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Volume 2016 (2016), Article ID 7026859, 10 pages
Research Article

Symbiotic N2-Fixation Estimated by the 15N Tracer Technique and Growth of Pueraria phaseoloides (Roxb.) Benth. Inoculated with Bradyrhizobium Strain in Field Conditions

1Center for African Area Studies, Graduate School of Asian and African Area Studies, Kyoto University, 46 Shimoadachi-cho, Yoshida, Sakyo-ku, Kyoto 606-8501, Japan
2Department of Plant Biology, Faculty of Science, University of Yaoundé I, P.O. Box 812, Yaoundé, Cameroon
3Regional Biocontrol and Applied Microbiology Laboratory, Institute of Agricultural Research for Development (IRAD), P.O. Box 2067, Yaoundé, Cameroon
4Graduate School of Agriculture, Soil Science Laboratory, Kyoto University, Kitashirakawa Oiwake-cho, Sakyo-ku, Kyoto 606-8502, Japan

Received 4 December 2015; Accepted 4 January 2016

Academic Editor: Juan Manuel Ruiz-Lozano

Copyright © 2016 Papa Saliou Sarr et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.


This field experiment was established in Eastern Cameroon to examine the effect of selected rhizobial inoculation on N2-fixation and growth of Pueraria phaseoloides. Treatments consisted of noninoculated and Bradyrhizobium yuanmingense S3-4-inoculated Pueraria with three replications each. Ipomoea batatas as a non-N2-fixing reference was interspersed in each Pueraria plot. All the twelve plots received 2 gN/m2 of 15N ammonium sulfate 10% atom excess. At harvest, dry matter yields and the nitrogen derived from atmospheric N2-fixation (%Ndfa) of inoculated Pueraria were significantly () higher (81% and 10.83%, resp.) than those of noninoculated Pueraria. The inoculation enhanced nodule dry weight 2.44-fold. Consequently, the harvested N significantly () increased by 83% in inoculated Pueraria, resulting from the increase in N2-fixation and soil N uptake. A loss of 55 to 60% of the N fertilizer was reported, and 36 to 40% of it was immobilized in soil. Here, we demonstrated that both N2-fixing potential of P. phaseoloides and soil N uptake are improved through field inoculations using efficient bradyrhizobial species. In practice, the inoculation contributes to maximize N input in soils by the cover crop’s biomass and represent a good strategy to improve soil fertility for subsequent cultivation.

1. Introduction

The genus Pueraria originates from South Asia, Southeast Asia, China, Japan, and parts of Oceania [1] and is now widespread throughout the humid tropics. Perennial legume cover crops such as Pueraria phaseoloides are commonly grown between the rows trees or used in improved fallows, in order to reduce soil erosion, improve soil fertility, and increase the growth and yield of associated plants [24]. Leguminous crops are a source of nitrogen and contribute to an increase in the nitrogen uptake of the nonleguminous associated crop [5]. A major advantage of growing a legume cover crop is its ability to fix N2 symbiotically and to accumulate nitrogen in the plantation agroecosystem. P. phaseoloides fixes nitrogen in symbiosis with Bradyrhizobium strains and is classified as “promiscuous ineffective” [6]. Nitrogen fixation is a process by which nitrogen in the atmosphere is converted into ammonium [7]. Both the plant and the rhizobia benefit from such a symbiotic relationship. Nitrogen is the most commonly deficient nutrient in many soils around the world and it is the most commonly supplied plant nutrient. However, the supply of nitrogen through fertilizers has severe environmental concerns. Atmospheric nitrogen fixed by the symbiotic association between soil bacteria (rhizobia) and crop legumes is likely to be in the order of 20 to 22 million tons of nitrogen each year [8].

