IntechOpen Book Series will also publish a program of research-driven Thematic Edited Volumes that focus on specific areas and allow for a more in-depth overview of a particular subject.
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IntechOpen Book Series will be launching regularly to offer our authors and editors exciting opportunities to publish their research Open Access. We will begin by relaunching some of our existing Book Series in this innovative book format, and will expand in 2022 into rapidly growing research fields that are driving and advancing society.
With the desire to make book publishing more relevant for the digital age and offer innovative Open Access publishing options, we are thrilled to announce the launch of our new publishing format: IntechOpen Book Series.
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Designed to cover fast-moving research fields in rapidly expanding areas, our Book Series feature a Topic structure allowing us to present the most relevant sub-disciplines. Book Series are headed by Series Editors, and a team of Topic Editors supported by international Editorial Board members. Topics are always open for submissions, with an Annual Volume published each calendar year.
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After a robust peer-review process, accepted works are published quickly, thanks to Online First, ensuring research is made available to the scientific community without delay.
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Our innovative Book Series format brings you:
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Topic Focused Publications - Each topic showcases high impact subject areas
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Renowned Editorial Expertise - Series Editors, Topic Editors, and a team of international Board Members that permanently support each Book Series
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Fast Publishing - quick turnaround which is unique for book publishing
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The benefit of ISSN and ISBN for increased citation and indexing possibilities
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IntechOpen Book Series will also publish a program of research-driven Thematic Edited Volumes that focus on specific areas and allow for a more in-depth overview of a particular subject.
\n\n
IntechOpen Book Series will be launching regularly to offer our authors and editors exciting opportunities to publish their research Open Access. We will begin by relaunching some of our existing Book Series in this innovative book format, and will expand in 2022 into rapidly growing research fields that are driving and advancing society.
We invite you to explore our IntechOpen Book Series, find the right publishing program for you and reach your desired audience in record time.
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Note: Edited in October 2021
\n'}],latestNews:[{slug:"webinar-introduction-to-open-science-wednesday-18-may-1-pm-cest-20220518",title:"Webinar: Introduction to Open Science | Wednesday 18 May, 1 PM CEST"},{slug:"step-in-the-right-direction-intechopen-launches-a-portfolio-of-open-science-journals-20220414",title:"Step in the Right Direction: IntechOpen Launches a Portfolio of Open Science Journals"},{slug:"let-s-meet-at-london-book-fair-5-7-april-2022-olympia-london-20220321",title:"Let’s meet at London Book Fair, 5-7 April 2022, Olympia London"},{slug:"50-books-published-as-part-of-intechopen-and-knowledge-unlatched-ku-collaboration-20220316",title:"50 Books published as part of IntechOpen and Knowledge Unlatched (KU) Collaboration"},{slug:"intechopen-joins-the-united-nations-sustainable-development-goals-publishers-compact-20221702",title:"IntechOpen joins the United Nations Sustainable Development Goals Publishers Compact"},{slug:"intechopen-signs-exclusive-representation-agreement-with-lsr-libros-servicios-y-representaciones-s-a-de-c-v-20211123",title:"IntechOpen Signs Exclusive Representation Agreement with LSR Libros Servicios y Representaciones S.A. de C.V"},{slug:"intechopen-expands-partnership-with-research4life-20211110",title:"IntechOpen Expands Partnership with Research4Life"},{slug:"introducing-intechopen-book-series-a-new-publishing-format-for-oa-books-20210915",title:"Introducing IntechOpen Book Series - A New Publishing Format for OA Books"}]},book:{item:{type:"book",id:"6328",leadTitle:null,fullTitle:"Past, Present and Future Trends in Cotton Breeding",title:"Past, Present and Future Trends in Cotton Breeding",subtitle:null,reviewType:"peer-reviewed",abstract:"Cotton, a source of natural fiber for textile industry, has a long breeding history aiming at increasing cotton fiber yield and its quality. Newly developed cotton varieties poorly respond in low-input environments. Secondly, the impact of changing climate may threaten the cotton production in the future. To address these challenges, efforts toward the development of resilient cotton varieties have been initiated using genetic and modern genomic approaches. In this book, research updates on cotton fiber types and properties, DNA markers for selecting desirable cotton plants, and cotton fiber genomics were compiled. Also, the modern breeding trends including development of transgenic cotton and the biosafety studies and possibilities of improving cotton genome using modern genome editing tools were also compressively discussed.",isbn:"978-1-78923-077-2",printIsbn:"978-1-78923-076-5",pdfIsbn:"978-1-83881-405-2",doi:"10.5772/intechopen.69672",price:119,priceEur:129,priceUsd:155,slug:"past-present-and-future-trends-in-cotton-breeding",numberOfPages:184,isOpenForSubmission:!1,isInWos:null,isInBkci:!1,hash:"53bcba3821a46d8ea2d64ff114a48246",bookSignature:"Mehboob-Ur-Rahman and Yusuf Zafar",publishedDate:"May 2nd 2018",coverURL:"https://cdn.intechopen.com/books/images_new/6328.jpg",numberOfDownloads:9112,numberOfWosCitations:21,numberOfCrossrefCitations:25,numberOfCrossrefCitationsByBook:0,numberOfDimensionsCitations:44,numberOfDimensionsCitationsByBook:1,hasAltmetrics:1,numberOfTotalCitations:90,isAvailableForWebshopOrdering:!0,dateEndFirstStepPublish:"June 26th 2017",dateEndSecondStepPublish:"July 17th 2017",dateEndThirdStepPublish:"October 13th 2017",dateEndFourthStepPublish:"January 11th 2018",dateEndFifthStepPublish:"March 12th 2018",currentStepOfPublishingProcess:5,indexedIn:"1,2,3,4,5,6",editedByType:"Edited by",kuFlag:!1,featuredMarkup:null,editors:[{id:"169707",title:"Dr.",name:"Mehboob-Ur-",middleName:null,surname:"Rahman",slug:"mehboob-ur-rahman",fullName:"Mehboob-Ur- Rahman",profilePictureURL:"https://mts.intechopen.com/storage/users/169707/images/4366_n.jpg",biography:"Dr Mehboob-ur-Rahman (Group Leader, Plant & Molecular Breeding Labs, NIBGE, Faisalabad Pakistan) has been involved in exploring genomes of cotton and wheat—paved the way for the development of nine cotton and one wheat varieties. His group has taken lead in introducing GM-cotton (containing Cry1Ac gene, Mon531) varieties to the farming community. These varieties uplifted the livelihood of 1.3 million cotton farmers (as land owner) and >7 million people (as labor force involved in undertaking various farm operations like sowing, weeding, etc.). He has published nine chapters in foreign publications, as well as over 50 publications. All these efforts were acknowledged by the International and National Agencies by bestowing him with several recognitions/awards including Pride of Performance, ICAC Cotton researcher of the Year 2014.",institutionString:null,position:null,outsideEditionCount:0,totalCites:0,totalAuthoredChapters:"6",totalChapterViews:"0",totalEditedBooks:"1",institution:null}],equalEditorOne:null,equalEditorTwo:null,equalEditorThree:null,coeditorOne:{id:"103521",title:"Dr.",name:"Yusuf",middleName:null,surname:"Zafar",slug:"yusuf-zafar",fullName:"Yusuf Zafar",profilePictureURL:"//cdnintech.com/web/frontend/www/assets/author.svg",biography:null,institutionString:null,position:null,outsideEditionCount:0,totalCites:0,totalAuthoredChapters:"3",totalChapterViews:"0",totalEditedBooks:"0",institution:{name:"National Institute for Biotechnology and Genetic Engineering",institutionURL:null,country:{name:"Pakistan"}}},coeditorTwo:null,coeditorThree:null,coeditorFour:null,coeditorFive:null,topics:[{id:"311",title:"Plant Genetics",slug:"agronomy-plant-genetics"}],chapters:[{id:"59372",title:"Introductory Chapter: Updates on Achieving Sustainable Cotton Production",doi:"10.5772/intechopen.74410",slug:"introductory-chapter-updates-on-achieving-sustainable-cotton-production",totalDownloads:835,totalCrossrefCites:0,totalDimensionsCites:1,hasAltmetrics:0,abstract:null,signatures:"Mehboob-ur-Rahman and Yusuf Zafar",downloadPdfUrl:"/chapter/pdf-download/59372",previewPdfUrl:"/chapter/pdf-preview/59372",authors:[{id:"169707",title:"Dr.",name:"Mehboob-Ur-",surname:"Rahman",slug:"mehboob-ur-rahman",fullName:"Mehboob-Ur- Rahman"},{id:"103521",title:"Dr.",name:"Yusuf",surname:"Zafar",slug:"yusuf-zafar",fullName:"Yusuf Zafar"}],corrections:null},{id:"59434",title:"Targeted Genome Editing for Cotton Improvement",doi:"10.5772/intechopen.73600",slug:"targeted-genome-editing-for-cotton-improvement",totalDownloads:1466,totalCrossrefCites:3,totalDimensionsCites:3,hasAltmetrics:0,abstract:"Conventional tools induce mutations randomly throughout the cotton genome—making breeding difficult and challenging. During the last decade, progress has been made to edit the gene of interest in a very precise manner. Targeted genome engineering with engineered nucleases (ENs) specifically zinc-finger nucleases (ZFNs), transcription activator-like effector nucleases (TALENs), and clustered regularly interspaced short palindromic repeat (CRISPR) RNA-guided nucleases (e.g., Cas9) has been described as a “game-changing technology” for diverse fields as human genetics and plant biotechnology. In eukaryotic systems, ENs create double-strand breaks (DSBs) at the targeted DNA sequence which are repaired by nonhomologous end joining (NHEJ) or homology-directed recombination (HDR) mechanisms. ENs have been used successfully for targeted mutagenesis, gene knockout, and multisite genome editing (GenEd) in model plants and crop plants such as cotton, rice, and wheat. Recently, cotton genome has also been edited for targeted mutagenesis through CRISPR/Cas for improved lateral root formation. In addition, an efficient and fast method has been developed to evaluate guide RNAs transiently in cotton. The targeted disruption of undesirable genes or metabolic pathway can be achieved to increase quality of cotton. Undesirable metabolites like gossypol in cottonseed can be targeted efficiently using ENs for seed-specific low-gossypol cotton. Moreover, ENs are also helpful in gene stacking for herbicide resistance, insect resistance, and abiotic stress tolerance.",signatures:"Zulqurnain Khan, Sultan Habibullah Khan, Muhammad Salman\nMubarik and Aftab Ahmad",downloadPdfUrl:"/chapter/pdf-download/59434",previewPdfUrl:"/chapter/pdf-preview/59434",authors:[{id:"212789",title:"Dr.",name:"Aftab",surname:"Ahmad",slug:"aftab-ahmad",fullName:"Aftab Ahmad"},{id:"213123",title:"Dr.",name:"Sultan",surname:"Habibullah Khan",slug:"sultan-habibullah-khan",fullName:"Sultan Habibullah Khan"},{id:"213124",title:"Mr.",name:"Zulqurnain",surname:"Khan",slug:"zulqurnain-khan",fullName:"Zulqurnain Khan"},{id:"213125",title:"Mr.",name:"Muhammad",surname:"Salman Mubarik",slug:"muhammad-salman-mubarik",fullName:"Muhammad Salman Mubarik"}],corrections:null},{id:"58787",title:"Impact of the Bijective Relationship between Single and Bundle Cotton Fiber’s in Cotton Breeding Programs",doi:"10.5772/intechopen.73328",slug:"impact-of-the-bijective-relationship-between-single-and-bundle-cotton-fiber-s-in-cotton-breeding-pro",totalDownloads:1026,totalCrossrefCites:0,totalDimensionsCites:0,hasAltmetrics:0,abstract:"In this chapter, we focus on the relationship between fibers’ mechanical properties and yarns’ ones by studying their relative behavior and the relationship between single and bundle cotton fibers (respectively, dispositions 1 and 2). For this purpose, three different types of cotton fibers were studied. These cottons were chosen from a list of 12 cottons covering a large panel of varieties and physical properties (maturity, fineness, micronaire, length, tenacity, etc.). Classifications per length classes and linear densities were done in order to have more precision and knowledge of cotton fiber behavior. Modeling the creep behavior of single and bundle fibers will help exploring data for the bijective relationship between the two dispositions. Properties evaluated will include elongation, single fibers and bundle tenacities, work of rupture, and so on. Quality of bundle fibers will be a good tool in predicting spinning performances and thus yarn quality.",signatures:"Wafa Mahjoub, Jean-Paul Gourlot, Jean-Yves