DOCSLIB.ORG

Chapter 7: Other Wastes

Total Page：16

File Type：pdf, Size：1020Kb

Download full-text PDF Read full-text
Chapter 7: Other Wastes East Sussex and Brighton & Hove Waste Local Plan Part 2: IMPLEMENTING THE WASTE LOCAL PLAN STRATEGY Chapter 7: Other wastes 103 East Sussex and Brighton & Hove Waste Local Plan Chapter 7: Other wastes Introduction 7.1 Other wastes include hazardous and clinical wastes, which require more stringent handling and treatment than other ‘controlled’55 wastes, and mineral, agricultural and sewage wastes, which are not classified as controlled wastes. This chapter describes the types of more specialised wastes that are produced in the Plan area, together with relevant policies against which proposals will be assessed by the WPAs. Applications will be assessed against the provisions of the whole Development Plan. This chapter deals with the following types of waste: (i) Mineral Waste (ii) Hazardous (Special) and Difficult waste (iii) Clinical Waste (iv) Wastewater and Sewerage (v) Landspreading of Liquid Wastes and Dredgings (vi) Liquid Waste Facilities (vii) Agricultural and Farm Waste (viii) Animal Carcass Waste (ix) Nuclear and Radioactive Waste (x) Contaminated Land Waste (i) Mineral Waste 7.2 Mineral waste mainly comprises overburden waste, unusable rock and process waste from screening and washing. There are few markets for these materials and they are usually incorporated into the restoration of the site. At sand and gravel sites with washing facilities silt is deposited in lagoons while at other mineral workings waste is deposited within the boundary of the site, as backfilling or screening. This is an appropriate re-use of the material provided it contributes to the beneficial restoration of the site or the temporary screening of operations. Opportunities for blending of mineral waste may arise if soil/compost materials are being produced on-site, the mixture yielding soil forming materials. The former Department of Environment, Transport & the Regions (DETR) document Soil Forming Materials – their use in Land Reclamation (1999) gives further guidance. 7.3 In the majority of cases, the use of mineral waste for screening and/or restoration projects will have been considered as part of the original mineral working application. However, where this is not the case, the WPAs will seek to ensure that all reasonable steps have been taken to re-use or recycle the material before giving consideration to supporting disposal to land. 55 Controlled Waste is defined in Section 75(4) of the Environmental Protection Act 1990 (see Glossary). 104 East Sussex and Brighton & Hove Waste Local Plan 7.4 Some mineral waste, most notably crushed rock, is suitable as a secondary aggregate. Minerals Planning Guidance Note 6 Guidelines for Aggregates Provision in England, advises planning authorities to pursue policies to facilitate the use of these materials where this is environmentally or economically acceptable. The use of mineral waste as a secondary aggregate is therefore supported in principle. 7.5 Within the Plan area reject rock from gypsum mining is used as a low grade fill, but poor quality inhibits its widespread use as a secondary aggregate. However, it has a value as a substitute for other minerals of greater value, such as chalk. POLICY WLP 26: Mineral Waste Proposals for the management of mineral waste will be permitted, subject to other policies of the Plan where relevant, where they: a) form an integral part of a proposal for mineral working; or b) constitute effective re-use or recycling of the material. (ii) Special and Difficult Waste 7.6 In 2005, new regulations, known as the ‘Hazardous Waste Regulations’, were brought into force which affect the management of ‘Special’ waste in a number of ways. This legislation superseded the Special Waste Regulations 1996, and the term ‘Special’ waste was formally superseded by the term ‘Hazardous’. As Hazardous Waste encompasses all wastes which were ‘Special’, Policy WLP 27 shall be applied to the management of all wastes which are now defined as ‘Hazardous’ under the Hazardous Waste Regulations. Difficult wastes, on the other hand, are not defined in these Regulations but can be described as Controlled Wastes that appear on the Hazardous Waste List57, which generate handling difficulties in disposal because of their chemical or physical properties, but do not display any of the properties exhibited by hazardous wastes. 7.7 Difficult wastes include clinical, liquid and scrap metal wastes, tyres, aerosols, sewage and other sludges, contaminated soils and contaminated packaging materials. Examples of hazardous waste include industrial solvents and other chemicals, waste oils, prescription-only medicines and certain clinical waste. These are subject to close monitoring from ‘cradle to grave’ by the Environment Agency. 