Determination of Selected Essential and Non-Essential Metals in Three Types of Teff ( Eragrostis tef ) Cultivated in Southern Ethiopia

Teff (Eragrostis tef) is used to supply staple food “injera” for many Ethio-pians. The present study was aimed toward determining the extent of selected metals that can exist in three types of teff cultivated in selected districts of southern Ethiopia. The level of those metals was determined by flame atomic absorption spectrometry. The optimized wet digestion procedure was eva-luated employing a spiking method and an acceptable percentage recovery of (91.1% - 108.9%) has been obtained for metals in the teff. Oven dried 1 g of teff samples were digested using 5 mL of HNO 3 and 1 mL of HClO 4 at 300˚C for 3 hours. The result indicated that the mean concentration of metals (in mg/kg dry weight basis) in teff samples were found to be from 1206.9 to 1768.9 of Ca, 2463.9 to 2554.7 of Mg, 82.6 to 109.9 of Na, 2879 to 3075 of K, 207.4 to 239.5 of Fe, 55.9 to 100.4 of Mn, 27.1 to 87.1 of Zn, 5.4 to 45.5 of Cu and 0.118 to 0.130 of Pb respectively. However, Cd is below the method detection limit. A statistical analysis of variance revealed that there was a significant difference (p ≤ 0.05) between the mineral content in three teff types and teff from the three districts. Red teff had higher essential metal contents except Cu followed by brown teff. Strong positive correlation was recognized between Mg with Ca and K, the rest have moderate or weak correlation. Fur-ther study has been done on the mineral contents of similar variety or three types of teff with the soil analysis from different locations.


Introduction
Teff (Eragrostis tef (Zucc.) Totter) is a tropical cereal crop. It had been believed How to cite this paper: Habte, A., Lelago, A., Doda, M.B. and Kanido, C.K. (2020) Determination of Selected Essential and Non-Essential Metals in Three Types of Journal of Agricultural Chemistry and Environment known about the nutritional composition and potential health benefits of teff. In Ethiopia, there is a prolonged consideration of teff grain as low nutritional value because of limited information in this regards. However, there has been a growing research interest globally by the nutritionist and food scientists due to its gluten-free nature, nutritional composition and accelerated teff-based products.
Studies conducted on the nutritional composition and health benefits of teff are limited and cannot take into account the differences in teff varieties and growing conditions. A few studies so far confirmed that teff has excellent nutritional profiles and suggested as considerable potential to be a functional food for health promotion and disease prevention [3].
Most of the researches conducted on teff are associated with genetic variety improvement and adaptability. No literature is found on the determination of essential and non-essential metals in teff types with respect to area of cultivation.
Therefore, studying the content of essential and non-essential metals in different sorts of teff is extremely important in dietary applications of food. Hence, the present study aimed toward determining the level of selected essential and non-essential metals (K, Mg, Ca, Na, Mn, Zn, Fe, Cu, Pb and Cd) that can exist in three types of teff mainly used by the peoples of study area in order to ensure health benefits of individuals. Furthermore, the results of this study may help to identify the difference in mineral content of teff with area of cultivation.

Equipment and apparatuses
Digital balance (Mettler Toledo, Model AG204 Switzerland) with ±0.0001 precision was used for weighing the samples. The washed teff samples were dried using a drying oven (DIGITHEAT, Spain). A high speed universal disintegrator was used to grind and powder the dried teff samples. A volumetric flask (100 ml) with grounded glass fitted with condenser was employed in digesting the sample on Kjeldahl heating apparatus (Gallenhamp, England). A 50, 100 and 250 ml volumetric flask were used during dilution of sample and preparation of metal standard and infusion solutions. Reagents, sample solutions and standard solutions of metals have been measured using measuring cylinders, pipettes, micropipettes (Dragonmed, 1 -10 µl, 100 -1000 µl, Shangai, China). A refrigerator (Hitachi, Tokyo, Japan) was used to keep the digested sample before analysis.
Buck Scientific Model 210VGP FAAS (East Norwalk, USA) equipped with deuterium arc background correctors was used for analysis of the metals (K, Mg, Ca, Na, Mn, Zn, Fe, Cu, Pb and Cd) using air-C 2 H 2 flame [17] [18].

