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Energy Technology 2019 Carbon Dioxide Management and Other Technologies Edited by Tao Wang Xiaobo Chen Donna Post Guillen Lei Zhang Ziqi Sun Cong Wang Nawshad Haque John A. Howarter Neale R. Neelameggham Shadia Ikhmayies York R. Smith Leili Tafaghodi Amit Pandey The Minerals, Metals & Materials Series Tao Wang • Xiaobo Chen • Donna Post Guillen • Lei Zhang • Ziqi Sun • Cong Wang • Nawshad Haque • John A. Howarter • Neale R. Neelameggham • Shadia Ikhmayies • York R. Smith • Leili Tafaghodi • Amit Pandey Editors Energy Technology 2019 Carbon Dioxide Management and Other Technologies 123 Editors Tao Wang Nucor Castrip Arkansas Blytheville, AR, USA Xiaobo Chen Royal Melbourne Institute of Technology Melbourne, VIC, Australia Donna Post Guillen Idaho National Laboratory Idaho Falls, ID, USA Lei Zhang University of Alaska Fairbanks Fairbanks, AK, USA Ziqi Sun Queensland University of Technology Brisbane, QLD, Australia Cong Wang Northeastern University Shenyang, China Nawshad Haque Commonwealth Scientific and Industrial Research Organization Clayton South, VIC, Australia John A. Howarter Purdue University West Lafayette, IN, USA Neale R. Neelameggham IND LLC South Jordan, UT, USA Shadia Ikhmayies Al-Isra University Amman, Jordan York R. Smith University of Utah Salt Lake City, UT, USA Leili Tafaghodi University of British Columbia Vancouver, BC, Canada Amit Pandey LG Fuel Cell Systems North Canton, OH, USA ISSN 2367-1181 ISSN 2367-1696 (electronic) The Minerals, Metals & Materials Series ISBN 978-3-030-06208-8 ISBN 978-3-030-06209-5 (eBook) https://doi.org/10.1007/978-3-030-06209-5 Library of Congress Control Number: 2018964932 © The Minerals, Metals & Materials Society 2019 This work is subject to copyright. All rights are reserved by the Publisher, whether the whole or part of the material is concerned, specifically the rights of translation, reprinting, reuse of illustrations, recitation, broadcasting, reproduction on microfilms or in any other physical way, and transmission or information storage and retrieval, electronic adaptation, computer software, or by similar or dissimilar methodology now known or hereafter developed. The use of general descriptive names, registered names, trademarks, service marks, etc. in this publication does not imply, even in the absence of a specific statement, that such names are exempt from the relevant protective laws and regulations and therefore free for general use. The publisher, the authors and the editors are safe to assume that the advice and information in this book are believed to be true and accurate at the date of publication. Neither the publisher nor the authors or the editors give a warranty, express or implied, with respect to the material contained herein or for any errors or omissions that may have been made. The publisher remains neutral with regard to jurisdictional claims in published maps and institutional affiliations. This Springer imprint is published by the registered company Springer Nature Switzerland AG The registered company address is: Gewerbestrasse 11, 6330 Cham, Switzerland Preface This volume contains selected papers presented at the Energy Technologies Symposium organized in conjunction with the TMS 2019 Annual Meeting & Exhibition in San Antonio, Texas, USA, and organized by the TMS Energy Committee. The papers in this volume intend to address the issues, intricacies, and the challenges relating to energy and environmental science. This volume also contains selected papers from the two other symposia: Solar Cell Silicon and 5th Symposium on Advanced Materials for Energy Conversion and Storage. The Energy Technologies Symposium was open to participants from both industry and academia and focused on energy-efficient technologies including innovative ore beneficiation, smelting technologies, recycling, and waste heat recovery. The volume also covers various technological aspects of sustainable energy ecosystems, processes that improve energy efficiency, reduce thermal emissions, and reduce carbon dioxide and other greenhouse emissions. The papers addressing renewable energy resources for metals and materials production, waste heat recovery, and other industrial energy-efficient technologies, new concepts or devices for energy generation and conversion, energy efficiency improvement in process engineering, sustainability and life cycle assessment of energy systems, as well as the thermodynamics and modeling for sustainable metallurgical processes are included. This volume also includes topics on CO2 sequestration and reduction in greenhouse gas emissions from process engineering, sustainable technologies in extractive metallurgy, as well as the materials processing and manufacturing industries with reduced energy consumption and CO2 emission. Contributions from all areas of nonnuclear and nontraditional energy sources, such as solar, wind, and biomass are also included in this volume. We hope this volume will provide a reference for materials scientists and engineers as well as metallurgists for exploring innovative energy technologies and novel energy materials processing. We would like to acknowledge the contributions from the authors of the papers in this volume, the efforts of the reviewers dedicated v to the manuscripts review process, and the help received from the publisher. We appreciate the efforts of Energy Committee members for enhancing this proceed- ings volume. We also acknowledge the organizers of the other symposia that contributed papers. Tao Wang Xiaobo Chen Donna Post Guillen Lei Zhang Ziqi Sun Cong Wang Nawshad Haque John A. Howarter Neale R. Neelameggham Shadia Ikhmayies York R. Smith Leili Tafaghodi Amit Pandey vi Preface Contents Part I 2019 Energy Technologies and Carbon Dioxide Management Symposium Analysis on Energy Efficiency and Optimization of HIsmelt Process . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3 Chao-zhen Cao, Yu-jie Meng, Fang-xing Yan, Dian-wei Zhang, Xin Li and Fu-ming Zhang The Characterizations of Hydrogen from Steam Reforming of Bio-Oil Model Compound in Granulated Blast Furnace Slag . . . . . . 13 Xin Yao, Qingbo Yu, Guowei Xu, Qin Qin and Ziwen Yan Feasibility of a District Heating System in Fjardabyggd Using Waste Heat from Alcoa Fjardaal . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 23 Leo Blaer Haraldsson, Gudrun Saevarsdottir, Maria S. Gudjonsdottir and Gestur Valgardsson Research and Application on Waste Heat Recycling and Preheating Technology of Iron-Making Hot Blast Stove in China . . . . . . . . . . . . . . 33 Xin Li, Fuming Zhang, Guangyu Yin and Chaozhen Cao Influence of Proportion of Pellet on Burden Distribution . . . . . . . . . . . . 47 Jiansheng Chen, Haibin Zuo, Jingsong Wang, Qingguo Xue and Jiapeng Liang High-Temperature Online Reforming of Converter Gas with Coke Oven Gas . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 57 Binglang Ren, Lin Lin and Jingsong Wang Preparation and Characterization of Manganese-Based Catalysts for Removing NO Under Low Temperatures . . . . . . . . . . . . . 69 Kaijie Liu, Qingbo Yu, Junbo San, Zhicheng Han and Qin Qin vii Simultaneous CO2 Sequestration of Korean Municipal Solid Waste Incineration Bottom Ash and Encapsulation of Heavy Metals by Accelerated Carbonation . . . . . . . . . . . . . . . . . . . . . . . . . . . . 81 T. Thriveni, Ch. Ramakrishna and Ahn Ji Whan Effect of Biomaterial (Citrullus Lanatus Peels) Nanolubricant on the Thermal Performance and Energy Consumption of R600a in Refrigeration System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 91 Oluseyi O. Ajayi, Caleb C. Aba-Onukaogu, Enesi Y. Salawu, F. T. Owoeye, D. K. Akinlabu,A. P. I. Popoola, S. A. Afolalu and A. A. Abioye Performance and Energy Consumption Analyses of R290/Bio-Based Nanolubricant as a Replacement for R22 Refrigerant in Air-Conditioning System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 103 Oluseyi O. Ajayi, Teddy I. Okolo, Enesi Y. Salawu, F. T. Owoeye, D. K. Akinlabu, E. T. Akinlabi, S. T. Akinlabi and S. A. Afolalu Characterizations of Manganese-Based Desulfurated Sorbents for Flue-Gas Desulfurization . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 113 Yanni Xuan, Qingbo Yu, Kun Wang, Wenjun Duan and Qin Qin The Manganese-Based Zirconium (Zr) and Chromium (Cr) Polymeric Pillared Interlayered Montmorillonite for the Low-Temperature Selective Catalytic Reduction of NOx by Ammonia (NH3) in Metallurgical Sintering Flue Gas . . . . . . . . . . . . . . . . . . . . . . . . . . . . 123 Zhicheng Han, Qingbo Yu, Kaijie Liu, Huaqing Xie and Qin Qin Characterization of Polymeric Solutions with TiO2 Photocatalytic Conversion Efficiency Exposed to Different CO2 Sources . . . . . . . . . . . . 133 Aline Hernández, Natalia Loera, Gerardo Pérez and Francisco Blockstrand Comparison Between Lactuca sativa L. and Lolium perenne: Phytoextraction Capacity of Ni, Fe, and Co from Galvanoplastic Industry . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 137 Aline Hernández, Natalia Loera, María Contreras, Luis Fischer and Diana Sánchez Determination of Crystallite Size and Its Effect on Sulfur Content, CO2 Reactivity, and Specific Electrical Resistance of Coke . . . . . . . . . . 