohui Yang and Xin Zhou; Visualization, Xiaxue Li and Yu Zhang; Writing original draft, Qiaohui Yang; Writing review & editing, Yan Zeng, Yunhua Zheng and Xin Zhou. All authors have read and agreed to the published version of the manuscript.

Funding

Sichuan Market Regulation Administration Science and Technology Project (SCSJZ2025013).

Acknowledgements

We acknowledge the financial support from Sichuan Market Regulation Administration Science and Technology Project (2025) and Agricultural Product Quality Safety Risk Monitoring Project of Sichuan Province of China in 2024.

Data Availability Statement

The data were released to the researchers without access to any personal data.

NOTES

*Co-first Author.

#Corresponding author.

Conflicts of Interest

The authors declare that they have no conflict of interest.

References

[1] Boxall, A.B.A., Kolpin, D.W., Halling-Sørensen, B. and Tolls, J. (2003) Peer Reviewed: Are Veterinary Medicines Causing Environmental Risks? Environmental Science & Technology, 37, 286A-294A.
https://doi.org/10.1021/es032519b
[2] Kang, J. (2014) Studies of Rapid Determination for Mutil-Residues of Veterinary Drug in Animal Derived Food and Establishment of the Accurate Mass Library. Dissertation, Yanshan University.
[3] Al Tamim, A., Alzahrani, S., Al-Subaie, S., Almutairi, M.A., Al Jaber, A. and Alowaifeer, A.M. (2022) Fast Simultaneous Determination of 23 Veterinary Drug Residues in Fish, Poultry, and Red Meat by Liquid Chromatography/Tandem Mass Spectrometry. Arabian Journal of Chemistry, 15, Article 104116.
https://doi.org/10.1016/j.arabjc.2022.104116
[4] Jung, Y.S., Kim, D., Nam, T.G., Seo, D. and Yoo, M. (2022) Identification and Quantification of Multi-Class Veterinary Drugs and Their Metabolites in Beef Using Lc-MS/MS. Food Chemistry, 382, Article 132313.
https://doi.org/10.1016/j.foodchem.2022.132313
[5] Chen, J., Ying, G. and Deng, W. (2019) Antibiotic Residues in Food: Extraction, Analysis, and Human Health Concerns. Journal of Agricultural and Food Chemistry, 67, 7569-7586.
https://doi.org/10.1021/acs.jafc.9b01334
[6] Alcántara-Durán, J., Moreno-González, D., Gilbert-López, B., Molina-Díaz, A. and García-Reyes, J.F. (2018) Matrix-Effect Free Multi-Residue Analysis of Veterinary Drugs in Food Samples of Animal Origin by Nanoflow Liquid Chromatography High Resolution Mass Spectrometry. Food Chemistry, 245, 29-38.
https://doi.org/10.1016/j.foodchem.2017.10.083
[7] Khaled, A., Gionfriddo, E., Acquaro, V., Singh, V. and Pawliszyn, J. (2019) Development and Validation of a Fully Automated Solid Phase Microextraction High Throughput Method for Quantitative Analysis of Multiresidue Veterinary Drugs in Chicken Tissue. Analytica Chimica Acta, 1056, 34-46.
https://doi.org/10.1016/j.aca.2018.12.044
[8] Park, H., Choi, S.Y., Kang, H. and Kwon, N.J. (2022) Multi Residue Determination of 96 Veterinary Drug Residues in Domestic Livestock and Fishery Products in South Korea. Aquaculture, 553, Article 738064.
https://doi.org/10.1016/j.aquaculture.2022.738064
[9] Park, H., Choi, S.Y., Kang, H. and Kwon, N.J. (2022) Multi Residue Determination of 96 Veterinary Drug Residues in Domestic Livestock and Fishery Products in South Korea. Aquaculture, 553, Article 738064.
https://doi.org/10.1016/j.aquaculture.2022.738064
[10] Barrasso, R., Bonerba, E., Savarino, A.E., Ceci, E., Bozzo, G. and Tantillo, G. (2019) Simultaneous Quantitative Detection of Six Families of Antibiotics in Honey Using a Biochip Multi-Array Technology. Veterinary Sciences, 6, Article 1.
https://doi.org/10.3390/vetsci6010001
