The Ecological Scarcity Method for the European Union A Volkswagen Research Initiative: Environmental Assessments
This book is published open access under a CC BY 4.0 license. This report transfers the Ecological Scarcity Method (ESM) to the EU and its 28 member states. It provides a powerful tool for unbiased environmental assessments in enterprises and surveys the current impacts and the targets published by...
Autores principales: | , , |
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Formato: | Libro electrónico |
Idioma: | Inglés |
Publicado: |
Cham
Springer Nature
2017
Wiesbaden : 2018. |
Edición: | 1st ed. 2018. |
Colección: | AutoUni – Schriftenreihe,
105 |
Materias: | |
Ver en Biblioteca Universitat Ramon Llull: | https://discovery.url.edu/permalink/34CSUC_URL/1im36ta/alma991009425411706719 |
Tabla de Contenidos:
- Intro
- Acknowledgement
- Preliminary Remarks
- Table of Contents
- Table of Figures and Tables
- 1 Management Summary
- 2 Introduction
- 2.1 Method Description
- 2.2 Initial Situation and Aim of the Initiative
- 2.3 Objectives for European Data
- 2.4 Project Implementation
- 3 Methodological Bases
- 3.1 Ecological Scarcity Method
- 3.1.1 How does the ESM fit to the Phases of the ISO Standard?
- 3.1.2 What are the Elements of the ESM?
- 3.2 Basic Principle
- 3.2.1 How can the ESM be applied?
- 3.2.2 Which Requirement apply to the ESM and its underlying Data?
- 3.2.3 Coordination with Environmental Authorities
- 3.2.4 Requirements for European Eco Factors
- 3.3 Method
- 3.3.1 Requirements for European Eco Factors
- 3.3.2 What further Options are there for Applying the ESM?
- 3.3.3 How can Traceability be communicated?
- 3.3.4 What Transparency Rules need to be observed?
- 3.3.5 Basis for Assessment
- 3.3.6 Rules for Assessment
- 3.3.7 What must be borne in Mind when drawing up Assessment?
- 3.4 Methods
- 3.4.1 The ESM: Midpoint or Endpoint Method?
- 3.4.2 Does the ESM comply with ISO 14040:2006 and 14044:2006?
- 3.5 Responsible Use of Environmental Impact Assessments
- 3.6 Use of Data
- 3.6.1 Types of Impact under Consideration
- 3.6.2 Comparability of Eco Factors and Eco Points
- 4 Data Collection
- 4.1 Methodology
- 4.2 Principles for Deriving Eco Factors
- 4.3 Use for Characterization Factors
- 4.3.1 Determination of Normalisation
- 4.3.2 Determination of Weighting
- 4.3.3 Eco-Factor Determination
- 4.3.4 Temporal Aspects of the Eco-Factor Dermination/ Time Horizons
- 4.4 General Data Situation
- 4.4.1 Reccording the Actual State
- 4.4.2 Articulating Political Will
- 4.4.3 Discussion of Procedure
- 5 Results Type of Impact
- 5.1 Emission to Air
- 5.1.1 Greenhouse Gases
- 5.1.2 Characterization.
- 5.1.3 Preliminary Remarks on Air Pollutants
- 5.1.4 NMVOC
- 5.1.5 NO
- 5.1.6 SO
- 5.1.7 PM2.5
- 5.1.8 NH
- 5.2 Emissions Surface Water
- 5.2.1 Nitrogen (as N)
- 5.2.2 Phosphorus (as P)
- 5.2.3 Nickel
- 5.2.4 Zinc
- 5.2.5 COD
- 5.2.6 Lead
- 5.2.7 Cadmium
- 5.2.8 Copper
- 5.2.9 EPA-PAH16
- 5.3 Consumption of Resources
- 5.3.1 Freshwater Consumption
- 5.3.2 Primary and Renewable Energy Consumption
- 5.4 Waste Generation
- 5.4.1 Non-Hazardous and Hazardous Waste
- 5.5 Derived Data Sets for Individual EU Countries
- 5.5.1 References to Calculation in the Datasheets
- 6 Eco Factors for EU-28 and Member States
- 6.1 EU-28 (Regarded as one Environmentally Decision-Making Unit)
- 6.2 Data sets of the EU Member States
- 6.2.1 Austria
- 6.2.2 Belgium
- 6.2.3 Bulgaria
- 6.2.4 Croatia
- 6.2.5 Cyprus
- 6.2.6 Czech. Republik
- 6.2.7 Denmark
- 6.2.8 Estonia
- 6.2.9 Finland
- 6.2.10 France
- 6.2.11 Germany (for the purpose of comparision)
- 6.2.12 Greece
- 6.2.13 Hungary
- 6.2.14 Ireland
- 6.2.15 Italy
- 6.2.16 Latvia
- 6.2.17 Lithuania
- 6.2.18 Luxembourg
- 6.2.19 Malta
- 6.2.20 Netherlands
- 6.2.21 Poland
- 6.2.22 Portugal
- 6.2.23 Romania
- 6.2.24 Slovakia
- 6.2.25 Slovenia
- 6.2.26 Spain
- 6.2.27 Sweden
- 6.2.28 United Kingdom
- 7 Environmental Impact Calculation
- 8 Sources.