Brazilian Land Use Model and Application for Ethanol Impacts

21
ICONE Brazilian Land Use Model and its application for ethanol impacts Laura Barcellos Antoniazzi Researcher, ICONE ([email protected]) Sao Paulo, May 15th 2009

description

Presentation of Laura Barcellos Antoniazzi for the “Workshop on the Impact of New Technologies on the Sustainability of the Sugarcane/Bioethanol Production Cycle” Apresentação de Marcos Laura Barcellos Antoniazzi realizada no “Workshop on the Impact of New Technologies on the Sustainability of the Sugarcane/Bioethanol Production Cycle”Date / Data : May 14 - 15th 2009/ 14 e 15 de maio de 2009 Place / Local: ABTLuS, Campinas, Brazil Event Website / Website do evento: http://www.bioetanol.org.br/workshop3

Transcript of Brazilian Land Use Model and Application for Ethanol Impacts

Page 1: Brazilian Land Use Model and Application for Ethanol Impacts

ICONE Brazilian Land Use Modeland its application for ethanol impacts

Laura Barcellos

AntoniazziResearcher, ICONE

([email protected])

Sao Paulo, May 15th 2009

Page 2: Brazilian Land Use Model and Application for Ethanol Impacts

2

Outline1.

Introduction.

2.

General structure of the land use model

Diagrams explaining the information flows, connections among variables and

effect-cause relations.

Assumptions.

3.

Summarized results.

Historic data.

Supply and demand projections for Brazil.

Area allocation at regional level.

Improvements under development

3.

Applications

Page 3: Brazilian Land Use Model and Application for Ethanol Impacts

3

Introduction

There are many concerns worldwide about the social and environmental impacts

of biofuels

productions and expansion.

Land Use Change

(LUC), as well as Indirect Land Use Change (ILUC), are now

being taking into account in many policies aiming to promote biofuels.

ICONE started to work on an Agriculture Projection Model in the beginning of 2008 in a joint effort with the Food and Agricultural Policy Research

Institute (FAPRI),

from Iowa State University, which is part of the Center for Agriculture and Rural Development (CARD).

Although the Brazilian model follows the same structure of the FAPRI Models, it was adapted to the specific conditions and situations of the Brazilian agricultural sector.

The Model aims to capture the Brazilian land use dynamics

observed in the past

and to forecast new dynamics

Page 4: Brazilian Land Use Model and Application for Ethanol Impacts

Agricultural Land use in Brazil (Agricultural census)

Source: IBGEP = Preliminary

Page 5: Brazilian Land Use Model and Application for Ethanol Impacts

Confidential. Do not quote or cite unless authorized. 5

General structure of the land use model

The model comprises two general sections: supply and demand

and land allocation.

Supply and demand, for a given year, is calculated at a national

level. Supply includes production and initial stocks (in the case of crops), and demand

includes domestic consumption, net trade and final stocks.

Supply (regional) = Demands (national)

Land allocation calculations are integrated to the supply side. Area is calculated at a regional level, as a function of the expected market profitability of the

product and of the competing products.

The amount of land allocated for a given crop, in a given region, depends on the response to expected market profitability, which means that regions with higher market returns will have higher planted area.

Allocation of land across regions Brazilian production national supply

The calculation of the expected planted area is also calibrated with the lagged area (area of the previous year) in order to avoid strong oscillations in the

planted area.

Page 6: Brazilian Land Use Model and Application for Ethanol Impacts

Confidential. Do not quote or cite unless authorized. 6

General structure of the land use model

Planted forests are also included in the area allocation section

of the model. For the version we are using now, projections of land allocation for planted forest are exogenous.

The model comprises 6 macro-regions in Brazil:

Region 1: South (States of Rio Grande do Sul, Santa Catarina

e Parana);

Region 2: Southeast (States of Sao Paulo, Minas Gerais, Espirito

Santo e Rio de Janeiro);

Region 3: Center-West Cerrado (States of Goias

and Mato

Grosso

do Sul

and the Cerrado area in Mato

Grosso);

Region 4: Amazon North (States of Amazonas, Para, Amapa, Acre, Rondonia, Roraima

and the Amazon area in Mato

Grosso);

Region 5: Coastal Northeast (States of Ceara, Alagoas, Sergipe, Pernambuco, Rio Grande do Norte and Paraiba);

Region 6: Mapito

e Bahia (States of Maranhao, Piaui, Tocantins e Bahia).

The regions are independent in the model in the sense that land allocation equations for each crop are different among regions. However, given that the total production must be equal to the demand, if a given crop looses area in a certain region, for

a given regional yield, other region will offset it with an increase in area.

