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Incubation Study of Kinetics and Mineralization Rate of Nitrogen in Organic Sources of Ultisol


Affiliations
1 School of Natural Resource Management, College of Post Graduate Studies in Agricultural Sciences (CPGS-AS), Central Agricultural University (CAU), Imphal, Umiam 793 103, India
 

Age-old traditional farming practices are generally followed by tribal inhabitants using locally available organic sources of plant nutrients. The aim of the present study was to determine the kinetics and rate of mineralization of different local organic sources of North East region of India. An incubation study of 100 days was carried out using locally available organic sources, i.e. farmyard manure (FYM; T1), poultry manure (T2), pig manure (T3) and vermicompost (T4) at the rate of 120 kg N/ha (considering recommended dose of fertilizer of rice as 120 kg N/ha). Bulk soil sample of Typic kandihumultis at 0–15 cm was collected from the College of Post Graduate Studies in Agricultural Sciences, Umiam, Meghalaya research farm and treated with organic sources and kept in an incubator at field capacity soil moisture and 25°C temperature. Observations were taken at 10 days interval up to 100 days of incubation (DOI). A control treatment (T0) of no organic source was used for comparison. The results showed that the average nitrogen mineralization rate (Nmin) of T3 was highest (64.88%), followed by T2 (57.77%), T4 (42.98%) and T1 (35.24%). The highest Nmin rate of T3 and T2 was noted at 60 DOI as 79.37% and 76.10% respectively. At 50–60 DOI, total nitrogen, available nitrogen and nitrogen fractions (ammonical nitrogen and nitrate nitrogen) released were the highest irrespective of the organic sources. R2 (coefficient of determinate) of first-order kinetics of all organic sources was found to be: 0.91 (T3) > 0.90 (T2) > 0.89 (T4) > 0.88 (T1), while R2 of second-order kinetics was: 0.66 (T3) > 0.65 (T2) > 0.64 (T1 and T4). It has been concluded that T3 is the best organic nutrient source among the treatments considered for this study.

