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P. Crill, P. Martikainen, H. Nykänen, J. Silvola (1994)
Temperature and N fertilization effects on methane oxidation in a drained peatland soilSoil Biology & Biochemistry, 26
J. Melin, H. Nōmmik (1983)
Denitrification Measurements in Intact Soil CoresActa Agriculturae Scandinavica, 33
C. Christianson, C. Cho (1983)
Chemical denitrification of nitrite in frozen soilsSoil Science Society of America Journal, 47
Hannu Nykanen, J. Alm, K. Lång, J. Silvola, P. Martikainen (1995)
Emissions of CH4, N20 and CO2 from a virgin fen and a fen drained for grassland in FinlandJournal of Biogeography, 22
S. Christensen, B. Christensen (1991)
Organic matter available for denitrification in different soil fractions: effect of freeze/thaw cycles and straw disposalEuropean Journal of Soil Science, 42
T. Parkin, A. Sexstone, J. Tiedje (1985)
Adaptation of Denitrifying Populations to Low Soil pHApplied and Environmental Microbiology, 49
R. Terry, R. Tate, J. Duxbury (1981)
Nitrous Oxide Emissions from Drained, Cultivated Organic Soils of South FloridaJournal of the Air Pollution Control Association, 31
A. Mosier, D. Schimel, D. Valentine, K. Bronson, W. Parton (1991)
Methane and nitrous oxide fluxes in native, fertilized and cultivated grasslandsNature, 350
(1996)
C - und N - Stoffflüsse auf Torfstichsimulationsfla ̈ chen im Donaumoos
J. Bandibas, A. Vermoesen, C. Groot, O. Cleemput (1994)
THE EFFECT OF DIFFERENT MOISTURE REGIMES AND SOIL CHARACTERISTICS ON NITROUS OXIDE EMISSION AND CONSUMPTION BY DIFFERENT SOILSSoil Science, 158
T. Granli, O. Boeckman (1994)
Nitrous oxide from agriculture
J. Duxbury, D. Bouldin, R. Terry, R. Tate (1982)
Emissions of nitrous oxide from soilsNature, 298
H. Flessa, P. Dörsch, F. Beese (1995)
Seasonal variation of N2O and CH4 fluxes in differently managed arable soils in southern GermanyJournal of Geophysical Research, 100
(1986)
Effect of acidity on denitrification
(1995)
Climate Change 1995. IPCC Second Assessment. A Report of the Intergovernmental Panel on Climate Change. World Meteorological Organisation and the United Nations Environment Program
H. Flessa, F. Beese (1995)
Effects of Sugarbeet Residues on Soil Redox Potential and Nitrous Oxide EmissionSoil Science Society of America Journal, 59
N. Loftfield, H. Flessa, J. Augustin, F. Beese (1997)
Automated Gas Chromatographic System for Rapid Analysis of the Atmospheric Trace Gases Methane, Carbon Dioxide, and Nitrous OxideJournal of Environmental Quality, 26
D. Burton, E. Beauchamp (1994)
Profile nitrous oxide and carbon dioxide concentrations in a soil subject to freezingSoil Science Society of America Journal, 58
S. Christensen, J. Tiedje (1990)
Brief and vigorous N2O production by soil at spring thawEuropean Journal of Soil Science, 41
Ying Chen, S. Tessier, A. Mackenzie, M. Laverdière (1995)
Nitrous oxide emission from an agricultural soil subjected to different freeze-thaw cyclesAgriculture, Ecosystems & Environment, 55
W. Koskinen, D. Keeney (1982)
Effect of pH on the rate of gaseous products of denitrification in a silt loam soilSoil Science Society of America Journal, 46
R. Striegl (1993)
Diffusional limits to the consumption of atmospheric methane by soilsChemosphere, 26
(1993)
Methane flux from boreal peatlands.Suo
B. Hütsch, C. Webster, D. Powlson (1993)
Long-term effects of nitrogen fertilization on methane oxidation in soil of the broadbalk wheat experimentSoil Biology & Biochemistry, 25
R. Raison, M. Connell, P. Khanna (1987)
Methodology for studying fluxes of soil mineral-N in situSoil Biology & Biochemistry, 19
Trace gas fluxes of N2O and CH4 were measured weekly over 12 months on cultivated peaty soils in southern Germany using a closed chamber technique. The aim was to quantify the effects of management intensity and of soil and climatic factors on the seasonal variation and the total annual exchange rates of these gases between the soil and the atmosphere. The four experimental sites had been drained for many decades and used as meadows (fertilized and unfertilized) and arable land (fertilized and unfertilized), respectively. Total annual N2O‐N losses amounted to 4.2, 15.6, 19.8 and 56.4 kg ha–1 year–1 for the fertilized meadow, the fertilized field, the unfertilized meadow and the unfertilized field, respectively. Emission of N2O occurred mainly in the winter when the groundwater level was high. At all sites maximum emission rates were induced by frost. The largest annual N2O emission by far occurred from the unfertilized field where the soil pH was low (4.0). At this site 71% of the seasonal variation of N2O emission rates could be explained by changes in the groundwater level and soil nitrate content. A significant relationship between N2O emission rates and these factors was also obtained for the other sites, which had a soil pH between 5.1 and 5.8, though the relation was weak (R2 = 15–27%). All sites were net sinks for atmospheric methane. Up to 78% of the seasonal variation in CH4 flux rates could be explained by changes in the groundwater level. The total annual CH4‐C uptake was significantly affected by agricultural land use with greater CH4 consumption occurring on the meadows (1043 and 833 g ha–1) and less on the cultivated fields (209 and 213 g ha–1).
European Journal of Soil Science – Wiley
Published: Jun 1, 1998
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