[11] Xiao, Z., Wang, J., Cao, Y., Yao, T., Wang, S., Liu, J., et al. (2023) Quick and High-Throughput Quantification of 22 β-Agonists Residues in Animal-Derived Foods Using Enzymatic Probe Sonication. Food Chemistry, 408, Article 135262.
https://doi.org/10.1016/j.foodchem.2022.135262
[12] Woodward, K.N. (2005) Veterinary Pharmacovigilance. Part 3. Adverse Effects of Veterinary Medicinal Products in Animals and on the Environment. Journal of Veterinary Pharmacology and Therapeutics, 28, 171-184.
https://doi.org/10.1111/j.1365-2885.2005.00647.x
[13] Chen, J.Y., He, Z.Y., Lu, Y., Xie, K.Z., Zhang, G.X., Zhang, T. and Dai, G.J. (2021) Comparison between China and the US, Japan, EU and CAC on the Maximum Residue Limit for Veterinary Drugs in Poultry Products. Jiangsu Agricultural Journal, 37, 754-762.
[14] Léger, A., Alban, L., Veldhuis, A., van Schaik, G. and Stärk, K.D.C. (2019) Comparison of International Legislation and Standards on Veterinary Drug Residues in Food of Animal Origin. Journal of Public Health Policy, 40, 308-341.
https://doi.org/10.1057/s41271-019-00169-2
[15] Ministry of Agriculture and Rural Affairs, National Health Commission and State Administration for Market Regulation. (2019) Maximum Residue Limit of Veterinary Drugs in Food: GB 31650-2019. China Standards Press.
[16] Hu, M., Ben, Y., Wong, M.H. and Zheng, C. (2021) Trace Analysis of Multiclass Antibiotics in Food Products by Liquid Chromatography-Tandem Mass Spectrometry: Method Development. Journal of Agricultural and Food Chemistry, 69, 1656-1666.
https://doi.org/10.1021/acs.jafc.0c05778
[17] Zhang, C., Deng, Y., Zheng, J., Zhang, Y., Yang, L., Liao, C., et al. (2019) The Application of the QuEChERS Methodology in the Determination of Antibiotics in Food: A Review. TrAC Trends in Analytical Chemistry, 118, 517-537.
https://doi.org/10.1016/j.trac.2019.06.012
[18] Chen, X.L., Li, Q., Wang, Z.F., Fang, H.X., Li, Y.G., Li, M.X. and Shao, J.L. (2021) Simultaneous Determination of Multiple Veterinary Medicine Residues in Chicken and Eggs by UHPLC-MS/MS. Journal of Chinese Mass Spectrometry Society, 42, 1046-1058.
[19] Zhao, F., Gao, X., Tang, Z., Luo, X., Wu, M., Xu, J., et al. (2017) Development of a Simple Multi-Residue Determination Method of 80 Veterinary Drugs in Oplegnathus punctatus by Liquid Chromatography Coupled to Quadrupole Orbitrap Mass Spectrometry. Journal of Chromatography B, 1065-1066, 20-28.
https://doi.org/10.1016/j.jchromb.2017.09.013
[20] Yin, Z., Chai, T., Mu, P., Xu, N., Song, Y., Wang, X., et al. (2016) Multi-Residue Determination of 210 Drugs in Pork by Ultra-High-Performance Liquid Chromatography-Tandem Mass Spectrometry. Journal of Chromatography A, 1463, 49-59.
https://doi.org/10.1016/j.chroma.2016.08.001
[21] Li, X., Fang, Z., He, X., Zhang, S., Ding, H. and Ye, H. (2021) Optimization of 204 Veterinary Drug Residues Method and Establishing Their Mass Spectrum Library. International Journal of Food Properties, 24, 1658-1680.
https://doi.org/10.1080/10942912.2021.1986524
[22] Desmarchelier, A., Bessaire, T., Savoy, M., Tarres, A., Mujahid, C., Beck, A., et al. (2021) Screening of 154 Veterinary Drug Residues in Foods of Animal Origin Using LC-MS/MS: First Action 2020.04. Journal of AOAC International, 104, 650-681.
https://doi.org/10.1093/jaoacint/qsaa168
[23] Song, L., Pan, C., Yang, J., Zeng, S. and Han, Y. (2020) Dual‐Layer Column Filtration Cleanup and Gas Chromatography‐Tandem Mass Spectrometry Detection for the Analysis of 39 Pesticide Residues in Porcine Meat. Journal of Separation Science, 43, 1306-1315.
https://doi.org/10.1002/jssc.201900850
[24] Dasenaki, M.E. and Thomaidis, N.S. (2015) Multi-Residue Determination of 115 Veterinary Drugs and Pharmaceutical Residues in Milk Powder, Butter, Fish Tissue and Eggs Using Liquid Chromatography-Tandem Mass Spectrometry. Analytica Chimica Acta, 880, 103-121.
