This presentation highlighted the process of developing and progress made in the development of the FR and FB DST.
The site-specific fertilizer recommendation (FR) tool is built to provide an optimized and profitable site-specific fertilizer recommendations for cassava growers. The tool considers the location, soil fertility, weather condition, available fertilizers in the area, prices for fertilizer and cassava root, planned planting and harvest dates and the investment capacity of the farmers.
The nutrient omission trials (NOT) in Nigeria and Tanzania conducted by ACAI, in collaboration with the national research and development partners, show a large variation in nutrient responses indicating the need for site-specific fertilizer recommendation. ACAI is developing a crosscutting system using machine learning techniques coupled with process based crop models, LINTUL and QUEFTS, and economic optimizer algorithms to provide the site-specific recommendations. ACAI is transforming available big data like GIS layers from SoilGrids and weather data from CHIRPS and NASA to useful information that can be used to model the relationship between apparent soil nutrient supply and soil properties. Effort has also been made to identify a generic soil fertility indicator that can be easily obtained from farmers and is useful covariate to improve the accuracy of apparent soil nutrient supply predictions.
The next steps in the FR tool development include, validating the FR tool both functionally, checking if the recommendations outperform the current practices in the field and architecturally, checking user friendliness and if the tool satisfies the needs of development partners to dissemination strategy.
Thesis presentation made by AGUNG WAHYUDI, during his master study in Ghent University 2008. He received 17 out of 20 for his thesis. He graduated with great distinction in the same year.
Developing a Modeling Framework to Characterize Manure Flows in TexasLPE Learning Center
Proceedings available at: www.extension.org/67646
In recent years, sharply rising costs of inorganic fertilizers have contributed to an increased demand for manure and compost in crop production acreage, transforming cattle manure from a valueless waste to a viable alternative to commercial fertilizer. If additional demand for manure as a bio-fuel were to arise manure could take on two distinct values, a fertilizer value and a fuel value. This potential “dual” value of manure begs several questions. What would the fertilizer and fuel markets of manure look like? Is there enough manure supply for the markets to operate independently? If not, which market would prevail? In essence, how, if at all, would manure’s potential value as a bio-fuel distort the traditional Panhandle manure market? A modeling framework was developed to assess the potential impacts of a manure-fired ethanol plant on the existing Texas Panhandle manure fertilizer market. Two manure-allocation runs were performed using a spreadsheet model. Run #1 allocated all available manure from dairies and feedlots to cropland as manure fertilizer; run #2 first allocated fuel manure to the ethanol plant and then allocated the remaining manure to cropland. Both model runs assumed a time horizon of one year and no antecedent nutrients in cropland soils. Other constraints included only irrigated acreages received manure and no supplemental fertilizer was used. The model revealed a 6.4% increase in cost per acre of fertilizing with manure for fields whose nutrient requirements were fully satisfied in both runs. The increase in cost per acre was likely due to an increase in hauling distances attributed to fewer CAFOs available for fertilizer manure. The model is not presented as a dynamic, systems model, but rather a static model with the potential to be incorporated into a more dynamic systems-based modeling environment. Suggestions for further model development and expansion including GAMS integration are presented.
This presentation highlighted the process of developing and progress made in the development of the FR and FB DST.
The site-specific fertilizer recommendation (FR) tool is built to provide an optimized and profitable site-specific fertilizer recommendations for cassava growers. The tool considers the location, soil fertility, weather condition, available fertilizers in the area, prices for fertilizer and cassava root, planned planting and harvest dates and the investment capacity of the farmers.
The nutrient omission trials (NOT) in Nigeria and Tanzania conducted by ACAI, in collaboration with the national research and development partners, show a large variation in nutrient responses indicating the need for site-specific fertilizer recommendation. ACAI is developing a crosscutting system using machine learning techniques coupled with process based crop models, LINTUL and QUEFTS, and economic optimizer algorithms to provide the site-specific recommendations. ACAI is transforming available big data like GIS layers from SoilGrids and weather data from CHIRPS and NASA to useful information that can be used to model the relationship between apparent soil nutrient supply and soil properties. Effort has also been made to identify a generic soil fertility indicator that can be easily obtained from farmers and is useful covariate to improve the accuracy of apparent soil nutrient supply predictions.
The next steps in the FR tool development include, validating the FR tool both functionally, checking if the recommendations outperform the current practices in the field and architecturally, checking user friendliness and if the tool satisfies the needs of development partners to dissemination strategy.
Thesis presentation made by AGUNG WAHYUDI, during his master study in Ghent University 2008. He received 17 out of 20 for his thesis. He graduated with great distinction in the same year.
