Abstract
This chapter describes computer simulation models developed for estimating greenhouse gas fluxes of different ecosystems. In general, each model is used for the simulation of specific parts of the complex systems; therefore, merging the results of various kind of models can give a better insight. In this chapter, we describe four models used for estimating biospheric fluxes of greenhouse gases in Hungary. The Biome-BGC and the DNDC models are process-based ecological models. The adapted version of Biome-BGC is capable of describing the carbon, nitrogen, and water fluxes of the Hungarian arable lands and grasslands. This model is used to estimate the net primary production (NPP) and the net biome production. DNDC is used to predict the soil fluxes of nitrous oxide and methane, and simulates the biogeochemical cycles of carbon and nitrogen occurring in agricultural soil. MOD17 is a simple lightweight model that is based on remote sensing and ancillary meteorological information, and provides gross primary production (GPP) and NPP data. The CASMOFOR model was developed to estimate how much carbon can be accumulated in afforestation projects.
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Notes
- 1.
Multi-objective optimization is the process of simultaneously optimizing two or more conflicting objectives, which means that more reference data are considered during the calibration procedure.
- 2.
Plant availabe water is the portion of the water field capacity that can be absorbed by plant.
- 3.
Field capacity is the soil water content after the soil has been saturated (all pores filled with water) and allowed to drain freely for about 24–28 h.
- 4.
Wilting point is the soil water content when plants have extracted all the water they can.
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Acknowledgments
Biome-BGC version 4.1.1 was provided by the NTSG at the University of Montana. NTSG assumes no responsibility for the proper use of Biome-BGC by others. We are very grateful to Maosheng Zhao (NTSG) for providing us the official MOD17 product, the version 5.1 model parameters, and the GMAO meteorological database. The DNDC simulations were supported by NitroEurope Integrated Project of the European Commission’s 6th R&D Framework Programme, and by GVOP AKF 3.1.1.2004–05 0358/3.0 research project. The development of CASMOFOR was supported by various Hungarian projects of the National Scientific Research Found, the Ministry of Environment and Water, the Ministry of Agriculture and Rural Development, as well as by the CarboInvent project (Multi-Source Inventory Methods For Quantifying Carbon Stocks And Stock Changes In European Forests; Contract number EVK2-CT-2002-00157), see www.joanneum.at/CarboInvent.
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Appendix
Appendix
1.1 Equations and Variables Applied in the Accounting System of CASMOFOR to Model the Carbon Cycle of Forests and Forestry
Equations of CASMOFOR describing the carbon cycle are listed below by pool, and classified in various categories. Balance equations (BE) are ones that are used to calculate new values of the carbon pools at time t. FLUX IN refers to a process, i.e. a sink, by the yield of which the carbon content of the whole forestry system increases. Similarly, FLUX OUT refers to emissions by the amount of which the carbon content of the whole forestry system decreases. The emissions can come from carbon that was fixed by the FLUX IN processes, or from carbon that was already stored in the soil before the start of the simulation. Some carbon that flows through various pools eventually goes to the long-term SINK (in the soil), and remains part of the forestry system for the entire period of the simulation. Equations that are not classified into any of the above categories are used to calculate variables in the above equations, and are noted by “other.” By the forest and forestry system, all the pools and processes of the systems diagram in Fig. 9.1 are meant.
Variables related to carbon pools (in italics) and rates of fluxes are expressed as amount of carbon (tonnes of carbon – tC), and is calculated once for each calendar year of the simulation for each species and yield class.
In the equations below, index t refers to any year of the simulation, (t-1) to the previous year, whereas index (t − x) refers to year x year(s) before the current year. Index (i) means that the variable is a vector of values from year 1 to year x (the factor used in the formula varies with age), where x depends on the process.
