Material Resources, Productivity and the Environment
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Raw Materials Use Reduction, Replacement, and Recycling - Tong Qiu
ENVIRONMENT AND DEVELOPMENT- Vol. II - Raw Materials Use Reduction, Replacement, and Recycling - Tong Qiu RAW MATERIALS USE REDUCTION, REPLACEMENT, AND RECYCLING Tong Qiu Department of Chemical Engineering, Tsinghua University, Beijing, People’s Republic of China Keywords: Raw materials, reduction, substitution, replacement, recycling, ecomaterials, LCA (life-cycle assessment), LCED (life-cycle engineering design) Contents 1. The Direction of Development—Ecomaterials 2. Life-Cycle Assessment 2.1. Life-Cycle Engineering Design 3. Raw Material Substitutes and Conservation 3.1. The Place of Science and Technology 3.2. Developing Clean Technology 3.3. Replacing Non-Renewable Resources with Renewable Resources 3.4. Material Re-production 3.5. Substitutes for Raw Materials Bibliography Biographical Sketch Summary This article discusses the development of ecomaterials, which is a trend in material industrial development. Furthermore, life-cycle assessment, life-cycle engineering design, and methods of reducing and replacing raw materials are also presented. Natural resources are not inexhaustible, and there are limits in terms of quantity and time to acquiring raw materials from the natural world. Industrial progress, economic development, and population growth in the twentieth century has led people to exploit natural resources in a predatory manner. With regard to mineral resources, statistics indicate that the rate of mineral resources consumption has always been higher than the rate of population growth. For example, while the world’s population doubled between 1950 andUNESCO 1990, the products using the – major EOLSS six minerals (aluminum, copper, lead, nickel, tin, and zinc) increased more than eight times. Although shortage of resources cast a shadow over the twentieth century, there was no continuous shortage of mineral resources. -
The Case Study Report Aims to Analyse More in Depth the Strategies
Rebound effects and the ecological rucksack in the light of resource policies ESDN Case Study No. 7 Nisida Gjoksi ESDN Office Team www.sd-network.eu June 2011 Table of Contents INTRODUCTION ..................................................................................................................................3 RESOURCE EFFICIENCY AND THE REBOUND EFFECTS .........................................................................3 DEFINITION OF THE REBOUND EFFECT ......................................................................................................4 TYPES OF REBOUND EFFECT ...................................................................................................................4 POLICY RESPONSES ..............................................................................................................................4 MAGNITUDE OF REBOUND EFFECTS .........................................................................................................5 RECOMMENDATIONS ...........................................................................................................................5 RESOURCE EFFICIENCY AND THE ECOLOGICAL RUCKSACK .................................................................6 DEFINITION OF THE ECOLOGICAL RUCKSACK ..............................................................................................6 WEAKNESSES OF THE ECOLOGICAL RUCKSACK FACTOR .................................................................................7 REFERENCES .......................................................................................................................................9 -
From Dirty Oil to Clean Batteries
Transport & Environment Published: March 2021 In-house analysis by Transport & Environment Authors: Lucien Mathieu (Sections 1-5) and Cecilia Mattea (Section 6) Modelling: Lucien Mathieu Expert group: Julia Poliscanova, Alex Keynes, Thomas Earl Editeur responsable: William Todts, Executive Director © 2021 European Federation for Transport and Environment AISBL To cite this study Transport & Environment (2021), From dirty oil to clean batteries Further information Lucien MATHIEU Transport & E-mobility Analyst Transport & Environment [email protected] Mobile: +32 (0)4 83 08 48 91 Square de Meeûs, 18 – 2nd floor | B-1050 | Brussels | Belgium www.transportenvironment.org | @transenv | fb: Transport & Environment Acknowledgements The authors kindly acknowledge the external peer reviewers James Frith (Bloomberg NEF, Head of Energy Storage) and Hans Eric Melin (Founder of Circular Economy Storage). The findings and views put forward in this publication are the sole responsibility of the authors listed above. The same applies to any potential factual errors or methodology flaws. A study by 2 Executive Summary In light of the urgency to decarbonise the transport sector, batteries offer the best route to a carbon free road transport system and are the key technology underpinning the transition of road vehicles to zero emissions, freeing the sector from its dependency on fossil-fuels. With battery electric vehicles (BEV) expected to replace conventional cars in Europe, the demand in battery cells and battery raw materials like lithium, nickel and cobalt is set to grow in the coming years. But how can the demand for battery materials be met sustainably? And how does a battery-based road transport system compare to the current fossil driven road mobility? In this report T&E analyses forecasted supply and demand of battery cells and associated raw materials in Europe, looking at how recycling can reduce the need for battery primary materials. -
