These books synthesize perspectives of renowned scientists from the world’s most prestigious institutions - from Fukushima Renewable Energy Institute in Japan to Stanford University in the United States, including Columbia University (US), University of Sidney (AU), University of Miami (USA), Cardiff University (UK), and many others.
\\n\\n
This collaboration embodied the true essence of Open Access by simplifying the approach to OA publishing for Academic editors and authors who contributed their research and allowed the new research to be made available free and open to anyone anywhere in the world.
\\n\\n
To celebrate the 50 books published, we have gathered them at one location - just one click away, so that you can easily browse the subjects of your interest, download the content directly, share it or read online.
IntechOpen and Knowledge Unlatched formed a partnership to support researchers working in engineering sciences by enabling an easier approach to publishing Open Access content. Using the Knowledge Unlatched crowdfunding model to raise the publishing costs through libraries around the world, Open Access Publishing Fee (OAPF) was not required from the authors.
\n\n
Initially, the partnership supported engineering research, but it soon grew to include physical and life sciences, attracting more researchers to the advantages of Open Access publishing.
\n\n\n\n
These books synthesize perspectives of renowned scientists from the world’s most prestigious institutions - from Fukushima Renewable Energy Institute in Japan to Stanford University in the United States, including Columbia University (US), University of Sidney (AU), University of Miami (USA), Cardiff University (UK), and many others.
\n\n
This collaboration embodied the true essence of Open Access by simplifying the approach to OA publishing for Academic editors and authors who contributed their research and allowed the new research to be made available free and open to anyone anywhere in the world.
\n\n
To celebrate the 50 books published, we have gathered them at one location - just one click away, so that you can easily browse the subjects of your interest, download the content directly, share it or read online.
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1. Introduction
The function of the gut microbiome and the bidirectional communication between the gastrointestinal tract (GIT) and the brain is increasingly recognized in health and disease and disruption in its composition is not unique to the autistic pathology. However, the bidirectional communication between the gut and the brain, “the gut-brain/brain-gut axis” in autism has been relatively understudied. In general, this communication between gut and brain occurs through a direct neuronal pathway via the vagus nerve, the hormonal pathway of several hormones involved in the regulation of food intake, such as cholecystokinin (CCK), ghrelin, leptin and insulin, and by the immunological signaling pathway involving cytokines. Recent studies indicate that the vagus nerve is involved in immunomodulation as suggested by its ability to attenuate the production of proinflammatory cytokines in experimental models of inflammation (de Jonge and Ullola, 2007). Furthermore, the gut microbiome emerges as a major player not only in the maturation of GIT tissue and the gut brain axis but also in brain maturation, through its effect on both the immune and endocrine systems. Many toxins, toxicants, infectious agents, diet or stress, affect an individual’s gut microbiome, which may be especially sensitive during the critical developmental period. Disruption of the developing microbiome may have profound consequences on the developing gut-brain axis including the brain as well as long-term effects on both the physical and psychological development.
This chapter attempts to bridge basic animal studies with clinical findings pertaining to the brain-gut and gut microbiome in autism, and includes a discussion of various strategies in managing autistic symptoms. The discussion also includes possible changes in the reward system(s) in autism as a consequence of altered gut microbiome. It is possible that aberrant regulation of the reward system(s) underlines behavioral abnormalities in ASD that could be targeted by future microbiome-targeting therapies.
2. Effect of perinatal infection and toxicants on the developing brain
In a continuing quest to understand the nature of gene-environment interactions in ASD, we have recently completed two animal studies examining the effect of perinatal exposure of thimerosal (TM) and lipopolysaccharides (LPS) on the developing rat central nervous system (CNS). Both TM and infections (modeled by LPS exposure) have been implicated in autistic pathology.
Organic mercury compounds are powerful toxicants with a range of harmful neurological effects in humans and animals. TM, which is metabolized to ethyl mercury, has been discontinued as a preservative from infant vaccines but continues to be used in several vaccines including a flu vaccine administered to pregnant and lactating mothers (Sulkowski et al., 2012). Perinatal maternal exposure of two strains of rats, Sprague Dawley (SD) and spontaneously hypertensive (SHR) rats, to thimerosal (200 ug/kg body weight) resulted in both sex- and strain-specific abnormalities in the neonatal rats (Sulkowski et al., 2012). Behavioral abnormalities included delayed startle response and decreased motor learning, with the effects being both sex- and strain-specific. TM exposure also resulted in a significant increase in cerebellar levels of an oxidative stress marker (3-nitrotyrosine) and a decrease in cerebellar type 2 deiodinase, responsible for local intrabrain conversion of thyroxine to the active hormone, 3’,3,5,-triiodothyronine (T3). These effects were associated with an increased expression of several genes negatively regulated by T3 (Sulkowski et al., 2012); Khan et al., 2012) suggesting that perinatal exposure to TM impacts the developing brain at the genetic level. As TM exposure during the postnatal phase coincided with lactation, some of the TM was delivered through the milk to the GIT and may have had an effect on the developing gut microbiome known to be sensitive to heavy metal exposure (Lapanje et al., 2007). This effect may be in part due to competition with zinc resulting in a disturbance in metallothionein function and general chelating capacity for other metals. Thus, at least part of the neonatal impact of TM/mercury could be mediated via its action on the gut microbiome.
In a related study (Xu et al., submitted) we examined the effect of E.coli lipopolysaccharides (LPS) exposure during critical developmental periods on the developing brain employing the animal model of infection. Clinical and epidemiological data suggest that maternal infection during pregnancy and nursing increases the probability of neonatal brain injury and may have a long-lasting impact on brain functions. Maternal infection during pregnancy has been linked to neurological and neurobehavioral disorders in humans such as cerebral palsy (Schendel, 2001; Schendel et al., 2002), neonatal strokes (Ferrieo, 2004), schizophrenia (Watson et al., 1999; Pearce, 2001) and affective disorders (Watson et al., 1999). Animal studies implicate bacterial infection in the pathology of Parkinson’s disease (Carvey et al., 2003), and notably, schizophrenia and autism (Patterson, 2002). The triggering signals for cytokine production are endotoxins, major components of the outer membrane of Gram-negative bacteria.
LPS exposure is one of the most acceptable models of infection; LPS is a sufficient trigger for cytokine production. LPS administered to the pregnant mother are transferred to the fetus through the placenta (Kohmura et al., 2000), and result in increased cytokines levels in the amniotic fluid (Urakabo et al., 2001; Gayle et al., 2004) and the fetal brain (Urakabo et al., 2001). Bacterial infection of lactating mothers also results in an increased level of cytokines in milk (Bannerman et al., 2004). Pretreatment of suckling rats with LPS (10 mg/kg-day x 5 days – the dose which produces weak, transient signs of endotoxemia) results in reduced pancreatic secretion and attenuates acute pancreatitis at adult age due to an increased concentration of the antioxidative enzyme SO in the pancreatic tissue, and to the modulation of cytokines production (Jaworek at al., 2007a, b). This late-effect of LPS is accompanied by dose-dependent reduction of mRNA signal for CCK1 receptor on pancreatic acini as well as modified expression of acinar pro-apoptotic heat shock protein-60 (HSP60) and Bax proteins (Jaworek et al., 2007b, 2008). Early postnatal LPS exposure results in inceased expression of toll-like receptor 4 (TLR4) and caspase-3 and 9- proteins in the pancreatic tissue of adult rats (Bonior et al., 2012). These studies clearly indicate that perinatal exposure to LPS may have long lasting consequences on the GIT function, and as expected, though not studied in detail, on the brain-gut axis.
Perinatal maternal exposure of two strains of rats, SHR or SD rat dams to LPS (200 µg/kg body weight) resulted in increased rollover time, delayed startle, and decreased motor learning, with the effects being both strain- and sex-specific. LPS challenge also resulted in a trend towards an increase in cerebellar levels of 3-NT and a decrease in D2 activities in LPS-exposed pups (Xu et al., submitted). Several genes were affected by LPS. Notably Type 2 deiodinase 2 (DIO2) and brain derived neurotrophic factor (BDNF) expression was significantly elevated, while transthyretin (TTR) expression was decreased following LPS exposure. In vitro, acute exposure of cerebellar cultures to LPS resulted in a decreased size of the dendritic area of Purkinje cells. Our data thus demonstrate that perinatal infection impacts the developing cerebellum in a sex- and strain-dependent manner via mechanisms involving oxidative stress, enzymes involved in maintaining local TH homeostasis, and downstream gene expression. Interestingly, gene changes observed in the brains of LPS-exposed rats were distinct from TM-associated gene effect suggesting that the underlying macromolecular mechanism may be trigger-specific.
Perinatal LPS exposure could have a profound effect on the gut microbiome similar to the effect of repeated treatment with antibiotics. Experiments in healthy mice have shown that disrupting the normal balance of the gut microbiome with antibiotics caused changes in mice behavior and was accompanied by changes in BDNF which has been linked to depression and anxiety (Bercik et al., 2011; Neufeld et al., 2011). Perinatal LPS exposure most likely affects gut motility as suggested by studies of irritable bowel syndrome (IBS), where mild bacterial overgrowth-associated motility disorder can be reversed by antimicrobials (Scarpignato and Pelosini, 1999). Animal studies have also shown that stress can change the composition of the microbiome, where the changes are associated with increased vulnerability to inflammatory stimuli in the GIT. Could gut dysbiosis be induced by recurrent infections? We have observed an increase in neurotrophin levels in the cerebella of rats exposed to LPS (Sajdel-Sulkowska et al, unpublished observation) and brain region-specific changes in neurotrophin levels in ASD (Sajdel-Sulkowska et al., 2011). Together these observations suggest that a bacterial infection could trigger the gut microbiome to induce cytokine overproduction leading to an imbalance of brain neurotrophins and contribute to developmental abnormalities.
3. Effect of environmental perturbations on the developing components of the brain-gut axis: Intestinal permeability, inflammation and gut microbiome
As indicated above the perinatal development of the CNS structure and function greatly depends on the gastrointestinal GIT function. Little is known about the regulation of embryonic gut epithelium or the effect of prenatal infection. The two key developmental time-points in the regulation of the GIT both occur postnatally, the first few days after birth when all gut digestive functions are launched by first colostrum ingestion and the second at weaning when the digestive system has to modify its function following a switch from mother’s milk to solid food. The first time-point is particularly relevant for all mammalian species since it is associated with a complex of dynamic changes in the GIT structure and function leading to a temporary drop in the gut permeability barrier. The secretion of digestive juices (e.g., gastric and pancreatic juice secretion) is obviously close to null before birth. Our studies indicate that in neonatal calves the exocrine pancreas secreted low but measurable amounts of pancreatic juice from the first postnatal day. The secretion responded to colostrum feeding showing a clear-cut cephalic phase associated with plasma pancreatic polypeptide (PP) elevation but no gastric or intestinal phase. Further studies involving vagal blockades and pharmacological cholecystokinin receptor antagonists indicated that in neonatal calves pancreatic response to first colostrum feeding is already controlled by a neuro-hormonal mechanism involving CCK and long vago-vagal reflex (Zabielski et al., 2002). Thus, the brain-gut axis control of the exocrine pancreas observed in one- and two-month old milk-fed calves is already present at birth, only the magnitude of the response increases with age reaching its peak at four weeks. The other GIT function in neonatal calves closely associated with the brain-gut axis control include periodic activity of GIT motility (migrating motor complex, MMC) and secretion (pancreatic juice periodic secretion) observed already two-three days after birth along with plasma PP oscillations (Zabielski et al., 2002). Plasma PP, a marker of efferent vagal activity, increased with age indicating that brain-gut axis further develops after birth (and may be potentially sensitive to any environmental modifications).
Intestinal functions in neonates are far more complex than in adults due to intensive developmental processes. The small intestine is one of the fastest body organs to grow in size postnatally as well as the fastest organ in rebuilding its structure. Relatively little is known regarding the development of the large intestine, a major organ inhabited by gut bacteria. At birth, the small intestinal mucosa is lined by enterocytes ready for rapid uptake of colostral macromolecules (open gut). These enterocytes, so called fetal type enterocytes, are equipped with a system of vesicles and cisterns (apical canalicular system, ACS) which form large size mobile vacuoles in the upper part of the cell enabling the transfer of intact colostral molecules into the blood (Baintner 2002). Approximately two days after birth, following substantial intake of colostral bioactive substances, the permeability of the gut epithelium is dramatically reduced to macromolecules due to the rapid replacement of fetal type enterocytes by adult type enterocytes, a phenomenon known as gut closure; the cell replacement is made by a receptor-mediated apoptosis involving TGF-β1 and TNF-α as mediators (Godlewski et al., 2005, Strzałkowski et al., 2007). Consequently, adult type enterocytes do not contain ACS and large vacuoles. Interestingly, in the gut of neonatal pigs the cells undergoing apoptosis, which is followed by unzipping-zipping events markedly disrupting epithelial cell continuity, are located on the entire length of the villi (Godlewski et al., 2005; see also Fig. 1). In contrast, in adult animals the apoptotic cells are observed only on the villi top, forming a so called extrusion zone. Therefore, in neonates there is a much wider absorptive surface that is potentially subject to environmental stimuli as compared to adults. Though, one population of fetal type enterocytes disappears within the first few days after birth, there is still another population of fetal type enterocytes existing in the lower small intestine, in piglets observed until approximately three weeks after birth. These enterocytes are important for the intracellular digestion of nutrients by lysosomal enzymes, and form digestive vacuoles as a result of non-selective macromolecule uptake. Their massive loss in piglets is observed 2-3 weeks after birth. Nevertheless the protection by intestinal mucus and colostral biologically active peptides and proteins, extensive apoptosis and unzipping-zipping of a great number of epithelial cells at the same time may potentially open epithelial gates for any xenobiotics and harmful bacteria, and thereby facilitate their transfer into blood circulation.
Figure 1.
Packetts of apoptotic cells in the epithelium of neonatal piglets. Massive apoptosis is evidenced by scanning electron microscope (SEM) image by shortened microvilli, several yet unzipped spaces between cells are present. (SEM images generously supplied by dr. Tomasz Skrzypek, Catholic University of Lublin, Poland)
Studies of preterm piglets and intrauterine growth retarded (IUGR) piglets demonstrated that the gut barrier in both groups of animals is open for a longer time than in full-term-appropriate weight piglets. Namely, the lower part of the small intestine of 28 day-old IUGR piglets still contained fetal type enterocytes expressing digestive vacuoles indicating marked delay in gut mucosa development (Mickiewicz et al. 2012 JPP). The gut epithelium continuity in IUGR and preterm neonates is not as finely controlled as in control rats; abnormalities of the gut epithelium may facilitate exposure of the gut and in turn the whole organism to external factors or xenobiotics. It is possible that gut permeability is altered in critically ill children and predispose them to bacterial translocation via a mechanism that creates a hostile environment in the gut and alters the gut microbiome favoring the growth of pathogens that promote bacterial translocation (Papoff et al., 2012).
Recent studies indicate that the vagus nerve is involved in immunomodulation as suggested by its ability to attenuate the production of proinflammatory cytokines in experimental models of inflammation (de Jonge and Ullola, 2007). Furthermore, functional development of the vagus nerve occurs at two stages with the neuronal population in the dorsal motor nucleus of the vagus (DMNV) maturing ahead of the sensory neuron population of the vagal sensory nucleus NTS (Islami et al., 2008). There appears to be an important link between the vagus nerve and memory recall in infancy suggesting that social learning, modulated by autonomic nervous system, may be jeopardized in preterm infants (Haley et al., 2010)
In conclusion, maturation of the autonomic nervous system may be delayed in preterm and IUGR animals. Furthermore, delayed development of the GIT in preterm and IUGR animals, including longer gut permeability, facilitates the toxic effect of external factors including bacterial translocation. Furthermore, the immature gut seemingly fails to stimulate the development of the vagus nerve. Importantly, there is some evidence pointing to altered gut permeability (leaky gut) in autism and possibly genetic predisposition to abnormalities in tight junctions in ASD (White, 2003; de Magistris et al, 2010).
4. Determinants of individual sensitivity of brain-gut axis and gut microbiome to environmental toxins; intrinsic and extrinsic components
Studies of the human microbiome revealed that even healthy individuals differ remarkably in the microbes of the gut. The gut microbiome is regulated by both extrinsic and intrinsic factors. While much of this biodiversity remains unexplained, extrinsic factors such as diet, environment, and early microbial exposure, and the intrinsic factors such as host genetics have been implicated (Human Microbiome Project Consortium, 2012); our own studies (Sulkowski et al., 2012) suggest that sex may play an important role. Diet-derived carbohydrates that are not fully digested in the upper gut are metabolized by bacteria in the human large intestine. These nondigestable carbohydrates influence microbial fermentation and total bacterial number in the colon. Human milk, unlike milk of other mammalian species, contains high amounts of oligosaccharides of yet unknown function, but one can speculate that dietary oligosaccharides may play an important function in the development of the microbiome in human neonates. Evidence exists that the amount and type of nondigestable carbohydrates influence the species composition of the intestinal microbiome. Individual variation in the gut microbiome may, in part reflect differences in dietary intake, but the response of the gut microbiome to dietary change can also differ among individuals (Flint, 2012)
Furthermore, an outcome of the exposure to infectious microbes or their toxins is also influenced by both microbial and host genes. Some host genes encode defense mechanisms, whereas others assist pathogen function. Extensive human diversity in cell lethality dependent on toxin binding and uptake has been observed (Martchenko et al., 2012). Furthermore, there is evidence that individuals may evolve their own specific microbiome (Clayton, 2012).
