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Article

Simultaneous Determination of Steroids and NSAIDs, Using DLLME-SFO Extraction and HPLC Analysis, in Milk and Eggs Collected from Rural Roma Communities in Transylvania, Romania

by
Mihaela Cătălina Herghelegiu
1,
Vlad Alexandru Pănescu
1,
Victor Bocoș-Bințințan
1,*,
Radu-Tudor Coman
2,
Vidar Berg
3,
Jan Ludvig Lyche
3,
Maria Concetta Bruzzoniti
4 and
Mihail Simion Beldean-Galea
1,*
1
Faculty of Environmental Science and Engineering, Babeș-Bolyai University, 1 Kogălniceanu Str., 400084 Cluj-Napoca, Romania
2
Faculty of Medicine, “Iuliu Hațieganu” University of Medicine and Pharmacy, 8 Babeș Str., 400012 Cluj-Napoca, Romania
3
Faculty of Veterinary Medicine, Norwegian University of Life Sciences, 1433 Ås-Oslo, Norway
4
Department of Chemistry, University of Turin, Via P. Giuria 5, 10125 Turin, Italy
*
Authors to whom correspondence should be addressed.
Molecules 2024, 29(1), 96; https://doi.org/10.3390/molecules29010096
Submission received: 30 November 2023 / Revised: 20 December 2023 / Accepted: 21 December 2023 / Published: 22 December 2023

Abstract

:
This research aims to determine five steroids and four non-steroidal anti-inflammatory drugs in milk and egg samples collected from rural Roma communities in Transylvania, Romania. Target compounds were extracted from selected matrices by protein precipitation, followed by extract purification by dispersive liquid–liquid microextraction based on solidification of floating organic droplets. The extraction procedure was optimized using a 24 full factorial experimental design. Good enrichment factors (87.64–122.07 milk; 26.97–38.72 eggs), extraction recovery (74.49–103.76% milk; 75.64–108.60% eggs), and clean-up of the sample were obtained. The method detection limits were 0.74–1.77 µg/L for milk and 2.39–6.02 µg/kg for eggs, while the method quantification limits were 2.29–5.46 µg/L for milk and 7.38–18.65 µg/kg for eggs. The steroid concentration in milk samples was <MDL up to 4.30 µg/L, decreasing from 17α-ethinyl estradiol, 17β-estradiol, and estrone to estriol. The NSAID concentration was <MDL up to 3.41 µg/L, decreasing from ibuprofen, diclofenac, and ketoprofen to naproxen. The steroid concentration in the egg samples was <MDL to 2.79 µg/kg, with all steroids detected, while the concentration of NSAIDs was <MDL to 2.28 µg/kg, with only ibuprofen, ketoprofen, and naproxen detected. The developed protocol was successfully applied to the analysis of target compounds in real milk and egg samples.

Graphical Abstract

1. Introduction

Milk and eggs are an indispensable part of the daily diet of individuals, as they contain the necessary nutrients (high-quality proteins, carbohydrates, vitamins, trace minerals) for human health [1,2]. These two foods are widely consumed, especially by growing children and elderly people, since they make a valuable contribution to the nutritional balance of the diet and overall are a relatively inexpensive source of nutrients [1,3].
However, currently, a range of veterinary drugs are widely used in animal husbandry both to prevent and treat diseases; they may also be used as growth promoters by direct application or mixed with feed [4,5].
As a result of the abuse of veterinary products or through their improper use, non-respected withdrawal periods, and cross-contamination, these drugs can be transferred and may accumulate in products of animal origin, which is definitely a potential risk to public health [4,5,6]. Non-steroidal anti-inflammatory drugs (NSAIDs) are widely used in veterinary medicine to treat inflammatory processes [7]. In order to protect consumers’ health, the European Union established threshold values called “maximum residue limits” (MRLs) in food of animal origin; for instance, that for diclofenac MRL is just 0.1 μg/kg [4,8]. Regarding the steroid hormones, the European Union banned their use as animal growth promoters [9,10], but despite this prohibition, there have been no specific maximum residue limits established [11]. Steroid hormones (17-β-estradiol or its ester-like derivatives) can only be used for the treatment of cattle in the case of fetus maceration or mummification and for pyometra (serious infection of the uterus) [10,12]. Glucocorticoids (like hydrocortisone) are used in the animal husbandry industry due to their anti-inflammatory and immunosuppressive properties [13]. Natural steroid hormones (the endoestrogens estrone, estradiol, and estriol) are natural substances that strongly influence female characteristics and are normally present in milk and eggs [12,14], while synthetic hormones (the exoestrogens, such as 17α-ethinylestradiol) are used to improve the weight gain of animals [12]. Human health can be affected (hormonal disorders and diseases) by food when estrogen levels are higher than normal [11] or, in the case of hydrocortisone, athletes can test positive for doping [13].
The low concentrations at which NSAIDs and estrogens are present in milk and eggs require a suitable method of extraction. A few scientists have already used liquid–liquid extraction (LLE) [14,15,16] and solid-phase extraction (SPE) [17] to isolate and concentrate NSAIDs and estrogens from milk and eggs. These two extraction techniques require, however, a relatively high consumption of solvent on one hand, and a number of purification steps that are time-consuming on the other.
To overcome these problems, over time, miniaturized extraction methods have been developed for both the solid phase [18] and the liquid phase [19], with the aim of reducing the volume and toxicity of the extraction solvent and the amount of sample being processed to reduce the extraction time [20]. Due to the advantages offered, their applications are numerous [21], which is why we only mention their applicability to the analysis of steroids in urine [22] and in water [23]; of NSAIDs in water [24]; of steroids and NSAIDs in wastewater [25]; and, last but not least, in the analysis of steroids and NSAIDs in food samples [5,26,27,28,29]. These are the target compounds selected for this study. These microextraction methods are faster, more environmentally friendly, and have higher enrichment factors [30].
The main aim of this study was to develop a dispersive liquid–liquid microextraction based on solidification of the floating organic droplet (DLLME-SFO) method, followed by HPLC-PDA analysis for the simultaneous determination of four NSAIDs (naproxen, ketoprofen, diclofenac, and ibuprofen), four estrogens (estrone, 17β-estradiol, 17α-ethinylestradiol, and estriol), and one glucocorticoid (hydrocortisone) in both bovine milk and chicken eggs. The developed DLLME-SFO–HPLC-PDA method was then successfully applied to the analysis of these drugs in bovine milk and chicken egg samples collected from households and local markets in 15 rural Roma communities in Transylvania, Romania.

