Isotopic compositions of uranium and plutonium in spent LWR fuel
\\n\\n
IntechOpen was founded by scientists, for scientists, in order to make book publishing accessible around the globe. Over the last two decades, this has driven Open Access (OA) book publishing whilst levelling the playing field for global academics. Through our innovative publishing model and the support of the research community, we have now published over 5,700 Open Access books and are visited online by over three million academics every month. These researchers are increasingly working in broad technology-based subjects, driving multidisciplinary academic endeavours into human health, environment, and technology.
\\n\\nBy listening to our community, and in order to serve these rapidly growing areas which lie at the core of IntechOpen's expertise, we are launching a portfolio of Open Science journals:
\\n\\nAll three journals will publish under an Open Access model and embrace Open Science policies to help support the changing needs of academics in these fast-moving research areas. There will be direct links to preprint servers and data repositories, allowing full reproducibility and rapid dissemination of published papers to help accelerate the pace of research. Each journal has renowned Editors in Chief who will work alongside a global Editorial Board, delivering robust single-blind peer review. Supported by our internal editorial teams, this will ensure our authors will receive a quick, user-friendly, and personalised publishing experience.
\\n\\n"By launching our journals portfolio we are introducing new, dedicated homes for interdisciplinary technology-focused researchers to publish their work, whilst embracing Open Science and creating a unique global home for academics to disseminate their work. We are taking a leap toward Open Science continuing and expanding our fundamental commitment to openly sharing scientific research across the world, making it available for the benefit of all." Dr. Sara Uhac, IntechOpen CEO
\\n\\n"Our aim is to promote and create better science for a better world by increasing access to information and the latest scientific developments to all scientists, innovators, entrepreneurs and students and give them the opportunity to learn, observe and contribute to knowledge creation. Open Science promotes a swifter path from research to innovation to produce new products and services." Alex Lazinica, IntechOpen founder
\\n\\nIn conclusion, Natalia Reinic Babic, Head of Journal Publishing and Open Science at IntechOpen adds:
\\n\\n“On behalf of the journal team I’d like to thank all our Editors in Chief, Editorial Boards, internal supporting teams, and our scientific community for their continuous support in making this portfolio a reality - we couldn’t have done it without you! With your support in place, we are confident these journals will become as impactful and successful as our book publishing program and bring us closer to a more open (science) future.”
\\n\\nWe invite you to visit the journals homepage and learn more about the journal’s Editorial Boards, scope and vision as all three journals are now open for submissions.
\\n\\nFeel free to share this news on social media and help us mark this memorable moment!
\\n\\n\\n"}]',published:!0,mainMedia:{caption:"",originalUrl:"/media/original/237"}},components:[{type:"htmlEditorComponent",content:'
After years of being acknowledged as the world's leading publisher of Open Access books, today, we are proud to announce we’ve successfully launched a portfolio of Open Science journals covering rapidly expanding areas of interdisciplinary research.
\n\n\n\nIntechOpen was founded by scientists, for scientists, in order to make book publishing accessible around the globe. Over the last two decades, this has driven Open Access (OA) book publishing whilst levelling the playing field for global academics. Through our innovative publishing model and the support of the research community, we have now published over 5,700 Open Access books and are visited online by over three million academics every month. These researchers are increasingly working in broad technology-based subjects, driving multidisciplinary academic endeavours into human health, environment, and technology.
\n\nBy listening to our community, and in order to serve these rapidly growing areas which lie at the core of IntechOpen's expertise, we are launching a portfolio of Open Science journals:
\n\nAll three journals will publish under an Open Access model and embrace Open Science policies to help support the changing needs of academics in these fast-moving research areas. There will be direct links to preprint servers and data repositories, allowing full reproducibility and rapid dissemination of published papers to help accelerate the pace of research. Each journal has renowned Editors in Chief who will work alongside a global Editorial Board, delivering robust single-blind peer review. Supported by our internal editorial teams, this will ensure our authors will receive a quick, user-friendly, and personalised publishing experience.
\n\n"By launching our journals portfolio we are introducing new, dedicated homes for interdisciplinary technology-focused researchers to publish their work, whilst embracing Open Science and creating a unique global home for academics to disseminate their work. We are taking a leap toward Open Science continuing and expanding our fundamental commitment to openly sharing scientific research across the world, making it available for the benefit of all." Dr. Sara Uhac, IntechOpen CEO
\n\n"Our aim is to promote and create better science for a better world by increasing access to information and the latest scientific developments to all scientists, innovators, entrepreneurs and students and give them the opportunity to learn, observe and contribute to knowledge creation. Open Science promotes a swifter path from research to innovation to produce new products and services." Alex Lazinica, IntechOpen founder
\n\nIn conclusion, Natalia Reinic Babic, Head of Journal Publishing and Open Science at IntechOpen adds:
\n\n“On behalf of the journal team I’d like to thank all our Editors in Chief, Editorial Boards, internal supporting teams, and our scientific community for their continuous support in making this portfolio a reality - we couldn’t have done it without you! With your support in place, we are confident these journals will become as impactful and successful as our book publishing program and bring us closer to a more open (science) future.”
\n\nWe invite you to visit the journals homepage and learn more about the journal’s Editorial Boards, scope and vision as all three journals are now open for submissions.
\n\nFeel free to share this news on social media and help us mark this memorable moment!
\n\n\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:"869",leadTitle:null,fullTitle:"Olive Oil - Constituents, Quality, Health Properties and Bioconversions",title:"Olive Oil",subtitle:"Constituents, Quality, Health Properties and Bioconversions",reviewType:"peer-reviewed",abstract:"The health-promoting effects attributed to olive oil, and the development of the olive oil industry have intensified the quest for new information, stimulating wide areas of research. This book is a source of recently accumulated information. It covers a broad range of topics from chemistry, technology, and quality assessment, to bioavailability and function of important molecules, recovery of bioactive compounds, preparation of olive oil-based functional products, and identification of novel pharmacological targets for the prevention and treatment of certain diseases.",isbn:null,printIsbn:"978-953-307-921-9",pdfIsbn:"978-953-51-4368-0",doi:"10.5772/1378",price:159,priceEur:175,priceUsd:205,slug:"olive-oil-constituents-quality-health-properties-and-bioconversions",numberOfPages:524,isOpenForSubmission:!1,isInWos:1,isInBkci:!0,hash:"b26e27a335ddfd64f9583593dbd8ceb5",bookSignature:"Boskou Dimitrios",publishedDate:"February 1st 2012",coverURL:"https://cdn.intechopen.com/books/images_new/869.jpg",numberOfDownloads:142607,numberOfWosCitations:256,numberOfCrossrefCitations:66,numberOfCrossrefCitationsByBook:5,numberOfDimensionsCitations:272,numberOfDimensionsCitationsByBook:17,hasAltmetrics:1,numberOfTotalCitations:594,isAvailableForWebshopOrdering:!0,dateEndFirstStepPublish:"February 22nd 2011",dateEndSecondStepPublish:"March 22nd 2011",dateEndThirdStepPublish:"July 27th 2011",dateEndFourthStepPublish:"August 26th 2011",dateEndFifthStepPublish:"December 24th 2011",currentStepOfPublishingProcess:5,indexedIn:"1,2,3,4,5,6,8,9",editedByType:"Edited by",kuFlag:!1,featuredMarkup:null,editors:[{id:"77212",title:"Dr.",name:"Dimitrios",middleName:null,surname:"Boskou",slug:"dimitrios-boskou",fullName:"Dimitrios Boskou",profilePictureURL:"https://mts.intechopen.com/storage/users/77212/images/3142_n.jpg",biography:"Dimitrios Boskou received his diploma in chemistry from the School of Chemistry, Aristotle University of Thessaloniki, Hellas; his Philosophy Doctor degree from the University of London, UK; and his degree of Doctor of Science from the School of Chemistry, Aristotle University of Thessaloniki, Hellas. He served as an assistant, lecturer, assistant professor, associate professor, professor and head of the Laboratory of Food Chemistry and Technology, School of Chemistry, Aristotle University of Thessaloniki (1970–2006). From 1986 to 1998, he was a member of the IUPAC Commission on Oils, Fats, and Derivatives. In the years 1995–2005, he served as a member of the Supreme Chemical Council, Athens. From 1995 to 2012, he was a member of the Scientific Committee for Food of the European Commission and a member and expert of the Food Additives Panel of the European Food Safety Authority. His achievements are: over 90 published papers and reviews; author and editor of 8 books; author of 22 chapters in books related to major and minor constituents of fats, natural antioxidants, olive oil and frying of food; and contributor to international scientific encyclopedias and the Lexicon of Lipid Nutrition, a joint IUPAC/IUNS work.",institutionString:null,position:null,outsideEditionCount:0,totalCites:0,totalAuthoredChapters:"0",totalChapterViews:"0",totalEditedBooks:"2",institution:null}],equalEditorOne:null,equalEditorTwo:null,equalEditorThree:null,coeditorOne:null,coeditorTwo:null,coeditorThree:null,coeditorFour:null,coeditorFive:null,topics:[{id:"327",title:"Food Safety",slug:"food-safety"}],chapters:[{id:"27024",title:"Volatile and Non-Volatile Compounds of Single Cultivar Virgin Olive Oils Produced in Italy and Tunisia with Regard to Different Extraction Systems and Storage Conditions",doi:"10.5772/28699",slug:"volatile-and-non-volatile-compounds-of-single-cultivar-virgin-olive-oils-produced-in-italy-and-tunis",totalDownloads:3101,totalCrossrefCites:2,totalDimensionsCites:3,hasAltmetrics:0,abstract:null,signatures:"Cinzia Benincasa, Kaouther Ben Hassine,Naziha Grati Kammoun and Enzo Perri",downloadPdfUrl:"/chapter/pdf-download/27024",previewPdfUrl:"/chapter/pdf-preview/27024",authors:[{id:"75035",title:"Dr.",name:"Enzo",surname:"Perri",slug:"enzo-perri",fullName:"Enzo Perri"},{id:"83499",title:"Dr.",name:"Cinzia",surname:"Benincasa",slug:"cinzia-benincasa",fullName:"Cinzia Benincasa"},{id:"124199",title:"Dr.",name:"Kaouther",surname:"Ben Hassine",slug:"kaouther-ben-hassine",fullName:"Kaouther Ben Hassine"},{id:"124200",title:"Dr.",name:"Naziha Grati",surname:"Kammoun",slug:"naziha-grati-kammoun",fullName:"Naziha Grati Kammoun"}],corrections:null},{id:"27025",title:"Olive Oil Composition: Volatile Compounds",doi:"10.5772/28512",slug:"oil-composition-volatiles",totalDownloads:6964,totalCrossrefCites:2,totalDimensionsCites:20,hasAltmetrics:0,abstract:null,signatures:"Marco D.R. 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",isbn:"978-1-83768-039-9",printIsbn:"978-1-83768-038-2",pdfIsbn:"978-1-83768-040-5",doi:null,price:0,priceEur:0,priceUsd:0,slug:null,numberOfPages:0,isOpenForSubmission:!0,isSalesforceBook:!1,isNomenclature:!1,hash:"000e31f2e2f7295805e9a3864158ad63",bookSignature:"Dr. Shafizan Mohamed and Dr. Shazleen Mohamed",publishedDate:null,coverURL:"https://cdn.intechopen.com/books/images_new/11437.jpg",keywords:"Digital Parenting, Digital Education, Screen Time, Family Communication, Smart Technologies, Global Village, Crisis Communication, Emergency Management, Fake News, Media Ideologies, Crowdsourcing, Information Security",numberOfDownloads:null,numberOfWosCitations:0,numberOfCrossrefCitations:null,numberOfDimensionsCitations:null,numberOfTotalCitations:null,isAvailableForWebshopOrdering:!0,dateEndFirstStepPublish:"May 11th 2022",dateEndSecondStepPublish:"June 8th 2022",dateEndThirdStepPublish:"August 7th 2022",dateEndFourthStepPublish:"October 26th 2022",dateEndFifthStepPublish:"December 25th 2022",dateConfirmationOfParticipation:null,remainingDaysToSecondStep:"14 days",secondStepPassed:!1,areRegistrationsClosed:!1,currentStepOfPublishingProcess:2,editedByType:null,kuFlag:!1,biosketch:"Shafizan Mohamed is an assistant professor in the Communications Department, International Islamic University of Malaysia. She holds a Ph.D. in Media Studies from Monash University, Australia. She is the author, co-author, and editor of several books, journal articles, and monographs on media and communication. Her research covers new media theory, political communication, health communication, and digital media literacy. Her recent research projects examined digital media skills.",coeditorOneBiosketch:"Dr. Shazleen Mohamed is the Head of Postgraduate Studies at Universiti Teknologi MARA's Faculty of Communication and Media Studies. She is an expert in broadcasting and media studies, with a particular emphasis on children's television reception. She has more than 20 years of experience in media academia as well as industry. She has also authored numerous articles for scholarly and public journals. She is currently the recipient of a research grant to examine the growth of content creation in Malaysian medi",coeditorTwoBiosketch:null,coeditorThreeBiosketch:null,coeditorFourBiosketch:null,coeditorFiveBiosketch:null,editors:[{id:"302450",title:"Dr.",name:"Shafizan",middleName:null,surname:"Mohamed",slug:"shafizan-mohamed",fullName:"Shafizan Mohamed",profilePictureURL:"https://mts.intechopen.com/storage/users/302450/images/system/302450.jpg",biography:"Shafizan Mohamed is an assistant professor in the Communications Department, International Islamic University of Malaysia. She holds a Ph.D. in Media Studies from Monash University, Australia. She is the author, co-author, and editor of several books, journal articles, monographs, and newspaper articles on media and communication. Her research covers the fields of new media theory, political communication, health communication, and digital media literacy. Her two recent research projects examined the digital media skills of underprivileged children and the communication of vaccination in mainstream and social media. Both studies are based on the experience of Malaysia. Aside from teaching and research, Dr. Mohamed loves food, music, and interior design.",institutionString:"International Islamic University Malaysia",position:null,outsideEditionCount:0,totalCites:0,totalAuthoredChapters:"0",totalChapterViews:"0",totalEditedBooks:"0",institution:{name:"International Islamic University Malaysia",institutionURL:null,country:{name:"Malaysia"}}}],coeditorOne:{id:"470881",title:"Dr.",name:"Shazleen",middleName:null,surname:"Mohamed",slug:"shazleen-mohamed",fullName:"Shazleen Mohamed",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0033Y00003SZ04xQAD/Profile_Picture_2022-04-29T11:29:48.png",biography:null,institutionString:"Universiti Teknologi MARA",position:null,outsideEditionCount:0,totalCites:0,totalAuthoredChapters:"0",totalChapterViews:"0",totalEditedBooks:"0",institution:{name:"Universiti Teknologi MARA",institutionURL:null,country:{name:"Malaysia"}}},coeditorTwo:null,coeditorThree:null,coeditorFour:null,coeditorFive:null,topics:[{id:"23",title:"Social Sciences",slug:"social-sciences"}],chapters:null,productType:{id:"1",title:"Edited Volume",chapterContentType:"chapter",authoredCaption:"Edited by"},personalPublishingAssistant:{id:"466997",firstName:"Patricia",lastName:"Kerep",middleName:null,title:"Ms.",imageUrl:"https://mts.intechopen.com/storage/users/466997/images/21565_n.jpg",email:"patricia@intechopen.com",biography:"As an Author Service Manager my responsibilities include monitoring and facilitating all publishing activities for authors and editors. 