Lead, Cadmium and Mercury Flow Analysis – Decision Support for Austrian Environmental Policy

Total Page:16

File Type:pdf, Size:1020Kb

Lead, Cadmium and Mercury Flow Analysis – Decision Support for Austrian Environmental Policy originalarbeit Hubert Reisinger 1, Gerald Schöller 2, Thomas Jakl ³, Raimund Quint ³, Brigitte Müller2, Alarich Riss 1 and Paul H. Brunner 2 Lead, Cadmium and Mercury Flow Analysis – Decision Support for Austrian Environmental Policy Summary: This paper discusses the sup- nen Datenlücken und widersprüchliche historic and existing material flows, stocks, port for environmental policy decisions Angaben aus unterschiedlichen Quellen emissions, and hot spots for which action that can be provided by substance flow entdeckt und fehlende Daten errechnet is most urgent. Such factual bases already analysis (SFA). Flows and stocks of lead werden. Zum anderen – und dies ist von have been provided for many substances (Pb), cadmium (Cd) and mercury (Hg) are besonderer Bedeutung für die Entschei- by substance flow analyses (SFA). To men- investigated through the Austrian eco- dungsfindung in der Umweltpolitik – ver- tion but a few: nomy and environment. Two advantages mittelt die SFA ein vollständiges Bild bei ■ ■ A pioneering MFA study on the histo- of SFA are emphasized: first, because SFA voller Transparenz. Sie ist ein nützliches rical pollution by heavy metals and is based on the law of conservation of Instrument zur Sichtbarmachung der Ge- PCBs in the Hudson River Basin was mass, input and output flows of processes samtauswirkungen von umweltpolitischen published by Ayres and Ayres in 1988. have to be balanced. This balancing prin- Maßnahmen – wie etwa Integrierte ■ ■ Stigliani et al. 1993 assessed the lead ciple allows identifying data gaps and con- Produktpolitik, Konsumentenschutz, pollution in the river Rhine basin by a tradicting information supplied by diffe- Emissionskontrolle und Abfallwirtschaft – material flow approach. rent sources, and helps to calculate missing auf die Wirtschaft eines Landes and seine ■ ■ Brunner 1998 investigated in the EU FP data. Second and most important for envi- Umwelt. Die SFA hilft auch, Gefahren- 4 project MAcTEmPo the potential of ronmental policy making, SFA gives the herde festzustellen, die zusätzliche SFA as a tool for decision making in en- “whole picture and full transparency”. It is Maßnahmen notwendig machen, um den vironmental policy. Imports and ex- instrumental in showing the combined ef- Druck auf die Umwelt zu reduzieren bzw. ports of all goods and selected substan- fect of different environmental policy mea- sekundäre anthropogene Lager zu nutzen. ces were assessed on the urban, sures such as integrated product policy, Die mittels SFA erhaltenen Daten sind regional and national level, and the an- consumer protection, emission control, sorgfältig auszuwerten, damit zwischen thropogenic material stocks investiga- and waste management on the economy nützlichen und schädlichen Stoffflüssen ted. As a result, implications such as of a country and its environment. SFA also und Lager unterschieden werden kann, the link between urban metabolism helps to identify hot spots for which addi- z. B. wenn Stoffe, die große Mengen an ge- and emissions, and the accumulation tional measures are required to reduce en- fährlichen Schwermetallen enthalten, of new anthropogenic resources were vironmental pressure or to make use of se- einer Wiederverwertung zugeführt wer- identified. condary anthropogenic stocks. SFA results den sollen. Um eine breite Basis für die ■ ■ Helmers et al. 1995 documented a lead must be carefully interpreted in order to zukünftige Gestaltung der Umweltpolitik contamination decrease in the German distinguish between beneficial and harm- zu erhalten, muss die quantitative SFA urban environment for the period 1972 ful flows and stocks, e. g. when materials durch qualitative Informationen sowie to 1992 of about 85 %. are recycled that contain large amounts of durch zusätzliche Beurteilungshilfen ■ ■ Svidén and Jonsson 2001 analyzed hazardous heavy metals. For a compre- ergänzt werden. mercury flows through the City of hensive base to design future environmen- Stockholm showing the trends for the tal policy, quantitative SFA needs to be period 1795 to 1995, identifying hitherto amended by qualitative information, and unknown mercury sources and show- by additional assessment tools. 1. Introduction ing that already emitted amounts of mercury exceeds the amount of mer- Stoffflussananlyse von Blei, Kadmium In industrialized countries, the last two cury still in anthropogenic stock by a und Quecksilber – Entscheidungshilfe centuries were characterized by the intro- factor of 30. für die österreichische Umweltpolitik duction and use of increasing amounts of ■ ■ Spatari et al. 2005 documented the US heavy metals. The utilization of these me- copper flow for the 20th century, in or- Zusammenfassung: Im vorliegenden Ar- tals in a wide range of products resulted in der to understand how and in what tikel wird die Stoffflussanalyse (SFA) als large economic benefits due to the new proportion materials were used, how Entscheidungshilfe auf dem Gebiet der functions