Are Black Carbon and Soot the Same? Title Page
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Aethalometer Is Located, Data from the Aethalometer Will Also Be Compared to the Sunset Semi-Continuous Analyzer
Sunset Carbon Evaluation Project QA Project Plan, Version 1, September 27, 2011 Sunset Carbon Evaluation Project Quality Assurance Project Plan (QAPP) QA Level IV U.S. Environmental Protection Agency Office of Air Quality Planning and Standards Air Quality Assessment Division Ambient Air Monitoring Group September 27, 2011 Page 1 of 41 Sunset Carbon Evaluation Project QA Project Plan, Version 1, September 27, 2011 Page 2 of 41 Sunset Carbon Evaluation Project QA Project Plan, Version 1, September 27, 2011 DISTRIBUTION LIST The following individuals have been provided with copies of this QAPP. Lewis Weinstock EPA Group Lead U.S. Environmental Protection Agency, Office of Air quality Planning and Standards, Research Triangle Park, NC Elizabeth Landis EPA Project Lead U.S. Environmental Protection Agency, Office of Air quality Planning and Standards, Research Triangle Park, NC Mike Papp QA EPA QA Officer U.S. Environmental Protection Agency, Office of Air quality Planning and Standards, Research Triangle Park, NC Joann Rice EPA Technical Advisor U.S. Environmental Protection Agency, Office of Air quality Planning and Standards, Research Triangle Park, NC Page 4 of 41 Sunset Carbon Evaluation Project QA Project Plan, Version 1, September 27, 2011 1.0 Introduction This is a level IV Quality Assurance Project Plan (QAPP) that covers an Environmental Data Operation (EDO) conducted by the EPA’s Office of Air Quality Planning and Standards (OAQPS) Ambient Air Monitoring Group (AAMG) and State and local monitoring agencies to collect field data at seven (7) sites across the United States. The selection of participating sites is in progress, and to date, monitoring agencies at 3 sites have agreed to participate. -
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. -
Effect of Heterogeneous Oxidative Aging on Light Absorption by Biomass Burning Organic Aerosol
Aerosol Science and Technology ISSN: 0278-6826 (Print) 1521-7388 (Online) Journal homepage: https://www.tandfonline.com/loi/uast20 Effect of heterogeneous oxidative aging on light absorption by biomass burning organic aerosol Eleanor C. Browne, Xiaolu Zhang, Jonathan P. Franklin, Kelsey J. Ridley, Thomas W. Kirchstetter, Kevin R. Wilson, Christopher D. Cappa & Jesse H. Kroll To cite this article: Eleanor C. Browne, Xiaolu Zhang, Jonathan P. Franklin, Kelsey J. Ridley, Thomas W. Kirchstetter, Kevin R. Wilson, Christopher D. Cappa & Jesse H. Kroll (2019) Effect of heterogeneous oxidative aging on light absorption by biomass burning organic aerosol, Aerosol Science and Technology, 53:6, 663-674, DOI: 10.1080/02786826.2019.1599321 To link to this article: https://doi.org/10.1080/02786826.2019.1599321 View supplementary material Accepted author version posted online: 26 Mar 2019. Published online: 15 Apr 2019. Submit your article to this journal Article views: 321 View Crossmark data Full Terms & Conditions of access and use can be found at https://www.tandfonline.com/action/journalInformation?journalCode=uast20 AEROSOL SCIENCE AND TECHNOLOGY 2019, VOL. 53, NO. 6, 663–674 https://doi.org/10.1080/02786826.2019.1599321 Effect of heterogeneous oxidative aging on light absorption by biomass burning organic aerosol Eleanor C. Brownea , Xiaolu Zhangb , Jonathan P. Franklinc, Kelsey J. Ridleyc, Thomas W. Kirchstetterd,e, Kevin R. Wilsonf , Christopher D. Cappag , and Jesse H. Krollc aDepartment of Chemistry and Cooperative Institute for Research -
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. -
Guidance for Using Continuous Monitors in Pm Monitoring