In Eastern Cameroon, short-term Pueraria fallows of two years are commonly practiced to restore soil fertility for subsequent cultivation of cassava which is a staple food in the area. Yield increments of cassava are related to soil quality improvement which includes soil erosion limitation, increase of soil organic carbon and nitrogen following a good decomposition of Pueraria litters. The phylogenetic diversity of nitrogen-fixing bacteria in the root nodules of Pueraria in Eastern Cameroon was previously investigated [9]. Using molecular biology techniques, these authors identified three groups of Bradyrhizobium species corresponding to B. sp., B. yuanmingense, and B. elkanii that nodulate Pueraria phaseoloides. By assessing the nitrogen fixation potential of these three groups using the Acetylene Reduction Activity (ARA) method, it was found that strains belonging to B. yuanmingense showed significant higher efficiency. The selection of appropriate rhizobial microsymbionts is becoming a complex procedure due to the fact that several legumes species can be nodulated by single rhizobia [10]. Yet the symbiotic association between the legumes and their microbial symbionts plays a significant role in agriculture worldwide by reducing ca. 100 million metric tons of atmospheric nitrogen saving US$ 8 billion/year on fertilizer N [11, 12]. The common approach to improving the symbiotic fixation of nitrogen and legume productivity, using superior or very effective exotic rhizobial strains as inoculants, often fails to achieve the desired responses [13, 14]. The failure has been attributed to the poor competitiveness of the introduced rhizobia [15], the nonspecificity of the bacteria, and the occurrence and resistance to stress of ineffective indigenous strains in soils [16]. To improve the N2-fixation and growth of Pueraria, the use of rhizobia, selected from indigenous community with capacity for nodulation and strong nitrogen-fixing activity, is believed to be an important agronomic approach.

Pueraria phaseoloides is used in the tropics as a forage and cover crop, but rhizobial inoculations of this legume in field conditions have not been widely tested. The importance of this work is to improve the nitrogen fixation potential and growth of Pueraria through field inoculations with effective strains of Bradyrhizobium, enabling enhancement of the input of nitrogen in the soil via biological process, to shorten the fallow period of Pueraria and put the land in faster use, as well as reduce environmental hazards that the use of chemical fertilizers to increase yields often poses. In this paper, we report on the effects of inoculating Pueraria with the selected efficient B. yuanmingense S3-4 strain [9] on its N2-fixation, dry biomass production, total N uptake, nitrogen fertilizer use efficiency, and soil fertility through a field experiment. Symbiotic nitrogen fixation was estimated using the 15N tracer technique and Ipomoea batatas (L.) Lam. was used as a nonfixing reference plant.

2. Materials and Methods

2.1. Study Site

The study was carried out in Andom village (5°15′N, 13°30′E) located in Eastern Cameroon, which is in the forest-savanna transition zone [17, 18]. The elevation of the plateau is 650–700 m a.s.l. and its basement consists of metamorphic rocks. The annual rainfall range of this area is 1350–1550 mm and the distribution of rainfall is bimodal according to field measurement carried out from 2008 to 2013 [19]. Rains begin in mid-March, a short dry season follows from mid-July to the end of August, and then the main rainy season extends from September to the middle of November. The mean annual temperature in the region is 25°C. The December–February period is the driest part of the year when the relative humidity may be higher than 60% [20]. The soil pH in the cultivated land varies from 4.82 to 5.17 with average levels of organic C, total N, and available P of 1.81%, 0.113%, and 4.57 ppm, respectively, and a C/N ratio of 15.91 [21]. Soils are classified as Typic Kandiudox according to USDA classification system [22]. The dominant forest vegetation is Albizia zygia, which dominates the tree layer. The dominant species in the savanna are the perennial grasses Pennisetum setaceum, Imperata cylindrica, and Chromolaena odorata [17, 18]. The experiment was set on a cleared natural fallow land previously dominated by Chromolaena odorata. There have been no planted legumes including Pueraria, and no history of rhizobial inoculation was observed in the site.

