Modelling the carbon and nitrogen balances of direct land use changes from energy crops in Denmark: a consequential life cycle inventory

This paper addresses the conversion of Danish agricultural land from food/feed crops to energy crops. To this end, a life cycle inventory, which relates the input and output flows from and to the environment of 528 different crop systems, is built and described. This includes seven crops (annuals and perennials), two soil types (sandy loam and sand), two climate types (wet and dry), three initial soil carbon level (high, average, low), two time horizons for soil carbon changes (20 and 100 years), two residues management practices (removal and incorporation into soil) as well as three soil carbon turnover rate reductions in response to the absence of tillage for some perennial crops (0%, 25%, 50%). For all crop systems, nutrient balances, balances between above‐ and below‐ground residues, soil carbon changes, biogenic carbon dioxide flows, emissions of nitrogen compounds and losses of macro‐ and micronutrients are presented. The inventory results highlight Miscanthus as a promising energy crop, indicating it presents the lowest emissions of nitrogen compounds, the highest amount of carbon dioxide sequestrated from the atmosphere, a relatively high carbon turnover efficiency and allows to increase soil organic carbon. Results also show that the magnitude of these benefits depends on the harvest season, soil types and climatic conditions. Inventory results further highlight winter wheat as the only annual crop where straw removal for bioenergy may be sustainable, being the only annual crop not involving losses of soil organic carbon as a result of harvesting the straw. This, however, is conditional to manure application, and is only true on sandy soils.

[1]  E. Hansen,et al.  Tillage effects on N2O emissions as influenced by a winter cover crop , 2011 .

[2]  Timothy D. Searchinger,et al.  Biofuels and the need for additional carbon , 2010 .

[3]  E. Hansen,et al.  Nitrate leaching as influenced by soil tillage and catch crop , 1997 .

[4]  Dmitri Chatskikh,et al.  Effects of reduced tillage on net greenhouse gas fluxes from loamy sand soil under winter crops in Denmark , 2008 .

[5]  A. Lindroth,et al.  Assessment of regional willow coppice yield in Sweden on basis of water availability , 1999 .

[6]  Marie-Hélène Jeuffroy,et al.  Biomass production and nitrogen accumulation and remobilisation by Miscanthus × giganteus as influenced by nitrogen stocks in belowground organs. , 2011 .

[7]  G. Blicher-Mathiesen,et al.  Reestimation and further development in the model N-LES, N-LES 3 to N-LES 4 , 2008 .

[8]  E. Stehfest,et al.  N2O and NO emission from agricultural fields and soils under natural vegetation: summarizing available measurement data and modeling of global annual emissions , 2006, Nutrient Cycling in Agroecosystems.

[9]  Henrik Wenzel,et al.  Environmental assessment of Ronozyme® P5000 CT phytase as an alternative to inorganic phosphate supplementation to pig feed used in intensive pig production , 2007 .

[10]  R. Clift,et al.  Soil Organic Carbon Changes in the Cultivation of Energy Crops: Implications for GHG Balances and Soil Quality for Use in LCA , 2011 .

[11]  R. Betts,et al.  Changes in Atmospheric Constituents and in Radiative Forcing. Chapter 2 , 2007 .

[12]  Jørgen E. Olesen,et al.  A simplified modelling approach for quantifying tillage effects on soil carbon stocks , 2009 .

[13]  Benoit Gabrielle,et al.  Life-cycle assessment of straw use in bio-ethanol production: a case study based on biophysical modelling. , 2008 .

[14]  J. Huijsmans,et al.  Ammonia volatilization from crop residues and frozen green manure crops , 2010 .

[15]  Eric D. Larson,et al.  A review of life-cycle analysis studies on liquid biofuel systems for the transport sector , 2006 .

[16]  L. S. Jensen,et al.  Catch crops and green manures as biological tools in nitrogen management in temperate zones , 2003 .

[17]  Jeroen C. J. H. Aerts,et al.  Partial costs of global climate change adaptation for the supply of raw industrial and municipal water: a methodology and application , 2010 .

[18]  C. Mari,et al.  Biogenic nitrogen oxide emissions from soils – impact on NO x and ozone over West Africa during AMMA (African Monsoon Multidisciplinary Experiment): modelling study , 2008 .

[19]  F. M. Andersen,et al.  Coherent Energy and Environmental System Analysis , 2011 .

[20]  J. Olesen,et al.  Clay Dispersibility and Soil Friability—Testing the Soil Clay‐to‐Carbon Saturation Concept , 2012 .

[21]  Uffe Jørgensen,et al.  Nitrate leaching during establishment of willow (Salix viminalis) on two soil types and at two fertilization levels , 1998 .

[22]  H. Eckersten,et al.  Modelling radiation use, water and nitrogen in willow forest , 2006 .

[23]  J. Lammel,et al.  Spatial and temporal distribution of the root system and root nutrient content of an established Miscanthus crop , 1999 .

