International frameworks and standards defining ESG factors.
\\n\\n
Released this past November, the list is based on data collected from the Web of Science and highlights some of the world’s most influential scientific minds by naming the researchers whose publications over the previous decade have included a high number of Highly Cited Papers placing them among the top 1% most-cited.
\\n\\nWe wish to congratulate all of the researchers named and especially our authors on this amazing accomplishment! We are happy and proud to share in their success!
Note: Edited in March 2021
\\n"}]',published:!0,mainMedia:{caption:"Highly Cited",originalUrl:"/media/original/117"}},components:[{type:"htmlEditorComponent",content:'IntechOpen is proud to announce that 191 of our authors have made the Clarivate™ Highly Cited Researchers List for 2020, ranking them among the top 1% most-cited.
\n\nThroughout the years, the list has named a total of 261 IntechOpen authors as Highly Cited. Of those researchers, 69 have been featured on the list multiple times.
\n\n\n\nReleased this past November, the list is based on data collected from the Web of Science and highlights some of the world’s most influential scientific minds by naming the researchers whose publications over the previous decade have included a high number of Highly Cited Papers placing them among the top 1% most-cited.
\n\nWe wish to congratulate all of the researchers named and especially our authors on this amazing accomplishment! We are happy and proud to share in their success!
Note: Edited in March 2021
\n'}],latestNews:[{slug:"intechopen-supports-asapbio-s-new-initiative-publish-your-reviews-20220729",title:"IntechOpen Supports ASAPbio’s New Initiative Publish Your Reviews"},{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"}]},book:{item:{type:"book",id:"3403",leadTitle:null,fullTitle:"Management Strategies to Adapt Alpine Space Forests to Climate Change Risks",title:"Management Strategies to Adapt Alpine Space Forests to Climate Change Risks",subtitle:null,reviewType:"peer-reviewed",abstract:'Climate scenarios suggest that current forest stands will face radically different temperature and precipitation conditions in the future. Developing future strategies for forest management in the face of uncertain and highly variable forecasts of future site conditions is a great challenge. Here we have analyzed transnational case studies dealing with different manifestations of climate change effects. We intend to stimulate the discussion on management strategies to adapt forests in the Alps to climate change risks.\nThe presented results are derived from the INTERREG project "Management Strategies to Adapt Alpine Space Forests to Climate Change Risks" that was implemented within the framework of the European Territorial Cooperation "Alpine Space Programme" 2007-2013.',isbn:null,printIsbn:"978-953-51-1194-8",pdfIsbn:"978-953-51-4240-9",doi:"10.5772/56933",price:139,priceEur:155,priceUsd:179,slug:"management-strategies-to-adapt-alpine-space-forests-to-climate-change-risks",numberOfPages:396,isOpenForSubmission:!1,isInWos:1,isInBkci:!0,hash:"b560c2950b8adbadfb2cfa9de3958030",bookSignature:"Gillian Ann Cerbu, Marc Hanewinkel, Giacomo Gerosa and Robert Jandl",publishedDate:"August 28th 2013",coverURL:"https://cdn.intechopen.com/books/images_new/3403.jpg",numberOfDownloads:44122,numberOfWosCitations:63,numberOfCrossrefCitations:26,numberOfCrossrefCitationsByBook:3,numberOfDimensionsCitations:72,numberOfDimensionsCitationsByBook:5,hasAltmetrics:1,numberOfTotalCitations:161,isAvailableForWebshopOrdering:!0,dateEndFirstStepPublish:"April 30th 2012",dateEndSecondStepPublish:"May 31st 2012",dateEndThirdStepPublish:"May 31st 2012",dateEndFourthStepPublish:"August 31st 2012",dateEndFifthStepPublish:"December 23rd 2012",currentStepOfPublishingProcess:5,indexedIn:"1,2,3,4,5,6,8,9",editedByType:"Edited by",kuFlag:!1,featuredMarkup:null,editors:[{id:"157359",title:"Dr.",name:"Gillian",middleName:null,surname:"Cerbu",slug:"gillian-cerbu",fullName:"Gillian Cerbu",profilePictureURL:"https://mts.intechopen.com/storage/users/157359/images/5397_n.jpg",biography:"Gillian Ann Cerbu is currently employed as a Forestry & Climate \nChange consultant. Prior to this, as part of her role as MANFRED \nproject manager, Gillian coordinated the implementation of deliverables the results of which are included in this publication. She is currently working on her Ph.D. on climate change mitigation in tropical forests \n(REDD+) as part of the Graduate School, ‘Environment, Society and Global Change’ at the University of Freiburg in Germany.",institutionString:null,position:null,outsideEditionCount:0,totalCites:0,totalAuthoredChapters:"1",totalChapterViews:"0",totalEditedBooks:"1",institution:{name:"Forstliche Versuchs- und Forschungsanstalt Baden-Württemberg",institutionURL:null,country:{name:"Germany"}}}],equalEditorOne:null,equalEditorTwo:null,equalEditorThree:null,coeditorOne:{id:"164924",title:"Prof.",name:"Marc",middleName:null,surname:"Hanewinkel",slug:"marc-hanewinkel",fullName:"Marc Hanewinkel",profilePictureURL:"https://mts.intechopen.com/storage/users/164924/images/system/164924.jpg",biography:null,institutionString:null,position:null,outsideEditionCount:0,totalCites:0,totalAuthoredChapters:"3",totalChapterViews:"0",totalEditedBooks:"0",institution:{name:"Swiss Federal Institute for Forest, Snow and Landscape Research",institutionURL:null,country:{name:"Switzerland"}}},coeditorTwo:{id:"43539",title:"Dr.",name:"Giacomo",middleName:"Al.",surname:"Gerosa",slug:"giacomo-gerosa",fullName:"Giacomo Gerosa",profilePictureURL:"https://mts.intechopen.com/storage/users/43539/images/115_n.jpg",biography:"Dr. Giacomo A. Gerosa, MD in Environmental Sciences (1997), PhD in Agricultural Ecology (2002); is ecologist and ecophysiologist with main research interests on the characterization of the exchange processes between atmosphere and biosphere, and on the effects of air pollutants on agricultural and forest ecosystems, with special regards to ozone. He is a researcher at the Department of Mathematics and Physics of the Catholic University of the Scared Heart of Brescia, Italy and professor of Ecology, Chemistry, Biology and Micrometeorology at the Faculty of Mathematics, Physics and Natural sciences of the same University. Formerly he was a professor of Ecotoxycology, Pollutants Control in Agricultural Environment, and Use and Recycle of Biomasses in Agriculture. He is a Scientific Director of CRINES (Center of Research on Air Pollution and Ecosystems) at Curno (Bergamo); Chair of the Laboratory of Ecophysiology and Environmental Physics of the Department of Mathematics and Physics at the Catholic University of SC of Brescia and President of Ecometrics Ltd., a Spin-Off company of the Catholic University of SC of Brescia. He is currently involved in many national and European research projects as a scientific reference for the Catholic University. He is the author of more than 60 papers in international peer reviewed journals and books, and referee for about 10 journals.",institutionString:null,position:null,outsideEditionCount:0,totalCites:0,totalAuthoredChapters:"7",totalChapterViews:"0",totalEditedBooks:"1",institution:{name:"Catholic University of the Sacred Heart",institutionURL:null,country:{name:"Italy"}}},coeditorThree:{id:"129604",title:"Dr.",name:"Robert",middleName:null,surname:"Jandl",slug:"robert-jandl",fullName:"Robert Jandl",profilePictureURL:"https://mts.intechopen.com/storage/users/129604/images/5463_n.jpg",biography:"Robert Jandl is a Research Coordinator for Climate Change Issues at the Austrian Forest Research Center (BFW). He has received his training as a soil scientist and forest ecologist from the University of Natural Resources and Life Sciences, Vienna (BOKU). His research interests cover the ecology of mountain forests, biogeochemical cycles of carbon and nitrogen in forests, and the provision of ecosystem services by forests. A particular research emphasis is on climate manipulation experiments.",institutionString:null,position:null,outsideEditionCount:0,totalCites:0,totalAuthoredChapters:"7",totalChapterViews:"0",totalEditedBooks:"0",institution:{name:"Austrian Research Centre for Forests",institutionURL:null,country:{name:"Austria"}}},coeditorFour:null,coeditorFive:null,topics:[{id:"874",title:"Climate Change",slug:"environmental-sciences-forestry-science-climate-change"}],chapters:[{id:"45371",title:"Management Strategies to Adapt Alpine Space Forests to Climate Change Risks – An Introduction to the Manfred Project",doi:"10.5772/56267",slug:"management-strategies-to-adapt-alpine-space-forests-to-climate-change-risks-an-introduction-to-the-m",totalDownloads:2695,totalCrossrefCites:1,totalDimensionsCites:6,hasAltmetrics:0,abstract:null,signatures:"Robert Jandl, Gillian Cerbu, Marc Hanewinkel, Fred Berger,\nGiacomo Gerosa and Silvio Schüler",downloadPdfUrl:"/chapter/pdf-download/45371",previewPdfUrl:"/chapter/pdf-preview/45371",authors:[{id:"157359",title:"Dr.",name:"Gillian",surname:"Cerbu",slug:"gillian-cerbu",fullName:"Gillian Cerbu"},{id:"164924",title:"Prof.",name:"Marc",surname:"Hanewinkel",slug:"marc-hanewinkel",fullName:"Marc Hanewinkel"},{id:"43539",title:"Dr.",name:"Giacomo",surname:"Gerosa",slug:"giacomo-gerosa",fullName:"Giacomo Gerosa"},{id:"129604",title:"Dr.",name:"Robert",surname:"Jandl",slug:"robert-jandl",fullName:"Robert Jandl"},{id:"160243",title:"Dr.",name:"Silvio",surname:"Schueler",slug:"silvio-schueler",fullName:"Silvio Schueler"},{id:"165100",title:"Dr.",name:"Frédéric",surname:"Berger",slug:"frederic-berger",fullName:"Frédéric Berger"}],corrections:null},{id:"44073",title:"Developing a Background for Forest Adaptation Strategies in the Alps: A Perspective for Policy Building",doi:"10.5772/56274",slug:"developing-a-background-for-forest-adaptation-strategies-in-the-alps-a-perspective-for-policy-buildi",totalDownloads:1815,totalCrossrefCites:0,totalDimensionsCites:1,hasAltmetrics:0,abstract:null,signatures:"Luca Cetara and Federico Mannoni",downloadPdfUrl:"/chapter/pdf-download/44073",previewPdfUrl:"/chapter/pdf-preview/44073",authors:[{id:"159989",title:"Dr.",name:"Luca",surname:"Cetara",slug:"luca-cetara",fullName:"Luca Cetara"},{id:"165433",title:"MSc.",name:"Federico",surname:"Mannoni",slug:"federico-mannoni",fullName:"Federico Mannoni"}],corrections:null},{id:"45271",title:"Future Climate of the European Alps",doi:"10.5772/56278",slug:"future-climate-of-the-european-alps",totalDownloads:2934,totalCrossrefCites:3,totalDimensionsCites:12,hasAltmetrics:0,abstract:null,signatures:"Niklaus E. 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Zimmermann, Robert Jandl, Marc Hanewinkel, Georges\nKunstler, Christian Kölling, Patrizia Gasparini, Andrej Breznikar,\nEliane S. Meier, Signe Normand, Ulrich Ulmer, Thomas\nGschwandtner, Holger Veit, Maria Naumann, Wolfgang Falk, Karl\nMellert, Maria Rizzo, Mitja Skudnik and Achilleas Psomas",downloadPdfUrl:"/chapter/pdf-download/45219",previewPdfUrl:"/chapter/pdf-preview/45219",authors:[{id:"165202",title:"Prof.",name:"Niklaus",surname:"Zimmermann",slug:"niklaus-zimmermann",fullName:"Niklaus Zimmermann"}],corrections:null},{id:"45243",title:"Risk Assessment for Biotic Pests Under Prospective Climate Conditions",doi:"10.5772/56410",slug:"risk-assessment-for-biotic-pests-under-prospective-climate-conditions",totalDownloads:1819,totalCrossrefCites:0,totalDimensionsCites:0,hasAltmetrics:0,abstract:null,signatures:"Holger Griess, Holger Veit and Ralf Petercord",downloadPdfUrl:"/chapter/pdf-download/45243",previewPdfUrl:"/chapter/pdf-preview/45243",authors:[{id:"165597",title:"Mr.",name:"Holger",surname:"Griess",slug:"holger-griess",fullName:"Holger Griess"}],corrections:null},{id:"45221",title:"Abiotic Stressors – Fire Hazard",doi:"10.5772/56273",slug:"abiotic-stressors-fire-hazard",totalDownloads:2140,totalCrossrefCites:0,totalDimensionsCites:1,hasAltmetrics:0,abstract:null,signatures:"Bruna Comini, Giampaolo Cocca, Elena Gagliazzi, Paolo Nastasio,\nEnrico Calvo, Roberto Colombo, B. 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In order to be effective, herbicides must overcome a variety of barriers (morphological, biological, and environmental) to their entry into plants. For example, trichomes on the leaf surface can reduce herbicide efficacy by intercepting spray droplets before they contact the epidermal surface [11]. Environmental stress (e.g., hot, dry weather) may develop a thicker than normal wax layer, or increase other defensive structures such as reducing the plant’s metabolic and transport processes that are required for adequate weed control.
Because of these reasons, adjuvants have been developed to assist herbicides, in that they:
Allow better mixing and handling with herbicide active ingredient [12]
Reduce or even eliminate spray application problems [13] (e.g., drift reduction) [14,15]
Allow contact to the weed target, increase droplet coverage, spray retention, and droplet drying [16,17]
Increase herbicide cuticle penetration and cellular accumulation [18,19]
Significantly enhance and improve an herbicide’s efficacy so that the concentration or total amount of herbicide required to achieve a given effect is reduced [20-26]
Decrease the amount of herbicide applied and lower total costs for weed control [27,28]
Enhance the formulation’s ability to kill the targeted species without harming other plants [29]
From an environmental aspect, can reduce leaching of herbicide through the soil profile [30,31]
However, it is important to note that in some circumstances, adding adjuvants will not significantly improve control [32]. Sometimes adjuvants can have negative effects, such as:
The history of adjuvants in agriculture dates back to the 18th and 19th centuries when additives such as resins, tar, flour, molasses, and sugar were used with lime, sulfur, copper or arsenates to improve adherence and biological performance of active ingredients by modifying the physicochemical properties of the spray solution [40].
