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Market-Based Instruments with Chinese Market-Based Instruments with Chinese Characteristics: Characteristics:
The Feasibility of Cap-and-Trade The Feasibility of Cap-and-Trade Implementation to Reduce SOImplementation to Reduce SO22 Emissions in Emissions in
China and the Role of the EPAChina and the Role of the EPA
June 20, 2007June 20, 2007
The La Follette School of Public Affairs MIPA Workshop ProjectThe La Follette School of Public Affairs MIPA Workshop Project
Aditya Chandraghatgi * Brandon Lamson * Leah Larson-Rabin Aditya Chandraghatgi * Brandon Lamson * Leah Larson-Rabin Raul Leon * William Lipske * Allison Quatrini * Marta SkwarczekRaul Leon * William Lipske * Allison Quatrini * Marta Skwarczek
Project MotivationProject Motivation
China and the U.S.: Can markets deliver ecological results?
Policy Report for Jeff Smoller, President of the Multi-State Working Group
June 15, 2006 Trilateral Agreement between the EPA, ADB and SEPA
Why SOWhy SO22 for Cap-and-Trade? for Cap-and-Trade?
China has the world’s highest sulfur dioxide emissions.
SO2 emissions in China are mostly generated from burning coal for electricity production.
SO2 causes severe health problems and environmental damage.
Problem StatementProblem Statement
Chinese leaders face the challenge of controlling SO2 emissions without derailing economic growth.
Analytical ApproachAnalytical Approach
Assess the feasibility of implementing cap-and-trade mechanisms in China
Evaluate feasibility in the current Chinese context based on three categories of criteria: political/regulatory, administrative, and economic
Identify the changes necessary for a successful cap-and-trade mechanisms and the potential role of the EPA
Political/Regulatory FeasibilityPolitical/Regulatory Feasibility Political willPolitical will
– Why it matters– Economic development vs. environmental protection
Political controlPolitical control– Nomenklatura and Green GDP– Directional flow of political power
Regulatory clarityRegulatory clarity– Accountability and predictability
A role for social pressureA role for social pressure– Where governments cannot or will not act– NGOs/GONGOs as extension of the State– The Fire-Alarm System
Political/Regulatory FeasibilityPolitical/Regulatory Feasibility
Political and RegulatoryPolitical and RegulatoryCriterionCriterion Status Quo in ChinaStatus Quo in China
Political willPolitical will Low:Low: Economic development continues to be primary concern
Political controlPolitical control Moderate:Moderate: Nomenklatura system potentially useful, but ambiguous political organization creates complications
Regulatory clarityRegulatory clarity Low:Low: Environmental regulation currently opaque
A role for social pressureA role for social pressure Low-Moderate:Low-Moderate: Very little political and regulatory space for non-governmental entities
Administrative FeasibilityAdministrative Feasibility
A relationship exists between institutional capacity and compliance in emission control
Capacity and commitment necessary for environmental policy to be effective
Administrative challenges: accurate measurement of emissions, monitoring of emission sources, and enforcement of policy present
Provincial Capacity Provincial Capacity
0
5
10
15
20
25
30
35
Tib
et
Hai
nan
Qin
ghai
Sha
nxi
Gan
su
Gui
zhou
Hun
an
Gua
ngxi
Anh
ui
Jilin
Jian
gxi
Inne
r M
ongo
lia
Liao
ning
Jian
gxi
Fui
jan
Hen
an
Nin
gxia
Xin
jang
Zhe
jiang
Sic
huan
Hei
long
jiang
Hub
ei
Yun
nan
Sha
ndon
g
Gua
ngdo
ng
Sha
ngha
i
Tia
njin
Bei
jing
Heb
ei
Cho
ngqi
ng
Sha
anxi
Province
Ra
nk
ing
Potential Capacity
Realized Capacity
Li, Wanxin. “A Survey of Institutional Capacity of Local EPBs in China.” Paper presented at 2005 Urban China Research
Network Annual Conference: Chinese Cities in Transition, 2 May 2005, in Shanghai, China.
Administrative FeasibilityAdministrative FeasibilityStatus Quo, by Local CapacityStatus Quo, by Local Capacity
AdministrativeAdministrativeCriterionCriterion Low Capacity AreaLow Capacity Area High Capacity AreaHigh Capacity Area
Accurate Accurate measurement of measurement of SOSO
2 2 emissions emissions
from all sourcesfrom all sources
Low:Low: Material balance calculations not accurate enough for measuring SO2
emissions
Moderate:Moderate: With increased funding, continuous emissions monitors would better estimate emission levels
Monitoring of Monitoring of SOSO
2 2 emission emission
sourcessources and and permitspermits
Low: Low: Continuous emissions monitors are needed but costly
Moderate:Moderate: State monitors inspect more often and more accurately
Consistent, Consistent, effective effective enforcementenforcement
Low: Low: Provincial compliance varies
Moderate-High:Moderate-High: Provinces have ability to increase fines for noncompliance
Economic FeasibilityEconomic Feasibility
Focused on Guangdong, a single high capacity province
Selected power and cement industries
Both industries are large emitters of SO2
Economic FeasibilityEconomic FeasibilityStatus Quo in Selected IndustriesStatus Quo in Selected Industries
Economic CriterionEconomic Criterion Power IndustryPower Industry Cement IndustryCement Industry
Area of targeted Area of targeted emissions that is emissions that is regional or regional or global in scopeglobal in scope
High:High: SO2 emissions travel
considerable distances
High:High: SO2 emissions are
regional. High concentration of plants across province
Multiple firms Multiple firms facing different facing different marginal marginal abatement costsabatement costs
Moderate:Moderate: Varying ranges of technology, emissions levels, and different management efficiencies
High:High: Firms have different technology and efficiency levels
Ability of firms Ability of firms to transfer to transfer burden of burden of pollution pollution abatement onto abatement onto consumersconsumers
Low:Low: Prices still highly regulated
High:High: Cement prices generally set by the market
Existence of Existence of competitive competitive marketmarket
Low:Low: Power plants not fully independent in decision making
Moderate:Moderate: Wide variety of ownership structure and many firms
The EPA’s Role in Cap-and-Trade The EPA’s Role in Cap-and-Trade Implementation in ChinaImplementation in China
Feasibility AreaFeasibility Area Change by Chinese CentralChange by Chinese CentralGovernmentGovernment
Feasibility of EPA’s Potential Feasibility of EPA’s Potential ImpactImpact
Political and Political and Regulatory Regulatory FeasibilityFeasibility
Reprioritize environmental protection
on par with economic development
Low-Moderate:Low-Moderate: The EPA must use whatever leverage available through its role as a U.S. government agency
AdministratiAdministrative ve FeasibilityFeasibility
Build human capitalModerate-High:Moderate-High: EPA should assist
with training, seminars, and hosting conferences to help build human capital
Increase incentives to break tiesbetween SEPA and industry
Economic Economic FeasibilityFeasibility
Create an industry sector made up of
multiple, independent firms
Low:Low: The EPA will have a limited role; technical assistance may increase deregulation
Summary of FindingsSummary of Findings
Cap-and-trade would not be successful in China under current conditions.
Significant changes would be necessary; it is unlikely that they will be implemented in the near future.
The EPA has little power to induce change in China to make cap-and-trade successful.
Final Recommendation and Final Recommendation and ConclusionConclusion
The EPA should focus on helping SEPA strengthen existing environmental command-and-control regulation.
A strong command-and-control foundation supports progression towards market-based instruments, and will provide immediate results in SO2 reduction.