2. Results and Discussion

2.1. Optimization of DLLME-SFO Conditions

Based on our previously published work [25], we choose 1-undecanol as the most suitable solvent for the extraction of the selected compounds and acetonitrile as the most suitable dispersion solvent.
For the optimization of DLLME-SFO, a water sample with a volume of 10 mL was spiked with 100 ng of each compound and then subjected to the extraction protocol under different extraction conditions. The extraction efficiency was expressed by relative extraction recovery of the selected compounds from each experiment, and was used to optimize the extraction conditions.
A total of sixteen experiments using different values of the four variables set at minimum (−1) and maximum (+1) values, and three experiments at the medium set point (0), were carried out. The obtained extraction recovery for each experiment is presented in the Supplementary Materials (Table S1).
The data obtained in the experiments were subjected to optimization using desirability functions (Supplementary Materials, Figure S1).
The maximum, minimum, and optimum extraction recoveries for each compound are presented in Table 1.
The mathematical relationship between the response Y (enrichment recovery) and the four independent variables, X1, X2, X3, and X4 can be modeled by a linear polynomial equation [31] including four linear terms, six two-way interaction terms, four three-way interaction terms, one four-way interaction term, and one intercept term, as follows:
Y = β0 + β1X1 + β2X2 + β3X3 + β4X4 + β12X1X2 + β13X1X3 + β14X1X4 + β23X2X3 + β24X2X4
+ β34X3X4 + β123X1X2X3+ β124X1X2X4 + β134X1X3X4 + β234X2X3X4 + β1234X1X2X3X4
where β0 is a constant; β1, β2, β3, and β4 are linear coefficients; and β12, β13, β14, β23, β24, β34, β123, β124, β13, β234, and β1234 are interaction coefficients.
For the present study, taking diclofenac as an example, the empirical relationship between the independent variables (X1, X2, X3, X4) and the response (Y) can be represented by the following equation:
Y = 74.6 + 2.00X1 + 0.65X2 + 10.99X3 + 1.70X4 + 0.98X1X2 + 0.11X1X3 − 3.24X1X4
− 0.98X2X3 − 0.64X2X4 − 3.38X3X4 + 0.39X1X2X3 + 0.35X1X2X4 − 1.53X1X3X4
1.28X2X3X4 + 2.11X1X2X3X4
The linear polynomial equation showed that the four linear coefficients had a positive effect. However, this positive effect was counterbalanced by the negative effects given by the interactions between two and three combined variables. The magnitude of these effects can be better seen in the histogram (Table S2) that includes the significance levels of the factors and their interactions.
It is important to specify that the magnitude of the influence of these factors is essentially related to the significance range used for each variable in the experimental design, since coded values were used for optimization.
The optimum conditions predicted by the model were, in coded values: +1 for salt, +0.518 for disperser volume, +0.518 for extraction solvent volume, and −0.497 for pH (Supplementary Materials Figure S1), which correspond to the following experimental conditions: salt (NaCl) amount (ionic strength): 500 mg, dispersion solvent volume (acetonitrile): 239.75 μL, extraction solvent volume (1-undecanol): 85.54 μL, and sample pH: 3.51. For a better measurement, we used the following values: amount of salt (NaCl): 500 mg, volume of dispersion solvent (acetonitrile): 240 μL, volume of extraction solvent (1-undecanol): 85 μL; and pH of the sample: 3.5.
The previously presented conditions are optimal theoretical conditions; therefore, to be used in subsequent experiments, they must be experimentally validated. This step is necessary because the chosen experimental design model is quite simple, and consequently, its predictive capabilities could be limited.

2.2. Validation of DLLME-SFO-LC-PDA Method

The performance of the developed DLLME-SFO was expressed in terms of accuracy, intra- and inter-day precision, linearity, limit of detection (LOD), limit of quantification (LOQ), extraction recovery (ER), and enrichment factor (EF).
The linearity of the method was studied in a concentration range between 1.5 and 25 ng/mL. For this, different standard mixtures were prepared at concentrations of 1.5, 3.0, 6.25, 12.5, and 25 ng/mL of each compound by successive dilution of the stock solution. After the HPLC analysis, calibration curves were constructed for each compound by graphically representing the peak area as a function of the analyte concentration. Good linearities were obtained for all compounds, with correlation coefficients (R2) greater than 0.99 (Table 2).
The instrument limit of detection (LOD) and limit of quantification (LOQ) were determined by statistical approaches using the standard deviation (SD) of the regression line and the slope (S) of each calibration curve.
The instrument limits of detection were between 0.07 and 0.21 ng/mL for steroids and between 0.8 and 0.12 ng/mL for NSAIDs; the instrument limits of quantification were between 0.22 and 0.65 ng/mL for steroids and between 0.24 and 0.35 ng/mL for NSAIDs (Table 2).
Accuracy was expressed by the extraction recovery of analytes from the spiked water sample. To this end, the optimal DLLME-SFO parameters predicted by the model were experimentally validated. In this regard, a volume of 10 mL of Milli-Q water was spiked with 100 ng of each selected compound, then acidified to pH 3.5. This was followed by the addition of 500 mg of NaCl, 85 μL of 1-undecanol as extraction solvent, and 240 μL acetonitrile as disperser, as well as centrifugation for 4 min at 4500 rpm. The obtained results were between 74.00 and 111.6% for all selected compounds, except hydrocortisone, for which the recovery was 14.99% (Table 2).
Intra- and inter-day precision were evaluated by relative standard deviations (RSD%) on Milli-Q water samples spiked with 100 ng of each compound. The obtained RSD% values were below 3.81% for the intra-day precision and below 3.84% for the inter-day precision for all the compounds tested (Table 2), thus agreeing with the requirements of the method’s validation procedures regarding the compounds in the range of concentration of the order of μg/L.
Enrichment factors were calculated considering the ratio of analyte concentration in the collected organic phase and the initial concentration of the analyte in the liquid sample. The results showed that the developed DLLME-SFO protocol provided an EF between 87.1 and 131.3, except for hydrocortisone, for which the EF was 17.64 (Table 2), comparable to classical solvent extraction [15,16].