2.2. Experimental Design

Treatments consisted of inoculated Pueraria and noninoculated Pueraria, each replicated three times in a complete randomized block design. Ipomoea batatas plots were interspersed in each Pueraria plot as non-N2-fixing references, giving a total of 12 plots (4 m2 plot−1) with a planting density of 9 plants per 1.5 m 1.5 m. I. batatas was used as a reference crop as it shares with Pueraria similar patterns of N uptake from the soil and will obtain similar 15N enrichment in the soil-derived N [23]. The use of a reference crop is important in estimating the amount of nitrogen derived from the atmosphere (Ndfa) of legumes. Each Pueraria-Ipomoea block was separated to others by a 2 m interval (Figure 1). Pueraria seeds were sown on 9 August 2014 at 50 cm spacing. Uniform Ipomoea seedlings of 10 cm length were obtained from farmers’ fields and transplanted in their corresponding plots at 50 cm spacing, two weeks after Pueraria seeds were sown.

Figure 1: Experimental design. IP = inoculated Pueraria, NIP = noninoculated Pueraria, and IpB = Ipomoea batatas. IP and NIP treatments were each replicated 3 times, giving a total of 6 Pueraria plots. Ipomoea plots (six) were interspersed in each Pueraria plot as non-N2-fixing references. Plot’s size was 4 m2. In each plot, plant spacing was 50 cm corresponding to 9 hills per 1.5 m 1.5 m for both Pueraria and Ipomoea. For Pueraria, seeds were sown but thinned to 3 plants per hill after the seedlings were well established while, for Ipomoea, uniform seedlings of 10 cm length were transplanted two weeks after the sowing of Pueraria seeds. Pueraria inoculation was performed using the effective strain B. yuanmingense S3-4 (2.094 108 cells per hill) three weeks after seed’s sowing. All plots received 2 gN/m2 of 15N labelled ammonium sulfate 10% atom excess applied at 1 and a half months after Pueraria seeds were sown. Plots were regularly weeded throughout the rain-fed prone experiment that lasted 4 months.
2.3. Rhizobial Inoculation and Application of 15N Labelled Ammonium Sulfate

Prior to this field experiment, rhizobial strains were isolated from Pueraria nodules collected from the experimental site and other neighboring fields and subjected to DNA-based molecular analysis [9]. The results showed that the native strains for Pueraria in the experimental field clustered into 3 groups corresponding to Bradyrhizobium yuanmingense, B. elkanii, and B. sp. By assessing their nitrogen fixation potential using the Acetylene Reduction Assay (ARA), it appeared the B. yuanmingense strains, and S3-4 in particular, showed a significant highest potential. Therefore, Bradyrhizobium yuanmingense S3-4 identified as an efficient Pueraria symbiont [9] was used in this field experiment. From glycerol stock, it was streaked on YMA agar plates [24] for one week. After colony development, one pure colony was grown in 20 mL YMB for another week to produce the inoculum. The obtained solution of 2.094 109 cells mL−1 was diluted 1000 times with sterilized water to give a concentration of 2.094 106 cells mL−1. The inoculation was carried 3 weeks after the sowing of Pueraria seeds (29 August 2014) when seedlings were well established. Above each Pueraria hill (in the three inoculated Pueraria plots), 100 mL of the diluted inoculum corresponding to 2.094 108 cells hill−1 was applied carefully. One and a half months after the starting of the experience when all crops were well established (22 September 2014) nitrogen fertilizer as 15N labelled ammonium sulfate enriched with 10% atom excess was applied at the rate of 2 gN/m2. When estimating the nitrogen fixation of legumes using labelled fertilizer N, lower rates of N fertilizer are preferably applied to avoid limiting the nitrogen fixation potential. Some authors [25, 26] also used the same rate of 2 gN/m2 during their studies on the N2-fixation of cowpea and Pueraria in field conditions. Prior to the fertilizer application, Pueraria seeds were thinned to three seedlings per hill. As 2 gN/m2 corresponds to 9.524 g of ammonium sulfate per square meter, the 12 plots in our experimental site required 475 g of ammonium sulfate. Considering the loss that may occur during the application of the fertilizer solution, we considered making a solution for 13 plots (495 g of ammonium sulfate). This amount was dissolved in 78 liters of water after which a 6-liter solution was carefully spread in each plot using a sprayer. Due to the high cost of labelled fertilizers, we limited the experimental unit to a 4 m2 area per plot. After the fertilizer solution was applied, a thin layer of soil was spread above the plots to mimic the atmospheric volatilization of the fertilizer. A portion of the solution was stored in a small bottle for further analysis of the exact atom percent excess of the fertilizer solution. Throughout the experimental period, plots were carefully and regularly weeded to avoid removing the 15N labelled ammonium sulfate outside the plots.

