Basil (
Selenium (Se) has been identified as a cofactor of the enzyme glutathione peroxidase, which is a catalyser in the reduction of peroxides that can damage cells and tissues, and it can act as an antioxidant (Puccinelli et al., 2017). Selenium is incorporated into selenoproteins that have a wide range of pleiotropic effects, ranging from antioxidant and anti-inflammatory effects to the production of active thyroid hormone (Rayman, 2012). Selenoproteins need several cofactors for their synthesis and they depend mainly on Se intake through the diet. Different forms of dietary Se may selectively increase synthesis of specific selenoproteins (Zoidis et al., 2018). Selenoproteins have pivotal significance for optimal human and animal health mainly due to their antioxidant activity (AOA) (EFSA, 2014). The European Recommended Dietary Allowance (RDA) of Se for humans is about 55 μg ∙ day−1 (Elmadfa et al., 2009).
The addition of nutrients, such as minerals and vitamins, to increase the nutritional value of processed food is called fortification (Gomez-Galera et al., 2010). Biofortification is a process of increasing the density of vitamins and minerals in a crop through plant breeding, transgenic techniques or agronomic practices. Biofortified staple crops, when consumed regularly, will generate measureable improvements in human health and nutrition (Bouis and Saltzman, 2018). Whereas conventional fortification requires artificial additives, biofortification involves the synthesis or accumulation of nutrients by plants at source (Díaz-Gómez et al., 2017). Se supplements include sodium selenate and sodium selenite (inorganic forms) and selenium-enriched yeast, selenomethionine and selenocysteine (organic forms) (Puccinelli et al., 2017). The results of investigations into the physico-chemical properties of different forms of Se have proven that dietary supplementation in the organic form showed higher biological availability than inorganic selenium (Fašiangová et al., 2017). Since selenium (Se) plays a significant role in antioxidant defence, biofortification with Se is a good way to improve the nutritional quality of sprouts, microgreens (Puccinelli et al., 2019) and other kind of vegetable (Hegedűsová et al., 2015; Hegedűsová et al., 2017; Andrejiová et al., 2019; Smoleń et al., 2016). Se concentrations in plant-derived foods are highly variable due to the genetic variation for Se accumulation and environmental conditions (Ozkutlu et al., 2011). Based on positive basil herb reaction to biofortification with selenium (Hawrylak-Nowak, 2008; Mezeyová et al., 2016; Mezeyová et al., 2018), our research paper was aimed to clarify how the mechanism of selenium incorporation into the seeds will take place after foliar biofortification with the sodium selenate in selected varieties of the genus
The experimental trial was carried out in 2017 and 2018 in the place of the Botanical Garden of the Department of Vegetable Production (Slovak University of Agriculture [SUA] in Nitra). Seed sowing and pre-propagation of plants were carried out in the greenhouse of the Botanical Garden SUA. The seeds were purchased from company Semo s.r.o. The pre-grown seedlings were planted in an area of 20.3 m2. Investigated varieties and species of basil are summarised in Table 1.
Basil varieties characterisation and 1000 seed weight in grams, Nitra, 2018 (photo: Mezeyová)
Basil species ‘variety’/1000 seed weight (g) | Botanical description | Picture of the herb |
---|---|---|
Plant native to tropical and subtropical Asia. It is an erect, much branched subshrub, 40–70 cm tall with hairy stems and simple opposite green or purple leaves that are strongly scented. Leaves have petioles and are ovate, up to 5 cm long and usually slightly toothed. The flowers are purplish in elongate racemes in close whorls. | ||
Cinnamon basil has a spicy, fragrant aroma and flavour. It contains methyl cinnamate, giving it a flavour reminiscent of cinnamon. It has narrow, slightly serrated, dark green, shiny leaves with reddish-purple veins and produces small, pink flowers. Its stems are dark purple. Cinnamon basil grows to 40–70 cm. | ||
Green leafy variety was bred in Italy. It is an aromatic, annual herb with large oval leaves, dark green-coloured and glossy, serrated. It reaches a height of up to 30 to 60 cm. Erect stem branches well. Inflorescences are white. It is characterised by a biting spicy sweet flavour and taste. |
The soil type of the experimental area is brown soil to chernozem on loess and loess loams and part along the River Nitra belongs to the area of fluvial soils, where the original soil type was fluvial and fluvial glue (Hreško et al., 2006). Fertilisation of the plants was done based on analysis of the experimental area in every evaluated year (Table 2). During the tested years, the soil from experimental area was analysed from the fertilising point of view by Department of Agro-chemistry and Plant Nutrition (Table 2).