Vegetable Oil Processing
Pollution Prevention and Abatement Handbook WORLD BANK GROUP Effective July 1998 Vegetable Oil Processing Industry Description and Practices to 5,000 mg/l). Seed dressing and edible fat and oil processing generate approximately 10–25 m3 The vegetable oil processing industry involves of wastewater per metric ton (t) of product. Most the extraction and processing of oils and fats from of the solid wastes (0.7–0.8 t/t of raw material), vegetable sources. Vegetable oils and fats are which are mainly of vegetable origin, can be pro- principally used for human consumption but are cessed into by-products or used as fuel. Molds also used in animal feed, for medicinal purposes, may be found on peanut kernels, and aflatoxins and for certain technical applications. The oils may be present. and fats are extracted from a variety of fruits, seeds, and nuts. The preparation of raw materi- Pollution Prevention and Control als includes husking, cleaning, crushing, and con- ditioning. The extraction processes are generally Good pollution prevention practices in the indus- mechanical (boiling for fruits, pressing for seeds try focus on the following main areas: and nuts) or involve the use of solvent such as hexane. After boiling, the liquid oil is skimmed; Prevent the formation of molds on edible after pressing, the oil is filtered; and after solvent materials by controlling and monitoring air extraction, the crude oil is separated and the sol- humidity. vent is evaporated and recovered. Residues are Use citric acid instead of phosphoric acid, conditioned (for example, dried) and are repro- where feasible, in degumming operations. -
Material Flow Analysis of the Forest-Wood
Material flow analysis of the forest-wood supply chain: A consequential approach for log export policies in France Jonathan Lenglet, Jean-Yves Courtonne, Sylvain Caurla To cite this version: Jonathan Lenglet, Jean-Yves Courtonne, Sylvain Caurla. Material flow analysis of the forest-wood supply chain: A consequential approach for log export policies in France. Journal of Cleaner Produc- tion, Elsevier, 2017, 165, pp.1296-1305. 10.1016/j.jclepro.2017.07.177. hal-01612454 HAL Id: hal-01612454 https://hal.archives-ouvertes.fr/hal-01612454 Submitted on 6 Oct 2017 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. Material flow analysis of the forest-wood supply chain: a consequential approach for log export policies in France Jonathan Lengleta,∗, Jean-Yves Courtonneb,c,d, Sylvain Caurlae aAgroParisTech, France bSTEEP team, INRIA Grenoble - Rhˆone-Alpes,Montbonnot, France cUniversit´eGrenoble Alpes, France dArtelia Eau et Environnement, Echirolles, France eUMR INRA – AgroParisTech, Laboratoire d’Economie´ Foresti`ere, 54042 Nancy Cedex, France Abstract. Part of the French timber transformation industry suffers from difficulties to adapt to recent changes on global markets. This translates into net exports of raw wood and imports of transformed products, detrimental to both the trade balance and the local creation of wealth. -
A Preliminary Assessment of Raw Material Inputs That Would Be Required for Rapid Growth in Nuclear Generating Capacity
Nuclear Development July 2011 www.oecd-nea.org A Preliminary Assessment of Raw Material Inputs that Would be Required for Rapid Growth in Nuclear Generating Capacity NUCLEAR ENERGY AGENCY NEA/NDC(2011)15 ORGANISATION FOR ECONOMIC CO-OPERATION AND DEVELOPMENT The OECD is a unique forum where the governments of 34 democracies work together to address the economic, social and environmental challenges of globalisation. The OECD is also at the forefront of efforts to understand and to help governments respond to new developments and concerns, such as corporate governance, the information economy and the challenges of an ageing population. The Organisation provides a setting where governments can compare policy experiences, seek answers to common problems, identify good practice and work to co-ordinate domestic and international policies. The OECD member countries are: Australia, Austria, Belgium, Canada, Chile, the Czech Republic, Denmark, Estonia, Finland, France, Germany, Greece, Hungary, Iceland, Ireland, Israel, Italy, Japan, Luxembourg, Mexico, the Netherlands, New Zealand, Norway, Poland, Portugal, the Republic of Korea, the Slovak Republic, Slovenia, Spain, Sweden, Switzerland, Turkey, the United Kingdom and the United States. The European Commission takes part in the work of the OECD. OECD Publishing disseminates widely the results of the Organisation’s statistics gathering and research on economic, social and environmental issues, as well as the conventions, guidelines and standards agreed by its members. This work is published on the responsibility of the OECD Secretary-General. The opinions expressed and arguments employed herein do not necessarily reflect the official views of the Organisation or of the governments of its member countries. -
Gum Naval Stores: Turpentine and Rosin from Pine Resin