The first agricultural adjuvant was a soap solution (Gillette 1888, 1890) (cit. by Hazen, [41]). Soap solutions and kerosene were used in the United States to kill insect eggs or were added to arsenical solutions to increase toxicity to weeds [42]. Animal oil soaps were common adjuvants in use before 1900, as well (Gillette1889) (cit. by Hazen, [41]). They were derived from animals, fish, and whale oil and were used to enhance the pesticide performance. Sugars and glue were considered as stickers and many other materials followed as adjuvant research continued [43].
The modern era of synthetic organic pesticides began in the 1930s. The research behind medical (including antibiotics) and military uses funded research that led to the discovery of many pesticide families that are still in use today. An initial breakthrough in weed control occurred with the introduction of 2,4-D in the 1940s for broad-spectrum broadleaf weed control in corn and cereal crops [44]. Soaps and mineral oils were replaced by nonionic surfactants. Nitrogen fertilizers like ammonium sulfate (AMS) and urea ammonium nitrate (UAN) were also used to enhance the herbicidal activity while glycerin was introduced as humectant.
In the 1960s and 1970s, modern types of adjuvants such as crop oil concentrates (COC) were developed, which were used to reduce doses of atrazine and to lower spray volumes. Organosilicone-based adjuvants, nonionic surfactants (NIS), which have excellent wetting and spreading capability and enhance the penetration of post-emergent herbicides, were developed later [45].
There are over 3,000 adjuvants available for use. These can be grouped into three general types:
Activators,
Spray modifiers and
Utility modifiers
Activators modify certain herbicide characteristics, including particle size and viscosity of the herbicide spray, evaporation rate, etc. Usually, they increase herbicide activity, herbicide spread, absorption into plant tissue, and rainfastness, and decrease photodegradation of the herbicide.
There are three categories of activators: surfactants, wetting agents, and oils.
Surfactants (SURFace ACTive AgeNTS) are a type of activators designed to improve the dispersing/emulsifying, absorbing, spreading, wetting, sticking, and/or penetrating properties of the spray mixture [6]. Surfactants primarily influence the ability of herbicides to penetrate the leaf\'s waxy cuticle. Most herbicides are prepared in a solution of water. Water is a chemically polar material and thus can be repelled by the waxy surface of leaves. Water containing a surfactant reduces the surface tension of water on plants, spread in a wet thin layer over a waxy leaf surface, and allow the herbicide formulation to enter into the plant.
Surfactants can be classified in four groups on the basis of the ability to ionize the aqueous solution. Those groups are:
Nonionic — are the most commonly used in agriculture and can be mixed readily with any herbicide. They produce little or no ionization in water (no electrical charge). Organosilicone and silicone surfactants are two types of nonionic surfactants.
Cationic — are not often used with herbicides. They have a positive charge,
Anionic — rarely used with herbicides, but mainly used in cosmetics, household cleaners, many domestic detergents, etc. They have a negative charge, and
Ampholytic (amphoteric) — have a both positive and negative charge, that is, in aqueous solution are capable forming cations or anions.
Wetting agents increase the ability of water to displace air or liquids from the leaf surface, allowing it to be wet by the herbicide. Wetting agents help spread the solution more evenly over the leaf.
Oils increase the retention time of a solution on leaves, allowing for an increase in herbicide uptake. Oils mostly contain emulsifiers to allow them to mix with water. Some claims regarding oils include reduced rainfast periods, more uniform droplet size (drift reduction), less spray evaporation, and better penetration of herbicide into waxy leaves.
All oils are basically mineral oils with different contents of surfactant in formulation (3%--20%). They can be classified as:
Crop oils
Dormant oils
Crop oil concentrates
Vegetable oils
Vegetable oil concentrate
Modified vegetable oil, and
Modified vegetable oil concentrate
Crop oils are emulsifiable petroleum oil-based products containing up to 5% w/w surfactant and the remainder of phytobland oil.
Dormant oils are horticultural spray oils applied during the dormant phase of the targeted plant [2]. There are ‘‘quick-break’’ or dormant oils that use a very low amount (2%--5%) of emulsifier for dispersion into the spray tank [41].
COC are the most commonly used oils in agriculture. They were introduced to the market in the 1960s [45]. COC are emulsifiable petroleum oil-based products containing 5%--20% w/w surfactant and a minimum of 80% w/w phytobland oil [2]. COC enhanced activity of aryloxyphenoxy propionates, cyclohexadinones, triazines, phenoxy acid urea herbicides, imidazolinones, etc. [46,47,26].
Vegetable oils are also used as herbicide adjuvants. The base in formulation is oil from sunflower, soybean, oilseed rape, peanut, or corn, which is combined with surfactants in different content.
Vegetable oil concentrates are emulsifiable vegetable oil products containing 5%--20% w/w surfactant and a minimum of 80% w/w vegetable oil [2]. There are some vegetable oil concentrates used in the same manner as the crop oil concentrates, typically based upon canola or soybean oil, using 5%--10% emulsifier for dispersion [41].
Modified vegetable oil is oil extracted from seeds that have been chemically modified. Methylated seed oils (MSO) are vegetable oils mainly from oilseed rape or sunflower esterified with alcohol ethanol to get methyl esters.
Modified vegetable oil concentrate is an emulsifiable, chemically modified vegetable oil product containing 5%--20% w/w surfactant and remain chemically modified vegetable oil. Some of the best vegetable-based products are those modified (derivatized) to methyl and other lower alkyl esters such as methylated soybean oil, methyl sunflowerate, or ethyl canolate.
Spray modifiers affect the delivery and placement of the spray solution. They confine or alter the physicochemical characteristics of the spray solution [48], and make the herbicide spray easier to aim, reduce herbicide drift in the air, and cause the spray to more readily adhere to the plant. Spray modifiers include:
Thickening agents (i.e., invert emulsions and polymers)
Stickers
Spreaders
Spreader-stickers
Foaming agents
Humectants, and
UV absorbents
Thickening agents modify the viscosity (thickness) of spray mixtures. They control drift or slow evaporation after the spray has been deposited on the target area. Slowing evaporation is important when using systemic herbicides, because they can penetrate the plant cuticle only as long as they remain in solution. Invert emulsions, polymers, and
Invert emulsions are mixtures of inverting oil and water, having a mayonnaise-like appearance on the water surface and a snowflake-like appearance under the water surface. Depending on their solubility, herbicides dissolve in either the oil or water component. The oil in the case of
Polymers are a very large, chain-like carbon molecules made up of monomers, up to 40,000 carbons in length, forming a thick mucus-like material which helps to break the surface tension of water and enhance sinking of herbicides [50,51].
Drift control agents modify spray characteristics to reduce spray drift, usually by minimizing small droplet formation. They are generally polyacrylamide or polyvinyl polymers [52].
Stickers assists the spray deposit to adhere or stick to the the leaf surface and may be measured in terms of resistance to time, wind, water, mechanical action, or chemical action [2]. Stickers may be heavy petroleum fractions, water-soluble polymers, acrylic latex, epoxidized seed oils (similar to boiled linseed oil, which dries on exposure to air), or alkylphenol condensates called resins. Stickers are commonly used in field crops (like corn and soybeans) where residue on leaves is not a problem. They are usually used for application of fungicides and insecticides rather than herbicides.
Spreaders are compounds that cause the surface tension of the herbicide to be reduced in such a way that it easily spreads into a very thin film over a leaf surface. Spreaders increase the efficiency of the herbicide dramatically. Typically, the alcohol ethoxylates [53] such as tridecanol ethylene oxide allow a spread diameter increase of two to three times. They may contain fatty acids, latex, aliphatic alcohols, crop oils such as cottonseed, or inorganic oils.
Spreader-stickers are essentially combinations of stickers and spreaders. They provide additional retention of herbicide in wet conditions. They are usually used with contact insecticides and fungicides for which complete coverage is critical.
Foaming Agents are compounds that facilitate formation of foam for reducing drift and evaporation. These agents are used infrequently for drift control of herbicide applications.
Humectants, like stickers, increase the amount of time that the herbicide is on the leaf, in a form available for uptake [41]. When water evaporates from the spray droplet and the herbicide becomes a crystalline residue, it is no longer available for uptake into the leaf. Humectants keep the spray deposit moist and in true solution, and therefore extend the time that it is available for absorption [54].
UV absorbents protect herbicides from the deleterious effect(s) of sunlight. They may do this by either physical or chemical processes, such as by increasing the rate of herbicide uptake into the cuticle, or by absorbing the UV-light themselves.
Utility modifiers help minimize handling and application problems. They do not directly improve efficacy, but widen the conditions when an herbicide can be used or maintain the integrity of the spray solution. For example, utility modifiers reduce foaming, increase solubility, modify pH, or reduce spray drift.
Types of modifiers include emulsifiers, dispersants, stabilizing agents, coupling agents, co-solvents, compatibility agents, buffering agents, antifoam agents, and ammonium fertilizers.
Emulsifiers are molecules with one hydrophilic and one hydrophobic end. They make it possible for water and oil to become finely dispersed in each other, creating a stable, homogeneous, smooth emulsion. Most crop oils contain emulsifiers to allow them to mix with water and some contain various levels of surfactants.
Dispersants are chemicals that are sprayed on a surface oil slick to break down the oil into smaller droplets that more readily mix with the water. These water soluble dispersants have been found to be unique and highly effective dispersants for water insoluble agricultural suspension concentrate formulations.
Stabilizing agents act as thickening or gelling agents that increase the viscosity of the final product. These agents stabilize emulsions, either by adsorbing to the outer surface of oil droplets. Stabilization can be achieved in agricultural suspension and emulsion through the use of fine-particle-size solids and fine liquid droplets in the disperse phase along with appropriate dispersants and wetting agents.
Coupling agents are compounds which provide a chemical bond between two dissimilar materials, usually an inorganic and an organic. Organosilanes are well-suited in this application because of the ability to incorporate an organic-compatible functionality and an inorganic-compatible functionality within the same molecule.
Cosolvents are defined as water-miscible organic solvents that are used in liquid herbicide formulations to increase the solubility of poorly water-soluble substances or to enhance the chemical stability of an herbicide.
Compatibility agents allow simultaneous application of two or more ingredients. They are most often used when herbicides are applied in liquid fertilizer solutions.
Buffering agents are used to change the pH and hardness of the water and to increase the dispersion or solubility of herbicides in alkaline or acid waters used in making up an herbicide solution. Ammonium sulfate (AMS) is sometimes added to reduce hard water problems.
Antifoam agents reduce foaming in spray mixtures that require vigorous agitation. They are particularly useful in soft water. Antifoam agents are usually siliconebased and used at 0.1% or less of the total spray volume [55].
Ammonium fertilizers are often added to spray solutions with foliar applied herbicides. The two most common ammonium fertilizers used are ammonium sulfate (AMS) and urea ammonium nitrate (UAN) solution (28-0-0). The exact mechanism of action for ammonium fertilizers is not known although increased herbicide uptake into plant has been reported [26].
Surfactants are the most widely used and probably the most important of all adjuvants [56]. They can be especially effective in improving the biological activity of many herbicides [57-59]. Nonionic surfactants (NIS) improved the effect of nicosulfuron [58] and enhanced glyphosate absorption, which was 20 times greater and the spread of spray drop was 200 greater than with no adjuvants added [60].
Several researchers have observed that adjuvant efficacy is dependent on the herbicide being applied and the characteristics of the target weed species [61-63]. For example, MSO increase foliar absorption and efficacy of many herbicides, including primisulfuron, rimsulfuron, imazethapyr, quinclorac, and several graminicides for grass weed control [21,64-66]. MSO was the only adjuvant used with foramsulfuron that provided acceptable giant foxtail control (
NIS have been effective in improving the activity of several sulfonylurea herbicides, including primisulfuron, rimsulfuron, and thifensulfuron, as well [57,58,68]. MSO and COC have been shown to further enhance the effectiveness of several herbicides on certain weed species, including nicosulfuron [23]. These adjuvants enhanced the effectiveness of chlorimuron and imazethapyr on purple nutsedge (
The addition of AMS or UAN to the spray solution can enhance herbicide effectiveness by further increasing herbicide absorption [26,72] which gives better result up to 12%--13.5% than use of herbicide alone [73]. For instance, thifensulfuron absorption into velvetleaf (
Considering environmental factors, rain shortly after an herbicide application is one of the most detrimental issues for herbicide performance. Adjuvants have been shown to improve the rainfastness of herbicides and the effect on rainfastness should be considered when selecting an adjuvant [90,91]. A number of studies have been published that outline the beneficial effects of OSL adjuvants in reducing the critical rain-free period after the foliar herbicidal application. Field and Bishop [92], Reddy and Singh [93], and Roggenbuck
Studies with 14C-labeled glyphosate have demonstrated that plants absorb as little as 22% of the amount applied; however, the addition of surfactant improved absorption up to 35% [94]. For instance, the OSL adjuvants produced rapid absorption of the 14C-glyphosate into the redroot pigweed (
In contrast to surfactants, water repellent adjuvants increase surface tension, thus inhibiting wetting of the leaf surface. The water repellent DC 1-6184 may have some utility for reducing corn injury when isoxaflutole is applied to corn foliage at early growth stages [99]. These results are consistent with the observation of Nelson and Penner [100] that DC 1-6184 applied in combination with herbicide safener R-29148 and isoxaflutole reduced injury to spike-stage corn (28%) as compared with isoxaflutole applied alone (53%) or isoxaflutole applied with only R-29148 (37%). Penner and Fausey [101] found that DC 1-6184 consistently reduced retention of flumioxazin spray on plant foliage by increasing the number of droplets that bounced off the foliage. Flumioxazin spray had the greatest retention of all herbicide treatments on tomato when DC 1-6184 was included. Also, the same water repellent, DC 1-6184, reduced isoxaflutole retention on tomato, wheat, and cabbage [100].
