- •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
- •Hong Kong
- •3.2.1 Concrete objectives
- •3.1.4 Paa and resources
- •3.1.5 Procedural elements
- •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
3.1.4 Paa and resources
The elements of this part describe the competent public actors as well as specific institutional principles to the arrangement of a public policy. As for Mainland China, the relevant actors are mainly in three areas: transport, environment and development departments. At national level, there are Department of pollution prevention & control, which is dominated by Ministry of Environmental Protection of the People’s Republic of China, Ministry of transport of the People’s Republic of China as well as National Development and Reform Commission. At provincial and municipal level, there will also be correspondent-dominating departments in these three areas respectively.
Of course, distribution of resources like technology, monitoring equipment, personnel, finance, should also be well dealt with between departments, making sure every procedure under control. It is noteworthy that time management has also to be taken into consideration: e.g. the new national environmental law (Ambient air quality standards) was formulated in 2012, but actually it will not come into force until 2016.
3.1.5 Procedural elements
Procedural elements are the external shells or layers of the PAP, to implement a public policy, actors have the responsibility to acknowledge relevant principles of PAP, to ensure financial resources and services, so as to achieve good interaction between themselves and those groups who are affected.
The transparency of the exchange of information is worth notable especially in Mainland China that the public may have doubts to which extent and through which approach that citizens have rights to access to monitoring data. From the governmental documents of monitoring act, it is stated that the monitoring information will be published through both governmental website and mass media like television and broadcast.
Aarhus Convention (The UNECE Convention on Access to Information, Public Participation in Decision-making and Access to Justice in Environmental Matters) is an international convention, which grants people right to access to local or national information freely concerning environmental issues. It is a sign of democratic progress in public transparency and participation, which promotes better trust of political-administrative authorities among the public. It was adopted on 25th June 1998 in the Danish city of Aarhus, as of 2 April 2013, there were 47 Parties to the Convention, 32 Parties to the Protocol on Pollutant Release and Transfer Registers (PRTRs) and 27 Parties to the amendment on public participation in decisions on the deliberate release into the environment and placing on the market of genetically modified organisms (GMOs). Unfortunately, as for Mainland China, it neither signed to the convention nor it was ratified.
Hong Kong
3.2.1 Concrete objectives
The air quality standards in Hong Kong are also in a period of transition. The current Air Quality Objectives was set up by the Environmental Protection Department in 1987, under the regulation of Air Pollution Control Ordinance (APCO) (see Figure 3.6). However, Hong Kong is also proposing a new Air Quality Objectives at present, which tends to be into force from 2014. Figure 3.7 gives the comparison between the old and new AQOs.
Figure 3.7 Current Air Quality Objectives (Hong Kong, until 2014)
Pollutant |
Concentration in Microgrammes per Cubic Metre (μg/m3) |
||||
Averaging time |
|||||
1hr |
8hrs |
24hrs |
3mths |
1yr |
|
Sulphur Dioxide (SO2) |
800 |
— |
350 |
— |
80 |
Total Suspended Particulates (TSP) |
— |
— |
260 |
— |
80 |
Respirable Suspended Particulates (PM10) |
— |
— |
180 |
— |
55 |
Nitrogen Dioxide (NO2) |
300 |
— |
150 |
— |
80 |
Carbon Monoxide (CO) |
30000 |
10000 |
— |
— |
— |
Photochemical Oxidants (as ozone) |
240 |
— |
— |
— |
— |
Lead (Pd) |
— |
— |
— |
1.5 |
— |
Figure 3.8 Proposed New Air Quality Objectives (Hong Kong, from 2014)
