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Pharmaceutica Analytica Acta
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Dietary Content and Evaluation of Metals in Four Types of Tea (White, Black, Red and Green) Consumed by the Population of the Canary Islands

Gonzalez-Weller D*, Rubio C, Gutiérrez AJ, Pérez B, Hernández-Sánchez C, Caballero JM, Revert C and Hardisson A

Department of Public Health and Toxicology, University of La Laguna, 38071, La Laguna, Tenerife, Spain

*Corresponding Author:
Gonzalez-Weller D
Department of Toxicology
University of La Laguna
38071, La Laguna, Tenerife, Spain
Tel: +34-616-992801
Fax: +34-922-626497
E-mail: [email protected]

Received date: September 29, 2015; Accepted date: October 16, 2015; Published date: October 19, 2015

Citation: Gonzalez-Weller D, Rubio C, Gutiérrez AJ, Pérez B, Hernández-Sánchez C, et al.(2015) Dietary Content and Evaluation of Metals in Four Types of Tea (White, Black, Red and Green) Consumed by the Population of the Canary Islands. Pharm Anal Acta 6:428. doi: 10.4172/2153-2435.1000428

Copyright: © 2015 Gonzalez-Weller D, et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.

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Objective: The aim of this study was to analyze the contents of Cd, Co, Cr, Cu, Fe, Mg, Ni, Pb, Zn in samples of four types of tea (Camellia sinensis) consumed in the Canary Islands: white, black, red and green tea, in order to determine their intake through consumption. Methods: A total of 80 samples (20 of each type of tea) were analyzed by ICP-OES. Results: The highest concentrations of Cd, Co, Mg, Pb and Zn were found in samples of white tea, those of Cr, Fe and Ni in the red tea, and those of Cu in green tea. While the lowest levels of Cd, Co, Fe, Pb and Zn were found in black tea, those of Cr, Mg and Ni in the green tea, and those of Cu in the white tea. Conclusion: The calculated intakes of each metal (assuming the consumption of a cup of tea 2 g/ day) shows that Cr, Cu, Fe, Mg and Zn make a negligible contribution to the RDI, and the same applies to Cd to the PTMI and Pb to the PTWI.


Metals; ICP-OES; Dietary assessment; Spanish population; Canary Islands


Tea or blends of tea are understood to be the buds, shoots and young leaves of the shrub Camellia sinensis (Theaceae) [1]. This shrub of Asian origin has been cultivated since ancient times [2] and is currently being grown in much of Asia, Africa, Turkey and other countries. The different types of tea are determined by a number of factors such as the time of harvest (depending on leaf development), the processing method, drying, roasting and fermentation processes [3].

The consumption of tea has been estimated to be about 18 to 20 billion cups of tea a day worldwide, meaning that it is the second most consumed beverage after water in the world [4,5].

Note that the four types of tea which are the objects of this study (white, black, red and green), have beneficial properties for human health, thus, black tea has antioxidant properties [6], hepatoprotective [7], antiarterioesclerotic [8], lipolytic, thermogenic [9,10], and anticarcinogenic [11]. Antioxidant properties are attributed to green tea [12-14], antiarterioesclerotic [15], hepatoprotective [16], lipolytic, thermogenic [17,18], anticarcinogenic [19,20] and reducing platelet aggregation [21]. White tea has neuroprotective properties [22,23], anticarcinogenic [24,25], protection from ultraviolet radiation when used topically [26] and inhibition of acetylcholinesterase [27]. Red tea has antioxidant features [28], antiarterioesclerotic [8], lipolytic, thermogenic [29] and anticarcinogenic [30].

Although metals are perhaps the oldest known most toxic agents, interest in them has not declined and knowledge concerning their potential toxic effects and mechanisms of action has increased in recent years [31]. Metals such as iron, copper and zinc are considered essential minerals for humans, although high concentrations could be potentially toxic [32-34]. Heavy metals, like lead and cadmium, are regarded as toxic environmental contaminants in food [35]. Compared with other toxic substances, heavy metals are considered to be most damaging to living systems. Food and water are the primary source of these metals for humans [36,37].

The main and most important feature of cobalt is that it is an integral part of a family of compounds called cobalamins; the most important of which are vitamin B12 and coenzyme B12. Coenzyme B12 is used as a cofactor for many enzymes, among which the mutases, diol dehydratase (deaminase) and ribonucleotide reductases are the most notable [38].

