",isbn:"978-1-80356-441-8",printIsbn:"978-1-80356-440-1",pdfIsbn:"978-1-80356-442-5",doi:null,price:0,priceEur:0,priceUsd:0,slug:null,numberOfPages:0,isOpenForSubmission:!0,isSalesforceBook:!1,isNomenclature:!1,hash:"9117bd12dc904ced43404e3383b6591a",bookSignature:"Assistant Prof. Erik Froyen",publishedDate:null,coverURL:"https://cdn.intechopen.com/books/images_new/11669.jpg",keywords:"Total Cholesterol, Triglycerides, Seizures, Epilepsy, Low-Fat Diet, High-Fat Diet, Cardiovascular Disease, Saturated Fatty Acids, Monounsaturated Fatty Acids, Polyunsaturated Fatty Acids, Fat Food Sources, Omega-3 Fatty Acids",numberOfDownloads:8,numberOfWosCitations:0,numberOfCrossrefCitations:0,numberOfDimensionsCitations:0,numberOfTotalCitations:0,isAvailableForWebshopOrdering:!0,dateEndFirstStepPublish:"March 1st 2022",dateEndSecondStepPublish:"May 3rd 2022",dateEndThirdStepPublish:"July 2nd 2022",dateEndFourthStepPublish:"September 20th 2022",dateEndFifthStepPublish:"November 19th 2022",dateConfirmationOfParticipation:null,remainingDaysToSecondStep:"2 months",secondStepPassed:!0,areRegistrationsClosed:!1,currentStepOfPublishingProcess:3,editedByType:null,kuFlag:!1,biosketch:"An assistant professor in the Department of Nutrition and Food Science at California State Polytechnic University, Pomona, with multiple publications and presentations on the mechanisms by which fatty acids impact the risk factors for cardiovascular disease.",coeditorOneBiosketch:null,coeditorTwoBiosketch:null,coeditorThreeBiosketch:null,coeditorFourBiosketch:null,coeditorFiveBiosketch:null,editors:[{id:"415310",title:"Assistant Prof.",name:"Erik",middleName:null,surname:"Froyen",slug:"erik-froyen",fullName:"Erik Froyen",profilePictureURL:"https://mts.intechopen.com/storage/users/415310/images/system/415310.jpg",biography:"Erik Froyen is an assistant professor in the Department of Nutrition and Food Science at California State Polytechnic University, Pomona. 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\n
1. Introduction
\n
1.1. Basic steroid chemistry and relevance of oxygenated steroids
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Steroid compounds are found in almost all living organisms [1, 2], having an important role in their vital activity [1–4]. The steroid hormones were discovered and characterized during the 1930s, and since then, it has been realized that steroid compounds can control important physiopathological conditions, being therefore important starting point for the development of new medicines [3]. Indeed, several natural and synthetic steroids are important therapeutic options for a wide range of diseases. These include sex and corticosteroid hormones, bile acids, vitamin D derivatives, and cardiotonic steroids, among others, that have shown unique therapeutic value for a broad array of medical conditions [1]. Due to their relevance, over the last decades, hundreds of steroid compounds have been isolated from natural sources, whereas many thousands of them have been obtained synthetically [2, 4] and their study has continued until present days in both chemical and biological perspectives.The steroidal basic structure constitutes a common chemical skeleton of four fused rings, consisting of three six-membered rings and a five-membered ring [1, 2, 5]. This hydrocarbon scaffold contains 17 carbons and has the cyclopentaneperhydrophenanthrene basic structure. The four steroid rings are labeled as A, B, C and D and their carbon atoms are numbered according to the universal convention according to the IUPAC-IUB (International Union of Pure and Applied Chemistry/International Union of Biochemistry) Joint Commission on Biochemical Nomenclature [6]. Angular methyl groups at C13 and C10 are designated as 18-CH3 and 19-CH3, respectively, and alkyl substituents at C17 are the steroid side-chain. The 18- and 19-methyl groups stand above the plane of the steroid skeleton and, by convention, have β-configuration. Therefore, as stated, other atoms or substituents located above this plane also have β-configuration, while those below it have α-configuration (Figure 1) [1, 2, 5, 6].
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Figure 1.
Chemical structure of the 5α-cholestane nucleus.
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The preparation of steroids containing oxygenated functions in the steroid nucleus is of high relevance and can be performed by means of several oxidative processes. Among the large variety of available methods, the allylic oxidation and epoxidation of alkenes and the alcohol oxidation are probably the most commonly used oxidative transformations [1, 2]. In fact, the allylic oxidation of steroidal alkenes to the corresponding enones, such as Δ5-7-ketones, is of great importance because of their significant biological properties. The diastereoselective epoxidation of steroidal alkenes is a relevant challenge because of the difficulty in the preparation of pure epoxides. This transformation is also very important not only because the epoxide moiety is of high synthetic interest for further elaboration but also because this functionality has been found in several biologically active steroids. The oxidation of steroidal alcohols is also considered in this chapter. A relevant example of high industrial interest is the transformation of Δ5-3β-hydroxylated steroids into the corresponding Δ4-3-ketones, a typical functionality of the major class of steroidal hormones [1, 2].
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1.2. The green chemistry concept and green nanotechnologies
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According to the Environmental Protection Agency, green or sustainable chemistry has been defined as “the design of chemical products and processes that reduce or eliminate the use or generation of hazardous substances” [7]. In fact, over the years, a large development in this field was observed and several new greener procedures are now being used in the chemical industry [8]. In the pharmaceutical industry, due to the complexity of the products involved as well as the characteristics/issues associated with their uses, the application of the green chemistry principles in the production of medicines has been an enormous challenge [8, 9]. Considering that the major sources of waste in the chemical/pharmaceutical industry are the use of stoichiometric reagents and solvent losses, and the clear solution to this problem is the development of catalytic reactions in alternative reaction media. Additionally, the possibility of recovery and reuse of the reactants/catalysts/solvents and the use of inexpensive, renewable and non-toxic materials are key issues in this context. Accordingly, over the years several greener approaches for the majority of chemical reactions have been developed [10–12].
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The development of catalytic processes has been the most explored strategy in green and sustainable chemistry, avoiding the use of numerous hazardous and/or expensive stoichiometric reactants. According to their nature, catalysts can be classified as metallic, organometallic, organocatalysts and biocatalysts. On the other hand, based on their physical state, catalysts can be grouped as homogeneous and heterogeneous [10–13]. In this context, the use of heterogeneous catalysts (either metallic or non-metallic) has the important advantage of allowing their recovery and reuse [14, 15]. Furthermore, of major relevance in the pharmaceutical industry is the synthesis of organic compounds devoid of metal contamination, which can be achieved by using organo- [16, 17] and biocatalytic [18] procedures. Biocatalysis also has several advantages in the context of green chemistry, including the fact that reactions are frequently performed under mild conditions of temperature, pressure and pH and using water as solvent. Moreover, the catalyst is biodegradable and derived from renewable raw materials. Noteworthy, biocatalysis frequently leads to higher chemo-, regio- and stereoselectivities, than traditional chemical processes [10].
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A special advance in green chemistry is the use of nanotechnologies. According to McKenzie and Hutchison, “Green nanoscience/nanotechnology involves the application of green chemistry principles to the design of nanoscale products, the development of nanomaterial production methods, and the application of nanomaterials” [19]. In organic chemical synthesis, the main application of this concept is the use of nanomaterials as nanocatalysts, being considered sustainable alternatives to conventional materials. In fact, the nanosized particles can offer some of the advantages of homogeneous catalysts because of an increased exposed surface area of the active component of the catalyst, which enhances dramatically the contact between reactants and catalyst. In addition, similarly to heterogeneous catalysts, their insolubility in the reaction solvents renders them easily separable from the reaction mixture, which consequently makes the product isolation stage effortless. Moreover, the activity and selectivity of nanocatalysts can be manipulated by tailoring chemical and physical properties such as size, shape, composition and morphology [20]. Due to these interesting properties, the use of nanocatalysts has been increasing over the years [21].
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Solvent selection is another important issue in the development of new synthetic processes, in the chemical and pharmaceutical industries [8, 22]. Actually, the highest part of the material usage for active pharmaceutical ingredient (API) manufacture is usually constituted by solvents. In fact, it was estimated that their use consumes more than 50% of the overall energy and accounts for half of the post-treatment green-house gas emissions. Ideally, reactions should be performed without any solvent (neat conditions). However, solvents are critical for the reaction rates and selectivities and are often required for heat and mass transfer. Consequently, solvents should be readily available, non-volatile, non-flammable, non-toxic, recyclable and cheap [8, 10, 22]. Attractive solvents from both economical and environmental point of view can include water [23, 24], ionic liquids [25, 26], fluorous solvents [27] as well as supercritical fluids (e.g., supercritical CO2) [28, 29].
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Green chemistry also deals with the minimization of energy usage. In fact, the addition of energy, mostly thermal, is necessary for the majority of organic reactions. For this reason, the strategy to develop chemical transformations under mild reaction conditions has been exploring alternative energy sources such as microwaves (MW), ultrasounds and even light [11, 12, 30]. In fact, successful advances have been made over the years mainly on MW-promoted reactions [30, 31] but also on sonochemistry [30, 32] and photochemistry [33].
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1.3. Scope and organization of this chapter
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Due to the above referred biological and synthetic importance of steroids, several new green chemical processes for the preparation and/or functionalization of the steroid nucleus have also been developed over the years [34, 35]. In this chapter, relevant applications of green oxidative chemical processes in steroid chemistry are described. Special emphasis is given to catalytic processes involving the use of heterogeneous catalysts, including nanocatalysts. Other green approaches, such as MW technologies as well as the use of ionic liquids as solvents, are presented. This chapter is organized according to the reaction type that includes alcohol oxidation, epoxidation, allylic oxidation and miscellaneous oxidative transformations.
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\n
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2. Alcohol oxidation
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The most common oxidative transformation in steroid chemistry is probably the oxidation of alcohols [34, 35]. Actually, not only several important natural and synthetic steroids have carbonyl groups but also this oxidation is frequently used as an intermediary step in the preparation of a large variety of bioactive steroids. For this reason, several oxidative processes for this reaction have been developed over the years. The most employed oxidants are transition metals, particularly chromium(VI) reagents. Nonetheless, other oxygen- and halogen-based oxidants as well as other oxidizing conditions, frequently combined with suitable catalysts, have been described [34, 35].
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As a relevant example, a heterogeneous catalyst described for the successful oxidation of 5α-cholestan-3β-ol to 5α-cholestanone (Scheme 1) was chromium exchanged zeolite (CrE-ZSM-5) combined with 70% aqueous tert-butyl hydroperoxide (TBHP), an oxygen-based oxidant. However, it was shown that the reaction was, at least partially, homogeneously catalyzed by leached chromium [36]. Recently, metal-monocatecholate species were immobilized in a Zr(IV)-based metal-organic framework (MOF) to create new efficient heterogeneous catalysts. Within these, Cr-metalated MOFs revealed to be useful in the oxidation of a wide range of alcohols to ketones with TBHP (80% TBHP in di-t-butyl peroxide/water 3:2 solution). Catalysis could be achieved with very low metal loadings (0.5−1 mol %), and these MOF-based catalysts were completely recyclable and reusable [37]. In spite of the fact that 5α-cholestan-3β-ol is too large to diffuse into the pore cage of this catalyst, this steroidal alcohol was also efficiently oxidized with this system and probably the catalysis occurred on the surface of the particles. The oxidation of several alcohols, including cholesterol (Scheme 1), was also reported in aqueous conditions using the same oxidant and vanadyl sulfate as catalyst. Noteworthy, after completion of the oxidation and isolation of the product by extraction, the catalyst was recovered in the aqueous layer and reused in a new reaction by simply adding CH3CN, substrate and TBHP [38]. The immobilization of a RuCl3 complex in an aluminum metal-organic framework (MOF), MOF-253, by post-synthetic modification, afforded an heterogeneous catalyst (MOF-253-Ru) that was used in the oxidation of primary and secondary alcohols with PhI(OAc)2 as the oxidant, under very mild reaction conditions. When applied to 5α-cholestan-3β-ol (Scheme 1), a fast and high-yielding reaction was observed and after 4 hours of reaction, the corresponding ketone was obtained in 89% yield. Interestingly, due to the structure of the catalyst, it seems that its pore size is large enough to accommodate this complex substrate. Moreover, the MOF-253-Ru could be successively recycled up to six times without significant loss of activity [39].
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Scheme 1.
Oxidation of 5α-cholestan-3β-ol and cholesterol to the corresponding 3-ketone derivatives.
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Of high interest in the context of green chemistry is the use of molecular oxygen combined with recoverable and reusable heterogeneous catalysts in the transformation of alcohols to carbonyl compounds. An important example is the use of the heterogeneous Pd catalyst consisting on the palladium(II) acetate-pyridine complex supported on hydrocalcite in the aerobic oxidation of 5α-cholestan-3β-ol (Scheme 1) by air at atmospheric pressure as the sole oxidant under mild conditions. This catalyst was easily prepared using only commercially available reagents and could be reused several times [40]. Later, diverse nanocatalyts were reported to be effective in this transformation under aerobic conditions. These include gold nanoparticles immobilized in aluminum oxyhydroxide [41] or supported in hydrotalcite [42], and palladium nanoparticles entrapped in aluminum hydroxide [43]. Other steroidal alcohols including 3α-hydroxy-5α-pregnan-20-one and nandrolone were oxidized under aerobic conditions catalyzed by in situ generated Pd nanoparticles from Pd(O2CCF3)2 and neocuproine. Interestingly, this reaction was performed in aqueous solvent [44]. The use of fluorinated solvents is another relevant strategy in this context not only because they can be recovered and reused, but also because of the fact that the solubilization of oxygen is favored in fluorinated solvents. A relevant example was the aerobic oxidation of 5α-cholestan-3β-ol to 5α-cholestanone by molecular oxygen (Scheme 1) in a fluorinated biphasic system composed by perfluorodecalin and toluene, under catalysis by palladium(II) acetate combined with a perfluoroalkylated-pyridine ligand [pyridine-3-carbaldehyde bis(3,3,4,4,5,5,6,6,7,7,8,8,9,9,10,10,10-heptadecafluorodecyl) acetal]. Of high interest is the fact that the fluorinated phase containing the active palladium species was easily separated and reused several times without significant loss of catalytic activity [45].
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The use of a readily available organic compound as hydrogen acceptor can provide an interesting alternative to aerobic conditions namely by overcoming safety concerns linked to the use of flammable solvents. A relevant example of this strategy is the use of styrene as hydrogen acceptor in the oxidation of steroidal alcohols such as 3β-hydroxy-5α-androstan-17-one catalyzed by a low loading supported copper catalyst (Cu/Al2O3) [46]. More recently, Mitsudome et al. described the successful oxidation of 5α-cholestan-3β-ol to 5α-cholestanone promoted by two different nanocatalysts (Scheme 1). These included hydrotalcite-supported copper nanoparticles [47] and hydrotalcite-supported silver nanoparticles [48], which were used in combination with mesitylene or p-xylene as hydrogen acceptor, respectively.