Reagents and Chemicals
Analytical grade reagents and standards were used in the analysis. Digestion of teff samples was done using HNO 3 (69% -72%) and HClO 4  sulfates. Stock standard solutions of 1000 mg/L, in 2% HNO 3 , of the metals K, Mg, Ca, Na, Mn, Zn, Fe, Cu, Pb and Cd were used for the preparation of calibration standards of each metal and in the spiking experiments. The working standards of each metal were prepared from intermediate standard solutions. Deionized water (Milli-Q) was used throughout the experiments for sample preparation, dilution, and rinsing apparatus prior to analysis and during analysis [7] [19].

Description of Study Area
The study was conducted in Gurage (Abeshege), Hadiya (Soro) and Halaba (Wera) zones, one district from each zone, of SNNPRS Ethiopia. The climatic condition and location of the study area are shown in Table 1 and Figure 1.

Sample Collection
White, brown and red teff samples were collected in polyethylene plastic bags from Soro, Abeshege and Wera districts of Southern Ethiopia which are known cultivating teff in large amount. To draw the representative sample from each Accordingly, ten trials were tested for digestion of the teff samples. The optimal digestion procedure chosen was the one that needs 3 hr for complete digestion of 1 g of teff powders, with 5 ml of 70% HNO 3 and 1 ml of 70% HClO 4 ( Table 2) were used throughout the analysis.

Instrument Operating Conditions
Secondary standard solutions containing 10 mg/L were prepared in 100 ml volumetric flask from the atomic absorption spectroscopy standard stock solutions that contained 1000 mg/L which was prepared from soluble salts of each metal. These secondary standards were diluted with deionized water to get five working standards for every metal of interest (Table S2). Then, the metal contents of sample (K, Mg, Ca, Na, Mn, Zn, Fe, Cu, Pb and Cd) were analyzed by FAAS equipped with deuterium arc background corrector and standard air-acetylene flame system using external calibration curve after the parameters (burner and lamp alignment, slit width and wavelength) were optimized for   Table S1.
The results obtained from FAAS were in mg/L, but it was converted into mg/kg (dry mass) by using the following equation.
where, W is the weight in g of the sample, and V is the final volume of solution [28].

Instrumental Calibration
The instrument was calibrated using five series of working standards for each  Table S2. From the correlation coefficients in Table S2 it is possible to say that, the change in absorbance with the concentration of each metal was in a good positive correlation and linearly fit. MDL is that the minimum amount of analyte which will be measured and reported within 99% confidence level that the analyte concentration is greater than zero [29]. In other words, it is the minimum amount of analyte which will be distinguished from statistical fluctuations in a blank, usually correspond to the signal of blank and three times the standard deviation of the sample blank [30].

Method of Performance and Method of Validation
In the present study, Seven blank samples were digested following an equivalent procedure as the teff samples and each of the blank samples were analyzed for metal concentrations of Na, K, Mg, Ca, Mn, Zn, Fe, Cu, Pb and Cd by FAAS.
The standard deviations for each metal were calculated from the seven blank triplicate measurements to work out method detection limit of the instrument.
Then the method detection limit of each metal was calculated as three times the standard deviation of the blank (3S blank , n = 21) ( Table 3).

Method Quantification Limits (MQL)
MQL is the lowest concentration at which a measurement is quantitatively meaningful. It is also commonly defined as 10 times the signal/noise ratio. If the noise is approximated as the standard deviation of the blank (S blank ), then MQL is 10 × S blank , n = 21 [18] [31]. The results in Table 3 have revealed that both MDL and MQL values were greater than the IDL; hence, the result of analysis could be reliable.

Recovery Tests
Analytical method is suitable when it's validated for its intended purpose. Due to the absence of certified reference material for the samples within the laboratory, the optimized digestion procedure was validated by spiking the samples with a typical of known concentration of the analyte metals and therefore the efficiency of the optimized procedure was checked. The spiked samples were digested in triplicate following an equivalent digestion procedure developed for Table 3. Instrument detection limit, method detection limit and quantification limit for metals of interest determined in teff samples.  (Table 4). Finally, % recovery decided by using recovery formula [32].
in spiked sample in nonspiked sample % Recovery 100 added for spiking where: m C is the concentration of metals in the sample.

