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Nitrogen dynamics of cattle dung and urine patches on intensively managed boreal pasture

Published online by Cambridge University Press:  27 April 2009

K. SAARIJÄRVI  and
P. VIRKAJÄRVI
K. SAARIJÄRVI*
Affiliation:
MTT Agrifood Research Finland, Halolantie 31 A, 71750Maaninka, Finland
P. VIRKAJÄRVI
Affiliation:
MTT Agrifood Research Finland, Halolantie 31 A, 71750Maaninka, Finland
*
*To whom all correspondence should be addressed. Email: [email protected]
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Summary

The aim of the present study was to investigate the nitrogen (N) dynamics in soil and N utilization by grass in dung pats and urine patches, and to quantify the amount of soluble organic N (SON) in grassland soil. The experiment was conducted in 2003/04 at MTT Agrifood Research, Maaninka, Finland. The study consisted of three treatments: dung pats, urine patches and a control patch without excreta. The soil (to a depth of 0·6 m) and herbage were sampled on 10 occasions over the course of 1 year. TN and SON in soil averaged 14 400 and 60 kg/ha N, respectively. Changes in soil mineral N were short-lived and a large proportion of excreta N was immobilized. The grass took up 27 kg excretal N/ha from the dung pat and 71 kg N/ha from the urine patch, which equals 0·07 and 0·19 of the excretal N given to each treatment, respectively. As a large proportion of the excretal N is immobilized and accumulates in soil, re-evaluation of the recommendations for N fertilization of pastures older than 2 years is justified.

Type
Crops and Soils
Information
The Journal of Agricultural Science , Volume 147 , Issue 4 , August 2009 , pp. 479 - 491
Copyright
Copyright © Cambridge University Press 2009