Developing a Modeling Framework to Characterize Manure Flows in TexasLPE Learning Center
Proceedings available at: www.extension.org/67646
In recent years, sharply rising costs of inorganic fertilizers have contributed to an increased demand for manure and compost in crop production acreage, transforming cattle manure from a valueless waste to a viable alternative to commercial fertilizer. If additional demand for manure as a bio-fuel were to arise manure could take on two distinct values, a fertilizer value and a fuel value. This potential “dual” value of manure begs several questions. What would the fertilizer and fuel markets of manure look like? Is there enough manure supply for the markets to operate independently? If not, which market would prevail? In essence, how, if at all, would manure’s potential value as a bio-fuel distort the traditional Panhandle manure market? A modeling framework was developed to assess the potential impacts of a manure-fired ethanol plant on the existing Texas Panhandle manure fertilizer market. Two manure-allocation runs were performed using a spreadsheet model. Run #1 allocated all available manure from dairies and feedlots to cropland as manure fertilizer; run #2 first allocated fuel manure to the ethanol plant and then allocated the remaining manure to cropland. Both model runs assumed a time horizon of one year and no antecedent nutrients in cropland soils. Other constraints included only irrigated acreages received manure and no supplemental fertilizer was used. The model revealed a 6.4% increase in cost per acre of fertilizing with manure for fields whose nutrient requirements were fully satisfied in both runs. The increase in cost per acre was likely due to an increase in hauling distances attributed to fewer CAFOs available for fertilizer manure. The model is not presented as a dynamic, systems model, but rather a static model with the potential to be incorporated into a more dynamic systems-based modeling environment. Suggestions for further model development and expansion including GAMS integration are presented.
Presentation by R Wassmann, International Rice Research Institute, at the CCAFS Workshop on Institutions and Policies to Scale out Climate Smart Agriculture held between 2-5 December 2013, in Colombo, Sri Lanka
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The Climate Food and Farming (CLIFF) Research Network is an international research network that helps to expand young researchers' knowledge and experience working on climate change mitigation in smallholder farming. CLIFF provides grants for selected doctoral students to work with CGIAR researchers affiliated with the Standard Assessment of Mitigation Potential and Livelihoods in Smallholder Systems (SAMPLES) project.
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Presentation by R Wassmann, International Rice Research Institute, at the CCAFS Workshop on Institutions and Policies to Scale out Climate Smart Agriculture held between 2-5 December 2013, in Colombo, Sri Lanka
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IFPRI Low Emissions Development Strategies (LEDS) Colombia
1. INTERNATIONAL FOOD POLICY RESEARCH INSTITUTE
Marco de Estrategias de
Desarrollo Bajo en Emisiones:
Resultados finales de escenario
de referencia.
LEDS: Low Emissions
Development Strategies
Dr. Alex De Pinto - Senior Research Fellow
2. Proyecto de USAID
LEDS: Estrategias de desarrollo económico
con bajas emisiones
Herramientas de evaluación de LEDS en el
sector de uso de la tierra
Colombia, Vietnam, Bangladesh, Zambia
Colaboración entre IFPRI, CIAT, y socios
nacionales
Marco de Estrategias de Desarrollo
Bajo en Emisiones
3. La idea es presentar a los paises un
portafolio de tecnologias que ayuden al
desarrollo economico, con diferentes
emisiones causadas.
Simulación a largo plazo del uso de tierra,
emisiones y secuestro de carbono,
debidas a la implementación de politicas
que afectan uso del suelo.
Incluye efecto de economía y
mercado global
Capaz del modelo en resumen
4. Some Lessons Learned
To a very complex problem follows a complex
analysis, therefore:
Modeling framework and tools should be
adaptable
Modeling framework and tools should be
flexible so that new information can be
incorporated in the analysis as it becomes
available
Modeling framework and tools should be fully
transparent, so that trust in the results can
be built
5. Parameter
estimates for
determinants of
land use change
Change in carbon stock
and GHG emissions
Policy scenario:
Ex. land use allocation
targets, infrastructure,
adoption of low-emission
agronomic practices
Land use
change
Future commodity
prices and
rate of growth of
crop areas
IMPACT model
Macroeconomic scenario:
Ex. GDP and population
growth
Model of
Land Use
Choices
Model of
Land Use
Choices
Ancillary data:
Ex. Soil type, climate, road
network, slope, population,
local ag. statistics
Satellite data
General Circulation Model
Climate scenario:
Ex. Precipitation and
temperature
Change in carbon
stock and GHG
emissions.