2.4. Data Collection

P. phaseoloides litter begins to accumulate on the soil surface about 6 months after establishment followed by subsequent mineralization [27]. To avoid entering the period of Pueraria leaves drop-off which would alter the results, this experiment lasted four months (August–December 2014). At term, the 9 central plants of each plot (to avoid the border effect) were harvested (Figure 1). The fresh shoots were separated from the fresh roots in each plot and their biomass was weighed. Pueraria root nodules were separated from the roots in each plot and their fresh weight was recorded. Fresh subsamples of known weights were collected from the shoot biomass and root biomass of each Pueraria and Ipomoea plot and together with the fresh nodules per Pueraria plot; they were oven-dried at 70°C for 48 hours in laboratory. Conversion calculations were made to determine the dry matter yields of inoculated Pueraria, noninoculated Pueraria, and Ipomoea. Composite soil samples were collected from each plot at the 0–15 cm horizon, air dried, and used for nutrient analysis.

The dried plant samples were ground at <0.5 mm and used for analysis. Total N was determined on the finely ground plant materials using 50 mg samples. The standard was 30 mg L-glutamic acid. Samples were packed in tin capsules and analyzed on a Carlo Erba NA1500 N/C elemental analyzer [28]. Total N (%) of soil samples was determined following the same procedure except that the amount of 500 mg was used. Total carbon was determined using a dry-combustion method with a C/N analyzer (VarioMax CHN; Elementar Analysensysteme GmbH, Hanau, Germany). The 15N enrichment in soil and plant materials was determined on an isotope ratio mass spectrometer (Delta Finnigan MAT 251, Bremen, Germany) coupled on-line to an elemental analyzer [28]. The 15N fertilizer solution used in this experiment was also analyzed to record the exact 15N atom% excess.

2.5. Calculations

The 15N atom% excess in plant materials was obtained by using the 15N atom% provided during the analysis and the atmospheric natural 15N abundance (0.3662%) by applying the equationIn addition, the total nitrogen (TN; g/m2), fertilizer nitrogen recovery (g/m2), fertilizer nitrogen use efficiency (%NUE), the percentage of N crops that derived from the fertilizer (%Ndff), nitrogen derived from atmosphere (%Ndfa), and nitrogen derived from soil (%Ndfs) were determined.

Most calculations in this paper were according to the International Atomic Energy Agency. The fertilizer nitrogen recovery, which corresponds to the amount of nitrogen in plants that derived from the applied nitrogen (Ndff), was calculated asThe %Ndff was calculated using the following equation:The TN and NUE were derived from the following calculations: DM (g/m2) corresponds to the dry matter yieldThe proportion of Pueraria nitrogen derived from the atmosphere (%Ndfa) was calculated using the 15N isotope dilution equation [29]:In (6), is the %Ndff of the N2-fixing plant and the %Ndff of the non-N2-fixing reference. As for Pueraria, the sources of nitrogen are the soil, the fertilizer, and the atmosphere; %Ndfs was calculated asFor the non-N2-fixing Ipomoea reference crop,The TN (g/m2) and Ndff (g/m2) in roots, shoots, and nodules of Pueraria were determined separately. The sum of TN in shoots, roots, and nodules gave the total nitrogen content in the plant while the sum of Ndff in the three components yielded the total Ndff in the plant. For Ipomoea, the TN (g/m2) in roots and shoots were summed to give the plant total nitrogen, and similarly, the total nitrogen derived from the fertilizer was the sum of those in shoots and roots. These total values were used in the final calculations. To calculate the %Ndfa in a Pueraria plot (Ndfa of plant or Ndfa of residual soil) we considered the %Ndff (Ndfa of plant or Ndfa of residual soil) of the Ipomoea grown in interspersed plots.

