- •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
3.2 Five constituent elements of the pap of Germany’s policy of waste importation
Objective
In the Regulation No 1013/2006 of The European Parliament And of The Council of 14 June 2006 on Shipments of Waste, the objective can be found as follows, “the main and predominant objective and component of this Regulation is the protection of the environment, its effects on international trade being only incidental”.22
This aim shall be achieved by means of stringent operational conditions and technical requirements, through setting emission limit values for waste incineration and co-incineration plants within the Community and also through meeting the requirements of Directive 75/442/EEC.23
Evaluative element
Measurement systems shall be required to monitor the parameters of an installation and relevant emissions. Emissions to air and to water must be measured continuously or periodically in accordance with Article 11 and Annex III of the Directive 2008/98/EC of the European Parliament and of the Council of 19 November 2008 on waste and repealing certain Directives.24
Operational elements
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.
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
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.
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.
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 on them.
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.
PAA and resources
Competent authorities responsible for the implementation of the WSR are to be designated by the Member States, as provided for in Art. 53 WSR. In addition, Art. 54 WSR provides that each Member State has to designate at least one correspondent, responsible for cooperation in particular between the Member States and the EU Commission and also for informing or advising persons or undertaking. In Germany, the Federal Environment Agency (Umweltbundesamt) has been designated as Focal Point in accordance with Art.15 of Waste Shipment Act (Ger.) and competent authority for the authorization of the transit of wastes in accordance with Art.14 Para.4 of Waste Shipment Act (Ger.). The competent authorities designated for the import and export of wastes in the Federal States are the regional authorities (district governments or district administrations in North-Rhine Westphalia, Hesse and Bavaria). Most of the Federal States have designated only one authority.25
Procedural elements
The procedure of movement document (Joachim Wuttke, 2007)
