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16 Carbon-Based Nanocarriers for Drug Delivery
spectroscopy, and X-ray diffraction (XRD). For a thorough characterization, many approaches must be used as they each give diverse morphological, physical, and chemical characteristics. The signicance and details of some of these characteriza­tion techniques related to CBNs are provided subsequently.
1.3.1 elecTron microscopy
The morphological investigation of CBNsand othernano-morphology may be car­ried out with the use of electron microscopicimaging techniques, including TEMand SEM. The dimensionalities and morphological congurations, and orientations of carbon-based nanomaterials, including graphene and its derivatives, CNTs, quantum dots and nanodiamonds, can be observed at the initial stages through these micro­scopical investigations. Higher resolution and the most comprehensive morpholog­ical, crystal, and topographic assessment are possible with high-resolution (HR) TEM. To determine the elementalcomposition of the CBNs, energy dispersive X-ray analysis (EDX) is frequently used in conjunction with electron microscopy. The ori­entation/alignment of CNTsand the patterned surfaces resulting from the various CNT growing processes were visualized usingSEM. SWCNTs and MWCNTs may be differentiated, and their diameters measured using HRTEM. Moreover, HRTEM­EDX is capable of detecting and identifying the existence of carbon-containing and catalytic nanoparticles [35,159]. The potential of HRTEM to determine the chiral indices of SWCNTs is more intriguing.
Moreover, it made it possible to recognize fullerenes (C60) within SWCNTs (pea­pod structures) [160] and even to see the deformation of tiny hydrocarbon molecules that were contained within carbon nanotubes [161].
1.3.2 FTir specTroscopy
The existence of various functional groups in pristine and functionalized CBNs can be validated through FTIR spectroscopic analysis. In the case of GO, the exis­tence of oxygenated functional groups such ashydroxyl, carboxyl,and epoxy groups was conrmed by FTIR. Although FTIR spectroscopy was widely employed for functionalized CBNs, the intensity signals from FTIR spectroscopy are often weak. Therefore,other methods, like Raman spectroscopy and XPS, are more suited for assessing pristinecarbon nanomaterials [35].
1.3.3 UV-Vis specTroscopy
UV-Vis spectroscopy was frequently employed to evaluate the absorption bands of numerous nanomaterials and nanocomposites, especially the materials that describe photoactivity. A π-π* transition of aromatic C = C interactions may be seen in graphene and CNTs, which exhibit a signicant absorption band at about 230 nm [162]. Incidentally, graphene has a smaller percentage of sp toGO, which illustrates how it is less transparent in the UV-visible spectrum. Such distinct characteristic was utilized to analyze reduction reactions or determine the degree of GO oxidation [163]. Also, as the quantity of layers in graphene climbs, the
2
carbons as compared
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absorbance of the material increases. Using this property, Sun etal. (2010) computed the number of layers of graphene using UV-visible absorbance at 550 nm [164].
UV-vis spectrophotometry was utilized in the instance of CNTs to evaluate the dispersion strategies of SWCNTs and MWCNTs since the intensity of the absorbance rises as the dispersion is enhanced. Furthermore, UV-vis absorbance may be used to estimate the concentration of CNTs that exist in a solution [35,165].
1.3.4 raman specTroscopy
The most adaptable tool for characterizing carbon-based nanomaterials is recognized as the Raman spectroscopy investigation. Such a nondestructive characterization method, which is widely employed for carbonaceous materials, yields critical frag­ments of information. This characterization techniqueenables one to examine func­tionalization, structure, and purity, among theother featuresof CBNs. According to Raman spectroscopy, the D, G, and 2D peaks, which are located about 1350, 1580, and 2700cm-1, correspondingly, are where carbon allotropes may be distinguished. The D-band (D-disorder) results from the out-of-plane vibrational modes, and it is evidence of the inclusion of sp3 carbon, whereas the G-band (G-graphite) belongs to the axially stretched (E2g) phase of graphite. As a result, the sp2-hybridized carbon atoms become disordered, which results in the structural aberrations observed in the twisted graphene sheet and/or tube ends. The second-order Raman scattering mechanism is the source of the 2D band, which has almost twice the frequency of the D band [35,166].
The intensity ofthe G-band of graphene increases with the increase inthe number of sheets. Moreover, this expansion broadens the 2D band in the plane of higherwave­number [166]. This phenomenon was used by Ferrari etal. (2006) to design a system for estimating the layers within graphene specimens [167]. The ratio of peak intensities ID/IG is another intriguing statistic since it could be employed to assess the degree of disorder in graphene. When thedefects are identied, two distinct phases have been outlined: the rst stage depicts the transformation from pure graphite to nanocrystalline graphite withlowerdefect density, while the second stage accounts for the shift from nanocrys­talline graphite to mostly sp2 amorphous carbon ofhigherdefect density [168].
The ID/IG ratio is another tool for evaluating the purity of CNTs, although it is relatively simple to comprehend. The proportion of defects increases as the ID/IG ratio rises. In addition to the D and G bands, the radial breathing modes (RBMs)provide another intriguing band, whichmay be detected at lower wavenumbers ranging from 160 to 350cm-1 [169]. These modes are produced through symmetric contractionand expansion ofthe tubes along the tube’s axis. RBM could be employed to investi­gate the electronic framework via its intensity (I diameter (dt) via its frequency (ω
). It could also be utilized to carry out an (n, m)
RBM
attribution of a solitary isolated SWCNT through the evaluation of both dt and I Additionally, the identication of the RBM spectrum provides a clear indication of the existence of SWCNTs. Inthe case ofMWCNTs, the RBM signal is barely per­ceptible. The reason for this is that the RBM band of wide-diameter tubesis often too weak, and the ensemble median of the inner tube diameter enhances the signal. The inverse relationship between RBM’s frequency and tube diameter is one of its most appealing characteristics [35].
and to evaluate the nanotube
RBM)
RBM.
