Measurement of Non-Exhaust Particulate Matter

Total Page:16

File Type:pdf, Size:1020Kb

Measurement of Non-Exhaust Particulate Matter PARTICULATES Characterisation of Exhaust Particulate Emissions from Road Vehicles Deliverable 8 Measurement of non-exhaust particulate matter Version 2.0 – October 2004 A project sponsored by: EUROPEAN COMMISSION Directorate General Transport and Environment In the framework of: Fifth Framework Programme Competitive and Sustainable Growth Sustainable Mobility and Intermodality Contractors LAT/AUTh: Aristotle University of Thessaloniki, Laboratory of Applied Thermodynamics - EL CONCAWE: CONCAWE, the oil companies' European organisation for environment, health and safety - B VOLVO: AB Volvo - S AVL: AVL List GmbH - A EMPA: Swiss Federal Laboratories for Material Testing and Research - CH MTC: MTC AB - S TUT: Tampere University of Technology - FIN TUG: Institute for Internal Combustion Engines and Thermodynamics, Technical University Graz - A IFP: Institut Français du Pétrole - F AEA: AEA Technology plc - UK JRC: European Commission – Joint Research Centre - NL REGIENOV: REGIENOV - RENAULT Recherche Innovation - F INRETS: Institut National de Recherche sur les Transports et leur Securité - F DEKATI: DEKATI Oy - FIN SU: Department of Analytical Chemistry, Stockholm University - S DHEUAMS: Department of Hygiene and Epidemiology, University of Athens Medical School - EL INERIS: Institut National de l’ Environnement Industriel et des Risques - F LWA: Les White Associates - UK TRL: Transport Research Laboratory - UK VKA: Institute for Internal Combustion Engines, Aachen University of Technology – D VTT VTT Energy – Engine Technology and Energy in Transportation - FI A project sponsored by: EUROPEAN COMMISSION Directorate General Transport and Environment In the framework of: Fifth Framework Programme Competitive and Sustainable Growth Sustainable Mobility and Intermodality Publication data form 1. Framework Programme 2. Contract No European Commission – DG TrEn, 5th Framework 2000-RD.11091 Programme Competitive and Sustainable Growth Sustainable Mobility and Intermodality 3. Project Title 4. Coordinator Characterisation of Exhaust Particulate Emissions from Road LAT/AUTh Vehicles (PARTICULATES) 5. Deliverable Title 6. Deliverable No Measurement of non-exhaust particulate matter 8 (revised) 7. Deliverable Responsible 8. Language 9. Publication Date Dr Paul Boulter - TRL English October 2004 10. Author(s) 11. Affiliation Lakhu Luhana1, Ranjeet Sokhi1, Lynne Warner1, Hongjun Mao1, Paul 1 University of Hertfordshire, College Boulter2, Ian McCrae2, Julian Wright3 and Daniel Osborn3 Lane, Hatfield, Herts AL10 9AB, UK. 2 TRL Ltd, Crowthorne House, Nine Mile Ride, Wokingham, Berkshire, RG40 3GA, UK 3 CEH, Abbots Ripton, Huntingdon, Cambridgeshire PE28 2LS, UK 12. Summary This report presents the findings of work undertaken to characterise airborne particles emitted by road traffic, with the aim of deriving emission factors for non-exhaust particle sources such as tyre wear, brake wear and road surface wear. The report includes a literature review which examines the state of the art in this field, and describes the formulation of an optimum methodology for determining emission factors. Wear rates for brake pads and tyres have been determined gravimetrically for in-service cars. Sampling campaigns have been carried out to collect ambient particulate matter and source materials, including road dust, tyre material and brake wear particles. Ambient airborne particles, as well as the source materials, have been characterised chemically and physically using a suite of analytical techniques including ICP/AES, ICP/MS and SEM. Levels of PM10 and PM2.5 have been estimated from gravimetric measurements at roadside and background sites at the University of Hertfordshire and London. The information from these campaigns and the literature review has been used to identify specific tracers for apportioning the sources of non-exhaust particles, and has assisted in the design of a main tunnel sampling campaign to derive appropriate emission factors. The main campaign has been conducted in the Hatfield Tunnel on the A1(M) motorway north of London. Emission factors for light-duty and heavy-duty vehicles have been determined using principle component analysis and multiple regression analysis. 13. Notes 14. Internet reference 15. Key Words 16. Distribution statement Non-exhaust particles, emission factors, receptor FREE modelling, tyre wear, brake wear, road dust 17. No of Pages 18. Price 19. Declassification date 20. Bibliography 96 FREE NO Acknowledgements The authors would like to take this opportunity to thank the following for their help and advice during this project: • Westminster City Council, London, UK. • Ana Deletic and David Orr, Aberdeen University, UK. • Professor Dick van den Hout, TNO Institute of Environmental Sciences: Energy Research and Process Innovation, the Netherlands. • Dr Peter Schmid, EMPA, Dubendorf, Switzerland. • Dr Jay Turner, Washington University, St. Louis, Missouri, USA. • Ms Laurel Martin at the California Institute of Technology, Pasadena, California. • Claire Wienburg, CEH, UK. • Sarah James, Nick Walsh