Health Effects of Black Carbon
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Carbon Additives for Polymer Compounds
Polymers Carbon Additives for Polymer Compounds Conductive Carbon Black Graphite & Coke www.timcal.com 1 Who are we? TIMCAL Graphite & Carbon has a strong tra- agement and continuous process improve- dition and history in carbon manufacturing. Its ment, all TIMCAL manufacturing plants comply first manufacturing operation was founded in with ISO 9001-2008. 1908. TIMCAL Graphite & Carbon is committed to Today, TIMCAL facilities produce and market a produce highly specialized graphite and car- large variety of synthetic and natural graphite bon materials for today’s and tomorrow’s cus- powders, conductive carbon blacks and water- tomers needs. based dispersions of consistent high quality. TIMCAL Graphite & Carbon is a member of IMERYS, Adhering to a philosophy of Total Quality Man- a world leader in adding value to minerals. Where are we located? With headquarters located in Switzerland, TIMCAL The Group’s industrial and commercial activities Graphite & Carbon has an international pres- are managed by an experienced multinational ence with production facilities and commercial team of more than 430 employees from many offices located in key markets around the globe. countries on three continents. HQ Bodio, Switzerland Willebroek, Belgium Lac-des-Îles, Canada Terrebonne, Canada Graphitization & pro- Manufacturing & pro- Mining, purification and Exfoliation of natural cessing of synthetic cessing of conductive sieving of natural graphite, processing of graphite, manufacturing carbon black graphite flakes natural and synthetic of water-based -
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. -
U.S. National Black Carbon and Methane Emissions a Report to the Arctic Council
U.S. NATIONAL BLACK CARBON AND METHANE EMISSIONS A REPORT TO THE ARCTIC COUNCIL AUGUST 2015 U.S. NATIONAL BLACK CARBON AND METHANE EMISSIONS A REPORT TO THE ARCTIC COUNCIL AUGUST 2015 TABLE OF CONTENTS EXECUTIVE SUMMARY. 1 ABOUT THIS REPORT. 1 SUMMARY OF CURRENT BLACK CARBON EMISSIONS AND FUTURE PROJECTIONS . 2 SUMMARY OF CURRENT METHANE EMISSIONS AND FUTURE PROJECTIONS. 4 SUMMARY OF NATIONAL MITIGATION ACTIONS BY POLLUTANT AND SECTOR . 6 BLACK CARBON . .6 METHANE . 11 HIGHLIGHTS OF BEST PRACTICES AND LESSONS LEARNED FOR KEY SECTORS . .16 TRANSPORT/MOBILE . 16 OPEN BIOMASS BURNING (INCLUDING WILDFIRES) . 16 RESIDENTIAL/DOMESTIC . .17 OIL & NATURAL GAS. .17 OTHER . 17 PROJECTS RELEVANT FOR THE ARCTIC. .18 ARCTIC AIR QUALITY IMPACT ASSESSMENT MODELING. 18 BLACK CARBON DEPOSITION ON U.S. SNOW PACK . .18 EMISSIONS AND TRANSPORT FROM AGRICULTURAL BURNING AND FOREST FIRES . .18 MEASUREMENT OF BLACK CARBON AND METHANE IN THE ARCTIC. .18 MEASUREMENT OF MARITIME BLACK CARBON EMISSIONS AND DIESEL FUEL ALTERNATIVES. .18 REDUCTION OF BLACK CARBON IN THE RUSSIAN ARCTIC. .19 VALDAY CLUSTER UPGRADE FOR BLACK CARBON REDUCTION IN THE REPUBLIC OF KARELIA, RUSSIAN FEDERATION. 19 AVIATION CLIMATE CHANGE RESEARCH INITIATIVE. .20 TRACKING SOURCES OF BLACK CARBON IN THE ARCTIC . 20 OTHER INFORMATION. .20 APPENDIX 1: U.S. BLACK CARBON EMISSIONS . .22 APPENDIX 2: U.S. METHANE EMISSIONS (MMT CO2E), 1990–2013 . 24 EXECUTIVE SUMMARY U.S. black carbon emissions are declining and additional reductions are expected, largely through strategies to reduce the emissions from mobile diesel engines that account for roughly 40 percent of the U.S. total. A number of fine particulate matter (PM2.5) control strategies have proven successful in reducing black carbon emissions from mobile sources. -
Climate Effects of Black Carbon Aerosols in China and India Surabi Menon, Et Al
Climate Effects of Black Carbon Aerosols in China and India Surabi Menon, et al. Science 297, 2250 (2002); DOI: 10.1126/science.1075159 The following resources related to this article are available online at www.sciencemag.org (this information is current as of October 3, 2008 ): Updated information and services, including high-resolution figures, can be found in the online version of this article at: http://www.sciencemag.org/cgi/content/full/297/5590/2250 Supporting Online Material can be found at: http://www.sciencemag.org/cgi/content/full/297/5590/2250/DC1 A list of selected additional articles on the Science Web sites related to this article can be found at: http://www.sciencemag.org/cgi/content/full/297/5590/2250#related-content This article cites 23 articles, 3 of which can be accessed for free: http://www.sciencemag.org/cgi/content/full/297/5590/2250#otherarticles on October 3, 2008 This article has been cited by 251 article(s) on the ISI Web of Science. This article has been cited by 8 articles hosted by HighWire Press; see: http://www.sciencemag.org/cgi/content/full/297/5590/2250#otherarticles This article appears in the following subject collections: Atmospheric Science http://www.sciencemag.org/cgi/collection/atmos www.sciencemag.org Information about obtaining reprints of this article or about obtaining permission to reproduce this article in whole or in part can be found at: http://www.sciencemag.org/about/permissions.dtl Downloaded from Science (print ISSN 0036-8075; online ISSN 1095-9203) is published weekly, except the last week in December, by the American Association for the Advancement of Science, 1200 New York Avenue NW, Washington, DC 20005. -
