Physicochemical composition.
\\n\\n
Released this past November, the list is based on data collected from the Web of Science and highlights some of the world’s most influential scientific minds by naming the researchers whose publications over the previous decade have included a high number of Highly Cited Papers placing them among the top 1% most-cited.
\\n\\nWe wish to congratulate all of the researchers named and especially our authors on this amazing accomplishment! We are happy and proud to share in their success!
Note: Edited in March 2021
\\n"}]',published:!0,mainMedia:{caption:"Highly Cited",originalUrl:"/media/original/117"}},components:[{type:"htmlEditorComponent",content:'IntechOpen is proud to announce that 191 of our authors have made the Clarivate™ Highly Cited Researchers List for 2020, ranking them among the top 1% most-cited.
\n\nThroughout the years, the list has named a total of 261 IntechOpen authors as Highly Cited. Of those researchers, 69 have been featured on the list multiple times.
\n\n\n\nReleased this past November, the list is based on data collected from the Web of Science and highlights some of the world’s most influential scientific minds by naming the researchers whose publications over the previous decade have included a high number of Highly Cited Papers placing them among the top 1% most-cited.
\n\nWe wish to congratulate all of the researchers named and especially our authors on this amazing accomplishment! We are happy and proud to share in their success!
Note: Edited in March 2021
\n'}],latestNews:[{slug:"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:"6432",leadTitle:null,fullTitle:"Hyperbaric Oxygen Treatment in Research and Clinical Practice - Mechanisms of Action in Focus",title:"Hyperbaric Oxygen Treatment in Research and Clinical Practice",subtitle:"Mechanisms of Action in Focus",reviewType:"peer-reviewed",abstract:"Hyperbaric oxygen treatment (HBO2) is a widely accepted adjuvant therapy in various health conditions that exhibit impaired tissue blood flow. At high pressures, the delivery of the dissolved oxygen in plasma is enhanced, which contributes to better tissue oxygenation, cellular metabolism and ultimately, healing. However, this is not the only beneficial outcome of HBO2 treatment since oxygen is a highly reactive molecule and can induce upregulation of many enzymatic systems in the cell at the cellular, genetic and molecular level. Particularly, vascular/endothelial function is affected by the HBO2. Our understanding of these mechanisms is still emerging. There have been many controversies related to the HBO2 protocols and indications. As well as exhibiting beneficiary effects on the tissue perfusion, it is known that HBO2 demonstrates high toxicity at higher pressures, due to increased oxidative stress and barotrauma. On the other hand, there is a lack of translation of the knowledge on the mechanisms of action of HBO2 obtained from the experimental research to the clinical practice. Thus, this book presents the reader with an overview of the current knowledge on the mechanisms of HBO2 effects in various experimental models and clinical treatment protocols, in an attempt to provide a better understanding of how and when HBO2 should be used as an effective therapy without unwanted side effects.",isbn:"978-1-78923-599-9",printIsbn:"978-1-78923-598-2",pdfIsbn:"978-1-83881-469-4",doi:"10.5772/intechopen.70322",price:119,priceEur:129,priceUsd:155,slug:"hyperbaric-oxygen-treatment-in-research-and-clinical-practice-mechanisms-of-action-in-focus",numberOfPages:130,isOpenForSubmission:!1,isInWos:null,isInBkci:!1,hash:"574f9e3775c072d689ca7cab789dd590",bookSignature:"Ines Drenjančević",publishedDate:"August 29th 2018",coverURL:"https://cdn.intechopen.com/books/images_new/6432.jpg",numberOfDownloads:7913,numberOfWosCitations:6,numberOfCrossrefCitations:7,numberOfCrossrefCitationsByBook:2,numberOfDimensionsCitations:12,numberOfDimensionsCitationsByBook:2,hasAltmetrics:0,numberOfTotalCitations:25,isAvailableForWebshopOrdering:!0,dateEndFirstStepPublish:"July 6th 2017",dateEndSecondStepPublish:"July 27th 2017",dateEndThirdStepPublish:"December 2nd 2017",dateEndFourthStepPublish:"January 21st 2018",dateEndFifthStepPublish:"March 22nd 2018",currentStepOfPublishingProcess:5,indexedIn:"1,2,3,4,5,6",editedByType:"Edited by",kuFlag:!1,featuredMarkup:null,editors:[{id:"186048",title:"Prof.",name:"Ines",middleName:null,surname:"Drenjančević",slug:"ines-drenjancevic",fullName:"Ines Drenjančević",profilePictureURL:"https://mts.intechopen.com/storage/users/186048/images/5818_n.jpg",biography:"Ines Drenjančević, MD, PhD is a tenure-track professor of physiology and immunology and Chair of the Dept of Physiology and Immunology, Faculty of Medicine Osijek, University Josip Juraj Strossmayer Osijek. She has obtained her PhD in Physiology at the Medical College of Wisconsin, Milwaukee, Wisconsin, USA (2004); MD degree (1993) and MS degree in clinical immunology and allergology (1997) from the Faculty of Medicine University of Zagreb, Croatia. Her research has been funded at national and international level. At the moment, she is PI of CSF project and co-leader of the national Scientific Centre of Excellence for Personalized Health Care. Her interests: mechanisms of microvascular reactivity, effects of various diets (high salt intake, functional food, microelements) and hyperbaric oxygenation-with the common denominator of oxygen sensing and metabolism of arachidonic acid.",institutionString:null,position:null,outsideEditionCount:0,totalCites:0,totalAuthoredChapters:"4",totalChapterViews:"0",totalEditedBooks:"1",institution:{name:"University of Osijek",institutionURL:null,country:{name:"Croatia"}}}],equalEditorOne:null,equalEditorTwo:null,equalEditorThree:null,coeditorOne:null,coeditorTwo:null,coeditorThree:null,coeditorFour:null,coeditorFive:null,topics:[{id:"177",title:"Emergency Medicine",slug:"emergency-medicine"}],chapters:[{id:"62535",title:"Introductory Chapter: Hyperbaric Oxygen Treatment: Old Treatment with New Understanding",doi:"10.5772/intechopen.79866",slug:"introductory-chapter-hyperbaric-oxygen-treatment-old-treatment-with-new-understanding",totalDownloads:807,totalCrossrefCites:1,totalDimensionsCites:1,hasAltmetrics:0,abstract:null,signatures:"Ines Drenjančević",downloadPdfUrl:"/chapter/pdf-download/62535",previewPdfUrl:"/chapter/pdf-preview/62535",authors:[{id:"186048",title:"Prof.",name:"Ines",surname:"Drenjančević",slug:"ines-drenjancevic",fullName:"Ines Drenjančević"}],corrections:null},{id:"59727",title:"Therapeutic Mechanisms of Action for Hyperbaric Oxygen on Femoral Head Necrosis",doi:"10.5772/intechopen.75026",slug:"therapeutic-mechanisms-of-action-for-hyperbaric-oxygen-on-femoral-head-necrosis",totalDownloads:1268,totalCrossrefCites:0,totalDimensionsCites:1,hasAltmetrics:0,abstract:"Femoral head necrosis (FHN) is a disease process resulting from inadequate blood perfusion of subchondral bone. While the etiology of this disease is still not fully understood, there are multiple traumatic and atraumatic factors that are associated with the disease. Pathophysiology of the disease is characterized by the death of bone marrow and osteocytes. If left untreated, the disease may progress to joint collapse. While initial stages of the disease are asymptomatic, painful limitation of active and passive motion of the hip is eventually present. The current body of literature cannot identify an optimal treatment protocol for FHN. Postcollapse cases require surgical intervention, core decompression, or total hip arthroplasty. However, current strides in conservative management are being made. One of the possible conservative modalities that may effectively delay hip arthroplasty or even prevent the need for a surgical approach is hyperbaric oxygen (HBO2) therapy. HBO2 increases extracellular oxygen concentration and reduces cellular ischemia and edema by inducing vasoconstriction. Studies have reported radiographic improvement, reduction in pain, and increases in range of motion for early stages of the disease. Hyperbaric oxygen therapy has also been shown to stimulate angiogenesis and enhance osteoclast and osteoblast function for remodeling and repair.",signatures:"Gerardo Bosco, Alex Rizzato, Giuliano Vezzani, Vincenzo Zanon and\nEnrico Camporesi",downloadPdfUrl:"/chapter/pdf-download/59727",previewPdfUrl:"/chapter/pdf-preview/59727",authors:[{id:"63693",title:"Prof.",name:"Enrico",surname:"Camporesi",slug:"enrico-camporesi",fullName:"Enrico Camporesi"},{id:"217606",title:"Associate Prof.",name:"Gerardo",surname:"Bosco",slug:"gerardo-bosco",fullName:"Gerardo Bosco"},{id:"243195",title:"MSc.",name:"Alex",surname:"Rizzato",slug:"alex-rizzato",fullName:"Alex Rizzato"},{id:"243196",title:"Dr.",name:"Giuliano",surname:"Vezzani",slug:"giuliano-vezzani",fullName:"Giuliano Vezzani"},{id:"243197",title:"Dr.",name:"Vincenzo",surname:"Zanon",slug:"vincenzo-zanon",fullName:"Vincenzo Zanon"}],corrections:null},{id:"59900",title:"Hyperbaric Oxygen Therapy in Traumatic Brain Injury: Cellular and Molecular Mechanisms",doi:"10.5772/intechopen.75025",slug:"hyperbaric-oxygen-therapy-in-traumatic-brain-injury-cellular-and-molecular-mechanisms",totalDownloads:1320,totalCrossrefCites:1,totalDimensionsCites:3,hasAltmetrics:0,abstract:"Traumatic brain injuries (TBI) are among the leading causes of death and chronic disability worldwide. TBI is a complex process encompassing primary injury to the brain tissue and cerebral vasculature induced by the initial impact, secondary injury, including cascade of subsequent neuroinflammatory processes, and regenerative responses with enhanced neurogenesis and angiogenesis. To date, there remains no approved pharmacological therapy that is able to prevent the secondary injury. Therefore, the development of safe and efficacious neuroprotective treatments currently represents the greatest unmet need in the management of TBI. Increasing number of experimental and clinical studies present convincing evidence that hyperbaric oxygen therapy (HBOT), as an adjunctive therapy, may be the suitable neurotherapeutic method for improving neurological outcome after TBI. Irrespective to treatment protocol HBOT appeared to alleviate the detrimental and neurotoxic effects of pathological sequel initiated by TBI and to stimulate endogenous reparative mechanisms. However, the exact mechanisms by which HBOT exerts its beneficial effects on recovery after brain injury are still deficient. In this review we will summarize up to date results of HBOT in experimental and clinical TBI and try to put more light on cellular and molecular mechanisms underlying beneficial effects of HBOT on functional recovery after brain injury.",signatures:"Sanja Pekovic, Sanja Dacic, Danijela Krstic, Rada Jeremic, Marina\nDjelic and Predrag