57 The Hazardous Waste List (HWL) (94/904/ec) lists the wastes on the european waste catalogue (EWC) (94/3/EC) considered to have hazardous constituents above certain thresholds. A waste listed on the HWL is more likely to be considered 'hazardous waste' in the UK 105 East Sussex and Brighton & Hove Waste Local Plan 7.8 The amount of hazardous and difficult waste generated in the Plan area is small, representing around 3% of overall ‘controlled’ waste arisings. Existing arrangements for these types of waste are expected to continue throughout the Plan period. However, where necessary, facilities for the transfer of hazardous and difficult waste could be accommodated at waste transfer sites and household waste sites while facilities for treatment and disposal may be accommodated at ‘strategic’ waste facility sites. 7.9 The former regional planning body SERPLAN58 (London & South East Regional Planning Conference) considered that sub-regional self-sufficiency in special waste (as hazardous waste was known at the time) disposal would not be feasible owing to the special requirements for management of these wastes, the relatively small amounts generated and the costs of establishing specialist management and disposal facilities. 7.10 At present there are insufficient hazardous or difficult waste transfer facilities in the Plan area to meet local requirements. If this situation remains unchanged, producers of this type of waste could face disposal problems over the period of this Plan, as the impact of the Hazardous Waste Regulations becomes clearer. Major waste developments in the Plan area will be expected to incorporate, where appropriate, facilities for the storage and transfer of these wastes. 7.11 Despite the current relatively small quantities generated, it is preferable to deal with Hazardous and difficult wastes, wherever practicable, as close as possible to their point of origin, because of the potential risks during transport and of the need to minimise the distance travelled between the source of the waste and it’s treatment/disposal point. It is acknowledged that this may not always represent the BPEO as the cost of installing facilities to deal with relatively small amounts of waste may be prohibitive. It is therefore anticipated that over the Plan period some Hazardous and difficult wastes will continue to be exported for treatment and/or disposal at specialist regional facilities. 7.12 Similarly, there could be a greater need within the Plan area in the future for facilities to handle imported Hazardous and difficult wastes as the EU Landfill Directive requiring the segregation of hazardous and non-hazardous wastes begins to take effect. Such facilities will be supported provided they also make a significant contribution to meeting local waste management needs and do not have any adverse environmental or traffic impacts. To facilitate the segregation of these wastes, the WPAs will seek the inclusion of appropriate sorting and transfer facilities in major waste developments and in new and upgraded household waste sites that can also be used by members of the public. 58 SERPLAN “Revised Waste Planning Advice; A Sustainable Waste Strategy for the South East 1996-2010”, SERP160. 106 East Sussex and Brighton & Hove Waste Local Plan POLICY WLP 27: Special and Difficult Wastes Proposals for the development of facilities for the handling, storage, treatment, processing and disposal of special and difficult waste will be required to demonstrate that: a) the waste arises within the Plan area or the facility forms part of a regional strategy for dealing with special and difficult waste which also makes a substantial contribution to meeting local waste management needs, and b) the proposed location and type of facility are appropriate to the nature and hazards of the waste. c) the co-location of waste facilities has been considered, where appropriate. N.B. In 2005, new regulations, known as the ‘Hazardous Waste Regulations’ came into force, this legislation superseded the Special Waste Regulations 1996, and the term ‘Special’ waste was formally superseded by the term ‘Hazardous’. As Hazardous Waste encompasses all wastes which were ‘Special’, this policy shall be applied to planning applications involving the management of all wastes which are now defined as ‘Hazardous’ under the Hazardous Waste Regulations. (iii) Clinical Waste 7.13 Clinical waste arises from the healthcare sector, from dental and veterinary practices, doctors’ surgeries and households. Some of these wastes can be disposed of at landfill sites, but infectious and other clinical waste posing a greater potential risk needs to be managed as hazardous waste. Most notifiable clinical waste is incinerated but new techniques such as sterilising or microwaving are being developed. 7.14 New emission standards for incinerators were introduced in October 1995 and, in recent years, all existing in-house hospital incinerators within the Plan area have closed down, as they have been unable to meet the new standards. Most clinical waste is now exported for treatment/disposal. In view of the environmental impact associated with transporting wastes over long distances, support should be given to new clinical waste management and disposal facilities, provided they are located within or adjacent to a facility that generates this type of waste. This applies equally to those facilities that are designed to cater for clinical wastes on a regional basis.