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. -
Carbon Nanomaterials: Building Blocks in Energy Conversion Devices
Mimicking Photosynthesis Carbon nanostructure-based donor- acceptor molecular assemblies can be engineered to mimic natural photo- synthesis. Fullerene C60 is an excellent electron acceptor for the design of donor-bridge-acceptor molecular systems. Photoinduced charge transfer processes in fullerene-based dyads and triads have been extensively investigated by several research groups during the last decade. In these cases the excited C60 accepts an electron from the linked donor group Carbon Nanomaterials: to give the charge-separated state under visible light excitation. Photoinduced charge separation in these dyads has Building Blocks in Energy been achieved using porphyrins, phtha- locyanine, ruthenium complexes, ferro- cene, and anilines as electron donors. Conversion Devices The rate of electron transfer and by Prashant Kamat charge separation efficiency is dependent on the molecular configuration, redox Carbon nanotubes, fullerenes, and mesoporous carbon potential of the donor, and the medium. Clustering the fullerene-donor systems structures constitute a new class of carbon nanomaterials with provides a unique way to stabilize properties that differ signifi cantly from other forms of carbon electron transfer products. The stability of C anions in cluster forms opens such as graphite and diamond. The ability to custom synthesize 60 up new ways to store and transport nanotubes with attached functional groups or to assemble photochemically harnessed charge. fullerene (C60 and analogues) clusters into three-dimensional Novel organic solar cells have (3D) arrays has opened up new avenues to design high surface been constructed by quaternary area catalyst supports and materials with high photochemical self-organization of porphyrin and fullerenes with gold nanoparticles. and electrochemical activity. -
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. -
Aerosols, Their Direct and Indirect Effects
5 Aerosols, their Direct and Indirect Effects Co-ordinating Lead Author J.E. Penner Lead Authors M. Andreae, H. Annegarn, L. Barrie, J. Feichter, D. Hegg, A. Jayaraman, R. Leaitch, D. Murphy, J. Nganga, G. Pitari Contributing Authors A. Ackerman, P. Adams, P. Austin, R. Boers, O. Boucher, M. Chin, C. Chuang, B. Collins, W. Cooke, P. DeMott, Y. Feng, H. Fischer, I. Fung, S. Ghan, P. Ginoux, S.-L. Gong, A. Guenther, M. Herzog, A. Higurashi, Y. Kaufman, A. Kettle, J. Kiehl, D. Koch, G. Lammel, C. Land, U. Lohmann, S. Madronich, E. Mancini, M. Mishchenko, T. Nakajima, P. Quinn, P. Rasch, D.L. Roberts, D. Savoie, S. Schwartz, J. Seinfeld, B. Soden, D. Tanré, K. Taylor, I. Tegen, X. Tie, G. Vali, R. Van Dingenen, M. van Weele, Y. Zhang Review Editors B. Nyenzi, J. Prospero Contents Executive Summary 291 5.4.1 Summary of Current Model Capabilities 313 5.4.1.1 Comparison of large-scale sulphate 5.1 Introduction 293 models (COSAM) 313 5.1.1 Advances since the Second Assessment 5.4.1.2 The IPCC model comparison Report 293 workshop: sulphate, organic carbon, 5.1.2 Aerosol Properties Relevant to Radiative black carbon, dust, and sea salt 314 Forcing 293 5.4.1.3 Comparison of modelled and observed aerosol concentrations 314 5.2 Sources and Production Mechanisms of 5.4.1.4 Comparison of modelled and satellite- Atmospheric Aerosols 295 derived aerosol optical depth 318 5.2.1 Introduction 295 5.4.2 Overall Uncertainty in Direct Forcing 5.2.2 Primary and Secondary Sources of Aerosols 296 Estimates 322 5.2.2.1 Soil dust 296 5.4.3 Modelling the Indirect -
Black Carbon-Induced Snow Albedo Reduction Over the Tibetan Plateau
