- •Sustainability Assessment
- •Sustainability Assessment
- •Academic Press is an imprint of Elsevier
- •First published 2013
- •Notices
- •British Library Cataloguing-in-Publication Data
- •A catalogue record for this book is available from the British Library
- •Library of Congress Cataloging-in-Publication Data
- •A catalog record for this book is available from the Library of Congress
- •For information on all Academic Press publications visit our website at store.elsevier.com
- •List of Abbreviations
- •1 Sustainability Assessment of Policy
- •1.1 Introduction
- •1.2 Rationale
- •1.3 Understanding Discourses
- •2 Sustainability Climate of Policy
- •2.1 Introduction
- •2.2 Emergence of Policy Sustainability
- •2.2.1 Population and Resource
- •2.2.2 Modernity and Sustainability
- •2.3 Concept of Sustainability
- •2.3.1 Steady-State Economy
- •2.3.2 Carrying Capacity
- •2.3.3 Ecospace
- •2.3.4 Ecological Footprints
- •2.3.5 Natural Resource Accounting/Green Gross Domestic Product
- •2.3.6 Ecoefficiency
- •2.4 Sustainability Initiative
- •3 Characterizing Sustainability Assessment
- •3.1 Introduction
- •3.2 Resource System
- •3.3 Social System
- •3.4 Global System
- •3.5 Target Achievement
- •3.5.1 Detection of Changes
- •3.5.2 Determining Operation Scale
- •3.5.3 Harmonizing Operation Sequence
- •3.6 Accommodating Tradition and Culture
- •3.7 Selection of Instrument
- •3.8 Integration of Decision System
- •3.9 Responding to International Cooperation
- •4 Considerations of Sustainability Assessment
- •4.1 Introduction
- •4.2 Socioeconomic Consideration
- •4.2.1 Nature of Poverty
- •4.2.2 Nature of Resource Availability
- •4.2.3 Nature of Economy
- •4.2.4 Nature of Capital
- •4.2.5 Nature of Institutions
- •4.3 Consideration of System Peculiarities
- •4.3.1 Temporal Scale
- •4.3.2 Spatial Scale
- •4.3.3 Connectivity and Complexity
- •4.3.4 Accumulation
- •4.3.5 Nonmarketability
- •4.3.6 Moral and Ethical Considerations
- •4.4 Consideration of Component Peculiarities
- •5 Issues of Sustainability Assessment
- •5.1 Introduction
- •5.2 Issues Related to Society
- •5.2.1 Social Modernization
- •5.2.2 Societal Relationship
- •5.2.3 Radicalization and Convergence
- •5.2.4 Boserupian/Neo-Malthusian Issues
- •5.2.5 Social Ignorance
- •5.2.6 Social Attitudes
- •5.3 Issues Related to Policy Discourse
- •5.3.1 Discourses of Story Line
- •5.3.2 Discourses of Disjunction Maker
- •5.3.3 Discourses of Symbolic Politics
- •5.3.4 Discourses of Sensor Component
- •5.4 Issues Related to Actors
- •5.4.1 Influences of Macroactors
- •5.4.2 Positioning of Actors
- •5.4.3 Way of Arguing
- •5.5 Black Boxing
- •6 Components of Sustainability Assessment
- •6.1 Introduction
- •6.2 Social Adequacy
- •6.3 Scientific Adequacy
- •6.4 Status Quo
- •6.5 Policy Process
- •6.6 Policy Stimulus
- •6.7 Participation
- •6.8 Sectoral Growth
- •6.9 Resource Exploitation
- •6.10 Traditional Practices
- •6.11 Role of Actors
- •6.12 Framework Assessment
- •6.13 Scope Evaluation
- •6.14 Evaluation of Implementation
- •6.15 Instrument Evaluation
- •6.16 Structural Evaluation
- •6.17 Cause Evaluation
- •6.18 Cost Evaluation
- •6.19 Impact Assessment
- •6.20 Quantitative Approach
- •6.21 Anthropogenic Evaluation
- •6.22 Influence of Other Policies
- •7 Linkages of Sustainability Assessment
- •7.1 Introduction
- •7.2 Parallel Linkage
- •7.3 Linkage of Ascendancy
- •7.4 Linkage of Descendancy
- •7.5 Linkage of Hierarchy
- •7.6 Horizontal Linkage
- •7.7 Quasi-political Linkages
- •7.8 External Linkage
- •7.9 Market Linkage
- •7.10 Evaluation of Link to the Past
- •7.11 Actors and Story Line
- •7.12 Practices and Story Line
- •7.13 Reflection of Image of Change
