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ASSESSMENT OF NITROGEN FIXATION POTENTIAL IN AHIPA (Pachyrhizus ahipa) AND ITS EFFECT ON ROOT AND SEED YIELD

Published online by Cambridge University Press:  01 April 2009

D. N. RODRÍGUEZ-NAVARRO*
Affiliation:
IFAPA, Centro Las Torres-Tomejil, CAP-Junta de Andalucía, Apdo. Oficial, 41200 Alcalá del Río, Sevilla, Spain
M. CAMACHO
Affiliation:
IFAPA, Centro Las Torres-Tomejil, CAP-Junta de Andalucía, Apdo. Oficial, 41200 Alcalá del Río, Sevilla, Spain
F. TEMPRANO
Affiliation:
IFAPA, Centro Las Torres-Tomejil, CAP-Junta de Andalucía, Apdo. Oficial, 41200 Alcalá del Río, Sevilla, Spain
C. SANTAMARÍA
Affiliation:
IFAPA, Centro Las Torres-Tomejil, CAP-Junta de Andalucía, Apdo. Oficial, 41200 Alcalá del Río, Sevilla, Spain
E. O. LEIDI
Affiliation:
Departamento de Biotecnología Vegetal, Instituto de Recursos Naturales y Agrobiología de Sevilla, CSIC, Av. Reina Mercedes 10, 41012 Sevilla, Spain
*
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Summary

Ahipa is a legume of great interest for the production of raw materials (starch, sugar, oil and proteins) for industrial use. Its yield potential and ability to fix atmospheric N2 in association with rhizobia makes it an attractive option for low input agriculture systems. At present, it is cultivated on a very small scale as a food crop in a few South American countries. Little information is available on symbiotic N2 fixation in ahipa and no work has been performed on strain selection for inoculant production. Soils in southwest Europe are devoid of specific rhizobia able to nodulate on ahipa. Selecting rhizobia for symbiotic effectiveness from a collection led to the isolation of strains which provided greater shoot growth and N content under controlled conditions. In the field, inoculation at sowing with the selected strains increased significantly seed and tuberous root yield and seed protein content. The amount of N2 fixed, estimated by 15N natural abundance, reached 160–260 kg N ha−1. In previous work, ahipa appeared to be a promising alternative crop for the production of industrial raw materials. The results of the present study showed a yield increase in tuberous roots and seeds when applying effective rhizobia inoculants. Furthermore, a positive soil N balance was left after its cultivation making ahipa even more interesting for sustainable farming systems.

Information

Type
Research Article
Copyright
Copyright © Cambridge University Press 2009
Figure 0

Table 1. Rhizobial strains, origin and plant host species and screening of their symbiotic performance on ahipa AC521. Shoot mass, leaf N concentration, nodule mass and number of nodules per plant after 10 weeks of growth under greenhouse conditions.

Figure 1

Table 2. Effect of the inoculation with different rhizobia strains (Spec1, PAC48, PAC55) on the shoot and root growth, N content and symbiotic parameters (number of nodules, nodule mass, nodule size) in ahipa landraces (AC102, AC521) at flowering-fruiting (79 DAS) grown under controlled conditions.

Figure 2

Table 3. Shoot growth, N content and symbiotic parameters (number of nodules, nodule mass, and nodule size) at flowering (57 DAS) in ahipa landraces (AC102, AC230, AC521, AC526) inoculated with different rhizobia strains (Spec1, PAC48, PAC51, PAC55).

Figure 3

Table 4. Effect of inoculation with different rhizobia strains on root and seed yield (in kg dry matter ha−1), root sugar concentration (Brix degrees) and seed protein and oil concentration (%) of ahipa landraces AC102 and AC521.

Figure 4

Table 5. Nitrogen concentration (%) in shoots, roots, seeds and estimates of N2 fixation by natural 15N abundance (P, proportion of plant N derived from nitrogen fixation, %) or relative ureide content of xylem sap (XRU, %) of ahipa landrace AC521 inoculated with different rhizobia strains harvested at 119 DAS.

Figure 5

Table 6. Gross estimation of the total N exported in seeds and roots at harvest of uninoculated (control) and inoculated ahipa landrace AC521, N recovery (total N remaining in dried shoots on the soil) and calculation of fixed N2 using the P values reported in Table 5. The amount of N remaining in the soil in secondary roots or pod walls after threshing was not considered. The gross N balance was then calculated as follows: N balance = (N recovery + N2 fixed seed + N2 fixed root) − (seed removal + root removal).