Open Access Article
This Open Access Article is licensed under a
Creative Commons Attribution 3.0 Unported Licence

Elemental composition as a tool for the assessment of type, seasonal variability, and geographical origin of wine and its contribution to daily elemental intake

S. Đurđića, M. Pantelićb, J. Trifkovića, V. Vukojevića, M. Natića, Ž. Tešića and J. Mutić*ac
aUniversity of Belgrade, Faculty of Chemistry, P.O. Box 51, 11158 Belgrade, Serbia
bInnovation Centre of Faculty of Chemistry Ltd, Studentski trg 12-16, 11000, Belgrade, Serbia
cGhent University Global Campus, Incheon, South Korea. E-mail: jelena.mutic@ghent.ac.kr

Received 12th October 2016 , Accepted 2nd December 2016

First published on 12th January 2017


Abstract

The elemental profiles of 63 red and white wine samples from four different regions in Serbia were investigated. Twenty-one elements were analysed (Ca, Mg, Na, K, Fe, Mn, Cu, Zn, Co, Se, Cr, V, Ni, Cd, As, Al, Sb, Pb, Ba, Rb, and Be) by inductively coupled plasma quadrupole mass spectrometry (ICP-Q-MS) and inductively coupled plasma with optical emission spectrometry (ICP-OES). A pattern recognition method was applied in order to classify and differentiate type, seasonal variability, and geographical origin of the wine. Dietary mineral intake for elements was calculated in order to assess their contribution to daily intake. The most important descriptors for discrimination among red and white wine samples were Be, Al, Rb, Mg, K, Cu, Mn, and Na, in descending order. The variables Cd, Pb, As, Sb, V, Na, K, and Zn have the highest influence on vintage-to-vintage classification of red wines. Furthermore, the model revealed the existence of three groups of descriptors for different regions of production. All obtained statistical models confirmed that data from the elemental content of wine samples could be used for accurate prediction of wine type, seasonal variability, and regional origin.


Introduction

Determination of the elemental composition of wines is useful for many reasons. Firstly, the concentration of elements in wine is useful information to viticulturists and oenologists for controlling the process of obtaining high-quality wine.1 Secondly, the elemental composition could be used as a wine fingerprint and represents one of the criteria for evaluating the authenticity of wine.2 Currently, determination of food authenticity is an important issue in quality control. However, the elemental composition of wines is influenced by numerous factors such as soil in the vineyard, wine processing equipment, and vinification.3 Based on these factors, the elements in wine can be classified into two groups: endogenous and exogenous.4 The most abundant are endogenous elements (Ca, Mg, Zn, Fe, P, Na, and K) that are related to the grape variety and maturity, type of soil in the vineyard, and climatic conditions. The exogenous elemental content (Al, Cd, Cr, Cu, Fe, and Zn) depends on external impurities during the growth of grapes and vinicultural and winemaking practices.1,5,6 Anthropogenic factors, such as application of pesticides, fungicides, and fertilisers during the growing season, can lead to an increase in Cd, Cu, Mn, As, and Zn in the resulting wine. The presence of Pb in wines can originate from sources like traffic, fertilisers, vessels, and pumps used during vinification.7 Finally, recent data indicate that some beverages, including wine, contribute to the total dietary intake of certain trace elements (B, Ba, Co, Mn, Ni, Rb, Sb, Tl, and V)8 and iron as well.9 Thus, determination of the elemental concentrations in wine allows calculation of their daily dietary intake from wine, which is of particular importance for toxic elements. Various instrumental techniques have been used to classify wine variety such as infrared spectroscopy (IR),10 nuclear magnetic resonance (NMR),11 gas chromatography (GC),12 high-performance liquid chromatography (HPLC),13,14 inductively coupled plasma optical emission spectrometry (ICP OES),5,15 and inductively coupled plasma mass spectrometry (ICP MS).4,16 The advantages of ICP-based techniques for the determination of trace elements are numerous: high sensitivity, a wide range of linearity, and simultaneous multielement analysis. Furthermore, a simple sample dilution has been proposed as the most advantageous because it is time-efficient, prevents contamination, and reduces the number of operation steps. According to Grindlay et al.,2 matrix effects were almost eliminated when 1[thin space (1/6-em)]:[thin space (1/6-em)]5 and 1[thin space (1/6-em)]:[thin space (1/6-em)]10 (v/v) dilution factors were employed for ICP OES and ICP MS analyses, respectively. In recent years, chemometric pattern-recognition techniques have also been applied, contributing to characterizing and classifying wine samples.15 However, wine quality control is still highly dependent on wine tasters.17 A human sensory panel can provide information about the sensory properties of wine that is far richer than can be provided by instrumental devices alone.

Serbia has a very long tradition of wine production due to its favourable climate and good geographical conditions, but export capacity is very small due to the lack of competitiveness in price as a consequence of the high cost of production in relatively small wineries. The elevated prices are justified by the wine quality and by the relationship between the quality and the region of origin. The evaluation of the quality and authenticity of the wine is a key factor in establishing cost-effective wine, which would help numerous small Serbian wineries to enter this highly competitive market. In that sense, the aim of this work was, firstly, to obtain basic information about the elemental composition of genuine Serbian wines. The second objective was to apply chemometric techniques, such as principal component analysis (PCA) and partial least squares-discriminant analysis (PLS-DA), in order to establish parameters that could be used for classification and differentiation of two types of wine (white and red), to determine which elements could be affected by seasonal variability between wines from one winery, and to try to establish the regional origin of red wine samples. A significant number of samples supplied by different wineries were collected from three different regions of Serbia. To the best of our knowledge, this is the first report on the influence of vintage on the elemental content of red wine samples analysed with chemometrics. The third objective was to evaluate the content of essential and toxic elements in wine samples in order to study their nutritional significance and to estimate the daily mineral intake provided by the consumption of this beverage.

Experimental

Site description and wine samples

A total of 63 wine samples were analysed (46 red wines and 17 white wines). Samples originated from four different regions in Serbia: Belgrade (n = 39), Central Serbia (n = 9), Vojvodina (n = 6), and South Serbia (n = 9). The regions, vineyards, wineries, and vintages are presented in Table S1 (ESI). The geographic distribution of wine samples is shown on the map in Fig. 1. Wines from the Belgrade region originated from “Radmilovac”, an experimental station which belongs to the Faculty of Agriculture, University of Belgrade. The location belongs to the Šumadija–Velika Morava wine region (Central Serbia – 44°45′24.66′′N–20°34′54.50′′E, elevation 153 m above sea level). All wines were provided by the wineries as finished wines in 750 mL glass bottles with cork stoppers and were stored at 3–4 °C before analysis. One bottle was used for each sample, and three replicates were taken.
image file: c6ra25105f-f1.tif
Fig. 1 Map of the geographic distribution of the wine samples.

Reagents and chemicals

ICP multi-element stock solutions (VHG standards, Manchester, UK) containing 1000 mg L−1 were used for calibration. Distilled, deionised water (Milli-Q Water System, Millipore Corporation, Bedford, MA) was used throughout. The isotopes 6Li, 45Sc, 115In, and 159Tb (VHG standards, Manchester, UK) were used as internal standards to cover the full mass range. All other chemicals were supplied by Merck (Darmstadt, Germany).