149 Saeb Sadeghi, Mohsen Ameri Siahooei, Sid Hadi Sajadi and Borzu Baharvand Determination of Limiting Current Density, Plateau Length, and Ohmic Resistance of a Heterogeneous Membrane for the Treatment of Industrial Wastewaters with Copper Ions in Acid Media . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 157 K. S. Barros, J. A. S. Tenório, V. Pérez-Herranz and D. C. R. Espinosa viii Contents Effect of pH and Potential in Chemical Precipitation of Copper by Sodium Dithionite . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 165 I. A. Anes, A. B. Botelho Junior, D. C. R. Espinosa and J. A. S. Tenório Study of Separation Between CO with H2 on Carbon Nanotube by Monte Carlo Simulation in Aluminum Smelter . . . . . . . . . . . . . . . . . 175 Mohsen Ameri Siahooei, Borzu Baharvand, Alireza Fardani, Mokhita Vahedi Zade and Sid Hadi Sajadi Vinylic and Waterproofing Paint with TiO2 as Photocatalytic Active Effects in Lolium Perenne Germination . . . . . . . . . . . . . . . . . . . . 183 Aline Hernández, Natalia Loera, Gerardo Pérez and Francisco Blockstrand Part II Solar Cell Silicon The Influence of Boron Dopant on the Structural and Mechanical Properties of Silicon: First Principles Study . . . . . . . . . 191 Shadia Ikhmayies and Yasemin Ö. Çiftci The Influence of Phosphorus Dopant on the Structural and Mechanical Properties of Silicon . . . . . . . . . . . . . . . . . . . . . . . . . . . 201 Shadia Ikhmayies and Yasemin Ö. Çiftci Simple and Highly Effective Purification of Metallurgical-Grade Silicon Through Metal-Assisted Chemical Leaching . . . . . . . . . . . . . . . . 213 Fengshuo Xi, Shaoyuan Li, Wenhui Ma, Kuixian Wei, Jijun Wu, Keqiang Xie, Yun Lei, Zhengjie Chen, Jie Yu, Xiaohan Wan and Bo Qin Wettability Behavior of Si/C and Si–Sn Alloy/C System . . . . . . . . . . . . 223 Yaqiong Li and Lifeng Zhang Phase Diagrams of Al–Si System . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 231 Shadia Ikhmayies The Separation of Refined Silicon by Gas Pressure Filtration in Solvent Refining Process . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 239 Tianyang Li, Lei Guo, Zhe Wang and Zhancheng Guo Part III 5th Symposium on Advanced Materials for Energy Conversion and Storage Comparison of Solar-Selective Absorbance Properties of TiN, TiNxOy, and TiO2 Thin Films . . . . . . . . . . . . . . . . . . . . . . . . . . 253 Hanan Abd El-Fattah, Iman El Mahallawi, Mostafa Shazly and Waleed Khalifa Electrophoretically Deposited Copper Manganese Spinel Coatings for Prevention of Chromium Poisoning in Solid Oxide Fuel Cells . . . . . 265 Zhihao Sun, Srikanth Gopalan, Uday B. Pal and Soumendra N. Basu Contents ix Observations on Accelerated Oxidation of a Ferritic Stainless Steel Under Dual Atmosphere Exposure Conditions . . . . . . . . . . . . . . . 273 Michael Reisert, Ashish Aphale and Prabhakar Singh DOC-Stabilized PVAc/MWCNTs Composites for Higher Thermoelectric Performance . . . . . . . . . . . . . . . . . . . . . . . . . 283 Hussein Badr, Mahmoud Sorour, Shadi Foad Saber, Iman S. El-Mahallawi and Fawzi A. Elrefaie Synthesis and Electrocatalytic Properties of Ni–Fe-Layered Double Hydroxide Nanomaterials . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 293 Mengxin Miao, Xiaobo Han, Rulong Jia, Wei Ma and Guihong Han Author Index . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 303 Subject Index. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 305 x Contents About the Editors Tao Wang is the Chief Metallurgist at Nucor Steel. He is the Lead Engineer in the process and product research and development areas. Dr. Wang’s current focus is to develop andmodify a novel thin strip casting technology, which uses up to 90% less energy to process liquid steel into hot rolled steel sheets than conventional casting methods. Dr. Wang has rich experience in metallurgical thermodynamics, thermal energy storage and transfer, steelmaking, metal solidification and casting, and metal corrosion. He obtained his Ph.D. and M.S. from the University of Alabama and received his B.S. from Xi’an Jiao Tong University in China. In his areas of research, Dr. Wang has published over 20 papers and patents which have led to breakthroughs in thermodynamic modeling, high-efficiency thermal energy transfer med- ium development, and thin strip metal casting technol- ogy. Dr. Wang received the 2017 SME Outstanding Young Manufacturing Engineers from Society of Manufacturing Engineers, and the 2013 Light Metals Division (LMD) Best Energy Paper Award from TMS. He is also the 2016 TMS Young Leaders Professional Development Award winner. Dr. Wang was selected to become amember of TMSEmerging Leaders Alliance in 2015. He serves on the TMS Energy Committee and Pyrometallurgy Committee, and the Metallurgy— Steelmaking & Casting Technology Committee and Continuous Casting Technology Committee, Southeast Chapter within the Association for Iron & Steel Technology (AIST). xi Xiaobo Chen earned his Ph.D. from Deakin University in 2010 for his work in materials science and engineer- ing and then joined the Department of Materials Science and Engineering at Monash University as Postdoctoral Research Fellow, DECRA Awardee, and Senior Research Fellow. He joined RMIT as VC Senior Research Fellow in March 2017 and is based in the School of Engineering at City Campus. His research is multidisciplinary and spans from chemistry and materials science through to corrosion, electrochemistry, and biomaterials, and shows promise in benefitting the wider community. Dr. Chen’s research aims to provide functional characteristics to the surface of light metals to satisfy a large range of engineering applications in automotive, 3C, and biomedical indus- tries. Dr. Chen has attracted extensive research funding from the ARC as the Lead Chief Investigator on a 3-year ARC Discovery Early Career Researcher Award (DECRA) in 2013, a 3-year ARC Linkage grant in 2015, and a 3-year research grant with the ARC Research Hub for nanoscience-based construction materials manufacturing in 2017. He hasalso worked with the Baosteel-Australia Joint Research and Development Centre and Mitsubishi Heavy Industry on three research contracts. Donna Post Guillen has more than 30 years of research and engineering experience and has served as Principal Investigator for numerous multidisciplinary projects encompassing energy systems, nuclear reactor fuels and materials experiments, and wasteform development. She is experienced with X-ray and neutron beamline experiments, computational methods, tools and software for data analysis, visualization, application development, machine learning and informatics, simulation, design, and programming. Her core areas of expertise are thermal fluids, computational fluid dynamics, and heat transfer analysis. She has performed irradiation testing of new materials and thermal analysis for nuclear reactor experiments in her role as Principal Investigator/ Technical Lead for the DOE Nuclear Science User Facility Program. She is the lead inventor on two patents for a new metal matrix material to produce a fast neutron flux environment within a pressurized water reactor. She xii About the Editors actively mentors students, routinely chairs and organizes technical meetings for professional societies, serves in leadership capacity for the American Nuclear Society (Thermal Hydraulics Executive and Program Committees), The Minerals, Metals & Materials Society (former Chair of the Energy Committee, JOM Advisor), and the American Society of Mechanical Engineers (Thermal Hydraulics and Computational Fluid Dynamic Studies Track Co-Chair), provides subject matter reviews for proposals and technical manuscripts, has published over 100 papers and received two Best Paper awards, authored technical reports and journal articles, and written/edited three books. Lei Zhang is an Associate Professor in the Department of Mechanical Engineering at the University of Alaska Fairbanks (UAF). Prior to joining the UAF, Dr. Zhang worked as a postdoctoral associate in the Department of Chemical and Biomolecular Engineering at the University of Pennsylvania. Dr. Zhang obtained her Ph.D. in Materials Science and Engineering from Michigan Technological University in 2011, and her M.S. and B.E. in Materials Science and Engineering from China University of Mining and Technology, Beijing, China, in 2008 and 2005, respectively. Her current research mainly focuses on the synthesis of metal-organic frameworks (MOFs) and MOF-based nanocomposites, and the manipulation of their proper- ties and applications in gas storage, separation, and water treatment. She is also working on the development and characterization of anticorrosion coatings on metal- lic alloys for aerospace and biomedical applications. Dr. Zhang has served on TMS Energy Committee since 2014, including the Vice-Chair role in 2018–2019, and served on a Best Paper Award Sub-committee of the committee. She has served as a frequent organizer and session chair of TMS Annual Meeting symposia (2015– present). She was the recipient of 2015 TMS Young Leaders Professional Development Award. About the Editors xiii Ziqi Sun is an Associate Professor and an ARC Future Fellow at the School of Chemistry, Physics and Mechanical Engineering, Queensland University of Technology, Australia. He received his Ph.D. in 2009 from Institute of Metal Research, Chinese Academy of Sciences and his B.Eng. in 1999 from Central South University China. He was awarded with prestigious awards and