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Venkateswarlu",coverURL:"https://cdn.intechopen.com/books/images_new/371.jpg",editedByType:"Edited by",editors:[{id:"58592",title:"Dr.",name:"Arun",surname:"Shanker",slug:"arun-shanker",fullName:"Arun Shanker"}],productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}},{type:"book",id:"72",title:"Ionic Liquids",subtitle:"Theory, Properties, New Approaches",isOpenForSubmission:!1,hash:"d94ffa3cfa10505e3b1d676d46fcd3f5",slug:"ionic-liquids-theory-properties-new-approaches",bookSignature:"Alexander Kokorin",coverURL:"https://cdn.intechopen.com/books/images_new/72.jpg",editedByType:"Edited by",editors:[{id:"19816",title:"Prof.",name:"Alexander",surname:"Kokorin",slug:"alexander-kokorin",fullName:"Alexander Kokorin"}],productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}},{type:"book",id:"314",title:"Regenerative Medicine and Tissue Engineering",subtitle:"Cells and Biomaterials",isOpenForSubmission:!1,hash:"bb67e80e480c86bb8315458012d65686",slug:"regenerative-medicine-and-tissue-engineering-cells-and-biomaterials",bookSignature:"Daniel Eberli",coverURL:"https://cdn.intechopen.com/books/images_new/314.jpg",editedByType:"Edited by",editors:[{id:"6495",title:"Dr.",name:"Daniel",surname:"Eberli",slug:"daniel-eberli",fullName:"Daniel Eberli"}],productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}},{type:"book",id:"57",title:"Physics and Applications of Graphene",subtitle:"Experiments",isOpenForSubmission:!1,hash:"0e6622a71cf4f02f45bfdd5691e1189a",slug:"physics-and-applications-of-graphene-experiments",bookSignature:"Sergey Mikhailov",coverURL:"https://cdn.intechopen.com/books/images_new/57.jpg",editedByType:"Edited by",editors:[{id:"16042",title:"Dr.",name:"Sergey",surname:"Mikhailov",slug:"sergey-mikhailov",fullName:"Sergey Mikhailov"}],productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}},{type:"book",id:"1373",title:"Ionic Liquids",subtitle:"Applications and Perspectives",isOpenForSubmission:!1,hash:"5e9ae5ae9167cde4b344e499a792c41c",slug:"ionic-liquids-applications-and-perspectives",bookSignature:"Alexander Kokorin",coverURL:"https://cdn.intechopen.com/books/images_new/1373.jpg",editedByType:"Edited by",editors:[{id:"19816",title:"Prof.",name:"Alexander",surname:"Kokorin",slug:"alexander-kokorin",fullName:"Alexander Kokorin"}],productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}}]},chapter:{item:{type:"chapter",id:"19680",title:"Isotopic Uranium and Plutonium Denaturing as an Effective Method for Nuclear Fuel Proliferation Protection in Open and Closed Fuel Cycles",doi:"10.5772/17822",slug:"isotopic-uranium-and-plutonium-denaturing-as-an-effective-method-for-nuclear-fuel-proliferation-prot",body:'The paper addresses to the problems related with protection of the existing and advanced nuclear fuel types against unauthorized proliferation via introduction of some admixtures into their composition. So, the task may be defined as follows: these admixtures must create the barriers difficult to overcome for the use of nuclear fuels in nuclear explosive devices (NED) but, at the same time, these admixtures must preserve (or even enhance) energy potential of nuclear fuels for further peaceful use at civilian nuclear power plants (NPP). Such an approach to proliferation protection of nuclear fuels is often called as an isotopic denaturing. The term “isotopic denaturing” is used to designate any artificial changes in isotopic composition of chemical element which can give some new desirable properties to this element.
As is known, main raw materials for NPP are natural uranium and thorium. Natural uranium contains 0.71% 235U, and self-sustainable chain fission reaction (CFR) may be maintained by thermal neutrons provided rather large amounts of uranium, graphite or heavy water are available. As for natural thorium, there are no fissile isotopes, like 235U, in its composition at all. So, manufacturing of a small-size NED with uranium charge requires application of isotopic enrichment in order to produce highly enriched (weapon-grade) uranium (HEU, 90-95% 235U). Some artificial fissile materials (plutonium or 233U) can be used as a nuclear charge but they may be produced only under neutron irradiation of natural uranium or thorium in nuclear reactors.
At present, nuclear reactors apply uranium fuels of various enrichments. So, isotopic composition of uranium-based fuel for civilian NPP takes an intermediate position between natural uranium and HEU. Conversion of civilian uranium fuel into HEU, or weapon-grade uranium, requires application of isotopic re-enrichment operations.
Plutonium, suitable element for NED, is produced by nuclear reactors in the process of their operation. As is known, weapon-grade plutonium (WGPu) consists mainly of 239Pu with small content of 240Pu (4-7%) and negligible amounts of heavier plutonium isotopes. WGPu may be produced in the special reactors with short irradiation cycle. Power reactors at NPP are operated with relatively long irradiation cycle and, thus, with high fuel burn-up. So, plutonium produced in power reactors (reactor-grade plutonium, RGPu) contains the larger amounts of heavier plutonium isotopes. Lengthy irradiation of uranium fuel can change significantly isotopic composition of uranium (in particular, isotopes 232U and 236U do appear). As an example, isotopic composition of uranium fuel (initial enrichment - 4.4% 235U) after LWR operation up to fuel burn-up of 4% HM is presented in Table 1. Thus, uranium fuel may be used to produce fissile materials, suitable for NED, in nuclear reactors but it requires application of some special operations.
Composition of fresh fuel | Composition of uranium and plutonium in spent fuel, % (fuel burn-up - 4 % HM) | |||||
4.4 % 235U | Uranium | 232U | 235U | 236U | 238U | |
1.4symbol 215 \\f "Symbol" \\s 9×10-9 | 1.26 | 0.59 | 98.15 | |||
Plutonium (RGPu) | 238Pu | 239Pu | 240Pu | 241Pu | 242Pu | |
1.7 | 58.0 | 22.3 | 12.3 | 5.7 |
Isotopic compositions of uranium and plutonium in spent LWR fuel
Artificial fissile uranium isotope 233U, high-efficiency material for NED, may be produced by neutron irradiation of natural thorium. However, undesirable by-products are generated in this process including other uranium isotopes, namely 232U, 234U and 236U. In particular, light uranium isotope 232U can complicate significantly any operations with produced uranium.
Radiochemical reprocessing of spent nuclear fuel (SNF) includes extraction of radioactive fission products (FP) whose intense emission of ionizing radiation creates a protective barrier against unauthorized access to fissile materials. So, SNF reprocessing can be regarded as an operation which can remove (or, at least, weaken under incomplete purification) the radiation barrier. SNF partitioning into separate elements or groups of elements can facilitate diversion of fissile materials. In order to reduce the diversion risk, appropriate protective actions should be undertaken. In addition to the organizing measures related with physical protection of nuclear enterprises and technological control, the following barriers against diversion of fissile materials should be considered:
Radiation barrier mainly formed by FP. Such a barrier can be formed in the process of the reactor operation and by a special short-term irradiation of fresh fuel assemblies in the dedicated nuclear facilities. Radiation background of fissile materials is one else component of the radiation barrier.
Incomplete SNF purification from radioactive FP can result in intense radiation fields which make very difficult any further operations with extracted fuel.
Isotopic dilution of 235U, i.e. the use of relatively low-enriched uranium (LEU).
Incomplete separation of uranium from plutonium (or full exclusion of any technological procedures needed for uranium-plutonium separation) in the course of SNF reprocessing. This measure makes it impossible to use these materials directly in NED.
Application of automatic remote technology for fuel, fuel rods and fuel assemblies fabrication. This measure can complicate access to fissile materials.
Dilution (or denaturing) of fissile materials by their isotopes which can complicate the use of fissile materials in NED. A particular case of isotopic denaturing is a well-known dilution of 235U by 238U, i.e. the use of LEU fuel. Another example: neutron irradiation of mixed uranium-thorium fuel in nuclear reactors can produce fissile isotope 233U isotopically diluted by 238U.
If we consider fissile plutonium isotope 239Pu, then the heavier plutonium isotopes (mainly, 240Pu) play the same role of isotopic diluents. In addition, light plutonium isotope 238Pu is an intense source of spontaneous fission neutrons and intense source of thermal energy from -decays (half-life of 238Pu is equal to 87.7 years).
In thorium fuel cycle the same role may be played by 232U (half-life – 68.9 years).
In practice, the measures listed above may be used in combinations. For example, open fuel cycle of power LWR is provided with the following protective barriers:
Isotopic dilution (LEU fuel).
Intense radiation background caused mainly by FP.
SNF contains non-separated mixture of uranium and plutonium.
Just this set of protective barriers represents a basis for the USA standard on SNF proliferation protection (Spent Fuel Standard (USA National Academy of Sciences, 2000)).
As 232U and its neutron predecessor 231Pa are nuclides of low abundance, it seems reasonable to consider their properties in detail.
Basic nuclear properties of main uranium isotopes are presented in Table 2 (Reilly et al., 1991; OECD Nuclear Energy Agency, 1997). As it may be seen, some nuclear properties of 232U make it a valuable material for proliferation protection of uranium-based nuclear fuel.
232U | 234U | 235U | 238U | |
Half-life, years | 68.9 | 2.45105 | 7.04108 | 4.47109 |
Specific yield of -particles, 1/(gs) | 81011 | 2.3108 | 7.9104 | 1.2104 |
Mean energy of -particles, MeV | 5.3 | 4.76 | 4.4 | 4.19 |
Specific yield of spontaneous fission neutrons, 1/(g s) | 1.3 | 5.0210-3 | 2.9910-4 | 1.3610-2 |
Fission cross-section (En 0.0253 eV), barns | 77.15 | 0.465 | 583.2 | 1.210-5 |
Basic nuclear properties of main uranium isotopes
232U is a starting isotope for chain of radioactive decays, and some 232U decay products (208Tl, 212Bi) emit high-energy gamma-radiation (2.6 MeV and 1.8 MeV, respectively) that improves detectability of 232U-containing nuclear materials (Gilfoyle & Parmentola, 2001) and complicates radiation conditions, especially for any unauthorized actions. Nuclear properties of main 232U decay products are presented in Table 3.
Decay products | 228Th | 224Ra | 220Rn | 216Po | 212Bi | 212Po |
Half-life | 1.91 years | 3.62 days | 55.6 sec | 0.145 sec | 1.01 hours | 310-7 sec |
Energy of -particles, MeV (relative intensity) | 5.42 (71.7%) 5.34 (27.6%) | 5.69 (94.9%) 5.45 (5.1%) | 6.29 (100%) | 6.78 (100%) | 6.09 (9.7%) 6.05 (25.2%) | 8.78 (100%) |
232U decay products, emitters of -particles
Like 238U, isotope 231Pa can play a role of a fertile nuclide which is not split by thermal neutrons but promotes breeding of fissile materials. Dependencies of radiative capture cross-sections on neutron energy are presented in Fig. 1 for isotopes 238U and 231Pa.
Dependency of radiative capture cross-sections on neutron energy for 238U and 231Pa
The following two important aspects should be noted here. Firstly, within thermal energy range, 231Pa is a superior neutron absorber as compared with 238U. For example, radiative capture cross sections of thermal neutrons (En 0.0253 eV) for these two isotopes are equal to: σc(231Pa) 227 barns, σc(238U) 3 barns. So, the presence of 231Pa in fuel composition can promote effective generation of fissile isotopes 232U and 233U. Secondly, there is a rather large energy distance between capture resonances of 238U and 231Pa. Capture resonances of 231Pa belong to relatively low energies (below 100 eV). This means the presence of 231Pa in fuel composition can depress thermal region in energy spectrum of neutrons (see Fig. 2).
It can be seen that, although neutron energy spectrum in VVER-1000 contains a certain fraction of thermal neutrons, introduction of 231Pa into fuel composition can remove the thermal fraction completely. That is why stainless steel may be used here as a structural material. Indeed, the absence of thermal fraction in neutron spectrum does not result in additional neutron loss but fuel rods can keep their ability for working up to the higher values of fuel burn-up than with zirconium-based alloys.
Now let us consider nuclear properties of 232U, product of neutron capture by 231Pa and rapid -decay of 232Pa (T1/2 (232Pa) 1,3 days (Babichev et al.,1991)). Like 235U, isotope 232U is a fissile nuclide. Dependencies of fission cross-sections on neutron energy are presented in Fig. 3 for isotopes 235U and 232U.
