Operating parameters of the laboratory test rig by modeling the plough body –soil interaction
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Barely three months into the new year and we are happy to announce a monumental milestone reached - 150 million downloads.
\n\nThis achievement solidifies IntechOpen’s place as a pioneer in Open Access publishing and the home to some of the most relevant scientific research available through Open Access.
\n\nWe are so proud to have worked with so many bright minds throughout the years who have helped us spread knowledge through the power of Open Access and we look forward to continuing to support some of the greatest thinkers of our day.
\n\nThank you for making IntechOpen your place of learning, sharing, and discovery, and here’s to 150 million more!
\n\n\n\n\n'}],latestNews:[{slug:"webinar-introduction-to-open-science-wednesday-18-may-1-pm-cest-20220518",title:"Webinar: Introduction to Open Science | Wednesday 18 May, 1 PM CEST"},{slug:"step-in-the-right-direction-intechopen-launches-a-portfolio-of-open-science-journals-20220414",title:"Step in the Right Direction: IntechOpen Launches a Portfolio of Open Science Journals"},{slug:"let-s-meet-at-london-book-fair-5-7-april-2022-olympia-london-20220321",title:"Let’s meet at London Book Fair, 5-7 April 2022, Olympia London"},{slug:"50-books-published-as-part-of-intechopen-and-knowledge-unlatched-ku-collaboration-20220316",title:"50 Books published as part of IntechOpen and Knowledge Unlatched (KU) Collaboration"},{slug:"intechopen-joins-the-united-nations-sustainable-development-goals-publishers-compact-20221702",title:"IntechOpen joins the United Nations Sustainable Development Goals Publishers Compact"},{slug:"intechopen-signs-exclusive-representation-agreement-with-lsr-libros-servicios-y-representaciones-s-a-de-c-v-20211123",title:"IntechOpen Signs Exclusive Representation Agreement with LSR Libros Servicios y Representaciones S.A. de C.V"},{slug:"intechopen-expands-partnership-with-research4life-20211110",title:"IntechOpen Expands Partnership with Research4Life"},{slug:"introducing-intechopen-book-series-a-new-publishing-format-for-oa-books-20210915",title:"Introducing IntechOpen Book Series - A New Publishing Format for OA Books"}]},book:{item:{type:"book",id:"5388",leadTitle:null,fullTitle:"Human Helminthiasis",title:"Human Helminthiasis",subtitle:null,reviewType:"peer-reviewed",abstract:"Human helminthiasis, known as worm infections, is any macroparasitic disease affecting humans, in which a part of the body is invaded by a lot of worms, known as helminths. They are broadly classified into flukes, tapeworms, and roundworms. Soil-transmitted helminthiasis and schistosomiasis are the most important, being included into the neglected tropical diseases. Helminthiasis has been found to result in poor birth outcome, less cognitive development, lower school and work performance, lower socioeconomic development, and poverty. Soil-transmitted helminthiases are responsible for parasitic infections in as much as a quarter of the human population worldwide. This group of infective diseases has been targeted under the joint action of the world's leading pharmaceutical companies and local governments, trying to achieve their eradication.",isbn:"978-953-51-2954-7",printIsbn:"978-953-51-2953-0",pdfIsbn:"978-953-51-7340-3",doi:"10.5772/62673",price:119,priceEur:129,priceUsd:155,slug:"human-helminthiasis",numberOfPages:158,isOpenForSubmission:!1,isInWos:1,isInBkci:!1,hash:"6f2002f4cb6e246a51ed8688e076db4d",bookSignature:"Luis Rodrigo",publishedDate:"February 15th 2017",coverURL:"https://cdn.intechopen.com/books/images_new/5388.jpg",numberOfDownloads:13102,numberOfWosCitations:19,numberOfCrossrefCitations:8,numberOfCrossrefCitationsByBook:2,numberOfDimensionsCitations:26,numberOfDimensionsCitationsByBook:2,hasAltmetrics:0,numberOfTotalCitations:53,isAvailableForWebshopOrdering:!0,dateEndFirstStepPublish:"March 22nd 2016",dateEndSecondStepPublish:"April 12th 2016",dateEndThirdStepPublish:"July 17th 2016",dateEndFourthStepPublish:"October 15th 2016",dateEndFifthStepPublish:"November 14th 2016",currentStepOfPublishingProcess:5,indexedIn:"1,2,3,4,5,6",editedByType:"Edited by",kuFlag:!1,featuredMarkup:null,editors:[{id:"73208",title:"Prof.",name:"Luis",middleName:null,surname:"Rodrigo",slug:"luis-rodrigo",fullName:"Luis Rodrigo",profilePictureURL:"https://mts.intechopen.com/storage/users/73208/images/system/73208.jpg",biography:"Dr. Luis Rodrigo, MD, is a Professor Emeritus of Medicine, at the University of Oviedo, Spain. He has been Chief of Gastroenterology Service at HUCA Hospital, Oviedo, for more than forty years. He obtained a Ph.D. in 1975 and has developed a long teaching and research career. Dr. Rodrigo has published 716 scientific papers, 435 written in English and the rest in Spanish. He has participated as the main investigator in forty-five clinical trials and has directed forty doctoral theses. He has contributed actively to the formation of around 100 specialists in gastroenterology working in his hospital and other hospitals in Spain and abroad. He has written around thirty-five book chapters and edited twenty-six books in his specialty and related diseases.",institutionString:"University of Oviedo",position:null,outsideEditionCount:0,totalCites:0,totalAuthoredChapters:"5",totalChapterViews:"0",totalEditedBooks:"16",institution:{name:"University of Oviedo",institutionURL:null,country:{name:"Spain"}}}],equalEditorOne:null,equalEditorTwo:null,equalEditorThree:null,coeditorOne:null,coeditorTwo:null,coeditorThree:null,coeditorFour:null,coeditorFive:null,topics:[{id:"1046",title:"Infectious Diseases",slug:"infectious-diseases"}],chapters:[{id:"54057",title:"World Wide Epidemiology of Helminths Infection",doi:"10.5772/67273",slug:"world-wide-epidemiology-of-helminths-infection",totalDownloads:3682,totalCrossrefCites:2,totalDimensionsCites:7,hasAltmetrics:0,abstract:"Helminths (from the Greek Helmins, meaning worm) include three groups of parasitic worm, large multicellular organisms with complex tissues and organs. Helminths do not replicate within the human host except Strongyloides stercoralis. Prevalence is commonly combined with worm burden (intensity of infection), which is commonly measured by the number of eggs per gram (EPGs) of faeces for intestinal helminths and schistosomes. Based on EPGs and their association with morbidity, individuals are classified into categories of light, moderate and heavy infection by the WHO. In the case of soil‐transmitted helminths, the WHO recommends use of both prevalence and intensity of infection to classify communities into transmission categories—category I (high), category II (medium), and category III (low). The neglected status of the helminthiasis should be addressed on community levels and globally all over the world.",signatures:"Mohamed S. Abdeltawabi, Nahla El Seddik and Hosni K. Salem",downloadPdfUrl:"/chapter/pdf-download/54057",previewPdfUrl:"/chapter/pdf-preview/54057",authors:[{id:"96052",title:"Prof.",name:"Hosni",surname:"Salem",slug:"hosni-salem",fullName:"Hosni Salem"},{id:"196491",title:"Dr.",name:"Mohamed S",surname:"Abdeltawab Ali",slug:"mohamed-s-abdeltawab-ali",fullName:"Mohamed S Abdeltawab Ali"},{id:"196493",title:"Dr.",name:"Nala",surname:"Seddik",slug:"nala-seddik",fullName:"Nala Seddik"}],corrections:null},{id:"52270",title:"Mass Spectrometry and Metabolomics—New Approaches for Helminth Biochemical Studies",doi:"10.5772/65040",slug:"mass-spectrometry-and-metabolomics-new-approaches-for-helminth-biochemical-studies",totalDownloads:1691,totalCrossrefCites:1,totalDimensionsCites:4,hasAltmetrics:0,abstract:"Metabolomics, the study of the endogenously synthesized small molecules repertoire (nonproteinaceous), is of great relevance for establishing a wide view of cell physiology at specific moments, linking metabolic profiles to phenotypes and genotypes. To better understand biological systems, such as helminths life cycle, helminthic infection, and host-parasite interaction, metabolomics studies are crucial. For that, mass spectrometry-based metabolomics is the most popular strategy. Nontargeted metabolomics allows researchers to profile entire metabolomes present in cells, tissues, biofluids, or even samples as complex as stools. Through different mass spectrometric techniques, it is possible to unveil chemical markers for helminths, such as Schistosoma mansoni (a trematode) and Ascaris lumbricoides (a nematode), in addition to study mechanisms of action for different drugs, which targets parasites. Therefore, mass spectrometry allows designing biochemical pathways that may clarify the processes of parasite life cycle, helminthic infection, and host-parasite interaction, providing targets to further interference for parasite control or even infection treatment.",signatures:"Estela O. Lima, Cibele Z. Esteves, Diogo N. Oliveira, Tatiane M.\nGuerreiro, Carlos F. O. R. Melo and Rodrigo R. Catharino",downloadPdfUrl:"/chapter/pdf-download/52270",previewPdfUrl:"/chapter/pdf-preview/52270",authors:[{id:"188794",title:"Prof.",name:"Rodrigo",surname:"Catharino",slug:"rodrigo-catharino",fullName:"Rodrigo Catharino"},{id:"194479",title:"Dr.",name:"Estela",surname:"Lima",slug:"estela-lima",fullName:"Estela Lima"},{id:"194480",title:"MSc.",name:"Diogo",surname:"Oliveira",slug:"diogo-oliveira",fullName:"Diogo Oliveira"},{id:"194481",title:"MSc.",name:"Cibele",surname:"Esteves",slug:"cibele-esteves",fullName:"Cibele Esteves"},{id:"194482",title:"MSc.",name:"Tatiane",surname:"Guerreiro",slug:"tatiane-guerreiro",fullName:"Tatiane Guerreiro"},{id:"194483",title:"Mr.",name:"Carlos",surname:"Melo",slug:"carlos-melo",fullName:"Carlos Melo"}],corrections:null},{id:"52071",title:"Helminths and their Role in Environmental Engineering",doi:"10.5772/64878",slug:"helminths-and-their-role-in-environmental-engineering",totalDownloads:2349,totalCrossrefCites:1,totalDimensionsCites:6,hasAltmetrics:0,abstract:"Helminth eggs represent an important challenge to environmental engineers as they are among the most difficult biological parasites to inactivate in wastewater and sludge. Even though no official data on helminthiasis exist, it is estimated that more than 2.6 billion people are affected. These parasites are of concern in developing countries, particularly in those areas where the reuse of wastewater and sludge for agriculture is common. With regard to this, the unrestricted use of wastewater for irrigation presents a serious health risk due to the dissemination of pathogens, particularly helminth eggs. Helminth eggs survive in water, soil, and crops for several months and over much longer periods than other microorganisms. Therefore, and in order to minimize risk, several guidelines and regulations exist which limit their content in wastewater and sludge. Risk assessment estimates that such regulations may be less strict in developing countries where higher concentrations of helminth eggs occur in wastewater and sludge. These eggs need to be removed from wastewater and inactivated in sludge using certain treatment processes, some of which are not feasible in developing countries. Adequate methods are needed to precisely identify and quantify helminth eggs in environmental samples. Therefore, a multidisciplinary approach is needed to address helminthiasis in environmental engineering issues.",signatures:"Blanca Jiménez, Catalina Maya, José A. Barrios and Inés Navarro",downloadPdfUrl:"/chapter/pdf-download/52071",previewPdfUrl:"/chapter/pdf-preview/52071",authors:[{id:"188693",title:"Dr.",name:"Jose",surname:"Barrios",slug:"jose-barrios",fullName:"Jose Barrios"}],corrections:null},{id:"53206",title:"Helminthiasis: A Systematic Review of the Immune Interactions Present in Individuals Coinfected with HIV and/or Tuberculosis",doi:"10.5772/66124",slug:"helminthiasis-a-systematic-review-of-the-immune-interactions-present-in-individuals-coinfected-with-",totalDownloads:2023,totalCrossrefCites:2,totalDimensionsCites:5,hasAltmetrics:0,abstract:"Helminth infections are highly endemic in parts of the world where the two killer epidemics caused by Mycobacterium tuberculosis (M.tb) and the human immunodeficiency virus (HIV) intersect. Sub-Saharan Africa is hardest hit by this epidemiological overlap. Consequently, several studies have investigated the immunological outcomes of helminth coinfection with either HIV or M.tb, to elucidate the central hypothesis that chronic infection with helminths exacerbates the course of HIV and tuberculosis disease. However, there is no conclusive evidence to confirm whether helminth-induced immunity modulates HIV- and TB-specific immune responses and their pathogenesis or vice versa. The present chapter summarizes the epidemiology, clinical course, and immune interactions during helminths and HIV/TB coinfections and undertakes a systematic review of the existing literature published from Africa on this subject. The aim was to determine if chronic helminthiasis has a negative impact on HIV and TB infections. A PubMed search was undertaken with no language and time restrictions. Search terms used included a varied combination of “Helminth coinfection and immunity and TB coinfection or TB immunity and HIV coinfection or HIV immunity and Africa.” Names of individual species were also permutated in the search terms. Reviews and bibliographies of selected articles were screened to identify additional relevant articles or studies. Of the total 1021 articles retrieved, 47 were relevant with 31 helminth and HIV coinfection and 16 helminths and TB coinfection articles. While many studies failed to find a negative impact of helminth infection on immune responses to HIV and/or TB, a significant number found evidence of deleterious effects of