Diesel Exhaust/Diesel Particulate Matter
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Report to the Legislature: Indoor Air Pollution in California
California Environmental Protection Agency Air Resources Board Report to the California Legislature INDOOR AIR POLLUTION IN CALIFORNIA A report submitted by: California Air Resources Board July, 2005 Pursuant to Health and Safety Code § 39930 (Assembly Bill 1173, Keeley, 2002) Arnold Schwarzenegger Governor Indoor Air Pollution in California July, 2005 ii Indoor Air Pollution in California July, 2005 ACKNOWLEDGEMENTS This report was prepared with the able and dedicated support from Jacqueline Cummins, Marisa Bolander, Jeania Delaney, Elizabeth Byers, and Heather Choi. We appreciate the valuable input received from the following groups: • Many government agency representatives who provided information and thoughtful comments on draft reports, especially Jed Waldman, Sandy McNeel, Janet Macher, Feng Tsai, and Elizabeth Katz, Department of Health Services; Richard Lam and Bob Blaisdell, Office of Environmental Health Hazard Assessment; Deborah Gold and Bob Nakamura, Cal/OSHA; Bill Pennington and Bruce Maeda, California Energy Commission; Dana Papke and Kathy Frevert, California Integrated Waste Management Board; Randy Segawa, and Madeline Brattesani, Department of Pesticide Regulation; and many others. • Bill Fisk, Lawrence Berkeley National Laboratory, for assistance in assessing the costs of indoor pollution. • Susan Lum, ARB, project website management, and Chris Jakober, for general technical assistance. • Stakeholders from the public and private sectors, who attended the public workshops and shared their experiences and suggestions -
Developmental Study of Soot-Oxidation Catalysts for Fireplaces: the Effect of Binder and Preparation Techniques on Catalyst Texture and Activity
catalysts Article Developmental Study of Soot-Oxidation Catalysts for Fireplaces: The Effect of Binder and Preparation Techniques on Catalyst Texture and Activity Pauliina Nevalainen, Niko Kinnunen * and Mika Suvanto University of Eastern Finland, Department of Chemistry, P. O. Box 111, FI-80101, Joensuu, Finland; Pauliina.Nevalainen@uef.fi (P.N.); mika.suvanto@uef.fi (M.S.) * Correspondence: niko.kinnunen@uef.fi Received: 8 October 2019; Accepted: 13 November 2019; Published: 15 November 2019 Abstract: An awareness of increasing climate and health problems has driven the development of new functional and affordable soot-oxidation catalysts for stationary sources, such as fireplaces. In this study, Al(OH)3, water glass and acidic aluminium phosphate binder materials were mixed with soot-oxidation catalysts. The effect of the binder on the performance of the Ag/La-Al2O3 catalyst was examined, while the Pt/La-Al2O3 catalyst bound with Al(OH)3 was used as a reference. Soot was oxidised above 340 ◦C on the Ag/La-Al2O3 catalyst, but at 310 ◦C with same catalyst bound with Al(OH)3. The addition of water glass decreased the catalytic performance because large silver crystals and agglomeration resulted in a blockage of the support material’s pores. Pt/La-Al2O3 bound with Al(OH)3 was ineffective in a fireplace environment. We believe that AgOx is the active form of silver in the catalyst. Hence, Ag/La-Al2O3 was shown to be compatible with the Al(OH)3 binder as an effective catalyst for fireplace soot oxidation. Keywords: binder; silver; Al(OH)3; fireplace; soot emission 1. -
Diesel Exhaust
DIESEL EXHAUST What is DIESEL EXHAUST? Vehicles that use diesel fuel release exhaust that is composed of a variety of compounds harmful to human health and the environment. Vehicles that use diesel fuel include trucks, commercial buses, school buses and construction equipment. Gases released in diesel exhaust can include benzene, formaldehyde and other compounds that can contribute to cancer and other health problems. In addition to the gases, diesel particulate matter (DPM) is released as solid particles of many sizes and compositions. How can people be exposed to diesel exhaust? Diesel engines are everywhere in the world, so most people are exposed to diesel exhaust on a nearly daily basis. The most common exposure is by breathing air that contains its gases or its particulates. Exposure to diesel