Sample preparation

For determination of the elemental content in wine, samples were diluted (1[thin space (1/6-em)]:[thin space (1/6-em)]10) with water containing 2% (v/v) nitric acid (Merck, Germany). Standards were prepared with 1% (v/v) ethanol and 2% (v/v) nitric acid in order to provide the same concentrations of ethanol and nitric acid as the samples.18 The certified reference material (CRM 1640a, trace elements in natural water) was prepared in the same manner as the standards. The samples were taken from their packages and filtered in a G3 Gooch filter to guarantee the absence of solid particles in order to avoid clogging the nebuliser.19

Instrumentation

ICP-OES (iCAP 6500 Duo Thermo Scientific, UK) was used for determination of calcium, sodium, potassium, magnesium, rubidium, iron, and arsenic. For the determination of arsenic, the system was equipped with an integrated unit for hydride generation.20 Table S2 (ESI) shows the analytical lines used for each element and the instrumental conditions. The limit of detection (LOD) for each element was calculated21 and is shown in Table S2. An inductively coupled plasma quadrupole mass spectrometer (ICP-QMS, Thermo Scientific Xseries 2, UK) was used for measurements of trace elements in wine. Fourteen elements (Ba, Be, Cd, Co, Cr, Ni, Sb, Pb, Se, V, Al, Mn, Zn, and Cu) were measured in no gas and/or collision cell mode.22 High-purity He and H2 (99.9999% H2, Messer, Serbia) were used as a collision gas (7% hydrogen in helium). The use of a cooled spray chamber was required in order to minimize the effect of the ethanol matrix. Measured isotopes and instrument operating conditions are given in Table S2 (ESI).

Due to the lack of a reference material for wine, the accuracy of the measurements of elements was verified by CRM 1640a (trace elements in natural water) which contained all analysed elements. The results of the analysis showed good agreement with the certified levels of the standard (±10%).

Statistical analysis

Descriptive statistics and the Mann–Whitney U-test were performed by a demo version of the NCSS statistical software.23 The Mann–Whitney U-test was carried out at a significance level of P = 0.05. PCA and PLS-DA were carried out by PLS_Tool Box, v.6.2.1, for MATLAB 7.12.0 (R2011a).

All data were auto-scaled prior to any multivariate analysis to bring values to compatible units. Metal content served as the input data matrix. The PCA was performed using a singular value decomposition algorithm with a 0.95 confidence level for Q and T2 Hotelling limits for outliers. The analysis was based on a correlation matrix, and factors with eigenvalues greater than 1 were retained. The PLS-DA used the SIMPLS algorithm without forcing orthogonal conditions on the model in order to condense Y-block variance into the first latent variables. The models were validated using a venetian blinds validation procedure. The quality of the models was monitored with two different sets of parameters. The values of Rcal2, the cumulative sum of squares of the Ys explained by all extracted components, RCV2, the cumulative fraction of the total variation of the Ys that can be predicted by all extracted components, and RPRED2, the cumulative fraction of the total variation of the Ys that can be predicted by test components should be as high as possible. In contrast, RMSEC (Root Mean Square Errors of Calibration), RMSECV (Root Mean Square Errors of Cross-Validation), and RMSEP (Root Mean Square Errors of Prediction) should be as low as possible, with minimal differences between them.24

Calculation of daily elements intake

A volume of 100 mL of wine and the 70 kg body weight of an average consumer (European Food Safety Authority, EFSA)25 were used to calculate elemental intakes per day. Daily mineral intake (DMI, %) and recommended daily allowance (RDA) values were calculated according to the European Economic Community (EEC).26 DMI was calculated using DMI = C × 100/RDA; where C is the elemental content (mg) in 100 mL of wine. According to the regulation EEC 90/496, the contribution is important if 100 mL contains at least 15% of the RDA. Daily Intake (DI, %) of As, Cd and Pb was calculated for 100 mL of red and white wine using DI = C × 100/MDI where MDI corresponds to the maximum tolerable daily intake established by the EFSA.

Results & discussion

Major and trace elements in wines

Twenty one elements, including major (Ca, Mg, Na, K, Rb, Fe, and Mn) and trace (Al, Cu, Zn, Be, V, Co, Ni, Cd, Sb, Ba, Cr, As, Se, and Pb) elements, were analysed in the set of 63 Serbian wine samples. The summarized parameters (mean, median, standard deviation, minimum and maximum value) obtained for the elemental content of wine samples of different types (red and white), seasonal variability, and geographical origin are presented in Tables 1–3. The concentration of major and trace metals in wines from different viticulture countries are presented in Table S3 (ESI). As expected, potassium was the most abundant element in all investigated red and white wine samples (Tables 1–3) since K is an essential element for the growth and development of plants and is often a component of fertiliser.21 According to our results, the K concentration was higher in red compared to white wines. The measured values ranged between 413 and 1170 mg L−1 for red wines and from 298 to 560 mg L−1 for white wines (Table 1). Similar K content was found in all investigated regions (Table 3). These results agree with values reported in the literature.15,27 Magnesium and calcium were the second most abundant elements found in our study (Tables 1–3). The magnesium concentration was higher in red wines (mean 94.9 mg L−1, values between 53.0 to 124.8 mg L−1) than in white wines (mean 84.6 mg L−1, values between 38.0 to 89.4 mg L−1), while calcium concentrations were similar in both types of wine (mean values of 83.1 mg L−1 and 84.6 mg L−1 for red and white wines, respectively) (Table 1). Paneque et al.28 observed that the Ca concentration depended on wine maturity. The young wines had slightly lower Ca content (mean 64.1 ± 16.1 mg L−1) than aged wines (mean 88.4 ± 17.7 mg L−1). The values obtained for the Mg and Ca contents in our selected wines were in good agreement with the results for Macedonian,5 Serbian,29 Croatian,13 and Czech30 wines. On the other hand, our Ca and Mg contents were significantly higher than published data for wines from Argentina31 and Belgium32 (Table S3, ESI). In contrast with Mg, the average content of Na was significantly higher in white wines than in red wines (Table 1). In the studied wines, Na content differed among the regions and decreased in the order Vojvodina > Central Serbia > South Serbia. The highest concentration of Na (mean 23.0 ± 11.7 mg L−1) (Table 3) was found in wines from Vojvodina region compared with the other three wine production areas. These results agree with Ražić and Onia29 where the obtained concentration of sodium in wine from North Serbia was 33 ± 11 mg L−1. The sodium content in our study agreed with results published on Serbian29 and Czech30 wines, but was lower compared to Spanish27 red wines. The higher content of sodium in Spanish wines has been attributed to the vicinity of the vineyards to the ocean.1 The rubidium concentration was significantly higher in red wines (mean values 2.57 mg L−1) compared to white wines (1.23 mg L−1) (Table 1). Similar data was obtained by Geana et al.33 for Romanian white wines (ranged from 0.22 mg L−1 to 2.066 mg L−1) and by Kment for Czech wine30 (ranged from 0.09 to 2.47 mg L−1), but rubidium content found in Belgian32 wines was lower (Table S3). Al, Cu, Mn, and Zn were also present in amounts similar to previously published results.13,27,30,33,34 These elements in our wines were significantly higher than in Belgian32 and Argentinian31 wines. The average values obtained for V were 3.07 μg L−1 and 1.54 μg L−1 in white and red wines, respectively (Table 1). These results indicated that Serbian wines are moderately rich in vanadium, have less vanadium than Macedonian,5 Spanish27 or Czech30 wines, and have more vanadium than Belgian32 ones. Higher concentrations of V in wine could be associated with storage.35 The content of trace elements (Be, Co, Sb, and Se) found in Serbian wines agreed with literature data (Table S3).5,16,30,33
Table 1 Descriptive statistics obtained from the analysis of metal content in two wine types
Wine type   K (mg L−1) Mg (mg L−1) Ca (mg L−1) Na (mg L−1) Fe (mg L−1) Rb (mg L−1) Mn (μg L−1) Al (μg L−1) Zn (μg L−1) Cu (μg L−1) V (μg L−1) Ba (μg L−1)
a Differences between two set of data is significant when P value is less or equal to P = 0.05.
Red wine (n = 46) Mean 690 94.9 83.1 8.48 1.32 2.58 1194 225 635 131 1.54 90.3
Stdev 173 15.7 21.3 7.45 0.93 0.72 681 186 263 135 2.58 66.4
Median 656 97.3 80.4 5.70 1.23 2.44 994 175 598 81 0.34 73.5
Min 413 53.0 41.2 2.94 0.01 1.25 385 6 287 24 0.02 20.6
Max 1167 124.8 131.2 37.0 6.01 4.70 3310 800 1499 646 14.62 301.2
White wine (n = 17) Mean 396 66.6 84.6 17.6 1.54 1.24 550 1145 977 558 3.07 79.9
Stdev 71 14.5 16.2 12.0 0.68 0.28 178 469 693 515 1.75 33.7
Median 400 68.1 83.8 13.7 1.37 1.20 562 1004 837 501 3.40 70.5
Min 298 38.0 55.3 4.5 0.36 0.79 294 514 215 33 0.83 35.4
Max 560 89.4 115.7 34.3 2.80 1.71 885 2189 2585 1684 7.22 157.4
Man–Whitney U-testa P value <0.0001 <0.0001 0.5562 0.0013 0.1371 <0.0001 <0.0001 <0.0001 0.0829 0.0008 0.0001 0.8892
H0 Reject Reject Accept Reject Accept Reject Reject Reject Accept Reject Reject Accept