Atmos. Chem. Phys., 18, 11507–11527, 2018 https://doi.org/10.5194/acp-18-11507-2018 © Author(s) 2018. This work is distributed under the Creative Commons Attribution 4.0 License. Black carbon-induced snow albedo reduction over the Tibetan Plateau: uncertainties from snow grain shape and aerosol–snow mixing state based on an updated SNICAR model Cenlin He1,2, Mark G. Flanner3, Fei Chen2,4, Michael Barlage2, Kuo-Nan Liou5, Shichang Kang6,7, Jing Ming8, and Yun Qian9 1Advanced Study Program, National Center for Atmospheric Research, Boulder, CO, USA 2Research Applications Laboratory, National Center for Atmospheric Research, Boulder, CO, USA 3Department of Climate and Space Sciences and Engineering, University of Michigan, Ann Arbor, MI, USA 4State Key Laboratory of Severe Weather, Chinese Academy of Meteorological Sciences, Beijing, China 5Joint Institute for Regional Earth System Science and Engineering, and Department of Atmospheric and Oceanic Sciences, University of California, Los Angeles, CA, USA 6State key laboratory of Cryospheric Science, Northwest Institute of Eco-Environment and Resources, Chinese Academy of Sciences, Lanzhou, China 7CAS Center for Excellence in Tibetan Plateau Earth Sciences, Beijing, China 8Multiphase Chemistry Department, Max Planck Institute for Chemistry, Mainz, Germany 9Atmospheric Sciences and Global Change Division, Pacific Northwest National Laboratory, Richland, WA, USA Correspondence: Cenlin He ([email protected]) Received: 12 May 2018 – Discussion started: 22 May 2018 Revised: 31 July 2018 – Accepted: 4 August 2018 – Published: 15 August 2018 Abstract. We implement a set of new parameterizations into regional and seasonal variations, with higher values in the the widely used Snow, Ice, and Aerosol Radiative (SNICAR) non-monsoon season and low altitudes. -
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. -
Hazardous Substance Fact Sheet
Right to Know Hazardous Substance Fact Sheet Common Name: CARBON BLACK Synonyms: C.I. Pigment Black 7; Channel Black; Lamp Black CAS Number: 1333-86-4 Chemical Name: Carbon Black RTK Substance Number: 0342 Date: December 2007 Revision: November 2016 DOT Number: UN 1361 Description and Use EMERGENCY RESPONDERS >>>> SEE BACK PAGE Carbon Black is black, odorless, finely divided powder Hazard Summary generated from the incomplete combustion of Hydrocarbons. It Hazard Rating NJDOH NFPA may contain Polycyclic Aromatic Hydrocarbons (PAHs) which HEALTH 3 - are formed during its manufacture and become adsorbed on FLAMMABILITY 1 - the Carbon Black. It is used in making tire treads, in abrasion REACTIVITY 0 - resistant rubber products, and as a pigment for paints and inks. CARCINOGEN SPONTANEOUSLY COMBUSTIBLE PARTICULATE POISONOUS GASES ARE PRODUCED IN FIRE Reasons for Citation Hazard Rating Key: 0=minimal; 1=slight; 2=moderate; 3=serious; Carbon Black is on the Right to Know Hazardous 4=severe Substance List because it is cited by OSHA, ACGIH, NIOSH and IARC. Carbon Black can affect you when inhaled. This chemical is on the Special Health Hazard Substance Carbon Black should be handled as a CARCINOGEN-- List as it is considered a carcinogen. WITH EXTREME CAUTION. Contact can irritate the skin and eyes. Inhaling Carbon Black can irritate the nose, throat and lungs. Finely dispersed Carbon Black particles may form explosive mixtures in air. SEE GLOSSARY ON PAGE 5. FIRST AID Workplace Exposure Limits Eye Contact OSHA: The legal airborne permissible exposure limit (PEL) is Immediately flush with large amounts of water for at least 15 3.5 mg/m3 averaged over an 8-hour workshift. -
Black Carbon and Methane in the Norwegian Barents Region Black Carbon and Methane in the Norwegian Barents Region | M276
REPORT M-276 | 2014 Black carbon and methane in the Norwegian Barents region Black carbon and methane in the Norwegian Barents region | M276 COLOPHON Executive institution The Norwegian Environment Agency Project manager for the contractor Contact person in the Norwegian Environment Agency Ingrid Lillehagen, The Ministry of Climate and Solrun Figenschau Skjellum Environment, section for polar affairs and the High North M-no Year Pages Contract number M-276 2014 15 Publisher The project is funded by The Norwegian Environment Agency The Norwegian Environment Agency Author(s) Maria Malene Kvalevåg, Vigdis Vestreng and Nina Holmengen Title – Norwegian and English Black carbon and methane in the Norwegian Barents Region Svart karbon og metan i den norske Barentsregionen Summary – sammendrag In 2011, land based emissions of black carbon and methane in the Norwegian Barents region were 400 tons and 23 700 tons, respectively. The largest emissions of black carbon originate from the transport sector and wood combustion in residential heating. For methane, the largest contributors to emissions are the agricultural sector and landfills. Different measures to reduce emissions from black carbon and methane can be implemented. Retrofitting of diesel particulate filters on light and heavy vehicles, tractors and construction machines will reduce black carbon emitted from the transport sector. Measures to reduce black carbon from residential heating are to accelerate the introduction of wood stoves with cleaner burning, improve burning techniques and inspect and maintain the wood stoves that are already in use. In the agricultural sector, methane emissions from food production can be reduced by using manure or food waste as raw material to biogas production.