Literature DB >> 20652650

Natural variation in grain selenium concentration of wild barley, Hordeum spontaneum, populations from Israel.

Jun Yan1, Fang Wang, Haibo Qin, Guoxiong Chen, Nevo Eviatar, Tzion Fahima, Jianping Cheng.   

Abstract

Wild barley (Hordeum spontaneum), the progenitor of cultivated barley, is an important genetic resource for cereal improvement. Selenium (Se) is an essential trace mineral for humans and animals with antioxidant, anticancer, antiarthropathy, and antiviral effects. In the current study, the grain Se concentration (GSeC) of 92 H. spontaneum genotypes collected from nine populations representing different habitats in Israel was investigated in the central area of Guizhou Province, China. Remarkable variations in GSeC were found between and within populations, ranging from 0 to 0.387 mg kg(-1) among the 92 genotypes with an average of 0.047 mg kg(-1). Genotype 20_C from the Sede Boqer population had the highest GSeC, while genotype 25_1 from the Atlit population had the lowest. The mean value of GSeC in each population varied from 0.010 to 0.105 mg kg(-1). The coefficient of variation for each population ranged from 12% to 163%. Significant correlations were found between GSeC and 12 ecogeographical factors out of 14 studied. Habitat soil type also significantly affected GSeC. The wild barley exhibited wider GSeC ranges and greater diversity than its cultivated counterparts. The higher Se grain concentrations found in H. spontaneum populations suggest that wild barley germplasm confer higher abilities for Se uptake and accumulation, which can be used for genetic studies of barley nutritional value and for further improvement of domesticated cereals.

Entities:  

Mesh:

Substances:

Year:  2010        PMID: 20652650      PMCID: PMC3152716          DOI: 10.1007/s12011-010-8770-6

Source DB:  PubMed          Journal:  Biol Trace Elem Res        ISSN: 0163-4984            Impact factor:   3.738


Introduction

The essential trace mineral selenium (Se) is of fundamental importance to human and livestock health [1-3]. Se enters the food chain mainly through plants. In many countries, soils are often low in available Se; hence, the food systems are deficient in Se [4-6]. Based on surveys of plasma or serum Se levels, Combs [4] estimated that from half a billion to a billion people worldwide may suffer from Se deficiency. Cereals, meat, and fish are the main sources of Se in most diets [4]. In foods, the Se exists in different chemical forms, with Se being generally more bioavailable from plants than from animal foodstuffs [7, 8]. More than 80% of the total Se in seleniferous corn, wheat, and soybean consists of l-(1)-selenomethionine [9], which is the most appropriate supplemental form of Se in major staple foods [10]. As a main source of calorie intake, cereal-based foods are extensively consumed in the developing world [11]. However, cereals are inherently very poor in both concentration and bioavailability of microelements such as Zn, Fe, and Se in the seeds, particularly when grown in microelement-deficient soils [8, 11, 12]. Cereal crops such as wheat, barley, rye, and oats are non-Se-accumulators, rarely accumulating more than 0.1 mg Se kg−1 dry weight [13]. Developing cereals that are genetically enriched in micronutrients and proteins and improving their bioavailability (biofortification) using genetics and genomics tools are considered as promising and cost-effective approaches to reducing malnutrition [6, 14–17]. Moreover, the existence of large genetic variation in grain micronutrients is essential for a successful breeding program aimed at the development of new micronutrient-rich plant genotypes. Wild barley, Hordeum spontaneum C. Koch, is the progenitor of cultivated barley, Hordeum vulgare L. ssp. vulgare [18]. It is widely distributed throughout the eastern Mediterranean rim and western Asian countries [18]. The center of diversity for H. spontaneum and the primary site of its domestication are considered to be the Fertile Crescent of the Near East [18-20]. In Israel, H. spontaneum is abundant, occupying an extraordinarily large diversity of habitats ranging from the mesic Mediterranean to the xeric southern steppes [21]. Several decades of studies on genetic resources of wild cereals (wheat and barley) for crop improvement, conducted at the Institute of Evolution at the University of Haifa, Israel, have revealed that the vast genetic resources of wild cereals have great potential for improving the narrowing genetic base of domesticated cereals [18, 21–26]. Moreover, barley has a self-fertile, diploid (2n = 2x = 14) genetic system and can therefore serve as a model species for genetic and physiological studies in Triticeae species [27]. In particular, barley cannot be grown in soil with excess Se without the risk of Se toxicity because it is a Se-sensitive plant [18]. Therefore, wild barley is an optimized model species for improving grain Se content in cereals via gene introgression. The objectives of the present study were to analyze the variation in grain Se concentration (GSeC) in Israeli H. spontaneum populations and to choose a set of donor parents for the breeding of Se-enriched barley cultivars.