and effects that these substan- they may have dissipated into the envi- Umweltpolitik besprochen. Die Flüsse und ces allowed in their applications. On the ronment, and how they partitioned Lager von Blei (Pb), Kadmium (Cd) und other side, the wide spread use of heavy into certain reservoirs. Quecksilber (Hg) in der österreichischen metals also created concerns regarding ■ ■ Lestel et al. 2007 describe the flow of 30 Wirtschaft und in die Umwelt werden un- their toxicity and negative impact on the metals from 24 sources within the Seine tersucht. Es werden vor allem zwei Vorteile environment. Therefore, measures are river basin in five-year-time steps for der SFA hervorgehoben. Zum einen beruht needed to control the efficient use of ma- the period 1950 to 2000. The special fo- die SFA auf dem Gesetz von der Erhaltung terials and their emissions into the envi- cus is on zinc and on a comparison bet- der Masse – Eintrag und Austrag sind ge- ronment, as well. The basis for designing ween the flows in the anthroposphere geneinander auszubilanzieren; damit kön- these measures is a proper knowledge of and in the Seine River. öwaw © Springer-Verlag 5-6/2009 63 originalarbeit achieved a certain tradition and a high le- vel of credibility in Austria. Still, a compre- hensive, consistent and nation-wide data set on lead (Pb), cadmium (Cd) and mer- cury (Hg) did not exist. Hence, when the European Commission asked the member states to supply information about Pb, Cd and Hg, the Austrian Ministry of Agricul- ture, Forestry, Environment and Water Management decided to use SFA metho- dology to commission a study on the pre- sent turnover of the three heavy metals on a country wide scale. A project was launched to link exis- ting information, and to quantify the flows and stocks of Pb, Cd, and Hg. The main ob- jective was to produce a consistent and ro- bust data set that can be used for decision making in environmental management as well as in waste and resources manage- ment. The study was jointly prepared by the Umweltbundesamt (Austrian EPA) and the Vienna University of Technology, and is described in detail in Reisinger et al. (2009). In the present article, the authors describe shortly the method applied, the data source, the results of the study, the implications for environmental policy, and the advantages and disadvantages of using SFA as a methodology for this study. Fig. 1: The system RUSCH of Austrian flows and stocks of Pb, Cd, and Hg, comprising 10 imports, 21 internal flows, and 16 exports, eight processes within and two processes outside the systems boundary. 2. Methods and Data With respect to integrating resource ma- recently, Substance Flow Analysis (SFA) In order to assess the flows and stocks of nagement and environmental policies a has gained momentum in particular by the three heavy metals investigated, mate- new impetus was given by the “Thematic the Center for Industrial Ecology at Yale rial flow analysis MFA and substance flow Strategy on the Sustainable Use of Natural University that produces valuable reports analysis SFA were used to link data that Resources” by the European Commission on flows and stocks of many metals on all had been collected beforehand in other (European Commission 2005), which has scales (e. g. Graedel et al. 2004). In Austria, contexts such as emission inventories, en- the objective to reduce the environmental data about the flows and stocks of materi- vironmental monitoring, and waste ma- impact of resource use. Within this frame- als have been collected by several institu- nagement. MFA/SFA were performed ac- work, European countries further limit the tions for individual purposes. Since the cording to (ÖNORM S 2096-1&2 2005) as flow of specific heavy metals. E. g. Sweden 1990ies, SFA has been established in Aus- described by (Brunner and Rechberger has decided to decrease the contents of tria as an acknowledged method. It has 2003). lead, cadmium and mercury in newly pro- been successfully applied in several stu- duced goods as far as possible (Kemi 2007). dies, in particular to support waste ma- 2.1. System Description Austria applies an extended mix of policy nagement decisions, and to deliver inputs measures in order to control the use and for the Federal Waste Management Plan. A The system boundary in terms of space emissions of heavy metals. Despite these National Standard for the application of was defined according to the political bor- measures considerable amounts of lead, SFA in waste management, defining terms, ders of Austria. The upper soil (pedo- cadmium and mercury are suspected to methodology, and range of application sphere) was included in the system. Since still remain in use and to be stored in the has been in use since the year 2006 it was not possible to determine all inputs anthroposphere. As a consequence, careful (ÖNORM S 2096-1&2 2005). For resource and outputs of the lithosphere, atmos- management of these three elements will management and the Federal Resource phere and hydrosphere, these processes remain important in the future, and additi- Report, an SFA study supplied the neces- were not balanced and thus were not in- onal policy measures may be required.
