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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1. Introduction
Usually project risk management plans deal with identifying, assessing and planning adequate responses to risks. The main problem is that there are many types of response plans, and we must be able to select the optimal one. The usual approach is to first handle the most “dangerous” risk (the risk with the maximum expected damage). However, handling this risk may also be very expensive and beyond the limitations of the allocated risk budget. The dilemma is how to select the right risks to be handled within a limited budget.
2. Risk management methodology
Risk management methodology was first described in detail by Wideman in [1]. The methodology was then improved by the PMI [2], adding details based on users’ experience.
Project Risk management involves the following steps:
Planning Risk Assessment, which includes selecting an assessment team, setting up rules, and determining the supporting risk management tools. The risk assessment team should include representatives from all areas related to the project.
Risk Identification is a process of defining future events that should be considered as risk events. The list is usually generated by a brain-storming session conducted by the projects’ experts. The list is then reduced to the most important risks. This step is sometimes subjective, but this issue is not relevant to this paper.
Risk Assessment is the quantification of identified risks, conducted in order to define priorities among the possible risk events. It usually includes the probability of the event and the severity of the damage. Later, the ranking of risks is based on these two parameters. One possible method is the Borda [3] methodology for ranking alternatives.
A Risk Response plan includes answers to the threats that are identified in the risk assessment phase. There are a number of ways to address these threats.
Avoidance - generate a course of action that eliminates the risk.
Transfer – transfer responsibility for the particular risk to a third party, either by utilizing insurance or, in the international arena, by forming treaties and international agreements.
Acceptance - a rational decision to accept a known risk without taking any action to prevent its outcome or deal with its consequences. The risk is usually dealt with when it is recognized as a risk. An acceptance of risk is recommended in situations where the consequences of the risk are less costly or less traumatic than the effort required preventing the risk.
Mitigation - refers to action taken to reduce either the probability of occurrence of an unfavorable event or the impact of this event. Mitigation is usually executed in the form of a plan designed to handle high-threat possible events.
Contingency Planning – refers to specific actions to be taken when a potential risk event occurs. In general, contingency plans should be developed in advance in preparation for the moment when risk events are realized.
Out of the five responses, only three (avoidance, transfer and mitigation) involve a real investment and require budget allocation.
A Control Plan is a series of course adjustments within the project’s main objectives. These adjustments include scheduling and tracing the advance of risk situations. The control plan defines indicators that provide warnings regarding the realization of specific risks.
Continuously assessing program risks is the implementation of the control plan by checking any changes in the assessment of risks, and conducting a continuous search for warning signs that indicate any realization of known risks.
This part of the project plan includes the updating of the risk management plan.
The current study concentrates on allocating a budget to the response plan in an optimal manner.
This paper includes a literature review, problem definition, algorithms’ definition, an example that is solved by all algorithms, and a comparison among the algorithms by simulation results. The research is quantitative and presents simulation results. Since the difference among the algorithms for different budgets are so big, statistical analysis is unnecessary.
The simulation and algorithms were verified by solving known problems and their solutions.
3. Literature review
Project risk management literature commonly describes the need to rank and prioritize project risks in order to focus the risk management effort on the higher risks. Baccarinia et al. in [4] describe the use of a methodology for the risk ranking of projects by some subjective judgment; this method has been implemented in construction projects and multi-project environments. Engert from MITRE [3] wrote a user’s manual for an Excel application for risk management. The application includes a ranking method of risks based on Borda’s method. The Borda method is more quantitative than the subjective judgment method, but still includes some fuzzy ranking when it combines the rank of risk probability with the rank of impact. Ochsner [5] emphasizes the limited attention to risk-based priorities and the growing consensus among industries that risk considerations need to be better integrated into decisions. He agrees that although money is not always the best way to measure risks, no better alternative has thus far been suggested. His ranking method is based on discussions with consultants and experts, assigning scores from 1 to 10 for each category. Li et al. [6] present a ranking method for multiple hazard risks; the method is based on screening all the risks with experts and weighting the risks according to frequency, severity, availability of warning, awareness, etc.