Materials and Methods

Plant Materials

Ninety-two genotypes from nine populations of the wild barley H. spontaneum, representing different geographical zones in Israel (Fig. 1 and Table 1), were used in the present study. All nine populations were selected from the Gene Bank Collection of the Institute of Evolution at the University of Haifa: six of them originated from mesic habitats in the north and center of Israel, with mean annual rainfall of >500 mm, Mt. Hermon (population 1), Maalot (10), Akhziv (24), Atlit (25), Caesarea (26), and “Evolution Canyon” (37); and the other three were from xeric habitats in Israel's central and southern regions, with mean annual rainfall of <300 mm, Sede Boqer (20), Mehola (22), and Ein-Zukim (near the Dead Sea; 32; Fig. 1 and Table 1). Ten barley cultivars from five provinces in China—Yangnongpi 5, Yancheng 01094, and Supi 4 from Jiangsu Province; Ganpi 3 from Gansu Province; Baoshan 8640-1, Yunpi 2, and Yunpi 6 from Yunnan Province; E32380 from Hubei Province; and Zhexiu 13 and Zhexiu 33 from Zhejiang Province—were used as controls. All cultivars were provided by the Hangzhou National Barley Improvement Center in China.
Fig. 1

Geographical location of Israeli Hordeum spontaneum populations used in the present study. 1, Mt. Hermon; 10, Maalot; 20, Sede Boqer; 22, Mehola; 24, Akhziv; 25, Atlit; 26, Caesarea; 32, Ein-Zukim; 37, “Evolution Canyon”

Table 1

Ecogeographical Factors of the Nine Hordeum spontaneum Populations in Israel

IDa PopulationLnLtAlTmTaTjTdTddEvRnRdHu14HuanSo
1Mt. Hermon35.7533.281,530112011961601,4007052581
10Maalot35.2733.005001723815101507855550642
20Sede Boqer34.7830.87450192691513168911536536
22Mehola35.4832.13−15022301317131802703934533
24Akhziv35.1033.051020261213101306205660673
25Atlit34.9532.70502026131391335004865724
26Caesarea34.9032.50102026131391305404865724
32Ein-Zukim35.4431.74−20024311516122101002035526
37Evolution Canyon34.5832.439022.528131591426004865671

Geographical variables: Ln = longitude (decimal), Lt = latitude (decimal), and Al = altitude (meters). Temperature variables: Tm = mean annual temperature (°C), Ta = mean August temperature (°C), Tj = mean January temperature (°C), Td = mean seasonal temperature difference (°C), Tdd = mean daily temperature difference (°C), and Ev = mean annual evaporation. Water variables: Rn = mean annual rainfall (millimeters), Rd = mean number of rainy days, Hu14 = mean humidity at 1400 hours (percent), Huan = mean annual humidity (percent), and Dw = mean number of dewy nights in summer (millimeters). Dummy soil variables: So = soil types, 1 terra rosa, 2 rendzina, 3 alluvium, 4 sandy loam, 6 loess (desert soil)

aPopulation IDs and selected environmental data are based on [21]; Ein-Zukim data is based on [63]