exhaust is not likely to occur through eating, drinking or skin contact. Diesel exhaust travels through the atmosphere and affect areas without obvious exhaust sources. How can diesel exhaust affect my health? Diesel exhaust is considered likely to cause cancer in humans. While the gaseous chemicals in diesel exhaust are a health concern and may cause cancer, there is significant concern about exposure to diesel particulate matter, especially the fine and ultra-fine particles. Exposure to diesel exhaust may irritate the eyes, nose, throat and lungs, and cause lightheadedness. Exposure to high concentrations can also cause problems for people with respiratory conditions, such as asthma. Chronic exposure can damage the lungs and affect immune system functions. What should I do if exposed to diesel exhaust? Breathing - Exposure to diesel exhaust becomes a concern only under certain conditions. -
Are Black Carbon and Soot the Same? Title Page
Discussion Paper | Discussion Paper | Discussion Paper | Discussion Paper | Atmos. Chem. Phys. Discuss., 12, 24821–24846, 2012 Atmospheric www.atmos-chem-phys-discuss.net/12/24821/2012/ Chemistry ACPD doi:10.5194/acpd-12-24821-2012 and Physics © Author(s) 2012. CC Attribution 3.0 License. Discussions 12, 24821–24846, 2012 This discussion paper is/has been under review for the journal Atmospheric Chemistry Are black carbon and Physics (ACP). Please refer to the corresponding final paper in ACP if available. and soot the same? P. R. Buseck et al. Are black carbon and soot the same? Title Page P. R. Buseck1,2, K. Adachi1,2,3, A. Gelencser´ 4, E.´ Tompa4, and M. Posfai´ 4 Abstract Introduction 1School of Earth and Space Exploration, Arizona State University, Tempe, AZ 85282, USA Conclusions References 2 Department of Chemistry and Biochemistry, Arizona State University, Tempe, AZ 85282, USA Tables Figures 3Atmospheric Environment and Applied Meteorology Research Department, Meteorological Research Institute, Tsukuba, Ibaraki, Japan 4Department of Earth and Environmental Sciences, University of Pannonia, Veszprem,´ J I Hungary J I Received: 1 September 2012 – Accepted: 3 September 2012 – Published: 21 September 2012 Back Close Correspondence to: P. R. Buseck ([email protected]) Full Screen / Esc Published by Copernicus Publications on behalf of the European Geosciences Union. Printer-friendly Version Interactive Discussion 24821 Discussion Paper | Discussion Paper | Discussion Paper | Discussion Paper | Abstract ACPD The climate change and environmental literature, including that on aerosols, is replete with mention of black carbon (BC), but neither reliable samples nor standards exist. 12, 24821–24846, 2012 Thus, there is uncertainty about its exact nature. -
2.2 Sewage Sludge Incineration
2.2 Sewage Sludge Incineration There are approximately 170 sewage sludge incineration (SSI) plants in operation in the United States. Three main types of incinerators are used: multiple hearth, fluidized bed, and electric infrared. Some sludge is co-fired with municipal solid waste in combustors based on refuse combustion technology (see Section 2.1). Refuse co-fired with sludge in combustors based on sludge incinerating technology is limited to multiple hearth incinerators only. Over 80 percent of the identified operating sludge incinerators are of the multiple hearth design. About 15 percent are fluidized bed combustors and 3 percent are electric. The remaining combustors co-fire refuse with sludge. Most sludge incinerators are located in the Eastern United States, though there are a significant number on the West Coast. New York has the largest number of facilities with 33. Pennsylvania and Michigan have the next-largest numbers of facilities with 21 and 19 sites, respectively. Sewage sludge incinerator emissions are currently regulated under 40 CFR Part 60, Subpart O and 40 CFR Part 61, Subparts C and E. Subpart O in Part 60 establishes a New Source Performance Standard for particulate matter. Subparts C and E of Part 61--National Emission Standards for Hazardous Air Pollutants (NESHAP)--establish emission limits for beryllium and mercury, respectively. In 1989, technical standards for the use and disposal of sewage sludge were proposed as 40 CFR Part 503, under authority of Section 405 of the Clean Water Act. Subpart G of this proposed Part 503 proposes to establish national emission limits for arsenic, beryllium, cadmium, chromium, lead, mercury, nickel, and total hydrocarbons from sewage sludge incinerators. -
