Protecting Property, HVAC Systems from Black Soot Deposition
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Yale University Design Standards 15815 CONTENTS A. Summary Metal Ducts B. System Design and Performance Requirements C. Materials This document provides design standards D. Installation Guidelines only, and is not intended for use, in whole E. Quality Control—Ductwork Field Tests or in part, as a specification. Do not copy F. Cleaning and Adjusting this information verbatim in specifications or in notes on drawings. Refer questions and comments regarding the content and use of this document to the Yale University Project Manager. A. Summary This section contains design criteria for rectangular and round metal ductwork, duct liners, and hangers for supply, return, and exhaust systems. B. System Design and Performance Requirements 1. Keep the ductwork layout simple. Use short, direct runs where ever possible, and conserve ceiling space. 2. All return/exhaust air must be ducted. The use of ceiling plenums for return/exhaust air is prohibited. 3. Perchloric acid fume exhaust ductwork must be individually ducted without connection to other exhausts. 4. Fume hoods and contaminated or hazardous areas must be exhausted by a system of ducts entirely separate from all other exhaust systems. The location of area exhausts should be carefully coordinated with reference to remoteness from supply air outlets, doors, and windows. Animal areas and toilet rooms shall have separate exhausts. See Section 00705: General HVAC Design Conditions. 5. Wherever possible, exhaust ducts carrying noxious or corrosive fumes must be under negative pressure; connect them on the suction side of the fan. 6. Review appropriate SMANCA sections (laboratory) when designing duct distribution systems. Subdivision 15800: Air Distribution 1 Revision 2, 05/13 Yale University Design Standards Section 15815: Metal Ducts 7. -
End of Section 23 31 14
University of Houston Master Construction Specifications Insert Project Name SECTION 23 31 14 - DUCTWORK ACCESSORIES PART 1 - GENERAL 1.1 RELATED DOCUMENTS: A. The Conditions of the Contract and applicable requirements of Division 1, "General Requirements", and Section 23 01 00, "Mechanical General Provisions", govern this Section. 1.2 DESCRIPTION OF WORK: A. Work Included: Provide ductwork accessories as shown on the Drawings, specified and required. B. Types: The types of ductwork accessories required for the project include, but are not limited to: 1. Flexible connections. 2. Direction and volume control dampers. 3. Fire dampers. 4. Fire/smoke dampers. 5. Smoke Dampers. 6. Radiation dampers. 7. Flashing and counterflashing. 8. Turning vanes. 9. Duct access doors and inspection plates. 10. Test openings. 11. Screens. 12. Miscellaneous ductwork materials. 1.3 QUALITY ASSURANCE: A. SMACNA Compliance: Comply with applicable portions of Sheet Metal and Air Conditioning Contractors' National Association (SMACNA) "HVAC Duct Construction Standards", current edition. B. ASHRAE Standards: Comply with American Society of Heating, Refrigerating, and Air-Conditioning Engineers, Inc. (ASHRAE) recommendations pertaining to construction of ductwork accessories, except as otherwise indicated. C. Certification: Fire, fire/smoke and smoke dampers shall be UL-listed, FM-approved and comply with applicable building code requirements. D. Manufacturers: Provide products complying with the specifications and produced by one of the following: 1. American Foundry. 2. Air Balance Inc. 3. Duro-Dyne. 4. Elgin Sheet Metal Products. 5. Nailor Industries. 6. Prefco. 7. Ruskin. 8. Tuttle and Bailey. 9. United Sheet Metal. 10. Vent-Fabrics, Inc. 11. Ventlok. 12. Young Regulator Co. 1.4 SUBMITTALS: AE Project Number: Ductwork Accessories 23 31 14 – 1 Revision Date: 1/29/2018 University of Houston Master Construction Specifications Insert Project Name A. -
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. -
CHAVEZ-DISSERTATION-2016.Pdf
