Distribution pattern of metals in mung bean varieties
The results showed that potassium, which ranged from 3670.72 to 3716.81 mg/kg, was found to be appreciably highest amount. One-way analysis of variance showed that the mean potassium concentration was significantly different among four mung bean varieties (p<0.001). The wide variation, potassium bioavailability in mung beans may be due to various genetic factors. From the study, ShewaRobitis the best variety regarding potassium content because potassium plays a vital role in human metabolism, may affect blood pressure, and can be a factor in general heart health
(Aslam et al., 2005).
Next to potassium, mung bean varieties have high magnesium (2422-2492.4 mg/kg) concentration. The highest concentration of Mg was recorded in Shewa Robit (2492.4±14.5 mg/kg) followed by China (2473±6 mg/kg), N-26 (2440±38.6 mg/kg) and NVL (2422±23 mg/kg), respectively. The mean concentration of magnesium in ShewaRobit was significantly higher than the mean concentration of magnesium in N-26 and NVL (p<0.001). However, the mean magnesium concentrations in ShewaRobit and China were not significantly different. The Mg contents were found to be higher than those reported in an earlier study
(Mubarak, 2005), in which Mg contents of raw and differently processed mung beans ranged from 440 to 556 mg/kg. According to
USDA (2001), the level of Mg in the current study is greater than the critical level of the standard.
As shown in Table 1, the calcium concentration in mung bean seed varieties ranged from 1418.02±17.7 to 1698±43.76 mg/kg. One-way analysis of variance showed that the mean calcium concentration was significantly different among four mung bean varieties (p<0.001). Fisher’s combined probability test using the LSD criterion for significance indicated that the mean calcium concentration in NVL was significantly higher than the mean calcium concentration in N-26, China and ShewaRobit with p<0.001. According to
USDA (2001), the level of Ca in the current study is greater than the critical level (132 mg/100 g), indicating that the mung bean is a good source of nutrients. The mung bean variety N-26 (235.5±2.2 mg/kg) was found to be highest in iron content, while a low amount of iron was present in the sample of China (196.2±6.4 mg/kg) variety. The Fe concentration pattern in mung bean seed was in the order of N-26 > NVL > Shewa Robit > China.
One-way analysis of variance showed that the mean concentration of iron was significantly different among four mung bean varieties, p<0.001, as shown in Table 1. The mean concentrations of iron in N-26 and NVL were not significantly different. USDA National Nutrient database reported the level of Fe as 6.74 mg/100 g
(USDA, 2001); these were lower than the present study result. The permissible limit of Fe set by FAO/WHO in the edible plant was 425.5 mg/kg
(FAO/WHO, 2001). Comparing the iron level in this study with the above values, it was lower than the permissible level of iron in edible plants.
The sodium concentration ranged from 88.92 to 106.75 mg/kg in mung bean seeds. The mean sodium concentration was not significantly different among four mung bean varieties (p>0.001). USDA National Nutrient database reported the level of Na as 15 mg/100 g
(USDA, 2001); these were higher than the present study result.
The highest concentration of Zn was recorded in NVL (103±10 mg/kg) followed by Shewa Robit (99.4±3.2 mg/kg), China (82±8.16 mg/kg) and N-26 (72±30 mg/kg), respectively. One-way analysis of variance showed that the mean zinc concentration was not significantly different among four mung bean varieties, p<0.001. Fisher’s combined probability test using the LSD criterion for significance indicated that the mean concentration of zinc in all four varieties was not significantly different with p<0.001. USDA National Nutrient database reported the level of Zn as 2.68 mg/100 g
(USDA, 2001); this was lower than the present study result. The permissible limit of Zn set by
FAO/WHO (2001) in the edible plant was 99.4 mg/kg.
The concentration of manganese was found to be higher in ShewaRobit (97.6±18 mg/kg), and its concentration in other varieties was found in order of N-26 (77±10.3 mg/kg), NVL (67.6±1.66 mg/kg) and China (51±7.2 mg/kg) respectively.
The mean manganese concentration was significantly different among four mung bean varieties, p<0.001. USDA National Nutrient database reported the level of Mn as 1.035 mg/100g
(USDA, 2001); this was lower than the present study result. The permissible limit of Mn set by
FAO/WHO (2001) in the edible plant was 500 mg/kg. This amount was higher than those recorded in the present study.