Wine type   Pb (μg L−1) Ni (μg L−1) Cr (μg L−1) Sb (μg L−1) As (μg L−1) Co (μg L−1) Be (μg L−1) Cd (μg L−1) Se (μg L−1)
Red wine (n = 46) Mean 47.8 37.5 5.49 8.78 16.1 3.89 0.129 1.99 3.40
Stdev 40.4 28.4 4.90 4.76 10.9 2.28 0.196 2.53 3.02
Median 26.3 27.8 4.73 8.50 18.1 3.59 0.023 0.82 2.31
Min 9.3 8.5 0.10 0.66 1.2 0.40 0.001 0.07 0.06
Max 168.5 123.6 20.67 18.65 37.9 9.16 1.028 11.1 10.52
White wine (n = 17) Mean 83.8 88.0 1.85 8.95 21.2 3.96 4.34 1.31 4.98
Stdev 52.5 122.9 1.72 5.92 9.46 2.60 1.55 1.47 2.07
Median 68.8 41.4 1.34 10.54 23.0 3.65 4.00 0.71 5.39
Min 16.0 8.58 0.10 0.06 2.00 0.50 0.39 0.14 1.19
Max 188.2 420.5 6.59 17.77 35.7 9.60 7.01 4.75 8.00
Man–Whitney U-test P value 0.0051 0.0492 0.0024 0.7217 0.0945 0.9938 <0.0001 0.9629 0.0132
H0 Reject Reject Reject Accept Accept Accept Reject Accept Reject


Table 2 Descriptive statistics obtained from the analysis of metal content in wine samples from different vintages
Vintage   K (mg L−1) Mg (mg L−1) Ca (mg L−1) Na (mg L−1) Fe (mg L−1) Rb (mg L−1) Mn (μg L−1) Al (μg L−1) Zn (μg L−1) Cu (μg L−1) V (μg L−1) Ba (μg L−1)
2012 (A) Mean 539 110.9 89.7 5.87 1.77 2.38 776 250 1013 230.2 0.82 66.4
Stdev 155 9.7 14.7 0.92 1.77 0.72 225 127 271 208.5 1.20 15.5
Median 493 110.3 84.2 6.09 1.13 2.25 784 187 920 131.3 0.20 61.5
Min 413 97.0 73.3 4.66 0.70 1.58 496 124 738 80.9 0.03 48.1
Max 903 124.8 112.9 7.30 6.01 3.69 1169 488 1499 645.8 3.32 88.6
2013 (B) Mean 635 94.5 78.0 4.41 1.42 2.53 966 112 420 63.1 0.88 43.5
Stdev 188 13.6 14.0 1.22 0.37 0.72 240 112 134 21.5 0.87 17.9
Median 613 95.4 75.7 4.01 1.36 2.58 995 66 357 71.1 0.34 38.1
Min 430 59.3 55.0 2.94 0.86 1.25 614 6 292 24.4 0.09 20.6
Max 1167 109.9 100.7 7.08 2.26 4.22 1384 356 742 89.2 2.33 75.4
2014 (C) Mean 897 99.1 120.1 3.98 1.23 3.37 1036 221 671 153.0 0.59 73.2
Stdev 73 4.9 7.9 0.57 0.24 1.03 125 160 97 116.8 0.80 7.9
Median 915 99.3 118.3 3.80 1.23 3.12 1015 165 690 137.4 0.23 76.1
Min 797 93.2 112.7 3.55 0.99 2.51 907 99 549 49.1 0.10 61.9
Max 961 104.5 131.2 4.78 1.49 4.70 1207 455 757 287.9 1.79 78.8
Kruskal–Wallis test P value 0.0120 0.0181 0.0047 0.0133 0.6873 0.1717 0.1144 0.0918 0.0002 0.0041 0.6565 0.0127
Z-Test C(A, B) A(B) C(A, B) B(A, C) A(B) A(B) A(B, C)

Vintage   Pb (μg L−1) Ni (μg L−1) Cr (μg L−1) Sb (μg L−1) As (μg L−1) Co (μg L−1) Be (μg L−1) Cd (μg L−1) Se (μg L−1)
2012 (A) Mean 44.1 34.5 3.63 13.56 19.5 3.65 0.049 1.07 2.88
Stdev 39.2 28.7 1.76 2.57 4.8 1.98 0.052 1.43 1.70
Median 26.0 21.9 3.59 12.46 19.0 3.28 0.023 0.55 3.57
Min 15.8 16.9 0.22 10.42 12.6 0.50 0.011 0.07 0.42
Max 128.6 102.1 5.89 17.51 26.7 7.35 0.138 4.44 4.76
2013 (B) Mean 49.4 18.6 2.33 6.18 23.2 3.12 0.042 2.84 3.40
Stdev 34.7 8.9 1.92 3.13 4.9 2.35 0.040 2.39 2.61
Median 44.2 15.8 2.12 6.56 22.1 2.49 0.023 2.82 3.57
Min 9.3 8.8 0.10 0.66 15.2 0.50 0.023 0.07 0.42
Max 100.3 41.1 5.10 11.13 30.7 6.81 0.131 6.43 6.67
2014 (C) Mean 55.7 26.2 4.27 6.89 20.2 4.03 0.103 3.33 6.03
Stdev 75.4 3.4 2.21 5.86 3.4 2.90 0.096 5.19 2.46
Median 20.8 25.5 4.26 4.95 21.5 3.65 0.087 0.87 6.67
Min 12.6 23.3 2.15 2.20 15.2 1.01 0.023 0.49 2.82
Max 168.5 30.7 6.42 15.45 22.7 7.80 0.214 11.10 7.96
Kruskal–Wallis test P value 0.8704 0.0249 0.1533 0.0022 0.2887 0.7373 0.4723 0.3384 0.1319
Z-Test A(B, C) B(A, C)


