African Journal of Biotechnology Vol. 8 (21), pp. 5711-5717, 2 November, 2009 Available online at http://www.academicjournals.org/AJB
ISSN 1684–5315 © 2009 Academic Journals
Full Length Research Paper
Growth, nodulation and yield of black gram [Vigna mungo (L.) Hepper] as influenced by biofertilizers and soil amendmentsEM (effective microorganisms) is a commercial biofertilizer mainly consists of photosynthetic and lactic acid bacteria, yeast and actinomycetes. The present study was undertaken to investigate the effect of EM application and two strains of nitrogen fixing Bradyrhizobium japonicum (TAL- 102 and MN-S) on plant growth, nodulation and yield of black gram [Vigna mungo (L.) Hepper] in different soil amendment systems including unamended soil, farmyard manure (FYM) @ 5 g 100 g-1, Trifolium alexandrinum green manure (GM) @ 4 g 100 g-1 and recommended dose of NPK fertilizers. Nodule number was significantly enhanced by inoculation of either of the two B. japonicum strains in NPK and un-amended soils. A marked increase in nodule biomass was also recorded due to B. japonicum inoculation in these 2 types of soils. Grain yield was significantly increased by 46% due to either of the two B. japonicum strains in NPK amended soil. EM application markedly enhanced nodule number in FYM amended soil. Conversely, EM application in combination with either of the two B. japonicum strains resulted in pronounced reduction both in number and biomass of nodules in NPK fertilizers amendment. EM application significantly enhanced grain yield by 48% in NPK amendment without B. japonicum inoculation.
Institute of Mycology and Plant Pathology, University of the Punjab, Quaid-e-Azam Campus Lahore, Pakistan. E-mail: email@example.com.
Accepted 7 August, 2009
Key words: Black grams, Bradyrhizobium japonicum, effective microorganisms, nitrogen fixation, soil amendments.
Chemical fertilizers are an indispensable component of today’s agriculture. About 60% of humanity eventually owes its nutritional survival to N fertilizers (Fixon and West, 2002). However, growing concern about the environmental consequences of mineral N use and its future cost perspectives emphasize the need to develop new production technologies that are sustainable both economically and ecologically (Khaliq et al., 2006). Organic materials hold great promise as a source of multiple nutrients and ability to improve soil characteris- tics (Soumare et al., 2003; Moller, 2009). Since the effect of organic nutrients on crop yield is long term and not immediate, thus farmers are reluctant to use organic fertilizers in their cropping system. Use of EM (effective microorganisms) along with organic materials possibly be an effective technique for stimulating release of nutrients from organic sources. EM technology was developed by Dr. Teuro Higa in 1970’s at the University of Ryukyus, Okinawa, Japan. Effective microorganisms culture con- sists of co-existing beneficial microorganisms, the main being the species of photosynthetic bacteria; Rhodopseu- domonas plastris and Rhodobacter sphacrodes; lacto- bacilli such as Lactobacillus plantarum, L. casei and Streptococcus lactis; yeasts (Saccharomyces spp) and Actinomycetes (Strptomyces spp.) which improve crop growth and yield by increasing photosynthesis, producing bioactive substances such as hormones and enzymes, controlling soil diseases and accelerating decomposition of lignin materials in the soil (Higa, 2000; Hussain et al., 2002). When effective micro-organisms cultures are applied to the soil they stimulate the decomposition of organic wastes and residues thereby releasing inorganic nutrients for plant uptake. Majority of the scientists who are engaged in promoting this technology have no doubt that plant growth is just as good or batter and quality of plant products is superior to conventional farming (Bajwa et al., 1999a; Iwaishi, 2000; Xu et al., 2000; Javaid, 2006). However, experiences of some workers revealed that the effect of effective microorganisms on crop yield was usually not evident or even negative particularly in the first test crop (Javaid et al., 2008). It is often difficult to establish the predominance of effective microorganisms cultures in soil with only a single application and during only one season. Certain soil properties and the indigenous soil microbial populations are often constraints to the establishment of these microorganisms (Bajwa et al., 1995; Javaid et al., 1997).
