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WG II: Land use change and management effects on soil C stocks
639 WG II: Land use change and management effects on soil C stocks Status report Lars Vesterdal, Christopher Poeplau, Axel Don, Jens Leifeld, Bas van Wesemael (WG2) Cost 639 MC meeting University of Limerick May 25, 2010
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Data needs for reporting?
Too few data per country? Use IPCC default factors? Recent efforts to review and summarize effects of land-use change and management, partly based on meta analyses of GLOBAL data: e.g. Post & Kwon, 2000; Guo & Gifford 2002; Paul et al., 2002; Johnson & Curtis, 2001; Jandl et al., 2007 LUC and MC effects remain to be quantified Need for summary of EU-specific knowledge on LUC and management change – tier 1 methodology for Europe? -but in which form?
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Environmental Management 33: 507-518 (2004)
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Carbon response functions as a tool?
Example: afforestation of arable land Mathematical function describing the response of a system The response changes with time West et al. 2004
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Pros and cons of carbon response functions
WGIV meeting 2008 Represents temporal C dynamics better than IPCC factors May not be the best solution in terms of transparency A solution in terms of economy when used as an alternative to reporting based on systematic inventories. Large variability in soils: systematic sampling may be preferable CRFs may be a relevant alternative for a country with little variability in site conditions. CRFs may also support reporting in cases where net emissions are around zero (i.e. go for cheap solution).
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Pros of carbon response functions in Cost 639
Such functions will be valuable as 1) a synthesis tool 2) for management and planning guidelines 3) reporting of soil C change.
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Time line of past activities
April 2007: Meeting in Vienna Spring 2007: Questionnaire on LUC and MC interests/data October 2007: Carbon Response Functions as a tool Feb. 2008: Workshop Udine: Meta-database framework established June 2008: Presentation at WGIV workshop for discussion relevance of CRFs August 27, 2008: EuroSoil 2008 Vienna, workshop 9. Greenhouse gas budget of soils –hotspots of emission.
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Time line of past activities
April 2007: Meeting in Vienna Spring 2007: Questionnaire on LUC and MC interests/data October 2007: Carbon Response Functions as a tool Feb. 2008: Workshop Udine: Meta-database framework established June 2008: Presentation at WGIV workshop for discussion relevance of CRFs August 27, 2008: EuroSoil 2008 Vienna, workshop 9. Greenhouse gas budget of soils –hotspots of emission. Nov. 2009: Expert meeting Copenhagen to set the scene for work in GHG-Europe/Cost639 February 2010: STSM/Expert meeting in Zürich for hard work May 2010: WG2 meeting as side event at EGU for discussion of next steps. Poster with first results
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Focus on LUC European Environmental Agency (2005)
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The Dataset Quality Criteria:
0<MAT<18, (temperate climate zone – defined by IPCC) Chronosequence, paired plot, mono-site design First hand data At least roughly known land use history, soil information Sampling by depth increments, not by horizons
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The Dataset Author, Year, Journal Country, Location
MAT, MAP, Elevation, Soil type, Sand/Silt/Clay % Sampling depth LU1: type, age – LU2: type, age Correction y/n C (unit) Bulk density Number of replicates (n) SD/SE Comment (important details, e. g. forest floor y/n…)
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The Dataset n=101, n(europe)=33
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The Dataset n(data points) = 869
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The Dataset Options for CRFs: Cropland to grassland and vice versa
Cropland to forest and vice versa Grassland to forest (Accumulation of forest floor)
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Data corrections The studies differ widely in quality! Major problems:
Missing bulk density information to calculate stock [t/ha] from concentration [%] PTF When comparing stocks, the same soil mass has to be compared Mass Correction
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Significance? Carbon Response Functions Explaining factors: Age
Soil Texture MAT MAP Sampling Depth Significance?
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Carbon Response Functions
Grassland to Cropland MAT MAP Wet (>900 mm) Intermediate ( mm) Dry (<600mm) Mean Warm (>10° C) Intermediate (7-10° C) Cold (<7° C) Mean
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Carbon Response Functions
Cropland to grassland Soils Depth 0-20 cm 0~35 cm 0-70 cm Subsoil (20 cm – bottom)
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Carbon Response Functions
Forest to Cropland Cropland to Forest MAT Soils Warm (>10° C) Intermediate (7-10° C) Cold (<7° C) Mean Sandy soils Loamy soils Clay soils Mean
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Carbon Response Functions
Grassland to Forest
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Mean sampling depth: ~30 (±4.7) cm, time: 100 years
Preliminary Conclusions +25 t/ha (+68 t/ha) +50% (+130%) +5% (+40%) +4 t/ha (+27 t/ha) -45% -66 t/ha +59 t/ha +120% -54 t/ha -36% Mean sampling depth: ~30 (±4.7) cm, time: 100 years
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Preliminary Conclusions
„Slow in, fast out!“ Site characteristics influence the change rate: sand > loam > clay warm > cold wet > dry topsoil > subsoil
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Next steps – validation on Belgian LUC data
Land use history Years Source: Van Wesemael (2009)
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Next steps Validation of CRFs using Belgian regional datasets on LUC (Bas van Wesemael) Writing journal publication (1 or 2) for GCB Contributing to book - Chapter 2 on LUC and GHG dynamics
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