Table 3 Parameters of descriptive statistics obtained from metal content analysis of wine samples from different regions
Regional origin   K (mg L−1) Mg (mg L−1) Ca (mg L−1) Na (mg L−1) Fe (mg L−1) Rb (mg L−1) Mn (μg L−1) Al (μg L−1) Zn (μg L−1) Cu (μg L−1) V (μg L−1) Ba (μg L−1)
Central Serbia (1) Mean 762 88.2 74.5 11.00 0.64 2.63 1632 325 617 176.4 2.73 175.2
Stdev 104 14.9 12.4 5.82 0.54 0.64 1056 247 178 184.4 4.56 76.5
Median 783 92.9 74.6 8.98 0.50 2.32 1172 305 601 110.7 1.72 138.9
Min 573 53.1 53.8 3.07 0.01 1.99 385 9 287 44.7 0.20 94.3
Max 877 102.6 93.9 21.26 1.62 3.69 3310 800 948 619.2 14.62 301.2
Vojvodina (2) Mean 678 101.9 78.0 23.02 2.01 2.13 1884 312 586 142.1 2.80 89.4
Stdev 74 16.3 7.3 11.68 0.52 0.32 718 201 207 38.4 2.62 47.4
Median 677 107.6 78.9 23.44 1.83 2.19 1921 321 511 150.0 3.20 79.1
Min 607 75.6 68.7 5.65 1.42 1.77 774 9 375 92.6 0.20 27.9
Max 798 118.7 86.0 37.05 2.81 2.51 2609 574 834 182.3 6.28 155.1
South Serbia (3) Mean 735 78.0 71.4 7.33 0.91 2.72 1141 148 567 68.3 0.67 99.6
Stdev 179 11.4 29.3 5.81 0.45 0.74 645 138 132 15.0 0.70 81.3
Median 621 76.5 67.2 4.82 0.69 2.35 895 122 550 72.5 0.20 62.8
Min 550 66.9 41.2 4.02 0.52 2.02 594 10 403 40.1 0.19 30.9
Max 998 100.1 127.4 20.30 1.87 4.20 2456 437 766 80.2 1.90 260.0
Kruskal–Wallis test P value 0.4768 0.0484 0.4668 0.0293 0.0058 0.1533 0.2232 0.2862 0.8237 0.0224 0.2558 0.0817
Z-Test 2(3) 2(3) 2(1) 2(3)

Regional origin   Pb (μg L−1) Ni (μg L−1) Cr (μg L−1) Sb (μg L−1) As (μg L−1) Co (μg L−1) Be (μg L−1) Cd (μg L−1) Se (μg L−1)
Central Serbia (1) Mean 61.9 67.7 10.44 9.78 5.1 4.75 0.292 2.38 2.02
Stdev 50.6 39.2 6.25 3.27 8.7 2.05 0.313 2.80 3.29
Median 61.5 52.1 10.19 10.59 2.3 4.39 0.262 0.35 0.42
Min 11.5 8.5 0.10 4.02 1.2 2.44 0.023 0.15 0.06
Max 154.7 123.6 20.67 14.48 28.3 9.16 1.028 7.31 10.52
Vojvodina (2) Mean 53.6 30.1 6.74 6.51 13.1 4.61 0.120 1.87 2.64
Stdev 31.1 17.7 4.23 7.23 10.8 2.61 0.156 2.37 2.36
Median 43.9 18.4 6.15 2.89 9.5 5.00 0.023 1.13 1.62
Min 27.9 15.8 1.06 0.69 5.0 0.40 0.023 0.13 0.93
Max 107.0 52.7 12.88 18.65 32.1 7.59 0.382 5.85 6.67
South Serbia (3) Mean 21.8 49.7 6.11 10.14 12.3 4.24 0.135 0.54 4.38
Stdev 11.9 12.9 6.15 3.97 16.4 2.29 0.227 0.96 4.50
Median 16.8 49.0 7.70 9.38 3.5 4.53 0.023 0.13 1.64
Min 14.5 33.1 0.10 4.72 1.4 0.59 0.001 0.07 0.47
Max 47.4 70.5 15.15 16.91 37.9 7.84 0.609 2.68 10.52
Kruskal–Wallis test P value 0.0916 0.1984 0.5340 0.3049 0.0802 0.8596 0.3375 0.1035 0.2027
Z-Test


Regarding the content of toxic elements (As, Cd, and Pb) (Tables 1–3), the As content was higher than in published data (Table S3)16,27,30,31,36 while the Pb content was lower than that in Czech30 and Romanian33 wines. The average content of Cd was slightly higher than in wines from Serbia's neighbouring countries Croatia16 and Macedonia.5 Only one sample contained elevated concentrations of this element. Analysing data from Table S3, Serbian wines were concluded to contain higher amounts of essential elements (Cu, Mn, and Zn) and major elements (Ca and Mg) in comparison to Belgian32 or Argentinian31 wines. Additionally, our wines contained less Ni, Pb, and V than Turkish,36 Czech,30 and Romanian33 wines, respectively. Although Serbian wines contained higher amounts of arsenic compared to other wines, its concentrations were under the maximum acceptable limit. Due to significant deviations from the normal distribution for each of the studied variables, statistical evaluation of the differences in the elemental content in the two wine types was evaluated by the Mann–Whitney U-test, while the differences in the elemental content according to the vintage and regional origin were determined by the Kruskal–Wallis test. Tests were employed for each variable taking the appropriate variety as a single factor. The results are presented in Tables 1–3. Differences between two or three sets of data were considered significant when the P value was less than or equal to P = 0.05. In the cases where the Kruskal–Wallis test has indicated a statistically significant difference between the medians, the Kruskal–Wallis multiple-comparison Z-value test was also performed. Vintages and regions with different contents of a given metal are denoted in parentheses with a letter or number (Tables 2 and 3).

The Mann–Whitney U-test revealed that the variables K, Mg, Na, Rb, Be, Cr, Ni, Pb, Se, V, Al, Mn, and Cu governed the differences between white and red wines (Table 1) and suggest a totally different elemental profile for the two wine types. The Kruskal–Wallis test revealed that the macro elements K, Mg, Ca, and Na and trace elements Al, Cu, Ba, Ni, and Sb had statistically significant differences between vintages (Table 2). Additionally, the statistically significant differences between the metal content of samples from different geographical regions could only be observed for the elements Mg, Na, Fe, and Cu with the differentiation in samples arising from the Vojvodina region (Table 3). Pearson correlation coefficients between all elemental contents in the wine samples were determined separately for white and red wines due to the observed differences in relationships between elements (Tables S4 and S5, ESI). Significant r values at the 99% confidence level37 are represented in bold. A significant correlation between two or more elements indicates a similar ability to penetrate the grape or the existence of the same source.16 Correlation matrices (Tables S4 and S5) showed that the different elements were mutually correlated for the two wine types indicating different sources of elements in red and white wines. Due to the high number of samples and the fact that t value for the correlation is directly proportional to the number of samples, a significant r value was very low in both cases. For that reason, herein we will discuss only dependencies with r > 0.700. For white wine samples, correlations were obtained between the following elements: Pb and Zn (r = 0.9177), Pb and Cu (r = 0.8824), Zn and Cu (r = 0.9247), and Mn with Ca (r = 0.7401) (Table S4). The correlations between Pb and these two essential metals could be explained by their similarity as micronutrients or by anthropogenic influences. Furthermore, the existence of a correlation between Mn and Ca could be attributed to the type of soil, which is rich in manganese, iron oxide minerals, and hydrated silicate of Na, Ca, Al, and Mg. In red wine samples, significant correlations were observed between Ba and Mn (r = 0.7519), Ba and Ni (r = 0.7054), Cd and Pb (r = 0.7527), and Mn and Na (r = 0.7001) (Table S5). Mn, Ba, and Ni together with alkali and alkaline earth metals belong to the lithophile elements which form the main components of the corresponding soil. Therefore, their origin in wine was likely mostly from the soil. On the contrary, Cd and Pb are toxic elements with similar chemical properties, and they predominately come from anthropogenic sources.