coinfection with helminths such as immune activation, impaired Th1 responses to TB antigens, higher viral loads, lower CD4+ counts, and increased risks of antiretroviral immunologic failure, mother to child HIV transmission or TB disease. Some of the helminth-induced immune dysregulation was reversed by deworming, while some studies found no benefit of antihelminthic treatment. More studies particularly in Southern Africa are needed to increase the much sought evidence of the impact of deworming among HIV-infected individuals as this seems the most feasible, cost-effective intervention with little or no serious adverse effects. Lastly, with the expansion of ART and increased access to HIV treatment, the effects of helminths on vaccines, TB, and antiretroviral treatments efficacy also need serious consideration, in light of the suggestive evidence of possible immunologic failure due to helminth coinfection.",signatures:"Zilungile L. Mkhize-Kwitshana, Rebecca Tadokera and\nMusawenkosi H.L. Mabaso",downloadPdfUrl:"/chapter/pdf-download/53206",previewPdfUrl:"/chapter/pdf-preview/53206",authors:[{id:"187123",title:"Dr.",name:"Zilungile",surname:"Mkhize-Kwitshana",slug:"zilungile-mkhize-kwitshana",fullName:"Zilungile Mkhize-Kwitshana"},{id:"195905",title:"Dr.",name:"Musawenkosi",surname:"Mabaso",slug:"musawenkosi-mabaso",fullName:"Musawenkosi Mabaso"},{id:"195906",title:"Dr.",name:"Rebecca",surname:"Tadokera",slug:"rebecca-tadokera",fullName:"Rebecca Tadokera"}],corrections:null},{id:"52540",title:"Atherosclerosis and Helminths Infection",doi:"10.5772/65515",slug:"atherosclerosis-and-helminths-infection",totalDownloads:1364,totalCrossrefCites:0,totalDimensionsCites:0,hasAltmetrics:0,abstract:"Atherosclerosis is a chronic disease that causes various cardiovascular complications. Plaque formation in atherosclerosis is considered similar to the pathogenesis of other autoimmune diseases; thus, immunomodulation and immunosuppression may present strategies for the treatment and prevention of these diseases. Interestingly helminth infection was found to inhibit T helper 1-mediated autoimmune diseases and T helper 2-mediated allergy and asthma, indicating significant potential for clinical application. Some study even found that therapeutic efficacy of the viable tapeworm was superior to dexamethasone treatment. Recently, some studies have shown an inverse association between helminth infections and inflammatory diseases, including diabetes mellitus, lipid abnormality, and atherosclerosis. Will the underlying mechanism bring us a new idea on the treatment for these diseases? We tried to find an answer by reviewing recent articles.",signatures:"Shi-Wei Shen, Yun Lu, Feng Li, Zhen-Hai Shen, Ming Xu, Wei-Feng\nYao, Hua-Jin Qi, Ling Zhou, Yin-Bo Feng, Ling Wang, Jing-Ting Yun\nand Da-Xin Tong",downloadPdfUrl:"/chapter/pdf-download/52540",previewPdfUrl:"/chapter/pdf-preview/52540",authors:[{id:"188535",title:"Dr.",name:"Zhenhai",surname:"Shen",slug:"zhenhai-shen",fullName:"Zhenhai Shen"}],corrections:null},{id:"52408",title:"Global Control Efforts of Schistosomiasis and Soil-Transmitted Helminthiasis",doi:"10.5772/65282",slug:"global-control-efforts-of-schistosomiasis-and-soil-transmitted-helminthiasis",totalDownloads:1993,totalCrossrefCites:2,totalDimensionsCites:4,hasAltmetrics:0,abstract:"Schistosomiasis is a waterborne disease whose life cycle involves freshwater sources conducive for the survival and reproduction of aquatic snails that form a connective link between man and water in the life cycle and transmission of schistosomiasis. The African region has network of rivers with freshwater suggesting the presence of schistosomiasis and difficulty to control. Some communities, due to socioeconomic challenges, have inadequate sanitation and water supply; use of bush toilets for excretion is commonly practiced. These conditions in Africa also promote transmission of soil-transmitted helminthiasis. The World Health Organization (WHO), in response to the public health and socioeconomic impact of neglected tropical diseases, is coordinating strategies for the control and elimination of the diseases including schistosomiasis and soil-transmitted helminthiasis. As one of the milestones, mapping of neglected tropical diseases in the African region has been prioritized for the implementation of control strategies. In countries where mapping has been completed, WHO and its partners are supplying medicines required for annual mass treatment for preventive chemotherapy and encourage countries to take ownership in implementing complementary strategies for morbidity control, elimination and eradication of country-specific neglected tropical diseases. The mainstay of helminthiasis control is preventive chemotherapy, targeting school age children to prevent morbidity and development of pathological manifestations, including urogenital schistosomiasis that is understood to contribute to HIV transmission. Vaccines are still to be discovered and designed, with many possible antigen candidates, but however the immune responses are still to be fully understood. There is need to understand the subtle link between each component of the immune responses and the host immunogenetics impacting on the translated immunological response of cytokines that are delicately controlled for cellular immunity and antibody production. Currently, preventive chemotherapy treatment is the only control method in concert with health education in an attempt to cut the helminthiasis life cycle.",signatures:"Takafira Mduluza, Tawanda J. Chisango, Agness F. Nhidza and\nAmos Marume",downloadPdfUrl:"/chapter/pdf-download/52408",previewPdfUrl:"/chapter/pdf-preview/52408",authors:[{id:"63704",title:"Prof.",name:"Takafira",surname:"Mduluza",slug:"takafira-mduluza",fullName:"Takafira Mduluza"},{id:"188575",title:"Dr.",name:"Tawanda",surname:"Chisango",slug:"tawanda-chisango",fullName:"Tawanda Chisango"},{id:"188576",title:"Dr.",name:"Agness",surname:"Nhidza",slug:"agness-nhidza",fullName:"Agness Nhidza"},{id:"188577",title:"MSc.",name:"Amos",surname:"Marume",slug:"amos-marume",fullName:"Amos Marume"}],corrections:null}],productType:{id:"1",title:"Edited Volume",chapterContentType:"chapter",authoredCaption:"Edited by"},subseries:null,tags:null},relatedBooks:[{type:"book",id:"8722",title:"E. 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Soil has an essential part in preserving life on earth. The main function of soil lies in the fact that it represents the support for the agriculture practice, aiming to insure the peoples’ alimentary security and safety, due to its physical and biological properties, to its fertility, to its capacity to provide plants with the water and nutrients needed for their growth.
Taking into account the intensive development of agriculture, the concept of “sustainable development” is a new and complex one, imposed to humanity by the need for the preservation of the soil functions and which is connected not only to agriculture but also to other knowledge fields.
Within the frame of this concept, a special place belongs to sustainable agriculture, which constitutes a system of technologies and good practices aiming not only towards better productions but also to achieve conservative goals.
The main objectives of sustainable agriculture are:
alimentary safety, by providing the human needs with the necessary food and fiber;
preservation of the quality of the environment and of the natural resources vital to the agriculture;
more efficient use of the renewable and non-renewable resources.
In essence, sustainable agriculture must harmoniously combine the three main dimensions: economical, social and ecological.
In order to achieve the goals of sustainable agriculture, the way in which soil tillage works are fulfilled is of an extreme importance, because the induced physical and mechanical changes affect the soil’s physical, chemical and biological processes. This is the reason why the concept of “conservative agriculture” (CA) was developed, as a part of the sustainable agriculture systems, which is based on the use of natural renewable resources, especially soil, and on real time soil regeneration; some complementary agricultural practices are included herein [9, 17]:
minimum soil disturbance (through reduced soil tillage works and stubble seeding), in order to preserve the soil’s structure, fauna and organic matter;
permanent soil coating (covering crops, residue, mulch), in order to protect it and contribute to the weeds removal;
different crops rotation and combination schemes, in order to stimulate soil microorganisms and to remove weeds, diseases and pests.
Hence, conservative agriculture is based on an unconventional soil tillage system, named “Soil conservation tillage system” (SCTS). Within this system, moldboard plowing is deferred (completely or partially), the number of agricultural operations is limited and at least 15...30% of the vegetable debris is kept on the soil surface. Worldwide, this system is used on nearly 45% of the farmland, and an increase to 60% is appraised for the next twenty years [9, 17]. The unconventional soil tillage system consists of very different methods, starting with the seeding in the untilled soil and ending with the deep loosening without furrow overturning. Between these two extreme methods, many other variants are possible: reduced tillage, minimum tillage (when up to 30% of the vegetable debris is left on the soil surface), minimum tillage with vegetable mulch (more than 30% of the vegetable debris is left on the soil surface), ridge seeding, partial or strip tillage etc. [9]
As a result, three directions were outlined in order to define the unconventional soil tillage systems:
direct sowing, when seeds are inserted into the practically non-tilled soil. In this case, soil is tilled only in order to create very small gutter, using small knives mounted on the seeding machine.
minimum tillage or reduced tillage. In this case, the fact that different types of soil must be differently loosened, in order to favor the normal plant growth, is taken into account. The minimum tillage system includes either the base soil loosening, without furrow overturn, or the superficial tillage, followed by seeding. Sometimes, a minimum of mechanical works is required in order to destroy the weeds, to favor some biologic processes and to support the development of the roots. This system allows the reduction of the energy consumption and working time.
“rotation” tillage represents another possibility to diminish the intensity of soil loosening. In this case, tillage should be very well correlated with crop rotation. This system is characterized by some peculiarities: the different plants, which are grown in a crop rotation system, have different requirements regarding the soil tillage system; soil requirements towards the tillage system are different from one crop to another; soil characteristics are gradually changing (in a favorable or unfavorable way). It is important to notice that the soil tillage system should be modified according to requirements of the respective crop.
Soil degradation is one of the most important problems to be faced nowadays. It is appraised that 5-7 mha of soil are degrading worldwide each year, with a tendency to attend 10 mil. ha per year in the near future [8]. Soil degradation may be physical, chemical and biological. In the case of the physical soil degradation, two important features are affected: bulk density and structure. This means that bulk density increases (the soil is compacted) and the structural elements are damaged (deformed, crushed, sheared, broken, fragmented) [4, 12, 15].
Mechanization of the agricultural processes and the use of heavy productive units, with high working width, resulted, over time, in soil compaction and reduction of harvest. The use of the organic fertilizers and deep tillage finally results in the diminishing of the content of organic matter and in an increased sensibility to compaction [20].
The artificial (anthropic) soil compaction is the result of exaggerated traffic imposed by agricultural operations, transport operations etc. The intensity of anthropic compaction depends on different factors. Some of them belong to soil, namely to its susceptibility to compaction: uneven grain size distribution, unstable structure, reduced humus content etc. Other factors are influenced by the characteristics of the agricultural equipment; this compaction is favored by the heavy machineries exerting high pressure over soil, by the increased number of passings, by the increased tire air pressure, by the agricultural traffic performed over wet soil etc.
Unlike the wheels (tracking wheels, driving wheels etc.), which compact the soil, the active parts of the tillage equipment (rotary cultivator tines, plow shares, cultivator tines etc.) loosen the soil; the rollers, the combined seedbed preparation devices and the combined cultivator are exceptions [6].
In the case of the active parts used for seedbed preparation, their destructive action over the soil structure elements is of an utmost importance. The active parts destroy, to a greater or a lesser extent, the structure elements through deformation, crumbling, cutting, breaking-up. The destruction of the soil’s structure is a general phenomenon, occurring at any tillage operation, but it gets large proportions in soils with a rough texture or average-rough texture (sandy soils, sand-loamy soils, clay-loamy soils) for which the mechanical stability of the structure elements is lower, due to the lower clay content. The recently tilled soils, the humid soils or the dry clay soils on which loosening is obtained by the means of rotating active parts (disc harrows, rotary cultivators) are also vulnerable [4].