From an environmental aspect, adjuvants can weakly bind herbicides and release them slowly in order to prolong the efficacy of herbicides and to minimize their leaching into groundwater. Enersol 12% adjuvant resulted in a 13%–18% reduction in leaching of dicamba and bromacil in five pore volumes of leachate. The leaching of simazine was significantly decreased when charcoal, three humic substances (Enersol SP 85%, Enersol 12%, and Agroliz), and a synthetic polymer (Hydrosorb) were used. However, the decrease in leaching was significantly greater when using Enersol SP 85% or Enersol 12% (24%–28%) than when using the other adjuvants (12%–16%) [30]. In a study by Locke
In many situations, as mentioned earlier, adjuvants can significantly enhance an herbicide’s effect [25]. However, it is important to note that in some circumstances, adding adjuvants will not significantly improve control. For example, several studies have shown that the addition of AMS to herbicides increases the control of
Sometimes adjuvants can decrease the killing power of the herbicide (antagonistic effects). The efficacy of sethoxydim or clethodim on large crabgrass [
Some adjuvants can increase harmful effects to non-target plants. Imazamox applied at 108 g/ha plus 1% (v/v) MSO applied in the fall consistently injured all wheat cultivars more than the same rate with NIS at 0.25% and 54 g/ha imazamox regardless of adjuvant and timing [37]. Injury caused by these treatments ranged from 23%to 70% for all cultivars. Adjuvant affected cotton injury from CGA 362622. NIS resulted in increased cotton injury at 29%, whereas COC increased cotton injury to 37%. [110]. Crooks
Sometimes adjuvants can have negative effects, such as increasing the formulation’s ability to spread or persist in the environment where it is not wanted. According to Kucharski and Sadowski [113], the addition of adjuvants caused an increase of the residues of active ingredients in the soil and roots of sugar beet compared to plots with a reduced dose of herbicide without adjuvants. Swarcewicz [114] and Swarcewicz
The agricultural adjuvants market, in terms of value, is projected to reach $3,183.04 million by 2019, at a CAGR of around 5.6% from 2014 [115]. Numerous factors such as, easy application, modern production practices, new product offerings, increased availability, increasing infestation of pests and diseases, and government regulations to protect the environment from hazardous chemical usage are the major drivers of the agricultural adjuvants market. Adjuvants are quietly helping to revolutionize the agrochemical business as they are the best tools for farmers to improve application, facilitate the right dosage, and achieve more cost-effective, better targeted, and environmentally acceptable pest control. Agricultural adjuvants play an essential role in the performance of most herbicides, fungicides, and insecticides, and function by transforming the dosage from preventative, high-dose applications to low dosages, specifically targeted for curative applications.
From all previous research mentioned, it can be concluded that the herbicide-adjuvant--plant-environment interaction is a complex system. Understanding the different roles of adjuvants in the behavior of herbicides is essential for their optimum utilization. Adjuvants can improve the biological activity of the herbicide active ingredient, the performance of the spray application, and the economics of herbicide applications, but in some circumstances adjuvants can manifest negative effects. Therefore, there is no universal adjuvant that can improve the performance for all herbicides, against all weeds, or under all environmental conditions. The herbicide and adjuvant selected and the relative amounts used must be tailored to the specific conditions of each application.
The chapter describes the change of banking regulation toward governance and environmental sustainability challenges. It shows that it has not been fully understood how these new types of environmental and social risks affect differently banking activity. As risks are global and systemic, it is necessary regulatory coordination. The main international and European initiative to assess the relevance of environmental climate risks for banking regulation considers some banking policy recommendations for countries to coordinate their regulatory actions. This is due to the fact that banks play a crucial role in providing credit and financial resources that can be used to mitigate the negative effects of environmental risks enabling the economy to become more resilient.
Regulators are now aware that there are linkages between natural disasters and financial market instability. In fact, climate change could potentially threaten financial resilience in general and economic prosperity over the longer term.
In recent times, the frequency and intensity of natural disasters have increased, causing much greater damage to economies. The negative effects are not only physical and material, but they can lead to high loan losses and provisioning for banks located in those areas with hard difficulties.
The main environmental risks create potentially negative externalities for the banking sector and for this reason banks are analyzing these risks and are putting them into their risk management models and governance frameworks.
By affording these challenges, banks also play an important role in supporting the economy’s adaptation to environmental changes and in creating financial resilience to environmental risks. For this reason, new loan policies are devoted to reallocating credit to more sustainable sectors of the economy; by doing so banks contribute to reducing environmental sustainability risks, mitigating their impact.
Banks are facing these risks by adopting different types of green banking practices. These practices are referred to as the option of the ESG guidelines with a particular focus on risk management in the area of project finance and the allocation of credit to renewable energy resources. Other practices are specifically positioned to mobilize capital to the green economy, including renewable and clean energy projects by making loans and investments, and structuring specialized transactions [1].
Banks are facing new challenges. For this reason the European regulatory framework for sustainable finance has greatly developed. European leadership in sustainable finance has given rise to several regulations. In particular, banks will consider the CRR Pillar 3 and EU taxonomy disclosures, also because EBA is also aligning its position to this view.
The structural shift toward the green transition and the climate crisis is exposing banks to physical and transition risks, which they need to be ready to manage. Banks will need to strengthen their risk management frameworks and reassess their business strategies. A recent ECB assessment shows that banks have made some progress in adapting their practices to manage these risks, but none are close to meeting the supervisory expectations [2]. For this reason, supervisors have already planned a number of specific measures for next years and beyond, including a thematic review of banks’ environmental risk management practices and a stress test on climate-related risks. Many of the proposed regulatory changes actually stem from research conducted by the European Banking Authority and the ECB and are focused on issues identified in the use of internal models by European banks. The chapter is structured with paragraph 2 that describes the relevance of ESG principles in the banking and financial sector and the source of ESG risks, with particular relevance for climate-related risk; paragraph 3 focuses on the difficulties of regulators to define so new rules and guidelines to define new strategies to control these new risks; paragraph 4 concludes the chapter pointing out the main policy implications of this new era for banks and financial institutions.
During the last years banking and financial sector has been involved in a great change, which has been characterized by the introduction of the new principles of Environmental Social and Governance (ESG). These principles are forcing banks toward an innovative vision of management both internal and external. It is known that there is a wide interpretation of the meaning of the ESG principles. In general, banks are becoming more and more active in investment and asset allocation, and in new business models as well. The attention to the environment and its exploitation, to the reduction of pollution or carbon emissions, are influencing their choices and strategies. New attention to social justice and social principles are very relevant so new governmental bodies are under control. The final goal is a more sustainable framework for financial activity with a selection of assets and sectors to finance.
The first step toward sustainable finance was the Action Plan of Financing Sustainable Growth, which was published in 2018 by the European Commission. The regulatory framework began to be defined to give banks and financial institutions a new scheme that granted the real development of innovative strategies about the introduction of sustainability principles as the basis for new growth of the financial system.
Beyond EC’s Action Plan there was EBA’s Plan which gave other guidelines to banks and rules about the adoption of ESG principles. In particular, it became necessary for regulators to implement ESG principles in their rules for the financial sector.
The definition of a complete framework of ESG principles is very important but it is still long to be completed; anyway it is important to reach a full acceptance and a full change toward sustainable finance.
The ESG principles are tied with the 2030 United Nations Sustainable Development Goals (SDG) agenda that considers environmental challenges, including climate change, as a major concern to the stability of the global economy. The most important step toward the control of the climate risk was the Paris Agreement was adopted in 2015 to strengthen the global response to the threat of climate change. Financial policy and regulation are increasingly recognized as important for managing the transition toward a more environmentally sustainable economy. The evolution to a more sustainable economy requires the adoption of new paradigms and the green guidelines in lending activity to reach a better selection of economic activities to finance [1]. At the same time, governmental or regulatory intervention is necessary to guide the banking sector in allocating more credit and investment to sustainable activity and in protecting the economy against related financial risks. The role of financial regulation in supporting the transition to a more sustainable economic path has been deemed critical by international organizations. The definition of ESG factors is not simple or easy also because there are a number of guidelines and rules formulated by various institutions. Table 1 presents the existing frameworks currently used by international institutions.
Framework | Year | Content |
---|---|---|
Equator Principles | 2003 | Guidelines used to identify, assess and manage environmental and social risks when financing projects |
Principles for Responsible Investment (PRI) | 2006 | Referred asset owners/institutional investors, investment managers, and service providers to incorporate ESG factors into their investment and ownership decision |
International Integrated Reporting Council (IIRC) | 2010 | Framework for integrated reporting along the lines of six capitals (financial, manufactured, intellectual, human, social and relationship and natural) |
International Finance Corporation Environmental and Social Performance Standards (IFC Performance Standards) | 2012 | Definition of IFC clients’ responsibilities for managing environmental and social risks. |
United Nations Sustainable Development Goals (SDGs) | 2015 | Collection of 17 interlinked global goals designed to be a blueprint to achieve a better and more sustainable future intended to be achieved by 2030 |
Global Sustainability Standards Board Global Reporting Initiative (GRI) | 2016 | Principles used by organizations to better understand, manage and communicate their impacts on sustainability-related issues |
OECD Due Diligence Guidance for Responsible Business Conduct | 2018 | Guidelines covering non-binding principles and standards for responsible business conduct in a global context consistent with applicable laws and internationally recognized standards |
Committee of Sponsoring Organizations of the Treadway Commission (COSO) and the World Business Council for Sustainable Development (WBCSD) Guidance for Applying Enterprise Risk Management to ESG-related risks | 2018 | Guidelines to overcome ESG-related risk challenges across the ERM process and provides methods for managing both upside and downside ESG-related risks. |
United Nations Environment Programme Finance Initiative (UNEP FI) | 2019 | Principles aiming at aligning banks’ business strategies with the objectives of the SDGs and the Paris Agreement |
Sustainability Accounting Standards Board (SASB) Standards | 2019 | Standards that help companies disclose financially-material sustainability information to investors |
World Economic Forum (WEF) report on ‘Measuring Stakeholder Capitalism’ | 2020 | Common metrics and disclosures on non-financial factors can be used by companies to align their mainstream reporting on performance against ESG indicators and track their contributions to the SDGs |
Recommendations of the Financial Stability Board Taskforce on Climate-related Financial Disclosures (TCFD) | 2017 | Framework to disclose climate-related risks and opportunities through their existing reporting processes. |
International Capital Market Association Green Bond Principles | 2017 1ST ed. updated 2021 | Principles for the qualification of green bonds |
Natural Capital Protocol + Supplement (Finance) | 2018 | Framework for organizations to identify, measure, and value their impacts and dependencies on natural capital. |
Climate Bond Initiative Climate Bonds Standard | 2018 | Sector-specific eligibility criteria for assets and projects that can be labeled as green investments |
Climate Disclosure Project (CDP), UN Global Compact (UNGC), World Resources Institute (WRI), and World Wildlife Fund (WWF) Science-Based Targets initiative (SBTi) | 2018 | Targets and guidelines referred to the Paris Agreement |
Partnership for Carbon Accounting Financials Global GHG Accounting and Reporting Standard for the Financial Industry | 2019 | Guidelines for the specific asset class |
International frameworks and standards defining ESG factors.
Elaboration from EBA 2021.
In Table 1, if one considers the frameworks addressing ESG factors, it can be noticed that the idea to have a wider vision of the factors different from the economic and financial ones, begins in 2003 with the Equator Principles that induce banks to consider and measure environmental and social risks in lending activity. The most recent Principles of UNEP FI are specifically devoted to the adoption of SDGs and the Paris Agreement in banking activity.
Guidelines, frameworks, and principles try to offer a multi-layer dimension of ESG factors. This effort is due to regulators’ position to recognize the relevance of these aspects for banks and to induce their choices and managerial strategies.
As concerns the environmental factors international institutions and authorities are working in recent times. It consists of guidelines and best practices proposed as suggestions to banks and financial institutions. These guidelines are important because they are the first step to having a uniform discipline about sustainable finance and green financial assets. On the basis of these initial definitions, banks and financial institutions must face new risks deriving from these factors that should be considered in financial management and the financial markets.
ESG factors are characterizing the definition of new strategies for banks and financial institutions. This paragraph starts from EBA’s definition of ESG risks and shows some considerations about their evaluation and management.
According to EBA [3] “
These risks may have different and typical features, due to their main causes and effects. ESG risks influence banking activity both in lending and in asset class allocation. For this reason, banks must classify ESG risks. By doing they must consider separately the three factors, Environmental, Social, and Governance. As concerns environmental risks, which are caused by a number of factors, banks must face both their physical impact and the effects of transition, as it is specifically happening in the so-called “green transition.” Social risks are caused by the diffusion of social inequality, health troubles, or the exploitation of human labor. The governance risks are important as well; and for example they are caused by corruption or similar in the board of directors of the company.
This complex articulation of such risks imposes banks to become more selective in their activity. Moreover, these risks are also more difficult to be measured as they are mainly focused on subjective elements and all quantitative indicators are still to be defined. For this reason, ESG risks are considered systemic and can impact the financial system as a whole. Institutions need to build their resilience to ESG risks across different time horizons, by taking a comprehensive and forward-looking view, as well as early and proactive actions, under supervisory control.
According to EBA, it is necessary to include ESG risks into the banking regulatory and supervisory framework, giving a particular emphasis on climate and environmental risks although social and governance risks are already important and necessitate attention. The main attention to these risks is due to the fact that they seem to be the most relevant because of climate change and the governments’ requirements to move toward “green economy” by converting the “brown business.”
To manage these risks, their transmission channels must be considered and incorporated into disclosures, risk management, and supervision. ESG disclosure is very relevant for stakeholders interested in assessing banks’ risks and their sustainable finance strategy [3]. This is why the Basel Third Pillar must be integrated and the non-financial reporting is linked to this need.
The analysis of ESG risks is very important because it is considered by supervisors as the new frontier to reach a resilient business model and risk management system to ensure banks’ preparedness for ESG-related challenges. ESG risks-related considerations must be fully taken into account in the definition of strategies and objectives, as the same must be done integrating ESG risks in governance structures, and managing these risks as drivers of financial risks. The actual regulatory framework is based on these actions expected by banks and the new supervisory and evaluation process (SREP) will be performed including these risks [2].
The materialization of ESG factors has consequences on banks’ performance because it is linked to all financial risks, such as credit, market, operational, liquidity, and funding risks. In general, we can maintain that ESG risks can be defined as the negative materialization of ESG factors through their counterparties or invested assets [3]. For example, if a bank grants a loan to a company that is suffering under the transition risk and costs of a green economy, its difficulties will influence the bank’s credit position and credit risk. This happens because this company will have problems in loan repayment and reimbursement due to the high expenses caused by the transition itself.
It is evident that ESG risks must be considered under a double perspective, proposed by EBA as an outside-in and inside-out perspective. According to the first dimension, banks can be impacted by ESG risks through their counterparties and invested assets, but at the same time, they may be impacted by or have an impact on (inside-out perspective) ESG factors. Even if both perspectives are important, the inside-out becomes much more relevant. The relationship between the inside-out and outside-in perspective is explained by the double materiality, which is divided into financial materiality and environmental and social materiality.
The double materiality implies that banks must measure and evaluate both the internal choices and the influence of the external behavior of companies and clients referring to ESG factors. The financial materiality can be explained by considering the effects on the company’s economic and financial activities. The environmental and social materiality refers to the influence of the above-mentioned company’s economic and financial activities on ESG factors themselves. With a circular process, this influence may cause, at the same time, financial materiality.
The assessment of ESG risks is done using three different methods—portfolio alignment method, risk framework method, and exposure method.