Discrimination of wines by type, seasonal variability, and regional origin

The chemometrics technique PCA was applied in order to classify and differentiate wine type (red vs. white), seasonal variability, and wine from diverse regional sites. The PCA was carried out at the exploratory level to provide insight into the structure of data and reveal some logical pattern in the data.24 In addition, PLS-DA was used as a multivariate classification model method aimed to find mathematical models that can assign each sample to an appropriate class of wine type.

Red vs. white wines

A PCA model applied to classify samples according to wine type resulted in a seven-component model that explained 76.09% of the total variance. Obtaining low overall data variance captured by a few PCs is not unusual, especially when the variability among the samples is relatively high (naturally occurring objects, samples), and a diverse set of parameters (variables) is considered. The parameters of the PCA model, eigenvalues, and percentage variance captured by each principal component (PC) are presented in Table S6 (ESI). Mutual projections of the scores and their loadings for the first two PCs are presented in Fig. 2. The score plot (Fig. 2a) of the model revealed the existence of two distinctive groups of characteristics belonging to different wine types (white and red) separated alongside PC1. The loading plot (Fig. 2b) implies that the variables Al, Be, and Cu have the most positive impact on the direction of PC1 and denote a group of white wine samples. Additional chemical indicators of this group were Zn, Pb, Na, V, Ni, As, and Se that had a lower influence on the classification. The variables K and Rb had the highest negative influence on PC1, and Mg, Mn and Cr had lower negative influence on PC1. Together, these variables characterize the red wine type. The results of differentiation of wine type agreed with previously published articles dealing with the elemental composition of red and white wines.29,38 Such classification could be attributed to differences in the winemaking process but could also be ascribed to grape variety.1,21 In addition, the largest influence on the differentiation of wine type was the lithophile elements (K, Mg, Rb, Mn, Cr, Ba, Al, and Be), which indicates their origin from vineyard soils, similar to the results obtained by other authors.3,16,21,39 On the other hand, a different elemental composition in wine may be the result of differences in the process of vinification, i.e. the difference between red and white wines occurs due to prolonged contact of skin and seeds of grapes with the must (juice) during the production of red wines (maceration).39,40 An increase in the Fe and Cr contents in red wines could also be the result of long maceration (7–21 days), which causes a more efficient extraction of chemical elements from the grapes.1,21,41 Also, an increased As concentration may occur due to the use of groundwater for irrigation of agricultural areas, which are contaminated with arsenic.42 Some authors emphasized that groundwater with increased concentration of As was detected in Vojvodina, which is one of our investigated regions.16 The high impact of Cu on differentiation could be the result of its accumulation in soil after the application of Bordeaux mixture or other copper-based fungicides or the use of equipment based on this metal.5,15,29 Also, the increase of Cu concentration may occur due to adding copper salts to remove H2S.1 The endogenous origin of zinc in wines is based on easy absorption of this element by plants due to its high mobility in soil.43 In contrast, the exogenous origin of zinc in wines is the consequence of long contact of wine with stainless steel wine-making machinery and pipes which were used for handling and storing the wine.31
image file: c6ra25105f-f2.tif
Fig. 2 Classification models for wine. (a) PCA scores plot for red and white wine samples, (b) PCA loadings plot for red and white wine samples, (c) PLS-DA score plot, (d) VIP scores for the PLS-DA model, (e) regression coefficients of the PLS-DA model for red wine samples, and (f) regression coefficients of the PLS-DA model for white wine samples.

Samples of different wine types were also modelled simultaneously using PLS-DA. The number of the latent variables (LVs) was selected based on the minimum value of RMSECV, which was achieved with one LV. Classification and validation results were expressed as Rcal2, RCV2, Rpred2, RMSEC, RMSECV, and RMSEP values. Two models were statistically significant, with relatively high values of Rcal2, RCV2, and Rpred2 (0.8484, 0.8094 and 0.8382, respectively), as well as low differences between RMSEC, RMSECV, and RMSEP values (0.169, 0.189, and 0.193, respectively). Hence, data from the elemental content of wine samples allows accurate prediction of wine type and provides a useful tool for their determination (Fig. 2c). The contribution of variables that had the strongest influence on differentiation between types was analysed using the variable importance in projection (VIP) value (Fig. 2d). The variables with a VIP score higher than one were considered the most relevant for classification of the wine samples by type. The most important descriptors for discrimination among red and white wine samples were Be, Al, Rb, Mg, K, Cu, Mn, and Na, in descending order. The standardized regression coefficients that indicate in which direction (i.e. positively or negatively) the element is contributing to the model are shown on Fig. 2e and f. The regression coefficients indicated identical but opposite influence of the variables in the two models. The highest positive impacts on classification of red wines arose from the elements Rb, K, Mg, Mn, and Cr. The model for white wines indicated high positive regression coefficients for Be, Al, Cu, Na, Ni, Pb, Zn, V, and Se. These differences could be attributed to differences in winemaking techniques between red and white grapes such as long maceration, length of time in contact with the grape skins, and the filtration process typically undergone by white wines.1,38–40,44

Vintage-to-vintage differences in red wines

The types of grapes that can be grown and overall wine quality that certain regions produce are a result of the baseline climate, while climate variability determines vintage-to-vintage quality differences.45 Many individual weather and climate factors can affect grape growth and wine quality, such as solar radiation, heat accumulation, temperature extremes, precipitation, wind, and extreme weather events such as hail. However, the growing season length and temperatures are critical aspects due to their major influence on the ability to ripen grapes to optimum levels of sugar, acid, and flavour in order to maximize a quality of wine.45

Annual reports for 2012, 2013, and 2014 about average air temperature, total rainfall, and total sunshine hours in Serbia were obtained from the Republic Hydrometeorological Service of Serbia (RHSS).46 According to these data, the three chosen vintages differed by rainfall and number of sunny days. The year 2012 had a high number of sunny days, an average temperature of 14.0 °C, and low rainfall (563 mm); in 2013, the rainfall was within normal limits (680.0 mm) and the average temperature was 11.6 °C. The average rainfall in the Serbia in 2014 was 1017.9 mm, which was the rainiest year in 60 years. The effect of vintage on the average content of some selected elements is presented in Fig. 3. Significant differences were found between the average content of Zn and Fe in the wine samples in 2012 where they were higher in comparison with other two years. The same trend was observed for the trace elements Sb and Ni. The content of Cr, Co, Cd, and Se observed in samples from 2014 was higher than in those from the other two other vintages. Similar results were also found for the content of Pb and Ba (Fig. 3). The variation of soil pH is known to be highly dependent on precipitation amount,14 and the (bio)availability of some elements from soil is influenced by water (in this case from rain). Therefore, a high amount of precipitation changed soil conditions and led to leaching of some elements dependent on their bound in soil substrate to make them available for plants. The changes in ionic strength of water and pH affect leaching of elements which are usually in ion-exchangeable forms in soil such as: Cu, Pb, Ni, As, Co, Cd, and Mg.47


image file: c6ra25105f-f3.tif
Fig. 3 Results from different vintages represented as an average of selected measured variables of the wines.

The influence of seasonal variability on the elemental content of red wine samples obtained from the same vineyard and with the same production procedure in the winery Radmilovac (Smederevo, Belgrade region) was analysed by PCA. To our knowledge, this is the first report of vintage-to-vintage influence on the elemental profile of wine. The PCA model resulted in a seven-component model that explained 78.99% of the total variance. The parameters of the PCA model, eigenvalues, and percentage variance captured by each PC are presented in Table S6 (ESI), and mutual projections of factor scores and their loadings are presented in Fig. 4. Score plots (Fig. 4a and b, seasonal classification) of the model revealed the existence of three distinctive groups of characteristics belonging to different vintages with some overlap of samples from 2013 and 2014. The loading plot (Fig. 4c) implies that variables Cd, Pb, As, Sb, V, Na, K, and Zn have the highest influence on the classification. Interestingly, Cd, Pb, As, and Sb are most probably derived from anthropogenic sources rather than from natural sources. Pb and Cd come predominately from atmospheric pollution or from fungicide treatment. Among these elements, Na, K and Zn are elements that derived from both natural and artificial sources with their concentration determined by many different factors. The results of the PCA confirm that seasonal variability does have a significant influence on the elemental profile of red wines.


image file: c6ra25105f-f4.tif
Fig. 4 PCA for seasonal and regional classifications: (a) 3D score plots, (b) 2D score plots, and (c) loading plots.