and Jacqui Duffett, Royal Holloway College, University of London, UK. • Carillion-URS plc, who operate the Hatfield Tunnel on behalf of the Highways Agency and, in particular, Mr Jeff Chappell the Hatfield Tunnel manager. Table of Contents 1 Introduction ......................................................................................................................................1 1.1 Background ...........................................................................................................................................1 1.2 Non-exhaust particle research in the PARTICULATES project ...............................................2 2 Review of non-exhaust particle research.................................................................................3 2.1 Atmospheric particulate matter........................................................................................................3 2.2 Tyre wear particles ..............................................................................................................................4 2.2.1 Factors affecting tyre wear.........................................................................................................4 2.2.2 Tyre wear rates............................................................................................................................5 2.2.3 Tyre composition .........................................................................................................................6 2.2.4 Tyre wear particle characteristics .............................................................................................7 2.3 Brake Wear particles ...........................................................................................................................9 2.3.1 Factors affecting brake wear .....................................................................................................9 2.3.2 Brake wear rates........................................................................................................................10 2.3.3 Brake composition.....................................................................................................................10 2.3.4 Brake wear particle characteristics.........................................................................................12 2.4 Clutch wear particles ........................................................................................................................13 2.5 Corrosion particles............................................................................................................................13 2.6 Road surface wear particles............................................................................................................14 2.7 Resuspension of Road Dust ...........................................................................................................16 2.7.1 Sources and composition.........................................................................................................16 2.7.2 Factors affecting resuspension ...............................................................................................17 2.7.3 Particle emission factors ..........................................................................................................18 2.8 Research methods.............................................................................................................................18 2.8.1 Methods for determining tyre wear and tyre particle emissions.........................................18 2.8.2 Methods for determining brake wear and particle emissions .............................................19 2.8.3 Methods for sampling road dust..............................................................................................19 2.8.4 Source apportionment methods: receptor modelling ...........................................................20 2.9 Summary of literature review..........................................................................................................23 2.9.1 Tyre wear particles....................................................................................................................23 2.9.2 Brake wear particles..................................................................................................................23 2.9.3 Clutch wear particles.................................................................................................................23
Recommended publications
  • GHOST GEAR: the ABANDONED FISHING NETS HAUNTING OUR OCEANS Sea Turtle Entangled in Fishing Gear in the Mediterranean Sea © Marco Care/Greenpeace CONTENTS