Results of our recent animal studies (Sulkowski et al, 2012; Khan et al, 2012, Xu et al, submitted; see also Fig. 2) indicate that the sensitivity of the developing CNS to both environmental toxins and infection, are both sex- and rat strain-dependent. It can be extrapolated that the sensitivity of the human microbiome is also sex-dependent. Because of this individual variability in host response it is not surprising that the results of human postmortem studies of ASD brains are difficult to interpret.
Figure 2.
The effect of LPS exposure on cerebellar gene expression. Gene expression was measured by quantitative RT-PCR in cerebellar tissue of rat pups exposed perinatally to LPS (200μg/kg BW) and was normalized to cyclophilin A. Panel A: males, Panel B: females. Data are presented as relative gene expression (mean±S.E.M.; *, p< 0.05; +, p< 0.1; Xu et al., submitted).
5. Microbiome
The human GIT harbors a large number (1000 to 1150) of bacterial species and is involved in maintaining homeostasis and well-being. Functions of this microbiome include the regulation of the mucosal immune system, GIT motility, epithelial barrier regulation, gut secretion, digestion and metabolism (Grenham et al., 2011). One of the main functions of gut microbes is to extract nutrients from otherwise indigestible fibers (Tremaroli and Backhed, 2012). The microbiome, absent at birth, is gradually colonized by facultative bacteria and anaerobic bacteria (Grenham et al., 2011).
Several lines of evidence point to both brain-gut axis and gut microbiome abnormalities in autism which are summarized in Fig 3. Children with ASD frequently present a variety of gastrointestinal (GI) symptoms, although some claim that the data supporting increased GI symptomology in autistic children not to be rigorous enough (Erickson et al., 2005). The so-called “bacterial theory” of autism proposes the GIT symptoms are associated with changes in microbial composition and that these changes could be involved in the pathogenesis or progression of several childhood diseases including autism (Somma et al., 2010).
Figure 3.
Altered gut microbiome and the brain gut axis in autism. S-R-CTR, social reward center; F-R CTR, food reward center.
It has been suggested that an abnormal gut microbiome in some ASD children may be due to certain antimicrobial drugs that play a key role in modifying the intestinal bacterial flora and selecting potentially harmful bacteria normally kept at bay by the innate intestinal flora. And so, both Clostridia (Finegold, 2011b) and Desulfovibrio (Finegold, 2011a) have been implicated in autistic pathology. Clostridia form spores and the spores could likely survive antibiotic treatment and subsequently flourish. Desulfovibrio is an anaerobic bacillus that does not produce spores and is resistant to some antibiotics such as cephalosporins used in treatment of common childhood diseases such as ear infections (Finegold, 2011a). An increase in Bacteroides, a decrease in Firmicutes with an overall increase in biodiversity has been observed in IBD, celiac disease and autism (Iebba et al., 2011). An increase in Clostridium histolyticum, a recognized toxin producer with systemic effects, has been observed in fecal samples of ASD children (Parracho et al., 2005). A strong correlation of gastrointestinal symptoms with autism, and a decrease in Bifidobacteria and increase in Lactobacilli, was observed in fecal samples of ASD children (Adams et al., 2011). An association between high levels of intestinal, mucoepithelial-associated Sutterella species and GI disturbances has been detected in intestinal biopsy samples in children with autism (Williams et al., 2012). This latter study may provide the most accurate picture of the gut microbiome as the data were derived directly from the gut.
A response to oral treatment with vancomycin, not absorbed from the GI tract, in autism suggests the importance of gut flora in a disease (Finegold, 2011a). Evidence suggests that ASD may be associated with altered innate immune response; thus children with GI problems may reflect inflammation as a reaction to an endotoxin produced by gut bacteria (Jyonouchi et al, 2002).
Our most recent studies suggest altered expression of ghrelin, the activating enzyme (ghrelin O-acyltransferase, GOAT) and the receptor in several brain areas of autistic children (Sajdel-Sulkowska, unpublished observation). A decrease in ghrelin mRNA has been also observed in the temporal gyrus of Alzheimer patients (Gahete et al., 2010) suggesting ghrelin may contribute to the severity of AD pathology. Since we have measured the levels of ghrelin mRNA, it can be assumed that the changes observed were due to the altered levels of brain ghrelin.
The majority of circulating ghrelin is synthesized by gastric mucosa X/A-like cells in response to negative energy status. These cells are not typical endocrine cells since the oxyntic mucosa cells produce HCl in the stomach lumen and ghrelin as a hormone. Ghrelin is the most potent orexigenic peptide, and plays an important role in glucose metabolism and also in GIT cytoprotection. In addition to its ability to stimulate appetite, ghrelin stimulates the release of growth hormone release via the growth secretagogue, GHS-R1a receptor. Ghrelin O-acyltransferase, GOAT, is the enzyme that activates ghrelin. The ghrelin/GHS-R/GOAT system may play an important role in metabolic disorders in children (Lim and Korbonits, 2012). In addition to the ghrelin of GIT origin, and the hypothalamus being the main source of brain ghrelin, ghrelin has been detected in the midbrain, hindbrain, hippocampus, spinal cord and several organs outside the brain. While the systemic endogenous ghrelin exerts a tonic stimulating effect on hypothalamic CRH (Rucinski et al., 2012), its function in the brain includes the modulation of membrane excitability, control of neurotransmitter release, neuronal gene expression, and neuronal survival and proliferation (Ferrini et al., 2009).
It has been reported that ghrelin of GIT origin interacts with bacterial toxins (Tiaka et al., 2011) and exerts a protective role in experimental colitis; is it possible that the ghrelin of brain origin plays a protective role as well? If so, changes in the level of brain-derived ghrelin could be detrimental to the developing brain.
6. Existing and emerging therapeutic strategies in autism targeting the gut-brain axis and gut microbiome: Role of individual microbes and dietary amino acids in maintaining gut-brain homeostasis
Existing therapies targeting the gut microbiome include diet, antibiotics, and probiotics. Dietary restriction, including the removal of dairy casein-containing products, wheat and gluten sources, sugar, chocolate, preservatives, and food coloring have all been found to be therapeutic in autism. Interestingly, dairy casein-containing products stimulate ghrelin (a hunger hormone) and reduce CCK (a satiety agent) production in the periphery and in the brain. Gastrointestinal problems in autism appear to respond to antimicrobial agents. Treatments targeting Candida, and probiotics have been used to reduce disbiosis and control gut permeability (Kidd, 2002). Other strategies include the removal of heavy metals (including mercury) by chelation and sulfur-sulphydryl repletion. Supplementation with dimethylglycine, vitamin B6, magnesium, vitamin B3, C, folic acid, calcium and zinc, cod liver, digestive enzymes, all appear to be beneficial in a number of autistic children (Kidd, 2002). Immune therapies, including pentoxifyllin, immunoglobulin, transfer factors and colostrums appear to work in a limited number of cases,
The initial promising use of secretin, a triggering factor for digestion, in the treatment of autism has been more recently disclaimed. In multiple randomized controlled trials secretin offered no significant benefit (Krishnaswami et al., 2011; Williams et al., 2012).
Abnormalities in the primary pathway for carbohydrate digestion and transporters, involving disaccharidases and hexose transporters, have been reported and found to be accompanied by dysbiosis as evidenced by a decrease in Bactoroidetes and an increase in the ratio of Firmicutes to Bacteroidetes (Williams et al., 2011). These abnormalities respond to probiotic and dietary responses (Williams et al., 2011). Probiotic therapy appears to influence microbiome composition, intestinal barrier function and mucosal immune responses (Critchfield et al., 2011). There is evidence to support alterations of fecal microbiome in autism, and in the majority of cases treatment with vancomycin, an antibiotic that targets gram positive anaerobes and is minimally absorbed by the gut, can improve symptoms (Sandler et al., 2000).
Recently therapies targeting the gut microbiome are emerging as a viable strategy in the treatment of CNS disorders (Forsythe et al., 2010). Preclinical studies of selected probiotics in healthy volunteers (Messaoudi et al., 2011) provided encouraging results for further studies exploring the concept of microbial targeting of the GIT under pathological conditions including autism. Individually tailored probiotic formulations, enriched in specific strains of gut bacteria, could one day be used in treatments of ASD even as an adjuvant to other treatments.
7. Possible connection of gut microbiome and behavior; microbiome and behavioral abnormalities in ASD
The intestinal microbiome participates in the development of the HPA axis (Sudo et al., 2004) and is critical to the development of appropriate stress response later in life, which occurs during a narrow, critical developmental window. This process involves both the regulation of the levels of brain derived neurotrophic factor (BDNF) and NMDA receptors (Sudo et al., 2004). The microbiome also plays an important role in anxiety-like behavior (Messaoudi et al., 2011), depressive behaviors (Neufield et al., 2011; Messaoudi et al., 2011), but the effects are diminished in vagatomized animals, suggesting either the direct communication between the bacteria and the brain (Bravo et al., 2011) or through the brain-gut axis. The latter possibility is an indirect action of bacteria on an afferent vagal pathway via gut immune, endocrine and enteric nervous system (ENS) controlling mechanisms.
Animal studies have also shown that stress can change the composition of the microbiome, where the changes are associated with increased vulnerability to inflammatory stimuli in the GIT (Gareau et al., 2006); here the microbiome plays an important role in memory dysfunction (Gareau et al., 2011). Stress is known to inhibit gut contraction, one of the crucial defense strategies against bacterial colonization of gut mucosa. Early psychological trauma of maternal separation resulted in persistent mucosal barrier dysfunction in neonatal rats, including host defense to luminal bacteria, by mechanisms involving peripheral CRH receptors (Gareau et al., 2006).
Oral antibiotics disrupt the microbiome and favor environment for opportunistic bacteria. Clostridium tetani, an anaerobic bacillus produces a potent neurotoxin, tetanus neurotoxin (TeNT) that is transported by the vagus nerve from the GI to the CNS. In the brain TeNT disrupts the release of neurotransmitters by the proteolytic cleavage of synaptobrevin, a synaptic vesicle membrane protein. This inhibition may be related to a variety of behavioral deficits characteristic of autism. Some children with autism treated with anti-clostridia antibiotics have shown a reduction in stereotyped behavior (Bolte, 1998).
8. The role of the reward system in gut-brain communication, the interaction between food-reward and social-reward systems; altered gut-microbiome regulation of the reward loop in autism?
Autism is characterized by both severe deficits in social interaction and communication and significant eating difficulties with a highly restricted range of food choices (Williams et al., 2000). It seems logical to hypothesize that altered composition of the gut microbiome under a “leaky gut” condition in autism interferes with the normal activity of the reward circuitry including both social and feeding behavior, as illustrated in Fig. 3. In support of this hypothesis are the neuroimaging, electrophysiological and neurochemical data suggesting a disruption in reward seeking tendencies in ASD, and especially in social contexts (Kohls et al., 2012). It has been proposed that this disruption is caused by abnormalities of the dopaminergic-oxytocinergic “wanting circuitry” that includes the ventral striatum, amygdale, and the ventromedial prefrontal cortex (Kohls et al., 2012). Indeed, Individuals with ASD are characterized by low responsiveness to social rewards (Dawson et al., 2005; Schultz, 2005; Neuhaus et al, 2010). Recent studies of the left amygdala and orbito-frontal cortex, which are the main components of the social brain, showed neuronal dysfunctions in these structures in autism (Mori et al, 2012). Furthermore, brain levels of serotonin, the “happy hormone” are regulated by gut bacteria as evidenced by studies involving germ-free animals (Clarke et al., 2012). Abnormalities in blood serotonin levels are consistently altered in a subset of children with ASD.
It is also possible that the abnormalities in vagus nerve functions may further contribute to social deficits in autism (Goetz et al., 2010). ). It is thus of interest (Ito and Craig, 2008) that there is a possibility that the vicerosensory information is sent via the vagus nerve directly to the reward centers. The vagus nerve is involved in our emotional responses and in feelings of compassion as shown in vagal stimulation, suggesting that the social bond is related to the gut-brain axis (Goetz et al., 2010). Studies utilizing single-photon emission tomography (SPET) provide evidence for the limbic system-vagal nerve connection (Barnes et al., 2003). Vagotomy was for decades a method of choice in treating a number of gastric diseases in adults; it would be of interest to address it in context of autistic pathology.
Furthermore, the intestinal microbiome regulates the HPA during both development and adulthood (Sudo et al., 2004) and plays an important role in the stress response. Activation of the HPA axis involves the release of endogenous opioids which are components of the brain reward system (Adam et al., 2007).
In humans, sensory factors, such as taste and smell, have an important role in reward-related feeding (Rolls, 2011); gustatory, olfactory, visual and somatosensory aspects of food are regulated by the orbitofrontal cortex. Environmental cues, as well as cognitive, reward, and emotional factors play an important role in food intake which may override the homeostatic requirements (Berthoud, 2006). Environmental cues regulate endocannabinoid and opioid systems which play an important role in reward-related feeding and have wide receptor distributions within the CNS (Cota et al., 2006). Hypothalamic endocannabinoids increase food intake through a leptin-regulated mechanism. The nucleus accumbens is a key limbic pathway and may be implicated in regulation of hedonistic and homeostatic feeding (Berthoud, 2006). Dopamine appears to be associated with reward-related food intake and with behaviors required to maintain feeding essential for survival (Di Marzo et al., 2001).
The neural circuit mediating reward-related behavior is a complex network that includes the midbrain, substantia nigra, the amygdala, the ventral striatum, the ventromedial prefrontal cortex and ventral anterior cingulated cortex with the central relay located in ventral striatum (Kohls et al., 2012).
It is interesting, that the ventral striatum is associated with both social-reward and food-reward circuitry (Adam et al., 2007). Although it is generally assumed that the two centers are separate, the observation of altered sucrose preference and positive correlation with ventral striatum dopamine levels under conditions of social isolation stress in perinatal rats lends support to the speculation of inter-connectivity of the two centers (Brenes and Fornaguera, 2008).
9. Conclusions
The “leaky gut” during development may be potentially more vulnerable to environmental insults than the normally developing GIT. Consequently, alterations in the gut microbiome may play an important role in autistic pathology. Evidence is growing that points to an early developmental abnormality in establishing GIT and innate microbial milieu. The gut microbiome, regulated by both intrinsic and extrinsic factors, may be further jeopardized by recurrent infections and/or recurrent use of antibiotics. A developmentally abnormal gut microbiome may in turn affect both the gut-brain axis and brain development and contribute to the etiology of ASD. Abnormalities in the gut-brain axis may further lead to the aberrant development of both the social and the food reward system(s) in autism. Future studies targeting the gut-brain/brain-gut axis in autism and the gut microbiome are warranted, but must take into consideration individual variation in gut microbiomes and intrinsic and extrinsic sensitivities and sex. Results of these studies will likely contribute to our understanding of ASD and advance new and viable therapies.