Statistical Analysis
Data obtained from laboratory entry management and preliminary summaries were done on Microsoft excel spreadsheet. All analyses were administered in triplicate and therefore the data was presented as mean ± standard deviations.
Differences between treatments of means were done by using analysis of variance (ANOVA). For comparison of the means of treatments, the Fisher's least significant difference (LSD) test was used at α = 0.05 significance level. Linear correlations coefficient (r) were determined using the Pearson product-moment correlation. All statistical analysis was done using SAS 9.1.3 windows version software program [33].

Concentration of Metals in Teff Samples
The results indicated that the samples had variable concentration of analyte metals in three types of teff from the three districts. Among the analyzed metals, cadmium was below the method detection limit. The results determined from each sampling sites were listed in terms of mean value and standard deviation of mg/kg dry weight (Table 5).

Distribution Patterns of Metals in Different Teff Samples
There was a variation in macro-essential metals concentration in three teff types ( Table 6). The concentration of K was the highest of all the major metals and ranges from 2879.3 -3074.7 mg/kg dry weight followed by Mg (2463.9 -2555.2 mg/kg dry weight) while Na (82.3 -109.7 mg/kg dry weight) was the least   one among the macro-essential minerals. Briefly, the concentration profile of macro-essential metals determined in teff was K > Mg > Ca > Na.
The higher levels of potassium and magnesium in teff are probably due to the fact that nutrient elements such as N, P, K, S, and Mg are highly mobile in the Journal of Agricultural Chemistry and Environment plant tissue and trans-located from old plant tissue to new plant tissue [34]. The other probable reasons for a higher concentration of K, Mg and Ca is if the soil that has been used for cultivating the plant, are highly fertilized with manure and organic residues, they were high in available potassium, calcium and magnesium. Hence, the plant has high amount of these metals [35].
From the level of essential trace metals, Fe (205.6 -239.9 mg/kg) was the most The level of non-essential heavy metals, Pb, detected in teff samples was in the range of 0.118 -0.13 mg/kg and that of Cd, was found to be below the method detection limit. In general the concentration pattern of metals in teff was observed as K > Mg > Ca > Fe > Na> Mn > Zn > Cu > Pb ( Figure 2, Table 5). Similarly, the levels of a given metal vary with types of teff. The concentration of all metals except Cu and Pb was highest in red teff varieties while the lowest values vary from metal to metal in different types of teff. The highest level of metals in red teff might be attributed to its genetic potential to absorb and accumulate these metals. Analysis of variance showed that the mean concentration of Ca was significantly (p < 0.05) different among the three types of teff and in the sample sites ( Table 5). The highest value (1738.5 ± 30.5 mg/kg) was detected in red teff from Sore district followed by the same type of teff from Wera district. The lowest level (1211 ± 4.47 mg/kg) of Ca was recorded from brown teff of Soro followed by white teff of Abeshege district. Fisher's combined probability test using the LSD criterion for significance indicated that the mean concentration of Ca in red teff significantly (p < 0.05) higher than brown and white teff. In red teff, there was significant (p < 0.05) difference in the mean concentration of calcium in three sample areas where the maximum and minimum level of Ca were recorded from Soro and Abeshege districts, respectively. Similarly, the mean concentration of Ca in brown and white teff was significantly (p < 0.05) different over the three locations where the highest levels of Ca were recorded from Wera district for both types of teff. While, the lowest values of Ca for both teff types were recorded from Soro district ( Table 5).
The variation on the level of Ca with differences on the types of teff and location might be attributed to genetic difference of the teff types to absorb the metals from the soil and accumulate in their tissues and also differences on soil conditions and agronomic practices carried out in this site. In addition to the genetic properties of crop numerous factors such as climatic conditions, soil characteristics and agronomic management practices influence the concentration of metals in plant tissues [37].
The concentration of Ca (1206.9 -1769.5 mg/kg) in this study agrees with the range of the value (124 -155 mg/100 g) reported by [14]. However, lower than the value (1800 mg/kg) reported by [38] and the value (168.64 ± 11.03 to 180.7 ± 14.65 mg/100 g) reported by [24]. But, it is higher than the values (83.85 ± 0.78 mg/100 g and 116.15 ± 0.35 mg/100 g) for white and brown teff respectively as reported by [39]. Magnesium Magnesium was the second most accumulated essential metal in the teff next to K ( Table 6). The mean concentration of Mg was significantly (p < 0.05) varied among the three types of teff over the three locations (  (Table 5). There was significant difference in the mean concentration of Mg in three types of teff in the three districts. The mean concentration of Mg in red teff from Soro district was significantly higher than Abeshege and Wera districts. But, there was no significant difference in the mean concentration of Mg in red teff in Abeshege and Wera districts. The mean concentration of Mg in brown teff from Wera district was significantly higher than Abeshege and Soro districts. While, the mean concentration of Mg in brown teff from Abeshege district was significantly higher than Soro district. Also, the mean con-Journal of Agricultural Chemistry and Environment centration of Mg in white teff from Abeshege district was significantly lower than Soro and Wera districts. However, there is no significant difference in the mean concentrations of metals in Soro and Wera districts. Such differences might be related to the environmental conditions of the study areas and the characteristics of the teff varieties. Differences in the environmental conditions and crop inherent potential to take nutrient from the soil resulted in the differences on their metabolic activities like accumulations of different metals in their body [40].
The concentrations of Mg found in this study ranges from 2464 -2555.2 mg/kg dry weight which was higher than the value (153.16 ± 9.45 to 173.7 ± 8.89 mg/100 g) reported by [19] and the value (1840 mg/kg) reported by [38]. The results of this study are in agreement with the study conducted by [39].