Soil sample analysis of the experimental area in mg ∙ kg−1
pH | Ninorganic mg ∙ kg−1 | Nutrient content in mg ∙ kg−1 (Mehl.III) | S | % | ||||
---|---|---|---|---|---|---|---|---|
P | K | Ca | Mg | Humus | ||||
2017 | 7.16 N | 10.0 M | 128.8 H | 567.5 VH | 6000 H | 799.4 VH | 62.5 G | 3.22 G |
2018 | 7.04 N | 6.4 L | 75.0 M | 368 V | 6350 H | 763.4 VH | 2.5 VL | 3.29 G |
Notes: soil pH: N, neutral pH; nutrients: VL, very low content; L, low content; M, medium content; G, good content; H, high content; VH, very high content.
In terms of climatic classification of the region, Nitra is situated in a warm and dry area of Slovakia. The evaluation of experimental years according to climatic normal is given in Tables 3 and 4.
Evaluation of months according to temperature climatic normal 1961–1990
Month | Normal (1961–1990) | Characteristic (2017) | Characteristic (2018) | ||
---|---|---|---|---|---|
V | 15.1 | 16.6 | Hot | 18.8 | Very hot |
VI | 18.0 | 21.2 | Extremely hot | 20.7 | Hot |
VII | 19.8 | 21.7 | Hot | 21.7 | Hot |
VIII | 19.3 | 22.4 | Extremely hot | 22.5 | Very hot |
IX | 15.6 | 14.6 | Normal | 16.4 | Normal |
Evaluation of months according to precipitation climatic normal 1961–1990
Month | Normal (1961–1990) | PRC (mm) 2017 | Characteristic (2017) | PRC (mm) 2018 | Characteristic (2018) |
---|---|---|---|---|---|
V | 58 | 14 | Extremely dry | 29 | Very dry |
VI | 66 | 26 | Very dry | 44 | Dry |
VII | 52 | 60 | Normal | 13 | Very dry |
VIII | 61 | 23 | Very dry | 3 | Extremely dry |
IX | 40 | 93 | Extremely wet | 55 | Wet |
The cultivation of plant material was carried out in accordance with modern agrotechnical practices of basil field cultivation. Seed sowing took place on 8 March 2017 and 15 March 2018 in greenhouse of the Botanical Garden (SUA, Nitra). Planting at the permanent place was carried out on 18 May 2017 and 10 May 2018 into well-prepared soil. Plants were planted in 3 rows of 10 plants per variety with a spacing of 0.35 × 0.40 m. The crops were cut after planting because of multiple inflorescences creation followed by plant irrigation. Based on the agrochemical analysis of the soil, fertilisation of the plants with ammonium with dolomite (27% N) at dosage 0.4 kg ∙ 100 m−2 was carried out in two doses in both experimental years. In the phenological stage of BBCH 61 (10% of flowering flowers), an aqueous solution of sodium selenate at a concentration of 50 mg Se ∙ 1 m−2 was applied foliarly. The plants were harvested at the stage of botanical maturity of the seeds (when two-third of the seeds on the plant changed colour from white to dark brown or black) at two different dates, as the varieties ripened gradually. The first harvest took place on 10 August 2017 in case of ‘Tulsi’ and ‘Dark Green’ and ‘Tulsi’, ‘Dark Green’ and ‘Cinamonette’ have been cut on 24 August 2017. Manual harvest of the Cinamonette and Tulsi varieties were carried out on 14 August 2018. The Dark Green variety was harvested on 17 August 2018. Subsequent drying and seed cleaning took place in well-ventilated department stores on dry web fabric.