2.3. Matrix Effect

To study the matrix effect, 100 ng of each selected compound was added to 10 mL of the milk sample and to 3 g of the homogenized egg sample, which was diluted to 10 g with double-distilled water. The resulting samples were subjected to deproteinization with 10 mL of ACN:acetic acid mixture (95:5, v/v) and 20 g of NaCl [32,33]. Afterwards, the samples were centrifuged at 4000 rpm for 5 min, after which the supernatant was collected and further cleared by defatting with 4 mL of n-hexane [12]. After the removal of the hexane layer, the remaining phase was evaporated to dryness, and the residue was reconstituted in 10 mL double-distilled water for both the milk and egg samples. The two resulting samples were subjected to the previously described DLLME-SFO protocol. All experiments were performed three times (Table S3). Method detection limits (MDL) and method quantification limits (MQL) were obtained by dividing the LOD and LOQ by the enrichment factors obtained for the milk and egg samples. The performances of the developed DLLME-SFO are presented in Table 3.
As shown in Table 3, the developed DLLME-SFO protocol provided good extraction recovery, enrichment factors, and method detection and quantification limits (MDL, MQL).
The extraction recoveries of the target compounds exceeded 80% in both the milk and egg samples, except for hydrocortisone, for which the ER was below 15%. For estriol (E3), the obtained ER varied between 74.49% for the milk samples and 75.64% for the egg samples, but, considering the quantity of the order of ng, this can be considered satisfactory. Moreover, the ER values for the milk and egg samples were comparable to the values obtained for the contaminated water samples (Table 2) suggesting that no matrix effect occurred for the milk and egg samples.
The enrichment factor (EF) for milk samples ranged between 87.64 and 122.07, while the EF for milk samples was between 26.97 and 38.72, with the unique exception of hydrocortisone, for which the EF was 14.49 for milk samples and 4.32 for egg samples.
The MDL varied between 0.74 and 1.77 µg/L for milk samples and between 2.39 and 6.02 µg/kg for egg samples.
The MQL varied between 2.29 and 5.46 µg/L for milk samples and between 7.38 and 18.65 µg/kg for egg samples. For hydrocortisone, the MDL and MQL were on the order of tens of µg/L and µg/kg, but considering the low ER, this cannot be used as a real value for practical application.
Furthermore, as demonstrated in Figure 1A,B, the extraction protocol provided good sample cleanup, with no other peaks interfering with the target compounds.
In conclusion, the developed protocol can be used for the analysis of target compounds in real milk and egg samples, meeting all the requirements for this type of analysis.

2.4. Analysis of Milk and Egg Samples Collected in Rural Roma Communities

After studying the matrix effect, the developed protocol was applied to the analysis of milk and egg samples collected from households and local markets in 15 rural Roma communities in Transylvania, Romania. A total of 15 milk samples and 15 egg samples were analyzed.
The results showed that, in the milk samples, steroids were found in 10 samples in concentrations that varied from <MDL to 4.30 µg/L; EE2 was found in 8 samples; and E2, E1, and E3 were found in just 3 samples. NSAIDs were found in seven samples in concentrations ranging from <MDL to 3.41 µg/L; their occurrence was as follows: ibuprofen was found in seven samples; diclofenac in three samples; ketoprofen in two samples, and naproxen in one sample. The results obtained for each compound in the analyzed milk samples are presented succinctly in the Supplementary Materials (Table S4).
In the egg samples, steroids were found in 13 samples in concentrations ranging from <MDL to 2.79 µg/kg; they ranked as follows: E3 (found in 7 samples), E2 (in 5 samples), EE2 (in 4 samples), and E1 (in just 1 sample). NSAIDs were found in 12 samples in concentrations that ranged from <MDL to 2.28 µg/kg; their occurrence was as follows: ibuprofen (found in 8 samples), naproxen (in 7 samples), and ketoprofen (in 6 samples). It is worth mentioning that diclofenac was not detected in any egg samples. The results obtained for each compound in the egg samples are briefly presented in the Supplementary Materials (Table S5).
If the concentrations of these target compounds in the analyzed milk samples are to be compared with other results obtained worldwide, one will notice that the concentrations of steroids obtained in this work were higher than those of US milk samples (estrone: 23–67 ng/L, estradiol: <10 ng/L) [34], but in the same concentration range as milk samples from Brazil (estradiol: 86.54–171.09 µg/L) [35] and China (0.05–3.2 µg/kg) [33].
The concentrations of steroids found in the egg samples were in the same range as samples from Spain (estrone: 0.48–1.7 µg/kg and 17-B estradiol: 1.7–2.7 µg/kg) [32] and China (estrone: 0.05–1.72 µg/kg; 17α-estradiol: <LOD—0.13 µg/kg; 17β-estradiol: <LOD—0.16 µg/kg [36]; and estrone: 0.12–0.84 µg/kg) [15].

2.5. Comparison with Other Reports

To highlight the benefits of the developed method, its performance was compared with the performances of other developed methods (Table 4). These performances were evaluated in terms of the amount of sample, volume of extraction solvent, LOQ, and ER.
By analyzing the data shown in Table 4, we can conclude that the developed method has a performance comparable to or better than other methods used for the analysis of NSAIDs and hormones in milk and egg samples. Thus, the method has an LOQ in the range of µg/L µg/kg and a recovery of over 80%, and requires a small amount of the sample and extraction solvent volume. Another advantage is the fact that both NSAIDs and steroids are extracted and analyzed together. We can, therefore, state that the method meets all the requirements for a green method of extraction and analysis.

3. Material and Methods

3.1. Chemicals and Reagents

For the proposed experiments, four NSAIDs, namely, diclofenac sodium salt (DIC), ibuprofen (IBU), ketoprofen (KET), and naproxen (NAP), together with four estrogens, namely, estrone (E1), 17β-estradiol (E2), 17α-ethynylestradiol (EE2), and estriol (E3), and one glucocorticoid, namely, hydrocortisone (HCOR), all with purity levels >98%, were purchased from Sigma-Aldrich (Steinheim, Germany). The molecular structure and some physico-chemical properties of all target compounds are presented in the Supplementary Materials (Table S6).
Stock standard solutions of the individual compounds, at a concentration of 1000 mg/L each, were prepared in acetonitrile for ibuprofen, ketoprofen, and naproxen, while diclofenac and the hormones were prepared in methanol. All prepared stock standards were stored at 4 °C in the dark until analysis. Acetonitrile and methanol of HPLC grade, 1-undecanol, NaCl, ortho-phosphoric acid, acetic acid, and n-hexane were all purchased from Merck (Darmstadt, Germany).
Milli-Q water was prepared using a Milli-Q-Plus ultrapure water system (Millipore, Milford, MA, USA). An Eppendorf centrifuge, model 5804 R (Eppendorf, Wien, Austria), was used for the centrifugation of the samples.