Geographical location of Israeli Hordeum spontaneum populations used in the present study. 1, Mt. Hermon; 10, Maalot; 20, Sede Boqer; 22, Mehola; 24, Akhziv; 25, Atlit; 26, Caesarea; 32, Ein-Zukim; 37, “Evolution Canyon” Ecogeographical Factors of the Nine Hordeum spontaneum Populations in Israel Geographical variables: Ln = longitude (decimal), Lt = latitude (decimal), and Al = altitude (meters). Temperature variables: Tm = mean annual temperature (°C), Ta = mean August temperature (°C), Tj = mean January temperature (°C), Td = mean seasonal temperature difference (°C), Tdd = mean daily temperature difference (°C), and Ev = mean annual evaporation. Water variables: Rn = mean annual rainfall (millimeters), Rd = mean number of rainy days, Hu14 = mean humidity at 1400 hours (percent), Huan = mean annual humidity (percent), and Dw = mean number of dewy nights in summer (millimeters). Dummy soil variables: So = soil types, 1 terra rosa, 2 rendzina, 3 alluvium, 4 sandy loam, 6 loess (desert soil) aPopulation IDs and selected environmental data are based on [21]; Ein-Zukim data is based on [63] A randomized complete block design with three replications was used. Seeds of the 92 wild barley genotypes and ten barley cultivars were sown in a field of loess soil under natural rainfall conditions at an experimental station in the central area of Guizhou Province, China (latitude 26°25′, longitude 106°40′, altitude 1,096 m, mean annual rainfall 1,500 mm, soil Se content 0.20 mg kg−1, and pH 6.6) in mid November 2006. Fully mature spikes were harvested manually from May to June 2007.

Determination of Se in Barley Seeds

The barley caryopses were dehulled by removing awn, glumes, lemma, and palea. Se concentration in the barley grains was determined by hydride generation-atomic fluorescence spectrometry (HG-AFS) following a modified protocol [28] at the State Key Laboratory of Environmental Geochemistry, Institute of Geochemistry, Chinese Academy of Sciences. The grains were washed thoroughly with deionized water, dried at 70°C, pulverized, and passed through a 100-mesh (0.149 mm) sieve. For digestion, 0.100 g of each sample was digested in a 50-mL PTFE tube with 3 mL HNO3 (GR grade, Merck) at room temperature for 3 h and then at 145°C for 8 h. After cooling to room temperature, the tube was opened, and 2 mL H2O2 (GR grade, Merck) was added. The mixture was evaporated to dryness at 70°C. The dried mixture was redissolved in 3 mL 5 M HCl (ACS grade, Fisher Scientific) and transferred to a 25-mL volumetric glass tube (Pyrex). The final solution was prepared by heating it at 90°C in a water bath for 90 min and then diluting it to 25 mL with deionized water. An atomic fluorescence spectrometer AFS-920 equipped with a sequential injection HG sampling system (Beijing Titan Instrumentals Co. Ltd., Beijing, China) was used for Se measurement. The Hg sampling system provides high sensitivity and rapid isolation of Se from the mixture. A Se hollow cathode lamp was used as the radiation source at 196.0 nm. The hydride was atomized with an argonhydrogen flame. The operating parameters of the HG-AFS were optimized and are summarized in Table 2. Titan standard software was used for system control and data analysis.
Table 2

Operating Parameters of the Hydride Generation-Atomic Fluorescence Spectrometry

ParametersSettings
Selenium hollow cathode lamp196.0 nm
Lamp current75 mA
Negative high voltage of photomultiplier265 V
Atomizer height8 mm
Atomization temperature200°C
Carrier HCL flow0.72 mol/L (6%)
KHB4 concentration1% (w/v) (in 0.2% (w/v) NaOH solution)
Carrier argon flow400 mL/min
Shield argon flow800 mL/min
Operating Parameters of the Hydride Generation-Atomic Fluorescence Spectrometry Se concentration was expressed as milligram per kilogram dry weight. During the analysis, a reference substance (GSV-1 and GSV-3, Se concentration of 0.184 ± 0.01 and 0.140 ± 0.01 mg kg−1, respectively), a blank, and duplicate samples (one duplicate per five samples) were used to ensure the accuracy and precision of the results (quality control). The measured values of GSV-1 and GSV-3 were 0.185 ± 0.01 (n = 6) and 0.153 ± 0.003 mg kg−1 (n = 4), respectively, which is consistent with the reference value. The blank was well below the detection limit (0.2 μg L−1). The results of the duplicate samples were relatively good with a coefficient of variation (CV) in the range of 1.3% to 6.0%.

