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Nitrogen turnover and loss during storage of slurry and composting of solid manure under typical Vietnamese farming conditions

Published online by Cambridge University Press:  05 October 2010

M. T. TRAN*
Affiliation:
Soils and Fertilizers Research Institute, Dong Ngac, Tu Liem, Hanoi, Vietnam Plant and Soil Science Section, Department of Agriculture and Ecology, Faculty of Life Sciences, University Copenhagen, Thorvaldsensveij 40, DK-1871, Frederiksberg C, Denmark
T. K. V. VU
Affiliation:
National Institute of Animal Sciences, Thuy Phuong, Tu Liem, Hanoi, Vietnam Institute of Chemical Engineering, Biotechnology and Environmental Engineering, Faculty of Engineering, University of Southern Denmark, Campusvej 55, 5230 Odense M, Denmark
S. G. SOMMER
Affiliation:
Institute of Chemical Engineering, Biotechnology and Environmental Engineering, Faculty of Engineering, University of Southern Denmark, Campusvej 55, 5230 Odense M, Denmark
L. S. JENSEN
Affiliation:
Plant and Soil Science Section, Department of Agriculture and Ecology, Faculty of Life Sciences, University Copenhagen, Thorvaldsensveij 40, DK-1871, Frederiksberg C, Denmark
*
*To whom all correspondence should be addressed. Email: [email protected]

Summary

A high proportion of plant nutrients present in animal feed are excreted and therefore animal manure can be an important source of nitrogen (N) for crop production if losses of plant nutrients to the environment during storage and processing are minimized. The present study examines gaseous N losses from stored pig slurry and during composting of solid manure as affected by protein and fibre content in the feed and manure management. Two slurry storage treatments (with and without cover) and three additives to solid manure composting (straw only, straw+lime and straw+superphosphate) were examined for three common types of pig feed in Vietnam (low-protein high-fibre, medium-protein medium-fibre and high-protein low-fibre).

Feed type was found to affect the N content in pig slurry or manure and thus potential N losses. The fraction of N loss caused by N emission from covered slurry storage was 0·25–0·30 of initial N content, while that from uncovered slurry was 0·60–0·70. After 90 days of storage, 1·15–1·20 times the initial ammonium-N (NH4-N) was found in the covered slurry and 0·40–0·50 in the uncovered. The fraction of N lost during composting with superphosphate was 0·25–0·35 of initial total N, while with lime or straw the total N loss was 0·45–0·55. With added superphosphate, 1·25–1·60 times the initial NH4-N in manure was found in the compost after 80 days compared with only 0·11–0·22 for lime and 0·22–0·36 for straw only. Covering stored slurry and addition of superphosphate when composting solid pig manure are thus important methods for Vietnamese farmers to minimize N losses and produce compost with a high content of plant-available N.