3.2. Instrumentation

HPLC analyses were carried out using Shimadzu equipment (SLC-40D) with a photodiode detector (SPD-M40). Instrument control and data acquisition were carried out via LabSolution software (Version 5.101). The separation of the target compounds was performed on a ZORBAX Eclipse Plus C18 (150 × 4.6 mm, 5 μm) column with a flow rate of 1.0 mL/min and an oven temperature of 40 °C. The injection volume was 20 µL. The gradient elution (acetonitrile ACN and KH2PO4 25 mM) program which was employed was 35% ACN, maintained for 2 min, then increased to 80% in 8 min and held for 5 min, then finally decreased to 35% ACN within 5 min.
The specific UV wavelengths used for PDA detection were as follows: ketoprofen—256 nm, naproxen—230 nm, diclofenac—200 nm, ibuprofen—190 nm, 17β-estradiol—200 nm, 17α-ethynylestradiol—195 nm, estrone—195 nm, estriol—197 nm, and hydrocortisone—247 nm. These UV wavelengths were established by UV spectra generated by the SPD detector for each single compound.

3.3. Extraction by DLLME-SFO Protocol

For the extraction procedure, 10 g of milk was weighed into a 50 mL polypropylene centrifuge tube. The eggs were shaken to mix the white and yolk, after which 3 g of the mixture was weighed and homogenized with 7 g of distilled water. For deproteinization, 10 mL of ACN:acetic acid mixture (95:5, v/v) and 2 g of NaCl were added to each tube and vortexed, followed by centrifugation at 4000 rpm for 5 min [32,33]. Afterwards, 8.5 mL of the supernatant was collected and further cleared by defatting with 4 mL of n-hexane [12]. The n-hexane phase was removed, and the acetonitrile phase was then evaporated to dryness. The resulting residues were reconstituted in 10 mL of water acidified at pH 3.5 with 10 µL 10% ortho-phosphoric acid solution, after which 0.500 g of NaCl was added, followed by the addition of 325 µL of extraction mixture containing 240 µL of ACN and 85 µL of 1-undecanol. After centrifugation at 4000 rpm for 5 min to separate the two phases, the tube was cooled in an ice-water bath for 15 min to solidify the 1-undecanol, which was then collected with a spatula and transferred to a conical ampoule [25]. After melting the extract at room temperature, a volume of 20 μL was directly injected into the HPLC for analysis.

3.4. Enrichment Factor and Extraction Recovery

DLLME-SFO efficiency was expressed by the enrichment factor (EF) and relative extraction recovery (ER%) using the following equations [37]:
E F = C c o l C a q
E R % = ( n c o l ) ( n a q ) × 100 = C c o l × V c o l C a q × V a q × 100
where Ccol is the analyte’s concentration in the collected organic phase; Caq is the initial concentration of the analyte in the liquid sample; ncol is the total amount of analyte extracted in the collected organic phase; naq is the total amount of analyte in the liquid sample; and Vcol and Vaq represent the volume of the collected organic phase and the volume of the liquid sample, respectively.
To achieve good efficiency of the extraction method, the extraction recovery must be between 80% and 120% [38].

3.5. Statistical Approach Used for DLLME-SFO Optimization

Optimizing the experimental conditions is a stage that requires a large number of experiments, which in turn depends on the number of variables (factors) that can affect the experimental results. Usually, the optimal conditions are determined by univariate approaches that consist of changing one variable and observing the effects, while the other variables are kept constant [39]. However, this approach is time-consuming and does not describe the potential interactions between the variables.
A very efficient way to minimize the number of experiments is the statistical approach, such as a multivariate experimental design strategy. This approach requires fewer experiments and can also be used for quantitative and qualitative modeling of relationships between factors and responses, with the goal of maximizing the extraction efficiency [40].
In the present study, a 24 experimental design with a triplicate center point (0) was chosen, and each variable was investigated at two levels (−1 and +1). The studied variables were the amount of sodium chloride (X1), the volume of the dispersant (X2), the volume of the extraction solvent (X3), and the pH of the sample (X4). The extraction efficiency was expressed by extraction recovery. The minimum values (−1), the center point (0), and the maximum values (+1) for each variable are presented in Table 5.
The desirability approach was used for the simultaneous optimization of variables to achieve maximum extraction recovery [41,42]. To this end, better individual desirability (value 1) corresponded to higher extraction recovery, while poor individual desirability (value 0) corresponded to zero extraction recovery, with a linear variation between these two values. Finally, the individual desirability of each compound contributed the same weight to the overall desirability function.
For all statistical modeling, the JMP14 (SAS Institute, Cary, NC, USA) statistical software package was used.

3.6. Sample Collection

For the analysis of the selected compounds (NSAIDs and steroids), samples of fresh cow’s milk and chicken eggs were collected from the local market and from local producers in 15 different rural Roma communities in the Transylvania region of Romania between June and November 2022. The spatial distribution of the sampling points is shown in the Supplementary Materials (Figure S2). Immediately after collection, the milk samples were frozen, and the egg samples were homogenized and stored in the freezer until analysis.

