1. INTRODUCTION
The biological roles ascribed to selenium (Se) including the prevention of cancer (Combs & Lu, 2001) cardiovascular disease (Rayman, 2002, Beckett et al., 2004) and viral mutation (Beck 2001). In addition, the trace element is essential for optimal endocrine and immune function and moderating the inflammatory response (McKenzie et al., 2002, Arthur et al., 2003). Recent evidence points to a role for selenium compounds as well as seleno-proteins in the prevention of some forms of cancer [1]. Unlike other metal elements that interact with proteins in form of co-factors, selenium becomes cotranslationally incurporated into the poly-peptide chain as part of the amino acid selenocysteine (Sec). The entry point of selenium in animals is via plants, which absorb the element in its inorganic form from the soil. On a global scale, selenium availability in the soil varies between areas. Low selenium content is observed in volcanic regions and in regions with “acid soil”, such as the south-eastern parts of the United States (239, 298) [2].
The official documentation of Turkey’s selenium (Se) status is relatively poor in comparison with other countries, with little detailed information available regarding the Se content of soil or foodstuffs [3]. By comparison, the government of Canada, for example, has published Canadian Soil Quality Guidelines for Se [4], the UK government conducts monitoring and provides recommendations related to Se intake (Ministry of Agriculture, Fisheries and Food [5], and both Finland and New Zealand have carefully monitored their countries’ Se status. All of these countries have also supported the use of Se in fertilizers on a national scale [6,7]. Earlier publications have reported Se soil concentrations in Turkey to be lower than those of other countries [8,9] and also it has been reported daily selenium intake in Turkey to be 30 μg/day, 20 - 53 μg/day and 30 - 40 μg/day, respectively [10-12].
An interesting study by Aras and Kumpulainen [13] measured the Se content of Turkish wheat from four different regions in 1986, 1987, 1990, 1992, 1993 and 1994 and reported a mean Se value of 32 µg/kg, whereas Cankur [14] reported wheat products from the same three regions to have an average Se value of 89 µg/kg between 1995 and 1996. With regard to these differences, it should be noted that Se content in soil is a reflection of the atmospheric and anthropogenic weathering of parent materials and is thus widely variable, even at different times in the same area [15]. A research conducted in the same areas during 1997 and 1998 measured Se levels in wheat using spectrofluorometry and found a mean value of 81 µg/kg. In the same study, corn samples from local markets in the Eastern Black Sea Region were found to have an average Se content of 52 µg/kg, which was lower than the average of 76 µg/kg reported for Central Anatolia by Giray and Hıncal [3].
Another interesting study was conducted by Tuzen et al. [16] to identify trace elements, including Se, in 25 honey samples from different botanical sources collected from throughout Turkey (Figure 1). The lowest Se content (38 µg/kg) was reported from Antalya (Mediterranean) and the highest Se (113 µg/kg) from Bursa (West Anatolia). A lack of similar studies made it impossible for the authors to compare these levels with those of honey from other countries or from other research in Turkey. Some authors have suggested that honey and other bee products could be representative bio-indicators of environmental pollution (Conti & Botre, 2001; Leita et al., 1996; Yazgan et al., 2006). While honey may not be the most sensitive tool for the evaluation of environmental contamination from heavy metals because of the low concentrations in which these materials are present and the great variability in products due to factors including botanical origin, floral density, season and rainfall (Fredes & Montenegro, 2006), examining the Se content of honey to gain an understanding of Se status in Turkey could prove interesting [16]. In another study by Tuzen et al. [17], the authors examined the trace element composition of mushroom species from the Eastern Black Sea Region of Turkey, collecting 48 samples that included 16 different mushrooms species from different localities within the region. The lowest Se concentrations (0.54 μg/g) were reported in Panellus stipticus and the highest (10.8 μg/g) in Amanita pantherina. The authors reported these values to be in line with studies by Piepponen, Liukkonen-Lilja, & Kuusi (1983), Huerta, Sanchez, & Sanz-Medel (2005), Kalač & Svoboda (2000) and Agrahar-Murugkar & Subbulakshmi (2005), who reported values of 0.05 - 37 μg/g, 1.30 - 21.5 μg/g, 1 - 367 μg/g and 0.17 - 975 μg/kg, respectively.
There is no information currently available regarding maximum Se levels for fish in Turkey. However, a recent study by Tuzen and Soylak [18] examining trace element contents of canned anchovies, tuna, Black Sea bonito, sardines and trachurus trachurus purchased from major supermarket chains in Turkey found samples to be very rich in Se (Table 1). Of the various types of fish examined, the highest Se levels were found in canned Trachurus trachurus (3.64 µg/g) and the lowest in canned Black Sea bonito (0.96 µg/g).