It should be emphasized that not only the active parts of the tillage equipments destroy the soil’s structure, but also the wheels of the tractors or the tracking wheels of the agricultural machinery. In this case, the wheel-soil contact pressure produces compaction as a result of the deformation and breaking-up of the structure elements. The division of the structure elements into fragments results in the increase of the bulk density because of a more stuffed settlement. Consequently, the soil’s capacity to drain and store water is diminished, the thermal regime worsens, the accessibility of plants to nutrients is diminished and the activity of the anaerobic microorganisms is reduced; on sloping lands, the erosion due to water is intensified, and the plants have difficulties in developing the root system, loose their stability and harvest is diminished [14].
The cutting edges of the tines of the rotary harrow cut some of the soil’s structural elements, which are also destroyed through deformation, breaking, fragmentation, crumbling, due to the peripheral speed of the tines, to the friction between tines and soil and to the impact between the slices and the housing of the rotary harrow. Pulverization of the structural elements may also occur, when some of them are fragmented to the maximum extent, resulting in particles of clay, silt and sand [19].
When using rotary harrows for the seedbed preparation care should be taken so that the width of the soil slices should not be less than 25 mm. In the working process, the number of destroyed structural elements increases when the slices get thinner. Therefore, the peripheral speed of the tines should no exceed 6 m/s, while the speed of the advance movement should not exceed 1 m/s.
During the working process, the cutting edge of the disc cuts some of the soil’s structural elements; the number of cut structural elements is higher when the disk’s cutting edge is indented. In the meantime, the bending of the soil layer, vertically and horizontally, its twisting, as well as the friction between soil and disk, cause the destruction of some structural elements, through deformation, breaking, fragmentation. The proportion of damaged structural elements increases with speed [22].
The weed cutting active parts are aimed to cut the weeds and loosen the soil. During the working process of the arrow type tines, soil is cut horizontally, at a certain depth; in the meantime, the weeds are cut and soil is loosened and crumbled.
The straight, chisel, diamond pointed and narrow arrow type loosening active parts are mounted on rigid or elastic holders. When elastic holders are used, the active part vibrates, exerting an energetic action over soil. As a result of the displacement of these active parts, the superficial soil layer is crumbled and loosened.
The weed cutting type active parts cut some of the soil’s structural elements. All the types of active parts (for both weed cutting and soil loosening) destroy the structural elements due to the advance movement, friction, breaking of soil layers, vibration; the structural elements are destroyed through deformation, crumbling, breaking, fragmentation. In order to diminish these adverse effects, speed should be limited to 10-12 km/h.
Physical degradation of the soil, caused by the interaction with the active parts and support wheels of the agricultural equipment, refers especially to structural deterioration and its compaction. In order to quantify these issues studies must be performed in order to establish the critical values of the working parameters (of the active parts and wheels) leading to the physical degradation of the soil. In the meantime, correlations should be established between the above-mentioned parameters and the ones characterizing soil structure and compaction.
With the purpose to perform these studies a laboratory test rig for the study of the interaction between the active parts and wheels of agricultural equipment, on one hand, and soil, on the other hand, was designed and built. The designing process has taken into account the similarity laws, in order to reproduce in laboratory conditions the complex processes occurring at the contact interface between the working parts and soil and between the wheels of the agricultural equipments and soil.
The test rig (Figure 1) consists of a rigid frame (1), the soil bin (2), the carriage (3), on which the active part (plough body) for soil working is mounted (6), the wheel with tire (7) and the drum for leveling - settling (8); at the end of laboratory test rig a winch is fixed, which is for trolley carriage with the cable (5). Due to its length (10240 mm), the soil bin is composed of five sections, joined together with screws. The bin was coated, at the inside, with a plastic sheet.
An electric motor (9) and a cylindrical gear (10) are used to drive the drum (11); the drum drives the cable (5), thus towing the cart (3). The ends of the traction cable are attached to the carriage by the means of the load cells (4).
The carriage is also fitted with an electric motor (12) and a gear transmission in order to drive the tire wheel (7). The working depth of the active body can be adjusted by the means of the screw mechanism (13). The screw mechanism (14) is used to adjust the vertical position of the tire wheel; the screw mechanism (15) is used to change the vertical position of the soil leveling and compaction drum. The soil leveling and compaction roller (8), mounted on the carriage, is used to achieve a certain soil compaction, before it is processed by the active body or performing various experiments with the tire wheel.
Four upper trundles – two in the front and two in the back – and four lower trundles - also two in the front and two in the back - are mounted on the carriage frame; the trundles are rolling on rails, mounted on each side of the soil channel frame.
When the carriage is towed by the means of the cable, the wheel (7) rotates due to the interaction with the soil and thus the conditions for a driven tractor wheel are simulated. When the carriage is not towed, the wheel (7) becomes a driving one, being driven by the electrical motor (12) by the means of a cylindrical gear drive and of a trapezoidal belt drive. Thus, the driving wheel of the tractor is simulated.
The towing cable is connected to the carriage by the means of two 1000 daN strain gauge load cells, allowing the measurement of the traction force needed to displace the carriage; the transducers are fitted with spherical joints at both ends and are connected to a programmable weighing controller, which displays the mean values of the corresponding sampling signal and eliminates the load spikes that could occur due to vibrations and soil unevenness.
A control panel (18) is used for the power supply of the two electric motors; the electric cables are guided by the steel cable (16), fixed between the pillars (17). The electrical motors are controlled by the means of a frequency converter, allowing the adjustment of the rotation speed when the frequency is modified between 3 and 50 Hz. The dynamic braking principle is used in order to stop the carriage at the end of travel. Switches on the control panel allow the selection of the electric motor (the carriage towing motor or the tire wheel driving motor), as well as its forward or reverse motion.
A bill chernozem type of soil was used to fill the soil channel bin, having a loam-clay texture, the aggregate size of 0.02... 50 mm and 17-19% humidity.
The test rig was tested in two phases. In the first phase, the laboratory test rig (soil channel) was tested to see if the prescribed constructive-functional parameters are attained. It was found that the test rig has the following constructive-functional parameters: depth of active enforcement machinery of working the soil: 0... 300 mm; adjustment of working angle of the active part relative to the soil surface: (-) 250... (+) 250; the speed of the carriage when it is hauled by the 5,5 kW electric motor: 0,5... 1,55 m/s (1,8... 5,58 km/h); the maximum pull-down force for the with tire wheel and the soil leveling and settlement drum: 500 daN; maximum traction force of the cable (of the carriage), at a speed of the trolley of 0,55 m/s: 800 daN; maximum traction force of the cable (of the carriage) at a speed of the carriage of 1,55 m/s: 280 daN; cable breakdown point: 40,83 kN. It was concluded that there were no significant differences between the design parameters and the achieved ones.
In the second phase, the laboratory test rig was used in order to study the soil - moldboard plough body interaction and the tire wheel-soil interaction (Figure 2).
The studies concerning the active part-soil interaction were performed over a semi helical moldboard plough body, with a working width of 200 mm. The plough body was mounted on the carriage of the test rig. The influence of working depth, soil resistance to penetration and travel speed on the traction resistance and specific power consumption were evaluated. The results presented in the Table 1 show that increasing the traveling speed of the plough body results in an increased traction resistance. In the meantime, as the plough body speed increases, the specific power consumption significantly increases.
When soil penetration resistance increases, the traction force and specific power consumption also increase.
As far as the working depth is concerned, it was concluded that the increase of the penetration depth of the plough body resulted in a significant increase of traction resistance.
It was also noticed that increasing the working depth of the plough body resulted in an uneven change of the specific power consumption: increasing the working depth from 100 mm to 150 mm caused a slight decrease of the specific power consumption; when the working depth was further increased from 150 mm to 200 mm, the specific power consumption increased. These variations of the power specific consumption could be explained as follows: for small working depths (below 15 cm) the soil slice was not yet deployed as furrow and was not overturned, so that the specific power consumption was low; for depths over 15 cm the conditions to overturn the furrow were better, so that supplementary power was consumed in order to overturn it.
In the series of experiments regarding the driving wheel mounted on the test rig, the tire wheel was used to drive the carriage along the soil channel, the wheel being driven by the 3 kW electric motor. The wheel was equipped with a 5.00-12/4PR TA60 traction tire (with angled lugs).
Laboratory test rig with soil channel for the study of the interaction between the active parts or agricultural wheels and the soil
The tests were aimed to evaluate the main operating parameters of the driving wheel test rig. The effects of the wheel speed, soil penetration resistance and wheel pushdown force over the carriage speed, wheel slip and wheel traction force were studied. The results obtained in these experiments are presented in Table 2.
Based on the experimental results it was concluded that wheel slip decreased when its speed was increased; in the meantime, the traction force decreased when its speed was increased.
As far as the soil resistance to penetration was concerned, it was concluded that its increase led to the increase of the wheel speed, because a more compact soil increases the adherence of the driving wheel; the increased adherence diminishes wheel slip, increases the carriage travel speed and also increases the traction force of the wheel.
Laboratory experiments in order to study of the interaction of tire wheel and active part with the soil
Working depth of plough body (mm) | Soil resistance to penetration (MPa) | Speed of plough body (m/s) | Traction force (N) | Specific power consumption (W/cm2) |
100 | 0,2 | 0,75 | 705 | 2,65 |
1,00 | 720 | 3,60 | ||
1,25 | 735 | 4,59 | ||
0,4 | 0,75 | 925 | 3,47 | |
1,00 | 940 | 4,70 | ||
1,25 | 960 | 6,00 | ||
150 | 0,2 | 0,75 | 1055 | 2,64 |
1,00 | 1070 | 3,57 | ||
1,25 | 1080 | 4,50 | ||
0,4 | 0,75 | 1380 | 3,45 | |
1,00 | 1400 | 4,67 | ||
1,25 | 1420 | 5,92 | ||
200 | 0,2 | 0,75 | 1450 | 2,72 |
1,00 | 1470 | 3,67 | ||
1,25 | 1485 | 4,64 | ||
0,4 | 0,75 | 1859 | 3,47 | |
1,00 | 1890 | 4,72 | ||
1,25 | 1930 | 6,03 |
Operating parameters of the laboratory test rig by modeling the plough body –soil interaction
Wheel speed (rot/min) | Soil resistance to penetration (MPa) | Down force over the wheel (N) | Speed of the trolley (m/s) | Driving wheel slip (%) | Traction force of the driving wheel (N) |
20 | 0,2 | 500 | 0,50 | 17 | 230 |
750 | 0,51 | 15 | 360 | ||
1000 | 0,53 | 14 | 580 | ||
0,4 | 500 | 0,51 | 15 | 290 | |
750 | 0,52 | 15 | 442 | ||
1000 | 0,54 | 13 | 610 | ||
30 | 0,2 | 500 | 0,75 | 16 | 220 |
750 | 0,76 | 15 | 350 | ||
1000 | 0,79 | 12 | 570 | ||
0,4 | 500 | 0,76 | 15 | 285 | |
750 | 0,77 | 14 | 438 | ||
1000 | 0,79 | 12 | 600 | ||
40 | 0,2 | 500 | 0,99 | 15 | 220 |
750 | 1,01 | 14 | 340 | ||
1000 | 1,02 | 11 | 560 | ||
0,4 | 500 | 1,01 | 14 | 280 | |
750 | 1,01 | 13 | 410 | ||
1000 | 1,04 | 10 | 580 |
Evaluation of the test rig’s key operating parameters with motored wheel
Regarding the effect of the wheel down force, it was established that an increased force resulted in an increased wheel speed and, consequently, an increased travel speed of the carriage, due to the diminished wheel slip. The explanation is that an increased down force leads to a lower wheel slip, due to the higher wheel adherence; for the same reason, traction force increased when the wheel down force was increased.
Based on the experimental results precise correlations could be established between soil compaction and wheel slip, for a given vertical force acting over the wheel. In the same manner, the relationship between the vertical force and the traction force of the wheel was established, for a certain state of the soil.
The finite volumes method (FVM) was used in order to model the interaction between the active parts of the agricultural equipment and soil. The equations specific to fluid flow are partial derivatives equations. Moreover, these equations are non-linear and interconnected. Under these circumstances, solving the equations is possible only by the means of numerical methods [1, 5].
There are several types of numerical methods for solving the flow equations; the finite volumes method was preferred because it was considered the most appropriate for the simulation of flow and other soil related phenomena, for the particular case of soil- agricultural active part interaction. Within this method, the main stages for solving a problem regarding the soil-active part interaction are as follows:
division of the soil model into control volumes (finite volumes), based on a computational mesh;
integration of the equations for each control volume in order to obtain the algebraic equations which are characteristic to the unknowns of the problem;
solving of the algebraic equations.