The Foundation for Global Action on Persistent Organic Pollutants: a United States Perspective
The Foundation for Global Action on Persistent Organic Pollutants: A United States Perspective Office of Research and Development Washington, DC 20460 EPA/600/P-01/003F NCEA-I-1200 March 2002 www.epa.gov Disclaimer Mention of trade names or commercial products does not constitute endorsement or recommendation for use. Cover page credits: Bald eagle, U.S. FWS; mink, Joe McDonald/Corbis.com; child, family photo, Jesse Paul Nagaruk; polar bear, U.S. FWS; killer whales, Craig Matkin. Contents Contributors ................................................................................................. vii Executive Summary ....................................................................................... ix Chapter 1. Genesis of the Global Persistent Organic Pollutant Treaty ............ 1-1 Why Focus on POPs? ................................................................................................. 1-2 The Four POPs Parameters: Persistence, Bioaccumulation, Toxicity, Long-Range Environmental Transport ......................................................... 1-5 Persistence ......................................................................................................... 1-5 Bioaccumulation ................................................................................................. 1-6 Toxicity .............................................................................................................. 1-7 Long-Range Environmental Transport .................................................................. 1-7 POPs -
Black Carbon's Properties and Role in the Environment
Sustainability 2010, 2, 294-320; doi:10.3390/su2010294 OPEN ACCESS sustainability ISSN 2071-1050 www.mdpi.com/journal/sustainability Review Black Carbon’s Properties and Role in the Environment: A Comprehensive Review Gyami Shrestha 1,*, Samuel J. Traina 1 and Christopher W. Swanston 2 1 Environmental Systems Program, Sierra Nevada Research Institute, University of California- Merced, 5200 N. Lake Road, Merced, CA 95343, USA; E-Mail: [email protected] 2 Northern Institute of Applied Carbon Science, Climate, Fire, & Carbon Cycle Science Research, Northern Research Station, USDA Forest Service, 410 MacInnes Drive, Houghton, MI 49931, USA; E-Mail: [email protected] * Author to whom correspondence should be addressed; E-Mail: [email protected]. Received: 13 November 2009 / Accepted: 7 January 2010 / Published: 15 January 2010 Abstract: Produced from incomplete combustion of biomass and fossil fuel in the absence of oxygen, black carbon (BC) is the collective term for a range of carbonaceous substances encompassing partly charred plant residues to highly graphitized soot. Depending on its form, condition of origin and storage (from the atmosphere to the geosphere), and surrounding environmental conditions, BC can influence the environment at local, regional and global scales in different ways. In this paper, we review and synthesize recent findings and discussions on the nature of these different forms of BC and their impacts, particularly in relation to pollution and climate change. We start by describing the different types of BCs and their mechanisms of formation. To elucidate their pollutant sorption properties, we present some models involving polycyclic aromatic hydrocarbons and organic carbon. Subsequently, we discuss the stability of BC in the environment, summarizing the results of studies that showed a lack of chemical degradation of BC in soil and those that exposed BC to severe oxidative reactions to degrade it. -
Addressing Persistent Organic Pollutants