The following reagents were used for the tests: (±)-6-hydroxy-2,5,7,8-tetramethylchromane-2-carboxylic acid (Trolox, 97%, Acros Organics™, Denmark), 2,2-diphenyl-1-picrylhydrazyl (DPPH, ≤ 100%, Sigma Aldrich), Folin–Ciocalteu reagent (Merck Germany), gallic acid (GA, Sigma Aldrich), sodium carbonate (solution 20% w/w, Merck Germany), nitric acid (HNO3, 67%), hydrogen peroxide (H2O2, 30%), palladium nitrate (Pd(NO3)2, palladium modifier, 0.1 mol ∙ l−1), ascorbic acid (AsA, solution 1%, w/w), methanol (pure pro analysis -purity grades of lab reagents, 70%, v/v, Fisher Scientific UK, Loughborough, UK).
Digestion of the plant material took place in the microwave digestion system type CEM Mars X-press (microwave digestion oven). In the digestion container, there was weighed 0.5 g of the sample. It was wetted with 1 ml double distilled water followed by the addition of 5 ml of concentrated HNO3 and 1 ml of H2O2. It was digested at 150°C for a period of 20 minutes. The digestion product was refilled into volumetric flask till 25 ml. Quantitative determination of Se was done by using of ET-AAS method with Zeeman-effect background correction. Atomic absorption spectrometer (SpectrAA240FS Varian, Mulgrave Virginia, Australia) was used to measure the total selenium content. Conditions for selenium measurement were set in the equipment according to the recommendations of the manufacturer for ET-AAS technique (Rothery and Beach, 1988).
The average sample was created from the analysed basil seeds (dried at room temperature in clean laboratory conditions of the department of vegetable production) by slicing them into tiny bits and homogenised. Then 1 g of homogenised mixture and 40 ml of methanol (70%, v/v) were added into 250-ml extraction flasks. They were allowed to stand at room temperature for 20 h and then extracted with horizontal shaker for 4 h (Melicháčová et al., 2010).
Determination of AOA was performed with a spectrophotometer Jenway 6301 (Bibby Scientific Ltd., UK) by the method of Hegedűs et al. (2019). DPPH inhibition and spectrophotometric measurements were performed after a constant time of 30 min. Of note, 0.1 ml of the extract was pipetted into the spectrophotometer cuvette (depending on the nature of the sample) and supplemented with 70% methanol to 2.0 ml, and 4 ml of DPPH solution of about 25 mg ∙ l−1 concentration was added. Immediately after the DPPH solution was added, the absorbance of the mixture was measured at 517 nm (
Expressed as a percentage of DPPH discolouration based on the following relationship:
Expressed as a Trolox equivalent antioxidant capacity (TEAC) calculated from calibration curve. Final value is an average expression of three measurements.
Total polyphenol content (TPC) was estimated by using Folin–Ciocalteu assay by the method of Lachman et al. (2003) and calculated in milligram of GA equivalent (GAE) per kilogram dried weight (d.w.). GA is generally used as a standard unit for phenolic content determination because of wide spectrum of phenolic compounds. The Folin–Ciocalteu phenol reagent was added to a volumetric flask containing 100 μl of extract. The content was mixed and 5 ml of a sodium carbonate solution (20%, w/w) was added after 3 min. The volume was adjusted to 50 ml by adding distilled water. After 2 h, the samples were centrifuged for 10 min and the absorbance was measured at 765 nm of wavelength against blank (spectrophotometer Shimadzu UV/VIS-1240). The concentration of polyphenols was calculated from a standard curve plotted with known concentration of GA.