Black gram is a grain legume widely cultivated in Pakistan, India and other Asian countries. It is part of diet for millions of people in these countries and a cheep source of protein with 17 - 34% of protein in seeds (Gour, 1993). An important feature of the mashbean plant is its ability to establish a symbiotic partnership with specific bacteria, setting up the biological N2-fixation process in root nodules by rhizobia that may supply the plant's needs for N (Mahmood and Athar, 2008; Mandal et al., 2009). The present study was carried out to investigate the effect of two Bradyrhizobium japonicum strains; TAL- 102 (soybean isolate) and MN-S (mungbean isolate) on growth, nodulation and yield of mashbean and role of EM in improving the efficacy of these strains in different soil amendment systems.
MATERIALS AND METHODS
Soil used in the experiment was sandy loam in texture having organic matter 0.9%, pH 8.1, EC 4.8 mS cm-1, nitrogen 0.05%, available phosphorus 14 mg.kg-1 and available potassium 210 mg.kg-1. The micronutrients Fe, Cu and Zn were 9.53, 1.71 and 4.42 mg kg-1 of soil, respectively.
This experiment was a continuation of a previous experiment where mungbean [Vigna radiata (L.) Wilczek] was cultivated. Experiment was conducted in earthen pots of 20 cm diameter and 30 cm deep. The pot soil was amended either with farmyard manure (FYM) @ 5 g/100 g, Trifolium alexandrianum green manure (GM) @ 4 g/100 g (on dry weight basis), NPK fertilizers or left unamended. A basal dose of 20 mg kg-1 N as urea, 30 mg kg-1 P2O5 as triple supper phosphate and 30 mg kg-1 K2O as potassium sulphate was supplied to the NPK amended pot soil. Pots were irrigated with tap water of good quality and left for 15 days for decomposition of organic matter. Mungbean was sown in these pots. After harvesting the mungbean crop, the present study was conducted in the same pots.
No more GM and FYM were added for the present study. However, NPK fertilizers were added to the respective pots at the same rate as was for mungbean mentioned above.
Procurement of B. japonicum and EM
Two peat based B. japonicum inocula namely B. japonicum st. TAL- 102 and B. japonicum st. MN-S were obtained from Nuclear Institute for Biotechnology and Genetic Engineering (NIBGE), Faisalabad, Pakistan. B. japonicum st. TAL- 102 is an exotic strain originally isolated from soybean while B. japonicum st. MN-S is a local strain isolated from mungbean.
EM stock solution in the commercial name of EM Bioaab was obtained from Nature Farming Research and Development Foundation, Faisalabad, Pakistan. The EM contained high popu- lations of lactic acid bacteria at 1 × 1011 cfu ml-1, photosynthetic bacteria at 1 × 106 cfu ml-1 and yeast 1 × 103 cfu ml-1 of suspension (Higa, 2000). The EM stock solution was diluted by adding water in the ratio of 1:1000. Respective pots of EM treatments were irrigated with 500 ml of dilute solution of EM (1:1000) 15 days prior to mung- bean sowing in the previous experiment. These pots also received 500 mL of dilute EM solution at fortnight intervals throughout the experimental period for mungbean (previous experiment) as well as for black grams (present experiment).
Treatments and experimental design
There were 6 treatments in each of the 4 soil amendment systems. These include:
i) Control (without any microbial inoculation).
ii) Effective Microorganisms (EM).
iii) B. japonicum st. MN-S. iv) B. japonicum st. MN-S + EM.
v) B. japonicum st. TAL- 102.
vi) B. japonicum st. TAL- 102 + EM.
