a 3-regional cge-model for china
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A 3-regional CGE-model for China. Development Research Centre, PRC. Presentation Outline. Introduction Economic part of the three-regional model Environmental part of the three-regional model Further Analysis. Introduction. The main goal: - PowerPoint PPT PresentationTRANSCRIPT
A 3-regional CGE-model for China
Development Research Centre, PRC
Development Research Center, The State Council, PRC
Presentation Outline
Introduction
Economic part of the three-regional model
Environmental part of the three-regional model
Further Analysis
Development Research Center, The State Council, PRC
Introduction
The main goal: To analyze environmental implications of Chin
a’s WTO accession Geographic differentiation: A single China-wide model A two regional model (GD-Guangdong and ROC-Rest of China)
A multi-regional model
Development Research Center, The State Council, PRC
The three-regional model• The three -region Chinese CGE model we employ in this
study is an extension of the following models that had been used in China’s WTO accession study the single region Chinese CGE model (Development Research Center,
1998) The two regional Chinese CGE model (Li and Zhai, 2000,2002)
• Three regions GD (Guangdong), SX (Shanxi) and Rest of China (ROC) Why?
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Introduce of the geographic differentiation into the model
- to reflect the different impact on different regions of WTO accession in China according to different regional comparative advantage, etc.
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Shanxi Province
GuangdongProvince
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The differentiation between GD and SX
Location, Area Population Nature Resource Economic development
• GDP, Per capita GDP, Market openness, Industrial structure, International trade, etc.
Infrastructure, FDI, Human resource, Institutions, etc.
……
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Some indicators for GD&SX in 2003SX GD
ChinaRatio to National
level
Ratio to National
level
Population (10000 persons) 3314 2.6 7954 6.2 129227
GDP ( 100 million RMB ) 2457 2.1 13626 11.6 117252
Per capita GDP (RMB) 7435 81.7 17213 189.1 9101
Import & Export (USD 10 000) 52 0.6 2892 34 8510
Export 37 0.8 1537 35.1 4382
Import 14 0.3 1355 32.8 4128
FDI(USD 10 000) 21361 0.4 782294
14.6 5350467
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Jilin、 Xinjiang、 Heilongjiang、 Liaoning
Beijing、 Tianjing、 Zhejiang、 Shanghai、 Guangdong、Fujiang、 Hebei、 Shandong
、 Hebei、 Jiangsu
Shaanxi、 Jiangxi、 Hunan、Ninxia、 Guizhou、 Yunnan、 Shanxi、 Chongqing、 Anhui、 Hainan、 Guangxi、 Sich
uan
Xizang、 Gansu、 Inner Mongolia、 Qinghai、 Henan
Per capita GDP
GDP growth HighLowAverage
High
Low
Average
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Guangdong Province
Guangdong province locates in southern China, neighboring Hong Kong and Macao. As one of the largest economies in China,
It accounts for 35 percent of national foreign trade in 2003.
The development of Guangdong since 1978 and its economic structure could be a representation of China’s coastal area.
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Shanxi Province
Shanxi, locates on the middle part of North China.
As the "Coal Warehouse of China", the output of coal in Shanxi ranks the first in China and accounts for nearly one-fourth of the country's total.
According to the UNIDO technique classification, resource-based manufactured export account for 61.94% of the total manufactured export in 2000.
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Difference between 2 regional model and 3 regional model
- “bilateral” to “triangular” , etc. Some important issues in the model
- data
- environmental issues
- “new” energy
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Economic part of the three-regional model
Data-three regional SAM
CGE-Model
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Data-three regional SAM
Inter-regional trade
Two separate trade regimes
Different household groups
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Inter-regional trade
In most countries, interregional trade is not covered by official statistics, which results in it having to be estimated by whoever has an interest in it (Pedro Ramos et al., 2003). In China, that is the case, too.
With regional IO tables and Customs Statistics, we can get international trade, inflow (not incl. import) and outflow (not incl. export)
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Table 1: The main methods for estimating the interregional trade
TECHNIQUE USED FOR THEESTIMATION
SOME MODELS
A P
OS
TE
RIO
RI →
A P
RIO
RI
INDIRECT ESTIMATION
Use of Gravitational model TIM, (Funck et al. 1975)
Use of Entropy Maximising Paradigm Batten (1983)
Pool-Approach of LeontiefLeontief (1977)INTERREG (Martellato et al, 1996)
DIRECT ESTIMATION BASE ON REAL DATA
Use of International trade flows EU-IRIO (Oosterhaven et al., 1995)
Use of Transport flows
MRIO-HERP (Polenske 1980);Hewings, 1993; Kazumi H., 2000.INTERTIO, (Llano, 2000)
Use of surveys designed ad-hoc forproducers and consumers.