Regional origin of red wines

Previously presented results revealed that the elemental composition of wine is closely related to the vineyard soil of its grapes.39,48 Namely, the same wine type might have quite different chemical composition, as accumulation of phytochemicals depends on climatic conditions (sunlight, moisture), soil characteristics, and the presence of different minerals in the soil.33,43

We tried to determine regional origin of red wine samples collected from three statistical regions of Serbia (Vojvodina, Central region, and South region) and from different wineries within each region, by using the elemental content and chemometrics. The PCA model resulted in a seven-component model that explained 82.92% of the total variance. Parameters of the PCA model, eigenvalues, and percentage variance captured by each PC are presented in Table S6. The score plots (Fig. 4a and b, regional classification) of the model revealed the existence of three groups of characteristics associated with different regions of production. Using this classification, we could assume that the regional origin of red wine from Serbia could be determined. However, we should emphasize that the three samples in the left upper part of the score plot (circled, Fig. 4b) represented samples whose grapes originated from the observed regions but were produced in Radmilovac, a winery that did not belong to the regions included in this analysis. Since each of the observed regions includes several different wineries whose production procedure does not have influence on classification, we assumed that the winery Radmilovac differed from all other wineries in Serbia. A similar conclusion was found by Atanacković et al.49 These authors studied the influence of winemaking techniques on the resveratrol content, total phenolic content, and antioxidant potential of red wines made at the oenological station Radmilovac from the grape varietals Merlot (M), Cabernet Sauvignon (KS), Pinot noir (PN) and Prokupac (P). Their results implied that the use of thermovinification procedures could enhance the phenolic composition. Obviously, besides the composition of soil, vintage, and grape varietal, the winery also contributes to the fingerprint of wine. The existence of three groups of characteristics associated with different regions of production could be explained by different types of soil in Serbian regions. Samples from the Central region form a cluster in the right lower part of score plot and showed higher content of the elements Al, Mn, Be, Ba, Cr, and Ni (Fig. 4b and c). In central Serbia, high concentrations of Cr and Ni in the soil on serpentine rocks was recorded.50 Compared to other soil types, the Rankers on serpentine stands out for having significantly higher concentrations of Ni and Cr, which is characteristic for soil on this substrate. Wines from Vojvodina, grouped in the right upper part of score plot, were characterized by higher content of Ca, Na, and Mg (Fig. 4b and c). The dominant soil type in Vojvodina is chernozem that is rich in humus and minerals such as hydrated silicate of Ca, Na, and Mg. Samples from the South region were positioned in the left lower part of the score plot and showed higher content of K and Rb (Fig. 4b and c). Limestone type soil in Southeast Serbia is rich in alkaline metals such as Rb and K. Rubidium content in soils is largely inherited from the parent rocks, as indicated by the highest mean Rb content in soils over granites, limestones, and calcareous rocks.51 Rubidium is very closely linked with K as their properties are similar, and it may partially substitute for K sites in plants.51

Estimation of dietary elemental intake

Calculated RDA and DMI values of essential elements and DI and MDI values of toxic elements for wine samples are given in Table 4.
Table 4 The daily mineral intake of essential and toxic elements for red and white wines
Essential element Average content in 100 mL wine (mg) RDA (mg per day) DMI (%)
Red White Red White
K 67.5 39.6 2000 3.38 1.98
Mg 9.74 6.66 375 2.60 1.78
Ca 8.18 8.46 800 1.02 1.06
Na 0.88 1.76 1500 0.06 0.12
Fe 0.131 0.15 14 0.94 1.10
Cu 0.0014 0.068 1 0.14 6.75
Zn 0.0065 0.098 10 0.07 0.98
Se 0.0003 0.0005 0.055 0.49 0.71
Mn 0.014 0.087 2 0.71 4.37
Cr 0.0010 0.0008 0.04 2.60 1.96

Toxic element Average content in 100 mL wine (μg) MDI (μg per day) DI (%)
Red White Red White
Pb 5.15 8.97 250 2.06 3.59
As 1.40 2.12 150 0.96 1.41
Cd 0.19 0.13 25 0.78 0.52


Essential elements

Recommended daily allowance for K is 2000 mg according to the EEC.26 The Scientific Committee on Food (SCF) established the acceptable range for Na from 1400 to 8800 mg per day for adults. A tolerable upper intake level (UL) for K and Na was not established.52 In the analysed wines, the calculated DMI for K was 3.38% and 1.98% of the RDA in red and white wines, respectively (Table 4). The DMI for Na was 0.06% and 0.12% in red and white wines, respectively. Based on the results of Na, a low percentage is suitable because increased concentration of Na in the body causes hypertension and diabetes.53 For Mg, the RDA for men aged 19 to 30 years is 400 mg per day (310 mg per day for women) and 420 mg per day for over 30 years old (320 mg per day for women).52 An UL for Mg could not be established due to lack of available data.52 However, the RDA according to EEC is 375 mg per day. In our wines, the calculated DMI for Mg was higher in red wines (2.60%) than in white wines (1.78%). The UL for Ca is proposed to be 2500 mg per day. In contrast to Mg, similar values of DMI obtained for Ca in both type of wines indicated that the consumption of red and white wines would lead to intake of almost identical amounts of Ca. Iron has important metabolic functions such as transfer of oxygen.52 Based on our results, its contribution to dietary intake was 0.94% and 1.10% for red and white wines, respectively (Table 4). Based on different intakes of Cu, the EFSA Panel on Dietetic Products, Nutrition and Allergies (NDA) set Adequate Intakes (AI) values for men and women. For men, the AI for Cu is 1.6 mg per day, and for women it is 1.3 mg per day.54 The RDA for Cu according to the EEC is 1 mg per day.26 Calculated DMI for Cu was 0.14% and 6.75% in red and white wines, respectively (Table 4), which indicated that the white wine significantly contributes to the daily mineral intake for this element. Copper in the human body preferably has a role as a catalyst but is also an integral part of the enzymes involved in the electron transport chain. This metabolic process plays an important role in the synthesis of ATP which is the main source of energy in cells.52 The European PRI for Zn for adult males and females is 9.5 mg per day and 7.0 mg per day, respectively.55 This value applies to pregnant and lactating women.52 The RDA for Zn according to the EEC is 10 mg per day.26 The DMI for Zn was 0.07% and 0.98% in red and white wines, respectively (Table 4). Compared with Cu, Mg and Zn, the non-metal Se is needed in much smaller doses; the current adequate dose of Se for humans is 1 μg per kg body weight (b.w.) per day, which corresponds 70 μg per day for an average consumer,56 with UL of 300 μg per day.52 At least eleven selenoproteins containing the amino acid selenocysteine have been identified in mammals. In addition, Se has been related to immune function, viral infection, and reproduction. In the analysed wines, the DMI for Se was 0.49% in red wines and was 1.71% in white wines (Table 4). Adequate Intake for Mn is 3 mg per day, while UL for Mn is not established.57 The RDA for Mn according to the EEC is 2 mg per day. From our research, it seems that one glass of white wine is a good source of Mn as it provides 4.37% of the recommended daily allowance. The RDA for Cr according to EEC is 40 μg per day.26 One glass of red wine contributes to 2.60% of the Cr-RDA, and one glass of white wine contributes to 1.96% of the RDA.