It can be seen that, within thermal energy range, fission cross-sections of 232U are substantially lower than those for 235U while radiative capture cross-sections of these isotopes are comparable each other. For example, radiative capture cross sections of thermal neutrons (En 0.0253 eV) for these two isotopes are equal to: σc(232U) 73 barns, σc(235U) 99 barns. So, neutron-multiplying properties of 232U are inferior to those of 235U within thermal energy range.
This conclusion can be confirmed by Fig. 4 which demonstrates energy dependency of (νef - 1), i.e. the number of excess fission neutrons per one absorbed neutron.
235U looks superior to 232U within thermal energy range but quite another situation takes place in resonance range. So, it may be expected that introduction of 231Pa into uranium-based fuel composition with aim to increase fuel burn-up will be more efficient just in resonance neutron spectrum.
effect on energy spectrum of neutrons
Dependency of fission cross-sections on neutron energy for isotopes 235U and 232U
Energy dependency of the number of excess fission neutrons per one absorbed neutron for isotopes 235U and 232U
Presently, there are different points of view on future development of nuclear fuel cycles. Some countries (USA, Canada, Germany and Sweden) are implementing in practice an open nuclear fuel cycle (Fig. 5) that does not foresee a radiochemical SNF reprocessing in the visible future. One of the reasons for this choice is a wish of decreasing a risk of nuclear weapon proliferation. SNF may be only converted into the forms suitable for long-term safe storage. However, such a strategy of nuclear power development has already resulted in large SNF stockpiles, potentially dangerous nuclear materials (NM). So, the preferable option for future development of nuclear power consists in transition to the closed fuel cycles with SNF reprocessing, separation of radioactive FP and recycling of residual fuel.
Open fuel cycle
LEU is a fresh fuel for open nuclear fuel cycle. Plutonium in spent fuel assemblies is protected by intense gamma-radiation of fission products (Fig. 5). That is why unirradiated materials are more vulnerable for unauthorized proliferation.
Isotopic uranium denaturing may be regarded as an effective method for upgrading self-protection of unirradiated uranium-containing materials. The term “isotopic denaturing” is used conventionally for designation of any artificial changes in natural isotopic composition of a chemical element with aim to give him some new, desirable properties. In practice, uranium may be denatured by the following two ways: direct introduction of intense radioactive isotope 232U into uranium fuel composition or direct introduction of relatively weaker radioactive isotope 231Pa into uranium fuel composition. 231Pa is a neutron predecessor of 232U, main isotope of uranium denaturing. So, only short-term pre-irradiation of fresh fuel assemblies in the research reactors may be sufficient to produce proliferation resistant fuel assemblies, suitable even for export deliveries.
Along with progress in development of high-efficiency enriching technologies, potential threat of LEU diversion and re-enrichment up to the weapon-grade level excites more and more apprehensions. These reasons indicate that, besides reduction of uranium enrichment below 20% 235U, other measures may be also required to upgrade LEU self-protection against its unauthorized re-enrichment. Taking into consideration the growing world-wide scope of LEU utilization, including LEU with enrichment in the vicinity of the upper boundary (20% 235U), high LEU vulnerability to unauthorized re-enrichment must be recognized. Particular apprehensions are related with 20%-uranium. So, some additional actions should be undertaken to protect LEU against its unauthorized re-enrichment.
The effects of 232U introduction into LEU are caused by the following specific properties of 232U (see Table 2):
Good neutron-multiplying properties of 232U (Ganesan et al., 2002) and its neutron predecessor 231Pa make it possible to extend time period of continuous reactor operation without refueling up to the values comparable with the reactor life-time. As a result, unauthorized extraction of plutonium from spent fuel assemblies becomes unfeasible.
It is impossible to remove 232U from denatured uranium without application of sophisticated and expensive isotope separation technologies.
232U is a neutron source from spontaneous fission reactions and a source of high-energy -particles. Alpha-particles emitted by 232U are able to dissociate molecules of uranium hexafluoride and, thus, could make it practically impossible to re-enrich denatured uranium up to the weapon-grade level. Besides, -particles are able to initiate (,n)-reactions with impurities of light elements (LE) and, thus, intensify internal neutron generation. Growth of neutron background in the re-enriching process of LEU-uranium containing 0.10.5% 232U can decrease the CFR energy yield by three orders of magnitude. In essence, NED with such a re-enriched uranium is a “dirty” bomb only. Thus, export deliveries of LEU-based fuel assemblies to foreign NPP receive an additional proliferation barrier.
One of specific features in operation of nuclear power reactors consists in a necessity to perform regular refuelings. This necessity is caused by the following effects: depletion of fissile materials, FP accumulation, potential rupture of fuel cladding with intense release of radioactive materials. LWR, the mostly spread type of power reactors, requires refueling every 1-2 years, when fuel burn-up reaches 4-6% HM.
Extension of fuel life-time up to relatively long time periods (several decades, for instance) can reduce drastically the number of refuelings or exclude them at all. Reduction or full exclusion of refueling procedures decreases the demands for fresh fuel and decreases quantity of SNF discharged per unit of produced energy. Those reactors, which are capable to operate for a sufficiently long time without any refueling, may be used as the only energy source in remote regions, at the floating NPP, as energy source for space investigations (research bases on the Moon or Mars, cosmic flights into the outer space). Our studies demonstrated that introduction of 231Pa into LWR fuel composition could extend significantly the fuel life-time and reach ultra-high fuel burn-up.
It should be noted that achievability of ultra-high fuel burn-up was studied here only from the standpoint of neutron-multiplying properties of advanced fuel compositions. The problems of suitable structural materials, evolution of their strength properties and durability for a long fuel life-time are not analyzed here. At present, maximal fuel burn-up (about 30% HM) was achieved in the research fast reactor BOR-60 (Grachev et al., 2003). It may be expected that the higher values of fuel burn-up could be achieved if the following operations would be multiply carried out: partial fuel burn-up (near to the practically achievable value of 30% HM), application of DUPIC-technology for removal of gaseous and volatile FP, re-fabrication of fresh fuel pellets.
In this section we compared time evolutions of neutron-multiplying properties in two isotopic chains: traditional chain that starts from 232Th (232Th → 233U → 234U → …) and non-traditional chain that starts from 231Pa (231Pa → 232U → 233U → …) (see Fig. 6). Radiative capture cross-sections σc and fission cross-sections σf were calculated for a typical neutron spectrum of VVER-1000 (β-decays were not taken into account).
Chains of isotopic transformations (232Th → 233U → 234U → …) and (231Pa → 232U → 233U → …) (neutron spectrum of VVER-1000)
It can be seen that neutron-multiplying properties in non-traditional chain are gradually improved: the starting isotope 231Pa is a neutron absorber, fission cross-section of the second isotope 232U prevails over its capture cross-section, and the third isotope 233U is a well-fissionable material. So, non-traditional chain represents the combination of two consecutive fissionable isotopes (232U and 233U) while, in traditional chain, the third isotope 234U is a neutron absorber only.
Thus, in non-traditional chain, parasitic neutron absorption by FP and depletion of fissile materials during the reactor operation can be partially compensated by 231Pa feeding. This makes it possible to talk about a possibility for substantial extension of fuel life-time and achievability of ultra-high fuel burn-up. By the way, in traditional LWR fuel, the negative effects caused by FP accumulation and depletion of fissile materials are compensated by 238U(n,γ)239Pu chain significantly weaker than by 231Pa(n,γ)232U(n,γ)233U chain in non-traditional fuel because of lower capture cross-sections: σc(238U) 0.9 barns, σc(231Pa) 43 barns.
So, it can be concluded that non-traditional chain (231Pa → 232U → 233U → …) appears to be more attractive from the standpoint of neutron-multiplying properties (as a consequence, from the standpoint of extended fuel life-time or achievability of ultra-high fuel burn-up) in comparison with traditional chain (232Th → 233U → 234U → …) due to the following reasons:
Combination of two consecutive well-fissionable isotopes (232U and 233U).
High rate of their generation from the starting isotope 231Pa, whose neutron capture cross-section is larger substantially than that for the starting nuclide 232Th in traditional chain of isotopic transformations.
It is noteworthy that 231Pa may be regarded, to a certain extent, as a burnable neutron poison: for fuel life-time 231Pa is burnt up to 80% and converted into well-fissionable isotopes, neutron capture cross-section of 231Pa is substantially larger than that of fertile isotope 232Th.
As is known, the existing LWRs are characterized by thermal neutron spectrum. In advanced LWR designs, for example, in LWR with supercritical coolant parameters (SCLWR), different regions of the reactor core are characterized by different neutron spectra depending on coolant density. Thermal spectrum prevails within the core region containing dense coolant (γ 0.72 g/cm3) while resonance neutron spectrum dominates within the core region containing coolant of the lower density (γ 0.1 g/cm3) (Kulikov, 2007).
Reasonability of 231Pa introduction into fuel composition for the cases of thermal and resonance neutron spectra is analyzed in the next section.
Numerical analyses of fuel depletion process were carried out with application of the computer code SCALE-4.3 (Oak Ridge National Laboratory, 1995) and evaluated nuclear data file ENDF/B-V for elementary cells of VVER-1000. The only exception consisted in the use of martensite steel MA956 (elemental composition: 74,5% Fe, 20% Cr, 4,5% Al, 0,5% Ti and 0,5% Y2O3) instead of zircaloy as a fuel cladding material. Substitution of martensite steel for zirconium-based cladding is caused by the higher values of fuel burn-up.
Traditional (232Th-233U) and non-traditional (231Pa-232Th-233U) fuel compositions were compared for the case of thermal neutron spectrum (coolant density – 0.72 g/cm3). Infinite neutron multiplication factor K∞ is shown in Fig. 7 as a function of fuel burn-up.
It can be seen that substitution of 231Pa for 232Th decreases K∞ at the beginning of cycle, i.e. decreases an initial reactivity margin to be compensated. This effect is caused by different capture cross-sections of these isotopes - 231Pa is a significantly stronger neutron absorber than 232Th. In parallel, thanks to the larger capture cross-section of 231Pa, intense breeding of two consecutive well-fissionable isotopes (232U and 233U) takes place. So, gradual introduction of 231Pa into fuel composition results in the smoother relaxation of neutron multiplication factor in the process of fuel burn-up.
Acceptable fraction of 231Pa in non-traditional fuel composition is limited by the value of neutron multiplication factor (above unity) at the beginning of cycle. So, the effects caused by introduction of 231Pa may take place only in those fuel compositions where fraction of main fissile isotope is sufficiently large. For example, fraction of main fissile isotope 233U may be increased up to the level corresponding to the situation when neutron multiplication factor at the beginning of cycle is equal to about 1.10 at full replacement of 232Th by 231Pa. The calculations showed that this condition may be satisfied at maximal 233U fraction about 30%. Evolution of neutron multiplication factor in the process of fuel burn-up is presented in Fig. 8 for traditional and non-traditional fuel compositions.
effects on fuel burn-up in thermal neutron spectrum
Achievability of ultra-high fuel burn-up by introduction of 231Pa (thermal neutron spectrum)
As is seen from Fig. 8, traditional thorium-based fuel (30% 233U + 70% 232Th) provides rather high reactivity margin (K∞ (BOC) ≈ 1,9) with achievable value of fuel burn-up about 29% HM. Introduction of 231Pa into fuel composition decreases initial reactivity margin but, at the same time, increases fuel burn-up. If 232Th is completely replaced by 231Pa, i.e. (30% 233U + 70% 231Pa) fuel composition is analyzed, then neutron multiplication factor remains practically unchanged in the vicinity of unity for a full duration of fuel life-time. This means that the negative effects from neutron absorption by FP and depletion of fissile isotope are almost completely compensated by breeding of secondary fissile isotopes from 231Pa. In this case, about 80%-part of 231Pa is converted into secondary fissile isotopes which can provide ultra-high fuel burn-up (near to 57% HM).
If fuel loading in such a reactor is similar to the fuel loading of VVER-1000 (about 66 tons), then achievable value of fuel life-time is near to 40 years for the reactor power of 3000 MWt.
It is interesting to note that 235U as well as 233U may be used to achieve ultra-high fuel burn-up. Moreover, 235U option looks very attractive because of two reasons: firstly, 235U resources are more available than resources of 233U, and, secondly, achievement of the same fuel burn-up will require lower quantity of 231Pa, artificial isotope to be produced in the dedicated nuclear power facilities.
Traditional (232Th-233U) and non-traditional (231Pa-232Th-233U) fuel compositions were compared for the case of resonance neutron spectrum (coolant density – 0.1 g/cm3). Infinite neutron multiplication factor K∞ is shown in Fig. 9 as a function of fuel burn-up.
effects on fuel burn-up in resonance neutron spectrum
Comparison of the curves presented in Figs. 7, 9 allows us to conclude that introduction of 231Pa into fuel composition is more preferable from the standpoint of higher fuel burn-up in the case of resonance neutron spectrum. This conclusion can be explained by better neutron-multiplying properties of 232U just in resonance neutron spectrum as compared with thermal neutron spectrum (see Fig. 4).
As it follows from Fig. 9, introduction of only 12% 231Pa increased fuel burn-up twice. Neutron multiplication factor at the beginning of cycle increased too, i.e. neutron-multiplying properties of fuel composition became better.
Like previous analysis, fraction of main fissile isotope 233U may be increased up to the level corresponding to the situation when neutron multiplication factor at the beginning of cycle is equal to about 1.10 at full replacement of 232Th by 231Pa. In addition, potential use of 235U instead of 233U was analyzed to evaluate a possibility for achieving ultra-high fuel burn-up.
So, numerical studies confirmed reasonability for introduction of 231Pa into fuel composition because this introduction results in reduction of initial reactivity margin and in substantial growth of fuel burn-up. Maximal positive effect from introduction of 231Pa may be observed in resonance neutron spectrum. Besides, introduction of 231Pa makes it possible to reach ultra-high fuel burn-up regardless of what main fissile isotope is used, 233U or 235U. In particular, (20% 233U + 80% 231Pa) fuel composition can reach fuel burn-up of 76% HM in resonance neutron spectrum (see Fig. 10).