Regarding the first stage, the computational mesh may be “structured” (the geometrical elements are 2D triangles or 3D parallelepipeds) or "unstructured” (the geometrical elements are 2D quadrilaterals or 3D tetrahedrons).
The numerical simulation of the physical phenomena characteristic to fluid flow by the means of the CFD (computer fluid dynamics) method is entirely based on the fundamental laws that describe the flow of a fluid: mass conservation, momentum conservation, energy conservation [11].
Five methods may be used in order to solve the problems regarding the interaction between soil and the active parts: empirical and semi empirical methods, dimensional analysis, finite elements method (FEM), discrete elements method (DEM) and the neuronal networks method – ANN (Figure 3) [13].
Methods for the numerical simulation of the active part-soil interaction
The mechanism of the active part-soil interaction may also be described using the rheological behavior of soil, taking into account its dynamic characteristics. The use of CFD method should take into account the dynamics of the active part-soil interaction, considering the irreversible deformations of the soil (see Figure 3) [21].
The design criteria taken into account when building a tillage active part are traction resistance, the volume of the tilled soil and the overall energy requirements. The traction force depends on the pressure exerted by soil over the surface of the active part; soil pressure and its distribution are important items that should be considered when designing the size and shape of the active part.
The condition of the tilled soil depends on the soil’s mechanical behavior and initial condition and on the characteristics of the active part. Soil is a complex material and its behavior is not yet fully understood. The complexity increases even further when taking into account different locations, with different climate conditions and different bulk densities. Several models for predicting the mechanical behavior of soil were considered over time, combining springs, dampers, slide-blocks, and from an elastic, plastic or viscous perspective. The behavior of most soils is non-linear and they can be considered as non-linear plastic or viscous-plastic materials. Thus, soil deformation may be described by a simple viscous-plastic model, the Bingham rheologic model.
The suggested shape of the winged share is a typical one (Figure 4a), but was adapted in order to increase its tillage performances. In the numerical simulation, the active part is mounted on a vertical holder (Figure 4b).
Winged share
The numerical simulation assumes that the active part is stationary, while the viscous-elastic soil is flowing around the tillage tool (Figure 5).
Schematics of the simulated domain (soil bin) and position of the active part
The active part acts as a resistance in the flow field and has the following dimensions: length T=140 mm, width W = 200 mm and height (equal to the working depth) H = 100 mm. The flow field is considered a parallelepiped with a length (8H+T) of 940 mm and a height (3H) of 300 mm. The sidewalls and the lower wall represent boundary conditions for the simulation field and their flow characteristics were neglected.
The CFD simulation showed that, for a soil bin seven times wider than the width of the active part, the wall effect of the bin disappears and an idealized flow pattern around the active part may be considered.
A mixed mesh was used in order to cover the computing domain, structured at the beginning and at the end of the bin and unstructured near the active part. At the tillage body level, the computational mesh was unstructured in the front and in the holder area, with a high density of the mesh, and structured behind the active part, with a lower mesh density (fig. 6). In order to cover the entire model 658000 elements were defined.
Computational mesh and elements for the arrow type tillage body:
Soil classification according to sand, silt and clay content (texture triangle) and models for numerical simulation (O – present case study for soil with 38% clay, 32% silt and 30% sand) [
The viscous-plastic parameters of soil, such as the dynamic viscosity and the shear yield stress 0, were evaluated at a constant speed, with a rheometer. Within the simulation the soil was considered at a humidity of 19% and a resistance to penetration of 400 kPa; other parameters taken into account were as follows: bulk density = 1250 kg/m3, dynamic viscosity = 900 Pas and shear yield stress 0 = 12 kPa. The soil flow speed was w = 3 m/s, this being the traveling speed of the active part.
The following hypothesis were considered in the numerical simulation: a constant working depth of the tillage body; the active part was considered to be rigid; the soil flow was considered laminar and axisymetrical relative to the vertical section; 3D soil crumbling; the soil was considered an continuous, homogenous and anisotropic medium; soil behaves like a viscous-plastic Bingham material; the movement of the active part is considered with a finite yield tension and the displacement of the active part is considered as interaction between the submerged body and the fluid; the interspace between the clods of soil is neglected and soil is considered to be incompressible; cracking of soil occurs when the shear yield for the soil in front of the active part is exceeded.
According to the second law of Newton, the acceleration of the volume of fluid (elementary volume) is directly related to the force acting upon it by the means of the momentum conservation equation:
where d/dt is the full derivative, g is the acceleration of the gravity field (m/s2), p is the hydrostatic pressure (Pa), ij is the tensor of the shear stress (Pa), is the density (kg/m3), ui is the travel speed (m/s) and x is the distance (m).
The full derivative of the fluid volume variation is a time and space dependent function:
Equation (2) shows that the gravitational force, the hydrostatic pressure and the viscous stress (hydrodynamic stress) balance the acceleration of the fluid element. According to this equation soil flowing may be processed taking into account several types of dynamic interactions between the active part and soil:
forces produced by the speed and acceleration of the active part;
soil pressure over the surface of the active part, taking into account the weight of soil;
soil cracking due to the viscous-plastic deformations.
For the Bingham type of plastic fluids, the strain-stress relationship may be written as:
where y = 0 is the yield stress (Pa), = is the plastic or dynamic viscosity ((Pas), is the shearing speed (u/h being the flowing speed gradient) (s-1) and h is the thickness of the sheared layer (m).
In a cartesian system of coordinates (x, y, z) the x component of the equation (1) may be expressed, based on the equations (2 - 4), in the form:
where xy is the shear stress in the xy plane (Pa), xz is the shear stress in the xz plane (Pa), x is the normal stress (Pa) and u, v, w are characteristic coefficients of the x, y, z axes.
In order to satisfy the assumption that the viscous-plastic fluid is homogenous and isotropic, the simulation assumes that the yield stress is not dependent on the position or the orientation of the fluid particles.
In the tillage process, the active body has to overcome soil rigidity and cracking appears only when the tangential stress exceeds the yield stress. When the applied force exceeds the yield stress limit, soil flows as a viscous-plastic fluid, due to shear cracking.
The traction force is equal to or higher than the drag force; in the present simulation the active part is considered to be submerged into soil; hence, the drag force F is given by the relation:
where CD is the drag coefficient, is the density of soil, (kg/m3); uz is the speed along the z axis (m/s), A is the characteristic area of the active part (m2).
The drag coefficient has two components: the drag coefficient due to pressure CDp and the drag coefficient due to friction, CDf :
The weight of each drag component (pressure and friction) depends on the geometrical shape of the active part. The aim of the simulation is to obtain the geometrical shape leading to a minimum drag of the active part with.
A value of 10-4 was considered as the convergence criterion for each iteration and for each of the equations of the flowing process. A relaxation coefficient of 0.3 was chosen in order to maintain a stable convergence (a higher relaxation coefficient increases the convergence time). The results of the simulations were than interpreted considering that the active part is traveling at a constant speed.
Simulations were performed over three types of active parts, with the same geometrical shape, but with different angles between the cutting edges: 2 = 600; 2 = 660; 2 = 700.
Pressure distribution over the surface of the arrow type active body depends on the position of the cutting surfaces and on the characteristics of the soil. The simulations show that the maximum pressure is recorded on the cutting edges.
Table 3 presents the effect of the 2 angle over the variation of the average normal pressure, for the same type of soil. The distribution of the normal pressure on the surface of the active part is shown in Figure 8.
2 (degrees) | 60 | 66 | 70 |
Average pressure (kPa) | 4.4 ... 45.2 | 4.5 ... 53.5 | 4.45 ... 53.35 |
Variation of the average normal pressure along the cutting edges
Distribution of the normal pressure (Pa) on the surface of the active part
As previously mentioned, drag has two components, one due to pressure and the other due to friction; therefore, the same two components (pressure and viscosity) are present within the traction force (Table 4).
The tangential stress distribution over the surface of the active part (the viscosity or friction component) reaches a maximum on the cutting edges and diminishes towards the inner part of the active body (Figure 9).
Figure 10 presents the variation of the soil speed; the soil is disturbed in front of the active body and the distribution pattern of the flowing speed clearly indicates the region where the cracks appear. Speed variation along the longitudinal (z) axis presents two distinct flowing regions (Figure 10b): one corresponds to the viscous-plastic flow, in the vicinity of the active part, when the tangent stress exceeds the yield point, and the second one corresponds to the area where the tangent stress does not exceed the yield point, while the second implies a flowing resistance (“solid flow”), when the tangent stress does not exceed the yield point; the soil is an elastic state.
Because the simulation assumes that soil flows while the active part is considered stationary, the soil speed on its surface is zero; speed is also zero in the contact area with the soil bin walls. Moving away from the surface of the active part, the speed increases; as a result, near the active part, the tangent stress records very high levels and the yield point is exceeded, leading to the formation of cracks and to a viscous-plastic strain.
Region | Force due to static pressure (N) | Force due to viscosity (N) | Overall force (N) | ||||||
2 = 600 | 2 = 660 | 2 = 700 | 2 = 600 | 2 = 660 | 2 = 700 | 2 = 600 | 2 = 660 | 2 = 700 | |
Surface of the active part | 86.1 | 95.6 | 102.4 | 415.6 | 520.4 | 642.3 | 501.7 | 616.0 | 744.7 |
Surface of the active part holder | 40.07 | 36.3 | 39.1 | 46.2 | 42.5 | 32.8 | 86.27 | 78.8 | 71.9 |
TOTAL | 126.17 | 131.9 | 141.5 | 461.8 | 562.9 | 675.1 | 587.97 | 694.8 | 816.6 |
Traction force for the winged share type active part
Distribution of the tangential stress (Pa)
The finite elements method (FEM) is used in order to study the bodies with a complex shape, providing numerical solutions for different physical characteristics when analytical solutions are impossible or very difficult to obtain. The finite element analysis (FEA) is used within this method [6].
Soil speed profile (m/s) in the longitudinal vertical plane XOZ (a) and horizontal plane YOZ (b), for 2=660.
The finite elements method is based on the principle of the overall potential energy, which states that a structure or a body is deformed or displaced in a position that minimizes the potential energy (overall potential). This is in correspondence with the second law of thermodynamics, which states that the entropy of an isolated system can only increase towards a maximum value, meaning that the capacity to produce mechanical work can only decrease.
The principle of the minimum potential energy has many applications in the mechanics of the solid bodies and in the analysis of structures. In these cases, the principle of the minimum overall potential is a special case of the principle of virtual mechanical work applied to systems being under the action of conservative forces. The principle of the virtual mechanical work states that the virtual mechanical work of the exterior forces is equal and opposed to the virtual mechanical work of the interior forces (normal stress, shear stress, torsion and bending stress). It is assumed that forces and stresses remain constant and only the variations of strains are taken into account; only the strains that satisfy the internal compatibility of the body and the boundary conditions (resulting from the connections to other bodies) are accepted.
The finite elements method was imposed by the need to solve complex problems regarding the mechanics of deformable bodies. The method may be also applied to the problems referring to the flow of fluids, heat transfer, magnetic fields etc. [16].
The first applications of the finite elements method – FEM – were aimed to simulate the linear elastic materials, but now this method is also used for non-linear, non –elastic materials like soil. Unlike metals, soil has a very low tensile strength; when compressed, the deformation reaches the plastic domain and soil has the tendency to remain in the deformed state. The wheel-soil interaction takes place in the non-linear domain, which means that a greater number of finite elements should be used in the simulation; the computation time increases accordingly.
In agriculture, the 3D simulations of the wheel-soil interaction aim to produce solutions leading to the limitation of soil compaction. A certain number of tests must be performed, with different types of soils and the results of the tests are than used in the numerical simulation in order to obtain a realistic prediction. These results allow the reduction of the design costs and the design time of the agricultural equipment according to the principles of sustainable agriculture.
The 3D numerical simulation based on FEM assumes some simplification hypothesis: the wheel is considered to be under the action of a dynamic vertical load; the wheel is assumed rigid; the number of vertices is limited by the computing power available; the soil characteristics are estimated ones, due to its heterogeneous characteristics.
The model is composed of two distinct 3D elements: a portion of the soil bin and the rigid wheel. In order to diminish the computation time, a vertical plane of symmetry, parallel to the direction of travel, was considered, dividing the contact patch into two symmetrical portions; simulation was therefore performed on only one half of the 3D soil-wheel model. The cartesian reference system was defined as follows (Figure 11): the negative z axis was considered to be along the travel direction, the positive x axis was perpendicular to the soil surface and the y axis was perpendicular to the travel direction and parallel to the wheel axis.