Recommended publications
  • Rethinking the Waste Hierachy
    R ethinking the Waste H i erarchy Environmental ASSESSMENT INSTITUTE MARCH 2005 INSTITUT FOR MILJ0VURDERING E nvironmental Assessment Institute Reference no.: 2002-2204-007 ISBN.: 87-7992-032-2 Editors: Clemen Rasmussen and Dorte Vigs0 Written by: Clemen Rasmussen (project manager), Dorte Vigs0, Frank Ackerman, Richard Porter, David Pearce, Elbert Dijkgraaf and Herman Vollebergh. Published: March 2005 Version: 1.1 ©2005, Environmental Assessment Institute For further information please contact: Environmental Assessment Institute Linnesgade 18 DK -1361 Copenhagen Phone: +45 7226 5800 Fax: +45 7226 5839 E-mail: [email protected] Web: www.imv.dk E nvironmental Assessment Institute Rethinking the Waste Hierarchy March 2005 Recommendations A number of specific recommendations for achieving cost-effective waste policies can be made based on both the US experience presented by Ackerman and Porter and on the analysis of European waste management presented by Pearce and Dijkgraaf & Vollebergh. The results of this project relate to both the target setting and the regulatory implementation of waste policy in the EU. The main recommendations for future waste policies in the EU and Member States are: ■ The waste hierarchy must be considered a very general and flexible guideline for formulating waste policies. What is environmentally desirable is not always a preferred solution, when considered from a socio economic perspective. The reason is that some environmental benefits may come at a comparably so­ cially high cost. The marginal costs and benefits will vary depending on mate­ rial and locality. It is recommended that social costs and benefits of new recy­ cling schemes should be analysed and that a critical assessment be made on to determine if further steps are in fact socially desirable.
    [Show full text]
  • Solid Waste Master Plan Source Reduction Discussion II
    John Fischer February 20, 2019 Master Plan Status & Schedule Update Spring, summer 2019: write draft plan Fall 2019: release public hearing draft Late 2020: publish final plan Upcoming Meetings March 14th C&D Subcommittee March 19th: Organics Subcommittee April 25th: Solid Waste Advisory Committee June 18th: C&D Suncommittee Source Reduction Strategies Identified at Jan. 17, 2019 Meeting Extended producer responsibility (EPR) PAYT and source reduction Right to repair The sharing economy Textile reuse Commercial waste reduction C&D source reduction Furniture refurbishment Resource management contracting Extended Producer Responsibility (EPR) Enforce cardboard manufacturer responsibility to promote a closed loop system. Hold producers responsible if their packaging is not recyclable. Manufacturers should pay for people to send packaging back to them. Packaging responsibility should drive producers to think more about their packaging, which could drive source reduction. Support paint and electronics EPR bills filed this session. Extended Producer Responsibility (EPR) Discussion question: What are the most important products or packaging for which we should establish EPR systems? PAYT and Source Reduction Promote PAYT within a framework of other initiatives that enable source reduction, e.g. a Library of Things. PAYT creates awareness, which can affect consumer behavior. PAYT and Source Reduction Discussion question: What steps should MassDEP take to increase/improve PAYT program adoption? Right to Repair Right to repair laws could help create new small repair businesses. Producers would be required to share all schematics of how a product works, which allows other businesses to repair the products, not just the original producers. Right to Repair Discussion question: What product categories provide the best repair business opportunities? The Sharing Economy Establish baseline of current reuse activities: identify the impact of systems such as Craigslist, Freecycle, Buy Nothing Facebook groups, and NextDoor.com.