Brkic",downloadPdfUrl:"/chapter/pdf-download/59900",previewPdfUrl:"/chapter/pdf-preview/59900",authors:[{id:"218312",title:"Prof.",name:"Predrag",surname:"Brkic",slug:"predrag-brkic",fullName:"Predrag Brkic"},{id:"218438",title:"Dr.",name:"Sanja",surname:"Pekovic",slug:"sanja-pekovic",fullName:"Sanja Pekovic"},{id:"218609",title:"Dr.",name:"Sanja",surname:"Dacic",slug:"sanja-dacic",fullName:"Sanja Dacic"},{id:"218611",title:"BSc.",name:"Rada",surname:"Jeremic",slug:"rada-jeremic",fullName:"Rada Jeremic"},{id:"218614",title:"Prof.",name:"Marina",surname:"Djelic",slug:"marina-djelic",fullName:"Marina Djelic"},{id:"238176",title:"Prof.",name:"Danijela",surname:"Krstic",slug:"danijela-krstic",fullName:"Danijela Krstic"}],corrections:null},{id:"60271",title:"Microcirculation and Hyperbaric Oxygen Treatment",doi:"10.5772/intechopen.75609",slug:"microcirculation-and-hyperbaric-oxygen-treatment",totalDownloads:1262,totalCrossrefCites:2,totalDimensionsCites:4,hasAltmetrics:0,abstract:"The microcirculation is anatomical and consists of arterioles, capillaries, and venules that perform metabolic requirements and oxygen distribution to the tissues. During physiological or pathological stress, it balances between the oxygen delivery and the demand. This delicate balance can play an important role in the progression of critical illnesses and has a role in the development of organ dysfunction. Reduced microvascular perfusion is seen in many diseases, and hyperbaric oxygen treatment (HBOT) has potentially beneficial effects on the microcirculatory environment. It has been shown that HBOT improves microcirculation independent from systemic hemodynamic parameters, which is a key therapeutic target in the critically ill patient. HBOT is emerging as an adjunct to traditional surgery and antibiotic therapy for the special kinds of problematic wounds or purpura fulminans, which are caused by meningococcal sepsis. HBOT also can increase oxygen supply to the ischemic tissue to reduce the extent of irreversible tissue damage in ischemic stroke, femoral head necrosis, diabetic foot ulcer, and carbon monoxide intoxication. In this chapter, we aim to describe microcirculation with its monitoring systems and to show the effectiveness of HBOT in different clinical settings, which are related to microcirculatory dysfunction.",signatures:"Fethi Gul, Omer Faruk Boran and Reyhan Arslantas",downloadPdfUrl:"/chapter/pdf-download/60271",previewPdfUrl:"/chapter/pdf-preview/60271",authors:[{id:"215553",title:"Dr.",name:"Fethi",surname:"Gul",slug:"fethi-gul",fullName:"Fethi Gul"},{id:"227505",title:"Dr.",name:"Reyhan",surname:"Arslantas",slug:"reyhan-arslantas",fullName:"Reyhan Arslantas"},{id:"238186",title:"Dr.",name:"Omer Faruk",surname:"Boran",slug:"omer-faruk-boran",fullName:"Omer Faruk Boran"}],corrections:null},{id:"60024",title:"Cell Culture Effects of Altered Oxygen Levels and Hyperbaric Treatment In Vitro",doi:"10.5772/intechopen.75378",slug:"cell-culture-effects-of-altered-oxygen-levels-and-hyperbaric-treatment-in-vitro",totalDownloads:1125,totalCrossrefCites:0,totalDimensionsCites:0,hasAltmetrics:0,abstract:"Hyperbaric oxygen therapy (HBOT) is a state-of-the-art medical treatment, which is proved to be beneficial in a number of diseases and promising in new fields as well. HBOT is evidence-based treatment for, among others, severe CO intoxication, decompression disease and chronic wound healing. Recent studies promise beneficial effects of HBOT in multiple sclerosis. In vitro, cellular models of these complex pathological conditions are limited. In this chapter, we aim to mirror in vitro effects of HBOT and other altered oxygen levels on endothelial cells, fibroblast, mesenchymal and pluripotent stem cells. Through these in vitro models, the role of HBOT in angiogenesis, blot clotting, wound healing, cell therapy and tissue engineering will be discussed. To summarize in vitro effects of HBOT, it has beneficial role on proliferation and viability of most cell types. Furthermore, functional characteristics of the investigated cell types, for example, angiogenesis by endothelial cells, are improved in response to HBOT. Standardized preclinical protocols with HBOT help to translate the benefits to clinical trials and clinical use.",signatures:"Edit Gara",downloadPdfUrl:"/chapter/pdf-download/60024",previewPdfUrl:"/chapter/pdf-preview/60024",authors:[{id:"198479",title:"Ph.D.",name:"Edit",surname:"Gara Dr",slug:"edit-gara-dr",fullName:"Edit Gara Dr"}],corrections:null},{id:"61293",title:"Mechanisms of HBO-Induced Vascular Functional Changes in Diabetic Animal Models",doi:"10.5772/intechopen.76569",slug:"mechanisms-of-hbo-induced-vascular-functional-changes-in-diabetic-animal-models",totalDownloads:992,totalCrossrefCites:2,totalDimensionsCites:2,hasAltmetrics:0,abstract:"The mechanisms by which HBO exerts its potentially beneficial effects are not completely clear. Interactions of mechanisms affecting endothelial dysfunction, NO synthesis, EETs and HETE formation, CYP expression changes, oxidative stress and antioxidant defense system changes, and multiple effects on inflammation take place that might be considered as mediating factors for the observed positive (or negative) clinical effects in diabetes mellitus (for instance in chronic diabetic wounds). Studies on vasculature in diabetic animal models can provide us with more information that can help us understand its effects on blood vessel function. This chapter discusses the most relevant studies that have assessed the potential mechanisms of HBO-induced vascular functional changes in diabetic animal models.",signatures:"Ivana Jukic, Mihael Mišir, Martina Mihalj, Zrinka Mihaljevic, Sanela\nUnfirer, Dijana Kibel and Aleksandar Kibel",downloadPdfUrl:"/chapter/pdf-download/61293",previewPdfUrl:"/chapter/pdf-preview/61293",authors:[{id:"183303",title:"Dr.",name:"Aleksandar",surname:"Kibel",slug:"aleksandar-kibel",fullName:"Aleksandar Kibel"},{id:"216257",title:"Dr.",name:"Ivana",surname:"Jukić",slug:"ivana-jukic",fullName:"Ivana Jukić"},{id:"216262",title:"Prof.",name:"Martina",surname:"Mihalj",slug:"martina-mihalj",fullName:"Martina Mihalj"},{id:"250064",title:"Dr.",name:"Mihael",surname:"Misir",slug:"mihael-misir",fullName:"Mihael Misir"},{id:"250066",title:"Dr.",name:"Zrinka",surname:"Mihaljevic",slug:"zrinka-mihaljevic",fullName:"Zrinka Mihaljevic"},{id:"250067",title:"Dr.",name:"Sanela",surname:"Unfirer",slug:"sanela-unfirer",fullName:"Sanela Unfirer"},{id:"250068",title:"Dr.",name:"Dijana",surname:"Kibel",slug:"dijana-kibel",fullName:"Dijana Kibel"}],corrections:null},{id:"61952",title:"Toxic Effects of Hyperbaric Conditions",doi:"10.5772/intechopen.78392",slug:"toxic-effects-of-hyperbaric-conditions",totalDownloads:1141,totalCrossrefCites:1,totalDimensionsCites:1,hasAltmetrics:0,abstract:"Hyperbaric oxygen therapy is highly safe in treatments based on internationally accepted treatment tables. However, in some long-term treatments, the internal adjuvant and the patient are exposed to some toxic effects. In the presence of compressed air environment, nitrogen can lead to drunkenness. Another cause of poisoning is oxygen. Oxygen shows toxic effects when inhaled in the high-pressure environment for long periods or above partial pressures on 3 ATA. The excess oxygen has a toxic effect on the lung and central nervous system (CNS). Oxygen poisoning can be seen in long-term oxygen therapy in intensive care, in closed or semi-closed circuit diving, in saturation dives, on decompressions on the surface, in recompression and hyperbaric oxygen therapy. The first goal during convulsion is to prevent trauma prevent the patient from biting his tongue during the seizure. However, in nitrogen narcosis, the first intervention should be to prevent the diver from diving deeper to reduce the effect of anesthesia. The lifeguard must prevent the unconscious movements of the diver, such as removing the regulator from his mouth and holding his breath. 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But it attracted much attention in 2008, when a TiO2‐based crossbar memory array was developed by the HP Labs, and the cross‐point storage element was recognized as the memristor [2]. Recently, a rather deep analysis has been provided concerning memristors [3], which shows conclusively that the memristor is not the long‐sought fourth circuit element but the memory extension to the concept of resistor. With unique superior properties, memristors have promising applications in non‐volatile memory (NVM), artificial neural networks, programmable logic devices, signal processing and pattern recognition circuits. Random access memory (RAM) is an important form of computer data storage. However, due to the technological and physical limitations imposed by dynamic random access memory (DRAM), static random access memory (SRAM) and flash memory towards low power, small size, fast speed, high density and non‐volatility, there is an urgent need of upcoming NVM technologies with low power, high density, high read/write endurance and scalability. In a memristor, a new memory device to solve these problems, a resistive random access memory (RRAM) is a good direction for the development of future memory technology. RRAM is a memory using a material whose resistance changes under electrical stimulus and can be seen as the most promising candidate for next generation memory both as embedded memory and a stand‐alone memory due to its high speed, long retention time, low power consumption, scalability and simple structure [4]. Typically, RRAM is a two‐terminal device that the switching medium is sandwiched between top and bottom electrodes (Figure 1) and the resistance of the switching medium can be modulated by applying electrical signal (current or voltage) to the electrodes. Appropriate value of programming voltage pulse can set the device from high‐resistance state (HRS) to low‐resistance state (LRS) known as SET or writing process. Similarly, switching back of the device from LRS to HRS using a voltage pulse known as RESET or erase process. Based on the voltage polarity used, RRAM can be categorized into two types: unipolar and bipolar resistive switching [5]. The switching operation is called unipolar, if the SET and RESET processes occur at the same voltage polarity. In the SET process, the current is usually constrained by current compliance. Whereas, the switching is bipolar if the SET and RESET processes occur at reversed polarity of voltages. In both switching modes, two resistance states are distinguished from each other at a small read‐out voltage, therefore read operation has no influence on the resistance state. However, the attractive properties of RRAM are low fabrication costs, scalability into the nanometre regime, fast write and read access, low power consumption and low threshold voltages.
Schematic and electrical configuration of a two‐terminal RRAM cell.