The finite soil elements are 3D solid parallelepipeds, with 8 vertices and only three degrees of freedom, corresponding to the translations along the directions x, y and z. The computation time is thus significantly reduced and the stability of the model is increased.
The 3D wheel-soil model
In order to extend the length and width of the simulation model to infinity, infinite solid elements were attached; they were considered 3D parallelepipeds, with eight vertices and one infinite face. These elements were used for the elastic linear deformation domain and were attached to the boundaries of the solid element.
The strain-stress curve was considered to be composed of linear portions, as shown in Table 5. The physical and mechanical properties of soil were those presented by Block [3]. The density of soil was = 1255.2 kg/m3, the modulus of elasticity was E = 0.3262 MPa and the initial Poisson’s ratio was assumed to be = 0.3.
Yield strength (MPa) | Volumetric strain | Yield strength (MPa) | Volumetric strain |
0 | 0 | 0.08 | 0.149679 |
0.005 | 0.014661 | 0.09 | 0.160028 |
0.01 | 0.028334 | 0.10 | 0.169280 |
0.02 | 0.053024 | 0.12 | 0.185036 |
0.03 | 0.074619 | 0.16 | 0.208422 |
0.04 | 0.093572 | 0.21 | 0.228045 |
0.05 | 0.110262 | 0.29 | 0.248232 |
0.06 | 0.125006 | 0.40 | 0.266976 |
0.07 | 0.138069 | 0.50 | 0.280999 |
The strain/stress curve
The infinite elements use the same material properties; the initial elasticity modulus increases with compaction, due to the increase of the rigidity. The Poisson’s ratio is modified during the simulation. The soil was modeled with ABAQUS/Explicit as “cap plasticity” and optionally as rigid “cap hardening”. These options allow the plastic strain to start from a prescribed level, which is included in the Drucker-Prager rigidity model. Each layer of soil has an initial volumetric strain corresponding to the hydrostatic pressure induced by the weight of the above layers. An initial compaction of the soil was taken into account. The “cap plasticity” option imposes the definition of three supplementary parameters (for the sandy clay soil): the cohesion coefficient c = 350 Pa, the friction angle = 57.80 and the “cap eccentricity” parameter R = 0.0005. The values “cap plasticity” and “cap eccentricity” were evaluated in the process of optimizing the Block model.
The yield strength due to the hydrostatic pressure was limited to values between 0.005 and 0.5 MPa.
Two constraints were defined for the wheel, referring to the acceleration of gravity and wheel rotation.
The interaction between wheel and soil was simulated by the means of two surfaces, corresponding to the cylindrical surface of the wheel and exterior soil surface. Thus, the wheel gradually loaded the soil. No slip was assumed during wheel rolling.
Three locations were chosen for the evaluation of the normal stress. The first one was placed at a depth of 0.3 m under the center of the wheel-soil contact patch, the second one was placed at a depth of 0.3 m under the outer edge of the wheel (y = 0,16 m) and the third one was placed at 0.15 m beneath the center of the contact patch. Table 6 presents the values of the normal stress, after 12 seconds, in the above-mentioned locations.
Wheel load (kN) | Indentation depth (m) | Location | Normal stress (kPa) |
5.8 | 0.101 | 1 | 14.5 |
2 | 7.0 | ||
3 | 17.0 |
Simulation results
The task of tillage is to prepare soils for productive use; it is performed in order to bring the seedlings into the soil and procure for them a good environment for further development. Tillage operations may have negative effects over the physical and mechanical properties of soil, over plant development and agricultural yield.
The experiments were aimed to investigate the effect of soil tillage technologies and soil compaction over the penetration resistance, apparent soil density, weighted average diameter of the soil’s structural elements and water stability of the aggregates.
The experiments were performed on a mezocalcaric cambic chernozem, with a clay-loam texture and eastern exposure.
The experimental field was seeded with the Glosa variety of autumn wheat (approved in Hungary, in 2005); the row spacing was 125 mm, and the seeding depth was 5 cm.
Agricultural equipments and operations | Soil compaction | Experimental variants |
Plowing with T190 + Opal 140 Secondary tillage with U-650 + GD-3,2 Sowing with U-650 + SUP-29 | non-compacted | V1 - control |
compacted once | V2 | |
compacted twice | V3 | |
Plowing with T190 + Opal 140 Secondary tillage with T190 – BS 400 A Sowing with U-650 + SUP-29 | non-compacted | V4 |
compacted once | V5 | |
compacted twice | V6 | |
Direct sowing, in untilled soil, with T190 + MCR-2,5 | non-compacted | V7 |
compacted once | V8 | |
compacted twice | V9 | |
Loosening of the unplough soil (14 cm), seedbed preparation and sowing with T190+OA+AGPS-24DR | non-compacted | V10 |
compacted once | V11 | |
compacted twice | V12 | |
Plowing with T190 + Opal 140 Seedbed preparation and sowing with T190+ AGPS-24DR | non-compacted | V13 |
compacted once | V14 | |
compacted twice | V15 |
Experimental variants
Evaluated soil degradation indices
very low (lower than 1.08 MPa);
low (1.08 – 2.45 MPa);
average (2.45 – 4.9 MPa);
high (4.9 – 9.81 MPa).
A specific penetration resistance lower than 2.45 MPa allows the normal development of plant roots; for values between 2.45 and 9.81 MPa the development of roots is partially limited; for values higher that 9.81 MPa, the roots development is stalled.
In order to evaluate this index untilled soil samples were taken ten days after sowing, from the following depths: 0 – 10 cm, 10 – 20 cm, 20 – 30 cm and 30 – 40 cm.
For the clay-loam soil, the bulk density is ranked as:
extremely low (loosened soil) – under 1.05 g/cm3;
very low (moderately loosened soil) - 1.05 – 1.18 g/cm3;
low (slightly loosened soil) - 1.19 – 1.31 g/cm3;
average (slightly compacted soil) - 1.32 – 1.45 g/cm3;
high (moderately compacted soil) - 1.46 – 1.58 g/cm3;
very high (very compacted soil) – over 1.58 g/cm3.
The weighted average diameter is calculated with the formula:
where pi is the share of each size fraction [%] and di is the mean diameter of each size fraction [mm].
The Tiulin- Erikson method ranks the weighted average diameter as:
very good (WAD = 2 – 5 mm);
good (WAD = 1 -2 mm and 5 – 7 mm);
acceptable (WAD = 0.25 – 1 and 7 – 10 mm);
poor (WAD under 0.25 and over 10 mm).
The aggregates retained on each sieve are weighted and the I1 water stability index is calculated with the formula:
where I is the percent of aggregates bigger than 5 mm, II is the percent of aggregates of 3 – 5 mm, III is the percent of aggregates of 2 – 3 mm, IV is the percent of aggregates with 1 – 2 mm and V is the percent of aggregates of 0.5 - 1 mm. According to I1, the water stability of aggregates is ranked as follows:
3.00 – 5.00 – very good structure;
0.61 – 3.00 – good structure;
0.30 – 0.61 – medium structure;
0.18 – 0.30 – poor structure;
lower than 0.18 – bad structure.
The experiments were aimed to investigate the effect of soil tillage technologies and soil compaction on the penetration resistance, apparent soil density, weighted average diameter of the soil’s structural elements and water stability of the aggregates.
The results show very low values of the penetration resistance (0.438); according to the agro technical requirements, values lower than 1.08 MPa are considered “very low” and roots may develop normally.
Based on the penetration resistance, the five variants referring to the non-compacted soil were ranked as follows: V13 (the best), V4, V1, V10 and V7 (the worst). Because soil was not compacted, these values were considered as reference in order to establish the effect of the tillage equipments.
Compaction | Penetration resistance [MPa] | ||||
Non-compacted | V1 | V4 | V7 | V10 | V13 |
0.247 | 0.236 | 0.286 | 0.260 | 0.215 | |
Compacted once | V2 | V5 | V8 | V11 | V14, |
0.326 | 0.315 | 0.356 | 0.347 | 0.306 | |
Compacted twice | V3 | V6 | V9 | V12 | V15 |
0.406 | 0.390 | 0.438 | 0.410 | 0.387 |
The effect of the tillage technologies over the resistance to penetration
The experimental data show that the compaction of the soil (once and respectively twice) has significantly increased the penetration resistance.
The lowest values of the penetration resistance were recorded for the variants V13 (non-compacted soil), V14 (compacted once) and V15 (compacted twice), when plowing was performed with the T190 + Opal 140 unit and the seedbed preparation and sowing were performed with the T190+ AGPS-24DR equipment.
Low values of the penetration resistance were also recorded for the variants V4 (non-compacted), V5 (compacted once) and V6 (compacted twice), when the same equipment was used for plowing (T190 + Opal 140) and the BS 400 combined equipment was used for seedbed preparation.
The increase of the penetration resistance (compared to variants V13, V14 and V15) was due to the presence of cage rollers and cross kill roller (mounted in the back of the equipment).
For the following variants (V10, V11 and V12), classical plowing was replaced by a tillage operation performed with the OA + AGPS-24DR complex equipment; the soil was loosened over a depth of 15 cm by the OA winged type shares, mounted in front of the rotary harrow. As a result, the penetration resistance increased significantly.
Strip tillage was performed for the variants V7, V8 and V9, by the means of the MCR 2.5 combined equipment; in this case, isolated bands of soil were tilled (only one third of the equipment’s working width), to a depth of 8 cm. This solution led to the higher values of the penetration resistance.
Compaction | Bulk density [g/cm3] | ||||
Non-compacted | V1 | V4 | V7 | V10 | V13 |
1.31 | 1.28 | 1.33 | 1.32 | 1.26 | |
Compacted once | V2 | V5 | V8 | V11 | V14, |
1.42 | 1.40 | 1.45 | 1.43 | 1.39 | |
Compacted twice | V3 | V6 | V9 | V12 | V15 |
1.51 | 1.49 | 1.58 | 1.54 | 1.46 |
Effect of tillage technologies over the bulk density of soil
For variants V13, V4 and V1 (non-compacted soil) the bulk density was low (poorly loosened soil), while average values were recorded for variants V10 and V7 (slightly compacted soil). Average values were also recorded for all the “compacted once” variants (slightly compacted soil); the high values of the bulk density reported for the “compacted twice” variants ranked them as “moderately compacted”.
Taking into account that lower values of the bulk density are desirable, the “non-compacted” variants were ranked as follows: V13 (the best), V4, V1, V10 and V7 (the worst).
The experimental results showed that bulk density increases when soil compaction increases. The “compacted once” and “compacted twice” variants were ranked exactly in the same order as the “non-compacted” variants, in terms of bulk density, because their ranking is only due to the type of tillage equipment. Moreover, the same ranking was recorded in terms of penetration resistance, because the both indices are characterizing the compaction state of soil and the increase of one index implies the increase of the other one, too.
Compaction | Weighted average diameter [mm] | ||||
Non-compacted | V1 | V4 | V7 | V10 | V13 |
3,70 | 3,68 | 3,56 | 3,40 | 3,35 | |
Compacted once | V2 | V5 | V8 | V11 | V14, |
3,05 | 3,09 | 3,34 | 3,20 | 3,19 | |
Compacted twice | V3 | V6 | V9 | V12 | V15 |
2,84 | 2,88 | 3,29 | 2,97 | 2,90 |
Effect of tillage technologies over the weighted average diameter.
WAD varied between narrow limits – 2.845 mm to 3.702 mm. The results include the weighted average diameter in the 2 – 5 mm class (very good), for all the variants. Within this class, the best weighted average diameter is the one that is closest to 3.5 mm.
According to this index, the “non-compacted” variants were ranked as follows: V7 (the best), V10, V13, V4 and V1 (the worst).
The “compacted once” and “compacted twice” variants were ranked exactly in the same order as the “non-compacted” variants, in terms of weighted average diameter, due to the facts previously mentioned.
Increasing the compaction of soil resulted in a marked destruction process, the weighted average diameter being diminished.
Variant V7 was ranked the first due to the limited tillage process, during which the soil aggregates were less affected; when using the MCR-2.5 equipment, only isolated bands of soil were tilled (on one third of the equipment’s working width), to a lower depth of 8 cm and thus the structural elements are preserved.
Variant V10 was ranked second because soil plowing was replaced by loosening to a depth of 15 cm. The fact that seedbed preparation and sowing were performed simultaneously also contributed to the preservation of the soil’s structure. In the same time, the more intense tillage (performed by the OA winged type shares and the rotary harrow) applied within this variant led to lower weighted average diameters of the aggregates.
In the case of variant V13, which was ranked the third, classic moldboard plowing led to the destruction of the structure elements; seedbed preparation by the means of the FRB-3 rotary harrow (part of the AGPS-24DR complex equipment) also contributed to the diminishing of the aggregates’ diameter.