Chromium is an essential mineral that seems to play a role in carbohydrate metabolism as a component of the glucose tolerance factor, involved in cardiovascular risk and the metabolic syndrome, as well as its antioxidant properties. The normal oxidation state in biological tissues is Cr (III), which is the nutritionally essential form of Cr for animals and humans [39,40].

Copper is required for the catalytic activities of many metalloenzymes such as cytochrome C oxidase, superoxide dismutase, dopamine β-hydroxylase, lysyl oxidase, and tyrosinase, apart from which it acts as a cofactor in various redox enzymes, in mitochondrial respiration, iron absorption, and elastin synthesis. Copper has recently been identified as a factor in prion disease prevention [41,42].

The key functions of iron include oxygen transport in blood and muscle tissue (through haemoglobin and myoglobin), taking part— along with copper—in redox processes, and iron has an important role in the biosynthesis of certain proteins like collagen and elastin [42,43].

Magnesium is a crucial element in the generation and use of adenosine triphosphate, and is required for oxidative phosphorylation. It is involved in energy metabolism, glucose utilization, protein synthesis, synthesis and degradation of fatty acids, ATPase functions, hormonal reactions, neuromuscular transmission signalling and cardiovascular health. Magnesium is also associated with the maintenance of cellular ionic balance through its relationsips with sodium, potassium and calcium [44-46].

Although nickel is an essential trace element for various animal species, its biochemical role in humans and higher animals has not been demonstrated. However, it may serve as a cofactor or structural component of several metalloenzymes with a variety of functions (hydrolysis, redox reactions) and in gene expression [34,47].

Zinc is involved in biochemical processes, such as cell respiration and the use of oxygen by cells, both DNA and RNA synthesis, the preservation of the cell membrane integrity, and the elimination of free radicals, a process executed through a cascade of enzymatic systems [42,48].

Cadmium and lead are not essential for the human organism [34]. Cadmium has a long residence time in human tissues (10-40 years), especially in the kidneys and liver, where it bio-accumulates [49,50] and its toxic effects are noticeable in various ways. It can interfere with some of the organism’s enzymatic reactions, substituting zinc and other metals, manifesting its action in several pathological processes such as renal dysfunctions, hypertension, arteriosclerosis, inhibition of growth, damage in the nervous system, bone demineralisation and endocrine disruption [37]. The main toxic effect of lead is the dysfunction of the nervous system in the foetus and infants. In adults, lead causes: adverse blood effects, reproductive dysfunctions; damage to the gastrointestinal track; nephropathies; damage to the central as well as the peripheral nervous system and interferences in the enzymatic systems that synthesise the HEME group [37].

Therefore, and assuming that food consumption is the main route of exposure of the general population to metals, that tea is a highly consumed food, that its metallic levels and the intake these are responsible for is unknown in the Canary islands, the main objective of this work has been to determine the concentrations of Cd, Co, Cr, Cu, Fe, Mg, Ni, Pb and Zn in tea (white tea, black, red and green) and to discover the dietary intakes resulting from its consumption.

Material and Methods


A total of 80 samples of different brands of tea sold on the island of Tenerife were analyzed: 20 black tea, 20 green tea, 20 red tea and 20 white tea. The samples were purchased in supermarkets, health food shops and pharmacies for four months (between January and April 2014).

Before sample preparation, all laboratory materials were washed with Acationox laboratory cleaning agent (Merck, Darmstadt, Germany) to avoid contamination and eliminate any possible trace metals. They were then kept in 5% nitric acid for 24 h and subsequently washed with Milli-Q (Millipore, Milford, MA) quality water.

After collection and classification, the food samples were homogenized, preserved at -18°C and analysed within 2 months.

Determination of metals

Ten grams of homogenized sample of each type of tea were weighed in triplicate in porous porcelain capsules on scales PB153-S / FACT (Mettler Toledo, Switzerland). The capsules with the samples were then subjected to drying in an oven (Selecta, Spain) at 60-70°C for 12-14 hours. Afterwards, the samples were placed in a muffle furnace (Nabertherm®, Germany) and the temperature was gradually increased (50°C / hour) until it reached 425 ± 15ºC, this temperature was maintained for 18-24 hours to destroy the organic matter in the sample. The white ashes obtained by this procedure were dissolved in 1.5% nitric acid to a final volume of 25 ml.