4. Conclusions

A simple, fast, and cheap DLLME-SFO procedure for the simultaneous extraction and preconcentration of NSAIDs and hormones in milk and egg samples was developed, optimized, validated, and finally tested using real food samples.
The target compounds (four estrogenic hormones + four NSAIDs + one corticoid) were extracted from milk and egg matrices after protein precipitation, followed by extract purification by DLLME-SFO.
The extraction procedure was optimized prior using a 24 full factorial experimental design.
Good enrichment factors (87.64–122.07 for milk and 26.97–38.72 for eggs) and extraction recovery values (74.49–103.76% for milk; 75.64–108.60% for eggs) were obtained.
The clean-up of the sample also translated into a simpler chromatographic response that was easier to interpret.
The method detection limits were between 0.74 and 1.77 µg/L for milk and between 2.39 and 6.02 µg/kg for eggs, while the method quantification limits were between 2.29 and 5.46 µg/L for milk and between 7.38 and 18.65 µg/kg for eggs.
Steroid concentrations in milk samples ranged from <MDL to 4.30 µg/L; these were found in decreasing concentrations in 17α-ethinyl estradiol, 17β-estradiol, estrone, and estriol.
The concentration of NSAIDs in the milk samples ranged from <MDL to 3.41 µg/L, and decreased in the order of ibuprofen > diclofenac > ketoprofen > naproxen.
The concentration of steroids in the egg samples ranged from <MDL to 2.79 µg/kg for all steroids detected.
The concentration of NSAIDs in egg samples ranged from <MDL to 2.28 µg/kg, with only ibuprofen, ketoprofen, and naproxen detected. Diclofenac was not found in any egg sample.
Fast analysis was achieved, with an DSSME-SFO extraction performed in ca. 20 min, followed by a chromatographic separation step performed in less than 10 min. The specificity was further enhanced by using different UV detection wavelengths for each target analyte.
Our experimental findings are consistent, in an excellent manner, with the experimental work achieved worldwide so far.
Finally, we can mention that the DLLME-SFO procedure proved its applicability to the analysis of real milk and egg samples, and could open the way to a suitable and green alternative to the traditional SPE and LLE techniques for sample preparation in terms of performance and speed.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/molecules29010096/s1, Table S1: The set code value of variables used in each experiment and the values of extraction recovery (%) obtained for each compound; Table S2: The magnitude of the effects and the significance level for the variables and their interactions; Table S3: Results obtained for contaminated milk and egg samples; Table S4: Results of steroids and NSAIDs obtained on the milk analyzed samples; Table S5: Results of steroids and NSAIDs obtained on the milk analyzed samples. Table S6. Physical-chemical properties of tested compounds and abbreviations; Figure S1: The optimal conditions predicted by model, minimum, maximum and optimum extraction recovery values, and the value of desirability function; Figure S2: Map indication of all 15 sampling points in the investigated area.

Author Contributions

Conceptualization, M.S.B.-G. and V.B.-B.; methodology, M.S.B.-G. and M.C.B.; validation, M.C.H. and M.S.B.-G.; formal analysis, M.C.H. and V.A.P.; investigation, V.A.P., M.S.B.-G., V.B., J.L.L., V.B.-B. and R.-T.C.; resources, M.S.B.-G. and V.B.; data curation, V.B.-B., M.C.B. and R.-T.C.; writing—original draft, M.C.H., M.S.B.-G., V.B.-B., M.C.B. and R.-T.C.; writing—review and editing, M.S.B.-G., V.B.-B. and M.C.B.; supervision, M.S.B.-G.; project administration, M.S.B.-G. and V.B.; funding acquisition, M.S.B.-G. and V.B. All authors have read and agreed to the published version of the manuscript.