Keywords

Incubation Study, Kinetics, Nitrogen Mineralization, Organic Sources, Traditional Farming Practice.
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  • Murugan, A. V. and Swarnam, T. P., Nitrogen release pattern from organic manures applied to an acid soil. J. Agric. Sci., 2013, 5(6), 174–184; ISSN 1916-9752, E-ISSN 1916-9760.
  • Grzyb, A., Wolna-Maruwka, A. and Niewiadomska, A., Environmental factors affecting the mineralization of crop residues. Agronomy, 2020, 10(12), 1951.
  • Risch, A. C. et al., Global impacts of fertilization and herbivore removal on soil net nitrogen mineralization are modulated by local climate and soil properties. Global Change Biol., 2020, 26(12), 7173–7185.
  • Braos, L. B., Ruiz, J. G. C. L., Lopes, I. G., Ferreira, M. E. and da Cruz, M. C. P., Mineralization of nitrogen in soils with application of acid whey at different pH. J. Soil Sci. Plant Nutr., 2020, 20(3), 1102–1109.
  • Neina, D., The role of soil pH in plant nutrition and soil remediation. Appl. Environ. Soil Sci., 2019, 2019, 1–9, Article ID 5794869; https://doi.org/10.1155/2019/5794869.
  • Dey, A., Srivastava, P. C., Pachauri, S. P. and Shukla, A. K., Time-dependent release of some plant nutrients from different organic amendments in a laboratory study. Int. J. Recycl. Org. Waste Agric., 2019, 8(1), 173–188.
  • Nishigaki, T., Tsujimoto, Y., Rinasoa, S., Rakotoson, T., Andriamananjara, A. and Razafimbelo, T., Phosphorus uptake of rice plants is affected by phosphorus forms and physicochemical properties of tropical weathered soils. Plant Soil, 2019, 435(1), 27–38.
  • TNAU Agritech portal, Organic farming, 2009; http://www.agritech.tnau.ac.in/org_farm/orgfarm_poultry.html (accessed on 12 June 2002).
  • Chanu, P. H., Bora, P. K., Thakuria, D. and Ram, V., Influence of land use type on different aggregating elements of acidic soil of Meghalaya India. Int. J. Chem. Stud., 2019, 7(1), 1819–1823.
  • International Society of Soil Science, Minutes of the First Commission Meetings. International Congress of Soil Science, Washington, DC, USA, 1929, pp. 215–220.
  • McLean, E. O., Soil pH and lime requirement. In Methods of Soil Analysis, Part 2: Chemical and Microbiological Properties (eds Page, A. L., Miller, R. H. and Keeney, D. R.), Agronomy Monographs, 9, American Society of Agronomy (ASA), Soil Science Society of America (SSSA), Crop Science Society of America (CSSA), Madison, WI, USA, 1982, 2nd edn, pp. 199–223.
  • Corwin, D. L. and Rhoades, J. D., An improved technique for determining soil electrical conductivity–depth relations from above ground electromagnetic measurements. Soil Sci. Soc. Am. J., 1982, 46(3), 517–520.
  • Walkley, A. and Black, I. A., An examination of the Degtjareff method for determining soil organic matter and proposed modification of the chromic and titration method. Soil Sci., 1934, 34, 29–38.
  • McGill, W. B., Cannon, K. R., Robertson, J. A. and Cook, F. D., Dynamics of soil microbial biomass and water-soluble organic C in Breton L after 50 years of cropping to two rotations. Can. J. Soil Sci., 1986, 66(1), 1–19.
  • Page, A. L., Miller, R. H. and Keneney, D. R. (eds), Chemical and microbiological properties. In Methods of Soil Analysis, Part 2, Agronomy Monography, 9, ASA, SSSA, CSSA, Madison, WI, USA, 1982, 2nd edn, pp. 961–1010.
  • Subbiah, B. V. and Asija, G. L., A rapid method for the estimation of nitrogen in soil. Curr. Sci., 1956, 26, 259–260.
  • Bremner, J. M. and Mulvaney, C. S., Nitrogen – total. In Methods of Soil Analysis, Part 2: Chemical and Microbiological Properties (eds Page, A. L., Miller, R. H. and Keeney, D. R.), Agronomy Monography, 9, ASA and SSSA, Madison, WI, USA, 1982, 2nd edn, pp. 595–624.
  • Keeney, D. R. and Nelson, D. W., Nitrogen-inorganic forms. In Methods of Soil Analysis, Part 2: Chemical and Microbiological Properties (eds Page, A. L., Miller, R. H. and Keeney, D. R.), Agronomy Monography, 9, ASA and SSSA, Madison, WI, USA, 1982, 2nd edn, pp. 643–698.
  • Richardson, H. L., The nitrogen cycle in grassland soils: with special reference to the Rothamsted Park Grass Experiment. J. Agric. Sci., 1938, 28(1), 73–121.
  • Pelican Equipment, model ROTEK LIS: Laboratory Incubator Shaker Variable RPM; https://www.pelicanequipments.com/ (accessed on 23 May 2022).
  • Preusch, P. L., Adler, P. R., Sikora, L. J. and Tworkoski, T. J., Nitrogen and phosphorus availability in composted and uncomposted poultry litter. J. Environ. Qual., 2002, 31(6), 2051–2057.
  • Stanford, G. and Smith, S. J., Nitrogen mineralization potentials of soils. Soil Sci. Soc. Am. J., 1972, 36(3), 465–472.