The digested samples were transferred into polyethylene containers and stored for a maximum of one month until analysis. The elements in the samples were determined by ICP-OES using a Thermo Scientific iCAP 6000 series spectrometer (Waltham, MA, USA). This reference technique for metal determination is highly sensitive with excellent data reproducibility [34]. The settings were as follows: approximate RF power, 1.2 kW; gas flow (nebulizer flow; auxiliary flow), 0.5 L/min; pump rate, 50 rpm; stabilization time 0 s. All analyzes were performed in duplicate.

The quality controls used in this work were chosen by the criterion of method accuracy. This was established by the average recovery obtained with reference material measured under reproducible conditions. The reference materials SRM 1515 Apple Leaves and SRM 1573a Tomato Leaves from the National Institute of Standards and Technology (NIST) were used. Recovery rates obtained from the reference materials were over 94.4% (Table 1). Instrumental detection and quantification limits in terms of reproducibility were calculated as three and ten times the standard deviation (SD) resulting from the analysis of 15 targets of acid digest [51] and are shown in table 2.

Reference material Element Certified valuea,b (mg/kg) Obtained valuea (mg/kg) Recovery (%)
SRM 1515 Apple Leaves Mg 0.271 ± 0.008c 0.281 ± 0.014 103.8
Cu 5.64 ± 0.24 5.55 ± 0.65 98.4
Ni 0.91 ± 0.12 0.88 ± 0.48 96.8
Pb 0.470 ± 0.024 0.45 ± 0.032 95.7
Zn 12.5 ± 0.3 12.4 ± 0.23 99.2
SRM 1573a Tomato Leaves Cd 1.52 ± 0.04 1.43 ± 0.1 94.4
Cr 1.99 ± 0.06 1.92 ± 0.09 96.6
Co 0.57 ± 0.02 0.54 ± 0.07 94.1
Fe 368 ± 7 375 ± 9 101.8

Table 1: Quality control of the method.

Element and wavelength Detection limit (LOD) (mg/l) Quantification limit (LOQ) (mg/l)
Cd (226.5 nm) 0.0003 0.001
Co (228.6 nm) 0.0006 0.002
Cr (267.7 nm) 0.003 0.008
Cu (327.3 nm) 0.004 0.012
Fe (259.9 nm) 0.003 0.009
Mg (279.1 nm) 0.583 1.943
Ni (231.6 nm) 0.0007 0.003
Pb (220.3 nm) 0.0003 0.001
Zn (206.2 nm) 0.002 0.007

Table 2: Detection and quantification limits.

Statistical analysis

The SPSS 22.0 software (IBM, USA) was used for the statistical analysis of the results. The normality of the data was checked using the Kolmogorov-Smirnov and Shapiro-Wilk [52], while the Levene test was used to check homogeneity of variance [53]. Given that the results of these tests showed neither normality nor homogeneity of variances, it was decided to perform a non-parametric statistical test (Kruskal-Wallis) to check whether there were significant differences between the studied samples and the Mann Whitney U test to clarify between which types of tea there were differences. P values<0.05 were considered statistically significant.

Results and Discussion

The mean concentrations of the metals which were the object of this study (wet weight) and their corresponding standard deviation are shown in Table 3.

  White Black Red Green
Cd (μg/Kg, wet weight) 38.20 ± 50.12 <LOQ1 31.00 ± 27.15 7.75 ± 13.88
Co (mg/Kg, wet weight) 0.70 ± 0.095 0.44 ± 0.09 0.45 ± 0.16 0.46 ± 0.20
Cr (mg/Kg, wet weight) 1.12 ± 0.38 0.38 ± 0.15 2.56 ± 0.54 0.26 ± 0.08
Cu (mg/Kg, wet weight) 5.46 ± 1.32 5.64 ± 1.19 7.76 ± 1.33 8.40 ± 4.5
Fe (mg/Kg, wet weight) 90.00 ± 28.85 33.29 ± 13.72 227.43±68.39 65.66 ± 26.77
Mg (mg/Kg, wet weight) 142.33±103.22 58.03±38.53 99.99±41.85 38.13±19.79
Ni (mg/Kg, wet weight) 3.38 ± 0.86 2.82 ± 0.53 3.87 ± 0.48 2.31 ± 0.54
Pb (μg/Kg, wet weight) 154.05 ± 183.74 26.00 ± 25.93 102.40± 47.51 38.90 ± 22.92
Zn (mg/Kg, wet weight) 7.35 ± 1.60 5.04 ± 0.80 7.20 ± 1.06 5.16 ± 1.11

Table 3: Cd, Co, Cr, Cu, Fe, Mg, Ni, Pb and Zn contents in the different types of tea: mean ± standard deviation.