Page 7: Brazilian Land Use Model and Application for Ethanol Impacts

Fig. 1 Brazilian

Biomes

and

States

AM

MT

PA

MS

RS

TO

GO

MA

PI

SC

PRSP

MG

BARO

APAP

CE RNPB

PEAL

SE

ES

RJ

AC

AM

MT

PA

MS

RS

TO

GO

MA

PI

SC

PRSP

MG

BARO

APRR

CE RNPB

PEAL

SE

ES

RJ

AC

Amazon

ForestAtlantic

ForestSavannaSteppePantanal wetlandSouth

Grassland

Page 8: Brazilian Land Use Model and Application for Ethanol Impacts

Confidential. Do not quote or cite unless authorized. 8

Fig. 2 Macro-regions used in the Land Use Model

Source: UFMG, ICONE.

North Amazonia

Center West Cerrado

MAPITO and Bahia

Northeast coast

Southeast

South

Page 9: Brazilian Land Use Model and Application for Ethanol Impacts

Confidential. Do not quote or cite unless authorized. 9

Figure 3. Land Use Model: Interactions Among Sectors

Cotton

Rice

Drybean

Corn

Soybean Soybean meal

Soybean oil

Sugarcane

Ethanol

Sugar

Beef

Pork

Poultry (eggs and chicken)

Pasture

Industry and biodiesel

Source: ICONE

Page 10: Brazilian Land Use Model and Application for Ethanol Impacts

Confidential. Do not quote or cite unless authorized. 10

Figure 4. General Structure of the Land Use Model

Source: ICONE.

Domestic consumption

Demand

Supply

Price

Costs

Expected return

Net exports

Final stocks

Production

Initial stocks

Yields

Area(t-1)

Exogenous variable

Endogenous variable

Exogenous macroeconomic data-

Population;-

World and national GDP;-

World oil price and domestic gasoline price;

-

Exchange rate;-

Inflation rate;-

Fertilizer price index;-

Vehicle fleet.

Page 11: Brazilian Land Use Model and Application for Ethanol Impacts

11

General structure of the land use model

One key output of the model is the total land allocated for agriculture and pastures. If this total, plus the exogenous planted forest area, is increasing over time, more natural land is brought for production purposes. This

excess allocation of

land can be explained by the combination of two factors:

Increase of cattle herd in regions with agricultural frontiers (regions 4 and 6 of the model), with a simultaneous reduction or stabilization of cattle herd in the traditional areas. This can be interpreted as an indirect effect

due to crops

expansion;

Expansion of crops in the frontier, which is a direct effect.

In order to measure the indirect effect it is necessary to isolate these two causes of crops and pasture expansion in the frontier regions.

Page 12: Brazilian Land Use Model and Application for Ethanol Impacts

12

Data Gathering and Preparation

In order to run the regressions and to calculate the parameters (elasticities and coefficients) used for the projections, a 13 year database was organized, from

1996 to 2008. Due to the lack of information with respect to prices and costs of production, data from 1997 and 2007 were used for the estimations.

With respect to the variables that are solved endogenously in the model, the following variables are included in the database:

Supply and demand balance sheets for Brazil;

Regional information on production, planted area, yields, prices

received by farmers, costs of production, cattle herd structure, animal production (beef, chicken, eggs, pork and milk).

The model requires a set of exogenous macroeconomic variables (presented in the figure 2). We are using exogenous macroeconomic variables supplied by FAPRI.

The model is prepared to project ethanol exports and domestic demand endogenously, but can also work with exogenous scenarios, such as different countries´

mandates. ICONE is ready also to create exogenous scenarios of ethanol world trade,

calculating supply and demand for the main producers and consumers (Unites States, European union, Japan, etc.).

Page 13: Brazilian Land Use Model and Application for Ethanol Impacts

Confidential. Do not quote or cite unless authorized. 13

Assumptions

Equilibrium price is obtained when supply is equal to demand, in

a given year, for a

given activity (crops or animal products).

Area allocated to a given crop, in a given year, is a result of the market equilibrium. Producers respond, in terms of planted area, according to the expected market return (costs of production of the current year and prices received in the previous year).

Prices received by farmers and prices paid by consumers follow the same trend over time.

The model assumes full availability of capital for investments and credit for working capital, which means that it does not capture negative effects of low availability of credit in the market.

Crops yields and total recoverable sugar factors, although regional, are projected as a time series trends.

Prices are solved at a national level and are transmitted to the

regions using

transmissions coefficients estimated by regressions. Improvements in infrastructure, which would may lead to increase prices and to reduce costs of production can be simulated as scenarios.

Page 14: Brazilian Land Use Model and Application for Ethanol Impacts

The two

model´s versions

First Version

Results are ready and have already been used for some projects. Results validation among analyzed sectors will be carry out soon.

The first version doesn't considered land availability, so that total agricultural land use can expand indefinitely.