The resistive switching effect has been explored until now in several materials including transition metal oxides, perovskite oxides, organic materials and carbon‐based materials. Carbon‐based materials have been researched extensively as an important class of materials for many years to defeat the technological barriers of conventional semiconductor electronics [6, 7, 8]. Previously, the efforts have been made to fabricate the field effect transistor (FET) devices [9, 10] based on carbon materials. Therefore, it is highly demandable to fabricate carbon‐based memory devices to integrate logic and memory devices based on same material. This chapter introduces RRAM properties of the carbon compound known as graphene oxide (GO). It is basically a wrinkled two‐dimensional carbon sheet with various oxygenated functional groups attached to its basal plane and peripheries, with the thickness of around 1 nm and lateral dimensions varying between a few nanometres and several microns. Graphene oxide has been synthesized by various chemical methods, such as Hummers’ method and its modification, Brodie method and Staudenmaier method. In contrast to the metallic nature of graphene, the graphene oxide is good insulating/semiconducting material, which can be readily obtained by oxidizing graphite with strong oxidants.GO sheets are heavily oxygenated, bearing hydroxyl and epoxide functional groups on their basal planes, in addition to carbonyl and carboxyl groups located at the sheet edges. Furthermore, the ability of these sheets to form covalent as well as non‐covalent (based on interactions) bonds encourages the fabrication of a wide variety of hybrid structures such as transistors, sensors, optoelectronic and memory devices etc. [11, 12]. The two dimensionality of GO permits scaling beyond the current limits of semiconductor technology, which is a key aspect for high‐density fabrication. Out of tremendous applications of graphene oxide, this chapter focuses on the memory device application. Graphene oxide (GO) with an ultrathin thickness is attractive due to its unique physical‐chemical properties. GO can be readily obtained through oxidizing graphite in mixtures of strong oxidants, followed by an exfoliation process. The presence of these functional groups makes GO sheets electrically insulating, with characteristics comparable to other thin‐layered oxide materials, with the advantage of being atomically thin, which makes GO the perfect candidate for the fabrication of memristive devices [13, 14]. As GO is water soluble which makes it facile to transfer onto any substrate in thin film form by simple methods of spin coating, drop‐casting, Langmuir‐Blodgett (LB) and vacuum filtration. The as‐deposited GO thin films can be further processed into functional devices using standard lithography processes without degrading the film properties [15, 16]. Furthermore, the band structure and electronic properties of GO can be modulated by changing the quantity of chemical functionalities attached to the surface. Therefore, GO is potentially useful for microelectronics production.
Graphene oxide‐based resistive memory devices have several advantages, such as easy synthesis and cost‐effective device fabrication, scaling down to few nanometres and compatibility for flexible device applications. Reliable and reproducible resistive switching behaviour was first reported in graphene oxide thin films prepared by the vacuum filtration method by He et al. in 2009 [17]. They observed very low switching voltages and low on/off ratio of about 20 in Cu/GO/Pt structure. Soon after that there were many reports published showing high on/off ratios in GO‐based RRAM devices [18, 19]. Mechanism for the resistive switching characteristics in GO‐based RRAM was found to be due to the oxygen migration, oxygen vacancies and the electrode diffusion [20, 21]. Furthermore, Jeong et al. presented a GO‐based memory that can be easily fabricated using a room temperature spin‐casting method on flexible substrates and has reliable memory performance in terms of retention and endurance [22]. Resistive switching effect was shown in Ni‐doped graphene oxide by Pinto et al. [23]. Transparent non‐volatile memory device based on SiO
Synthesis of graphene oxide presented in this chapter has been carried out by modified Hummers method [25, 26]. In brief, highly oriented pyrolytic graphite (HOPG, 2 g) was oxidized using potassium permanganate (KMnO4, 7 g) in the presence of concentrated H2SO4 (50 ml) in ice bath. After the reaction, excess distilled water was added to the solution. With continuous stirring a 30 wt.% of hydrogen peroxide (H2O2) was added slowly until the gas evolution had stopped. Further 15 more‐minute stirring was done to the resultant mixture, and then it was filtered through nylon membrane. Repeated washing was done by distilled water and 5% HCl solution until the filtrate was neutral. Finally, the obtained dark brown slurry was dried for 24 hour in a vacuum oven at 60°C. A colloidal suspension of GO was prepared in distilled water by sonicating graphite oxide in water for 2 hour. Such a solution of GO was used to fabricate the thin films by spin coating process on ITO/Glass substrate. To construct metal-insulator-metal (MIM) devices, platinum top electrodes with an area of 40 × 40 μm2 were deposited by DC sputtering utilizing a shadow mask. The schematic representation of fabricated Pt/graphene oxide/imdium-tin oxide (GO/ITO) is shown in Figure 2.
Schematic representation of GO‐based MIM devices [
To observe the switching characteristics of the device, I‐V measurements for the Pt/GO/ITO device at 300 and 500 K were performed as shown in Figure 3a and b). The Pt/GO/ITO device was found initially in low‐resistance state having resistance value of ∼40 ohm. Figure 3 shows that as the positive voltage was increased, a sudden fall in current was observed at a voltage of ∼3.2 V indicating abrupt increase in the resistance of the device. This is known as RESET process and device transformed from its initial low‐resistance state (LRS) to high‐resistance state (HRS) also known as OFF state.
Current‐voltage characteristics of the Pt/GO/ITO device at (a) 300 K and (b) 500 K [
The low‐resistance state of GO‐based MIM devices once obtained persisted even when the applied voltage was reduced to zero indicating non‐volatility. In high‐resistance state, when the voltage was swept a sudden increase in current was observed at a voltage of approximately −1.2 V indicating abrupt decrease in the resistance of device and switching from high‐resistance state to low‐resistance state as shown in Figure 3a. This is known as the SET process which switched the MIM device in LRS or ON state. The LRS of device remained preserved even when the applied bias voltage was removed. During this set process, current compliance was kept fixed at 100 mA to avoid the breakdown of GO film due to high current flow in low‐resistance state. By repeating the set and reset processes over 100 cycles, it was observed that the reset voltage was larger than the set voltage and spread over a small window of voltage between ∼3 and 3.4 V, whereas the set voltage had a spread between approximately −1.2 and −1.8 V. Thus, the device showed a typical bipolar resistive switching (BRS) behaviour with an on/off current ratio of 104 over 100 test cycles. Switching characteristics of the device were also studied at elevated temperature of 500 K (as shown in Figure 3b). Reduction in the value of reset voltage at 500 K was observed which could be attributed to enhanced diffusivity of oxygen ions at elevated temperature compared to that of room temperature. However, contrary to that we found increment in the set voltage at elevated temperature. Further at high temperature of 500 K, the on/off ratio of the device was found to decrease up to ∼102 compared to its value at 300 K which was ∼104; however, this ratio of high‐ and low‐resistance states is sufficient for operation of memory devices. Low‐ and high‐resistance states were stable up to 104 seconds and up to 100 cycles indicating good retention and endurance characteristics of the device at elevated temperature of 500 K.
Based on the conduction mechanism, it was observed that GO device contains conducting paths between top and bottom electrode perhaps due to the presence of oxygen vacancies and electron traps in graphene oxide layer forming electron hopping path [27]. Presence of oxygen vacancies in graphene oxide indicates partial reduction of GO and dominance of sp2 character over sp3 character providing high conducting channel in GO film and initial low‐resistance state without any forming process. In Pt/GO/ITO devices, the bottom electrode ITO acts as a source/reservoir of oxygen ions [28]. To ascertain the presence of sp2 and sp3 characters of carbon, Raman spectroscopy measurements were carried out on the Pt/GO/ITO devices both in LRS and HRS and are shown in Figure 4. As can be seen in Figure 4 that in case of as‐grown device and the device in LRS, the presence of G peak signifying the sp2 character is larger in intensity compared to the same peak when the device was switched into HRS by the application of suitable bias voltage. This indicates that the sp2 character dominates in LRS. While in case of HRS, the sp2 character is suppressed. These RRAM devices based on GO layer fabricated by a simple process of spin coating show a forming free bipolar resistive switching (BRS) in Pt/GO/ITO structure with high on/off ratio of 104 exhibiting good retention and endurance properties at room and elevated temperatures.
Raman spectra for Pt/GO/ITO device in LRS (upper curve) and HRS (lower curve) [
Organic memory devices have gained much attention as future information and storage components owing to their low weight, flexibility, inexpensive and facile fabrication methods [29, 30]. Recent reports have shown that organic memory devices have been developed through layer stacking [31] and using advanced memory architectures [32, 33, 34, 35]. However, the most organic memory devices are suffering with slow switching [36] and low storage capacity [37, 38]. RRAM performance of the organic memories can be greatly enhanced by forming hybrid organic structures [39], organic/inorganic composites [40] or by dispersing nanomaterials [41, 42]. Among all other organic polymers, polyvinylidene fluoride (PVDF) was used due to its non‐reactive nature, better heat resistance, flexibility and low weight. As mentioned above, hybrid structures of organic memory devices provide enhanced memory characteristics; therefore, heterostructure of PVDF was fabricated using a charge trapping element in it. In this study, reduced graphene oxide nanoflakes (GR) were used as a charge trapping layer owing to their unique chemical structure and exceptional properties [6, 43, 44, 45, 46, 47] that make it ideal for charge trapping [48] and storage [49] for memory applications. Also, the defects (vacancy, interstitial sites, etc.) present in GR also work as the charge trapping nodes [50]. Tri‐layer structure was fabricated by assembling graphene nanoflakes (GR) between PVDF polymer layers [51] through spin coating process on ITO/glass substrate as shown in Figure 5. DC sputtering was used to deposit platinum top electrode having area (100 μm × 100 μm) through shadow mask to obtain devices from the stacked structure.
Schematic diagram of the layer‐by‐layer fabricated Pt/PVDF/rGO/PVDF/ITO memory devices. Top electrode of platinum (Pt) having area 100 × 100 μm2 was deposited using DC sputtering [
As the voltage was increased, multi‐stage SET and RESET were observed in positive and negative polarities, respectively, as shown in Figure 6a. This process was repeatable for a number of cycles, which established the device as a non‐volatile memory with multilevel conductance states. The multilevel SET process occurring in the device can be due to multi‐channels formation as trapping sites in graphene bear different threshold potentials. Electrons occupied these trapping sites even if the applied voltage is removed, thus preserving the non‐volatile nature of the device in ON state. When negative voltage is applied to the device, current firstly increases with voltage due to the presence of trapped charges in the nodes. At a particular negative bias, current jumps to low value due to the de‐trapping of electrons from the trapping nodes which initiates the breaking of conducting channels. Further at a particular negative bias, when most of the electrons de‐trapped and ejected back to ITO, the conducting path completely disrupts and the device transits to OFF state bearing high resistance. The multi‐channel RESET process occurring in the device is also due to the same mechanism as discussed in the SET process. In brief, it may be due to the breaking of multi‐channels at different potentials. Reports have shown that the intermediate stage present in the device revealing multi‐level switching is due to the formation of multi‐filaments [52] having different threshold potentials [53]. The device was further subjected to different compliance currents of 1, 10 and 100 μA during the SET process and correspondingly obtained different low‐resistance states as shown in Figure 6b.