    [Show full text]
  • Life Cycle Assessment
    Life cycle assessment http://lcinitiative.unep.fr/ http://lca.jrc.ec.europa.eu/lcainfohub/index.vm http://www.lbpgabi.uni-stuttgart.de/english/referenzen_e.html "Cradle-to-grave" redirects here. For other uses, see Cradle to the Grave (disambiguation). Recycling concepts Dematerialization Zero waste Waste hierarchy o Reduce o Reuse o Recycle Regiving Freeganism Dumpster diving Industrial ecology Simple living Barter Ecodesign Ethical consumerism Recyclable materials Plastic recycling Aluminium recycling Battery recycling Glass recycling Paper recycling Textile recycling Timber recycling Scrap e-waste Food waste This box: view • talk • edit A life cycle assessment (LCA, also known as life cycle analysis, ecobalance, and cradle-to- grave analysis) is the investigation and valuation of the environmental impacts of a given product or service caused or necessitated by its existence. Contents [hide] 1 Goals and Purpose of LCA 2 Four main phases o 2.1 Goal and scope o 2.2 Life cycle inventory o 2.3 Life cycle impact assessment o 2.4 Interpretation o 2.5 LCA uses and tools 3 Variants o 3.1 Cradle-to-grave o 3.2 Cradle-to-gate o 3.3 Cradle-to-Cradle o 3.4 Gate-to-Gate o 3.5 Well-to-wheel o 3.6 Economic Input-Output Life Cycle Assessment 4 Life cycle energy analysis o 4.1 Energy production o 4.2 LCEA Criticism 5 Critiques 6 See also 7 References 8 Further reading 9 External links [edit] Goals and Purpose of LCA The goal of LCA is to compare the full range of environmental and social damages assignable to products and services, to be able to choose the least burdensome one.
    [Show full text]
  • The Consumer's Handbook for Reducing Solid Waste
    United States EPA 530-K-96-003 Environmental Protection September 1996 Agency Solid Waste and Emergency Response (5305W) The Consumer’s Handbook for Reducing Solid Waste Reduction Reuse Recycle Response This booklet describes how people can help solve a growing prob- lem...garbage! Individual consumers can help alleviate America’s mounting trash problem by making environmentally aware decisions about everyday things like shopping and caring for the lawn. Like the story that says cats have nine lives, so do many of the items we use every day. Empty cans and jars can be reused to store many items, such as nails or thumbtacks. The baking soda bought to bake a cake also can be used to scrub kitchen counters. The container that began its life as a plastic milk jug can be washed and reused to water plants, create an arts and crafts project, or be transformed into a bird feeder. Eventually, the milk jug can be recycled to create a new plastic product. Reusing products is just one way to cut down on what we throw away. This booklet outlines many practical steps to reduce the amount and toxicity of garbage. These aren’t the only steps that can be taken to reduce waste, but they’re a good start. L 1 Reduction Solid Waste Source Reduction A Basic Solution General Overview of What’s in America’s Trash Metals Yard Trimmings Source reduction is a basic solu- other management options that tion to the garbage glut: less waste deal with trash after it is already means less of a waste problem.