Black gram seeds were surface sterilized with 1.0% sodium hypo- chlorite solution followed by several washings with sterilized water. Seeds were soaked in sterilized water for 2 h and left in covered petri plates over night to facilitate rapid and uniform germination. Seeds for respective B. japonicum treatments were pelted with peat based single strain inocula of B. japonicum st. TAL- 102 and B. japonicum st. MN-S with concentrated sugar solution as an ad- hesive. Initially 4 seeds were sown in each pot, which were thinned to 2 uniform seedlings on emergence. Each treatment was replica- ted 3 times. Pots were arranged in a completely randomized design on a bench in a wire netting house under natural conditions of light and temperature. Plants were irrigated with tap water of good quality whenever required.
Data collection and statistical analysis
Plants were harvested at flowering and maturity stages. The data regarding shoot length, root and shoot biomass were recorded at both the harvesting stages while that of number and biomass of nodules were recorded only at flowering stage. Data regarding various yield parameters; pod number, pod length, number of seeds per pod and grain yield were recorded at maturity. All the data were analyzed statistically by applying ANOVA followed by Duncan’s multiple range test (Steel and Torrie, 1980) to separate the treatment means.
Table 1. ANOVA for the effect of growth stage, soil amendments, B. japonicum and effective microorganisms (EM) on root and shoot growth of V. mungo.
*, ** Significant at P 0.01 and 0.001, respectively.
Effect of microbial inoculation on shoot and root growth
variance shows that effect of B. japonicum (B) inoculation was
significant for shoot length (Table 1). At flowering stage, effect of
either of the two B. japonicum strains was not much pronounced. However,
at maturity stage, both the B. japonicum strains markedly enhanced
shoot length in un-amended and farmyard manure (FYM) amended soils
(Table 2). Both the B. japonicum strains enhanced shoot biomass in NPK
amended soil. Effect of B. japonicum st. MN-S was more pronounced and
signi- ficant both at flowering stage and maturity (Table 2). Effect of
B. japonicum inoculation was also significant for root biomass (Table
1). In green manure (GM) amended soil, both the B. japonicum strains
markedly suppressed root biomass at maturity stage. By contrast, in NPK
amended soil a significant increase in root biomass was recorded by
inoculation of either of the two B. japonicum strains. In un-amended as
well as in FYM amended soil, neither of the two B. japonicum strains
exhibited pro- nounced effect on root biomass (Table 2).
of variance reveals the significant effect of EM application on shoot
length and biomass as well as on root biomass. The interactive effect of
EM and soilamendment (A) was also significant for shoot length. Similarly, the
effect of A × B × EM was significant for root biomass (Table 1). The
most pronounced and significant effect of EM application was observed on
shoot dry bio- mass in NPK amendment. Similar effect of EM appli-
cation on root dry biomass was also recorded in NPK amendment at
maturity stage. Neither of the two B. japonicum strains showed
significant response to EM application with respect to root and shoot
growth in any of the 4 soil amendment systems (Table 2).
Effect of microbial inoculation on nodulation
Effect of soil amendments was significant both for num- ber and fresh biomass of nodules (Table 3). The highest nodules number was recorded in un-amended soil followed by NPK amendment. Both the organic amend- ments resulted in a marked suppression in nodules number. Adverse effect was more pronounced due to GM than FYM amendment (Table 4).
B. japonicum inoculation showed a significant effect on nodulation. Nodules number was significantly enhanced by both the B. japonicum strains in un-amended as well as in NPK amended soil. B. japonicum st. MN-S was more effective in un-amended soil while st. TAL-102 was more effective in NPK amendment. Effect of inoculationon nodules biomass was also much pronounced in these two types of soils.
Conversely, inoculation of either of the two B. japonicum strains
failed to show significant effect on number and biomass of nodules in GM
and FYM amended soils (Table 4).
Table 2. Effect of B. japonicum and EM application on plant vegetative growth in V. mungo.
In a column, values with different letters in a column show significant difference at P 0.05 as determined by Duncan’s multiple range test.