Variant V4 was ranked the fourth due to conventional plowing, followed by the secondary tillage performed with the BS 400A combined equipment. The great number of tillage equipments within its structure, of which three are rollers, had an unfavorable effect over the soil structure.
Compaction | I1 index | ||||
Non-compacted | V1 | V4 | V7 | V10 | V13 |
3.60 | 3.61 | 4.18 | 3.70 | 3.68 | |
Compacted once | V2 | V5 | V8 | V11 | V14, |
2.84 | 2.96 | 3.43 | 3.18 | 3.02 | |
Compacted twice | V3 | V6 | V9 | V12 | V15 |
2.64 | 2.68 | 2.93 | 2.77 | 2.78 |
Effect of tillage technologies over the water stability of aggregates (I1 index)
The values of the I1 index were comprised between 2.64 and 4.18, which means that two classes were included: very good structure (3.00 – 5.00) and good structure (0.61 – 3.00). The higher the I1 index, the better the soil structure. Within the 3.00 – 5.00 class, the best soil structure is the one that is closest to 4.00.
For the “non-compacted” variants, their ranking was as follows: V7 (first place), V10, V13, V4 and V1 (last place).
The “compacted once” and “compacted twice” variants were ranked exactly in the same order as the “non-compacted” variants in terms of weighted average diameter, due to the previously mentioned facts regarding soil compaction.
The ranking of the variants respected the same order as in the case of the weighted average diameter.
It should be mentioned that an increased soil compaction results in a lower I1 index; this tendency becomes more important when passing from the “non-compacted” variants to the “compacted once” variants.
The experimental variants are the ones already presented in the discussion referring to the effect of soil tillage and compaction over the physical and mechanical properties of soil.
The results regarding the seed yield are presented in table 12, being the averaged values for three agricultural years.
The experimental variants on the first five places (“non-compacted” soil) are ranked as follows: V10 (best), V7, V13, V4 and V1 (5th place).
The next five places belong to the “compacted once” variants, in the following order: V11 (6th place), V8, V14, V5 and V2 (10th place).
The last five places were taken by the “compacted twice” variants: V12 (11th place), V9, V15, V6 and V3 (15th place).
As far as the tillage and sowing technology are concerned, the order is similar for the “non-compacted”, “compacted once” and “compacted twice” variants, as only the type of tillage and sowing equipment affected ranking.
It should be noticed that yield decreases when soil compaction increases; this tendency is more significant when passing from the “non-compacted” variants to the “compacted once” variants.
Tillage and sowing equipments | Compaction | Experimental variants | Seed yield, kg/ha |
Valtra T190 + Opal 140; U-650 + GD-3,2; U-650 + SUP-29 | non-compacted | V1 - witness | 5765 |
compacted once | V2 | 4453 | |
compacted twice | V3 | 4025 | |
Valtra T190 + Opal 140; Valtra T190 + BS 400 A; U-650 + SUP-29 | non-compacted | V4 | 5800 |
compacted once | V5 | 4518 | |
compacted twice | V6 | 4104 | |
Valtra T190 + MCR-2,5 | non-compacted | V7 | 6016 |
compacted once | V8 | 4789 | |
compacted twice | V9 | 4258 | |
Valtra T190 + OA + AGPS-24DR | non-compacted | V10 | 6268 |
compacted once | V11 | 5461 | |
compacted twice | V12 | 4297 | |
Valtra T190 + Opal 140 Valtra T190 + AGPS-24DR | non-compacted | V13 | 5834 |
compacted once | V14 | 4557 | |
compacted twice | V15 | 4182 |
. Seed yield for the autumn wheat crop
Soil has an essential part in maintaining life on earth because it represents the support for the agriculture practice, creating the necessary conditions for obtaining the food products, due to its physical and biological properties, to its fertility, to its capacity to provide plants with the water and nutrients needed for their growth.
The intensification of the agricultural processes - mechanization, fertilization - led to a continuous degradation of soil, affecting five to seven million hectares each year. Sustainable agriculture could be a solution to this problem.
Sustainable agriculture is based on the soil conservation tillage system (SCTS). Within the unconventional soil tillage system moldboard plowing is deferred (completely or partially), the tillage works are limited and at least 15...30% of the vegetable debris is kept on the soil surface. The unconventional soil tillage system consists of very different methods: seeding in the untilled soil, reduced soil tillage, minimum soil tillage (when up to 30% of the vegetable debris is left on the soil surface), minimum tillage with vegetable mulch (more than 30% of the vegetable debris is left on the soil surface), ridge seeding, partial or strip tillage, deep loosening without furrow overturning etc.
The intensity of the anthropic soil compaction is affected by the type of agricultural machinery; compaction is promoted by the use of heavy machinery, with high wheel-soil contact pressures, by the increased number of passings, by the increased tire air pressure, by the agricultural traffic performed over wet soil. As far as the active parts for seedbed preparation are concerned, their destructive action over the structure elements of soil is of an utmost importance. The structure elements are destroyed through deformation, breaking, fragmentation, and cutting; in order to preserve soil structure one should comply with the technical recommendations of the equipment’s manufacturer regarding the working speed and peripheral speed of the active parts.
In order to reproduce, in laboratory conditions, the working process of the active parts of the tillage equipment, a test rig was designed and built. The rig was used in order to study the soil - moldboard plough body interaction and the tire wheel-soil interaction; the results were then used to simulate the respective processes. The mathematical and physical simulations were performed by the means of CFD method. It was concluded that, in the case of the winged share type of active part, the maximum pressure would be recorded on the cutting edges. Based on the results of the simulations and on further field tests, new types of active parts will be developed; within the frame of conservative agriculture, this method allows the reduction of the time needed to produce new types of active parts.
The results of the mathematical and physical simulation were focused on soil, aiming to evaluate the compaction depth, the wheel indentation depth and the normal soil stress. The dynamic 3D simulation of a wheel rolling over an isotropic and non-linear soil produced truthful results regarding soil deformation and stresses at different depths, emphasizing the remanent soil stresses which lead to soil compaction and to the deterioration of its structure.
The laboratory results were validated by the field experiments, in which the effects of different agricultural equipments and of soil compaction over the penetration resistance, soil structure and yield were investigated.
Based on the results regarding the penetration resistance and bulk density, the variants (as presented in Table 7) were ranked as follows: V13 (1st place), V4 (2nd place) and V1-witness (3rd place).
The analysis of the weighted average diameter and water stability of the aggregates led to the following rating: V7 (1st place), V10 (2nd place) and V13 (3rd place).
The analysis of the seed yield led to the following rating: V10 (1st place), V7 (2nd place) and V13 (3rd place).
When the indices referring to soil structure were considered, the best results were obtained by the variant V7 (non compacted soil; tillage and sowing performed with the T190 + MCR-2.5 equipment); the second place was taken by variant V10 (non-compacted soil; tillage and sowing performed with the T190 + OA + AGPS-24DR equipment); variant V13 (plowing performed with the T190 + Opal 140 equipment, sowing performed with the T190 + AGPS-24DR equipment) was ranked the third.
Taking into account all the facts we consider that all decision makers, who are connected in anyway with soil (farmers, equipment producers, chemical products manufacturers, researchers), should be focused on the degradation of the arable layer and encourage agricultural technologies aiming to its preservation.
Surfactants are surface-active agents that reduce water–oil, liquid–gas, and solid–liquid or solid–gas medium surfaces and interfacial tension [1, 2]. The surface energy is reduced by the presence of hydrophilic and hydrophobic sections of the same surfactant molecule owing to preferred interactions at surfaces and interfaces. In aqueous solution, surfactant molecules arrange themselves at the interface, where the hydrophobic part is in the air (or oil) and the hydrophilic part is in water, while at high concentration or concentrations above the critical micelle concentration (CMC), surfactant molecules self-assemble into micelles (Figure 1). Not only are they widely used as cleaning agents, but also other beneficial properties, such as foaming, emulsification, and particle suspension, make surfactants known for their wetting ability and effectiveness such as emulsifiers and stabilizers. Due to this characteristic, surfactants are found in a variety of products that we use every day, including food, pharmaceuticals, toiletries, detergents, automotive fluids, paints, and coatings [2]. Surfactants have steadily grown in popularity since their debut in the early twentieth century, and they are now among the most widely used synthetic compounds on the planet [3, 4].
(a) Simplified surfactant molecule, (b) arrangement of surfactant monomers at the water surface, and (c) micelle formation above critical micelle concentration (CMC).
Petrochemical and renewable sources are the two primary feedstock groups used in the manufacture of surfactants [5, 6]. The development of petrochemical processing led to the acquisition of hydrophobic structures of surfactant molecules through polymerization of alkenes, such as ethylene or propylene. Although ethylene has been employed as a carbon chain-building block, its increased applicability in industrial production has resulted from the production of an intermediate or precursor, ethylene oxide [7]. Natural surfactants are usually derived from triglycerides found in vegetable oils or animal fats. The surfactant industry was focused on the saponification of oils and fats prior to petrochemical processing [8, 9]. Surfactants infiltrate water bodies after usage, where they can create issues if they remain for a long time, resulting in the buildup of potentially toxic or otherwise hazardous substances causing significant environmental concerns [10, 11, 12]. Synthetic surfactant-related water contamination has increased in recent years because of its widespread usage in domestic, agricultural, and other cleaning activities. This occurrence has caused global concern, forcing establishment of a series of new rules governing its usage and disposal [13, 14]. In addition, experts relate the production of petrochemical-based surfactants to the high net output of CO2, a greenhouse gas linked to climate change and global warming. By switching to renewable feedstock, this rate can be minimized. A previous study shows that using renewable resources instead of petrochemicals for surfactant synthesis would cut CO2 emissions by 37% in the EU [15]. Beside environmental concerns and regulations, growing consumer awareness and market pressures have prompted considerable R&D into bio-based surfactants as potential substitutes for synthetic surfactants.
The term “bio-based surfactant” refers to a surfactant produced by a chemical or enzymatic process that uses renewable substrates as raw materials [16, 17]. According to ISO/DIS 21680, a bio-based surfactant is defined as a surfactant wholly or partly derived from biomass (based on biogenic carbon) [18]. Most applications need further processing of bio-based feedstocks to incorporate functional groups that can give the surfactant’s functional characteristics, resulting in a variety of anionic, cationic, nonionic, and amphoteric products. Many of these processes require the use of petroleum-based feedstocks or moieties that are not always environmentally friendly. The European Commission of Standardization has created categories for biosurfactants, including >95% completely bio-based, 50–94% majority bio-based, 5–49% minority bio-based, and 5% non-bio-based to assist in analyzing the bio-based surfactants’ sustainability criteria (Table 1) [19].
Surfactant class | Bio-based carbon content X% ( |
---|---|
Wholly bio-based surfactant | ≥95 |
Majority bio-based surfactant | 95 ≥ X > 50 |
Minority bio-based surfactant | 50 ≥ X ≥ 5 |
Non-bio-based surfactant | X < 5 |
Bio-based surfactant classes according to CEN/TS 17035 [19].
The hydrophobe, hydrophile, or both, which are derived from natural sources, can be used in the production of bio-based surfactants. Plant oil, fatty acids, and animal fat are examples of natural hydrophobes, while glycerol, glucose, sucrose, and amino acids (aspartame, glutamic, lysine, arginine, alanine, and protein hydrolysates) are examples of natural hydrophiles. They can be either directly utilized in their original form or produced from complicated sources, such as vegetable oil, sugarcane, sugar beets, and starch-producing crops. As for biosurfactants, they consist of hydrophilic sugar or peptide component and hydrophobic saturated or unsaturated fatty acid chains that are naturally produced by bacteria, yeast, and fungi. Hence, a biosurfactant is classified as a wholly bio-based surfactant since all its raw materials are considered natural [20, 21, 22].
The hydrophobic part of bio-based and biosurfactant feedstock is mostly from fatty acyl groups. The fatty acyl groups are generally obtained from oilseeds in the form of triacylglycerol, but they may also be derived from oleochemical by-products such as free fatty acid or phospholipids. Fatty acyl groups are generally utilized as lipophilic building blocks for surfactants in the form of free fatty acids or fatty acyl esters, which are produced
Algae are another potential renewable source of fatty acids. It has been an active research area in recent years due to its potential for high oil production per acre and the ability to leverage on nonarable soil [28, 29, 30]. Previously, Unilever has partnered with Solazyme, a microalgae firm, with the aim of finding a palm-oil-free replacement for its soaps and surfactants. Solazyme used the advantage of its intellectual property in the areas of recombinant DNA expression in algae and algae bioprocessing to create oils with specific fatty acyl compositions [31]. Solazyme, later renamed as TerraVia, was acquired by Carbion in 2017 to focus on delivering innovative and high-value ingredients for food, personal care, and industrial applications [32]. Lignin has also been used as a feedstock in surfactant production due to its hydrophobic aromatic structure. Lignin-based surfactants are usually made by grafting hydrophilic groups or monomers onto the lignin to enhance its surface properties [33, 34, 35]. Extensive investigations are necessary to expedite the commercialization of lignin-based surfactants to the market since information on connecting performance and characteristics of lignin-based surfactants for their optimal usage is still lacking.