Minnesota Journal of Law & Inequality Volume 30 Issue 1 Article 3 June 2012 Arctic Justice: Addressing Persistent Organic Pollutants Elizabeth Burleson Stephanie Dodson Dougherty Follow this and additional works at: https://lawandinequality.org/ Recommended Citation Elizabeth Burleson & Stephanie Dodson Dougherty, Arctic Justice: Addressing Persistent Organic Pollutants, 30(1) LAW & INEQ. 57 (2012). Available at: https://scholarship.law.umn.edu/lawineq/vol30/iss1/3 Minnesota Journal of Law & Inequality is published by the University of Minnesota Libraries Publishing. 57 Arctic Justice: Addressing Persistent Organic Pollutants Elizabeth Burlesont & Stephanie Dodson Doughertytt Introduction Persistent Organic Pollutants (POPs), anthropogenic chemicals produced for or by agricultural and industrial uses, contaminate all regions of the world.! There are three general categories of POPs: pesticides (including insecticides, herbicides, and fungicides), industrial chemicals, and unintentionally produced byproducts of certain chemical and combustion processes.2 The pesticide dichlorodiphenyltrichloroethane (DDT) is perhaps the most well known of the POPs.' It was heavily relied upon during World War II to control the spread of certain diseases and is still used to control malaria in several developing nations.' Another POP is a class of chemicals collectively known as polychlorinated biphenyls (PCBs), which are widely used as dielectric fluid in transformers and capacitors. Dioxins are an example of unintentionally produced POPs.' These are chemicals released by incomplete combustion or by the manufacture of certain pesticides.' Although these chemicals are produced for beneficial purposes (or as a byproduct), it has become apparent t. Professor Elizabeth Burleson has an LL.M. from the London School of Economics and Political Science and a J.D. from the University of Connecticut School of Law. -
Impact from Exhaust Gas Cleaning Systems (Scrubbers) on the Marine Environment (Ad Hoc)
ICES VIEWPOINT BACKGROUND DOCUMENT: IMPACT FROM EXHAUST GAS CLEANING SYSTEMS (SCRUBBERS) ON THE MARINE ENVIRONMENT (AD HOC) VOLUME 2 | ISSUE 86 ICES SCIENTIFIC REPORTS RAPPORTS SCIENTIFIQUES DU CIEM ICES INTERNATIONAL COUNCIL FOR THE EXPLORATION OF THE SEA CIEM COUNSEIL INTERNATIONAL POUR L’EXPLORATION DE LA MER International Council for the Exploration of the Sea Conseil International pour l’Exploration de la Mer H.C. Andersens Boulevard 44-46 DK-1553 Copenhagen V Denmark Telephone (+45) 33 38 67 00 Telefax (+45) 33 93 42 15 www.ices.dk [email protected] The material in this report may be reused for non-commercial purposes using the recommended cita- tion. ICES may only grant usage rights of information, data, images, graphs, etc. of which it has owner- ship. For other third-party material cited in this report, you must contact the original copyright holder for permission. For citation of datasets or use of data to be included in other databases, please refer to the latest ICES data policy on ICES website. All extracts must be acknowledged. For other reproduction requests please contact the General Secretary. This document is the product of an expert group under the auspices of the International Council for the Exploration of the Sea and does not necessarily represent the view of the Council. ISSN number: 2618-1371 I © 2020 International Council for the Exploration of the Sea ICES Scientific Reports Volume 2 | Issue 86 ICES VIEWPOINT BACKGROUND DOCUMENT: IMPACT FROM EXHAUST GAS CLEANING SYSTEMS (SCRUBBERS) ON THE MARINE ENVIRONMENT (AD HOC) Recommended format for purpose of citation: Hassellöv, I.M., Koski, M., Broeg, K., Marin-Enriquez, O., Tronczynski, J., Dulière, V., Murray, C., Bailey, S., Redfern, J., de Jong, K., Ponzevera, E., Belzunce-Segarra, M.J., Mason, C., Iacarella, J.C., Lyons, B., Fernandes, J.A. -
A Practical Guide to Exhaust Gas Cleaning Systems for the Maritime Industry
EGCSA H A NDBOOK 2012 A practical guide to exhaust gas cleaning systems for the maritime industry EGCSA Handbook 2012 Exhaust Gas Cleaning Systems are a highly effective solution to the challenges of IMO MARPOL Annex VI air pollution regulations and the added complexities of regional and national emissions legislation. It is crucial that ship owners and operators fully understand their options for compliance. To aid decision making this guide contains a wealth of information, including: • The impact of emissions, current and future regulation and the IMO Guidelines for Exhaust Gas Cleaning Systems • Types of Exhaust Gas Cleaning System for SOx, PM and NOx, including system configuration and installation, materials of construction and compliance instrumentation • Scrubbing processes, dry chemical treatment and washwater handling • Comprehensive details of commercially available systems from EGCSA members As exhaust gas cleaning technologies and legislation evolve, it is intended to further update this publication to keep pace with developments and EGCSA encourages all with an interest in this business critical area to take full advantage of each new edition as it is released. Price: £105.00 Contents CONTENTS................................................................ 