Uwe A. Schneider
University of Hamburg
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Featured researches published by Uwe A. Schneider.
Philosophical Transactions of the Royal Society B | 2008
Pete Smith; Daniel Martino; Zucong Cai; Daniel Gwary; H. Henry Janzen; Pushpam Kumar; Bruce A. McCarl; Stephen M. Ogle; Frank P. O'Mara; Charles W. Rice; Bob Scholes; Oleg Sirotenko; Mark Howden; Tim A. McAllister; Genxing Pan; Vladimir Romanenkov; Uwe A. Schneider; Sirintornthep Towprayoon; Martin Wattenbach; Jo Smith
Agricultural lands occupy 37% of the earths land surface. Agriculture accounts for 52 and 84% of global anthropogenic methane and nitrous oxide emissions. Agricultural soils may also act as a sink or source for CO2, but the net flux is small. Many agricultural practices can potentially mitigate greenhouse gas (GHG) emissions, the most prominent of which are improved cropland and grazing land management and restoration of degraded lands and cultivated organic soils. Lower, but still significant mitigation potential is provided by water and rice management, set-aside, land use change and agroforestry, livestock management and manure management. The global technical mitigation potential from agriculture (excluding fossil fuel offsets from biomass) by 2030, considering all gases, is estimated to be approximately 5500–6000 Mt CO2-eq. yr−1, with economic potentials of approximately 1500–1600, 2500–2700 and 4000–4300 Mt CO2-eq. yr−1 at carbon prices of up to 20, up to 50 and up to 100 US
Comparative Biochemistry and Physiology C-toxicology & Pharmacology | 2002
Paul R. Paquin; Joseph W. Gorsuch; Simon C. Apte; Graeme E. Batley; Karl C. Bowles; Peter G. C. Campbell; Charles G. Delos; Dominic M. Di Toro; Robert L. Dwyer; Fernando Galvez; Robert W. Gensemer; Gregory G. Goss; Christer Hogstrand; Colin R. Janssen; James C. McGeer; Rami B. Naddy; Richard C. Playle; Robert C. Santore; Uwe A. Schneider; William A. Stubblefield; Chris M. Wood; Kuen Benjamin Wu
t CO2-eq.−1, respectively. In addition, GHG emissions could be reduced by substitution of fossil fuels for energy production by agricultural feedstocks (e.g. crop residues, dung and dedicated energy crops). The economic mitigation potential of biomass energy from agriculture is estimated to be 640, 2240 and 16 000 Mt CO2-eq. yr−1 at 0–20, 0–50 and 0–100 US
Environmental and Resource Economics | 2003
Uwe A. Schneider; Bruce A. McCarl
t CO2-eq.−1, respectively.
Agricultural and Resource Economics Review | 2005
Uwe A. Schneider; Bruce A. McCarl
During recent years, the biotic ligand model (BLM) has been proposed as a tool to evaluate quantitatively the manner in which water chemistry affects the speciation and biological availability of metals in aquatic systems. This is an important consideration because it is the bioavailability and bioreactivity of metals that control their potential to cause adverse effects. The BLM approach has gained widespread interest amongst the scientific, regulated and regulatory communities because of its potential for use in developing water quality criteria (WQC) and in performing aquatic risk assessments for metals. Specifically, the BLM does this in a way that considers the important influences of site-specific water quality. This journal issue includes papers that describe recent advances with regard to the development of the BLM approach. Here, the current status of the BLM development effort is described in the context of the longer-term history of advances in the understanding of metal interactions in the environment upon which the BLM is based. Early developments in the aquatic chemistry of metals, the physiology of aquatic organisms and aquatic toxicology are reviewed first, and the degree to which each of these disciplines influenced the development of water quality regulations is discussed. The early scientific advances that took place in each of these fields were not well coordinated, making it difficult for regulatory authorities to take full advantage of the potential utility of what had been learned. However, this has now changed, with the BLM serving as a useful interface amongst these scientific disciplines, and within the regulatory arena as well. The more recent events that have led to the present situation are reviewed, and consideration is given to some of the future needs and developments related to the BLM that are envisioned. The research results that are described in the papers found in this journal issue represent a distinct milestone in the ongoing evolution of the BLM approach and, more generally, of approaches to performing ecological assessments for metals in aquatic systems. These papers also establish a benchmark to which future scientific and regulatory developments can be compared. Finally, they demonstrate the importance and usefulness of the concept of bioavailability and of evaluative tools such as the BLM.