At the core of the portfolio alignment method, there is the meaning of alignment. According to this method banks, investors and supervisors will consider how far portfolios are aligned with globally agreed targets. This method could mainly be used for strategic purposes rather than risk management purposes because it does not explain the link between the global targets and the risk indicators of the bank.
The risk framework method includes the climate-stress test. This method is particularly relevant for climate risk, which is a forward-looking risk and stress testing over a future time horizon is, therefore, a useful tool for modeling climate risk impacts. On the contrary, the other ESG risks are in general more backward-looking. The risk framework method focuses on the sensitivity of portfolios and the impact that climate change has on the real risk of the exposures. The actions to face the risk are derived from the level of measured sensitivity or direct risk of losses considering the current level of environmental factors (or climate factors, more specifically) and the possible developments under the selected scenario. The application of this method brings to a risk-based adjusted portfolio in the medium-long term and makes it possible to consider also internal components of banking and trading book.
An exposure method is a tool that banks can apply directly to the assessment of individual counterparties and individual exposures, even in isolation. This method is based on a direct evaluation of the performance of exposure in terms of its ESG attributes. This method can be used to complement the standard assessment of financial risk categories. Thanks to this approach, there is a calibration at the specific company level. It is possible to put in evidence the specific sensitivities to ESG factors of different segments and sub-segments of economic activity. This method suits well to all three aspects of ESG.
This method is considered the most suitable if compared with the others. Even if it is not based on complex scenario analysis, it considers backward-looking metrics and makes banks able to classify their ESG risks’ exposures. This method gives banks the possibility to take adequate decisions to face ESG risks. The exposure method has developed some methodologies that can bring to ESG risks measurement. Regulators classify them in the following four methodologies—a. ESG ratings provided by specialized rating agencies; b. ESG evaluations provided by credit rating agencies; c. ESG evaluation models developed by banks in-house for their own assessment; and d. ESG scoring models developed by asset managers and data providers.
With the first methodology ESG ratings are provided by specialized rating agencies. They are stand-alone ratings on ESG factors, and consider the risk exposure to ESG factors. Rating agencies consider also the ability of the management to afford risks and to catch opportunities. These methodologies are generally built on a quantitative analysis of key issues identified for each company, but they also consider qualitative information collected by analysts from public information and engagement with companies.
In the case of ESG evaluations provided by credit rating agencies (e.g., S&P ESG), these evaluations integrate ESG factors into the standard credit analysis. They measure how ESG factors affect both certain scorecard components such as cash flows and leverage, and elements outside of the scorecard. They contribute to giving additional input to the existing financial risk assessment. Anyway, some difficulties in comparing ESG ratings by different providers are present as they include the different weights applied to the individual elements of ESG factors.
The internal methodologies have been developed by larger banks that were organizing their information systems on the basis of internal data deriving from wide data sets concerning their customers. These are internal and need the validation of regulatory authorities to be compliant with the existing rules. Finally, the ESG scoring models developed by asset managers and data providers, are publicly available.
Even if there are a number of methodologies, they are still improving both by banks and by regulators and they can be still considered at the early stages of development. These methods are very different both for the factors that are considered and for the results. They also differ for time horizons and for these reasons banks are experimenting with them all on different basis and portfolios. Anyway, the exposure origination is very important because it shows the future composition of a bank’s portfolio and signals to counterparties, investors, and wider market participants that investments are no longer sustainable and supported by the financial sector. This is true and relevant because the EBA Guidelines on Loan Origination and Monitoring are oriented to consider ESG factors as taken into account in banks’ credit risk appetite, policies and procedures.
The analysis of ESG risks requires a real ESG disclosure; this means that banks must map all business units and divisions on the basis of ESG risks’ framework and above all on the basis of the inside-out and outside-in perspective.
This mapping is finalized to manage the risk of conflicting or inconsistent information being disclosed; to ensure consistency and/or alignment of the disclosure; and to identify the overlaps in the reporting pillars where common reporting metrics can be considered. This kind of risk disclosure is important as it is the expression of internal analysis and mapping of ESG risks, which must be constantly monitored in the next future. This mapping can be considered as an absolute improvement of Basel Third Pillar.
The environmental aspect is really important as it is considered as the core for climate risk. Climate risk has a double dimension; in fact, banks and financial institutions are both impacted by and contribute to climate risks. For this reason, regulators are prioritizing appropriate climate risk disclosures as part of ensuring the broader transition of the financial industry to more sustainable, and positively impactful business models. According to the Financial Stability Board [4], climate risk must be considered by banks as physical risk and transition risk.
Physical risk is
Transition risk
Many stakeholders are interested in these two dimensions of climate risk and want to understand banks’ strategies in financing the transition to a zero-carbon economy. Under EBA’s requirement banks are required to disclose information on climate risks, mitigation action, and green asset ratio [5].
The disclosure about climate risks is due to the fact that according to EBA it is important to put in evidence how climate change may reinforce and worsen other risks in banks’ balance sheets. Concerning mitigating actions banks must inform about what they have in place to address those risks including financing activities that reduce carbon emissions.
With the Green Asset Ratio, it is possible to understand how institutions are financing activities that will meet the publicly agreed Paris agreement objectives of climate change mitigation and adaptation based on the EU taxonomy of green activities. The Green Asset Ratio is based on the EU taxonomy. It is a measure of the financial support that banks are willing to give to sustainable activities. Through this ratio, it is possible to put in evidence the assets that can be considered environmentally sustainable as they are referred to grant finance to activities of climate change mitigation on climate change adaptation. It is important in setting strategies, and even a bank with a low Green Asset Ratio can identify how it wants to change its financing activities over time to meet the Paris agreement objectives and measures. It gives information about a strategy that must be monitored. It is expected by EBA to receive from counterparties subject to NFRD disclosure obligations reliable data for the Green Asset Ratio from December 2022, developing a framework that identifies the required disclosure standards and their materiality triggers. The most commonly referenced framework in the case of climate disclosures is the TCFD framework, which is recognized by regulators in the EU and is considered as guidance on climate-related disclosures.
Banks and financial institutions are exposed to climate-related risks through both their own operational impacts and the activities of their borrowers, customers, or counterparties. According to the outside-in and inside-out approaches, banks that provide loans or trade the securities of companies with direct exposure to climate-related risks suffer and accumulate climate-related risks via their credit and equity operations. In addition, as the markets for lower-carbon and energy-efficient alternatives grow, firms may assume material exposures in their lending and investment businesses.
The ECB Guide [5] represents a shared document that shows how relevant are a disclosed analysis of such risks to grant that banks are managed in a sound and safe way. The relevance of climate-related risks is really great and the ECB has declared that banks conducted a self-assessment in light of the supervisory expectations outlined in the guide and to draw up action plans on that basis. The self-assessment plans will be considered by ECB as the first step toward more accurate monitoring of climate risk among all typical financial risks. This importance is also evident in the declaration of the climate-related risks stress test that will be run by ECB during this year.
As it has been described above, physical risks are specifically referred to as natural catastrophes and the economic losses caused by them; and this situation has increased in the last decades. The number of some types of extreme weather events has globally increased. Such events have become more likely or more severe due to the effects of climate change, and it is known that further warming will intensify them and consequently the negative effects at the basis of the increase of climate risk.
Physical risks include losses stemming from changes in physical capital because natural disasters destroy infrastructure and divert resources toward reconstruction and replacement. These risks affect also human capital, through deterioration in health and living conditions. The hard conditions due to the physical risks may have consequences on future expectations with a reduction of investment, given the prevailing uncertainty about future demand and growth prospects.
If there is no action to reduce the effects of climate change, physical risks will continue to increase in the future. The frequency and severity of extreme weather events might increase non-linearly and become increasingly correlated with each other over time. The consequences of physical risks can affect mainly market and credit risks.
The climate risk consequences may influence the value of financial assets causing losses for banks, investors, and financial institutions. The losses are the expression of market risk, but they are not directly caused by negative movement of financial variables (i.e., interest rates or assets prices), instead, their origin is connected with the losses due to the material destruction due to physical risk. As concerns credit risk it is almost easier to be understood as it is the consequence of the impossibility to repay and/or to reimburse loans, because of the physical destruction of assets, things, or the death of human beings. It is evident that banks are in presence of a large and composite number of risks and aspects of the same risk [4].
The impact of physical risk is not easy to be estimated with the effect on a bank’s assets. Estimates are based on a number of assumptions and subject to numerous sources of uncertainty concerning the global emissions with the potential increases in global temperatures and the severity of extreme weather events. So, the macroeconomic scenario and the variation in financial assets value are highly uncertain. Finally, there are the uncertainties associated with the future path of climate change and its impact on asset prices. Heating temperatures are increasing climate risk and physical risk in particular. They seem to be unavoidable, and this will cause an increase of negative effects on the financial system and assets prices [6, 7]. As physical risks are different in the sector and geographical areas, market and credit risks may be affected by these differences. This condition reinforces the situation in which other differences and in particular significant losses derive also from the disruption at the national level, and concentrated in certain countries with and exposure to operational risks that could disrupt firms’ operations, and affect other firms (financial and non-financial) provided by banks’ financial services amplifying risks for financial stability.
It is known the necessity of bringing the temperature to be below 2° C above pre-industrial level. Transition risks stem from the possible process of adjustment to a low carbon economy, and its possible effects are expected on the value of financial assets and liabilities. Such a transition to a low carbon economy would imply significant structural changes to the economy, including a major reallocation of investment. This could have a significant impact on firms involved in the production of fossil fuels, as well as other sectors whose business models rely on using such fossil fuels or that are energy intensive. The effect changes in asset prices with consequences on banks’ portfolios. These prospective effects might have also the consequence of reallocating financial resources from highly risky sectors or businesses tied, for example, in fossil fuels to new and less pollutant activities, by doing so supporting a real transition to a green economy. We can affirm that there will be a transformation of banks’ strategies and the support of market segments devoted to new and more sustainable sectors. We can say that the transition risks represent the lever to accelerate banks’ contribution to a renewal of economy and financial flows besides the real beginning of sustainable finance. On the contrary, a disorderly transition to a low-carbon economy, unanticipated by market participants, could have a destabilizing effect on the financial system. The most relevant effect will be an increase in credit risk due to the instability of such companies operating in brown sectors and receiving loans from banks. A transition to a low-carbon economy might reduce some borrowers’ capacity to generate sufficient income to service and repay their debts [8]. From this situation, banks are forced to face a higher credit risk, which is the result of a double scenario. The former is connected to the well-known difficulties in payments, and the latter is the increasing risks connected with the reduction of collateral value [7]. Transition scenarios are not able to catch all policy, technology and/or consumer preferences they change very rapidly. Moreover firms’ vulnerability to transition risks isn’t easy to be evaluated; in fact it is not only due to the firms’ operations, but also to their suppliers and customers.
Since time regulators are exploring this kind of risk and its widespread and are also analyzing possible ways to reduce them. However, the control of climate and ESG risks is at an early stage [9, 10, 11]. In the Appendices at the end of the chapter, there are the main initiatives that show the timeline and the complexity of the regulators’ activity with regard to ESG disclosure, climate risk analysis, and reporting for banks.
In this context, financial regulators are defining the principles about which climate risks are managed by banks. This interest derives from the necessity to reduce their impact both for banks themselves and for the financial system as a whole. Supervisory expectations aim at covering some institutional risk management elements (i.e., governance, strategy, scenario analysis, and/or risk management) and some financial standard-setting bodies are also starting to work on supervisory guidance related to climate risk. In fact, till now climate risks are considered as the worst for financial stability.
For example, scenario analysis can be used to quantify the totality of exposures of banks to climate-related risks within their framework and this is also called “climate stress test” [5]. There is also a significant approach to consider macro-prudential policies to mitigate climate risks to save the stability of the financial system, by giving banks a major resilience.
A large number of guidelines, best practices, and notices are the evidence that banking regulation shows a kind of difficulties to make a unitary proposal. As it has been said climate risk has a “liquid” structure that makes it really complex for banks to define their ambits and strategies.
The further evolution is the complete introduction of the ESG factors and ESG risks in the supervisory process and all control systems. These risks are not yet explicitly included in the CRD, the IFD, or in the SREP guidelines; at the same time, the consideration of these factors by supervisory authorities should be made with respect to the principle of proportionality, that links the conditions of each bank and its exposure to risks specifically referred to their dimension, context, and background [3].
Any way the integration of ESG risks into the supervisory review will be implemented gradually, considering the development of the related methodologies for the qualitative and quantitative assessment of ESG risks. The first step is the integration of these factors in the strategies and policies adopted by banks, with an improvement of the corporate and risk culture, and of the risk management frameworks. Only after the initial period when ESG risks will be completely introduced in banking management and there will be structured data, the supervisory assessment might cover all risks with the analysis of capital and liquidity.
The mechanism of the supervisory review is based on the consideration of the risk profile, but also the business model and the strategies adopted by the bank. Moreover, another check should be compliant with the IFD and IFR and with the financial risks afforded by the bank. The supervisory review is defined on the basis of the SREP elements; and so there is the business model analysis, the evaluation of the internal governance, of the internal controls, the analysis of the risks to capital and to liquidity and funding.
ESG factors are ESG matters that may have different impacts on banks’ financial performance because they can turn into ESG risks as financial risks as they are in the analysis of the supervisory process and in particular of the assessment of the viability and sustainability of banks’ business model. For this reason, supervisors are interested in the forward-looking analyses implemented by the banks themselves, in non-financial reporting that contains a number of information useful to discover the level of attention to a sustainable economy and in the bank’s ESG ratings. The supervisory process is changing in line with these new risks; banks are compelled to show their capacity and ability to afford and manage adequately their impact. New business models and a new and more effective supervisory function should be a forward-looking assessment of the future business environment.
In the previous paragraphs, the relevance of ESG factors and their possible characteristic of being a source of risks have been described. In addition, climate risk is considered one of the most important and actual risks in banks’ regulation. These two assumptions are influencing also banks’ business models.
Banks are organizing their activities to control their CO2 impact. At the same time, it is entering new selective methods in granting funds to green projects, avoiding the greenwashing trap that could increase ESG risks.
The business model is analyzed both under a quantitative dimension and from a qualitative point of view. The new business model being influenced by new risks requires also different capital adequacy. This adequacy is measured with respect to the capacity of absorbing ESG risks, while the qualitative analysis aims at the evaluation of the bank’s performance considering its risk appetite, but also the presence of other drivers.