Funding

The research leading to these results received funding from the Norway Grants 2014–2021 under Project contract no. 23/2020.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Data are contained within the article and Supplementary Materials.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Badali, A.; Javadi, A.; Mogaddam, M.R.A.; Mashak, Z. Dispersive solid phase extraction-dispersive liquid–liquid microextraction of mycotoxins from milk samples and investigating their decontamination using microwave irradiations. Microchem. J. 2023, 190, 108645. [Google Scholar] [CrossRef]
  2. Liu, Y.; Qing, M.; Zang, J.; Chi, Y.; Chi, Y. Effects of CaCl2 on salting kinetics, water migration, aggregation behavior and protein structure in rapidly salted separated egg yolks. Food Res. Int. 2023, 163, 112266. [Google Scholar] [CrossRef] [PubMed]
  3. Applegate, E. Introduction: Nutritional and Functional Roles of Eggs in the Diet. J. Am. Coll. Nutr. 2000, 19, 495S–498S. [Google Scholar] [CrossRef] [PubMed]
  4. Dasenaki, M.E.; Thomaidis, N.S. Multi-residue determination of 115 veterinary drugs and pharmaceutical residues in milk powder, butter, fish tissue and eggs using liquid chromatography–tandem mass spectrometry. Anal. Chim. Acta 2015, 880, 103–121. [Google Scholar] [CrossRef]
  5. Teglia, C.M.; Gonzalo, L.; Culzoni, M.J.; Goicoeche, H.C. Determination of six veterinary pharmaceuticals in egg by liquid chromatography: Chemometric optimization of a novel air assisted dispersive liquid-liquid microextraction by solid floating organic drop. Food Chem. 2019, 273, 194–202. [Google Scholar] [CrossRef]
  6. Zhou, J.; Xu, J.J.; Cong, J.M.; Cai, Z.X.; Zhang, J.S.; Wang, J.L.; Ren, Y.P. Optimization for quick, easy, cheap, effective, rugged and safe extraction of mycotoxins and veterinary drugs by response surface methodology for application to egg and milk. J. Chromatogr. A 2018, 1532, 20–29. [Google Scholar] [CrossRef]
  7. Rúbies, A.; Guo, L.; Centrich, F.; Granados, M. Analysis of non-steroidal anti-inflammatory drugs in milk using QuEChERS and liquid chromatography coupled to mass spectrometry: Triple quadrupole versus Q-Orbitrap mass analyzers. Anal. Bioanal. Chem. 2016, 408, 5769–5778. [Google Scholar] [CrossRef]
  8. EUR-Lex Acces to European Union Law. Available online: http://data.europa.eu/eli/reg/2010/37(1)/oj (accessed on 29 November 2023).
  9. EUR-Lex Acces to European Union Law. Available online: https://eur-lex.europa.eu/eli/dir/1996/22/oj (accessed on 29 November 2023).
  10. EUR-Lex Acces to European Union Law. Available online: http://data.europa.eu/eli/dir/2003/74/oj (accessed on 29 November 2023).
  11. Socas-Rodríguez, B.; Herrera-Herrera, A.V.; Hernández-Borges, J.; Rodríguez-Delgado, M.A. Multiresidue determination of estrogens in different dairy products by ultra-high-performance liquid chromatography triple quadrupole mass spectrometry. J. Chromatogr. A 2017, 1496, 58–67. [Google Scholar] [CrossRef]
  12. Socas-Rodríguez, B.; Asensio-Ramos, M.; Hernández-Borges, J.; Herrera-Herrera, A.V.; Rodríguez-Delgado, M.A. Chromatographic analysis of natural and synthetic estrogens in milk and dairy products. Trends Anal. Chem. 2013, 44, 58–77. [Google Scholar] [CrossRef]
  13. Yan, Y.; Ai, L.; Zhang, H.; Kang, W.; Zhang, Y.; Lian, K. Development an automated and high-throughput analytical platform for screening 39 glucocorticoids in animal-derived food for doping control. Microchem. J. 2021, 165, 106142. [Google Scholar] [CrossRef]
  14. Mi, X.; Li, S.; Li, Y.; Wang, K.; Zhu, D.; Chen, G. Quantitative determination of 26 steroids in eggs from various species using liquid chromatography–triple quadrupole-mass spectrometry. J. Chromatogr. A 2014, 1356, 54–63. [Google Scholar] [CrossRef] [PubMed]
  15. Yang, Y.; Shao, B.; Zhang, J.; Wu, Y.; Duan, H. Determination of the residues of 50 anabolic hormones in muscle, milk and liver by very-high-pressure liquid chromatography–electrospray ionization tandem mass spectrometry. J. Chromatogr. B 2009, 877, 489–496. [Google Scholar] [CrossRef] [PubMed]
  16. Zhan, J.; Yu, X.J.; Zhong, Y.Y.; Zhang, Z.T.; Cui, X.M.; Peng, J.F.; Feng, R.; Liu, X.T.; Zhu, Y. Generic and rapid determination of veterinary drug residues and other contaminants in raw milk by ultra performance liquid chromatography–tandem mass spectrometry. J. Chromatogr. B 2012, 906, 48–57. [Google Scholar] [CrossRef] [PubMed]
  17. Gallo, P.; Fabbrocino, S.; Dowling, G.; Salini, M.; Fiori, M.; Perretta, G.; Serpe, L. Confirmatory analysis of non-steroidal anti-inflammatory drugs in bovine milk by high-performance liquid chromatography with fluorescence detection. J. Chromatogr. A 2010, 1217, 2832–2839. [Google Scholar] [CrossRef] [PubMed]
  18. Guo, W.; Tao, H.; Tao, H.; Shuai, Q.; Huang, L. Recent progress of covalent organic frameworks as attractive materials for solid-phase microextraction: A review. Anal. Chim. Acta 2023, 23, 341953. [Google Scholar] [CrossRef]
  19. Rutkowska, M.; Płotka-Wasylka, J.; Sajid, M.; Andruch, V. Liquid–phase microextraction: A review of reviews. Microchem. J. 2019, 149, 103989. [Google Scholar] [CrossRef]
  20. Kokosa, J.M. Principles for developing greener liquid-phase microextraction methods. Trends Anal. Chem. 2023, 167, 117256. [Google Scholar] [CrossRef]
  21. El-Deen, A.K.; Shimizu, K. Deep Eutectic Solvents as Promising Green Solvents in Dispersive Liquid–Liquid Microextraction Based on Solidification of Floating Organic Droplet: Recent Applications, Challenges and Future Perspectives. Molecules 2021, 26, 7406. [Google Scholar] [CrossRef]
  22. Dmitrieva, E.; Temerdashev, A.; Azaryan, A.; Gashimova, E. Quantification of steroid hormones in human urine by DLLME and UHPLC-HRMS detection. J. Chromatogr. B. 2020, 1159, 122390. [Google Scholar] [CrossRef]
  23. El-Deen, A.K.; Shimizu, K. Deep eutectic solvent as a novel disperser in dispersive liquid-liquid microextraction based on solidification of floating organic droplet (DLLME-SFOD) for preconcentration of steroids in water samples: Assessment of the method deleterious impact on the environment using Analytical Eco-Scale and Green Analytical Procedure Index. Microchem. J. 2019, 149, 10398. [Google Scholar]
  24. El-Deen, A.K.; Shimizu, K. Application of D-Limonene as a Bio-based Solvent in Low Density Dispersive Liquid–Liquid Microextraction of Acidic Drugs from Aqueous Samples. Anal. Sci. 2019, 35, 1385–1391. [Google Scholar] [CrossRef]
  25. Beldean-Galea, M.S.; Klein, R.; Coman, M.V. Simultaneous determination of four nonsteroidal anti-inflammatory drugs and three estrogen steroid hormones in wastewater samples by dispersive liquid-liquid microextraction based on solidification of floating organic droplet and HPLC. J. AOAC Int. 2020, 103, 392–398. [Google Scholar] [CrossRef]
  26. Alshana, U.; Göger, N.G.; Ertas, N. Dispersive liquid–liquid microextraction combined with field-amplified sample stacking in capillary electrophoresis for the determination of non-steroidal anti-inflammatory drugs in milk and dairy products. Food Chem. 2013, 138, 890–897. [Google Scholar] [CrossRef]
  27. Qiao, L.; Sun, R.; Yu, C.; Tao, Y.; Yan, Y. Novel hydrophobic deep eutectic solvents for ultrasound-assisted dispersive liquid-liquid microextraction of trace non-steroidal anti-inflammatory drugs in water and milk samples. Microchem. J. 2021, 170, 106686. [Google Scholar] [CrossRef]
  28. Xu, X.; Liang, F.; Shi, J.; Zhao, X.; Liu, Z.; Wu, L.; Song, Y.; Zhang, H.; Wang, Z. Determination of hormones in milk by hollow fiber-based stirring extraction bar liquid–liquid microextraction gas chromatography mass spectrometry. Anal. Chim. Acta 2013, 790, 39–46. [Google Scholar] [CrossRef]
  29. Shishov, A.; Nechaeva, D.; Bulatov, A. HPLC-MS/MS determination of non-steroidal anti-inflammatory drugs in bovine milk based on simultaneous deep eutectic solvents formation and its solidification. Microchem. J. 2019, 150, 104080. [Google Scholar] [CrossRef]
  30. Sajid, M. Dispersive liquid-liquid microextraction: Evolution in design, application areas, and green aspects. TRAC Trends Anal. Chem. 2022, 152, 116636. [Google Scholar] [CrossRef]
  31. Chormey, D.S.; Bodur, S.; Baskın, D.; Fırat, M.; Bakırdere, S. Accurate and sensitive determination of selected hormones, endocrine disruptors, and pesticides by gas chromatography–mass spectrometry after the multivariate optimization of switchable solvent liquid-phase microextraction. J. Sep. Sci. 2018, 41, 2895–2902. [Google Scholar] [CrossRef]