\n',keywords:null,chapterPDFUrl:"https://cdn.intechopen.com/pdfs/43455.pdf",chapterXML:"https://mts.intechopen.com/source/xml/43455.xml",downloadPdfUrl:"/chapter/pdf-download/43455",previewPdfUrl:"/chapter/pdf-preview/43455",totalDownloads:3816,totalViews:480,totalCrossrefCites:1,totalDimensionsCites:4,totalAltmetricsMentions:1,impactScore:3,impactScorePercentile:86,impactScoreQuartile:4,hasAltmetrics:1,dateSubmitted:"April 18th 2012",dateReviewed:"December 6th 2012",datePrePublished:null,datePublished:"March 6th 2013",dateFinished:"March 1st 2013",readingETA:"0",abstract:null,reviewType:"peer-reviewed",bibtexUrl:"/chapter/bibtex/43455",risUrl:"/chapter/ris/43455",book:{id:"3293",slug:"recent-advances-in-autism-spectrum-disorders-volume-i"},signatures:"Elizabeth M. Sajdel-Sulkowska and Romuald Zabielski",authors:[{id:"35197",title:"Prof.",name:"Elizabeth",middleName:null,surname:"Sajdel-Sulkowska",fullName:"Elizabeth Sajdel-Sulkowska",slug:"elizabeth-sajdel-sulkowska",email:"esulkowska@rics.bwh.harvard.edu",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. Effect of perinatal infection and toxicants on the developing brain",level:"1"},{id:"sec_3",title:"3. Effect of environmental perturbations on the developing components of the brain-gut axis: Intestinal permeability, inflammation and gut microbiome ",level:"1"},{id:"sec_4",title:"4. Determinants of individual sensitivity of brain-gut axis and gut microbiome to environmental toxins; intrinsic and extrinsic components",level:"1"},{id:"sec_5",title:"5. Microbiome",level:"1"},{id:"sec_6",title:"6. Existing and emerging therapeutic strategies in autism targeting the gut-brain axis and gut microbiome: Role of individual microbes and dietary amino acids in maintaining gut-brain homeostasis",level:"1"},{id:"sec_7",title:"7. Possible connection of gut microbiome and behavior; microbiome and behavioral abnormalities in ASD ",level:"1"},{id:"sec_8",title:"8. The role of the reward system in gut-brain communication, the interaction between food-reward and social-reward systems; altered gut-microbiome regulation of the reward loop in autism?",level:"1"},{id:"sec_9",title:"9. Conclusions",level:"1"}],chapterReferences:[{id:"B1",body:'Adam TC, Epel ES. Stress, eating and the reward system. Physiology and Behavior 2007; 91:449-458.'},{id:"B2",body:'Adams JB, Johansen LJ, Powell LD, Quig D, Rubin RA. Gastrointestinal flora and gastrointestinal status in children with autism – comparisons to typical children and correlation with autism severity. 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Public health issues related to infection in pregnancy and cerebral palsy. Ment Retard Dev Disabilit Res Rev 2001; 8:39-45.'},{id:"B63",body:'Schultz RT. Developmental deficits in social perception in autism: the role of amygdale and fusiform face area. In J Dev Neurosci 2005; 23:125-141.'},{id:"B64",body:'Sajdel-Sulkowska EM, Xu M, McGinnis W, Koibuchi N. Brain region-specific changes in oxidative stress and neurotrophin levels in autism spectrum disorders (ASD). Cerebellum 2011; 10:43-48.'},{id:"B65",body:'Somma F, Castagnola R, Bollino D, Marigo L. Oral inflammatory process and general health. Part 1: The focal infection and the oral inflammatory lesion. Eur Rev Med Pharmacol Sci. 2010;14:1085-95.'},{id:"B66",body:'Strzałkowski AK, Godlewski MM, Hallay N, Kulasek G, Gajewski Z, Zabielski R. The effect of supplementing sow with bioactive substances on neonatal small intestinal epithelium. J Physiol Pharmacol. 2007; 58 Suppl 3:115-22.'},{id:"B67",body:'Sudo N, Chida Y, Aiba Y, Sonoda J, Oyama N, Yu XN, Kubo C, Koga Y. Postnatal microbial colonization programs the hypothalamic-pituitary-adrenal system for stress response in mice. J Physiol. 2004; 558:263-275.'},{id:"B68",body:'Sulkowski ZL, Chen T, Midha S, Zavacki AM, Sajdel-Sulkowska EM. Maternal thimerosal exposure results in aberrant cerebellar oxidative stress, thyroid hormone metabolism, and motor behavior in rat pups; sex- and strain-dependent effect. Cerebellum 2012; 11:575-586.'},{id:"B69",body:'Tiaka EK, Manolakis AC, Kapsoritakis AN, Potamianos SP. Unraveling the link between leptin, ghrelin and different types of colitis. Annals of Gastroentrology 2420-28.'},{id:"B70",body:'Tremaroli V, Bäckhed F. Functional interactions between the gut microbiota and host metabolism. Nature 2012; 489:242-249. '},{id:"B71",body:'Urakubo A, Jarskog Lf, Lieberman JA, Gilmore JH. Prenatal exposure to maternal infection alters cytokine expression in the placenta, amniotic fluid, and fetal brain. Schizophr Res 2001; 47:27-36.'},{id:"B72",body:'Watson JB, Mednick SA, Huttunen M, Wang X. Prenatal teratogens and the development of adult mental illness. Dev Psychopathol. 1999; 11:457-466.'},{id:"B73",body:'White JF. Intestinal pathophysiology in autism. Exp Biol Med (Maywood).2003; 22:639-649.'},{id:"B74",body:'Williams BL, Hornig M, Parekh T, Lipkin WI. Application of novel PCR-based methods for detection, quantitation, and phylogenic characterization of Sutterella species in intestinal biopsy samples from children with autism and gastrointestinal disturbances. Mbio. 2012; 3. E00261-11.'},{id:"B75",body:'Williams K, Wray JA, Wheeler DM. Intravenous secretin for autism spectrum disorders (ASD). Cochrane Database Syst Rev. 2012; 4:'},{id:"B76",body:'Williams PG, Dalrymple N, Neal J. Eating habits of children with autism. Pediatr Nurs. 2000; 26:259-264.'},{id:"B77",body:'Xu M, Sulkowski ZL, Parekh P, Khan A, Chen T, Midha S, Iwasaki N, Koibuchi N, Zavacki AM, Sajdel-Slkowska EM. Effects of perinatal lipopolysaccharide (LPS) exposure on the developing rat cerebellum; modeling the effect of maternal infection on the developing human CNS Cerebellum (submitted).'},{id:"B78",body:'Zabielski R, Morisset J, Podgurniak P, Romé V, Biernat M, Bernard C, Chayvialle JA, Guilloteau P. Bovine pancreatic secretion in the first week of life: potential involvement of intestinal CCK receptors. Regul Pept. 2002; 103:93-104.'}],footnotes:[],contributors:[{corresp:"yes",contributorFullName:"Elizabeth M. Sajdel-Sulkowska",address:"esulkowska@rics.bwh.harvard.edu",affiliation:'
Dept. Psychiatry Harvard Medical School and BWH, USA
DDept. Physiological Sciences, Warsaw University of Life Sciences, Poland
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Application",doi:"10.5772/intechopen.105439",slug:"biochar-development-as-a-catalyst-and-its-application",body:'
1. Introduction
With energy shortages and pollution escalating worldwide, renewable feedstocks are crucial for human long-term development. There are many natural sources of animal fats, including lignocellulosic biomass, crops, aquatic culture, biowaste generated by waste management, and domestic and urban waste recycling [1]. Utilizing thermochemical decomposition processes like gasification or pyrolysis, biofuels (bio-oil and syngas) can be produced from biomass and a carbon-based solid residue called biochar [2].
As a porous solid with high carbon content, biochar is formed during the thermal decomposition of biomass at moderate temperatures (e.g., 350–700°C) and under oxygen-limited conditions [3, 4, 5, 6, 7]. Despite its chemical and physical properties, biochar’s thermochemical process and the intrinsic properties of biomass feedstock are two of the factors that influence its properties [4]. Due to its porosity and large surface area, biochar is classified as activated carbon (AC), yet it also contains numerous surface functional groups (carbon monoxide, hydroxyl, carbonyl, carboxylic acid, among others) that can be easily tuned and used to make various functionalized carbon materials. As well as being used for AC production and soil amendment, biochar serves as an adsorbent for pollutants in water and air [5].
Recent research has revealed that biochar is widely utilized as support for metals in catalysis, due to its feedstock availability, large surface area (for good metal phase dispersion and stability), low cost, and stability in basic and acidic media [6]. In addition to catalysis, biochar’s excellent performance in supporting and catalyzing a wide range of reactions has been demonstrated: electrochemical reactions, hydrolysis, gasification/pyrolysis, catalytic reforming/cracking, esterification/transesterification, peroxide/peroxynmonosulfate oxidation, and many more.
Biochar-based catalysts have been utilized for a variety of applications, including water and soil remediation. On the other hand, current perspectives tend to concentrate on applications designed to remediate soils, revegetate, and restore them, convert energy, and remove contaminants from water and wastewater. Despite this, there is still a lack of understanding regarding the synthesis, development, and novel applications of biochar-based catalysts. This chapter provides a comprehensive overview of recent developments in the production, application, and limitations of biochar-based catalysts. Various emerging catalytic applications of biochar-based catalysts are also addressed in this chapter. Further, the benefits of using biochar as catalysts and catalyst supports, as well as the correlations between structural and physical properties of biochar, which provide insights into the development of effective and promising biochar-based catalysts will be highlighted. The challenges and future advancements of using biochar-based catalyst materials are further discussed.
1.1 Properties of biochar
Biochar is a form of organic material that is mostly rich in carbon and other elements such as nitrogen (N), oxygen (O), and hydrogen (H). Biochar has a carbon (C) content ranging from 380 to 800g kg−1 and has both alkyl and aromatic structures [7]. Biochar is also composed of inorganic elements including phosphorus (P), calcium (Ca), aluminum (Al), potassium (K), and silicon (Si), whose quantities vary according to the feedstock used [8]. It has been reported that acidic pH can occur during pyrolysis, depending on conditions of production and the raw materials [9]. Other factors can affect the biochar pH, ranging from neutral to alkaline [10]. In general, biochar has a pH between 5 and 12, and its pH tends to increase in response to increased pyrolysis temperature as bionic acid decomposes, and mineral alkali elements increase [11]. Also, the high pH of biochar can be attributed to the functional organic groups present in it, namely hydroxyl-, aldehyde, and ketone- [12]. As a buffer between acid and bases, these functional organic groups influence biochar’s hydrophobicity and hydrophilicity as well as its adsorption properties [8]. The functional organic groups have the effect of lowering the negative charge on biochar, and therefore, enhancing its cation exchange capacity (CEC) [13].
Due to its high carbon content, biochar has a complex microstructure with numerous pores, which maximizes its surface area [14]. Biochar’s surface area and total pore volume typically range from 8 to 132 m2/g and 0.016–0.083 cm3/g, respectively. Using the right precursor and pyrolysis parameters, biochar can have surface areas and pore volumes as high as 490.8 m2/g [15] and 0.25 cm3/g [16]. Following effective post-treatments, such as potassium hydroxide (KOH) activation, the surface area and total pore volume of biochar can be enhanced to 3263 m2/g and 1.772 cm3/g, respectively [17], which is comparable to or even greater than commercial activated carbon. Biochar’s surface area and porosity are greatly affected by the pyrolysis temperature [16]. Biochar with a higher pyrolysis temperature within a certain temperature range has a greater surface area [12]. As temperature rises in biochar pyrolysis, volatile substances are forced out of the char, causing pores to form a larger surface area [17]. Due to its high porosity/high amount of residual pores and large surface area, biochar can retain a large quantity of water [14, 18, 19, 20]. In contrast, a high pyrolysis temperature diminishes the polar functional groups found in biochar, thereby increasing its hydrophobicity [18]. According to the above characteristics, biochar can influence the, pH, soil water-holding capacity, as well as base saturation, and CEC [14]. It is generally possible to modify the properties of biochar by modifying its conditions of preparation [19], as outlined in the next section.
1.2 Biochar production
To produce biochar from different feedstocks, several approaches have been developed. Torrefaction, pyrolysis, gasification, hydrothermal carbonization (HTC), and flash carbonization are the most prominent thermochemical conversion technologies (Figure 1).
Figure 1.
Overview of biochar-based system production and applications.
1.2.1 Torrefaction
Torrefaction is a mild pre-treatment consisting of slow heating at 200–300°C, followed by a short retention time before gasification or pyrolysis [20]. Often, the resultant solid product is porous, low density, and carbon-enriched, with low moisture content and O/C ratio, an increase in energy density, and improved grindability, making it easier to store and deliver [21]. Its carbon yield can be affected by temperature, retention times, raw material types, and furnace atmosphere [22]. At 200°C, for example, beech lignin began to degrade, the majority of biomass developed at 230°C and cellulose only degraded over 270°C [22]. Using a pilot process, hardwood and switchgrass pellets produced solid yields above 77 wt% [23]. Oil palm fiber pellets were torrefied in an inert atmosphere for 30 min and in an oxidizing atmosphere for 30 min at 275–350°C to yield 43 and 65 wt% biochar, respectively [24].
1.2.2 Pyrolysis
Pyrogenic carbons are produced by the decomposition of biomass at 300–1200°C without oxygen (or with limited oxygen). During pyrolysis, biochar is produced at temperatures ranging from 300 to 700°C. A pyrolysis process can be classified into slow, fast, intermediate, flash, and vacuum modes [25].
1.2.2.1 Slow pyrolysis
In slow pyrolysis, the process temperature is lower (400–600°C), the heating rate is slower (~10°C min−1), the vapor residence time is much longer (5–30 minutes), and the holding time is long (hours to days) [25]. Biochar typically yields 20–40 wt%, with yields decreasing with increasing pyrolysis temperature and heating rate [26], however, biochar characteristics are also affected by the procedure and feedstock used [27]. Comparing biochars derived from the wood stem and bagasse with palm kernel shell, paddy straw, and cocopeat, biochar derived from the wood stem and bagasse exhibited a wide range of pores and a high surface area. Biochar develops a significant surface area structure and pore structure at around 500°C [28] with a wide range of mineral compositions and high thermal stability [29].
1.2.2.2 Fast pyrolysis
Fast pyrolysis refers to the treatment of biomass at high temperatures without oxygen [30]. It is usually necessary to dry and grind the feedstock to facilitate effective heat exchange and conversion. This technique produces high liquid yields (bio-oil) rather than solid char (15–25 wt%) [31]. In contrast to the slow pyrolysis of wheat straw, fast pyrolysis generated biochar with a labile un-pyrolyzed carbohydrate fraction (8.8%) rather than carbonized completely [32]. There was a significant difference in the pH, particle size, and specific surface area for biochars produced using these two methods at 400°C, as well as a significant increase in surface area at 500°C (175.4 m2 g−1), in comparison to 300°C (2.9 m2 g−1) and 400°C (4.8 m2 g−1) [21, 33].
1.2.2.3 Intermediate pyrolysis
Intermediate pyrolysis produces 15–35 wt% dry and brittle biochar at temperatures between slow and fast pyrolysis, i.e., solid residence durations of 0.5–25 min, vapor residence times of 2–4 s, and moderate temperatures up to 500°C [34]. Utilizing barley straw and wood pellets, a pilot-scale production yielded 30 wt% char with a carbon content of 75 wt% [25]. The process produces 51.7 wt% char from the organic fraction of municipal solid waste as a result of inert fractions in the biomass [35]. Table 1 illustrates the product yield of pyrolysis processes.
Fast pyrolysis Short hot residence time (<2 s) Moderate temperature (~500°C)
75% (25% water)
15–25%
10–25%
Intermediate pyrolysis Moderate hot vapor residence time Low-moderate temperature (300–400°C)
50% (50% water)
25%
20–30%
Slow pyrolysis Long residence time Low-moderate temperature (200–300°C)
50% (50% water)
35%
35%
Gasification Long vapor residence time High temperature (>700°C)
5% tar (5% water)
10%
85%
Table 1.
Summary of product yield of pyrolysis processes [36].
1.2.3 Gasification
Carbonaceous materials are turned into char, tars, and syngas through gasification at high temperatures (~800°C) in the presence of a gaseous active medium (e.g., carbon dioxide, air, nitrogen, oxygen, steam, or gas mixtures) [37, 38]. During this process, the material is dried, pyrolyzed, partially oxidized, and reduced. Generally, char only makes up 5–10 wt% of the mass of the feedstock [39]. As a by-product of large-scale processes, biochar is produced in large quantities every day. Biochar produced through gasification usually has smaller particles than biochar produced by pyrolysis, lower surface area, and a lower total pore volume [40]. Since the aromatic rings are condensed, gasification chars contain little carbon (20–60 wt%) but are highly stable, preventing microbial mineralization and chemical oxidation; however, their surface chemistry is constrained by their absence of functional groups [34]. Biodiesel generation, catalytic tar decomposition, soil amendment, anode materials for direct carbon fuel cells, and anaerobic digestion additives are just a few of the uses for gasification char [41].
1.2.4 Hydrothermal carbonization
Biomass can be processed using a thermochemical process called hydrothermal carbonization (HTC). In closed vessels with liquid water and autogenous pressure of 2–10 MPa, the feedstock is heated from 200 to 300°C and hydrochar is produced [42]. The thermal stability of hydrochar is improved by high temperatures (300°C). Wet torrefaction or wet pyrolysis are other terms for HTC [43, 44]. In comparison with biochar, hydrochar contains less carbon, ash, surface area, and a smaller pore volume [39].
1.2.5 Flash carbonization
Through flash carbonization, biomass can be transformed into biocarbon (i.e., charcoal) rapidly and efficiently, typically by starting and controlling a flash fire at a high temperature within a packed bed (~1 MPa) [45]. The biomass is transformed into gas and charcoal in less than 30 min when the combustion flame flows in the opposite direction of the airflow. Charcoal yields are typically approximately 40 wt% [45].
1.3 Biochar as a promising catalyst
Biochar can serve as catalyst support. Besides stabilizing and dispersing nanoparticles, biochar can also provide more active sites for catalytic degradation reactions [46]. Biochar’s mesoporous structure enhances the proper dispersion of immobilized metal particles while also preventing particle aggregation owing to intra-particle interaction [47]. The incorporation or fixing of metal elements, for example, magnesium (Mn), copper (Cu), cobalt (Co), and iron (Fe) into biochar pores result in no or minimal metal escape into the aqueous phase [48].
As a heterogeneous catalyst or support, biochar offers many advantages including large surface area, lower cost, functional group tailoring, etc., which makes it highly beneficial for many catalytic applications. There are several intrinsic properties of biochar that contribute to its effectiveness as a catalyst [49]. It has a good thermal, stable structure, mechanical stability, and a chemically hierarchical structure that originates from biomass. Biochar-based catalysts have the following distinctive characteristics: (i) heterogeneity, i.e., the reaction mixture can be easily isolated from other reactants; (ii) bifunctionality, i.e., transesterification and esterification are involved; (iii) recyclable; (iv) porous; (v) non-graphițable, i.e., it does not form crystal at high temperatures [50]. Comparing biochar-based catalysts with other solid-based catalysts, biochar has the advantages of being cost-effective, eco-friendly, easy to produce, reusable, and biodegradable.