According to EBA and Basel Committee [3, 6], to understand the impact of ESG factors on the current business model, the quantitative analysis should be based on the consideration of the portion of the bank’s profitability that derives from assets that are more exposed to ESG risks. The differences in the profitability of conventional loans and loans that include ESG risk-related objectives must be compared as the concentration of assets, highly exposed to ESG risks. The geographical concentration of lending or deposit-taking from households in a region where the economy heavily depends on carbon-intensive industries or that is prone to disasters is an example of the possible effects of ESG risks. The consequence is the search of assets and liabilities with more complex variables. For this reason, regulators are presenting new guidelines and banks are looking for new schemes for the development of more effective strategies.
From the previous discussion, it is evident that ESG risks impact the existing financial risks (e.g., credit risk, market risk, and operational risk). If it is so, it is evident that regulators and supervisors need to consider the impact on capital requirement [11]. According to the function of capital requirement, its entity is tied to the classification of risks to be faced. The risk-weighted assets are expressed on the basis of quantitative inputs classified by each bank starting from authorities’ rules and regulations. The definition of capital requirement for ESG risks is influenced by their measurement and it is not yet well complied. In fact, as concerns climate-related risks and environmental risks a number of quantitative indicators are developing; on the contrary social and governance risks are mainly managed through qualitative methods. The supervisory position is focused on the way used to manage these risks, or better to analyze how banks are becoming aware of these risks. Right now the relationship under monitoring is the effects on credit risk profile.
As concerns ESG climate risk and environmental risks in determining capital adequacy is relevant the consideration that they are long term risk; in fact, the physical impact of environmental change and/or because previously insufficient political action forces a sudden and comprehensive transition.
Consequently, the supervisory process will be adapted to review whether and how the banks ensure that their banking book is sustainable in the medium to long term. To simulate the condition of risk, banks can adopt scenario analysis that gives a measure of the bank’s resilience.
Supervisory activity tests capital adequacy by considering both qualitative and quantitative information. Anyway, the most important aspect is referred to the quantitative methodologies in which supervisory authorities assess bank’s risk measurement tools. Starting from this approach to measure the relationship between credit risk and ESG risk, the standard credit risk assessment is used to take into account the impact of ESG risks. As credit risk is assessed in the short to medium term, the use of forward-looking metrics is relevant to measure the impact of ESG factor on bank’s own exposure to credit risk. This evaluation is important to measure the sustainability of long-term loans in the bank’s banking book. In determining the capital requirement, the maturity of the loan portfolio is more and more important to absorb the impact of ESG risks. The starting point is connected to the evaluation of the awareness of how ESG risks drive credit risk for each portfolio and the connection with the risk appetite framework of the bank. For this reason, supervisors might check that institutions have properly embedded the material ESG factors into their rating assignment and review process.
The above-mentioned geographical variable is relevant also for determining capital adequacy; in fact, as said, the location has an influence on physical risk, so the higher is the risk of natural disaster, the higher should be the capital requirement to cover unexpected risks.
Even if there is the incorporation of ESG risks into the review of the credit quality of the portfolio, this causes a number of questions, one of which is the availability of reliable data and information. Supervisors will consequently check that the credit strategy is fully aligned and properly reflects the underlying ESG risk appetite. Performing these assessments also implies controlling how the responsibilities for implementing and monitoring the ESG-related targets are set.
The control of credit and loans implies the analysis of loans originating. At the end of this step, it means that it is necessary to identify projects, activities, and criteria used to select environmentally sustainable lending. This analysis is a guide to avoid greenwashing activities that might require a higher capital level, with a higher risk level [10]. This check on loan activity to quantify the capital requirement is necessary to cover the bank from the reputational risk, it might incur in.
While the link between ESG risks and liquidity and funding is seen by institutions as more indirect, it is deemed important to not overlook these links when evaluating the risks to liquidity and funding; ESG factors could also result in funding issues for institutions or make some assets less liquid. The evaluation of liquidity needs in the short and medium term, in particular, whether ESG risks could cause net cash outflows that negatively impact the institution’s liquidity position.
The analysis of ESG risks is still at an early stage, also because it is not yet simple in banking activity but it is relevant also for supervisory authority to assess the adequacy of internal capital to face these risks.
Environmental conditions and climate changes are influencing banking activity and regulators’ duties. For a few years, ESG factors are impacting financial context and are inducing managers to adopt new approaches in running their business. Banks are changing their methods to consider the principles of sustainable finance both as concerns the banking book and consequently the loans activity, but also the new green investments. On the other side, climate changes and climate-related risks have demonstrated that the brown economy must leave the place to a green economy.
This new approach has induced banks to consider new risks deriving from the ESG factor and from climate change itself. Banking managers are reshaping their risk management scheme introducing also ESG and climate-related risks.
The framework is aggravated by the fast evolution of the social and governance models that must be structured in a new way.
Regulators and supervisors are running in giving guidelines and new frameworks to induce banks to pay more and more attention to these risks.
The whole supervisory process is reshaping by introducing the measurement of ESG risks and climate-related risks but the greatest problem is due to the huge relevance of these risks and the overlapping of rules, regulations, and guidelines that are still at an early stage but are renewing the banking activity whose main role to bring the economy to put in practice a real new green deal.
Directive 2013/36/EU – Capital Requirement Directive Regulation (EU) 2019/876 – Capital Requirement Regulation Financial market participant Directive (EU) 2019/2034 – The Investment Firms Directive Regulation (EU) 2019/2033 Regulation (EU) 2019/2089 – The Low Carbon Benchmark Regulation Directive 2014/95/EU – The Non-Financial Reporting Directive Regulatory Technical Standards Regulation (EU) 2019/2088 – The Sustainable Finance Disclosure Directive Supervisory Review and Evaluation Process Regulation (EU) 2020/852 Task Force on Climate-related Financial Disclosures
Year/Date | |
---|---|
Banks must consider NFDR | |
February | EBA launches consultation about the revision of NFDR |
April | LCBMR in force |
September | EBA opens a survey on Pillar 3 disclosure on ESG risks |
November | Opening of EBA’s consultation on management and supervision of ESG risks for credit institutions and investment firms |
December | LCMBR level II in force |
Closing of IFRS consultation on Sustainable Reporting | |
February | Closing of EBA’s consultation on management and supervision of ESG risks for credit institutions and investment firms |
SFDR final draft RTS on indicators for the adverse impact of environment delivered to EC | |
March | Opening of EBA consultation on draft ITS on Pillar 3 disclosure |
SFDR principal website disclosure obligations apply to sustainability risk management; PAis; and remuneration policy | |
June | Proposal regarding the review of NFRD |
Closing of EBA consultation on draft ITS on Pillar 3 disclosure | |
EBA report on management and supervision of ESG risks | |
November | EBA on sustainable securitization |
December | SFDR final draft RTS on indicators for social and human matters |
EBA’s submission of the final draft of ITS on Pillar 3 disclosure | |
EBA guidelines and Standards on ESG integration in risk management and supervision | |
Publication of EBA discussion paper with a consultation on the classification and prudential treatment of assets from a sustainability perspective | |
EBA final report on the classification and prudential treatment of assets from a sustainability perspective |
Year/Date | |
---|---|
TCFD Guidelines available | |
June | EU publishes guidelines on reporting of climate-related information |
July | EU Taxonomy Regulation enters in force |
EBA delivers advice to EC on KPIs and methodology for disclosure under NFRD | |
June | EC adoption of a delegated act on the additional transparency requirement for financial and non-financial undertakings under the EU Taxonomy Regulation |
January | EU Taxonomy Regulation delegated acts on climate change mitigation and adaptation to apply |
Application of all EU Taxonomy Regulation delegated acts other than on climate change mitigation and adaptation |
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',metaTitle:"Terms and Conditions",metaDescription:"These terms and conditions outline the rules and regulations for the use of IntechOpen Website at https://intechopen.com and all its subdomains owned by Intech Limited located at 7th floor, 10 Lower Thames Street, London, EC3R 6AF, UK.",metaKeywords:null,canonicalURL:"/page/terms-and-conditions",contentRaw:'[{"type":"htmlEditorComponent","content":"By accessing the website at www.intechopen.com you are agreeing to be bound by these Terms of Service, all applicable laws and regulations, and agree that you are responsible for compliance with any applicable local laws. Use and/or access to this site is based on full agreement and compliance of these Terms. All materials contained on this website are protected by applicable copyright and trademark laws.
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\n\nThe following terminology applies to these Terms and Conditions, Privacy Statement, Disclaimer Notice, and any or all Agreements:
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S. Lisar, Rouhollah Motafakkerazad, Mosharraf M. Hossain and Ismail M. M. Rahman",authors:[{id:"110740",title:"Dr.",name:"Ismail M.M.",middleName:null,surname:"Rahman",slug:"ismail-m.m.-rahman",fullName:"Ismail M.M. Rahman"}]},{id:"62247",doi:"10.5772/intechopen.77315",title:"Application of Biosorption for Removal of Heavy Metals from Wastewater",slug:"application-of-biosorption-for-removal-of-heavy-metals-from-wastewater",totalDownloads:7633,totalCrossrefCites:75,totalDimensionsCites:149,abstract:"Fresh water accounts for 3% of water resources on the Earth. Human and industrial activities produce and discharge wastes containing heavy metals into the water resources making them unavailable and threatening human health and the ecosystem. Conventional methods for the removal of metal ions such as chemical precipitation and membrane filtration are extremely expensive when treating large amounts of water, inefficient at low concentrations of metal (incomplete metal removal) and generate large quantities of sludge and other toxic products that require careful disposal. Biosorption and bioaccumulation are ecofriendly alternatives. These alternative methods have advantages over conventional methods. Abundant natural materials like microbial biomass, agro-wastes, and industrial byproducts have been suggested as potential biosorbents for heavy metal removal due to the presence of metal-binding functional groups. Biosorption is influenced by various process parameters such as pH, temperature, initial concentration of the metal ions, biosorbent dose, and speed of agitation. Also, the biomass can be modified by physical and chemical treatment before use. The process can be made economical by regenerating and reusing the biosorbent after removing the heavy metals. Various bioreactors can be used in biosorption for the removal of metal ions from large volumes of water or effluents. The recent developments and the future scope for biosorption as a wastewater treatment option are discussed.",book:{id:"6137",slug:"biosorption",title:"Biosorption",fullTitle:"Biosorption"},signatures:"Sri Lakshmi Ramya Krishna Kanamarlapudi, Vinay Kumar\nChintalpudi and Sudhamani Muddada",authors:[{id:"238433",title:"Associate Prof.",name:"Sudhamani",middleName:null,surname:"Muddada",slug:"sudhamani-muddada",fullName:"Sudhamani Muddada"},{id:"244937",title:"Mrs.",name:"S L Ramyakrishna",middleName:null,surname:"Kanamarlapudi",slug:"s-l-ramyakrishna-kanamarlapudi",fullName:"S L Ramyakrishna Kanamarlapudi"},{id:"244938",title:"Mr.",name:"Vinay Kumar",middleName:null,surname:"Chintalpudi",slug:"vinay-kumar-chintalpudi",fullName:"Vinay Kumar Chintalpudi"}]},{id:"53211",doi:"10.5772/66416",title:"Biofloc Technology (BFT): A Tool for Water Quality Management in Aquaculture",slug:"biofloc-technology-bft-a-tool-for-water-quality-management-in-aquaculture",totalDownloads:16954,totalCrossrefCites:64,totalDimensionsCites:147,abstract:"Biofloc technology (BFT) is considered the new “blue revolution” in aquaculture. Such technique is based on in situ microorganism production which plays three major roles: (i) maintenance of water quality, by the uptake of nitrogen compounds generating in situ microbial protein; (ii) nutrition, increasing culture feasibility by reducing feed conversion ratio (FCR) and a decrease of feed costs; and (iii) competition with pathogens. The aggregates (bioflocs) are a rich protein-lipid natural source of food available in situ 24 hours per day due to a complex interaction between organic matter, physical substrate, and large range of microorganisms. This natural productivity plays an important role recycling nutrients and maintaining the water quality. The present chapter will discuss some insights of the role of microorganisms in BFT, main water quality parameters, the importance of the correct carbon-to-nitrogen ratio in the culture media, its calculations, and different types, as well as metagenomics of microorganisms and future perspectives.",book:{id:"5355",slug:"water-quality",title:"Water Quality",fullTitle:"Water Quality"},signatures:"Maurício Gustavo Coelho Emerenciano, Luis Rafael Martínez-\nCórdova, Marcel Martínez-Porchas and Anselmo Miranda-Baeza",authors:[{id:"146126",title:"Dr.",name:"Maurício Gustavo Coelho",middleName:null,surname:"Emerenciano",slug:"mauricio-gustavo-coelho-emerenciano",fullName:"Maurício Gustavo Coelho Emerenciano"},{id:"186970",title:"Prof.",name:"Marcel",middleName:null,surname:"Martínez-Porchas",slug:"marcel-martinez-porchas",fullName:"Marcel Martínez-Porchas"},{id:"186971",title:"Prof.",name:"Anselmo",middleName:null,surname:"Miranda-Baeza",slug:"anselmo-miranda-baeza",fullName:"Anselmo Miranda-Baeza"},{id:"195101",title:"Dr.",name:"Luis Rafael",middleName:null,surname:"Martínez-Córdoba",slug:"luis-rafael-martinez-cordoba",fullName:"Luis Rafael Martínez-Córdoba"}]}],mostDownloadedChaptersLast30Days:[{id:"69568",title:"Water