Among the most significant feedstocks for renewable hydrophile sources are vegetable oils (for glycerol), sugarcane and sugar beets (for sucrose), and starch-producing crops, such as maize, wheat, potato, and tapioca (for glucose) [4, 23, 36]. The use of glycerol as an alternative hydrophilic building block to replace ethylene oxide in the synthesis of nonionic surfactants is a feasible option. The major glycerol-based surfactants in the market are ester-based mono- and diglycerides, which are made by transesterifying triglycerides with excess glycerol and a base catalyst [4, 26, 37]. Carbohydrates, such as sugar and sucrose, are another useful biorefinery feedstock that make up as surfactant hydrophiles. The discovery of sucrose monoesters, or long-chain fatty acid esters, was one of the first major achievements of the Sugar Research Foundation (SRF) and led to their use as nonionic surfactants, food additives, and emulsifiers [38]. The global sucrose esters market amounted to $71.9 M in 2018 and is expected to reach $137.85 M by 2027 [39]. However, selectivity in the synthesis of these esters remains a challenge where acylation with a single fatty acid can yield many different isomers with various degrees of substitution [40]. One of the solutions to tackle the selectivity problem is by using lipases and proteases for regioselective sucrose ester production [41, 42]. Further improvement
Glucose is utilized as a hydrophile in the manufacture of a variety of surfactants, both directly and indirectly. It can react directly with fatty alcohol in a glycosidation process to produce alkyl polyglucosides (APGs), a nonionic surfactant class with growing production and popularity. Indirectly, glucose may be chemically converted to sorbitol, sorbitan, N-methyl glucamine, and O-methylglucoside, or enzymatically converted to amino, lactic, and citric acids, all of which can be leveraged to produce surfactants (Figure 2) [4].
Simplified transformations pathway from glucose to several surfactant building blocks and surfactants.
Sugar-derived surfactants have a higher market demand than synthetic chemicals and surfactants due to their low toxicity, low cost, biodegradability, good cleaning and washing abilities, environmental compatibility, and high surface activity [43, 44]. However, if the demand for sugar surfactants grows in the long run, feedstock availability will become a concern. New methods that use bacteria and microorganisms to manufacture glucose are emerging; however, the issue of scalability has yet to be solved.
The creation of new amino acid-based surfactants may be influenced by advancements in biotechnological amino acid synthesis. Other than L-glutamic acid and L-lysine, which are the two most produced amino acids in the market, alanine, aspartic acid, glycine, and arginine, as well as protein hydrolysates, are also used in the manufacture of some commercial surfactants [45, 46, 47]. Another type of amino acid surfactant, sarcosine-based surfactants, has been in the market for decades. Even though sarcosine is a naturally occurring molecule, it is mostly synthesized on a large scale by combining chloroacetic acid with N-methylamine [48, 49, 50]. Betaine, another naturally occurring molecule, is also synthesized in large scale using petrochemical-based trimethylamine and chloroacetic acid. Most betaine surfactants use an oleochemical hydrophobe precursor obtained from tropical oils as the bio-based component [51]. Glycine betaine is a promising biosurfactant that can be commercially extracted from brown algae and sugar beet molasses [52, 53].
Glycolipids are a type of complex carbohydrate that contains both a glycan and a lipid component. They are usually the main lipids of bacterial and fungal cell walls. In an aqueous solution, glycolipids are amphiphilic substances that form stable micelles, and these molecules have the capacity to offer low interfacial tension [54, 55]. Rhamnolipids and sophorolipids are among the glycolipids that have been utilized the most as biosurfactants. Rhamnolipids are produced as one or two rhamnose sugar groups attached to one or two fatty acid chains by different bacterial species (i.e.,
Regulations on the environmental impact and hazardous chemicals are highly stringent, particularly in Europe and North America, which are the two largest markets for surfactants, especially in the home and personal care sectors. As a result, the surfactant industry is commencing to develop biosurfactants, which have lower levels of toxicity and a more environmentally friendly manufacturing process. Apart from complying with environmental regulations, the industry is seeing bio-based surfactants to achieve a sustainable competitive edge. The advent of biotechnology in the twenty-first century promoted the creation of novel bio-based and biosurfactants along with their enhanced commercial and economic viability. Extensive and significant R&D has also enabled high-quality and high-functionality bio-based surfactant formulations to evolve from the lab scale to niche applications to commercial-scale production. Some of the bio-based surfactants that are commercially available in the market, their main manufacturers, and their applications are listed in Table 2.
Bio-based surfactants | Selected manufacturers | Fields of applications |
---|---|---|
Anionic | ||
Lignosulfonate Methyl ester sulfonates Anionic derivatives of alkyl polyglucoside | Vanderbilt Minerals, LLC Huish Detergents, Inc., Lion Corp., Longkey, Stepan Cognis, Colonial Chemical |
|
Nonionic | ||
Fatty alcohol alkoxylate Fatty acid alkoxylate Alkyl polyglucoside Sorbitan ester Alkanoyl- Alkyl ethoxylated mono- and diglycerides Polyglycerol esters | BASF, Dow BASF, Clariant, Croda, Croda, Esterchem, Huntsman Akzo Nobel, BASF, Colonial Chemical, Dow, Huntsman BASF, Croda, Huntsman Clariant, Kao, Kerry Ingredients and Flavors BASF, Colonial Chemical, Hychem Corp., Kerry Ingredients and Flavors |
|
Amphoteric | ||
Cocoamidopropyl betaine Cocoamidopropyl hydroxysultaine Lauryl hydroxysultaine | BASF, Colonial Chemical, Stepan Colonial Chemical, Stepan Colonial Chemical, Stepan |
|
Glycolipid | ||
Sophorolipid Rhamnolipid | BASF, Clariant, Ecover, Evonik, MG Intobio Co. Ltd., Saraya Co. Ltd., Soliance AGAE Technologies, BASF, Biotensidon GmbH, Clariant, Evonik, GlycoSurf, Henkel, Jeneil Biotech Inc., Logos Technology Rhamnolipid Companies Inc., TeeGene Biotech |
|
Amino acid surfactants | ||
Sodium cocoyl glutamate Sodium methyl cocoyl taurate α-Acyl glutamate and sarcosinate | Ajinomoto Co. Inc., Stepan, Zschimmer and Schwarz Clariant Schill+Seilacher |
|
Commercially available bio-based surfactants, their manufacturers, and their applications.
In the current development of novel surfactants, there is a growing trend of utilizing nontraditional naturally occurring branching hydrophobic chains [61, 62, 63]. Nonionic surfactants based on twin tail glycerol have been synthesized and they have good oil-in-water and water-in-oil emulsifying characteristics [64]. Other structural analogs of glycerol-based surfactants have recently been created by employing heterogeneous interfacial acidic catalysts to directly etherify glycerol and dodecanol. These surfactants have been shown to be comparable with commercially available surfactants in terms of physicochemical assessment and detergency ability [37]. Another class of amphiphilic compounds with a glycerol backbone is bio-based dialkyl glycerol ethers. These compounds have good solvo-surfactant characteristics and can function as solubilizers for hydrophobic dyes in aqueous media [65].
Natural edible flavor vanillin is used to create a cleavable vanillin-based polyoxyethylene nonionic surfactant. Because it contains cleavable acetal bonds that break down quickly under acidic circumstances, this environmentally beneficial surfactant is totally biodegradable in nature. The surfactant’s surface activity, wettability, and emulsifying and foaming properties are on par with nonylphenol ethoxylate surfactants, which are highly toxic to aquatic organisms and environment [66]. Several novel types of sustainable surfactant have been created in recent years by employing various types of terpenes, which are the major components of essential oils derived from a variety of plants and flowers [67, 68, 69, 70]. The terpenes were transformed to branched hydrophobic tail containing quaternary ammonium surfactants. Natural farnesol, a 15-carbon acyclic sesquiterpene alcohol found in neroli, lemongrass, tuberose, rose, citronella, and other plant species, was used to create a new form of terpene-based sustainable surfactant, which has demonstrated excellent surfactant performance [70]. Under the trade name ECOSURF, Dow Chemical Co. is now offering a range of sustainable oilseed-based nonionic surfactants. These surfactants are claimed to have minimal aquatic toxicity and are biodegradable in nature, making them suitable candidates for paints and coatings, as well as home, industrial, and institutional cleansers and textiles [71].
TegraSurf, a range of sustainable water-based surfactants developed for energy, mining, agricultural, water treatment, and other industrial applications, was released in July 2021 by Integrity BioChem (IBC), a technology-driven business producing next-generation biopolymers. TegraSurf is made of sustainable vegetal materials and is certified Readily Biodegradable by the OECD 301B guideline. After 90 days, it is no longer present in the environment, making it safer and healthier for local populations and allowing formulators to fulfill industry sustainability criteria [72]. BASF and Solazyme Inc. recently released Dehyton® AO 45, the first commercial microalgae-derived betaine surfactant made from microalgae oils as an alternative to conventional amidopropyl betaine surfactants [73]. Following the launch of sophorolipid-based surfactants in 2020, BASF formed an exclusive partnership with Holiferm Ltd. in the United Kingdom to focus on the development of glycolipids other than sophorolipids for personal and home care as well as for industrial uses [74].
Croda expanded its commercial-scale bio-based manufacturing capabilities and technology leadership in renewable raw materials by unveiling its 100% bio-based ethylene oxide production facility as an effort to make the world’s products greener. Ethylene oxide is the key raw material used to produce surfactants. Croda’s Atlas Point manufacturing plant in New Castle, Delaware, is the first of its type in the United States for the manufacture of 100% sustainable, 100% bio-based nonionic surfactants [75]. Ajinomoto is increasing to 60% of its global capacity for its Amisoft range of amino acid-based liquid surfactants by building a new plant in Brazil [76]. Sironix Renewables received $645,000 in investment from the University of Minnesota Discovery Capital Investment program and investors as well as a $1.15 million grant from the US Department of Energy Advanced Manufacturing Office, to help them scale up their Eosix® production. The new renewable oleo-furans-based surfactants are 100% plant-based that offer unique and adjustable characteristics in a wide range of areas, including cleaning products, cleaners, cosmetics and personal care, agriculture and inks, and paint and coatings [77].
This section covers the market performance, demand drivers, and growth prospects of biosurfactants. The market trend on bio-based and biosurfactants is discussed for the different geographic regions and in terms of changing market trends for biosurfactants in various application areas. Analysis of the industrial challenges of biosurfactants, which include the growth-restraining factors and future opportunities, is provided.
The worldwide surfactant industry, estimated to be worth $39 billion in 2019, is expected to expand at a rate of 2.6% per year over the following five years, reaching $46 billion in 2024. Surfactants are produced in total of 17 million metric tons per year [78]. In the EU, of the 3 million metric tons of surfactants produced in 2019, roughly 50% were bio-based [79]. A market study by Market Research Future [80] indicated that the global biosurfactants’ market value is around USD 2.1 billion in 2020 and predicted it to reach USD 2.8 billion by 2026, with a compound annual growth rate of over 5% from 2021 to 2026. The attractive performance of biosurfactants advances their high potential to substitute synthetic-based surfactants for drop-in applications and with unique properties that can overcome entry barriers for the emerging industrial areas. Major types of biosurfactants, such as sophorolipids, glycolipids, lipopeptides, polymeric biosurfactants, phospholipids and fatty acids, generally form the product demand application. Among biosurfactants, sophorolipids provide the largest global market demand with detergents and industrial cleaning applications. The leading demand drivers for biosurfactants comprise a growing consumer preference, increasingly stringent regulatory requirements, and rising awareness toward eco-friendly alternatives. By being environmentally compatible and with low toxicity, many studies have considered biosurfactants as the next generation of industrial surfactants [81, 82, 83]. In terms of end-user applications, biosurfactants are finding usage in household detergents, industrial and institutional cleaners, cosmetics, and personal care within the major markets in Europe and North America [80]. Recently, they have been gaining acceptance in the newer application areas such as in oil and gas as well as in agricultural industries.