Effect of EM application on nodulation was variable with respect to soil amendments. Analysis of variance shows that the interactive effect of EM and soil amend- ments was highly significant (P 0.01 and 0.001) both for nodule number and biomass (Table 3). In FYM amended soil, EM application markedly enhanced nodule number both in B. japonicum inoculated and un-inoculated treat- ments. In contrast to that, in NPK amendment, EM application suppressed number as well as biomass of nodules in B. japonicum inoculated plants. In other soil amendment systems, effect of EM application on nodulation was not much pronounced (Table 4).
Effect of microbial inoculation on yield
Analysis of variance shows that effect of soil amend- ments was significant for various yield parameters; num- ber of pods per plants, pod length, number of seeds per pod and grain yield (Table 3). Generally, values of these parameters were lower in GM amendment as compared to other soil amendment systems (Table 4). B. japonicum st. MN-S enhanced number of pods per plant by 26% in un-amended soil. By contrast, both the species reduced pod number by 40% in GM amendment. However, all the effects were insignificant statistically. Effect of B. japo- nicum inoculation on pod length and number of seeds per pod was also insignificant in all the 4 soil amendment systems. Grain yield was significantly enhanced by 46% due to each of the two B. japonicum strains in NPK amended soil. EM application resulted in significant increase of 48% in grain yield in NPK amended soil. In general, effect
of EM application on various yield para- meters was insignificant
(Tables 3 and 4).
Table 3. ANOVA for the effect of soil amendments, B. japonicum and effective microorganisms (EM) on nodulation and yield characteristics of Vi. mungo.
*, **, ***, significant at P 0.05, 0.01 and 0.001, respectively; ns: Non significant.
In the present study, suitability of cross inoculation of two B. japonicum strains; TAL-102 (soybean isolate) and MN- S (mungbean isolate) inoculation to mashbean for bather growth, yield and nodulation characteristics was studied in different soil amendment systems. Both the strains proved suitable for mashbean. However, the affectivity of the two inoculated strains was associated with the type of soil amendment. Nodule number was significantly in- creased by inoculation of either of the two strains in NPK amendment. Nodule biomass was also markedly enhanced in inoculated treatments in this soil amendment system. As a consequence of improved nodulation, a similar significant improvement in grain yield was also evident due to inoculated B. japonicum strains. Earlier, Dubey (1998) obtained highest grain yield in soybean when host plant was inoculated with Bradyrhizobium in combination with NPK fertilizers. In the present study, response of nodulation to B. japonicum strains inocula- tion in un-amended soil was similar to that of response in NPK fertilizers amendments. However, unlike that of NPK fertilizer amendment, grain yield was not enhanced in un- amended soil in response to B. japonicum inoculation. Earlier, Mahmood and Athar (2008) reported that cross inoculation of mashbean with rhizobia isolated from Dalbergia sissoo, Leucaena leucocephala, Pithecel- lobium dulce, Prosopis cineraria, Prosopis glandulosa and Prosopis juliflora significantly enhanced dry weight and nitrogen contents of mashbean. In the present study, in both the organic matter amendments; farmyard and green manure amended soils, nodulation was very poor as compared to NPK amended and un-amended soils. Inoculation of both the B. japonicum strains failed to enhance nodulation in these two organic matters amended soils.
Effect of EM application on nodulation was variable in different soil amendment systems. EM application mar- kedly enhanced nodule number both in B. japonicum inoculated and un-inoculated treatments in FYM amen- ded soil. Conversely, in NPK amendment, EM application adversely affected the nodulation both in terms of number and biomass. In GM amendment as well as in un- amended soil, effect of EM application was not pronoun- ced. Earlier reports regarding the effect of EM application on nodulation are also contradictory. EM application caused a significant reduction in nodule number but increased the size and biomass of nodules in Trifolium alexand rinum (Bajwa et al., 1999b). By contrast, Javaid et al. (2000) noted a significant increase in nodulation in Vigna radiata due to EM application. Javaid et al. (2002) have reported similar effects of long-term EM application and organic manures on nodulation in Phaseolus vulgaris L. In seems probable that soil amendments as well as indigenous population of soil microorganisms determine the nodulation response of host plant to EM application.