Typical I‐V characteristic curves plotted in semi‐logarithmic scale of Pt/PVDF/rGO/PVDF/ITO device (a) showing the presence of intermediate state. (b) Under different compliance currents of 1, 10 and 100 μA showing different low‐resistance states corresponding to the compliance current applied [
When the highest value of ICC was imposed, the device was observed in lowest resistance state. However, the HRS value for different ICC was almost the same. All four different states including one HRS and three LRS were observed in the device. It was proposed that with the highest compliance current applied during SET process, maximum number of trapping nodes are filled and hence maximum number of conductive channels are formed resulting in the lowest resistance state, while with the application of the lowest compliance current, small number of trapping nodes are filled having less number of conducting channels, leading to higher resistance state. To observe the performance and stability of the memory device, its endurance and retention properties were studied. Figure 7a represents the endurance characteristics of the device for all the four resistance states tested against number of cycles. As can be seen from Figure 7a, the four different states including one HRS and three LRS (LRS1, LRS2 and LRS3) were stable with no overlapping of resistances tested over the 150 number of cycles. Figure 7b shows the retention properties observed in the device where the resistance of all four states were measured using a read voltage of 0.1 V over a period of 104 seconds. The graph shows well‐differentiated resistance states of HRS and three LRS with no degradation in resistance values over the long time. These measurements for retention and endurance for the device showed that it has well performance and good stability. This tri‐layer structure fabricated by simple spin coating method can be seen as a potential candidate for future memory devices qualifying the need for high‐density storage media.
Resistances of the device in all LRS and HRS under different compliance currents of 1, 10 and 100 μA with read voltage of 0.1 V. (a) Endurance properties over 150 cycles with enough margin between the states. (b) Retention characteristics over 104 seconds for all four states [
Flexible RRAM devices have shown good potential for bendable memory systems [54, 55, 56, 57, 58].These memories are in much demand due to the qualities of inexpensive, low weight, portability and user‐friendly interfaces over conventional rigid silicon technology [59]. The substrates for flexible memories could not bear high temperatures used in growth techniques, this limitation demands for the need for materials which can be grown on these substrates at room temperature. Obeying this condition, GO is readily oxidizable and water soluble, which qualifies to be fabricated in thin films on flexible substrates at room/moderate temperatures. There are reports which have shown that integration of nanomaterials into oxides is helpful in enhancing the resistive switching properties of the devices [60, 61, 62]. In this work [63], ZnO nanorods (ZNs) were grown in horizontal direction on GO sheets to maximize the contact area between the nanorods and GO sheets [64, 65]. The consequence of this was observed in significant reduction in switching voltages in comparison to GO alone. The solution of GOZNs was spin coated to ITO‐coated polyethylene terephthalate (indium-tin oxide on polyester film (ITOPET)) substrates to fabricate the films. Initially, the Al/GOZNs/ITOPET devices were in high‐resistance state (HRS). In the very first cycle, a forming voltage around 5 V with current compliance of 2 mA was applied to activate these devices. Device showed SET and RESET processes on positive and negative voltages having non‐volatile nature. To investigate the effect of ZNs addition into the GO matrix, another device Al/GO/ITOPET was fabricated following the same process except the incorporation of ZNs in it, and this device showed comparatively higher values of SET and RESET voltages.
I‐V measurements performed on both devices, shown in Figure 8, have clearly shown that SET and RESET voltages in the device containing ZNs were severely reduced to approximately half in comparison to the device containing no ZNs. To further understand the effect of changing ZNs ratio in GO matrix on resistive switching, the I‐V characteristics of different compositions (10:1, 5:1, 3:1 and 2:1) were studied and found that 3:1 was the best among all. In Al/GOZNs/ITOPET devices, we propose that the conducting filament formation during the SET process is due to the oxygen vacancies. Oxygen concentration gradient exists at the interface of GO, and Al has high oxidation tendency. Therefore, oxygen ions from GO move towards and react with Al forming a new interfacial Al oxide layer [66]; also this process induces the oxygen vacancies into the GO region. With the positive bias is applied to the top electrode, these induced oxygen vacancies are deeply inserted into the GO matrix and providing the conductive paths during the SET process. With the negative polarity these oxygen vacancies are pushed back resulting in rupture of the conducting channel during the RESET process. But with the incorporation of ZNs into the GO matrix, significant reduction in the switching voltages was observed and this is due to the desorption/adsorption of oxygen at the interface of GO and ZNs, which stimulates the formation/rupture of conducting paths on the application of suitable polarity voltages. This mechanism based on oxygen vacancies is well supported by the X-ray photoemission spectroscopy (XPS) measurements of these samples shown in Figure 9.
Typical I‐V switching characteristics in Al/GOZNs/ITOPET devices. Inset shows the I‐V characteristics for Al/GO/ITOPET device [
(a) Comparative XPS spectra of GO and GOZNs for C1S peak. (b) XPS spectra of ZNs and GOZns showing O1S peak resolved into two components O1 and O2. (c) Zn2p spectra of ZNs and GOZNs samples [
Figure 9a is the XPS graph for C1s peak in GO and GOZNs samples. The C1s graph of GO contains sp2 and C─O─C peaks, whereas for the GOZNs sample, the C─O─C peak has disappeared having only sp2 peak in the spectra. The XPS study showed the reduction in oxygen content with the disappeared C─O─C peak for the GO matrix having ZNs, which demonstrates that GO has become comparatively less resistive having sp2 character dominant. However, ZNs are well known for chemisorption of oxygen at its periphery and it can be evidenced by the fitted O2 peak for O1s spectra in Figure 9b. Also, the peak positions for these O1 and O2 in GOZNs sample were found to be little shifted towards lower energy. Furthermore, a noticeable increment in the intensity of O2 peak was also observed in GOZNs in comparison to ZNs. The O1s peak was also found to be shifted to lower binding energy due to the additional oxygen absorbed by ZNs as shown in Figure 9b [67]. Further, the presence of excess oxygen can also be clearly observed in Figure 9c which shows the shift in the Zn 2p peak towards lower energy in GOZNs sample in comparison to ZNs sample [67]. The performance of flexible electronic devices can be tested through flexibility and mechanical endurance measurements. The flexibility measurements were done on the Al/GOZNs/ITOPET devices and the value of resistance was plotted as a function of bending radii as shown in Figure 10a. The resistance was measured up to the maximum bending radius of 4 mm and amazingly found that the LRS and HRS were widely separated and can be well distinguished. The mechanical reliability test was also performed by constantly flexing the device many times to the bending radius of 6 mm and the resistance was plotted against number of bending cycles as shown in Figure 10b. The HRS and LRS resistances show no noticeable degradation even up to 1000 times of repeated bending. The measurements performed on the Al/GOZNs/ITOPET device show excellent flexibility and mechanical endurance results and provide the data which show that the devices are capable for flexible memory applications. This study shows that the devices based on ZNs embedded in GO are potential candidate for future flexible non‐volatile memory applications.
(a) Flexibility test for various bending radius on Al/GOZNs/ITOPET RRAM device. (b) Mechanical bending endurance of device at bending radius of 6 mm on Al/GOZNs/ITOPET RRAM device [
RRAM devices based on oxide have good switching characteristics, but still there are two major downsides with these memories: first one is the need of an initial forming voltage [68, 69, 70] to initiate the switching mechanism, which is detrimental to device performance, however, this issue can be resolved by manipulating the deposition and growth process and the other problem is the uncontrolled position of conductive channels formation during repetitive applied bias. To address the problem of initial forming in graphene oxide (GO)‐based devices, we adopted the method of electrophoresis to deposit the device structure [71]. Reports have shown that the graphene oxide films grown by electrophoresis are conducted or reduced in nature [72, 73].As the oxygen functional groups attached to its basal plane get removed, the graphene oxide films become semiconducting having localized π‐π electrons network. These functional groups can be eliminated by passing the current during electrophoresis deposition process, resulting GO to be reduced or semiconducting in nature. In this study, the films were deposited by electrophoresis and as deposited films were found to be in low‐resistance state; therefore, no high forming voltages were required to initiate the switching process. To resolve the problem of confined conducting channels, we have to understand that there is random formation of conductive filaments at nanoscale with applied bias in un‐doped films, and it is hard to confine their position precisely. The reports for RRAM devices based on transition metal oxides infused with metallic nanoparticles have shown enhancement in switching properties with the addition of metal nanoparticles [61, 74]. The present study is focused on improved switching characteristics of graphene oxide films embedded with gold nanoparticles (Au Nps), which helps to confine the conducting filaments during numerous sweep cycles. A colloidal suspension of GO with Au Nps was obtained by sonication. The films were deposited by electrophoresis process using the sonicated GO with Au Nps (GOAu) solution [71]. Electrophoresis was performed using a home‐built assembly with a pair of ITO/glass as electrodes and a Keithley current source. GOAu films were deposited at room temperature by varying the current value ranging from 0.1 to 1.0 mA for 1–10 minutes having 1.5 cm distance between the electrodes as shown in Figure 11.
GO films grown by electrophoresis process.
The thickness of deposited GOAu film was measured to be ∼85 nm. The GO layers were in the size range of 3–5 μm and Au Nps were found in the range of 10–15 nm. The switching matrix constitutes the stack of GO layers with Au Nps. Aluminium (Al) top electrodes were deposited by thermal evaporation method through a shadow mask having diameter of 200 μm. Thus, the device structure formed was Al/GOAu/ITO/glass. Another sample was also fabricated using GOAu solution by spin coating on ITO/glass substrate for XPS study. To know the chemical composition of as‐grown GOAu films by electrophoresis, XPS study was performed as shown in Figure 12. These XPS measurements were done to illustrate the amount of oxygen functional groups present in electrodeposited GOAu films (Figure 12a) and spin coated GOAu films (Figure 12b) (XPS for spin coating films was performed to compare the amount of oxy groups). The peaks corresponding to C1s spectra as depicted in Figure 12 are C─C, C─O and C═O which are at respective binding energies of 284.6, 286.5 and 288.4 eV. In electrodeposited film, the C─O peak has low intensity in comparison to the C─C peak which shows that the oxygen content is less in the film. The lower oxygen content or presence of oxygen vacancies is favourable for as‐deposited films to be in low‐resistance and hence eliminating the need of forming voltages. Inset of Figure 12a shows the presence of Au 4f7/2and Au 4f5/2 peaks at their respective binding energies of 84 and 87.5 eV.
(a) XPS spectra for C1s peak of GOAu film grown by electrophoresis. Inset shows Au peaks for the GOAu film. (b) C1s peak of spin‐coated GOAu film [
To demonstrate the effect of Au Nps in GO devices, another film of GO having no Au Nps on ITO/glass by electrophoresis keeping same deposition parameters having Al top electrodes (Al/GO/ITO) was fabricated and measured its switching characteristics. Figure 13a shows typical I‐V switching characteristics of Al/GO/ITO (inset) and Al/GOAu/ITO devices, respectively. The initial resistance of the devices was found 3.5 × 104 Ω with Au Nps and 1.3 × 106 Ω without Au Nps. Therefore, the initial resistance of the device incorporated with Au Nps was found to be 100 times lower than that of the pristine GO device. The on/off ratio between LRS and HRS in pristine GO devices is very low and that too at high voltages. GOAu devices have enhanced on/off ratio at very low switching voltages as compared to pristine GO devices which is due to the presence of Au Nps, which are working as charge trapping centres.