Drean and Omar\nHarzallah",downloadPdfUrl:"/chapter/pdf-download/58787",previewPdfUrl:"/chapter/pdf-preview/58787",authors:[{id:"176347",title:"Prof.",name:"Jean-Yves",surname:"Drean",slug:"jean-yves-drean",fullName:"Jean-Yves Drean"},{id:"216317",title:"Dr.",name:"Wafa",surname:"Mahjoub",slug:"wafa-mahjoub",fullName:"Wafa Mahjoub"},{id:"217133",title:"Dr.",name:"Omar",surname:"Harzallah",slug:"omar-harzallah",fullName:"Omar Harzallah"},{id:"226875",title:"Dr.",name:"Jean-Paul",surname:"Gourlot",slug:"jean-paul-gourlot",fullName:"Jean-Paul Gourlot"}],corrections:null},{id:"59774",title:"Temperature Extremes in Cotton Production and Mitigation Strategies",doi:"10.5772/intechopen.74648",slug:"temperature-extremes-in-cotton-production-and-mitigation-strategies",totalDownloads:1522,totalCrossrefCites:17,totalDimensionsCites:29,hasAltmetrics:0,abstract:"Cotton is an important cash crop, providing raw material for different industries and plays crucial role in the economy of several countries. It requires optimum temperature for economic production and causes reduced yield otherwise. Extreme temperature, more importantly, high temperature causes serious yield reduction in cotton by affecting its physiology, biochemistry and quality leading to poor agronomic produce. Freezing temperature also affect the germination percentage and seedling establishment. Several breeding and genomics based studies were conducted to improve the cotton production under high and low temperature stress in cotton. Here we overviewed several agronomic practices to mitigate the effect of extreme temperature, and multiple breeding and molecular approaches to enhance the genetic potential of cotton for temperature tolerance by Marker assisted selection or transgenic approach.",signatures:"Syed Adeel Zafar, Mehmood Ali Noor, Muhammad Ahmed Waqas,\nXiukang Wang, Tayyaba Shaheen, Mubashar Raza and Mehboob-\nUr-Rahman",downloadPdfUrl:"/chapter/pdf-download/59774",previewPdfUrl:"/chapter/pdf-preview/59774",authors:[{id:"169707",title:"Dr.",name:"Mehboob-Ur-",surname:"Rahman",slug:"mehboob-ur-rahman",fullName:"Mehboob-Ur- Rahman"},{id:"185474",title:"Prof.",name:"Tayyaba",surname:"Shaheen",slug:"tayyaba-shaheen",fullName:"Tayyaba Shaheen"},{id:"211571",title:"Dr.",name:"Syed Adeel",surname:"Zafar",slug:"syed-adeel-zafar",fullName:"Syed Adeel Zafar"},{id:"211575",title:"Dr.",name:"Mehmood Ali",surname:"Noor",slug:"mehmood-ali-noor",fullName:"Mehmood Ali Noor"},{id:"229267",title:"Mr.",name:"Muhammad Ahmed",surname:"Waqas",slug:"muhammad-ahmed-waqas",fullName:"Muhammad Ahmed Waqas"},{id:"229269",title:"Mr.",name:"Mubashar",surname:"Raza",slug:"mubashar-raza",fullName:"Mubashar Raza"},{id:"247980",title:"Dr.",name:"Xiukang",surname:"Wang",slug:"xiukang-wang",fullName:"Xiukang Wang"}],corrections:null},{id:"59766",title:"Genetic Mapping in Cotton",doi:"10.5772/intechopen.74513",slug:"genetic-mapping-in-cotton",totalDownloads:1465,totalCrossrefCites:0,totalDimensionsCites:0,hasAltmetrics:0,abstract:"The genus Gossypium provides natural fiber for textile industry worldwide. Genetic improvement in cotton for traits of interest is not up to mark due to scarcity of adequate information about fiber production and quality. Use of DNA markers for overcoming the issues of selection associated with complex traits is the ultimate choice which may lead to initiate breeding by design. Numerous marker-trait associations have been identified for economical traits using linkage analysis in cotton. Currently there is need for developing high-density genetic maps using next-generation sequencing approaches together with genome-wide association studies (GWAS). Efforts have been started in this direction and several QTLs including fiber quality, yield traits, plant architecture, stomatal conductance and verticillium wilt resistance were identified. This chapter narrates genetic diversity, QTL mapping, association mapping and QTLs related to fiber quality traits. The incorporation of various genomic approaches and previously described marker strategies will pave the way for increase in fiber production.",signatures:"Adem Bardak, Khezir Hayat, Oktay Erdogan, Zahid Mahmood,\nNoor-ul-Islam Khan, Muhammad Atif Iqbal, Halil Tekerek, Mehboob-ur-Rahman and Hafiz Muhammad Imran",downloadPdfUrl:"/chapter/pdf-download/59766",previewPdfUrl:"/chapter/pdf-preview/59766",authors:[{id:"169707",title:"Dr.",name:"Mehboob-Ur-",surname:"Rahman",slug:"mehboob-ur-rahman",fullName:"Mehboob-Ur- Rahman"},{id:"183690",title:"Dr.",name:"M Atif",surname:"Iqbal",slug:"m-atif-iqbal",fullName:"M Atif Iqbal"},{id:"187958",title:"Dr.",name:"Adem",surname:"Bardak",slug:"adem-bardak",fullName:"Adem Bardak"},{id:"187959",title:"Mr.",name:"Khezir",surname:"Hayat",slug:"khezir-hayat",fullName:"Khezir Hayat"},{id:"218301",title:"Dr.",name:"Halil",surname:"Tekerek",slug:"halil-tekerek",fullName:"Halil Tekerek"},{id:"243091",title:"Associate Prof.",name:"Oktay",surname:"Erdogan",slug:"oktay-erdogan",fullName:"Oktay Erdogan"}],corrections:null},{id:"58544",title:"Recent Developments in Fiber Genomics of Tetraploid Cotton Species",doi:"10.5772/intechopen.72922",slug:"recent-developments-in-fiber-genomics-of-tetraploid-cotton-species",totalDownloads:1249,totalCrossrefCites:2,totalDimensionsCites:5,hasAltmetrics:0,abstract:"Cotton (Gossypium spp.) produces naturally soft, single-celled trichomes as fiber on the seed coat supplying the main source of natural raw material for the textile industry. It is economically considered as one of the most leading cash crops in the world and evolutionarily very important as a model system for detailed scientific investigations. Cotton production is going through a big transition stage such as losing the market share in competition with the synthetic fibers, high popularity of Bt and herbicide resistance genes in cotton cultivars, and the recent shift of fiber demands to meet the standard fiber quality due to change of textile technologies to produce high superior quality of fibers in the global market. Recently, next-generation sequencing technologies through high-throughput sequencing at greatly reduced costs provided opportunities to sequence the diploid and tetraploid cotton genomes. With the availability of large volume of literatures on molecular mapping, new genomic resources, characterization of cotton genomes, discoveries of many novel genes, regulatory elements including small and microRNAs and new genetic tools such as gene silencing or gene editing technique for genome manipulation, this report attempted to provide the readers a comprehensive review on the recent advances of cotton fiber genomics research.",signatures:"Mirzakamol S. Ayubov, Ibrokhim Y. Abdurakhmonov, Venkateswara\nR. Sripathi, Sukumar Saha, Tokhir M. Norov, Zabardast T. Buriev,\nShukhrat E. Shermatov, Khurshida A. Ubaydullaeva, Jack C. McCarty,\nDewayne D. Deng and Johnie N. Jenkins",downloadPdfUrl:"/chapter/pdf-download/58544",previewPdfUrl:"/chapter/pdf-preview/58544",authors:[{id:"105070",title:"Dr.",name:"Sukumar",surname:"Saha",slug:"sukumar-saha",fullName:"Sukumar Saha"},{id:"188207",title:"Dr.",name:"Venkateswara R.",surname:"Sripathi",slug:"venkateswara-r.-sripathi",fullName:"Venkateswara R. Sripathi"},{id:"213340",title:"Dr.",name:"Mirzakamol",surname:"Ayubov",slug:"mirzakamol-ayubov",fullName:"Mirzakamol Ayubov"},{id:"213344",title:"Prof.",name:"Ibrokhim Y.",surname:"Abdurakhmonov",slug:"ibrokhim-y.-abdurakhmonov",fullName:"Ibrokhim Y. Abdurakhmonov"},{id:"213345",title:"Mr.",name:"Tokhirbek",surname:"Norov",slug:"tokhirbek-norov",fullName:"Tokhirbek Norov"},{id:"213347",title:"Dr.",name:"Zabardast",surname:"Buriev",slug:"zabardast-buriev",fullName:"Zabardast Buriev"},{id:"213348",title:"Dr.",name:"Shukhrat E.",surname:"Shermatov",slug:"shukhrat-e.-shermatov",fullName:"Shukhrat E. Shermatov"},{id:"213349",title:"Dr.",name:"Khurshida",surname:"Ubaydullaeva",slug:"khurshida-ubaydullaeva",fullName:"Khurshida Ubaydullaeva"},{id:"213351",title:"Dr.",name:"Dewayne",surname:"Deng",slug:"dewayne-deng",fullName:"Dewayne Deng"},{id:"213355",title:"Dr.",name:"Johnie",surname:"Jenkins",slug:"johnie-jenkins",fullName:"Johnie Jenkins"},{id:"238901",title:"Dr.",name:"Jack C",surname:"McCarty",slug:"jack-c-mccarty",fullName:"Jack C McCarty"}],corrections:null},{id:"58892",title:"Transgenic Bt Cotton: Effects on Target and Non-Target Insect Diversity",doi:"10.5772/intechopen.73182",slug:"transgenic-bt-cotton-effects-on-target-and-non-target-insect-diversity",totalDownloads:1552,totalCrossrefCites:3,totalDimensionsCites:6,hasAltmetrics:1,abstract:"Occurrence of diversity in ecosystem sustains particular characteristic of a biological community and also ensures stability of the community. Transgenic crops may affect insect biodiversity by unintended impacts on non-target arthropod population. For example, transgenic GM cotton specific to target lepidopterous pests can change the cotton pest spectrum and may induce the growth of new harmful pest species having no pest status. The change in species composition may influence IPM approach in cotton crop. The results of authors’ research studies as well as global impact indicate that GM cotton is highly specific to target pests and has no unintended impact on non-target insect population. GM cotton provides significant season-long field control of target pests (Helicoverpa armigera, Earias spp. and Pectinophora gossypiella), with no significant control of Spodoptera species. The decreased insecticide use in GM cotton has a positive impact on beneficial insect populations and can increase the stability of rare species. Bt cotton has no resistance against non-target sucking insect pests. As GM cotton has no adverse effects on the non-target insect population and can reduce the use of broad-spectrum insecticides, it can become an important tool of IPM program in cotton agro-ecosystem of Pakistan.",signatures:"Muhammad Arshad, Rashad Rasool Khan, Asad Aslam and\nWaseem Akbar",downloadPdfUrl:"/chapter/pdf-download/58892",previewPdfUrl:"/chapter/pdf-preview/58892",authors:[{id:"62420",title:"Dr.",name:"Muhammad",surname:"Arshad",slug:"muhammad-arshad",fullName:"Muhammad Arshad"},{id:"214320",title:"MSc.",name:"Asad",surname:"Aslam",slug:"asad-aslam",fullName:"Asad Aslam"},{id:"214322",title:"Dr.",name:"Rashad",surname:"Rasool Khan",slug:"rashad-rasool-khan",fullName:"Rashad Rasool Khan"}],corrections:null}],productType:{id:"1",title:"Edited Volume",chapterContentType:"chapter",authoredCaption:"Edited by"},subseries:null,tags:null},relatedBooks:[{type:"book",id:"3060",title:"Plant Breeding from Laboratories to Fields",subtitle:null,isOpenForSubmission:!1,hash:"5b517f307caac739435f7fbaed5326ac",slug:"plant-breeding-from-laboratories-to-fields",bookSignature:"Sven Bode Andersen",coverURL:"https://cdn.intechopen.com/books/images_new/3060.jpg",editedByType:"Edited by",editors:[{id:"79388",title:"Prof.",name:"Sven Bode",surname:"Andersen",slug:"sven-bode-andersen",fullName:"Sven Bode Andersen"}],equalEditorOne:null,equalEditorTwo:null,equalEditorThree:null,productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}},{type:"book",id:"3554",title:"Rice",subtitle:"Germplasm, Genetics and Improvement",isOpenForSubmission:!1,hash:"4bd6a333920f0f208c44c2e9fbfdd215",slug:"rice-germplasm-genetics-and-improvement",bookSignature:"Wengui Yan and Jinsong Bao",coverURL:"https://cdn.intechopen.com/books/images_new/3554.jpg",editedByType:"Edited by",editors:[{id:"94348",title:"Dr.",name:"Wengui",surname:"Yan",slug:"wengui-yan",fullName:"Wengui Yan"}],equalEditorOne:null,equalEditorTwo:null,equalEditorThree:null,productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}},{type:"book",id:"1404",title:"Aflatoxins",subtitle:"Detection, Measurement and Control",isOpenForSubmission:!1,hash:"e3a2b9bd1c46dd47875d6a0f3d8b2a39",slug:"aflatoxins-detection-measurement-and-control",bookSignature:"Irineo Torres-Pacheco",coverURL:"https://cdn.intechopen.com/books/images_new/1404.jpg",editedByType:"Edited by",editors:[{id:"62984",title:"Dr.",name:"Irineo",surname:"Torres-Pacheco",slug:"irineo-torres-pacheco",fullName:"Irineo Torres-Pacheco"}],equalEditorOne:null,equalEditorTwo:null,equalEditorThree:null,productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}},{type:"book",id:"2079",title:"Problems, Perspectives and Challenges of Agricultural Water Management",subtitle:null,isOpenForSubmission:!1,hash:"183bb777195754e887da67131255661f",slug:"problems-perspectives-and-challenges-of-agricultural-water-management",bookSignature:"Manish Kumar",coverURL:"https://cdn.intechopen.com/books/images_new/2079.jpg",editedByType:"Edited by",editors:[{id:"102967",title:"Dr.",name:"Manish",surname:"Kumar",slug:"manish-kumar",fullName:"Manish Kumar"}],equalEditorOne:null,equalEditorTwo:null,equalEditorThree:null,productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}},{type:"book",id:"597",title:"Crop Production Technologies",subtitle:null,isOpenForSubmission:!1,hash:"7f87c31dfd7e38f3e10cf7ec02df2201",slug:"crop-production-technologies",bookSignature:"Peeyush Sharma and Vikas Abrol",coverURL:"https://cdn.intechopen.com/books/images_new/597.jpg",editedByType:"Edited by",editors:[{id:"73200",title:"Dr.",name:"Peeyush",surname:"Sharma",slug:"peeyush-sharma",fullName:"Peeyush Sharma"}],equalEditorOne:null,equalEditorTwo:null,equalEditorThree:null,productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}},{type:"book",id:"3800",title:"World Cotton Germplasm Resources",subtitle:null,isOpenForSubmission:!1,hash:"c8454ec008f1d20ebe7387b1be02b2db",slug:"world-cotton-germplasm-resources",bookSignature:"Ibrokhim Y. 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\n