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Several ionic liquids can be used as compatible supports for or catalyst/reagent immobilization with the advantage of allowing its recovery and recycling. In this context, an organosulfoxide anchored on imidazolium ionic liquid scaffold was used in the oxidation of 5α-cholestan-3β-ol to 5α-cholestanone (Scheme 1) in 85% yield, under Swern oxidation conditions. This ionic liquid-supported reagent has the advantages of being non-volatile and odorless but also recoverable and reusable after reoxidation of the sulfide with periodic acid [49]. The oxidation of several alcohols including 5α-cholestan-3β-ol using ion-supported methyl sulfoxides and methyl sulfides through Swern and Corey-Kim reaction conditions, respectively, was also reported. Again, unpleasant odor was not detected in both procedures, and good yields and high purity of the products were achieved after straightforward work-ups. Moreover, the reactants could also be recovered and reused [50]. A similar strategy involved the use of ion-supported (diacetoxyiodo)benzenes (IS-DIB) in the presence of a catalytic amount of 2,2,6,6-tetramethylpiperidine-1-oxy radical (TEMPO) to efficiently transform a large variety of alcohols including 5α-cholestan-3β-ol (Scheme 1) under mild conditions. Ion-supported iodobenzenes, the co-products derived from IS-DIB in this oxidation, were recovered in good yields by a simple extraction and were then re-oxidized with sodium peroxoborate, for reuse in the same transformation [51].
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The preparation of oxandrolone intermediates required the oxidation of 17α-methylandrostan-3β,17β-diol, which was accomplished by means of several mild, efficient and eco-friendly oxidizing conditions involving the use of NaOCl or H2O2/catalytic Na2WO4 under phase transfer conditions [52]. The oxidation of this substrate was also studied using the environmentally benign ionic liquid [bmim][Br] and mild and inexpensive reagent 2-iodoxybenzoic acid (IBX). Interestingly, it was observed that the relative amount of oxidant determined the products obtained. In effect, using 1.2 eq. of IBX, mestanolone was the only product, however, with 2.4 eq., a 1,2-dehydrogenation occurred along with the oxidation to the carbonyl functionality, affording 17β-hydroxy-17α-methyl-Δ1-androsten-3-one as the major product in a one-pot reaction. Moreover, by simply concentrating the filtrate under reduced pressure, the ionic liquid was recovered and effectively reused up to three times [53].
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In addition to the previously described use of fluorinated solvents and ionic liquids, subcritical water may also be useful to replace environmentally unacceptable solvents in numerous organic reactions, including in oxidations of alcohols. This fact results from a dramatic decrease in solvent viscosity and an increase in substrate solubility observed with its use. Similarly to the observed with fluorinated solvents, molecular oxygen has a relevant solubility in subcritical water. In this context, Ozen and Kus reported a metal-free procedure using this solvent in several oxidations, including in the transformation of alcohols to carbonyl compounds. Under these conditions, cholesterol originated cholest-5-en-3-one (Scheme 1) in high yields [54].
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The use of MW technology for the oxidation of alcohols to the corresponding carbonyl functions was also reported. Among other relevant substrates, diosgenin and cholesterol (Scheme 1) were oxidized to their Δ5-3-ketone derivatives in high isolated yields and after 2 minutes of reaction with pyridinium chlorochromate (PCC) and under MW irradiation [55].
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3. Epoxidation
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Epoxysteroids, namely several withanolides and oxysterols, exhibit diverse biological activities [34, 35, 56, 57]. In addition, the epoxide functional group has high synthetic interest because the facile ring opening allows the stereoselective introduction of various functionalities into the steroidal nucleus.
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Classically, the preparation of epoxysteroids involves the use of peroxacids, such as meta-chloroperoxybenzoic acid (MCPBA), usually originating α-epoxides [58]. The stoichiometric combination of KMnO4 and metal salts, on the other hand, allows the successful selective synthesis of β-epoxides. Steroidal epoxides can also be prepared using other oxidative procedures involving, for example, the use of isolated or in situ generated dioxiranes, aziridines and peroxides, frequently combined with adequate promoters. More recently, due to their greener nature, several catalytic epoxidations have been reported as well as various procedures using more environmental friendly oxidants in combination with metal and non-metal catalysts [34, 35]. For example, new iron- and manganese-based catalysts were recently reported to efficiently epoxidize several unsaturated steroids in combination with H2O2 [59–62]. In addition, the possibility of the recovery and reuse of the catalysts as well as the use of alternative solvents were also considered greener approaches to perform this transformation [34, 35].
\n
Stereoselective syntheses of several β-epoxysteroids were described with combinations of oxidant/catalysts including 2,6-dichloropyridine N-oxide (DCPNO)/Ru-based catalysts and iodosylbenzene (PhIO)/Mn-porphyrins [34, 35]. In this context, among other interesting and advantageous heterogeneous catalytic procedures, the use of a polymer-supported manganese(III) porphyrin as heterogeneous catalyst and PhIO as oxidant has been reported for the β-selective epoxidation of several Δ4- and Δ5-steroids (Scheme 2) [63] Similar results were observed using DCPNO as oxidant combined with a ruthenium(II) tetrafluorophenylporphyrin (TFPP) carbonyl complex [Ru(TFPP)CO] covalently attached to functionalized silica [64] or with [RuII(F20-TPP)CO] (TPP = tetraphenylporphyrin) covalently attached to poly(ethylene glycol) [65]. Other green approach for the effective preparation of 5β,6β-epoxides from Δ5-steroids (Scheme 2) involves the use of O2 combined with a sacrificial aldehyde (Mukaiyama reaction conditions) and heterogeneous catalysts mainly bearing cobalt as the metal centre [66, 67]. Later, a SiO2-supported Ru-monomer complex was described as catalyst for the epoxidation of cholesteryl benzoate under similar oxidative conditions [68].
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Scheme 2.
Epoxidation of Δ5-steroids affording 5β,6β- and 5α,6α-epoxides.
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An alternative strategy to allow the recovery and efficient reuse of the catalysts is their use in perfluorinated compounds to mediate the oxidative reactions, being the fluorinated solvents also recoverable and reusable. Accordingly, it was reported that both 2,4-bisperfluorooctylphenyl butylselenide combined with H2O2 [69] and a ruthenium-pyridine-benzimidazole complex bearing perfluorinated ‘ponytails’ under Mukaiyama reaction conditions [70] catalyzed the epoxidation of various olefins, including 3β-chlorocholest-5-ene in a fluorous biphasic system.
\n
The epoxidation of Δ5-steroids (Scheme 2) mediated by organocatalysts has been reported as an interesting approach to obtain these biological and pharmaceutical interesting steroids avoiding the contamination with metal compounds. A representative example is the regio- and stereoselective epoxidation of cholesteryl benzoate performed with O2 in the presence of benzhydrol catalyzed by N-hydroxyphthalimide (NHPI) and hexafluoroacetone. Among other epoxides, this metal-free aerobic procedure allowed the selective preparation of 5α,6α-epoxycholesteryl benzoate in moderate yield [71]. Additionally, other 5β,6β-epoxysteroids (Scheme 2) were efficiently prepared using chiral ketones [e.g. 1,1,3(S),5(R)-tetramethyl-4-oxo-2(R),6(S)-diphenylpiperidinium triflate] as organocatalysts and OxoneTM as oxidant [72]. More recently, Dansey et al. [73] reported the application of a chiral and bulky fructose-derived ketone as catalyst also combined with OxoneTM for the regio- and stereoselective epoxidation of a diene A-homosteroid that occurred in the steroidal A-ring and afforded the corresponding β-epoxide as the only product in 35% yield [73].
\n
The previously referred hexahaloacetones, including hexafluoroacetone, can be used as catalysts in combination with H2O2 for the epoxidation of several estra-5(10),9(11)-dienes to obtain the corresponding 5α,10α-epoxy derivatives (Scheme 3) as the major reaction products. An improvement of the α:β ratio of isomers to 7:1 was observed in the epoxidation of the substrate 3,3-ethylenedioxo-17α-(1-propynyl)estra-5(10),9(11)-dien-17β-ol using chiral ammonium salts derived from cinchona alkaloids as phase-transfer enantioselective catalysts under similar oxidation conditions [74]. Other oxidative conditions to perform this transformation (Scheme 3) used stoichiometric MCPBA or metal catalysts under homogeneous conditions. These included methylrhenium trioxide combined with H2O2 or urea-hydrogen peroxide or FeII-phthalocyanine and PhIO. However, the results were poorer than those observed with the combination of hexahaloacetones and H2O2 [75].
\n
Scheme 3.
Regioselective epoxidation of 3,3-ethylenedioxo-Δ5(10),9(11)-steroidal dienes.
\n
Guggulsterones are natural steroids with high potential therapeutic interest namely as hypocholesterolemic agents, and therefore it is important to study their chemical reactivity including under oxidative conditions. For this purpose, the use of H2O2 combined with different 5,10,15,20-tetraarylporphyrinatoiron(III)chlorides (e.g., iron(III) 5,10,15,20-tetrakis(2′,6′-dichloro-3′-sulfonatophenyl)porphyrin, [Cl8TPPS4Fe(III)]) in dichloromethane as well as in the ionic liquid [bmim]BF4 was evaluated by Singhal and Chauhan. Interestingly, in both solvents the 17,20-epoxide was formed in moderate yields along with minor hydroxylated products and it was observed that the reaction was more effective with Z-guggulsterone than its geometric isomer E-guggulsterone. In addition, the use of ionic liquid allowed the easy isolation of the products from the reaction mixture, leaving behind the water-soluble iron(III)porphyrin catalyst immobilized in it [76].
\n
A recent and interesting example involving nanotechnologies was reported by Banerjee et al., who developed a heterogeneous CoxOy–N/C (x=1,3; y=1,4) catalyst composed by cobalt oxide nanoparticles with varying size along with very few large particles with a metallic Co core and an oxidic shell. This catalyst was applied to efficient epoxidation reactions of aromatic and aliphatic olefins using TBHP as the terminal oxidant. Interestingly, among the substrates included in the study, only the linear double bond of 20-oxopregn-5-en-3β-yl trans-styrylates was epoxidized. This cobalt oxide catalyst can be recycled up to five times without significant loss of activity or change in structure [77].
\n
\n
4. Allylic oxidation
\n
The allylic oxidation allows the synthesis of allylic alcohols, esters, ethers and α,β-unsaturated carbonyl compounds and has attracted interest over the years [78]. In the steroids field, the oxidation of alkenes to the corresponding enones, such as Δ5-7-ketones (Scheme 4), is an important reaction, not only because this functionality can be found in biologically active compounds, namely in the nutraceutical 7-oxodehydroepiandrosterone, but also because of its synthetic interest, associated with the further functionalization of the intact double bond or of the carbonyl group [78–80].
\n\n
Typically, the oxidation of Δ5-steroids to Δ5-7-ketones (Scheme 4) has been performed using either chromium(VI) reagents in stoichiometric conditions or with TBHP combined with metal catalysts under homogeneous conditions [34, 35]. Very recently vanadyl acetylacetonate [81] or activated manganese dioxide [82] was explored as interesting catalysts for this reaction, using a 70% aqueous solution of TBHP. In addition, this oxidant was combined with the catalysts NHPI and Co(OAc)2 in another optimized protocol described by Zhao et al. [83] for the regio- and chemoselective allylic oxidation of several functionalized Δ5-steroids.
\n
Scheme 4.
Allylic oxidation of Δ5-steroids to Δ5-7-ketones.
\n
Greener approaches to prepare Δ5-7-oxosteroids from Δ5-steroids (Scheme 4) involved the use of catalysts immobilized on heterogeneous supports, which may allow their recovery and reuse. In fact, several heterogeneous catalysts including KMnO4/SiO2 in benzene or chromium(VI) adsorbed on SiO2/ZrO2, cobalt(II), copper(II), manganese(II) and vanadium(II) immobilized on silica and BiCl3/montmorillonile K-10 were described for the allylic oxidation of Δ5-steroids in combination with TBHP as oxidant [34, 84].
\n
The use of recyclable/reusable acetylacetone-metal catalysts modified by a pyridinium salt as co-catalysts in a NHPI-catalyzed oxidation of cholesteryl acetate by molecular oxygen under mild conditions was described. The pyridinium salt interacting with the acetylacetone ligand behaved as an electron-withdrawing group and as a co-catalyst for the decomposition of the alkyl hydroperoxides formed, allowing the relevant isolated yields. Interestingly, the catalyst [Co(acac-py)2][Cl2] could be easily recovered by a water wash method and reused at least four times with only a slight loss of catalytic activity [85].
\n
Recently, the preparation of multifunctional core-shell nanospheres consisting of a core of metal clusters and an outer microporous silica shell was described. Interestingly, the Pd clusters encapsulated in hybrid core-shell structures exhibit exceptional size-selective catalysis in aerobic allylic oxidations of substrates. In fact, after 60 minutes, conversions of 23.1% and 9.8% were observed for cyclohexene and cholesteryl acetate, respectively, affording mainly allylic oxidation products. These reactivities can be explained by the different sizes of these substrates (cyclohexene ~0.5 nm, cholesteryl acetate ~1.91 nm), which can determine their diffusion to inside the pores of the catalyst [86].
\n
As previously referred, synthetic transformations avoiding the use of toxic and expensive metals are especially attractive for the preparation of compounds that do not tolerate metal contamination such as APIs [87]. A relevant application of this concept was the use of household laundry bleach and aqueous TBHP at sub-ambient temperature for the oxidation of steroidal olefins (Scheme 4) and benzylic compounds to α,β-enones. This procedure is not only simple and economical but also has the advantage of using water as solvent [88]. Later, our group described that various Δ5-steroids could be selectively oxidized to Δ5-7-ketones (Scheme 4) by sodium chlorite associated with NHPI as catalyst in aqueous solvents, achieving good yields [35, 89].
\n
The use of water as solvent was also described in the preparation of several steroidal Δ4-3,6-diketones from Δ4-3-ketones (Scheme 5) catalyzed by dirhodium caprolactamate [Rh2(cap)4] and 70% TBHP in water [90]. This allylic oxidation was also carried out with 5 mol% of CrO3 as catalyst combined with the same oxidant but using benzotrifluoride as a recoverable fluorous solvent [91].
\n
Scheme 5.
Allylic oxidation of Δ4-3-ketone steroids to Δ4-3,6-diketones.
\n
The oxidation of 3β-cholesteryl benzoate to the corresponding Δ5-4-ketone derivative was also described involving the same fluorous solvent and perfluorooctylseleninic acid as catalyst along with PhIO2 as oxidant. Interestingly, this catalyst could be recovered by fluorous extraction as bis(perfluorooctyl)diselenide, which served as a catalyst precursor [92].
\n
Alternative energy sources such as light can also be useful in allylic (Scheme 4) and benzylic oxidation reactions. In this context, the irradiation of olefins such as cholesteryl acetate with UV light in open flasks in the presence of HgBr or N-bromosuccinimide originated the corresponding allylic oxidation products in high yields [93]. More recently, the same transformation was performed by means of a photocatalytic system consisting on the combination of a recoverable graphitic carbon nitride (g-C3N4) and N-hydroxy compounds (e.g., NHPI) to activate O2. Despite the low to moderate conversions, this mild photocatalytic strategy also has the advantages of avoiding the employment of metal derivatives or organic oxidizing agents [94].