Statistical Analysis

JMP6.0 (SAS Institute) software was used to perform analysis of variance (ANOVA). Tukey–Kramer's honestly significant difference (HSD) test was used to compare means of all pairs (significance level, 5%). Spearman's rho correlation was used to analyze the multivariate correlations.

Results

Natural Variation in H. spontaneum GSeC

Large variations were observed in H. spontaneum GSeC among the 92 genotypes and nine populations, respectively (Fig. 2 and Table 3). GSeC among the 92 genotypes ranged from 0 to 0.387 mg kg−1, with an average of 0.045 mg kg−1. The genotype with the highest GSeC was 20_C, which originated in the Sede Boqer population, while that with the lowest GSeC was 25_1, originating from the Atlit population. The mean value of GSeC in each population varied from 0.010 to 0.105 mg kg−1. GSeC of the Sede Boqer population, which ranged from 0.010 to 0.387 mg kg−1 and averaged 0.105 mg kg−1, ranked highest among the nine populations, while GSeC of the Atlit population, ranging from 0 to 0.014 mg kg−1 and averaging 0.010 mg kg−1, ranked the lowest. One-way ANOVA indicated significant differences in GSeC among the nine H. spontaneum populations (P ≤ 0.001). The population CV showed large differences among the nine populations, ranging from 12% for the “Evolution Canyon” population to 163% for the Caesarea population.
Fig. 2

GSeC of 92 Hordeum spontaneum genotypes

Table 3

GSeC of Nine Hordeum spontaneum Populations and Ten Hordeum vulgare Cultivars

IDPopulations/varietySamplesGSeC (mean ± SD; mg kg−1)Range (mg kg−1)CV (%)
1Mt. Hermon90.015 ± 0.0040.010–0.02631
10Maalot100.019 ± 0.0070.011–0.13139
20Sede Boqer100.105 ± 0.1330.010–0.387128
22Mehola80.015 ± 0.0040.010–0.02127
24Akhziv80.015 ± 0.0050.012–0.02429
25Atlit80.010 ± 0.0040.000–0.01442
26Caesarea100.053 ± 0.0870.010–0.244163
32Ein-Zukim220.080 ± 0.0720.015–0.21190
37Evolution Canyon70.039 ± 0.0460.014–0.12312
Sum of Wild barley920.045 ± 0.0700.000–0.38712–163
Zj1Yunpi 21 × 30.028 ± 0.003
Zj2Yunpi 61 × 30.039 ± 0.008
Zj3Zhexiu 121 × 30.134 ± 0.012
Zj4E323801 × 30.073 ± 0.013
Zj5Yangnongpi 51 × 30.077 ± 0.005
Zj6Baoshan8640-11 × 30.000 ± 0.000
Zj7Yancheng 010941 × 30.000 ± 0.000
Zj8Zhexiu331 × 30.144 ± 0.010
Zj9Ganpi 31 × 30.000 ± 0.000
Zj10Supi 41 × 30.000 ± 0.000
Sum of cultivars10 × 30.050 ± 0.0560.000–0.144112
GSeC of 92 Hordeum spontaneum genotypes GSeC of Nine Hordeum spontaneum Populations and Ten Hordeum vulgare Cultivars

GSeC of Cultivated Barley as Compared with H. spontaneum

The GSeCs of the ten barley cultivars ranged from 0.000 to 0.144 mg kg−1 (Table 3). Baoshan 8640-1 from Yunnan Province, Ganpi 3 from Gansu Province, and Yancheng 01094 and Supi 4 from Jiangsu Province had the lowest value of 0.000 mg kg−1, whereas Zhexiu 13 and Zhexiu 33 from Zhejiang Province had the highest values, 0.134 and 0.144 mg kg−1, respectively. However, the highest GSeC in a cultivar, that of cv. Zhexiu 33, was far lower than the highest GSeC in a wild barley genotype, that of 20_C (0.387 mg kg−1). A total of 11 H. spontaneum genotypes (three genotypes from Sede Boqer, six from Ein-Zukim, and two from Caesarea) had higher GSeCs than Zhexiu 33. The CV for the ten cultivars was 112%, which was also lower than the highest CV (163%) in the Caesarea wild barley population. As expected, the cultivars exhibited a narrower GSeC range and less diversity than the wild barley.