Economic trade-offs
Land use
change
Baseline
Policy Simulation
Crop Model
Crop Model
8. A Parcel of Land…
Is operated by individual or group to
maximize benefits deriving from using the
land (utility)
Has an exogenous set of geophysical and
socioeconomic characteristics that influence
production choices and productivity
Has a set of possible production choices
(relates inputs to possible outputs) that
determine land use
9. Benefits at One Location from
several possible uses
𝑙– location of a parcel
h – possible use at location 𝑙
𝑿𝒍 is vector of factors that affect the stream of
benefits deriving from farming
X= Elevation, slope, soil pH, precipitation,
temperature, crop suitability, crop price
f – technology function that relates inputs to each possible
output h
𝐵𝑙,ℎ = 𝑓 𝑋𝑙,ℎ
10. Farmer at One Location Makes a
Choice
Farmer chooses the use that returns the
highest benefit B
𝐵𝑙,𝑀𝑎𝑖𝑧𝑒 = 𝑓 𝑋𝑙,𝑀𝑎𝑖𝑧𝑒
𝐵𝑙,𝑅𝑖𝑐𝑒 = 𝑓 𝑋𝑙,𝑅𝑖𝑐𝑒
𝐵𝑙,𝐶𝑎𝑠𝑠𝑎𝑣𝑎 = 𝑓 𝑋𝑙,𝐶𝑜𝑓𝑓𝑒𝑒
.
.
.
𝐵𝑙,𝐹𝑜𝑟𝑒𝑠𝑡 = 𝑓 𝑋𝑙,𝐹𝑜𝑟𝑒𝑠𝑡
11. Choose Land Use to Maximize Net
Present Value
Net Present
Value (NPV)
Value of
Output
Cost of
Inputs
Discount
effect
One optimization for each possible land use h at location l
at time T
Choose land use (categorical variable) with highest benefit
minusequals
𝐵𝑙ℎ,𝑇 =
𝑡=0
∞
𝑃𝑙ℎ𝑇_𝑡 𝑄𝑙ℎ𝑇+𝑡 − 𝐶𝑙ℎ𝑇+𝑡 𝑋𝑙ℎ𝑇+𝑡 𝑒 𝑖,𝑡
𝑑𝑡
15. Land-use Choices Are Observed
Data from satellite
images are
processed into
land-use maps.
We observe the
choices made by
whomever has
control over the
land.
16. Many Sources of Data
But also statistical data on hectares
allocated to rice, maize, cassava, etc, at
the province or municipio level.
17. Method of estimation: discrete choice models, e.g.
multinomial logit, nested logit, etc.
For each land use we estimate the probability for
that use to be chosen
We statistically evaluate the effect
of each explanatory variable
.....3
210
lmaizelmaize
lmaizemaizelmaizemaizejlmaize
price
soilslopeB
Prob. Forest
Prob. Agriculture
Prob. Pasture
18. Model Specification:
Two-level Nested Logit
Cocoa
Coffee
Palm
Plantain
Other Perennials
Pasture ForestPerennial
Crops
Annual
Crops
Forest Other
Uses
Cassava
Maize
Potato
Rice
Sugarcane
Other Annuals
Land-use
choice
Crop
choice
19. Model Specification:
Two-level Nested Logit
Prob. Forest
Prob. Agriculture
Prob. Pasture
Prob. Maize
Prob. Rice
Prob. Sugarcane
Land-use
choice
Crop
choice
The estimated probabilities are used to
allocate total area changes predicted by
the IMPACT model
21. Variables dependientes de uso de la
tierra
Uso de
tierra
año Nivel Fuente
Area
cultivo
2008 Municipio Ministerio de
Agricultura y
Desarrollo Rural
2008
Area pasto 2007 Municipio IDEAM, IGAC,
IAvH, Invemar, I.
Sinchi e IIAP
Area
bosque
2007 Municipio IDEAM, IGAC,
IAvH, Invemar, I.
