- •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
12.2. Political-administrative arrangements
The PAAs of China's policy of import of solid waste represent the structured group of public and para-state actors who are responsible for its implementation. In a policy, for different outputs, there are different PAAs. Here the PAAs of the enterprises using imported solid waste will be discussed.
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.
Figure VIII: The PAA of licensing the enterprises using solid waste
Based on The Center of Administration of Solid Waste online information: http://ncswm.mep.gov.cn/wwwroot/gfmh/upload/Image/mrtp/2500834571.gif (in Chinese)
Figure IX: The PAAs of licensing the domestic consignees
Based on the online information of Raoping Entry-exit Inspection and Quarantine Bureau. Available at http://www.rp.gdciq.gov.cn/zxbs/bgxzspgk/201209/t20120912_19146.htm (in Chinese).
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. This can be explained by China's system of centrality.
12.3. The actors' games at the stage of policy programming – the example of China's Association of Plastics Processing Industry
In The Announcement No. 36 of 2007 issued by the State Council, it is stipulated that governments at various levels should authorize some responsibilities to associations of industries. When issuing the policies relevant to the development of industries, governments shall consult and discuss with the related associations of industries. Associations of industries should also keep up with the trends, improve their ways of working, conduct researches on industries so as to actively reflect the opinions of the enterprises, provide suggestions on industrial developments and law-making, and to participate in the drafting of laws, regulations, standards and plans related to industries, which will promote the industrial developments.91 Also, in The Announcement No. 126 of 2009 issued by The Ministry of Industry and Information Technology, there are details articles concerning the roles that the associations can play in formulating policies and standards of industries.92 These are institutional rules which enable associations of industries to participate in the programming stage of policies.
China's Association of Plastics Processing Industry (CAPPI) is funded in 1989 by the combined efforts of the enterprises using waste plastics. After more than 20 years of development, the membership has covered more than 2000 enterprises. The purpose of the Association is to study the industrial developments of waste plastics; to represent the interests of the industry of waste plastics recycling by proposing suggestions and requirements to governments; to monitor the operation of association members; and to provide technological guidance to enterprises as well as coordinate the development of the industry.93
According to the interviews with the Wang Wang, the Chief Secretary of CAPPI, the Association actively participated in consulting with the Ministry of Environmental Protection when the Ministry drafted The Rules on Environmental Protection of Import of Waste Plastics in 2012. They held sessions and consultation among member enterprises and public authorities in September, 2012. Moreover, they handed over a proposal to the Ministry of Environmental Protection by providing the authorities with the enterprises' first hand experiences of dealing with the recycling and reuse of waste plastics.94 At the same time, they also participated in the formulation of several standards of imported waste plastics, such as The Controlling Standards of Environmental Prevention of Reuse and Recycling of Waste Plastics (HJ/T 364-2007).
Therefore, from the above analysis, it can be shown that, at the stage of policy programming, based on the institutional rules of participation of associations of relevant industries, China's Association of Plastics Processing Industry, which represents the interests of target groups, employs the resources of information and organization to influence the policy product at this stage.