fellowships including the TMS Young Leaders Development Award from The Minerals, Metals & Materials Society (TMS, 2015), Future Fellowship (FT2, 2018) and Discovery Early Career Research Award (DECRA, 2014) from Australian Research Council, Alexander von Humboldt Fellowship from AvH Foundation Germany (2009), Australian Postdoctoral Fellowship from Australian Research Council (APD, 2010), and Vice-Chancellor’s Research Fellowship from University of Wollongong (2013). He is also serving as Chair of the Energy Committee of TMS, Editor of Sustainable Materials and Technologies (Elsevier), Principal Editor of Journal of Materials Research (MRS), Associate Editor of Surface Innovations (ICE Science), Editorial Board Member of Scientific Reports (Nature Publishing Group), and Journal of Materials Science and Technology (Elsevier). He was also Guest Professor of Shenzhen Institute, Peking University, and Honorary Fellow of University of Wollongong. Dr. Sun is the program leader for three ongoing Australian Research Council Projects. He held the roles as lead organizer in TMS conferences, ACerS annual conferences, and AM&ST18 symposium. His major research interest is the rational design of bio-inspired metal-oxide nano- materials for sustainable energy harvesting, conversion, and storage. xiv About the Editors Cong Wang is a Professor in the School of Metallurgy, Northeastern University, China. Prior to joining the faculty of his alma mater, he worked in Northwestern University, Saint-Gobain, and Alcoa, all in the United States. He obtained his Ph.D. from Carnegie Mellon University, M.S. from Institute of Metal Research, Chinese Academy of Sciences, and B.S. (with honors) from Northeastern University. He is now leading a group dedicated to oxide metallurgy. Dr. Wang is an active member and a prolific scholar in the global metallurgy community. He has been recognized with distinctions such as TMS Early Career Faculty Fellow Award, CSM Youth Metallurgy S&T Prize, Newton Advanced Fellowship, JSPS Invitational Fellowship, TÜBİTAK Fellowship, and SME Out- standing Young Manufacturing Engineer Award. He serves as a Key Reader and Vice-Chair for the Board of Review forMetallurgical and Materials Transactions B; Review Editor for Journal of Materials Science and Technology; Editorial Board Member of International Journal of Refractory Metals and Hard Materials and Journal of Iron and Steel Research, International; and Corresponding Expert for Engineering. He chaired the TMS Energy Committee from 2016 to 2017. He is the inaugural chair for the ASM Shenyang Chapter, and faculty advisor for Material Advantage North- eastern University. He initiated the International Metallurgical Processes Workshop for Young Scholars (IMPROWYS), and organized major conferences/ symposia of technical significance. Nawshad Haque is a Senior Scientist at the Australian national research agency Commonwealth Scientific and Industrial Research Organization (CSIRO). He is leading a range of projects that evaluates technology for resources industries for saving energy, water and operating costs. Currently his main projects are to study the techno-economic and environmental impacts of hydrogen and ammonia production technologies, fuel cells, off-grid, solar, wind, biomass and hybrid energy systems, and life cycle based emission studies of LNG production. He joined CSIRO Mineral Resources as a Research Scientist (Process Modelling) in 2007. His current research focuses on process, project, and About the Editors xv technology evaluation applying life cycle assessment (LCA) methodology and techno-economic capabilities using various tools, software, and databases. He has contributed to develop a number of novel technologies and flowsheets for “Mine to Metal” production and energy processing at CSIRO. His publications and industry reports are widely used internally and exter- nally and assist in decision-making both in Australia and internationally. Dr. Haque completed his Doctorate in Engineering at the University of Sydney on process modeling, simulation, and optimization in 2002. He commenced work as a Research Scientist at New Zealand Forest Research Institute (Scion) and later seconded to CSIRO at Clayton to conduct research on drying process simulation and technology evaluation for industries. He is an active leader in professional societies—anelected Fellow of the Australian Institute of Energy and the Australasian Institute of Mining and Metallurgy, a member of The Minerals, Metals & Materials Society, and a Director of Australian Life Cycle Assessment Society. Dr. Haque has supervised undergraduate and Ph.D. students, and he coordinates and offers mineral processing and life cycle assessment courses for undergraduate students and workshops for professionals. He has a number of international collab- orations with the universities and publicly funded research laboratories on mineral, metal processing, energy processing, and sustainability. John A. Howarter is an Associate Professor in Materials Engineering at Purdue University with a joint appointment in Environmental & Ecological Engineering. His research interests are centered on synthesis, processing, and characterization of sustain- able polymers and nanocomposites, value recovery through recycling and reprocessing of waste materials, and sustainable materials which can enable improved design for the environment. John is Chair of the TMS Public and Governmental Affairs committee and serves on the TMS Board of Directors. Since 2014, he has served as the chapter advisor for the Purdue University Material Advantage student organization. John earned a B.S. from The Ohio State University in 2003 and Ph.D. from Purdue University in 2008, both in Materials Engineering. xvi About the Editors From 2009 to 2011, he was a National Research Council postdoctoral scholar in the Polymers Division of the National Institute of Standards and Technology in Gaithersburg, Maryland. Neale R. Neelameggham is “The Guru” at IND LLC, involved in international technology and management consulting in the field of critical metals and associated chemicals, thiometallurgy, energy technologies, soil biochemical reactor design, lithium-ion battery design, and agricultural uses of coal. He was a visiting expert at Beihang University of Aeronautics and Astronautics, Beijing, China and a plenary speaker at the Light Metal Symposium in South Africa on the topic of low carbon dioxide emission processes for magnesium. Dr. Neelameggham has more than 38 years of expertise in magnesium production and was involved in process development of the startup company NL Magnesium through to the present US Magnesium LLC, UT until 2011. He and Brian Davis authored the ICE-JNME award-winning (2016) article “21st Century Global Anthropogenic Warming Convective Model.” He is presently developing “stored renewable energy in coal” Agricoal™ for greening arid soils and has authored an e-book Eco-stoichiometry of Anthropogenic CO2 That Returns to Earth on a new discovery of quantification of increasing CO2 returns to Earth. Dr. Neelameggham holds 16 patents and patent applications, and has published several technical papers. He has served in the Magnesium Committee of the TMS Light Metals Division (LMD) since its inception in 2000, chaired it in 2005, and in 2007 he was made a permanent coorganizer for the Magnesium Technology Symposium. He has been a member of the Reactive Metals Committee, Recycling Committee, and Titanium Committee, and was a Program Committee Repre- sentative for LMD. Dr. Neelameggham was the inaugural chair, when in 2008, LMD and the Extraction and Processing Division created the Energy Committee, and he has been a coeditor of the Energy Technology symposium through the present. He received the LMDDistinguished Service Award in 2010. While he was the chair of Hydromet- allurgy and Electrometallurgy Committee, he initiated the Rare Metal Technology symposium in 2014. He is About the Editors xvii coeditor for the 2019 symposia on Magnesium Technology, Energy Technology, Rare Metal Technology, REWAS 2019, and Solar Cell Silicon. Shadia Ikhmayies received B.Sc. and M.Sc. from the physics department at the University of Jordan in 1983 and 1987, respectively, and a Ph.D. on the topic of producing CdS/CdTe thin film solar cells from the same university in 2002. She now works at Isra University in Jordan as an Associate Professor. Her research is focused on producing and characterizing semiconductor thin films, and thin film CdS/CdTe solar cells. She also works in characterizing quartz in Jordan for the extraction of silicon for solar cells and characterizing different materials by computation. She has published 48 research papers in international scientific journals, 73 research papers in conference proceedings, and 3 chapters in books. She is the author of two books for Springer, Silicon for Solar Cell Applications and Performance Optimization of CdS/CdTe Solar Cells (both in production), editor of the book Advances in II–VI Compounds Suitable for Solar Cell Applications (Research Signpost), the book Advances in Silicon Solar Cells (Springer), an eBook series about material science (in development with Springer), and several TMS proceedings publications. She is the winner of the TMS Frank Crossley Diversity Award (2018), and the World Renewable Energy Congress 