Furthermore, biochar as a catalyst can be used in many different fields, including agriculture, environment, and energy, for biodiesel production, tar removal, waste management, production of syngas, production of chemicals, and removal of contaminants, etc. [45, 51]. Biochar is an excellent catalyst with several beneficial properties. Biochar, for instance, is catalytically active in cracking tar because of its presence of inorganic elements including Fe and K [47]. A biochar-supported metal catalyst can be synthesized by adsorbing metal precursors on its surface functional groups [52]. Despite this, biochar has some properties that preclude it from functioning as a catalyst, such as poor porosity and low surface area. Considering that biochar contains more functional groups, it must have a large surface area for catalysis. A functional group, such as OH, adsorbs norfloxacin. Adsorption of ammonium is possible through C〓O and ▬OH groups. To endow biochar with specific properties, it is necessary to develop a variety of modification strategies. Furthermore, several processes can be used to activate feedstocks, control synthesis conditions, functionalize materials on the surfaces, form composites with other materials [53], etc.
1.4 Characteristics of biochar based catalyst
In addition to its properties, biochar’s potential for specific applications is dependent on both the biomass source and the conditions of preparation. Biochar, for instance, is suitable as an electrode material because it is electrically conductive and porous [54]. It has been proven that structurally bound nitrogen groups and high porosity biochar make superior supercapacitor electrode materials [55]. However, the intrinsic inorganics, matrix nature, and surface functionality of biochar have a significant influence on its catalytic performance.
1.4.1 Bulk element and inorganics
The carbon content of activated carbon from coal is approximately 80–95%; however, that content is lower for biochar (45–60 wt%) than carbon black (98%) [5]. Biochar also contains substantial amounts of hydrogen and oxygen. Another characteristic of biochar is that it contains small amounts of inorganic elements like potassium, sodium, calcium, magnesium, sodium, iron, and calcium. The nature of raw biomass greatly affects the amount and composition of inorganics. Woody biomass, as well as herbaceous and hydrophyte biomass, usually have a much lower inorganic content than biochar made from these sources [56, 57].
The inorganic components of biochar are crucial to many of the biochar’s catalytic applications [47], including tar cracking [58], methane decomposition, and bio-oil upgrading [59].
1.4.2 Chemistry of biochar matrix
Amorphous crystalline sheets of high-conjugated aromatics make up most of the biochar matrix. As shown in Figure 2, these aromatic sheets are crosslinked randomly. In response to rising processing temperatures, biochar crystallites increase in size, and order is created throughout the entire structure [62]. The aromatic structure of biochar may also contain heteroatoms, including N, P, and S. These heteroatoms have a different electronegativity from the aromatic C, which results in biochar’s chemical heterogeneity. This plays a key role in catalytic applications [58].
Figure 2.
Chemical structures of (a) pyrochar and (b) hydrochar (adapted from Shi & Lee) [60, 61].
1.4.3 Surface functional groups
Comparing biochar to other carbon materials including (activated carbon and carbon black), Figure 3 shows that it typically contains large numbers of surface functional groups. Biochar can be functionalized using its surface functional groups. Moreover, biochar has been shown to facilitate the loading of metal precursors onto metal catalysts as part of the synthesis of a metal catalyst supported by biochar [52]. Biochar-based catalysts can also work better for certain reactions if they contain some surface functional groups. Biochar-based solid-acid catalysts are typical examples. Kitano, Yamaguchi [63] demonstrated that sulfonated carbon is more effective at hydrolyzing cellohexaose, than sulfonic acid (SO3H)—bearing resins. Adsorption sites, in this case, were found in the carboxylic acid (COOH) and hydroxyl (OH) groups of phenolic groups in the carbon material. Researchers found that the combination of functional groups on biochar-based solid acids was efficient for hydrolyzing cellulose and 1,4-glucan.
Figure 3.
A porous biochar model with multiple functional groups (adapted from Yang et al [61]).
2. Preparation of biochar-based catalyst
Biochar has been activated and functionalized in various ways to adjust its physicochemical properties, leading to enhanced reactivity in a range of processes and applications [48]. Impregnation and physical or chemical activation are the most popular methods. In-situ or post-synthesis methods are employed in such modifications. Biochar-based catalysts have the potential to be a feasible alternative to metal-based catalysts and carbon catalysts driven by fossil fuels. Table 2 lists the types of biomass used to make biochar-based catalysts.
Production methods and feedstocks for biochars and biochar-based catalysts.
2.1 Impregnation
This technique involves mixing feedstock and metallic precursors (in-situ) into biochar structures to incorporate active metallic species into them [64]. With the use of biochar, lignin magnetite pellets were synthesized into zero-valent iron at 900°C [64]. It was possible to remove trichloroethylene by both adsorptive and degradative mechanisms due to the macro-porosity developed. Rice straw biochar was impregnated with cobalt nitrate (Co(NO3)2), then hydrothermally treated and calcined to produce the composite [65]. In comparison to pure biochar (43.0 m2 g−1, 0.081 cm3 g−1) and cobalt (II, III) oxide (CO3O4 (37.0 m2 g−1, 0.184 cm3 g−1), the composite showed greater SBET (62.7 m2 g−1) and total pore volume (0.207 cm3 g−1). The catalyst was shown to be effective for oxidatively degrading ofloxacin (over 90% removal in 10 min) using peroxymonosulfate (PMS). An X-ray photoelectron spectrometer (XPS) study revealed that the rich mesoporous support contains many CO▬OH groups, which are important for activation. The obtained pristine biochar may also contain metal species varying in amounts and characteristics, depending on the biomass source. Despite this, impregnation typically produces composites rather than carbonaceous biochar, so one could compare biochar with impregnated composites and exhausted catalysts.
2.2 Physical activation
A physical activation process involves exposing the pyrolyzed biochar materials to a streamflow control or carbon dioxide or a mixture of both when temperatures exceed 700°C. Gaseous activation agents, depending on the degree of C▬H2O and/or C▬CO2 gasification that occurs at such high temperatures, are capable of partially eroding carbon atoms in the as-prepared biochar matrix [66]. By physically activating the carbonized material, most of the reactive carbon parts can be eliminated and the enclosed pores in the biochar matrix can be opened and interconnected [67]. Consequently, the surface area of biochar increases significantly, resulting in an improved micropore structure and a lower mesopore content [68]. Figure 4 illustrates the process for producing biochar-based catalysts.
Figure 4.
Method involved in producing biochar-based catalyst.
Activated biochars differ significantly from one another in terms of a specific area, pore size distribution, and porosity based on the type of biomass, reaction parameters, and activating gas [66]. Lima et al. [62] for example, evaluated the effects of steam activation on the surface areas and porosities of different biochars, as well as their metal ion adsorptive capabilities. They found that steam-activating biochars at 800°C for 45 minutes dramatically increased the surface area and micropore volume from less than (5 m2 g−1) to (136–793) m2 g−1. In addition, due to the increased porosity and surface area, these biochars were able to improve their metal ion adsorption performance to varying degrees after activation [69]. In addition, Kołtowski et al. [60] utilized steam and CO2 to activate biochar produced from the slow pyrolysis of willow. Their findings revealed that both steam and carbon dioxide activation considerably increased the porosity and surface area of biochar. Additionally, steam-activated biochar (840.6 m2 g−1) and CO2-activated biochar (512.0 m2 g−1) showed significantly larger surface areas than those of unactivated biochar (11.4 m2 g−1). In contrast with the CO2-activated biochar, steam-activated biochar was found to have higher specific surface areas and pores [60].
2.3 Chemical treatment
Chemical activation involves mixing freshly prepared biochar with activation agents (e.g., KOH, ZnCl2, K2CO3, H2SO4, H3PO4, etc.). The biochar is subsequently heated at high temperatures in an inert gas flow [70]. While the mechanism for chemical activation is still unclear, chemical activation is more corrosive than physical activation [71]. However, high temperatures can significantly enhance the corrosion properties of chemical activation substances. Aside from removing some carbon atoms from the biochar matrix, these chemicals might suppress tar formation and/or facilitate the formation of volatile compounds [67]. It was reported by Liu et al. [59], that chemical erosion and physical activation lead to large surfaces and high porosities in KOH-activated biochar, and metallic K intercalation. Chemical activation generally results in a higher activation efficiency than physical activation, and chemical activation may be performed at a relatively lower temperature, resulting in a more porous and higher surface area biochar [43]. Although chemical activation leaves biochar with improved surface area and porosity, it is usually necessary to wash it to remove impregnating agents and salts [50]. The use of chemical activation is, therefore, affected to some extent by several factors, including corrosion of equipment, chemical recycling, secondary pollution, etc. [43].
Several factors affecting the chemically activated biochar, including the temperature of activation, feedstock type, the type, and concentration of the activating agent, etc., are significant [66]. Biochar impregnated with KOH solution has been investigated by Dehkhoda et al. [65] to determine how activation temperature (685–700°C) influenced the electrosorption performance, porosity, and surface area. In their study, there was an increase in the surface area of the biochar from (1.66 m2 g−1) to (614–990 m2 g−1), as well as its porosity, which increased from negligible to 0.6–0.9 m3 g−1. Additionally, as the temperature rises, a decrease in biochar surface area is observed, by collapsing and burning off the micropore walls or causing the formation of graphite-like structures in the matrix. Since biochar activated at 675°C contains more micropores and oxygen-containing functional groups, its overall electrosorption capacitance was more than twice as high as that of activated biochar at 1000°C [68].
3. Application of biochar catalyst
The growing discovery of biochar as a diverse material for catalytic activities has prompted preliminary study into the catalytic potential of biochar as well as applications in different processes.
3.1 Biodiesel production on biochar catalysts
It has been demonstrated that biodiesel can be used as a renewable alternative to traditional petrochemical-derived diesel [67, 72]. The application of traditional catalysts in the synthesis of biodiesel from biomass (vegetable oils) has been extensively explored. However, the manufacture of such catalysts necessitates the use of costly metal precursors. Because of their low cost and versatility, sulfonated biochars have been utilized to produce biodiesel. It has been demonstrated that sulfonated biochar can produce the maximum productivity (88%) of biodiesel products from vegetable oil in the esterification of FFAs (free fatty acids) and transesterification of TGs (triglycerides) carried out simultaneously at 100°C for 15 h [72, 73, 74]. It was observed that after five recycles of the catalyst, the output of methyl esters reduced from 88% to 80%, due to the leaching of ▬SO3H functional groups [74]. Using a biochar catalyst made from palm kernel shells to transesterify sunflower oil, Kostić et al. [69] investigated the catalytic activity. With the deposition of 3 wt% catalysts into a reaction, the production of methyl esters was 99% at 65°C [75]. The solid acid/base biochar catalysts mentioned above resulted in a significant synthesis of biodiesel from a variety of edible oils. In contrast, both catalysts exhibited signs of deactivation after many re-uses in the laboratory. While transesterification was taking place, the base catalyst was contaminated by undesired secondary products formed by CaO and the feed oil interactions [75]. The ester output (from TGs and FFAs) is comparable to that obtained from non-biochar catalysts. However, to make biochar catalysts for biodiesel generation more realistic, the stability of biochar catalysts must be increased to prevent the need for post-treatment processes to remove S or Ca from the catalyst [75]. The biodiesel production efficiency of different biochar and non-biochar-based catalysts is shown in Table 3.
A comparison of biochar and non-biochar-based catalysts for biodiesel production.
3.2 Biomass hydrolysis on biochar catalysts
Biochar catalysis has been applied in biomass hydrolysis. The fact that most biochar-based catalysts are more effective than commercially available and traditional catalysts has long been recognized. According to Ormsby et al. [75], pinewood chips and peanut hulls that were sulfonated with H2SO4 were used as the raw materials for biochar. When used to hydrolyze xylan, the sulfonated pine chip-biochar catalyst demonstrated an 85% transformation rate in 2 h at 393 K. On the other hand, while having a greater surface area (1391 m2g−1) than the biochar catalyst (365 m2g−1), industrial activated carbon only achieved a 57% transformation in 24 hours [84]. Furthermore, biochar catalysts showed greater starting process rates for the hydrolysis of cellobiose and xylan when compared to other catalysts (activated carbon and Amberlyst-15) [84], indicating that they were more efficient than the other two catalysts. Moreover, the hydrolysis of maize stover, switchgrass, and prairie cordgrass biomass was accomplished using a corn stover-biochar mixture [85]. Compared to a traditional homogeneous H2SO4 catalyst, the catalyst exhibited a stronger preference for glucose and xylose, confirming its superior efficiency in biomass hydrolysis. The existence of sulfonated corn stover-based biochar increased the production of glucose and xylose from lignocellulosic biomass [48]. The glucose output was 8–10% and the xylose yield was 23–41% when compared to the equivalent polysaccharide [85]. The findings were equivalent to those obtained from the hydrolysis of model substances using a similar catalyst: cellulose yielded 3% glucose and xylan yielded 40% xylose. This indicated that the biochar was able to sustain good efficiency even when exposed to contaminants and a complex matrix of biomass materials. The performance of different biochar based catalysts for hydrolysis is shown in Table 4.
Feedstock
Condition of catalyst preparation
Feedstocks
Condition of reaction
Catalyst performance
Ref.
Forestry wood waste
Slow pyrolysis at 700°C for 15 h; sulfonated with 30 w/v% H2SO4.
Fructose or maltose
Ccata = 25 w/v%, T = 1 h (maltose: 160°C and fructose: 180°C), CF = 5 w/v%
80% sulfuric acid treatment; immersion in oleum and heating with N2; ultrasonic vibration treatment with NaCl saturated aqueous solution; treatment with an excess of IL-Cu in anhydrous MeCN
Hydroxymethyl furfural = HMF, reducing sugars = RSs, TON = turnover number, temperature = Temp, time = T, catalyst amount = Ccata, feedstocks concentration = CF, imidazolium chloride = IL-Cu; anhydrous MeCN = anhydrous acetonitrile.Source: Adapted from Shan et al. [90].
3.3 Production of biogas
3.3.1 Tar reforming (syngas synthesis)
Tar reforming is the process of converting the hydrocarbon combination that is inevitably generated following the gasification and pyrolysis of biomass into useful syngas (combination of CO and H2). Syngas is a multipurpose intermediate and/or beginning raw material for the synthesis of fuels and chemicals. As a result of this fact, several studies have investigated the potential involvement of biochar catalysts in the generation of syngas in recent years [58]. Biochar comprises catalytic centers that are similar to those found in traditional catalysts, such as dolomites (MgCO3·CaCO3), olivine ((Mg2+, Fe2+)2SiO4), and Ni- and alkali metal-based catalysts, could be efficient for tar reforming [78]. The switchgrass biochar that had been activated by KOH demonstrated the highest efficacy, with around 90% elimination of toluene. This was likely owing to the increased surface area of the switchgrass biochar. Iron calcined biochar [79] and nickel nanoparticle-embedded biochar [80] have also been shown to be efficient. Ren et al. [58] noted that the application of a biochar catalyst improved the quantity of syngas produced during biomass pyrolysis. At 480°C, it was discovered that the syngas output increased from 15 wt% to 46 wt% in the absence and presence of biochar catalyst respectively. According to Ren et al. [58, 81], the hydrogen content in syngas rose significantly with the addition of the biochar catalyst (27 vol%), in contrast to when the catalyst was not employed. A current investigation shows that biochar can be applied in the dry reforming process [82]. The dry reforming of CH4 was carried out on a tungsten carbide [83] Based on a biochar (WC-biochar) catalyst. As the CH4/CO2 ratio rose, the CH4 transformation reduced, while the CO2 transformation improved. Increases in the CH4/CO2 ratio and temperature resulted in greater H2 production, and the WC-biochar catalyst remained stable for 500 hours after being introduced into the system [82].
3.3.2 Tar elimination
The gasification of biomass is a viable sustainable energy pathway since it has the potential to enhance the generation of large quantities of syngas. A consequence of its synthesis, however, is the formation of condensable hydrocarbons (tar). Tars can accumulate in pipelines throughout a system, causing them to become clogged and potentially inhibiting downstream operations [84]. To commercialize biomass gasification for syngas generation, the elimination and/or mitigation of tar is a vital first stage in the procedure [85, 90]. In reality, catalytic tar cracking was carried out at 823–1173 K, with dolomite, olivine, and base metals including nickel [78], serving as catalysts. These conventional tar cracking catalysts, on the other hand, were susceptible to deactivation as a result of coking and contamination [91]. It has been attempted numerous times to degrade tars using a secondary reactor containing noble metal catalysts (e.g., platinum, palladium, and rhodium) [92], but the restoration of the catalyst has remained a difficult process. The introduction of an affordable catalyst for tar breakdown is therefore preferable in this situation. In this regard, biochar was found to be superior to traditional catalysts when used as a catalyst to remove tar [93]. The tar removal efficiency of biochar catalysts is summarized in Figure 5. The majority of investigations have relied on model processes of tar disintegration with toluene, naphthalene, and phenol. Moreover, the biochar-based metal catalysts (e.g., Nickel and Iron) outperformed the typical mineral catalysts in terms of tar removal efficiency. For example, a catalyst constituted of a combination of NiO and wood-biochar eliminated 97% of the genuine tars formed during sawdust gasification, resulting in an improvement in syngas synthesis attributed to the catalytic reformation of the tars [94]. According to Shen et al. [79], bimetallic catalysts based on rice husk-biochar generated seven times fewer tars in the biomass combustion process than monometallic catalysts and raw biochars during the pyrolysis of biomass. The NiO-biochar catalyst combination remained stable for an 8-h time in the stream (TOS). One of the limitations linked to biochar and metal-biochar catalysts for tar reduction is the process temperature, as tar elimination occurs at >973 K. At reduced temperatures (i.e., 843 K) with the typical nickel catalyst, tar removal can be commenced [92], however, biochar is not yet efficient at these lower temperatures [95]. To overcome these restrictions and broaden the scope of biochar’s application as a catalyst, future work must concentrate on overcoming these constraints.