JAPAN IRIO TABLES (1960-70)
Source: Carlos Llano Verduras, the estimation of the interregional trade in the context of an interregional input-output model for the Spanish economy,
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Inter-regional trade
The main method used to estimate the inter-regional trade in this study
Indirect Estimation--Use of Gravitational model
We only estimation the inter-regional trade Matrix (3×3) for merchandise trade.
For services trade we use the net outflow.
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12T 13T 1OF
21T 23T 2OF
31T 32T3OF
1IF2IF
Table 2: The schematic interregional trade matrix
Regions GD SX ROC Total
GD
SX
ROC
Total
Notes: GD-Guangdong Province, SX-Shanxi Province, ROC-the Rest of China.
3IF
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Gravity model
d
OIOIGDPGDP
TDS
SDT jijiij
ij
2121
Where, suffix i refers to the origin, j refers to the destination. Dj i
s the total demand for a given commodity in region j; Si is the tot
al supply in region i; TDS is the total demand (or total supply) for the three regions. GDP is the regional economic size (share of GDP). OI is the trade openness index. d is the distance between the region i and j. α,β ,γ andδ are parameters.
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first step :To choose the parameters, we structure the following programming problem :
0 0
)(
..
min
,
2
2121
ROCROC
ij
j iij
ROC
ROCROCROC
jiij
jijiij
ij
jj
iij
OFIFT
OFIFOUTPUT
OFIFOI
OFTd
OIOIGDPGDP
TDS
SDT
ts
IFTtion destina
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Second step :To balance the trade matrix, we use Cross Entropy Methods:
0
,
,
..
min0
0
ij
ijij
jiij
i j ij
ij
j
ij
T
"GD","SX"jIFT
"GD","SX"iOFT
ts
T
TLN
OF
T entropy
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sector β sector β sector β sector βAutomobile 0.632 Logging 3.813 Textile 11.202 Printing 15.498
corn 0.777 Leather 4.004 CoalMin 11.705 Instrumnt 15.754
Sawmills 0.923 OthManuf 4.217 OthAg 12.206 rice 16.215
Tobacco 1.467 Machinery 5.187 Beverage 12.797 ElecMach 16.792
NFerProd 1.48 Gas 5.611 FoodProc 12.818 Fishing 17.127
FerOreMin 1.952 wheat 5.651 OthCrop 13.478 SocActProd 23.217
Wool 2.239 Apparel 8.318 SpecEquip 13.5 BuildMat 25.566
Chemical 2.746 Quarrying 8.44 RefPet 13.844 GrainForage 37.231
MetalProd 2.763 Water 9.67 IronSteel 13.863 Medicine 61.694
Plastic 3.49 Forestry 9.771 Electron 14.293 Sugar 193.282
The verification of the result
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(Continued)
The statistic transportation yearbook provide the inter-regional transport data for coal.
The correlation coefficient between the published trade matrix and estimated trade matrix is 0.82.
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Two separate trading regimes
Two separate trading regimes Processing trade
Ordinary trade
In this SAM, both production and trade are divided between ordinary trade and processing trade.
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Different household groups
In the SAM, all households are divided into 14 groups, 7 groups of urban households and 7 groups of rural households.
LowestLowLower-middleMiddleUpper-middleHighHighest
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CGE-Model
Model Dimension Production and Factor Markets Interregional and Foreign Trade Income Distribution and Demands Central and Regional Governments, and Extra-
budget Public Sector Macro Closure Recursive Dynamics Data Parameters of the model
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Environmental part of the three-regional model
Emission of Pollutant
CO2,SO2,NMVOC,NOX,PM10, CH4 and N2O
The impact on human health and other
environmental end-points like crop damage
and material damage
Additional topic-Biomass
Development Research Center, The State Council, PRC
In the three regional CGE model, the total amount of a given polluting emission takes the following form:
j
jji
iii j
jiji XAXPCE ,,
I
Emission with
intermediate consumption
III
Emission with
final consumption
II
Emission with
sectoral production
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where i is the sector index, j the consumed product index, C intermediate consumption, XP output, XA final consumption, the emission volume associated with one unit consumption of product j used by sector i; the emission volume associated with one unit production of sector i. the emission volume associated with one unit consumption of product j in final consumption .
ij
i
j
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Health benefit
Step 1: introduce of dispersion model
Estimate impacts on air pollution exposure
Step 2: introduce of dose-response function
Step 3: introduce of VSL (Value of a statistical life)
Estimate impacts on mortality etc. health risk end-points
Estimate units values of health risk end-points
Emission Change
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Biomass In China the biomass energy plays a very important
role in the total energy consumption, especially in rural energy consumption and plays an important role in the discharge of GHG.