2018 (WREC-18) Pioneering Award. Dr. Ikhmayies is amember of theTheMinerals,Metals & Materials Society (TMS) and the World Renewable Energy Network (WREN). She is a member of the international organizing committee and the interna- tional scientific committee in the European Conference on Renewable Energy Systems (ECRES2015– ECRES2018). She is a member of the editorial board of the International Journal of Materials and Chemistry (Scientific & Academic Publishing), and has served as a technical advisor/subject editor for JOM (2014 and 2019). She has been a guest editor for topical collections from the European Conference on Renewable Energy Systems in the Journal of Electronic Materials, and an editorial advisory board member for Recent Patents on Materials Science (Bentham Science). She is a reviewer for 24 international journals, was the Chair of the TMS xviii About the Editors Materials Characterization Committee (2016–2017), and has been lead organizer of more than four symposia at the TMS Annual Meeting and Exhibition. York R. Smith is an Assistant Professor of Metallurgical Engineering in the College of Mines and Earth Sciences at the University of Utah, where he specializes in extractive metallurgy. Growing up in Northern Michigan, his love for snow-covered peaks and open spaces led him to the University of Nevada, Reno where he obtained his B.S. and M.S. in Chemical Engineering. Given his only criterion of decent skiing, he then moved to the University of Utah where he obtained his Ph.D. in Metallurgical Engineering. After a postdoctoral research appointment from the U.S. Department of Energy, Office of Energy Efficiency and Renewable Energy, Dr. Smith joined the faculty of the College of Mines and Earth Sciences at the University of Utah. His current research interests include nonfer- rous metal recycling, electrochemistry and interfacial phenomena, and sustainable/green metallurgical engi- neering. Leili Tafaghodi is an Assistant Professor and the extractive metallurgy industry research chair at the University of British Columbia, Vancouver, Canada. Leili’s research is built around the idea of sustainable high-temperature extraction and refining of materials. She obtained her Ph.D. from the University of Toronto and specializes in thermodynamics and kinetics of high-temperature materials processes and synthesis and refining of high-quality metals and alloys. About the Editors xix Amit Pandey is a Manager (Manufacturing Innovation and Integration) at LG Fuel Cell Systems (LGFCS) in North Canton, Ohio. Previously, he was employed at Johns Hopkins University (JHU) and Oak Ridge National Laboratory (ORNL). He is primarily interested in structural and functional materials for energy con- version and storage. Dr. Pandey received his B.S. (2003) in Mining Engineeringfrom Indian Institute of Technology (IIT– BHU) Varanasi, India. Later, he received his M.S. (2005) in Civil Engineering from University of Arizona and Ph.D. (2010) in Mechanical Engineering from University of Maryland. He has Google Scholar citations *700 and has received young leader awards from various materials societies (ACerS, TMS, ASM). In 2017, he was selected to attend the US. Frontiers of Engineering Symposium, National Academy of Engineering, USA. xx About the Editors Part I 2019 Energy Technologies and Carbon Dioxide Management Symposium Analysis on Energy Efficiency and Optimization of HIsmelt Process Chao-zhen Cao, Yu-jie Meng, Fang-xing Yan, Dian-wei Zhang, Xin Li and Fu-ming Zhang Abstract HIsmelt process is a clean and efficient iron-making technology. The production of the first HIsmelt commercial plant of China, which was built in 2016, is stable at present, and remarkable results have been achieved in environmental protection and production cost aspects. The energy efficiency and itsmain influencing factors of HIsmelt process were systematically analyzed in this paper, combining with China’s HIsmelt plant production practice. It has been pointed out that the main restrictive factors are the high efficient utilization of high temperature and low calorific value SRV off-gas to further improve the energy efficiency of HIsmelt. It introduced the process improvement and optimization of the HIsmelt plant in China, around the hot air blast position control, iron ore powder preheating, gas purification, and waste heat recovery. Keywords HIsmelt · Smelting reduction · Iron-making · Energy efficiency Improvement HIsmelt process is a typical “one-step” melting reduction process; its reduction and melting process take place in the same vessel, which can directly use powder ore and pulverized coal in. It did not use coke anymore, and the raw materials do not need to be agglomerated. So it is a meaningful smelting reduction process [1]. China’s first HIsmelt plant with annual production of 80×104 t hot metal was put into operation in 2016, and this plant has achieved significant results in rawmaterial flexibility, envi- ronmental protection, and production costs. Compared with blast furnace process, the successful implementation of Chinese HIsmelt plant has a significant and lead- ing role in promoting the development of smelting reduction iron-making technology [2]. HIsmelt process as a representative “metal bath” smelting reduction process, the raw materials were deep injected into the iron bath specially. On the one hand, the C. Cao (B) · Y. Meng · F. Yan · X. Li · F. Zhang Beijing Shougang International Engineering Technology Co., Ltd, Beijing, China e-mail: cczts@sina.com D. Zhang Shougang Research Institute of Technology, Beijing, China © The Minerals, Metals & Materials Society 2019 T. Wang et al. (eds.), Energy Technology 2019, The Minerals, Metals & Materials Series, https://doi.org/10.1007/978-3-030-06209-5_1 3 4 C. Cao et al. pulverized coal inject into the iron bath can be directly carburized by the molten iron; on the other hand, under the action of carrier gas the iron bath produces strong stirring; it forms “fountain”. The liquid slag and iron droplet splashing after being heated in the upper high-temperature zone, and then returned to the metal bath. The heat generated by off-gas post-combustion continuous transfers to the bath,which can be achieved higher heat transfer efficiency under the higher post-combustion degree, which is a key part of the whole process. Currently, compared with the blast furnace process, there are still some gaps in energy utilization efficiency, which shows that the process energy consumption is higher, so it is important to optimize the energy efficiency of the HIsmelt plant in order to improve the technology competitiveness. Operation Practice of Chinese HIsmelt Plant In 2012, Rio Tinto signed a licensing agreement with Chinese companies to build HIsmelt industrial plants in China. In the design and construction periods, this Chi- nese HIsmelt plant has carried out the improvement and optimization in accordance with the problems occurred on the equipment, technology, and production process in Kwinana plant. After more than 5 years working on process adjustment and equip- ment optimization, it accomplished continuous stable production in 2017 [3]. Chinese HIsmelt plant started construction in 2013, completed in August 2016, it goes into stable production in September 2017. It has a total of 450,000 tons of high- purity pig iron until March 2018, daily maximum production reached 1930 t; average daily output reached 1685 t in October 2017, monthly output reached 51,714 t, coal consumption per iron tons gradually reduced, it goes to 900 kg/thm during the stable production, and the lowest coal consumption is 810 kg/tHM, close to the reach design value. The molten iron contains less P, the harmful element content is very low, and the quality of pig iron has reached to Chinese high pure pig iron national standard level. SRV lining condition is still good, and the first campaign life of SRV lining has been more than 450,000 tons iron, only a partial repair, especially the slag line part erosion problem has been better resolved [4] (Table 1; Fig. 1). Table 1 Production indexes of Chinese HIsmelt plant Items Index Time Daily maximum output 1930 t 2017 year Monthly maximum output 51714 t 2017 year Minimum coal consumption 810 kg/tHM 2017 year Weekly maximum operating rate 100% 2017 year Continuous production record 116 days 2017 year Erosion of the lining 45 Mt hot metal Never changed Analysis on Energy Efficiency and Optimization of HIsmelt Process 5 Fig. 1 Chinese HIsmelt plant SRV Heat Balance Analysis Based on the Chinese HIsmelt plant production practice and technological parame- ters, the SRV thermal equilibrium is calculated and analyzed, and the calculation is shown in Table 2 (Fig. 2). As shown in the calculation results, the SRV heat incomes mainly come from the pulverized coal burning, which accounts for 78% of the total heat income, the higher post-combustion degree of the hearth gas, the more heat is generated. In the heat expenditure items, hot metal taken away accounted for 7.6%, slag taken away accounted for 3.5%, iron oxide reduction and coal and carbonate decomposition endothermic amount accounted for about 48%, gas away heat for 33.4%, and SRV furnace heat loss accounted for about 7%, which shows that in addition to reducing Table 2 Heat balance calculation of Chinese HIsmelt plant Serial no. Items GJ/tHM % Serial no. Items GJ/tHM % 1 Hot blast 3.4 14.8 1 Hot metal 1.7 7.6 2 Coal combustion 17.8 78.0 2 Slag 0.8 3.5 3 Hot ore 1.3 5.8 3 Off-gas 7.6 33.4 4 Coal and fluxes 0.1 0.5 4 Dust 0.1 0.4 5 Slag forming heat 0.2 1.0 5 Endothermic reactions 11.0 48.1 6 Heat loss 1.6 6.9 Total 22.8 100.0 Total 22.8 100.0 6 C. Cao et al. 14.8 , 15% 78.0 , 78% 5.8 , 6% 0.5 , 0% 1.0 , 1%Heat Income Hot blast Coal combustion Hot ore Coal& fluxes Slag forming heat 7.6 , 8% 3.5 , 4% 33.4 , 33% 0.4 , 0% 48.1 , 48% 6.9 , 7% Heat Expenditures Hot metal Slag Offgas Dust Endothermic reaction Heat loss Fig. 2 Energy balances calculation of SRV heat consumption, SRV exhaust took too much heat; this is mainly because the off- gas of the SRV temperature is very high, and at 1450 °C above, the off-gas volume of per ton hot metal is about 2240 Nm3/tHM, so how to further improve the heat transfer efficiency in the furnace, reduce the heat brought out by off-gas per ton hot metal and to achieve higher energy recovery efficiency of waste heat of SRV off-gas, it is a key point to improving the energy utilization efficiency of HIsmelt process. SRV Heat TransferProcess Analysis The Heat Transfer Efficiency of the Fountains in SRV The heat of the SRV mainly comes from the high-temperature flame zone which is generated by oxygen-enriched hot blast of HAB and hearth gas combustion; its heat transfer is divided into three parts: (1) heat transfer to the bath, (2) heat to the gas and ash, and (3) heat to the side cooling wall. Among them, the heat transfer to the coal gas and ash is about 7.7 GJ/tHM, the heat transfer to the sidewall is 1.6 GJ/tHM, the heat transfer to the slag iron is 13.5 GJ/tHM, and the effective thermal efficiency is only 59.2%. The Factors Affecting SRV Fountain Heat Transfer Efficiency The SRV heat transfer from the post-combustion high-temperature zone to molten slag and iron includes three ways: radiation, conduction, and convection. These three kinds of heat transfer methods must be considered when the slag layer forms the fountain. The formation of slag fountain area gives the primary and post-combustion heat and fountain flow a good heat transfer conditions in SRV; the falling droplets get the heat and merge with the rising droplet. And there is a balance transfer process Analysis on Energy Efficiency and Optimization of HIsmelt Process 7 through conduction and convection. After the droplets return to the slag layer, remix the pulverized coal which was just injected into the fountain, accepting the new heat transfer so the cycle repeats. The main factors affect the heat transfer efficiency in bath include: (1) The contact surface area between the high-temperature air flow and the fountain flow generated by the primary and post-combustion The contact surface area of hot blast flow and fountain flow depends on the lances height, injection angle, injection pressure, slag viscosity, etc., which the slag viscosity may be the critical factor affecting the fountains forming effect. The greater the slag viscosity, the smaller the depth of the fountain penetrating high-temperature airflow, the larger the diameter of slag droplets in the fountain flow, and the worse the dispersion and uniformity in the off-gas, thus affecting the convective heat transfer effect. In addition, the contact area between the high-temperature airflow and the slag surface is affected by the distance between the lance and the slag face. The different heights of the lance position will directly affect the heat transfer and the effect of post-combustion. (2) Temperature gradient between high-temperature air flow and slag droplet in fountains The temperature gradient between the high-temperature airflow and the droplet can be improved by increasing the post-combustion degree, hot air temperature, and oxygen enrichment rate. The post-combustion degree has a great relationship with the high-temperature gas recirculation ratio; the lower the cycle ratio, the higher the oxygen potential in the airflow and the higher the post-combustion degree; the higher the cycle ratio, the lower the combustible gas concentration and the lower the post-combustion degree. The high-temperature airflow recirculation ratio is related to the furnace size H/D (the height from the outlet to bath/furnace diameter) and the lance height, as well as the reasonable position distribution between the lance inlet and the flue gas outlet. (3) Reduce the sensible heat taken away by off-gas The sensible heat of off-gas depends on the volume and temperature. The off-gas quantity reduction focuses on reducing the N2 content and reducing the SRV off-gas temperature to improve heat transfer. (4) Reduce the heat taken away by cooling water The radiation heat transfer from high-temperature combustion zone to the furnace wall should be effectively controlled. On the one hand, to strengthen the fountain effect and increase the radiation to the slag, thereby inhibiting the radiation to the furnacewall. On the other hand, the cooling panel should forma stable and reasonable thickness of the slag layer, which can reduce the heat conduction of the furnace wall significantly. 8 C. Cao et al. The Influence of SRV Heat Transfer on Reduction Reaction The slag layer and fountain in SRV is a multiphase reaction system with gas, liquid, and solid coexistence. After the iron ore powder injects in the iron bath, iron oxides will be reduced by carbon or CO in the slag to produce hot metal. The hot metal and non-molten carbon contact with the upper zone O2 and CO2 by the fountain action and are reoxidized; this process is called “reverse reaction”. In order to ensure that the reduction reaction can be carried out smoothly, and at the same time, it is better to inhibit the occurrence of the inverse reaction, the droplet should have a certain degree of particle size, which is a pair of contradictions with heat transfer to the droplet size requirements. Controlled the particle size distribution of the molten droplets is a crucial operation to achieve the optimal equilibrium of the heat transfer and reduction reaction. Energy Efficiency Optimization of the HIsmelt Plant in China In order to further improve the energy efficiency, the processes have been optimized in the design and construction process on the basis of the Kwinana practice, which includes the lance position control, the iron ore powder preheating system, the gas purification, and the waste heat utilization. And these have been practical applied in China HIsmelt factory. Optimization of Lance Position Control for HAB The structure, position control, and swirl characteristic of theHABare very important to control the degree of inverse reaction in the SRV and improve the heat transfer efficiency in the molten bath. A relative lower position of the HAB is conducive to improving the heating strength, but an excessively low HAB position will cause an excessive reverse reaction, so the best position of the HAB can maximize the transmission of energy to the molten bath, and ensure that the reduction reaction can proceed normally. In order to improve the heat transfer efficiency in the SRV and adjust the lance position of the HAB, the HAB position design has been optimized in the design process of the HIsmelt plant in China. The HAB position can be adjusted according to production requirements, by four 600 mm water-cooled spools. By adjusting the position of four water-cooled short tubes, the height gradient of HAB can be adjusted to 0, 0.6, and 1.2 m, which can provide more control means to ensure the working state of the HAB (Fig. 3). Analysis on Energy Efficiency and Optimization of HIsmelt Process 9 Fig. 3 Position adjustment schematic of HAB Optimization of Off-Gas Waste Heat Utilization Wet dedusting process is used for SRV off-gas scrubbing in Kwinana plant, in which the high-temperature gas enters the water-cooled hood, the temperature dropped to 800–1000 °C, and then dedusted and cooled through the ring seam scrubbing tower. After that, the gas temperature is dropped to below 100 °C, and the off-gas dust content is below 10 mg/Nm3; then after further cooling, quality of the gas can meet the requirements of the following procedure. The above dedusting process can meet the dust content requirements of the gas, but the disadvantage is that the physical heat of the gas below 1000 °C cannot be recycled. In order to achieve efficient utilization of waste heat and purification of SRV off- gas, the new process is adopted in the Chinese plant (see Fig. 4). The SRV off-gas with temperature of 1450–1650 °C is cooled firstly through the water-cooled hood down to 800–1000 °C, and then enters the cyclone to catch large particle dust, so that the dust content of the gas decreases to 20 g/Nm3. The gas temperature drops to 200–250 °C in waste heat boiler, and then the gas is further dedusted and cooled by ring seam scrubbing tower. The highest production of middle pressure steam is about 56 t/h (5.4 MPa). By adoptingthe above process, the utilization efficiency of the waste heat of SRV off-gas can be remarkably improved. 