Figure 5.
Evaluation of tar elimination using biochar-based catalysts at 973–1173 K (adapted from Lee et al. [84] with modifications).
3.4 Wastewater treatment
Due to its ability to remedy environmental pollutants, biochars are becoming highly significant for enhancing environmental quality in the world today [96]. Wastewater, which is a result of household, commercial, and agricultural operations, has long been a global concern since it affects everyone. Biochars offer a significant deal of promise for use in wastewater remediation applications. Biochar’s applications in the cleanup of different wastewaters are the primary focus of this section.
3.4.1 Industrial wastewater remediation
Industrial wastewater originates from a variety of sources. In addition, heavy metals and organic contaminants are the most prevalent contaminants in industrial wastewater. It has been demonstrated that biochars can be used in the treatment of industrial effluent. It is possible to cast membranes, beads, and solutions from a biochar-chitosan combination that has been cross-linked. It has the potential to be used efficiently as an adsorbent for the adsorption of heavy metals in industrial wastewater. The amount of chitosan and biochar used in the adsorption of Cu, Pb, As, Cd and other heavy metals in industrial wastewater would depend on the ratio of the two materials [97]. Gliricidia biochar has shown promise in the elimination of crystal violet (CV) from aquatic environments in dye-based industries. A biochar’s pH value, surface area, and pore volume are all important factors to consider throughout the CV sorption process [98]. Biochar made from bagasse was employed to absorb lead from the effluent of the battery production sector. The maximal adsorption ability can attain 13 mg/g, and the adsorptive activity is dependent on the moderate pH value, contact time, and concentration [99]. So far, the majority of the trials on the utilization of biochar in the clean-up of contaminants from industrial wastewater have been carried out in a laboratory environment; however, additional study and deployment in the actual situation are required.
3.4.2 Treatment of municipal wastewater
Biochar can be employed alone or in combination with other techniques for municipal wastewater treatment, resulting in the retrieval of labile nitrogen and phosphorus [100]. Engineered biochar containing aluminum oxyhydroxides (AlOOH) was used to recover and restore phosphorus from tertiary remediated wastewater [101]. The adsorption strategy of phosphorus is mostly based on electrostatic interaction. Phosphorus adsorbed on manufactured biochar has the potential to be used as a slow-release fertilizer for agricultural activities. Biochar generated from digested sludge was employed as an adsorbent for the elimination of NH4 from municipal wastewater. Biochar produced at 723 K has the maximum NH4 reduction capability due to its increased functional group density and surface area, and the procedure is governed by chemisorption [102]. This shows that biochar derived from waste sludge can be utilized to ozonate refinery effluent and achieve a significant reduction rate of total organic carbon (TOC) [103].
3.4.3 Wastewater treatment in the agricultural sector
Because of the rapid development of the agriculture sector, agricultural pollution is getting extremely serious. As a result, pesticides and toxic heavy metals are released into croplands in large quantities, the situation is becoming increasingly worrisome [104, 105]. The use of biochar and its modified forms in the remediation of agricultural wastewater pollution has been investigated. Pesticides such as atrazine and pentachlorophenol are two of the most often used in agriculture. Adsorption of atrazine and imidacloprid from agricultural wastewater by rice straw biochar and phosphoric acid-modified rice straw biochars is much higher than that of adjusted rice straw biochar [106]. Corn straw and soybean biochars both exhibit strong atrazine reduction potentials, with the adsorption efficiency owing mostly to the pH value and pore volume of the biochars [107]. Steam-activated biochar is efficient at eliminating sulfamethazine, and the rate at which it absorbs the substance is reliant on the pH value [108]. The presence of hazardous heavy metals in agricultural wastewater is yet another widespread issue.
4. Emerging advances in the applications of biochar catalyst
Recent advancements in the use of biochar for processes other than agriculture have been linked to biochar’s various properties. Among other characteristics that are suitable for electrode materials, biochar has high porosity and high electrical conductivity [54]. It is preferred to use biochar with structurally bound nitrogen groups and high porosity as electrode materials for supercapacitors [55]. During catalysis, surface functionality, matrix nature, and intrinsic inorganic components are all important factors [49]. Unlike activated carbon derived from coal, biochar has a considerable amount of other organics present in it based on the biomass feedstock. These organics aid its compatibility, utilization, and effectiveness for varying applications than activated carbon.
There are several advantages to using biochar as a catalyst or catalyst support. Firstly, since biomass resources are sustainable and synthesis techniques have been developed, the process for producing biochar is simple and inexpensive. Secondly, the physicochemical properties of biochar can be easily tuned through a variety of methods. As a third consideration, biochar may be of interest in catalytic applications because of its surface functional groups, a hierarchical structure derived from the biomass matrix, and the presence of inorganic species [48]. Additionally, active metals and biochar support may, in some cases, have synergistic effects on catalysis [49].
4.1 Energy storage and conversion
Due to excess energy generation, energy storage is becoming more popular in some developed countries, and stored energy can also be used as a backup in the event of an emergency. The increased use of electric vehicles necessitates the continuous development of batteries with greater energy storage capacity. Despite continuous battery development, there are times when an unplanned situation may occur in electric vehicles. To alleviate such a situation, supercapacitors, which are energy storage devices primarily made of carbon materials, have been applied as continuous power sources in digital communications systems and electric vehicles. Because of its wide availability and low environmental impact, carbon materials with a high surface area and a rich porous structure are the primary raw materials for making super-capacitors [98]. It is crucial to the development of the supercapacitor industry to produce attractive, high-quality carbon materials at a reasonable price [99].
The utilization of biochar as material for supercapacitors has been tested by researchers with incredible results obtained. Biochar is made from paper cardboard and woody biomass. Based on the pyrolysis of woody biomass, the biochar supercapacitor electrodes exhibited a potential window of about 1.3 V, and fast charging-discharging behaviors with about 14 F/g gravimetric capacitance [100]. The authors also enhanced the performance of woody biochar by activating it with nitric acid. According to the researchers, the nitric acid treatment helped increased the capacitance from 14 to 115 F/g with 5000 usage cycles [100]. Likewise, Liu et al. [98] also created a high-performance supercapacitor out of biochar-derived carbon monolith, which was created by pyrolyzing poplar wood at 900°C for 6 h and then surface-modifying with nitric acid. The supercapacitor was discovered to have a highly consistent structure as well as a high porosity. The maximum specific capacitance was high (234 F/g) and cyclic stability was excellent [98, 99].
With the recent development of direct carbon fuel cell (DCFC) which converts carbonaceous material directly into electricity. The DCFC directly oxidizes solid carbon to produce electricity by using the chemical energy contained therein. Fuel utilization can reach nearly 100% if fuel feed and product gases are separated easily. The use of biochar as an energy source for this fuel cell has shown tremendous results. In a study by Kacprzak et al. [101], nine different carbonaceous fuels were tested, including commercial graphite, a carbon black, two commercial types of hard coal, and four biochars made by the authors, and one commercial biochar. At 0.5 V, commercial biochar had the second-highest current density (64.22 mA/cm2) and the third-highest power density (32.8 mW/cm2). Biochar produced in the laboratory had a high current density (36–44.6 mA/cm2) and power density (18–22.4 mW/cm2) [102].
4.2 Challenges and prospects of biochar-based catalyst applications
The use of biochar just as any other material has some limitations in its application for energy storage, conversion, and electrocatalyst. In terms of energy storage, the performance efficiency of tested biochar is still low when compared to its counterparts, though the biochar is easy to access and economical. Likewise, in the use of biochar in DCFC, it has been reported that upon consumption of the carbon content, the ash content present in biochar blocks the active surface area thereby impeding the effectiveness of the whole process [102]. In terms of reusability as a catalyst, further work still needs to be done as biochar from some feedstocks is reusable after the second attempt. For electrochemical oxidation of fuel, an ideal anode should have a large surface area, high porosity, and a continuous frame to ensure mechanical strength. Boosting the DCFC’s power output and durability is therefore possible by improving its anode material [99].
Along with biochar’s widespread use in wastewater remediation, scientists should consider its possible adverse impact on the ecosystem. To effectively employ biochar, one of the most significant features that must be considered is its capacity to maintain its stability throughout time. The aromaticity and extent of aromatic condensation of biochar are two factors that influence the stability of biochar [103]. When biochar is employed for wastewater detoxification, the possible emission of carbon from the biochar can cause the carbon concentration of the solution to be treated to rise. Moreover, the discharge of heavy metals from biochar formed from sludge is a possibility, particularly for biochar generated from sludge. Huang et al. [105] demonstrated that the dissolution of organic materials from biochar into an aqueous solution is caused by the biochar’s instabilities. In addition, it was discovered that the stability of the biochar deteriorated after multiple cycles when it was employed as a support for a catalyst. This can be attributed to variations in the carbon framework of the biochar. It is usually acknowledged that the stability of biochar relies on the type of the starting feedstock as well as the experimental settings utilized during its thermal transformation. As a result, it is required to establish a relationship between these two factors and the stability of the biochar. Another significant element to consider is the renewal and restoration of biochar after it has been utilized. The adsorption procedure is characterized by the transition of pollution from the liquid stage to the solid material/adsorbent phase in most cases. As a result, it is critical to transforming the hazardous pollutants that are bonded to biochar into non-toxic conditions to control them effectively [101].
5. Challenges, prospects, and future perspectives
5.1 Challenges and prospects of effective application of biochar-based catalyst
The use of biochar-based catalysts can be beneficial in several catalytic processes, including biodiesel production, bio-oil up-gradation, reforming, and various organic reactions involving specialty or functional chemicals. These are currently in their infancy and must be scaled up. Biochar production systems must be set up on an industrial scale to enable the scaling up of these processes. The biggest barriers to scaling up biochar production are multiple competing end-users, as well as the collection and transportation of raw materials to the facilities that manufacture biochar. Homagain [107] studied the sensitivity of transportation distance and distinct carbon offset values and found that the system is financially viable at 200 km with good biomass availability. Furthermore, the seasonal biomass production cycle makes it difficult to maintain a steady supply of sustainable and reliable fuel.
The moisture content and particle size are other critical parameters in the synthesis of biochar. The biochar production method requires a lot of energy to process feedstocks with a high moisture content or large particle size. During biochar production, it is necessary to pre-process feedstock by drying and reducing its size. The heat resistance of feedstocks, on the other hand, limits heat transfer during biochar formation. Due to temperature differences, this phenomenon causes unconverted feedstock to accumulate on the inner walls of reactors, posing a significant barrier to the widespread production of uniform biochar [103].
Biochar’s properties can also be difficult to fine-tune once it has been produced to achieve the required transformation. Following the proper design of biochar-based catalysts, the resulting materials will have real-world applications and will be able to replace catalysts that are expensive, non-renewable, and harmful to the environment. These conditions can be met by conducting mechanistic investigations during the char activation/synthesis/loading of necessary metals and catalytic processes. It is critical to comprehend two key factors in the catalytic process. The first is the interaction between biochar’s physicochemical properties and its catalytic activity. The second step is to tune physicochemical parameters during the char production and activation process based on catalytic activity. Regarding this, the investigation of high surface area, active sites, and optimal pores is critical to managing the combined impacts of important production process variables (e.g., reagent gas, duration, heating rate, and temperature) and activation process variables (e.g., chemical, and physical). Just a few experiments have been conducted to control the physicochemical parameters of biochar for catalytic applications. However, the biorefinery of the future will require a single-step method for producing biochar with effective porous structure and functionality that is closely related to the production of biochemicals, biogas, and biofuels.
5.2 Future perspectives
Although biochar has many applications, biochar-based catalysts are still in the very early stages of development. Therefore, it is imperative to develop a method that can maximize catalytic activity. Researchers are currently exploring the modifications that can be carried out on biochar-based catalysts to apply them in future fields such as catalysis, environmental pollution, energy storage and conservation, and even chromatography.
Laboratory research is still underway for biochar-based catalysts. A purpose-driven synthesis and modification will be necessary for the future of an industrial application. Mechanistic studies may help to achieve this. A first step would be to investigate how biochar’s catalytic properties relate to its physicochemical properties. To accomplish this, advanced characterization techniques of catalytic materials can be combined with theoretical modeling of the mechanisms involved. Second, it is critical to determine how biochar’s properties are affected by synthesis conditions and feedstock. It is extremely difficult to work with biomass because of its complex composition and complex formation mechanism. The application of advanced characterization techniques, such as pyrolysis/gas chromatography/mass spectrometry (Py/GC/MS), and thermogravimetric analysis/Fourier-transform infrared spectroscopy/mass spectrometry (TGA/FTIR/MS), is potentially vital for the future.
In terms of process optimization, the role of catalysts in biochar synthesis must be given much more thought. The presence of some inorganic species in biomass feedstock can catalyze pyrolysis. However, their autocatalysis is not enough to ignite the process. A catalyst must achieve at least one of the following goals: (1) to reduce reaction temperature or residence time so that biochar can be produced more efficiently; (2) to make biochar with desirable properties in a single step instead of having modification and synthesis done separately. In the future, we may be able to produce biochar-supported catalysts directly from biomass using catalysts that can produce effective functional groups and porous structures in a single step. A biomass refinery would also be able to produce biofuels and biochemicals in close coordination with manufacturing biochar-based catalysts, allowing for a more integrated and environmentally sustainable process for using biomass.
Biochars intended for use as catalysts require a functionalization and/or activation process because of their limited porosity, surface area, and surface functional groups. According to the activation technique, biochar can have varying physicochemical properties, such as surface area or porosity. Activated biochar can be endowed with specialized properties via the addition of functional groups or substances, such as selectivity, catalysis, and selective adsorption. Although biochars vary significantly according to the type of biomass they are produced from, as well as their production conditions and functionalization or activation. Future research should focus on the production of biochar with stable properties on an industrial scale.
6. Conclusion
The use of biochar-based catalysts in environmental applications has excellent catalytic properties. Recent achievements of biochar catalyst preparation procedures, as well as their performance, were examined from a range of applications. Additionally, the catalytic properties of biochar were examined further by its production and activation methods. Through various chemical and/or physical treatments, biochar can be modified in terms of morphology and surface functionality. Therefore, biochar has a strong potential for replacing costly and non-renewable conventional catalysts.
It has been demonstrated that biochar-derived catalysts are effective in a variety of reactions, including the production of biodiesel from biomass, removal of tars from bio-oil and syngas, and production of syngas. However, biochar catalyst properties (including surface functionality, surface area, porosity, and acidity) vary widely with biomass origin, biochar synthesis conditions, and pre/post-treatment. Yet, there is limited information about how biochar’s properties can be controlled to enable its catalytic applications. Therefore, further research is needed to develop the catalytic properties of biochar to design active, stable, and selective biochar catalysts. Also, if biochar is to be considered as an industrial heterogeneous catalyst, the development of a method that allows for the manufacture of biochar on an industrial scale is extremely desirable. For large-scale production, it is also challenging to secure stable sources of raw biochar materials. To meet these challenges, biochar catalysts must be stimulated and facilitated to be used in real-world applications to replace costly, non-environmentally benign catalysts, which have been used for a wide range of applications until now.