    GHOST GEAR: THE ABANDONED FISHING NETS HAUNTING OUR OCEANS Sea turtle entangled in fishing gear in the Mediterranean Sea © Marco Care/Greenpeace CONTENTS 4 Zusammenfassung 5 Executive summary 6 Introduction 8 Main types of fishing – Nets – Lines – Traps & pots – FADs 11 Ghost gear impacts – Killing ocean creatures – Damaging habitats – Economic and other impacts 13 Current regulations – International agreements and recommendations – Other programmes and resolutions – A cross-sector approach – The need for a Global Ocean Treaty 16 References 2019 / 10 Published by Greenpeace Germany November 2019 Stand Greenpeace e. V., Hongkongstraße 10, 20457 Hamburg, Tel. 040/3 06 18 - 0, [email protected] , www . greenpeace . de Authors Karli Thomas, Dr. Cat Dorey and Farah Obaidullah Responsible for content Helena Spiritus Layout Klasse 3b, Hamburg S 0264 1 Contents 3 DEUTSCHE ZUSAMMENFASSUNG DER STUDIE GHOST GEAR: THE ABANDONED FISHING NETS HAUNTING OUR OCEANS → Rund 640.000 Tonnen altes Fischereigerät inklusive Geisternetzen, Bojen, Leinen, Fallen und Körbe landen jährlich als Fischereimüll in den Ozeanen. → Weltweit trägt altes Fischereigerät zu etwa zehn Prozent zum Plastikeintrag in die Meere bei. → 45 Prozent aller Arten auf der Roten IUCN-Liste hatten bereits Kontakt mit Plastik im Meer. → Sechs Prozent aller eingesetzten Netze, neun Prozent aller Fallen und 29 Prozent aller Langleinen gehen jährlich auf den Ozeanen verloren und enden als Meeresmüll. → Treibnetze, Fallen und Fischsammler (Fish Aggregating Devices, FADs) gehen weltweit am häufigsten als Müll auf den Ozeanen verloren und bergen die meisten Risiken für Meereslebewesen. → Durch FADs sterben 2,8 bis 6,7 Mal mehr Tiere - darunter bedrohte Arten wie Haie – als Beifang als die Zielarten, für die sie eingesetzt werden.
    [Show full text]
  • Municipal Solid Waste Landfill Operation and Management Workbook
    MUNICIPAL SOLID WASTE LANDFILL OPERATION AND MANAGEMENT WORKBOOK Revised April 2018 Preface In many ways, constructing, operating and maintaining a municipal solid waste landfill is similar to constructing, operating, and maintaining a highway, dam, canal, bridge, or other engineered structure. The most important similarity is that landfills, like other engineered structures, must be constructed and operated in a manner that will provide safe, long-term, and reliable service to the communities they serve. Proper design, construction, operation, monitoring, closure and post-closure care are critical because after disposal the waste can be a threat to human health and the environment for decades to centuries. This workbook is intended to provide municipal landfill operators and managers in Wyoming with the fundamental knowledge and technical background necessary to ensure that landfills are operated efficiently, effectively, and in a manner that is protective of human health and the environment. This workbook contains information regarding basic construction and operation activities that are encountered on a routine basis at most landfills. The basic procedures and fundamental elements of landfill permitting, construction management, monitoring, closure, post-closure care, and financial assurance are also addressed. The workbook includes informative tips and information that landfill operators and managers can use to conserve landfill space, minimize the potential for pollution, reduce operating costs, and comply with applicable rules and regulations. In addition to this workbook, operators and managers need to become familiar with the Wyoming Solid Waste Rules and Regulations applicable to municipal solid waste. The DEQ also provides numerous guidelines that may help understand regulatory requirements in more detail.
    [Show full text]
  • Use of Waste-Tire Materials in Architectural Application in Egypt International Journal of Chemtech Research
    International Journal of ChemTech Research CODEN (USA): IJCRGG, ISSN: 0974-4290, ISSN(Online):2455-9555 Vol.9, No.12 pp 14-27, 2016 Use of Waste-Tire Materials in Architectural Application in Egypt Farrag, Nermin Mokhtar* Civil and Architectural Engineering Department, National Research Center, Egypt Abstract : With the increase in the production of the automobile, a lot of waste tire need to be disposed. Due to the reduction of available sites for waste disposal, a lot of countries forbid the disposal of waste tire rubber in landfills. Researches seek for a long time to find alternatives to the waste tire. Reusing and recycled waste tire rubber is the promising material in the Architectural Applications due to its light weight, flexibility, insulating properties, and energy absorption. There are many studies show that Egypt capable of competing within the global tires Reusing sector, the paper aims to how to improve this Sector to face its future challenges and attract Foreign Investment, many points should be considered such as improving the legislative framework, rising of awareness, developing business development service and, role of external institutionalization and financing. Keywords: tires wastes, Tires bales, sound barrier, landscaping mulch, Architectural Applications, reuse management. Introduction Recycling waste materials is not a new phenomenon, Fig.1. The reuse of solid waste can improve of environmental quality, contribute to solutions of urban issues, energy shortage, and waste disposal. Recycling provide job opportunities to the needy people, conserve finite resources and save the environment. Recycling of rubber receives less attention than other waste materials such as Paper, glass, steel cans due to its final product, quality and public acceptance, financial value, marketability, and margin of the earning.