\n
Several electrochemical methods were applied in the oxidation of cholesterol and derivatives affording, namely, allylic acetoxylation or hydroxylation products [95, 96]. In effect, an electrochemical system for the aerobic oxidation of cholesteryl acetate induced by iron picolinate complexes was reported by Okamoto et al. Interestingly, this procedure mainly afforded 7-hydroxylated products with high stereoselectivity (α:β ratio > 100:9), despite relatively low yields [97]. Later, it was described that cholesterol can undergo direct electrochemical oxidation on platinum electrode in glacial acetic acid containing sodium perchlorate and sodium acetate as supporting electrolytes. This preparative electrolysis mainly led to 7α- and 7β-acetoxycholesterol in a 10:3 ratio. These products were also found when sodium acetate was replaced by sodium trifluoroacetate, but the stereoselectivity of the reaction was lost and the yields of the oxidized products were low to moderate [95].
\n
\n
5. Other oxidation reactions
\n
Electrochemical methods were also developed and applied in the halogenation of steroids [96, 98–100], including Δ5-steroids, to afford 5α,6β-halogenated derivatives that have high biological interest and can be useful in the protection of the double bond in synthetic chemistry. In addition, these procedures can be valuable alternatives to the use of less green reagents namely chlorine gas.
\n
Another important oxidation reaction to which new sustainable procedures have been developed is the Baeyer-Villiger rearrangement [101]. However, within the steroidal field, this reaction is classically performed by means of peroxyacids, such as MCPBA. In this context, the use of MW irradiation to accelerate the oxidation of several steroidal ketones was described. In fact, after few minutes of reaction, the corresponding esters/lactones were successfully obtained (Scheme 6) [102]. A more sustainable oxidant used to perform this reaction is H2O2 which, in combination with the lipophilic catalyst Ca[B(C6F5)4]2 allowed, for example, the preparation of estrolactone from estrone in 88% yield after 4 hours of reaction [103].
\n
Scheme 6.
Baeyer-Villiger oxidation of 17-oxo-5α-androstan-3β-yl acetate by MCPBA under MW.
\n
The dihydroxylation of olefins is an important reaction because the 1,2-diol functionality is present in many synthetic and natural relevant molecules and is a very useful synthetic building block. The most efficient approach for the preparation of steroidal syn-diols is the direct dihydroxylation of olefins, [35, 75], whereas the trans-dihydroxylation of olefins occurs mainly by epoxidation and hydrolysis [104]. Recently, the Brønsted acid p-toluenesulfonic acid (PTSA) was described as a catalyst for the direct trans-dihydroxylation of olefins including cholesterol affording the 5α,6β-diol derivative in 56% yield, in aqueous media. This procedure has the advantages of being mild and metal-free and compatible with a considerable range of organic functional groups, and the catalyst could be recycled and reused [105].
\n
Water was also used as solvent in combination with Aliquat 336 and sand for several reactions of very sparingly soluble high melting-point organic substrates, such as steroids. In this system, Aliquat 336 works as both catalyst and solvent, and its efficiency is enhanced by the moving sand under mechanical stirring. This mixture was successfully applied in the good-yield oxidation of pseudosapogenins into 16-dehydropregnenolone acetate and its analogues using H2O2 and catalyzed by V2O5 [106]. This transformation is of high impact because 16-dehydropregnenolone acetate and similar compounds are important starting materials for the preparation of several semisynthetic steroid drugs [2].
\n
The metal-free oxidation of spironolactone-related sulfides to corresponding sulfoxides and sulfones was performed by the green oxidant H2O2 in the presence of the organocatalyst N-hydroxysuccinimide (NHS). In this high-yielding process, a full oxidation to sulfones occurred in methanol at room temperature, whereas sulfoxides could be selectively obtained using acetone as solvent under reflux temperature (example in Scheme 7). Both processes were compatible with the presence of sensitive groups including ketones, alkenes, hydroxyl groups and benzylic carbons under the described reaction conditions [107].
\n
Scheme 7.
Organocatalytic oxidation of 7α-(phenylmethylthio)-17-hydroxy-3-oxo-17α-pregn-4-ene-21-carboxylic acid γ-lactone by H2O2.
\n
\n
6. Conclusions and future perspectives
\n
Currently, pharmaceutical chemistry is moving towards the incorporation of the sustainable chemistry principles into the development of new reactions and processes. In the oxidation of steroids, however, green approaches are still relatively limited and mostly involving catalytic methods. In addition, the application of nanocatalysts to steroid chemistry has started to emerge.
\n
Considering the importance of sustainability in oxidative process research and development and the biological and synthetic relevance of oxygenated steroid compounds in medicinal chemistry, it is mandatory to increase the efforts to enlarge the scope of the new green chemistry tools, such as novel catalysts, solvents and technologies. Therefore, in the near future, it can be expected an increase in the use of greener solvents, such as water and fluorous solvents. The application of alternative energy sources, including microwaves, sonochemistry and photo irradiation, will contribute to reduce reaction times and overall energy consumption. Furthermore, the continuous replacement of stoichiometric methods by catalytic reactions, preferably avoiding metal catalysts and involving heterogeneous catalysts is also expected.
\n
In spite of some limitations, such as the shape and complexity of steroid compounds, which are responsible for their singular chemo-, regio- and stereoselectivities, their solubility problems and their rigid molecular framework, nanocatalysts, will certainly be increasingly applied in catalytic oxidative processes namely in steroid chemistry.
\n
\n
Acknowledgments
\n
JAR Salvador and MMC Silva thank University of Coimbra and SM Silvestre thanks University of Beira Interior for their financial support.
\n
\n',keywords:"green pharmaceutical chemistry, steroids, catalysis, oxidation, green technologies, nanocatalysts",chapterPDFUrl:"https://cdn.intechopen.com/pdfs/50132.pdf",chapterXML:"https://mts.intechopen.com/source/xml/50132.xml",downloadPdfUrl:"/chapter/pdf-download/50132",previewPdfUrl:"/chapter/pdf-preview/50132",totalDownloads:2392,totalViews:256,totalCrossrefCites:0,totalDimensionsCites:0,totalAltmetricsMentions:0,impactScore:0,impactScorePercentile:14,impactScoreQuartile:1,hasAltmetrics:0,dateSubmitted:"October 27th 2015",dateReviewed:"February 3rd 2016",datePrePublished:null,datePublished:"June 1st 2016",dateFinished:"March 18th 2016",readingETA:"0",abstract:"Steroids and their oxidation products are widely distributed in living organisms and are important intermediates for the synthesis of many biologically active molecules. Due to their pharmacological and synthetic relevance, several oxidative chemical processes for the functionalization of the steroid nucleus have been developed. Green chemistry principles have been incorporated in some oxidative transformations of steroids, allowing significant advances in synthetic chemistry applied to these compounds. This chapter presents a selection of relevant applications of pharmaceutical green chemistry to steroid’s oxidative processes. Special emphasis is given to catalytic processes encompassing heterogeneous nanocatalysts, whose application in this context is increasing over the past years. This chapter is organized according to the reaction type that includes alcohol oxidation, epoxidation of alkenes, and allylic oxidation of alkenes to enones, among other relevant oxidative transformations. Biocatalytic oxidative methods applied to steroid synthesis are not included in this review.",reviewType:"peer-reviewed",bibtexUrl:"/chapter/bibtex/50132",risUrl:"/chapter/ris/50132",book:{id:"5170",slug:"green-nanotechnology-overview-and-further-prospects"},signatures:"Samuel M. Silvestre, M. Manuel C. Silva and Jorge A. R. Salvador",authors:[{id:"69976",title:"Prof.",name:"Jorge António Ribeiro",middleName:null,surname:"Salvador",fullName:"Jorge António Ribeiro Salvador",slug:"jorge-antonio-ribeiro-salvador",email:"salvador@ci.uc.pt",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/69976/images/system/69976.png",institution:{name:"University of Coimbra",institutionURL:null,country:{name:"Portugal"}}},{id:"157541",title:"Prof.",name:"Samuel",middleName:null,surname:"Silvestre",fullName:"Samuel Silvestre",slug:"samuel-silvestre",email:"samuel@fcsaude.ubi.pt",position:null,profilePictureURL:"//cdnintech.com/web/frontend/www/assets/author.svg",institution:null},{id:"185027",title:"Prof.",name:"Maria Manuel Cruz",middleName:null,surname:"Silva",fullName:"Maria Manuel Cruz Silva",slug:"maria-manuel-cruz-silva",email:"msilva@ff.uc.pt",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/185027/images/system/185027.png",institution:{name:"University of Coimbra",institutionURL:null,country:{name:"Portugal"}}}],sections:[{id:"sec_1",title:"1. Introduction",level:"1"},{id:"sec_1_2",title:"1.1. Basic steroid chemistry and relevance of oxygenated steroids",level:"2"},{id:"sec_2_2",title:"1.2. The green chemistry concept and green nanotechnologies",level:"2"},{id:"sec_3_2",title:"1.3. Scope and organization of this chapter",level:"2"},{id:"sec_5",title:"2. Alcohol oxidation",level:"1"},{id:"sec_6",title:"3. Epoxidation",level:"1"},{id:"sec_7",title:"4. Allylic oxidation",level:"1"},{id:"sec_8",title:"5. Other oxidation reactions",level:"1"},{id:"sec_9",title:"6. Conclusions and future perspectives",level:"1"},{id:"sec_10",title:"Acknowledgments",level:"1"}],chapterReferences:[{id:"B1",body:'Brueggemeier RW, Li P-K. Fundamentals of steroid chemistry and biochemistry. In: Abraham DJ, editor. Burger\'s Medicinal Chemistry and Drug Discovery, Vol. 3. Cardiovascular Agents and Endocrines. 6th ed. New York: John Wiley & Sons; 2003. pp. 594-627. DOI: 10.1002/0471266949'},{id:"B2",body:'Lednicer D. Steroid Chemistry at a Glance. 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Catalysis Communications. 2012; 25:28-31.'},{id:"B77",body:'Banerjee D, Jagadeesh RV, Junge K, Pohl M-M, Radnik J, Bruckner A, Beller M. Convenient and mild epoxidation of alkenes using heterogeneous cobalt oxide catalysts. Angewandte Chemie-International Edition. 2014; 53:4359-4363.'},{id:"B78",body:'Bulman Page PC, McCarthy TJ. Oxidation adjacent to C=C Bonds. In: Trost BM, Flemming I, chief editors; Ley SV, volume editor. Comprehensive Organic Synthesis. Oxford-New York-Seoul-Tokyo: Pergamon Press; 1991. Vol. 7, pp. 83-117. ISBN: 0-08-040598-3.'},{id:"B79",body:'Arsenou ES, Fousteris MA, Koutsourea AI, Nikolaropoulos SS. 7-keto-Δ5-steroids: Key-molecules owning particular biological and chemical interest. Mini Reviews in Medicinal Chemistry. 2003; 3(6):557-567.'},{id:"B80",body:'Parish EJ, Kizito SA, Qiu ZH. Review of chemical syntheses of 7-keto-Δ5-sterols. Lipids. 2004; 39(8):801-804.'},{id:"B81",body:'Grainger WS, Parish EJ. 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Chromium(VI) oxide-catalysed oxidations by tert-butyl hydroperoxide using benzotrifluoride as solvent. Comptes Rendus de l\'Académie des Sciences - Series IIC – Chemistry. 2000; 3(9):747-750.'},{id:"B92",body:'Crich D, Zou YK. Catalytic allylic oxidation with a recyclable, fluorous seleninic acid. Organic Letters. 2004; 6(5):775-777.'},{id:"B93",body:'Friedman N, Gorodets M, Mazur Y. Photo-oxidations of olefins and benzene derivatives. Journal of the Chemical Society D-Chemical Communications. 1971; (15):874.'},{id:"B94",body:'Zhang P, Wang Y, Yao J, Wang C, Yan C, Antonietti M, Li H. Visible-light-induced metal-free allylic oxidation utilizing a coupled photocatalytic system of g-C3N4 and N-Hydroxy compounds. Advanced Synthesis & Catalysis. 2011; 353(9):1447-1451.'},{id:"B95",body:'Kowalski J, Ploszynska J, Sobkowiak A, Morzycki JW, Wilczewska AZ. Direct electrochemical acetoxylation of cholesterol at the allylic position. 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Electrochemical bromination of cholest-5-enes. Steroids. 2005; 70:867-872.'},{id:"B101",body:'ten Brink GJ, Arends I, Sheldon RA. The Baeyer-Villiger reaction: New developments toward greener procedures. Chemical Reviews. 2004;104,(9):4105-4123.'},{id:"B102",body:'Borah JM, Chowdhury P. Expedited Baeyer-Villiger oxidation of steroidal ketones by microwave irradiation. Steroids. 2011; 76(12):1341-1345.'},{id:"B103",body:'Uyanik M, Nakashima D, Ishihara K. Baeyer–Villiger oxidation and oxidative cascade reactions with aqueous hydrogen peroxide catalyzed by lipophilic Li[B(C6F5)4] and Ca[B(C6F5)4]2. Angewandte Chemie - International Edition. 2012; 51:9093-9096.'},{id:"B104",body:'Yudin AK, editor. Aziridines and epoxides in organic synthesis. Weinheim: Wiley-VCH; 2006. 516 p. ISBN: 978-3-527-31213-9'},{id:"B105",body:'Rosatella AA, Afonso CAM. Brønsted acid-catalyzed dihydroxylation of olefins in aqueous medium. 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Health Sciences Research Centre, University of Beira Interior, Covilhã, Portugal
Center for Neuroscience and Cell Biology, University of Coimbra, Coimbra, Portugal
'},{corresp:null,contributorFullName:"M. Manuel C. Silva",address:null,affiliation:'
Center for Neuroscience and Cell Biology, University of Coimbra, Coimbra, Portugal
Pharmaceutical Chemistry Laboratory, University of Coimbra, Coimbra, Portugal
'},{corresp:"yes",contributorFullName:"Jorge A. R. Salvador",address:"salvador@ci.uc.pt",affiliation:'
Center for Neuroscience and Cell Biology, University of Coimbra, Coimbra, Portugal
Pharmaceutical Chemistry Laboratory, University of Coimbra, Coimbra, Portugal
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1. Introduction
Sewage sludge (SS) is formed as a by-product at a wastewater treatment plant (WWTP) and represents a heterogeneous mixture. This complex suspension consists of solid organic and inorganic substances and colloids, which have been separated from the wastewater during the treatment process [1]. The global production of SS is estimated at 45 million t of dry matter per year [2, 3]. During the last decade the SS production in EU countries increased by 1.5 million t of dry matter (DM), that is, from 11.5 million t in 2010 to 13 million t in 2020 [3], therefore, its management is a problem of great concern. The SS disposal reaches up to 60% of the total operating costs of WWTP, and, hence, makes this process problematic and expensive [4].