The available amount of nitrogen in the soil [total soil N (g/m2)] in terms of equivalents units of ammonium sulfate was estimated in each plot. By using a labelled fertilizer source it is possible to determine the plant available amount of nutrient in the soil and this amount is expressed relatively to the amount available in the fertilizer source. Some authors [3032] assumed that when a plant is confronted with two or more sources of a nutrient element, the nutrient uptake from each of these sources is proportional to the amounts available in each source. Implicit in this assumption is the fact that there is a complete mixture of the isotopes or isotopic equilibria. In this situation, the following equation was proposed: Therefore, N immobilization that corresponds to the portion of fertilizer N remaining in the soil at harvest is calculated as Following that, the amount of fertilizer N lost during the trial was calculated as follows:Finally, N loss values can be transformed into percentages.

All data were subjected to analysis of variance (ANOVA) using the CropStat 7.2 software (International Rice Research Institute, Manila, Philippines) at a probability level of 5%. Mean separation was performed using Fisher’s least significant difference (LSD) test whenever a significant result () was obtained.

3. Results and Discussion

3.1. Growth Response of Plants to Bradyrhizobial Inoculation and Fertilizer Application

Fresh and dry matter yields of Pueraria and Ipomoea are reported in Table 1. It shows a positive effect () of inoculation with Bradyrhizobium yuanmingense S3-4 on P. phaseoloides growth 4 months after seed sowing. Total fresh and dry weights were significantly higher in inoculated Pueraria than in noninoculated Pueraria. This difference originated from the difference in shoot production, given that no significant difference in root’s yield was recorded between the inoculated and the noninoculated Pueraria. The inoculation contributed to increase the total fresh and dry weights of Pueraria 2.02- and 1.81-fold, respectively. The 1.81-fold increase of the dry weight of P. phaseoloides receiving the inoculation was 81% higher compared to that of Pueraria without inoculation. The nodule fresh and dry weights were also significantly () improved 2.32- and 2.44-fold by the inoculation, respectively. The increase in nodule dry weight from 0.283 g/m2 in the noninoculated Pueraria to 0.690 g/m2 in the inoculated Pueraria after 4-month growth (Table 1) could derive from the increase in nodule number or bigger nodule size. In this study, the nodule number was not counted at the field during the harvest due to high numbers but rather their total fresh and dry weights per plot were recorded. However, it is well known that matured bigger nodules with stronger hemoglobin activity are better drivers for increased N2-fixation in legume crops [33] rather than a high number of small immature nodules. It was found that the N2-fixation in groundnut was stimulated along with growth of nodules by application of another external source as millet straw [34]. Similarly, Pueraria plants with a greater mass of effective nodules tend to develop greater plant biomass.

Table 1: Growth characteristics of plants (inoculated and noninoculated Pueraria, Ipomoea) after 4-month cultivation.

In addition, although the main goal of this work was to compare the effect of the inoculation on Pueraria growth characteristics and N2-fixation, we observed that the dry matter production of the reference crop (I. batatas) was not significantly different from that of Pueraria.