(a) Typical I‐V characteristics of the Al/GOAu/ITO device in semi‐log scale; inset shows I‐V characteristics for the Al/GO/ITO device. (b) log‐log I‐V plot for the GOAu device [
The slope of the I‐V curve in LRS was found to be ∼1 as shown in Figure 13b; however, this linear current‐voltage relationship need not be ohmic: It can be Schottky‐limited conduction in the Simmons’ limit of short electron mean free paths [75],while in the high voltage regime of HRS, the slope was found to be ∼4.4, which reveals that a strong space charge limited current (SCLC) mechanism also known as trapped charge limited current (TCLC) mechanism is prevailing in the device [76]. The TCLC behaviour of the films is in agreement with the presence of Au Nps in the films, which are working as charge trapping centres. Hence the charges get trapped in one voltage polarity transiting the device to HRS and detrapped in the opposite polarity rendering back the device to LRS again. Therefore, the device shows bipolar switching behaviour exhibiting trapping/detrapping mechanism. GO sheets have different types of defects, such as oxygen vacancies, dislocations etc. [77, 78]. The defects and trapping nodes present in GO sheets play a significant role in switching behaviour. Initially, the device was in LRS due to the presence of large number of oxygen vacancies and the Au Nps. The device performed well in both states showing retention, endurance and statistical distribution over different cells as shown in Figure 14a–c.
(a) Retention, (b) endurance properties and (c) statistical distribution over different cells of GOAu device in LRS and HRS [
As discussed above, Au Nps dispersed in GO layers trap the charge, resulting in capacitive behaviour of the devices. In order to test this scenario, capacitance‐voltage (C‐V) measurements were carried out. Figure 15a and b shows the C‐V curves of the Al/GO/ITO and Al/GOAu/ITO devices. The measured capacitance was found to be ∼3.4 pF in LRS and ∼11.2 pF in HRS in GO device, whereas it was ∼9 pF in LRS and ∼350 pF in HRS in the GOAu device. It was observed that in both the resistance states, capacitance values were increased by a factor of ∼10 in HRS/LRS in GOAu devices in comparison to GO devices, which is mainly due to the charge trapping process by Au Nps. In GO matrix having Au Nps, this can be explained as follows: the array of Au Nps induces the coupling capacitance and the trapping energy levels are set by the work function of Au Nps.
C‐V curves of (a) GO and (b) GOAu devices in LRS and HRS [
Followed by an initial random charging, the charge carriers around a single Au Np may increase due to trapping process, which results in increasing the capacitive coupling and finally increases the coulomb repulsion. Au Nps embedded in GO matrix act as small capacitors having large capacitance due to their big surface/volume area and the associated interfacial polarization. An additional barrier will be created by these metal‐island capacitors which prevent the movement of electrons in the matrix and the charge transfer through these small metal‐islands, below a particular threshold voltage gets blocked (charges get trapped) leading to an increase in resistance as well. Therefore, in GOAu devices, achieving such a huge resistance in HRS can be attributed to the coulomb blockade effect imparted by the Au Nps which is associated to the quantum effect of metal nanoparticles [79, 80].
In summary, graphene oxide is a promising material for RRAM devices due to its high scalability and unique physical‐chemical properties. Fabrication of GO and its films, composites and heterostructures are very cost effective and opens up the direction for commercialization. Showing forming‐free behaviour is an excellent property of GO devices over other oxide‐based devices that require initial high voltages to start the switching process. Multi‐level switching in GO‐based heterostructures has the potential of high‐density data storage, which is the need of future non‐volatile memories. Flexibility and mechanical endurance observed in GO‐based composite RRAM devices have prospects in portable and flexible devices which is advantageous over the rigid silicon technology. Gold nanoparticles embedded in GO have shown enhanced switching properties with very high on/off resistance ratio and very low switching voltages, which are suitable for low power resistive memory devices. The mechanism underlying the graphene oxide‐based memories is the formation of conductive filaments due to the roles played by oxygen ions and vacancies. Therefore, GO‐based RRAM devices have enough potential to become one of the important non‐volatile memories due to their encouraging properties of forming free, multi‐bit data storage and low power flexible devices. However, further research is still needed towards scaling of these devices below 10 nm node and that too having fast switching speeds to establish graphene oxide‐based non‐volatile resistive devices achieve a niche in memory industry.
The authors acknowledge the financial support from DOD Grant (AFOSR‐FA9550‐16‐1‐0295) and IFN‐NSF Grant (EPS‐01002410) for travel support.
One of the great problems of the coastal zone of the Gulf of Mexico is the diverse and significant water load of the different anthropogenic activities which have not taken into account the volume that must be conserved for the ecological services for which have been lost atmospheres of diverse biological wealth. The coastal flood plains in the Gulf, associated with coastal zones on the border with the terrestrial zone and the sea, are subject to flooding by rainfall, excess fluvial contribution that makeup dikes and channels but that play important roles in the coastal landscape and they contribute to the high production of the coastal zone, however; they run the risk of various deteriorations with or without recovery [1, 2, 3, 4, 5, 6].
The coastal zone associated with rivers, is interconnected by an extensive network of wetlands and floodplains temporary and perennial that allow the retention of water, act as filters, deposits and source for various substances and re the habitat of plant species adapted to these conditions and fauna associated with this vegetation both emerging and submerged. The main problems that lagoons located within or near urban areas have are eutrophication, siltation caused almost always by inadequate management of the urban basin and lack of control of wastewater inlets, but in particular agriculture refuses [7, 8, 9]. The Gulf of Mexico is the ninth largest body of water in the world, with five Mexican states to the west. Due to its physical and chemical characteristics, it is a very diverse internal sea as a result of its latitudinal location; from tropical, subtropical to temperate, with climates classified as “dry” (spring), rainy (summer, autumn) and northern (winter) [10]. The coastal lagoons and estuaries of the Gulf of Mexico have been characterized environmentally taking into account: their location, shape, size, runoff and tributary streams, number and size of the mouths of connection with the sea, their behavior throughout the year, their bathymetry, internal currents, the type of sediment they receive from the watershed to which they are associated, gases, dissolved solids or salinity and primary productivity, among others [11]. Based on the foregoing, each coastal lagoon and estuary differs in their mentioned characteristics. Given the high number of coastal systems of the Gulf, the present work has the objective of choosing four coastal lagoons (Figure 1) to exemplify their physicochemical natural variations in space and time considering their geographic location two; as well as the level metals, hydrocarbons, and pesticides. This chapter is comprised: a brief description of a four coastal lagoon of the Gulf of Mexico chosen in this study, as well as of the incorporation of previously published information with the methods used to obtain data; the presentation of the results and the consequent discussion; and brief comparison with other lagoons of the coastal region; and the most outstanding conclusion.
Location of main coastal lagoons in the Gulf of Mexico.
The technique used for metals was that described [12] consisting of a digestion in a microwave oven (CEM Mars5x) with 3 mL of HF, 10 mL of reagent water and 5 mL of super-pure HNO3. The samples were read in an ICP-MS (ICP 7500c). Analytical quality was controlled using approved standards, reference material certified for marine sediments (IAE-433). The methodologies used for the analysis of metals are based mainly on the use of acid digestion in a microwave, obtaining afterward the concentrations in an Atomic Absorption Spectrophotometer or in ICP-MS.
The samples were analyzed for the 16 priority PAHs [13] following the method recommended [14] and used worldwide in marine pollution studies [15, 16, 17]. This method involves an organic extraction with n-hexane: methylene chloride 50:50 v/v, concentration of the extract, clean-up using a silica pack, aluminium oxide and anhydrous sodium sulfate, eluted with n-hexane mixtures: methylene chloride 80:20 and 50:50 to obtain the aromatic fraction; the samples were concentrated under a soft N2 current to dryness.
The OCs included the HCH (alpha, beta, gamma and delta isomers), DDT and its metabolites (
A flame ionization detector (FID) and an electron capture detector (ECD) were used for PAHs and the organochlorine compounds, respectively. Quantification was carried out using the internal calibration method based on a five-point calibration curve for individual components. The percentage of recovery of PAHs and OCs ranged from 85 to 105%. For each batch of 10 samples, a procedural blank, a spiked blank and reference standard material were processed (IAEA-417). Detection limits (DLs) were 0.01 μg g−1 for PAHs and 0.01 ng g−1 for OCs.
Tampamachoco lagoon system (TLS) is located in the Coastal Plain of the Gulf of Mexico, in the state of Veracruz, between the parallels 20°58′ 15″–21°05″ N and the meridians 97°20′ 30″–97 24″ W [23]. It is formed by the Tampamachoco lagoon (1500 ha), occupying a total area of 6870 ha. The climate is of the “Aw type 2” (e) that is to say warm subhumid with rain in the summer [24], with an annual rainfall of 1900 mm, being January the driest month and September the rainiest. Is a shallow system with an average depth of one-meter, high turbidity [25] and only discharges to the south the river called Tuxpan near the marine mouth, through which it communicates with the Gulf of Mexico [26, 27]. Total nitrogen and total phosphorus are high, which represent the anthropogenic influence (Table 1).
Physicochemical parameters | ||||||||
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Area | Salinity | Temperature | Dissolved oxygen | Total nitrogen | Total phosphorus | Ammonium | Orthophosphates | Chlorophyll “a” |
ups | °C | mg/L | μM | μM | μM | μM | mg/m3 | |
Tampamachoco lagoon system (TLS) | 11–38 | 18–32 | 0.3–9 | 5–71 | 2.6–123 | 1–35 | 0–89 | 2–14 |
Mandinga lagoon system (TLS) | 8–32 | 28–33 | 4–6 | 5–17 | 5–10 | 2–10 | 0.2–2 | 10–52 |
Alvarado lagoon system | 0.3–34 | 25–31 | 10–18 | 36–429 | 17–41 | 15–25 | 0.4–6 | 22–49 |
Terminos lagoon system (TELS) | 28–34 | 26–32 | 3–10 | 2–30 inorg. | 4–26 | 0.1–7 | 3–20 | |
Yucateco lagoon, Tabasco state | 0.5–33 | 21–35 | 0.5–8 | 7–228 | 3–138 | 0.5–31 | 0.5–18 | jul-28 |
Mecoacan lagoon, Tabasco state | 1–14 | 24–30 | 3–5 | 29.41 | 5–14 | 0.4–4 | 7–21 |
Physicochemical composition.
Mandinga lagoon system (MLS) is located between 19°00′ and 19°06′ N and 6°02′ and 96°06′ W. It has a complex morphological conformation constituted by three lagoon bodies; it has an extension of 3250 ha [9]; these. Receives several affluent of other less important rivers [28]. The type of climate in the MLS is Aw2 (w) (i) W “with average rainfall of 1676 mm/year and average evaporation of 1500 mm/year [28]. The temperature has an interval between 25 and 31°C approximately similar to that of the bottom, according to the geomorphology and the annual climate (rains and drought) (Figure 1). This lagoon has a high chlorophyll that represented high primary production (Table 1).