Sludge from WWTP is recovered by compost production, the application directly to agricultural and forest land, production of growing substrates, and energy recovery [5]. For practical and legal reasons, SS is increasingly reused rather than landfilled. This approach aims to minimize generated waste and promote the development of the bioeconomy that provides intelligent waste management, and, hence, is consistent with zero-waste strategy [3, 6]. Different countries have chosen different strategies for the use of urban SS. Analysis of the Eurostat data in the period from 2014 to 2018 showed that the use of SS in agriculture, in combination with compost, had been the main route for sludge disposal in the EU with 44.58%, followed by incineration (32.70%) and other methods of disposal (9.16%). Landfill disposal was at the level of 7.81%. Comparing the costs of different sludge disposal methods, the application on land and agriculture involves the lowest cost compared to composting, drying, incineration, and landfill.
At WWTPs, with more than 10,000 inhabitants, the sludge is divided into primary and secondary sludge. The primary sludge contains settling substances (from primary settling tanks), usually, it has a granular structure. Secondary sludge, also called excess sludge, consists of a mixture of microorganisms and settable substances from the biological stage of the WWTP. Primary sludge and secondary sludge are referred to as so-called raw sludge. The raw sludge is still microbially active, it can contain pathogenic microorganisms, with the total content of organic substances in the dry matter at about 70%. However, dewatered sludge (20–45% DM) is considered harmless and suitable for agriculture, because of high content of organic matter and biogenic elements (C, N, P), which increases soil fertility and is essential for plant growth and development as well as for soil microbiota [1]. Therefore, the use of SS on agricultural land is the best way to recycle the nutrients it contains, thus making the SS an important biological resource for sustainable agriculture [7, 8, 9]. On the other hand, the application rate is of great importance. Excessive concentrations of plant nutrients, mainly nitrogen and phosphorus, can also harm the environment, especially inland waters.
Another important issue is related to the abundance of hazardous and very persistent substances, such as heavy metals, polycyclic aromatic hydrocarbons, polychlorinated biphenyls, halogenated hydrocarbons, polychlorinated dibenzo-p-dioxins and dibenzofurans, pesticides, personal care products, hormonal substances, drugs and their metabolites, microplastics, and nanoparticles [8].
Therefore, the incorporation of sludge and its compost in the soil is regulated by various legislative acts [9]. The annual emission limit values for dry matter, heavy metals, total nitrogen, and total phosphorus are the maximum mass of these substances that can be applied per hectare of sludge or compost on average per year. Emission limit values for sludge dry matter vary considerably between the EU Member States, ranging from 1 to 10 t ha−1 per year. According to Mercl et al. [10], a high rate of SS composts applied once (60 t ha−1 compost in seedbed) is not recommendable since high nitrate concentration is not taken up by maize and increases the leaching risk. Furthermore, SS commonly contains high amounts of human pathogenic bacteria excreted in feces and urine, so the SS should be appropriately hygienized before application in agriculture.
The aim of this chapter was to summarize the main aspects of SS treatment for its application in agriculture, with emphasis on process efficiency, safety, and feasibility. The dual role of SS as a fertilizer and amendment in the soil is widely described in the literature, referring to the supply of nutrients to plants and improving the soil’s physical conditions, respectively. Our own results on SS treatment have been incorporated into the review of recent scientific literature and legislative documents.
2. Characteristics of sewage sludge as a potential soil amendment/fertilizer
Sludge is rich in organic matter, nitrogen, phosphorus, and other macro and microelements, which makes it a useful raw material to be used in agriculture. Dry SS contains on average 50–70% organic matter and 30–50% mineral components [8]. Physicochemical and biological characteristics of agricultural soils, which are amended with the organics-rich SS, can be considerably improved. Particularly, a reduced bulk density leads to an increased soil porosity and soil-air recirculation, as well as improved soil structure and water holding capacity. Besides, the concentration of soil humus is increased. Organic matter of SS enhances soil nutrient storage, soil biota, and diversity, as well as reduces exposure to erosion. High organic matter content facilitates the formation of stable organic complexes with humic acids, thus reducing metal availability [11]. A slow release of mineral elements from SS to soil also changes the physical, chemical, and biological parameters of soil and benefits from increased gas exchange, better water infiltration, and its retention. The compounds of SS are available for a longer period [12].
Mbagwu and Piccolo [13] found that the decomposition of organic materials in sludge enhances the availability of nutrients such as nitrogen and phosphorus substantially. Application of SS at a rate of 200 t ha−1 increased the total nitrogen of soil aggregates by 57% and available phosphorus by 64.2%.
The formation of organic and inorganic acids throughout the decomposition process of SS components under aerobic conditions increases soil acidity. Soil salinity positively correlates with the increased application rate of SS. Amendment of loamy-clay soil with SS at dose 60 t ha−1 increased soil carbon content from 0.16% to 1.45% [14].
Comparison of physicochemical characteristics of SS of different origins showed that average concentrations of nitrogen, phosphorus, and potassium are similar and reach up to 3.20%, 1.75%, and 0.5% per kg of treated dry SS, respectively [15, 16, 17]. Often the potassium content in SS is considered insufficient for plant nutrition [8]. Some studies indicate that SS is an efficient replacement for chemical fertilizers, especially phosphorus. Indeed, Switzerland, Germany, and Austria are developing legislation to make P recovery mandatory from municipal SS [18, 19].
Nevertheless, there are some site-specific factors (e.g., applied technology, quantity, and the origin of raw wastewaters, which differ by the composition of macro- and microelements and risk compounds), that make each SS unique, hence this specificity must be considered to predict the outcome of SS treatment. Determination of these factors remains challenging [20].
3. Legislative aspects in the use of sewage sludge in agriculture
The management of SS in the EU is regulated by various legislative acts. The Directive 2008/98/EC establishes the fundamental ideas and terminologies, such as waste, recycling, and recovery [21]. It explains the basic concepts of waste management, the distinction between waste and secondary raw material (“end-of-waste criteria”), waste, and by-products. The directive lays down basic principles of waste management without adversely affecting human life, health, nature, and the environment. Waste legislation and policy of the EU Member States shall apply as a priority order with the waste management hierarchy (Figure 1).
Figure 1.
The Waste Framework Directive 2008/98/EC priority order with the waste management hierarchy [21].
SS dose/soil
Plant species and effect
Reference
Field experiments
8.3% w/w/clayey–silty
Yield increase by mulching 65.7%, by mixing 91.5%: wheat (Triticum durum)
Increase by 42.3% in comparison with control, decrease by 31.8% in comparison with RDMF, that is, 45.5% and 22.1%; 46.3% and 18.9%; 51.6% and 27.8%; 52.1% and 8.5%; 35.5% and 16.2%: carrots (Daucus sativus); turnips (Brassica rapa); radish (R. sativus); tomatoes (Solanum lycopersicum); onion (Allium cepa); summer squash (Cucurbita pepo), respectively
Seed germination rate increased by 9.6, 19.0, 28.6, and 28.6%, respectively, total biomass increased by 146, 236, 278, and 400%: broad bean (Faba sativa)
Plant growth in response to the presence of SS in soil.
RDMF: recommended dose of mineral fertilizers; MF: mineral fertilizers.
An ex-post evaluation of the SS Directive 86/278/EEC in 2014 showed that its initial objectives were achieved, in spite of large variations in the amount of SS used in agriculture in the Member States (from none to well over 50%) [21, 22]. Currently (2020–2021), the EU initiated an evaluation of legislation efficiency, as well as the risks and opportunities of SS used in farming [23, 24].
Furthermore, two EU working documents on sludge have been produced: the EU Working Document on sludge (2000) and the EU Working Document on sludge and biowaste (2010). The EU Working Document on sludge (2000) indicates that to be used without restrictions, sludge should undergo an hygienization process by an “advanced treatment,” which should result in at least a 6-log-unit reduction in Escherichia coli, as well as create a sludge that meets the following criteria: In 50 g, there is no Salmonella (wet weight, WW) and E. coli <500 colony-forming unit CFU g−1. It was also proposed that sludge produced by “conventional treatments” should show a 2-log-unit reduction of E. coli, and its use is allowed with restrictions on its application time, site, and modality. Mesophilic anaerobic digestions at a temperature of 35°C with a mean retention time of 15 days and thermophilic anaerobic digestions at a temperature of at least 53°C for 20 h as a batch, without admixture or withdrawal during the treatment, are indicated, among others, as conventional and advanced treatment processes, respectively. The more recent EU document only suggests the limited absence of Salmonella in 25–50 g and E. coli <5 × 105 g−1 WW as possible criteria for the use of sludge in agriculture [25].
According to the EPA Environmental guidelines published in 2000 on stabilization of biosolids products [26], a biosolids product must meet at least one pathogen reduction requirement and at least one vector attraction reduction requirement [27]. Stabilization Grade A includes thermally treated biosolids (at least 50°C), high pH-high temperature process and biosolids from unknown processes, while stabilization Grade B—anaerobic digestion, aerobic digestion, air drying, composting, lime stabilization, extended aeration, and other processes accepted by the EPA products [26].
4. Economical aspects: technological efficiency and circular economy
In the context of sustainable development principles some main components, which determine the rational solution of the multi-faceted problem of municipal SS, must be considered. Poor farming practices combined with the overuse of chemical fertilizers on poor soils have caused a negative environmental impact, which leads to the degradation of arable land. The effort to increase productivity by increasing the use of various chemicals in fertilizers further diminishes soil fertility. With each harvest, the soil loses organic compounds, and permanent aggravation of improper agricultural practices often prevents the land from recovering. World chemical fertilizer consumption increased from 70.95 kg/ha in 1976 to 138.16 kg/ha in 2016. And in some regions, the fertilization dose increased up to hundreds and even thousands of kilograms per hectare (Figure 2) [28].
Figure 2.
Fertilizer consumption by different countries and regions. (a) Data on some countries and regions with fertilizer consumption below 500 kg/ha; (b) data on countries with rapid growth of fertilizer consumption, which exceeded 500 kg/ha [28].
The quantity of organic elements in the soil constantly decreases. A significant part of the SS does not return to the soil, but is disposed into the sea, is incinerated, or is subject to other different kinds of destructive effects, leading to drastic decreases in soil fertility and continuous soil degradation.
The quantity of the SS constantly increases. The peculiarity of SS lies in its multi-mineral compound and a huge range of organic matter; in fact, the SS is a nitrogen-phosphorus-potassium organic fertilizer, containing a full set of microelements necessary for the growth of crops. However, due to the high risk of pathogenic impact, a huge part of human and material resources is directed to the destruction of this important resource.
The overwhelming majority of the SS disposal methods are expensive, harmful, or contain both factors. Most municipalities face the growing problem of wastewater treatment. In many cases, waste is dumped into landfills, oceans, or incinerated. The rational solution to the problem of municipal SS disposal lies in an integrated approach to returning the sludge into the agricultural cycle [29].
The directive introduces the “polluter pays” principle and the extended producer responsibility. Some existing projects of producing energy, for example, biogas, minerals, and chemicals out of the sludge, do not prove to be sustainable and viable financially. Furthermore, in most cases, most of the sludge is eventually dumped at the end of the process. Incineration represents the total elimination of the sludge but is extremely expensive. It seems to be the most rational to consider SS not as a problem, but as a valuable resource.
In recent years, out of concern for the profound soil degradation, a growing trend of shifting to organic fertilizers is taking over within the agricultural industry.
The global fertilizer market was valued at around $360 billion before the COVID-19 pandemic with organic fertilizer making up just $6.8 billion. The organic fertilizer market is described as steadily increasing and expected to post a CAGR (Compound Annual Growth Rate) of 14% during the period 2019–2023, with the key factor being increased food demands and agricultural shortages due to population growth and climate change [30].
In case of the continuing negative influence of the high transport, logistics, and energy costs, the SS processing can offset the lack of fertilizers through a domestic product that costs only a fraction of the price to make, creating a local commodity with a considerable economic edge.
Sewage sludge is a natural epidemic focus, and the detection of SARS-CoV-2 in fecal masses led to the long-overdue conclusion to strengthen human health protective measures and counteract the emergence of epidemics [31]. The necessity of the implementation of new biological safety criteria can have a significant economical and long-term structural influence on the development of the entire sphere of processing and use of SS. For instance, regarding the sediment formed during the epidemic, it is recommended to avoid its traditional aerobic composting. At once, in the sludge undergoing thermal disinfection treatment, the risk of infection with SARS-CoV-2 is considered in the range from low to negligible [32]. Intensive decontamination measures will make the product more expensive, but more in line with the requirements of sustainable development.
To prevent potential biological threats toward the environment and human health, it becomes increasingly important to develop the most isolated from the environment hermetic methods for the SS disposal, without destroying the organic component, valuable for agriculture.
Economic aspects of SS hygienization have been analyzed [33]. The energy requirement per 100 tons of sludge was estimated depending on different disinfection conceptions. Thus, solar dehydration and chemical treatment with alkali consume 11.7 and 148.3 kW h with the production of 80 tons and 99.6 tons, respectively. In turn, the most expensive technology is gamma irradiation, which consumes 64,800 kW h for obtaining 97.6 tons of the product. The thermal drying also requires quite a high energy consumption, that is, 21,000 kW h for 20 tons of product. The composting does not consume electricity [33]. The high costs of thermal hydrolysis and ultrasonic methods and the need for a neutralizing agent in acid solubilization limit the rapid implementation of these processes in industrial practice [34].
Our testing of the infrared heating method for SS disinfection demonstrated successful results. It took 15 min for the material with an 80% humidity, including the time it required to heat the layer to 95°C, which is below the temperature at which the organic matter decomposes [35].
The widespread usage of SS biomethanation has resulted in the building of a number of complex installations that combine biological wastewater treatment facilities with anaerobic digesters. The development of digestate-derived granulated soil fertilizers is based on physicochemical processing of biostabilized sludges, in keeping with the circular economy concept and the concept of “waste-to-product” [36].
In this respect, the costs of pretreatment technologies for SS biomethanation with further conversion of digestate to fertilizers should be taken into consideration. The estimated energy utilized for the mechanical operations during SS disintegration and anaerobic digestion (stirring and pumping) was calculated to be 1253.6 kW h per ton [37]. The energy spent for SS pretreatment may vary depending on the solubilization [38], used consumables [39], and methods [40]—thermochemical (TC), sonic, thermo-chemo-sonic, etc. It is experimentally proven that combined disintegration pretreatment should be more efficient. The energy consumption for TC sludge pretreatment (30% solubilization) for biogas production was calculated to be 1588.552 kW h per ton of sludge. The thermos-chemo-ozone (TCO3) pretreatment can optimize the total energy input up to ~721.766 kW h per ton [41].
The evaporation of water should be weighed out between the energy costs in the process and the SS management costs without drying [42].
According to the economic feasibility review of our project for fast SS recycling into biological fertilizers, the energy cost will be nearly $30 per ton of fertilizers (with its humidity ~50% and energy costs $0.1 per kW h and initial SS humidity ~80%). The tested method allows providing 1 ton of bio-pathogenic-free fertilizers due to utilizing up to 1.5 tons of SS and withal avoid other SS disposal costs (Figure 3) [43].