Similar to that of nodulation, effect of EM application on plant growth and yield was also variable in different soil amendments. The most pronounced and significant effect of EM application on shoot and root dry biomass was observed in NPK amendment. Likewise, EM application resulted in 48% increase in grain yield in NPK amended soil without B. japonicum inoculation. In rest of the treat- ments, effect of EM application was not much pro- nounced. Earlier there are contradictory reports regarding the effect of EM application on crop growth and yield. Many workers have
reported increase in crop growth and yield by the application of EM
(Daly and Stewart, 1999; Yan and Xu, 2002; Javaid, 2006; Khaliq et al.,
2006). However, the investigations of other workers have revealed that
the effect of EM on crop growth and yield was usually not evident or
even negative especially in the first test crop (Bajwa et al., 1995,
1999b; Diass et al., 2008; Javaid et al., 2008). Certain soil properties
and the indigenous soil microbial populations are often con- straints
to the establishment of EM cultures. Studies have shown that these
constrains can be overcome through periodic repeated applications of EM
at least during the first few years (Sangakkara et al., 1998; Javaid et
al., 2000, 2002). According to Kinjo et al. (2000) the lack of
consistency in results of the experiments regarding EM application may
be due to variable cultural conditions employed in previous studies.
Imai and Higa (1994) stated that the observed decline in crop yields
could often be attributed to the fact that soils, where conventional
farming is practiced, have become disease-inducing or putrefactive soils
from long-term use of pesticides and chemical fertilizers.
Consequently, it takes time to establish a disease-suppressive or
zymogenic soil. Until this conversion process is completed, it is
virtually impos- sible to exceed crop yields that were obtained with
conventional farming methods. However, the present study reveals that
the effect of EM application on crop growth and yield is associated with
the type of soil amendment used. This study concludes that the benefits
of B. japonicum strains TAL- 102 and MN-S and EM to black gram can be
best exploited by applying these biofertilizers in NPK amended soils.
However, further field trials are required before these findings are
recommended to the farmers for field application of these biofertlizers.
Table 4. Effect of B. japonicum and EM application on nodulation and yield of V. mungo.
In a column, values with different letters in a column show significant difference at P 0.05 as determined by Duncan’s multiple range test.
Prof. Dr Tahir Hussain, Director Nature Farming Research Centre Faisalabad provided EM solution and Dr. Fouzia Yousaf Hafeez, NIBGE Pakistan provided B. japonicum cultures.
Bajwa R, Javaid A, Tasneem Z (1995). Response of indigenous soil microflora to EM inoculation in Pakistan. Biota 1: 73-79.
Bajwa R, Javaid A, Haneef B (1999a). EM and VAM Technology in Pakistan V: Response of chickpea (Cicer arietinum L.) to co- inoculation of effective microorganisms (EM) and VA mycorrhiza under allelopathic stress. Pak. J. Bot. 31: 387-396.
Bajwa R,Javaid A, Rabbani N (1999b). EM and VAM technology in Pakistan. Effect of organic amendments and EM on VA mycorrhiza, nodulation and crop growth in Trifolium alexandrianum L. Pak. J. Biol. Sci. 2: 590-593.
Daly MJ, Stewart DPC (1999). Influence of ‘‘effective microorganisms’’ (EM) on vegetative production and carbon mineralization- a preliminary investigation. J. Sustain Agric. 14: 15-25.
Diass N, Lobo MG, Socorro AR, Bruckner U, Heller J, Gonzalez M (2008). The effect of three organic pre-harvest treatments on Swiss chard (Beta vulgaris L. var. cycla L.) quality. Eur. Food Res. Technol. 226: 345-353.