Achievability of ultra-high fuel burn-up by introduction of 231Pa (resonance neutron spectrum)
On the one hand, introduction of 231Pa into fuel composition can provide small value of initial reactivity margin and high value of fuel burn-up. On the other hand, if relatively large 231Pa fraction is introduced into fuel composition, reactivity feedback on coolant temperature becomes positive, and safety of the reactor operation worsens.
Numerical studies demonstrated that, if maintenance of favorable reactivity feedback on coolant temperature during fuel life-time is a mandatory requirement, then, in thermal neutron spectrum, 231Pa fraction in fuel composition is limited by a quite certain value while, in resonance neutron spectrum, introduction of 231Pa is impossible at all. However, this conclusion is correct only for large-sized reactors, where neutron leakage is negligible.
So, only thermal neutron spectra should be considered to provide favorable reactivity feedback on coolant temperature. The results presented in Fig. 11 demonstrate a possibility for increasing fuel burn-up in thermal neutron spectrum by introduction of 231Pa into fuel composition.
Achievability of ultra-high fuel burn-up by introduction of 231Pa with conservation of favorable feedback on coolant temperature (thermal neutron spectrum)
As is known, fuel burn-up in VVER-1000 can reach a value about 4% HM. Introduction of 231Pa and higher contents of 235U can increase fuel burn-up by a factor of 8 with the same initial reactivity margin, i.e. more powerful system of reactivity compensation is not required.
Requirement of favorable reactivity feedback on coolant temperature completely excludes any introduction of 231Pa into fuel composition in the case of large-sized reactors with resonance neutron spectra. But, introduction of 231Pa into fuel composition of small-sized reactors does not worsen safety of the reactor operation because of relatively large neutron leakage. This indicates that the mostly attractive area for 231Pa applications is a small nuclear power including small-sized NPP for remote regions, for the floating NPP, for space stations on the Moon or Mars and for cosmic flights into the outer space.
The following conclusions can be made in respect of potential 231Pa applications:
Application of 231Pa as a burnable neutron poison can reduce initial reactivity margin and increase fuel burn-up.
Introduction of 231Pa into fuel composition makes it possible to reach ultra-high fuel burn-up (above 30% HM) both in thermal and resonance neutron spectra.
The actual problem of 231Pa production in significant amounts should be resolved.
NPP operation in open fuel cycle results in accumulation of huge SNF stockpiles that represents a long-term hazard to the humankind. Ultimate SNF disposal is a difficult technical problem requiring large number of practically “eternal” deep underground repositories. That is why many various options for closure of nuclear fuel cycle (NFC) are currently under research and development including extraction of residual uranium, plutonium and minor actinides from SNF.
As known, closed uranium-plutonium NFC includes reprocessing and recycling of nuclear fuel and evokes a lot of contradictory opinions with respect to potential risk of plutonium proliferation. This connected with two points:
Although plutonium extracted from SNF of power reactors (for example, LWR of PWR, BWR or VVER type) is not the best material for nuclear weapons, nevertheless it can be used in NED of moderate energy yield (Mark, 1993).
Recycled plutonium will be disposed at the facilities of closed NFC, and this will increase the probability of it using for illegal aims (diversion, theft).
Under these conditions, the absence of any internationally coordinated plan concerning the utilization or ultimate SNF disposal enforced the leading nuclear countries to undertake the steps directed to strengthening the nonproliferation regime (IAEA safeguards, Euratom\'s embargo on the export of SNF reprocessing technology). But several countries, in the first turn the USA, refused from deployment of breeder reactors which are intended for operation in closed NFC, and focused at once-through NFC. On the other hand, the social demand of solving excess fissile materials (plutonium, the first of all) problem which have both civil and military origins, stimulated carrying out the research on plutonium utilization in MOX-fuel. At the same time, the studies of advanced NFC protected against uncontrolled proliferation of fissile materials have been initiated.
Specialists from ORNL (USA) investigated the ways for introduction of -radiation sources into fresh fuel (Selle et al., 1979). Sixty-four -active radionuclides were selected and studied as candidates for admixing into fresh fuel (see Fig. 12).
Closed (U-Pu)-fule cycle protected (ORNL, USA)*
Radionuclides 137Cs (T1/2 30 years) and 60Co (T1/2 5.27 years) appeared the most preferable candidates. But cesium is a volatile element, and it can be easily removed from fuel by heating up. Intensity of -radiation emitted by 60Co rapidly relaxes.
Specialists from LANL (USA) proposed the advanced version of the international NFC that enhances proliferation resistance of plutonium (Cunningham et al., 1997). This proposal constituted a basis for the US President’s initiative on the Global Nuclear Energy Partnership (GNEP) that was supported by many countries (including Russia) with well-developed nuclear technologies (see Fig. 13).
According to the proposal, spent fuel assemblies discharged from power reactors of a country-user must be transported to the Nuclear Club countries for full-scale reprocessing. Extracted plutonium and minor actinides must be incinerated in the reactors placed on the territory of the International nuclear technology centers. Plutonium is not recycled in power reactors of a country-user. The Nuclear Club countries provide fresh LEU fuel deliveries into a country-user.
Open fuel cycle protected (LANL, USA)
Upon exhaustion of rich and cheap uranium resources, nuclear power has to use artificial kinds of fresh fuel (plutonium, 233U or their mixtures). The GNEP initiative does not consider this opportunity. It is proposed to use such power reactors which are able to work without refueling for 15-20 years. After this time interval they must be returned to the Nuclear Club countries for SNF discharging and reprocessing and for insertion of fresh fuel. The concentrated incineration of plutonium and minor actinides in the International nuclear technology centers can lead to unacceptably large local release of thermal energy with unpredictable negative environmental and climatic effects. As for reactors with long-life cores, these are small and medium-sized power reactors. Besides, during transportation and mounting, they can be very attractive sources of plutonium in amounts large enough for manufacturing of several dozens of nuclear bombs.
Some nuclear properties of 238Pu make this isotope a valuable material for proliferation protection of uranium-plutonium fuel. Firstly, 238Pu is an intense source of thermal energy (T1/2 87 years, specific heat generation - 570 W/kg). So, introduction of 238Pu into plutonium creates almost insuperable barrier to manufacturing of even primitive implosion-type NED. Plutonium heating up by isotope 238Pu can provoke undesirable phase transitions and thermal pyrolysis of conventional explosives applied for compression of central plutonium charge. Secondly, 238Pu is an intense source of spontaneous fission neutrons, even more intense than 240Pu. As a consequence, probability of premature CFR initiation in NED sharply increases while energy yield of nuclear explosion drastically drops down to the levels comparable with energy yield of conventional explosives. Thus, LWR MOX-fuel cycle with ternary fuel compositions (Np-U-Pu) is characterized by enhanced proliferation resistance.
Like uranium, plutonium can be isotopically denatured by two ways: either direct introduction of intensely radioactive isotope 238Pu into MOX-fuel composition or introduction of relatively low intense radioactive isotope 237Np into MOX-fuel composition. 237Np is the nearest neutron predecessor of main denaturing isotope 238Pu. So, only short-term pre-irradiation of fresh MOX-fuel assemblies would be sufficient to produce proliferation resistant fuel assemblies, suitable even for export deliveries to any countries.
It is proposed that the equilibrium isotope vectors are obtained for MOX-fuel circulating between LWR, spent fuel reprocessing as fuel manufacturing facilities. The fuel feed includes isotopes 237Np, 238Pu and 239Pu is produced in Hybrid Thermonuclear Installation (HTI) blankets.
Using the code GETERA (Belousov et al., 1992) for cell calculations of fuel burn-up, Pu isotopic compositions of MOX-fueled PWR were determined for moments of the beginning and end of cycle. 238Pu fraction in plutonium was adopted to be an index of Pu protection against uncontrolled proliferation. It means that the impact of higher plutonium isotopes on neutronics of chain reaction in imploded plutonium charge of NED was not taken into account.
The fuel being loaded in PWR may be considered as material consisting of two parts: the first part includes equilibrium composition of 238U and plutonium isotopes produced by 238U while the second part ("feed part of fuel") includes equilibrium composition of 237Np, 238Pu and other plutonium isotopes produced entirely by the feed. Equilibrium contents of 238Pu in plutonium of PWR fuel depending on 238Pu contents in plutonium of feed (with different 237Np fractions in "feed part of fuel") for equilibrium multi-cycle operation regime are presented in Fig. 14.
The plot region situated under the bisectrix B is a region where plutonium protection in feed is higher than plutonium protection in fuel. Respectively, the plot region situated above the bisectrix B is a region where plutonium protection in fuel is higher than that in feed. The curves of this figure characterize the correlation between plutonium protection levels in feed and fuel when the "feed part of fuel" contains 237Np in addition to plutonium. Basing on these data, it is possible to select the appropriate equilibrium regime of NFC.
Proper selection of the feed compositions, i.e. fractions of 238Pu and 237Np, makes it possible to attain the same level of fuel plutonium protection for various combinations of 238Pu and 237Np content in feed. For example, 32%-level of fuel plutonium protection can be attained in case of feed containing (0% 237Np, 52% 238Pu) or (20% 237Np, 43% 238Pu) or (40% 237Np, 32% 238Pu). The latter option corresponds to equal level of plutonium protection both in fuel and in feed. The line "S" that connects the right ends of the curves shown in Fig. 14 may be regarded as an "ultimate option" of the (Np-U-Pu) NFC considered here. The points of this line correspond to particular option of the (Np-U-Pu) NFC where 238U is absent in fuel composition, and its fertile functions passed to 238Pu and 237Np. So, this NFC may be called as a (Np-Pu) NFC. In this NFC the highest fuel Pu protection level (65% 238Pu) can be reached with feed Pu protection of 90% 238Pu. As known, the IAEA safeguards are not applied to plutonium containing 80% 238Pu or more (Rolland-Piegue, 1995; Willrich & Taylor, 1974; Massey & Schneider, 1982).
Proliferation resistance of plutonium in fuel as function of proliferation resistance of plutonium in feed and 237Np content in "feed" part of fuel. B - bisectrix.
Inherent heat generation of plutonium is considered as a significant factor of its protection. The rates of inherent heat generation for various feed compositions are presented in Table 4. Here, the rates of specific heat generation for weapons-grade plutonium (WGPu) and reactor-grade plutonium (RGPu) are presented as well.
238Pu/Pu in fuel and in feed | |||||
( Np/(Np + Pu) in feed ) | |||||
Generation | WG Pu | RG Pu | 17% (7%) | 33% (15%) | 44% (19%) |
qPu, W/kg Pu | 2.3 | 13. | 97 | 186 | 248 |
nsfPu, 106(n/sec)/kg Pu | 0.06 | 0.38 | 0.71 | 1.06 | 1.30 |
qfuel, W/kg fuel | --- | --- | 14.9 | 41.2 | 99.5 |
nsffuel, 106(n/sec)/kg fuel | --- | --- | 0.11 | 0.24 | 0.53 |
Feed 237Np/238Pu/239Pu, kg/(GWe*a) | --- | --- | 38 / 82 / 402 | 103 / 194 / 377 | 176 / 318 / 421 |
Decay heat generation (qPu) and neutron generation by spontaneous fissions (nsfPu) in LWR fuel with equal plutonium protection both in fuel and in feed.
Basing on the results shown above, it can be concluded that denatured fuel plutonium containing more than 25% 238Pu is characterized by the internal heat generation which exceeds that of RGPu by more than order of magnitude and, by the larger extent, that of WGPu. In addition, denatured fuel plutonium is characterized by the higher neutron background caused by spontaneous fissions. The factors mentioned above enhance plutonium protection against its utilization in NED. The same factors complicate, to certain degree, the handling procedures with such a fuel in nuclear technologies.
Values of specific heat generation and neutron emission due to spontaneous fission of MOX-fuel being loaded for the equilibrium cycle options analyzed are shown in Table 4 also. For comparison, "dry" technology for handling with spent fuel assemblies may be applied if specific heat generation does not exceed 20-35 W/kg fuel. It may be also concluded that plutonium denaturing with 238Pu is restricted by thermal constraints imposed on permissible specific heat generation of fuel. The same tendency exists in connection with spontaneous neutrons emission. These constraints need to be taken into account in fuel fabrication, fuel rods and fuel assemblies manufacturing and transport operations. These complications of fuel management may be considered as certain "payment" for proliferation resistance of MOX-fuel cycle.
Actually speaking, the protection of plutonium in (Np-U-Pu)-fuel cycle is supposed to be enhanced due to addition 237Np and 238Pu into fuel. The degree of fissile nuclides protection depends mainly on magnitude of 238Pu fraction in plutonium. Meanwhile, 237Np itself can be also considered as a potential material for NED. For example, critical mass of 237Np (metal sphere, steel reflector) is about 55 kg (Koch et al., 1997). It’s ten times more than that of 239Pu. The magnitude of critical mass of 237Np is sensitive with respect of its dilution. For example, minimum critical mass of NpO2 is as much as 315 kg (Nojiri & Fukasaku, 1997; Ivanov et al. 1997). Besides, in fuel composition 237Np is present together with plutonium which is characterized by essential neutron source strength due to spontaneous fissions. Therefore, in order to apply extracted 237Np in NED it is needed to perform effective 237Np purification from plutonium (plutonium fraction is restricted by value of 10-4 - 10-3).
Good neutron-multiplying properties of 238Pu and its neutron predecessor 237Np make it possible to extend substantially time period for continuous reactor operation without refuelings. As a consequence, unauthorized extraction of plutonium from SNF becomes practically unfeasible.
Indeed, under reactor irradiation of (Np-U-Pu) fuel it is occurs the following “non-traditional” transition chain (see Fig. 15): 237Np 238Pu 239Pu ... A successive transition of these nuclides leads to enhancement of multiplication properties.
Actually, as it can be seen in Fig. 16, excess neutron generation per one absorption (eff-1) in 237Np is negative for neutrons of all energy range (excepting fast neutrons), positive for neutrons with En > 1 KeV for 238Pu and, as is known, essential positive one for 239Pu.
So, for (Np-U-Pu)-fuel the nuclides we are dealing with can be characterized as follows (Table 5).