  32. Azzouz, A.; Ballesteros, E. Multiresidue method for the determination of pharmacologically active substances in egg and honey using a continuous solid-phase extraction system and gas chromatography–mass spectrometry. Food Chem. 2015, 178, 63–69. [Google Scholar] [CrossRef]
  33. Liu, H.; Lin, T.; Cheng, X.; Li, N.; Wang, L.; Li, Q. Simultaneous determination of anabolic steroids and -agonists in milk by QuEChERS and ultra high performance liquid chromatography tandem mass spectrometry. J. Cromatogr. B 2017, 1043, 176–186. [Google Scholar] [CrossRef] [PubMed]
  34. Tso, J.; Aga, D.S. A systematic investigation to optimize simultaneous extraction and liquid chromatography tandem mass spectrometry analysis of estrogens and their conjugated metabolites in milk. J. Chromatogr. A 2010, 1217, 4784–4795. [Google Scholar] [CrossRef] [PubMed]
  35. Florez, D.H.A.; de Oliveira, H.L.; Borges, K.B. Polythiophene as highly efficient sorbent for microextraction in packed sorbent for determination of steroids from bovine milk samples. Microchem. J. 2020, 153, 104521. [Google Scholar] [CrossRef]
  36. Wang, Q.L.; Zhang, A.Z.; Pan, X.; Chen, L.R. Simultaneous determination of sex hormones in egg products by ZnCl2 depositing lipid, solid-phase extraction, and ultra performance liquid chromatography/electrospray ionization tandem mass spectrometry. Anal. Chim. Acta 2010, 678, 108–116. [Google Scholar] [CrossRef] [PubMed]
  37. Hashemi, B.; Zohrabi, P.; Kim, K.H.; Shamsipur, M.; Deep, A.; Hong, J. Recent advances in liquid-phase microextraction techniques for the analysis of environmental pollutants. Trends Anal. Chem. 2017, 97, 83–95. [Google Scholar] [CrossRef]
  38. Perestrelo, R.; Silva, P.; Porto-Figueira, P.; Pereira, J.A.M.; Silva, C.; Medina, S.; Câmara, J.S. QuEChERS—Fundamentals, relevant improvements, applications and future trends. Anal. Chim. Acta 2019, 1070, 1–28. [Google Scholar] [CrossRef] [PubMed]
  39. Callao, M.P. Multivariate experimental design in environmental analysis. Trends Anal. Chem. 2014, 62, 86–92. [Google Scholar] [CrossRef]
  40. Dil, E.A.; Ghaedi, M.; Asfaram, A.; Zare, F.; Mehrabi, F.; Sadeghfar, F. Comparison between dispersive solid-phase and dispersive liquid– liquid microextraction combined with spectrophotometric determination of malachite green in water samples based on ultrasound-assisted and preconcentration under multi-variable experimental design optimization. Ultrason. Sonochem. 2017, 39, 374–383. [Google Scholar]
  41. Alinat, E.; Delaunay, N.; Archer, X.; Vial, J.; Gareil, P. Multivariate optimization of the denitration reaction of nitrocelluloses for safer determination of their nitrogen content. Forensic Sci. Int. 2015, 250, 68–76. [Google Scholar] [CrossRef]
  42. Beldean-Galea, M.S.; Vial, J.; Thiébaut, D.; Coman, M.V. Analysis of multiclass organic pollutant in municipal landfill leachate by dispersive liquid-liquid microextraction and comprehensive two-dimensional gas chromatography coupled with mass spectrometry. Environ. Sci. Pollut. Res. 2020, 27, 9535–9546. [Google Scholar] [CrossRef]
Figure 1. Chromatograms obtained at 190 nm of milk sample ((A) black color) and spiked milk sample with 100 ng of each compound ((A) green color). Chromatograms of egg sample ((B) black color) and spiked egg sample with 100 ng of each compound ((B) green color).
Figure 1. Chromatograms obtained at 190 nm of milk sample ((A) black color) and spiked milk sample with 100 ng of each compound ((A) green color). Chromatograms of egg sample ((B) black color) and spiked egg sample with 100 ng of each compound ((B) green color).
Molecules 29 00096 g001
Table 1. Maximum, minimum, and optimum extraction recoveries obtained by simulation.
Table 1. Maximum, minimum, and optimum extraction recoveries obtained by simulation.
CompoundAbbrev.Extraction Recovery %
MinimumMaximumOptimum
HydrocortisoneHCOR15.2532.0323.64
EstroneE142.5096.7769.64
17-β estradiolE260.79107.9684.37
17-α ethynilestradiolEE276.9389.3783.16
EstriolE345.0987.9766.53
KetoprofenKET48.99114.0981.54
NaproxenNAP51.92117.8584.88
IbuprofenIBU72.3198.3485.32
DiclofenacDIC69.86100.2285.04
Table 2. Figure of merits: linearity, correlation coefficient (R2), LOD, LOQ, intra-day precision, inter-day precision, extraction recovery (ER), and enrichment factor (EF).
Table 2. Figure of merits: linearity, correlation coefficient (R2), LOD, LOQ, intra-day precision, inter-day precision, extraction recovery (ER), and enrichment factor (EF).
CompoundCalibration Curve DataLOD
(µg/mL)
LOQ (µg/mL)Precision [RSD%]ER
[%]
EF
SlopeSDIntra-Inter-
HCOR42,4541145.510.090.273.132.8314.9917.64
E1148,5219617.50.99930.210.653.353.65110.5130.1
E2143,6014070.90.99980.090.282.552.91111.6130.0
EE2143,7414473.10.99750.100.312.562.87110.5131.3
E3117,9292612.20.99990.070.223.703.3574.087.1
KET76,4072193.30.99990.090.292.733.2689.3105.0
NAP304,1207921.00.99980.090.262.193.1093.2109.6
DIC149,5793557.80.99990.080.243.812.9185.1100.2
IBU244,1088562.20.99880.120.353.653.84111.2130.8
Table 3. The performances of the developed DLLME-SFO for milk and egg samples.
Table 3. The performances of the developed DLLME-SFO for milk and egg samples.
CompoundMilk Amount (ng) *Egg Amount (ng) **ER
(%)
EFMilk
(µg/L)
Egg
(µg/kg)
Initial FoundInitialFoundMilkEggMilkEggMDLMQLMDLMQL
HCORnd10.47nd10.3112.3212.1314.494.326.2118.6320.8362.50
E10.1186.060.2883.40101.1297.79118.9634.861.775.466.0218.65
E20.0688.260.2689.92103.76105.48122.0737.600.742.292.397.45
EE21.1783.05nd88.8996.32104.58113.3237.280.882.742.688.32
E30.0863.320.3564.2974.4975.6487.6426.970.802.512.608.16
KETnd77.860.1776.0891.6089.31107.7631.840.842.692.839.11
NAP0.4074.400.8276.7087.0689.27102.4231.830.882.542.838.17
DIC0.0774.580.1277.6387.6691.19103.1332.510.782.332.467.38
IBU0.3087.731.5793.88102.86108.60121.0138.720.992.893.109.04
* Standard deviation range: 0.34 to 1.72; ** standard deviation range: 0.47 to 2.27a; “nd”: not detected.
Table 4. Comparison of the proposed method with other reports.
Table 4. Comparison of the proposed method with other reports.
Analyzed CompoundsMethodMatrixSample AmountExtractantLOQER (%)Ref.
Hormones
10 steroidsDLLMEurine3.0 mLCloroform0.25–10 µg/L70–90%[22]
9 steroidsDLLME-SFODwater5 mL2-dodecanol1.0–9.7 µg/L41–105%[23]
9 steroidsHF-SEBLLMEmilk 10 mLEthyl acetate0.07–0.19 μg/L93.6–104.6%[28]
Progesterone, prednisolone, estradiolMEPSmilk5 mLPolythiophene16 μg/L88.29–98.68%[35]
NSAIDs
Indomethacin, flufenamic acid, nimesulide, phenylbutazoneDLLMEwater5 mLD-limonene0.36–2.69 µg/L80.99–104.92%[24]
Diclofenac, ibuprofen ketoprofen, naproxen, E2, EE2, E3DLLME-SFOwastewater101-undecanol0.22–1.29 µg/L59.3–92.5[25]
Etodolac, naproxen, ketoprofen, diclofenac, flurbiprofen DLLME-FASS-CEmilk, dairy products2.0 gChloroform10.0–43.7 μg/kg77.4–109.3% [26]
Ibuprofen, diclofenac, oxaprozin, salicylic acidUA-HDES-DLLMEwater, milk30 mLHDES1–5 μg/L79.42–107.52%[27]
Diclofenac, mefenamic acid, flurbiprofen, ketoprofen LLME-DESmilk10 g Menthol0.01–0.03 μg/kg82–91%[29]
Diclofenac, ibuprofen, ketoprofen, naproxen, E1, E2, E3, EE2DLLME-SFOmilk,
egg
10 mL,
3 g
1-undecanol2.29–5.46 µg/L
7.38–18.65 µg/kg
74.49–108.6%This work
HF-SEBLLME—hollow fiber-based stirring extraction bar liquid–liquid microextraction; MEPS—microextraction in packed sorbent; DLLME-FASS-CE—dispersive liquid–liquid microextraction coupled with field-amplified sample stacking in capillary electrophoresis; LLME-DES—liquid–liquid microextraction with deep eutectic solvent; UA-HDES-DLLME—ultrasound-assisted-hydrophobic deep eutectic solvents with dispersive liquid–liquid microextraction.
Table 5. The minimum, central point, and maximum value of the variables used for experimental design modeling.
Table 5. The minimum, central point, and maximum value of the variables used for experimental design modeling.
VariablesValues
Lowest (−1)Central Point (0)Highest (+1)
NaCl (mg) (X1)0250500
Disperser (µL) (X2)50175300
Extractant (µL) (X3)4070100
pH (X4)257
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Herghelegiu, M.C.; Pănescu, V.A.; Bocoș-Bințințan, V.; Coman, R.-T.; Berg, V.; Lyche, J.L.; Bruzzoniti, M.C.; Beldean-Galea, M.S. Simultaneous Determination of Steroids and NSAIDs, Using DLLME-SFO Extraction and HPLC Analysis, in Milk and Eggs Collected from Rural Roma Communities in Transylvania, Romania. Molecules 2024, 29, 96. https://doi.org/10.3390/molecules29010096