Load more

Recommended publications
  • Waste Minimisation
    Waste Minimisation An Environmental Good Practice Guide For Industry This guide will help industry and the Environment Agency move forward together to minimise waste and achieve national environmental goals WASTE MINIMISATION An Environmental Good Practice Guide for Industry “The cost of your waste is not so much the cost of getting rid of it as the value of what you are getting rid of!” Published by the Environment Agency April 2001, to help business achieve sustainable practice through waste minimisation. Revised edition April 2001. First published April 1998. i Waste Minimisation Good Practice Guide Environment Agency April 2001 FOREWORD Minimise waste – maximise profit The way we use our planet’s natural resources is now widely recognised as one of the root causes of many environmental problems. Waste and industrial emissions have a major impact on the environment both nationally and globally. Effects such as global warming, ozone depletion, acid rain, air and water pollution are all derived from local emissions, but the resources consumed may be mined and manufactured from anywhere in the world. From extraction to consumption the global economy consumes vast quantities of raw materials, water and energy. In the UK some 600 million tonnes of raw materials, excluding water, are used each year. More than 90 per cent of the resources we consume are either thrown away as wastes or discharged to the environment as effluent or air emissions. Since the Environment Agency first published this guide in 1998, waste minimisation has become an established business practice for many organisations and thousands of businesses have now implemented waste reduction programmes.
    [Show full text]
  • Waste Management
    10 Waste Management Coordinating Lead Authors: Jean Bogner (USA) Lead Authors: Mohammed Abdelrafie Ahmed (Sudan), Cristobal Diaz (Cuba), Andre Faaij (The Netherlands), Qingxian Gao (China), Seiji Hashimoto (Japan), Katarina Mareckova (Slovakia), Riitta Pipatti (Finland), Tianzhu Zhang (China) Contributing Authors: Luis Diaz (USA), Peter Kjeldsen (Denmark), Suvi Monni (Finland) Review Editors: Robert Gregory (UK), R.T.M. Sutamihardja (Indonesia) This chapter should be cited as: Bogner, J., M. Abdelrafie Ahmed, C. Diaz, A. Faaij, Q. Gao, S. Hashimoto, K. Mareckova, R. Pipatti, T. Zhang, Waste Management, In Climate Change 2007: Mitigation. Contribution of Working Group III to the Fourth Assessment Report of the Intergovernmental Panel on Climate Change [B. Metz, O.R. Davidson, P.R. Bosch, R. Dave, L.A. Meyer (eds)], Cambridge University Press, Cambridge, United Kingdom and New York, NY, USA. Waste Management Chapter 10 Table of Contents Executive Summary ................................................. 587 10.5 Policies and measures: waste management and climate ....................................................... 607 10.1 Introduction .................................................... 588 10.5.1 Reducing landfill CH4 emissions .......................607 10.2 Status of the waste management sector ..... 591 10.5.2 Incineration and other thermal processes for waste-to-energy ...............................................608 10.2.1 Waste generation ............................................591 10.5.3 Waste minimization, re-use and
    [Show full text]
  • WASTE MANAGEMENT ARRANGEMENT of SECTIONS PART I Preliminary SECTION 1