1. Introduction
\n
It has become obvious that global stability, economic prosperity, and quality of life are linked intimately with sufficient supplies of clean energy. Searching for energy resources to meet the world’s growing demand is a major challenge for the next half century. Traditional energy sources are currently depleted at the rate of approximately 4.1 × 1020 J/yr, which is equivalent to continuous power consumption of 13 trillion watt [1]. An increase in the global population to 9 billion people, along with the rapid worldwide technology development and economic growth, leads to an inevitable increase of more than double the demand for energy (to 30 TW) by 2050 and above the triple demand (to 40 TW) by the end of this century [2]. Because of the dramatic hydrocarbon-based power consumption, the harmful effects (such as global warming, acid precipitation, air pollution, ozone depletion, and forest destruction) are increasingly in catastrophic forms. In the pursuit of limiting these drawbacks, suitable actions aimed at reducing the dependence on the fossil fuels are mandatory. The most urgent challenge is in the search for clean and renewable alternative energy resources required for the sustainable development of human civilization. The Sun is the primary source for clean and abundant energy, with nearly 120,000 TW of incident radiations on the earth’s surface which has the potential for covering the human needs [3, 4]. This contains 1.5 × 1018 KWh of energy; which is larger than that of the traditional reserves of oil, coal, and gas which form 1.75 × 1015, 1.4 × 1015, and 5.5 × 1015 KWh, respectively [5, 6]. Hence, solar radiation annually provides over 100 times the energy supplied by the entire known fossil fuel sources. Harvesting solar power has become the modern trend in worldwide research projects reported in the scientific community [5, 6]. The photovoltaics (PVs) or solar cell (SC) devices are considered a promising technology that converts the sunlight directly into electricity on a very large scale without causing pollution [7]. The PVs are considered attractive and a promising candidate that would significantly contribute in the future global renewable energy sources. The main challenge in the PV devices is the cost reduction per watt with respect to the fossil fuel technologies. The cost/watt ratio of the photovoltaic devices is at least 1.5 times higher than the electricity generated from the fossil fuels [8]. The main factor influencing the cost/watt ratio is the size of the active material, mostly crystalline silicon (c-Si), and the manufacturing process. The 30–40% of cost/watt in the c-Si SCs is mainly due to the silicon substrate.
\n
Until now, over 90% of the photovoltaic market is currently dominated by the c-Si solar cells. A maximum power conversion efficiency of 25.6% has been achieved for the c-Si solar cell which is approaching the Shockley-Queisser theoretical limit of 29.4%. Therefore, further improvement in the Si solar cell efficiency is required to compete with the fossil fuels and other alternative sources of energy [9]. Different efficient and reliable avenues have been used to enhance the solar cell efficiency and reduce the cost/watt ratio [9]. In the attempt to do so, different materials have been used, such as crystalline silicon (c-Si) [10], amorphous silicon (a-Si) [11], gallium arsenide (GaAs) [12], copper indium gallium selenide (CIGS) cadmium telluride (CdTe) [9, 13], GaSb/GaAs quantum rings [14], organic material [15], and tandem solar cells by combining several materials [16]. The c-Si material is commercially used because it is cheap and abundant compared to other materials. However, the absorption of the c-Si is poor, and a very large thickness is needed to absorb the solar energy. The bandgap of silicon (1.12 eV) is not at the perfect bandgap for solar spectrum, which severely limits the efficiency of the solar cell. Alternatively, a-Si has a better absorption, and it is usually used for thin-film solar cell materials; however, its efficiency is not higher than the c-Si solar cells. The GaAs has high conversion efficiency up to 30% because its bandgap is close to the optimized bandgap for single absorbed material on the expenses of the high total cost. Also, the cadmium telluride (CdTe) has good conversion efficiency, and the cost can be minimized due to the rapid technology development based on this material. However, the Cd is a highly polluted material, and it has several drawbacks. Recently, different materials can be used to absorb various spectra of solar energy with high efficiency [17, 18]. However, such multi-junction designs need complicated fabrication techniques and expensive manufacturing processes. Thus, the multi-junction solar cells are difficult to be commercialized in the near future.
\n
Currently, the thicknesses of the crystalline silicon wafers used in solar cell market is about 180–300 μm which affects the total cell price due to the silicon materials and processing. Therefore, thin film solar cells attract a great attention, with film thickness in the range of 1–2 μm, as it can be deposited on cheap substrates such as glass, plastic, or stainless steel. However, thin-film solar cell suffers from its weak absorption near the material bandgap especially when using indirect bandgap materials (Si). One of the most alternative important approaches to increase the thin-film solar cell efficiency is the light-trapping techniques to enhance the light absorption into the solar cell active materials. These techniques can increase the light path of the trapped photons in the solar cell materials to generate the electron-hole pair under light illumination. Consequently, the material cost can be minimized by using cheap substrate and solar cell materials with high efficiency. Further, semiconductor nanowires with a few nanometers in diameters can reduce SC material cost with high efficiency. The antireflection layers can be also used to improve the light transmission efficiency [19]. The refractive index of the antireflection layer is chosen between the refractive indices of the active material and surrounding air. The most widely used antireflection materials include SiO2, SiNx, TiO2, Al2O3, CeO2, etc. [20]. The antireflection layer can be merged with the textured structures for better light-trapping improvements. The textured silicon surface structures can be etched by various etchants, such as NaOH [21], TMAH [22, 23], and KOH [24]. Different textured structures have been introduced, including the pyramidal textured surfaces [25], inverted pyramidal [26], honeycomb [27], nanowire [28, 29], gratings [30], V-grooved [31], and other types of structures [32–34]. Most of these structures have large size and are not suitable for thin-film SCs with micrometer or sub-micrometer ranges [30]. Recently, the plasmonic SCs attract sharp attention because it can be used for efficient light trapping through the active layer of the SC. Further, it is simple to merge the plasmonic materials into nanowire and thin-film SC designs [35]. Therefore, the plasmonic nanoparticles are considered as pivotal cornerstone in increasing the light trapping in thin-film and nanowire SCs.
\n
Following this introduction, a review of plasmonic light-trapping techniques for solar cell applications will be discussed. In addition, the recent trends in NW SCs are introduced thoroughly. Further, two novel designs of plasmonic NW SCs are presented and analyzed using 3D full-vectorial finite-difference time-domain method (FDTD). In this regard, plasmonic funnel-shaped SiNWs and plasmonic diamond SiNWs are investigated to present the effect of adding plasmonic materials through or above the SiNWs. The performance of the suggested NWSCs has been investigated in terms of the ultimate efficiency and short-circuit current density, open-circuit voltage, power conversion efficiency, and absorbed field profiles. The reported funnel-shaped SiNWs with plasmonic core show an ultimate efficiency of 36.9% which is higher than cylindrical and conical counterparts by 36.7 and 22.2%, respectively. Further, the plasmonic funnel-shaped design has short-circuit current density of 30.2 mA/cm2 which is greater than 24.5 and 22.12 mA/cm2 of the conical and cylindrical designs. The enhancement in the ultimate efficiency and hence short-circuit current density apparently can be attributed to the combination between three types of optical modes that are supported by the upper cylinder, the lower tapered cone, and the plasmonic material. On the other hand, the SiNW decorated by Ag diamond shows an ultimate efficiency of 25.7% which is higher than conventional SiNWs without plasmonic material by 63%. Additionally, the reported design with Ag diamond shows short-circuit current density of 21.03% mA/cm2 which is greater than the conventional counterpart SiNWs with an improvement of 32.6%.
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2. Review of plasmonic light trapping for solar cell applications
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At the emergence of the eighteenth century, metallic nanoparticles have gained much interest in the research community for their optical properties. Years later, the Raman scattering was enhanced through the utilization of metallic structures [36] which attracted more researchers to the field of plasmonic nanoparticles. Since then, plasmonic resonance, with its fundamental properties, has been introduced to various applications such as integrated optics, biosensing [37, 38], and energy harvesting [39–41]. In metallic nanoparticles, plasmon resonances give rise to a resonance scattering which reduces the reflection over the spectral range. This antireflection effect, caused by random and periodic arrays of metallic nanoparticles, has been extensively studied, theoretically and experimentally, for photovoltaic applications [42, 43]. Stuart and Hall have led the research work in the field of light-sensitive devices enhanced by plasmonic resonance where an enhancement factor of 18 has been reported for a silicon-on-insulator photodetector at 800 nm wavelength. This device has a thickness of 165 nm and is covered by silver nanoparticles on its surface [44]. Additionally, Schaadt et al. [45] proposed a highly doped wafer-based solar cells coated by gold nanoparticles on its surface which achieved an enhancement of 80% for the photocurrent at 500 nm wavelength. Gold nanoparticles have been also used in amorphous thin-film silicon SCs, by Derkacs et al. [43], which improved the overall power conversion efficiency (PCE) by 8%. Pillai et al. [46] achieved 19 and 33% increase in the overall photocurrent for wafer-based SCs and 1.25 μm thick silicon-on-insulator design, respectively, using silver nanoparticles on the cells’ surface. Ouyang et al. [47] employed self-assembled Ag nanoparticles on the surface of thin-film silicon SCs which enhanced the short-circuit current density by 27%. A relative photocurrent enhancement of 10% was reported by Beck et al. [48] for silicon cell of thickness 22 μm covered by an array of Ag nanoparticles. In recent years, Tan et al. [49] used Ag nanoparticles as a plasmonic back reflector which offered a net short-circuit current density gain of 2 mA/cm2. Moreover, different types of solar cells have achieved a performance enhancement based on the plasmonic effect of metallic nanoparticles such as organic and dye-sensitized SCs [50, 51]. In a pioneering breakthrough by Ding et al. [52], plasmonic effect was used to enhance the light absorption and hence, the efficiency of dye-sensitized SCs which achieved a PCE of 5.9% [52]. For a dye-sensitized TiO2 film, reported by Hägglund et al. [53], an enhanced carrier generation was achieved by employing gold nanodisc. Rand et al. [54] also introduced organic SCs based on ultrathin film using tiny silver nanoparticles which enhanced the cell efficiency. Furthermore, an efficiency enhancement of 1.7 in magnitude was reported by Morfa et al. for organic bulk heterojunction solar cells [55]. Another organic SCs proposed by Chen et al. achieved an improved PCE using Au nanoparticles incorporated into anodic buffer layer [56].