In [7] the author presents the difficulties involved in ranking risks. He utilizes the following framework: Risk = Threat×Vulnerability×Consequence, which is usually used in military operations research. The Threat×Vulnerability framework actually reflects the probability to damage a target, when the consequence is the damage impact. Our study is important in that for some qualitative measures, it presents counter examples that highlight the limitation of this measurement type. Klein [8] developed a conceptual model for analyzing alternative risk mitigation responses, while accounting for the possibility of trade-off risk among the three main success criteria: cost, duration and scope (or quality). He showed that, given the numerical estimates of risks probabilities and impacts, of all the relevant responses, mathematical techniques - such as dynamic programming or integer programming - could be applied to find the best combination of responses that minimizes project uncertainty. This approach analyzes trade-off among success criteria.
Ben-David et al. [9] analyzes a problem that is similar to the current one, but takes a different approach. Assuming that several risk mitigation responses can be implemented with different costs and different expected results, a selection of the best combination of responses is needed. All of the responses are broken down to their work elements, so that each risk can belong to several of them. The Total Risk Cost (TRC) is minimized by two heuristic algorithms; the greedy and the naïve, after which a comparison is presented. The current manuscript does not take into account the budget limitation, and assumes that as long as risk can be mitigated and it is worthwhile from the budget point of view – it will be done.
There are many studies that use subjective judgment to rank risks in different areas, industries, projects and programs. However, none of these ranking methods take into account the response capability to risks. There might be a huge difference between two risks that have the same probability to occur and the actual impact, when one of the risks occurs. However, for the first risk there is a mitigation plan that reduces its effect substantially and costs $1,000, while for the second risk, any type of mitigation plan costs more than $100,000. The study of Gonen et al. [10] proposes an additional criterion for the assessment of risks – that of controllability. The introduction of this criterion adds a third dimension to the risk evaluation process, in addition to its probability and impact. The controllability of a given risk reflects the ability to control it, mitigate it, or even prevent it. Assessing controllability may reduce the efforts and spending of managerial time and expenses on non-controllable risks and, in the end, direct the attention of management solely to controllable risks.
Controllability adds a new criterion that takes into account the response capability, but still does not propose a method to quantitatively rank the risks. In the current paper, we overcome the problem of ranking risks by utilizing a method of selecting the optimal mitigation plan for a given budget, and therefore, the risks to be mitigated or transferred.
Kutsch et al. [11] have investigated the type of risks that can be deliberately ignored. In the current study, we deal with risks that are not supposed to be ignored.
4. Defining the problem
The problem we will address in this study is the allocation of a risk management budget among the possible responses. The solution to this problem is not only ranking the risks to be dealt with, but also recommending the best risk response investment.
As was mentioned in Section 2, Part 4, responses to identified risks can be divided into two groups: Responses that include a real money investment - like transfer, avoidance and mitigation - and the other responses, which do not require any investment - like accepting the risk or preparing a contingency plan. Our study concentrates on the responses that require an investment and examines how to select the right set of responses when we are limited by a well-defined budget. In order to clarify these issues, let us look at the following theoretical example:
Assume there are two risks in a project - R1 and R2. R1 will occur with probability P1 and the damage in this case will be D1. R2 will occur with probability P2 and the damage in this case will be D2. In order to overcome these risks, we can either transfer the risk R1 (by purchasing insurance), which will cost C11 and the policyholder\'s participation D11 or respond to risk R1 with a mitigation plan that will cost C12. After its application, the remaining probability to occur is P12 with damage when it occurs of D12. For risk R2, we have one mitigation plan that costs C21; after its application, the remaining probability to occur is P21 with damage when it occurs of D21. We have a risk mitigation budget of B that we can invest to handle these risks and we would like to know what our best policy is (B is usually determined by the project’s customer).
In this study, we assume a linear utility function. This means that we will choose the policy that will reduce our expected cost to a minimum. The following table presents a numeric example of the dilemma described above:
Risk
P
D
Expected Damage
Response
Cost
Pij
Dij
Expected Damage+Cost
R1(*)
0.2
1000
200
Transfer
80
0.2
50
90
Mitigation
50
0.1
500
100
R2(*)
0.3
700
210
Mitigation
50
0.3
200
110
Table 1.