The analysis of variance (ANOVA), the multifactor analysis of variance (MANOVA) and the multiple range test were carried out using the Statgraphic Centurion XVII (StatPoint Inc., USA).
Selenium biofortification with foliar-applied sodium selenate solution in concentration of 5 mg Se ∙ 1 m−2 significantly (
Selenium content in basil seeds (mg ∙ kg−1 d.w.)
Control | Selenium | ||
---|---|---|---|
2017A | Tulsi | 0.025 ± 0.004 a | 0.809 ± 0.051 c |
Cinamonette | 0.017 ± 0.003 a | 0.437 ± 0.149 b | |
Dark Green | 0.020 ± 0.001 a | 0.370 ± 0.299 b | |
2018A | Tulsi | 0.055 ± 0.001 a | 0.528 ± 0.026 b |
Cinamonette | 0.083 ± 0.003 a | 0.748 ± 0.048 c | |
Dark Green | 0.078 ± 0.001 a | 0.823 ± 0.055 d | |
Average (2017–2018) | Tulsi | 0.040 ± 0.003 a | 0.669 ± 0.039 b |
Cinamonette | 0.050 ± 0.003 a | 0.593 ± 0.099 b | |
Dark Green | 0.049 ± 0.001 a | 0.597 ± 0.177 b |
Values with different letters are significantly different at
Figure 1
The effect of selenisation on selenium content in basil seeds (d.w.), 2017–2018. K, control variant and Se, selenised variant.

The content of selenium ranged from 9 to 95 μg ∙ kg−1. Foliar application of inorganic selenium very significantly increased the content of selenium in basil herb according to the research study by Mezeyová et al. (2016). The most effective here seemed to be the double dose of selenium (5 mg Se ∙ m−2) when in ‘Red Rubin’ was incorporated in 7.859 ± 0.9 mg ∙ kg−1 of selenium in comparison with 0.058 ± 0.004 mg ∙ kg−1 (control variant) and in ‘Dark Green’ 4.017 ± 0.8 mg ∙ kg−1 in comparison with control value 0.154 ± 0.05 mg ∙ kg−1. Puccinelli et al. (2019) also tested the ability of basil plants grown in hydroponics to take up Se from the growth substrate and to study the effects of Se concentration on plant growth and Se accumulation. Se concentration increased during seedling growth, was highest in younger leaves and then declined before or on flowering.
After application of 5 mg Se ∙ m−2 in two varieties of peas, 25-fold increase in the selenium content in seeds was reported in comparison with control in the study by Hegedűsová et al. (2015). As lot of other crops such as peas, rice, corn, wheat (Gomez-Galera et al., 2010; Ozkutlu et al., 2011; Poblaciones et al., 2014; Premarathna et al., 2012; Manojlović et al., 2019; Hawkesford and Zhao, 2007; Poblaciones and Rengel, 2018; Fernandes et al., 2014) were positive in test for incorporation of selenium in grains, there was prediction of selenium increasing possibility in basil seeds. In selenised basil seeds, the increase in selenium content in case of Tulsi was 17-fold in comparison with control variant, 12-fold in ‘Cimonette’ and 12-fold in ‘Dark Green’ compared with control.
On the other hand, the optimum dosage of the selenium fertiliser is very important because of possible selenium toxicity in plants. It mainly depends on their ability to divert selenium away from the accumulation of selenocysteine and selenomethionine which ranges from 2 mg ∙ kg−1 in non-accumulators, such as rice, and 330 mg ∙ kg−1 in white clover, to several thousands of mg ∙ kg−1 in the accumulator
The values of AOA reached from 714.22% inhibition (‘Cinamonette’, 2018, selenised variant) to 1,061.03% inhibition (‘Tulsi’, 2018, selenised variant) as shown in Table 6. The impact of fortification with selenium was not significant (
AOA in basil seeds (% inhibition d.w.)