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3. State of the art of semiconductor nanowire solar cells
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The current crystalline Si cells are widely used in the PV market with efficiency in the proximity of 25% [57]. A major dilemma lies in the high material cost. The use of cheaper materials, such as polycrystalline thin films or organic semiconductors, decreases the material cost. The amount of required absorbing material can be further decreased by increasing the concentration of the light through a small area [58]. A dramatic improvement in the fabrication techniques can further minimize the loss mechanism and hence increase the SC efficiency. The use of semiconductor nanoantennas (NAs) or NWs readily fulfills all these requirements. In this regard, the NW SCs with structures of a few nanometers in diameters have been considered for PV power generation. The semiconductor NWs have advantages in terms of optical absorption enhancement [59]. This is mainly due to the small reflectivity of the NW array (NWA) with large open area on the frontal surface. The light is trapped by multiple total internal reflections through each nanoscale cylindrical NW resonator [60]. In 2007, Hu and Chen [59] introduced the cylindrical SiNWs with an ultimate efficiency of 15.5%. The behavior of the semiconductor NWs strongly depends on their structural geometrical parameters [59]. Consequently, intense theoretical studies of the optical absorption are required to maximize the ultimate efficiency of the NWA-based SCs. The NWAs with optimized parameters apparently offer higher broadband absorption than solid films [61]. As the NW diameter, period, and wavelength are of the same order, strong light scattering and further light trapping occur [61]. The modified design presented by C. Lin and Povinelli [62] have enhanced the ultimate efficiency up to 23.84% through increasing the lattice constant to 600 nm [62]. The ultimate efficiency of 20.44% was obtained using partially aperiodic vertically SiNWs [63]. Li et al. [64] accomplished an ultimate efficiency of 30.5% by tuning silicon nanowire parameters. The NWAs with random orientation, length, diameter, and position have been experimentally investigated in 2008 [65]. It has been shown that reflection or backscattering was detected with slight effects on the absorption. The optical properties of vertically aligned silicon NWAs with three types of structural randomness, i.e., random position, diameters, and lengths, were numerically investigated [66]. The NWAs with random position displayed slight absorption enhancement, while those with random diameter or length exhibited a significant absorption enhancement. Therefore, the structural randomness in vertical nanowire arrays can further enhance the optical absorption compared to ordered nanowire arrays. The substantial reflectance and absorption of slanting silicon NWAs attracted attention due to their established applications in SCs [67]. The slanting NWAs achieve a significant suppression of light reflection and an enhancement of light-harvesting ability than the conventional vertical structure. The slanted NWAs offer an ultimate efficiency of 33.45%, which exceeds the 30.5% of optimum vertical SiNWs [67]. Wanget al. [68] also reported an ultimate efficiency of 29.1% by using elliptical SiNWAs. On top of that, an ultimate efficiency of 39.3% is achieved using SiNWs arranged in a decagonal lattice [28]. Additionally, periodic vertical cone arrays form a promising family of structures that are currently under examination for PV technology. Wang et al. proved that the light absorption can be considerably enhanced by using nanocones [69, 70]. In addition, Ko et al. [71] demonstrated that an ultimate efficiency of 28.9% can be obtained by decreasing the cone bottom diameter to 20 nm. Further, the SiNWs funnel shape achieved an ultimate efficiency of 41.8% [29].
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4. Simulation methodology and numerical results
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4.1. Plasmonic funnel SiNWs
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The optical simulation of the suggested designs is carried out using 3D finite-difference time-domain (FDTD) method via Lumerical FDTD solution software package [72]. The FDTD method is widely used in solar cell applications due to its ability to make the simulation physically realistic through using the multi-coefficient material model. Moreover, the FDTD has the capacity to simulate broadband frequency ranges in a single simulation run. In this study, the 3D FDTD method is employed for investigating the optical properties of the SiNWs over the main region of the solar spectrum [72]. Figure 1(a) shows the utilized computational domain for the proposed plasmonic funnel-shaped SiNW unit cell in x-z plane. However, Figure 1(b) illustrates the x-y view of the suggested design. The top and bottom of the unit cell are surrounded by perfectly matched layers (PML) boundary conditions, while the unit cell is surrounded by periodic boundary conditions (BCs) along x and y directions to simulate periodic square SiNW array. The width and length of the unit cell are equal to 500 nm, while the height is taken as 4000 nm. In order to achieve high accuracy, fine meshing of Δx = Δy = Δz = 5 nm is used, which is less than 1/60 of the shortest wavelength. The proposed plasmonic design is specifically illuminated from the top by a plane wave ranging from 300 to 1100 nm, which covers the main part of the solar spectrum. The incident wave is normal to the x-y plane with the electric field polarized along the x-axis as shown in Figure 1(a). In this study, we only consider lightly doped silicon material. At frequencies above the bandgap, the difference in the optical constants between lightly doped and intrinsic silicon is negligible, which gives us the convenience of using the same optical constants for both p and n regions of the core-shell structure in silicon NW SC [59]. The refractive indices of the SiNWs are taken from experimentally measured optical constants from Ref. [73]. The plasmonic funnel SiNW design shown in Figure 1 consists of silicon cylinder of height h1 and a cone of height h2. The total thickness is equal to h1+h2 which is fixed to 2.33 μm that is comparable to the thickness of thin-film solar cell. The Si cylinder has a diameter d1 with a gold core of diameter dg, while the cone has upper and lower base diameters of d2 and d3, respectively. In this investigation, the NWs are arranged in a square lattice with a periodicity of Ʌ = 500 nm.
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Figure 1.
The computational domain of the plasmonic funnel SiNW unit cell in the (a) x-z plane and (b) x-y plane.
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The amount of the total absorbed power by the suggested design can be calculated as a function of the wavelength λ using the total reflection R (λ) and total transmission T (λ) according to the following relation:
where Ag(λ) is the absorbed power by the plasmonic material. The wavelength-dependent reflection and transmission are calculated by using two frequency domain monitors (M1) and (M2), placed above and below the unit cell, respectively, as shown in Figure 1(a). In order to have a convergent absorption, the source and reflection monitors are placed above the SiNWs at a distance 400 and 600 nm, respectively. However, the transmission monitor is placed below the structure by 300 nm. The ultimate efficiency (ƞ) defined as a figure of merit is used to evaluate the absorption capability of the proposed structures for solar cell applications. The ultimate efficiency is calculated from the following equation [4, 8]:
where λ is the wavelength of the incident light, Eg is the bandgap wavelength of the Si, and Fs(λ) is the photon flux density in the ASTM AM 1.5 solar spectrum [74]. In this study, λg is taken as 1100 nm, corresponding to the energy gap of the silicon material. The short-circuit current density (Jsc) is related to the ultimate efficiency by assuming perfect carrier collection efficiency, i.e., each photon absorbed with energy higher than the bandgap produces one electron-hole pair, and all generated carriers are collected to produce current without recombination losses [28, 29]. The short-circuit current density Jsc of the proposed design can be expressed as [29]
where KB (ev/K) is the Boltzmann constant, Tc is the ambient temperature of the solar cell temperature that is assumed to be equal to the ambient temperature (i.e., 300 K), and J0 is the dark saturation current density. The semiempirical expression for the dark saturation current density is given by [75]:
where Iin is the incident power density at AM 1.5 and is equal to 900.14 w/m2 [76].
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Figure 2(a) depicts the absorption spectra of the cylindrical, conical, and proposed plasmonic funnel NWs versus the wavelength. It should be noted that the absorption of the suggested plasmonic design α(λ) shown in this figure is due to the Si only. In this study, d1 = 300 nm, d2 = 400 nm, dg = 120 nm, d3 = 500 nm, h1 = 500 nm, and h2 = 1830 nm. Further, the studied three shapes have the same total height of 2330 nm. It is revealed from this figure that the plasmonic funnel shape shows superior absorption than conical and cylindrical counterparts over the entire wavelength band. Figure 2(b) shows the ultimate efficiency and short-circuit current density of the investigated NWs. The ultimate efficiencies of these structures are equal to 27, 30.2, and 36.9%, respectively. Therefore, it may be noted that the plasmonic funnel-shaped NWs offer an overall enhancement of 36.7 and 22.2% over the cylindrical and conical counterparts. Further, the funnel-shaped design has short-circuit current density of 30.2 mA/cm2 which is greater than 24.5 and 22.12 mA/cm2 of the conical and cylindrical designs. The enhancement in the ultimate efficiency and hence short-circuit current density apparently can be attributed to the combination between the modes supported by the upper cylinder and the lower tapered cone along with the plasmonic modes generated by the gold core. Additionally, the proposed design offers continuous reflections between the SiNWs until the incident angle becomes smaller than the critical angle resulting in high light trapping and broadband absorption. Furthermore, the absorption enhancement can be also explained from the waveguide modal dispersion of the NWs [29]. The leaky mode resonance relies on the NW diameter. Therefore, the use of plasmonic funnel-shaped NW with multiple diameters will increase the number of leaky mode resonances. The cylindrical part with small diameter d1 can absorb short wavelength spectrum. However, the long wavelength spectrum is absorbed by the conical part with upper and lower base diameters d2 and d3, respectively. Additionally, the gold core generates plasmonic modes which play an important role for the broadband absorption.
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Figure 2.
(a) Absorption spectra and (b) ultimate efficiency and short-circuit current density of the cylindrical, conical, and plasmonic funnel NWs.
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To further confirm the underlying mechanism of the absorption enhancement, the absorbed field profiles inside the cylindrical, conical, and plasmonic funnel shapes have been presented in Figure 3(a)–(c), respectively in x-z plane at λ = 688 nm. It is reveled from these figures that the incident light has more penetration and confinement through the proposed funnel shape with plasmonic core than the conventional conical and cylindrical Si structures. Therefore, the absorption and consequently the ultimate efficiency are enhanced.
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Figure 3.
Absorbed field profiles of the (a) cylindrical, (b) conical, and (c) plasmonic funnel SiNWs in x-z plane at λ = 688 nm.
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In order to ensure that the absorption enhancement of the suggested design is due to the enhanced light trapping in the Si material, the absorption through the plasmonic core and the surrounding Si material are calculated and shown in Figure 4. The absorption of the Si NW funnel design [29] without plasmonic material is also plotted in Figure 4. It may be noted from this figure that the absorption through the plasmonic metal is small. Further, the plasmonic funnel design has better absorption than that of the Si funnel design [29]. The simulation results also reveal that the plasmonic funnel-shaped NWs achieve an ultimate efficiency of 36.9% which is higher than that of the Si funnel counterpart of ultimate efficiency of 33.5%. The metallic core supports plasmonic modes which increase the light confinement through the silicon NWs. Therefore, the hybrid funnel nanowires improve the light trapping and hence the ultimate efficiency.
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Figure 4.
Absorption spectra through the Si funnel [29], metallic layer, and plasmonic funnel NWs.
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To understand the electrical enhancement in the reported design, the ultimate efficiency (ƞ), short-circuit current density (Jsc), open-circuit voltage (Voc), fill factor (FF), and power conversion efficiency (PCE) are calculated and shown in Table 1. In this table, the calculated values of ƞ, Jsc, Voc, FF, and PCE of the cylindrical [66], conical [70], Si funnel [29], and proposed plasmonic funnel SiNWs are listed in detail. It may be noted from this table that the Voc and PCE of the plasmonic funnel shape are higher than that reported in Refs. [29, 66, 70]. Additionally, the PCE of the reported design is higher than that of the cylindrical SiNWs [66] and Si funnel [29] counterparts by 9.95 and 38.2%, respectively. This enhancement is attributed to the better absorption in the plasmonic funnel design which is responsible for enhancing the conversion efficiency. Therefore, the suggested design has a better conversion from optical to electrical power than the previously published design [29, 66, 70].
The ultimate efficiency (ƞ), short-circuit current density (Jsc), open-circuit voltage (Voc), fill factor (FF), and power conversion efficiency (PCE) of different structures.
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In order to enhance the absorption capabilities of the proposed funnel-shaped SiNWs with plasmonic core, the effects of the structure geometrical parameters are investigated. Figure 5(a) shows the effect of the top cylindrical diameter (d1) on the ultimate efficiency and short-circuit current density for the suggested structure. In this investigation, the other parameters Ʌ, h1, d2, d3, and h2 are kept constants at 500, 500, 400, 500, and 1830 nm, respectively. As the diameter (d1) increases from 60 to 180 nm, the absorption through the SiNWs and hence the ultimate efficiency increase. The ultimate efficiency and short-circuit current density have maximum values of 36.9% and 30.2 mA/cm2 at d1 = 180 nm, respectively. As d1 is further increased, the reflection will be increased, and hence the absorption and ultimate efficiency are decreased. As a result, the short-circuit current density decreases from 30.2 to 24.9 mA/cm2 by increasing d1 from 180 to 420 nm, respectively. Therefore, the tuned d1 = 180 nm will be used for the subsequent simulations. Next, the effect of the cylinder height h1 of the suggested design is also investigated. As h1 increases from 0 to 200 nm, the ultimate efficiency and short-circuit current density are increased. Therefore, it is concluded that the funnel shape has a better absorption capability than the conical design at h1 = 0. It may be also seen from Figure 5(b) that the cylinder height has a slight effect on the short-circuit current density of the proposed design when h1 ≥ 300 nm. This is due to the fixed cylindrical diameter d1 which faces the incident light. Therefore, the amount of trapped light inside the proposed design is slightly changed with h1 variation. The maximum ultimate efficiency of 36.9% is obtained at h1 = 200 nm.
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Figure 5.
Variation of the short-circuit current density and ultimate efficiency with the (a) cylinder diameter d1 and (b) cylinder height h1.