Quality Parameters",slug:"water-quality-parameters",totalDownloads:10165,totalCrossrefCites:14,totalDimensionsCites:36,abstract:"Since the industrial revolution in the late eighteenth century, the world has discovered new sources of pollution nearly every day. So, air and water can potentially become polluted everywhere. Little is known about changes in pollution rates. The increase in water-related diseases provides a real assessment of the degree of pollution in the environment. This chapter summarizes water quality parameters from an ecological perspective not only for humans but also for other living things. According to its quality, water can be classified into four types. Those four water quality types are discussed through an extensive review of their important common attributes including physical, chemical, and biological parameters. These water quality parameters are reviewed in terms of definition, sources, impacts, effects, and measuring methods.",book:{id:"7718",slug:"water-quality-science-assessments-and-policy",title:"Water Quality",fullTitle:"Water Quality - Science, Assessments and Policy"},signatures:"Nayla Hassan Omer",authors:null},{id:"58138",title:"Water Pollution: Effects, Prevention, and Climatic Impact",slug:"water-pollution-effects-prevention-and-climatic-impact",totalDownloads:21554,totalCrossrefCites:18,totalDimensionsCites:38,abstract:"The stress on our water environment as a result of increased industrialization, which aids urbanization, is becoming very high thus reducing the availability of clean water. Polluted water is of great concern to the aquatic organism, plants, humans, and climate and indeed alters the ecosystem. The preservation of our water environment, which is embedded in sustainable development, must be well driven by all sectors. While effective wastewater treatment has the tendency of salvaging the water environment, integration of environmental policies into the actor firms core objectives coupled with continuous periodical enlightenment on the present and future consequences of environmental/water pollution will greatly assist in conserving the water environment.",book:{id:"6157",slug:"water-challenges-of-an-urbanizing-world",title:"Water Challenges of an Urbanizing World",fullTitle:"Water Challenges of an Urbanizing World"},signatures:"Inyinbor Adejumoke A., Adebesin Babatunde O., Oluyori Abimbola\nP., Adelani-Akande Tabitha A., Dada Adewumi O. and Oreofe Toyin\nA.",authors:[{id:"101570",title:"MSc.",name:"Babatunde Olufemi",middleName:null,surname:"Adebesin",slug:"babatunde-olufemi-adebesin",fullName:"Babatunde Olufemi Adebesin"},{id:"187738",title:"Dr.",name:"Adejumoke",middleName:"Abosede",surname:"Inyinbor",slug:"adejumoke-inyinbor",fullName:"Adejumoke Inyinbor"},{id:"188818",title:"Dr.",name:"Abimbola",middleName:null,surname:"Oluyori",slug:"abimbola-oluyori",fullName:"Abimbola Oluyori"},{id:"188819",title:"Mrs.",name:"Tabitha",middleName:null,surname:"Adelani-Akande",slug:"tabitha-adelani-akande",fullName:"Tabitha Adelani-Akande"},{id:"208501",title:"Dr.",name:"Adewumi",middleName:null,surname:"Dada",slug:"adewumi-dada",fullName:"Adewumi Dada"},{id:"208502",title:"Ms.",name:"Toyin",middleName:null,surname:"Oreofe",slug:"toyin-oreofe",fullName:"Toyin Oreofe"}]},{id:"45422",title:"Urban Waterfront Regenerations",slug:"urban-waterfront-regenerations",totalDownloads:14203,totalCrossrefCites:4,totalDimensionsCites:12,abstract:null,book:{id:"3560",slug:"advances-in-landscape-architecture",title:"Advances in Landscape Architecture",fullTitle:"Advances in Landscape Architecture"},signatures:"Umut Pekin Timur",authors:[{id:"165480",title:"Dr.",name:"Umut",middleName:null,surname:"Pekin Timur",slug:"umut-pekin-timur",fullName:"Umut Pekin Timur"}]},{id:"24941",title:"Tsunami in Makran Region and Its Effect on the Persian Gulf",slug:"tsunami-in-makran-region-and-its-effect-on-the-persian-gulf",totalDownloads:7575,totalCrossrefCites:4,totalDimensionsCites:7,abstract:null,book:{id:"406",slug:"tsunami-a-growing-disaster",title:"Tsunami",fullTitle:"Tsunami - A Growing Disaster"},signatures:"Mohammad Mokhtari",authors:[{id:"52451",title:"Dr.",name:"Mohammad",middleName:null,surname:"Mokhtari",slug:"mohammad-mokhtari",fullName:"Mohammad Mokhtari"}]},{id:"66307",title:"Bio-hydrogen and Methane Production from Lignocellulosic Materials",slug:"bio-hydrogen-and-methane-production-from-lignocellulosic-materials",totalDownloads:2953,totalCrossrefCites:6,totalDimensionsCites:8,abstract:"This chapter covers the information on bio-hydrogen and methane production from lignocellulosic materials. Pretreatment methods of lignocellulosic materials and the factors affecting bio-hydrogen production, both dark- and photo-fermentation, and methane production are addressed. Last but not least, the processes for bio-hydrogen and methane production from lignocellulosic materials are discussed.",book:{id:"7608",slug:"biomass-for-bioenergy-recent-trends-and-future-challenges",title:"Biomass for Bioenergy",fullTitle:"Biomass for Bioenergy - Recent Trends and Future Challenges"},signatures:"Apilak Salakkam, Pensri Plangklang, Sureewan Sittijunda, Mallika Boonmee Kongkeitkajorn, Siriporn Lunprom and Alissara Reungsang",authors:null}],onlineFirstChaptersFilter:{topicId:"12",limit:6,offset:0},onlineFirstChaptersCollection:[{id:"82465",title:"Agroforestry: An Approach for Sustainability and Climate Mitigation",slug:"agroforestry-an-approach-for-sustainability-and-climate-mitigation",totalDownloads:0,totalDimensionsCites:0,doi:"10.5772/intechopen.105406",abstract:"Agroforestry Systems (AFS), or the association of trees with crops (or animals), is a strategy for land management and use that allows production within the sustainable development: (a) environmentally (production environmentally harmonic); (b) technically (integrating existing resources on the farm); (c) economically (increase in production), and (d) socially (equality of duties and opportunities, quality of life of the family group). As an intentional integration of trees or shrubs with crop and animal production, this practice makes environmental, economic, and social benefits to farmers. Given that there is a set of definitions, rather than a single definition of Agroforestry (AF) and AFS, it is justified to explore the historical evolution and the minimum coincidences of criteria to define them and apply them in the recovery of degraded areas. Knowing how to classify AFS allows us to indicate which type or group of AFS is suitable for a particular area with its characteristics. The greatest benefit that AFS can bring to degraded or sloping areas lies in their ability to combine soil conservation with productive functions. In other words, AF is arborizing agriculture and animal production to obtain more benefits including climate change adaptation and mitigation by ecosystem services.",book:{id:"11663",title:"Vegetation Dynamics, Changing Ecosystems and Human Responsibility",coverURL:"https://cdn.intechopen.com/books/images_new/11663.jpg"},signatures:"Ricardo O. Russo"},{id:"82754",title:"Impact of Revegetation on Ecological Restoration of a Constructed Soil in a Coal Mining in Southern Brazil",slug:"impact-of-revegetation-on-ecological-restoration-of-a-constructed-soil-in-a-coal-mining-in-southern-",totalDownloads:3,totalDimensionsCites:0,doi:"10.5772/intechopen.105895",abstract:"The main problems in the constructed soils are the generation of acid mine drainage promoted by the presence of coal debris in the overburden layer and the compaction of the topsoil promoted by the machine traffic when the material used in the overburden cover is more clayey. This book chapter aimed to show an overview of the impact of more than a decade of revegetation with different perennial grasses on the chemical, physical, and biological quality of constructed soil after coal mining. The study was carried out in a coal mining area, located in southern Brazil. The soil was constructed in early 2003 and the perennial grasses, Hemarthria altissima; Paspalum notatum cv. Pensacola; Cynodon dactylon cv Tifton; and Urochloa brizantha; were implanted in November/December 2003. In 11.5, 17.6 and 18 years of revegetation soil samples were collected and the chemical, physical, and biological attributes were determined. Our results show that liming is an important practice in the restoration of these strongly anthropized soils because this positively impacts the plants’ development, facilitating the roots system expansion. Biological attributes such as soil fauna and the microorganism’s population are the attributes that possibly takes longer to establish itself in these areas.",book:{id:"11663",title:"Vegetation Dynamics, Changing Ecosystems and Human Responsibility",coverURL:"https://cdn.intechopen.com/books/images_new/11663.jpg"},signatures:"Lizete Stumpf, Maria Bertaso De Garcia Fernandez, Pablo Miguel, Luiz Fernando Spinelli Pinto, Ryan Noremberg Schubert, Luís Carlos Iuñes de Oliveira Filho, Tania Hipolito Montiel, Lucas Da Silva Barbosa, Jeferson Diego Leidemer and Thábata Barbosa Duarte"},{id:"82936",title:"Soil Degradation Processes Linked to Long-Term Forest-Type Damage",slug:"soil-degradation-processes-linked-to-long-term-forest-type-damage",totalDownloads:2,totalDimensionsCites:0,doi:"10.5772/intechopen.106390",abstract:"Forest degradation impairs ability of the whole landscape adaptation to environmental change. The impacts of forest degradation on landscape are caused by a self-organization decline. At the present time, the self-organization decline was largely due to nitrogen deposition and deforestation which exacerbated impacts of climate change. Nevertheless, forest degradation processes are either reversible or irreversible. Irreversible forest degradation begins with soil damage. In this paper, we present processes of forest soil degradation in relation to vulnerability of regulation adaptability on global environmental change. The regulatory forest capabilities were indicated through soil organic matter sequestration dynamics. We devided the degradation processes into quantitative and qualitative damages of physical or chemical soil properties. Quantitative soil degradation includes irreversible loss of an earth’s body after claim, erosion or desertification, while qualitative degradation consists of predominantly reversible consequences after soil disintegration, leaching, acidification, salinization and intoxication. As a result of deforestation, the forest soil vulnerability is spreading through quantitative degradation replacing hitherto predominantly qualitative changes under continuous vegetation cover. Increasing needs to natural resources using and accompanying waste pollution destroy soil self-organization through biodiversity loss, simplification in functional links among living forms and substance losses from ecosystem. We concluded that subsequent irreversible changes in ecosystem self-organization cause a change of biome potential natural vegetation and the land usability decrease.",book:{id:"11457",title:"Forest Degradation Under Global Change",coverURL:"https://cdn.intechopen.com/books/images_new/11457.jpg"},signatures:"Pavel Samec, Aleš Kučera and Gabriela Tomášová"},{id:"82828",title:"Vegetation and Avifauna Distribution in the Serengeti National Park",slug:"vegetation-and-avifauna-distribution-in-the-serengeti-national-park",totalDownloads:6,totalDimensionsCites:0,doi:"10.5772/intechopen.106165",abstract:"In order to examine the bird species changes within different vegetation structures, the variations were compared between Commiphora-dominated vegetations with those of Vachellia tortilis and Vachellia robusta-dominated vegetations, and also compared the birds of grassland with those of Vachellia drepanolobium and Vachellia seyal-dominated vegetations. This study was conducted between February 2010 and April 2012. A total of 40 plots of 100 m × 100 m were established. Nonparametric Mann-Whitney U-test was used to examine differences in bird species between vegetations. Species richness estimates were obtained using the Species Diversity and Richness. A total of 171 bird species representing 103 genera, 12 orders, and 54 families were recorded. We found differences in bird species distribution whereby V. tortilis has higher bird species richness (102 species), abundance, and diversity when compared with Commiphora with 66 species and V. robusta with 59 species. These results suggest that variations in bird species abundance, diversity, and distribution could be attributed to differences in the structural diversity of vegetation. Therefore it is important to maintain different types of vegetation by keeping the frequency of fire to a minimum and prescribed fire should be employed and encouraged to control wildfire and so maintain a diversity of vegetation and birds community.",book:{id:"11663",title:"Vegetation Dynamics, Changing Ecosystems and Human Responsibility",coverURL:"https://cdn.intechopen.com/books/images_new/11663.jpg"},signatures:"Ally K. Nkwabi and Pius Y. Kavana"},{id:"82808",title:"Climate Change and Anthropogenic Impacts on the Ecosystem of the Transgressive Mud Coastal Region of Bight of Benin, Nigeria",slug:"climate-change-and-anthropogenic-impacts-on-the-ecosystem-of-the-transgressive-mud-coastal-region-of",totalDownloads:8,totalDimensionsCites:0,doi:"10.5772/intechopen.105760",abstract:"The transgressive mud coastal area of Bight of Benin is a muddy coastal complex that lies east of the Barrier/lagoon coast and stretches to the Benin River in the northwestern flank of the Niger Delta Nigeria. It constitutes a fragile buffer zone between the tranquil waters of the swamps and the menacing waves of the Atlantic Ocean. Extensive breaching of this narrow coastal plain results in massive incursion of the sea into the inland swamps with serious implications for national security and the economy. Climate change impacts from the results of meteorological information of the regions shows a gradual degradation in the past 30 years. Temperature, rainfall and humidity increase annually depict climate change, resulting from uncontrolled exploitation of natural resources is rapidly pushing the region towards ecological disasters. The ecosystem is very unique being the only transgressive mud coastal area of the Gulf of Guinea. The chapter describes the geomorphology, tidal hydrology, relief/drainage, topography, climate/meteorology, vegetation, economic characteristics, anthropogenic activities and their impacts on the ecosystem.",book:{id:"11663",title:"Vegetation Dynamics, Changing Ecosystems and Human Responsibility",coverURL:"https://cdn.intechopen.com/books/images_new/11663.jpg"},signatures:"Patrick O. Ayeku"},{id:"82697",title:"Analyzing the Evolution of Land-Use Changes Related to Vegetation, in the Galicia Region, Spain: From 1990 to 2018",slug:"analyzing-the-evolution-of-land-use-changes-related-to-vegetation-in-the-galicia-region-spain-from-1",totalDownloads:6,totalDimensionsCites:0,doi:"10.5772/intechopen.106015",abstract:"Considering the complex dynamics, patterns, and particularities that the Galicia region present—e.g., the fragility, shown to achieve sustainable development and growth—a study that analyzes the Land-Use related to the vegetation of this region is seen as pivotal to identifying barriers and opportunities for long-term sustainable development. Using GIS (Geographic Information Systems), the present chapter enables us to identify the dynamics and patterns of the evolution of the Land-Use Changes related to vegetation in the Galicia Region from 1990 to 2018 (years 1990, 2000, 2012, and 2018 using CORINE (Coordination of Information on the Environment) data). This study permits us to reinforce that the Land-Use Changes related to vegetation in the Galicia Region have undergone multiple changes—marked by increasing and decreasing periods. Also, can be considered a surveying baseline for the comparative analysis of