Cadmium concentrations ranged from 38.20 mg/kg in white tea and the levels in black tea were below the detection limit (<2.5 mg/ kg). The maximum concentration for cobalt of this element, 0.70 mg/ kg, was found in white tea and the minimum, 0.44 mg/kg, was in black tea, although very similar to those in the red and black teas, 0.45 and 0.46 mg/kg, respectively. In the case of chromium, 2.56 mg/kg was the maximum content which was found in the red tea and the minimum was 0.26 mg/kg which was found in the green tea. The highest copper content was found in the green tea (8.40 mg/kg) and the lowest in the white tea (5.46 mg/kg). With respect to iron, the red and black teas had the greatest and least amounts of this element (227.43 and 90.00 mg/kg, respectively). The highest concentration of magnesium was detected in the white and that of nickel in the red tea, (142.33 mg/kg of magnesium and 3.87 mg/kg of nickel), but the lowest amounts of these metals were found in the green tea (38.13 and 2.31 mg/kg respectively). Finally, as for lead and zinc, the largest quantities of both these elements were observed in the white tea (154.05 mg/kg and 7.35 mg/kg, respectively) and the smallest quantities in the black tea (26.00 mg/kg and 5.04 mg/ kg, respectively).

Therefore, cadmium, cobalt, magnesium, lead and zinc were found to be present in the greatest quantities in the samples of white tea, while chromium, iron and nickel had the greatest presence in the red tea, and copper in the green tea. The lowest levels of cadmium, cobalt, iron, lead and zinc were observed in the black tea, chromium, magnesium and nickel levels were lowest in the green tea and copper in the white tea.

It is noteworthy that, in some of the analyzed teas, the variability of the results is high. However, this variability in biological samples is considered normal, since the metal content in foods, both plants and animals, depends on various factors ranging from environmental conditions to the production and processing methods [54].

Significant differences were observed for the metal concentrations depending on the type of tea. In the case of cadmium, white tea and red tea had significantly greater differences (p<0.05) compared to black tea and green tea. In the case of cobalt, white tea differed significantly (p<0.05) from black, red and green tea. As regards chrome, red tea was different from white tea, and they in turn differed from black tea and green tea (p<0.05). With regard to copper content, this was significantly higher (p<0.05) in red and green tea when compared to black and white tea, and similar to that observed for iron, although in this case, red tea was differentiated from black tea, and both of these in turn from white tea and green tea (p<0.05). As for magnesium concentrations, those in the white tea differed from those in the red tea, and both of them differed from the black and green teas (p<0.05). Red tea had significantly higher concentrations of nickel (p<0.05) with respect to the white, green and black teas. In case of lead, red tea and white tea are significantly differentiated by their higher lead contents (p<0.05) with respect to the black and green teas and finally the zinc contents in the white tea and the red tea were significantly differentiated from the black tea and the green tea (p<0.05).

A correlation study was also performed using the Pearson correlation test, yielding the following positive correlations between elements: Cr / Fe, Cr / Ni, Cr / Zn, Cr / Mg, Cr / Cd, Co / Ni, Co / Zn, Co / Mg, Fe / Cr, Fe / Cu, Fe / Ni, Fe / Zn, Fe / Cd, Ni / Zn, Ni / Mg, Ni / Cd, Ni / Pb, Zn / Mg, Zn / Cd, Zn / Pb , Mg / Cd, Mg / Pb, Cd / Pb and the only negative correlation was between Co / Cu (Table 4).

  Cr Co Fe Cu Ni Zn Mg Cd Pb
Cr 1 -0.05 0.943** 0.154 0.647** 0.583** 0.281* 0.341** 0.198
Co -0.05 1 -0.138 -0.306** 0.254* 0.26* 0.349** 0.151 0.213
Fe 0.943** -0.138 1 0.322** 0.533** 0.573** 0.175 0.34** 0.142
Cu 0.154 -0.306** 0.322** 1 0.017 0.13 -0.158 0.033 -0.064
Ni 0.647** 0.254* 0.533** 0.017 1 0.614** 0.500** 0.33** 0.385**
Zn 0.583** 0.26* 0.573** 0.13 0.614** 1 0.623** 0.504** 0.477**
Mg 0.281* 0.349** 0.175 -0.158 0.5** 0.623** 1 0.475** 0.556**
Cd 0.341** 0.151 0.34** 0.033 0.33** 0.504** 0.475** 1 0.298**
Pb 0.198 0.213 0.142 -0.064 0.385** 0.477** 0.556** 0.298** 1

Table 4: Pearson co-relation test.