10 C. Cao et al. Fig. 4 SRV off-gas purification and energy recovery process Ore+Coal Ore+Coal Coal Coal Ore Ore Ore Ore Coal Coal Coal Coal Fig. 5 Schematic of SRV ore+coal injection Optimization of Solid Lance Arrangement The design philosophy of multi points and small lances of ore and coal injection is used in SRVofKwinana plant. The purpose is, throughmultipoint injection, to realize a uniform distribution of iron slag and solid material in the hearth, which helps to improve the kinetic condition of hearth reaction. There are four coal injection lances and four ore injection lances, which are located above hearth refractory and evenly alternately distributed along the circumferential direction (Fig. 5). Analysis on Energy Efficiency and Optimization of HIsmelt Process 11 It has been proved by the research and production practice that the size range control ability of the slag and iron droplet can be further improved by reducing the number of lances and increasing the injection capacity of single mega lance, which can meet the need of heat transfer and reduction reaction and the requirement of the active furnace cylinder and the ore-coal injection amount. During the design process of the new plant, the design scheme of solid injection lances is simplified by reducing the lances from 8 to 4, which can realize the coal and oremixed injection, simplify the solid injection system, reduce the equipment failure potential, and further improve the SRV production efficiency. Conclusions (1) The Chinese HIsmelt plant has been completed and put into operation in August 2016. At present, the plant operation is stable. Compared with the blast furnace process, the HIsmelt technology has significant advantages in the raw material flexibility, environmental protection, production cost, and so on, which has a bright development perspective. (2) The SRV off-gas takes up about 33.4% of the total heat income, further improv- ing the heat transfer efficiency and efficient utilization of the SRV off-gas is the key to improve the energy utilization efficiency of the HIsmelt process. (3) The effective heat transfer efficiency in the SRV furnace is 59.2%, which is affected by the contact surface area in gas–liquid two-phase flow, temperature gradient, and the high-temperature gas quantity. (4) In order to further improve the energy efficiency of theHIsmelt plant, the process improvement and optimization of the HIsmelt plant in China are carried out in the position control of HAB, ore powder preheating, gas purification, and waste heat utilization. References 1. Goodman N, Dry R (2010) HIsmelt ironmaking process. World Steel 2:1–5 2. Cao C, Men X, Zhang F (2017) Latest progress and design optimization of the first HIsmelt process in China. AIST2017, pp 421–429 3. Men X, Lin LI, Zhang F (2015) Application on HIsmelt smelting reduction process in China. Association for iron and steel technology. AISTech2015 proceedings. Association for iron and steel technology, Cleveland, pp 1135–1145 4. Cao C, Meng Y, Mei C (2017) Latest progress in industrialization of HIsmelt process. In: 11th iron and steel conference of China proceedings, pp 1–7 The Characterizations of Hydrogen from Steam Reforming of Bio-Oil Model Compound in Granulated Blast Furnace Slag Xin Yao, Qingbo Yu, Guowei Xu, Qin Qin and Ziwen Yan Abstract The purpose of this research investigating the characterizations of steam reforming of bio-oil model compound in granulated BF (blast furnace) slag was to recoverwaste heat and obtain hydrogen. The results indicated that hydrogen yield and hydrogen fraction first increased and then decreasedwith the increase of temperature. When S/C increased, hydrogen yield and hydrogen fraction increased. But they decreased with the increasing LHSV. Hydrogen yield and hydrogen fraction were 1.68 m3 per kg of bio-oil model compound and 65.39% at the optimum condition with the temperature, S/C and LHSV reaching 750 °C, 9, and 0.9 h−1, respectively. Granulated BF slag containing metallic oxides as CaO and Fe2O3 could promote hydrogen yield and hydrogen fraction, so it was regarded as an excellent heat carrier for the reaction of steam reforming of bio-oil model compound. Keywords Hydrogen · Steam reforming · Bio-oil model compound Granulated blast furnace slag · Heat recovery Introduction Biomass with high production and low ash is recognized as an excellent material to produce hydrogen [1]. There are many chemical processes obtaining hydrogen through biomass such as pyrolysis, gasification, and fermentation [2]. Meanwhile, flash pyrolysis biomass then steam reforming of bio-oil obtained from the pyrolysis process is known as one of the promising methods to obtain hydrogen, which is first proposed by Wang [3]. The technology of flash pyrolysis biomass is developed X. Yao · Q. Yu (B) · G. Xu · Q. Qin · Z. Yan School of Metallurgy, Northeastern University, Shenyang 110819, Liaoning, People’s Republic of China e-mail: yuqb@smm.neu.edu.cn Q. Yu Northeastern University, NO 11, Lane 3, Wenhua Road, Heping District, 345, Shenyang, Liaoning, People’s Republic of China © The Minerals, Metals & Materials Society 2019 T. Wang et al. (eds.), Energy Technology 2019, The Minerals, Metals & Materials Series, https://doi.org/10.1007/978-3-030-06209-5_2 13 14 X. Yao et al. maturely and the researchers mainly focus on the catalysts of steam reforming of bio-oil to promote hydrogen yield and hydrogen fraction [4]. But it is uneconomical to provide heat for the endothermal reaction of steam reforming of bio-oil using fossil fuels. So, searching an appropriate heat carrier is also a key factor for the industrial application of steam reforming of bio-oil. On the other side, blast furnace (BF) slag as a byproduct in the pig iron process is discharged at 1550 °C [5]. Molten BF slag through rotary cup atomizer (RCA) as one of the treatment technologies can obtain granulated BF slag with high glassy phase, which can be used as the raw material of cement [6, 7]. Besides, the obtained granulatedBFslag is also discharged at 1100 °Cwith high-gradeheat.Using chemical reaction to recover waste heat of granulated BF slag has drawn many researchers’ attentions in recent years. Luo [8] investigated biomass steam gasification recovering waste heat from granulated BF slag, demonstrating that granulated BF slag could be used as not only a heat carrier, but also a catalyst for the gasification reaction. Using coal gasification [9], biomassCO2 gasification [10], sludge pyrolysis [11], and sludge gasification [12] to recover waste heat from granulated BF slag were investigated. These results indicated that granulated BF slag could weaken C–C bond and promote the decomposition of hydrocarbons and decrease activation energy of reactions. Therefore, the steam reforming of bio-oil recovering waste heat from granulated BF slag is feasible but lacks the corresponding study. Besides, the components of bio- oil were so complicated that researchers generally investigated the steam reforming of bio-oil model component before that of true bio-oil [13, 14]. In this paper, the steam reforming of bio-oil model component in granulated BF slag was investigated to evaluate the effects of temperature, S/C (mole ratio of steam to carbon in bio-oil model compound), and liquid hourly space velocity (LHSV) on hydrogen yield and hydrogen fraction, obtaining the optimal parameters to guide industrial production. Experiment Materials The compositions of true bio-oil were extremely complex, thus the model compound of bio-oil was used to replace true bio-oil to master the characterizations of steam reforming of bio-oil in granulated BF slag generally and easilyin the studies [13, 14]. The true bio-oil mainly contained acids, alcohols, ketones, and phenols, so the mixture of acetic acid, ethanol, acetone, and phenol with equal quality was used as bio-oil model compound in this study [13]. The chemical component of BF slag analyzed through X-ray fluoroscopy (XRF) is placed in Table 1. Granulated BF slag with diameter less than 2 mm was obtained through the RCA. In order to master the effects of granulated BF slag on the steam reforming of bio-oil model compound, the ceramic ball with similar diameter was used as a blank heat carrier, which had no catalytic effect on the steam reforming reaction [8]. The Characterizations of Hydrogen from Steam Reforming … 15 Table 1 The chemical component of BF slag BF slag SiO2 CaO MgO Al2O3 Fe2O3 TiO2 Trace component Mass% 34.38 41.21 8.22 11.05 2.78 0.35 2.01 Apparatus and Procedures The schematic diagram of the experiment of steam reforming of bio-oil model com- pound is shown in Fig. 1. The systems contained reaction system, cooling system, and analysis system. Themodels of equipmentwere explained in our previous studies [13, 15]. First, granulated BF slag or ceramic ball with height of 15 cm was heated to the desired temperature with a heating rate of 10 °C/min under nitrogen atmosphere. The desired temperature was held for 10 min to maintain temperature balance in the furnace. Then, the different proportions of bio-oil model compound and water were carried into the electric furnace through peristatic pump for 20 min. The syngas was cooled and analyzed in the cooling system and analysis system, respectively. The gas meter and gas analyzer recorded gas volume and gas fraction, respectively. Last, when the fractions of H2, CO, CO2, and CH4 in the syngas were equal to zero, the electric furnace was shut down. Fig. 1 Schematic diagram of experiments of steam reforming of bio-oil model compound 16 X. Yao et al. Steam Reforming Reaction and Evaluation During the process of steam