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References

REFERENCES

Appel, T. & Mengel, K. (1993). Nitrogen fractions in sandy soils in relation to plant nitrogen uptake and organic matter incorporation. Soil Biology and Biochemistry 25, 685–691.CrossRefGoogle Scholar
Deenen, P. J. A. G. & Middelkoop, N. (1992). Effects of cattle dung and urine on nitrogen uptake and yield of perennial ryegrass. Netherlands Journal of Agricultural Science 40, 469–482.CrossRefGoogle Scholar
Dickinson, C. H., Underhay, V. S. H. & Ross, V. (1981). Effect of season, soil fauna and water content on the decomposition of cattle dung pats. New Phytologist 88, 129–141.CrossRefGoogle Scholar
Eldin, N. N. (1991). Effect of artificial salting on freezing behavior of silt soil. Journal of Cold Regions Engineering 5, 143–157.CrossRefGoogle Scholar
FAO (1998). World Reference Base for Soil Resources. World Soil Resources Reports 84. Rome: FAO.Google Scholar
Haynes, R. J. & Williams, P. H. (1993). Nutrient cycling and soil fertility in the grazed pasture ecosystem. Advances in Agronomy 49, 119–199.CrossRefGoogle Scholar
Jones, D. L., Shannon, D., Murphy, D. V. & Farrar, J. (2004). Role of dissolved organic nitrogen (DON) in soil N cycling in grassland soils. Soil Biology and Biochemistry 36, 749–756.CrossRefGoogle Scholar
Kayser, M., Müller, J. & Isselstein, J. (2007). Potassium leaching from cut grassland and urine patches. Soil Use and Management 23, 384–392.CrossRefGoogle Scholar
Killham, K. (1994). Soil Ecology. Cambridge: Cambridge University Press.CrossRefGoogle Scholar
Littell, R. C., Milliken, G. A., Stroup, W. W. & Wolfinger, R. D. (1996). SAS® System for Mixed Models. Cary, NC, USA: SAS Institute Inc.Google Scholar
Middelkoop, N. & Deenen, P. J. A. G. (1990). The local influence of cattle dung and urine and its interactions with fertilizer nitrogen on herbage dry matter production. In Proceedings of 13th General Meeting of the European Grassland Federation. Volume II Soil-Grassland-Animal Relationships (Eds Gaborcik, N., Krajovic, V. & Zimkova, M.), pp. 67–70. Banska Bustrica, Czechoslovakia: European Grassland Federation.Google Scholar
Murphy, D. V., Macdonald, A. J., Stockdale, E. A., Goulding, K. W. T., Fortune, S., Gaunt, J. L., Poulton, P. R., Wakefield, J. A., Webster, C. P. & Wilmer, W. S. (2000). Soluble organic nitrogen in agricultural soils. Biology and Fertility of Soils 30, 374–387.CrossRefGoogle Scholar
Petersen, S. O., Sommer, S. G., Aaes, O. & Søegaard, K. (1998). Ammonia losses from urine and dung of grazing cattle: effect of N intake. Atmospheric Environment 32, 295–300.CrossRefGoogle Scholar
Phillips, C. J. C., Youssef, M. Y. I. & Chiy, P. C. (1999). The effects of introducing timothy, cocksfoot and red fescue into a perennial ryegrass sward and the application of sodium fertilizer on the behaviour of male and female cattle. Applied Animal Behaviour Science 61, 215–226.CrossRefGoogle Scholar
Pietola, L., Horn, R. & Yli-Halla, M. (2004). Effects of trampling by cattle on the hydraulic and mechanical properties of soil. Soil and Tillage Research 82, 99–108.CrossRefGoogle Scholar
Ryan, M. C., Kachanoski, R. G. & Gillham, R. W. (2000). Overwinter soil nitrogen dynamics in seasonally frozen soils. Canadian Journal of Soil Science 80, 541–550.CrossRefGoogle Scholar
Saarijärvi, K., Mattila, P. & Virkajärvi, P. (2006). Ammonia volatilization from artificial dung and urine patches measured by the equilibrium concentration technique (JTI method). Atmospheric Environment 40, 5137–5145.CrossRefGoogle Scholar
Saarijärvi, K., Virkajärvi, P. & Heinonen-Tanski, H. (2007). Nitrogen leaching and herbage production on intensively managed grass and grass-clover pastures on sandy soil in Finland. European Journal of Soil Science 58, 1382–1392.CrossRefGoogle Scholar
Saarijärvi, K., Virkajärvi, P., Heinonen-Tanski, H. & Taipalinen, I. (2004). N and P leaching and microbial contamination from intensively managed pasture and cut sward on sandy soil in Finland. Agriculture, Ecosystems and Environment 104, 621–630.CrossRefGoogle Scholar
SFS 3031 (1990). Finnish Standard for Nitrogen with Peroxy-Sulphate-Oxidation Method, p. 6. Helsinki, Finland: Finnish Standards Association.Google Scholar
Shand, C. A., Williams, B. L., Dawson, L. A., Smith, S. & Young, M. E. (2002). Sheep urine affects soil solution nutrient composition and roots: differences between field and sward box soils and the effects of synthetic and natural sheep urine. Soil Biology and Biochemistry 34, 163–171.CrossRefGoogle Scholar
Tyson, K. C., Scholefield, D., Jarvis, S. C. & Stone, A. C. (1997). A comparison of animal output and nitrogen leaching losses recorded from drained fertilized grass and grass/clover pasture. Journal of Agricultural Science, Cambridge 129, 315–323.CrossRefGoogle Scholar
Viljavuuspalvelu Oy. (2000). Viljavuustutkimuksen Hyväksikäyttö Peltoviljelyssä.. Mikkeli, Finland: Viljavuuspalvelu Oy (In Finnish).Google Scholar
Vuorenmaa, J., Juntto, S. & Leinonen, L. (2001). Sadeveden Laatu ja Laskeuma Suomessa 1998. Suomen Ympäristö 468. Helsinki, Finland: Ministry of the Environment (In Finnish).Google Scholar
Wachendorf, C., Taube, F. & Wachendorf, M. (2005). Nitrogen leaching from N-15 labelled cow urine and dung applied to grassland on a sandy soil. Nutrient Cycling in Agroecosystems 73, 89–100.CrossRefGoogle Scholar
Wachendorf, C., Lampe, C., Taube, F. & Dittert, K. (2008). Nitrous oxide emissions and dynamics of soil nitrogen under 15N-labeled cow urine and dung patches on a sandy grassland soil. Journal of Plant Nutrition and Soil Science 171, 171–180.CrossRefGoogle Scholar
Williams, P. H. & Haynes, R. J. (1994). Comparison of initial wetting pattern, nutrient concentrations in soil solution and the fate of 15N-labelled urine in sheep and cattle urine patch areas of pasture soil. Plant and Soil 162, 49–59.CrossRefGoogle Scholar