  • Abbasi, M. K. and Khaliq, A., Nitrogen mineralization of a loam soil supplemented with organic–inorganic amendments under laboratory incubation. Front. Plant Sci., 2016, 7, 1038.
  • Nair, K. P. P., Intelligent Soil Management for Sustainable Agriculture: The Nutrient Buffer Power Concept, Springer Nature Switzerland AG, Gewerbestrasse, Cham, Switzerland, 2019, pp. 1–389, ISBN 978-3-030-15529-2 ISBN 978-3-030-15530-8 (eBook); https://doi.org/10.1007/978-3-030-15530-8.
  • Bunnett, J. F., Kinetics in solution. In Investigations of Rates and Mechanisms of Reactions (ed. Bernasconi, C. F.), Wiley, New York, USA, 1986, 4th edn, pp. 171–250.
  • Joffre, R. and Agren, G. I., From plant to soil: litter production and decomposition. In Terrestrial Global Productivity (eds Roy, J., Saugier, B. and Mooney, H. A.), Academic Press, New York, USA, 2001, pp. 83–99.
  • Singh, B. P., Rengel, Z. and Bowden, J. W., Carbon, nitrogen and sulphur cycling following incorporation of canola residue of different sizes into a nutrient poor sandy soil. Soil. Biol. Biochem., 2006, 38, 32–42.
  • Ge, J., Huang, G., Huang, J., Zeng, J. and Han, L., Mechanism and kinetics of organic matter degradation based on particle structure variation during pig manure aerobic composting. J. Hazard. Mater., 2015, 292, 19–26.
  • Baharuddin, A. S. et al., Characteristics and microbial succession in co-composting of oil palm empty fruit bunch and partially treated palm oil mill effluent. Open Biotechnol. J., 2009, 3, 92–100.
  • Ravindran, B. and Sekaran, G., Bacterial composting of animal fleshing generated from tannery industries. Waste Manage., 2010, 30, 2622–2630.
  • Gómez, E. F., Luo, X., Li, C., Michel, F. C. and Li, Y., Biodegradability of crude glycerol-based polyurethane foams during composting, anaerobic digestion and soil incubation. Polym. Degrad. Stab., 2014, 102, 195–203.
  • Boyd, G. E., Myers Jr, L. S. and Adamson, A. W., The exchange adsorption of ions from aqueous solutions by organic zeolites. III. Performance of deep adsorbent beds under non-equilibrium conditions. J. Am. Chem. Soc., 1947, 69(11), 2849–2859; https://doi.org/10.1021/ja01203a067.
  • Glaski, F. A. and Dranoff, J. S., Ion exchange kinetics: a comparison of models. Am. Inst. Chem. Eng. J., 1963, 9(3), 426–431.
  • Smith, T. G. and Dranoff, J. S., Film diffusion-controlled kinetics in binary ion exchange. Ind. Eng. Chem. Fundam., 1964, 3(3), 195–200; https://doi.org/10.1021/i160011a003.
  • Sharma, H. D., Jervis, R. E. and McMillen, L. W., Kinetics of ion exchange. Diffusion of trace components. J. Phys. Chem., 1970, 74, 969–978.
  • Bitou, M. and Okamoto, M., Fabrication of porous 3-D structure from poly (l-lactide)-based nano-composite foams. Effect of foam structure on enzymatic degradation. Polym. Degrad. Stab., 2008, 93, 1081–1087.
  • Sam, S., Ismail, H. and Ahmad, Z., Soil burial of polyethylene-g-(maleic anhydride) compatibilised LLDPE/soya powder blends. Polym. Plast. Technol. Mater., 2011, 50, 851–861.
  • Cheng, J., Lin, R., Xia, A., Liu, Y., Zhou, J. and Cen, K., Sequential generation of fermentative hydrogen and methane from swine manure with physicochemical characterization. Energy Fuel, 2013, 28, 563–570.
  • Lashermes, G., Barriuso, E., Le Villio-Poitrenaud, M. and Houot, S., Composting in small laboratory pilots: performance and reproducibility. Waste Manage., 2012, 32, 271–277.
  • Razali, W. A. W., Baharuddin, A. S., Talib, A. T., Sulaiman, A., Naim, M. N., Hassan, M. A. and Shirai, Y., Degradation of oil palm empty fruit bunches (OPEFB) fibre during composting process using in-vessel composter. BioResources, 2012, 7, 4786–4805.
  • Sanders, W. T. M., Geerink, M., Zeeman, G. and Lettinga, G., An-aerobic hydrolysis kinetics of particulate substrates. Water Sci. Technol., 2000, 41, 17–24.
  • Liotta, F. et al., Effect of moisture on disintegration kinetics during anaerobic digestion of complex organic substrates. Waste Manage. Res., 2014, 32, 40–48.
  • Frissel, M. J. and van Veen, J. A., Simulation model for nitrogen immobilization and mineralization. In Modeling Wastewater Renovation by Land Disposal (ed. Iskandar, I. K.), Wiley, New York, USA, 1981, pp. 359–381.
  • Beek, J. and Frissel, M. J., Simulation of Nitrogen Behavior in Soils, Centre for Agricultural Publishing and Documentation, Wageningen, The Netherlands, 1973, pp. 1–67.
  • Mehran, M. and Tanji, K. K., Computer modeling of nitrogen transformations in soils. J. Environ. Qual., 1974, 3, 391–395.
  • Jastrow, J. D., Boutton, T. W. and Miller, R. M., Carbon dynamics of aggregate-associated organic matter, estimated by C-13 natural abundance. Soil Sci. Soc. Am. J., 1996, 60, 81–807.