- •7.14 Integrating Information
- •7.15 Forecasting
- •7.16 Assessing Options
- •7.17 Post-decision Assessment
- •8 Assessment of Policy Instruments
- •8.1 Introduction
- •8.2 Approaches of Implementation
- •8.3 Attributes of Instrument
- •8.4 Choice of Instruments
- •8.5 Instruments as a Component of Policy Design
- •8.6 Addressing the Implementation of Instruments
- •9 Social Perspectives of Sustainability
- •9.1 Introduction
- •9.2 Participation Evaluation
- •9.3 Process Evaluation
- •9.4 Retrospective Policy Evaluation
- •9.5 Evaluation of Policy Focus
- •9.6 Deductive Policy Evaluation
- •9.7 Comparative Modeling
- •9.8 Deductive Modeling
- •9.9 Optimizing Perspectives
- •9.10 Political Perspectives
- •10 Factors of Sustainability Assessment
- •10.1 Introduction
- •10.2 Actor as Policy Factor
- •10.3 Global Resource Factor
- •10.4 Local Resource Factors
- •10.5 Participation Factor
- •10.6 Participation Catalyst
- •10.7 Economic Factors
- •10.7.1 Influence of Macroeconomic Factors
- •10.7.2 Influence of Microeconomic Factors
- •10.7.3 Influence of Private Investment
- •10.7.4 Influence of Public Investment
- •10.7.5 Influence of Economic Incentives
- •10.8 Administrative Factor
- •10.8.1 Right and Tenure
- •10.8.2 Decentralization
- •10.8.3 Accessibility
- •10.9 Market Influence
- •10.10 Historical Factor
- •10.11 Other Factors
- •11 Tools for Sustainability Assessment
- •11.1 Introduction
- •11.2 Indicators for Evaluating Resource Dimension
- •11.2.1 SOR Indicators
- •11.2.2 NFR Indicators
- •11.2.3 Effectiveness Indicators
- •11.2.4 Comparing Indicators of Resources
- •11.2.5 Explanatory Variables
- •11.2.6 Tools for Assessing Human Dimension
- •12 Problems in Sustainability Assessment
- •12.1 Introduction
- •12.2 Boundary Problem
- •12.3 Problem with Social Concern
- •12.4 Role of Science
- •12.5 Institutional Difficulty
- •12.6 Implementation Problem
- •12.6.1 Circumstances External to the Implementing Agency
- •12.6.2 Inadequacy of Time, Resources, and Programs
- •12.6.3 Lack of Understanding Between Cause and Effect
- •12.6.4 Minimum Dependency Relationship of Decisions
- •12.6.5 Lack of Understanding of, and Agreement on, Objectives
- •12.6.6 Policy Tasks not Specified in Correct Sequence
- •12.6.7 Lack of Perfect Communication and Coordination
- •12.6.8 Rare Perfect Compliance of Implementing Body
- •13 Discussion and Recommendation
- •13.1 Discussion
- •13.2 Recommendation
- •13.3 Importance
- •Summary
- •References
CHAPTER 5
Issues of Sustainability Assessment
5.1INTRODUCTION
5.2ISSUES RELATED TO SOCIETY 5.2.1 Social Modernization
5.2.2 Societal Relationship
5.2.3 Radicalization and Convergence 5.2.4 Boserupian/Neo-Malthusian Issues 5.2.5 Social Ignorance
5.2.6 Social Attitudes
5.3ISSUES RELATED TO POLICY DISCOURSE 5.3.1 Discourses of Story Line
5.3.2 Discourses of Disjunction Maker 5.3.3 Discourses of Symbolic Politics 5.3.4 Discourses of Sensor Component
5.4ISSUES RELATED TO ACTORS
5.4.1Influences of Macroactors
5.4.2Positioning of Actors
5.4.3Way of Arguing
5.5 BLACK BOXING
5.1 INTRODUCTION
There are certain issues on the basis of which it is possible to identify the nature of policy sustainability. Environmental concern can be considered as the most important of all the issues. Initially, environmental problems were treated as an ad hoc or expost problem requiring some remedial measures. The understanding of environment as a structural problem was realized toward the end of 1980s, which resulted in an emergence of environmental discourse called
Sustainability Assessment. DOI: http://dx.doi.org/10.1016/B978-0-12-407196-4.00005-2
© 2013 Elsevier Inc. All rights reserved.
