NET N MINERALISATION IN COCONUT/NITROGEN FIXING TREE BASED SYSTEM
Abstract
To study the net N mineralisation rates of coconut/NFT plantations, a field incubation technique was carried out. In this study, four types of NFT i.e. Acacia auriculiformis, Calliandra calothyrsus, Gliricidia sepium, Leucaena leucocephala and coconut monocropping were selected. Forty plastic tubes were inserted into the soil, to a depth of 15 cm at a distance of 2 m and l m away from coconut palm, for field incubation period of 2 weeks. Similarly another set of forty tubes were inserted for a 4 week field incubation period, after removing the previous set of tubes. Fresh soll samples (same depth) were also taken close to the inserted tubes on the day on which tubes were inserted for the estimation of initial N concentrations in the soil. Mineralised N concentrations were extracted by 2 M KCl and the net N mineralisation rates were calculated.
Net N mineralisation was significantly higher (P= 0.001) 4 weeks after field incubation peniod than 2 weeks and also, the significant higher (P= 0.001) net N mineralisation was shown 2 m away from coconut than l m away from coconut. The highest net N mineralisation (4.9 ‑ 15.5 kgha-1) was found in Gliricidia site than in the other NFT sites, followed by Leucaena > Calliandra > Acacia. The lowest net N mineralisation (1.2 ‑ 2.2 kgha-1) was recorded in the coconut monocrop, either 2 weeks or 4 weeks incubation period. This study clearly indicated that growing NFTs with coconut enhances N availability in coconut lands and Gliricidia being the most promismig.
References
BLONDEL, D. 1971. Rolle de la mateie're organique libredaus la mineralisation en sol sableurx relation aral' alimentation azotee dn mil Agronomy. In: Microbiological considerations of the N cycle in West African Ecosystem (ed T. Rosswall) pp 55 72 500 PE/UNDP, Royal Swedish Academy of Sciences.
CLARK, F. E. 1981. The N cycle viewed with poetic license. In: Terrestrial N cycles (eds F.E. Clark and T. Rosswall). Ecological Bulletin (Stockholm) 33:13 24.
GHEY, T.J. YAVITT, J.B. PERSON JA, and KNIGHT, D.H. 1985. The nitrogen cycle in lodegepole pine forests, South Eastern Wycomin. Biogeochemistry 1:257 275.
GOSZ, J.R. 1981. Nitrogen cycling mi coniferous ecosystems In: Terrestrial N cycles (eds F.E. Clark and T. Rosswall). Ecological Bulletin (Stockholm) 33:405 426.
GUNARATNE, W.D.L. and HEENKENDE, A.P. 1994. Evaluation of leguminous tree species for biomass production and on soil properties in coffee based cropping systems. In: Mulipurpose tree species in Sri Lanka (ed. H.P.M. Gunasena), p 57 63, Sri Lanka.
KILLHALM, K. 1994. Soil Ecology. Cambridge University Press UX.
MARR, I.L. and CRESSOR, M.S. 1983. Enviromental Chemical Analysis. International Textbook Company, New York.
NADELHOFFER, K.J., ABEF, J.D. and MELILLO, J.M. 1983. Leaf litter production and soil organic matter dynamics along a nitrogen availability gradientmi Southern Wisconsin (USA). Canadian Journal of Forest Research 13:12 2 1.
TENNAKOON, NA. 1990. Effed of organic and inorganic fertilizer combinations on soil biological and chemical properties and the nutrient status of the coconut palm M.Phil. Thesis, University of Kelaruiya, Sri Lanka.
WHITE, C.S., GOSH, J.R., HOMER, J.D. and MOORE, D.I. 1988. Seasonal annual and treatment induced vaniation of available N pools and N cycling processes in solls of two douglas fir stands. Biological Fertility and Soil 6: 93 99.