- •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
Intervention Hypothesis
Intervention Hypothesis 1: If political-administrative actors would like to oblige the producer, the brokers, the consignees, the facilities to ensure that any waste they ship is managed without endangering human health and in an environmentally sound manner throughout the period of shipment, the political-administrative actors should divide waste into three categories: waste for disposal, green-listed waste for recovery and hazardous waste for recovery.
Intervention Hypothesis 2: If political-administrative actors would like to oblige the producer, the brokers, the consignees, the facilities to ensure that any waste they ship is managed without endangering human health and in an environmentally sound manner throughout the period of shipment, the political-administrative should ban the import of solid waste for disposal from other countries except from states which are Parties of the Basel Convention, members of EFTA and Parties to the Basel Convention, or with which the EU or individual Members States has or have concluded bilateral or multi-lateral agreements or arrangements
Intervention Hypothesis 3: If political-administrative actors would like to oblige the producer, the brokers, the consignees, the facilities to ensure that any waste they ship is managed without endangering human health and in an environmentally sound manner throughout the period of shipment, the political-administrative actors should oblige them to acquire consent after written notification for importing hazardous waste for disposal or recovery.
Intervention Hypothesis 4: If political-administrative actors would like to oblige all the target groups to ensure that any waste they ship is managed without endangering human health and in an environmentally sound manner throughout the period of shipment, the political-administrative actors should oblige them to file the movement document.
Intervention Hypothesis 5: If political-administrative actors would like to oblige all the brokers to ensure that any waste they ship is managed without endangering human health and in an environmentally sound manner throughout the period of shipment, the political-administrative actors should oblige them to acquire a license.
Intervention Hypothesis 6: If political-administrative actors would like to oblige transporters to ensure that any waste they ship is managed without endangering human health and in an environmentally sound manner throughout the period of shipment, the political-administrative actors should oblige them to acquire a license.
Intervention Hypothesis 7: If political-administrative actors would like to oblige operators of facilities to ensure that any waste they dispose or recovery without endangering human health and in an environmentally sound manner, the political-administrative actors should oblige them to acquire a permit of operating.
The triangles of actors of Germany’s policy
2.3 Comparative studies
The political problem definition of China’s policy of importation of solid waste, which can be found in the Measures of administration of import of solid waste, issued by the five ministries of China13, is built by political-administrative actors.
The political problem of Germany’s policy of import of waste is built by the analysts through referring to the problem definition of EU’s policy.14
Country |
China |
Germany |
Problems |
Environmental problem Public health problem Resource wasting problem Unhealthy development of domestic recling industry problem |
Environmental problem Public health problem Resource wasting problem |
China put more emphasis on the problem of unhealthy development of the recycling economy, which can be illustrated by the fact that building the recycling economy is a very important part of China’s “12th Five-Year Plan”.15
There are some differences between the beneficiary groups of the policies of the two countries.
Firstly, in China’s policy of import of solid waste, the beneficiary groups also include the enterprise using imported solid waste in an environmentally way, which is also one of the target groups. As the cost of the enterprises using imported solid waste without any prevention of environmental pollution is much lower than that of the enterprises using imported solid waste in an environmentally way, which will put the latter in a disadvantage position in the market.
Secondly, the beneficiary groups of Germany’s policy not only includes the residents living around the facilities disposing or recovering waste, but also those who are under the risk of being exposed to the pollution caused by the transportation of waste.
In the two countries, there are cases in which residents demonstrate against the pollution caused by the imported waste.16
Also the unions of enterprise using solid waste or facilities will also try to influence the political definition of problem.
In Germany, green party will also use the political power to influence the political definition of problem.
Concerning the differences between the Causal Hypothesis of the two countries, the transporters is also included in the target group of Germany’s policy, as the road systems of European Union is so advanced, transport also should be controlled.
Concerning the intervention hypothesis, all the instruments of the two policies are in regulatory models. However, China’s political administrative actors produce more kinds of outputs.
PAP
