- •Public Policy Analysis
- •IMpa Grands exercices de cours
- •1. Introduction 99
- •The Analysis of China’s Policy of Importing Solid Waste Zhanyu Li
- •1. Introduction 99
- •1. Introduction 99
- •8. Conclusion 129
- •Introduction
- •1.1 The choice of policies and countries
- •1.2 Short history of China’s policy of waste importation
- •1.3 Short history of Germany’s policy of waste importation
- •The Political Definition of the Problem
- •2.1 China’s political definition of the problem
- •Intervention hypothesis
- •2.2 Germany’s political definition of the problem
- •Intervention Hypothesis
- •2.3 Comparative studies
- •3.1 Five constituent elements of the pap of China’s policy of waste importation
- •3.2 Five constituent elements of the pap of Germany’s policy of waste importation
- •3.3 Comparative studies
- •China’s paAs
- •The paa of licensing the domestic consignees
- •4.2 Germany’s paAs
- •4.3 Comparative studies
- •5.1 China’s aPs
- •5.2 Germany’s aPs
- •5.3 Comparative studies
- •The outputs
- •6.1 China’s output of licensing enterprises using solid waste
- •6.2 Germany’s output of written consent of shipment of waste
- •6.3 Comparative studies
- •Evaluative Statements
- •7.1 Evaluating China’s output of licensing solid waste
- •7.2 Evaluating Germany’s output of consent
- •7.3. Comparative Studies
- •Conclusion
- •References
- •The Analysis of China’s Policy
- •Of Importing Solid Waste
- •Zhanyu Li
- •Abstract
- •Research Background
- •1.1 The definition of solid waste
- •1.2. The double-edged solid waste
- •1.3. The global waste trade
- •1.4. International conventions and agreements
- •Research Rationale
- •Literature Review and Conceptual Framework
- •3.1 The literatures on solid waste
- •3.2. The literatures on China’s import of solid waste
- •3.3. Conceptual framework
- •Research questions
- •Data Collection and Methodology
- •The overall description of solid waste imported by China
- •The driving force behind China's import of solid waste
- •7.1 The imported solid waste can mitigate the domestic lack of resources.
- •7.2. The cheap labour resources in China
- •7.3. The needs arising from certain industries
- •7.4. The underdeveloped domestic collecting system
- •7.5. Low shipping costs
- •The challenges facing Chinese public authorities
- •8.1. The transferring, renting and faking of import license.
- •8.2. The waste trafficking
- •8.3. The lack of public awareness of significance of imported solid waste
- •8.4. The inadequacy of technologies, personnel and other public resources
- •8.5. The secondary environmental pollution caused by inappropriate use of
- •Imported solid waste
- •The evolution of Chinese policies of importing solid waste
- •The current regimes of regulating import of solid waste
- •10.1. The competent authorities
- •10.2. The legal framework
- •Political agenda setting
- •Policy Programming
- •12.1. Political-administrative programs
- •12.2. Political-administrative arrangements
- •12.3. The actors' games at the stage of policy programming – the example of China's Association of Plastics Processing Industry
- •Policy implementation
- •13.1. Action plans
- •13.2. The operational analysis of aPs of enclosed management zone
- •Implementation acts (outputs)
- •14.1. Operational analysis of implementation acts
- •14.2. The Game of Policy Actors at the Stage of Policy Implementation- The example of the implementation of policy of imported solid waste at Luqiao District of Taizhou City.
- •Evaluating policy effects
- •15.1. The dimensions of evaluating the policy of import of solid waste
- •15.2. Data collections
- •15.3. Other independent variants
- •Appendix I
- •References
- •Introduction
- •Causal Model
- •2.3 Comparative discussions
- •Causal hypothesis
- •Political-administrative Program (pap)
- •Mainland China
- •3.1.1 Concrete objectives
- •3.1.2 Evaluative elements
- •3.1.3 Operational elements
- •3.1.4 Paa and resources
- •3.1.5 Procedural elements
- •Hong Kong
- •3.2.1 Concrete objectives
- •3.2.2 Evaluative elements
- •3.2.3 Operational elements
- •3.2.4 Paa and resources
- •3.2.5 Procedural elements
- •3.3 Comparisons between Mainland China and Hong Kong
- •Political-administrative Arrangement (paa)
- •4.1 Mainland China
- •4.2 Hong Kong
- •4.3 Comparisons between Mainland China and Hong Kong
- •Action plan (ap)
- •5.1 Mainland China
- •5.3 Comparisons between Mainland China and Hong Kong
- •Outputs
- •Mainland China (Beijing)
- •6.1.1 Output one: Restrictions on the last digit of vehicle plate numbers
- •6.1.2 Output two: Lottery systems for new car plates
- •Hong Kong
- •6.2.1 Output one: Improvement of the interchange between private and public transport modes.