https://doi.org/10.1016/j.aca.2015.04.013
[25] Lin, S., Zhao, Z., Lv, Y., Shen, S. and Liang, S. (2021) Recent Advances in Porous Organic Frameworks for Sample Pretreatment of Pesticide and Veterinary Drug Residues: A Review. The Analyst, 146, 7394-7417.
https://doi.org/10.1039/d1an00988e
[26] Ministry of Agriculture and Rural Affairs (2018) Technical Specifications for the Management of Agricultural Products Testing Samples: NY/T 3304-2018. China Standards Press.
[27] EU Commission Implementing Regulation (2021) 2021/808 of 22 March 2021 on the Performance of Analytical Methods for Residues of Pharmacologically Active Sub-stances 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 (Text with EEA Relevance). Official Journal of the European Union L 180, 84-109.
[28] Alcántara-Durán, J., Moreno-González, D., Gilbert-López, B., Molina-Díaz, A. and García-Reyes, J.F. (2018) Matrix-Effect Free Multi-Residue Analysis of Veterinary Drugs in Food Samples of Animal Origin by Nanoflow Liquid Chromatography High Resolution Mass Spectrometry. Food Chemistry, 245, 29-38.
https://doi.org/10.1016/j.foodchem.2017.10.083
[29] Chen, F.F. (2014) A Brief Introduction to the Safety Detection Technology of Several Livestock Products. Animals Breeding and Feed, 9, 30-31.
[30] Tian, Y., Jia, J., He, J., Huang, J., Wen, Y., Jiang, Y., et al. (2016) Simultaneous Detection of 46 Veterinary Drug Residues in Animal Meat by UHPLC. Chromatographia, 79, 457-471.
https://doi.org/10.1007/s10337-016-3041-0
[31] Taylor, M.J., Giela, A., Sharp, E.A., Senior, C.C. and Vyas, D.S. (2019) A Rapid Multi-Class, Multi-Residue UHPLC-MS/MS Method for the Simultaneous Determination of Anticoagulant Rodenticides, Pesticides and Veterinary Medicines in Wild Animals, Pets and Livestock. Analytical Methods, 11, 1087-1101.
https://doi.org/10.1039/c8ay02367k
[32] Zhu, W., Yang, J., Wang, Z., Wang, C., Liu, Y. and Zhang, L. (2016) Rapid Determination of 88 Veterinary Drug Residues in Milk Using Automated Turborflow Online Clean-Up Mode Coupled to Liquid Chromatography-Tandem Mass Spectrometry. Talanta, 148, 401-411.
https://doi.org/10.1016/j.talanta.2015.10.037
[33] Ministry of Agriculture and Rural Affairs, National Health Commission and State Administration for Market Regulation (2022) GB 31658.17-2021. National Food safety Standard Determination of Tetracyclines, Sulfonamides and Fluoroquinolones Residues in Animal Derived Food by Liquid Chromatography-Tandem Mass Spectrometric Method. China Standards Press.
[34] Yang, G., Zhang, J., Tang, Y., Kong, C., Li, S., Wang, S., et al. (2024) Development and Validation of Rapid Screening of 192 Veterinary Drug Residues in Aquatic Products Using HPLC-HRMS Coupled with QuEChERS. Food Chemistry: X, 22, 101504.
https://doi.org/10.1016/j.fochx.2024.101504
[35] Panuwet, P., Hunter, R.E., D’Souza, P.E., Chen, X., Radford, S.A., Cohen, J.R., et al. (2016) Biological Matrix Effects in Quantitative Tandem Mass Spectrometry-Based Analytical Methods: Advancing Biomonitoring. Critical Reviews in Analytical Chemistry, 46, 93-105.
https://doi.org/10.1080/10408347.2014.980775
[36] Ministry of Agriculture and Rural Affairs, National Health Commission and State Administration for Market Regulation (2019) GB 31650-2019 National Food Safety Standard-Maximum Residue Limits for Veterinary Drugs in Foods. China Agricultural Press.

Copyright © 2025 by authors and Scientific Research Publishing Inc.

Creative Commons License

This work and the related PDF file are licensed under a Creative Commons Attribution 4.0 International License.