\n',keywords:"biochar, biodiesel, biomass, catalyst, pyrolysis, tar reforming, wastewater treatment",chapterPDFUrl:"https://cdn.intechopen.com/pdfs/82348.pdf",chapterXML:"https://mts.intechopen.com/source/xml/82348.xml",downloadPdfUrl:"/chapter/pdf-download/82348",previewPdfUrl:"/chapter/pdf-preview/82348",totalDownloads:12,totalViews:0,totalCrossrefCites:0,dateSubmitted:"May 10th 2022",dateReviewed:"May 17th 2022",datePrePublished:"June 29th 2022",datePublished:null,dateFinished:"June 23rd 2022",readingETA:"0",abstract:"Biochar is a carbon-rich pyrogenic material that is made from carbon-neutral sources (i.e., biomass). It offers key strategies for carbon capture and storage (CCS) as well as being an environmentally friendly means of soil amendment. The recent recognition of biochar as a versatile media for catalytic applications has prompted preliminary research into biochar’s catalytic capacity and mechanistic practices via various routes. This chapter provides a review of biochar production technologies, biochar’s catalyst development, and its application in various catalytic processes as well as descriptions of the benefits and drawbacks of the various applications currently available. The characteristics of biochar-based catalysts, challenges of effective application of this catalyst system, emerging application, prospects, and future work consideration for effective utilization of biochar-based catalysts were presented.",reviewType:"peer-reviewed",bibtexUrl:"/chapter/bibtex/82348",risUrl:"/chapter/ris/82348",signatures:"Stephen Okiemute Akpasi, Ifeanyi Michael Smarte Anekwe, Jeremiah Adedeji and Sammy Lewis Kiambi",book:{id:"11537",type:"book",title:"Biochar - Productive Technologies, Properties and Application",subtitle:null,fullTitle:"Biochar - Productive Technologies, Properties and Application",slug:null,publishedDate:null,bookSignature:"Dr. Mattia Bartoli, Dr. Mauro Giorcelli and Prof. Alberto Tagliaferro",coverURL:"https://cdn.intechopen.com/books/images_new/11537.jpg",licenceType:"CC BY 3.0",editedByType:null,isbn:"978-1-80356-252-0",printIsbn:"978-1-80356-251-3",pdfIsbn:"978-1-80356-253-7",isAvailableForWebshopOrdering:!0,editors:[{id:"188999",title:"Dr.",name:"Mattia",middleName:null,surname:"Bartoli",slug:"mattia-bartoli",fullName:"Mattia Bartoli"}],productType:{id:"1",title:"Edited Volume",chapterContentType:"chapter",authoredCaption:"Edited by"}},authors:null,sections:[{id:"sec_1",title:"1. Introduction",level:"1"},{id:"sec_1_2",title:"1.1 Properties of biochar",level:"2"},{id:"sec_2_2",title:"1.2 Biochar production",level:"2"},{id:"sec_2_3",title:"1.2.1 Torrefaction",level:"3"},{id:"sec_3_3",title:"Table 1.",level:"3"},{id:"sec_3_4",title:"1.2.2.1 Slow pyrolysis",level:"4"},{id:"sec_4_4",title:"1.2.2.2 Fast pyrolysis",level:"4"},{id:"sec_5_4",title:"Table 1.",level:"4"},{id:"sec_7_3",title:"1.2.3 Gasification",level:"3"},{id:"sec_8_3",title:"1.2.4 Hydrothermal carbonization",level:"3"},{id:"sec_9_3",title:"1.2.5 Flash carbonization",level:"3"},{id:"sec_11_2",title:"1.3 Biochar as a promising catalyst",level:"2"},{id:"sec_12_2",title:"1.4 Characteristics of biochar based catalyst",level:"2"},{id:"sec_12_3",title:"1.4.1 Bulk element and inorganics",level:"3"},{id:"sec_13_3",title:"1.4.2 Chemistry of biochar matrix",level:"3"},{id:"sec_14_3",title:"1.4.3 Surface functional groups",level:"3"},{id:"sec_17",title:"2. Preparation of biochar-based catalyst",level:"1"},{id:"sec_17_2",title:"2.1 Impregnation",level:"2"},{id:"sec_18_2",title:"2.2 Physical activation",level:"2"},{id:"sec_19_2",title:"2.3 Chemical treatment",level:"2"},{id:"sec_21",title:"3. Application of biochar catalyst",level:"1"},{id:"sec_21_2",title:"3.1 Biodiesel production on biochar catalysts",level:"2"},{id:"sec_22_2",title:"3.2 Biomass hydrolysis on biochar catalysts",level:"2"},{id:"sec_23_2",title:"3.3 Production of biogas",level:"2"},{id:"sec_23_3",title:"3.3.1 Tar reforming (syngas synthesis)",level:"3"},{id:"sec_24_3",title:"3.3.2 Tar elimination",level:"3"},{id:"sec_26_2",title:"3.4 Wastewater treatment",level:"2"},{id:"sec_26_3",title:"3.4.1 Industrial wastewater remediation",level:"3"},{id:"sec_27_3",title:"3.4.2 Treatment of municipal wastewater",level:"3"},{id:"sec_28_3",title:"3.4.3 Wastewater treatment in the agricultural sector",level:"3"},{id:"sec_31",title:"4. Emerging advances in the applications of biochar catalyst",level:"1"},{id:"sec_31_2",title:"4.1 Energy storage and conversion",level:"2"},{id:"sec_32_2",title:"4.2 Challenges and prospects of biochar-based catalyst applications",level:"2"},{id:"sec_34",title:"5. Challenges, prospects, and future perspectives",level:"1"},{id:"sec_34_2",title:"5.1 Challenges and prospects of effective application of biochar-based catalyst",level:"2"},{id:"sec_35_2",title:"5.2 Future perspectives",level:"2"},{id:"sec_37",title:"6. Conclusion",level:"1"}],chapterReferences:[{id:"B1",body:'Lam E, Luong JH. Carbon materials as catalyst supports and catalysts in the transformation of biomass to fuels and chemicals. ACS Catalysis. 2014;4(10):3393-3410'},{id:"B2",body:'Czernik S, Bridgwater A. Overview of applications of biomass fast pyrolysis oil. Energy & Fuels. 2004;18(2):590-598'},{id:"B3",body:'Laird DA, Brown RC, Amonette JE, Lehmann J. 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Organic Geochemistry. 2015;78:135-143'},{id:"B104",body:'Wei D et al. Biochar-based functional materials in the purification of agricultural wastewater: Fabrication, application and future research needs. Chemosphere. 2018;197:165-180'},{id:"B105",body:'Huang M et al. Application potential of biochar in environment: Insight from degradation of biochar-derived DOM and complexation of DOM with heavy metals. Science of the Total Environment. 2019;646:220-228'},{id:"B106",body:'Li X et al. Effect of cassava waste biochar on sorption and release behavior of atrazine in soil. Science of the Total Environment. 2018;644:1617-1624'},{id:"B107",body:'Homagain K et al. Life cycle cost and economic assessment of biochar-based bioenergy production and biochar land application in Northwestern Ontario, Canada. Forest Ecosystems. 2016;3(1):1-10'},{id:"B108",body:'Mašek O et al. Consistency of biochar properties over time and production scales: A characterization of standard materials. Journal of Analytical and Applied Pyrolysis. 2018;132:200-210'}],footnotes:[],contributors:[{corresp:"yes",contributorFullName:"Stephen Okiemute Akpasi",address:"stephenakpasi48@gmail.com",affiliation:'
Department of Chemical Engineering, Durban University of Technology, South Africa
'},{corresp:null,contributorFullName:"Ifeanyi Michael Smarte Anekwe",address:null,affiliation:'
School of Chemical and Metallurgical Engineering, University of the Witwatersrand, South Africa
Department of Chemical Engineering, School of Engineering, University of KwaZulu-Natal, South Africa
'},{corresp:null,contributorFullName:"Sammy Lewis Kiambi",address:null,affiliation:'
Department of Chemical Engineering, Durban University of Technology, South Africa
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IntechOpen’s Academic Editors and Authors have received funding for their work through many well-known funders, including: the European Commission, Bill and Melinda Gates Foundation, Wellcome Trust, Chinese Academy of Sciences, Natural Science Foundation of China (NSFC), CGIAR Consortium of International Agricultural Research Centers, National Institute of Health (NIH), National Science Foundation (NSF), National Aeronautics and Space Administration (NASA), National Institute of Standards and Technology (NIST), German Research Foundation (DFG), Research Councils United Kingdom (RCUK), Oswaldo Cruz Foundation, Austrian Science Fund (FWF), Foundation for Science and Technology (FCT), Australian Research Council (ARC).
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In order to help Authors identify appropriate funding agencies and institutions, we have created a list, based on extensive research on various OA resources (including ROARMAP and SHERPA/JULIET) of organizations that have funds available. Before consulting our list we encourage you to petition your own institution or organization for Open Access funds or check the specifications of your grant with your funder to ascertain if publication costs are included. Where you are in receipt of a grant you should clarify:
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If you are associated with any of the institutions in our list below, you can apply to receive OA publication funds by following the instructions provided in the links. Please consult the Open Access policies or grant Terms and Conditions of any institution with which you are linked to explore ways to cover your publication costs (also accessible by clicking on the link in their title).
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Please be aware that you must be a member, or grantee, of the institutions/funders listed in order to apply for their Open Access publication funds.
Open Access publication costs can often be designated directly in the grants or in specific budgets allocated for that purpose. Many of the most important funding organisations encourage, and even request, that the projects they fund are made available at no cost to the wider public. IntechOpen strives to maintain excellent relationships with these funders and ensures compliance with mandates.
\n\n
In order to help Authors identify appropriate funding agencies and institutions, we have created a list, based on extensive research on various OA resources (including ROARMAP and SHERPA/JULIET) of organizations that have funds available. Before consulting our list we encourage you to petition your own institution or organization for Open Access funds or check the specifications of your grant with your funder to ascertain if publication costs are included. Where you are in receipt of a grant you should clarify:
\n\n
\n\t
Does your institution already have a budget for covering Open Access publication costs?
\n\t
Does your grant list Open Access publication fees as legitimate direct/indirect costs?
\n
\n\n
If you are associated with any of the institutions in our list below, you can apply to receive OA publication funds by following the instructions provided in the links. Please consult the Open Access policies or grant Terms and Conditions of any institution with which you are linked to explore ways to cover your publication costs (also accessible by clicking on the link in their title).
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Throughout the life cycle, many of them thrive in pathogen-rich environments, manage harsh weathers, exposed to a number of allochemicals, and adapt well to both terrestrial and marine ecosystems. Their remarkable ability to cope up with the enormous oxidative stress generated in all these circumstances, make them attractive models in this field of research. Endocrine control of oxidative stress in insects is recently emerging. Adipokinetic hormone, glucagon, ecdysteroids and juvenile hormone have been implicated in antioxidative protective role in insects. Drosophila and Caenorhabditis elegans have provided the largest body of evidence addressing the free radical theory of ageing. Oxidative stress is also induced by pesticides/insecticides. In mollusks, pesticides exert their biological effects via generation of ROS. Oxidative stress has been shown to be associated with exposure to several organophosphorous compounds and different classes of pyrethroids. Malathion is a potential hazard to the environment. Adverse effects induced by malathion in earthworms and insects have been reported. Information is now available in great detail on the role of ROS in modulating insect immunity during parasite invasion and bacterial infection. In Drosophila melanogaster ROS are actively produced in the midgut at a basal level in the presence of commensal microbiota and highly generated upon bacterial challenge. The involvement of reactive oxygen species (ROS) in mosquito immunity against bacteria and Plasmodium was investigated in the malaria vector Anopheles gambiae. The concentration of ROS increased in sand fly midguts after they fed on the insect pathogen Serratia marcescens. Elevated oxidative stress was previously reported for a mosquito line experimentally infected with Wolbachia, indicating that oxidative stress may be important for Wolbachia-mediated antiviral protection. 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The standard of care remains a combination of debulking surgery and platinum‐ and taxanes‐based cytotoxic chemotherapy. Even though metastasis is the leading cause of ovarian cancer related fatalities, our understanding of the process remains limited. Ovarian cancer has a unique pattern of metastasis where the hematogenous spread is less common. Ovarian cancer cells mainly metastasize within the peritoneal cavity, which involves exfoliation from the primary tumor, survival, and transport in the peritoneal fluid followed by metastatic colonization of the organs within the peritoneal cavity. A key step for successful metastasis is their attachment and productive interactions with the mesothelial cells covering the metastatic organs for the establishment of metastatic tumors. This chapter provides an overview of ovarian cancer metastasis highlighting the unique dissemination and the underlying mechanisms of regulation of the steps involved. The role of the microenvironment in the process of metastasis will also be reviewed.",book:{id:"5267",slug:"tumor-metastasis",title:"Tumor Metastasis",fullTitle:"Tumor Metastasis"},signatures:"Anirban K. Mitra",authors:[{id:"185152",title:"Dr.",name:"Anirban",middleName:"Kumar",surname:"Mitra",slug:"anirban-mitra",fullName:"Anirban Mitra"}]},{id:"51903",doi:"10.5772/64787",title:"Role of Oxygen Free Radicals in Cancer Development and Treatment",slug:"role-of-oxygen-free-radicals-in-cancer-development-and-treatment",totalDownloads:3610,totalCrossrefCites:14,totalDimensionsCites:17,abstract:"It is well known that species derived from oxygen are cytotoxic and are involved in the etiology of cancer. Several carcinogens during metabolism exert their effect by producing reactive oxygen species (ROS). One of the consequences of oxidative damage to cellular DNA is mutated. It plays a vital role in the process of carcinogenesis (especially in the initiation and progression). The alters, including rearrangement of DNA sequence, base modification, DNA miscoding lesions, gene amplification, and the activation of oncogenes, could be implicated in the initiation stage of several cancers. Mitochondrial changes in the cancer cells are well known and as a result are respiratory injured. Mitochondrial dysfunction could lead to a low coupling efficiency of the mitochondrial electron transport chain (mETC), raising electron leakage and increased ROS formation. It has been documented that by reducing and inactivation of antioxidant system, the oxidative stress (OS) in cancer cells is higher. Cancer cells exhibit a higher oxidative stress level compared to normal cells, rendering tumor cells more vulnerable to raise ROS levels. Therefore, increasing ROS levels through redox modulation can be a strategy to selectively kill cancer cells but not normal cells. A promising anti-cancer method named “oxidation therapy” has been developed by causing cytotoxic oxidative stress for cancer therapy. In this chapter, we described the role of ROS as a double-edged sword in cancer development and treatment.",book:{id:"5121",slug:"free-radicals-and-diseases",title:"Free Radicals and Diseases",fullTitle:"Free Radicals and Diseases"},signatures:"Jalal Pourahmad, Ahmad Salimi and Enaytollah Seydi",authors:[{id:"172672",title:"Prof.",name:"Jalal",middleName:null,surname:"Pourahmad",slug:"jalal-pourahmad",fullName:"Jalal Pourahmad"}]},{id:"44689",doi:"10.5772/55415",title:"Drug Resistance and Molecular Cancer Therapy: Apoptosis Versus Autophagy",slug:"drug-resistance-and-molecular-cancer-therapy-apoptosis-versus-autophagy",totalDownloads:3951,totalCrossrefCites:2,totalDimensionsCites:14,abstract:null,book:{id:"2857",slug:"apoptosis",title:"Apoptosis",fullTitle:"Apoptosis"},signatures:"Rebecca T. Marquez, Bryan W. Tsao, Nicholas F. 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Autophagy is physiologic process of eukaryotic systems, which have significant role in adaptation to oxidative stress by degradation of metalloproteins and oxidatively damaged macromolecules. By oxidizing, membrane injuries allow the leakage of enzymes and contribute to cell damage. However, recent publications demonstrate the protecting role of lysosome system during excessive reactive oxygen species (ROS) production by the elimination of damaged proteins or organelles. Activation of autophagic or lysosomal system can eliminate the oxidizing components of cell in oxidative stress response. This chapter aims to provide the novel insight data for oxidative damage-mediated autophagy as well as their metabolic networks.",book:{id:"5121",slug:"free-radicals-and-diseases",title:"Free Radicals and Diseases",fullTitle:"Free Radicals and Diseases"},signatures:"Adem Kara, Semin Gedikli, Emin Sengul, Volkan Gelen and Seckin\nOzkanlar",authors:[{id:"177953",title:"Dr.",name:"Adem",middleName:null,surname:"Kara",slug:"adem-kara",fullName:"Adem Kara"},{id:"178363",title:"Dr.",name:"Emin",middleName:null,surname:"Sengul",slug:"emin-sengul",fullName:"Emin Sengul"},{id:"178365",title:"Dr.",name:"Semin",middleName:null,surname:"Gedikli",slug:"semin-gedikli",fullName:"Semin Gedikli"},{id:"178366",title:"Dr.",name:"Volkan",middleName:null,surname:"Gelen",slug:"volkan-gelen",fullName:"Volkan Gelen"},{id:"178367",title:"Dr.",name:"Seckin",middleName:null,surname:"Ozkanlar",slug:"seckin-ozkanlar",fullName:"Seckin Ozkanlar"}]}],mostDownloadedChaptersLast30Days:[{id:"44699",title:"Apoptosis and Activation-Induced Cell Death",slug:"apoptosis-and-activation-induced-cell-death",totalDownloads:2924,totalCrossrefCites:0,totalDimensionsCites:0,abstract:null,book:{id:"2857",slug:"apoptosis",title:"Apoptosis",fullTitle:"Apoptosis"},signatures:"Joaquín H. Patarroyo S. and Marlene I. Vargas V",authors:[{id:"141183",title:"Prof.",name:"Joaquín",middleName:null,surname:"Patarroyo",slug:"joaquin-patarroyo",fullName:"Joaquín Patarroyo"},{id:"146188",title:"Prof.",name:"Marlene",middleName:null,surname:"Vargas",slug:"marlene-vargas",fullName:"Marlene Vargas"}]},{id:"44689",title:"Drug Resistance and Molecular Cancer Therapy: Apoptosis Versus Autophagy",slug:"drug-resistance-and-molecular-cancer-therapy-apoptosis-versus-autophagy",totalDownloads:3935,totalCrossrefCites:2,totalDimensionsCites:14,abstract:null,book:{id:"2857",slug:"apoptosis",title:"Apoptosis",fullTitle:"Apoptosis"},signatures:"Rebecca T. Marquez, Bryan W. Tsao, Nicholas F. Faust and Liang Xu",authors:[{id:"19713",title:"Dr.",name:"Liang",middleName:null,surname:"Xu",slug:"liang-xu",fullName:"Liang Xu"},{id:"149902",title:"Dr.",name:"Rebecca",middleName:null,surname:"Marquez",slug:"rebecca-marquez",fullName:"Rebecca Marquez"}]},{id:"51334",title:"Free Radicals and Biomarkers Related to the Diagnosis of Cardiorenal Syndrome",slug:"free-radicals-and-biomarkers-related-to-the-diagnosis-of-cardiorenal-syndrome",totalDownloads:3743,totalCrossrefCites:1,totalDimensionsCites:2,abstract:"The National Heart, Lung, and Blood Institute Working Group has postulated the cardiorenal syndrome (CRS) as an interaction between the kidneys and the cardiovascular system in which therapy to relieve congestive heart failure (HF) symptoms is limited by the further worsening renal function. CRS is classified from type I to V, taking into account the progression of the symptoms in terms of mechanisms, clinical conditions, and biomarkers. Experimental and clinical studies have shown the kidney as both a trigger and a target to sympathetic nervous system (SNS) overactivity. Renal damage and ischemia, activation of the renin angiotensin aldosterone system (RAAS), and dysfunction of nitric oxide (NO) system are associated with kidney adrenergic activation. Indeed, the imbalances of RAAS and/or SNS share an important common process in CRS: the activation and production of free radicals, especially reactive oxygen species (ROS). The present chapter addresses connections of the free radicals as potential biomarkers as the imbalances in the RAAS and the SNS are developed. Understanding the involvement of free radicals in CRS may bring knowledge to design studies in order to develop accurate pharmacological interventions.",book:{id:"5121",slug:"free-radicals-and-diseases",title:"Free Radicals and Diseases",fullTitle:"Free Radicals and Diseases"},signatures:"Carolina B.A. Restini, Bruna F.M. Pereira and Tufik M. Geleilete",authors:[{id:"178144",title:"Dr.",name:"Carolina",middleName:null,surname:"Baraldi A. Restini",slug:"carolina-baraldi-a.