United States Office of Air Quality EPA-454/R-98-012 Environmental Protection Planning and Standards May 1998 Agency Research Triangle Park, NC 27711 Air GUIDANCE FOR USING CONTINUOUS MONITORS IN PM2.5 MONITORING NETWORKS GUIDANCE FOR USING CONTINUOUS MONITORS IN PM2.5 MONITORING NETWORKS May 29, 1998 PREPARED BY John G. Watson1 Judith C. Chow1 Hans Moosmüller1 Mark Green1 Neil Frank2 Marc Pitchford3 PREPARED FOR Office of Air Quality Planning and Standards U.S. Environmental Protection Agency Research Triangle Park, NC 27711 1Desert Research Institute, University and Community College System of Nevada, PO Box 60220, Reno, NV 89506 2U.S. EPA/OAQPS, Research Triangle Park, NC, 27711 3National Oceanic and Atmospheric Administration, 755 E. Flamingo, Las Vegas, NV 89119 DISCLAIMER The development of this document has been funded by the U.S. Environmental Protection Agency, under cooperative agreement CX824291-01-1, and by the Desert Research Institute of the University and Community College System of Nevada. Mention of trade names or commercial products does not constitute endorsement or recommendation for use. This draft has not been subject to the Agency’s peer and administrative review, and does not necessarily represent Agency policy or guidance. ii ABSTRACT This guidance provides a survey of alternatives for continuous in-situ measurements of suspended particles, their chemical components, and their gaseous precursors. Recent and anticipated advances in measurement technology provide reliable and practical instruments for particle quantification over averaging times ranging from minutes to hours. These devices provide instantaneous, telemetered results and can use limited manpower more efficiently than manual, filter-based methods. -
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. -
Solid Waste Incineration Modelling for Advanced Moving Grate Incinerators
sustainability Article Solid Waste Incineration Modelling for Advanced Moving Grate Incinerators 1, 1, 1,2, Mingtao Jiang y, Adrian C. H. Lai y and Adrian Wing-Keung Law * 1 Environmental Process Modelling Centre, Nanyang Environment and Water Research Institute, Nanyang Technological University, 50 Nanyang Avenue, Singapore 639798, Singapore; [email protected] (M.J.); [email protected] (A.C.H.L.) 2 School of Civil and Environmental Engineering, Nanyang Technological University, 50 Nanyang Avenue, Singapore 639798, Singapore * Correspondence: [email protected]; Tel./Fax: +65-6790-5296 Mingtao Jiang and Adrian C. H. Lai contributed equally to this work as first authors. y Received: 27 August 2020; Accepted: 22 September 2020; Published: 28 September 2020 Abstract: Currently, the design of advanced moving grate (AMG) incinerators for solid waste is aided by computational simulations. The simulation approach couples a waste bed model to characterize the incineration processes of the waste material on top of the moving grate, with a computational fluid dynamics (CFD) model to reproduce the heated air movement and reactions in the incinerator space above. However, the simulation results of AMG incinerators are rarely compared with actual field measurements for validation in the literature so far. In this study, we first examine the sensitivity of pyrolysis kinetics in the waste bed model using three existing alternatives. The predictions of combustion characteristics, including the bed height, flow and temperature distributions, composition of stack gases and gas emissions are obtained for the three alternatives and compared with measurements from a simple laboratory furnace. The results show that the pyrolysis kinetics mechanism can significantly affect the outputs from the waste bed model for incineration modelling. -
Monitoring for Fine Particulate Matter
Monitoring for Fine Particulate Matter Elisa Eiseman Critical Technologies Institute R The research described in this report was conducted by RAND’s Critical Technologies Institute. ISBN: 0-8330-2618-6 RAND is a nonprofit institution that helps improve policy and decisionmaking through research and analysis. RAND’s publications do not necessarily reflect the opinions or policies of its research sponsors. © Copyright 1998 RAND All rights reserved. No part of this book may be reproduced in any form by any electronic or mechanical means (including photocopying, recording, or information storage and retrieval) without permission in writing from RAND. Cover design: Elisa Eiseman Published 1998 by RAND 1700 Main Street, P.O. Box 2138, Santa Monica, CA 90407-2138 1333 H St., N.W., Washington, D.C. 20005-4707 RAND URL: http://www.rand.org/ To order RAND documents or to obtain additional information, contact Distribution Services: Telephone: (310) 451-7002; Fax: (310) 451-6915; Internet: [email protected] This document is available on the World Wide Web at http://www.rand.org/publications/MR/MR974 PREFACE In accordance with the Clean Air Act, the United States Environmen- tal Protection Agency (EPA) has reviewed the National Ambient Air Quality Standards (NAAQS) for particulate matter (PM) and set new standards for fine particulate matter with a diameter less than or μ equal to 2.5 m (PM2.5). This document reviews the new Federal Ref- erence Method (FRM) developed by the EPA for monitoring PM2.5, which is a manual method that will be used to ensure national con- sistency in PM2.5 monitoring and compliance with the EPA’s new standards for PM. -