1 5.1.1 Wet scrubbers.................................................. 58 LIST OF FIGURES......................................................... 2 5.1.2 Dry scrubbers................................................... 63 LIST OF INFO BOXES.................................................. -
Smog Check Inspection Procedures Manual
SMOG CHECK INSPECTION PROCEDURES MANUAL August 2009 BUREAU OF AUTOMOTIVE REPAIR PREFACE This manual is incorporated by reference in Section 3340.45, Title 16, of the California Code of Regulations. It provides procedures for performing official Smog Check inspections. Licensed Smog Check stations and technicians must follow these procedures and the Emission Inspection System prompts when conducting Smog Check inspections. Prepared by: Department of Consumer Affairs Bureau of Automotive Repair Standards & Training Unit 10240 Systems Parkway Sacramento, CA 95827 Written suggestions for improvement to this manual are welcomed. They should be directed to the Bureau of Automotive Repair’s Standards and Training Unit at the above address, or via the Smog Check website, www.smogcheck.ca.gov. SCIP 8-09 I Table of Contents Smog Check Inspection Procedures Pre-Test Check List........................................................................................................1 Test Application.............................................................................................................1 Vehicle Identification 1.1.0 Technician Access........................................................................................................2 1.1.1 Vehicle Identification Information ............................................................................3-4 Emissions Measurement Test (Gasoline Only) 1.2.0 Before Test Conditions.................................................................................................5 1.2.1 -
Field Measurement of Diesel Particulate Matter Emissions JON C
Ann. Occup. Hyg., pp. 1–7 Published by Oxford University Press on behalf of the British Occupational Hygiene Society doi:10.1093/annhyg/mem069 Field Measurement of Diesel Particulate Matter Emissions JON C. VOLKWEIN1* , STEVEN E. MISCHLER1, BRIAN DAVIES2 and CLIVE ELLIS3† 1 Centers for Disease Control and Prevention, National Institute for Occupational Safety and Health, 2 Pittsburgh Research Laboratory, PO Box 18070, Pittsburgh, PA 15236, USA; School of Health 3 Sciences, University of Wollongong, NSW 2522, Australia; NSW Department of Mineral Resources, PO Box 76, Lidcombe, NSW 2141, Australia Received 11 December 2006; in final form 17 December 2007 A primary means to reduce environmental levels of diesel particulate matter (DPM) exposure to miners is to reduce the amount of DPM emission from the engine. A quick and economic method to estimate engine particulate emission levels has been developed. The method relies on the measurement of pressure increase across a filter element that is briefly used to collect a DPM sample directly from the engine exhaust. The method has been refined with the inclu sion of an annular aqueous denuder to the tube which permits dry filter samples to be obtained without addition of dilution air. Tailpipe filter samples may then be directly collected in hot and water-supersaturated exhaust gas flows from water bath-cooled coal mine engines without the need for dilution air. Measurement of a differential pressure (DP) increase with time has been related to the mass of elemental carbon (EC) on the filter. Results for laboratory and field measurements of the method showed agreement between DP increase and EC collected on the filter with R2 values >0.86.