60 Sustainability Assessment
“ecological modernization” (Hajer, 1995). Ecological modernization assumed that existing environmental problems can be internalized by political, economic, and social institutions and can care for the sustainability. The concept of “ecological modernization” as introduced in the discourse of environmental sustainability can be outlined as follows:
1.It assumes that environmental degradation is calculable most notably by combining the monetary units and discursive elements from different branches of natural and social sciences of which cost benefit analysis of environment is one of the examples.
2.It assumes that effective management of environmental problems is possible by collective action; if every individual, firm, and at the larger arena if every country participates, management of sustainable environment is possible.
3.Economic growth and the resolution of ecological problems can be reconciled; that is, the discourse of environmental sustainability follows a utilitarian logic.
Sustainability thus covers a broader realm than that of environmental concerns which utilizes the basis of ecological modernization and observes the following few realms:
1.A shift in environmental policy measures. The old principle of “react and cure” has been replaced by an “anticipate and prevent” discipline.
2.Integration of compartmental division. Division of environmental boundaries through regional pact and/or international convention.
3.Inclusion of deregulation methods replacing the hierarchical legislative system involved in environmental management. The organization or institution itself will be responsible for environmental management. As a result, last few years have witnessed impact assessment, risk analysis, polluters pay principle, cost benefit analysis, precautionary principles, tradable pollution rights, levy of charges as well as debates on resource rent and emission taxes.
4.Influence of science in policy making. Science, as an evaluator of
damaging effects of environmental and social change, provides a basis for an exact input for policy making. For example, the concept of critical load and more benignly the concepts of multiple stress. The concept of multiple stress has transformed the
Issues of Sustainability Assessment |
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reductionist scientific view of “critical role” to orientalist idea of “integrated role” (NCEDR, 1998).
5.Replacement of unproductive investment at microeconomic level by anticipatory investment (e.g., filter technology in industries). At the microeconomics level, the shift toward environmental sustainability drives the idea of “environmental protection solely increases the cost” to the concept that “pollution prevention pays back.” The inclusion of the concept in the policy has led to promoting low and nonwaste technologies in developed countries and put forward the idea of “multivalued auditing” (success is measured not only in terms of money but also taking energy and usage into account).
6.Conceptualization of nature as “public goods” in the macroeconomic level. Nature used to be treated as “free goods.” Nature including forest was utilized as a sink, but under the present concept this cannot be done without paying for it. Therefore, externalization of economic costs of environmental pollution has been reduced and thereby, the concept can put a great emphasis on the conservation of natural resources by stimulating ecological pricing, recycling, reusing, and technological innovations.
7.Change in the characteristics of legislative discourse. Modern approaches assume that environmental sustainability of resources would depend how the price of the environment is included in the resource valuation (OECD, 1985). In this discourse frame, statistical prediction has become the basis for collective liability of policy sustainability.
8.Consideration of participatory practices. This concept seeks a plausible solution between the requirement of resources and minimization of problem. Therefore, it acknowledges the most proliferated and effective actors like NGOs.
These principles and objectives show that the policy climate for environmental sustainability could be pursued through ecological modernization. This could lead to the increased influence of science and decreased influence of legislative and regulatory system in policy climate. Understanding may take the place of compulsion in management. Thus, environmental sustainability possesses some special dimensions in policy climate that are important for considering transitions to policy evaluation. The following section presents a brief review of basic issues for policy evaluation.