The comparison of the concentrations of metals in this study with those of other authors, could only be carried out in the case of black and green tea, because in the cases of white and red tea no references from other studies were found to perform the said comparison. Table 5 shows the comparison of the metal concentrations in black tea obtained in this study with other previous studies of metals in black tea. It is observed that the cadmium levels obtained in the present study (<0.0025 mg/kg), are lower compared to those obtained by the other studies, particularly with regard to teas from Saudi Arabia (1.1 mg / kg) [3]. Cobalt levels (0.44 ± 0.09 mg/kg) are consistent with other studies, except for the case of tea from Saudi Arabia (10.98 mg/kg) [3] and Turkey (14.5 ± 7.1 mg/kg) [56], which are in the order of 25 and 33 times higher, respectively. The values of chromium (0.38 ± 0.15 mg/ kg) are much lower than those observed by other studies, and were up to 34 times lower than the tea from Turkey (13.0 ± 1.7 mg/kg) [56]. The concentration of copper in the present study (5.64 ± 1.19 mg/kg) is about 18 times greater than that reported in the study on teas produced in Taiwan (7.92 mg/kg) [57], lower than the other works, and was up to 5 times lower than the value reported by Matsuura et al., in 2001 in Japan (27.7 ± 0.7 mg/kg). The iron levels (33.29 ± 13.72 mg/kg) are only greater than those from Taiwan (0.9 mg/kg), about 37 times higher, but lower than for the other authors. As regards magnesium concentrations, the levels of the present study (58.03 ± 38.53 mg/kg) are lower than those described by Matsuura et al., in 2001, in Japan (2070 ± 30 mg/kg) and Shen and Chen, in 2008, in Taiwan (135.3 mg/kg). In the case of nickel, the levels of the study here (2.82 ± 0.53 mg/kg) are in line with other authors, except for Saudi Arabian tea (16.8 mg/kg) and Turkish tea (23.3 ± 9.6 mg/kg). The lead levels reported in the present work are low (0.026 ± 0.0259 mg/kg), particularly when compared with those of Turkish tea (17.9 ± 7.1 mg/kg) [56] (approximately 688 times higher). The same applies in the case of zinc, the level reported in the teas by Narin et al., in 2004, Turkey (129.0 ± 12.9 mg/kg) are much higher than those found here (5.04 ± 0.81 mg/kg).

Metal Population Reference Concentration (mg/kg)
Cd The Canary Islands The present study <LOQ1
Japan [55] 0.018 ± 0.0003
Turkey [56] 2.3 ± 0.4
Taiwán [57] 0.07
Saudi Arabia [3] 1.1
India [33] 0.14
Pakistan [58] 0.0121
Co The Canary Islands The present study 0.44 ± 0.09
Japan [55] 0.506 ± 0.042
Turkey [56] 14.5 ± 7.1
Taiwán [57] 0.2
Saudi Arabia [3] 10.98
Pakistan [58] 1.14
Cr The Canary Islands The present study 0.38 ± 0.15
Turkey [56] 13.0 ± 1.7
Taiwan [57] 7.92
Saudi Arabia [3] 9.8
India [33] 4.76
Pakistan [58] 12.63
Cu The Canary Islands The present study 5.64 ± 1.19
Japan [55] 27.7 ± 0.7
Turkey [56] 16.5 ± 3.9
Taiwan [57] 0.3
Saudi Arabia [3] 18.1
India [33] 24.07
Pakistan [58] 21.39
Fe The Canary Islands The present study 33.29 ± 13.72
Japan [55] 134 ± 48
Taiwan [57] 0.9
Saudi Arabia [3] 250.46
Pakistan [58] 118.46
Mg The Canary Islands The present study 58.03 ± 38.53
Japan [55] 2070 ± 30
Taiwan [57] 135.3
Ni The Canary Islands The present study 2.82 ± 0.53
Japan [55] 8.06 ± 0.19
Turkey [56] 23.3 ± 9.6
Saudi Arabia [3] 16.8
India [33] 2.53
Pakistan [58] 6.78
Pb The Canary Islands The present study 0.026 ± 0.0259
Japan [55] 0.709 ± 0.020
Turkey [56] 17.9 ± 7.1
Taiwan [57] 2.01
Saudi Arabia [3] 1
India [33] 0.81
Pakistan [58] 0.37
Zn The Canary Islands The present study 5.04 ± 0.81
Japan [55] 36.6 ± 0.7
Turkey [56] 129.0 ± 12.9
Taiwan [57] 1.2
Saudi Arabia [3] 65.71
Pakistan [58] 25.47

Table 5: Comparison of the Cd, Co, Cr, Cu, Fe, Mg, Ni, Pb and Zn concentrations in black tea: population of the Canary Islands against other populations.