    CHAPTER 65:06 WASTE MANAGEMENT ARRANGEMENT OF SECTIONS PART I Preliminary SECTION 1. Short title 2. Interpretation PART II Establishment of Department 3. Establishment of Department 4. Staff of Department 5. Identity card of an officer PART III Functions of Department 6. Functions of Department 7. Annual Report 8. Qualifications of officers and managers PART IV Waste Management Plans 9. Local and national waste management plans 10. Waste recycling plan 11. Litter plan PART V Registration and Licensing of Waste Carriers 12. Registration of waste carrier 13. Licensing of waste carriers PART VI Registration of Waste Disposal Sites and Licensing of Waste Management Facilities 14. Registration of waste disposal sites 15. Unlicenced waste management facility prohibited 16. Licensing of waste management facility 17. Consultation 18. Conditions of waste management facility licence 19. Variation of conditions 20. Transfer of waste management facility licence 21. Suspension of waste management facility licence 22. Revocation of waste management facility licence 23. Surrender of waste management facility licence 24. Exemption from holding licence 25. Public register of issued waste management facility licences 26. Closure of facility by order of Minister Copyright Government of Botswana 27. Appeals 28. Offence and penalty PART VII Powers and Duties of Local Authorities 29. Collection of waste 30. Receptacles for household waste 31. Disposal of waste 32. Removal of waste 33. Power to recycle waste PART VIII Litter 34. Prohibition to litter 35. Abatement of litter 36. Dumping of litter 37. Principal Litter Authority 38. Notices for depositing litter PART IX Enforcement Powers 39. Power to obtain information 40. Power of search and seizure 41.
    [Show full text]
  • What Is Controlled Waste?
    Controlled waste fact sheet What is controlled waste? Under the Environmental Protection (Controlled Waste) Regulations 2004 Waste means any: (the Regulations): a) discarded, rejected, unwanted, surplus or abandoned matter; or 2. Controlled waste means any matter b) otherwise discarded, rejected, that is — unwanted, surplus or abandoned a) within the definition of waste in matter intended for: the NEPM for the Movement of (i) recycling, reprocessing, Controlled Waste between recovery, reuse, or States and Territories;* and purification by a separate b) listed in Schedule 1 … operation from that which produced the matter; or (ii) sale, whether of any value or not. 3. (4) Subject to subregulations (5) Is my waste a controlled waste? and (6), these regulations apply to a controlled waste that is produced by or To determine if waste is a controlled as the result of — waste, information about its a) an industrial or commercial composition, pH, flashpoint and/or the activity; process that generated the waste may b) a medical, nursing, dental, be required. veterinary, pharmaceutical or For some waste, knowing how it was other related activity; generated is sufficient to establish c) activities carried out on or at a whether it is a controlled waste; for laboratory; or d) an apparatus for the treatment of example, waste from a septic tank. sewage. However, for certain waste, chemical analysis is needed to determine the *Under the National Environment composition of the waste and identify Protection (Movement of Controlled whether it is a controlled waste as Waste between States and Territories) listed in Schedule 1 of the Regulations. Measure: If a waste has been determined to be a controlled waste listed in Schedule 1 of the Regulations, it can be found on the waste category list — a quick- reference guide to recording controlled waste in short-form for tracking purposes.