Figure 3.
Technology of the fast recycling of SS into organic fertilizer. Methods are according to Chukurna et al. [43].
The applied methods and technical decisions have international priority under the Paris Convention for the Protection of Industrial Property, the World Intellectual Property Organization (WIPO) Eurasian Patent Organization (EAPO) and national patent organizations.
5. Sewage sludge treatment technologies
5.1 Stabilization
Stabilization of SS aims at reducing some disadvantages of SS (e.g., odor, leaching of heavy metals, etc.), thus considerably extending the potential of SS application. The extent to which readily biodegradable organic matter has degraded is referred to as the degree of stability [44]. Mixing of SS with fly ash, lime, peat, clay, straw, and other residues considerably improve SS characteristics, reducing leachability for metals and soil loss [45, 46]. The addition of wheat straw to the bioaugmented SS after 16 days incubation demonstrated the highest and most stable respiration intensity, the lowest ammonia emission, and the highest stimulation effect on the cress seedling growth, as compared to other treatment types [47].
Santos et al. [22] compared the performance of six residues serving for (i) sludge drying and (ii) improving agronomic properties of the final product. Weathered coal fly ash, bottom biomass ash, green liquor dregs, lime mud, eggshell, and rice husk were chosen as adjuvants based on circular economy and industrial ecological parameters. (0.15 g adjuvant/g SS wet basis). The addition of bottom biomass ash to SS promoted the highest diffusion coefficient and drying rate. The highest positive effect on agronomic parameters was shown for the SS amended with eggshell. Among evaluation criteria were acid neutralization capacity, oxygen uptake rate, and germination index [22].
5.2 Disinfection
Sludge treatment technologies for preparing a valuable fertilizer must meet legislative criteria on sludge hygienization. Numerous technological approaches on SS treatment, which were conducted at ambient temperature or under mesophilic conditions, had a strong effect on biological liquid sludge stabilization and natural dewatering and drying technologies, although disinfection efficiency was unsatisfactory [48, 49, 50]. In this respect, further comprehensive research on SS treatment should be focused on a combination of different physical (especially, thermal) and chemical processes, which would convert SS into a qualitative fertilizer with safe microbiological characteristics. Figure 4 summarizes a broad spectrum of methods for SS disinfection. Several studies have experimented with hybrid methods where two or more technologies can be integrated to increase treatment efficiency and performance [62].
Figure 4.
Methods of sludge disinfection. Combination of different methods is indicated by asterisks of the same color. By Izydorczyk et al. [34, 51, 52, 53, 54, 55, 56, 57, 58, 59, 60, 61].
The disinfection approaches should be optimized to minimize potential adverse impacts, such as antimicrobial resistance [62]. Another inherent problem with all sludges rich in nutrients is pathogen regrowth. Offensive odors serve as indicators of microbial regrowth because they are produced as bacteria break down proteins and other organic compounds containing nitrogen and sulfur [63].
6. Changes of microbial community composition in the sewage sludge and soil upon sludge treatment and application
The SS is characterized by a great microbial diversity, which may vary depending on the origin of sewage, its treatment, and industrial activity. Microbial activity in SS, transformation by-products, and residues may impact soil quality if SS is used as fertilizer/amendment [64]. The number of different groups of indicator microorganisms in 1 g of raw SS (wet) on average is 102–103 for Salmonella (bacteria), Enteroviruses (viruses), Giardia (protozoa), and Ascaris (helminths), while 106 – for bacteria Escherichia coli [56, 65].
6.1 Microbial community structure in the raw and treated sewage sludge
Many factors modulate microbial community structure within SS, which may change from autotrophic to heterotrophic bacteria depending on the effluent source. According to Nascimento et al. and Nielsen et al. [64, 66], Proteobacteria phylum (21–65%) is predominant in municipal SS. This phylum was primarily dominated by Betaproteobacteria that represents bacteria involved in organic matter degradation and nutrient cycling. Bacteroidetes, Acidobacteria, and Chloroflexi were among the less prominent species. Our recent experiments have also revealed Proteobacteria to dominate in the raw SS (60.17% reads), which consisted of 16.40%, 29.18%, and 12.33% of Alphaproteobacteria, Betaproteobacteria, and Gammaproteobacteria, respectively. At the genus level, the most abundant were Streptomyces (5.68%) and Pseudomonas (3.48%) (Figure 5A) [47].
Figure 5.
Relative abundance of microorganisms in sewage sludge. A—at the genus level with relative abundance ≥1% (29% from the total reads); B—Salmonella enterica and Escherichia coli in the sewage sludge before and after the 16-day incubation with different carbon amendments. Methods are according to Rimkus et al. [47].
Considerable changes in the microbial community structure of SS occur during biological treatment. Proteobacteria and Bacteroidetes were the most abundant in aerobic and anaerobic conditions, respectively [67, 68]. As reported by Rimkus et al. [47], addition of three types of carbon sources (faba bean straw, wheat straw, and wood-chip pellets) to the raw SS resulted in considerable changes in microbial community structure after 16 days of aerobic incubation. In particular, abundance of Firmicutes increased from 5% in the raw SS to 35–50% in the treated samples. In turn, abundance of Proteobacteria decreased from 62% in the raw SS to 32–45% in the treated samples. Yet, the SS incubation without C amendment resulted in a remarkable increase in virus abundance (i.e., 0.34% reads) [47]. The relative abundance of Salmonella enterica and Escherichia coli has been increased in the treated sludges, as compared to the raw SS (Figure 5B).
6.2 Shift in soil microbial community structure after application of the sludge-derived fertilizer
When SS is applied to soil, it causes changes in the structure and functioning of the agroecosystem. The most sensitive component is the soil microbiota, which can undergo both stimulatory and inhibitory changes in the activity and structure. These changes are greatly dependent on soil characteristics and SS application rate.
The microcosm experiment with SS-amended sandy soil (25.71 g SS/kg dry soil) after 119 days has revealed significant changes in prokaryotic community composition at the phylum level, as compared to the non-amended control [48]. Specifically, in SS-amended soil, the relative abundance of Firmicutes reduced from 58.6% at Day 0 to 18.7% at Day 119, while Proteobacteria increased from 15.5% to 36.4%, respectively [69]. In the control soil, these two respective phyla did not change considerably for 119 days. The relative abundance of Actinobacteria in SS-amended soil has increased from 3.1% to 13.2%, while in the control soil decreased from 27.6% to 19.4% [69].
The use of sludge as a soil amendment has been shown to increase the activity of soil enzymes, for example, arylsulfatase, acid phosphatase, and alkaline phosphatase. Basal respiration and the fluorescein diacetate hydrolysis activity increased with increasing the dose of SS [70]. Changes in urease activity by soil microorganisms can be discussed in two aspects. First, urease activity reflects the activity of microorganisms involved in the nitrogen cycle in soil [71]. Another aspect is related to the global loss of nitrogen (up to 70%) due to urease activity if urea is applied as a fertilizer. Therefore, urease inhibition is one of the strategies worldwide to maintain soil fertility [72]. In our experiments, combination of dry SS with nitrogen-containing fertilizer resulted in inhibition of urease activity in loamy soil during the vegetation experiment with maize [73].
The addition of SS-derived organics to soil increases the Cmic/Ctotal and Nmic/Ntotal ratios in the soil. At the same time, application of SS containing heavy metals, according to Fließbach et al. [8] and Chander and Brookes [74], Cmic/Ctotal ratio decreases to 32% and 50%, respectively. This effect can be developed greater in sandy soil than in clayey soils [75].
6.3 Indicators of microbiological contamination
In the early nineteenth century, the total coliforms, fecal coliforms, and fecal streptococci were considered as typical indicator bacteria. Later it was shown that these pathogens are not a major concern in solid waste landfills or leachate [62, 76]. Nowadays, different types of bacteria (fecal coliforms and Escherichia coli, Salmonella, Shigella, Vibrio cholerae); diverse parasite cysts and eggs (Balantidium coli, Entamoeba histolytica, and Giardia lamblia, helminths); viruses (human adenoviruses, enteroviruses (e.g., polioviruses), diarrhea-causing viruses (e.g., rotavirus), hepatitis-A virus and reoviruses) and fungi are monitored as biological contaminants of SS. Depending on the type and amount, they can all be harmful to the environment and human health [62, 76].
7. Effect of sludge-derived fertilizers on the plant growth
Soil amendment with SS is useful for enhancing crop production, as well as the accumulation of nutrients and organic matter in the soil. However, the accumulation of humic substances (HS) in soil and plant tissues must be regularly observed in case the SS is continuously used [14]. The SS can be used as fertilizers also after pyrolysis [77]. Both sole application of SS and their respective biochars provided enough P for the plants to achieve biomass higher than conventional P-fertilizer [77].
The effect of SS on plant growth differs depending on the SS application method, that is, at the soil surface “mulching” or mixed homogeneously with soil. The application of SS on the surface has some advantages, that is, water evaporation is limited by forming a physical barrier that allows soil moisture to be retained longer. Due to those, the biological and chemical processes of organic matter transformation intensified [78]. For example, the best yield of wheat (Triticum durum Desf.) was obtained when SS (dried) is applied at the clayey-silty soil surface (mulching) as compared to homogeneously mixed SS with soil [78]. Plant response to SS in dependence on SS application rate, plant species, soil type, and experiment conditions is shown in Table 1.
Importantly, a direct application of SS on agricultural soils is not recommended. It was shown that the hygienically treated (by liming) SS inhibited the growth of white mustard (Sinapis alba L.) already at a ratio of 10%. The addition of compost (5%, 15%, and 25%) resulted in the suppressed phytotoxicity of sludge in all tested ratios, that is, from 5 to 50% [92].
Our experiments showed that the use of SS affects the germination and development of seedlings. Concentrations exceeding 7 g kg−1 inhibited the germination of cucumber seeds and resulted in necrotizing primary roots. In the study with air-dried SS mixed with agricultural sandy loam soil at rates of 0 (control), 10, 20, 30, 40, and 50 g kg−1 (equal to 0, 30, 60, 90, 120, and 150 t ha−1), seed germination of broad beans (Faba sativa Bernh.) decreased from 70.0% (control), to 63.3, 56.7, 50.0, 50.0 and 46.7%, respectively [14]. Nevertheless, all the growth and morphometric parameters of broad beans positively respond to SS-amended soil compared to non-amended soil. The most effective for biomass yield of broad beans was the application of 120 t ha−1 SS [14]. In experiments with barley, the stimulation effect of SS also was shown, particularly, the addition of SS 40 g kg−1 soil led to an increase of dry weight, leaf area, number of leaves, and tillers per plant [18].
Our recent study demonstrated a positive effect of SS on maize growth and soil microbiological activity, when SS is applied in combination with mineral fertilizers [73]. Additional experiments have been performed also with cucumbers and leaf mustard. The SS preparation alone did not provide the plants with mineral nutrients in appropriate values, while the combination of SS preparation with nitrogen-containing fertilizers significantly improved the plant growth and promoted plant development [73] (Figure 6). This may have a long-term favorable effect on plant mineral nutrition. Our data also showed that different plants respond to the SS differently. A species-specific effect, in that case, can be explained by (i) different sensitivity of plants to the compounds in SS preparations; (ii) demand for mineral elements at the early stages of ontogenesis due to slow release of nutrients from SS; (iii) insufficient maturing and the presence of growth inhibitors in SS.
Figure 6.
The effect of SSP on the growth of plants: A—cucumbers, B—leaf mustard, C–E—maize. Label color: pink—SSP + NPK, orange—NPK, blue—SSP + PK, green—SSP, yellow—vermicompost, white—soil without fertilizers. SSP—sewage sludge preparation; PK—phosphorus and potassium-containing fertilizer; NPK—nitrogen, phosphorus, and potassium-containing fertilizer. Controls—loamy soil without additional fertilizer, soil mixed with mineral fertilizer (Kristalon 18:18:18). Period of vegetation experiment A—18 days, B—47 days, C—33 days, E—46 days, and D—62 days. The application rate of SSP is 17.3 g L−1 in a loamy soil. Methods are according to Dubova et al. [73].
8. Environmental impact of the sewage sludge
Sludge production globally in 2017 was 45 MT by dry matter, and now it is increasing annually due to urbanization and population growth [34, 93]. In this respect, the environmental impact of SS in the case of landfill disposal, agricultural use, or other applications is of great importance. Particularly, the contribution of different processes of SS treatment for agricultural use is recently studied by [59]. Energy consumption for SS treatment contributed mostly to global warming (>50%), while SS transportation to agricultural areas affected terrestrial and freshwater ecotoxicity, as well as ozone formation—terrestrial ecosystems (Figure 7AandB). Sludge disposal in agricultural areas mostly contributed to human toxicity, terrestrial acidification, and freshwater ecotoxicity (Figure 7C). The main impacts of SS in soil are related to the presence of Zn, which affects freshwater ecotoxicity and human toxicity [94].
Figure 7.
Environmental life-cycle assessment of the sewage treatment plant: contribution of different activities. A—energy consumption; B—transport of sludge to agricultural areas; C—agricultural areas sludge disposal. By Do Amaral et al. [94].
Biogeochemical emissions from SS handling and spreading on land are expected to be minimized in the future by efficient utilization of nutrients and other resources derived from SS, according to the principles of a circular economy [95, 96]. The processed land-applied SS can emit volatile chemicals and gases that may act alone or in combination with one another to produce the kinds of symptoms [63].
The composition of the sludge and the concentration of pollutants in it predetermine the possibilities of its use. The presence of heavy metals, organic pollutants, and/or pathogens are the main issues associated with the reuse of SS or biosolids extracted from it. According to Manzetti and van der Spoel [97], the following aspects can be reported—(a) raising of the levels of persistent toxins in soil, vegetation, and wildlife, (b) potentially slow and long-termed biodiversity reduction through the fertilizing nutrient pollution operating on the vegetation, (c) greenhouse gas emissions, and (d) the release of odorous compounds. Groundwater contamination from biosolids with pathogenic microorganisms is one of the greatest problems worldwide, due to the lack of adequate and equitable sanitation of SS [98]. Chemical contaminants in processed SS may potentially interact with microbial pathogens, thus, causing or facilitating the disease process via allergic and nonallergic mechanisms, as well as microbial byproducts [63]. Furthermore, endotoxins and exotoxins, which are produced by most bacteria in SS and retain their toxicity at extremely high dilutions, can cause severe illness or death. Endotoxins are heat stable even upon autoclaving, while can be inactivated with dry heat at temperature above 200°C for 1 h [79, 99, 100]. A high microbial diversity of SS leads to the horizontal gene transfer and proliferation of antimicrobial resistance (AMR) [101]. The virus persistence in SS is dependent on the physicochemical and biological properties. For example, enveloped viruses survive for 6–7 days in SS [102], while SARS-CoV-2 might persist on the surfaces up to 72 h [69]. Coronavirus can persist in domestic and hospital SS also for a longer period of time at lower temperatures (4°C) [62, 103].