A study of trace element contents in marine algae species collected from the Black Sea coast showed Se levels ranging from 11 µg/kg to 694 µg/kg [19].
In a recent study by Gezgin et al. [20], the Se content of various forms of black and green tea was evaluated using inductively coupled plasma atomic emission spectrometry (ICP-AES). Considering that tea is the most popular beverage in Turkey and is usually consumed on a daily basis, the results of this study are very important in terms of daily Se levels among the Turkish population. As Table 2 shows, Rize Turist black tea was found to have the highest Se levels of the various beverages tested.
Özcan [21] reported on the Se content of 32 plants used as spices and condiments in Turkey (Table 3). Samples were purchased from open markets in the Central Anatolian city of Konya. While the majority of plants tested had no detectable levels of Se, mustard, black cumin and parsley were found to have high levels of Se.
Figure 1. Honey samples collected from different cities of Turkey (Adapted from Tuzen et al., 2007a).
Table 1. Selenium content of canned fish samples from Turkey (adapted from Tuzen and Soylak, 2007).
Table 2. Selenium contents (ppm) of hot water extract (infusion) obtained from several commercial Turkish Teas (adapted from Gezgin et al., 2006).
A study by Demirezen and Uruç [22] used ICP-AES to identify the Se content in a total of 34 samples including 11 varieties of fish, meat and meat products representing approximately 80% - 90% of the fish, meat and meat products traditionally consumed in Turkey. Samples were obtained from local shops and producers in Kayseri during 2003 and 2004. Se levels were as follows: soudjouck, 3.9 ± 0.89 μg/100g; salami, 1.6 ± 0.98 μg/100g; sausage, 1.8 ± 0.6 μg/100g; pastırma, 4.6 ± 0.5 μg/100g; meat, 3.2 ± 0.99 μg/100g; minced meat, 1.6 ± 0.7 μg/100g; Pomatomus saltatrix (blue fish), 3.68 ± 0.7 μg/100g; Micromesistius poutassou (mackerel), 1.32 ± 2.98 μg/100g; Saurel, Engraulis encrasicholus (anchovy), 3.3 ± 0.8 μg/100g; Gadus euxina (blue whiting), 1.8 ± 0.9 μg/100g; Sarda sarda (bonito), 2.3 ± 0.98 μg/100g. Mean concentrations of Se in fish (2.8 μg/100g) were similar to values recommended by the World Health Organization (2.55 μg/100g) for Turkey (WHO, 1992), and mean concentrations of Se in meat and meat products (2.8 μg/100g) exceeded those reported by the World Health Organization (1.6 μg/100g) (WHO, 1992) [22].
Beytut et al., [23] examined the Se contents in soil, meadow hay and sheep heart and gluteal muscles in the Kars region, a major sheep-rearing area in Turkey and one where there is a high lamb mortality rate due to white muscle disease (WMD). Se levels in soil and meadow hay collected from the disease foci were found to be 0.03 ppm and 0.07 ppm (dry weight), respectively. The authors noted that these levels were low in comparison to the literature, which included reported soil levels of 0.1 (Bostedt & Schramel, 1990) and 2.0 ppm Andres et al. (1997) and pasture and forage levels of at least 0.1 ppm (McDowell, 1992).
Se contents in milk and other dairy products from the Central Anatolian Region of Turkey have been reported on by Ayar et al. [24] (Table 4); no discernible Se contents were detected in ice cream, milk powder, whey powder or yogurt samples. The highest average Se content was found in Tulum cheese (0.43 mg/kg), followed by butter (0.315 mg/kg). The authors reported that the Se contents in milk, butter, white cheese, yellow cheese and Tulum cheese consumed in Turkish society on a daily basis was higher than the RDA [24].
Demirel et al. [25]; have provided assessments of the Se content of a variety of commonly consumed fresh and canned foods from the Central Anatolian city of Tokat (Table 5). Of the various samples tested, the highest Se levels were found in tomato sauce (0.801 μg/g) and the lowest in beer (0.026 μg/mL). The authors also reported a Se level of 151 ng/g in garlic, which was lower than a previous study by Inam and Somer (1999), which reported a range of 365 - 485 ng/g.
Turkish hazelnuts have, in general, been reported to have a high Se content. A study by Dundar and Altuntag [26] examined the Se content of three different varieties of hazelnut cultivated in the Kocaali, Karasu, Akyazı,
Table 3. Selenium content of plants (adapted from Özcan 2004).
Table 4. The average selenium content (mg/kg) of milk and dairy products in middle Anatolia (Adapted from Ayar et al., 2009).
Table 5. Selenium content of some foods from Tokat (Adapted from Demirel et al., 2008).
