Quantitative Determination of Minerals and Toxic Elements Content in Tropical and Subtropical Fruits by Microwave-Assisted Digestion and ICP-OES.

In the presented study, 15 tropical and subtropical fruits were studied for their mineral composition ranging from trace to major elements by ICP-OES after microwave digestion. The moisture amounts were assigned to be between 21.90 (tamarind) and 95.66% (pepino). The differences between the macroelement quantities of the fruits were established to be statistically significant (p<0.01). P and K quantities of fruits were displayed to be between 53.40 (pepino) and 927.74 mg/kg (tamarind) to 720.27 (pepino) and 13441.12 mg/kg (tamarind), respectively. While Ca quantities of fruits vary between 123.71 (pineapple) and 1519.76 mg/kg (blood orange), Mg quantities of fruits were established to be between 78.66 (pepino) and 875.02 mg/kg (tamarind). In general, the lowest macroelement quantities were determined in pepino fruit, but the highest P and K contents were determined in Gooseberry and Tamarind fruits, respectively. The microelement amounts of the fruits were established to be at very low levels compared to the macroelement contents. In general, the most abundant element in fruits was Fe, followed by Zn, Cu, Mn and B in decreasing order. In general, heavy metal quantities of fruits were detected at very low levels (except As and Ba). As and Ba quantities of fruits were assigned to be between 0.972 µg/g (mandarin) and 5.86 (kiwi) to 0.103 (pineapple) and 4.08 (avocado), respectively. As with macro and microelements, results regarding heavy metal concentrations varied depending on fruit types.

The Role of Edible Bulbous Layers on Macro, Micro, and Heavy Metal Contents of Leek (Allium porrum) Plant.

In this study, the degree of accumulation of biogenic element and heavy metal contents of different parts and edible layers of leeks cultivated in Konya in Turkey was revealed. The amounts of P and K of leek were determined from 154.69 (leaf top of leek) and 985.05 mg/kg (root of leek) to 1377.63 (onion part of leek) and 2688.50 mg/kg (root of leek), respectively. P and K contents of leek layers changed from 139.45 (1st layer) and 446.63 mg/kg (7th layer) to 1596.69 (2nd layer) and 2201.53 mg/kg (4th layer), respectively. While Ca amounts of leek parts vary between 577.09 (leaf of leek) and 666.87 mg/kg (root of leek), Mg contents of leek parts were determined between 130.70 (onion part of leek) and 264.58 mg/kg (root of leek). All of the macro elements were detected in the highest amount in the root of the leek, followed by the leaf and bulb parts in decreasing order. Fe and Zn contents of different parts of leeks varied from 0.506 (onion part of leek) and 22.71 mg/kg (root of leek) to 1.53 (leaf top of leek) and 5.85 mg/kg (root of leek), respectively. In general, the heavy metals found in the highest amount both in different parts of the leek and in the edible bulbous layers were As and Ba. The layers of the leeks are rich in potassium, phosphorus, iron, and zinc.

The accumulation of element and heavy metal concentrations in different parts of some carrot and radish types.

Vegetables, which are an important part of human nutrition, are very rich in minerals necessary for human health, and heavy metals can be found in vegetables at high rates because they can be easily taken by plant roots and leaves. In this study, the macro, micro element and heavy metal element concentrations accumulated in different parts of some carrot and radish types were investigated. The element concentrations in the samples were analyzed by Inductively coupled plasma optical emission spectrometry (ICP-OES; Varian-Vista Model) equipment. P, K, Ca, Mg and S contents of the head of orange and black carrot samples were determined as 602.30 and 727.23 mg/kg, 19,790.91 and 22,230.21 mg/kg, 1765.66 and 1609.41 mg/kg, 580.34 and 660.79 mg/kg and 376.21 and 4444.46 mg /kg respectively. Also, exterior parts of orange and black carrots contained 281.65 and 336.43 mg/kg P, 7768.37 and 10,109.44 mg/kg K, 169.88 and 272.18 mg/kg Ca, 112.08 and 189.28 mg/kg Mg and 135.43 and 217.60 mg/kg S, respectively. P and K contents of the head parts of radish samples (white, red and black radish) were determined between 302.14 (red radish) and 1111.53 mg/kg (black radish) to 13,717.2 (red radish) and 22,202.4 mg/kg (white radish), respectively. Fe amounts of the roots of radish samples changed between20.47 (red radish) and 45.93 mg/kg (white radish). As and Ba were the most abundant heavy metals in both carrot and radish parts. The Ni contents of the parts of the carrots contain more than 50% lower than the head part. Also, while Pb contents of the parts of orange carrot change between 0.189 µg/g (interior of body) and 0.976 µg/g (shell), Pb amounts of the black carrot parts were recorded between 0.136 (head) and 0.536 µg/g (interior of body). The results obtained differed according to the vegetable type and parts. The head part of the radishes was the richest in zinc, followed by root, shell, exterior of body and interior of body in descending order. In general, the parts where heavy metals were most localized were the head and shell parts. The most localized parts of heavy metals in radishes were the head, shell and root parts. As a result, the most of the edible inner parts of carrots and radishes are thought to have a positive effect on human health, since their heavy metal content is low.

Macro-, micro-, and heavy metal element levels in different parts of celery (Apium graveolens L.) plant.