    [Show full text]
  • Urbanization As a Threat to Biodiversity: Trophic Theory, Economic Geography, and Implications for Conservation Land Acquisition
    Proceedings of a Symposium at the Society for Conservation Biology 2004 Annual Meeting URBANIZATION AS A THREAT TO BIODIVERSITY: TROPHIC THEORY, ECONOMIC GEOGRAPHY, AND IMPLICATIONS FOR CONSERVATION LAND ACQUISITION Brian Czech1 ABSTRACT—Habitat loss is often cited as the primary cause of species endangerment in the United States, followed by invasive species, pollution, and direct take. Urbanization, one type of habitat loss, is the leading cause of species endangerment in the contiguous United States and entails a relatively thorough transformation from the “economy of nature” to the human economy. Principles of economic geography indicate that urbanization will continue as a function of economic growth, while principles of conservation biology indicate that the most thorough competitive exclusion occurs in urban areas. These findings suggest the need for an ecologically macroeconomic approach to conservation land acquisition strategies. “Habitat loss” is often cited as the primary cause of species these types of habitat loss are considered separate causes of endangerment in the United States, followed by invasive species endangerment, invasive species are identified as the species, pollution, disease, and direct take. However, vari- leading cause of species endangerment in the United States, ous types of habitat loss are readily identified, such as log- including Hawaii and Puerto Rico (Czech et al. 2000). On ging, mining, agriculture, and urbanization (table 1). When the mainland United States, however, urbanization is the Table 1.— Causes of endangerment for the first 877 (of the current 1,262) species in the United States and Puerto Rico classified as threatened or endangered by the United States Fish and Wildlife Service (from Czech et al.
    [Show full text]
  • Toxic Tide: the Threat of Marine Plastic Pollution in Australia
    The Senate Environment and Communications References Committee Toxic tide: the threat of marine plastic pollution in Australia April 2016 © Commonwealth of Australia 2016 ISBN 978-1-76010-400-9 Committee contact details PO Box 6100 Parliament House Canberra ACT 2600 Tel: 02 6277 3526 Fax: 02 6277 5818 Email: [email protected] Internet: www.aph.gov.au/senate_ec This work is licensed under the Creative Commons Attribution-NonCommercial-NoDerivs 3.0 Australia License. The details of this licence are available on the Creative Commons website: http://creativecommons.org/licenses/by-nc-nd/3.0/au/. This document was printed by the Senate Printing Unit, Parliament House, Canberra Committee membership Committee members Senator Anne Urquhart, Chair ALP, TAS Senator Linda Reynolds CSC, Deputy Chair (from 12 October 2015) LP, WA Senator Anne McEwen (from 18 April 2016) ALP, WA Senator Chris Back (from 12 October 2015) LP, WA Senator the Hon Lisa Singh ALP, TAS Senator Larissa Waters AG, QLD Substitute member for this inquiry Senator Peter Whish-Wilson (AG, TAS) for Senator Larissa Waters (AG, QLD) Former members Senator the Hon Anne Ruston, Deputy Chair (to 12 October 2015) LP, SA Senator the Hon James McGrath (to 12 October 2015) LP, QLD Senator Joe Bullock (to 13 April 2016) ALP, WA Committee secretariat Ms Christine McDonald, Committee Secretary Mr Colby Hannan, Principal Research Officer Ms Fattimah Imtoual, Senior Research Officer Ms Kirsty Cattanach, Research Officer iii iv Table of Contents List of recommendations ..................................................................................vii List of abbreviations ....................................................................................... xiii Chapter 1: Introduction ..................................................................................... 1 Conduct of the inquiry ............................................................................................ 1 Acknowledgement .................................................................................................