Association of H. spontaneum GSeC with Ecogeographical Factors

Of the 14 correlations analyzed between GSeC and ecogeographical factors, 12 were statistically significant (Fig. 3). GSeC was negatively correlated with latitude, altitude, mean annual rainfall, mean number of rainy days, mean humidity at 1400 hours, and mean annual humidity and positively correlated with mean annual temperature, mean August temperature, mean January temperature, mean seasonal temperature difference, mean daily temperature difference, and mean annual evaporation, indicating that GSeC increased with temperature and evaporation and decreased with latitude, altitude, rainfall, and humidity, irrespective of longitude. Therefore, GSeC was mainly influenced by temperature and water conditions. One-way ANOVA showed that the mean GSeC of xeric genotypes was significantly greater than that of mesic genotypes (P = 0.0004).
Fig. 3

Spearman's rho correlation between GSeC and ecogeographical data (Table 1) of the original sites of nine Hordeum spontaneum populations in Israel

Spearman's rho correlation between GSeC and ecogeographical data (Table 1) of the original sites of nine Hordeum spontaneum populations in Israel Moreover, nine H. spontaneum populations were derived from five soil types (Table 4), and one-way ANOVA indicated a significant difference in GSeCs among the H. spontaneum originating from those five soil types (P = 0.0003). GSeC of H. spontaneum originated from loess was the highest, while that of H. spontaneum originated from alluvium was the lowest. Tukey–Kramer HSD test indicated that except for loess, the other four soil types—terra rosa, rendzina, alluvium, and sandy loam—gave similar GSeC values, and there was a significant difference in this parameter between loess and these other four soil types (Table 4).
Table 4

GSeC of Hordeum spontaneum Originated From Five Different Soil Types in the Collection Site in Israel

Soil type (in the collection site)SamplesPopulationMean ± SD (mg kg−1)Range (mg kg−1)CV (%)Tukey–Kramer HSD test, P < 0.05a
1, Terra Rosa16Mt. Hermon0.016 ± 0.0040.010–0.02623b
Evolution Canyon
2, Rendzina10Maalot0.019 ± 0.0070.011–0.03139b
3, Alluvium16Mehola0.015 ± 0.0040.010–0.02427b
Akhziv
4, Sandy loam18Atlit0.034 ± 0.0670.000–0.244196b
Caesarea
6, Loess32Sede Boqer0.088 ± 0.0940.010–0.387107a
Ein-Zukim
ANOVA P ≤ 0.001

aDifferent letters stand for significant differences among soil types

GSeC of Hordeum spontaneum Originated From Five Different Soil Types in the Collection Site in Israel aDifferent letters stand for significant differences among soil types Moreover, there were no significant correlations between GSeC and 1,000-grain weight for either wild H. spontaneum (P = 0.08) or barley cultivars (P = 0.41), indicating that higher GSeC is not necessarily related to small grain weight in barley.