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  • Incubation Study of Kinetics and Mineralization Rate of Nitrogen in Organic Sources of Ultisol

Abstract Views: 183  |  PDF Views: 75

Authors

Lumbini Kalita
School of Natural Resource Management, College of Post Graduate Studies in Agricultural Sciences (CPGS-AS), Central Agricultural University (CAU), Imphal, Umiam 793 103, India
N. J. Singh
School of Natural Resource Management, College of Post Graduate Studies in Agricultural Sciences (CPGS-AS), Central Agricultural University (CAU), Imphal, Umiam 793 103, India
Lala I. P. Ray
School of Natural Resource Management, College of Post Graduate Studies in Agricultural Sciences (CPGS-AS), Central Agricultural University (CAU), Imphal, Umiam 793 103, India
A. K. Singh
School of Natural Resource Management, College of Post Graduate Studies in Agricultural Sciences (CPGS-AS), Central Agricultural University (CAU), Imphal, Umiam 793 103, India

Abstract


Age-old traditional farming practices are generally followed by tribal inhabitants using locally available organic sources of plant nutrients. The aim of the present study was to determine the kinetics and rate of mineralization of different local organic sources of North East region of India. An incubation study of 100 days was carried out using locally available organic sources, i.e. farmyard manure (FYM; T1), poultry manure (T2), pig manure (T3) and vermicompost (T4) at the rate of 120 kg N/ha (considering recommended dose of fertilizer of rice as 120 kg N/ha). Bulk soil sample of Typic kandihumultis at 0–15 cm was collected from the College of Post Graduate Studies in Agricultural Sciences, Umiam, Meghalaya research farm and treated with organic sources and kept in an incubator at field capacity soil moisture and 25°C temperature. Observations were taken at 10 days interval up to 100 days of incubation (DOI). A control treatment (T0) of no organic source was used for comparison. The results showed that the average nitrogen mineralization rate (Nmin) of T3 was highest (64.88%), followed by T2 (57.77%), T4 (42.98%) and T1 (35.24%). The highest Nmin rate of T3 and T2 was noted at 60 DOI as 79.37% and 76.10% respectively. At 50–60 DOI, total nitrogen, available nitrogen and nitrogen fractions (ammonical nitrogen and nitrate nitrogen) released were the highest irrespective of the organic sources. R2 (coefficient of determinate) of first-order kinetics of all organic sources was found to be: 0.91 (T3) > 0.90 (T2) > 0.89 (T4) > 0.88 (T1), while R2 of second-order kinetics was: 0.66 (T3) > 0.65 (T2) > 0.64 (T1 and T4). It has been concluded that T3 is the best organic nutrient source among the treatments considered for this study.

Keywords


Incubation Study, Kinetics, Nitrogen Mineralization, Organic Sources, Traditional Farming Practice.

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DOI: https://doi.org/10.18520/cs%2Fv125%2Fi7%2F765-770