Sodium
The concentration of Sodium in the studied teff samples ranged from 82.3 -109.7 mg/kg dry weight which showed a significant (p < 0.05) difference over locations for the three types of teff ( Table 5). The higher concentration of Na was found in red teff from Wera district and the lower concentration was observed in white teff from Soro district ( Table 5). The concentration of sodium was relatively lower than other macro essential metals in this study. The mean concentration of Na in white teff from Soro district was significantly higher than Abeshege and Wera districts. The mean concentration of Na in white teff from Wera district was significantly higher than Abeshege and Soro districts. The mean concentration of Na in brown teff from Abeshege district was significantly higher than the Soro district. The mean concentration of Na in red teff from Wera district was significantly higher than Abeshege and Soro districts. Also, the mean concentration of Na in red teff from Abeshege district was significantly higher than Wera district.
The range of mean concentration of Na in this study (82.3 -109.7 mg/kg dry weight) was higher than the values 2.32 ± 0.35 and 2.85 ± 0.20 mg/100 g for white and brown teff respectively, as reported by [39]. But, lower than the value (22.06 -25.68 mg/100 g) reported by [19] and the value (150 mg/kg) reported by [38].

Potassium
Potassium was the most accumulated metal in teff with the mean concentration ranges from 2879 -3074.7 mg/kg. Analysis of variance showed that the mean concentration of K was significantly (p < 0.05) different among teff types as well as locations ( Table 5). The highest level of K (3070.9 ± 3.7 mg/kg) was observed in Soro district red teff and the lowest (2882.9 ± 3.7 mg/kg) concentration was found in Soro district white teff. The higher concentration of K in the teff may be due to its higher abundance in the soil. The addition of K fertilizers to the soils rapidly increases the concentration of available K that could be attributed to mineralization of organic matter, the solubilization effect of rain water and due to increased chemical and biological fixation of potassium in the presence of fertilizers [35].

A. Habte et al. Journal of Agricultural Chemistry and Environment
The mean concentration of K in white teff from Soro district was significantly (p < 0.05) lower than Abeshege and Wera districts. However, there was no significant difference in Abeshege and Wera districts. The mean concentration of K in brown teff from Wera district was significantly (p < 0.05) higher than Abeshege and Soro districts. The mean concentration of K in brown teff from Abeshege district was significantly (p < 0.05) higher than that in Soro district. The mean concentration of K in red teff from Soro district was significantly (p < 0.05) higher than Abeshege and Wera districts. The mean concentration of K in red teff from Wera district was significantly higher than Abeshege district.
The range of mean concentration of K (2879 -3074.7 mg/kg) in this study was higher than the result (198.7 -230.8 mg/100 g) reported by [19] while lower than the reported values (486.80 ± 8.48 mg/100 g) for brown teff, 383.70 ± 3.25 mg/100 g for white teff [39] and the mean concentration of (4270 mg/kg) as reported by [38].