-restini",fullName:"Carolina Baraldi A. Restini"},{id:"178387",title:"Ms.",name:"Bruna",middleName:null,surname:"Pereira",slug:"bruna-pereira",fullName:"Bruna Pereira"},{id:"184159",title:"Dr.",name:"Tufik",middleName:null,surname:"Geleilete",slug:"tufik-geleilete",fullName:"Tufik Geleilete"}]},{id:"52345",title:"Oxidative Stress in Invertebrate Systems",slug:"oxidative-stress-in-invertebrate-systems",totalDownloads:2451,totalCrossrefCites:8,totalDimensionsCites:21,abstract:"Invertebrates have been valuable research models in the discovery of many scientific principles owing to the numerous advantages they provide. Throughout the life cycle, many of them thrive in pathogen-rich environments, manage harsh weathers, exposed to a number of allochemicals, and adapt well to both terrestrial and marine ecosystems. Their remarkable ability to cope up with the enormous oxidative stress generated in all these circumstances, make them attractive models in this field of research. Endocrine control of oxidative stress in insects is recently emerging. Adipokinetic hormone, glucagon, ecdysteroids and juvenile hormone have been implicated in antioxidative protective role in insects. Drosophila and Caenorhabditis elegans have provided the largest body of evidence addressing the free radical theory of ageing. Oxidative stress is also induced by pesticides/insecticides. In mollusks, pesticides exert their biological effects via generation of ROS. Oxidative stress has been shown to be associated with exposure to several organophosphorous compounds and different classes of pyrethroids. Malathion is a potential hazard to the environment. Adverse effects induced by malathion in earthworms and insects have been reported. Information is now available in great detail on the role of ROS in modulating insect immunity during parasite invasion and bacterial infection. In Drosophila melanogaster ROS are actively produced in the midgut at a basal level in the presence of commensal microbiota and highly generated upon bacterial challenge. The involvement of reactive oxygen species (ROS) in mosquito immunity against bacteria and Plasmodium was investigated in the malaria vector Anopheles gambiae. The concentration of ROS increased in sand fly midguts after they fed on the insect pathogen Serratia marcescens. Elevated oxidative stress was previously reported for a mosquito line experimentally infected with Wolbachia, indicating that oxidative stress may be important for Wolbachia-mediated antiviral protection. In a nutshell, this chapter highlights the current advances of oxidative stress in invertebrate model systems and its implications.",book:{id:"5121",slug:"free-radicals-and-diseases",title:"Free Radicals and Diseases",fullTitle:"Free Radicals and Diseases"},signatures:"R.K. Chaitanya, K. Shashank and P. Sridevi",authors:[{id:"178087",title:"Dr.",name:"Rk",middleName:null,surname:"Chaitanya",slug:"rk-chaitanya",fullName:"Rk Chaitanya"}]},{id:"51782",title:"Is Extracellular Matrix a Castle Against to Invasion of Cancer Cells?",slug:"is-extracellular-matrix-a-castle-against-to-invasion-of-cancer-cells-",totalDownloads:2317,totalCrossrefCites:2,totalDimensionsCites:4,abstract:"Metastasis is a complicated course that involves the spread of a neoplasm to distant parts of the body from its original site. A cancer cell must complete a series of steps before it becomes a clinically detectable lesion for successful colonization in the body. These are separation from the primary tumor, invasion and penetration of their basement membranes, entry into the blood vessels and survival within blood, and entry into lymphatics. A major challenge in extracellular matrix (ECM) biology is to understand the roles of the ECM and how disruption of ECM dynamics may contribute to cancer. A noteworthy area of forthcoming cancer research will be to determine whether abnormal ECM could be an effective cancer therapeutic target. We should understand how ECM composition and organization are normally maintained and how they may be deregulated in cancer. So the aims of this chapter were to focus on extracellular matrix. Invasion and metastatic skills, properties and functions of the ECM, abnormal ECM dynamics, tumor microenvironment and ECM, details of ECM invasion, role of ECM and ECM‐associated proteins in metastasis, tumor dormant and metastatic process, essential component of the niches, role of the ECM in tumor angiogenesis and lymphangiogenesis are be briefly explained in this chapter.",book:{id:"5267",slug:"tumor-metastasis",title:"Tumor Metastasis",fullTitle:"Tumor Metastasis"},signatures:"Serdar Altınay",authors:[{id:"185324",title:"Associate Prof.",name:"Serdar",middleName:null,surname:"Altınay",slug:"serdar-altinay",fullName:"Serdar Altınay"}]}],onlineFirstChaptersFilter:{topicId:"411",limit:6,offset:0},onlineFirstChaptersCollection:[],onlineFirstChaptersTotal:0},preDownload:{success:null,errors:{}},subscriptionForm:{success:null,errors:{}},aboutIntechopen:{},privacyPolicy:{},peerReviewing:{},howOpenAccessPublishingWithIntechopenWorks:{},sponsorshipBooks:{sponsorshipBooks:[],offset:8,limit:8,total:0},allSeries:{pteSeriesList:[{id:"14",title:"Artificial Intelligence",numberOfPublishedBooks:9,numberOfPublishedChapters:90,numberOfOpenTopics:6,numberOfUpcomingTopics:0,issn:"2633-1403",doi:"10.5772/intechopen.79920",isOpenForSubmission:!0},{id:"7",title:"Biomedical Engineering",numberOfPublishedBooks:12,numberOfPublishedChapters:104,numberOfOpenTopics:3,numberOfUpcomingTopics:0,issn:"2631-5343",doi:"10.5772/intechopen.71985",isOpenForSubmission:!0}],lsSeriesList:[{id:"11",title:"Biochemistry",numberOfPublishedBooks:32,numberOfPublishedChapters:320,numberOfOpenTopics:4,numberOfUpcomingTopics:0,issn:"2632-0983",doi:"10.5772/intechopen.72877",isOpenForSubmission:!0},{id:"25",title:"Environmental Sciences",numberOfPublishedBooks:1,numberOfPublishedChapters:12,numberOfOpenTopics:4,numberOfUpcomingTopics:0,issn:"2754-6713",doi:"10.5772/intechopen.100362",isOpenForSubmission:!0},{id:"10",title:"Physiology",numberOfPublishedBooks:11,numberOfPublishedChapters:141,numberOfOpenTopics:4,numberOfUpcomingTopics:0,issn:"2631-8261",doi:"10.5772/intechopen.72796",isOpenForSubmission:!0}],hsSeriesList:[{id:"3",title:"Dentistry",numberOfPublishedBooks:8,numberOfPublishedChapters:133,numberOfOpenTopics:2,numberOfUpcomingTopics:0,issn:"2631-6218",doi:"10.5772/intechopen.71199",isOpenForSubmission:!0},{id:"6",title:"Infectious Diseases",numberOfPublishedBooks:13,numberOfPublishedChapters:113,numberOfOpenTopics:3,numberOfUpcomingTopics:1,issn:"2631-6188",doi:"10.5772/intechopen.71852",isOpenForSubmission:!0},{id:"13",title:"Veterinary Medicine and Science",numberOfPublishedBooks:11,numberOfPublishedChapters:107,numberOfOpenTopics:3,numberOfUpcomingTopics:0,issn:"2632-0517",doi:"10.5772/intechopen.73681",isOpenForSubmission:!0}],sshSeriesList:[{id:"22",title:"Business, Management and Economics",numberOfPublishedBooks:1,numberOfPublishedChapters:19,numberOfOpenTopics:3,numberOfUpcomingTopics:0,issn:"2753-894X",doi:"10.5772/intechopen.100359",isOpenForSubmission:!0},{id:"23",title:"Education and Human Development",numberOfPublishedBooks:0,numberOfPublishedChapters:5,numberOfOpenTopics:1,numberOfUpcomingTopics:1,issn:null,doi:"10.5772/intechopen.100360",isOpenForSubmission:!0},{id:"24",title:"Sustainable Development",numberOfPublishedBooks:0,numberOfPublishedChapters:16,numberOfOpenTopics:5,numberOfUpcomingTopics:0,issn:null,doi:"10.5772/intechopen.100361",isOpenForSubmission:!0}],testimonialsList:[{id:"13",text:"The collaboration with and support of the technical staff of IntechOpen is fantastic. The whole process of submitting an article and editing of the submitted article goes extremely smooth and fast, the number of reads and downloads of chapters is high, and the contributions are also frequently cited.",author:{id:"55578",name:"Antonio",surname:"Jurado-Navas",institutionString:null,profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bRisIQAS/Profile_Picture_1626166543950",slug:"antonio-jurado-navas",institution:{id:"720",name:"University of Malaga",country:{id:null,name:"Spain"}}}},{id:"6",text:"It is great to work with the IntechOpen to produce a worthwhile collection of research that also becomes a great educational resource and guide for future research endeavors.",author:{id:"259298",name:"Edward",surname:"Narayan",institutionString:null,profilePictureURL:"https://mts.intechopen.com/storage/users/259298/images/system/259298.jpeg",slug:"edward-narayan",institution:{id:"3",name:"University of Queensland",country:{id:null,name:"Australia"}}}}]},series:{item:{id:"24",title:"Sustainable Development",doi:"10.5772/intechopen.100361",issn:null,scope:"
\r\n\tTransforming our World: the 2030 Agenda for Sustainable Development endorsed by United Nations and 193 Member States, came into effect on Jan 1, 2016, to guide decision making and actions to the year 2030 and beyond. Central to this Agenda are 17 Goals, 169 associated targets and over 230 indicators that are reviewed annually. The vision envisaged in the implementation of the SDGs is centered on the five Ps: People, Planet, Prosperity, Peace and Partnership. This call for renewed focused efforts ensure we have a safe and healthy planet for current and future generations.
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\r\n\tThis Series focuses on covering research and applied research involving the five Ps through the following topics:
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\r\n\t1. Sustainable Economy and Fair Society that relates to SDG 1 on No Poverty, SDG 2 on Zero Hunger, SDG 8 on Decent Work and Economic Growth, SDG 10 on Reduced Inequalities, SDG 12 on Responsible Consumption and Production, and SDG 17 Partnership for the Goals
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\r\n\t2. Health and Wellbeing focusing on SDG 3 on Good Health and Wellbeing and SDG 6 on Clean Water and Sanitation
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\r\n\t3. Inclusivity and Social Equality involving SDG 4 on Quality Education, SDG 5 on Gender Equality, and SDG 16 on Peace, Justice and Strong Institutions
\r\n
\r\n\t
\r\n
\r\n\t4. Climate Change and Environmental Sustainability comprising SDG 13 on Climate Action, SDG 14 on Life Below Water, and SDG 15 on Life on Land
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\r\n\t
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\r\n\t5. Urban Planning and Environmental Management embracing SDG 7 on Affordable Clean Energy, SDG 9 on Industry, Innovation and Infrastructure, and SDG 11 on Sustainable Cities and Communities.
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\r\n\tThe series also seeks to support the use of cross cutting SDGs, as many of the goals listed above, targets and indicators are all interconnected to impact our lives and the decisions we make on a daily basis, making them impossible to tie to a single topic.
",coverUrl:"https://cdn.intechopen.com/series/covers/24.jpg",latestPublicationDate:"July 5th, 2022",hasOnlineFirst:!0,numberOfPublishedBooks:0,editor:{id:"262440",title:"Prof.",name:"Usha",middleName:null,surname:"Iyer-Raniga",slug:"usha-iyer-raniga",fullName:"Usha Iyer-Raniga",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bRYSXQA4/Profile_Picture_2022-02-28T13:55:36.jpeg",biography:"Usha Iyer-Raniga is a professor in the School of Property and Construction Management at RMIT University. Usha co-leads the One Planet Network’s Sustainable Buildings and Construction Programme (SBC), a United Nations 10 Year Framework of Programmes on Sustainable Consumption and Production (UN 10FYP SCP) aligned with Sustainable Development Goal 12. The work also directly impacts SDG 11 on Sustainable Cities and Communities. She completed her undergraduate degree as an architect before obtaining her Masters degree from Canada and her Doctorate in Australia. Usha has been a keynote speaker as well as an invited speaker at national and international conferences, seminars and workshops. Her teaching experience includes teaching in Asian countries. She has advised Austrade, APEC, national, state and local governments. She serves as a reviewer and a member of the scientific committee for national and international refereed journals and refereed conferences. She is on the editorial board for refereed journals and has worked on Special Issues. Usha has served and continues to serve on the Boards of several not-for-profit organisations and she has also served as panel judge for a number of awards including the Premiers Sustainability Award in Victoria and the International Green Gown Awards. Usha has published over 100 publications, including research and consulting reports. Her publications cover a wide range of scientific and technical research publications that include edited books, book chapters, refereed journals, refereed conference papers and reports for local, state and federal government clients. She has also produced podcasts for various organisations and participated in media interviews. She has received state, national and international funding worth over USD $25 million. Usha has been awarded the Quarterly Franklin Membership by London Journals Press (UK). Her biography has been included in the Marquis Who's Who in the World® 2018, 2016 (33rd Edition), along with approximately 55,000 of the most accomplished men and women from around the world, including luminaries as U.N. Secretary-General Ban Ki-moon. In 2017, Usha was awarded the Marquis Who’s Who Lifetime Achiever Award.",institutionString:null,institution:{name:"RMIT University",institutionURL:null,country:{name:"Australia"}}},editorTwo:null,editorThree:null},subseries:{paginationCount:5,paginationItems:[{id:"91",title:"Sustainable Economy and Fair Society",coverUrl:"https://cdn.intechopen.com/series_topics/covers/91.jpg",isOpenForSubmission:!0,annualVolume:11975,editor:{id:"181603",title:"Dr.",name:"Antonella",middleName:null,surname:"Petrillo",slug:"antonella-petrillo",fullName:"Antonella Petrillo",profilePictureURL:"https://mts.intechopen.com/storage/users/181603/images/system/181603.jpg",biography:"Antonella Petrillo is a Professor at the Department of Engineering of the University of Naples “Parthenope”, Italy. She received her Ph.D. in Mechanical Engineering from the University of Cassino. Her research interests include multi-criteria decision analysis, industrial plant, logistics, manufacturing and safety. She serves as an Associate Editor for the International Journal of the Analytic Hierarchy Process. She is a member of AHP Academy and a member of several editorial boards. 