- z NON-WOOD FORESTFOREST PRODUCTSPRODUCTS ~-> 2 Gum naval stores:stores: turpentine and rosinrosin from pinepine resinresin Food and Agriculture Organization of the Unaed Nations N\O\ON- -WOODWOOD FOREST FOREST PRODUCTSPRODUCTS 22 Gum navalnaval stores:stores: turpentine• and rosinrosin from pinepine resinresin J.J.W.J.J.W. Coppen andand G.A.G.A. HoneHone Mi(Mf' NANATURALTURAL RESRESOURCESOURCES INSTITUTEIN STITUTE FFOODOOD ANDAN D AGRICULTUREAGRIC ULTURE ORGANIZATIONORGANIZATION OFOF THETH E UNITEDUNITED NATIONSNATIONS Rome,Rome, 19951995 The designationsdesignations employedemployed andand thethe presentationpresentation of of materialmaterial inin thisthis publication do not imply the expression of any opinionopinion whatsoever onon thethe partpart ofof thethe FoodFood andand AgricultureAgriculture OrganizationOrganization ofof thethe UnitedUnited Nations concernconcerninging thethe legal status of any countrycountry,, territory, city or areaareaorofits or of its auauthorities,thorities, orconcerningor concerning the delimitationdelirnitation of itsits frontiers or boundaries.boundaries. M-37M-37 IISBNSBN 92-5-103684-5 AAllll rights reserved.reserved. No part of this publication may be reproduced, stored in a retrretrievalieval systemsystem,, oror transmitted inin any form or byby anyany means,means, electronic,electronic, mechanimechanicai,cal, photocphotocopyingopying oror otherwise, withoutwithout thethe prior permission ofof the copyright owner. AppApplicationslications forfor such permission,permission, with a statementstatement -
Adaptive Model Building Framework for Production Planning in the Primary Wood Industry
Article Adaptive Model Building Framework for Production Planning in the Primary Wood Industry Matthias Kaltenbrunner * , Maria Anna Huka and Manfred Gronalt Institute of Production and Logistics, Department of Economics and Social Sciences, BOKU–University of Natural Resources and Life Science, Feistmantelstrasse 4, 1180 Vienna, Austria; [email protected] (M.A.H.); [email protected] (M.G.) * Correspondence: [email protected] Received: 29 October 2020; Accepted: 23 November 2020; Published: 26 November 2020 Abstract: Production planning models for the primary wood industry have been proposed for several decades. However, the majority of the research to date is concentrated on individual cases. This paper presents an integrated adaptive modelling framework that combines the proposed approaches and identifies evolving planning situations. With this conceptual modelling approach, a wide range of planning issues can be addressed by using a solid model basis. A planning grid along the time and resource dimensions is developed and four illustrative and interdependent application cases are described. The respective mathematical programming models are also presented in the paper and the prerequisites for industrial implementation are shown. Keywords: production planning; sawmill; modelling framework; mathematical programming; integrated planning 1. Introduction In production planning, the quantities to be produced are planned taking into account capacities, processes, the availability of raw materials and demanded products. In the primary wood industry, logs are used as raw materials in sawmills and processed into many intermediate products for further processing. These value-adding processes are usually carried out at one location. Three different value-added stages—sawing, drying and planing—are performed by a sawmill. -
MATERIAL INTENSITY of the ECONOMY Consumption and Material Consumption Core Indicator Production Patterns
MATERIAL INTENSITY OF THE ECONOMY Consumption and Material Consumption Core indicator Production Patterns 1. INDICATOR (a) Name: Material Intensity of the Economy. (b) Brief Definition: Ratio of Domestic Material Consumption (DMC) to Gross Domestic Product (GDP) at constant prices. (c) Unit of Measurement: Kilograms per $1,000 of GDP. (d) Placement in the CSD Indicators Set: Consumption and Production Patterns/Material Consumption. 2. POLICY RELEVANCE (a) Purpose: The indicator provides a basis for policies to increase the efficient use of raw materials in order to conserve natural resources and reduce environment degradation resulting from primary extraction, material processing, manufacturing and waste disposal. (b) Relevance to Sustainable/Unsustainable Development (theme/sub-theme): Improving the efficiency with which materials are used and consequently reducing stresses on the environment are the subjects of chapter 4 of Agenda21, Changing Consumption Patterns. Primary extraction of raw materials, processing of the materials into products, and ultimate disposal of the waste material has major environmental impacts. Reducing the material intensity of production and consumption of goods and services is essential to environmental protection and resource conservation. Reductions in intensity of material use can be achieved by more efficient use of natural resources in production and consumption, by recycling used and waste material, and by shifts in consumption patterns to less material intensive goods and services. The indicator allows an analysis of consumption of natural resources, as well as trends in recovery and recycling. Per-capita consumption of the materials could also be determined, facilitating the interpretation of trends in material intensity. The indicator can also be used as a proxy for assessing trends in industrial pollution. -
Resource Productivity As Sustainability Indicator May Need Developing Resource Productivity Has Become a Popular Indicator of Environmental Sustainability