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Figure 6(a) displays the relation between the short-circuit current density and ultimate efficiency against the cone upper base diameter (d2) for the suggested design. In this study, the tuned geometrical parameters of the plasmonic design are taken as d1 = 180 nm, d3 = 500, and h1 = 200 nm. As d2 increases from 160 to 360 nm, the active material increases, and hence higher order optical modes are generated. Therefore, the ultimate efficiency is increased from 33.3 to 36.96%. The tapered shape of the plasmonic design with d2 = 360 nm has maximum ultimate efficiency of 36.9% and Jsc of 30.2 mA/cm2. The effect of the cone base diameter (d3) is also studied and shown in Figure 6(b). It is revealed from Figure 6(b) that as the cone base diameter (d3) of the plasmonic funnel design increases, the active material will be increased which decreases the transmission through the proposed design. Therefore, the absorption and ultimate efficiency are increased. An optimum ultimate efficiency of 36.9% and Jsc of 30.2 mA/cm2 are obtained at 500 nm cone base diameter.
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Figure 6.
Variation of the short-circuit current density and ultimate efficiency with the cone (a) top diameter d2 and (b) bottom diameter d3.
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From the practical point of view, the absorption spectra of the funnel SiNWs with plasmonic core and cylindrical SiNWs decorated on 2 μm Si substrate and Ag back reflector of thickness 200 nm are calculated and shown in Figure 7. Compared with the cylindrical SiNWs of ultimate efficiency = 30.6%, the proposed plasmonic design shows an ultimate efficiency of 44% with an enhancements of 43.3% [7]. Additionally, short-circuit current densities of 36 mA/cm2 and 25.1 mA/cm2 are achieved by the plasmonic funnel design and cylindrical SiNWs, respectively. This is due to the coupling between the nanowire arrays and underlying substrate which leads to a strong absorption enhancement in the lower energy region as well as good light-trapping improvement in the longer wavelength as displayed in Figure 7(a).
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Figure 7.
(a) Absorption spectra and (b) ultimate efficiency and short-circuit current density of the proposed plasmonic funnel SiNWs and cylindrical SiNWs with Si substrate and Ag back reflector.
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4.2. SiNWs decorated by plasmonic diamond
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In order to test the effect of plasmonic material over the NW structure, the cylindrical SiNWs decorated by Ag diamond is studied. Figure 8(a) illustrates the computational domain of the proposed plasmonic unit cell in the x-z plane, while Figure 8(b) shows the top view of the suggested design. The positive and negative z directions of the unit cell are surrounded by PML boundary conditions, while the unit cell is surrounded by periodic BCs along x and y directions to simulate periodic square SiNW array. The reported design of the silicon NWs decorated by Ag diamond is specifically illuminated from the top by a plane wave ranging from λ = 300 to 1100 nm, which covers the main part of the solar spectrum. Two frequency-domain field monitors M1 and M2 are placed at the top and bottom of the cell, respectively, to calculate the absorption in the SiNW which is defined by ASi = M1−M2. In this study, the height and the diameter of the Si nanowire are equal to 500 and 400 nm, respectively. Furthermore, the major and minor axes of the Ag diamond shape are taken as x and y, respectively. In this investigation, x = y = 320 nm, while the diamond thickness h is equal to 80 nm.
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Figure 8.
Computational domain of the proposed cylindrical SiNWs decorated by Ag diamond in the (a) x-z plane and (b) x-y plane.
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Figure 9(a) shows the absorption spectra of the cylindrical SiNWs and cylindrical SiNWs decorated by Ag diamond. It is revealed from this figure that the cylindrical SiNWs with Ag diamond show superior absorption than cylindrical counterpart over the entire wavelength band. Additionally, Figure 9(b) shows the ultimate efficiency and short-circuit current density of the studied designs. The ultimate efficiency of the plasmonic design is equal to 21.1% which is greater than the conventional cylindrical design of ultimate efficiency = 16%. Therefore, the cylindrical-shaped design with Ag diamond offers an overall enhancement of 31.9% over the cylindrical SiNWs counterpart. Further, the plasmonic design has a short-circuit current density of 17.3 mA/cm2 which is greater than that of the conventional cylindrical design of 13.1 mA/cm2. The enhancement in the ultimate efficiency and hence short-circuit current density can be attributed to the generated plasmonic mode by the upper Ag diamond which is responsible for improving the absorption through the SiNWs.
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Figure 9.
(a) Absorption spectra and (b) ultimate efficiency and short-circuit current density of cylindrical SiNWs and cylindrical SiNWs decorated by Ag diamond.
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Table 2 shows the calculated ƞ, Jsc, Voc, FF, and PCE of the cylindrical SiNWs and cylindrical SiNWs decorated by Ag diamond. It is found that the electrical parameters are also enhanced due to the existing plasmonic materials above the active layer. Additionally, the Voc is increased from 640 to 647 mV, and the PCE is also improved from 7.9 to 10.6 with 34.1% enhancement over the cylindrical SiNW counterpart.
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Structure
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ƞ
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Jsc (mA/cm2)
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Voc (v)
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FF
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PCE
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Cylindrical SiNWs
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16%
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13.1
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0.64
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0.835
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7.9
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Cylindrical SiNWs decorated with Ag diamond
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21.1%
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17.3
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0.647
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0.8369
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10.6
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Table 2.
The calculated values of ƞ, Jsc, Voc, FF, and PCE for cylindrical SiNWs and cylindrical SiNWs decorated by Ag diamond.
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To further explore the underlying mechanism of the absorption enhancement in the proposed design, the field profiles in x-y and x-z planes at λ = 616 nm are shown in Figure 10. As shown from Figure 10(b) and (d), the field penetration through the proposed design is greater than that of the conventional SiNWs. This is due to the plasmonic particles that have increased the light confinement around the plasmonic material and, thus, allowed more waveguide modes to couple into the SiNWs which is responsible for the absorption enhancement. Additionally, the figures show high field intensity penetration inside the reported SiNWs which is defined by the field hot spots in the figures.
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Figure 10.
Absorbed field profiles for cylindrical SiNWs without and with Ag diamond particle in the (a, b) x-y plane and in the (c, d) x-z plane at λ = 616 nm.
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In order to further enhance the absorption capabilities of the proposed SiNWs decorated by Ag diamond, the effects of the structure geometrical parameters are studied. Figure 11(a) shows the impact of the diamond minor axis (x) on the ultimate efficiency and short-circuit current density. In this investigation, the other parameters Ʌ, h1, and y are kept constant at 500, 500, 400, and 320 nm, respectively. It is concluded that as the minor axis (x) increases to 280 nm, the absorption and hence the ultimate efficiency and short-circuit current density also increase. A maximum ultimate efficiency and short-circuit current density of 21.4% and 17.5 mA/cm2, receptively, are obtained at x = 280 nm. If the minor axis is further increased, the ultimate efficiency and short-circuit current density will be decreased. Therefore, the tuned value of 280 nm for the minor axis will be used for the subsequent simulations. Next, the effect of the major axis y of the Ag diamond is also investigated and shown in Figure 11(b). It may be seen from this figure that the ultimate efficiency and short-circuit current density have maximum values of 21.9% and 17.1% at y = 360 nm, respectively. If the major axis y is further increased, the reflection will be increased which decreases the absorption and ultimate efficiency as shown in Figure 11(b).
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Figure 11.
Variation of the short-circuit current density and ultimate efficiency of the conventional SiNWs and SiNWs decorated by Ag diamond with the (a) minor axis x and (b) major axis y.
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Next, the effect of the diamond thickness (h) on the ultimate efficiency and short-circuit density is also investigated and shown in Figure 12(a). It is revealed from this figure that the diamond height has a slight effect on the absorption and hence short-circuit current density and ultimate efficiency. A maximum ultimate and short-circuit current density of 22.5% and 18.4 mA/cm2, respectively, occur at h = 120 nm. Figure 12(b) shows the variation of ultimate efficiency and short-circuit density with the periodicity of the NW, while the other parameters are kept constant at h = 120 nm, h1 = 500 nm, x = 280 nm, and y = 360 nm. As the periodicity decreases, the ultimate efficiency and short-circuit current density increase. The maximum ultimate efficiency of 25.7% is obtained at periodicity of 400 nm which is higher than that of the conventional SiNWs without plasmonic material by 63% at the same periodicity. This enhancement is due to the change of the periodicity which leads to a change in the filling ratio (at fixed diamond size) which in turn influences the generated localized surface plasmon resonance.
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Figure 12.
Variation of the short-circuit current density and ultimate efficiency for the conventional SiNWs and SiNWs decorated by Ag diamond with the (a) diamond height and (b) periodicity.
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5. Conclusion
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In this chapter, the possibility of improving the light trapping through the SiNWs by using plasmonic materials is discussed and studied. In this regard, the effects of using plasmonic materials inside or above the SiNWs are introduced. In these investigations, two novel designs of plasmonic SiNW solar cells are presented and analyzed using the 3D FDTD method. A full study for optical and analytical electrical efficiencies has been carried out. The ultimate efficiency and power conversion efficiency have been calculated to quantify the overall performance of the proposed designs. Further, the designed geometrical parameters are tuned to maximize the optical and electrical efficiencies. The obtained ultimate efficiency and power conversion efficiency of the plasmonic funnel design are equal to 44 and 18.9% with an enhancement of 43.3% over its cylindrical NW counterpart. Additionally, the cylindrical SiNWs decorated by Ag diamond offer an ultimate efficiency and short-circuit current density of 25.7% and 21.03 mA/cm2, respectively, with an improvement of 63% over the conventional SiNWs. The proposed plasmonic solar cell designs could be very crucial to present low-cost, high-absorption efficiency, and shape-controlled nanopillars for energy-harvesting applications.
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\n\n',keywords:"light trapping, plasmonic solar cells, nanowires, finite-difference time-domain",chapterPDFUrl:"https://cdn.intechopen.com/pdfs/54251.pdf",chapterXML:"https://mts.intechopen.com/source/xml/54251.xml",downloadPdfUrl:"/chapter/pdf-download/54251",previewPdfUrl:"/chapter/pdf-preview/54251",totalDownloads:1482,totalViews:201,totalCrossrefCites:3,totalDimensionsCites:4,totalAltmetricsMentions:0,impactScore:1,impactScorePercentile:67,impactScoreQuartile:3,hasAltmetrics:0,dateSubmitted:"September 27th 2016",dateReviewed:"January 25th 2017",datePrePublished:null,datePublished:"July 5th 2017",dateFinished:"February 28th 2017",readingETA:"0",abstract:"Light trapping is crucial for low-cost and highly efficient nanowire (NW) solar cells (SCs). In order to increase the light absorption through the NWSCs, plasmonic materials can be incorporated inside or above the NW design. In this regard, two novel designs of plasmonic NWSCs are reported and analyzed using 3D finite difference time domain method. The geometrical parameters of the reported designs are studied to improve their electrical and optical efficiencies. The ultimate and power conversion efficiencies (PCE) are used to quantify the conversion efficiency of the light into electricity. The first design relies on funnel shaped SiNWs with plasmonic core while the cylindrical NWs of the second design are decorated by Ag diamond shaped. The calculated ultimate efficiency and PCE of the plasmonic funnel design are equal to 44% and 18.9%, respectively with an enhancement of 43.3 % over its cylindrical NWs counterpart. This enhancement can be explained by the coupling between the three optical modes, supported by the upper cylinder, lower cone and plasmonic material. Moreover, the cylindrical SiNWs decorated by Ag diamond offer an ultimate efficiency and short-circuit current density of 25.7%, and 21.03 mA∕cm2, respectively with an improvement of 63% over the conventional cylindrical SiNWs.",reviewType:"peer-reviewed",bibtexUrl:"/chapter/bibtex/54251",risUrl:"/chapter/ris/54251",book:{id:"5747",slug:"nanowires-new-insights"},signatures:"Mohamed Hussein, Mohamed Farhat Othman Hameed and Salah S.\nA. Obayya",authors:[{id:"195512",title:"Dr.",name:"Mohamed",middleName:null,surname:"Hameed",fullName:"Mohamed Hameed",slug:"mohamed-hameed",email:"mfarahat@zewailcity.edu.eg",position:null,profilePictureURL:"//cdnintech.com/web/frontend/www/assets/author.svg",institution:{name:"Zewail City of Science and Technology",institutionURL:null,country:{name:"Egypt"}}},{id:"195741",title:"Prof.",name:"Salah",middleName:null,surname:"Obayya",fullName:"Salah Obayya",slug:"salah-obayya",email:"sobayya@zewailcity.edu.eg",position:null,profilePictureURL:"//cdnintech.com/web/frontend/www/assets/author.svg",institution:{name:"Zewail City of Science and Technology",institutionURL:null,country:{name:"Egypt"}}},{id:"195747",title:"Dr.",name:"Mohamed",middleName:null,surname:"Hussein",fullName:"Mohamed Hussein",slug:"mohamed-hussein",email:"mhussein@zewailcity.edu.eg",position:null,profilePictureURL:"//cdnintech.com/web/frontend/www/assets/author.svg",institution:null}],sections:[{id:"sec_1",title:"1. Introduction",level:"1"},{id:"sec_2",title:"2. Review of plasmonic light trapping for solar cell applications",level:"1"},{id:"sec_3",title:"3. State of the art of semiconductor nanowire solar cells",level:"1"},{id:"sec_4",title:"4. Simulation methodology and numerical results",level:"1"},{id:"sec_4_2",title:"4.1. Plasmonic funnel SiNWs",level:"2"},{id:"sec_5_2",title:"4.2. SiNWs decorated by plasmonic diamond",level:"2"},{id:"sec_7",title:"5. Conclusion",level:"1"}],chapterReferences:[{id:"B1",body:'G. Sadashivappa, and N. Sharvari, "Nanoantenna-a review," International Journal of Renewable Energy Technology Research, Vol. 4, pp. 1-9, 2015.\n'},{id:"B2",body:'M. A. Khan, P. Sichanugrist, S. Kato, and Y. Ishikawa, "Theoretical investigation about the optical characterization of cone-shaped pin-Si nanowire for top cell application," Energy Science & Engineering, Vol. 4, pp. 383-393, 2016.\n'},{id:"B3",body:'L. Mescia, and A. 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Ayon, "Nanostructured thin film silicon solar cells efficiency improvement using gold nanoparticles," Physica Status Solidi (a), Vol. 209, pp. 1475-1480, 2012.\n'}],footnotes:[],contributors:[{corresp:null,contributorFullName:"Mohamed Hussein",address:null,affiliation:'
Centre of Photonics and Smart Materials, Zewail City of Science and Technology, Giza, Egypt
Faculty of Science, Ain Shams University, Cairo, Egypt
Centre of Photonics and Smart Materials, Zewail City of Science and Technology, Giza, Egypt
Faculty of Engineering, Mansoura University, Mansoura, Egypt
'},{corresp:"yes",contributorFullName:"Salah S. A. Obayya",address:"sobayya@zewailcity.edu.eg",affiliation:'
Centre of Photonics and Smart Materials, Zewail City of Science and Technology, Giza, Egypt
Faculty of Engineering, Mansoura University, Mansoura, Egypt
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1. Introduction
The CE has emerged as an alternative model to the prevailing “take–make–waste” approach to production and consumption in contemporary economic systems, which is an unsustainable path leading to resource depletion and severe environmental problems, such as climate change, air and water pollution, and biodiversity loss [1, 2]. In the linear economy, resources are extracted from nature, transformed into products that are then consumed within the human economic system until they are finally disposed of as waste back to nature [2]. By contrast, the CE model fosters the responsible and cyclical use of resources to maintain their value within the economy, while minimizing pressures on the environment [3, 4]. It operates at three system levels; the micro level (products, consumers, companies), the meso level (eco-industrial parks), and the macro level (cities, regions, countries), with the ultimate aim to achieve sustainable development [5].