    [Show full text]
  • RCRA, Superfund & EPCRA Call Center Training Module
    United States Solid Waste and EPA530-K-02-019I Environmental Protection Emergency Response October 2001 Agency (5305W) RCRA, Superfund & EPCRA Call Center Training Module Introduction to: RCRA Solid Waste Programs Updated October 2001 DISCLAIMER This document was developed by Booz Allen Hamilton Inc. under contract 68-W-01-020 to EPA. It is intended to be used as a training tool for Call Center specialists and does not represent a statement of EPA policy. The information in this document is not by any means a complete representation of EPA s regulations or policies. This document is used only in the capacity of the Call Center training and is not used as a reference tool on Call Center calls. The Call Center revises and updates this document as regulatory program areas change. The information in this document may not necessarily reflect the current position of the Agency. This document is not intended and cannot be relied upon to create any rights, substantive or procedural, enforceable by any party in litigation with the United States. RCRA, Superfund & EPCRA Call Center Phone Numbers: National toll-free (outside of DC area) (800) 424-9346 Local number (within DC area) (703) 412-9810 National toll-free for the hearing impaired (TDD) (800) 553-7672 The Call Center is open from 9 am to 5 pm Eastern Time, Monday through Friday, except for federal holidays. RCRA SOLID WASTE PROGRAMS CONTENTS 1. Introduction............................................................................................................. 1 2. Municipal Solid Waste ......................................................................................... 2 2.1 EPA's Integrated Waste Management Hierarchy .................................... 3 2.2 Source Reduction ........................................................................................... 4 2.3 Recycling ........................................................................................................... 5 2.4 Combustion ....................................................................................................
    [Show full text]
  • Material Flows and Stocks in the Urban Building Sector: a Case Study from Vienna for the Years 1990–2015
    sustainability Article Material Flows and Stocks in the Urban Building Sector: A Case Study from Vienna for the Years 1990–2015 Jakob Lederer 1,2,*, Andreas Gassner 1, Florian Keringer 3, Ursula Mollay 3, Christoph Schremmer 3 and Johann Fellner 1 1 Christian Doppler Laboratory for Anthropogenic Resources, Institute for Water Quality and Resource Management, TU Wien, Karlsplatz 13/226, 1040 Vienna, Austria; [email protected] (A.G.); [email protected] (J.F.) 2 Institute of Chemical, Environmental and Bioscience Engineering, TU Wien, Getreidemarkt 9/166-01, 1060 Vienna, Austria 3 Austrian Institute of Regional Studies (OIR GmbH), Franz-Josefs-Kai 27, 1010 Vienna, Austria; [email protected] (F.K.); [email protected] (U.M.); [email protected] (C.S.) * Correspondence: [email protected] Received: 2 December 2019; Accepted: 27 December 2019; Published: 30 December 2019 Abstract: Population growth in cities leads to high raw material consumption and greenhouse gas emissions. In temperate climates were heating of buildings is among the major contributors to greenhouse gases, thermal insulation of buildings became a standard in recent years. Both population growth and greenhouse gas mitigation may thus have some influence on the quantity and composition of building material stock in cities. By using the case study of Vienna, this influence is evaluated by calculating the stock of major building materials (concrete, bricks, mortar, and plaster, steel, wood, glass, mineral wool, and polystyrene) between the years 1990 and 2015. The results show a growth of the material stock from 274 kt in the year 1990 to 345 kt in the year 2015, resulting in a total increase of 26%.
    [Show full text]
  • CHAPTER 4. FUTURE VISIONING the Purpose of This Chapter Is to Outline the Goals and Objectives of This RSWMP Document
    CHAPTER 4. FUTURE VISIONING The purpose of this chapter is to outline the goals and objectives of this RSWMP document. Based on stakeholder input, analysis results, and a review of existing programs and practices related to regional solid waste management, a series of goals and subgoals was created to guide the TCOG Region over the next twenty years. These goals were periodically reviewed with the NRAC, TCOG staff and were further refined based on feedback received. A particular focus on waste minimization, cooperative commitment, public education, and outreach, and recommendations for a compost program were a primary focus during the development of these goals. Goals In total, there are four primary goals intended to guide the Region’s solid waste management practices over the next twenty years. Each primary goal is also supported by a series of corresponding subgoals, which outline more specific recommendations to incrementally achieve primary goals. Primary goals include the following: 1. Ensure adequate levels of transportation and disposal capabilities throughout the region. 2. Develop local programs in source reduction, waste minimization, reuse, recycling, and composting in order to conserve disposal capacity and resources. 3. Develop programs to assist regional and local entities in controlling and stemming illegal and improper disposal practices. 4. Develop cost-effective, efficient, and environmentally suitable solid waste management systems throughout the region. These four functional goals have served as the guiding principles for the Region since the original RSWMP was adopted in 1993. Upon review of stakeholder feedback and analysis results, these goals were deemed appropriate to continue functioning as guiding principles for the Region.
