3 research outputs found
Application of hydrolytic enzymes for improving biogas feedstock fluidity
The composition of feedstock for biogas plants has changed during recent years. There has been an increase in the share of energy crops and residue from agriculture. As a consequence the contents of digesters are less fluid and hence, the effort for mixing has increased. Applying enzymes seems to be a promising way of improving fluidity. In this study the effects of enzyme application were investigated for a set of materials – grass silage, feed residue, maize silage, and rough-ground rye as feedstock for anaerobic digestion. After enzyme application these materials were mixed with cattle slurry and the probable effect was assessed with three different apparatus – fluidmeter, rotation rheometer, and torquemeter. The instruments proved applicable, in general, whereas grass silage could only be measured with the torquemeter. Fluidity of untreated material increased in the following row: grass silag
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Nitrous oxide emissions from winter oilseed rape cultivation
Winter oilseed rape (Brassica napus L., WOSR) is the major oil crop cultivated in Europe. Rapeseed oil is predominantly used for production of biodiesel. The framework of the European Renewable Energy Directive requires that use of biofuels achieves GHG savings of at least 50% compared to use of fossil fuel starting in 2018. However, N2O field emissions are estimated using emission factors that are not specific for the crop and associated with strong uncertainty. N2O field emissions are controlled by N fertilization and dominate the GHG balance of WOSR cropping due to the high global warming potential of N2O. Thus, field experiments were conducted to increase the data basis and subsequently derive a new WOSR-specific emission factor. N2O emissions and crop yields were monitored for three years over a range of N fertilization intensities at five study sites representative of German WOSR production. N2O fluxes exhibited the typical high spatial and temporal variability in dependence on soil texture, weather and nitrogen availability. The annual N2O emissions ranged between 0.24 kg and 5.48 kg N2O-N ha−1 a−1. N fertilization increased N2O emissions, particularly with the highest N treatment (240 kg N ha−1). Oil yield increased up to a fertilizer amount of 120 kg N ha−1, higher N-doses increased grain yield but decreased oil concentrations in the seeds. Consequently oil yield remained constant at higher N fertilization. Since, yield-related emission also increased exponentially with N surpluses, there is potential for reduction of the N fertilizer rate, which offers perspectives for the mitigation of GHG emissions. Our measurements double the published data basis of annual N2O flux measurements in WOSR. Based on this extended dataset we modeled the relationship between N2O emissions and fertilizer N input using an exponential model. The corresponding new N2O emission factor was 0.6% of applied fertilizer N for a common N fertilizer amount under best management practice in WOSR production (200 kg N ha−1 a−1). This factor is substantially lower than the linear IPCC Tier 1 factor (EF1) of 1.0% and other models that have been proposed. © 201