    [Show full text]
  • Rates of Particulate Pollution Deposition Onto Leaf Surfaces: Temporal and Inter-Species Magnetic Analyses
    ARTICLE IN PRESS Environmental Pollution xxx (2010) 1–7 Contents lists available at ScienceDirect Environmental Pollution journal homepage: www.elsevier.com/locate/envpol Rates of particulate pollution deposition onto leaf surfaces: Temporal and inter-species magnetic analyses R. Mitchell a,*, B.A. Maher a, R. Kinnersley b a Centre for Environmental Magnetism and Palaeomagnetism, Lancaster Environment Centre, University of Lancaster, Lancaster LA1 4YQ, UK b Evidence Directorate, Environment Agency, Olton Court, 10 Warwick Road, Olton, Solihull B92 7HX, UK This research uses biomagnetic techniques to enable quantitative mapping of particulate pollution distribution at uniquely high spatial resolution. article info abstract Article history: Evaluation of health impacts arising from inhalation of pollutant particles <10 mm (PM10) is an active Received 1 September 2009 research area. However, lack of exposure data at high spatial resolution impedes identification of Received in revised form causal associations between exposure and illness. Biomagnetic monitoring of PM10 deposited on tree 11 December 2009 leaves may provide a means of obtaining exposure data at high spatial resolution. To calculate ambient Accepted 16 December 2009 PM10 concentrations from leaf magnetic values, the relationship between the magnetic signal and total PM10 mass must be quantified, and the exposure time (via magnetic deposition velocity (MVd) Keywords: calculations) known. Birches display higher MV (w5cmÀ1) than lime trees (w2cmÀ1). Leaf saturation Magnetic biomonitoring d w Deposition velocity remanence values reached ‘equilibrium’ with ambient PM10 concentrations after 6 ‘dry’ days (<3 mm/day rainfall). Other co-located species displayed within-species consistency in MV ; robust PM10 monitoring d Tree leaves inter-calibration can thus be achieved, enabling magnetic PM10 biomonitoring at unprecedented spatial Inter-species calibration resolution.
    [Show full text]
  • HEPA) Filter - Ultra Low Penetration Air (ULPA) Filter (Also Referred to As Extended Media
    EPA-452/F-03-023 Air Pollution Cocntrol Technology Fact Sheet Name of Technology: Paper/Nonwoven Filter - High Efficiency Particle Air (HEPA) Filter - Ultra Low Penetration Air (ULPA) Filter (also referred to as Extended Media) Type of Technology: Control Device - Capture/Disposal Applicable Pollutants: Submicron Particulate Matter (PM) greater than or equal to 0.3 micrometer (µm) in aerodynamic diameter, and PM greater than or equal to 0.12 µm in aerodynamic diameter that is chemically, biologically, or radioactively toxic; hazardous air pollutants (HAPs) that are in particulate form, such as most metals (mercury is the notable exception, as a significant portion of emissions are in the form of elemental vapor). Achievable Emission Limits/Reductions: HEPA and ULPA filters are classified by their minimum collection efficiency. Many international standards and classes currently exist for high efficiency filters (Osborn, 1989). In general, HEPA and ULPA filters are defined as having the following minimum efficiency rating (Heumann, 1997): HEPA: 99.97% efficiency for the removal of 0.3 µm diameter or larger PM, ULPA: 99.9995% efficiency for the removal of 0.12 µm diameter or larger PM. Some extended media filters are capable of much higher efficiencies. Commercially available filters can control PM with 0.01 µm diameter at efficiencies of 99.99+% and PM with 0.1 µm diameter at efficiencies of 99.9999+% (Gaddish, 1989; Osborn, 1989). Several factors determine HEPA and ULPA filter collection efficiency. These include gas filtration, velocity, particle characteristics, and filter media characteristics. In general, the collection efficiency increases with increasing filtration velocity and particle size.