[24]  Uffe Jørgensen,et al.  Genotypic variation in dry matter accumulation and content of N, K and Cl in Miscanthus in Denmark. , 1997 .

[25]  Henrik Wenzel,et al.  Environmental consequences of future biogas technologies based on separated slurry. , 2011, Environmental science & technology.

[26]  Matthew J. Aylott,et al.  Greenhouse gas emissions from four bioenergy crops in England and Wales: Integrating spatial estimates of yield and soil carbon balance in life cycle analyses , 2009 .

[27]  Ulrich Dämmgen Calculations of emissions from German agriculture - national emission inventory report (NIR) 2006 for 2004 : tables , 2009 .

[28]  E. Robert,et al.  Indirect Land Use Change From Increased Biofuels Demand - Comparison of Models and Results for Marginal Biofuels Production from Different Feedstocks , 2010 .

[29]  T. Suzuki [Nitrogen oxides]. , 1971, Naika. Internal medicine.

[30]  Michael Zwicky Hauschild,et al.  Spatial differentiation in life cycle impact assessment - the EDIP-2003 methodology. Guidelines from the Danish EPA , 2004 .

[31]  P. Ambus,et al.  Emissions of nitrous oxide from arable organic and conventional cropping systems on two soil types , 2010 .

[32]  Jørgen E. Olesen,et al.  A flexible tool for simulation of soil carbon turnover , 2002 .

[33]  R. Harrison,et al.  A review of the effect of N fertilizer type on gaseous emissions , 2001 .

[34]  T. Ochsner,et al.  Tillage and soil carbon sequestration—What do we really know? , 2007 .

[35]  M. Andersen,et al.  Irrigation strategy, nitrogen application and fungicide control in winter wheat on a sandy soil. I. Yield, yield components and nitrogen uptake , 2000, The Journal of Agricultural Science.

[36]  M. Hauschild,et al.  Methodology, tools and case studies in product development , 2000 .

[37]  B. M. Petersen,et al.  Estimating soil C loss potentials from the C to N ratio , 2008 .

[38]  Bram Govaerts,et al.  Conservation Agriculture and Soil Carbon Sequestration: Between Myth and Farmer Reality , 2009 .

[39]  Keith A. Smith,et al.  N 2 O release from agro-biofuel production negates global warming reduction by replacing fossil fuels , 2007 .

[40]  Francesco Cherubini,et al.  Energy- and greenhouse gas-based LCA of biofuel and bioenergy systems: Key issues, ranges and recommendations , 2009 .

[41]  Kristian Kristensen,et al.  Winter wheat yield response to climate variability in Denmark , 2010, The Journal of Agricultural Science.

[42]  Bruno Mary,et al.  Modeling consequences of straw residues export on soil organic carbon , 2008 .

[43]  Pål Börjesson,et al.  Agricultural crop-based biofuels – resource efficiency and environmental performance including direct land use changes , 2011 .

[44]  Jane M. F. Johnson,et al.  Estimating Source Carbon from Crop Residues, Roots and Rhizodeposits Using the National Grain-Yield Database , 2006 .

[45]  Iris Lewandowski,et al.  Delayed harvest of miscanthus—influences on biomass quantity and quality and environmental impacts of energy production , 2003 .

[46]  Edwards Robert,et al.  Biofuels in the European Context , 2007 .

[47]  Root carbon input in organic and inorganic fertilizer-based systems , 2012, Plant and Soil.

[48]  B. M. Petersen,et al.  Developments in greenhouse gas emissions and net energy use in Danish agriculture - how to achieve substantial CO(2) reductions? , 2011, Environmental pollution.

[49]  S. Solomon The Physical Science Basis : Contribution of Working Group I to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change , 2007 .

[50]  Stefan Bringezu,et al.  Towards Sustainable Production and Use of Resources: Assessing Biofuels , 2009 .

[51]  Detlef P. van Vuuren,et al.  Contribution of N2O to the greenhouse gas balance of first‐generation biofuels , 2009 .

[52]  G. Robertson,et al.  Greenhouse gases in intensive agriculture: contributions of individual gases to the radiative forcing of the atmosphere , 2000, Science.

[53]  C. Mari,et al.  Biogenic nitrogen oxide emissions from soils – impact on NO x and ozone over West Africa during AMMA ( African Monsoon Multidisciplinary Experiment ) : modelling study , 2008 .

[54]  J. Olesen,et al.  Nitrate leaching from organic arable crop rotations is mostly determined by autumn field management , 2011 .

[55]  Gjalt Huppes,et al.  Environmental assessment of products , 1999 .

[56]  Bruno Mary,et al.  Nitrate leaching in intensive agriculture in Northern France: Effect of farming practices, soils and crop rotations , 2005 .

[57]  J. Porter,et al.  Soil properties, crop production and greenhouse gas emissions from organic and inorganic fertilizer-based arable cropping systems , 2010 .