- •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
6.2 Germany’s output of written consent of shipment of waste
The perimeter:
There is a website specially designed indicating the designated “pre-consented recovery facilities” by their competent authorities within OECD countries33. And this corresponds with the action plan based on functional criteria.
The institutional content:
In usual cases, the validity of consent lasts 1 year and has to be reapplied afterwards. But according to the European Council Decision34, the maximum validity for the consent with pre-consented recovery facilities could be 3 years.
Degree of formalization:
According to the decision of OECD countries, only the competent authority of transit can give its consent in a tacit way while the other two counterparts have to give their feedback in writing. Therefore, we consider the output as formal.
The status:
Due to the fact that after the notification process, there still exists a movement document procedure before getting the final certification, we consider the output of consent as intermediary.
Coherence within the policy:
The competent authority of dispatch and transit has to inform the other two parties each time they require additional documentation and information. This means that although the whole process would not go through any public department at national level, the three political-administrative actors need sufficient communication among them. And as stated above, our group believes that some kind of quota decided at national level, which means coherence vertically still exists though not proved by official documents.
The degree of coordination with other public policies:
Similar to the situation of the Chinese case, the idea of protecting the environment through regulating solid waste importation means crash with economic policies and other policies aiming at decreasing unemployment. Due to the fact that European countries put much emphasis on safe transportation of solid waste for historical reasons and even issue special certificate for transportation, certain coordination with transportation policies is expected.
6.3 Comparative studies
The outputs of both the countries are very formal. It will take much time and resources for administrations as well as the beneficiaries to settle all these kinds of paperwork and it will cost more when some information is not complete.
Evaluative Statements
7.1 Evaluating China’s output of licensing solid waste
The dimensions of evaluating the output of licensing the enterprise using solid waste
Other independent variants
A. The macro environment of global waste trade
The macro environment of global waste trade, including higher global price of solid waste, competition from other import countries, as well as decreasing provision of solid waste from developed countries due to economic crisis can also leads to the impact of the shutdown of small and home workshop enterprises.
B. Other Domestic policies: recycled economy policy, infrastructure policy and transportation policy
The policy of recycled economy can produce the output of subsidy to the environmental-friendly equipment and technologies, which will lead to impact on enterprises to invest more in environmental-friendly equipment and technologies
In General Report of China’s Environment of 2011 issued by China’s Ministry of Environmental Protection35, we can know that 14844 licenses were authorized to 2913 enterprises in the year of 2011. Therefore this evaluative statement focus on the output, that is, the question of “doing something”.