Hendek, and Ferizli districts of the province of Sakarya in the Marmara Region of Turkey during the 2001 harvesting season. Mean Se levels of unhulled and hulled Kara Fındık, Tombul and Delisava hazelnut varieties were found to be 4.7 μg/g and 7.0 μg/g, 3.6 μg/g and 9.5 μg/g, and 16.9 μg/g and 6.6 μg/g, respectively. The difference in Se content between hulled and unhulled hazelnut kernels as well as the differences in Se content among regions were found to be statistically significant. The highest Se levels were observed in hulled Tombul hazelnuts from Ferizli, and the lowest Se levels were observed in unhulled Kara Fındık and Tombul hazelnuts from Karasu. Another study by Simsek and Aykut [27] examined Se content in 16 hazelnut varieties collected in 2002 by the Hazelnut Research Institute from the provinces of Ordu and Giresun in the Black Sea Region. Reported Se levels (0.96 - 1.39 μg/g) were significantly lower than those reported by Dundar and Altuntag [26].
Most of the above-mentioned reports indicate low Se levels in the Black Sea Region. This could be due to low soil selenium levels in the region, which has consistently high rainfall, which could result in leaching of minerals from the soil to the sea.
2. BLOOD SELENIUM LEVELS AMONG THE TURKISH POPULATION
In their first report on the Se levels among the Turkish population, Hıncal et al [28] found a mean blood Se level of 88 ± 12 µg/l serum among a population of 76 middle-to-upper-middle-income children living in Ankara. A subsequent study by Hıncal et al. [29] conducted among a socio-economically heterogeneous population of 218 subjects from urban Ankara reported mean Se levels of 45 ± 10 µg/l in cord blood at birth, 74 ± 14 µg/l in children aged 2 - 16 years and 74 ± 16 µg/l in adults aged 18 - 48. In an extended study by Giray and Hıncal [3] conducted in all seven geographical regions of Turkey, the authors reported a mean Se plasma level of 71 ± 15 µg/l among 274 subjects aged 19 - 61 years randomly selected from middle to middle-upper income families. No Se deficiency was observed in any region, although the Black Sea Region had the lowest mean Se level (Table 6). Similar results were obtained by Mengubas et al. [30] who measured Se plasma levels in 250 school-age children from four different regions of Turkey and found mean levels of 75 ± 9 μg/l for boys and 65 ± 10 μg/l for girls. Two other studies of schoolchildren were conducted by Isbir et al. [31,32]. The first study, conducted in Adana, reported serum Se levels of 0.73 ± 0.11 μmol/l and 0.92 ± 0.10 μmol/l among children aged 7 - 8 years and 11 - 12 years, respectively. The second study, conducted in Konya, reported a similar level among 600 healthy children aged 7 - 12. Our own research Ozdemir et al. [33]
Table 6. Plasma selenium levels of adults (19 - 61 years old) from different geographical region of Turkey (adapted from Giray and Hıncal, 2004).
conducted in the Van Basin in Eastern Turkey, found a mean plasma Se level 68.52 ± 3.57 ng/ml among 30 pregnant women aged 26.4 ± 2.1 years. This value is much higher than that reported in a study among pregnant women in the Central Anatolian province of Kayseri, which found a mean Se value of 35.14 ± 6.71 ng/ml (range: 23.22 - 53.86 ng/ml). Kilinc et al. [34] reported that se blood level of Women with 10 - 14 of gestational weeks was 44.85 ± 9.23; in 16 - 20 weeks of gestation was 47.18 ± 10.92; in non-pregnant women was 55.38 ± 8.81 respectively in Kahramanmaras. According to report of Dobrzynskia et al., 1998; for optimum balance of pregnancy at least 100 mg dietary Se is needed. Therefore reported results (47.18 ng/ml) from Kahramanmaras almost the half of the needed level of Se pregnancy (at least 100 mg dietary).
3. CONCLUSION
This review is the first to report on all published information available on Se status in Turkey, including Se levels in soils, foods and human plasma. The Se cycle begins and ends with the soil, with the need for Se supplements among human or animal populations based on the chemical composition and Se concentrations in soil. However, currently available data on Se intake in humans and Se soil levels are based on limited, local data that cannot be generalized to the Turkish population and area as a whole. Therefore, further studies need to be conducted to determine soil Se content for Turkey as soon as possible. Furthermore, in Turkey, most small ruminants and native cattle spend half the year grazing extensively and are not provided with supplemental feed and are thus significantly and directly affected by Se deficiencies in soil. If it is determined that Se deficiency is a problem in Turkey, solutions may include direct supplements for humans and animals, the addition of Se to fertilizers, as is done in some Scandinavian countries, or the coating of seeds with Se, as in Canada. Given the majority of data from the Black Sea Region, it can be expected that this population may suffer from Se deficiencies.