    [Show full text]
  • Extended Producer Responsibility: the Next Phase of the US Recycling Movement
    Extended Producer Responsibility: The Next Phase of the US Recycling Movement A Review of the Take It Back! Pacific Rim: Forging New Alliances for Waste Reduction Conference, held February 28 – March 1, 2000 in Los Angeles, California. The conference was produced by Raymond Communications, Inc. and Huls Environmental, L.L.C. and sponsored by The City of Los Angeles, California Integrated Waste Management Board, GTE Recycling, E-tech Products, Inc., and Waste Management of Orange County. By Neil N. Seldman Institute for Local Self-Reliance (ILSR) 2425 18th Street, NW Washington, DC 20009 (202)-232-4108 Neil Seldman is the director of the Institute for Local Self-Reliance’s (ILSR’s) Waste to Wealth Program. Under a grant from the Flora Foundation in San Francisco, California, ILSR will be exploring extended producer responsibility strategies and other rules that help close the loop locally. The U.S. recycling movement once again is flexing its muscles, this time in the direction of Extended Producer Responsibility (EPR). EPR proponents see discarded products and packages are an “unfunded mandate.” While some see unfunded mandates only as federal dictates that force spending at the local level, EPR advocates see unfunded mandates as corporate dictates that force local governments and small businesses to spend $43.5 billion annually for handling the materials that manufacturers so carelessly let loose upon the land. The EPR concept originated in Europe in the last decade, but now is emerging in Central and South America and Asia as well; paralleling the global path of the product and packaging manufacturers against whom the movement is aimed.
    [Show full text]
  • Quantification of Anthropogenic Metabolism Using Spatially Differentiated Continuous MFA Across the Country
    Change Adaptation Socioecol. Syst. 2017; 3: 119–132 Research Article Georg Schiller, Karin Gruhler, Regine Ortlepp* Quantification of anthropogenic metabolism using spatially differentiated continuous MFA https://doi.org/10.1515/cass-2017-0011 across the country. In Germany, such disparities mean that received April 13, 2017; accepted January 16, 2018 there will be a shortfall in RA of 6.3 Gt by the year 2020, Abstract: Coefficient-based, bottom-up material flow while the technically available but unusable RA (due to a analysis is a suitable tool to quantify inflows, outflows regional mismatch of potential supply and demand) will and stock dynamics of materials used by societies, and total 3.2 Gt. Comprehensive recycling strategies have to thus can deliver strategic knowledge needed to develop combine high-quality recycling with other lower-grade circular economy policies. Anthropogenic stocks and flows applications for secondary raw materials. Particularly in are mostly of bulk nonmetallic mineral materials related the case of building materials, essential constraints are to the construction, operation and demolition of buildings not only technical but also local conditions of construction and infrastructures. Consequently, it is important to be and demolition. These interrelations should be identified able to quantify circulating construction materials to and integrated into a comprehensive system to manage help estimate the mass of secondary materials which can the social metabolism of materials in support of circular be recovered such as recycled aggregates (RA) for fresh economy policies. concrete in new buildings. Yet as such bulk materials are high volume but of low unit value, they are generally Keywords: continuous material flow analysis (C-MFA), produced and consumed within a region.
    [Show full text]
  • Consideration of the Solid Waste Hierarchy
    CHAPTER 4.0 CONSIDERATION OF THE SOLID WASTE HIERARCHY 4.0 CONSIDERATION OF THE SOLID WASTE HIERARCHY 4.1 The Solid Waste Hierarchy The Code of Virginia (Section 10.1-1411) and the Virginia Solid Waste Management Regulations (9 VAC 20-130-10 et seq.) require local governments to develop a comprehensive and integrated solid waste management plan. The Plan, at a minimum, must consider and address all components of the solid waste hierarchy for all types of nonhazardous solid waste generated in the region or locality (Figure 4-1). The solid waste management hierarchy ranks methods of handling solid waste from most preferred methods of source reduction, reuse, and recycling, in that order, to least preferred methods of energy/resource recovery/incineration and landfilling. Figure 4-1: Solid Waste Management Hierarchy (9 VAC 20-130-30) Source Reduction Most Preferred Reuse Recycling Resource Recovery Least Preferred Incineration Landfilling The Plan must provide an integrated solid waste management strategy that considers all elements of waste management during generation, collection, transportation, treatment, storage, and disposal. Finally, the Plan must describe how the mandatory recycling rate of 25% of the total municipal solid waste (MSW) generated annually will be met or exceeded (9 VAC 20-130-120 B & C). No single waste management approach is appropriate for all communities. Integrated solid waste management uses a combination of techniques and approaches to handle targeted portions of the waste stream. It is important to realize that the portions of the hierarchy interact with each other and that change on one level will impact or influence another level.