The concentration of copper ranged from 7.8±1.3 to 27.4±2.4 mg/kg in mung bean seeds. The concentration of Cu in mung bean seed was in the order of NVL>N-26> Shewa Robit > China and its mean was significantly different among four mung bean varieties, p<0.001. USDA National Nutrient database reported level of Cu was 0.941 ìg/100g
(USDA, 2001); these were lower than the present study result. The permissible limit of Cu set by FAO/WHO in the edible plant was 73.3 mg/kg
(FAO/WHO, 2001); these were higher than those recorded in the present study.
The proximate composition in the mung bean sample
Crude protein (%)
As shown in Table 2, the average protein contents ranged from 17.86 to 28.29% in different mung bean varieties. Variety NVL exhibited maximum crude protein content (28.29%) followed by N-26 (26.32%), China (24.13%), and ShewaRobit (17.86%).
Crude fat (%)
Crude fat ranged between 1.05% to 1.49 per cent (Table 2). From the varieties, maximum crude fat was found in NVL (1.49%), followed by N-26 (1.28%), ShewaRobit (1.11%), and China (1.05%). Mungbean is not a good source of fat as all the varieties yielded a minimal quantity of crude fat less than 1.5 per cent
(Tresina et al., 2010). The mean crude fat content was significantly different among four mung bean varieties, p<0.001.
Ash contents (%)
Ash content ranged between (2.9-3.35%). Some researchers like
Agugo and Onimawo (2009);
(Habib et al., 2007); Mubarak (2005) and
(Paul et al., 2003) were reported 3.75 to 4% ash content in mung bean, which are relatively higher than those recorded in the present study. However, some other workers namely
Blessing and Gregory (2010);
(Pasha et al., 2011); (Shaheen et al., 2012) and
(Tresina et al., 2010) reported 3.0, 2.97, 2.91 and 3.12% of ash content, respectively, which were in good agreement to those recorded in the present study while
(Bhatty et al., 2000) reported higher ash contents (4.63 g/100g) in green mung bean. The ash contents in mung bean seed was significantly different in four varieties, p<0.001.
Moisture (%)
The data in Table 2 revealed that moisture contents varied from 5.76 to 7.57% in various varieties. The highest Moisture (7.57%) was found in China, followed by NVL (7.4%), ShewaRobit (6.12%) and N-26 (5.76%).
Khatoon and Prakash (2006) reported the mung bean moisture content of 5.25 to 9.3%, agreeing with those recorded in the present study. The pattern of moisture content in mung bean seed was in the order of China > NVL > Shewa Robit > N-26. One-way analysis of variance showed that the moisture content level was significantly different among four mung bean varieties, p<0.001.
Distribution pattern of metals in mung bean growing soils
The concentrations of soil nutrients are good indicators of soil quality and productivity because of their favorable effects on soil’s physical, chemical, and biological properties (Cao, 2011). As shown in Table 3, the concentration of K (449.24 mg/kg), Ca (2524.44 mg/kg), Mg (260.93 mg/kg), Fe (241.63 mg/kg), Mn (241.68 mg/kg), Zn (15.00 mg/kg), Cu (1.05 mg/kg) and Na (32.87 mg/kg). In general, the concentration pattern of metals in soil was found as order Ca > K > Mg > Mn > Fe > Na > Zn.
Comparisons of metal levels between mung bean and soil sample
Plants absorb whatever is present in the soil medium. Therefore, the metals are also absorbed and become bioaccumulated in the plant’s roots, stems, fruits, grains, and leaves, which may finally be transferred to human in the food chain. The sorption processes of metals by plants is significantly affected by metal level in the soil, soil pH, the presence of competing ligands, the ionic strength of the soil solution and the simultaneous presence of competing metals
(Zubillaga, 2008).
In this work, a comparative study has been established to correlate the metal level of mung bean with the soil where it has grown. As shown in Table 4, for most elements (K, Mg, Ca, Na, Zn, Fe, Cu,) the metal levels of mung bean were directly proportional to the metal levels of soil where it has grown. This relation partly verifies that the metal content of the plant is a function of the metal level in the soil where it has grown. For the rest metal (Mn), the metal levels in the sampling area of mung bean were varied to metal levels in the corresponding soil. This unproportional variation in the level of metals in mung bean and soil may have resulted from the difference in availability of the absorbable form of metals in soil due to differences in soil acidity or the presence of competing ligands
(Snober et al., 2011).