Table 2 shows the nitrogen status in plants at harvest. Total N uptake in the reference crop (Ipomoea) was not significantly different from that of the noninoculated Pueraria but was significantly lower than that of the inoculated Pueraria. In addition, the harvested total N harvested from inoculated Pueraria was significantly higher than that harvested from noninoculated Pueraria at 5% probability level. The higher N content in inoculated Pueraria could be expected since it is strongly related to the higher dry matter production in this treatment. An overall increase of 0.825 g/m2 was obtained in inoculated plots within four months. To understand whether this increase in total N was a consequence of the obtained improvement of the N2-fixation itself, the total N in inoculated and noninoculated Pueraria plants was fractionated into nitrogen derived from soil (Ndfs), nitrogen derived from fertilizer (Ndff), and nitrogen derived from atmosphere (Ndfa), and that in Ipomoea was fractionated into Ndfs and Ndff, and results are shown in Figure 2. We observed that as a non-N2-fixing reference crop Ipomoea extracted most of its N from soil. The contribution of the N2-fixation in the plant’s N pool was significantly higher () in inoculated than in noninoculated Pueraria. The nitrogen derived from N2-fixation accounted for 26.25% in noninoculated Pueraria and 37.08% in inoculated Pueraria (Table 2). The results of plant N fractionation indicated that the surplus of 0.825 gN/m2 in the inoculated Pueraria did not derive only from the improvement of N2-nitrogen fixation. While +0.388 gN/m2 (47%) in inoculated Pueraria was added by the N2-fixation, the others, 0.398 gN/m2 (48.3%) and 0.039 gN/m2 (4.61%), derived from the soil and applied fertilizer N, respectively. This clearly indicates that the inoculation of Pueraria with B. yuanmingense S3-4 not only enhances the N2-fixation but also may make a positive contribution in facilitation of a better uptake of N from the soil and from the applied fertilizer. For instance, Table 2 shows better fertilizer N use efficiency of the inoculated Pueraria than the noninoculated Pueraria. It is important to note that as the harvested plants were located in the middle of each plot, there was no risk of nutrient uptake from the external soil environment which would result in erratic data due to the dilution of the isotope. Furthermore, the interspersed design where each Pueraria plot was next to a plot of the reference Ipomoea reduced the fertility gradient that may exist in the experimental site.

Table 2: N status in plants (inoculated and noninoculated Pueraria, Ipomoea) at harvest.
Figure 2: Sources and amount of plant N (g/m2) harvested per treatment during the four-month experiment period. Ndfs = nitrogen derived from soil, Ndff = nitrogen derived from fertilizer, and Ndfa = nitrogen derived from atmosphere. IP = inoculated Pueraria, NIP = noninoculated Pueraria. In a column, values correspond to the amount of N (g/m2) per N source (soil, fertilizer, and atmosphere). One-way ANOVA using CropStat ver. 7.2 was applied to the same N source for IP, NIP, and Ipomoea and no significant difference was observed except for Ndfa between IP and NIP with different letters.

The dual increase of N from N2-fixation and soil N uptake in inoculated Pueraria as shown in Figure 2 is not surprising and agrees with Butler and Ladd [35]. These authors also found that the amount of N2 fixed in medic (Medicago littoralis) and pea (Pisum sativum) increased together with increasing uptake of soil N in different soils when amounts of available N did not exceed 35 µg N g−1 soil for medic and 74 µg N g−1 soil for pea. The amount of soil N in the Pueraria plots of this study (Table 4) was higher (2.1 mg g−1 on average) than those values reported by Butler and Ladd [35]. However, Vesterager et al. [27] reported that apparently P. phaseoloides is tolerant towards the elevated inorganic N levels in the soil, which is an important quality for a cover crop in order to accumulate N in plantation systems. Moreover, by studying the effect of litter application on the N2-fixation of Pueraria, these authors found a higher amount of total N in the plants supplied with litter since the total uptake of soil N increased considerably by litter application. Similarly to their finding, the effect of the fertilizer N in our experiment was slightly improved by the bradyrhizobial inoculation as indicated by the %NUE and described above.

Table 3 shows the N status in shoots, roots, and nodules of inoculated Pueraria, noninoculated Pueraria, and Ipomoea. It indicates that the inoculation did not influence the N concentration in P. phaseoloides. Therefore, the 83% increase in total N of inoculated Pueraria compared to noninoculated Pueraria as shown in Table 2 was a result of the higher dry matter yield (Table 1) which resulted from a combination of (i) higher N2-fixation, (ii) soil N uptake, and (iii) a better use efficiency of the fertilizer N.