    [Show full text]
  • Environmental Management and Pollution Control (Waste Management) Regulations 2010
    Contents (2010 - 104) Environmental Management and Pollution Control (Waste Management) Regulations 2010 Long Title Part 1 - Preliminary 1. Short title 2. Commencement 3. Interpretation 4. Application Part 2 - Management of Controlled Waste 5. Controlled wastes 6. General responsibilities 7. Production, storage and treatment of controlled waste 8. Disposal of controlled waste Part 3 - Management of General Waste 9. Disposal of general waste Part 4 - Miscellaneous 10. Approved management method 11. Prohibited activities at facilities 12. Environmental approvals 13. Transitional and savings provisions 14. Legislation rescinded Schedule 1 - Legislation rescinded Environmental Management and Pollution Control (Waste Management) Regulations 2010 Version current from 1 January 2017 to date (accessed 17 October 2018 at 15:45) Environmental Management and Pollution Control (Waste Management) Regulations 2010 I, the Governor in and over the State of Tasmania and its Dependencies in the Commonwealth of Australia, acting with the advice of the Executive Council, make the following regulations under the Environmental Management and Pollution Control Act 1994 . 25 October 2010 PETER G. UNDERWOOD Governor By His Excellency's Command, D. J. O'BYRNE Minister for Environment, Parks and Heritage PART 1 - Preliminary 1. Short title These regulations may be cited as the Environmental Management and Pollution Control (Waste Management) Regulations 2010 . 2. Commencement These regulations take effect on the day on which their making is notified in the Gazette.
    [Show full text]
  • INTEGRATED SOLID WASTE MANAGEMENT for LOCAL GOVERNMENTS a Practical Guide
    INTEGRATED SOLID WASTE MANAGEMENT FOR LOCAL GOVERNMENTS A Practical Guide Improving solid waste management is crucial for countering public health impacts of uncollected waste and environmental impacts of open dumping and burning. This practical reference guide introduces key concepts of integrated solid waste management and identifi es crosscutting issues in the sector, derived mainly from fi eld experience in the technical assistance project Mainstreaming Integrated Solid Waste Management in Asia. This guide contains over 40 practice briefs covering solid waste management planning, waste categories, waste containers and collection, waste processing and diversion, landfi ll development, landfi ll operations, and contract issues. About the Asian Development Bank ADB’s vision is an Asia and Pacifi c region free of poverty. Its mission is to help its developing member countries reduce poverty and improve the quality of life of their people. Despite the region’s many successes, it remains home to a large share of the world’s poor. ADB is committed to reducing poverty through inclusive economic growth, environmentally sustainable growth, and regional integration. Based in Manila, ADB is owned by members, including from the region. Its main instruments for helping its developing member countries are policy dialogue, loans, equity investments, guarantees, grants, and technical assistance. INTEGRATED SOLID WASTE MANAGEMENT FOR LOCAL GOVERNMENTS A Practical Guide ASIAN DEVELOPMENT BANK 6 ADB Avenue, Mandaluyong City 1550 Metro Manila, Philippines 9 789292 578374 ASIAN DEVELOPMENT BANK www.adb.org Tool Kit for Solid Waste Management in Asian_COVER.indd 1 6/1/2017 5:14:11 PM INTEGRATED SOLID WASTE MANAGEMENT FOR LOCAL GOVERNMENTS A Practical Guide Improving solid waste management is crucial for countering the public health impacts of uncollected waste as well as the environmental impacts of open dumping and burning.
    [Show full text]
  • Disposing of Clinical and Dental Waste
    FEATURE CORE CPD: Disposing of clinical ONE HOUR and dental waste By Rebecca Allen1 ental professionals Defining different types of waste Amalgam waste is waste consisting are under increasing Clinical waste is defined as ‘any waste which of amalgam in any form and includes pressure to understand consists wholly or partly of human or animal all other materials contaminated with and adhere to clinical tissue, blood or other body fluids, excretions, amalgam. Amalgam waste is hazardous waste regulations. Proper drugs or other pharmaceutical products, due to the potential of harm to humans management and disposal swabs or dressings, syringes, needles or other and the environment caused by mercury. Dof clinical waste is vital and there is strict sharp instruments’. This type of waste may Any amalgam waste should be placed in a legislation in place to prevent harm being prove hazardous to any person coming into specialist dental container, with a mercury caused to the environment and to contact with it unless it is rendered safe. suppressant, to prevent the risk of harm to human health. Waste is defined as ‘hazardous’ when the your dental team from the mercury vapours. To dispel some of the misconceptions waste itself or the material or substances In addition all dental practices should have around clinical waste and to enable it contains are harmful to humans or the an amalgam separator installed to capture any organisations to clearly verify if they need environment. The other main waste stream amalgam particulates in waste water. These to take further steps to become compliant is known as offensive waste, which primarily should be fitted both to the dental chair and with all regulations, this article outlines contains waste that is considered unpleasant dirty sink.