Numeric Example of the Dilemma
Let B=50. In this case, we can either choose the second or the third row. If we choose the second row, we reduce the expected damage of Risk 1 to 100 and stay with Risk 2 at an expected damage of 210. All together, the expected damage of both risks is 310. The same is true if we choose to handle Risk 2 and reduce the expected damage to 110. Since the expected damage of Risk 1 is 200, the total is 310. Let B=80. In this case, we can choose the first row or the previous option of B=50. Choosing Row 1 derives the total expected damage to 90+210=300 (the 210 is from R2). If we choose the second row (mitigating R1), our total expected damage will be 310, and the third row (mitigating R2) will be the same - 310. However, in both mitigation plans we only invest 50, while in the transfer policy we invest a minimum of 80. People who are risk-averse will prefer this option, while others who are attracted to risk might prefer the second or third row. If B=100, then an additional option is open which allows us to choose Rows 2 and 3 and reduce the expected damage to 210. If B=130 and up, we can choose Rows 1 and 3 and reduce the expected damage to 200.
If we try to minimize the expected damage when B=80, then transferring R1 would be optimal, although usually risk management methods will rank R2 higher and recommend treating it first.
In order to define the optimal response problem, we will use the following terminology and symbolization:
There are n risks R1,…,Rn. For each risk Ri, the probability of its occurrence is Pi and the damage when it occurs is Di. Therefore, for each risk Ri, the expected damage is Qi\n\t\t\t\t= Pi Di. Index i will be used for risks.
For each risk Ri, there are k responses (some can be empty; others can be transfer or mitigation) out of which we can choose, at most, one. This can be done by combining mitigation plans together. Index j will be used for a response plan.
The response j to risk Ri costs Cij; after its implementation, the probability of its occurrence is Pij and the corresponding damage is Dij. The expected damage after its implementation is
Qij= Pij Dij.
A response plan is defined as “worthwhile” only if
\n\t\t\tQi≤Cij+Qij\n\tfor\n\ti=1,‧,nE1
\n\t\t\t
(Only if the investment + the expected damage after the implementation are lower than the original expected damage). A response plan that is not worthwhile will not be included in the list of possible responses. Actually, the savings in selecting response j to risk Ri is:
\n\t\t\tQi-Cij+QijE2
.
Let us now define the decision variables Xij as 1, if response j is selected for risk Ri, and 0, otherwise.
Only one response can be selected (if the user wants to enable selecting two responses to risk Ri, he can combine both responses into one plan with the accumulated cost). From the definition of Xij, the expected value of all the risks will be:
After opening the equation, it is clear that the expected value of all the risks (that we would like to minimize) is:
\n\t∐i=1nQi-∐i=1n∐j=1kXij(Qi-Cij+Qij)\n\tE4
\n\t\t\t
Since ∐i=1nQi does not depend on the selection of risks to be handled, the problem can be defined as an integer programming problem, as follows:
\n\tmax∐i=1n∐j=1kXij(Qi-Cij+Qij)E5
\n\t\t\t
s.t.
\n\t∐j=1kXij\n\t\t≣1\n\t\tfor\n\t\ti=1,‧,nE6
\n\t\t\t
\n\t∐i=1n∐j=1kXijCij≣BE7
(budget constraint)
And Xij can be either 0 or 1 for i=1,…,n and j=1,…, k.
5. Solving the problem
The problem can be solved by Integer Linear Programming (ILP), as was mentioned in [9, 12]. In this paper, we compare 3 heuristic algorithms that solve this ILP. The algorithms are as follows:
1. The Most Dangerous Risk (MDR) method (PMI, 2008) is used to show the “naïve” solution. In the current case, the first risk to be handled is the one with maximum Qi. For the selected risk, the most effective response is selected and the accumulated budget is increased by Cij.
For each selected risk, the response with the maximum savings (Qi-(Cij+Qij)) will always be selected. The algorithm that is used is as follows:
Sort the risks according to Qi from higher to lower.