Long-term accumulation of toxic elements in soil and their uptake by plants is currently the biggest concern in terms of direct SS land application. The bioavailability of heavy metals in the soil is closely related to the value of the soil exchange reaction (soil pH measured in KCl or CaCl2 form), as well as to the sorption properties of the soil, which change with the addition of SS. According to published data, the availability of heavy metals in soils decreases in the order (Zn + Cd) > (Ni + Cu) > (Pb + Cr). However, in connection with physicochemical processes, the accumulation of heavy metals may occur over time, so it is necessary to monitor their concentration for a long time after the application of sludge [104]. When sludge is incorporated into the soil, the heavy metals in it bind to organic matter and clay particles, which usually accumulate in the soil [8, 105].
In Latvia, no more than 14 t ha−1 of dry matter may be incorporated at a time with sludge or compost. This corresponds to 55 t ha−1 of naturally moist sludge with a dry matter content of about 25% [106]. For 18 years, the concentration of heavy metals in Jelgava SS has significantly decreased. Similar trends have been observed in other treatment plants and this shows that heavy metals are no longer the most important limiting factor for the use of SS.
Wastewater can transport plastics from many different sources, such as fibers from washing machines, personal care products, and facial scrubs. WWTP efficiently removes the microplastics (MPs) from the wastewater, essentially trapping the particles in the sludge [107, 108]. Studies of Peterson [76] showed that 9 years of repeated sludge application led to the accumulation of MPs in the soil. According to various studies, MPs pose various negative effects on soil ecosystems, such as affecting soil fertility, soil organisms’ fitness, soil texture, and decreasing crop yield [109, 110].
Pignattelli et al. [111] highlighted the toxicity caused by small MPs (PP, PE, and PVC) on the growth of garden cress (Lepidium sativum). Hernández-Arenas et al. [112] studied the effect of MPs in sludge on the growth of tomato plants and discovered that plants grown in soils treated with sludge with a high concentration of MPs had the lowest biomass and did not produce any fruits during the experiment.
Domestic SS is a major source of pharmaceuticals, drugs, and antibiotic resistance genes, so it is important to ensure its biodegradation during sludge treatment. Drugs can remain in the sludge even after stabilization (dewatering), due to their high sorption capacity [113]. Ivanová et al. [114] discovered more than 100 types of drugs and their metabolites in SS. The amount and type of antibiotics in wastewater affect also the composition of bacteria [115].
Pharmaceutical substances are subject to thermal decomposition over a wide temperature range; therefore, it is possible to expect a reduction in the content or their complete removal during thermal processes [116]. Szabová et al. [117] achieved almost 100% drug removal in the sludge by heat treatment at 250°C and incineration at 550°C. Furthermore, pyrolysis at 350–500°C is able to decrease the concentration of MPs in sludge by more than 99% [118].
9. Future direction, challenges, and scope of sewage sludge as a soil fertilizer
The efficient use of waste-derived fertilizers in agriculture needs more empirical knowledge on markets with further research focused on variability, interactivity, and uncertainty. The site-specific factors (e.g., applied technology, quantity, and the origin of raw wastewater differed by the composition of macro- and microelements and risk compounds, soil types, and crops) make each SS unique, hence this specificity must be considered to predict the outcome of SS treatment. New efficient technologies for onsite sludge disinfection are necessary and urgent. Interdisciplinary activities on the safe use of SS upon treatment and application need to be thoroughly analyzed and developed, for example, planning, servicing, diagnosing, storing, and others. Furthermore, macroeconomic factors can considerably influence technology stocks. Soaring gas prices directly affected the production of synthetic fertilizers costs. High prices as well as the disruption of transport and production logistics lead to a real threat of a dramatic reduction in supply on the mineral fertilizers market. Combined with higher prices, an increase in demand for less volatile organic fertilizers can be expected.
10. Conclusions
Summarizing our experimental data on optimization of SS treatment and its application in agriculture, as well as recent findings of other authors in this field, the following conclusions were drawn:
The technology, which was newly developed by Earth Revival Ltd., offers an innovative and comprehensive solution to the problem of SS disposal and soil degradation, which includes aspects of agriculture, healthcare, epidemics, ecology, economics, and the social sphere. Costs can be recuperated through sludge treatment service fees and fertilizer sales.
The infrared heating system, used for SS disinfection, has shown consistently successful results. For the material with a humidity of 80%, it took 15 min, considering the heating time of the layer to 95°C, which is below the temperature of the organic matter decomposition. Research and experiments related to the neutralization of the spore-forming bacteria are planned to be realized in the next stage of the project.
The technology (SS transportation system, maturation process) can be used for fast, safe, and efficient SS processing into organic fertilizer. It also combines well with the anaerobic digestion process as it can complete the digestive sludge transformation to a huge quality fertilizer.
Sewage sludge can replace mineral fertilizers in crop production. Attention should be paid to the amount and ratio of mineral elements available to the plant during plant growth. Sewage sludge may not fully provide plants with potassium and phosphorus. Sewage sludge is recommended for plants with a longer vegetation period due to the slow release of nutrients. A phytotoxic effect may occur during seed germination.
Acknowledgments
This research is being conducted based on agreement with SIA “ETKC” (Centre of Competence for Energy and Transportation) within the framework of project Nr.1.2.1.1/18/A/001 co-funded by the European Regional Development Fund.
Conflict of interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
\n',keywords:"circular economy, fertilizer, life-cycle assessment, plant growth, sewage sludge hygienization",chapterPDFUrl:"https://cdn.intechopen.com/pdfs/81415.pdf",chapterXML:"https://mts.intechopen.com/source/xml/81415.xml",downloadPdfUrl:"/chapter/pdf-download/81415",previewPdfUrl:"/chapter/pdf-preview/81415",totalDownloads:56,totalViews:0,totalCrossrefCites:0,dateSubmitted:"January 4th 2022",dateReviewed:"March 4th 2022",datePrePublished:"April 20th 2022",datePublished:"June 28th 2022",dateFinished:"April 20th 2022",readingETA:"0",abstract:"Disposal of sewage sludge, which is a by-product of wastewater treatment, has become one of the greatest challenges of the twenty-first century. Conversion of sewage sludge to a soil amendment can be performed by a broad spectrum of methods, which greatly differ by substrate/amendment composition, treatment time, and physicochemical conditions. The book chapter is focused on (i) environmental and legislative aspects of sewage sludge application in agriculture; (ii) risk factors related to the abundance of pathogens in sewage sludge and methods of SS hygienization; (iii) optimization of the use of SS-derived fertilizers. Application of sewage sludge in combination with mineral fertilizers positively influenced crop growth and soil microbiological activity. An environmental impact of sewage sludge related to its disposal to agricultural areas has been analyzed in terms of global warming, ecotoxicity, and other internationally recognized issues. Narrowly targeted measures may aggravate the situation. Some site-specific factors make sewage sludge unique, hence this specificity must be considered to predict the outcome of its treatment. Determination of these factors remains challenging. Therefore, the complexity of sewage sludge can be reduced by employing integrated biorefinery approaches that will result in circular bioeconomy and industrial ecology solutions.",reviewType:"peer-reviewed",bibtexUrl:"/chapter/bibtex/81415",risUrl:"/chapter/ris/81415",signatures:"Olga Muter, Laila Dubova, Oleg Kassien, Jana Cakane and Ina Alsina",book:{id:"11083",type:"book",title:"Hazardous Waste Management",subtitle:null,fullTitle:"Hazardous Waste Management",slug:"hazardous-waste-management",publishedDate:"June 28th 2022",bookSignature:"Rajesh Banu Jeyakumar, Kavitha Sankarapandian and Yukesh Kannah Ravi",coverURL:"https://cdn.intechopen.com/books/images_new/11083.jpg",licenceType:"CC BY 3.0",editedByType:"Edited by",isbn:"978-1-80355-379-5",printIsbn:"978-1-80355-378-8",pdfIsbn:"978-1-80355-380-1",isAvailableForWebshopOrdering:!0,editors:[{id:"218539",title:"Dr.",name:"Rajesh Banu",middleName:null,surname:"Jeyakumar",slug:"rajesh-banu-jeyakumar",fullName:"Rajesh Banu Jeyakumar"}],productType:{id:"1",title:"Edited Volume",chapterContentType:"chapter",authoredCaption:"Edited by"}},authors:[{id:"440343",title:"Dr.",name:"Olga",middleName:null,surname:"Muter",fullName:"Olga Muter",slug:"olga-muter",email:"olga.mutere@lu.lv",position:null,profilePictureURL:"//cdnintech.com/web/frontend/www/assets/author.svg",institution:null},{id:"451623",title:"Dr.",name:"Laila",middleName:null,surname:"Dubova",fullName:"Laila Dubova",slug:"laila-dubova",email:"laila.dubova@llu.lv",position:null,profilePictureURL:"//cdnintech.com/web/frontend/www/assets/author.svg",institution:null},{id:"451624",title:"Mr.",name:"Oleg",middleName:null,surname:"Kassien",fullName:"Oleg Kassien",slug:"oleg-kassien",email:"oleg.kassien@earth-revival.com",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/451624/images/21137_n.png",institution:null},{id:"451625",title:"M.Sc.",name:"Jana",middleName:null,surname:"Cakane",fullName:"Jana Cakane",slug:"jana-cakane",email:"jana.uhrincatova@gmail.com",position:null,profilePictureURL:"//cdnintech.com/web/frontend/www/assets/author.svg",institution:null},{id:"451626",title:"Prof.",name:"Ina",middleName:null,surname:"Alsina",fullName:"Ina Alsina",slug:"ina-alsina",email:"ina.alsina@llu.lv",position:null,profilePictureURL:"//cdnintech.com/web/frontend/www/assets/author.svg",institution:null}],sections:[{id:"sec_1",title:"1. Introduction",level:"1"},{id:"sec_2",title:"2. Characteristics of sewage sludge as a potential soil amendment/fertilizer",level:"1"},{id:"sec_3",title:"3. Legislative aspects in the use of sewage sludge in agriculture",level:"1"},{id:"sec_4",title:"4. Economical aspects: technological efficiency and circular economy",level:"1"},{id:"sec_5",title:"5. Sewage sludge treatment technologies",level:"1"},{id:"sec_5_2",title:"5.1 Stabilization",level:"2"},{id:"sec_6_2",title:"5.2 Disinfection",level:"2"},{id:"sec_8",title:"6. Changes of microbial community composition in the sewage sludge and soil upon sludge treatment and application",level:"1"},{id:"sec_8_2",title:"6.1 Microbial community structure in the raw and treated sewage sludge",level:"2"},{id:"sec_9_2",title:"6.2 Shift in soil microbial community structure after application of the sludge-derived fertilizer",level:"2"},{id:"sec_10_2",title:"6.3 Indicators of microbiological contamination",level:"2"},{id:"sec_12",title:"7. Effect of sludge-derived fertilizers on the plant growth",level:"1"},{id:"sec_13",title:"8. Environmental impact of the sewage sludge",level:"1"},{id:"sec_14",title:"9. Future direction, challenges, and scope of sewage sludge as a soil fertilizer",level:"1"},{id:"sec_15",title:"10. Conclusions",level:"1"},{id:"sec_16",title:"Acknowledgments",level:"1"},{id:"sec_19",title:"Conflict of interest",level:"1"}],chapterReferences:[{id:"B1",body:'Gray NF. Water Technology: An Introduction for Environmental Scientists and Engineers. 3rd ed. IWA Publishing; 2010. p. 747'},{id:"B2",body:'Zhang S, Yang Z, Lv X, Zhi S, Wang Y, Li Q , et al. Novel electro-dewatering system for activated sludge biosolids in bench-scale, pilot-scale and industrial-scale applications. Chemical Engineering Research and Design. 2017;121:44-56'},{id:"B3",body:'Buta M, Hubeny J, Zieliński W, Harnisz M, Korzeniewska E. 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Effects of polystyrene microplastics on the fitness of earthworms in an agricultural soil. In: IOP Conference Series: Earth and Environmental Science. Vol. 61. 2017. p. 012148'},{id:"B110",body:'Gao Q , Xu J, Bu XH. Recent advances about metal–organic frameworks in the removal of pollutants from wastewater. Coordination Chemistry Reviews. 2019;378:17-31'},{id:"B111",body:'Pignattelli S, Broccoli A, Renzi M. Physiological responses of garden cress (L. sativum) to different types of microplastics. Science of the Total Environment. 2020;727:138609'},{id:"B112",body:'Hernández-Arenas R, Beltrán-Sanahuja A, Navarro-Quirant P, Sanz-Lazaro C. The effect of sewage sludge containing microplastics on growth and fruit development of tomato plants. Environmental Pollution. 2021;268:115779'},{id:"B113",body:'Plekancová M, Szabová P, Šefčíková T, Bodik I, Grabic R, Staňová AV. Čo sa deje s farmaceutikami v tepelne upravenom kale? In: 29 konferencia KALY A ODPADY [Internet]. 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Faculty of Biology, Department of Microbiology and Biotechnology, University of Latvia, Latvia
Institute of Soil and Plant Sciences, Latvia University of Life Sciences and Technologies, Latvia
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UK Research and Innovation (former Research Councils UK (RCUK) - including AHRC, BBSRC, ESRC, EPSRC, MRC, NERC, STFC.) Processing charges for books/book chapters can be covered through RCUK block grants which are allocated to most universities in the UK, which then handle the OA publication funding requests. It is at the discretion of the university whether it will approve the request.)