Alvarado lagoon system (ALS) is located in the South Coastal Plain of the Gulf of Mexico, between the coordinates 18°44′00″ and 18°52′15″ of latitude N and 95°44′00″ and 95°57′00″ of longitude W (Figure 1). This lagoon system leads to several rivers within the most important is Papaloapan, and it is made up of several internal (7162 ha), the type of climate is subhumid warm (Aw2), with little thermal oscillation. According to INEGI (National Institute of Statistic and Geography) [29], the climate is warm-sub-humid-the wettest of the sub-humid-with rain in summer. The dry season occurs between the months of January to May, the rainy season begins in June and the north winds season which are cold wind masses. In addition, this water body is affected by depressions, tropical storms, and hurricanes. The main river basin is the Papaloapan River, which has a complex system of wetlands and borders on its active agricultural activity. The ALS, is considered the third largest wetland in Mexico (National Commission of Biodiversity) [30, 31], it is also one of the most productive systems of the Gulf of Mexico [32] and a shelter area for the feeding and reproduction of numerous populations of fish and crustaceans [33]. The region where this lagoon is located presents several environmental problems: change in land use such as road construction, landfills, agriculture; also the mangrove felling and modification of the vegetation; the use of biocides (organochlorine, organophosphorus), discharge of urban and industrial waters such as sugar, paper and even urban wastewater from cities upstream, overfishing, among others [34]. Total nitrogen, total phosphorus and ammonium are so high (Table 1).
Terminos lagoon system (TELS) is considered the largest coastal estuary in Mexico, it is located at the eastern end of the extensive and complex delta of the Usumacinta River that extends approximately 125 km along the southern coast of the Gulf of Mexico, with an average depth of 3.5 m. The TELS lies between 91°10′ and 92°00′ W longitude and parallels 18°20′and 19°00′ N latitude, in the state of Campeche. Had two marine mouths that communicate it permanently with the Gulf of Mexico [25]. The lagoon receives large volumes of fresh water that vary according to the climatic epochs in a 49,700 km2 basin. It also receives water from the Yucatan Peninsula, the lowlands of Tabasco and the highlands of Chiapas and Guatemala [35]. Three main rivers discharge their waters to the lagoon. The type of climate is warm sub-humid Amw [36] isothermal, with a rainy season from June to October, Northwinds from November to March and a dry season from April to June. It is influenced by extraordinary natural processes such as northerly and tropical storms and hurricanes [37]. The margins of the lagoon are covered by mangroves with a predominance of
Oil pollution and its derivatives are considered to be one of the biggest environmental problems in the Gulf of Mexico [40] and in its waters have been occurred the two largest oil spills at the sea, such as: the Ixtoc-1 well in the Campeche Sound and that of the Deepwater Horizon, off the coast of Louisiana, USA. Both affected significantly the diverse ecosystems of the coastal areas. Thus and in spite of the fact that the Mexican coastal lagoons settled on the margins of Veracruz, Tabasco, and Campeche, are highly productive and of high economic value. Analysis of petroleum hydrocarbons conducted in these lagoons showed important concentrations of aromatic hydrocarbons originating from the intense oil activities that develop along their coasts. In the present contribution, the updated available information on the levels of concentration of PAHs in sediments of the lagoons of Tampamachoco, Mandinga, Alvarado in the state of Veracruz and one of Terminos in Campeche is gathered. In the cases of the lagoons of Tampamachoco and Alvarado also sedimentary nuclei analysis were carried out, which give us a historical view of these pollutants for approximately 80 years old and in the same way the tendency in time that have these compounds.
The sediments of the TLS and the Tuxpan River, Veracruz, were evaluated during the end of July 2012. From the results of the 16 priority PAHs determined, the greater (1.30 μg g−1 ΣHAPs) was registered in the station located in front of the Thermoelectric Power Plant (CTPALM) and the minimum (0.02 μg g−1) in site located in the north of the lagoon body. The analysis of a sedimentary core [7] in the TLS showed an average concentration of PAHs of the nucleus of 0.98 ± 0.38 μg g−1. When analyzing the vertical distribution of the PAHs content, it was found that the historical pattern showed an increase from the basal level of the ΣPAHs of 0.29 μg g−1 at the beginning of the last century (1908), until reaching the maximum of 1.79 μg g−1 in 1999, and decrease towards the beginning of the twenty-first century in 0.58 μg g−1 (2003) to show a new increase in 2010 with 0.84 μg g−1. The compounds with the highest concentrations were, dibenzo[ah]anthracene (0.28 μg g−1), in order of decreasing followed fluorene (0.13 μg g−1) and benzo[a]anthracene (0.12 μg g−1). The molecular profile in the eight analyzed strata, changed, of petrogenic origin in 1908, to be dominated by pyrolytic compounds and to a lesser extent by petrogenic from 1999 to the present time. It should be noted that the individual concentrations of PAHs in sediments were lower than the international sedimentary quality criterion (Figure 3), with less probability of causing adverse effects to the benthic community. Thus, it can be said that there is no risk derived from the intrinsic toxicity of the coastal sediments analyzed from this group of hydrocarbons.
From the analysis of individual PAHs, it can be seen that the predominance of compounds with 3–4 rings indicates inputs of pyrolytic and petrogenic hydrocarbons from human activities around the lagoon.
In
The analysis conducted in a sediment core into ALS did not show a tendency to increase over time, possibly due to the source types of those compounds. The average sum of the 16 PAHs analyzed in the four strata was 1.84 ± 0.54 μg g−1, which indicates a downtrend from the year 1929 to 1971 (with values from 1.5 to 1.3 μg g−1), and a slight increase near the superficial stratum corresponding to the year 1998 (about 2.0 μg g−1). These values are far below the ERL index of 4.02 μg g−1. The compound with the highest value in all core strata was chrysene, except for the stratum from 26 to 36 cm, where it was below the detection limit; the highest concentration in this stratum corresponded to benzo[α]anthracene with 0.591 μg g−1, benzo[κ]fluoranthene and indeno[1,2,3,c,d]pyrene compounds were not detected by the analytical method employed for their determination [41]; only the latter showed a concentration of 0.0427 μg g−1 in the deepest stratum corresponding to the year 1929. This study showed that compounds with four aromatic rings were predominant in all core strata (Figure 2), which suggests that they were byproducts of pyrolytic processes near the study zone, such as high-temperature combustion of organic matter and fossil fuels. The sum of the four-ring PAHs presented practically the same collective tendency as the sum of the 16 quantified PAHs. This indicates that the contribution to the entire historical profile of both five and six-ring PAHs, as well as two and three-ring ones (which originate from petrogenic sources associated to drilling activities, such as oil extraction and oil spills), was minor (Figure 2).
ALS core concentrations of PAHs (μg g−1) based on number of aromatic rings.
Most of the PAHs in the sediments proceed from pyrolytic sources, while the sources of compounds consisting of two and three rings are of petrogenic origin. The total PAHs sum was mostly contributed to by compounds consisting of four benzene rings, namely chrysene. Despite slightly higher than ERL index concentrations for anthracene, acenaphthylene, fluorene and dibenzo[α,h]anthracene, the total PAH sum did not exceed that limit. It has to be pointed that human activities are very intense in the lagoon as fisheries, shipping port, storage of petroleum and agriculture.
On the other hand, TELS has been intensively studied for organic and inorganic pollutants due to its importance as a fisheries center. Thus, Ref. [42] indicates the presence of PAHs in sediments and oysters of this lagoon, reported PAHs in oyster tissue and the predominance of alkylated compounds of medium and low molecular weight indicating a petrogenic origin attributed basically to off-shore oil activities. This lagoon it is located in front of the main oil wells in the Bank of Campeche were the most intense exploration and exploitation of crude oil takes place.
Another study of PAHs performed on fish tissue from the western zone of TELS, showed that its concentrations exceeded the values maximum recommended by international regulation (greater than 40.0 μg g−1) for the
Individual PAHs and ERL sedimentary quality criteria in the sedimentary core of TLS.
The investigations on metals in sediments that have been carried out in three of the main coastal lagoons of the Veracruz state, show significant results: the Cd registered similar concentrations for the TLS and MLS with values of 0.46 and 0.66 μg g−1 respectively, and these values were below the ERL that is 1.2 μg g−1, levels that produce adverse biological effects in sediments [43]. On the other hand, the highest concentration of Cr was for the TLS with 20.52 μg g−1, the concentrations for ALS and MLS registered similar values with 13 μg g−1. The concentrations for the three lagoons were below the limit of the ERL which is 81 μg g−1. The Cu values for MLS and ALS were 15.77 and 17.49 μg g−1 respectively. These also stayed below the ERL which is 34 μg g−1. The Pb showed values for MLS and ALS of 23.37 and 27.49 μg g−1, while for TLS they recorded lower values (11.42 μg g−1). The concentrations of this metal in the three lagoons remained below the ERL which is 46.7 μg g−1. They report that Zn showed similar values for ALS and MLS with 55.81 and 56.14 μg g−1 respectively, and their concentrations were below the ERL which is 150 μg g−1. The Ni was presented with values of 71.80 and 72.26 μg g−1 in the lagoons of ALS and MLS respectively, and which are above the ERL which is 20.9 μg g−1. The enrichment of Ni in the surface sedimentary substrate is due to the contribution of urban discharges from urban discharges and industries that are close to the coastal areas where the present study was conducted (Figure 4) [1, 44].
Average concentrations of metals in superficial sediments of coastal lagoons of the Veracruz state.
Villanueva and Ramirez [6] carried out the determination of Cd, Cr, Ni, Pb and V in sediments of the TLS, collected in seven stations. The concentrations decreased in the following order Cr > Ni > Pb > V > Cd, where the latter has not increased since 2010. Although Cd and Pb did increase in 2012, the determined values did not exceed the ecological criteria of the minimum and maximum adverse conditions for the biota (ERL and ERM), while the levels of Ni decreased compared to 2010, since they have a direct influence of the terrestrial and riparian drainages, which present higher hydrodynamics and a greater mixture due to the salt wedge coming from the sea. Likewise, there were no specific changes in metal concentrations between the years 1985 and 1988, the period in which the Thermoelectric Power Plant was built and started to operate. In the period from 1996 to 2012, the concentrations of Cd, Cr and Pb showed slight increases, while the Ni showed variation. Similarly, Vazquez-Botello et al. [23] performed the analysis of a sedimentary core in this lagoon, which concludes that there is a tendency to increase from the oldest stratum (1908) with surface maximums, the values of Ni and Pb are below the concentrations reported in Literature for other coastal and lacustrine systems. The basal values of Cd (0.22 μg g−1), Cr (31 μg g−1), Ni (26 μg g−1) and Pb (12 μg g−1) were also determined. From previous reports, becomes clear that the atmospheric transport is one of the main sources of Pb towards the lagoons, rivers, and oceans; and this is reflected in its levels in the sediments of the lagoons studied. For which it is recommended to analyze sedimentary nuclei and determine the origin of it. Also, the Ni detected in the studied lagoons, has a mixed origin: one part is of lithological origin and another part from the urban discharges through the particulate solids, as well as through the use of fertilizers and the mining industry and steel, and whose concentration surpasses the ELR and ERM values proposed by Long et al. [43] to the up to 100%, causing enrichment of the sedimentary substrate analyzed.