Control | Selenium | ||
---|---|---|---|
2017A | Tulsi | 861.87 ± 195.82 a | 1011.91 ± 97.76 b |
Cinamonette | 857.63 ± 143.60 a | 922.56 ± 13.32 ab | |
Dark Green | 916.67 ± 121.66 ab | 1032.72 ± 51.03 b | |
2018A | Tulsi | 1075.11 ± 118.02 c | 1061.03 ± 116.78 c |
Cinamonette | 843.34 ± 93.31 ab | 714.22 ± 78.17 a | |
Dark Green | 821.51 ± 90.50 ab | 932.60 ± 102.85 bc | |
Average (2017–2018) | Tulsi | 968.49 ± 156.92 bc | 1036.47 ± 107.27 c |
Cinamonette | 850.49 ± 118.45 ab | 818.39 ± 45.74 a | |
Dark Green | 869.09 ± 106.08 ab | 982.66 ± 76.94 bc |
Values with different letters are significantly different at
Figure 2
The effect of selenisation on AOA (% inhibition) in basil seeds (d.w.), 2017–2018. K, control variant and Se, selenised variant.

In basil seeds, the selenium content was increased without significant impact (
According to Sarfraz et al. (2011) total AOA of
AOA in basil seeds (mmol Trolox ∙ kg−1 d.w.)
Control | Selenium | ||
---|---|---|---|
2017A | Tulsi | 27.43 ± 3.90 bc | 27.63 ± 2.23 bc |
Cinamonette | 27.43 ± 2.83 bc | 25.60 ± 0.26 abc | |
Dark Green | 28.57 ± 2.41 c | 28.10 ± 1.15 c | |
2018A | Tulsi | 29.90 ± 3.61 c | 30.30 ± 3.63 c |
Cinamonette | 26.50 ± 3.22 bc | 21.40 ± 2.61 a | |
Dark Green | 23.95 ± 2.90 ab | 26.85 ± 3.25 bc | |
Average (2017–2018) | Tulsi | 28.67 ± 3.76 b | 28.97 ± 2.93 b |
Cinamonette | 26.97 ± 3.02 ab | 23.50 ± 1.44 a | |
Dark Green | 26.26 ± 2.66 ab | 27.48 ± 2.20 b |
Values with different letters are significantly different at
Figure 3
The effect of selenisation on AOA (mmol Trolox · kg−1) in basil seeds (d.w.), 2017–2018. K, control variant and Se, selenised variant.

The content of polyphenols in average ranges from 1414.61 μg GA ∙ g−1 d.w. (‘Tulsi’, selenised variant) to 1681.75 μg GA ∙ g−1 d.w. (‘Dark Green’, control) as shown in Table 8. Statistical significance of variety was confirmed (
TPC in basil seeds (μg GA ∙ g−1 d.w.)
Control | Selenium | ||
---|---|---|---|
2017A | Tulsi | 1188.74 ± 112.16 a | 1270.15 ± 318.06 a |
Cinamonette | 1766.68 ± 391.88 ab | 1573.24 ± 355.33 ab | |
Dark Green | 1996.16 ± 214.47 b | 1540.95 ± 316.67 ab | |
2018A | Tulsi | 1824.35 ± 41.02 b | 1559.08 ± 21.01 a |
Cinamonette | 1368.52 ± 19.62 a | 1449.95 ± 24.59 a | |
Dark Green | 1367.35 ± 25.01 a | 1462.71 ± 28.44 a | |
Average (2017–2018) | Tulsi | 1506.55 ± 76.59 a | 1414.61 ± 169.54 a |
Cinamonette | 1567.60 ± 205.75 a | 1511.60 ± 189.96 a | |
Dark Green | 1681.75 ± 119.74 a | 1501.83 ± 172.56 a |
Values with different letters are significantly different at
Total phenolic content ranged from 22.9 to 65.5 mg GA ∙ g−1 d.w. in 23 Iranian basil accessions according to Javanmardi et al. (2003) as they determined total phenolic contents by using a spectrophotometric technique based on the Folin–Ciocalteu reagent. In frozen sample of Cinnamon, basil leaves were found 4.4 ± 0.1 (mg CAE ∙ g−1 fresh weight) according to Abramovič et al. (2018). Regarding the total phenolic content in seeds, Marineli et al. (2014) found out in chia seeds samples from Chile 0.94 mg GA ∙ g−1, which was similar to previous reports Reyes-Caudillo et al. (2008), where chia seed from two different regions in Mexico showed values between 0.88 and 0.92 mg GA ∙ g−1. In climate conditions of Slovakia, it has not been possible to grow the seeds of
Figure 4
The effect of selenisation on TPC in basil seeds (d.w.), 2017–2018. K, control variant and Se, selenised variant.