Iron
Analysis of variance showed that the mean concentration of Fe was significantly (p < 0.05) different among three teff types ( Table 5). The highest mean concentration (238.6 ± 0.9 mg/kg) was observed in red teff from Abeshege district followed by the same type of teff from Soro district. The lowest mean concentration (211.7 ± 1.1 mg/kg) was found in white teff from Wera district followed by the same type of teff from Abeshege district. Fisher's combined probability test using the LSD criterion for significance indicated that the mean concentration of Fe in red teff is significantly (p < 0.05) higher than that in brown and white teffs. There was no significant difference in the mean concentration of Fe in white and brown teff in all sample sites. The mean concentration of Fe in red teff from Wera district was significantly (p < 0.05) lower than Abeshege and Soro districts. However, there is no significant difference in the mean concentrations of Fe in red teff in Soro and Abeshege districts.
The concentration of Fe was found to be the highest of all trace essential metals measured in teff samples. The mean concentration of Fe in this study varies from 205.6 -239.9 mg/kg. The pattern of mean concentration of Fe in teff varieties was in the order of red > brown > white in the sample sites. The concentration range of Fe obtained in this study was in agreement with the range of values (14.1 -27.1 mg/100 g) reported by [19] and lower than the value reported by [14].
The mean concentration of Fe in teff samples of this study ranges from 205.6 -239.9 mg/kg, which was below the maximum permissible level of 425.5 mg/kg set by [41]. Manganese The mean concentration of Manganese in teff was ranged from 55.8 -100.1 mg/kg dry weight which showed significant (p < 0.05) difference over locations for the three types of teff ( Table 5). The highest level of Mn was observed in red teff from Abeshege district sample and the lowest concentration was found in brown teff from Abeshege district (Table 5). Fisher's combined probability test using the LSD criterion for significance indicated that there was significance (p < 0.05) difference in the mean concentration of Mn in three types of teff. The mean concentration of Mn in red teff from Abeshege district was significantly (p < 0.05) higher than that in Soro and Wera districts. Also, the mean concentration of Mn in red teff from Wera district was significantly (p < 0.05) higher than in Soro district. The mean concentration of Mn in brown teff from Soro district was significantly higher than Abeshege and Wera districts. Similarly, the mean concentration of Mn in brown teff from Wera district was significantly (p < 0.05) higher than Abeshege district. The mean concentration of Mn in white teff from Abeshege district was significantly (p < 0.05) higher than Soro and Wera districts. Also, the mean concentration of Mn in white teff from Soro district was significantly higher than Wera district.
The result (55.8 -100.1 mg/kg) of Mn in this study was in agreement with the range of value (4.84 -22.36 mg/100 g) reported by [19]. The concentration of Mn in this study was below maximum permissible level 500 mg/kg dry weight set by [41].

Zinc
The mean concentration of Zn in teff was ranged from 27 -87.3 mg/kg dry weight. The highest level (84.7 ± 2.3 mg/kg) of Zn was observed in red teff of Soro district and the lowest (35.1 ± 8 mg/kg) concentration was found in white teff of Abeshege district. Fisher's combined probability test using the LSD criterion for significance indicated that there was significant (p < 0.05) difference in the mean concentration of Zn in three types of teff in the three districts ( Table  5). The mean concentration of Zn in red teff from Soro district was significantly (p < 0.05) higher than that in Abeshege and Wera districts. Also, the mean concentration of Zn in red teff from Abeshege district was significantly (p < 0.05) higher than that in Wera districts. The mean concentration of Zn in brown teff from Abeshege district was significantly (p < 0.05) higher than Soro and Wera districts. Similarly, the mean concentration of Zn in brown teff from Wera district was significantly (p < 0.05) higher than of Soro districts. The mean concentration of Zn in white teff from Wera district was significantly higher than that in Abeshege and Soro districts. Also, the mean concentration of Zn in white teff from Soro district was significantly higher than Abeshege districts with p < 0.05.
The concentration range of Zn (27 -87.3 mg/kg) in this study was higher than the value (2.98 -4.79 mg/100 g) reported by [19] and the value (36.3 mg/kg) reported by [38]. The mean concentration of Zn in this study ranges from 27 -87.3 mg/kg dry weight which was below maximum permissible level 99.4 mg/kg dry weight set by [7].
Copper The concentration of Cu in this study varies from 5.4 -45.5 mg/kg dry weight. The highest concentration (42 ± 3.5 mg/kg) of Cu was observed in brown teff in the Abeshege district and the lowest level (6.7 ± 1.3 mg/kg) was found in brown teff in the Soro district. Analysis of variance revealed that the mean concentration of Copper was significantly different among teff types in the sample dis-Journal of Agricultural Chemistry and Environment tricts. Fisher's combined probability test using the LSD criterion for significance indicated that the mean concentration of Cu in white teff from Abeshege district was significantly (p < 0.05) higher than that in Soro and Wera districts. Also, the mean concentration of Cu in white teff from Wera district was significantly (p < 0.05) higher than Soro district. Similarly, the mean concentration of Cu in brown teff from Abeshege district was significantly (p < 0.05) higher than Soro and Wera districts. The mean concentration of Cu in brown teff from Wera district was significantly (p < 0.05) higher than Soro district. Also, the mean concentration of Cu in red teff from Abeshege district was significantly (p < 0.05) higher than that in Soro and Wera districts. The mean concentration of Cu in red teff from Wera district was significantly (p < 0.05) higher than Soro district.
The mean concentration of Cu (5.4 -45.5 mg/kg) in this study was higher than the value (1.08 -2.51 mg/100 g) reported by [19] and the value (8.1 mg/kg) reported by [38]. The permissible limit of copper for human consumption recommended by FAO/WHO is 73.3 mg/kg [42]. The present investigation revealed that the concentration of Cu was below the maximum permissible limit 73.3 mg/kg for human health set by [41].