    [Show full text]
  • Environmental Protection (Controlled Waste) Regulations 2004
    Western Australia Environmental Protection Act 1986 Environmental Protection (Controlled Waste) Regulations 2004 As at 24 Jan 2017 Version 01-c0-00 Extract from www.slp.wa.gov.au, see that website for further information Western Australia Environmental Protection (Controlled Waste) Regulations 2004 Contents Part 1 — Preliminary 1. Citation 1 2. Terms used 1 3. Application of regulations 4 Part 2 — Licensing Division 1 — General matters 4. Application for licence 6 5. Licensing 6 6. Conditions 7 7. Refund of fee 8 8. Validity of licence 9 9. Renewal of licence 9 10. Cancellation or suspension of, refusal to renew, licence 9 Division 2 — Carriers 11. Certain carriers to be licensed 11 12. Refusal of licence 11 13. Sub-contractors 11 14. Employment of unlicensed driver to transport bulk controlled waste 12 15. Notification of employment of licensed drivers 12 16. Interstate carriers 12 Division 3 — Drivers 17. Drivers to be licensed 13 18. Refusal of licence 13 As at 24 Jan 2017 Version 01-c0-00 page i Extract from www.slp.wa.gov.au, see that website for further information Environmental Protection (Controlled Waste) Regulations 2004 Contents 19. Driver identification card 14 20. Recognition of licence issued in another State or a Territory 14 Division 4 — Vehicle or tank 21. Vehicles and tanks of carriers to be licensed 15 22. Application for licence and inspection of vehicle or tank 15 23. Issue of licence 16 24. Validity of licence 16 Division 5 — Assignment of carrier’s business and transfer of licence 25A. Terms used 17 25B. Assignment of carrier’s business 17 25C.
    [Show full text]
  • Waste Management HSEQ Operational Procedure What This Procedure Describes
    Waste Management HSEQ Operational Procedure What this procedure describes How to manage TasNetworks waste materials by providing guidance on the identification, handling, storage, transport and disposal procedures for wastes including: contaminated soil and construction waste general office wastes hazardous substances IT assets, office furniture and equipment pole ash sharps waste scrap wood, wooden cross arms, burnt bushfire waste pole ash, treated and untreated wood poles •most preferable Avoid concrete, steel concrete poles, street light •lowering the amount of poles Reduce steel, copper and aluminium waste produced •using materials repeatedly SF6 equipment and gas Reuse metres, metre panels, electrical •using materials to make new Recycle equipment excluding oil insulated products transformers and equipment •recovering energy from waste cable insulation and jointing kits Recover light globes and batteries •safe disposal of waste to landfill Landfill packaging, pallets and cable drums •least preferable gas cylinders waste water and waste to sewer waste from vegetation clearing Why it is required To assist you to apply the waste management hierarchy to avoid, reduce, reuse, recycle, recover and dispose to landfill waste. TasNetworks is required to manage the waste in accordance with relevant health, safety and environmental legislation and codes of practice. To prevent environmental pollution associated with the handling, storage and disposal of waste materials. The procedure supports the TasNetworks goal of Zero
    [Show full text]
  • (Specially Controlled Waste) Regulations, 2010
    GUERNSEY STATUTORY INSTRUMENT The Waste Control and Disposal (Specially Controlled Waste) Regulations, 2010 Made 4 Coming into Operation 1"' June, 201 0 Laid before the States THE DIRECTOR OF ENVIRONMENTAL HEALTH AND POLLUTION REGULATION, in exercise of the powers conferred on her by sections 26 and 34 of the Environmental Pollution (Waste Control and Disposal) b ordinancea, 20 10, section 72 of the Environmental Pollution (Guernsey) Law, 2004 and of all other powers enabling her in that behalf, hereby orders:- Interpretation. 