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Outline. What are included in Biogeochemistry Models?Soil C, N, and P cycling modelsSoil carbon model descriptionSoil nitrogen cycling modelsSoil phosphorus modelsConclusions. Data Sets Used to Test and Parameterize Soil Carbon Models. Total soil carbon from long-term experimentsAgricultural e
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1. Process Oriented Biogeochemistry Models
2. Outline What are included in Biogeochemistry Models?
Soil C, N, and P cycling models
Soil carbon model description
Soil nitrogen cycling models
Soil phosphorus models
Conclusions
3. Data Sets Used to Test and Parameterize Soil Carbon Models Total soil carbon from long-term experiments
Agricultural experiments
Grassland and forest experiments
Spatial patterns in soil carbon for undisturbed ecosystems
Soil texture has more impact than climate on soil carbon levels
More carbon with clay soils
Less carbon for sandy soils
4. Data Sets Used to Test and Parameterize Soil Carbon Models C14 dating of soil fractions
Turnover of SOM fractions range from <1 year to >5000 years – 0-20 cm depth turnover =200-400 years
Labeled C14 and ?C13 addition experiments – adding of labled C14 and ?C13 plant material to the soil in the lab and field
5. Data Sets Used to Test and Parameterize Soil Carbon Models Long term laboratory incubations of the soil – CO2 loss decreases exponentially with time
Physical and chemical soil fractionation experiments – attempts to measure SOM fractions used in models and relate SOM fractions to soil fertility
6. What do these experiments indicate? Clear evidence for fractions of SOM that have different turnover times (<1 to >5000 years)
There are no robust soil fractionation techniques that measure the pools used in SOM models
Soil texture has a large impact on stabilization of carbon in the soil
Inversely proportional to sand content
Proportional to clay content
Total soil carbon levels is the best index of soil fertility and used extensively to test models
10. Model Comparisons of Soil Carbon Models Smith et al. 1997 – Geoderma 81: 152-225
Nine model comparison
Use long-term soil carbon data sets from seven experimental sites
11. Model Comparisons of Soil Carbon Models Moorhead et al. 1999 – Global Biogeochemical Cycles 13: 575-590
Four model comparison
Use litter decay data from LIDET Biomass and nitrogen data
13. Soil Carbon Model Conclusions Most models use 5 to 7 pools to describe soil carbon dynamics
Current biogeochemistry match observed soil carbon data quite well
We can not currently measure the different carbon pools used in SOM models
Extensive data exists to parameterize and test SOM models
Impact of soil texture, climate and management on total soil C
17. N Model Comparison Frolking et al. – Nutrient Cycling in Agroecosystems 52: 77-105
Four model comparison
Daycent, DNDC, ExpertN, CASA-NASA
Compare soil NO3, NH4, N-Min, T, H2O, and N2O at four sites
19. N Model Comparison Results Most models results compared well to observed data
Difficulty in simulating large N2O fluxes during winter thaw events
Annual N2O fluxes are simulated well but daily fluxes are not well simulated
Big differences in modeled Nox, NH3, and N2 gas fluxes
21. Phosphorus Model Comparisons Lewis and McGechan. 2002. – Biosystems Engineering 82: 359-380
Compared four P cycling models Daycent, ANIMO, GLEAMS, EPIC
22. Phosphorus Model Comparisons Gijsman et al. 1996. – Journal of Agronomy 88: 894-903.
23. OverallBiogeochemistry Model Conclusions There are many soil C, N, and P cycling models available for simulating Soil C, N and P dynamics and N trace gas fluxes
It is difficult to evaluate which of these models is the “best biogeochemistry model”
Model comparisons are needed where all of the important output vaiables are observed:
Inorganic and organic soil C, N, and P
N trace gas fluxes (N2O, NH3, Nox, and N)
Soil NO3, NH4, and soil NO3 leaching
24. OverallBiogeochemistry Model Conclusions Good soil water and temperature and plant production models are needed to drive soil biogeochemistry model
Key inputs soil for Biogeochemistry models:
Soil water and temperature
Plant demand for N and P uptake
Vertical and horizontal water flow
Dead plant material inputs (C, N, and P)
Fert. and atmospheric inputs of N and P
27. N Model Conclusions It is unclear which of the current N cycling models is the “BEST”
It is very difficult to evaluate N cycling submodel performance since there are many important output variables:
Soil NO3, NH4, and organic N
N gas fluxes – NH4, N2O, Nox, and N2
Soil NO3 leaching