    [Show full text]
  • REFERENCES Abufayed, AA, & Schroeder, ED
    REFERENCES Abufayed, A. A., & Schroeder, E. D. (1986) Performance of SBR/denitrification with a primary sludge carbon source. Journal WPCF 5 (58); 387 Adriaanse, A., Bringezu, S., Hamond, A., Moriguchi, Y., Rodenburg, E., Rogich, D., Schütz, H. (1997). Resource Flows: The Material Base of Industrial Economies. World Resource Institute, Washington. Agamuthu P. & Fauziah,S.H. (2010) Impact of Landfill Gas on Climate Change, International Conference on Climate Change and Bioresource (ICCCB 2010) 9th- 12th February 2010, Department of Biotechnology, Bharathidasan University India. Agamuthu,P., Fauziah, S.H. and Khidzir, K.M. (2009) Evolution of solid waste management in Malaysia : Impacts and implications of the solid waste bill 2007. Journal of Material Cycles and Waste Management, 11(2): 96-103. Agamuthu,P., Fauziah, S.H. and Lingesveeramani, M (2004) Evolution of MSW in Malaysia- An overview. Paper presented in the World Congress ISWA 2004, 17-21 October 2004, Rome Italy. Agamuthu,P.,Fauziah,S.H. and Khidzir,K.M.,(2003) Municipal solid waste management; A comparative study on selected landfill in Selangor.In Proceedings of Environment 2003 Environmental Management and Sustainable Development for Better Future Growth.18th- 19th February 2003: pp434-437.Penang, Malaysia. Agamuthu, P. (2001) Solid Waste : Principle and Management. University of Malaya Press: 9-27 Albers, H. & Krückeberg, G, 1992) Combination of aerobic pre-treatment, carbon adsorption and coagulation. Landfilling of waste: leachate. Elsevier applied science. London and New York.305pp. Alhumoud, J.M.(2005)Municipal solid waste recycling in the Gulf Co-operation Council states. Resources,Conservation and Recycling 45(2):142-158. Alhumoud,J.M., Al-Ghusain, I.
    [Show full text]
  • Briefing Paper: Oregon's Solid Waste Hierarchy
    Briefing Paper: Oregon’s Solid Waste Hierarchy - Intent and Uses September 27, 2011 Primary Authors: David Allaway & Peter Spendelow "Reduce, Reuse, Recycle " has been part of the environmental lexicon since at least the first Earth Day in 1970, but Oregon was among the first states to adopt this as official policy in state law. The Recycling Opportunity Act of 1983 adopted a 5-step hierarchy for managing solid waste, with energy recovery and landfilling added below the other three. Passage of the 1991 Recycling Act added composting to the hierarchy below recycling and above energy recovery, so that the current law reads as follows: 459.015 Policy. (1).... (2) In the interest of the public health, safety and welfare and in order to conserve energy and natural resources, it is the policy of the State of Oregon to establish a comprehensive statewide program for solid waste management which will: (a) After consideration of technical and economic feasibility, establish priority in methods of managing solid waste in Oregon as follows: (A) First, to reduce the amount of solid waste generated; (B) Second, to reuse material for the purpose for which it was originally intended; (C) Third, to recycle material that cannot be reused; (D) Fourth, to compost material that cannot be reused or recycled; (E) Fifth, to recover energy from solid waste that cannot be reused, recycled or composted so long as the energy recovery facility preserves the quality of air, water and land resources; and (F) Sixth, to dispose of solid waste that cannot be reused, recycled, composted or from which energy cannot be recovered by landfilling or other method approved by the Department of Environmental Quality.
    [Show full text]