At the same time, during irradiation in reactor core FP accumulation results in growth of neutron absorption. So, these tendencies can be counterbalanced and such fuel will be characterized by stabilized neutron-multiplying properties over long burning-up.
Burn-up calculations for mono-nitride fuel in cell of PWR-type reactor with heavy water as a coolant were performed by using code GETERA. The cell parameters were similar to that of VVER-1000 cell (see Table 6):
Chain of isotopic transformations in uranium-plutonium fuel cycle
237Np | 238Pu | 239Pu |
"Burnable poison" nuclide | Moderate fissile nuclide (En"/> 1 KeV) | Well-known fissile nuclide |
Characteristics of nuclides for (Np-U-Pu)-fuel
Fuel rod diameter | 9.1 mm |
Thickness of stainless steel cladding | 0.4 mm |
Coolant ( heavy water ) | D2O |
Water volume / fuel volume | 1.6 |
Fuel | Mono-nitride ( porosity - 30% ) |
Specific heat generation | 110 kW/l |
Cell parameters of PWR-type reactor
In Fig. 17 it is shown the dependence of K on fuel burn-up for various fuel compositions. For comparison it is demonstrated also a curve of K for LWR-UOX. It can be seen that, actually, there is possibility to attain fuel burn-up of 25-30%HM ( corresponding residence time is about 20-25 years.). It is worth-while mentioning that, according to papers (Ivanov et al. 1997; Bychkov et al. 1997) presented at the International Conference “GLOBAL’97”, vibro-packed MOX fuel in stainless steel cladding was irradiated in fast reactor BOR-60 (Russia) and it was obtained burn-up of 26% HM on standard fuel assemblies and burn-up of 32% HM in experimental fuel rods. No thermal-mechanical and physical-chemical fuel-cladding interaction was observed in any of the analyzed cross-sections.
Dependencies of excessive neutron number per one absorption (eff-1) on neutron energy for nuclides of uranium-plutonium fuel cycle
The results mentioned above referred to so-called "ultimate" fuel compositions which didn\'t contain 238U. Actually speaking, these results can be considered as preliminary ones to demonstrate scale of benefit. Undoubtedly, it is needed to analyze impact of wide fuel compositions (including 238U) on stabilized multiplication properties of ultra long-life cores taking into consideration reactor safety in both critical and sub-critical regime of operations.
Anyway, application of ultra long-life core concepts will lead to essential decrease of SNF flow rate, reduction of reprocessing, remanufacturing and shipping operations. It’s a factor for internationalization of Nuclear Energy System fuel cycle. Since fuel cycles been discussed are “rich” with respect to excess neutron generation in CFR, there is no necessity to perform fine purification of fuel being reprocessed. It’s a factor of enhancement of the fuel cycles protection.
Application of NPP with ultra long-life core concepts is expected to be profitable for electricity generation in developing countries which have not improved nuclear technology infrastructure.
Dependencies of K on fuel burn-up for various fuel compositions
Plutonium has no its own “fertile” isotope. So, it is impossible to protect plutonium by isotopic dilution, like uranium. Upon exhaustion of cheap 235U resources, the isotope dilution principle can be applied to 233U-238U mixture. So, it seems reasonable to consider the following proliferation resistant fuel - (232Th-233U-238U) [23]. If 238U content is small but sufficient for low content of 233U in uranium fraction, then plutonium build-up may be suppressed.
In other words, the mixed (232Th-233U-238U-Pu) fuel cycle should be studied along with “classical” (232Th-233U) and (238U-Pu) cycles. In both “classical” cycles, fissile materials (233U or Pu) may be figuratively called by “highly-enriched” fuel. In the mixed cycle, on the contrary, fissile isotope 233U is diluted with 238U in uranium fraction, and thus (233U-238U) mixture may be regarded as a “low-enriched” fuel. It is noteworthy that homogeneous mixture of two fertile isotopes 238U and 232Th is a more effective neutron absorber than both separate isotopes. This effect can improve neutron-physical properties of the mixed fuel because it can increase fuel burn-up and thus reduce flow rate of spent fuel assemblies for reprocessing (Kulikov, 2007).
In the mixed fuel cycle, the following double-strata structure may be estimated as an effective and proliferation resistant option (Figs. 18, 19): the top stratum includes full-scale reprocessing of spent fuel assemblies in the International nuclear technology centers with complete incineration of plutonium and minor actinides, the bottom stratum includes a simplified thermal-chemical (DUPIC-type) re-fabrication of fresh fuel with feeding by proliferation resistant 233U. Such a closed nuclear fuel cycle may be equally effective in power reactors of PWR and CANDU types.
So, if fuel contains homogeneous mixture of two fertile isotopes 238U and 232Th, the following new qualities do appear:
Fissile isotope 233U produced in neutron irradiation of thorium is diluted with fertile isotope 238U. So, 233U-238U mixture represents, in essence, a kind of “low-enriched” uranium.
Reduced content of 238U suppresses build-up rate of plutonium.
Mixed fuel is highly effective not only in thermal but in resonant neutron spectrum too because fissile isotope 233U has sufficiently good neutron-multiplying properties both in thermal and resonant neutron spectra.
Fissile isotope 239Pu converts rapidly into heavier plutonium isotopes with low neutron-multiplying properties because of larger c/f. So, plutonium loses its attractiveness as a material suitable for NED manufacturing.
As is known (Benedict et al., 1981), fissile isotope 233U can be additionally protected by its denaturing with 232U because this isotope has the following proliferation-resistance properties (Fig. 19):
232U is an intense source of high-energy -radiation emitted by its decay products.
232U is an intense source of spontaneous neutrons, i.e. spontaneous fission neutrons plus neutrons from (,n)-reactions with light impurities.
232U is an intense heat source from its own -decays and from decays of its daughter products.
Double-Strata closed fuel cycle protected
as a Spikant
Qsf (Spontaneous Fission Neutrons) 1.3 103 n/(s kg 232U);
Q,n (Uranium Dioxide) 15 106 n/(s kg 232U) ( 20 – equilibrium);
232U–leader among U isotopes as a spontaneous neutrons generator.
Neutron irradiation of natural thorium in blanket region of Hybrid Fusion Facility (HFF) based on (D,T)-plasma can produce many thorium, protactinium and uranium isotopes. High-energy (14 MeV) thermonuclear neutrons are able to initiate some threshold (n,xn)-reactions leading to intense generation of 230Th, 231Pa, 232U, 233U and 234U. The longer irradiation time, the larger content of these isotopes in irradiated thorium. Content of 232U, for example, can reach a value of several percents.
NFC closure and SNF reprocessing can release huge amounts of fissionable materials: about 210 000 tons of uranium regenerate, RGPu and minor actinides, where uranium regenerate is a dominant fraction. Uranium regenerate may be regarded as a fertile material suitable for further use by nuclear power industry. Uranium regenerate will be released in the amounts large enough to feed NPP of total electric power at the level of 1500 GWe, i.e. 4 times higher that total power of global nuclear energy system today.
Uranium regenerate contains the following isotopes: 232U, 233U, 234U (minor fraction) and 235U, 236U, 238U (main fraction). Uranium produced in thorium blanket of HFF contains only isotopes of minor fraction, i.e. 232U, 233U and 234U. So, if HFF-produced uranium is admixed to uranium regenerate, content of only minor fraction increases. Content of minor fraction can be made comparable with content of main fraction. In the extreme case, minor fraction becomes a dominant one, and NFC shifts towards 233U-based fuel.
Thus, uranium fraction of nuclear fuel represents a mixture of practically all significant uranium isotopes: 232U, 233U, 234U, 235U, 236U, 238U. The following three aspects should be noted. Firstly, main fissile isotopes, 233U and 235U, are accompanied by lighter and heavier uranium isotopes, essential neutron absorbers. Secondly, if 232Th and 231Pa are introduced into fuel composition replacing partially uranium regenerate, then plutonium generation rate is suppressed. Thirdly, the presence of 236U in fuel composition can initiate the chain of isotopic transformations leading to accumulation of 232U, 233U, 238Pu, main isotope for plutonium denaturing (De Volpi, 1982):
236U(n,γ)237U(β-, T1/2 7 days)237Np (n,)238Np (β-, T1/2 2.1 days)238Pu
So, produced plutonium will contain not only 240Pu, usually accompanying isotope to 239Pu in power reactors, but 238Pu too.
In mixed (Th-U-Pu) fuel cycle, plutonium plays an auxiliary role only while 233U is a main fissile isotope, and plutonium content in fuel composition may be diminished. Finally, plutonium could be removed from global nuclear energy system for peaceful utilization in the dedicated nuclear power facilities. The GNEP initiative advanced by the US President (Sokolova, 2008) foresees just a similar option. This aspect represents a special significance from the standpoint of plutonium protection against unauthorized diversion to non-energy purposes (Mark, 1993).
Uranium fraction consisting of practically all significant uranium isotopes from 232U to 238U is, in essence, low-enriched uranium with rather small content of main fissile isotopes (233U and 235U). Isotopic enrichment of such a multi-isotope composition will be a very difficult problem for potential proliferators in the case of its unauthorized diversion.
The presence of α-emitters (mainly, 232U, 233U and 234U) in uranium fraction can initiate physical and chemical processes leading to α-radiolysis of uranium hexafluoride including molecular dissociation with generation of minor fluorides, exchange reactions of recombination and coagulation. These processes can provoke serious violations in the correspondence between the order in masses of uranium isotopes and the order in masses of uranium hexafluoride molecules. This correspondence is a necessary condition for successful uranium enrichment.
So, closed mixed (233U-232Th-238U) fuel cycle can offer the following advantages in comparison with “classical” (238U-Pu) and (232Th-233U) cycles:
Fissile isotope 233U is diluted by fertile isotope 238U in uranium fraction of fuel composition.
238U content in fuel composition may be diminished thus suppressing plutonium production. As a consequence, load of the International centers on plutonium utilization may be reduced.
General conclusion can be defined as follows: fuel of mixed (Th-U-Pu) cycle contains fissile isotopes with upgraded level of their protection against any unauthorized attempts of their diversion to non-energy purposes.
Proliferation protection of uranium and uranium-plutonium fuel can be quantitatively evaluated within the frames of the concept developed for risk assessment in authorized applications of nuclear materials. The concept includes some relationships which can be used to evaluate probability for a certain chain of unauthorized actions (UAA) to occur and to evaluate damage from potential NED applications.
One of main directions in nuclear non-proliferation ensuring is a formation of inaccessibility conditions for NM against any UAA. This is a main strategic function of MPC&A system at any nuclear-dangerous objects. However, the following questions arise:
What can occur with nuclear materials, if these conditions are violated due to some kind of reasons?
How can we estimate the threats?
What must we do under these accidental conditions? Answers to the questions are related to the threats of NM diversion including the threat of NED manufacturing from diverted NM and its military application. In order to give a correct response to these questions, two, at least, conditions must be satisfied:
We must know how to evaluate the threats of NED manufacturing from diverted NM and their military applications.
We must work out the recommendations on effective countermeasures to be undertaken against any UAA.
An important condition for successful counteraction against the use of diverted NM in NED manufacturing consists in development of the control system over illegal NM trafficking. External UAA monitoring system can apply various strategies of the searching process for potential UAA objects.
Unlike authorized activity, unauthorized actions with NM can be characterized by the following specific features:
Secrecy of unauthorized works. The secrecy level is defined by NM properties and financial expenses to be paid by potential proliferators.
Striving for manufacturing of NED with maximal destructive capability.
Striving for maximal shortening of UAA time which follows from the fact that potential proliferator understands properly the threats from external UAA monitoring system.
These tendencies are the conflicting ones from position of potential proliferator who strives to reach his ultimate purpose. For example, proliferator strives for NED manufacturing with maximal destructive capability but this requires application of sophisticated nuclear technologies for processing of diverted NM. In their turn, nuclear technologies require large financial and long time expenses with appropriate reduction of the secrecy level and rising of the detection probability.
So, when analyzing various scenarios of NM diversion, we presumed a rational behavior of nuclear proliferators, i.e. the proliferator has to accept a certain compromise between his striving for manufacturing of NED with maximal destructive capability and rising of the detection probability caused by application of sophisticated nuclear technologies. In any case rather long chain of technological processes is required to manufacture NED from diverted NM.
Potential risk of NM application for NED manufacturing and military use by terrorist groups can be evaluated as follows:
Probability
Assumption on a rational behavior of nuclear proliferator enables us to think that proliferator will follow the well-grounded plan with proper accounting for the detection probability, if sophisticated nuclear technologies are applied for processing of diverted NM (for example, fine NM purification with removal of all significant impurities, isotopic re-enrichment and so on). So, the risk of NED manufacturing and military use can reach a maximal point either within or on the boundaries of the domain that includes all potential UAA undertaken by nuclear proliferators. The maximal risk and its location in UAA domain depends on the level of external UAA monitoring and on financial capabilities of nuclear proliferators (see Fig. 20).
Variations of the risk related with NM application in destructive purposes when sophisticated nuclear technologies are involved into NM processing
This circumstance can be used to simplify analysis by using a conservative approach to evaluating the maximal risk of NM usage for NED manufacturing. Within the frames of this approach, probability P for successful completion of UAA chain (from initial state
The following problem is considered below: it is required to search for UAA object which was created on a certain territory. Let’s consider a discrete limited set
Let’s assume that UAA object is not moved and UAA can be unambiguously detected by one identification procedure. If the identification rate
where
If UAA can not be detected for one identification step, or if UAA object moves during the identification process, then a necessity arises to perform a repeat examination of the regions which were checked up previously. In this case, time dependency of non-detection probability may be written in the following form:
The following main links can be identified in UAA chains resulting in NED manufacturing from diverted uranium-containing NM: NM theft → chemical and physical reprocessing → isotopic re-enrichment → manufacturing of main NED components → military use of NED.
Each link of UAA chain is defined by its duration t
where P
UAA object can be detected from the really existing indicators including the indicators related with consumption of energy and water resources in the unauthorized activity. The following indicators can be used in the search for UAA aimed at NED manufacturing and military use:
Emission rate (A).