reforming of bio-oil model compound, the primary reactions contained thermal cracking reaction, steam reforming reactions, water gas reaction, and water gas shift reaction, respectively. Those equations were shown as follows. The thermal cracking reaction is CnHmOk → CxHyOz + oH2 + pCO + qCO2+rCH4 + sC, �Hθ800 ◦C > 0 (1) The steam reforming reactions are C2H6O + 3H2O → 2CO2 + 6H2, �Hθ800 ◦C � 210.26 kJ/mol (2) C2H4O2 + 2H2O → 2CO2 + 4H2, �Hθ800 ◦C � 153.33 kJ/mol (3) C3H6O + 5H2O → 3CO2 + 8H2, �Hθ800 ◦C � 295.90 kJ/mol (4) C6H6O + 11H2O → 6CO2 + 14H2, �Hθ800 ◦C � 473.68 kJ/mol (5) CH4 + 2H2O → CO2 + 4H2, �Hθ800 ◦C � 191.10 kJ/mol (6) The water gas reaction is C + H2O → CO + H2, �Hθ800 ◦C � 135.77 kJ/mol (7) The water gas shift reaction is CO + H2O ↔ H2 + CO2, �Hθ800 ◦C � −34.12 kJ/mol (8) The methanation reaction is C + H2 → CH4, �Hθ800 ◦C � −89.45 kJ/mol (9) The hydrogen yield and syngas fraction were used to evaluate the characteriza- tions of steam reforming reaction to obtain the optimum condition in the industrial application. They were defined as follows. The H2 yield (YH2 , Nm 3/kg) was calculated using the following equation: YH2 � VH2 mbio-oil (10) where VH2 and mbio-oil were the volume of hydrogen (Nm 3) and quality of bio-oil model compound (kg), respectively. The syngas fraction (X, %) was calculated using the following equation: The Characterizations of Hydrogen from Steam Reforming … 17 XH2(CO,CO2,CH4) � nH2(nCO, nCO2 , nCH4) nH2 + nCO + nCO2 + nCH4 × 100% (11) where nH2(nCO, nCO2 , nCH4) was the mole of H2 (CO, CO2, and CH4) in the syngas. The liquid hourly space velocity (LHSV, h−1) was controlled through the fre- quency of peristatic pump and it was defined in the following equation: LHSV � Volumetric flow rate of bio-oil model compound volume of granulated BF slag (12) Results and Discussion Effect of Temperature Figure 2 shows H2 yield and syngas fraction at different temperature, S/C of 9 and LHSV of 0.9 h−1 with granulated BF slag. It could be obtained that H2 yield and H2 fraction first increased then decreasedwith the increasing temperature.When temper- ature reached 750 °C, themaximumvalues ofH2 yield andH2 fractionwere obtained, whichwere 1.68m3 per kg of bio-oil model compound and 65.39%, respectively. The variation of CO2 fraction showed the opposite trend compared to that of H2 fraction. While CO fraction increased but CH4 fraction decreased with the increase of tem- perature. The reasons were shown as follows. With the increasing temperature, the endothermic reactions (Eqs. 1–7) shifted to the right side, increasing H2 yield and H2 fraction. But the increasing temperature would shift the exothermic reaction (Eq. 8) to the left side, decreasing H2 yield and fractions of H2 and CO2, but increasing CO fraction. It could be obtained from Table 1 that granulated BF slag contained 41.21% CaO. The increasing temperature was adverse to endothermic reaction (CaO + CO2 →CaCO3), increasing CO2 fraction in the syngas. The endothermic steam reforming of CH4 (Eq. 6) would shift to the right side, decreasing CH4 fraction in the syngas. Thus, the optimal temperature was 750 °C during the process of steam reforming of bio-oil model compound recovering waste heat from granulated BF slag. Effect of S/C Figure 3 shows H2 yield and syngas fraction at different S/C, 750 °C, and LHSV of 0.9 h−1 with granulated BF slag. It could be obtained that H2 yield and H2 fraction first increased then changed not obviously with the increasing S/C. When S/C was up to 9, H2 yield and H2 fraction were almost up to maximum values. The variation of fractions of CO and CO2 showed the opposite trend compared to that of H2 fraction. The S/C had no obvious effect on CH4 fraction. With the increasing S/C, the steam reforming reactions (Eqs. 2–6), water gas reaction (Eq. 7), and water 18 X. Yao et al. Fig. 2 Effects of temperature on hydrogen yield and syngas fraction Fig. 3 Effects of S/C on hydrogen yield and syngas fraction gas shift reaction (Eq. 8) would shift to the right side, increasing H2 yield and H2 fraction. The decreasing fractions of CO, CO2, and CH4 could bemainly attributed to the increasing H2 yield. Meanwhile, the increasing H2 yield would shift methanation reaction (Eq. 9) to the right side, increasingCH4 fraction. Thus, CH4 fraction changed not obviouslywith the increasing S/C.WhenS/Cwas up to 9,H2 yield andH2 fraction were almost invariablewith the continuously increasing S/C. Besides, the higher S/C, the more heat would be carried from granulated BF slag, which was disadvantageous to the industrial application. Considering all the factors, the optimal S/Cwas 9 during the process of steam reforming of bio-oil model compound recovering waste heat from granulated BF slag. Effect of LHSV Figure 4 shows H2 yield and syngas fraction at different LHSV, 750 °C, and S/C of 9 with granulated BF slag. It could be obtained that H2 yield and H2 fraction The Characterizations of Hydrogen from Steam Reforming … 19 Fig. 4 Effects of LHSV on hydrogen yield and syngas fraction decreased with the increasing LHSV. While the variation of CO2 fraction showed the opposite trend compared to that of H2 fraction with the increase of LHSV. The LHSV had little effect on fractions of CO and CH4 during the steam reforming of bio-oil model compound process. The higher LHSV, the steam reforming reaction was more insufficient, decreasing H2 yield and H2 fraction. But the higher LHSV, the more handing capacity of bio-oil model compound was obtained in the industrial application. As shown in Fig. 4, H2 yield and H2 fraction decreased not obviously with the LHSV increasing from 0.6 h−1 to 0.9 h−1. Considering all the factors, the optimal LHSV was 0.9 h−1 during the process of steam reforming of bio-oil model compound recovering wasteheat from granulated BF slag. Effect of Granulated BF Slag The effects of granulatedBF slag on theH2 yield and syngas fraction at 750 °C, S/C of 9, and LHSV of 0.9 h−1 are listed in Table 2. As shown in Table 2, granulated BF slag could promoteH2 yield and fractions ofH2 andCO, and decrease the fractions of CO2 and CH4 in the syngas. It could be obtained that granulated BF slag could catalyze the reaction of steam reforming of bio-oil model compound. As shown in Table 1, granulated BF slag contained 41.21% CaO and 2.78% Fe2O3. Those metallic oxides could weaken C–C bond and promote the decomposition of hydrocarbon, which was illustrated in the corresponding researches [8, 11, 15, 16]. Thus, there was no doubt that granulated BF slag could be beneficial to the process of steam reforming of bio-oil model compound. 20 X. Yao et al. Table 2 Effects of granulated BF slag on hydrogen yield and syngas fraction Conditions Production fraction (%) H2 yield (m3/kg) H2 CO CO2 CH4 With BF slag 65.39 7.40 20.94 6.27 1.68 Without BF slag 56.57 5.84 30.89 6.70 1.44 Conclusions The steam reforming of bio-oil model compound recovering waste heat from gran- ulated BF slag was proposed. The characterizations of steam reforming of bio-oil model compound in granulated BF slag were illuminated through fixed bed exper- iments. The results indicated that granulated BF slag could provide heat for the reaction of steam reforming of bio-oil model compound and catalyze steam reform- ing reaction, increasing hydrogen yield and hydrogen fraction in the syngas. Thus, granulated BF slag was regarded as a superior heart carrier for the reaction of steam reforming of bio-oil model compound. The optimal temperature, S/C, and LHSV for the reaction of steam reforming of bio-oil model compound in granulated BF slag were 750 °C, 9, and 0.9 h−1, respectively. At the optimum condition, hydrogen yield and hydrogen fraction were up to 1.68 m3 per kg of bio-oil model compound and 65.39%, respectively. Acknowledgements This research was supported by the Major State Research Development Pro- gram of China (2017YFB0603603), the National Natural Science Foundation of China (51576035), the Fundamental Research Funds for the Central Universities (N172504019), the National Natu- ral Science Foundation of China (51604077), the National Natural Science Foundation of China (51704071), the Fundamental Research Funds for the Central Universities (N170204016). References 1. Doranehgard MH, Samadyar H, Mesbah M, Haratipour P, Samiezade S (2017) High-purity hydrogen production with in situ CO2 capture based on biomass gasification. Fuel 202:29–35 2. 