    [Show full text]
  • Review of the Human Health & Ecological Safety of Exposure to Recycled Tire Rubber Found at Playgrounds and Synthetic Turf F
    Review of the Human Health & Ecological Safety of Exposure to Recycled Tire Rubber found at Playgrounds and Synthetic Turf Fields Prepared for: Rubber Manufacturers Association Washington, DC Prepared by: Cardno ChemRisk Pittsburgh, PA August 1, 2013 Executive Summary Increasingly, tires that reach the end of their serviceable life are processed for beneficial reuse in novel applications. Some of these include soil and surface amendments at athletic fields, playground and garden mulch, and bound surfaces at playgrounds and athletic facilities. These modern artificial surfaces reduce the likelihood of personal injury, provide uniform recreational playing surfaces, promote energy conservation, eliminate pesticide and fertilizer usage, and support waste recycling. Tires are manufactured with a variety of materials and additives to ensure optimum product safety, reliability and performance. Some tire ingredients are considered to be human health hazards at exposure levels several orders of magnitude greater than possible from contact with finished consumer products. Accordingly, athletes, parents and other stakeholders have expressed questions and concerns about the potential for adverse human health or ecological effects from the use of recycled tires in sport surface or playground materials. The purpose of this report is to evaluate the health and ecological risks associated with the use of recycled tire rubber in consumer applications, particularly playgrounds and athletic fields. In doing so, a thorough review of available literature was conducted including studies from both advocates and opponents to the use of recycled tire materials. An examination of the weight of evidence across all of the available studies was conducted to enable a comprehensive assessment of potential risk.
    [Show full text]
  • WHO Guidelines for Indoor Air Quality : Selected Pollutants
    WHO GUIDELINES FOR INDOOR AIR QUALITY WHO GUIDELINES FOR INDOOR AIR QUALITY: WHO GUIDELINES FOR INDOOR AIR QUALITY: This book presents WHO guidelines for the protection of pub- lic health from risks due to a number of chemicals commonly present in indoor air. The substances considered in this review, i.e. benzene, carbon monoxide, formaldehyde, naphthalene, nitrogen dioxide, polycyclic aromatic hydrocarbons (especially benzo[a]pyrene), radon, trichloroethylene and tetrachloroethyl- ene, have indoor sources, are known in respect of their hazard- ousness to health and are often found indoors in concentrations of health concern. The guidelines are targeted at public health professionals involved in preventing health risks of environmen- SELECTED CHEMICALS SELECTED tal exposures, as well as specialists and authorities involved in the design and use of buildings, indoor materials and products. POLLUTANTS They provide a scientific basis for legally enforceable standards. World Health Organization Regional Offi ce for Europe Scherfi gsvej 8, DK-2100 Copenhagen Ø, Denmark Tel.: +45 39 17 17 17. Fax: +45 39 17 18 18 E-mail: [email protected] Web site: www.euro.who.int WHO guidelines for indoor air quality: selected pollutants The WHO European Centre for Environment and Health, Bonn Office, WHO Regional Office for Europe coordinated the development of these WHO guidelines. Keywords AIR POLLUTION, INDOOR - prevention and control AIR POLLUTANTS - adverse effects ORGANIC CHEMICALS ENVIRONMENTAL EXPOSURE - adverse effects GUIDELINES ISBN 978 92 890 0213 4 Address requests for publications of the WHO Regional Office for Europe to: Publications WHO Regional Office for Europe Scherfigsvej 8 DK-2100 Copenhagen Ø, Denmark Alternatively, complete an online request form for documentation, health information, or for per- mission to quote or translate, on the Regional Office web site (http://www.euro.who.int/pubrequest).
    [Show full text]
  • Emission Control Technology for Masonry Fireplaces
    Revolutionary Emission Control System for Masonry Fireplace Retro-Fits from FMI Products Emission Control Technology for Masonry Fireplaces Wood smoke emissions are currently one of the most significant health risks in the US. New regulatory standards for wood burning fireplaces are being passed to reduce smoke and particulate emissions nationwide. Wood burning fireplaces are being restricted by Clean Air Regulators in almost every state. The PureFire Wood Burning Fireplace PureFire™ Technology is designed to solve this problem. Fireplace Technology FMI Products has successfully developed a wood burning fireplace emission control technology that reduces particulate emissions by 80%. The PureFire™ system reduces airborne PM2.5 particulates in masonry fireplaces to 4.3 g/kg. This is well below the EPA Phase 2 emissions limit of 5.1 g/kg. The PureFire™ system is catalytic and uses a patented hood device to isolate the offensive pollutants and wood smoke. The particulates are then destroyed by a state-of-the-art catalytic system. The PureFire™ System can be installed in less than an hour, it doesn’t require any power or connections, it is maintenance free and it is affordable to the homeowner. The US Environmental Protection Agency promotes fireplace technologies that meet the Phase 2 emission limit of 5.1 g/kg. Existing fireplaces currently emit 12-15 g/kg of particulate pollution. There hasn’t been a technological solution for masonry wood burning fireplaces to meet the new EPA Phase 2 emissions limit. UNTIL NOW! The PureFire™ System was tested to stringent EPA requirements at Omni Test Laboratory in Portland OR.
