Documentation for GCAM
The Global Change Analysis Model
View the Project on GitHub JGCRI/gcam-doc
Table 1: Inputs required by the supply module 1
Name | Resolution | Unit | Source |
---|---|---|---|
Land use and land cover | By GLU, land type, and year | thousand \(km^2\) | Land Allocator |
Historical harvested area (used to calculate historical yield) | By GLU, crop, management practice, and year | thousand \(km^2\) | Exogenous |
Historical production (used to calculate historical yield) | By GLU, crop, management practice, and year | thousand \(km^2\) | Exogenous |
Agriculture productivity growth (used to calculate future yield) | By GLU, crop, management practice, year | % per year | Exogenous |
Non-fertilizer, non-water, non-land variable cost of production | By GLU, crop, management practice, and year | 1975$/kg | Exogenous |
Fertilizer coefficients | By GLU, crop, management practice, and year | 1975$/kg | Exogenous |
Water coefficients | By GLU, crop, management practice, and year | 1975$/kg | Exogenous |
Commodity prices | By region, commodity, and year | 1975$/kg | Marketplace |
Fertilizer prices | By region, commodity, and year | 1975$/kg | Marketplace |
Water prices | By basin and year | 1975$/m3 | Marketplace |
1: Note that this table differs from the one provided on the Supply Inputs Page in that it lists all inputs to the land supply module, including information passed from other modules. Additionally, the units listed are the units GCAM requires, rather than the units the raw input data uses.
Variable costs are defined here as the non-land costs of crop production, per-unit of crop. We model the cost of fertilizer and water explicitly, including input-output coefficients and prices of each. Other components of variable cost are derived from USDA cost data.
Variable costs set hard price floors in the model: production goes to zero when price is less than or equal to the variable costs. As a result, these costs should be interpreted as pure minimum or shut-down costs. They should be just the cost of materials and hired labor for producing a crop or product with a given technology in a subregion.
Value-added categories are not included in the variable costs. In addition, variable costs do not include land costs, as the model is based on allocating land on per unit profits. They should also not include cost categories that represent return to capital or profits. We can assume these costs are captured in the distribution of profit rates behind the logit. Otherwise, consider that if these costs are put into our variable costs, ultimately all marginal profit rates (from economic theory) would be zero and provide no value to our modeling. In addition, accounting costs such as depreciation should not be part of variable costs.
Data on labor costs can be difficult to use, since some farm wage categories are income that the farmer either earns or expects to be paid and thus, some labor costs are really profit to the land-owner (i.e., farmer). Therefore, we have restricted our variable cost data to include what is labeled as “hired labor”.
Note that introducing variable costs that differ by region can result in unintended consequences. Different variable costs create different price floors, which can result in a region ceasing production of a particular product if technical change lowers the global product price significantly (i.e., to a point where the variable cost is less than the price received).
The main points can be summarized as:
Profit rate for all agricultural production technologies is calculated as:
\[profitRate = 1e9*( price + subsidy - varCost - inputCosts + secondaryValue ) * yield + impliedSubsidy\]where \(price\) is the commodity price, \(subsidy\) is any exogenously-specified subsidy, \(varCost\) is the non-land variable cost, \(inputCosts\) are the costs of inputs (e.g., fertilizer, water), \(yield\) is the yield for the technology, and \(impliedSubsidy\) is an implicit subsidy calculated in the calibration periods to ensure profits are above a specified threshold. Note that the subsidy is multiplied by \(1e9\), as the land allocator expects profit rates in 1975$/billion m2.
See calcProfitRate
in ag_production_technology.cpp.
Agricultural supply is calculated as:
\[supply = yield * land\]where \(yield\) is the yield for the technology and \(land\) is the land allocation (retrieved from the land allocation module).
See calcSupply
in ag_production_technology.cpp.
For technologies that have production in the historical period, yield for the historical period is calculated as:
\[yield = supply / land\]For all technologies, future yield is calculated as:
\[yield_{t} = yield_{t-1} * (1 + APG)^{timestep}\]where \(yield_{t}\) is the yield in time \(t\), \(APG\) is the agricultural productivity growth rate and \(timestep\) is the number of years between \(t\) and \(t-1\).
See initCalc
in ag_production_technology.cpp.
GCAM uses one of two different logit formulations to calculate the shares for each technology or subsector. For livestock, subsectors represent different production systems, where technologies represent different feed sources.
The first option, also known as the relative-cost-logit
, is:
where \(s_i\) is the share of technology or subsector \(i\), \(alpha_i\) is the share weight, \(c_i\) is the cost of technology or subsector \(i\), and \(beta\) is the logit exponent.
The second option, also known as the absolute-cost-logit
, is:
where \(s_i\) is the share of technology or subsector \(i\), \(alpha_i\) is the share weight, \(c_i\) is the cost of technology or subsector \(i\), and \(beta\) is the logit exponent.
See relative cost logit and absolute cost logit.
There are a number of ways that policies can be applied directly to influence the land sector in GCAM. These include the following.
Protected Lands: With this policy, GCAM users can set aside a fraction of natural land, removing it from economic competition. This land cannot be converted to crops, pasture, or any other land type. This is similar to real-world policies such as reducing emissions from deforestation and forest degradation (REDD). See more on how these assumptions can be adjusted here.
Valuing carbon in land: When applying a price on carbon through any of the emissions-related policy approaches, GCAM users can choose whether that price extends to land use change CO2 emissions. This policy is modeled as a subsidy to land-owners for the holding carbon stocks as opposed to a price on the emissions themselves.
energy.NEG_EMISS_GDP_BUDGET_PCT
in constants.R. To enforce the constraint the model will scale back the value of the subsidy given to bioenergy to stay within the budget. Thus limiting the value but not necessarily the quantity of negative emissions. Note this budget is also applied to the valuation of carbon in land when running such a policy, however the actual value of those emissions are not included in this budget at the moment.Land-use modification strategies reduce the cost of limiting atmospheric CO2 concentrations, but can make crop prices rise and transform human diets, for example, when people consume less beef and other carbon-intensive protein sources. The rate at which crop productivity is improved has a strong influence on emissions from land-use change. Thus, the technology used for growing crops is potentially as important for limiting atmospheric CO2 as are approaches like CO2 capture and storage (Wise et al. 2009).
Agricultural commodities