Type
Crops and Soils
Copyright
Copyright © Cambridge University Press 2010

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References

Amon, B., Kryvoruchko, V., Frohlich, M., Amon, T., Pollinger, A., Mosenbacher, I. & Hausleitner, A. (2007). Ammonia and greenhouse gas emissions from a straw flow system for fattening pigs: housing and manure storage. Livestock Science 112, 199207.CrossRefGoogle Scholar
Bhatta, R., Enishi, O., Takusari, N., Higuchi, K., Nonaka, I. & Kurihara, M. (2008). Diet effects on methane production by goats and a comparison between measurement methodologies. Journal of Agricultural Science, Cambridge 146, 705715.Google Scholar
Canh, T. T., Aarnink, A. J. A., Schutte, J. B., Sutton, A., Langhout, D. J. & Verstegen, M. W. A. (1998). Dietary protein affects nitrogen excretion and ammonia emission from slurry of growing-finishing pigs. Livestock Production Science 56, 181191.Google Scholar
Delaune, P. B., Moore, P. A., Daniel, T. C. & Lemunyon, J. L. (2004). Effect of chemical and microbial amendments on ammonia volatilization from composting poultry litter. Journal of Environmental Quality 33, 728734.Google Scholar
Eghball, B., Power, J. F., Gilley, J. E. & Doran, J. W. (1997). Nutrient, carbon, and mass loss during composting of beef cattle feedlot manure. Journal of Environmental Quality 26, 189193.Google Scholar
Fangueiro, D., Cabral, F., Vasconcelos, E., Ribeiro, H. & Coutinho, J. (2009). Effect of pig slurry treatment by acidification followed by solid-liquid separation on nitrogen mineralization after application to soil. In Proceedings of the 16th Nitrogen Workshop, Turin, Italy, 28 June–1 July 2009 (Eds Grignani, C., Acutis, M., Zavattaro, L., Bechini, L., Bertora, C., Marino Gallina, P. & Sacco, D.), pp. 357358. Turin, Italy: University of Turin.Google Scholar
Hansen, M. N., Henriksen, K. & Sommer, S. G. (2006). Observations of production and emission of greenhouse gases and ammonia during storage of solids separated from pig slurry: effects of covering. Atmospheric Environment 40, 41724181.CrossRefGoogle Scholar
Kai, P., Pedersen, P., Jensen, J. E., Hansen, M. N. & Sommer, S. G. (2008). A whole-farm assessment of the efficacy of slurry acidification in reducing ammonia emissions. European Journal of Agronomy 28, 148154.Google Scholar
Kovar, J. L. (2003). Methods of determination of P, K, Ca, Mg and trace elements. In Recommended Methods of Manure Analysis (Eds Peter, J., Combs, S., Hoskins, B., Jarman, J., Kovar, J., Watson, M., Wolf, A. & Wolf, N.), pp. 3947. Madison, WI: University of Wisconsin-Extension.Google Scholar
Le, P. D., Aarnink, A. J. A. & Jongbloed, A. W. (2009). Odour and ammonia emission from pig manure as affected by dietary crude protein level. Livestock Science 121, 267274.Google Scholar
Martins, O. & Dewes, T. (1992). Loss of nitrogenous compounds during composting of animal wastes. Bioresource Technology 42, 103111.Google Scholar
Oenema, O., Bannink, A., Sommer, S. G. & Velthof, G. L. (2001). Gaseous nitrogen emissions from livestock farming systems. In Nitrogen in the Environment: Sources, Problems and Management (Eds Follett, R. F. & Hatfield, J. L.), pp. 255289. Amsterdam: Elsevier Science.CrossRefGoogle Scholar
Petersen, J. & Sorensen, P. (2008). Loss of nitrogen and carbon during storage of the fibrous fraction of separated pig slurry and influence on nitrogen availability. Journal of Agricultural Science, Cambridge 146, 403413.Google Scholar
Petersen, S. O., Lind, A.-M. & Sommer, S. G. (1998). Nitrogen and organic matter losses during storage of cattle and pig manure. Journal of Agricultural Science, Cambridge 130, 6979.Google Scholar
Portejoie, S., Martinez, J., Guiziou, F. & Coste, C. M. (2003). Effect of covering pig slurry stores on the ammonia emission processes. Bioresource Technology 87, 199207.Google Scholar
Portejoie, S., Dourmad, J. Y., Martinez, J. & Lebreton, Y. (2004). Effect of lowering dietary crude protein on nitrogen excretion, manure composition and ammonia emission from fattening pigs. Livestock Production Science 91, 4555.CrossRefGoogle Scholar
SAS Institute (1988). SAS/STAT User's guide, Release 6.03 Edition. Cary, NC: SAS Institute Inc.Google Scholar
Schulte, E. E. & Hopkins, B. G. (1996). Estimation of organic matter by weight loss-on-ignition. In Soil Organic Matter: Analyses and Interpretation (Ed. Magdoff, F. R., Tabatabai, M. A. & Hanlon, E. A.), pp. 2131. SSSA Special Publication 46. Madison, WI: SSSA.Google Scholar
Sommer, S. G. (1997). Ammonia volatilization from farm tanks containing anaerobically digested animal slurry. Atmospheric Environment 31, 863868.Google Scholar
Sommer, S. G. (2001). Effect of composting on nutrient loss and nitrogen availability of cattle deep litter. European Journal of Agronomy 14, 123133.Google Scholar
Sommer, S. G. & Dahl, P. (1999). Nutrient and carbon balance during the composting of deep litter. Journal of Agricultural Engineering Research 74, 145153.Google Scholar
Sommer, S. G., Petersen, S. O. & Sogaard, H. T. (2000). Greenhouse gas emission from stored livestock slurry. Journal of Environmental Quality 29, 744751.Google Scholar
Sommer, S. G., Jensen, L. S., Clausen, S. B. & Sogaard, H. T. (2006). Ammonia volatilization from surface-applied livestock slurry as affected by slurry composition and slurry infiltration depth. Journal of Agricultural Science, Cambridge 144, 229235.Google Scholar
Sommer, S. G., Petersen, S. O., Sørensen, P., Poulsen, H. D. & Møller, H. B. (2007). Greenhouse gas emission and nitrogen turnover in stored liquid manure. Nutrient Cycling in Agroecosystems 78, 2736.Google Scholar
Sorensen, P. & Fernandez, J. A. (2003). Dietary effects on the composition of pig slurry and on the plant utilization of pig slurry nitrogen. Journal of Agricultural Science, Cambridge 140, 343355.Google Scholar
Thomsen, I. K. (2000). C and N transformations in N-15 cross-labelled solid ruminant manure during anaerobic and aerobic storage. Bioresource Technology 72, 267274.Google Scholar
Van Der Stelt, B., Temminghoff, E. J. M., Van Vliet, P. C. J. & Van Riemsdijk, W. H. (2007). Volatilization of ammonia from manure as affected by manure additives, temperature and mixing. Bioresource Technology 98, 34493455.Google Scholar
Vu, T. K. V., Tran, M. T. & Dang, T. T. S. (2007). A survey of manure management on pig farms in Northern Vietnam. Livestock Science 112, 288297.Google Scholar
Vu, T. K. V., Prapaspongsa, T., Poulsen, H. D. & Jorgensen, H. (2009). Prediction of manure nitrogen and carbon output from grower-finisher pigs. Animal Feed Science and Technology 151, 97110.CrossRefGoogle Scholar