26 May 2011 Resource productivity as sustainability indicator may need developing Resource productivity has become a popular indicator of environmental sustainability. However, new research has demonstrated that it is influenced by national income and its current use tends to support a simultaneous growth in economic productivity and resource consumption. In order to shape policy effectively, the study suggests that targets should directly emphasise resource consumption and emissions. In order for environmental policy to set effective targets, representative indicators of sustainability are needed. ‘Resource productivity’ is the Gross Domestic Product (GDP) output per resource input (measured in tonnes). It is interpreted as a sign of efficient use of resources and is now used widely as an indicator of environmental sustainability. However, there are some concerns about how this measure is used and interpreted. The researchers conducted an international study of resource productivity for a range of resources in the year 2000. They measured the income elasticities of resource consumption, i.e. the degree that resource consumption varies with national income. They divided resources into the categories of biomass, fossil fuels and ‘other’ (which includes hydraulic and nuclear energy, construction materials and ores and industrial minerals). The results indicated that the consumption of fossil fuels has a high income elasticity, which means that as the national income increases, so too does fossil fuel consumption. However, biomass consumption is inelastic and does not vary with income. Consumption in the ‘other’ category has an intermediate income elasticity. Further analysis indicated that if resource consumption varies with income, resource productivity does not. This is most likely because resource productivity is calculated by dividing income by consumption, so if consumption is proportional to income, there will be no variation in productivity. -
Measuring Resource Productivity a Background Paper by David Pearce
measuring resource productivity a background paper by David Pearce for the Department of Trade and Industry & Green Alliance conference: Revolutionising resource use: measuring radical improvements in resource productivity London, 14 February 2001 “green alliance... This paper is intended as a brief background 'benchmark' paper to assist with discussion of the notion of resource productivity.A far more detailed paper, prepared for DG Environment of the European Commission, and titled Public Policy and Natural Resources Management: a Framework for Integrating Concepts and Methodologies for Policy Evaluation, is available on the Commission's web site at www.europa.eu.int/comm/environment/enveco/s tudies2.htm, or by contacting the author at [email protected] extended paper deals with related notions such as 'sustainable consumption', 'sustainable development', 'ecological footprints', 'environmental space', 'genuine savings' etc. which are not addressed here. David Pearce David Pearce, Department of Economics, University College London and OXERA Ltd, Oxford. Department of Trade and Industry Department of Trade and Industry Environment Directorate 151 Buckingham Palace Road London SW1W 9SS tel: 020 7215 1975 fax: 020 7215 1621 e-mail: [email protected] contents web: www.dti.gov.uk/sustainability/ preface 1 Green Alliance summary of key issues and options 2 Green Alliance 1 defining resource productivity 3 40 Buckingham Palace Road London SW1W 0RE 2 is the notion of resource tel: 020 7233 7433 fax: 020 7233 9033 productivity new? 3 e-mail: [email protected] 3 why raise resource productivity? 3 web: www.green-alliance.org.uk 4 How far can resource productivity be raised? 4 Green Alliance is a registered charity number 1045395. -
Vegetable Oil Processing
AP42 Section: 9.1 1.I Title: Vegetable Oil Processing Comments and letters from industry 1995 MIDWEST RESEARCH INSTITUTE Suite 350 401 Harrison Oak Boulevard Cery. North Carolina 27513-2412 Telephone (919) 6774249 FAX (919) 6774065 Date: May 20, 1996 Subject: Site Visit -- Cargill Emission Factor Documentation for AP-42, Section 9.11.1 EPA Contract No. 68-D2-0159;MRI Project No. 4602-03 From: Tom Lapp To: AP-42 Section 9.11.1 Project File I. Purpose The purpose of the visit was to briefly review comments from the National Oilseed Processors Association (NOPA) and to conduct a walking tour of the soybean crush plant. This information will be incorporated into the revision of the background report and AP-42 Section 9.11.1, Vegetable Oil Processing. 11. Place and Date Cargill, Incorporated River Road, Box 2309 Fayetteville, North Carolina 28302 August 2, 1995 111. Attendees NationaPOilseed Processors Association David C. Ailor Director of Regulatory Affairs Washington, DC Carsill, Inc. Ron Moeller Assistant General Superintendent Operations and Engineering Minneapolis, MN Tom Richardson Plant Superintendent Fayetteville, NC U. S. Environmental Protection Asency Dallas Safriet, EFIG Ron Ryan, EFIG Roy Huntley, EFIG Midwest Research Institute (MRII Tom Lapp IV. Discussion The visit as held primarily to conduct a walking tour of the facility in order to observe the actual processing steps in operation. Prior to the tour, a brief meeting was held to discuss general information on the soybean processing industry and to review suggested NOPA process diagrams for incorporation into the final report. This discussion presents information on the soybean processing industry and a description of the refining of edible soybean oil.