- •6.2.2 Output two: Use of Alternative Fuel Vehicles to replace Diesel Vehicles
- •6.3 Comparisons between Mainland China and Hong Kong
- •6.3.1. Strategies
- •6.3.2. Six dimensions of the analysis of the outputs
- •Evaluative statement
- •7.1 The evaluative statement in Beijing
- •7.2 The evaluative statement in Hong Kong
- •7.3 Comparative discussion
- •Conclusion
- •References
3.3 Comparative studies
The legal basis of PAP of China’s policy includes laws, ordinances and measures at both national and local level.
National level |
The Revised Law of the People's Republic of China on the Prevention and Control of Environmental Pollution Caused by Solid Waste (2005) The Measures on Administration of Import of Solid Waste (2012) The Measures on Implementation of Registration of Foreign Suppliers (2009) |
Provincial level |
The Revised Law of Guangdong Province of the People's Republic of China on the Prevention and Control of Environmental Pollution Caused by Solid Waste (2005) The Measures on Administration of Import of Solid Waste of Guangdong Province (2012) The Measures on Implementation of Registration of Foreign Suppliers of Guangdong Province (2009) |
Municipal level |
The Measures on Administration of Import of Solid Waste of Taizhou City (2012) The Measures on Implementation of Registration of Foreign Suppliers of Taizhou City (2009) |
The legal basis of PAP of Germany’s policy includes European law, German federal law, the regional laws of the federal states and the statutes of the local authority waste management services. It is also based on the precautionary principle, the polluter-pays principle and the principle of co-operation. The main pillar is the Closed Substance Cycle and Waste Management Act. This act will be further developed by the end of 2010 on the basis of the new EU Waste Framework Directive in order to strengthen waste prevention and recovery.
PAP of China’s policy is a framework program with diverse implementation. Such regimes enable the development of very different implementation approaches at local levels; it is also a centralized PAP, as the essential part of the PAP will be assigned at national level. In a word, the PAP of this policy corresponds to a mixed PAP, which combines concrete objectives, evaluative element, operational elements, and a concrete definition of the organization and procedure.
In contrast, PAP of Germany’s policy is a detailed program with homogeneous implementation. The PAP of this policy tends to be corresponded to the substantive model, as it clearly articulates the objective, operational element, as well as procedure, but leave local level to decide the competent authority.
PAAs
China’s paAs
China’s PAA of licensing the enterprise using solid waste
The paa of licensing the domestic consignees
The enterprise using imported solid waste shall submit a written application attached by the environmental assessment report and related documents to the local environmental protection department.
The local environmental department shall examine the application documents concerning the completeness and contents. After the examination, the local environmental protection department sends their decision and all the documents to the provincial level of environmental department, who shall then examine the decision and documents and send their decision and the documents to the Waste Import Registration Management Center.
In the Waste Import Registration Management Center, all the decisions and documents will be carefully examined according to related laws, regulations and ordinances. After the examination, the center shall put their decision on the official website of the ministry of environmental protection. After three days of public notification, the center shall then send their decision and public opinion to the ministry of environmental protection, where the final decision will be made.
The ministry of environmental protection shall issue the permit to the Waste Import Registration Management Center, who shall then mail the permit and charge bill to the enterprise directly or to the provincial level of environmental protection department, who will then send the permit and charge bill to the enterprise.
From above analysis, China’s PAA of licensing the domestic consignees is PAA of multiple actors. The main responsibility, including the horizontal and vertical cooperation falls on the shoulder of Inspection and Quarantine Bureau at provincial level. Therefore, it is a centralized PAA.