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Her focus is on quality, innovation, leadership, and personalised learning. She works primarily at the strategic and policy levels, both nationally and internationally, and with key international organisations. She is committed to promoting and improving OFDL in the context of SDG4 and the future of education. Ossiannilsson has more than 20 years of experience in her current field, but more than 40 years in the education sector. She works as a reviewer and expert for the European Commission and collaborates with the Joint Research Centre for Quality in Open Education. Ossiannilsson also collaborates with ITCILO and ICoBC (International Council on Badges and Credentials). She is a member of the ICDE Board of Directors and has previously served on the boards of EDEN and EUCEN. Ossiannilsson is a quality expert and reviewer for ICDE, EDEN and the EADTU. She chairs the ICDE OER Advocacy Committee and is a member of the ICDE Quality Network. She is regularly invited as a keynote speaker at conferences. She is a guest editor for several special issues and a member of the editorial board of several scientific journals. She has published more than 200 articles and is currently working on book projects in the field of OFDL. Ossiannilsson is a visiting professor at several international universities and was recently appointed Professor and Research Fellow at Victoria University of Wellington, NZ. Ossiannilsson has been awarded the following fellowships: EDEN Fellows, EDEN Council of Fellows, and Open Education Europe. She is a ICDE OER Ambassador, Open Education Europe Ambassador, GIZ Ambassador for Quality in Digital Learning, and part of the Globe-Community of Digital Learning and Champion of SPARC Europe. On a national level, she is a quality developer at the Swedish Institute for Standards (SIS) and for ISO. She is a member of the Digital Skills and Jobs Coalition Sweden and Vice President of the Swedish Association for Distance Education. She is currently working on a government initiative on quality in distance education at the National Council for Higher Education. She holds a Ph.D. from the University of Oulu, Finland.",institutionString:"Swedish Association for Distance Education, Sweden",institution:null},editorTwo:null,editorThree:null},{id:"94",title:"Climate Change and Environmental Sustainability",coverUrl:"https://cdn.intechopen.com/series_topics/covers/94.jpg",isOpenForSubmission:!0,annualVolume:11978,editor:{id:"61855",title:"Dr.",name:"Yixin",middleName:null,surname:"Zhang",slug:"yixin-zhang",fullName:"Yixin Zhang",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002aYWJgQAO/Profile_Picture_2022-06-09T11:36:35.jpg",biography:"Professor Yixin Zhang is an aquatic ecologist with over 30 years of research and teaching experience in three continents (Asia, Europe, and North America) in Stream Ecology, Riparian Ecology, Urban Ecology, and Ecosystem Restoration and Aquatic Conservation, Human-Nature Interactions and Sustainability, Urbanization Impact on Aquatic Ecosystems. He got his Ph.D. in Animal Ecology at Umeå University in Sweden in 1998. He conducted postdoc research in stream ecology at the University of California at Santa Barbara in the USA. After that, he was a postdoc research fellow at the University of British Columbia in Canada to do research on large-scale stream experimental manipulation and watershed ecological survey in temperate rainforests of BC. He was a faculty member at the University of Hong Kong to run ecological research projects on aquatic insects, fishes, and newts in Tropical Asian streams. He also conducted research in streams, rivers, and caves in Texas, USA, to study the ecology of macroinvertebrates, big-claw river shrimp, fish, turtles, and bats. Current research interests include trophic flows across ecosystems; watershed impacts of land-use change on biodiversity and ecosystem functioning; ecological civilization and water resource management; urban ecology and urban/rural sustainable development.",institutionString:null,institution:{name:"Soochow University",institutionURL:null,country:{name:"China"}}},editorTwo:null,editorThree:null},{id:"95",title:"Urban Planning and Environmental Management",coverUrl:"https://cdn.intechopen.com/series_topics/covers/95.jpg",isOpenForSubmission:!0,annualVolume:11979,editor:{id:"181079",title:"Dr.",name:"Christoph",middleName:null,surname:"Lüthi",slug:"christoph-luthi",fullName:"Christoph Lüthi",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bRHSqQAO/Profile_Picture_2022-04-12T15:51:33.png",biography:"Dr. Christoph Lüthi is an urban infrastructure planner with over 25 years of experience in planning and design of urban infrastructure in middle and low-income countries. 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Dr. Şentürk currently works as an professor of Biochemistry in the Department of Basic Pharmacy Sciences, Faculty of Pharmacy, Ağri Ibrahim Cecen University, Turkey. \nDr. Şentürk published over 120 scientific papers, reviews, and book chapters and presented several conferences to scientists. \nHis research interests span enzyme inhibitor or activator, protein expression, purification and characterization, drug design and synthesis, toxicology, and pharmacology. \nHis research work has focused on neurodegenerative diseases and cancer treatment. Dr. Şentürk serves as the editorial board member of several international journals.",institutionString:"Ağrı İbrahim Çeçen University",position:null,outsideEditionCount:0,totalCites:0,totalAuthoredChapters:"2",totalChapterViews:"0",totalEditedBooks:"1",institution:{name:"Ağrı İbrahim Çeçen University",institutionURL:null,country:{name:"Turkey"}}}],equalEditorOne:null,equalEditorTwo:null,equalEditorThree:null}],selectedSeries:null,selectedSubseries:null},seriesLanding:{item:{id:"11",title:"Biochemistry",doi:"10.5772/intechopen.72877",issn:"2632-0983",scope:"Biochemistry, the study of chemical transformations occurring within living organisms, impacts all areas of life sciences, from molecular crystallography and genetics to ecology, medicine, and population biology. Biochemistry examines macromolecules - proteins, nucleic acids, carbohydrates, and lipids – and their building blocks, structures, functions, and interactions. Much of biochemistry is devoted to enzymes, proteins that catalyze chemical reactions, enzyme structures, mechanisms of action and their roles within cells. Biochemistry also studies small signaling molecules, coenzymes, inhibitors, vitamins, and hormones, which play roles in life processes. Biochemical experimentation, besides coopting classical chemistry methods, e.g., chromatography, adopted new techniques, e.g., X-ray diffraction, electron microscopy, NMR, radioisotopes, and developed sophisticated microbial genetic tools, e.g., auxotroph mutants and their revertants, fermentation, etc. More recently, biochemistry embraced the ‘big data’ omics systems. Initial biochemical studies have been exclusively analytic: dissecting, purifying, and examining individual components of a biological system; in the apt words of Efraim Racker (1913 –1991), “Don’t waste clean thinking on dirty enzymes.” Today, however, biochemistry is becoming more agglomerative and comprehensive, setting out to integrate and describe entirely particular biological systems. The ‘big data’ metabolomics can define the complement of small molecules, e.g., in a soil or biofilm sample; proteomics can distinguish all the comprising proteins, e.g., serum; metagenomics can identify all the genes in a complex environment, e.g., the bovine rumen. This Biochemistry Series will address the current research on biomolecules and the emerging trends with great promise.",coverUrl:"https://cdn.intechopen.com/series/covers/11.jpg",latestPublicationDate:"July 5th, 2022",hasOnlineFirst:!0,numberOfOpenTopics:4,numberOfPublishedChapters:319,numberOfPublishedBooks:32,editor:{id:"31610",title:"Dr.",name:"Miroslav",middleName:null,surname:"Blumenberg",fullName:"Miroslav Blumenberg",profilePictureURL:"https://mts.intechopen.com/storage/users/31610/images/system/31610.jpg",biography:"Miroslav Blumenberg, Ph.D., was born in Subotica and received his BSc in Belgrade, Yugoslavia. He completed his Ph.D. at MIT in Organic Chemistry; he followed up his Ph.D. with two postdoctoral study periods at Stanford University. Since 1983, he has been a faculty member of the RO Perelman Department of Dermatology, NYU School of Medicine, where he is codirector of a training grant in cutaneous biology. Dr. Blumenberg’s research is focused on the epidermis, expression of keratin genes, transcription profiling, keratinocyte differentiation, inflammatory diseases and cancers, and most recently the effects of the microbiome on the skin. He has published more than 100 peer-reviewed research articles and graduated numerous Ph.D. and postdoctoral students.",institutionString:null,institution:{name:"New York University Langone Medical Center",institutionURL:null,country:{name:"United States of America"}}},subseries:[{id:"14",title:"Cell and Molecular Biology",keywords:"Omics (Transcriptomics; Proteomics; Metabolomics), Molecular Biology, Cell Biology, Signal Transduction and Regulation, Cell Growth and Differentiation, Apoptosis, Necroptosis, Ferroptosis, Autophagy, Cell Cycle, Macromolecules and Complexes, Gene Expression",scope:"The Cell and Molecular Biology topic within the IntechOpen Biochemistry Series aims to rapidly publish contributions on all aspects of cell and molecular biology, including aspects related to biochemical and genetic research (not only in humans but all living beings). We encourage the submission of manuscripts that provide novel and mechanistic insights that report significant advances in the fields. Topics include, but are not limited to: Advanced techniques of cellular and molecular biology (Molecular methodologies, imaging techniques, and bioinformatics); Biological activities at the molecular level; Biological processes of cell functions, cell division, senescence, maintenance, and cell death; Biomolecules interactions; Cancer; Cell biology; Chemical biology; Computational biology; Cytochemistry; Developmental biology; Disease mechanisms and therapeutics; DNA, and RNA metabolism; Gene functions, genetics, and genomics; Genetics; Immunology; Medical microbiology; Molecular biology; Molecular genetics; Molecular processes of cell and organelle dynamics; Neuroscience; Protein biosynthesis, degradation, and functions; Regulation of molecular interactions in a cell; Signalling networks and system biology; Structural biology; Virology and microbiology.",annualVolume:11410,isOpenForSubmission:!0,coverUrl:"https://cdn.intechopen.com/series_topics/covers/14.jpg",editor:{id:"165627",title:"Dr.",name:"Rosa María",middleName:null,surname:"Martínez-Espinosa",fullName:"Rosa María Martínez-Espinosa",profilePictureURL:"https://mts.intechopen.com/storage/users/165627/images/system/165627.jpeg",institutionString:null,institution:{name:"University of Alicante",institutionURL:null,country:{name:"Spain"}}},editorTwo:null,editorThree:null,editorialBoard:[{id:"79367",title:"Dr.",name:"Ana Isabel",middleName:null,surname:"Flores",fullName:"Ana Isabel Flores",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bRpIOQA0/Profile_Picture_1632418099564",institutionString:null,institution:{name:"Hospital Universitario 12 De Octubre",institutionURL:null,country:{name:"Spain"}}},{id:"328234",title:"Ph.D.",name:"Christian",middleName:null,surname:"Palavecino",fullName:"Christian Palavecino",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0033Y000030DhEhQAK/Profile_Picture_1628835318625",institutionString:null,institution:{name:"Central University of Chile",institutionURL:null,country:{name:"Chile"}}},{id:"186585",title:"Dr.",name:"Francisco Javier",middleName:null,surname:"Martin-Romero",fullName:"Francisco Javier Martin-Romero",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bSB3HQAW/Profile_Picture_1631258137641",institutionString:null,institution:{name:"University of Extremadura",institutionURL:null,country:{name:"Spain"}}}]},{id:"15",title:"Chemical Biology",keywords:"Phenolic Compounds, Essential Oils, Modification of Biomolecules, Glycobiology, Combinatorial Chemistry, Therapeutic peptides, Enzyme Inhibitors",scope:"Chemical biology spans the fields of chemistry and biology involving the application of biological and chemical molecules and techniques. In recent years, the application of chemistry to biological molecules has gained significant interest in medicinal and pharmacological studies. This topic will be devoted to understanding the interplay between biomolecules and chemical compounds, their structure and function, and their potential applications in related fields. Being a part of the biochemistry discipline, the ideas and concepts that have emerged from Chemical Biology have affected other related areas. This topic will closely deal with all emerging trends in this discipline.",annualVolume:11411,isOpenForSubmission:!0,coverUrl:"https://cdn.intechopen.com/series_topics/covers/15.jpg",editor:{id:"441442",title:"Dr.",name:"Şükrü",middleName:null,surname:"Beydemir",fullName:"Şükrü Beydemir",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0033Y00003GsUoIQAV/Profile_Picture_1634557147521",institutionString:null,institution:{name:"Anadolu University",institutionURL:null,country:{name:"Turkey"}}},editorTwo:{id:"13652",title:"Prof.",name:"Deniz",middleName:null,surname:"Ekinci",fullName:"Deniz Ekinci",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002aYLT1QAO/Profile_Picture_1634557223079",institutionString:null,institution:{name:"Ondokuz Mayıs University",institutionURL:null,country:{name:"Turkey"}}},editorThree:null,editorialBoard:[{id:"219081",title:"Dr.",name:"Abdulsamed",middleName:null,surname:"Kükürt",fullName:"Abdulsamed Kükürt",profilePictureURL:"https://mts.intechopen.com/storage/users/219081/images/system/219081.png",institutionString:null,institution:{name:"Kafkas University",institutionURL:null,country:{name:"Turkey"}}},{id:"241413",title:"Dr.",name:"Azhar",middleName:null,surname:"Rasul",fullName:"Azhar Rasul",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bRT1oQAG/Profile_Picture_1635251978933",institutionString:null,institution:{name:"Government College University, Faisalabad",institutionURL:null,country:{name:"Pakistan"}}},{id:"178316",title:"Ph.D.",name:"Sergey",middleName:null,surname:"Sedykh",fullName:"Sergey Sedykh",profilePictureURL:"https://mts.intechopen.com/storage/users/178316/images/system/178316.jfif",institutionString:null,institution:{name:"Novosibirsk State University",institutionURL:null,country:{name:"Russia"}}}]},{id:"17",title:"Metabolism",keywords:"Biomolecules Metabolism, Energy Metabolism, Metabolic Pathways, Key Metabolic Enzymes, Metabolic Adaptation",scope:"Metabolism is frequently defined in biochemistry textbooks as the overall process that allows living systems to acquire and use the free energy they need for their vital functions or the chemical processes that occur within a living organism to maintain life. Behind these definitions are hidden all the aspects of normal and pathological functioning of all processes that the topic ‘Metabolism’ will cover within the Biochemistry Series. Thus all studies on metabolism will be considered for publication.",annualVolume:11413,isOpenForSubmission:!0,coverUrl:"https://cdn.intechopen.com/series_topics/covers/17.jpg",editor:{id:"138626",title:"Dr.",name:"Yannis",middleName:null,surname:"Karamanos",fullName:"Yannis Karamanos",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002g6Jv2QAE/Profile_Picture_1629356660984",institutionString:null,institution:{name:"Artois University",institutionURL:null,country:{name:"France"}}},editorTwo:null,editorThree:null,editorialBoard:[{id:"243049",title:"Dr.",name:"Anca",middleName:null,surname:"Pantea Stoian",fullName:"Anca Pantea Stoian",profilePictureURL:"https://mts.intechopen.com/storage/users/243049/images/system/243049.jpg",institutionString:null,institution:{name:"Carol Davila University of Medicine and Pharmacy",institutionURL:null,country:{name:"Romania"}}},{id:"203824",title:"Dr.",name:"Attilio",middleName:null,surname:"Rigotti",fullName:"Attilio Rigotti",profilePictureURL:"//cdnintech.com/web/frontend/www/assets/author.svg",institutionString:null,institution:{name:"Pontifical Catholic University of Chile",institutionURL:null,country:{name:"Chile"}}},{id:"300470",title:"Dr.",name:"Yanfei (Jacob)",middleName:null,surname:"Qi",fullName:"Yanfei (Jacob) Qi",profilePictureURL:"https://mts.intechopen.com/storage/users/300470/images/system/300470.jpg",institutionString:null,institution:{name:"Centenary Institute of Cancer Medicine and Cell Biology",institutionURL:null,country:{name:"Australia"}}}]},{id:"18",title:"Proteomics",keywords:"Mono- and Two-Dimensional Gel Electrophoresis (1-and 2-DE), Liquid Chromatography (LC), Mass Spectrometry/Tandem Mass Spectrometry (MS; MS/MS), Proteins",scope:"With the recognition that the human genome cannot provide answers to the etiology of a disorder, changes in the proteins expressed by a genome became a focus in research. Thus proteomics, an area of research that detects all protein forms expressed in an organism, including splice isoforms and post-translational modifications, is more suitable than genomics for a comprehensive understanding of the biochemical processes that govern life. The most common proteomics applications are currently in the clinical field for the identification, in a variety of biological matrices, of biomarkers for diagnosis and therapeutic intervention of disorders. From the comparison of proteomic profiles of control and disease or different physiological states, which may emerge, changes in protein expression can provide new insights into the roles played by some proteins in human pathologies. Understanding how proteins function and interact with each other is another goal of proteomics that makes this approach even more intriguing. Specialized technology and expertise are required to assess the proteome of any biological sample. Currently, proteomics relies mainly on mass spectrometry (MS) combined with electrophoretic (1 or 2-DE-MS) and/or chromatographic techniques (LC-MS/MS). MS is an excellent tool that has gained popularity in proteomics because of its ability to gather a complex body of information such as cataloging protein expression, identifying protein modification sites, and defining protein interactions. The Proteomics topic aims to attract contributions on all aspects of MS-based proteomics that, by pushing the boundaries of MS capabilities, may address biological problems that have not been resolved yet.",annualVolume:11414,isOpenForSubmission:!0,coverUrl:"https://cdn.intechopen.com/series_topics/covers/18.jpg",editor:{id:"200689",title:"Prof.",name:"Paolo",middleName:null,surname:"Iadarola",fullName:"Paolo Iadarola",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bSCl8QAG/Profile_Picture_1623568118342",institutionString:null,institution:{name:"University of Pavia",institutionURL:null,country:{name:"Italy"}}},editorTwo:{id:"201414",title:"Dr.",name:"Simona",middleName:null,surname:"Viglio",fullName:"Simona Viglio",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bRKDHQA4/Profile_Picture_1630402531487",institutionString:null,institution:{name:"University of Pavia",institutionURL:null,country:{name:"Italy"}}},editorThree:null,editorialBoard:[{id:"72288",title:"Dr.",name:"Arli Aditya",middleName:null,surname:"Parikesit",fullName:"Arli Aditya Parikesit",profilePictureURL:"https://mts.intechopen.com/storage/users/72288/images/system/72288.jpg",institutionString:null,institution:{name:"Indonesia International Institute for Life Sciences",institutionURL:null,country:{name:"Indonesia"}}},{id:"40928",title:"Dr.",name:"Cesar",middleName:null,surname:"Lopez-Camarillo",fullName:"Cesar Lopez-Camarillo",profilePictureURL:"https://mts.intechopen.com/storage/users/40928/images/3884_n.png",institutionString:null,institution:{name:"Universidad Autónoma de la Ciudad de México",institutionURL:null,country:{name:"Mexico"}}},{id:"81926",title:"Dr.",name:"Shymaa",middleName:null,surname:"Enany",fullName:"Shymaa Enany",profilePictureURL:"https://mts.intechopen.com/storage/users/81926/images/system/81926.png",institutionString:"Suez Canal University",institution:{name:"Suez Canal University",institutionURL:null,country:{name:"Egypt"}}}]}]}},libraryRecommendation:{success:null,errors:{},institutions:[]},route:{name:"chapter.detail",path:"/chapters/43455",hash:"",query:{},params:{id:"43455"},fullPath:"/chapters/43455",meta:{},from:{name:null,path:"/",hash:"",query:{},params:{},fullPath:"/",meta:{}}}},function(){var e;(e=document.currentScript||document.scripts[document.scripts.length-1]).parentNode.removeChild(e)}()