Sinchi e IIAP
22. Explanatory Variables for Colombia
Explanatory variables
Lower level:
Choice variable: crop shares within
provinces (2008 and 2030)
Crop area, crop suitability, commodity producer price,
elevation, terrain slope, soil pH, annual precipitation,
annual mean temperature
Upper level:
Choice variable: land cover (2008 and
2030)
Land cover, elevation, terrain slope, soil pH, annual
precipitation, annual mean temperature, population
density, travel time to major cities, conserved areas,
indigenous reserves
23. Variables independientes, capa de uso
del suelo (2008)
Variables año Nivel Fuente
Suitabilidad para cultivo 2009 10km
square
IIASA/FAO
Altitud 2012 1km square World Harmonized
Soil DB
Gradiente 2012 1km square World Harmonized
Soil DB
PH de suelo 2012 10km
square
ISRIC-WISE
Precipitación anual 1950-2000 1km square WorldClim
Temparetura promedio
anual
1950-2000 1km square WorldClim
Population density 2000 CIESIN
Tiempo de viaje a
ciudades grandes
-2000 1km square JRC-IES-LRM
Precio de carne 2007 nacionál FAO
Valores inclusivos para
cultivo
Derived from lower
model
24. Variables independentes, capa de uso
del suelo (2008)
Variables año Nivel Fuente
Valores inclusivos para
cultivo
Derived from lower
model
Inertia variable
Parques nacionáles 2012 250m
square
RUNAP / SINAP
Areas conservaciónes
regionales
2012 250m
square
RUNAP / SINAP
Reservas Naturales de
la Sociedad Civil
2012 250m
square
RUNAP / SINAP
Reservas forestales 2011 250m
square
RUNAP / SINAP
Reserva Indigena 2012 250m
square
SIGOT
Areas
Afrodescendentes
2012 250m
square
SIGOT
25. Assumptions, Problems, and
Shortcomings
Stationary state and dynamic processes
• Processes of land use change are inherently dynamic
Property rights
• Competitive bidding process breaks down when property rights are
poorly defined or inexistent.
Spatial effects and interdependent behavior
• Possible interactions among several decision makers and eco-
biological processes can transcend parcel boundaries
Nonlinearity in the objective function
• Problem specifications force a linear relationship between dependent
and independent variables.
Profit/Utility-maximizing operator
• Self-sufficiency or risk minimization might be the goal in land use
decisions
29. Enfoque tecnico
Modelo de uso del suelo espacialmente
explicito
IMPACT: modelo global de equilibrio partial
para el sector de agropecuario
DNDC: Modelo cultivo que simula cosecha,
emisiones y cambio de almacenamiento de
carbono
Combina y reconcilia los modelos
30. Parameter
estimates for
determinants of
land use change
Change in carbon stock
and GHG emissions
Policy scenario:
Ex. land use allocation
targets, infrastructure,
adoption of low-emission
agronomic practices
Land use
change
Future commodity
prices and
rate of growth of
crop areas
IMPACT model
Macroeconomic scenario:
Ex. GDP and population
growth
Model of
Land Use
Choices
Model of
Land Use
Choices
Ancillary data:
Ex. Soil type, climate, road
network, slope, population,
local ag. statistics
Satellite data
General Circulation Model
Climate scenario:
Ex. Precipitation and
temperature
Change in carbon
stock and GHG
emissions.
Economic trade-offs
Land use
change
Baseline
Policy Simulation
Crop Model
Crop Model
34. Escenario de referencia
Cambio de uso de la tierra 2008 - 2030
Land use
category
2008
area
(Mha)
2030
area
(Mha)
Change
2008–
2030
(Mha)
Change
(%)
Perennial crops 1.9 2.1 0.1 7
Annual crops 2.4 2.5 0.1 5
Pasture 29.2 31.8 2.6 9
Forest 58.7 55.3 -3.4 -6
Other land
uses
22.1 22.7 0.5 2
Total 114.4 114.4
40. Policy Scenarios
Land use policy scenario from identifies after
consultation with stakeholders
Scenario 1 Reduction of pastureland by 10 million hectares
Scenario 3 Total halt to deforestation in the Amazon
Scenario 4 Total land allocated to palm production reaches a total
of 1.3 million hectares
41. INTERNATIONAL FOOD POLICY RESEARCH INSTITUTE
Scenario 1: Reduction of
pastureland by 10 million
hectares
49. Results
*Includes changes in SOC, Above and Below ground C caused by land use change.
**Changes in emissions from cropland and livestock caused by land use change. Exclude burning
**Changes in revenue from crop and meat production
Change in C
stock
(Tg C)
Change in
GHG emission
(Tg CO2eq)
Change in
total revenue
(US$ billion)
Reduce
pasture by
10 million
hectares
Cropland 144 26.7 56
Livestock -1,297 -184 -22
Forest 895 - -
Other 660 - -
Total 402 -157 34
Zero
deforestation
in the
Amazon
Cropland 4 -0.8 -1
Livestock -97 -16 -2
Forest 245 - -
Other -41 - -
Total 111 -17 -3
Increase area
allocated to
palm by 1.5
million
hectares
Cropland 18 24.5 -57
Livestock -10 -1 0
Forest -7 - -
Other -11 - -
Total -11 24 -57