A 100 mL glass of analysed wine will provide significant amounts of essential elements including Cu (white wine), Mn (white wine), K (red wine) and seem to be good source of these metals. These results highlight that no element could be labelled as significant in a single dose, since none achieves 15% of the RDA, as recommended for labelling purposes.26 Importantly, the presence of other bioactive compounds in the beverages can influence the bioavailability of the minerals.

Toxic elements

Concentrations of As, Cd, and Pb in analysed wine samples were under Maximum Acceptable Limits (MAL) at 0.2 mg L−1, 0.01 mg L−1, and 0.15 mg L−1, respectively, as published by the Organization of Vine and Wine.58 Provisional tolerable weekly intake (PTWI) for inorganic As is 15 μg per kg b.w., which corresponds to an intake of 2.1 μg per kg b.w per day. This daily intake is equivalent to an intake of 150 μg per day for the average consumer.59

For Cd, the EFSA's Panel on Contaminants in the Food Chain (CONTAM Panel) set the Tolerable Weekly Intake (TWI) of 2.5 μg per kg b.w.60 in order to ensure a high level of protection for all consumers, which corresponds 25 μg per day for an adult person of 70 kg. The provisional tolerable weekly intake for Pb of 25 μg per kg b.w. is no longer appropriate.61 The respective benchmark dose lower confidence limit (BMDL) derived from blood lead levels in μg L−1 (corresponding to dietary intake values in μg per kg b.w. per day) were the following: developmental neurotoxicity BMDL01 12 μg L−1 (0.50 μg per kg b.w. per day), effects on systolic blood pressure BMDL01 36 μg L−1 (1.50 μg per kg b.w. per day), and effects on kidney in adults BMDL10 15 μg L−1 (0.63 μg per kg b.w. per day).55 Lead has the greatest concentration in wine of the toxic elements (3.59% and 2.06% of DI for white and red wines, respectively). In the studied wines, the contribution to the daily intake decreased in the order Pb > As > Cd. Estimated daily intake of toxic elements from consumption of 100 mL wine hence poses no toxicological risk.

Conclusions

Characterisation of Serbian wines according to their elemental composition was performed, and the obtained results were similar to literature data. Potassium, magnesium, and calcium were the most abundant elements in all investigated red and white wine samples.

PCA and PLS-DA were applied in order to establish parameters for classification and differentiation of two types of wine (white and red). Data from the elemental content of wine samples allows accurate prediction of wine type and provides a useful tool for their determination. The most important descriptors for discrimination among red and white wine samples were Be, Al, Rb, Mg, K, Cu, Mn, and Na, in descending order. In addition, PCA was applied to determine which elements affected seasonal variability between wines from one winery. The obtained model revealed the existence of three distinctive groups of characteristics associated with three vintages with the highest influence from the variables Cd, Pb, As, Sb, V, Na, K and Zn. The entire elemental profile of wine is influenced by rain and number of sunny days during the vintage. A pattern recognition technique was also applied for the determination of regional origin of red wine samples. A significant number of samples were supplied by different wineries from three different regions of Serbia. The PCA model revealed the existence of three groups of characteristics associated with different regions of production which could be explained by different soil types in the selected Serbian regions.

A 100 mL glass of the analysed wines will provide significant amount of Cu (white wine, 6.7% of RDA), Mn (white wine, 4.4% of RDA), and K (red wine, 3.4% of RDA). These results highlight that no element could be labelled as significant in a single dose and that the estimated daily intake of toxic elements hence posed no toxicological risk.

Acknowledgements

This research was financially supported by the Ministry of Education, Science and Technological Development of the Republic of Serbia, project No. 172030 and 172017.

