- •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. Conceptual framework
In this thesis, the concepts proposed by Peter Knoepfel in his work public policy analysis will be adopted to understand China's policy of importing solid waste.
In the work of Public Policy Analysis, a public policy is defined as a set of decisions and activities resulting from the interaction between public and private actors, whose behavior is influenced by the resources at their disposal, the general institutional rules (that is, the rules concerning the overall functioning of the political system) and specific institutional rules (that is, the rules specific to the area of intervention under scrutiny).
In the basic triangle of the policy actors proposed by Knoepfel, the political-administrative authorities who are vested with public authority, target groups (the actors whose behaviour is politically defined as the (in)direct cause of a problem or who are able to take action to deal with it), and end beneficiaries (actors who experience the negative effects of a particular problem and whose situation should be improved following the implementation of public intervention), these different types of actors, constitute the three points of the triangle. Actors affected indirectly by policy (third parties constituting either negatively affected third parties or positively affected third parties) are located at the peripheries of two of these three poles.
The causal hypothesis provides a political response to the question as to who or what is guilty or objectively responsible or able to make changes to enable the collective problems to be resolved. Thus, the definition of the causal hypothesis of a policy consists in designating the policy target groups and the end beneficiaries.
The intervention hypothesis establishes how the collective problem requiring resolution can be mitigated and, indeed, resolved by a policy. It defines the methods of government action that will influence the decisions and activities of the designated target groups so that these will be compatible with the political aims. Thus the state can compel them to change their behavior, induce a change of behaviors by positive or negative economic incentives, or again suggest it through the manipulation of symbols and information.
The availability of different resources to the actors involved in a policy process, their production, management, exploitation, combination, and even their substitution or exchange, can exert a significant influence on the processes, results and effects of a policy. The book mainly proposes the following types of resources: force, law, personnel, money, information, organization, consensus, time, infrastructure, political support.
Thus, a policy process can be interpreted in terms of the following four main stages: (1) the stage of political agenda setting, that is, the placing of the problem to be resolved on the governmental agenda; (2) the stage of policy programming, that is, the legislative and regulatory programming of the public intervention; (3) the stage of policy implementation, that is, the implementation of the political-administrative program (PAP) by means of action plan (APs) and formal acts (outputs); and (4) the stage of policy evaluation, that is, the evaluation of the resulting effects (impacts and outcomes).
Therefore, there are six products in the four stages of a policy process.
Figure III:The policy cycle of four stages (Knoepfel, 2011)
In the analysis model proposed by Peter Knoepfel, the substantive and institutional dimensions of policy products are variables to be explained, while the actors' game, the resources and the institutional rules are explanatory variables. Besides, there are two postulates. Firstly, the substantive and institutional results of a policy stage (for example, the PAP and PAA) directly influence the results of the following stages (for example, the APs and formal implementation acts). Secondly, during each stage, the public policy actors resort to institutional rules and combination of resources to influence the results of the stage in question if necessary even deviating from the results of the previous stages.