The transition toward the CE requires, among others, the development of new technologies [6, 7]. An emerging technology that could promote the operationalization of the CE model is biochar systems. These are multifunctional systems that can produce bioenergy and biochar through the thermochemical conversion of different types of biomass feedstocks (e.g., wood, agricultural residues, and wastewater sludge) in an oxygen-limited environment [8, 9]. Biochar is a porous solid carbonaceous material with versatile physicochemical properties that has a multitude of applications, including its use for amendment of agricultural soils, water purification and wastewater treatment, concrete and steel production, and remediation of contaminated soils [10]. The application of biochar to soils is probably its most prominent application, as, apart from improving soil quality, it sequesters atmospheric CO2, thereby contributing to climate change mitigation [11]. The multi-functionality of the biochar systems offers opportunities for developing integrated systems for valorizing different waste streams [12, 13], which is vital for the implementation of the CE model.
In this chapter, biochar systems, for valorizing wood waste and contaminated soils, are presented, and the potential role of these systems in the CE is explored. The rest of the chapter is structured as follows: Section 2 provides an overview of the CE concept and its principles to set the context of the study; Section 3 provides a brief description of different biochar systems; Section 4 focuses on biochar systems for valorizing wood waste and contaminated soils, and describes a case study, where the environmental performance of such systems is assessed; Section 5. discusses the role of biochar systems in the CE; and Section 6 summarizes the conclusion of the study.
2. The circular economy
The concept of CE originates in different schools of thought, including industrial ecology, general systems theory, and ecological and environmental economics [14]. Its conceptual roots can be traced back to notions put forth decades ago, such as the “Spaceship economy,” [15] the irreversible degradation of natural resources when used by economic activities [16], the economy of loops [17], and the analogy between ecosystems and industrial systems [18]. The contemporary conceptualizations of CE include features from relevant concepts, including, but not limited to, the regenerative design [19], industrial symbiosis [20], “cradle to cradle” design [21], and performance economy [22].
Over the past 10–15 years, the CE has been attracting increasing attention from academia, companies, citizens, and policymakers [23]. It is regarded as a potential solution to the challenges of resource depletion and environmental degradation caused by the unsustainable linear “take–make–waste” paradigm that has dominated the contemporary economic systems [1, 2]. To address these challenges, the CE promotes system innovations that aim to maximize resource value, promote the cascading use of renewable resources and minimize waste generation to reduce negative environmental impacts and build natural, social, and economic capital [1, 24].
Overall, there is a general understanding that the CE is connected to sustainability and sustainable development. Geissdoerfer et al. [23] identified three different general types of relationships between the CE and sustainability; 1) conditional, where the CE is seen as one of the main conditions to attain sustainability, 2) beneficial, where the CE is regarded as beneficial in regard to sustainability, and 3) trade–off, where the CE is seen as a concept that can generate both benefits and costs in terms of sustainability. Having this study as a point of departure, Suárez-Eiroa et al. [25] suggested that there is a close relationship between the CE and sustainability and that the CE is at least beneficial for achieving sustainable development, as it can address some of the causes of current sustainability-related problems. The relevance of CE for achieving sustainable development was also confirmed by Schroeder et al. [26], who demonstrated that CE practices can contribute to achieve a significant number of Sustainable Development Goal targets. Despite these perspectives, the exact relationship between the CE and sustainability and sustainable development remains still unclear and debatable [27, 28].
Moreover, there is a lack of consensus in defining the CE. Kirchherr et al. [5] provided evidence of the heterogeneity in the definitions of the CE, by identifying 114 different definitions within academic articles, policy documents, and reports. The scholars also found that only a few of the identified definitions show explicit linkages between the CE concept and sustainable development. They also highlighted that the social dimension of sustainable development is highly overlooked, compared to the environmental and economic dimensions.
There is also a lack of consensus in conceptualizing the CE principles. A principle is defined “as a basic idea or rule that explains or controls how something happens or works.” [29] Reike et al. [30] analyzed 69 academic articles and identified that divergent approaches in conceptualizing the CE principles dominate the literature. More specifically, the scholars focused on the R-principles of the CE and found varying numbers of these R-imperatives, ranging from 3Rs (Reduce–Reuse–Recycle) through 5Rs (Reduce–Reuse–Remanufacture–Recycle–Recover) to the more nuanced 10Rs (Refuse, Rethink, Reduce, Reuse, Repair, Refurbish, Remanufacture, Repurpose, Recycle, Recover). In addition, they revealed that different authors ascribe different meanings in their conceptualizations of the R-principles and that some authors apply a clear hierarchy when defining them, while others are more vague and suggestive.
Apart from the R-principles, alternative CE principles have also been proposed in the literature. Suárez-Eiroa et al. [25] used the term operational principles to define theoretical strategies that explain how CE operates. They proposed seven operational principles: (1) Adjusting inputs to the system to regeneration rates, (2) Adjusting outputs from the system to absorption rates, (3) Closing the system, 4) Maintaining the value of resources within the system, (5) Reducing the system’s size, (6) Designing for CE, and (7) Educating for CE. Moreover, Bocken et al. [31] introduced the three principles: (1) Narrowing loops, (2) Slowing loops, and (3) Closing loops, to guide business strategists and designers in the transition from a linear to a CE. In a recent study, Velenturf and Purnell [28] proposed 10 principles for the design, implementation, and evaluation of sustainable CE. These are: 1) Beneficial reciprocal flows of resources between nature and society, 2) Reduce and decouple resource use, 3) Design for circularity, 4) Circular business models to integrate multi-dimensional value, 5) Transform consumption, 6) Citizen participation in sustainable transitions, 7) Coordinated participatory and multi-level change, 8) Mobilize diversity to develop a plurality of circular economy solutions, 9) Political economy for multi-dimensional prosperity, and 10) Whole system assessment.
According to Kalmykova et al. [32], the divergent approaches in defining and conceptualizing the CE can hamper the advancement of the CE. However, the CE is an evolving and dynamic field that involves different stakeholders with different interests and priorities and thus the adoption of a single unifying definition is perhaps impossible and undesirable, as it would disregard some interests and fail to capture recent developments [33]. This, of course, is not a reason to stop striving for greater conceptual clarity on the CE. In this context, it is important to define explicitly the concept and its principles early in a study.
In this chapter, we embrace the definition proposed by Kirchherr et al.6(p229):
“A circular economy describes an economic system that replaces the ‘end-of-life’ concept with reducing, alternatively reusing, recycling and recovering materials in production/distribution and consumption processes. It operates at the micro level (products, companies, consumers), meso level (eco-industrial parks) and macro level (city, region, nation and beyond), with the aim to accomplish sustainable development, thus simultaneously creating environmental quality, economic prosperity and social equity, to the benefit of current and future generations. It is enabled by novel business models and responsible consumers.”
We adopt this definition as a basis for exploring the role of biochar systems in the CE, as we consider it as one of the most comprehensive and insightful definitions of the CE in the literature. It highlights that the transition toward the CE requires the implementation of the model at three system levels (micro, meso and macro level). Moreover, it clearly relates the CE with the three dimensions of sustainable development (social, economic, environmental) and indicates that the CE has a key role as a means to achieve sustainable development. It is also important that it has an explicit reference to the 4Rs (Reduce–Reuse–Recycle–Recover) principle of the CE.
3. Biochar systems
Biochar is the porous solid carbonaceous material derived from the thermochemical conversion of biomass in an oxygen-limited environment [9]. It can be produced from various biomass feedstocks, including wood, wood waste, agricultural wastes (e.g., straw, rice husk), wastewater sludge, and food waste [8]. The most commonly used thermochemical conversion process for biochar production is pyrolysis, though other processes, such as gasification, torrefaction, and hydrothermal conversion, can also be used [34]. Pyrolysis is the thermochemical decomposition of biomass into condensable liquids, non-condensable gases, and biochar in the absence of oxygen [35]. The distribution of these end products and their properties depends on the process conditions (i.e., temperature, heating rate, and residence time) and the type of biomass feedstock [36]. Based on the process conditions, pyrolysis is classified as slow, fast, rapid, or flash, with slow pyrolysis being more appropriate for a biochar targeted product [37].
Biochar systems using pyrolysis can be deployed at different scales (small-, medium- and large–scale) and can perform multiple functions, as they can be used for biowaste treatment and bioenergy generation, along with biochar production and use [38]. Bioenergy can be produced through the combustion of the pyrolytic gas and oil products, known as syngas and bio-oil (or bio-tar), respectively. Moreover, bioenergy can be produced by using the produced biochar as solid fuel [9]. In addition to bioenergy production, biochar can be used for a variety of applications, mainly because of its versatile physicochemical properties [8, 10].
The most prominent application of biochar is probably its application to soils. Biochar can be used as a soil amendment for agricultural soils, as it can improve their physicochemical properties and structure, increasing soil fertility and crop productivity [34, 37, 39]. At the same time, the production of biochar and its incorporation into soils sequesters carbon. More specifically, the thermo-chemical conversion of biomass into biochar increases the recalcitrance of carbon, enhancing its resistance to chemical and biological degradation [34]. Thus, when biochar is incorporated into the soil, the return of biomass carbon to the atmosphere as CO2 is impeded [11, 40]. In this way, biochar can act as a carbon sink, thereby contributing to climate change mitigation, and for that reason, the production of biochar with its incorporation in soils has been recognized as a carbon dioxide–removal (CDR) technology [41].
Besides soil amendment and carbon sequestration, biochar has numerous applications across various sectors. Biochar can be used as an additive for production of cement [13], cement mortar [42] and concrete [43], adsorbent for wastewater treatment and water purification, coke replacement in metallurgical processes, raw material for the manufacture of activated carbon, and novel specialty materials for electronic devices, such as carbon nanotubes and nanosheets [10], and platform material for energy storage and conversion, including hydrogen storage and production, fuel cells and lithium/sodium-ion batteries [44]. It can also be used as a feed supplement for poultry or ruminants to improve the health and productivity of the animals, reduce odors and nutrient losses from the manure, and serve, in combination with the manure, as a slow-release fertilizer [45]. Moreover, the sorption properties of biochar have sparked an interest in the use of biochar for remediating soils contaminated with organic and/or inorganic pollutants [9, 46, 47].