To check that all carbon is accounted for, i.e. all incoming fluxes equal to all outgoing fluxes + changes of the carbon content of the system (including permanent sinks), an additional equation is tested to conserve mass:
1.1.1 Aboveground Biomass
Type of equation | Equations, variables and parameters (all pools and processes in terms of tC, and calculated once for year t) |
---|---|
BE | AGWB t = AGWB t−1 + CAIC − M − TH − FC |
AGWB: Aboveground woody biomass | |
CAIC: current annual increment of aboveground woody biomass | |
M: mortality | |
TH: thinning | |
FC: final cuttings | |
Flux IN | CAIC = CAI * d * cf |
CAI: current annual increment of tree volume; m−3 | |
d: weight of oven-dry biomass/volume of fresh wood (at the stand level); tdm m−3 | |
cf: carbon fraction of oven dry wood; tC tdm−1 | |
Other | M = AGWB t−1 * (ddm + dim) |
ddm: density dependent mortality rate; species dependent; dimensionless | |
dim: density independent mortality rate; randomly generated; dimensionless | |
ddm + dim <= 0.4 | |
Other | TH = AGWB t−1 * thr |
thr: species specific, depends on age and yield class; dimensionless | |
FC = AGWB t−1 of stands of rotation age | |
(final cutting is supposed to take place at the beginning of the year, and is immediately followed by regeneration) | |
Rotation age: species specific, depends on yield class |
1.1.2 Dead Wood
Type of equation | Equations, variables and parameter (all pools and processes in terms of tC ha−1) |
---|---|
BE | DW = DW t−1 + DWI − EW |
DW: dead wood | |
DWI: deadwood increment | |
EW: decomposition of (i.e., emission from) decomposable dead wood | |
Other | DWI = [M + TH * (1 − wpTH − fpTH ) + FC * (1 − wpFC − fpFC )] * (1 − ndf) |
wpTH : wood product part of TH, dimensionless | |
fpTH : fuelwood part of TH, dimensionless | |
wpFC :wood product part of FC, dimentionless | |
fpFC: fuelwood part of FC; dimensionless | |
ndf: nondecomposable fraction; dimensionless | |
Flux OUT | EW = Sum i (DW t−i /DTw i ) for i = 1 to x |
DTw: time needed for deadwood to decompose, years | |
Flux to SINK | UWI = [M + TH * (1 − wpTH − fpTH ) + FC * (1 − wpFC − fpFC )] * ndf |
UWI: Nondecomposable dead wood fraction |
1.1.3 Living Leaves
Type of equation | Equations, variables, and parameters (all pools and processes in terms of tC ha−1) |
---|---|
BE | LL = LL t−1 + LI − DLI − DLI * ndf /(1 − ndf) |
LL: amount of (living) leaves | |
LI: increment due to tree growth | |
DLI: decomposable leaf loss due to harvest and mortality at the end of year | |
Flux IN | LI = CAIC * increment ratio |
increment ratio: leaf increment/aboveground woody biomass increment; dimensionless | |
other | DLI = [(LL t−1 + LI) * nll + (LL t−1 + LI) * (1 − nll ) * fdlleaves ] * (1 − ndf) |
nll : ratio of nonliving/living biomass = DWI/AGWB t−1 ; dimensionless | |
fdlleaves : fraction of leaves dying and falling at the end of year; species specific (broadleaves: 1; conifers: <1); dimensionless | |
Flux to SINK | ULI = DLI * ndf /(1 − ndf) |
ULI: Nondecomposable fraction; dimensionless |
1.1.4 Dead Leaves
Type of equation | Equations, variables, and parameters (all pools and processes in terms of tC ha−1) |
---|---|
BE | DL = DL t−1 + DLI − EL |
DL: dead decomposable leaves | |
DLI: amount of decomposable leaves that die in year | |
EL: decomposition of dead leaves | |
Flux OUT | EL = Sum i (DL t−i /DTL t ) for i = 1 to x |
EL: Total emission due to decomposition of leaves | |
DTL: time needed to decompose; year |
1.1.5 Living Roots (Belowground Biomass)
Type of equation | Equations, variables and parameters (all pools and processes in terms of tC ha−1) |
---|---|
BE | R = R t−1 + RI − DRI − DRI * ndf /(1 − ndf) |
R: amount of roots | |
RI: increase of root biomass | |
DRI: amount of decomposable roots that die in year | |
Flux IN | RI = CAIC * rts |
rts : root-to-shoot ratio | |
Other | DRI = [(R t−1 + RI) * nll + (LI t−1 + LRI) * (1 − nll ) * fdlroots ] * (1 − ndf) |
fdlroots : Fraction of roots of trees (relative to root increment) that dies at the end of year | |
Flux to SINK | URI = DRI * ndf /(1 − ndf) |
URI: Nondecomposable fraction; dimensionless |
1.1.6 Dead Roots
Type of equation | Equations, variables, and parameters (all pools and processes in terms of tC ha−1) |
---|---|
BE | DR = DR t−1 + DRI – ER |
ER: decomposition of (i.e., emission from) decomposable dead roots | |
Flux OUT | ER = DR t−i / DTR i |
