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Soil C in agriculture: the big uncertainty Franco Miglietta IBIMET-CNR, Firenze, Italy
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Climate variability, extreme events increasing atmospheric greenhouse gas concentrations Forest soils Peatland Permafrost Agricultural soils Land Use & Management Terrestrial carbon storage, exchange flows and soil carbon dynamics The climate feedback +
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Uncertainty on Anthropogenic Carbon Emissions Up to 250 ppm IPCC SRES 2000; Friedlingstein et al. 2006 Vulnerability of the Carbon Cycle in the 21 st century Up to 200 ppm Uncertainty of the Biospheric-Carbon-Climate Feedback Slide courtesy of Pep Canadell, GCP
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EU25: Utilised agricultural area = 164 051 000 ha; Land under permanent crops = 11 594 000 ha; Land under cereals (excluding rice) = 51 610 000 ha; Permanent grassland = 57 124 000 ha; Arable land = 97 065 000 ha Forest area ~ 140 000 000 ha
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Ploughed out grassland. Highfield, Rothamsted, UK C-content of agricultural soils is sensitive to management
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100 years 20 years Micro's aggregates type 0mMM 0 20 40 60 80 100 120 140 160 180 200 B B A B B A g C kg –1 sand free micro’s 100 agricultural use 20 years afforestation AFN AFN Source: II° Università di Napoli, Caserta – Università di Udine Del Galdo et al. Global Change Biology (2003) Assolari et al., Soil Biology and Biochemistry (2003) +3% per year-1.3% per year
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Davidson & Jansseens, Nature Vol.440, March 2006 Giardina, C.P. & Ryan, M.G. (2000) Evidence that decomposition rates of organic carbon in mineral soil do not vary with temperature. Nature, 404, 858-861. Fang, C., Smith, P., Moncrieff, J.B. & Smith, J.U. (2005) Similar response of labile and resistant soil organic matter pools to changes in temperature. Nature, 433, 57-59. Knorr, W., Prentice, I.C., House, J.I. & Holland, E.A. (2005) Long-term sensitivity of soil carbon turnover to warming. Nature, 433, 298-301. C-content of agricultural soils sensitive to climate ?
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Reductionist’s approach Temperature sensitivity of decomposition Irrigation Ploughing Fertilization
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Relating fractions to the pools used in models
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Experimentalist’s approach Manipulation experiments: Temperature + Precipitation/Irrigation+ Elevated CO2 + Crop management = Model validation datasets Short-term: Flux changes Long-term: stock changes
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OTC Pro: Relatively easy to make Con: Unavoidable decoupling between crop/soil-atmosphere Free Air CO2 Enrichment (FACE) Pro: Realistic Con: Very-high CO2 demand, Difficult to sustain in the long-term Manipulation strategies I: (CO2)
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Automated Rain Shelters Pro: Excellent control / manipulation Con: Expensive, major infrastructure Throughfall displacement Pro: Simple installation, low cost Con: Soil shadowing Manipulation strategies II: (Water)
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Soil warming Pro: Relatively easy to make Con: Unrealistic, due to the decoupling crop/soil processess Free Air Thermal Enhancement (FATE) Pro: Very Realistic Con: High energy demand, Temp & Vpd, difficult to sustain in the long-term Monolith transplanting Pro: Very realistic, easy to make Con: Requires proper and extended networking, long-term complications, potential confounding effects Manipulation strategies III: (Temperature) Passive heating Pro: Relatively easy to make Con: Not very realistic, sometimes small effects
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CONCLUSIONS OF DOE(USA) ON FATE A plot 10 m wide with vegetation 0.5 m tall and an average wind speed of 1 m s-1. A volume of 18,000 m3 hr-1 would have to be heated. If the heat treatment was set at 4°C above ambient this would require 1,448 kWh. For a 24-hr operation, and at US$ 0.1/kWh, this would cost US$ 108,000
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Lateral-view Heaters/Blowers °C +2°C
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Top-view: surface 30cm above ground °C +2°C
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Courtesy of Wayne Polley USDA-ARS, TX
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European Soil Monolith Exchange Network
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EuroSOMNET + Monolith Exchange
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+2°C Model validation Fluxes Stock change Further manipulation (Water / CO2 / Management)
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CONCLUSION - We can’t predict climate change effects on soil C in croplands. The big uncertainty. New knowledge on thermal response of decompositoin of SOM fractions is required. - Experimental manipulations are necessary to learn more about such response. Networking should be a priority, linking observations and modelling -Detailed measurements (sensu Zimmermann et al. 2007) are also required to constrain our models. Towards standard fractions/pools protocols?
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Very large C-sequestration in agricultural soils
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