    [Show full text]
  • Evaluation of Health Effects of Recycled Waste Tires in Playground and Track Products
    Contractor’s Report to the Board Evaluation of Health Effects of Recycled Waste Tires in Playground and Track Products Produced under contract by: January 2007 S TATE OF C ALIFORNIA Arnold Schwarzenegger Governor Linda S. Adams Secretary, California Environmental Protection Agency INTEGRATED WASTE MANAGEMENT BOARD Margo Reid Brown Wesley Chesbro Jeffrey Danzinger Board Chair Board Member Board Member Rosalie Mulé Gary Petersen Vacant Position Board Member Board Member Board Member Mark Leary Executive Director For additional copies of this publication, contact: Integrated Waste Management Board Public Affairs Office, Publications Clearinghouse (MS–6) 1001 I Street P.O. Box 4025 Sacramento, CA 95812-4025 www.ciwmb.ca.gov/Publications/ 1-800-CA-WASTE (California only) or (916) 341-6306 Publication #622-06-013 Copies of this document originally provided by CIWMB were printed on recycled paper containing 100 percent postconsumer fiber. Copyright © 2007 by the California Integrated Waste Management Board. All rights reserved. This publication, or parts thereof, may not be reproduced in any form without permission. Prepared as part of contract number IWM-C2070, $420,000 The California Integrated Waste Management Board (CIWMB) does not discriminate on the basis of disability in access to its programs. CIWMB publications are available in accessible formats upon request by calling the Public Affairs Office at (916) 341-6300. Persons with hearing impairments can reach the CIWMB through the California Relay Service, 1-800-735-2929. Disclaimer: This report to the Board was produced under contract by the Office of Environmental Health Hazard Assessment of California Environmental Protection Agency. The statements and conclusions contained in this report are those of the contractor and not necessarily those of the California Integrated Waste Management Board, its employees, or the State of California and should not be cited or quoted as official Board policy or direction.
    [Show full text]
  • Indoor Air Quality in Commercial and Institutional Buildings
    Indoor Air Quality in Commercial and Institutional Buildings OSHA 3430-04 2011 Occupational Safety and Health Act of 1970 “To assure safe and healthful working conditions for working men and women; by authorizing enforcement of the standards developed under the Act; by assisting and encouraging the States in their efforts to assure safe and healthful working conditions; by providing for research, information, education, and training in the field of occupational safety and health.” This publication provides a general overview of a particular standards-related topic. This publication does not alter or determine compliance responsibili- ties which are set forth in OSHA standards, and the Occupational Safety and Health Act of 1970. More- over, because interpretations and enforcement poli- cy may change over time, for additional guidance on OSHA compliance requirements, the reader should consult current administrative interpretations and decisions by the Occupational Safety and Health Review Commission and the courts. Material contained in this publication is in the public domain and may be reproduced, fully or partially, without permission. Source credit is requested but not required. This information will be made available to sensory- impaired individuals upon request. Voice phone: (202) 693-1999; teletypewriter (TTY) number: 1-877- 889-5627. Indoor Air Quality in Commercial and Institutional Buildings Occupational Safety and Health Administration U.S. Department of Labor OSHA 3430-04 2011 The guidance is advisory in nature and informational in content. It is not a standard or regulation, and it neither creates new legal obligations nor alters existing obligations created by OSHA standards or the Occupational Safety and Health Act.
    [Show full text]