Applied dose of sodium selenate at a concentration of 5 mg Se ∙ 1 m−2 had a positive effect on increasing the selenium content in the seed of basil and it did not have significant effect (
Figure 1

Figure 2

Figure 3

Figure 4

Basil varieties characterisation and 1000 seed weight in grams, Nitra, 2018 (photo: Mezeyová)
Basil species ‘variety’/1000 seed weight (g) | Botanical description | Picture of the herb |
---|---|---|
Plant native to tropical and subtropical Asia. It is an erect, much branched subshrub, 40–70 cm tall with hairy stems and simple opposite green or purple leaves that are strongly scented. Leaves have petioles and are ovate, up to 5 cm long and usually slightly toothed. The flowers are purplish in elongate racemes in close whorls. | ||
Cinnamon basil has a spicy, fragrant aroma and flavour. It contains methyl cinnamate, giving it a flavour reminiscent of cinnamon. It has narrow, slightly serrated, dark green, shiny leaves with reddish-purple veins and produces small, pink flowers. Its stems are dark purple. Cinnamon basil grows to 40–70 cm. | ||
Green leafy variety was bred in Italy. It is an aromatic, annual herb with large oval leaves, dark green-coloured and glossy, serrated. It reaches a height of up to 30 to 60 cm. Erect stem branches well. Inflorescences are white. It is characterised by a biting spicy sweet flavour and taste. |
Selenium content in basil seeds (mg ∙ kg−1 d.w.)
Control | Selenium | ||
---|---|---|---|
2017 | Tulsi | 0.025 ± 0.004 | 0.809 ± 0.051 c |
Cinamonette | 0.017 ± 0.003 | 0.437 ± 0.149 b | |
Dark Green | 0.020 ± 0.001 | 0.370 ± 0.299 b | |
2018 | Tulsi | 0.055 ± 0.001 | 0.528 ± 0.026 b |
Cinamonette | 0.083 ± 0.003 | 0.748 ± 0.048 c | |
Dark Green | 0.078 ± 0.001 | 0.823 ± 0.055 d | |
Average (2017–2018) | Tulsi | 0.040 ± 0.003 | 0.669 ± 0.039 b |
Cinamonette | 0.050 ± 0.003 | 0.593 ± 0.099 b | |
Dark Green | 0.049 ± 0.001 | 0.597 ± 0.177 b |
Evaluation of months according to temperature climatic normal 1961–1990
Month | Normal (1961–1990) | Characteristic (2017) | Characteristic (2018) | ||
---|---|---|---|---|---|
V | 15.1 | 16.6 | Hot | 18.8 | Very hot |
VI | 18.0 | 21.2 | Extremely hot | 20.7 | Hot |
VII | 19.8 | 21.7 | Hot | 21.7 | Hot |
VIII | 19.3 | 22.4 | Extremely hot | 22.5 | Very hot |
IX | 15.6 | 14.6 | Normal | 16.4 | Normal |
TPC in basil seeds (μg GA ∙ g−1 d.w.)