4. Biochar systems for synergistic valorization of wood waste and contaminated soil
Contamination of soils from human activities is a widespread environmental problem around the globe [47]. Only in EU-28, it has been estimated that 2.8 million potentially contaminated sites exist [48]. A widely applied technique for remediating contaminated sites worldwide is the “dig and dump” technique, where the contaminated soil is excavated and landfilled, and the excavated site is usually backfilled with virgin material [49]. However, this technique is not sustainable because of high-energy requirements, scarcity of landfill space, high costs, and decreasing availability of natural resources for backfilling [49]. Hence, various alternative techniques are being explored, including the application of biochar to contaminated soils.
Biochar exhibits good sorption properties for organic compounds, such as polycyclic aromatic hydrocarbons (PAHs), and inorganic substances, such as heavy metals, because of their large surface area, porous structure, and cation-exchange capacity [9, 46, 47]. Therefore, the mixing of biochar with soils contaminated with these substances is considered a potential option for stabilizing the contaminants. The efficacy of this technique depends on the properties of the utilized biochar and the type and concentration of contaminants in the soil [50]. For example, the efficacy of biochar for sorption of PAHs and heavy metals, such as Cd, Zn, Pb, and Cu, have been reported as good [51, 52], while for negatively charged metal(loid)s, such as As and Mo, the sorption capacity of biochar is low [47, 50]. Furthermore, the interplay between positive and negative effects has been reported for contaminated soils with multiple contaminants [46]. This indicates that the utilization of biochar for remediation of contaminated soils may not be suitable for all types of contaminated soil and thus case–specific assessments are generally required.
To explore the potential of using biochar for remediating contaminated soils with PAHs, heavy metals and metal(loid)s in Sweden, the research project “Biochar-RE: Source” was carried out between 2018 and 2020 [53]. The purpose of the project was to test and assess a new technique for remediation of contaminated soils excavated in urban areas, which is based on biochar made from urban wood waste. As part of the research, different biochar systems that use pyrolysis were designed and their environmental performance was assessed and compared to that of the “dig and dump” technique, which is the prevailing method for handling contaminated sites in Sweden [54]. The assessment of these systems is described by Papageorgiou et al. [55]. The following sections of this chapter (4.1 and 4.2) describe these systems and provide an overview of the methodological approach followed for the assessment and a summary of the results of the assessment. For more details see Papageorgiou et al. [55].
4.1 Systems description
Figure 1 depicts three different systems for the management of urban wood waste and contaminated soil. System 1 (S1) depicts how these two waste streams are currently managed in the urban area of Helsingborg in southern Sweden, which was the case study area for the research project. Systems 2 and 3 (S2 and S3) depict two alternative options for managing wood waste and contaminated soil based on biochar systems. More details for each system are provided below.
S1: “Dig and dump”. In S1, contaminated soil with PAHs and metal(loid)s is excavated from various sites in Helsingborg and the excavated sites are backfilled with virgin material (gravel). The excavated soil is transported to the local waste management (WM) facility, where it is landfilled. Moreover, garden waste from the urban area is transported to the WM facility and is sorted, via shredding and sieving, into wood waste and green waste (mostly leaves and soil). The sorted waste is then transported to an incineration facility, where it is combusted for district heating. The green waste is processed through windrow composting.
S2: Off-site remediation with biochar. In S2, the collected wood waste is first dried and processed into woodchips and then converted via pyrolysis (slow) into biochar and syngas. The syngas is combusted, and the generated heat is partly used for district heating and partly for drying the wood waste before pyrolysis. The biochar is mixed with contaminated soil (6% biochar, 94% soil, weight-to-weight), which is transported to the WM facility from excavation sites in Helsingborg. It is assumed that the excavated soil is transported for treatment to the facility due to technical or/and legislative restrictions that do not allow its mixing with biochar on-site and its direct reuse for backfilling. Instead, virgin soil (gravel) is used to backfill the excavated sites and the biochar-soil mix is reused in other applications (e.g., for noise barrier construction).
S3: On-site remediation with biochar. The main difference between S3 and S2 is that the produced biochar is transported to the excavation sites and there it is mixed with the contaminated soil (6% biochar, 94% soil). The biochar-soil mix is then reused on-site for backfilling.
Figure 1.
The three studied systems for the management of wood waste and contaminated soil.
4.2 Environmental performance
4.2.1 Methods
The environmental performance of the three above–described systems was assessed by combining three Industrial Ecology tools, that is, Material and Energy Flow Analysis (MEFA), Substance Flow Analysis (SFA), and Life Cycle Assessment (LCA).
The goal of the MEFA was to map and quantify material and energy flows in the three systems in order to provide an understanding of the functioning of the systems and create the quantitative basis for the application of the LCA. The system boundaries of the MEFA included all processes for managing the contaminated soil (e.g., excavation and mixing) and wood waste (e.g., incineration and pyrolysis) and transportation between processes. However, they did not include the composting of the green waste, as the focus of the assessment was on the sorted wood waste, and the leaching of PAHs and metal(loid)s from the landfilled contaminated soil (S1) or the reused soil (S2 & S3), as it was studied through an SFA. The time boundary of the assessment was annual. The estimation of the material and energy flows was done by combining primary data and data from the literature.
The LCA was a comparative process-based LCA and its goal was to assess the life cycle environmental impacts of the studied systems. The system boundaries of the LCA were the same as those of the MEFA. They also included upstream impacts from the supply of backfill material, downstream impacts from the disposal of wood waste incineration ash, and impacts from capital goods (e.g., machinery). The functional unit was set as “1 year of operation of the pyrolysis plant (0.8 t/h dry wood, 1250 t/year biochar).” This functional unit is equivalent to the treatment of 5,650 t wood waste for district heating and remediation of 12,240 m3 contaminated soil with biochar. To handle allocation issues and keep the functional unit constant the system expansion approach was followed. The modeling of the Life Cycle Inventory (LCI) was carried out using the LCA software Brightway2 [56] based on the Ecoinvent database (version 3.6 – cut-off) [57]. For the Life Cycle Impact Assessment (LCIA), the ILCD 2.0 impact assessment method [58] was used. From the 15 impact categories, the toxicity-related impact categories carcinogenic effects, non-carcinogenic effects, and freshwater ecotoxicity were not included, as the fate of the contaminants in the soil was investigated separately through an SFA.
The SFA was conducted to map and quantify the flows of the contaminants (PAHs and metal(loid)s) in the landfilled contaminated soil and the remediated soil. The analysis was carried out taking a life cycle perspective, as the system boundaries included flows from all the processes included in the LCA. In addition, they included leaching of the contaminants from the soils, which was excluded from the MEFA and LCA. The amounts of contaminants leaching from the soils were calculated within a 100-year timeframe, using data from leaching experiments that were performed in the context of the “Biochar-RE: Source” research project and assuming a certain degree of water infiltration in the soils.
4.2.2 Results
The main results from the application of the MEFA are summarized in Table 1. The analysis revealed that on-site remediation with biochar (S3) can deliver significant fuel (diesel and biodiesel) savings, as it involves less transportation of materials than the “dig and dump” system (S1) and off-site remediation (S2). Moreover, on-site remediation minimizes the use of virgin material (gravel) for backfilling, as the remediated soil is directly reused on-site. By contrast, in S1 and S2, virgin material is required for backfilling. In addition, the analysis indicated that the pyrolysis of wood waste can supply less heat to the district heating network than incineration and that a considerable amount of auxiliary electricity is needed for the operation of the pyrolysis plant.
Material and energy flows
S1
S2
S3
Wood waste (t)
5,650
5,650
5,650
Contaminated soil (t)
19,580
19,580
19,580
Biochar produced (t)
—
1,250
1,250
Fossil fuels (diesel) used (t)
84.1
131
5,9
Biofuels (biodiesel) used (t)
90.3
15,8
13,1
Virgin material (gravel) used (t)
19,580
19,580
—
Landfilled contaminated soil (t)
19,580
—
—
Reused remediated soil (t)
—
19,580
19,580
District heating supply (TJ)
58.2
36
36
Electricity consumed (TJ)
—
14.2
14.2
Table 1.
Main material and energy flows of the three systems.
Table 2 presents the results of the LCA for the three systems and Figure 2 shows the environmental impacts of S2 and S3, normalized to S1 (S1 = 100%), as well as the contribution of each process. Overall, biochar systems (S2 & S3) perform better than the “dig and dump” system (S1) in 10 out of 12 environmental impact categories. When comparing off-site (S2) and on-site remediation (S3), the former has lower environmental impacts in all impact categories. The main reason is that S3 entails less transportation of materials and saves virgin soil. Notably, both biochar systems have negative scores for climate change, as carbon sequestration in the biochar is 2.3 and 4.5 times higher than direct greenhouse gas emissions in S2 and S3, respectively. The biochar systems S2 and S3 had more impacts than S1 only in the impact categories Ionizing radiation and Fossils. The principal cause is the increased consumption of electricity for the operation of the pyrolysis plant, as a significant share of electricity in Sweden is from nuclear power, which is associated with these two impacts.
Impact categories
S1
S2
S3
Climate change (106 kg CO2-eq)
1.01
−2.02
−2.31
Freshwater and terrestrial acidification (103 mol H+-eq)
Life cycle environmental impacts of the three systems.
The negative scores for Climate change mean that the uptake of greenhouse gases is larger than direct emissions to the atmosphere (Data source: Papageorgiou et al. [55]).
Figure 2.
Life cycle environmental impacts of the biochar systems (S2 and S3), normalized to the “dig and dump” system (S1) (S1 = 100%) with process contributions (Data source: Papageorgiou et al. [55]).
Moreover, transportation and the incineration of wood waste are the most significant contributors in almost all impact categories for S1 (c.f., Figure 2). For the biochar systems S2 and S3, pyrolysis of wood waste and heat substitution are significant contributors. Heat substitution represents the additional heat that needs to be generated to compensate for the reduced heat production in S2 and S3, as pyrolysis produces less energy than incineration because a large share of the initial energy content in the biomass remains in the biochar. For S2, transportation is another significant contributor, as off-site remediation requires transportation of large quantities of materials, for example, virgin soil for backfilling.
The results of the SFA for PAHs are summarized in Table 3. The analysis showed that for all PAHs, except benzo(a)pyrene, the leached amounts from the contaminated soil and the biochar-remediated soil are significantly higher than their life cycle emissions from the other processes of the systems. However, the leached amounts of PAHs constitute only a small part of their initial content in the soils. The analysis showed that remediation with biochar can stabilize PAHs in the soil, as less than 0.1% of the initial content of these contaminants in the soil will leach out within a 100-year period.
PAHs
Life cycle emissions, without emissions from disposal of contaminated soil or reuse of biochar-remediated soil (kg)
Initial amount in the contaminated soil (kg)
Amount released from the disposed contaminated soil (kg)
Amount released from the reused remediated soil (kg)
For the metal(loid)s the results of the SFA are presented in Table 4. Contrary to PAHs, the leached amounts of most metal(loid)s from the landfilled or remediated soil are lower than their life cycle emissions. The only exceptions are Mo and Ba. Moreover, the analysis showed that less than 0.8% of the initial content of metal(loid)s in the contaminated soil leaches out, except for Ba where 1.1% leaches out in S2 and S3, and Mo where 4.7% and 25% of the initial content leaches out in S1, S2, and S3, respectively. Furthermore, the SFA indicated that the application of biochar can reduce the leaching of Cu, Zn, Ni, and Hg, while it does not have the same positive effects for the other metal(loid)s. A sensitivity analysis showed that the results for metal(loid)s were sensitive to the assumed degree of water infiltration in the soils, contrary to the results for PAHs, which showed low sensitivity.
Metal(loid)s
Life cycle emissions, without emissions from disposal of contaminated soils (kg)
Initial amount in the contaminated soil (kg)
Amount released from the disposed contaminated soil (kg)
Overall, the SFA showed that the treatment of contaminated soils with biochar is effective for stabilizing PAHs. For metal(loid)s, however, the results of the SFA were more varied and sensitive to modeling assumptions. Therefore, further investigation is required to evaluate the effectiveness of this technique for remediating contaminated soils with metal(loid)s and identify and assess potential ecological and human health risks associated with it.
5. The role of biochar systems in the circular economy
To explore the role of biochar systems in the CE, the definition of the CE by Kirchherr et al. [5] (see Section 2) is used as a conceptual basis. More specifically, it is examined how the studied biochar systems can satisfy key elements of the definition.
The definition has an explicit reference to the 4Rs (Reduce–Reuse–Recycle–Recover) principle highlighting that, in the CE, a top priority is given on reducing the use of materials, and then on reuse, recycling, and recovery. On-site remediation with biochar (S3) can contribute to both reduction and reuse of materials, as the remediated soil can be reused on-site preventing the use of virgin soil for backfilling. Moreover, on-site remediation can generate significant fuel savings, as it involves less transportation compared to off-site remediation (S2) and landfilling of contaminated soil with the incineration of wood waste (S1). Off-site remediation cannot offer the same benefits as on-site remediation, as the remediated soil is not used on-site for backfilling. Nonetheless, the remediated soil can be reused in other applications (e.g., construction of noise barriers), preventing the use of virgin soil for these applications. In addition, both off-site and on-site remediation recover energy from the sorted wood waste and at the same time prevent the landfilling of the contaminated soil. Hence, it is evident that both biochar systems, especially S3, contribute to fulfilling the 4Rs principle of the CE.