Copyright by Kyle Feliciano Chavez 2016 The Dissertation Committee for Kyle Feliciano Chavez certifies that this is the approved version of the following dissertation: Variable Incidence Angle Film Cooling Experiments on a Scaled Up Turbine Airfoil Model Committee: David G. Bogard, Supervisor Frederick Todd Davidson Atul Kohli Ofodike A. Ezekoye Michael E. Webber Variable Incidence Angle Film Cooling Experiments on a Scaled Up Turbine Airfoil Model by Kyle Feliciano Chavez, B.S.; M.S. Dissertation Presented to the Faculty of the Graduate School of The University of Texas at Austin in Partial Fulfillment of the Requirements for the Degree of Doctor of Philosophy The University of Texas at Austin May 2016 Dedication This document is dedicated to my family. Dad, you have always been so encouraging, helpful, and levelheaded. If not for all of your help and encouragement, I’m not sure I’d be where I’m at today. To my brother, I’m so happy for the years we spent growing up together. They are some of my fondest memories and I’ll never forget them. Mom, if you were still here today, you’d be so proud. I think of you all constantly, and I love you all. Acknowledgements I would like to first and foremost thank Dr. Bogard, who has supported and taught me so much along the way. Your dedication to your field of research is an inspiration to me, and you’ve helped shape me in to the engineer I am today. You also taught me how great it is to be “mighty fine” all the time, and that’s priceless in and of itself. -
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. -
23.31.00 Ductwork
UNIVERSITY OF PENNSYLVANIA Design Standards Revision July 2019 SECTION 233100 – DUCTWORK 1.0 Acoustical duct lining in any part of the duct system is prohibited. All ductwork requiring insulation shall be externally insulated (Refer to the Sheet Metal Ductwork Insulation Schedule in Section 230700 for insulation types and thickness). Double walled ducts consisting of an outer wall of galvanized sheet metal, an inner wall of perforated galvanized sheet metal with insulation sandwiched between the layers is permitted. 2.0 All ductwork shall be designed, constructed, supported and sealed in accordance with SMACNA HVAC Duct Construction Standards and pressure classifications. When the ductwork pressure classification of these standards is exceeded, construct ductwork in accordance with SMACNA Round and Rectangular Industrial Duct Construction Standards. The following preferences or modifications to the Standards shall be specified: A. Radius elbows with a construction radius of 1.5 the duct width are preferred to square elbows. B. All square elbows must be constructed with single thickness turning vanes, Runner Type 2 as shown in Figures 4-3 and 4-4 of SMACNA Duct Construction Standards - Metal and Flexible. Where a rectangular duct changes in size at a square-throat elbow fitting, use single thickness turning vanes with trailing edge extensions aligned with the sides of the duct. C. Air extractors and splitter dampers are not permitted. D. Transitions and offsets shall follow Figure 4-7 of SMACNA HVAC Duct Construction Standards - Metal and Flexible, except that sides of transitions shall slope a maximum of 15 degrees. E. Minimum duct gauge shall be 22 for ducts up through 43", 20 gauge up through 60" and 18 gauge above 60". -
Myths and Mythtery of Air Flow Do Not Be Swayed by Misconceptions About Air Flow in the Industry
Myths And Mythtery of Air Flow Do not be swayed by misconceptions about air flow in the industry. By R.B. (Buzz) Est E s , C M s n HVAC system cannot function optimally or properly unless the duct system is properly designed and installed. AToo often customers buy “high efficiency” systems that do not deliver the energy-saving performance because of a defi- cient duct system. This is usually because many contractors “design” systems based on ignorance and superstition instead Discerning fact from fiction is half the battle to under- of correct knowledge of air flow. Following are some of these standing air flow and HVAC system/duct design. myths and explanations as to why they are incorrect. exhausting air from it. The relative numbers remain the same. Duct is too big—a.k.a. never let the air velocity get too Perhaps some numbers might be negative, relative to the air low. False. The limiting factors on duct size are space and outside the room, but that does not change any of the math. cost. Instead of a complicated technical explanation, imag- ine a room with 10 ft x 10 ft x 10 ft of air-tight construction Any obstruction in a fluid flow stream will add tur- except for two 1-sq.-ft openings in opposite walls. One of the bulence and restriction (T&R), this includes turning openings has a fan blowing 100 cfm at a velocity of 100 fpm. vanes. False. Installing turning vanes can improve the flow The middle of the room has a velocity of 100 cfm over an around an ell so much that the overall result is much less area of 100 sq. -
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. -
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.