Equations for Allocation Area are independent in each Region. Historical planted areas are considered as an explanatory variable.

Improved Version

Area allocated for each crop and pasture will be defined by two equations

1.

Expansion Equation: it will define total agricultural area and it is subject to land availability.

2.

Shares Equation: for each crop and pasture, its share on the total agricultural area is the dependent variable. Returns of all crops are used as explanatory variables.

Equations for Allocation Area are simultaneously in each Region.

Page 15: Brazilian Land Use Model and Application for Ethanol Impacts

Net Growth of Agricultural Land Uses Area and Cattle Herd, 2002-06 (1,000 ha and heads)

Source: PAM/IBGE, Agricultural Census/IBGE and PPM/IBGE.

State Sugarcane

(ha)Other

crops

(ha) Pasture

(ha) Total used

area

(ha)Cattle

Herd

(hd)

São Paulo 622 -224 -882 -484 -909

Minas Gerais 153 389 -625 -82 1,644

Paraná 74 850 -1 287 -284

Mato Grosso do Sul 41 1 -985 -210 558

Goiás 34 576 -2,041 -1,431 545

Bahia 26 492 143 661 912

Mato Grosso 25 1,634 -1,437 0 3,881

Maranhão 16 298 -463 -148 1.835

Pará 3 115 2,502 2,620 5,311

South-Centre 949 3,226 -5,971 -1,920 5,435

Total 1,000 5,446 -5,385 1,061 18,383

Page 16: Brazilian Land Use Model and Application for Ethanol Impacts

Source: CONAB; USDA; ABIEC; ABIPECS; ABEF. Elaboration: ICONE

Brazil: Crops Area (excluding 2nd crop) and Production and Meat Production

Performance

0

100

200

300

400

500

600

700

800

900

96/9

7

98/9

9

00/0

1

02/0

3

04/0

5

06/0

7

0

20

40

60

80

100

120

140

160

Production Planted Area

0

2

4

6

8

10

12

90 92 94 96 98 00 02 04 06

08(e)

0

2

4

6

8

10

12

14

16

18

Chicken Beef Pork

Crops Area and Production(million tons and million ha) Meat (million tons)

Page 17: Brazilian Land Use Model and Application for Ethanol Impacts

Brazil: Livestock

dynamics

0

10000

20000

30000

40000

50000

60000

70000

1997 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007 2008

(1,0

00 h

ds)

SouthSoutheastCenter West CerradoNorth AmazoniaMAPITO and BahiaNortheast coast

0

10000

20000

30000

40000

50000

60000

1997 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007 2008

(1,0

00 h

a)

SouthSoutheastCenter West CerradoNorth AmazoniaMAPITO and BahiaNortheast coast

Catle

Herd in the Model´s

RegionsPasture Area in the Model´s

Regions

Page 18: Brazilian Land Use Model and Application for Ethanol Impacts

Source: CONAB; IBGE;

UNICA. Elaboration: ICONE

Brazil: Sugarcane, Sugar and Ethanol Production

0

100

200

300

400

500

600

90/91

92/93

94/95

96/97

98/99

00/01

02/03

04/05

06/07

Million ton

0

1

2

3

4

5

6

7

8Million ha

Production Planted Area

0

5

10

15

20

25

30

35

90/91

92/93

94/95

96/97

98/99

00/01

02/03

04/05

06/07

Million ton

0

10

20

30

40

50

60Billion ltr

Sugar Ethanol

Sugarcane Production and Area Sugar and Ethanol Production

Page 19: Brazilian Land Use Model and Application for Ethanol Impacts

Source: CONAB; IBGE;

UNICA. Elaboration: ICONE

Brazil: Ethanol Supply & Demand(billion liters)

0

10

20

30

40

50

60

96/97

97/98

98/99

99/00

00/01

01/02

02/03

03/04

04/05

05/06

06/07

07/08(e)

0

10

20

30

40

50

60Production Exports Domestic Consumption

Page 20: Brazilian Land Use Model and Application for Ethanol Impacts

Overview of Sugarcane in Brazil

Page 21: Brazilian Land Use Model and Application for Ethanol Impacts

Applications

The model is very

flexible

and can be used for different types of simulations and

scenarios.

The model is also prepared to simulate impacts of variables

that are not explicit in

the model, such as improvements in transportation infrastructure

(construction of an ethanol pipeline, for example), costs reduction due to he adoption of new technologies (second generation ethanol and GMOs

adoption), among others

applications.

Useful for specific sector analysis

Regional land use results can be disaggregate for smaller scales

(World Bank´s

Brazil Low Carbon Study)

Land use changes can be converted into carbon emissions.

It is possible to connect the Brazilian Model with world models.

It is used to compare land use results from other models (GTAP-

CARB)