For each risk, select the response j with the higher (Qi-(Cij+Qij)).
Calculate the accumulated cost of applying the responses according to the sorted list.
Calculate the accumulated savings.
If the accumulated cost of risk responses is less than the budget, go back to Step 1.
2. The Most Profitable Response (MPR) method is defined as follows:
Sort the responses according to (Qi-(Cij+Qij)) from higher to lower.
Choose the upper risk in the sorted list that was not selected yet.
Calculate the accumulated cost of applying the responses according to the sorted list.
Calculate the accumulated savings.
If the accumulated cost of risk responses is less than the budget, go back to Step 1.
In this algorithm, the response savings plays a major role and the decision is made according to the possible savings.
3. The Best Saving Ratio (BSR) method is defined as follows:
Definition: The ratio between the savings in expected damage and the cost of the response will be called the savings ratio. Mathematically, it is defined as (\n\t\t\tQi-Cij+Qij)/Cij. The economic meaning of this ratio is the amount of savings in expected damage per each unit of investment in the response.
The algorithm will be as follows:
Sort the responses according to the savings ratio (Qi-(Cij+Qij))/Cij from higher to lower.
Choose the upper risk in the sorted list that was not selected yet.
Calculate the accumulated cost of applying the responses according to the sorted list.
Calculate the accumulated savings.
If the accumulated cost of risk responses is less than the budget, go back to Step 1.
In order to clarify the three algorithms, let us demonstrate them by an example:
In the following table (Table 2) there are 6 risks; for each risk there are three possible response plans. The table includes the Pi, Di, Qi, Cij, Pij, Dij, Qij, and both the savings in expected damage + cost and the savings ratio.
Table 2.
Numeric Example to compare the three algorithms
The numeric example is generated by a simulation that will be described later. Table 2 includes all the information needed for applying the algorithms MDR, MPR and BSR.
Tables 3, 4, 5 present the MDR, MPR and BSR solutions accordingly.
In Table 3, the ranked risk =1 means the first risk to respond. The first risk that is handled is Risk number 2, since its Qi is 145 (from Table 2). The response is selected as the highest savings solution. Total handling of the 6 risks requires a budget of 90.1 and saves 236.7 in expected damages, plus the cost of applying the responses.
Table 4 shows that the selection order is different from MDR. However, the accumulated savings converges to the same amount, since at the end both algorithms use the same response plans. The difference is in the selection order.
Most Dangerous Risk (MDR)
Ranked Risk
Risk Number
Response Number
Cost
Accumulated Budget
Savings
Accumulated Savings
1
2
1
31.06
31.06
96.31
96.31
2
3
2
14.02
45.08
58.76
155.07
3
6
2
37.98
83.06
13.94
169.01
4
1
3
0.67
83.72
34.34
203.35
5
5
3
1.54
85.27
22.40
225.75
6
4
2
4.83
90.10
10.99
236.73
Table 3.
Solution of the example using the MDR algorithm
Most Profitable Response (MPR)
Ranked Risk
Risk Number
Response Number
Cost
Accumulated Budget
Savings
Accumulated Savings
1
2
1
31.06
31.06
96.31
96.31
2
3
2
14.02
45.08
58.76
155.07
3
1
3
0.67
45.75
34.34
189.40
4
5
3
1.54
47.29
22.40
211.80
5
6
2
37.98
85.27
13.94
225.75
6
4
2
4.83
90.10
10.99
236.73
Table 4.
Solution of the example using the MPR algorithm
Table 5 shows that the BSR uses different response options and therefore converges to different accumulated savings. In this example, the BSR is the worst option out of the 3 algorithms, although this result does not represent the most common situation, as will be seen later.
Best Savings Ratio (BSR)
Ranked Risk
Risk Number
Response Number
Budget
Accumulated Budget
Savings
Accumulated Savings
1
1
3
0.67
0.67
34.34
34.34
2
5
3
1.54
2.21
22.40
56.73
3
3
3
4.11
6.32
31.57
88.30
4
2
1
31.06
37.38
96.31
184.61
5
4
3
3.85
41.22
10.41
195.02
6
6
3
6.46
47.69
4.30
199.32
Table 5.