Table 3: Effect of bradyrhizobial inoculation on plant N status after 4-month growth.
Table 4: Soil N status in inoculated and noninoculated Pueraria and Ipomoea plots at harvest.

In the present study, the contribution of the symbiotic N2-fixation to the total N in P. phaseoloides (26–37%) was lower than that found by some authors in pot [27] and in field [23, 36] conditions which reached 70%. P. phaseoloides without inoculation was estimated by 15N isotope dilution to fix between 60 and 80% of the N it accumulated in a 2-year-old palm plantation in Malaysia, amounting to 151 kg N ha−1 year−1 [26]. Galiana et al. [37] inoculated Acacia mangium trees with two effective Bradyrhizobium sp. strains and estimated their nitrogen fixation by the 15N natural abundance method and reported that 55–62% of N derived from atmosphere in the inoculated trees while the noninoculated control trees fixed 41% of their nitrogen. The lower N2-fixation level in our experiment could partly be related to the lower plant density (9 plants/1.5 m 1.5 m) we used for the purpose of the trial. The most adequate spacing for Pueraria for a fast soil cover was estimated to be 25 cm [38] which would result in a density of 25 plants/1.25 1.25 m. The shortage of rains during the first weeks of the experiment at the end of August 2014 (data not shown) that led to watering of the plants could be another reason. Furthermore, given that our experiment was set on a cleared natural fallow land, adequate N amount from the soil and the subsequent mineralization of residual litters may also have lowered the nitrogen fixation potential. High inorganic N concentrations are known to inhibit N2-fixation [39]. However, variation exists in the sensitivity of symbiotic N2-fixation to combined N between and within legume species [40, 41]. For instance, with C. caeruleum, no response to inoculation with several rhizobial strains was found in four experiments in Malaysia, even though the inoculant strains formed over 70% of the nodules in some cases [23]. In further experiments, inoculation of C. caeruleum and Pueraria with different strains of Bradyrhizobium also failed to improve their growth [42]. In some cases, the failure of cover crop establishment has been linked to the lack of suitable inoculants.

The 15N% atom excess in Pueraria (inoculated or noninoculated) shoots was found to be lower than that in Ipomoea (Table 3). This is to be expected since the N obtained by Pueraria from the soil and fixation from the atmosphere has reduced the 14N/15N ratio in the tissues [41] of the legume crop, contrary to the nonnodulating reference crop. Although it was not significant, the 15N enrichment in shoots, roots, and nodules of Pueraria slightly decreased by the bradyrhizobial inoculation, justifying the slight reduction of the 14N/15N ratio and increase in N2-fixation in these three plant components. In P. phaseoloides, the enrichment was higher in roots than in shoots and nodules. A similar result was obtained in a study of the symbiotic N2-fixation of P. phaseoloides as influenced by litter mineralization, using the grass Axonopus compressus as a non-N2-fixing reference crop [27]. This has been attributed to a relatively higher dilution of labelled 15N in shoots of legumes than in roots by symbiotically fixed N [35, 43]. Our results agree with Oghoghorie and Pate [44] who found that symbiotically fixed N accumulated in shoots and nodules whereas the roots derived most of its N from mineral sources. The pattern of higher enrichment in shoots than in roots in I. batatas might be a result of variations in the enrichment in available N with time. Such variations may be affected by soil type, plant species, and length of the growth period [27]. The total N in shoots, roots, and nodules reported in Table 3 indicates that rather than the roots and the nodules the shoots explain better the difference in total dry matter yield and total N harvest between the inoculated and the noninoculated Pueraria. For this reason many studies using the 15N enrichment technique focus on analyzing only the aboveground biomass.