The comparisons of the metal concentrations in green tea obtained in this study with those of previous studies are shown in Table 6. The levels of cadmium and cobalt found here are very similar to those of other studies. The chromium concentration in Thai tea (1,476 mg/kg) [32] is 6 times higher than those consumed in the Canary Islands (0.26 ± 0.08 mg/kg). The results for copper are similar, where the copper levels reported by Nookabkaew et al., in 2006, also in Thailand (15.20 mg/kg), are 2 times higher than those consumed in the Canary Islands (8.40 ± 4.5 mg/kg) although Taiwanese tea (0.4 mg/kg) [57] has copper concentrations which are 21 times lower. The iron concentration found in the present study (65.66 ± 26.77 mg/kg) is much higher than that reported by Shen and Chen in 2008 in Taiwan (0.6 mg/kh), but lower than that of other authors. The magnesium levels in the study (38.13 ± 19.79 mg/kg) are much lower than those from Thailand [32] and Japan [59] which were 2017 and 2200 ± 60 mg/kg, respectively. The nickel concentration reported here is similar to that of other authors, with that of lead being lower. Specifically, the lead levels reported in the teas from Thailand [32] are 103 times higher than those found in the present study (3.930 mg/kg versus 0.03890 ± 0.02292). The zinc levels found here (5.16 ± 1.11 mg/kg) are similar to those described by Shen and Chen, 2008, in Taiwan (6.3 mg/kg) but lower than the rest.

Metal Population Reference Concentration (mg/kg)
Cd The Canary Islands The present study 0.00775 ± 0.01388
Japan [59] 0.0405 ± 0.0041
Thailand [32] 0.035
Taiwan [57] ND1
Co The Canary Islands The present study 0.46 ± 0.20
Japan [59] 0.226 ± 0.004
Thailand [32] 0.294
Taiwan [57] 0.7
Cr The Canary Islands The present study 0.26 ± 0.08
Thailand [32] 1.476
Taiwan [57] 0.1
Cu The Canary Islands The present study 8.40 ± 4.5
Japan [59] 10.5 ± 0.2
Thailand [32] 15.20
Taiwan [57] 0.4
Fe The Canary Islands The present study 65.66 ± 26.77
Japan [59] 112 ± 5
Thailand [32] 167.1
Taiwan [57] 0.6
Mg The Canary Islands The present study 38.13 ± 19.79
Japan [59] 2200 ± 60
Thailand [32] 2017
Taiwan [57] 175.9
Ni The Canary Islands The present study 2.31 ± 0.54
Japan [59] 4.65 ± 0.19
Thailand [32] 5.633
Pb The Canary Islands The present study 0.03890 ± 0.02292
Japan [59] 0.734 ± 0.021
Thailand [32] 3.930
Taiwan [57] 0.01
Zn The Canary Islands The present study 5.16 ± 1.11
Japan [59] 28.1 ± 0.8
Thailand [32] 32.17
Taiwan [57] 6.3

Table 6: Comparison of the Cd, Co, Cr, Cu, Fe, Mg, Ni, Pb and Zn concentrations in green tea: population of the the Canary Islands against other populations.

In order to calculate the intakes of the metals in this work, the percentage of each metal transferred to the infusion of tea according to the references consulted has been taken into account (Table 7). Since transfer data were not found in the literature consulted here for all of the types of tea studied, a value of 100% was given to the metal transfer in the cases where data was not found. This procedure was performed in such a way, by assuming the highest transfer value, in order to consider the case of maximum exposure to the metals studied for tea consumption. In other words, to consider the cases of maximum intake. The aim of this measure is to provide the maximum protection for the health of consumers. In cases where more than one transfer data for the same type of tea has been found and, also and as in the previous case, the highest consulted transfer value has been chosen to protect the health of consumers.