Resource consumption rate (W).
Capital expenses (К).
When searching the UAA-object being to several independent indicators, then total non-detection probability is a product of partial non-detection probabilities for different UAA indicators, i.e.
where
where – efficiency of the searching process for appropriate UAA indicators.
Relationship between UAA indicators and detection parameters can be derived from the following models for strategic behavior of nuclear proliferator:
The proliferator creates a new infrastructure for his unauthorized activity. According to equation (2), UAA detection parameter in the random searching process for new resources is proportional to the scale of new resources which were put in operation. In the simplest case, the scale is defined by the resource consumption rate W and capital expenses K. So, in this case: λ
The proliferator applies already available infrastructure to perform UAA. Let’s assume that industrial enterprises in the search region consumes resources W in accordance with distribution N(W), and frequency of the inspecting actions F
In both models the emission rate parameter is proportional to the territorial area where abnormal emission level was observed, i.e. λ
For example, detection parameter λ
The following problems are considered below: it is required to analyze dependency of metal uranium proliferation protection on uranium enrichment at different efficiencies of the searching process, and it is required to analyze the effects of uranium denaturing on its proliferation resistance, if uranium is denatured by admixing small amounts of 232U that intensifies inherent neutron background. Nuclear proliferator does not resort to uranium re-enrichment up o the weapon-grade level, his main goal consists in a NED manufacturing.
Relative values of uranium proliferation protection were calculated for different efficiencies α of the searching process including the case when α 0, i.e. the case of uranium self-protection.
Mark-Hippel-Lyman model (Mark, 1993) of CFR initiation and propagation was used to evaluate damage from NED manufacturing and military use. CFR parameters were calculated by direct mathematical simulation of neutron multiplication process with application of Monte Carlo code MCNP-4B (Briesmeister, 1997) and evaluated nuclear data file ENDF/B-VI (National Nuclear Data Center, 2001). Mathematical model and algorithm for determination of the model parameters correspond to the approach described in paper (Kryuchkov et al., 2008).
The results obtained in calculations of relative proliferation protection (inverse value to the risk) for different monitoring efficiencies and for different levels of uranium denaturing by 232U are presented in Fig. 21.
Proliferation protection of metal uranium as a function of its enrichment
The following conclusions can be derived from numerical evaluations of metal uranium proliferation protection:
Measures of external monitoring (outside of MPC&A system) are ineffective ones in comparison with the measures aimed at upgrading of uranium self-protection for highly-enriched compositions.
Efficiency of external monitoring can excel efficiency of inherent self-protection for uranium enriched below 20% 235U.
Upgrading of uranium self-protection by its denaturing, i.e. by formation of internal neutron source, weakly depends on uranium enrichment and provides approximately the same effect in a rather wide range of uranium enrichments.
So, nuclear non-proliferation requires maximal restrictions to be imposed on any transactions of pure HEU while free material must be maintained in a self-protected state produced by isotopic denaturing, for instance.
Aquatic ecosystems are complex systems that are the compass of nutrients, biotic pelagic and benthic communities, pools of detritus and that have the bulk of both water and sediment [1, 2]. Anthropogenic activities lead to multiple types of stresses, including emissions of pesticides and nutrients into the environment [3, 4]. These pesticides are capable of affecting species in the aquatic ecosystems and the nutrients can cause eutrophication. Emissions of pesticides can also lead to accumulation in the environmental compartments of water and the complex matrix that forms the sediment. Simultaneous pesticides bioaccumulation into organic substances such as biota and detritus prove to have an adverse effect on aquatic bio-species. Various toxicokinetic models have described these types of accumulations [5].
Recently, the cry for environmental pesticides pollution is heard from every nook and crannies of the world. Pollution of pesticides has now become a distinct threat to the very existence of mankind and animals on this earth. It is a problem challenge for our days. In the past, man has been disturbing the balance of nature for comfort, wealth, and ego, but now nature has started disturbing the balance of nature. In the late century, there has been growing concern in developing countries and developed countries over the pollution effects from sources, such as sewage, pesticides, and trade effluents discharged from domestic habitations and by the industrial units [6].
The immediate catastrophic effects of pesticides pollution by some industrial units and agricultural application of pesticides have pointed out the essence of its environmental effects: prevention and control. There is now a global awareness that pesticides production and utilization activities in the future time need to be assessed for their environmental hazard or effects without any form of compromise to the said assessment. Too much rise in pesticides application and their industrial production activities in the past have led to the emission of harmful pesticides into human and aquatic habitats and have led to various ecological issues.
Disturbance of pesticides emission has become a serious threat to both human and animals life and it puts the ecosystem out of balance. Maintenance of ecological balance and environmental purity due to the sudden increase in the production of pesticides and their applications in both the home and agricultural sector should be the inclusive concern of each member of society. This situation could be improved through awareness program creation, which must gain the support of people from all works of life with the aim of enlighten them on its pros and cons and their responsibilities that will meet up with the global standard. Pesticides pollution under discussion here has a different meaning and environmental disorder to different biological organisms. Human beings feed on aquatic animals, fishes and drink untreated water. Thus, they are more susceptible to multiple pesticides effects than aquatic animals that feed on prey and uptake water only. This discussion cannot exclude how water is important to all living organisms as it sustains life as the human body depends on water for about seventy percent (70%) to function normally.
Yichen et al. [5] also pointed out the indisputable dependability of water by living organisms as it functions in every living organism cell and cell is said to be the smallest unit of life. In order to reduce and prevent the issues of pesticides pollution in an aquatic habitat, law enforcement agencies have primary responsibilities of ensuring that laws and implantation of pesticides used must be seriously put in place. Companies or industries operating along rivers, seas, and lakes banks, to mention a few, need to redirect their discharge wastes formally channeled into water bodies to a sustainable environment (Figure 1) [7].
Environmental pollution.
Pesticides pollution have different routes into aquatic organism domesticated habitat such as leaching from the agricultural farm, erosion from farmlands during rainfall, and become available in the water body through spills from industrial effluents and discharges of environmental wastes into water bodies [8]. Pesticides have different meanings to different people. Generally, pesticides are large classification or group of chemical substances that are developed to model and thereafter substitute for a unique molecule in a particular biological process. This implies that the mode of action of pesticides is peculiar to specific organism, plant, or grass such as pests, weeds to mention a few [9].
The issue of poor quality of water is of the utmost environmental problem in the human health-related issues [10]. Pollution from pesticides has contributed to the said threat and it will continue to gain more ground in as much as they are present in water bodies. The primary aim of pesticides production is mostly for specific targeted organisms or plants but their effects are non-targeted as it affects humans, animals, and plants and produces range of toxicity effects which include carcinogenicity [11] and have the ability to disrupt endocrine [12].
The wide usage of pesticides are detected across different nations such as Europe’s freshwater. In Ireland, pesticides are present beyond the European Union (EU) permission limit bound on different numbers of inspections [8, 13]. In Europe, freshwaters in the UK were found to be susceptible to pesticide pollution and in Germany, groundwater and sediment materials were specifically polluted due to pesticides applications and discharge [14].
EC legislators have provided different legislation or laws in place to prevent or minimize the discharge of pesticides and their applications in their environment. The legislation includes Water Framework Directive [15], the strategy for the prevention of endocrine-disrupting compounds [16], and the Stockholm convention [17].”
The normal water purification tools or equipment have proved inefficient to remove toxic pesticides substances from water bodies [16]. The need to have an efficient method is of utmost importance to be researched. Up to now, the best efficient pesticides removal methods include photocatalysis and adsorption [18, 19].
Human activities like land cover change, urbanization and industrialization have impaired ecosystems for several decades in order to increase the access to natural resources for an exponentially growing population [20, 21]. The activities of humans have led to the impairment of the planet earth’s boundaries and are causing biodiversity loss and climate changes [22, 23]. Keeping the account of human activities on the global freshwater, land use, acidification of oceans, rivers, lakes, and streams are already tending to a threshold value [22]. Rockström et al. [22] in their study have noted that the human population is facing un-quantifiable threats due to freshwater contamination by different forms of contaminants that are unknown in an aquatic environment.
More than 14 million different chemical compounds exist, out of which above 100,000 synthetic chemical compounds are frequently used in consumer products in different countries of the world for different purposes [24, 25]. Thus, an uncertain number of chemicals may potentially be released into the aquatic environment by diverse routes like point sources, remobilization from contaminated sediments, and groundwater input (Figure 2) [26].
Pesticides pollution.
A lot of literature has identified different routes of pesticides to the aquatic environment [27, 28]. It was observed mainly that the rate at which pesticides enter the aquatic environment is not the same with all pesticides. The routes mainly depend on the physiochemical properties, that is, the ability of pesticides to persist for several years or a decade in an environment without totally losing their concentrations. The land use and climate changes facilitate pesticides entering into an aquatic environment where it was not originally applied. Majorly, pesticides enter into aquatic environment through wind drift during pesticides applications, erosion due to rainfall immediately after pesticides applications to agricultural farmland, migration of living organisms that were affected by the pesticides concentration into the aquatic environment, and through drainage to mention a few.
In an aquatic environment, different contaminants especially pesticides pollution have been found with different names and concentrations. These pesticides have been found to integrate with each other and form different pesticides with different concentration levels in aquatic habitat [29].
In this century, many agricultural investors (e.g., farmers) have priority for growing high-yielding species of different crops to meet the increasing population demand for food. However, one of the essential phenomena of this subject of discussion is that varieties are that most of those crops are highly prone to different diseases and pests [30], which was evidence to cause about 40–50% of crop loss [31]. As a result of this information, the use of pesticides to protect crops from those pests and diseases, and reduce crop lost, herewith improving the yield quality as well as quantity became necessary [32, 33, 34]. In Bangladesh, pesticides were introduced in 1951 but their uses were negligible until the end of the 1960s [35]. An exponential increase in their uses have occurred from 7350 metric tons of active ingredient of pesticides in 1992 to about 45,172 metric tons in 2010 [34].
One of the major reasons for the high rate of pesticides application in some countries such as Bangladesh is due to the adoption of the government policy to increase the control of pests and diseases of crops through a chemical measure process in order to increase overall crop yield and to prevent and control crops losses [34].
More so, about eighty-four (84%) of pesticides significant materials are in the family of 242 trade names of a different group of chemicals namely: organochlorine compound, carbamates, organophosphate, neonicotinoids, pyrethroids, nitro compound, heterocyclic pesticides that are registered in Bangladesh and other parts of the world and are used in the agricultural sector and household applications [35]. However, organochlorine pesticides have been banned in Bangladesh in 1993 [36] and in many countries of the world because of the nature of their toxicities in both human and aquatic environments and they are capable to bioaccumulate and biomagnify in the biological process of feeding such as food chain [37, 38]. Considering other group of pesticides available, the organophosphorus pesticide has gained popularity in the application by farmers in Bangladesh. In addition, more than 35% of their farmers use organophosphorus pesticide to treat varieties of crops for protection reasons [39].”
Pesticides applied on agricultural land have the capability to reach the aquatic environment through several ways which may include but are not limited to leaching of groundwater, spray drift, runoff of surface water, disposal of pesticides containers nearby or inside rivers, cleaning of pesticides equipment in rivers or lakes [40, 41, 42]. The indiscriminate use of pesticides and their disposal methods constitute a major threat to the aquatic organism and have led to eco-toxicological risk. More than sixty percent (60%) of animal protein emanated from fish [43]. Since fish serves as the major source of protein in man’s food, the indiscriminate use of pesticides in an aquatic environment needs to be reviewed as their toxic effects on fishes are harmful to their normal behavior, physiology and sometimes lead to their deaths [30, 44, 45, 46, 47, 48, 49, 50, 51, 52, 53, 54].
Different studies [55, 56] have shown the adverse effects of pesticides on fish species which include but not limited to histopathological alterations such as kidney, gonad, liver, and gill tissue. A study by Dutta and Maxwell (2003) reported that bluegill fish shows histopathological alteration in the ovary namely; cytoplasmic reaction, cytoplasm, and karyoplasmic clumping, necrosis, and thinning of follicular lining exposed to diazinon, atretic oocytes, and adhesion (Figure 3).
Mixtures of pesticides.
Manufacturers of pesticides especially those that are licensed by the legislators of their respective countries always ensure their products to be selective and specific to targeted organisms in terms of their toxicity effects. Yet, some of them are totally specific, a few of them are relatively specific while the majority of them are not due to their biodegradable process. Pesticides toxicity most times always depends on the mode of applications. Pesticides applied during wind action and those applied closely to rainfall time always drift from the specific area of application to the non-targeted area. Biodegradation and degradation of pesticides vary from one pesticides compound to another. This is always due to their respective elements that are made up of a particular chemical organic compound. Some are more toxic than their original parent compounds while others are less toxic during the splitting of the individual elements that are made up of the compounds [57].
The susceptibility of humans and animals to pesticides mixtures always produces toxicological interactions effects [58]. Exposure effects of multiple pesticides may be toxic or less toxic or have the same effects with exposure to their individual component. Most times, it is more poisonous to be susceptible to pesticides mixture than exposure to their respective individual element at different time period due to their effect of synergy [58].
Some of the related terminologies used for explaining toxicological interactions of exposure to multiple pesticides include but are not limited to:
Effect of synergy: This happens due to the greater effects of two pesticides affecting biological organism at the same time than the sum of their individual effects when they are applied individually or separately.
Effect of antagonist: This exists whenever two pesticides are applied at the same time and each of the pesticides action interferes with the other pesticide that was mixed or combined with.
Effect of additive: It usually takes place or happens whenever the addition of two pesticides has the same toxicity effects with the sum of the effects of the individual pesticides applied separately.
Potentiating: It happens when a pesticide produces a toxic effect anytime is applied together with another pesticide(s).
The effects of exposure to the interactions of pesticides depend on the quality of their application and the prediction of their effects requires enough information regarding the factors responsible for pesticides exposures such as magnitude, time, and toxicity to mention a few.
Antagonism process of pesticides interaction includes functional, chemical, dispositional, and receptor. Functional antagonism occurs when two pesticides counterbalance one another by opposite effects on the same physiological function. Chemical antagonism is a chemical reaction between two pesticides to produce a less toxic product [59].
