UK losses of soil carbon – due to climate change? Pat Bellamy Natural Resources Department Cranfield University UK Outline • Brief overview of Carbon losses from all soils across England and Wales 1978-2003 published in Nature 2005 • Potential causes of carbon loss • Changes that have occurred in UK over the twenty years between samplings • How we are investigating what is driving the change in soil carbon • Preliminary results based on simple models • Work in progress The National Soil Inventory of England & Wales The National Soil Inventory was made to obtain an unbiased estimate of the distribution of the soils of England and Wales and of the chemistry of the topsoil (0–15 cm depth) • Whole of England & Wales sampled at each intersect of a 5 km x 5 km grid – 1979-1983. • Soil profiles described and topsoil (0-15cm) samples taken • For each sample organic carbon, pH, metal concentrations and nutrients measured. • Site properties such as land use, slope, aspect recorded. 20m 20m Sampling at each site Soil organic carbon content c.1980 Resampling of NSI • Proportion of NSI sites were re-sampled: 1994-1996 (cropland and managed grassland) 2002-2003 (forestry, moorland, extensive grazing land) • Sampling scheme designed to detect changes of organic carbon ± 2 g kg-1 Resampling of the NSI Protocols verified for: • Original surveyor • Field sampling – methods and tools • Site location • Laboratory analyses © Bellamy et al (2005) Co Ar De nife ab ci ro Ro du us B le ta ou w og t o Lo ions w od Pe w a oo rm la l gr d n Roane d hass ug nt ea h gr th gr as Up la Up azins nd la Sc g he nd rub at gr h/ as m s oo r Rate of change (g kg-1 yr-1) Results from resampling of NSI Annual change in carbon – grouped by land use 2 0 -2 -4 -6 Results from NSI across all land uses Annual change in carbon (g/kg/yr) All land uses Rate of change (g kg-1 yr-1) 2 0 -2 -4 -6 Eqn (1) -8 0 © Bellamy et al (2005) 100 200 300 400 500 Corg (g kg-1) Eqn (1): Rate of change = 0.6 - 0.0187 × Corg Changes in soil carbon 1978-2003 Annual change in carbon g/kg/yr •Carbon lost from soils at a mean rate of 0.6 gm of organic carbon per kg of soil per year. •For soils with more than 100 gm per kg carbon rate of loss greater than 2 gm per kg per year Annual changes in soil carbon stocks Organic Carbon (%) No Data 0-1 1-2 2-5 5 - 10 10 - 25 25 - 35 > 35 Estimated annual soil C loss: England & Wales ≈ 4.4 million tonnes UK ≈ 4.4 x UK / E&W C stock ≈ 13 million tonnes For comparison: UK industrial CO2 emission ≈ 140 million tonnes Reduction since 1990 ≈ 13 million tonnes Potential causes of carbon losses Land use/management Extension of agriculture - e.g. grassland and woodland conversion to cropland Intensification of land use - e.g. drainage, increased nutrient loading, pesticide use Non-agricultural land uses - e.g. afforestation on wet land, managed burning Environmental change Atmospheric - e.g. decreased acid rain, increased nitrogen deposition Climatic - e.g. temperature and precipitation 20 16 Tmax 15 rain 14 12 Tmin 10 10 5 0 8 1 2 3 4 5 6 7 8 Rainfall (cm) Temperature (oC) Mean monthly UK temp and rainfall 1978-2003 (a) Annual pattern 6 9 10 11 12 Month of year 1.5 1.0 1.0 0.5 0.0 -0.5 -1.0 -1.5 0.5 0.0 -0.5 -1.0 -1.5 0 5 10 15 20 ∆ monthly precip (cm) 1.5 ∆ monthly Tmin (oC) ∆ monthly Tmax (oC) (b) Changes since 1978 0 5 10 15 Year after 1978 20 Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec 4 2 0 -2 -4 0 5 10 15 20 Jan Changes in soil pH between NSI samplings Original pH Annual change in pH (over 12-25 yr) How do we investigate what is driving the change in soil carbon? • We do not have detailed information on many of the potential drivers of soil carbon change at the NSI sites • An alternative approach is to use simple models of soil carbon turnover to evaluate possible explanations for the observed trends based on changes in land management or environmental change including climate change • We can reject explanations for the changes that require unrealistic parameters to deliver the measured magnitudes of change Soil carbon dynamics Plant carbon Atmosphere CO2 Soil carbon immobilization mobilization Soil C accumulates if immobilization > mobilization Lost if mobilization > immobilization Leached carbon Simple carbon model Rate of change = Input – k x organic carbon (k = decomposition rate constant) • Assume Input & k changed some time before first sampling – i.e. soils are adjusting to earlier change - Input & k independent of OC, dependant on land use only • Assume change in decomposition rate, k, (proportional to organic carbon) – i.e. decomposition rate changes in response to climate change • Assume change in Input (proportional to carbon content) – i.e. Input changes in response to environmental change The model fitted to data for each land use class Simple carbon model: results 1.0 0.8 Arable 0.6 0.4 Arable and rotational grassland 0.2 0.0 -0.2 -0.4 -0.6 observed predicted -0.8 -1.0 -1.2 0 2 4 6 8 10 12 14 16 18 -1 0.6 Rate of change (kg C m y ) 0.8 -2 1.0 Permanent grass 0.4 Permanent grassland 0.2 0.0 -0.2 -0.4 -0.6 -0.8 -1.0 -1.2 0 2 4 6 8 10 12 14 16 18 1.0 0.8 Non-agricultural Non-agricultural 0.6 0.4 0.2 0.0 -0.2 -0.4 -0.6 -0.8 -1.0 -1.2 0 2 4 6 8 10 12 14 -2 Mean soil carbon content (kg C m ) 16 18 Simple carbon model: results • The model parameter estimates were assessed against known effects of land use/management change, climate change and environmental change Simple carbon model: results • Estimates of k and Input obtained for each land use • If k changed proportional to OC the large changes required suggest climate change cannot be sole driver • Large changes in Input required suggest environmental changes not a major driver Initial conclusions Results so far indicate the dominant driver of soil carbon losses was changes in land use/management, but climate change was responsible for part of the losses, and is likely to cause increased losses in future Further work in progress • More sophisticated models of carbon change are being developed which will represent the whole range of soils in England and Wales • These models are being validated using the NSI data • These will allow more precise estimation of the contribution of climate change to the change in soil carbon observed in the NSI data Acknowledgements • Funding for the National Soil Inventory of England and Wales came from Defra (Department for Environment Food and Rural Affairs UK) • I would like to thank past and present colleagues at the National Soil Resources Institute at Cranfield University including Ian Bradley, Guy Kirk, Peter Loveland, Richard Andrews, Ilkka Leinonen and Bob Jones, also Murray Lark at Rothamsted Research. Carbon losses from all soils across England and Wales 1978-2003 (2005) Pat H. Bellamy, Peter J. Loveland, R. Ian Bradley, R. Murray Lark & Guy J.D. Kirk Nature 437 pp245 - 248
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