similar works for different Land-Use Changes related to vegetation trends in Europe or worldwide. Land-Use Changes related to vegetation studies are reliable tools to evaluate the human activities and footprint of proposed strategies and policies in a territory. This chapter also enables us to understand that the main actors should design development policies to protect, preserve and conserve these incomparable landscapes, environments, ecosystems, and the region as a whole.",book:{id:"11663",title:"Vegetation Dynamics, Changing Ecosystems and Human Responsibility",coverURL:"https://cdn.intechopen.com/books/images_new/11663.jpg"},signatures:"Sérgio Lousada and José Manuel Naranjo Gómez"}],onlineFirstChaptersTotal:77},preDownload:{success:null,errors:{}},subscriptionForm:{success:null,errors:{}},aboutIntechopen:{},privacyPolicy:{},peerReviewing:{},howOpenAccessPublishingWithIntechopenWorks:{},sponsorshipBooks:{sponsorshipBooks:[],offset:8,limit:8,total:0},allSeries:{pteSeriesList:[{id:"14",title:"Artificial Intelligence",numberOfPublishedBooks:9,numberOfPublishedChapters:90,numberOfOpenTopics:6,numberOfUpcomingTopics:0,issn:"2633-1403",doi:"10.5772/intechopen.79920",isOpenForSubmission:!0},{id:"7",title:"Biomedical Engineering",numberOfPublishedBooks:12,numberOfPublishedChapters:107,numberOfOpenTopics:3,numberOfUpcomingTopics:0,issn:"2631-5343",doi:"10.5772/intechopen.71985",isOpenForSubmission:!0}],lsSeriesList:[{id:"11",title:"Biochemistry",numberOfPublishedBooks:33,numberOfPublishedChapters:330,numberOfOpenTopics:4,numberOfUpcomingTopics:0,issn:"2632-0983",doi:"10.5772/intechopen.72877",isOpenForSubmission:!0},{id:"25",title:"Environmental Sciences",numberOfPublishedBooks:1,numberOfPublishedChapters:19,numberOfOpenTopics:4,numberOfUpcomingTopics:0,issn:"2754-6713",doi:"10.5772/intechopen.100362",isOpenForSubmission:!0},{id:"10",title:"Physiology",numberOfPublishedBooks:14,numberOfPublishedChapters:145,numberOfOpenTopics:4,numberOfUpcomingTopics:0,issn:"2631-8261",doi:"10.5772/intechopen.72796",isOpenForSubmission:!0}],hsSeriesList:[{id:"3",title:"Dentistry",numberOfPublishedBooks:9,numberOfPublishedChapters:139,numberOfOpenTopics:2,numberOfUpcomingTopics:0,issn:"2631-6218",doi:"10.5772/intechopen.71199",isOpenForSubmission:!0},{id:"6",title:"Infectious Diseases",numberOfPublishedBooks:13,numberOfPublishedChapters:122,numberOfOpenTopics:4,numberOfUpcomingTopics:0,issn:"2631-6188",doi:"10.5772/intechopen.71852",isOpenForSubmission:!0},{id:"13",title:"Veterinary Medicine and Science",numberOfPublishedBooks:11,numberOfPublishedChapters:112,numberOfOpenTopics:3,numberOfUpcomingTopics:0,issn:"2632-0517",doi:"10.5772/intechopen.73681",isOpenForSubmission:!0}],sshSeriesList:[{id:"22",title:"Business, Management and Economics",numberOfPublishedBooks:1,numberOfPublishedChapters:21,numberOfOpenTopics:3,numberOfUpcomingTopics:0,issn:"2753-894X",doi:"10.5772/intechopen.100359",isOpenForSubmission:!0},{id:"23",title:"Education and Human Development",numberOfPublishedBooks:0,numberOfPublishedChapters:10,numberOfOpenTopics:1,numberOfUpcomingTopics:1,issn:null,doi:"10.5772/intechopen.100360",isOpenForSubmission:!0},{id:"24",title:"Sustainable Development",numberOfPublishedBooks:1,numberOfPublishedChapters:19,numberOfOpenTopics:5,numberOfUpcomingTopics:0,issn:"2753-6580",doi:"10.5772/intechopen.100361",isOpenForSubmission:!0}],testimonialsList:[{id:"13",text:"The collaboration with and support of the technical staff of IntechOpen is fantastic. 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He is on the editorial board of several international peer-reviewed journals and has published many papers. Additionally, he has participated in many international and national congresses, seminars, and workshops with oral and poster presentations. He is an active member of many local and international organizations.",institutionString:"İskenderun Technical University",institution:{name:"İskenderun Technical University",country:{name:"Turkey"}}},{id:"61139",title:"Dr.",name:"Sergey",middleName:null,surname:"Tkachev",slug:"sergey-tkachev",fullName:"Sergey Tkachev",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/61139/images/system/61139.png",biography:"Dr. Sergey Tkachev is a senior research scientist at the Institute of Fundamental Medicine and Biology, Kazan Federal University, Russia, and at the Institute of Chemical Biology and Fundamental Medicine SB RAS, Novosibirsk, Russia. He received his Ph.D. in Molecular Biology with his thesis “Genetic variability of the tick-borne encephalitis virus in natural foci of Novosibirsk city and its suburbs.” His primary field is molecular virology with research emphasis on vector-borne viruses, especially tick-borne encephalitis virus, Kemerovo virus and Omsk hemorrhagic fever virus, rabies virus, molecular genetics, biology, and epidemiology of virus pathogens.",institutionString:"Russian Academy of Sciences",institution:{name:"Russian Academy of Sciences",country:{name:"Russia"}}},{id:"310962",title:"Dr.",name:"Amlan",middleName:"Kumar",surname:"Patra",slug:"amlan-patra",fullName:"Amlan Patra",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/310962/images/system/310962.jpg",biography:"Amlan K. Patra, FRSB, obtained a Ph.D. in Animal Nutrition from Indian Veterinary Research Institute, India, in 2002. 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In 1992, Dr. Babinszky obtained a Ph.D. in Animal Nutrition from the University of Wageningen. His main research areas are swine and poultry nutrition. He has authored more than 300 publications (papers, book chapters) and edited four books and fourteen international conference proceedings.",institutionString:"University of Debrecen",institution:{name:"University of Debrecen",country:{name:"Hungary"}}},{id:"201830",title:"Dr.",name:"Fernando",middleName:"Sanchez",surname:"Davila",slug:"fernando-davila",fullName:"Fernando Davila",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/201830/images/5017_n.jpg",biography:"I am a professor at UANL since 1988. My research lines are the development of reproductive techniques in small ruminants. We also conducted research on sexual and social behavior in males.\nI am Mexican and study my professional career as an engineer in agriculture and animal science at UANL. Then take a masters degree in science in Germany (Animal breeding). Take a doctorate in animal science at the UANL.",institutionString:null,institution:{name:"Universidad Autónoma de Nuevo León",country:{name:"Mexico"}}},{id:"309250",title:"Dr.",name:"Miguel",middleName:null,surname:"Quaresma",slug:"miguel-quaresma",fullName:"Miguel Quaresma",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/309250/images/9059_n.jpg",biography:"Miguel Nuno Pinheiro Quaresma was born on May 26, 1974 in Dili, Timor Island. He is married with two children: a boy and a girl, and he is a resident in Vila Real, Portugal. He graduated in Veterinary Medicine in August 1998 and obtained his Ph.D. degree in Veterinary Sciences -Clinical Area in February 2015, both from the University of Trás-os-Montes e Alto Douro. He is currently enrolled in the Alternative Residency of the European College of Animal Reproduction. He works as a Senior Clinician at the Veterinary Teaching Hospital of UTAD (HVUTAD) with a role in clinical activity in the area of livestock and equine species as well as to support teaching and research in related areas. He teaches as an Invited Professor in Reproduction Medicine I and II of the Master\\'s in Veterinary Medicine degree at UTAD. Currently, he holds the position of Chairman of the Portuguese Buiatrics Association. He is a member of the Consultive Group on Production Animals of the OMV. He has 19 publications in indexed international journals (ISIS), as well as over 60 publications and oral presentations in both Portuguese and international journals and congresses.",institutionString:"University of Trás-os-Montes and Alto Douro",institution:{name:"University of Trás-os-Montes and Alto Douro",country:{name:"Portugal"}}},{id:"38652",title:"Prof.",name:"Rita",middleName:null,surname:"Payan-Carreira",slug:"rita-payan-carreira",fullName:"Rita Payan-Carreira",position:null,profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bRiFPQA0/Profile_Picture_1614601496313",biography:"Rita Payan Carreira earned her Veterinary Degree from the Faculty of Veterinary Medicine in Lisbon, Portugal, in 1985. She obtained her Ph.D. in Veterinary Sciences from the University of Trás-os-Montes e Alto Douro, Portugal. After almost 32 years of teaching at the University of Trás-os-Montes and Alto Douro, she recently moved to the University of Évora, Department of Veterinary Medicine, where she teaches in the field of Animal Reproduction and Clinics. Her primary research areas include the molecular markers of the endometrial cycle and the embryo–maternal interaction, including oxidative stress and the reproductive physiology and disorders of sexual development, besides the molecular determinants of male and female fertility. She often supervises students preparing their master's or doctoral theses. She is also a frequent referee for various journals.",institutionString:null,institution:{name:"University of Évora",country:{name:"Portugal"}}},{id:"283019",title:"Dr.",name:"Oudessa",middleName:null,surname:"Kerro Dego",slug:"oudessa-kerro-dego",fullName:"Oudessa Kerro Dego",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/283019/images/system/283019.png",biography:"Dr. Kerro Dego is a veterinary microbiologist with training in veterinary medicine, microbiology, and anatomic pathology. Dr. Kerro Dego is an assistant professor of dairy health in the department of animal science, the University of Tennessee, Institute of Agriculture, Knoxville, Tennessee. He received his D.V.M. (1997), M.S. (2002), and Ph.D. (2008) degrees in Veterinary Medicine, Animal Pathology and Veterinary Microbiology from College of Veterinary Medicine, Addis Ababa University, Ethiopia; College of Veterinary Medicine, Utrecht University, the Netherlands and Western College of Veterinary Medicine, University of Saskatchewan, Canada respectively. He did his Postdoctoral training in microbial pathogenesis (2009 - 2015) in the Department of Animal Science, the University of Tennessee, Institute of Agriculture, Knoxville, Tennessee. Dr. Kerro Dego’s research focuses on the prevention and control of infectious diseases of farm animals, particularly mastitis, improving dairy food safety, and mitigation of antimicrobial resistance. Dr. Kerro Dego has extensive experience in studying the pathogenesis of bacterial infections, identification of virulence factors, and vaccine development and efficacy testing against major bacterial mastitis pathogens. Dr. Kerro Dego conducted numerous controlled experimental and field vaccine efficacy studies, vaccination, and evaluation of immunological responses in several species of animals, including rodents (mice) and large animals (bovine and ovine).",institutionString:"University of Tennessee at Knoxville",institution:{name:"University of Tennessee at Knoxville",country:{name:"United States of America"}}},{id:"251314",title:"Dr.",name:"Juan Carlos",middleName:null,surname:"Gardón Poggi",slug:"juan-carlos-gardon-poggi",fullName:"Juan Carlos Gardón Poggi",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/251314/images/system/251314.jpeg",biography:"Juan Carlos Gardón Poggi received University degree from the Faculty of Agrarian Science in Argentina, in 1983. Also he received Masters Degree and PhD from Córdoba University, Spain. He is currently a Professor at the Catholic University of Valencia San Vicente Mártir, at the Department of Medicine and Animal Surgery. He teaches diverse courses in the field of Animal Reproduction and he is the Director of the Veterinary Farm. He also participates in academic postgraduate activities at the Veterinary Faculty of Murcia University, Spain. His research areas include animal physiology, physiology and biotechnology of reproduction either in males or females, the study of gametes under in vitro conditions and the use of ultrasound as a complement to physiological studies and development of applied biotechnologies. Routinely, he supervises students preparing their doctoral, master thesis or final degree projects.",institutionString:null,institution:{name:"Valencia Catholic University Saint Vincent Martyr",country:{name:"Spain"}}},{id:"309529",title:"Dr.",name:"Albert",middleName:null,surname:"Rizvanov",slug:"albert-rizvanov",fullName:"Albert Rizvanov",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/309529/images/9189_n.jpg",biography:'Albert A. Rizvanov is a Professor and Director of the Center for Precision and Regenerative Medicine at the Institute of Fundamental Medicine and Biology, Kazan Federal University (KFU), Russia. He is the Head of the Center of Excellence “Regenerative Medicine” and Vice-Director of Strategic Academic Unit \\"Translational 7P Medicine\\". Albert completed his Ph.D. at the University of Nevada, Reno, USA and Dr.Sci. at KFU. He is a corresponding member of the Tatarstan Academy of Sciences, Russian Federation. Albert is an author of more than 300 peer-reviewed journal articles and 22 patents. He has supervised 11 Ph.D. and 2 Dr.Sci. dissertations. Albert is the Head of the Dissertation Committee on Biochemistry, Microbiology, and Genetics at KFU.\nORCID https://orcid.org/0000-0002-9427-5739\nWebsite https://kpfu.ru/Albert.Rizvanov?p_lang=2',institutionString:"Kazan Federal University",institution:{name:"Kazan Federal University",country:{name:"Russia"}}},{id:"210551",title:"Dr.",name:"Arbab",middleName:null,surname:"Sikandar",slug:"arbab-sikandar",fullName:"Arbab Sikandar",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/210551/images/system/210551.jpg",biography:"Dr. Arbab Sikandar, PhD, M. Phil, DVM was born on April 05, 1981. He is currently working at the College of Veterinary & Animal Sciences as an Assistant Professor. He previously worked as a lecturer at the same University. \nHe is a Member/Secretory of Ethics committee (No. CVAS-9377 dated 18-04-18), Member of the QEC committee CVAS, Jhang (Regr/Gen/69/873, dated 26-10-2017), Member, Board of studies of Department of Basic Sciences (No. CVAS. 2851 Dated. 12-04-13, and No. CVAS, 9024 dated 20/11/17), Member of Academic Committee, CVAS, Jhang (No. CVAS/2004, Dated, 25-08-12), Member of the technical committee (No. CVAS/ 4085, dated 20,03, 2010 till 2016).