Dubey SK (1998). Response of soybean (Glycine max) to biofertilizers with and without nitrogen, phosphorus and potassium on swell-shrink soil. Indian J. Agron. 43: 546-549.
Gour YD (1993). Microbiology, physiology and agronomy of nitrogen fixation: Legume-Rhizobium symbiosis. Proc. Indian Nat. Sci. Acad. B 59: 333-358.
Higa T (2000). What is EM technology? EM World J. 1: 1-6. Hussain T, Anjum AD, Tahir J (2002). Technology of beneficial micro-
organisms. Nature Farm Environ. 3: 1-14. Imai S, Higa T (1994). Kyusei nature farming in Japan. Effect of EM on
growth and yield of spinach. In: Proceedings of 2nd International Conference on Kyusei Nature Farming, Brazil, Oct. 7-11, 1991. pp. 92-96.
Iwaishi S (2000). Effect of organic fertilizer and effective microorganisms on growth, yield and quality of paddy-rice varieties. J. Crop Prod. 3: 269-273
Javaid A (2006). Foliar application of effective microorganisms on pea as an alternative fertilizer. Agron. Sustain Dev. 26: 257-262
Javaid A, Bajwa R, Ahmad Q, Rabbani N (1997). Effect of EM application on growth, yield, nodulation and nitrogen nutrition in pea (Pisum sativum L.) in heat sterilized and unsterilized soil. Sci. Int. (Lahore) 9: 307-309.
Javaid A, Bajwa R, Rabbani N, Uzma M (2000). EM and VAM technology in Pakistan. IX: Effect of EM application on growth, yield, nodulation and VA mycorrhizal colonization in Vigna radiata (L) Wilczek. Pak. J. Biol. Sci. 3: 694-698.
Javaid A, Anjum T, Bajwa R (2002). EM and VAM technology in Pakistan. XII: Growth, nodulation and VA mycorrhizal response of Phaseolus vulgaris to long-term EM application. Pak. J. Phytopathol. 14: 57-61.
Javaid A, Bajwa R, Anjum T (2008). Effect of heat sterilization and EM (effective microorganisms) application of wheat (Triticum aestivum L.) grown in organic matter amended soils. Cereal Res. Commun. 36: 489-499.
Khaliq A, Abbasi MK, Hussain T (2006). Effect of integrated use of organic and inorganic nutrient sources with effective microorganisms (EM) on seed cotton yield in Pakistan. Bioresour. Technol. 97: 967- 972.
Kinjo T, Perez K, de Almeida E, Ramos MAG, Oliveia de JO (2000). Plant growth affected by EM-Bokashi and chemical fertilizers. Nature Farm Environ. 1: 33-38.
Mahmood A, Athar M (2008). Cross inoculation studies: Response of Vigna mungo to inoculation with rhizobia from tree legumes growing under arid Environment. Int. J. Environ. Sci. Technol. 5: 135-139.
Mandal S, Mandal M, Das A (2009). Stimulation of indoleacetic acid production in a Rhizobium isolate of Vigna mungo by root nodule phenolic acids. Arch. Microbiol. 191: 389-393.
Moller K (2009). Influence of different manuring systems with and without biogas digestion on soil organic matter and nitrogen inputs, flows and budgets in organic cropping systems. Nutr. Cycling Agroecosyst. 84: 179-202.
Sangakkara UR, Marambe B, Attanayake AMU, Piyadasa ER (1998). Nutrient use efficiency of selected crops grown with effective microorganisms in organic systems. In: Proceedings of 4th International Conference on Kysei Nature Farming held in Paris, France, June 19-21, 1995. pp. 111-117.
Xu HL, Wang R, Mridha MAU (2000). Effects of organic fertilizers and a microbial inoculant on leaf photosynthesis and fruit yield and quality of tomato plants. J. Crop Prod. 3: 173-182.
Yan PS, Xu HL (2002). Influence of EM Bokashi on nodulation, physiological characters and yield of peanut in nature farming fields. J. Sustain Agric. 19: 105-112.