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Energy 113:845–851 Feasibility of a District Heating System in Fjardabyggd Using Waste Heat from Alcoa Fjardaal Leo Blaer Haraldsson, Gudrun Saevarsdottir, Maria S. Gudjonsdottir and Gestur Valgardsson Abstract The Alcoa Fjarðaál smelter in Iceland consumes 4600 GWh annually to produce aluminum. About 50% of the total energy absorbed by the cells is reduced to waste heat of which roughly 40% is currently lost through exhaust gases. The exhaust gases leave the cells at about 110 °C before entering the gas treatment center (GTC). The feasibility of operating heat exchangers upstream of GTCs has been demonstrated at other smelters. Reyðarfjordur, which is 5.5 km from Fjarðaál currently uses electricity for domestic heating, like other surrounding communities. Previous research has shown that the waste heat from Fjarðaál is more than enough to supply space heating for the local community. This paper will address the technical challenges and suggest solutions to deliver heat in a closed-loop heating circuit from the Fjarðaál plant to Reydarfjordur and estimate the total investment cost for the heat regeneration system. Keywords Heat regeneration · Waste heat · Exhaust gases · Heat exchanger Energy recovery Introduction The aluminum production industry requires a lot of energy. In many cases, power plants are installed specifically for aluminum plants. Indeed, this is the case for Alcoa Fjarðaál in Reyðarfjörður, Iceland. The annual production of aluminum at Fjarðaál is about 350,000 tons. This results in roughly 4600 GWh per year being delivered [1]. The sad thing is that only about 50% of this energy ends up as chemical energy in the aluminum metal and the other 50% is lost in various ways. Figure 1 shows the distribution of heat loss in a typical cell. The heat lost through flue gases is about L. B. Haraldsson (B) · G. Saevarsdottir · M. S. Gudjonsdottir Reykjavik University, Menntavegi 1, Reykjavik 101, Iceland e-mail: leobharaldsson@gmail.com L. B. Haraldsson · G. Valgardsson EFLA Consulting Engineers, Höfðabakki 9, Reykjavík 110, Iceland © The Minerals, Metals & Materials Society 2019 T. Wang et al. (eds.), Energy Technology 2019, The Minerals, Metals & Materials Series, https://doi.org/10.1007/978-3-030-06209-5_3 23 24 L. B. Haraldsson et al. Fig. 1 Heat loss from a typical Hall Heroult cell [2] 40% of the total heat loss but is quite accessible.In view of the vast amounts of heat lost through flue gases, it begs the question of whether or not it could be possible to regenerate some of this heat, for example, by adding a heat regeneration unit. Alcoa Fjarðaál is located in the east part of Iceland next to Reyðarfjörður where, currently, there is no geothermal source being utilized to provide hot water and heat- ing for homes.Whether this is due to a lack of a usable geothermal heat source in this location or lack of initiative is up for debate. The lack of hot water from a geothermal source is rather uncharacteristic for Iceland since about 90% of Icelandic houses are heated with geothermal hot water [3]. Therefore, there is a strong awareness of the benefits of district heating in Iceland, and a good reason to explore whether heat recovery from the pot-room flue gas is a viable option. Background When it comes to locating a heat regeneration system there are two options; upstream or downstream from the gas treatment center (GTC). Implementing a heat regener- ation system upstream from the gas treatment center, or on the dirty side, has its benefits as well as drawbacks. The temperature of the gas before it enters the GTC is higher than after the gas has been treated, by roughly 15 °C [4].When considering the total amount of gas flowing in the system, this energy is quite substantial, in particu- lar as the temperature of the flue gas is not much higher than the serving temperature Feasibility of a District Heating System in Fjardabyggd Using … 25 Fig. 2 Relationship between gas temperature and HF emission [5] of a typical district heating system. Therefore, from an efficiency standpoint, when it comes to energy regeneration, placing a heat regeneration system on the dirty side seems to be a clear choice. Reducing the temperature of the gas before it goes through the GTC can also be beneficial. Hydrogen fluoride (HF) emission has been shown to be directly related to gas temperature. A test performed by Geir Wedde shows that the relationship appears to be exponential, meaning that with higher gas temperature entering the dry scrubber HF emission increases exponentially [5]. Figure 2 shows the results of Wedde’s test. Filter bags also have an increased lifetime if the temperature of the gas is lower [5]. This means that even if the heat regenerated is not being utilized, there are clear benefits from just reducing the temperature of the gas before it enters the gas treatment center. The challenge in placing a heat regeneration unit on the dirty side is just that—it is dirty. The gas is filled with all sorts of particles that form residue or fouling inside pipes [6]. Too much fouling could reduce the performance of a heat exchanger drastically, so much so that the cost of maintenance for the heat exchanger could outweigh the benefits. This is something that could possibly be solved through clever design. There are existing solutions that tackle the problem with fouling on the dirty side. Fives Group has developed, but not implemented, a heat exchanger on the dirty side, and General Electric (Alstrom) has developed and successfully implemented heat exchangers into the flow of gas at the dirty side. For example, in Mosjoen, Norway, a counterflow fire tube heat exchanger from General Electric has been operational for over 8 years without having required cleaning due to pressure loss, while still maintaining an acceptable heat transfer coefficient. General Electric has four solutions set up around the world. One in Mosjoen, Norway, another one in 26 L. B. Haraldsson et al. Fig. 3 Relationship between heat regeneration capacity and outlet temperature of gas [2] Karmoy, Norway, the third in Hamburg, Germany, and the last one in Bahrain, Saudi Arabia [7, 8]. At Fjarðaál, the total volumetric flow rate of flue gas is 910 m3/s. The amount of energy that can be regenerated depends on the outlet temperature of the gas. The acid dew point of the gas is 84 °C and in regular practice, it is not advisable to cool the gas below that mark to avoid corrosion [2]. However, it has been shown that since the amount of acid in the gas is limited, or only 1–2% of the gas, it is safe to cool the gas to 40–50 °C without running into corrosion problems [7, 9]. The amount of energy relative to an outlet temperature of the gas is shown in Fig. 3. The temperature of the gas when it comes out of the pot rooms is roughly 110 °C. The average ambient temperature difference among seasons in Iceland is relatively small compared to other countries, which results in the temperature difference of the gas also being relatively small. The average temperature of the gas ranges from 95 to 130 °C [2]. System Description The goal of the system is to utilize enough heat from the exhaust gases from Fjarðaál to supply Reyðarfjörður with hot water for district heating as well as consumable hot water. The current heat demand for district heating in Reyðarfjörður is roughly 4 MWth and about 5 MWth when consumable hot water is included [10, 11]. One idea is to have the heat delivered in a closed-loop heating circuit from Fjarðaál to Reyðarfjörður. A flow diagram for a suggested system is shown in Fig. 4. Water is heated to about 80 °C and pumped to a storage tank in Reyðarfjörður. From there the water is either distributed into the town for district heating or run through another heat exchanger to heat cold water for domestic use. The water is then returned to Fjarðaál at about 40 °C and heated back up to 80 °C. Feasibility of a District Heating System in Fjardabyggd Using … 27 Fig. 4 Flow diagram of the suggested heating system Assuming the heat in the gas is utilized so that �T�60 °C (110–50 °C), theo- retically only roughly 1/10 of the gas flow is needed to supply Reyðarfjörður with hot water for district heating and domestic consumption. However, achieving such a high �T might not only be difficult, but also unnecessary. At Fjarðaál there are two GTCs (west and east), which both operate on half of the total gas flow in the plant. There are two branches leading into each GTC, each supplying a quarter of the total gas flow. These branches are then split into two separate branches that gather the exhaust gases from 42 pots each, or an eighth of the total gas flow in the plant. Intuitively, there are two ideal locations to place a heat regeneration unit at Fjarðaál; either connecting to the branch carrying a quarter of the gas or an eighth. These locations are shown in Fig. 5. Having equal suction from each pot is important since an imbalance in suction can lead to increased emission an unequal gas collection efficiency between the pots [12]. At Fjarðaál, the gas is sucked through the piping system with main fans at each GTC. This means that the only way to control the suction to each pot rooms is to change the suction to half of the pot rooms at the plant. This means that placing a heat exchanger system at, for example, a single 1/8 location wouldn’t be ideal since it would create unequal suction in the plant. Having the same size heat exchanger system at each 1/4 branch or at each 1/8 branch would work with regards to suction. There is, however, one other possible solution. Currently, the suction at Fjarðaál is not completely balanced. As seen in Fig. 5 the distance from the gas treatment center to the pot rooms is much greater at one end compared to the other. This results 28 L. B. Haraldsson et al. Fig. 5 Layout of west wing piping system to the GTC in a greater pressure loss at one end, or about 200–300 Pa more [13]. Designing a heat regeneration system where the pressure loss is within 600 Pa and placing it on the shorter end would result in an unchanged �P in the system. Having the pressure loss of the heat regeneration system at about 300 Pa would even mitigate the suction imbalances in the plant. This might
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