Metal Tipo de té Porcentajes de transferencia
Cd Black 40.3% [57]
Green 14.18% [32]
White 100%
Red 100%
Co Black 25.3% [57]
Green 49.27% [32]
59.3% [57]
White 100%
Red 100%
Cr Black 67.5% [57]
Green 11.45% [32]
12.4% [57]
White 100%
Red 100%
Cu Black 21.8% [57]
Green 12.96% [32]
22.9% [57]
White 100%
Red 100%
Fe Black 30.9% [57]
Green 2.39% [32]
10.9% [57]
White 100%
Red 100%
Mg Black 50.6% [57]
Green 34.26% [32]
34.6% [57]
White 100%
Red 100%
Ni Black 50.49% [57]
Green 67.71% [32]
White 100%
Red 100%
Pb Black 58.6% [57]
Green 7.11% [32]
7.1% [57]
White 100%
Red 100%
Zn Black 9.6% [57]
Green 32.15% [32]
60.7% [57]
White 100%
Red 100%

Table 7: Percentages of metals transferred to the brewed tea.

The total intakes of cadmium, cobalt, chromium, copper, iron, magnesium, nickel, lead and zinc from the consumption of black, green, white and red tea in the Canary Islands are shown in Table 8. The calculation of the intakes was based on a daily consumption of tea prepared with 100 ml of boiling distilled water in which 2 g of tea were brewed for 5-10 minutes. Distilled water was used in the preparation of the different types of tea to prevent any interference from metals that may be present in drinking water.

Metal Type of tea Intake (μg/day)
Cd Black -
Green 0.0022
White 0.0764
Red 0.0620
Co Black 0.2226
Green 0.5456
White 1.4000
Red 0.9000
Cr Black 0.5130
Green 0.0645
White 2.2400
Red 5.1200
Cu Black 2.4590
Green 3.8472
White 10.9200
Red 15.5200
Fe Black 20.5732
Green 14.3139
White 180.0000
Red 454.8600
Mg Black 58.7264
Green 26.3860
White 284.6600
Red 199.9800
Ni Black 2.8476
Green 3.1282
White 6.7600
Red 7.7400
Pb Black 0.0305
Green 0.0055
White 0.3081
Red 0.2048
Zn Black 0.9677
Green 6.2642
White 14.7000
Red 14.4000

Table 8: Intakes of Cd, Co, Cr, Cu, Fe, Mg, Ni, Pb and Zn from the different types of tea.

The white tea provided the greatest intake of cadmium (0.0764 μg/day). The maximum intake of cobalt (1.4 μg/day) came from the white tea and the minimum (of 0.2226 μg/day) from the black tea. The greatest chromium intake was 5.12 μg/day from the red tea and the lowest was 0.0645 μg/day from the green tea. The red tea provided the largest intake of copper (15.52 μg/day) and the lowest intake of copper came from the black tea (2.4590/d μg ay). The red and the green tea supplied the highest and lowest intakes of iron (14.3139 and 454.86 μg/ day, respectively). The highest intakes of magnesium and lead came from the white tea (284.66 and 0.3081 μg/day, respectively), and lowest from the green tea (26.3860 and 0.0055 μg/day, respectively). Red tea provided the highest intake of nickel (7.74 μg/day) and the lowest nickel intake came from the black tea (2.8476 μg/day). Finally, the highest intake of zinc was from the white tea (14.7 μg/day), and this was similar to the zinc provided by the red tea (14.4 μg/day), while the black tea provided the lowest zinc intake (0.9677 μg/day).

If the average consumption of tea by the Canary population is one cup (2 g) per day, the contribution of these teas to the Dietary Reference Intakes (DRI) of chromium, copper, iron, magnesium and zinc should be taken into account. Although the DRI are dietary recommendations, both Canadian and American, to evaluate the intakes of the metals studied in the food groups of this work, they were selected here because they are the most recent established dietary guidelines.

The DRIs of chromium, copper, iron, magnesium and zinc for adults (men and women) are: Cr 20-35 ug / day, Cu 700-900 ug/day, 8-18 mg (8000-18000 ug) of Fe/day, 240-420 mg (240,000 to 420,000 ug) of Mg/day, 8-11 mg (8000-11000 ug) of Zn/day [60]. Therefore, the contributions to the DRIs (in percentage terms) involving established intakes of chromium, copper, iron, magnesium and zinc from the consumption of 2 g of black, green, white and red tea per adult and day are shown in Table 9.