Pesticides enter into the aquatic environment through different routes such as direct application of pesticides to rivers, seas, lakes, or any other water source to prevent or control weeds, pests, or diseases of crops [59]. Atmospheric nature may truly take place due to the movement of the spray of pesticides from crops surfaces or soil surfaces to the aquatic environment. Yeo et al. [60] noted from their work the effects of atmospheric concentration of pesticides compounds such as organochlorine pesticides which include: Dichlorodiphenyltrichloroethane (DDTs), heptachlor, endosulfan, chlordane, hexachlorocyclohexanes have reported to have minimum and maximum seasonal variation in a rural setting [61]. Furthermore, plantations have been shown to help in reducing surface soil erosion and influence pesticides biodegradation over time, and could lead to the concentration of pesticides in water [62] (Figure 4).
Effect of pesticides on aquatic organisms.
Pesticides have the potential to change their state from one form of state of matter into another [63]. The process of the term pesticide volatilization is motivated and catalyzed by pesticides transportation such as soil, water, plant, and surface matrix sorption [64], transportation by air, and diffusion through the boundary layer. The following factors are said to influence the volatilization of pesticides which include physicochemical properties of pesticides [65] including vapor pressure, water solubility, Henry’s law constant, adsorption properties, and some environmental factors including soil moisture and soil/air temperature.
Photolysis of pesticides occurs whenever pesticide compounds have adequate energy from light and causes decomposition of the compound molecules through either direct or indirect process [66].
Photolysis is also known to involve in some form of organic pesticides compounds reaction such as carbon bond, isomerization, decarboxylation, and ester cleavage [67]. Different type of photolysis rate of reaction always depends on the absorption spectrum of the pesticides involved (Dureja, 2012; [68]). Direct photolysis is said to take place when pesticide absorbs directly from light energy and result in some form of chemical reaction [69].
Pesticides mixture toxicity is always difficult or complex to predict their toxic effects. Various models that are used to predict a toxic mixture of pesticides effects are always based on their structures activity composition and are always formulated for the complex organic compound of heavy pesticides.
However, different pesticides mixtures are expected to change the behavior of biological species from their combined effects than those effects from the concentration of a single compound.
A lot of studies have been carried out on the pesticides effects in relation to different ecological settings which mainly focused on the restricted compound known as organochlorines [70, 71, 72]. This said organic compound is capable of assimilating into crops, animals, and entire ecosystem at high rates of pesticides concentration emission [73, 74].
Several researchers were able to point out that “the degradation of pesticides rates are faster and higher under hot weather. In addition, pesticides solubility is temperature-dependent, that is, the higher the temperature the more soluble it becomes and light intensity was also found to be responsible for the high rate of pesticides degradation [75].” More so, hydrolysis has been found as one of the factors that are responsible for the speedy degradation of pesticides especially when combined with changes in pH and aerobic/anaerobic conditions. The transformation process is mediated by living organisms such as plants, algae, bacteria, or fungi as a result of biodegradation. Complex pesticides like carbon compounds such as synthetic pesticides are used for crops growth as the nutrient substrate is capable of degrading into other compounds or elements [76, 77, 78].
Degradation process of the majority of pesticides is mostly affected by bacteria and fungi such as DDT pesticide, chlophyrifos, and cypermethrin. Some factors such as plants, animals (e.g., earthworms), soil moisture, temperature, pH, soil organic matter, carbon source concentration of pesticides greatly influence microbial degradation of pesticides [79, 80, 81, 82, 83, 84, 85]. On the whole, most of the microbial activities are found during warm temperatures and in moist soil [9].
During the application of pesticides to a specific area of concern, for instance, crops farm, such pesticides concentration may be watered down by irrigation, runoff water, leaching, rainfall, drainage to the non-targeted environment like groundwater usually pollute aquatic habitant. In addition, pesticides present in the atmosphere, water, soil, or sediment can be degraded via photolysis, hydrolysis, microbial degradation, and biotic uptake [9].
Few workers of the Environmental Protection Agency (EPA) have researched on the possible effects of combined pesticides on aquatic biological species, most especially fish. They reported from their studies that the combined effects of pesticides are often determined as a simulation of their separate effects. Their findings may not mirror the combined effects of pesticides as one may expect because pesticides exist in synergistic form. After their finding, much work has been published in respect of the toxicity effects of combined pesticides effects on fishes and other aquatic organisms. They later found out that accurate and comprehensive data are required to model the effects of pesticides mixture on aquatic and any other living organisms’ population.
The toxicity of pesticides on aquatic organisms can be measured in a number of ways. The World Health Organisation [86] measures the toxicity of pesticides under the following headings.
Toxicity effect of pesticide(s) on microorganisms;
Toxicity effect of pesticide(s) on aquatic organisms;
Toxicity effect of pesticide(s) on terrestrial organisms.
The World Health Organisation only reports the toxicity of individual pesticides in their study on the effects of pesticides on the targeted organism [86]. Most of the harmful pesticides such as LC50, LD50, and the physiochemical pesticides properties were considered (Figure 5).
Degradation of pesticides.
The use and improper handling of pesticides during their application cause a lot of problems to human health in developing countries. Many studies have pointed out the occupational health hazards of farmers posed by the unsafe use of pesticides. The adverse effects usually observed by farmers after the usage of pesticides on their farms include but are not limited to eye irritation, vomiting, and headache. About eighty percent (80%) of farmers are aware of the adverse health symptoms poses by pesticides as a result of their intoxication at the time of their applications [42].
The outcomes of their study on the adverse effects of pesticides have similar results with other research works carried out in other developing countries. For instance, Dasgupta et al. [87] reported “negative health effects such as headache, dizziness, eye irritation, vomiting, dermal diseases and gastrointestinal problems after pesticide application in different parts of developing countries.” More so, a study by Miah et al. [88] found some similar negative health symptoms. Also, nausea in farmers that grow vegetables in south-east Bangladesh was attributed to pesticides effects. The majority of the negative health effects or signs were reported after the application of pesticides in some countries in South Asia like Pakistan, India, and Nepal [89, 90, 91].
However, most of the negative health issues reported by the farmers after pesticides application were due to their inability to follow safety measures on the labels of the pesticides such as spraying pesticides without the use of a nose and mouth mask, covering shoes, and without covering other part of their body effectively [87, 88].
Although, a report issued by Sumon et al. [42] stated that about 82% of farmers normally cover their faces and body with clothes during pesticides application. However, mere covering of the face and body are not enough preventive measures to observe during pesticides application. The more advanced ways of pesticides effects preventive measures during application require farmers or pesticides users to follow the guidelines stipulated by Kabir and Rainis [92]. In their study, they gave some preventive measures required by every pesticides applicator to observe during pesticides application which include: wearing gum-boots, hand gloves, masks during pesticides application and washing of spraying equipment, and taking bath immediately after application.
Furthermore, to reduce or eliminate the dilemma of pesticides risks, it must be the primary responsibility of both governmental and non-governmental organizations to shoulder the responsibility of creating awareness programs in the communities where the pesticides applicators lived. More so, the government must be responsible for the training of farmers to ensure that agricultural workers have good knowledge of the protective guidelines or measures. To achieve this, pesticides industries can bring about product stewardship programs making the industries themselves co-responsible for their products during usage in the field, and the storage. Furthermore, the public sector that is, the government needs to ensure basic training among the agricultural workers that use pesticides for farming to gather knowledge and to build awareness on the safe use and handling of pesticides and subsequently can introduce laws on the use of pesticides and the license for pesticide spraying only for the trained farmers.
In order to create a sound ecological environment, the total removal of harmful pesticides (Chlorfenvinphos, Diuron, Atrazine, Endosulfan, Alachlor, Pentachlorophenol to mention a few) that were banned as reported in their studies as a result of their persistence in the environment should be implemented without any form of compromise to the said assessments [15, 93, 94, 95].
Pesticide-related pollution has been causing a persistent and continuous environmental problem [96]. Pesticides pose potential risks to air and water quality, crops, animal health, and human health, to mention but just a few. Significant issues related to pesticide use and application, include over-application, contamination of surface and underground water [97], and drift to unintended targets environment thereby affecting non-target organisms.
Pesticide drift which signifies the amount of pesticide active ingredient that is deflected out of the treated area by the action of air currents has the potential to affect non-target organisms and the environment [98]. Greater proportions of pesticides concentration were unable to reach the targeted area [99]. However, the presence of pesticides concentration in an unwanted area always leads to the loss of some crops, wildlife population and sometimes cause chaos in natural environment [100]. In the past, the EU has experienced serious concerns about the dispersal of pesticides categorized as persistent organic pollutants (POPs). These POPs are capable of transporting across international boundaries far from their original sources, even to regions where they have never been used or produced (Figures 6 and 7) [101].
Effect of pesticides on human health 1.
Effect of pesticides on human health 2.
The increase in usage of pesticides on agricultural farms has led to ecosystems disturbance. As a result of this incident, the need for research on how pesticides should be applied to increase agricultural productivity without compromising the ecological standard became necessary over the years. The study of the effect of chemicals/pesticides on biological species is known as ecotoxicology. The science of ecotoxicology and environmental toxicology [102] includes:
Mathematics
Environmental biology and
Chemistry
Due to the involvement of different disciplines, they are different aims of ecotoxicology research [102] which include the following:
Field of ecotoxicology.
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On September, 29th 2006 he has won a post PhD fellowship from the university of Bologna (from October 2006 to October 2008), at the competitive examination he was ranked first in the industrial engineering area. He extensively served as referee for several international journals. He is author/coauthor of more than 100 research papers. He has been involved in some projects supported by MURST and European Community. 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Other positions she has held at the university include Vice-Dean of Master Programs, Vice-Dean of the Degree in Biology and Vice-Dean for Mobility and Enterprise and Engagement at the Faculty of Science (University of Alicante). She received her Bachelor in Biology in 1998 (University of Alicante) and her PhD in 2003 (Biochemistry, University of Alicante). She undertook post-doctoral research at the University of East Anglia (Norwich, U.K. 2004-2005; 2007-2008).\nHer multidisciplinary research focuses on investigating archaea and their potential applications in biotechnology. She has an H-index of 21. She has authored one patent and has published more than 70 indexed papers and around 60 book chapters.\nShe has contributed to more than 150 national and international meetings during the last 15 years. Her research interests include archaea metabolism, enzymes purification and characterization, gene regulation, carotenoids and bioplastics production, antioxidant\ncompounds, waste water treatments, and brines bioremediation.