Discussion

General Overview of Se in Food Plants

Se levels in food plants are generally low, with worldwide data on cereal and grain Se levels reporting <0.1 to 0.8 mg kg−1 [29]. However, cereals and their products make a major contribution to the dietary intake of Se in the population worldwide, especially in developing countries such as China and India [11]. The World Health Organization and Food and Agriculture Organization normative requirement estimates of dietary Se are 0.04 and 0.03 mg day−1 for men and women, respectively [30]. The US, Canadian, and European recommended dietary allowance (RDA) for Se is 0.055 mg day−1 [31, 32]. In Australia and New Zealand, the RDA for adult men and women is 0.07 and 0.06 mg day−1, respectively [33]. In the UK, the reference nutrient intake is set at 0.075 and 0.060 mg day−1 for adult males and females, respectively [34]. In many countries, rice and wheat are the most commonly consumed cereals. Nevertheless, Se levels in rice and wheat sold for domestic consumption are insufficient in some countries, for example, a mean Se level in rice of 0.05 mg kg−1 in Thailand and 0.02 mg kg−1 in China [2]. British wheat has low Se status [35], with Se levels in bread being approximately 0.039 to 0.048 mg kg−1 [2]. The average wheat GSeC in Scandinavian countries ranges from 0.007 to 0.018 mg kg−1 [36]. Aro et al. [37] reported mean wheat GSeCs of 0.001, 0.005, and 0.028 mg kg−1, respectively, in three studied villages of Transbaikalian Russia. Most of the world's wheat falls within the ca. 0.002 to 0.060 mg kg−1 range [38]. Consequently, Se malnutrition afflicts quite a few people, especially those living in areas of very low Se availability in soils and extremely low Se concentrations in staple crops [4, 8]. On the other hand, the bioavailability of organic Se in plant and animal sources is higher than that of the inorganic selenate and selenite [31]. Moreover, Se in wheat grain is highly bioavailable compared to some fish and vegetables [32, 39, 40], and wheat is the most efficient Se accumulator of the common cereal crops [5]. Therefore, in recent years, researchers have focused on strategies to exploit genetic resources and develop genetically Se-enriched and protein-Se-enriched wheat using genomics tools [5, 6, 15, 31, 41–44].