Comparison of Different Aethalometer Correction Schemes and a Reference Multi-Wavelength Absorption Technique for Ambient Aerosol Data
Atmos. Meas. Tech., 10, 2837–2850, 2017 https://doi.org/10.5194/amt-10-2837-2017 © Author(s) 2017. This work is distributed under the Creative Commons Attribution 3.0 License. Comparison of different Aethalometer correction schemes and a reference multi-wavelength absorption technique for ambient aerosol data Jorge Saturno1, Christopher Pöhlker1, Dario Massabò2, Joel Brito3, Samara Carbone4, Yafang Cheng1, Xuguang Chi5, Florian Ditas1, Isabella Hrabeˇ de Angelis1, Daniel Morán-Zuloaga1, Mira L. Pöhlker1, Luciana V. Rizzo6, David Walter1, Qiaoqiao Wang1, Paulo Artaxo7, Paolo Prati2, and Meinrat O. Andreae1,8,9 1Biogeochemistry and Multiphase Chemistry Departments, Max Planck Institute for Chemistry, P.O. Box 3060, 55020 Mainz, Germany 2Department of Physics & INFN, University of Genoa, via Dodecaneso 33, 16146, Genoa, Italy 3Laboratory for Meteorological Physics, University Blaise Pascal, Clermont-Ferrand, France 4Institute of Agrarian Sciences, Federal University of Uberlândia, Uberlândia, Minas Gerais, Brazil 5Institute for Climate and Global Change and School of Atmospheric Sciences, Nanjing University, Nanjing, China 6Department of Earth and Exact Sciences, Institute of Environmental, Chemical and Pharmaceutics Sciences, Federal University of São Paulo, São Paulo, Brazil 7Department of Applied Physics, Institute of Physics, University of São Paulo, Rua do Matão, Travessa R, 187, CEP 05508-900, São Paulo, SP, Brazil 8Scripps Institution of Oceanography, University of California San Diego, La Jolla, CA 92098, USA 9Geology and Geophysics Department, King Saud University, Riyadh, Saudi Arabia Correspondence to: Jorge Saturno ([email protected]) Received: 31 October 2016 – Discussion started: 13 December 2016 Revised: 19 February 2017 – Accepted: 12 July 2017 – Published: 9 August 2017 Abstract. Deriving absorption coefficients from Aethalome- increase the short-wavelength absorption coefficients. -
Training Course: Magee AE33 / TAPI-633
Aethalometer® Training Course: Magee AE33 / TAPI-633 Instructor: George Allen, NESCAUM gallen (at) nescaum . org Portions of this material are from Aerosol and TAPI manuals and service documents Updated: November 5, 2015 Course Overview Magee AE33 and TAPI 633 are the same instrument. Made at Aerosol in Slovenia Method principle and history Routine Operation and Maintenance, Things you need to know Troubleshooting and Repair Data Logging, Processing and Validation, Data Mashers Discussion/Q&A All Training Materials: tinyurl.com/AethTraining 2 Black Carbon (BC): what is it? EPA Report to Congress on Black Carbon (2012): “BC is defined as the carbonaceous component of particulate matter that absorbs all wavelengths of solar radiation” http://cfpub.epa.gov/si/si_public_record_report.cfm?dirEntryID=240148 (388 pages...) “Stuff that looks black” when collected on a filter or impaction surface (think FRM WINS): Source in ambient air: Primary product of combustion (example: diesel) Directly emitted - not secondary Nearly all BC mass < 1 µm diameter 3 BC is related to “elemental carbon” (EC) Usually highly correlated Relationship is EC method dependent (TOR/TOT, NIOSH-5040, ...) CSN/STN TOR EC: ~ Aethalometer BC Sunset/NIOSH EC: ~ 1/2 Aethalometer BC Similar to classic Coefficient of Haze (COH) measurement: Average black carbon concentration as a function of coefficient of haze. The circles represent the average BC concentration at each COH level, and the error bars represent the standard error. Only COH levels which occurred three times or more during the study period are included. Regression of average BC on COH (dotted line) yields an R2 of 0.988, a slope of 5.66, and an intercept of -0.26.