The data for organochlorine pesticides (OC) are presented in sediments of the lagoon systems considered in this study. The TLS has records of these agrotoxics of three practically continuous annual cycles (2009, 2010 and 2012), while the remaining ecosystem data correspond to a particular year; the values are given in ng g−1 dry weight. Figure 5 shows the total data of the OC (ΣOC) reported in sediments of these coastal lagoons. For ALS the sediments evaluated in 2009 occupy the first place with a value of 36.2 ng g−1 [3] while in lower concentrations were TLS in the same year with 13.3 ng g−1 decreasing to 4 ng g−1 in 2012 and the lowest total concentration of organochlorines was for the TELS with 0.18 ng g−1 [4]. This marked difference between lagoon systems in the same coastal region of Mexico may be due to the local uses of these agrochemicals, as well as to the particular conditions of temporary runoff and large permanent flows and to the human activities carried out in the nearby of these ecosystems. The area of continental influence of the ALS has a great agricultural activity mainly due to the sugarcane plantations and its main tributaries, the Blanco and Papaloapan rivers, that cross several hundred kilometers of cultivation areas ending in this lagoon. Thus, the suspended material with large amounts of organic matter and a high probability of carrying adsorbed pesticides are finally stored in the lagoon sediments. On the other hand, the hydrodynamics of the TLS is contrasted since human activity in this area is more urban and industrial, and applying pesticides as vector control and to a lesser extent to the agricultural use. The TELS in the south of the GoM, has greater dimensions and a great interaction with the GoM in the replacement of its body of water, as well as a more estuarine environment due to the mixture with tributaries of the flow fluvial Grijalva-Usumacinta which can contribute with materials and energy to the lagoon system and likewise export to the GoM what can explain the low concentration of reported OC.
Total concentration of organochlorine pesticides (ΣOC) in coastal lagoon sediments of three Mexican systems, Tampamachoco, Alvarado and Terminos in the Gulf of Mexico. Values in ng g−1 dry weight.
The diversity of OC reported for these three Mexican lagoon systems is presented in Figure 6, where 16 representative compounds of the three major chemical families were registered: alicyclic or Lindane group, aromatics or conglomerate of DDT and cyclodienes the most diverse group that includes the “Drines,” Heptachlor and Endosulfan. The highest data corresponded to the ALS, the
Individual pattern of organochlorine pesticides in coastal lagoon sediments of three Mexican systems, Tampamachoco, Alvarado and Terminos in the Gulf of Mexico. Values in ng g−1 dry weight.
Because there are no maximum permissible limits for OC in coastal sediments in Mexico, it is important to consider the international sedimentary quality criteria that environmental agencies such as the NOAA of the United States of America have as the reference [46]. In this sense, the concentrations reported for lindane or the gamma-HCH isomer were higher than the threshold concentration or TEL by its acronym in English, of 0.32 ng g−1 to cause adverse effects to estuarine benthos for the coastal system TLS of 2009 and ALS of the same year and also in the first case was also greater than the criterion of probable alteration known as PEL of 0.99 ng g−1, so it can be considered a scenario of real anthropogenic environmental alteration and of potential risk to human health since various benthic organisms of these coastal sites are for food consumption [47]. Another similar case is that which occurs for
The study and protection of coastal systems, such as coastal lagoons, wetlands, and estuaries, should be a priority for countries that have benefited from an extensive coastal zone such as Mexico. However, the accelerated development and industrialization of these areas have led to processes of degradation and alteration in these important systems.
Although Mexican coastal lagoons are important sites for fishing, aquaculture, the development of communities and that provide economic resources of great value, reports on increasing levels not only in nutrients, hydrocarbons, metals and pesticides two, that appear in the literature every day and lately plastics and microplastics that impact them and put at risk environmental and human health.
The coastal system of Gulf of Mexico has different climate, morphology and complex river flow which discharges to the lagoons, resulting in wide natural physicochemical water composition, but it must be considered the high urban settlement with their economic activities as different industry that incremented the concentration of certain chemical compounds. This is the case of inorganic nutrients that in the present work included four coastal aquatic system (Tampamachoco, Mandinga, Alvarado and Terminos lagoons), all of them with a eutrophication conditions by high total nitrogen, total phosphorus and ammonium result of urban, agriculture and others economic activities, settlement in the margin of the river and lagoons and the residual water that are dispose to this system. This situation is in a great number of many lagoon system in the Gulf of Mexico; for example: la Mancha, Farallon, El Llano and El Verde located at the north of the Gulf of Mexico, in which were register high concentration of nitrogen, phosphorus and ammonia that result in eutrophication two [40, 48].
The results on PAHs indicate that these compounds are widely distributed in coastal areas and are stored in lagoons, estuaries, and wetlands. There is abundant literature on this [49] and thanks to the use of sedimentary cores we know that these pollutants have been introduced to the lagoons more than 50 years ago and that their presence can originate as waste from oil activities or by the pyrolysis such as volcanism, burning of coal, burning of pastures and forest fires. Regarding its presence, the dominant PAHs are formed by four rings (pyrolytic) such as chrysene, benzo[a]anthracene, benzo[k]fluoranthene and benzo[b]fluoranthene. In general, their concentrations do not exceed the criterion of maximum concentration to cause adverse biological effects [46].
Comparing the concentrations of metals in the sediments listed in Table 2, the Yucateco and Mecoacan lagoons report high levels with respect to the three lagoons considered in this study. The Cd presented up to an order of magnitude higher (1.84 and 1.46 μg g−1), this shows that Cd has a lithological as well as anthropogenic origin. The Cr and Pb are up to 100% above the areas of this study (36.32 and 48.30 μg g−1), while Pb has a natural origin, by atmospheric transport, as well as anthropogenic. However, the V was the one that reported the highest concentrations in the Mecoacan lagoon with 18.78 μg g−1. What is clear is that part of the Ni and V has their origin in the composition of the dominant oil in the area. These levels can be considered normal and expected, since there are oil wells in the vicinity of the Yucateco lagoon and Mecoacan lagoon. In Table 2, it is clearly observed how the variations in the concentrations of the metals analyzed are influenced by the activities carried out in each of the surrounding areas, as well as the special and temporary hydrodynamic predominant according to the different seasons of the year [50, 51].
Pollutants | |||||||||
---|---|---|---|---|---|---|---|---|---|
Area | PAHs (μg g−1) | Cd (μg g−1) | Cr (μg g−1) | Cu (μg g−1) | Pb (μg g−1) | Ni (μg g−1) | V (μg g−1) | Zn (μg g−1) | OC (ng g−1) |
Tampa-machoco lagoon system (TLS) | 0.98 | 0.46 | 20.52 | N.D | 11.42 | 31.11 | 13.91 | N.D | 19.65 |
Mandinga lagoon system (TLS) | 5.68 | 0.66 | 13.00 | 15.77 | 23.37 | 72.26 | N.D | 56.14 | NR |
Alvarado lagoon system | 2.00 | N.D | 13.75 | 17.49 | 27.49 | 71.80 | N.D | 55.81 | 36.21 |
Terminos lagoon system (TELS) | 6.12 | 0.18 | |||||||
Yucateco lagoon, Tabasco state | 3.85 | 1.84 | 36.32 | 48.30 | 53.90 | 1.61 | 57.71 | ||
Mecoacan, Tabasco state | 0.15 | 1.47 | 28.93 | 21.22 | 58.94 | 18.78 | 5.1 |
Average levels of pollutants in sediments of the four lagoons analyzed.
The analysis carried out to determine the presence of OC in sediments of various coastal lagoon ecosystems of the Gulf of Mexico, provides information on the anthropogenic alteration that has been occurring for several years on these sites, given the lack of vigilance on the part of the Mexican environmental authorities in order to avoid the use of banned pesticides and internationally designated as highly dangerous, so it is urgent to modify agricultural practices, and to promote the integrated management of pests that include biological control and agroecology [52]. For comparison purposes, in Table 2, OC data from two tropical coastal lagoons of the Gulf of Mexico were integrated, the first being El Yucateco, whose history of anthropogenic impact has been remote since 1950 at the beginning of oil exploration and exploitation. The second is Mecoacán, considered the area of greatest fishing production in this Mexican coastal region, both located in the tropical state of Tabasco. The data of the ΣOC recorded in the recent sediments of El Yucateco were the highest in the comparison, with a value of 57.71 ng g−1 and the high presence of beta-HCH one of the highly persistent isomers of Lindane as an unequivocal trace of the use commercial of this acaricide, as well as high levels of Heptachlor epoxide, records of other cyclodienes, mainly Aldrin, Endosulfan sulfate as a product of biogeochemical transformation of the commercial product Endosulfan and the whole group of DDT with higher prevalence of
The difference physicochemical characteristic and pollutants concentrations of analyzed in the coastal lagoons of the Gulf of Mexico are due to the biochemical behavior, climatic factors and, of course, the industrial and urban discharges that reach these lagoons over time. Other factors are the morphology of the coastal lagoons, presence of mangrove isles that can serve as traps of inorganic or organic matter and pollutants retention. In general, it is considered that urban wastewater constituted the most important source of nutrients which tendency to eutrophication in those lagoons.
This urban wastewater constitutes the most important source of metals in rivers and lagoons two. These effluents consist of (1) untreated or mechanically treated waters only; (2) substances which have passed through filters and biological treatment plants, either solubilized or as finely divided particles; and (3) substances that are served by an emitter and that discharge to the coastal zone. The solid particles of wastewater from coastal cities cause the enrichment of metals, such as Cr, which can have high concentrations, as well as the use of chromates in petrochemical processes during oil extraction. It is worth mentioning that there are numerous studies on the role of atmospheric transport as a source of pollutants (metals, pesticides and aromatic hydrocarbons) and the one that stands out is the contribution of Pb which has been demonstrated in the ice of the North Pole and Greenland, where concentrations of 0.200 μg Pb/kg of ice [56]. The foregoing reveals the fact that the atmospheric contribution, far from being assumed insignificant, even becomes the main source of supply of some pollutants for coastal systems. However, the accelerated development of certain economic activities such as the oil industry, energy generation, tourism, agricultural development and maritime transport have led to disorderly growth in the national coastal areas, with consequent environmental conflicts arising from competition for space, the use of resources and the generation of toxic and polluting waste. Indeed, the conflicts that affect the quality of life and decrease the competitiveness of the same sectors and their economic activities.
We thank Salvador Hernandez Pulido for his support in the elaboration of the figures and bibliographic search.