Wellcome Trust (Funding available only to Wellcome-funded researchers/grantees)
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Aalborg University has Two Satellite Campuses, one in Copenhagen (Aalborg University Copenhagen) and the other in Esbjerg (Aalborg University Esbjerg).\n· He is a member of prestigious IEEE (Institute of Electrical and Electronics Engineers), and IAENG (International Association of Engineers) organizations. \n· He is the chief Editor of the Journal of Software Engineering.\n· He is the member of the Editorial Board of International Journal of Computer Science and Software Technology (IJCSST) and International Journal of Computer Engineering and Information Technology. \n· He is also the Editor of Communication in Computer and Information Science CCIS-20 by Springer.\n· Reviewer For Many Conferences\nHe is the lead person in making collaboration agreements between Aalborg University and many universities of Pakistan, for which the MOU’s (Memorandum of Understanding) have been signed.\nProfessor Akbar is working in Academia since 1990, he started his career as a Lab demonstrator/TA at the University of Sussex. After finishing his P. hD degree in 1992, he served in the Industry as a Scientific Officer and continued his academic career as a visiting scholar for a number of educational institutions. In 1996 he joined National University of Science & Technology Pakistan (NUST) as an Associate Professor; NUST is one of the top few universities in Pakistan. In 1999 he joined an International Company Lineo Inc, Canada as Manager Compiler Group, where he headed the group for developing Compiler Tool Chain and Porting of Operating Systems for the BLACKfin processor. The processor development was a joint venture by Intel and Analog Devices. In 2002 Lineo Inc., was taken over by another company, so he joined Aalborg University Denmark as an Assistant Professor.\nProfessor Akbar has truly a multi-disciplined career and he continued his legacy and making progress in many areas of his interests both in teaching and research. 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by"}},{type:"book",id:"7687",title:"Reliability and Maintenance",subtitle:"An Overview of Cases",isOpenForSubmission:!1,hash:"14790fdcb395faea44e1351e45cb20a5",slug:"reliability-and-maintenance-an-overview-of-cases",bookSignature:"Leo Kounis",coverURL:"https://cdn.intechopen.com/books/images_new/7687.jpg",editedByType:"Edited by",editors:[{id:"111582",title:"Dr.",name:"Leo",middleName:"Dimitrios",surname:"Kounis",slug:"leo-kounis",fullName:"Leo Kounis"}],equalEditorOne:null,equalEditorTwo:null,equalEditorThree:null,productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}},{type:"book",id:"9373",title:"Engineering Failure Analysis",subtitle:null,isOpenForSubmission:!1,hash:"c9ba52779a6412cacf546d387eb932f3",slug:"engineering-failure-analysis",bookSignature:"Kary Thanapalan",coverURL:"https://cdn.intechopen.com/books/images_new/9373.jpg",editedByType:"Edited by",editors:[{id:"219186",title:"Dr.",name:"Kary",middleName:null,surname:"Thanapalan",slug:"kary-thanapalan",fullName:"Kary Thanapalan"}],equalEditorOne:null,equalEditorTwo:null,equalEditorThree:null,productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}},{type:"book",id:"6197",title:"System of System Failures",subtitle:null,isOpenForSubmission:!1,hash:"4ff73e8bf2376a39046fe3b26e18da0e",slug:"system-of-system-failures",bookSignature:"Takafumi Nakamura",coverURL:"https://cdn.intechopen.com/books/images_new/6197.jpg",editedByType:"Edited by",editors:[{id:"206988",title:"Dr.",name:"Takafumi",middleName:null,surname:"Nakamura",slug:"takafumi-nakamura",fullName:"Takafumi Nakamura"}],equalEditorOne:null,equalEditorTwo:null,equalEditorThree:null,productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}},{type:"book",id:"5720",title:"Failure Analysis and Prevention",subtitle:null,isOpenForSubmission:!1,hash:"f79dd2c5b85e97fc2d94924ff4931bb1",slug:"failure-analysis-and-prevention",bookSignature:"Aidy Ali",coverURL:"https://cdn.intechopen.com/books/images_new/5720.jpg",editedByType:"Edited by",editors:[{id:"13626",title:"Prof.",name:"Aidy",middleName:null,surname:"Ali",slug:"aidy-ali",fullName:"Aidy Ali"}],equalEditorOne:null,equalEditorTwo:null,equalEditorThree:null,productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}},{type:"book",id:"6024",title:"System Reliability",subtitle:null,isOpenForSubmission:!1,hash:"5cf0113f60979705f5b0b0ea0bac3028",slug:"system-reliability",bookSignature:"Constantin Volosencu",coverURL:"https://cdn.intechopen.com/books/images_new/6024.jpg",editedByType:"Edited by",editors:[{id:"1063",title:"Prof.",name:"Constantin",middleName:null,surname:"Volosencu",slug:"constantin-volosencu",fullName:"Constantin Volosencu"}],equalEditorOne:null,equalEditorTwo:null,equalEditorThree:null,productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}},{type:"book",id:"5317",title:"Concise Reliability for Engineers",subtitle:null,isOpenForSubmission:!1,hash:"8dd29c0cfec89eb0c272c374e903b3da",slug:"concise-reliability-for-engineers",bookSignature:"Jaroslav Mencik",coverURL:"https://cdn.intechopen.com/books/images_new/5317.jpg",editedByType:"Authored by",editors:[{id:"142710",title:"Prof.",name:"Jaroslav",middleName:null,surname:"Menčík",slug:"jaroslav-mencik",fullName:"Jaroslav Menčík"}],equalEditorOne:null,equalEditorTwo:null,equalEditorThree:null,productType:{id:"3",chapterContentType:"chapter",authoredCaption:"Authored by"}}],booksByTopicTotal:7,seriesByTopicCollection:[],seriesByTopicTotal:0,mostCitedChapters:[{id:"57936",doi:"10.5772/intechopen.71926",title:"Power System Reliability: Mathematical Models and Applications",slug:"power-system-reliability-mathematical-models-and-applications",totalDownloads:2799,totalCrossrefCites:5,totalDimensionsCites:10,abstract:"This chapter deals with power systems reliability including technical, economical, and decisional aspects. Knowing that almost 90% of failures occur in the distribution systems, great interest was dedicated to this part of the system, and the first work was oriented to reliability indices defined as objectives to attempt and as performance measures in the electricity market. Some works deal with the managers’ behavior, and the customers reactions are modeled using economic criteria in uncertain future and inspired from game theory. When studying components, degradation models were introduced and combined with the effects of socks to study the reliability changing during system operation. In some works, the correlation between maintenance policies and reliability aspects was highlighted. In a recent work, considering the importance of new technologies integration and renewable energy insertion to power systems, it was revealed that reliability aspects and energy sustainability are two fundamental issues of progress in a given society.",book:{id:"6024",slug:"system-reliability",title:"System Reliability",fullTitle:"System Reliability"},signatures:"Rabah Medjoudj, Hassiba Bediaf and Djamil Aissani",authors:[{id:"182165",title:"Dr.",name:"Rabah",middleName:null,surname:"Medjoudj",slug:"rabah-medjoudj",fullName:"Rabah Medjoudj"},{id:"182167",title:"Prof.",name:"Djamil",middleName:null,surname:"Aissani",slug:"djamil-aissani",fullName:"Djamil Aissani"},{id:"208149",title:"Ms.",name:"Hassiba",middleName:null,surname:"Bediaf",slug:"hassiba-bediaf",fullName:"Hassiba Bediaf"}]},{id:"56062",doi:"10.5772/intechopen.69721",title:"A Decision Support System for Planning and Operation of Maintenance and Customer Services in Electric Power Distribution Systems",slug:"a-decision-support-system-for-planning-and-operation-of-maintenance-and-customer-services-in-electri",totalDownloads:1702,totalCrossrefCites:4,totalDimensionsCites:7,abstract:"This chapter aims to present the design and development of a decision support system (DSS) for the analysis, simulation, planning, and operation of maintenance and customer services in electric power distribution system (EPDS). The main objective of the DSS is to improve the decision‐making processes through visualization tools and simulation of real cases in the EPDS, in order to allow better planning in the short, medium, and long term. Therefore, the DSS helps managers and decision‐makers to reduce maintenance and operational costs, to improve system reliability, and to analyze new scenarios and conditions for system expansion planning. First, we introduce the key challenges faced by the decision‐makers in the planning and operation of maintenance and customer services in EPDS. Next, we discuss the benefits and the requirements for the DSS design and development, including use cases modeling and the software architecture. Afterwards, we present the capabilities of the DSS and discuss important decisions made during the implementation phases. We conclude the chapter with a discussion about the obtained results, pointing out the possible enhancements of the DSS, future extensions, and new use cases that may be addressed.",book:{id:"6024",slug:"system-reliability",title:"System Reliability",fullTitle:"System Reliability"},signatures:"Carlos Henrique Barriquello, Vinícius Jacques Garcia, Magdiel\nSchmitz, Daniel Pinheiro Bernardon and Júlio Schenato Fonini",authors:[{id:"180154",title:"Dr.",name:"Daniel",middleName:"P",surname:"Bernardon",slug:"daniel-bernardon",fullName:"Daniel Bernardon"},{id:"180657",title:"Dr.",name:"Vinicius Jacques",middleName:"Jacques",surname:"Garcia",slug:"vinicius-jacques-garcia",fullName:"Vinicius Jacques Garcia"},{id:"203699",title:"Dr.",name:"Carlos",middleName:null,surname:"Barriquello",slug:"carlos-barriquello",fullName:"Carlos Barriquello"},{id:"206560",title:"Mr.",name:"Magdiel",middleName:null,surname:"Schmitz",slug:"magdiel-schmitz",fullName:"Magdiel Schmitz"},{id:"206562",title:"BSc.",name:"Júlio",middleName:null,surname:"Schenato Fonini",slug:"julio-schenato-fonini",fullName:"Júlio Schenato Fonini"}]},{id:"66913",doi:"10.5772/intechopen.85571",title:"Reliability Evaluation of Power Systems",slug:"reliability-evaluation-of-power-systems",totalDownloads:2013,totalCrossrefCites:3,totalDimensionsCites:6,abstract:"Reliability evaluation of electric power systems is an essential and vital issue in the planning, designing, and operation of power systems. An electric power system consists of a set of components interconnected with each other in some purposeful and meaningful manner. The object of a reliability evaluation is to derive suitable measures, criteria, and indices of reliable and dependable performance based on component outage data and configuration. For evaluating generated reliability, the components of interest are the generating units and system configuration, which refer to the specific unit(s) operated to serve the present or future load. The indices used to measure the generated reliability are probabilistic estimates of the ability of a particular generation configuration to supply the load demand. These indices are better understood as an assessment of system-wide generation adequacy and not as absolute measures of system reliability. The indices are sensitive to basic factors like unit size and unit availability and are most useful when comparing the relative reliability of different generation configurations. The system is deemed to operate successfully if there is enough generation capacity (adequate reserve) to satisfy the peak load (maximum demand). Firstly, generation model and load model are convolved (mutually combined) to yield the risk of supply shortages in the system. Secondly, probabilistic estimates of shortage risk are used as indices of bulk power system reliability evaluation for the considered configuration.",book:{id:"7687",slug:"reliability-and-maintenance-an-overview-of-cases",title:"Reliability and Maintenance",fullTitle:"Reliability and Maintenance - An Overview of Cases"},signatures:"Abdullah M. Al-Shaalan",authors:[{id:"274935",title:"Prof.",name:"Abdullah",middleName:"Mohammed",surname:"Al-Shaalan",slug:"abdullah-al-shaalan",fullName:"Abdullah Al-Shaalan"}]},{id:"56115",doi:"10.5772/intechopen.69440",title:"Mixed-Mode Delamination Failures of Quasi-Isotropic Quasi- Homogeneous Carbon/Epoxy Laminated Composite",slug:"mixed-mode-delamination-failures-of-quasi-isotropic-quasi-homogeneous-carbon-epoxy-laminated-composi",totalDownloads:1355,totalCrossrefCites:5,totalDimensionsCites:5,abstract:"This chapter characterised the delamination behaviour of a quasi-isotropic quasi-homogeneous (QIQH) multidirectional carbon/epoxy-laminated composite. The delaminated surface constituted of 45°//0 layers. Specimens were tested using mode I double cantilever beam (DCB), mode II end-notched flexure (ENF) and mixed-mode I+II mixed-mode flexure (MMF) tests at constant crosshead speed of 1 mm/min. Results showed that the fracture toughness increased with the mode II component. Specifically, the mode I, mode II and mixed-mode I+II fracture toughness were 508.17, 1676.26 and 927.52 N/m, respectively. When the fracture toughness values were fitted using the Benzeggagh-Kenane (BK) criterion, it was found that the best-fit material parameter, η, was attained at 1.21. Furthermore, fibre bridging was observed in DCB specimens, where the steady-state fracture toughness was approximately 80% higher compared to the mode I fracture toughness. Finally, through scanning electron micrographs, it was found that there was resin-rich region at the crack tip of the specimens. In addition, fibre debonding of the 45°layer was found to be dominant in the DCB specimens. Significant shear cusps were noticed in the ENF specimens. As for the MMF specimens, matrix cracking and fibre debonding of the 0°layer were observed to be the major failure mechanisms.",book:{id:"5720",slug:"failure-analysis-and-prevention",title:"Failure Analysis and Prevention",fullTitle:"Failure Analysis and Prevention"},signatures:"Mahzan Johar, King Jye Wong and Mohd Nasir Tamin",authors:[{id:"196884",title:"Prof.",name:"Mohd Nasir",middleName:null,surname:"Tamin",slug:"mohd-nasir-tamin",fullName:"Mohd Nasir Tamin"},{id:"197028",title:"Dr.",name:"King Jye",middleName:null,surname:"Wong",slug:"king-jye-wong",fullName:"King Jye Wong"},{id:"203971",title:"Dr.",name:"Mahzan",middleName:null,surname:"Johar",slug:"mahzan-johar",fullName:"Mahzan Johar"}]},{id:"55938",doi:"10.5772/intechopen.69286",title:"Imperfect Maintenance Models, from Theory to Practice",slug:"imperfect-maintenance-models-from-theory-to-practice",totalDownloads:2147,totalCrossrefCites:2,totalDimensionsCites:5,abstract:"The role of maintenance in the industrial environment changed a lot in recent years, and today, it is a key function for long-term profitability in an organization. Many contributions were recently written by researchers on this topic. A lot of models were proposed to optimize maintenance activities while ensuring availability and high-quality requirements. In addition to the well-known classification of maintenance activities—preventive and corrective—in the last decades, a new classification emerged in the literature regarding the degree of system restoration after maintenance actions. Among them, the imperfect maintenance is one of the most studied maintenance types: it is defined as an action after which the system lies in a state somewhere between an “as good as new” state and its pre-maintenance condition “as bad as old.” Most of the industrial companies usually operate with imperfect maintenance actions, even if the awareness in actual industrial context is limited. On the practical definition side, in particular, there are some real situations of imperfect maintenance: three main specific cases were identified, both from literature analysis and from experience. Considering these three implementations of imperfect maintenance actions and the main models proposed in the literature, we illustrate how to identify the most suitable model for each real case.",book:{id:"6024",slug:"system-reliability",title:"System Reliability",fullTitle:"System Reliability"},signatures:"Filippo De Carlo and Maria Antonietta Arleo",authors:[{id:"161657",title:"Dr.",name:"Filippo",middleName:null,surname:"De Carlo",slug:"filippo-de-carlo",fullName:"Filippo De Carlo"},{id:"171361",title:"Dr.",name:"Maria Antonietta",middleName:null,surname:"Arleo",slug:"maria-antonietta-arleo",fullName:"Maria Antonietta Arleo"}]}],mostDownloadedChaptersLast30Days:[{id:"50094",title:"Reliability of Systems",slug:"reliability-of-systems",totalDownloads:3450,totalCrossrefCites:1,totalDimensionsCites:0,abstract:"Many objects consist of more components. The mutual arrangement of the individual elements influences the resultant reliability. The formulae are shown for the resultant reliability of series arrangement, as well as for parallel and combined arrangement. The possibility of reliability increasing by means of redundancy is