Se in Barley

Surprisingly, reports on GSeC in barley have been scant in recent years. Barley is one of the principal cereal crops, the fourth largest in the world. It serves as a major animal feed crop and as human food it is used for malting, which in turn is used to make beer, whisky, and several other products such as bread, biscuits, and soups. In Chinese Tibet, barley was grown mostly as a staple food for humans. Recently, however, interest in barley as a food grain is reviving due to heightened consumer awareness of good nutrition and increased interest in foods and food ingredients that are enriched in dietary fiber [45]. Barley is not only an economically important crop but it is also considered as a model species for genetic studies [46, 47]. Wild barley, as the progenitor of cultivated barley, is an important genetic resource that can be exploited in breeding programs for the introduction of resistance to a broad range of diseases and pests, tolerance to drought, salt, poor soils and climate factors, and key properties, e.g., malting content, kernel weight, size, color, and dormancy [22, 23, 48–52]. In the current study, a wide range and very high GSeCs were found in 92 genotypes of H. spontaneum from nine populations. GSeCs of 11 H. spontaneum genotypes were higher than that of the highest cultivar (Zhexiu 33) out of ten Chinese cultivars. The genotype of H. spontaneum with the highest GSeC (20_C) had 2.7 times the GSeC of cv. Zhexiu 33 (Table 3 and Fig. 2). Furthermore, in the current set of experiments, the grains were harvested from plants that had been grown in the same location, at the same time, under the same conditions. Therefore, the variation in GSeC revealed genetic differences resulting from the adaptation of H. spontaneum to different eco-environments. Our results demonstrate the huge potential of wild barley for improvement of GSeC. These high-GSeC H. spontaneum genotypes can be utilized as a set of donor parents for biofortification of barley cultivars and as optimized model plants for the improvement of cereal Se concentration via gene introgression, towards the development of Se-enriched cereals in the future. The environment is a key contributor to the range of morphological variation found in various organisms [53]. Associations between the performance of wild barley populations and the ecogeographical conditions of their collection sites can shed light on the major driving forces contributing to the ecological fitness of these populations and, more specifically, to the development of their Se uptake and accumulation mechanisms. In the current study, Spearman correlation analysis showed that high temperature and evaporation and low latitude, altitude, rainfall, and humidity at the site in which H. spontaneum originated are favorable to wild barley having gained a strong ability to take up Se from the soil and to accumulate Se in its grains during evolution. This could explain why the Sede Boqer and Ein-Zukim populations, which originated in sites with the lowest latitude, altitude, and rainfall and highest temperature and evaporation, had the highest GSeCs, while the Mt. Hermon population, originating in the site with the lowest temperature and highest latitude, altitude, and rainfall, was ranked second lowest in GSeC of the nine populations. Soil type at the H. spontaneum collection site was also an important factor affecting its ability to take up Se and to accumulate Se in its grains. The report drew particular attention to the wide range of Se concentrations in different types of foods and revealed that the variations are due to differences in Se availability in the soil on which an animal is raised or a plant grown [2]. In the present study, nine H. spontaneum populations were derived from five soil types. GSeC of H. spontaneum originating from loess soil was highest and significantly higher than the GSeC in H. spontaneum originating from alluvium (lowest), terra rosa, rendzina, and sandy loam (Table 4). Our results suggest that loess has low Se availability and that the wild barley growing there has developed strong Se uptake and accumulation abilities. Se occurs in well-drained alkaline soils chiefly as selenates, which are highly available for absorption by plant roots. In contrast, in acidic, poorly drained soils, it is present mainly as selenides, which are not available to plants, and sometimes as elemental Se [54]. In reality, the loess soil in both Sede Boqer and Ein-Zukim was not true loess, but a desert soil which was very poorly drained. However, to support this hypothesis, additional studies are required to determine soil Se content and availability in the original sites from which the H. spontaneum populations were collected. All of the results of this study clearly demonstrate that the evolutionary background of the environments has a strong effect on GSeC of wild barley. H. spontaneum is hermaphroditic and self-pollinating [55], with a fragile rachis that breaks apart after maturation [56], such that the spikelets become entangled in the remains of their dry mother plants, contributing to the development of local genotypes. The great biodiversity found among these genotypes is the result of adaptations to local environmental factors in each area and microhabitat. These factors include the amount of rain, temperature, type and depth of soil, slope direction, shade, presence of stones, rocks, salinity, and possibly also other factors [57]. A particular food may show an over tenfold difference in Se content, depending on where it was produced. Se levels in foods can vary enormously, not only between countries but also between regions within a country [2]. Stochastic environmental fluctuations create a mosaic of habitats in which variation takes place in a temporal rather than spatial dimension [58]. Therefore, the genetic population structure of barley is a mosaic. In the present study, though the Caesarea population originated in a mesic habitat, it ranked third out of nine populations in GSeC. The Mehola population, originating in a xeric habitat, ranked second lowest in GSeC. Our results indicate that large differences exist between and within populations. The CV of each of the nine populations ranged from 12% to 163%. In the Sede Boqer population, the CV was large (128%), and the GSeC of the highest genotype 20_C was 38.7 times higher than that of genotype 20_40. Thus, the genetic mosaic appears to reflect the underlying ecological heterogeneity, which derives from local and regional geological, edaphic, climatic, and biotic differentiations [59]. The genetic mosaicism of wild barley GSeCs is the basis of barley GSeC improvement. The high-GSeC genotypes selected in the present study will be used to breed for barley cultivars with high GSeC. Cultivated barley contains, on average, 40% H. spontaneum alleles [60]. Because H. spontaneum and cultivated barley are inter-fertile, H. spontaneum can be used to increase the genetic diversity of cultivated barley by crosses [61]. In the past, breeders were reluctant to use exotic germplasm in their breeding programs due to linkage drag of negative traits. However, modern genomic technologies have led to the development of marker-assisted selection (MAS) approaches that enable efficient transfer of only small chromosome segments carrying the target gene and therefore avoiding linkage drag of negative traits. For example, the stripe rust resistance gene Yr15, derived from wild emmer wheat, is being utilized in MAS wheat breeding programs in the USA (http://maswheat.ucdavis.edu/Index.htm). A few years ago, the high grain protein and mineral gene, Gpc-B1 (TtNAM-B1), was cloned from wild emmer wheat [14]. The absence of the functional TtNAM-B1 wild emmer allele in modern germplasm suggests a broad potential impact of this gene in breeding of cultivated wheat varieties [14]. Moreover, a homologous barley gene, designated HvNAM-1 was shown to be responsible for the grain protein QTL located on barley chromosome 6H [62]. Therefore, the results presented in the current and previous studies demonstrate the potential of wild cereal populations as a rich source for grain protein and mineral content genes for crop improvement.
  19 in total