Lead
In this study, the concentration of lead in teff ranged from 0.118 -0.130 mg/kg dry weights. The highest (0.128 ± 0.002 mg/kg) concentration of Pb was found in white teff from Abeshege district and the lowest (0.12 ± 0.002 mg/kg) concentration of Pb was detected in red teff from the Soro district. One-way Analysis of variance revealed that the mean concentration of Pb was significantly different among teff types in the sample districts. Fisher's combined probability test using the LSD criterion for significance indicated that the mean concentration of Pb in white teff from Abeshege district was significantly (p < 0.05) higher than that in Soro and Wera districs. The mean concentration of Pb in white teff from Wera district was significantly (p < 0.05) higher than Soro districts. The mean concentration of Pb in brown teff from Soro district was significantly (p < 0.05) lower than Abeshege and Wera districts. However, there was no significant difference in brown teff from Abeshege and Wera districts with p < 0.05. The mean concentration of Pb in red teff from Wera district was significantly (p < 0.05) higher than Soro and Abeshege districts. Also, the mean concentration of Pb in red teff from Abeshege district was significantly (p < 0.05) higher than that in Soro district.
The concentration of Pb (0.118 -0.13 mg/kg) in this study was lower than the value (0.05 mg/100 g) reported by [39]. The concentration of lead observed in teff in this study was below the recommended limit 0.3 mg/kg as set by [41]. Cadmium The level of cadmium in teff varieties of all sample districts was below the method detection limit indicating that there is no Cd contamination.

Pearson Correlation of Metals
In this study, to correlate the effect of one metal concentration on the concentration of another metal, the Pearson correlation matrices using correlation Journal of Agricultural Chemistry and Environment coefficient (r) for the samples were used and presented in Table 7.
In the teff samples analyzed for the metal levels, the correlation was strong (close to ±1) for some metals, moderate (around ± 0.5) for some other metals and weak (< ±0.5) for the remaining metals. The poor relationship may be due to the fact that different soil types, environmental conditions and capacity of the plant to accumulate specific metal. There

Conclusions
The contents of all essential and non-essential metals in the three teff varieties of present study were within the recommended level. However, the level of toxic metals such as Pb was below the permissible limit and that of Cd was below the method detection limit. Hence, it is safe for daily human consumption. So that this study helped to provide information on that the consumption of these teffs A statistical analysis of variance at 95% confidence level revealed that there were significant differences in the mean concentrations of all metals between the three types of teff and teff from the three grown districts. This could be attri- Experimental investigations indicated that the Red teff contains higher amount of essential metals than brown and white teffs. It also contains higher amount of iron relative to brown and white teff kinds. Therefore, based on the results Red teff can be considered as a good source for prevention of iron deficiency especially for infants and pregnant woman.

Authors' Contributions
AH collected, analyzed and interpreted the data, which was part of his MSC thesis of Analytical Chemistry at Wolaita Sodo University, Ethiopia. AL supervised data collection and interpretation; helped to draft the manuscript as well as approved the final manuscript. MB and CK revised the final manuscript. The final manuscript has been approved by all authors.

Availability of Data and Materials
Data generated during this research work can be available upon request. Journal of Agricultural Chemistry and Environment