DTR: time needed to decompose; year |
1.1.7 (Industrial) Wood Products
Type of equation | Equations, variables, and parameters (all pools and processes in terms of tC ha−1) |
---|---|
BE | WP = WP t−1 + WPI – WPU |
WP: wood products | |
WPI: wood product increment | |
WPU: wood products becoming unused | |
Other | WPI = [FC * used part * (1 − fuelwood part ) + TH * used part (t) * (1 − fuelwood part (t)] * (1 − lost part) |
used part : ratio of wood harvested that is used for wood products, dimensionless | |
fuelwoodpart : ratio of wood harvested that is used for fuelwood, dimensionless | |
lost part: ratio unused part of wood harvested, dimensionless | |
Other | WPU = WPI t−i |
Maximum of i: mean life time of wood product (species-specific); years | |
Flux OUT | EUUWP = WPU t−1 * (1 − unburnt )* WTD |
EUUWP: Emission from (decomposition of) unused and unburned wood product | |
unburnt: unburned fraction; dimensionless | |
WTD: (mean) time needed to decompose the wood products |
1.1.8 Fuelwood
Type of equation | Equations, variables, and parameters (all pools and processes in terms of tC ha−1) |
---|---|
BE | FW = FW t−1 + FWI + LWP + UWPF − EFW |
FW: fuelwood | |
FWI: fuelwood increment (from harvest) | |
LWP: loss in wood processing | |
UWPF: unused wood products becoming fuelwood | |
EFW: emission from firewood | |
Other | FWI = FC * used part * fuelwood part + TH * used part t * fuelwood part t |
Other | LWP = WPI * lost part /(1 − lost part) |
Other | UWPF = WPU t−1 * unburnt |
Flux OUT | EFW = FW t−1 * (1 − unburn) |
unburn: unburnable fraction; dimensionless | |
Flux to Sink | UFWI = FW t−1 * unburn |
UFWI: unburnable fuelwood |
1.1.9 Soil
Type of equation | Equations, variables, and parameters (all pools and processes in terms of tC ha−1) Equations, variables, and parameters (all pools and processes in terms of tC ha−1) |
---|---|
BE | S = St−1 + FS − CLO − GAL |
S: soil | |
FS: net flux to sink | |
CLO: loss of C from soil due to afforestation and regeneration operations | |
GAL: loss of C from soil due to afforesting grasslands | |
(Net flux to sink, which includes soil respiration, and loss due to afforesting grasslands are only calculated for 75 years after afforestations. After that time, net flux to sink is supposed to be zero, i.e. transfer of carbon from other compartments to soil is equal to soil respiration, and no more losses are supposed to take place due to converting grassland to forest.) | |
Other | CLO = A * asl |
A: afforestation area by tree species and yield class; ha (to be provided by the user before running of the model) | |
asl: area specific carbon loss; to be specified by the user; tC ha-1 | |
Other | GAL = A * glp * diff _CL_GL |
glp: percent of area afforested on former grassland; to be specified by the user; percent | |
diff_CL_GL: time-dependent difference of carbon stock between cropland and grassland; tC ha−1 | |
Flux to SINK | FS = ULI + URI + UWI + UFWI |
1.2 Equations and Variables Applied to Model Carbon Economics in CASMOFOR
where Total of all annual costs t is the sum of all costs, at current prices, (in either EUR or Hungarian Forints, HUF) of all forestry operation on all area of the afforestation project that are due in year t; and Total of all annual revenues t is the sum of all revenues, at current prices, of all forestry operation on all area of the afforestation project that are due in year t.
where Total net forestry costs t is the total costs from the beginning of the afforestation project, i.e. year 1, summed up to year t; and i = 1 to t.
where Total carbon in forestry system t is the total amount of carbon accumulated in the afforestation project area up to year t in all carbon pools since year 1; all other symbols as in the table above.
where Total net specific costs t is the total net forestry costs per tonne of CO2 sequestered by the afforestation system by year t.
Total net specific costs t are also calculated with only the sum of AGWB t + R t in the denominator to estimate total net specific costs of sequestering carbon in the tree biomass only.
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Somogyi, Z. et al. (2011). Models and Their Adaptation. In: Haszpra, L. (eds) Atmospheric Greenhouse Gases: The Hungarian Perspective. Springer, Dordrecht. https://doi.org/10.1007/978-90-481-9950-1_9
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