3.2. Uptake of Fertilizer and Soil N

The recoveries of labelled fertilizer N (Ndff) in inoculated Pueraria, noninoculated Pueraria, and Ipomoea were 6.16%, 7.78%, and 10.27%, respectively (Table 2). The percentage of fertilizer N recovered in the nonfixing Ipomoea crop was significantly higher than that in the legume crop. This is particularly important since non-N2-fixing references require more nitrogen from other sources such as applied fertilizer N compared to legumes that fix atmospheric nitrogen as another source of N. However, the recovery of labelled fertilizer N was very low compared to the results of other studies. It reached 63% for P. phaseoloides and 71% in the A. compressus reference [27]. However, the %Ndff in this study was similar to that obtained in cowpea grown in field conditions [25]. The low recovery of labelled fertilizer N in the present study which correlated with the low NUE (%) could be related to the high loss (55–60%) of labelled fertilizer N from the top 15 cm of soils (Table 4). Nitrogen can become unavailable to the crop by leaching or as gaseous losses due to denitrification and/or volatilization. The concept of fertilizer use efficiency implies not only the maximum uptake of the applied nutrient by the crop but also the availability of the applied nutrient under variable climatic and edaphic conditions. Although this study was carried out to determine the nitrogen fixation of Pueraria following field inoculations, it is important to study the efficient use of fertilizers in order to obtain the highest possible yield with a minimum fertilizer application. Moreover, 36 to 40% of the labelled fertilizer N was immobilized in the soil (Table 4). Immobilization refers to the incorporation of nitrate and exchangeable ammonium into organic forms that are not available to plants. This occurs as microorganisms compete with plants for available nitrogen, which results in a decrease in the nitrogen availability for the crop. The low recovery of the labelled fertilizer N justified the high proportions (%) of Ndfs in plant materials. It was significantly higher in the reference crop (89.73%) than in the inoculated (56.77%) and the noninoculated (66.92%) Pueraria as shown in Table 2. Although no significant difference was observed in the %Ndfs between the inoculated and noninoculated Pueraria biomass, there was an overall increase in the amount of N uptake (g/m2) from soil. This is in contradiction with other studies which demonstrated that plants tend to extract lesser nutrients from the soil stock when other sources are available. In this regard, Rees et al. [45] reported a reduced uptake of soil N following application of legume residues with a high N content. A reduction of the recovery of 15N labelled fertilizer by application of legume residues with a low C/N ratio was also reported [46]. Although the analysis was not significant at 5% probability level, the residual soil N mainly derived from the original soil solution, small N portions were recovered from the applied ammonium sulfate fertilizer but also from the N2 fixed and returned to the soil within the four-month growth.

4. Conclusion

The inoculation with an effective bradyrhizobial strain stimulated the growth of field grown P. phaseoloides and increased the total N amount via an increase of the amounts of N derived from symbiotic N2-fixation and from soil. The positive effect of the inoculation on the nodulation phenotype (increase of nodule dry weight) and N2-fixation of P. phaseoloides shown in this study indicates that the introduced B. yuanmingense S3-4 was competitive with indigenous strains in field conditions. However, to find out whether this improvement was mainly due to the inoculation, the identification of infection with the used strain in the nodules would provide more accurate information. This study is important in that it is the first report describing the nitrogen fixation potential and growth of inoculated P. phaseoloides in field conditions with an effective Bradyrhizobium strain in Eastern Cameroon. Furthermore, it showed the positive contribution of field inoculations in maximizing N input in soils during fallows, for subsequent cultivation. The subject of the study has some relevance to soil fertility management in Cameroon which is one of the limiting factors of agricultural production.

Conflict of Interests

The authors declare that there is no conflict of interests regarding the publication of this paper.


This work was supported by the Science and Technology Research Partnership for Sustainable Development (SATREPS) program of the Japan Science and Technology Agency (JST) and the Japan International Cooperation Agency (JICA) which funded the Cameroon Forest-Savanna Sustainability (FOSAS) project. To SATREPS, the authors express their sincere gratitude. The authors also would like to thank Mr. Dieudonne Ndong, the Field Research Technician of the FOSAS project, for his valuable support during the field work. They also acknowledge Mr. Shinichi Watanabe from the Soil Science Laboratory of the Graduate School of Agriculture, Kyoto University, for his support during the 15N isotopic analyses.


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