Solution of the example using the BSR algorithm
6. Comparison of the three algorithms
In order to compare the three algorithms, a scenario simulation was generated with 15 risks and 3 responses per risk. The simulation draws the probabilities and damages according to the following rules:
Draw Pi distributed U(0.01.0.9) (uniform between 0.01 and 0.9)
Draw Di distributed U(10,200)
Draw Pij distributed U(0,Pi)
Draw Dij distributed U(0,Di)
Draw Cij distributed U(0.1, Qi-Qij) where Qi = Pi Di and Qij=Pij Dij
For all i=1,….15, j=1,…,3
The following chart (Figure 1) shows an example of the behavior of the three algorithms, while the budget increases, step by step.
Figure 1 is an example of a typical situation in which, for a limited budget the BSR is the best algorithm, while for an unlimited budget, the other algorithms can produce better results. This phenomenon holds in most of the simulation examples, but there are cases where the BSR is better for all budgets and cases.
In order to compare the three algorithms, 100 simulations were generated. For each simulation, the maximum needed budget was calculated. (Since the Cij are drawn, the required budget is stochastic and different in each simulation). For each simulation, the savings was calculated for an investment of 20%, 40%, 60%, 80% and 100% of the budget.
For each percentage investment, the savings was calculated for each algorithm. Later, the best algorithm was defined as the successor, for each specific budget, and the frequency of its success was calculated. The following table (Table 6) summarizes the number of successes of each algorithm
Table 6 shows that for a low budget (20 to 60 percent) the BSR is the best algorithm, while for an unlimited budget the MPR behaves better. In many cases, the MPR and MDR behave the same and reach the same savings.
Figure 1.
The savings of each algorithm regarding the limited budget
The main conclusion from Table 6 is that there is no optimal heuristic algorithm. Moreover, if only part of the risks budget can be handled, it is recommended to use the BSR algorithm.
Table 6.
Distribution of success of each algorithm
7. Discussion
Findings
The paper presented three heuristic algorithms for risk response selection. In many cases, the ranking of risks is not enough for project managers and they need to know how to invest their risk management budget among the possible responses. We observe that for a limited budget the BSR algorithm is better than the MDR or MPR method, while for a budget that can cover all the risks, the MDR or MPR are better. Currently, in most projects, the customer asks to see the risk management plan. The above method adds the selection method of risks to be mitigated. It should be an essential part of the risk management plan.
A stronger result is that risk ranking is no longer needed. This saves the effort of ranking risks, which is usually subjective.
Limitations
One limitation of the current paper is that estimating the probabilities and damages for each risk and response is usually considered to be a very difficult task. However, it is required by most of the risk management standards. Tools, like mathematical models and simulations, are available for this task and there are already many projects that include these estimations.
Another limitation is that we assume that responses with a negative expected savings cannot be selected. However, in reality, there are responses, like insurance, that are based on negative expected savings (otherwise, insurance company would not sell insurance policies).
A third limitation is the dependencies among risks. It might be that a delay in one task is not critical, while a delay in a second task, together with delay in the first task, might prove to be a severe problem.
8. Conclusion
In this article, we describe a method for how to allocate a risk management budget among the possible mitigation or transfer plans. In most of today’s literature, the risk management plan usually ranks the risks and recommends handling those with high rankings. Almost no consideration is given to either response plans or response feasibility. This study proposes three heuristic algorithm approaches to budget allocation, and demonstrates the method, including a sensitivity analysis of the budget constraint. The results are encouraging and help define rules about risk management budgeting.
The model is based on the expected damage, and assumes we will always prefer to reduce expected damages plus their cost. It does not discuss the question of risk taking.
A simulated scenario with 15 risks and 45 response plans was demonstrated. The most important lesson learned from the example tested in the study is that the solution is mainly influenced by the response plan, and not only by the expected damage of the risk, as all of the ranking methods recommend. Moreover, for a limited budget, the BSR is usually the best algorithm, while for an unlimited budget the MDR or MPR algorithms are more preferable..
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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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