AMA Style

Herghelegiu MC, Pănescu VA, Bocoș-Bințințan V, Coman R-T, Berg V, Lyche JL, Bruzzoniti MC, Beldean-Galea MS. Simultaneous Determination of Steroids and NSAIDs, Using DLLME-SFO Extraction and HPLC Analysis, in Milk and Eggs Collected from Rural Roma Communities in Transylvania, Romania. Molecules. 2024; 29(1):96. https://doi.org/10.3390/molecules29010096

Chicago/Turabian Style

Herghelegiu, Mihaela Cătălina, Vlad Alexandru Pănescu, Victor Bocoș-Bințințan, Radu-Tudor Coman, Vidar Berg, Jan Ludvig Lyche, Maria Concetta Bruzzoniti, and Mihail Simion Beldean-Galea. 2024. "Simultaneous Determination of Steroids and NSAIDs, Using DLLME-SFO Extraction and HPLC Analysis, in Milk and Eggs Collected from Rural Roma Communities in Transylvania, Romania" Molecules 29, no. 1: 96. https://doi.org/10.3390/molecules29010096

APA Style

Herghelegiu, M. C., Pănescu, V. A., Bocoș-Bințințan, V., Coman, R. -T., Berg, V., Lyche, J. L., Bruzzoniti, M. C., & Beldean-Galea, M. S. (2024). Simultaneous Determination of Steroids and NSAIDs, Using DLLME-SFO Extraction and HPLC Analysis, in Milk and Eggs Collected from Rural Roma Communities in Transylvania, Romania. Molecules, 29(1), 96. https://doi.org/10.3390/molecules29010096

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