\n\nDr. Arbab Sikandar contributed in five days hands-on-training on Histopathology at the Department of Pathology, UVAS from 12-16 June 2017. He received a Certificate of appreciation for contributions for Popularization of Science and Technology in the Society on 17-11-15. He was the resource person in the lecture series- ‘scientific writing’ at the Department of Anatomy and Histology, UVAS, Lahore on 29th October 2015. He won a full fellowship as a principal candidate for the year 2015 in the field of Agriculture, EICA, Egypt with ref. to the Notification No. 12(11) ACS/Egypt/2014 from 10 July 2015 to 25th September 2015.; he received a grant of Rs. 55000/- as research incentives from Director, Advanced Studies and Research, UVAS, Lahore upon publications of research papers in IF Journals (DR/215, dated 19-5-2014.. He obtained his PhD by winning a HEC Pakistan indigenous Scholarship, ‘Ph.D. fellowship for 5000 scholars – Phase II’ (2av1-147), 17-6/HEC/HRD/IS-II/12, November 15, 2012. \n\nDr. Sikandar is a member of numerous societies: Registered Veterinary Medical Practitioner (life member) and Registered Veterinary Medical Faculty of Pakistan Veterinary Medical Council. The Registration code of PVMC is RVMP/4298 and RVMF/ 0102.; Life member of the University of Veterinary and Animal Sciences, Lahore, Alumni Association with S# 664, dated: 6-4-12. ; Member 'Vets Care Organization Pakistan” with Reference No. VCO-605-149, dated 05-04-06. :Member 'Vet Crescent” (Society of Animal Health and Production), UVAS, Lahore.",institutionString:"University of Veterinary & Animal Science",institution:{name:"University of Veterinary and Animal Sciences",country:{name:"Pakistan"}}},{id:"311663",title:"Dr.",name:"Prasanna",middleName:null,surname:"Pal",slug:"prasanna-pal",fullName:"Prasanna Pal",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/311663/images/13261_n.jpg",biography:null,institutionString:null,institution:{name:"National Dairy Research Institute",country:{name:"India"}}},{id:"202192",title:"Dr.",name:"Catrin",middleName:null,surname:"Rutland",slug:"catrin-rutland",fullName:"Catrin Rutland",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/202192/images/system/202192.png",biography:"Catrin Rutland is an Associate Professor of Anatomy and Developmental Genetics at the University of Nottingham, UK. She obtained a BSc from the University of Derby, England, a master’s degree from Technische Universität München, Germany, and a Ph.D. from the University of Nottingham. She undertook a post-doctoral research fellowship in the School of Medicine before accepting tenure in Veterinary Medicine and Science. Dr. Rutland also obtained an MMedSci (Medical Education) and a Postgraduate Certificate in Higher Education (PGCHE). She is the author of more than sixty peer-reviewed journal articles, twelve books/book chapters, and more than 100 research abstracts in cardiovascular biology and oncology. She is a board member of the European Association of Veterinary Anatomists, Fellow of the Anatomical Society, and Senior Fellow of the Higher Education Academy. Dr. Rutland has also written popular science books for the public. https://orcid.org/0000-0002-2009-4898. www.nottingham.ac.uk/vet/people/catrin.rutland",institutionString:null,institution:{name:"University of Nottingham",country:{name:"United Kingdom"}}},{id:"283315",title:"Prof.",name:"Samir",middleName:null,surname:"El-Gendy",slug:"samir-el-gendy",fullName:"Samir El-Gendy",position:null,profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bRduYQAS/Profile_Picture_1606215849748",biography:"Samir El-Gendy is a Professor of anatomy and embryology at the faculty of veterinary medicine, Alexandria University, Egypt. Samir obtained his PhD in veterinary science in 2007 from the faculty of veterinary medicine, Alexandria University and has been a professor since 2017. Samir is an author on 24 articles at Scopus and 12 articles within local journals and 2 books/book chapters. His research focuses on applied anatomy, imaging techniques and computed tomography. Samir worked as a member of different local projects on E-learning and he is a board member of the African Association of Veterinary Anatomists and of anatomy societies and as an associated author at local and international journals. Orcid: https://orcid.org/0000-0002-6180-389X",institutionString:null,institution:{name:"Alexandria University",country:{name:"Egypt"}}},{id:"246149",title:"Dr.",name:"Valentina",middleName:null,surname:"Kubale",slug:"valentina-kubale",fullName:"Valentina Kubale",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/246149/images/system/246149.jpg",biography:"Valentina Kubale is Associate Professor of Veterinary Medicine at the Veterinary Faculty, University of Ljubljana, Slovenia. Since graduating from the Veterinary faculty she obtained her PhD in 2007, performed collaboration with the Department of Pharmacology, University of Copenhagen, Denmark. She continued as a post-doctoral fellow at the University of Copenhagen with a Lundbeck foundation fellowship. She is the editor of three books and author/coauthor of 23 articles in peer-reviewed scientific journals, 16 book chapters, and 68 communications at scientific congresses. Since 2008 she has been the Editor Assistant for the Slovenian Veterinary Research journal. She is a member of Slovenian Biochemical Society, The Endocrine Society, European Association of Veterinary Anatomists and Society for Laboratory Animals, where she is board member.",institutionString:"University of Ljubljana",institution:{name:"University of Ljubljana",country:{name:"Slovenia"}}},{id:"258334",title:"Dr.",name:"Carlos Eduardo",middleName:null,surname:"Fonseca-Alves",slug:"carlos-eduardo-fonseca-alves",fullName:"Carlos Eduardo Fonseca-Alves",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/258334/images/system/258334.jpg",biography:"Dr. Fonseca-Alves earned his DVM from Federal University of Goias – UFG in 2008. He completed an internship in small animal internal medicine at UPIS university in 2011, earned his MSc in 2013 and PhD in 2015 both in Veterinary Medicine at Sao Paulo State University – UNESP. Dr. Fonseca-Alves currently serves as an Assistant Professor at Paulista University – UNIP teaching small animal internal medicine.",institutionString:null,institution:{name:"Universidade Paulista",country:{name:"Brazil"}}},{id:"245306",title:"Dr.",name:"María Luz",middleName:null,surname:"Garcia Pardo",slug:"maria-luz-garcia-pardo",fullName:"María Luz Garcia Pardo",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/245306/images/system/245306.png",biography:"María de la Luz García Pardo is an agricultural engineer from Universitat Politècnica de València, Spain. She has a Ph.D. in Animal Genetics. Currently, she is a lecturer at the Agrofood Technology Department of Miguel Hernández University, Spain. Her research is focused on genetics and reproduction in rabbits. The major goal of her research is the genetics of litter size through novel methods such as selection by the environmental sensibility of litter size, with forays into the field of animal welfare by analysing the impact on the susceptibility to diseases and stress of the does. Details of her publications can be found at https://orcid.org/0000-0001-9504-8290.",institutionString:null,institution:{name:"Miguel Hernandez University",country:{name:"Spain"}}},{id:"350704",title:"M.Sc.",name:"Camila",middleName:"Silva Costa",surname:"Ferreira",slug:"camila-ferreira",fullName:"Camila Ferreira",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/350704/images/17280_n.jpg",biography:"Graduated in Veterinary Medicine at the Fluminense Federal University, specialist in Equine Reproduction at the Brazilian Veterinary Institute (IBVET) and Master in Clinical Veterinary Medicine and Animal Reproduction at the Fluminense Federal University. She has experience in analyzing zootechnical indices in dairy cattle and organizing events related to Veterinary Medicine through extension grants. I have experience in the field of diagnostic imaging and animal reproduction in veterinary medicine through monitoring and scientific initiation scholarships. I worked at the Equus Central Reproduction Equine located in Santo Antônio de Jesus – BA in the 2016/2017 breeding season. I am currently a doctoral student with a scholarship from CAPES of the Postgraduate Program in Veterinary Medicine (Pathology and Clinical Sciences) at the Federal Rural University of Rio de Janeiro (UFRRJ) with a research project with an emphasis on equine endometritis.",institutionString:null,institution:null},{id:"41319",title:"Prof.",name:"Lung-Kwang",middleName:null,surname:"Pan",slug:"lung-kwang-pan",fullName:"Lung-Kwang Pan",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/41319/images/84_n.jpg",biography:null,institutionString:null,institution:null},{id:"125292",title:"Dr.",name:"Katy",middleName:null,surname:"Satué Ambrojo",slug:"katy-satue-ambrojo",fullName:"Katy Satué Ambrojo",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/125292/images/system/125292.jpeg",biography:"Katy Satué Ambrojo received her Veterinary Medicine degree, Master degree in Equine Technology and doctorate in Veterinary Medicine from the Faculty of Veterinary, CEU-Cardenal Herrera University in Valencia, Spain.Dr. Satué is accredited as a Private University Doctor Professor, Doctor Assistant, and Contracted Doctor by AVAP (Agència Valenciana d'Avaluació i Prospectiva) and currently, as a full professor by ANECA (since January 2022). To date, Katy has taught 22 years in the Department of Animal Medicine and Surgery at the CEU-Cardenal Herrera University in undergraduate courses in Veterinary Medicine (General Pathology, integrated into the Applied Basis of Veterinary Medicine module of the 2nd year, Clinical Equine I of 3rd year, and Equine Clinic II of 4th year). Dr. Satué research activity is in the field of Endocrinology, Hematology, Biochemistry, and Immunology in the Spanish Purebred mare. She has directed 5 Doctoral Theses and 5 Diplomas of Advanced Studies, and participated in 11 research projects as a collaborating researcher. She has written 2 books and 14 book chapters in international publishers related to the area, and 68 scientific publications in international journals. Dr. Satué has attended 63 congresses, participating with 132 communications in international congresses and 19 in national congresses related to the area. Dr. Satué is a scientific reviewer for various prestigious international journals such as Animals, American Journal of Obstetrics and Gynecology, Veterinary Clinical Pathology, Journal of Equine Veterinary Science, Reproduction in Domestic Animals, Research Veterinary Science, Brazilian Journal of Medical and Biological Research, Livestock Production Science and Theriogenology, among others. Since 2014 she has been responsible for the Clinical Analysis Laboratory of the CEU-Cardenal Herrera University Veterinary Clinical Hospital.",institutionString:null,institution:null},{id:"201721",title:"Dr.",name:"Beatrice",middleName:null,surname:"Funiciello",slug:"beatrice-funiciello",fullName:"Beatrice Funiciello",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/201721/images/11089_n.jpg",biography:"Graduated from the University of Milan in 2011, my post-graduate education included CertAVP modules mainly on equines (dermatology and internal medicine) and a few on small animal (dermatology and anaesthesia) at the University of Liverpool. After a general CertAVP (2015) I gained the designated Certificate in Veterinary Dermatology (2017) after taking the synoptic examination and then applied for the RCVS ADvanced Practitioner status. After that, I completed the Postgraduate Diploma in Veterinary Professional Studies at the University of Liverpool (2018). My main area of work is cross-species veterinary dermatology.",institutionString:null,institution:null},{id:"291226",title:"Dr.",name:"Monica",middleName:null,surname:"Cassel",slug:"monica-cassel",fullName:"Monica Cassel",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/291226/images/8232_n.jpg",biography:'Degree in Biological Sciences at the Federal University of Mato Grosso with scholarship for Scientific Initiation by FAPEMAT (2008/1) and CNPq (2008/2-2009/2): Project \\"Histological evidence of reproductive activity in lizards of the Manso region, Chapada dos Guimarães, Mato Grosso, Brazil\\". Master\\\'s degree in Ecology and Biodiversity Conservation at Federal University of Mato Grosso with a scholarship by CAPES/REUNI program: Project \\"Reproductive biology of Melanorivulus punctatus\\". PhD\\\'s degree in Science (Cell and Tissue Biology Area) \n at University of Sao Paulo with scholarship granted by FAPESP; Project \\"Development of morphofunctional changes in ovary of Astyanax altiparanae Garutti & Britski, 2000 (Teleostei, Characidae)\\". She has experience in Reproduction of vertebrates and Morphology, with emphasis in Cellular Biology and Histology. She is currently a teacher in the medium / technical level courses at IFMT-Alta Floresta, as well as in the Bachelor\\\'s degree in Animal Science and in the Bachelor\\\'s degree in Business.',institutionString:null,institution:null},{id:"442807",title:"Dr.",name:"Busani",middleName:null,surname:"Moyo",slug:"busani-moyo",fullName:"Busani Moyo",position:null,profilePictureURL:"//cdnintech.com/web/frontend/www/assets/author.svg",biography:null,institutionString:null,institution:{name:"Gwanda State University",country:{name:"Zimbabwe"}}},{id:"439435",title:"Dr.",name:"Feda S.",middleName:null,surname:"Aljaser",slug:"feda-s.-aljaser",fullName:"Feda S. 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The applications of this research cover many related fields, such as biotechnology and medicine, where, for example, Bioinformatics contributes to faster drug design, DNA analysis in forensics, and DNA sequence analysis in the field of personalized medicine. Personalized medicine is a type of medical care in which treatment is customized individually for each patient. Personalized medicine enables more effective therapy, reduces the costs of therapy and clinical trials, and also minimizes the risk of side effects. Nevertheless, advances in personalized medicine would not have been possible without bioinformatics, which can analyze the human genome and other vast amounts of biomedical data, especially in genetics. The rapid growth of information technology enabled the development of new tools to decode human genomes, large-scale studies of genetic variations and medical informatics. The considerable development of technology, including the computing power of computers, is also conducive to the development of bioinformatics, including personalized medicine. In an era of rapidly growing data volumes and ever lower costs of generating, storing and computing data, personalized medicine holds great promises. Modern computational methods used as bioinformatics tools can integrate multi-scale, multi-modal and longitudinal patient data to create even more effective and safer therapy and disease prevention methods. Main aspects of the topic are: Applying bioinformatics in drug discovery and development; Bioinformatics in clinical diagnostics (genetic variants that act as markers for a condition or a disease); Blockchain and Artificial Intelligence/Machine Learning in personalized medicine; Customize disease-prevention strategies in personalized medicine; Big data analysis in personalized medicine; Translating stratification algorithms into clinical practice of personalized medicine.",coverUrl:"https://cdn.intechopen.com/series_topics/covers/7.jpg",hasOnlineFirst:!0,hasPublishedBooks:!0,annualVolume:11403,editor:{id:"351533",title:"Dr.",name:"Slawomir",middleName:null,surname:"Wilczynski",slug:"slawomir-wilczynski",fullName:"Slawomir Wilczynski",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0033Y000035U1loQAC/Profile_Picture_1630074514792",biography:"Professor Sławomir Wilczyński, Head of the Chair of Department of Basic Biomedical Sciences, Faculty of Pharmaceutical Sciences, Medical University of Silesia in Katowice, Poland. 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Editor-in-chief of the journal in the field of aesthetic medicine and dermatology - Aesthetica.",institutionString:null,institution:{name:"Medical University of Silesia",institutionURL:null,country:{name:"Poland"}}},editorTwo:null,editorThree:null,series:{id:"7",title:"Biomedical Engineering",doi:"10.5772/intechopen.71985",issn:"2631-5343"},editorialBoard:[{id:"5886",title:"Dr.",name:"Alexandros",middleName:"T.",surname:"Tzallas",slug:"alexandros-tzallas",fullName:"Alexandros Tzallas",profilePictureURL:"https://mts.intechopen.com/storage/users/5886/images/system/5886.png",institutionString:"University of Ioannina, Greece & Imperial College London",institution:{name:"University of Ioannina",institutionURL:null,country:{name:"Greece"}}},{id:"257388",title:"Distinguished Prof.",name:"Lulu",middleName:null,surname:"Wang",slug:"lulu-wang",fullName:"Lulu Wang",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bRX6kQAG/Profile_Picture_1630329584194",institutionString:"Shenzhen Technology University",institution:{name:"Shenzhen Technology University",institutionURL:null,country:{name:"China"}}},{id:"225387",title:"Prof.",name:"Reda R.",middleName:"R.",surname:"Gharieb",slug:"reda-r.-gharieb",fullName:"Reda R. 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