Control | Selenium | ||
---|---|---|---|
2017 | Tulsi | 1188.74 ± 112.16 | 1270.15 ± 318.06 |
Cinamonette | 1766.68 ± 391.88 | 1573.24 ± 355.33 | |
Dark Green | 1996.16 ± 214.47 b | 1540.95 ± 316.67 | |
2018 | Tulsi | 1824.35 ± 41.02 b | 1559.08 ± 21.01 |
Cinamonette | 1368.52 ± 19.62 | 1449.95 ± 24.59 | |
Dark Green | 1367.35 ± 25.01 | 1462.71 ± 28.44 | |
Average (2017–2018) | Tulsi | 1506.55 ± 76.59 | 1414.61 ± 169.54 |
Cinamonette | 1567.60 ± 205.75 | 1511.60 ± 189.96 | |
Dark Green | 1681.75 ± 119.74 | 1501.83 ± 172.56 |
AOA in basil seeds (% inhibition d.w.)
Control | Selenium | ||
---|---|---|---|
2017 | Tulsi | 861.87 ± 195.82 | 1011.91 ± 97.76 b |
Cinamonette | 857.63 ± 143.60 | 922.56 ± 13.32 | |
Dark Green | 916.67 ± 121.66 | 1032.72 ± 51.03 b | |
2018 | Tulsi | 1075.11 ± 118.02 c | 1061.03 ± 116.78 c |
Cinamonette | 843.34 ± 93.31 | 714.22 ± 78.17 | |
Dark Green | 821.51 ± 90.50 | 932.60 ± 102.85 bc | |
Average (2017–2018) | Tulsi | 968.49 ± 156.92 bc | 1036.47 ± 107.27 c |
Cinamonette | 850.49 ± 118.45 | 818.39 ± 45.74 | |
Dark Green | 869.09 ± 106.08 | 982.66 ± 76.94 bc |
Evaluation of months according to precipitation climatic normal 1961–1990
Month | Normal (1961–1990) | PRC (mm) 2017 | Characteristic (2017) | PRC (mm) 2018 | Characteristic (2018) |
---|---|---|---|---|---|
V | 58 | 14 | Extremely dry | 29 | Very dry |
VI | 66 | 26 | Very dry | 44 | Dry |
VII | 52 | 60 | Normal | 13 | Very dry |
VIII | 61 | 23 | Very dry | 3 | Extremely dry |
IX | 40 | 93 | Extremely wet | 55 | Wet |
AOA in basil seeds (mmol Trolox ∙ kg−1 d.w.)
Control | Selenium | ||
---|---|---|---|
2017 | Tulsi | 27.43 ± 3.90 bc | 27.63 ± 2.23 bc |
Cinamonette | 27.43 ± 2.83 bc | 25.60 ± 0.26 | |
Dark Green | 28.57 ± 2.41 c | 28.10 ± 1.15 c | |
2018 | Tulsi | 29.90 ± 3.61 c | 30.30 ± 3.63 c |
Cinamonette | 26.50 ± 3.22 bc | 21.40 ± 2.61 | |
Dark Green | 23.95 ± 2.90 | 26.85 ± 3.25 bc | |
Average (2017–2018) | Tulsi | 28.67 ± 3.76 b | 28.97 ± 2.93 b |
Cinamonette | 26.97 ± 3.02 | 23.50 ± 1.44 | |
Dark Green | 26.26 ± 2.66 | 27.48 ± 2.20 b |
Soil sample analysis of the experimental area in mg ∙ kg−1
pH | Ninorganic mg ∙ kg−1 | Nutrient content in mg ∙ kg−1 (Mehl.III) | S | % | ||||
---|---|---|---|---|---|---|---|---|
P | K | Ca | Mg | Humus | ||||
2017 | 7.16 N | 10.0 M | 128.8 H | 567.5 VH | 6000 H | 799.4 VH | 62.5 G | 3.22 G |
2018 | 7.04 N | 6.4 L | 75.0 M | 368 V | 6350 H | 763.4 VH | 2.5 VL | 3.29 G |
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