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Oxidative stress has been considered a major contributory factor to the diseases. They are mainly derived from oxygen (reactive oxygen species (ROS)) and nitrogen (reactive nitrogen species (RNS)) and are generated in our body by various endogenous systems and exposure to different physicochemical conditions or pathophysiological states. Free radical damage to protein can result in loss of enzyme activity. There are epidemiological evidences correlating higher intake of components/foods with antioxidant abilities to lower incidence of various human morbidities or mortalities. The sources and origin of antioxidants which include fruits and vegetables, meats, poultry, and fish were treated in this study. The classification and characteristics of antioxidant, its measurements and level in food and free radicals, were also documented. 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The whole process of submitting an article and editing of the submitted article goes extremely smooth and fast, the number of reads and downloads of chapters is high, and the contributions are also frequently cited.",author:{id:"55578",name:"Antonio",surname:"Jurado-Navas",institutionString:null,profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bRisIQAS/Profile_Picture_1626166543950",slug:"antonio-jurado-navas",institution:{id:"720",name:"University of Malaga",country:{id:null,name:"Spain"}}}}]},series:{item:{id:"6",title:"Infectious Diseases",doi:"10.5772/intechopen.71852",issn:"2631-6188",scope:"This series will provide a comprehensive overview of recent research trends in various Infectious Diseases (as per the most recent Baltimore classification). Topics will include general overviews of infections, immunopathology, diagnosis, treatment, epidemiology, etiology, and current clinical recommendations for managing infectious diseases. 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He is the president of the Travel Medicine Committee of the Pan-American Infectious Diseases Association (API), as well as the president of the Colombian Association of Infectious Diseases (ACIN). He is a member of the Committee on Tropical Medicine, Zoonoses, and Travel Medicine of ACIN. He is a vice-president of the Latin American Society for Travel Medicine (SLAMVI) and a Member of the Council of the International Society for Infectious Diseases (ISID). Since 2014, he has been recognized as a Senior Researcher, at the Ministry of Science of Colombia. He is a professor at the Faculty of Medicine of the Fundacion Universitaria Autonoma de las Americas, in Pereira, Risaralda, Colombia. He is an External Professor, Master in Research on Tropical Medicine and International Health, Universitat de Barcelona, Spain. He is also a professor at the Master in Clinical Epidemiology and Biostatistics, Universidad Científica del Sur, Lima, Peru. In 2021 he has been awarded the “Raul Isturiz Award” Medal of the API. Also, in 2021, he was awarded with the “Jose Felix Patiño” Asclepius Staff Medal of the Colombian Medical College, due to his scientific contributions to COVID-19 during the pandemic. He is currently the Editor in Chief of the journal Travel Medicine and Infectious Diseases. His Scopus H index is 47 (Google Scholar H index, 68).",institutionString:"Institución Universitaria Visión de las Américas, Colombia",institution:null},editorTwo:null,editorThree:null},subseries:{paginationCount:12,paginationItems:[{id:"38",title:"Pollution",coverUrl:"https://cdn.intechopen.com/series_topics/covers/38.jpg",editor:{id:"110740",title:"Dr.",name:"Ismail M.M.",middleName:null,surname:"Rahman",slug:"ismail-m.m.-rahman",fullName:"Ismail M.M. Rahman",profilePictureURL:"https://mts.intechopen.com/storage/users/110740/images/2319_n.jpg",biography:"Ismail Md. Mofizur Rahman (Ismail M. M. 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He also achieved a Diploma in Environment from the Tokyo Institute of Technology, Japan (2005). Besides, he has an M.Sc. degree in Applied Chemistry and a B.Sc. degree in Chemistry, all from the University of Chittagong, Bangladesh. \nDr. Rahman’s research interest includes the study of the fate and behavior of environmental pollutants in the biosphere; design of low energy and low burden environmental improvement (remediation) technology; implementation of sustainable waste management practices for treatment, handling, reuse, and ultimate residual disposition of solid wastes; nature and type of interactions in organic liquid mixtures for process engineering design applications.",institutionString:null,institution:{name:"Fukushima University",institutionURL:null,country:{name:"Japan"}}},editorTwo:{id:"201020",title:"Dr.",name:"Zinnat Ara",middleName:null,surname:"Begum",slug:"zinnat-ara-begum",fullName:"Zinnat Ara Begum",profilePictureURL:"https://mts.intechopen.com/storage/users/201020/images/system/201020.jpeg",biography:"Zinnat A. Begum received her Ph.D. in Environmental Analytical Chemistry from Kanazawa University in 2012. She achieved her Master of Science (M.Sc.) degree with a major in Applied Chemistry and a Bachelor of Science (B.Sc.) in Chemistry, all from the University of Chittagong, Bangladesh. Her work affiliations include Fukushima University, Japan (Visiting Research Fellow, Institute of Environmental Radioactivity: Mar 2016 to present), Southern University Bangladesh (Assistant Professor, Department of Civil Engineering: Jan 2015 to present), and Kanazawa University, Japan (Postdoctoral Fellow, Institute of Science and Engineering: Oct 2012 to Mar 2014; Research fellow, Venture Business Laboratory, Advanced Science and Social Co-Creation Promotion Organization: Apr 2018 to Mar 2021). 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Graduate in Sciences (Chemist), graduate in Geography and History (Geography), master in Water Management, Treatment, master in Fertilizers and Environment and master in Environmental Management; Ph.D. in Environmental Sciences. His research is focused on soil-water and waste-environment relations, mainly on soil-water and soil-waste interactions under different management and waste reuse. His work is reflected in more than 230 communications presented in national and international conferences and congresses, 29 invited lectures from universities, associations and government agencies. Prof. Navarro-Pedreño is also a director of the Ph.D. Program Environment and Sustainability (2012-present) and a member of several societies among which are the Spanish Society of Soil Science, International Union of Soil Sciences, European Society for Soil Conservation, DessertNet and the Spanish Royal Society of Chemistry.",institutionString:"Miguel Hernández University of Elche, Spain",institution:null},editorTwo:null,editorThree:null,editorialBoard:[{id:"177015",title:"Prof.",name:"Elke Jurandy",middleName:null,surname:"Bran Nogueira Cardoso",slug:"elke-jurandy-bran-nogueira-cardoso",fullName:"Elke Jurandy Bran Nogueira Cardoso",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bRGxzQAG/Profile_Picture_2022-03-25T08:32:33.jpg",institutionString:"Universidade de São Paulo, Brazil",institution:null},{id:"147289",title:"Prof.",name:"Francisco",middleName:null,surname:"Guevara-Hernández",slug:"francisco-guevara-hernandez",fullName:"Francisco Guevara-Hernández",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bRCgVQAW/Profile_Picture_2022-06-27T11:25:21.png",institutionString:null,institution:{name:"Autonomous University of Chiapas",institutionURL:null,country:{name:"Mexico"}}},{id:"211260",title:"Dr.",name:"Sandra",middleName:null,surname:"Ricart",slug:"sandra-ricart",fullName:"Sandra Ricart",profilePictureURL:"https://mts.intechopen.com/storage/users/211260/images/system/211260.jpeg",institutionString:null,institution:{name:"University of Alicante",institutionURL:null,country:{name:"Spain"}}}]},{id:"40",title:"Ecosystems and Biodiversity",coverUrl:"https://cdn.intechopen.com/series_topics/covers/40.jpg",editor:{id:"209149",title:"Prof.",name:"Salustiano",middleName:null,surname:"Mato",slug:"salustiano-mato",fullName:"Salustiano Mato",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bRLREQA4/Profile_Picture_2022-03-31T10:23:50.png",biography:"Salustiano Mato de la Iglesia (Santiago de Compostela, 1960) is a doctor in biology from the University of Santiago and a Professor of zoology at the Department of Ecology and Animal Biology at the University of Vigo. 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He is presently associate editor of Water International (official journal of the International Water Resources Association). He was also invited to serve as an associate editor for special issues of the Journal of the American Water Resources Association. He has served as an editorial member for international journals such as Hydrology, Journal of Ecology & Natural Resources, and Hydro Science & Marine Engineering, among others. He has chaired or acted as a technical committee member for twenty-five international forums (conferences). Dr. Shang graduated from Tsinghua University, China, in 2010 with a Ph.D. in Engineering. Prior to that, he worked as a research fellow at Harvard University from 2008 to 2009. Dr. Shang serves as a senior research engineer at the China Institute of Water Resources and Hydropower Research (IWHR) and was awarded as a distinguished researcher at National Taiwan University in 2017.",institutionString:"China Institute of Water Resources and Hydropower Research",institution:{name:"China Institute of Water Resources and Hydropower Research",institutionURL:null,country:{name:"China"}}},editorTwo:null,editorThree:null,editorialBoard:[{id:"216491",title:"Dr.",name:"Charalampos",middleName:null,surname:"Skoulikaris",slug:"charalampos-skoulikaris",fullName:"Charalampos Skoulikaris",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bRMsbQAG/Profile_Picture_2022-04-21T09:31:55.jpg",institutionString:null,institution:{name:"Aristotle University of Thessaloniki",institutionURL:null,country:{name:"Greece"}}},{id:"300124",title:"Prof.",name:"Thomas",middleName:null,surname:"Shahady",slug:"thomas-shahady",fullName:"Thomas Shahady",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002kuIgmQAE/Profile_Picture_2022-03-18T07:32:10.jpg",institutionString:null,institution:{name:"Lynchburg College",institutionURL:null,country:{name:"United States of America"}}}]}]},overviewPageOFChapters:{paginationCount:10,paginationItems:[{id:"82380",title:"Evolution of Parasitism and Pathogenic Adaptations in Certain Medically Important Fungi",doi:"10.5772/intechopen.105206",signatures:"Gokul Shankar Sabesan, Ranjit Singh AJA, Ranjith Mehenderkar and Basanta Kumar Mohanty",slug:"evolution-of-parasitism-and-pathogenic-adaptations-in-certain-medically-important-fungi",totalDownloads:6,totalCrossrefCites:0,totalDimensionsCites:0,authors:null,book:{title:"Fungal Infectious Diseases - Annual Volume 2022",coverURL:"https://cdn.intechopen.com/books/images_new/11400.jpg",subseries:{id:"4",title:"Fungal Infectious Diseases"}}},{id:"82367",title:"Spatial Variation and Factors Associated with Unsuppressed HIV Viral Load among Women in an HIV Hyperendemic Area of KwaZulu-Natal, South Africa",doi:"10.5772/intechopen.105547",signatures:"Adenike O. 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Saxena",hash:"105e347b2d5dbbe6b593aceffa051efa",volumeInSeries:1,fullTitle:"Influenza - Therapeutics and Challenges",editors:[{id:"158026",title:"Prof.",name:"Shailendra K.",middleName:null,surname:"Saxena",slug:"shailendra-k.-saxena",fullName:"Shailendra K. Saxena",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bRET3QAO/Profile_Picture_2022-05-10T10:10:26.jpeg",biography:"Professor Dr. Shailendra K. Saxena is a vice dean and professor at King George's Medical University, Lucknow, India. His research interests involve understanding the molecular mechanisms of host defense during human viral infections and developing new predictive, preventive, and therapeutic strategies for them using Japanese encephalitis virus (JEV), HIV, and emerging viruses as a model via stem cell and cell culture technologies. His research work has been published in various high-impact factor journals (Science, PNAS, Nature Medicine) with a high number of citations. 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