Metal DRI (μg/day) Type of tea Intake (μg/day) Contribution to the DRI (%)
Cr 20-35 Black 0.5130 1.466-2.565
Green 0.0645 0.184-0.322
White 2.2400 6.400-11.200
Red 5.1200 14.629-25.600
Cu 700-900 Black 2.4590 0.273-0.351
Green 3.8472 0.427-0.550
White 10.9200 1.213-1.560
Red 15.5200 1.724-2.217
Fe 8000-18000 Black 20.5732 0.114-0.257
Green 14.3139 0.080-0.179
White 180.0000 1.000-2.250
Red 454.8600 2.527-5.686
Mg 240000-420000 Black 58.7264 0.014-0.024
Green 26.3860 0.006-0.011
White 284.6600 0.068-0.119
Red 199.9800 0.048-0.083
Zn 8000-11000 Black 0.9677 0.009-0.012
Green 6.2642 0.057-0.078
White 14.7000 0.134-0.184
Red 14.4000 0.131-0.180
Metal PTMI (μg/day) Type of tea Intake (μg/day) Contribution to the PTMI (%)
Cd 3.17 Black - -
Green 0.0022 0.069
White 0.0764 2.410
Red 0.0620 1.956
Metal PTWI (μg/day) Type of tea Intake (μg/day) Contribution to the PTWI (%)
Pb 250 Black 0.0305 0.012
Green 0.0055 0.002
White 0.3081 0.123
Red 0.2048 0.082

Table 9: Contribution to the DRIs from intakes of chrome, copper, iron, magnesium and zinc and to the PTMI and PTWI of cadmium and lead.

Furthermore, considering the abovementioned average consumption (one cup of tea 2 g/day), the contributions from the daily intake of the types of tea evaluated in this work to the Provisional Tolerable Monthly Intake (PTMI) of cadmium and Provisional Tolerable Weekly Intake (PTWI) of lead have been studied. In the case of cadmium, and because of its long half-life, the daily food intake has a small or even a negligible effect on the overall exposure. Therefore, and in order to assess the risks in the short or long term, the intake should be evaluated over a period of months, specifically, for at least one month. Thus, the Joint Expert Committee on Food Additives of FAO / WHO decided to set the tolerable upper intake level of this metal as a monthly value of 25 micrograms / kg body weight (3.17 mg/day for an adult of 70 kg) [61]. The PTWI value for lead will be 25 mg/kg body weight (250 mg/day for an adult of 70 kg), although since 2011 this value has been outdated and we are waiting for the Committee to set a new PTWI value that is considered protective for people’s health [61]. The contributions to the PTMI and PTWI for cadmium and lead (in percentage terms) are also shown in Table 9.

According to the above, a daily consumption of one cup of tea (2 g) by an adult makes a negligible contribution of the metals studied here, not only to the RDI, but also to the PTMI and PTWI. However, it is noteworthy that although the daily consumption of tea in the Canary population is relatively low, it should be borne in mind that there are other sources that may provide cadmium, chromium, copper, iron, magnesium, lead and zinc.


Iron was the most abundant metal in the four types of tea studied in the case of red tea, with a mean value of 227.43 ± 68.39 mg/kg, while the cadmium was the least abundant in black tea, whose value was not quantifiable. The intakes of chromium, copper, iron, magnesium and zinc found from the consumption of 2 g of black tea, green, white and red per adult per day, contribute little to the DRIs, with the maximum contribution being that of the chromium in the case of red tea, assuming 100% metal transfer to the brewed tea. The toxicological analysis revealed that the same consumption of 2 g of black, green, white and red tea per adult per day, contributes between 0069-1.956 % of the PTMI of Cd and between 0002-0123% of the PTWI of Pb to an average person of 70 Kg. One, therefore, cannot suspect that there is a toxic risk from the consumption of the different types of tea evaluated in this work, although it should be borne in mind that there are other sources that can provide the population of the Canary Islands with not only cadmium and lead, but also the other the metals studied here.

Declaration of Interest

Dr. Dailos González-Weller, corresponding author of the manuscript titled “Dietary content and evaluation of Cd, Co, Cr, Cu, Fe, Mg, Ni, Pb and Zn in four types of tea (white, black, red and green) consumed by the population of the Canary Islands” declares that has not received any financial, consulting, and personal relationships with other people or organizations, writing assistance, grant support and numbers, and statements of employment that could influence this work.


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