1. (1) In these Regulations, unless the context otherwise requires - "commercial waste" means waste arising from any activity carried on by way of business, and includes agricultural and horticultural waste other than such waste arising from use of the curtilage of a dwelling house for purposes connected with the use of that dwelling house, a Approved by resolution of the States on 28t" April, 201 0. Order in Council No. XI11 of 2004. "Director" means the person appointed as Director of Environmental Health and Pollution Regulation under section 4 of the Law, "dwelling house" means a building or part of a building used as a permanent residence for members of one household, and includes the curtilage of such a building, but does not include a hotel, hospital or other place where persons may temporarily live, "enactment" includes an instrument and any Directive, Regulation or Decision of any institution of the European Union, "European Waste Catalogue" means the list of wastes pursuant to Article l(a) of Directive
    [Show full text]
  • Decision-Makers Guide (PDF)
    © 2000 The International Bank for Reconstruction and Development / THE WORLD BANK 1818 H Street, N.W. Washington, D.C. 20433, U.S.A. All rights reserved Manufactured in the United States of America First printing June 2000 This report has been prepared by the staff of the World Bank. The judgments expressed do not necessari- ly reflect the views of the Board of Executive Directors or of the governments they represent. The material in this publication is copyrighted. The World Bank encourages dissemination of its work and will normally grant permission promptly. Permission to photocopy items for internal or personal use, for the internal or personal use of specific clients, or for educational classroom use, is granted by the World Bank, provided that the appropriate fee is paid directly to the Copyright Clearance Center, Inc., 222 Rosewood Drive, Danvers, MA 01923, U.S.A., tele- phone 978-750-8400, fax 978-750-4470. Please contact the Copyright Clearance Center before photocopying items. For permission to reprint individual articles or chapters, please fax your request with complete informa- tion to the Republication Department, Copyright Clearance Center, fax 978-750-4470. All other queries on rights and licenses should be addressed to the World Bank at the address above or faxed to 202-522-2422. Cover photo by unknown. Contents Foreword v Solid Waste Incineration 1 Institutional Framework 2 Waste as Fuel 5 Economics and Finance 7 Project Cycle 10 Incineration Technology 11 iii Foreword The Decision Makers’ Guide to Incineration of Municipal the project is not institutionally, economically, techni- Solid Waste is a tool for preliminary assessment of the cally, or environmentally feasible.
    [Show full text]
  • Towards Zero Waste One Wales: One Planet Welsh Government Draft Position Statement on Agricultural Waste
    Welsh Government Towards Zero Waste One Wales: One Planet Welsh Government Draft Position Statement on Agricultural Waste June 2014 Digital ISBN 978 1 4734 1395 5 © Crown copyright 2014 WG21892 Contents 1 - Agricultural Waste in Wales ............................................................................. 2 2 - Sector plans ....................................................................................................... 3 3 - Current Situation ............................................................................................... 3 4 - Regulation ........................................................................................................ 13 5 - Actions in place to secure the more sustainable management of agricultural waste ............................................................................................. 18 6 - Sources of Information, Advice and Guidance on Agricultural Waste ....... 20 Annex A – Definitions ........................................................................................... 22 1 1 - Agricultural Waste in Wales This draft position statement has been developed with input from a wide range of interested parties, and a stakeholder event was held to elicit input to the document. It would be useful to those reading this paper to refer to the Codes of Good Agricultural Practice (CoGAP) (Protection of Water, Soil and Air for Wales). Part 3, Section 7 of the CoGAP contains information on the legal requirements on agricultural waste management, together with useful advice and guidance
    [Show full text]