Furthermore, the increasing consumer awareness of the benefits of biosurfactants and their wide range of application sectors form market drivers that increase their future growth potential. Higher growth of biosurfactants is seen in Asia-Pacific (APAC), especially in Southeast Asian countries that have slightly different demand factors that involve the increasing purchasing power of mass consumers, growing concern on environmental issues, and the generation of harmful chemical by-products. In terms of APAC market segmentation, the major sales revenue for biosurfactants resides within the home care and personal care applications, as rising urbanization becomes the dominant factor for surfactant growth. More importantly, a key growth enabler is in the innovative research on biosurfactants, especially when it can generate multifunctional and diversified products using renewable feedstock. This technological progress contributes to the desirable properties of biosurfactants to meet the changing consumer lifestyles in developing economies and consequently their increasing preference for usage in the end-user product formulation. As an example, within the home care detergent industry, the usage of biosurfactants as environmentally friendly products provides sustainable alternatives that are gaining a large market share [81, 84, 85].
The highest adoption of bio-based and biosurfactants is in Europe and North America, which dominate bio-based surfactant market share in terms of revenue and volume. Increasingly stringent regulatory requirements enable a wider acceptance of biosurfactants in the place of synthetic surfactants. For example, the imposed government regulations, such as CEN/TC-276, define the standards for surface-active agents and detergents to enhance the EU bio-based economy, detergent regulation (EC) No 648 that require surfactants used in detergents to be biodegradable under aerobic conditions as per OECD 301 test series. In addition, the COVID-19 pandemic results in a sharp increase in the bio-based surfactant product demand for household detergents, personal care, and industrial cleaners due to the rising trend for sanitation.
Bio-based surfactants are synthesized
A second challenge is the dependency of biosurfactant demand on the volatility and economic downturn of downstream end-user industries. Industries that are applicable for biosurfactant applications, such as oil and gas, enhanced oil recovery, food industry, construction, textiles, paints, pharmaceutical, and detergents, are known to be susceptible to general macroeconomic performance. In addition, the COVID-19 pandemic further leads to disruption in the end-user industrial demand and sustainability concern on the raw material supply. The sustainability of raw materials is a major concern as these contribute up to 50% of the glycolipid production cost and 10–30% of the overall cost for other biosurfactant products. Purification accounts for 60% of the production cost, but this can be minimized for the case of biosurfactant application in crude forms, such as in an industrial environment [88]. However, for high-purity applications, improvement in downstream processing methods is needed to attain a competitive cost of production. Opportunity exists in developing a new technology solution that utilizes a low-cost raw material such as industrial wastes for biosurfactant production. However, this needs to consider the overall production impact factors that include the availability, stability, and variability of each component [88]. The economic viability criteria for biosurfactant production, therefore, include microorganism performance, bioreactor design, target market, purification process, product properties, production condition, fermentation cycle time, and production yield [89].
Additionally, several operation and control factors provide important handles to minimize biosurfactant production costs. Batch cycle optimization on the fermentation and purification process can reduce the idle time between batches and minimize chemical usage for equipment cleaning and energy use during sterilization. Productivity is the most important factor in the manufacturing economics of biosurfactant production at commercial scales [8]. Optimum batch-sequencing campaign minimizes startup and shutdown frequency to lower the production downtime that improves productivity. Lastly, biosurfactant product development will need to fulfill time-consuming and expensive legislative requirements, which restrain market growth [90]. These add a high cost of compliance to the product development cost that is incurred by biosurfactant manufacturers. Other market entry requirements include the biosurfactant products that are tested for long shelf life and the ability to maintain stable properties in the industrial environment [91].
The development of bio-based surfactants from renewable feedstocks is an attractive alternative to fossil-based surfactants with a significantly growing market attributed to their performance, biodegradability, biocompatibility, and nontoxicity [22, 33]. Additionally, advances in renewable technology, increased environmental concern, consumer awareness, and stringent regulatory requirements provide a continued push toward the demand of bio-based surfactants. Potential areas for use are growing fast, and valuable outcomes depend on whether the bio-based surfactants can be customized for specific applications along with if they can be produced at a price that will make them attractive alternatives to the fossil-based surfactants. The simultaneous design of bio-based surfactants for functional, economic, and environmental benefits will be taxing, but it will ensure the replacement of conventional fossil-based surfactants provided they can offer comparable or superior performance and a unique value proposition.
Presently, fossil-based surfactants are less expensive than bio-based surfactants [4, 92, 93]. However, this trend will likely change in the future, thereby increasing the prospects of bio-based surfactants. Feedstocks and how the bio-based surfactants are produced are the two key factors governing final product costs [4, 36, 94, 95]. To use renewable feedstock in the industry, they should be cost-effective, available in large quantities, and can effectively be converted to value-added surfactants [95]. Renewable feedstocks used as starting materials to produce surfactants usually face severe economic competition from their fossil-based counterparts. Surfactants comprised of hydrophilic head group and hydrophobic tail group, which are linked by a chemical bond generating an amphiphilic molecule that can be used directly or further modified. Surfactant design requires careful selection of the hydrophile and hydrophobe pair so that they can be easily synthesized with minimum purification and provide the desired properties for the intended application [4, 16, 92, 96]. Triglycerides, fatty acid methyl esters, fatty alcohols, fatty acids, and fatty amines are common examples of renewable hydrophobes used to produce bio-based surfactants. Sustainable hydrophilic headgroups can be designed using several molecules such as glycerol, carbohydrate feedstocks such as sucrose, glucose, organic acids, and amino acids [4, 36, 94, 95]. Additionally, the use of renewable feedstock for surfactant manufacturing also helps reduce CO2 emissions because once the bio-based surfactants degrade, they only release back the quantitative amount of the carbon used by the plant to produce the surfactants [36]. Other than the starting material mentioned above, the use of alternative substrates, such as agro-based industrial wastes or other suitable simple waste substrate, is gaining a lot of research interest and can lead to significant cost reduction [97].
Researchers are continually improving the cost-effectiveness of production methods as well as enhancing the current technologies with green manufacturing principles to convert renewable feedstocks into valuable and new biobased surfactants. Some of the key focus areas include developing biobased surfactants from cheaper feedstocks, higher performance catalysts, green solvents, optimized reaction processes, and effective downstream purification could entice the industry players and end-use customers to make the switch from fossil-based surfactants to biobased surfactants. Catalyst design is also crucial to ensure high selectivity of the processes to limit or eliminate the formation of by-products and to help push the reaction forward towards completion faster [98, 99, 100]. Other than that, researchers are looking into equipment miniaturization such as continuous reactors to help reduce the raw material consumption and effluent production. Process intensification is another aspect that could help to reduce the investment costs [99]. Research focusing on alternative or green solvents dedicated to the conversion of renewable feedstock to value-added products has led to several publications. Among those being researched include bio-based ionic liquids, deep eutectic solvents, bio-based solvents, CO2-switchable solvents and supercritical fluids [101, 102, 103].
In terms of market penetration of bio-based surfactants, customers tend to choose cost-effective surfactants. Despite much progress in technical knowledge, the large-scale production of bio-based surfactants using the methods described above is still limited. The commercial production of bio-based surfactants still faces many challenges that must be addressed for them to be economically viable. One major obstacle is the homogeneity and consistency of the feedstock, which can lead to inconsistency in the final bio-based surfactants. Variation in the surfactant properties and performance could lead to unsatisfactory properties. Thorough testing on the use of bio-based surfactants in place of fossil-based ones will also be needed to provide enough and convincing data on the merits of bio-based surfactants. It is hoped that these efforts will lead to broader use of bio-based surfactants in the future, offering enormous benefits such as excellent physicochemical properties, biodegradability, lower risk to human health, and minimum harm to the environment.
Surfactant manufacturers have introduced numerous new eco-friendly surfactant-based products to the market in the past few years. Increased consumer awareness, along with a responsibility for sustainable development, has resulted in the creation of several novel surfactant types based on renewable building blocks. These surfactants have improved biodegradation characteristics and low toxicity, making them a preferred alternative for innovative formulations in the industrial and consumer markets. However, these “drop-in” surfactant molecules, which aim to directly replace their petrochemical-based equivalents, face a huge challenge since prices must be as competitive as their fossil counterparts. Moreover, while several personal care and consumer product businesses have shown interest in 100% bio-based surfactants, only a few green premium products have been accepted into the market. More assessments and surveys need to be done to gauge consumer willingness to pay premium prices for other than commodity products. With increasing innovative formulations to meet consumer, legislative, and sustainability demands, it is obvious that the global demand for both petroleum- and bio-based surfactants will continue to grow, while manufacturers are challenged to balance cost-effective formulations with efficient performance.
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From mechanical production powered by steam engines between 1700s and 1800s to the second Industrial Revolution mass production powered by electricity between 1800s and 1900s to the third Industrial Revolution powered by electronic and IT automation and finally to Industry 4.0 Revolution cyber systems in 2000 and beyond, human capital has generated innovative solutions to human problems more than ever before. 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The stabilization programs proposed by the IMF led to government guarantee of private sector external debts in the developing countries and led to a rapid increase in the public debt stock.",book:{id:"7598",slug:"public-economics-and-finance",title:"Public Economics and Finance",fullTitle:"Public Economics and Finance"},signatures:"Sibel Aybarç",authors:[{id:"286689",title:"Dr.",name:"Sibel",middleName:null,surname:"Aybarç",slug:"sibel-aybarc",fullName:"Sibel Aybarç"}]},{id:"58010",title:"Fourth Industrial Revolution: Current Practices, Challenges, and Opportunities",slug:"fourth-industrial-revolution-current-practices-challenges-and-opportunities",totalDownloads:6296,totalCrossrefCites:41,totalDimensionsCites:66,abstract:"The globalization and the competitiveness are forcing companies to rethink and to innovate their production processes following the so-called Industry 4.0 paradigm. 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Local and regional authorities then appear as an essential link in the implementation of public policies at the local level. Their genuine autonomy in financial and administrative matters is a necessary condition for achieving local development objectives. 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On the other hand, the transformation in low-tech and traditional industries progresses more slowly. Especially, the human factor is greater in the food manufacturing industry, which retains many more labor-intensive elements. This is because the development of foods was traditionally customized to the cultures of particular regions, so many foods were not suitable for mass production, which has led to the high level of personal skills. However, new trends have been shown recently in the sake manufacturing industry. Head craftsmen at a sake brewery, known as Toji, have managed the entirety of the manufacturing process and determined the length and timing of each process for hundreds of years. In these circumstances, some sake breweries have started to make sake in a new way that breaks with tradition. They implement smart manufacturing and customization to respond to diversified customer needs without altering the product price through the digitization of the manufacturing process and the formalization of personal skills. 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From\r\n1964 to 1974, he worked as Assistant in Biochemistry at the School of MedicineUniversidad Nacional de La Plata, Argentina. From 1974 to 1976, he was a Fellowof the National Institutes of Health (NIH) at the University of Connecticut, Health Center, USA. From 1985 to 2004, he served as a Full Professor oBiochemistry at the Universidad Nacional de La Plata, Argentina. He is Member ofthe National Research Council (CONICET), Argentina, and Argentine Society foBiochemistry and Molecular Biology (SAIB). His laboratory has been interested for manyears in the lipid peroxidation of biological membranes from various tissues and different species. Professor Catalá has directed twelve doctoral theses, publishedover 100 papers in peer reviewed journals, several chapters in books andtwelve edited books. Angel Catalá received awards at the 40th InternationaConference Biochemistry of Lipids 1999: Dijon (France). 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He was head of this department from 1993 to 2003. His specializations are medicine, gastroenterology, clinical pharmacology, clinical nutrition, and dietetics. His research fields are biochemical pharmacological examinations in the human gastrointestinal (GI) mucosa, mechanisms of retinoids, drugs, capsaicin-sensitive afferent nerves, and innovative pharmacological, pharmaceutical, and nutritional (dietary) research in humans. He has published about 360 peer-reviewed papers, 197 book chapters, 692 abstracts, 19 monographs, and has edited 37 books. He has given about 1120 regular and review lectures. He has organized thirty-eight national and international congresses and symposia. He is the founder of the International Conference on Ulcer Research (ICUR); International Union of Pharmacology, Gastrointestinal Section (IUPHAR-GI); Brain-Gut Society symposiums, and gastrointestinal cytoprotective symposiums. He received the Andre Robert Award from IUPHAR-GI in 2014. 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He\nreceived a short-term scholarship to carry out his post-doctoral\nstudies abroad, from Japan International Cooperation Agency\n(JICA), in coordination with the Egyptian government. Dr.\nShalaby speaks fluent English and his native Arabic. He has 77\ninternationally published research papers, has attended 15 international conferences, and has contributed to 18 international books and chapters.\nDr. Shalaby works as a reviewer on over one hundred international journals and is\non the editorial board of more than twenty-five international journals. 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