\nRosa María’s other roles include editorial board member for several journals related\nto biochemistry, reviewer for more than 60 journals (biochemistry, molecular biology, biotechnology, chemistry and microbiology) and president of several organizing committees in international meetings related to the N-cycle or respiratory processes.",institutionString:null,institution:{name:"University of Alicante",institutionURL:null,country:{name:"Spain"}}},editorTwo:null,editorThree:null},{id:"15",title:"Chemical Biology",coverUrl:"https://cdn.intechopen.com/series_topics/covers/15.jpg",isOpenForSubmission:!0,editor:{id:"441442",title:"Dr.",name:"Şükrü",middleName:null,surname:"Beydemir",slug:"sukru-beydemir",fullName:"Şükrü Beydemir",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0033Y00003GsUoIQAV/Profile_Picture_1634557147521",biography:"Dr. Şükrü Beydemir obtained a BSc in Chemistry in 1995 from Yüzüncü Yıl University, MSc in Biochemistry in 1998, and PhD in Biochemistry in 2002 from Atatürk University, Turkey. He performed post-doctoral studies at Max-Planck Institute, Germany, and University of Florence, Italy in addition to making several scientific visits abroad. He currently works as a Full Professor of Biochemistry in the Faculty of Pharmacy, Anadolu University, Turkey. Dr. Beydemir has published over a hundred scientific papers spanning protein biochemistry, enzymology and medicinal chemistry, reviews, book chapters and presented several conferences to scientists worldwide. He has received numerous publication awards from various international scientific councils. He serves in the Editorial Board of several international journals. Dr. Beydemir is also Rector of Bilecik Şeyh Edebali University, Turkey.",institutionString:null,institution:{name:"Anadolu University",institutionURL:null,country:{name:"Turkey"}}},editorTwo:{id:"13652",title:"Prof.",name:"Deniz",middleName:null,surname:"Ekinci",slug:"deniz-ekinci",fullName:"Deniz Ekinci",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002aYLT1QAO/Profile_Picture_1634557223079",biography:"Dr. Deniz Ekinci obtained a BSc in Chemistry in 2004, MSc in Biochemistry in 2006, and PhD in Biochemistry in 2009 from Atatürk University, Turkey. He studied at Stetson University, USA, in 2007-2008 and at the Max Planck Institute of Molecular Cell Biology and Genetics, Germany, in 2009-2010. Dr. Ekinci currently works as a Full Professor of Biochemistry in the Faculty of Agriculture and is the Head of the Enzyme and Microbial Biotechnology Division, Ondokuz Mayıs University, Turkey. He is a member of the Turkish Biochemical Society, American Chemical Society, and German Genetics society. Dr. Ekinci published around ninety scientific papers, reviews and book chapters, and presented several conferences to scientists. He has received numerous publication awards from several scientific councils. Dr. Ekinci serves as the Editor in Chief of four international books and is involved in the Editorial Board of several international journals.",institutionString:null,institution:{name:"Ondokuz Mayıs University",institutionURL:null,country:{name:"Turkey"}}},editorThree:null},{id:"17",title:"Metabolism",coverUrl:"https://cdn.intechopen.com/series_topics/covers/17.jpg",isOpenForSubmission:!0,editor:{id:"138626",title:"Dr.",name:"Yannis",middleName:null,surname:"Karamanos",slug:"yannis-karamanos",fullName:"Yannis Karamanos",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002g6Jv2QAE/Profile_Picture_1629356660984",biography:"Yannis Karamanos, born in Greece in 1953, completed his pre-graduate studies at the Université Pierre et Marie Curie, Paris, then his Masters and Doctoral degree at the Université de Lille (1983). He was associate professor at the University of Limoges (1987) before becoming full professor of biochemistry at the Université d’Artois (1996). He worked on the structure-function relationships of glycoconjugates and his main project was the investigations on the biological roles of the de-N-glycosylation enzymes (Endo-N-acetyl-β-D-glucosaminidase and peptide-N4-(N-acetyl-β-glucosaminyl) asparagine amidase). From 2002 he contributes to the understanding of the Blood-brain barrier functioning using proteomics approaches. He has published more than 70 papers. His teaching areas are energy metabolism and regulation, integration and organ specialization and metabolic adaptation.",institutionString:null,institution:{name:"Artois University",institutionURL:null,country:{name:"France"}}},editorTwo:null,editorThree:null},{id:"18",title:"Proteomics",coverUrl:"https://cdn.intechopen.com/series_topics/covers/18.jpg",isOpenForSubmission:!0,editor:{id:"200689",title:"Prof.",name:"Paolo",middleName:null,surname:"Iadarola",slug:"paolo-iadarola",fullName:"Paolo Iadarola",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bSCl8QAG/Profile_Picture_1623568118342",biography:"Paolo Iadarola graduated with a degree in Chemistry from the University of Pavia (Italy) in July 1972. He then worked as an Assistant Professor at the Faculty of Science of the same University until 1984. In 1985, Prof. Iadarola became Associate Professor at the Department of Biology and Biotechnologies of the University of Pavia and retired in October 2017. Since then, he has been working as an Adjunct Professor in the same Department at the University of Pavia. His research activity during the first years was primarily focused on the purification and structural characterization of enzymes from animal and plant sources. During this period, Prof. Iadarola familiarized himself with the conventional techniques used in column chromatography, spectrophotometry, manual Edman degradation, and electrophoresis). Since 1995, he has been working on: i) the determination in biological fluids (serum, urine, bronchoalveolar lavage, sputum) of proteolytic activities involved in the degradation processes of connective tissue matrix, and ii) on the identification of biological markers of lung diseases. In this context, he has developed and validated new methodologies (e.g., Capillary Electrophoresis coupled to Laser-Induced Fluorescence, CE-LIF) whose application enabled him to determine both the amounts of biochemical markers (Desmosines) in urine/serum of patients affected by Chronic Obstructive Pulmonary Disease (COPD) and the activity of proteolytic enzymes (Human Neutrophil Elastase, Cathepsin G, Pseudomonas aeruginosa elastase) in sputa of these patients. More recently, Prof. Iadarola was involved in developing techniques such as two-dimensional electrophoresis coupled to liquid chromatography/mass spectrometry (2DE-LC/MS) for the proteomic analysis of biological fluids aimed at the identification of potential biomarkers of different lung diseases. He is the author of about 150 publications (According to Scopus: H-Index: 23; Total citations: 1568- According to WOS: H-Index: 20; Total Citations: 1296) of peer-reviewed international journals. He is a Consultant Reviewer for several journals, including the Journal of Chromatography A, Journal of Chromatography B, Plos ONE, Proteomes, International Journal of Molecular Science, Biotech, Electrophoresis, and others. He is also Associate Editor of Biotech.",institutionString:null,institution:{name:"University of Pavia",institutionURL:null,country:{name:"Italy"}}},editorTwo:{id:"201414",title:"Dr.",name:"Simona",middleName:null,surname:"Viglio",slug:"simona-viglio",fullName:"Simona Viglio",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bRKDHQA4/Profile_Picture_1630402531487",biography:"Simona Viglio is an Associate Professor of Biochemistry at the Department of Molecular Medicine at the University of Pavia. She has been working since 1995 on the determination of proteolytic enzymes involved in the degradation process of connective tissue matrix and on the identification of biological markers of lung diseases. She gained considerable experience in developing and validating new methodologies whose applications allowed her to determine both the amount of biomarkers (Desmosine and Isodesmosine) in the urine of patients affected by COPD, and the activity of proteolytic enzymes (HNE, Cathepsin G, Pseudomonas aeruginosa elastase) in the sputa of these patients. Simona Viglio was also involved in research dealing with the supplementation of amino acids in patients with brain injury and chronic heart failure. She is presently engaged in the development of 2-DE and LC-MS techniques for the study of proteomics in biological fluids. The aim of this research is the identification of potential biomarkers of lung diseases. She is an author of about 90 publications (According to Scopus: H-Index: 23; According to WOS: H-Index: 20) on peer-reviewed journals, a member of the “Società Italiana di Biochimica e Biologia Molecolare,“ and a Consultant Reviewer for International Journal of Molecular Science, Journal of Chromatography A, COPD, Plos ONE and Nutritional Neuroscience.",institutionString:null,institution:{name:"University of Pavia",institutionURL:null,country:{name:"Italy"}}},editorThree:null}]},overviewPageOFChapters:{paginationCount:50,paginationItems:[{id:"81927",title:"Purinergic System in Immune Response",doi:"10.5772/intechopen.104485",signatures:"Yerly Magnolia Useche Salvador",slug:"purinergic-system-in-immune-response",totalDownloads:0,totalCrossrefCites:null,totalDimensionsCites:null,authors:null,book:{title:"Purinergic System",coverURL:"https://cdn.intechopen.com/books/images_new/10801.jpg",subseries:{id:"17",title:"Metabolism"}}},{id:"80495",title:"Iron in Cell Metabolism and Disease",doi:"10.5772/intechopen.101908",signatures:"Eeka Prabhakar",slug:"iron-in-cell-metabolism-and-disease",totalDownloads:7,totalCrossrefCites:0,totalDimensionsCites:0,authors:null,book:{title:"Iron Metabolism - Iron a Double‐Edged Sword",coverURL:"https://cdn.intechopen.com/books/images_new/10842.jpg",subseries:{id:"17",title:"Metabolism"}}},{id:"81799",title:"Cross Talk of Purinergic and Immune Signaling: Implication in Inflammatory and Pathogenic Diseases",doi:"10.5772/intechopen.104978",signatures:"Richa Rai",slug:"cross-talk-of-purinergic-and-immune-signaling-implication-in-inflammatory-and-pathogenic-diseases",totalDownloads:10,totalCrossrefCites:0,totalDimensionsCites:0,authors:null,book:{title:"Purinergic System",coverURL:"https://cdn.intechopen.com/books/images_new/10801.jpg",subseries:{id:"17",title:"Metabolism"}}},{id:"81764",title:"Involvement of the Purinergic System in Cell Death in Models of Retinopathies",doi:"10.5772/intechopen.103935",signatures:"Douglas Penaforte Cruz, Marinna Garcia Repossi and Lucianne Fragel Madeira",slug:"involvement-of-the-purinergic-system-in-cell-death-in-models-of-retinopathies",totalDownloads:5,totalCrossrefCites:0,totalDimensionsCites:0,authors:null,book:{title:"Purinergic System",coverURL:"https://cdn.intechopen.com/books/images_new/10801.jpg",subseries:{id:"17",title:"Metabolism"}}}]},overviewPagePublishedBooks:{paginationCount:27,paginationItems:[{type:"book",id:"7006",title:"Biochemistry and Health Benefits of Fatty Acids",subtitle:null,coverURL:"https://cdn.intechopen.com/books/images_new/7006.jpg",slug:"biochemistry-and-health-benefits-of-fatty-acids",publishedDate:"December 19th 2018",editedByType:"Edited by",bookSignature:"Viduranga Waisundara",hash:"c93a00abd68b5eba67e5e719f67fd20b",volumeInSeries:1,fullTitle:"Biochemistry and Health Benefits of Fatty Acids",editors:[{id:"194281",title:"Dr.",name:"Viduranga Y.",middleName:null,surname:"Waisundara",slug:"viduranga-y.-waisundara",fullName:"Viduranga Y. Waisundara",profilePictureURL:"https://mts.intechopen.com/storage/users/194281/images/system/194281.jpg",biography:"Dr. Viduranga Waisundara obtained her Ph.D. in Food Science and Technology from the Department of Chemistry, National University of Singapore, in 2010. She was a lecturer at Temasek Polytechnic, Singapore from July 2009 to March 2013. She relocated to her motherland of Sri Lanka and spearheaded the Functional Food Product Development Project at the National Institute of Fundamental Studies from April 2013 to October 2016. She was a senior lecturer on a temporary basis at the Department of Food Technology, Faculty of Technology, Rajarata University of Sri Lanka. She is currently Deputy Principal of the Australian College of Business and Technology – Kandy Campus, Sri Lanka. She is also the Global Harmonization Initiative (GHI) Ambassador to Sri Lanka.",institutionString:"Australian College of Business & Technology",institution:null}]},{type:"book",id:"6820",title:"Keratin",subtitle:null,coverURL:"https://cdn.intechopen.com/books/images_new/6820.jpg",slug:"keratin",publishedDate:"December 19th 2018",editedByType:"Edited by",bookSignature:"Miroslav Blumenberg",hash:"6def75cd4b6b5324a02b6dc0359896d0",volumeInSeries:2,fullTitle:"Keratin",editors:[{id:"31610",title:"Dr.",name:"Miroslav",middleName:null,surname:"Blumenberg",slug:"miroslav-blumenberg",fullName:"Miroslav Blumenberg",profilePictureURL:"https://mts.intechopen.com/storage/users/31610/images/system/31610.jpg",biography:"Miroslav Blumenberg, Ph.D., was born in Subotica and received his BSc in Belgrade, Yugoslavia. He completed his Ph.D. at MIT in Organic Chemistry; he followed up his Ph.D. with two postdoctoral study periods at Stanford University. Since 1983, he has been a faculty member of the RO Perelman Department of Dermatology, NYU School of Medicine, where he is codirector of a training grant in cutaneous biology. Dr. Blumenberg’s research is focused on the epidermis, expression of keratin genes, transcription profiling, keratinocyte differentiation, inflammatory diseases and cancers, and most recently the effects of the microbiome on the skin. He has published more than 100 peer-reviewed research articles and graduated numerous Ph.D. and postdoctoral students.",institutionString:null,institution:{name:"New York University Langone Medical Center",institutionURL:null,country:{name:"United States of America"}}}]},{type:"book",id:"7978",title:"Vitamin A",subtitle:null,coverURL:"https://cdn.intechopen.com/books/images_new/7978.jpg",slug:"vitamin-a",publishedDate:"May 15th 2019",editedByType:"Edited by",bookSignature:"Leila Queiroz Zepka, Veridiana Vera de Rosso and Eduardo Jacob-Lopes",hash:"dad04a658ab9e3d851d23705980a688b",volumeInSeries:3,fullTitle:"Vitamin A",editors:[{id:"261969",title:"Dr.",name:"Leila",middleName:null,surname:"Queiroz Zepka",slug:"leila-queiroz-zepka",fullName:"Leila Queiroz Zepka",profilePictureURL:"https://mts.intechopen.com/storage/users/261969/images/system/261969.png",biography:"Prof. Dr. Leila Queiroz Zepka is currently an associate professor in the Department of Food Technology and Science, Federal University of Santa Maria, Brazil. She has more than fifteen years of teaching and research experience. She has published more than 550 scientific publications/communications, including 15 books, 50 book chapters, 100 original research papers, 380 research communications in national and international conferences, and 12 patents. She is a member of the editorial board of five journals and acts as a reviewer for several national and international journals. Her research interests include microalgal biotechnology with an emphasis on microalgae-based products.",institutionString:"Universidade Federal de Santa Maria",institution:{name:"Universidade Federal de Santa Maria",institutionURL:null,country:{name:"Brazil"}}}]},{type:"book",id:"7953",title:"Bioluminescence",subtitle:"Analytical Applications and Basic Biology",coverURL:"https://cdn.intechopen.com/books/images_new/7953.jpg",slug:"bioluminescence-analytical-applications-and-basic-biology",publishedDate:"September 25th 2019",editedByType:"Edited by",bookSignature:"Hirobumi Suzuki",hash:"3a8efa00b71abea11bf01973dc589979",volumeInSeries:4,fullTitle:"Bioluminescence - Analytical Applications and Basic Biology",editors:[{id:"185746",title:"Dr.",name:"Hirobumi",middleName:null,surname:"Suzuki",slug:"hirobumi-suzuki",fullName:"Hirobumi Suzuki",profilePictureURL:"https://mts.intechopen.com/storage/users/185746/images/system/185746.png",biography:"Dr. Hirobumi Suzuki received his Ph.D. in 1997 from Tokyo Metropolitan University, Japan, where he studied firefly phylogeny and the evolution of mating systems. He is especially interested in the genetic differentiation pattern and speciation process that correlate to the flashing pattern and mating behavior of some fireflies in Japan. He then worked for Olympus Corporation, a Japanese manufacturer of optics and imaging products, where he was involved in the development of luminescence technology and produced a bioluminescence microscope that is currently being used for gene expression analysis in chronobiology, neurobiology, and developmental biology. Dr. Suzuki currently serves as a visiting researcher at Kogakuin University, Japan, and also a vice president of the Japan Firefly Society.",institutionString:"Kogakuin University",institution:null}]}]},openForSubmissionBooks:{},onlineFirstChapters:{},subseriesFiltersForOFChapters:[],publishedBooks:{},subseriesFiltersForPublishedBooks:[],publicationYearFilters:[],authors:{}},subseries:{item:{},onlineFirstChapters:{},publishedBooks:{},testimonialsList:[]},submityourwork:{pteSeriesList:[],lsSeriesList:[],hsSeriesList:[],sshSeriesList:[],subseriesList:[],annualVolumeBook:{},thematicCollection:[],selectedSeries:null,selectedSubseries:null},seriesLanding:{item:null},libraryRecommendation:{success:null,errors:{},institutions:[]},route:{name:"chapter.detail",path:"/chapters/19680",hash:"",query:{},params:{id:"19680"},fullPath:"/chapters/19680",meta:{},from:{name:null,path:"/",hash:"",query:{},params:{},fullPath:"/",meta:{}}}},function(){var e;(e=document.currentScript||document.scripts[document.scripts.length-1]).parentNode.removeChild(e)}()