Water Resources Research | 2010
Timm Sauer; Petr Havlik; Uwe A. Schneider; Erwin Schmid; Georg Kindermann; Michael Obersteiner
Use of biofuels diminishes fossil fuelcombustion thereby also reducing net greenhousegas emissions. However, subsidies are neededto make agricultural biofuel productioneconomically feasible. To explore the economicpotential of biofuels in a greenhouse gasmitigation market, we incorporate data onproduction and biofuel processing for thedesignated energy crops switchgrass, hybridpoplar, and willow in an U.S. AgriculturalSector Model along with data on traditionalcrop-livestock production and processing, andafforestation of cropland. Net emissioncoefficients on all included agriculturalpractices are estimated through crop growthsimulation models or taken from the literature. Potential emission mitigation policies ormarkets are simulated via hypothetical carbonprices. At each carbon price level, theAgricultural Sector Model computes the newmarket equilibrium, revealing agriculturalcommodity prices, regionally specificproduction, input use, and welfare levels,environmental impacts, and adoption ofalternative management practices such asbiofuel production. Results indicate no rolefor biofuels below carbon prices of
Biodiversity and Conservation | 2011
Kerstin Jantke; Christine Schleupner; Uwe A. Schneider
40 perton of carbon equivalent. At these incentivelevels, emission reductions via reduced soiltillage and afforestation are more costefficient. For carbon prices above
Environmental Science & Technology | 1995
Uwe A. Schneider; Merrilu M. Brown; Reneee A. Logan; Lorna C. Millar; Nigel J. Bunce
70,biofuels dominate all other agriculturalmitigation strategies.
International Journal of Agricultural Sustainability | 2009
Nikolinka G. Koleva; Uwe A. Schneider
Policies to mitigate greenhouse gas emissions are likely to increase energy prices. Higher energy prices raise farmer costs for diesel and other fuels, irrigation water, farm chemicals, and grain drying. Simultaneously, renewable energy options become more attractive to agricultural producers. We consider both of these impacts, estimating the economic and environmental consequences of higher energy prices on U.S. agriculture. To do this we employ a price-endogenous agricultural sector model and solve that model for a range of carbon-tax-based energy price changes. Our results show mostly positive impacts on net farm income in the intermediate run. Through market price adjustments, fossil fuel costs are largely passed on to consumers. Additional farm revenue arises from the production of biofuels when carbon taxes reach
Environmental Science and Pollution Research | 2014
Graham Merrington; Youn-Joo An; Eric P. M. Grist; Seung-Woo Jeong; Chuthamat Rattikansukha; Susan Roe; Uwe A. Schneider; Suthipong Sthiannopkao; Glenn W. Suter; Rick A. van Dam; Patrick Van Sprang; Ju-Ying Wang; Michael Warne; Paul T. Yillia; Xiaowei Zhang; Kenneth M.Y. Leung
30 per ton of carbon or more. Positive environmental benefits include not only greenhouse gas emission offsets but also reduced levels of nitrogen leaching.
Scandinavian Journal of Forest Research | 2013
Pekka Lauri; Maarit Kallio; Uwe A. Schneider
Fertile land and freshwater constitute two of the most fundamental resources for food production. These resources are affected by environmental, political, economic, and technical developments. Regional impacts may transmit to the world through increased trade. With a global forest and agricultural model, we quantify the impacts of increased demand for food due to population growth and economic development on potential land and water use until 2030. In particular, we investigate producer adaptation regarding crop and irrigation choice, agricultural market adjustments, and changes in the values of land and water. In the context of resource sustainability and food security, this study accounts for the spatial and operational heterogeneity of irrigation management to globally assess agricultural land and water use. Agricultural responses to population and economic growth include considerable increases in irrigated area and water use but reductions in the average water intensity. Different irrigation systems are preferred under different exogenous biophysical and socioeconomic conditions. Negligence of these adaptations would bias the burden of development on land and water scarcity. Without technical progress, substantial price adjustments for land, water, and food would be required to equilibrate supply and demand.