1.  Wild barley: a source of genes for crop improvement in the 21st century?

Authors:  R P Ellis; B P Forster; D Robinson; L L Handley; D C Gordon; J R Russell; W Powell
Journal:  J Exp Bot       Date:  2000-01       Impact factor: 6.992

2.  The international barley sequencing consortium--at the threshold of efficient access to the barley genome.

Authors:  Daniela Schulte; Timothy J Close; Andreas Graner; Peter Langridge; Takashi Matsumoto; Gary Muehlbauer; Kazuhiro Sato; Alan H Schulman; Robbie Waugh; Roger P Wise; Nils Stein
Journal:  Plant Physiol       Date:  2009-01       Impact factor: 8.340

3.  Selenium distribution in wheat grain, and the effect of postharvest processing on wheat selenium content.

Authors:  Graham H Lyons; Yusuf Genc; James C R Stangoulis; Lyndon T Palmer; Robin D Graham
Journal:  Biol Trace Elem Res       Date:  2005-02       Impact factor: 3.738

Review 4.  Nutritional selenium supplements: product types, quality, and safety.

Authors:  G N Schrauzer
Journal:  J Am Coll Nutr       Date:  2001-02       Impact factor: 3.169

5.  Selenium in Australia: selenium status and biofortification of wheat for better health.

Authors:  Graham H Lyons; Geoffrey J Judson; Ivan Ortiz-Monasterio; Yusuf Genc; James C R Stangoulis; Robin D Graham
Journal:  J Trace Elem Med Biol       Date:  2005       Impact factor: 3.849

Review 6.  The importance of selenium to human health.

Authors:  M P Rayman
Journal:  Lancet       Date:  2000-07-15       Impact factor: 79.321

7.  Absorption of selenium from wheat, garlic, and cod intrinsically labeled with Se-77 and Se-82 stable isotopes.

Authors:  Tom E Fox; Caroline Atherton; Jack R Dainty; D John Lewis; Nicola J Langford; Malcolm J Baxter; Helen M Crews; Susan J Fairweather-Tait
Journal:  Int J Vitam Nutr Res       Date:  2005-05       Impact factor: 1.784

Review 8.  Selenium in global food systems.

Authors:  G F Combs
Journal:  Br J Nutr       Date:  2001-05       Impact factor: 3.718

9.  Genetic diversity of wild emmer wheat in Israel and Turkey : Structure, evolution, and application in breeding.

Authors:  E Nevo; A Beiles
Journal:  Theor Appl Genet       Date:  1989-03       Impact factor: 5.699

10.  Selenium distribution in camel blood and organs after different level of dietary selenium supplementation.

Authors:  Rabiha Seboussi; Bernard Faye; Ghaleb Alhadrami; Mustafa Askar; Wissam Ibrahim; Baaha Mahjoub; Khalil Hassan; Tarik Moustafa; Ahmed Elkhouly
Journal:  Biol Trace Elem Res       Date:  2009-06-02       Impact factor: 3.738

View more
  4 in total

Review 1.  Selenium accumulation by plants.

Authors:  Philip J White
Journal:  Ann Bot       Date:  2015-12-29       Impact factor: 4.357

2.  A Bibliometric Analysis of Research on Selenium in Drinking Water during the 1990-2021 Period: Treatment Options for Selenium Removal.

Authors:  Ricardo Abejón
Journal:  Int J Environ Res Public Health       Date:  2022-05-11       Impact factor: 4.614

Review 3.  An Overview of Selenium Uptake, Metabolism, and Toxicity in Plants.

Authors:  Meetu Gupta; Shikha Gupta
Journal:  Front Plant Sci       Date:  2017-01-11       Impact factor: 5.753

4.  The draft genome of a wild barley genotype reveals its enrichment in genes related to biotic and abiotic stresses compared to cultivated barley.

Authors:  Miao Liu; Yan Li; Yanling Ma; Qiang Zhao; Jiri Stiller; Qi Feng; Qilin Tian; Dengcai Liu; Bin Han; Chunji Liu
Journal:  Plant Biotechnol J       Date:  2019-08-04       Impact factor: 9.803

  4 in total

北京卡尤迪生物科技股份有限公司 © 2022-2023.