The definition also indicates that a multi-level implementation of the CE model at the micro, meso and macro level is required for the transition to the CE. The versatility of biochar systems offers opportunities for the operationalization of the CE model at different system levels. The studied systems in this chapter demonstrate how biochar systems could form the basis of circular models for valorizing different waste streams in urban areas (macro level). Nonetheless, similar systems based on pyrolysis of biomass waste or other biomass feedstocks could also be developed in symbiosis with other industrial facilities in eco-industrial parks (meso level). For example, biomass waste (e.g., from a paper or pulp mill) could be pyrolyzed to supply heat and/or electricity for industrial processes within the eco-industrial park, while the produced biochar could be used as a resource for the manufacture of other materials, such as concrete, steel or activated carbon (see Section 3). In addition, biochar systems offer circular economy pathways at the micro level. It has been reported that decentralized biochar systems using agro-industrial wastes could be deployed in farms and small and medium enterprise (SME) activities to generate bioenergy and produce biochar that can be used as amendment of agricultural soils [12] or feed supplements for poultry or ruminants [45]. For example, a pyrolysis-biochar system could be integrated into an olive–grove farm in symbiosis with an olive mill, where residues from the olive grove and oil extraction are used as feedstock for the pyrolysis to produce heat and power for olive milling operations and biochar for amending the soil in the olive grove [37].
Moreover, according to the definition, the ultimate goal of operationalizing the CE model at different levels is to achieve sustainable development. One aspect of this goal is the creation of environmental quality. The assessment of the environmental performance of the biochar systems described in this chapter highlighted that these systems have great potential to improve environmental quality. First, they can contribute substantially to climate change mitigation through carbon sequestration in the biochar. Moreover, when compared to the conventional “dig and dump” system, the biochar system for on-site remediation can provide additional greenhouse gas emission savings, as it delivers fuel and virgin material savings. Apart from contributing to climate change mitigation, the assessed biochar systems can also provide additional environmental benefits, as they perform better than the “dig and dump” system in 10 out of 12 analyzed impact categories (see Section 4.2.2). However, there are also trade–offs associated with these systems, as they cause more impacts in the impact categories of ionizing radiation and fossils. The reason is that the technology for pyrolysis of wood waste used in this specific case requires considerable amounts of auxiliary electricity, which in Sweden is derived to a large extent from nuclear power, which is associated with these environmental impacts. Furthermore, the efficacy of biochar to stabilize certain metal(loid)s was not as high as for PAHs, and, in general, the extent of potential ecological and human health risks from the reuse of the remediated soil is still unknown.
To understand the role of biochar systems in CE it should be noted that CE, as defined here, does not imply “re–circulation of everything.” One of the key benefits of biochar is to remove carbon from the atmosphere, thus contributing to climate change mitigation, by turning biomass into a stable material with a long lifetime in soils. Thus, the carbon cycle from atmospheric carbon dioxide to organic matter and back to the atmosphere is not closed, but slowed down, fitting into the CE concept of “slowing loops” [31].
Apart from environmental quality, other aspects of the desired goal to achieve sustainable development are the creation of economic prosperity and social equity. These aspects were not included in the scope of the above–described assessment, as it was focused only on the environmental sustainability of the studied systems. Nevertheless, it has been reported in the literature that biochar systems can generally have positive economic effects, as they can create new revenue opportunities, cut costs by reducing resource use and improving logistics, and create new business opportunities [34, 37]. Moreover, they can deliver social benefits, as they can create employment, promote food security through improved crop production from enhanced soil productivity, and offer energy diversification and security of supply [34, 37]. Moreover, the creation of new job opportunities and the associated increase in income are important factors for poverty reduction, which can help in reducing inequalities in society [59].
The above–mentioned environmental, social, and economic benefits of biochar systems are good indications that these systems have the potential to contribute to achieving sustainable development, which is the ultimate goal of the CE. Nevertheless, further research is required to identify and assess potential risks and drawbacks with these systems. From an environmental perspective, it is essential to investigate further various types of biochar systems to ascertain whether they could create risks to environmental quality. For example, in the case of the studied biochar systems, in this chapter, further research could be directed toward identifying and assessing the magnitude of potential risks associated with the reuse of the remediate soils within urban environments. From a social and economic perspective, further research is needed to identify and assess potential socio-economic implications of biochar systems, including those described in this chapter.
6. Conclusion
The CE has emerged as an alternative development model to the unsustainable “take–make–waste” approach that characterizes the contemporary economic systems. The transition toward the CE requires the implementation of new innovative technological solutions that can foster CE principles and help operationalize the CE model at different system levels. One emerging technology that can have a role in the transition toward the CE is biochar systems. These are multifunctional systems that can be deployed for biowaste treatment, and bioenergy and biochar production. As the produced biochar has versatile physicochemical properties, it can be used in various applications. Perhaps, the most prominent application of biochar, is its incorporation into soils, as it can contribute to climate change mitigation through carbon sequestration and at the same time amend the properties of soils. Overall, the multifunctionality of biochar systems, in combination with the versatility of the produced biochar, makes them suitable to function as a basis for developing circular models of waste management.
This chapter describes two biochar systems that could be developed for valorizing wood waste and contaminated soil in an urban area in Sweden. In the studied systems, wood waste is converted via pyrolysis into syngas and biochar. The syngas is used as the energy source for district heating supply. The produced biochar is applied to contaminated soil, either on-site or off-site, to sequester carbon and at the same time to remediate the soil to enable its reuse and prevent its landfilling.
The environmental performance of the two biochar systems was assessed and compared to the conventional “dig and dump” system, where the wood waste is incinerated for energy recovery and the contaminated soil is disposed of in a landfill. The assessment was carried out by combing LCA with MEFA and SFA. The MEFA showed that the biochar system for on-site remediation could provide large fuel and virgin soil savings, compared to the biochar system for off-site remediation and the “dig and dump” system. The LCA revealed that the two biochar systems performed better than the “dig and dump” system in 10 out of 12 analyzed impact categories. The two biochar systems performed remarkably well in the climate change category, as they can achieve net negative GHG emissions, because of carbon sequestration in the biochar. Between the two biochar systems, on-site remediation with biochar performs better than off-site in all impact categories, as the former provides fuel and virgin soil savings. However, there are also trade–offs with the biochar systems, as the pyrolysis of wood waste contributes to ionizing radiation and fossils depletion due to increased consumption of auxiliary electricity. Moreover, the SFA showed that the efficacy of biochar to stabilize certain metal(loid)s is not as good as for PAHs. Hence, the extent of potential risks (e.g., ecological and human health) associated with the reuse of biochar-remediated soils is still unknown.
Based on the findings from the assessment of the studied biochar systems and using the definition of the CE by Kirchherr et al. [5] as a conceptual basis, it was highlighted that these systems can have an important role in the transition toward the CE. It was established that these systems, especially the one for on-site remediation, fulfill the 4Rs principle of the CE. It was also suggested that the versatility of biochar systems creates opportunities for operationalizing the CE model at different system levels. Furthermore, based on the findings of the environmental assessment and findings from the literature, it was inferred that the biochar systems have the potential to provide environmental, social, and economic benefits and thus to contribute to achieving sustainable development, the ultimate goal of the CE. Nevertheless, further research is required to assess whether the reuse of the biochar-remediated soil creates potential risks to ecosystem quality and human health. Moreover, further research could assess potential social and economic implications from the development of these systems.
Acknowledgments
Rajib Sinha gratefully acknowledges FORMAS (project number 2018-01545) for financial support to write the chapter. This work was supported by the Swedish Energy Agency [2018-002148], Sweden’s innovation agency (Vinnova) and Formas - a Swedish Research Council for Sustainable Development.
\n',keywords:"circular economy, sustainable development, biochar systems, wood waste, contaminated soil",chapterPDFUrl:"https://cdn.intechopen.com/pdfs/81303.pdf",chapterXML:"https://mts.intechopen.com/source/xml/81303.xml",downloadPdfUrl:"/chapter/pdf-download/81303",previewPdfUrl:"/chapter/pdf-preview/81303",totalDownloads:32,totalViews:0,totalCrossrefCites:0,dateSubmitted:"February 5th 2022",dateReviewed:"March 7th 2022",datePrePublished:"April 28th 2022",datePublished:null,dateFinished:"April 16th 2022",readingETA:"0",abstract:"The circular economy is considered as an alternative model to the unsustainable linear “take–make–waste” approach that characterizes contemporary economic systems. It aims to achieve sustainable development by promoting the responsible and cyclical use of resources to maintain their value in the economy and minimize pressures on the environment. Biochar systems offer opportunities for operationalizing the CE model. They are multifunctional systems that can be used for bioenergy and biochar production using an extensive range of biomass feedstocks, including biowaste. They can contribute to climate change mitigation, as producing biochar and mixing it with soil is a means for sequestering atmospheric CO2. Moreover, the produced biochar has a wide range of applications, including its use for agricultural soil amendment, wastewater treatment, manufacturing of cement, and remediation of contaminated soils. This versatility of biochar systems creates great opportunities for developing circular models of waste management that can valorize different waste streams. This chapter provides an overview of the CE concept and describes biochar systems, focusing on systems for the synergistic valorization of wood waste and contaminated soils. It also discusses the role of these systems in the CE indicating that they can contribute to the transition toward the CE.",reviewType:"peer-reviewed",bibtexUrl:"/chapter/bibtex/81303",risUrl:"/chapter/ris/81303",signatures:"Asterios Papageorgiou, Rajib Sinha, Elias Sebastian Azzi, Cecilia Sundberg and Anja Enell",book:{id:"11256",type:"book",title:"Circular Economy - Recent Advances of Sustainable Waste Management",subtitle:null,fullTitle:"Circular Economy - Recent Advances of Sustainable Waste Management",slug:null,publishedDate:null,bookSignature:"Associate Prof. Tao Zhang",coverURL:"https://cdn.intechopen.com/books/images_new/11256.jpg",licenceType:"CC BY 3.0",editedByType:null,isbn:"978-1-80355-913-1",printIsbn:"978-1-80355-912-4",pdfIsbn:"978-1-80355-914-8",isAvailableForWebshopOrdering:!0,editors:[{id:"185487",title:"Associate Prof.",name:"Tao",middleName:null,surname:"Zhang",slug:"tao-zhang",fullName:"Tao Zhang"}],productType:{id:"1",title:"Edited Volume",chapterContentType:"chapter",authoredCaption:"Edited by"}},authors:null,sections:[{id:"sec_1",title:"1. Introduction",level:"1"},{id:"sec_2",title:"2. The circular economy",level:"1"},{id:"sec_3",title:"3. Biochar systems",level:"1"},{id:"sec_4",title:"4. Biochar systems for synergistic valorization of wood waste and contaminated soil",level:"1"},{id:"sec_4_2",title:"4.1 Systems description",level:"2"},{id:"sec_5_2",title:"4.2 Environmental performance",level:"2"},{id:"sec_5_3",title:"4.2.1 Methods",level:"3"},{id:"sec_6_3",title:"Table 1.",level:"3"},{id:"sec_9",title:"5. The role of biochar systems in the circular economy",level:"1"},{id:"sec_10",title:"6. Conclusion",level:"1"},{id:"sec_11",title:"Acknowledgments",level:"1"}],chapterReferences:[{id:"B1",body:'Kristensen HS, Mosgaard MA. A review of micro level indicators for a circular economy: Moving away from the three dimensions of sustainability? Journal of Cleaner Production. 2020;243:118531'},{id:"B2",body:'Korhonen J, Honkasalo A, Seppälä J. Circular economy: The concept and its limitations. 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Journal of Open Source Software. 2017;2(12):236'},{id:"B57",body:'Wernet G, Bauer C, Steubing B, Reinhard J, Moreno-Ruiz E, Weidema B. The ecoinvent database version 3 (part I): overview and methodology. International Journal of Life Cycle Assessment. 2016;21(9):1218-1230'},{id:"B58",body:'European Commission, Joint Research Centre, Institute for Environment And Sustainability. Characterisation factors of the ILCD Recommended Life Cycle Impact Assessment Methods. Luxemburg: Database and Supporting Information - First Edition; 2012'},{id:"B59",body:'Kamali M, Sweygers N, Al-Salem S, Appels L, Aminabhavi TM, Dewil R. Biochar for soil applications-sustainability aspects, challenges and future prospects. Chemical Engineering Journal. 2022;428:131189'}],footnotes:[],contributors:[{corresp:"yes",contributorFullName:"Asterios Papageorgiou",address:"asterios@kth.se",affiliation:'
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