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Mitteilungen der Gesellschaft für Pflanzenbauwissenschaften Band 23

Mitteilungen der Gesellschaft für Pflanzenbauwissenschaften Band 23

Mitteilungen der Gesellschaft für Pflanzenbauwissenschaften Band 23

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Mitt. Ges. Pflanzenbauwiss. <strong>23</strong>: 43–44 (2011)<br />

Processes and drivers of N2O emissions from soils<br />

after application of organic fertilizers such as biogas residues<br />

Mehmet Senbayram 1,2 , Jan Reent Köster 1 , Karl H. Mühling 1 and Klaus Dittert 1,3<br />

1 Institute of Plant Nutrition and Soil Science, Christian-Albrechts-University Kiel; 2 Present address:<br />

Hanninghof Research Center, Yara GmbH & Co. KG, Dülmen; 3 Present address: Plant Nutrition and<br />

Crop Physiology, Department of Crop Sciences, University of Göttingen. E-Mail:<br />

khmuehling@plantnutrition.uni-kiel.de<br />

Introduction<br />

Greenhouse gas (GHG) emissions during agricultural production of energy crops are<br />

a serious constraint to one of the central aims of bioenergy production: reducing CO2<br />

emissions by reducing fossil fuel consumption. The biogas fermentation process<br />

produces substantial amounts of fermentation effluents, also called biogas residues<br />

(BGR), that may serve as nutrient source for agricultural production but that are also<br />

a new source of GHG emissions. Therefore the present study aimed at evaluating<br />

favorable biogas crops (maize, wheat and grassland) in two agro-ecological regions<br />

of Northern Germany for their productivity and their environmental impact. We<br />

focused on nitrous oxide, carbon dioxide, and methane fluxes from soil with various<br />

rates and types of nitrogen fertilizers. The objectives of our study were i) obtaining<br />

year-round trace gas flux data of biogas crops, and ii) evaluating effects after<br />

application of biogas residues as manure in comparison to other organic and mineral<br />

fertilizers. Attribution of nitrous oxide (N2O) emission to organic and inorganic N<br />

fertilizers requires un<strong>der</strong>standing of how these inputs affect the two biological N2O<br />

generating processes, i.e. denitrification and nitrification. Therefore, we setup three<br />

additional pot trials in or<strong>der</strong> to study these relationships.<br />

Materials and Methods<br />

A two-year field experiment was conducted at two sites with different soil type and<br />

soil fertility but similar temperate maritime climate (ø 684 mm, 9.0°C). Site one was<br />

characterized by its Luvisol soil with sandy loam texture and the soil type at the<br />

second site was a gleyic Podzol <strong>der</strong>ived from glacio-fluvial deposits of the last<br />

glaciation with a texture being dominated by sand. As silage maize is currently the<br />

standard crop grown for biogas fermentation purposes, we compared silage maize to<br />

alternative bioenergy-crops. Thus at site one, we evaluated trace gas fluxes from<br />

silage maize and wheat (whole crop) - Italian ryegrass (catch crop) rotation that was<br />

grown in parallel plots (12 x 12 m) with both main crops in both years. At site two,<br />

maize monoculture was compared to a four-cut silage grass system. We evaluated<br />

three levels of nitrogen fertilizer rates (0, 120, 360 kg N ha -1 for maize and wheat; 0,<br />

160, 480 kg N ha -1 for grassland), with the highest level - chosen for modeling purposes<br />

- being clearly beyond recommended rates. Three forms of fertilizers/manures<br />

were given: calcium ammonium nitrate, cattle / pig slurry, biogas residue. Fertilizers<br />

were applied in 2 to 4 split dressings. In the pot experiments, we compared mineral N<br />

(ammonium sulfate) and biogas residues for their effects on N2O fluxes using either<br />

stable isotope labeling or N2O isotopomer measurements for differentiation of nitrification<br />

and denitrification-<strong>der</strong>ived N2O emission. In another experiment we tested the<br />

effect of more than 40 years of organic fertilizer application on the denitrification<br />

potential of soils and the denitrification product stoichiometry (N2O / N2 ratio) by using<br />

an anoxic incubation system.

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