explained, and also the principle of optimal allocation of reliabilities to individual elements. Everything is illustrated on examples.",book:{id:"5317",slug:"concise-reliability-for-engineers",title:"Concise Reliability for Engineers",fullTitle:"Concise Reliability for Engineers"},signatures:"Jaroslav Menčík",authors:[{id:"142710",title:"Prof.",name:"Jaroslav",middleName:null,surname:"Menčík",slug:"jaroslav-mencik",fullName:"Jaroslav Menčík"}]},{id:"50095",title:"Time to Failure of Deteriorating Objects",slug:"time-to-failure-of-deteriorating-objects",totalDownloads:1690,totalCrossrefCites:0,totalDimensionsCites:0,abstract:"This chapter explains the prediction of the time to failure in the following cases: fatigue of metallic components under cyclic loading or in the presence of cracks, static fatigue, wear and creep, variable loading (damage accumulation). Prediction of the time to failure based on monitoring of the changing response. Probabilistic aspects of the lifetime prediction. The determination of the time to failure is illustrated on examples.",book:{id:"5317",slug:"concise-reliability-for-engineers",title:"Concise Reliability for Engineers",fullTitle:"Concise Reliability for Engineers"},signatures:"Jaroslav Menčík",authors:[{id:"142710",title:"Prof.",name:"Jaroslav",middleName:null,surname:"Menčík",slug:"jaroslav-mencik",fullName:"Jaroslav Menčík"}]},{id:"66913",title:"Reliability Evaluation of Power Systems",slug:"reliability-evaluation-of-power-systems",totalDownloads:2013,totalCrossrefCites:3,totalDimensionsCites:6,abstract:"Reliability evaluation of electric power systems is an essential and vital issue in the planning, designing, and operation of power systems. An electric power system consists of a set of components interconnected with each other in some purposeful and meaningful manner. The object of a reliability evaluation is to derive suitable measures, criteria, and indices of reliable and dependable performance based on component outage data and configuration. For evaluating generated reliability, the components of interest are the generating units and system configuration, which refer to the specific unit(s) operated to serve the present or future load. The indices used to measure the generated reliability are probabilistic estimates of the ability of a particular generation configuration to supply the load demand. These indices are better understood as an assessment of system-wide generation adequacy and not as absolute measures of system reliability. The indices are sensitive to basic factors like unit size and unit availability and are most useful when comparing the relative reliability of different generation configurations. The system is deemed to operate successfully if there is enough generation capacity (adequate reserve) to satisfy the peak load (maximum demand). Firstly, generation model and load model are convolved (mutually combined) to yield the risk of supply shortages in the system. Secondly, probabilistic estimates of shortage risk are used as indices of bulk power system reliability evaluation for the considered configuration.",book:{id:"7687",slug:"reliability-and-maintenance-an-overview-of-cases",title:"Reliability and Maintenance",fullTitle:"Reliability and Maintenance - An Overview of Cases"},signatures:"Abdullah M. Al-Shaalan",authors:[{id:"274935",title:"Prof.",name:"Abdullah",middleName:"Mohammed",surname:"Al-Shaalan",slug:"abdullah-al-shaalan",fullName:"Abdullah Al-Shaalan"}]},{id:"58172",title:"X-Ray Techniques",slug:"x-ray-techniques",totalDownloads:2443,totalCrossrefCites:1,totalDimensionsCites:3,abstract:"This chapter reviewed existing X-ray techniques that can be used for the analysis of materials, inclusive of those used as engineering and structural components. These techniques are X-ray fluorescence (XRF) spectrometry, proton-induced X-ray emission (PIXE) spectrometry, and X-ray diffraction (XRD). These analytical techniques provide qualitative and quantitative information on the composition and structure of materials with precision. XRD gives information on the crystalline forms and amorphous content of materials, which could be quite useful in failure analysis if the type of failure brings about morphological changes in the material under investigation. PIXE and XRF provide information on the types of elements present in a sample material and their concentrations. PIXE is however preferable to XRF due to its higher sensitivity to trace elements and lower atomic number elements as well as its faster analysis. XRF and XRD are more commonly used than PIXE which is a powerful, high-tech method that is relatively new in the field of chemical research. In this chapter, the theory and principles of these analytical techniques are explained, and diagrams showing the components of spectrometers and diffractometers are provided with descriptions of how they function.",book:{id:"5720",slug:"failure-analysis-and-prevention",title:"Failure Analysis and Prevention",fullTitle:"Failure Analysis and Prevention"},signatures:"Clementina Dilim Igwebike-Ossi",authors:[{id:"219931",title:"Dr.",name:"Clementina",middleName:null,surname:"Igwebike-Ossi",slug:"clementina-igwebike-ossi",fullName:"Clementina Igwebike-Ossi"}]},{id:"57936",title:"Power System Reliability: Mathematical Models and Applications",slug:"power-system-reliability-mathematical-models-and-applications",totalDownloads:2799,totalCrossrefCites:5,totalDimensionsCites:10,abstract:"This chapter deals with power systems reliability including technical, economical, and decisional aspects. Knowing that almost 90% of failures occur in the distribution systems, great interest was dedicated to this part of the system, and the first work was oriented to reliability indices defined as objectives to attempt and as performance measures in the electricity market. Some works deal with the managers’ behavior, and the customers reactions are modeled using economic criteria in uncertain future and inspired from game theory. When studying components, degradation models were introduced and combined with the effects of socks to study the reliability changing during system operation. In some works, the correlation between maintenance policies and reliability aspects was highlighted. In a recent work, considering the importance of new technologies integration and renewable energy insertion to power systems, it was revealed that reliability aspects and energy sustainability are two fundamental issues of progress in a given society.",book:{id:"6024",slug:"system-reliability",title:"System Reliability",fullTitle:"System Reliability"},signatures:"Rabah Medjoudj, Hassiba Bediaf and Djamil Aissani",authors:[{id:"182165",title:"Dr.",name:"Rabah",middleName:null,surname:"Medjoudj",slug:"rabah-medjoudj",fullName:"Rabah Medjoudj"},{id:"182167",title:"Prof.",name:"Djamil",middleName:null,surname:"Aissani",slug:"djamil-aissani",fullName:"Djamil Aissani"},{id:"208149",title:"Ms.",name:"Hassiba",middleName:null,surname:"Bediaf",slug:"hassiba-bediaf",fullName:"Hassiba Bediaf"}]}],onlineFirstChaptersFilter:{topicId:"828",limit:6,offset:0},onlineFirstChaptersCollection:[],onlineFirstChaptersTotal:0},preDownload:{success:null,errors:{}},subscriptionForm:{success:null,errors:{}},aboutIntechopen:{},privacyPolicy:{},peerReviewing:{},howOpenAccessPublishingWithIntechopenWorks:{},sponsorshipBooks:{sponsorshipBooks:[],offset:0,limit:8,total:null},allSeries:{pteSeriesList:[],lsSeriesList:[],hsSeriesList:[],sshSeriesList:[],testimonialsList:[]},series:{item:{id:"14",title:"Artificial Intelligence",doi:"10.5772/intechopen.79920",issn:"2633-1403",scope:"Artificial Intelligence (AI) is a rapidly developing multidisciplinary research area that aims to solve increasingly complex problems. In today's highly integrated world, AI promises to become a robust and powerful means for obtaining solutions to previously unsolvable problems. This Series is intended for researchers and students alike interested in this fascinating field and its many applications.",coverUrl:"https://cdn.intechopen.com/series/covers/14.jpg",latestPublicationDate:"June 11th, 2022",hasOnlineFirst:!0,numberOfPublishedBooks:9,editor:{id:"218714",title:"Prof.",name:"Andries",middleName:null,surname:"Engelbrecht",slug:"andries-engelbrecht",fullName:"Andries Engelbrecht",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bRNR8QAO/Profile_Picture_1622640468300",biography:"Andries Engelbrecht received the Masters and PhD degrees in Computer Science from the University of Stellenbosch, South Africa, in 1994 and 1999 respectively. He is currently appointed as the Voigt Chair in Data Science in the Department of Industrial Engineering, with a joint appointment as Professor in the Computer Science Division, Stellenbosch University. Prior to his appointment at Stellenbosch University, he has been at the University of Pretoria, Department of Computer Science (1998-2018), where he was appointed as South Africa Research Chair in Artifical Intelligence (2007-2018), the head of the Department of Computer Science (2008-2017), and Director of the Institute for Big Data and Data Science (2017-2018). In addition to a number of research articles, he has written two books, Computational Intelligence: An Introduction and Fundamentals of Computational Swarm Intelligence.",institutionString:null,institution:{name:"Stellenbosch University",institutionURL:null,country:{name:"South Africa"}}},editorTwo:null,editorThree:null},subseries:{paginationCount:6,paginationItems:[{id:"22",title:"Applied Intelligence",coverUrl:"https://cdn.intechopen.com/series_topics/covers/22.jpg",isOpenForSubmission:!0,annualVolume:11418,editor:{id:"27170",title:"Prof.",name:"Carlos",middleName:"M.",surname:"Travieso-Gonzalez",slug:"carlos-travieso-gonzalez",fullName:"Carlos Travieso-Gonzalez",profilePictureURL:"https://mts.intechopen.com/storage/users/27170/images/system/27170.jpeg",biography:"Carlos M. Travieso-González received his MSc degree in Telecommunication Engineering at Polytechnic University of Catalonia (UPC), Spain in 1997, and his Ph.D. degree in 2002 at the University of Las Palmas de Gran Canaria (ULPGC-Spain). He is a full professor of signal processing and pattern recognition and is head of the Signals and Communications Department at ULPGC, teaching from 2001 on subjects on signal processing and learning theory. His research lines are biometrics, biomedical signals and images, data mining, classification system, signal and image processing, machine learning, and environmental intelligence. He has researched in 52 international and Spanish research projects, some of them as head researcher. He is co-author of 4 books, co-editor of 27 proceedings books, guest editor for 8 JCR-ISI international journals, and up to 24 book chapters. He has over 450 papers published in international journals and conferences (81 of them indexed on JCR – ISI - Web of Science). He has published seven patents in the Spanish Patent and Trademark Office. He has been a supervisor on 8 Ph.D. theses (11 more are under supervision), and 130 master theses. He is the founder of The IEEE IWOBI conference series and the president of its Steering Committee, as well as the founder of both the InnoEducaTIC and APPIS conference series. He is an evaluator of project proposals for the European Union (H2020), Medical Research Council (MRC, UK), Spanish Government (ANECA, Spain), Research National Agency (ANR, France), DAAD (Germany), Argentinian Government, and the Colombian Institutions. He has been a reviewer in different indexed international journals (<70) and conferences (<250) since 2001. He has been a member of the IASTED Technical Committee on Image Processing from 2007 and a member of the IASTED Technical Committee on Artificial Intelligence and Expert Systems from 2011. \n\nHe has held the general chair position for the following: ACM-APPIS (2020, 2021), IEEE-IWOBI (2019, 2020 and 2020), A PPIS (2018, 2019), IEEE-IWOBI (2014, 2015, 2017, 2018), InnoEducaTIC (2014, 2017), IEEE-INES (2013), NoLISP (2011), JRBP (2012), and IEEE-ICCST (2005)\n\nHe is an associate editor of the Computational Intelligence and Neuroscience Journal (Hindawi – Q2 JCR-ISI). He was vice dean from 2004 to 2010 in the Higher Technical School of Telecommunication Engineers at ULPGC and the vice dean of Graduate and Postgraduate Studies from March 2013 to November 2017. He won the “Catedra Telefonica” Awards in Modality of Knowledge Transfer, 2017, 2018, and 2019 editions, and awards in Modality of COVID Research in 2020.\n\nPublic References:\nResearcher ID http://www.researcherid.com/rid/N-5967-2014\nORCID https://orcid.org/0000-0002-4621-2768 \nScopus Author ID https://www.scopus.com/authid/detail.uri?authorId=6602376272\nScholar Google https://scholar.google.es/citations?user=G1ks9nIAAAAJ&hl=en \nResearchGate https://www.researchgate.net/profile/Carlos_Travieso",institutionString:null,institution:{name:"University of Las Palmas de Gran Canaria",institutionURL:null,country:{name:"Spain"}}},editorTwo:null,editorThree:null},{id:"23",title:"Computational Neuroscience",coverUrl:"https://cdn.intechopen.com/series_topics/covers/23.jpg",isOpenForSubmission:!0,annualVolume:11419,editor:{id:"14004",title:"Dr.",name:"Magnus",middleName:null,surname:"Johnsson",slug:"magnus-johnsson",fullName:"Magnus Johnsson",profilePictureURL:"https://mts.intechopen.com/storage/users/14004/images/system/14004.png",biography:"Dr Magnus Johnsson is a cross-disciplinary scientist, lecturer, scientific editor and AI/machine learning consultant from Sweden. \n\nHe is currently at Malmö University in Sweden, but also held positions at Lund University in Sweden and at Moscow Engineering Physics Institute. \nHe holds editorial positions at several international scientific journals and has served as a scientific editor for books and special journal issues. \nHis research interests are wide and include, but are not limited to, autonomous systems, computer modeling, artificial neural networks, artificial intelligence, cognitive neuroscience, cognitive robotics, cognitive architectures, cognitive aids and the philosophy of mind. \n\nDr. Johnsson has experience from working in the industry and he has a keen interest in the application of neural networks and artificial intelligence to fields like industry, finance, and medicine. \n\nWeb page: www.magnusjohnsson.se",institutionString:null,institution:{name:"Malmö University",institutionURL:null,country:{name:"Sweden"}}},editorTwo:null,editorThree:null},{id:"24",title:"Computer Vision",coverUrl:"https://cdn.intechopen.com/series_topics/covers/24.jpg",isOpenForSubmission:!0,annualVolume:11420,editor:{id:"294154",title:"Prof.",name:"George",middleName:null,surname:"Papakostas",slug:"george-papakostas",fullName:"George Papakostas",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002hYaGbQAK/Profile_Picture_1624519712088",biography:"George A. 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His research interests include computer/machine vision, machine learning, pattern recognition, computational intelligence. \nDr. Papakostas served as a reviewer in numerous journals, as a program\ncommittee member in international conferences and he is a member of the IAENG, MIR Labs, EUCogIII, INSTICC and the Technical Chamber of Greece (TEE).",institutionString:null,institution:{name:"International Hellenic University",institutionURL:null,country:{name:"Greece"}}},editorTwo:null,editorThree:null},{id:"25",title:"Evolutionary Computation",coverUrl:"https://cdn.intechopen.com/series_topics/covers/25.jpg",isOpenForSubmission:!0,annualVolume:11421,editor:{id:"136112",title:"Dr.",name:"Sebastian",middleName:null,surname:"Ventura Soto",slug:"sebastian-ventura-soto",fullName:"Sebastian Ventura Soto",profilePictureURL:"https://mts.intechopen.com/storage/users/136112/images/system/136112.png",biography:"Sebastian Ventura is a Spanish researcher, a full professor with the Department of Computer Science and Numerical Analysis, University of Córdoba. 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He obtained both his M.Sc. and Ph.D. from the University of Liverpool, England, in the field of Intelligent Systems. He is a full professor at the Universidad Autonoma de Queretaro, Mexico, and a member of the National System of Researchers (SNI) since 2009. Dr. Aceves Fernandez has published more than 80 research papers as well as a number of book chapters and congress papers. He has contributed in more than 20 funded research projects, both academic and industrial, in the area of artificial intelligence, ranging from environmental, biomedical, automotive, aviation, consumer, and robotics to other applications. He is also a honorary president at the National Association of Embedded Systems (AMESE), a senior member of the IEEE, and a board member of many institutions. 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