References

  1. P. Pohl, Trends Anal. Chem., 2007, 26(9), 941 CrossRef CAS.
  2. G. Grindlay, J. Mora, S. Maestre and L. Gras, Anal. Chim. Acta, 2008, 629, 24 CrossRef CAS PubMed.
  3. T. Stafilov and I. Karadjova, Int. J. Pure Appl. Chem., 2006, 1(2), 273 Search PubMed.
  4. G. Grindlay, J. Mora, L. Gras and M. T. C. de Loos-Vollebregt, Anal. Chim. Acta, 2011, 691, 18 CrossRef CAS PubMed.
  5. V. Ivanova-Petropulos, H. Wiltsche, T. Stafilov, M. Stefova, H. Motter and E. Lankmayr, Maced. J. Chem. Chem. Eng., 2013, 32(2), 265 CAS.
  6. A. Versari, V. F. Laurie, A. Ricci, L. Laghi and G. P. Parpinello, Food Res. Int., 2014, 60, 2 CrossRef CAS.
  7. C. M. R. Almeida and M. T. S. D. Vasconcelos, Anal. Chim. Acta, 1999, 396, 45 CrossRef CAS.
  8. C. Minoia, E. Sabbioni, A. Ronchi, A. Gatti, R. Pietra, A. Nicolotti, S. Fortaner, C. Balducci, A. Fonte and C. Roggi, Sci. Total Environ., 1994, 141, 181 CrossRef CAS.
  9. G. Darret, F. Couzy, J. M. Antoine, C. Magliola and J. P. Mareschi, Ann. Nutr. Metab., 1986, 30, 335 CrossRef CAS PubMed.
  10. C. J. Bevin, R. G. Dambergs, A. J. Fergusson and D. Cozzolino, Anal. Chim. Acta, 2008, 621, 19 CrossRef CAS PubMed.
  11. R. Godelmann, F. Fang, E. Humpfer, B. Schütz, M. Bansbach and H. Schäfer, et al., J. Agric. Food Chem., 2013, 61, 5610 CrossRef CAS PubMed.
  12. B. T. Weldegergis, A. de Villiers and A. M. Crouch, Food Chem., 2011, 1100 CrossRef CAS.
  13. V. Vrček, M. Bojić, I. Žuntar, G. Mendaš and M. Medić-Šarić, Food Chem., 2011, 124, 354 CrossRef.
  14. O. R. Dinca, R. E. Ionete, D. Costinel, I. E. Geana, R. Popescu, I. Stefanescu and G. L. Radu, Food Analytical Methods, 2016, 9, 2406 CrossRef.
  15. M. Álvarez, I. M. Moreno, S. Pichardo, A. M. Cameán and A. G. González, Food Chem., 2012, 135, 309 CrossRef.
  16. Ž. Fiket, N. Mikac and G. Kniewald, Food Chem., 2011, 126, 941 CrossRef.
  17. X. Cetó, A. González-Calabuig, N. Crespo, S. Pérez, J. Capdevila, A. Puig-Pujol and M. del Valle, Talanta, 2017, 162, 218 CrossRef PubMed.
  18. D. Kruzlicova, Ž. Fiket and G. Kniewald, Food Res. Int., 2013, 54, 621 CrossRef CAS.
  19. J. Mutic, D. Manojlovic, R. Kovacevic, J. Trifunovic, N. R. Amaizah and L. Ignjatovic, Microchem. J., 2011, 98, 11 CrossRef CAS.
  20. J. J. Mutic, D. D. Manojlovic, D. Stankovic and A. D. Lolic, Pol. J. Environ. Stud., 2011, 20, 133 CAS.
  21. S. M. Rodrigues, M. Otero, A. A. Alves, J. Coimbra, M. A. Coimbra, E. Pereira and A. C. Duarte, J. Food Compos. Anal., 2011, 24, 548 CrossRef CAS.
  22. M. Dimitrijević, V. D. Mitić, J. S. Cvetković, V. P. Stankov-Jovanović, J. J. Mutić and S. D. Nikolić-Mandić, Eur. Food Res. Technol., 2016, 242, 1 CrossRef.
  23. J. Hintze, Number Cruncher Statistical Systems, Kaysville, 2001, www.ncss.com Search PubMed.
  24. P. Ristivojević, F. L. Andrić, J. Đ. Trifković, I. Vovk, L. Ž. Stanisavljević, Ž. L. Tešić and D. M. Milojković-Opsenica, J. Chemom., 2014, 28, 301 CrossRef.
  25. EFSA, Guidance on selected default values to be used by the EFSA Scientific Committee, Scientific Panels and Units in the absence of actual measured data, EFSA J., 2012, 10(3), 2579 CrossRef.
  26. EEC, Amending Council Directive 90/496/EEC on nutrition labelling for foodstuffs as regards recommended daily allowances, energy conversion factors and definitions, Official Journal of the European Union, Commission Directive 2008/100/EC.
  27. M. Iglesias, E. Besalú and E. Anticó, J. Agric. Food Chem., 2007, 55, 219 CrossRef CAS PubMed.
  28. P. Paneque, M. T. Álvarez-Sotomayor, A. Clavijo and I. A. Gómez, Microchem. J., 2010, 94, 175 CrossRef CAS.
  29. S. Ražić and A. Onjia, Am. J. Enol. Vitic., 2010, 61, 506 CrossRef.
  30. P. Kment, M. Mihaljevič, V. Ettler, O. Šebek, L. Strnad and L. Rohlová, Food Chem., 2005, 91, 157 CrossRef CAS.
  31. R. Lara, S. Cerutti, J. A. Salonia, R. A. Olsina and L. D. Martinez, Food Chem. Toxicol., 2005, 43, 293 CrossRef CAS PubMed.
  32. P. P. Coetzee, F. P. van Jaarsveld and F. Vanhaecke, Food Chem., 2014, 164, 485 CrossRef CAS PubMed.
  33. I. Geana, A. Iordache, R. Ionete, A. Marinescu, A. Ranca and M. Culea, Food Chem., 2013, 138, 1125 CrossRef CAS PubMed.
  34. I. M. Moreno, D. González-Weller, V. Gutierrez, M. Marino, A. M. Cameán, A. G. González and A. Hardisson, Talanta, 2007, 72, 263 CrossRef CAS PubMed.
  35. P. L. Teissèdret, M. Krosniak, K. Portet, F. Gasc, A. L. Waterhouse, J. J. Serrano, J. C. Cabanis and G. Cros, Food Addit. Contam., 1998, 15, 585 CrossRef PubMed.
  36. İ. M. Alkış, S. Ö. Arda Atakol, N. Yılmaz, R. E. Anlı and O. Atakol, J. Food Compos. Anal., 2014, 33, 105 CrossRef.
  37. J. N. Miller and J. C. Miller, Statistics and Chemometrics for Analytical Chemistry, Pearson Education Limited, Edinburgh, 6th edn, 2010 Search PubMed.
  38. A. E. Martin, R. J. Watling and G. S. Lee, Food Chem., 2012, 133, 1081 CrossRef CAS.
  39. C. M. R. Almeida and M. T. S. D. Vasconcelos, J. Agric. Food Chem., 2003, 51, 4788 CrossRef CAS PubMed.
  40. J. D. Greenough, L. M. Mallory-Greenough and B. J. Fryer, Geoscience Canada, 2005, 32(3), 129 Search PubMed.
  41. M. I. Spranger, M. C. Clímaco, B. Sun, N. Eiriz, C. Fortunato, A. Nunes, M. C. Leandro, M. L. Avelar and A. P. Belchior, Anal. Chim. Acta, 2004, 513, 151 CrossRef CAS.
  42. D. Manojlović, A. Popara, B. P. Dojčinović, A. Nikolić, B. M. Obradović, M. M. Kuraica and J. Purić, Vacuum, 2009, 83, 142 CrossRef.
  43. H. Hopfer, J. Nelson, T. S. Collins, H. Heymann and S. E. Ebeler, Food Chem., 2015, 172, 486 CrossRef CAS PubMed.
  44. M. Del Mar Castiñeira Gómez, R. Brandt, N. Jakubowski and J. T. Andersson, J. Agric. Food Chem., 2004, 52, 2953 CrossRef PubMed.
  45. G. V. Jones, M. A. White, O. R. Cooper and K. Storchmann, Clim. Change, 2005, 73, 319 CrossRef.
  46. Republic Hydrometeorological Service of Serbia (RHSS), http://www.hidmet.gov.rs/index_eng.php, accessed October 2016.
  47. R. Krgović, J. Trifković, D. Milojković-Opsenica, D. Manojlović and J. Mutić, Sci. World J., 2014, 212506 Search PubMed.
  48. J. D. Greenough, H. P. Longerich and S. E. Jackson, Aust. J. Grape Wine Res., 1997, 3, 75 CrossRef CAS.
  49. M. Atanacković, A. Petrović, S. Jović, L. Gojković-Bukarica, M. Bursać and J. Cvejić, Food Chem., 2012, 131, 513–518 CrossRef.
  50. V. Mrvić, G. Antonović, D. Čakmak, V. Perović, S. Maksimović, E. Saljnikov and M. Nikoloski, Pedological and pedogeochemical map of Serbia, Belgrade, September, 2013 Search PubMed.
  51. A. Kabata-Pendias, Trace Elements in Soils and Plants, CRC Press LLC, Boca Raton, 4h edn, 2001 Search PubMed.
  52. EFSA (2006), Tolerable upper intake levels for vitamins and minerals; Scientific Committee on Food, Scientific Panel on Dietetic Products, Nutrition and Allergies, http://www.efsa.europa.eu/sites/default/files/efsa_rep/blobserver_assets/ndatolerableuil.pdf, accessed March 2016.
  53. H. Karppanen and E. Mervaala, Prog. Cardiovasc. Dis., 2006, 49(2), 59 CrossRef CAS PubMed.
  54. EFSA, Scientific opinion on dietary reference values for copper. EFSA Panel on Dietetic Products, Nutrition and Allergies (NDA), EFSA J., 2015, 13(10), 4253 CrossRef.
  55. V. Stefanović, J. Trifković, J. Mutić and Ž. Tešić, Environ. Sci. Pollut. Res., 2016, 23, 13178 CrossRef PubMed.
  56. EFSA, Scientific opinion on dietary reference values for selenium. EFSA Panel on Dietetic Products, Nutrition and Allergies (NDA), EFSA J., 2014, 12(10), 3846 CrossRef.
  57. EFSA, Scientific opinion on dietary reference values for manganese. EFSA Panel on Dietetic Products, Nutrition and Allergies (NDA), EFSA J., 2013, 11(11), 3419 CrossRef.
  58. OIV, Organisation Internationale de la Vigneet du Vin, Compendium of International Methods of Wine and Must Analysis, Paris, 2008 Search PubMed.
  59. EFSA, Dietary exposure to inorganic arsenic in the European population. European Food Safety Authority, EFSA J., 2014, 12(3), 3597 CrossRef.
  60. EFSA, Cadmium dietary exposure in the European population, EFSA J., 2012, 10(1), 2551 CrossRef.
  61. EFSA, Scientific opinion on lead in food. EFSA Panel on Contaminants in the Food Chain (CONTAM), EFSA J., 2010, 8(4), 1570 CrossRef.

Footnote

Electronic supplementary information (ESI) available. See DOI: 10.1039/c6ra25105f

This journal is © The Royal Society of Chemistry 2017
Click here to see how this site uses Cookies. View our privacy policy here.