Potassium (K) was found in the highest amount in the macroelements of the celery plant, followed by P, Ca, Mg, and S in decreasing order. P and K amounts of celery plant parts were measured between 619.57 (leaf of celery) and 1244.80 mg/kg (root of celery) to 5594.83 (head of celery) and 7587.35 mg/kg (root of celery), respectively. Exterior and interior parts of celery body contained 866.51 and 1017.45 mg/kg P, 6786.97 and 7325.07 mg/kg K, 615.13 and 491.59 mg/kg Ca, and 286.34 and 224.74 mg/kg Mg, respectively. In general, the celery part with the richest microelements was the leaves, followed in descending order by the head of celery, exterior of celery body, interior of celery body, and root. Fe and Mn contents of the parts of celery plants were recorded between 0.351 (interior of celery body) and 67.79 mg/kg (leaf of celery) to 2.70 (root) and 6.84 mg/kg (leaf of celery), respectively. The lowest and highest concentrations of each heavy metal were found in different parts of the celery plant. In general, the leaves were the part of the celery plant with the most heavy metals. As and Pb accumulated in large amounts in the inner parts of the celery tuber. The highest Pb (0.530 µg/g) was determined in interior of celery body. The highest Co (0.409 µg/g), Cr (0.377 µg/g), Mo (0.854 µg/g), and Ni (0.741 µg/g) were found in the leaf of celery plant.

Determination of macro-, micro-element and heavy metal contents localized in different parts of three different colored onions.

The element found at the highest amount in onion samples was sulfur, and followed by K, Ca, P, Na, and Mg in decreasing order. While K contents of white onion parts are determined between 1406.31 (outer most edible) and 1758.72 mg/kg (inner most edible), K contents of the parts of brown onions were measured between 1779.79 (head) and 2495.89 mg/kg (inner most edible). Also, K amounts of purple onions were detected between 2248.73 (shell) and 3064.64 mg/kg (middle edible). In addition, in general, the highest P, S, and K were detected in the middle edible and inner most edible parts of the edible onion samples. While the highest Ca content was localized in brown and purple onion roots, it was most localized in the shell part of white onions. In edible white and brown onions, the highest Na content was found in the inner most edible part. Fe amounts of white and brown onion samples were identified between 7.94 (head) and 20.41 mg/kg (root) to 9.56 (middle edible) and 23.67 mg/kg (head), respectively. Also, Fe contents of the parts of purple onions varied between 13.04 (shell) and 20.61 mg/kg (inner most edible). While the highest Fe and Zn are determined in the middle edible part in edible white onions, the highest Fe and Zn were determined in the outer most edible part in brown onions. In general, the most heavy metals were localized in the bark, head, and root parts of the onions. This had a positive effect on the safe edibility of onions. The heavy metal detected in the highest amount in onion samples was arsenic, followed by Cr, Al, Ni, Se, Ba, Pb, Mo, Co, and Cd in descending order. Generally, purple onion type showed maximum values. Therefore, results of the present study seen to be beneficial in the way that it allowed us to selected some varieties with nutrition value that could be interesting to introduce in gastronomy.

Nutrient Homeostasis of Aegilops Accessions Differing in B Tolerance Level under Boron Toxic Growth Conditions.

Boron (B) is a crucial microelement for several biological processes in plants; however, it becomes hazardous when present in excess in the soil. B toxicity adversely affects the wheat yield all around the world, particularly in the arid and semiarid regions. Aegilops, the nearest wild wheat relatives, could be an efficient source to develop B toxicity tolerance in modern cultivars. However, to potentially utilize these species, it is necessary to understand the underlying mechanisms that are involved in providing them tolerance. Other than hampering cellular and physiological activities, high B inhibits the uptake of nutrients in wheat plants that lead to nutrients deficiency causing a hindered growth. Thus, it is crucial to determine the effect of B toxicity on nutrient uptake and finally, to understand the role of nutrient homeostasis in developing the adaptive mechanism in tolerant species. Unfortunately, none of the studies to date has explored the effect of high B supply on the nutrient uptake in B toxicity tolerant wild wheat species. In this study, we explored the effect of 1 mM B (toxic B), and 10 mM B (very toxic B) B on the nutrient uptake in 19 Aegilops genotypes differing in B tolerance in contrast to Bolal 2973, the familiar B tolerant genotype. The obtained outcomes suggested a significant association between the B toxicity tolerance and the level of nutrient uptake in different genotypes. The B toxicity tolerant genotypes, Ab2 (TGB 026219, A. biuncialis genotype) and Ac4 (TGB 000107, A. columnaris genotype) were clustered together in the nutrient homeostasis-based heat map. Though B toxicity mostly had an inhibitory effect on the uptake of nutrients in root-shoot tissues, the tolerant genotypes revealed an increase in nutrient uptake under B toxicity in contrast with Control. The study directs towards future research where the role of external supply of few nutrients in enhancing the B toxicity tolerance of susceptible genotypes can be studied. Moreover, the genotype-dependent variation in the nutrient profile of the studied Aegilops genotypes under high B suggested that increasing number of Aegilops germplasm should be screened for B toxicity tolerance for their successful inclusion in the pre-breeding programs focusing on this issue.