While we consider only commercial energy sources both renewable and natural resources are explicitly treated. Traditional biomass fuels are ignored since national accounts and official input-output data do not include their value (Rana, 1999).
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In China, the biomass also does not introduce into the official account
How to Import the residential combustion of biomass to China’s environmental CGE
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Import biomass to CGE
What determines the choice of biomass energy
Key issues of adding the biomass energy in the model
The function for the biomass consumption
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What determines the choice of biomass energy
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Agricultural ModernizationDevelopment
Township EnterprisesDevelopment
Labor Transfer From Agriculture To Other Industries etc.
The Increase income Of Peasants
High Quality of
Living Standard
Transition ofEnergy Consumption
Development of large mines and
power generation etc.
Construction and Opening-up of energy market
Decrease of the biomass energy consumption
Substitution
Energy ladder
Figure 2: The transition of energy consumption
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The factors
Cost
Opportunity cost of collecting biomass and price of other energy
Income
Living custom etc.
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Key issues of adding the biomass energy in the model
“Exogenous”-simple
“Semi-exogenous”
“Endogenous”-complicated
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The function for the biomass consumption
Demand
-income
Supply
-the forest coverage rate and per cap output of grain
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Where, denote the forest coverage rate and per cap output of grain respectively.
itittittitttit zzyq 2211ln
1z 2z
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For the data of non-commercial biomass consumption in rural area, there is only ten-years-series data of non-commercial biomass consumption at national level. Maybe the data is too short for econometric analysis.
Fortunately we have pooled data, non-commercial biomass consumption by province (31 provinces) and by years (1991, 1992, 1993, 1995, 1996, 1998, and 1999). So our empirical analysis is based on the pooled data.
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Table 2 Partial empirical result for non-commerce biomass consumption in rural
area
1991 1992 1993 1995 1996 1998 1999
I ntercept - - - - - - -
-203. 6522 -188. 8393 -136. 5411 -186. 4200 -84. 8028 -83. 1575 -115. 7410 Ln( I NC)
(Per net i ncome i n rural area) ( -3. 646318) ( -4. 350736) ( -3. 318059) ( -3. 654203) ( -3. 010487) ( -3. 356177) ( -3. 687193)
250. 0117 225. 4915 179. 9735 254. 9298 126. 5163 127. 6774 166. 3154 l n(GRAI NP)
(Per cap output of grai n) (4. 358807) (4. 996974) (4. 094587) (4. 331719) (3. 827585) (4. 408217) (4. 412811)
4. 7703* 6. 2152 4. 8507 4. 3929* 3. 6836 3. 2955 2. 9507* FCR
(Forest coverage rate) (2. 776916) (4. 448686) (3. 041686) (2. 161174) (3. 130782) (3. 267888) (2. 150377)
R2 0. 49070 0. 61935 0. 47488 0. 51589 0. 47540 0. 51104 0. 45200
Adj usted R2 0. 44642 0. 58625 0. 43287 0. 46979 0. 43343 0. 47343 0. 41141
D. W. 1. 56799 1. 53491 1. 24243 1. 61724 1. 84065 1. 42560 1. 62037
Notes: 1.All the results are derived from the estimation by Eviews
3.1.
2.* Significant at the level of 5%.
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per capita annual
biomass consumption*
Income Elasticity of
biomass consumption
1991 -203.7 295.1 -0.69
1992 -188.8 250.8 -0.75
1993 -136.5 265.5 -0.51
1995 -186.4 273.9 -0.68
1996 -84.8 220.7 -0.38
1998 -83.2 224.9 -0.37
1999 -115.7 220.1 -0.53
Average -0.56
Notes: * Per capita annual biomass consumption in national level, unit:10-3tce/person.
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“Semi-exogenous”
Link the biomass consumption function to the model
-the income is the linkage
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Further Analysis
To design scenarios of China’s WTO accession
To analyze environmental implications of Chin
a’s WTO accession