18 Carbon-Based Nanocarriers for Drug Delivery
1.3.5 X-ray phoToelecTron specTroscopy (Xps)
An effective qualitative investigation of the nanomaterials as well as the surface chemistry of CBNs can be performed using the nondestructive characterization method known as XPS. It serves as the most trustworthy characterization method for determining the elemental composition, chemical state, and electronic state, along with the functional groups present within the CBNs. The sp2 carbon (C-C), epoxy (C-O), hydroxyl (C-OH),and carboxyl (COO) peaks in the XPS spectra (C1s)for GO and GONS are located at binding energies of285, 287, and 290 eV, correspondingly [100,170]. XPS examination was extensivelyused to evaluate variations in oxygen­atedfunctional entitiesinGO and rGO.
1.3.6 X-ray DiFFracTion
The XRDtechniques play a signicant role in the assessment of amorphous and crystalline materials by offering insights about phase recognition, lattice struc­ture, and qualitative evaluation. This method can estimate interlayer spacing and is effective for describing and identifying polycrystalline phases. Because of these factors, XRD has been extensively used to track the oxidation of graphite and the subsequent exfoliation of graphite oxide to graphene oxide. According to the XRD pattern, pure graphite has a basal reection (002) peak at 2θ=26o (interlayer spacing 0.34 nm), while graphite oxide was found at 2θ=12o (interlayer distance
0.7 nm). An interlayer extension in graphite oxide is caused by the complexation of oxygen species among the graphite layers. As oxidation progressed, the (0 0 2) diffraction line’s strength progressively faded until it eventually vanished. Simul­taneously, oxidation enhanced the strength of the diffraction peak at 12o. The peak at 12 The literature’s diverse research concluded that the peak emerged in the region 2θ =23.0–23.5°, which reects the rGO of (0 0 2) plane. The XRD pattern in range 2θ=9–11.20°, on the other hand, reects the (0 0 1) plane of GO. Due to the addition of hydrophilic groups brought about via oxidation and GO synthesis, there is an increase in the interlayer spacing in the crystallographic planes of graphite [100].
talline frameworks that exhibit a peak at 2θ=6o in the XRDspectra [173]. This method makes it possible to determine the number ofSWCNTs present within every bundle [159]. A (0 0 2) plane for apeak ofgraphite is visible in MWCNTs at 2θ=26o. The growth of the MWCNTs has been demonstrated using these signals [35].
o
vanished after complete exfoliation of the graphite oxide [102,171,172].
In comparison to CNTs, as-produced SWCNTs have the propensity to form crys-
1.4 APPLICATIONS OF CBNS
The development of unique nanomaterials with extraordinary functionalities has resulted in the expansion of nanotechnology in almost all commercial areas in recent years. CBNs have potential applications as nanomaterials in a variety of elds, including biomedical, energy, electronics, andenvironmental remediation.The enor­mous potential of these materials should continue to pique scientic interest, and any
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use of the new technology is anticipated to transform human civilization. Herein, we briey cover studies on and applications for carbon-based nanomaterials and nano­compositesin therapeutics and environmental remediation.
1.4.1 TherapeUTics
The human race has been provided with a variety of nano-enabled commodities or nanosystems, which are now used for a variety of biomedical applications. In the realm of nanostructure purview, such nano-constructs and combinations with phar­maceuticals, enzymes, nucleic acids, viruses, proteins, cellular lipid bilayers, cellular receptor sites, and antigens (crucial for immunotherapy) are multidimensional [174]. Agroup of nanosystems that have been extensivelyinvestigated for drug delivery and other biomedical applications is theCBNs. Recently, they have demonstrated effectiveness in elds including theranostics [175], cancer treatment [10,176], and regenerative medicine [177]. (See Figure1.5)[178].
Certain characteristics of carbon nanomaterials, including their large surface areas and outstanding electrical and mechanical characteristics, encourage their uti­lization in the diagnostic and therapeutic domains as well. The major advantages over the utilization of CBNs in the eld of therapeutics and diagnostics are:
1. They may absorb a signicant amount of drug due to their supramolecular
“π–πstacking” characteristic.
2. CBNs can be used as novel therapeutic components due to their distinct
optical properties and easy fusion with illuminating components.
FIGURE 1.5 The Biomedical Application of Carbon-Based Nanomaterials. [Replicated with permission from Mahor et al. (2021)] [178].
20 Carbon-Based Nanocarriers for Drug Delivery
3. CBNs have outstanding near-infrared (NIR) heat conversion competence
that makes them a good choice for photothermal treatment (PTT).
4. Therapeutic agents can be released under regulated conditions using tunable
surface chemistry.
The deployment of CBNs in the biomedical eld is hindered by theircolloidal sta­bility in organic or aqueous environments [20]. Nevertheless, this could be resolved by stimulating the surface of CBNsusing functionalization via covalent and non­covalent approaches. One such inevitable stage that modulates the surface by incor­porating distinct functional entities is the functionalization of CBNs. There are several methods for covalent functionalization, including oxidation,plasma treat­ments,dehydrogenation, etc. [178]. Due in signicant part to the surface modica­tion of CBNs, which allows them to, for example, penetrate biological membranes, theyhave been widely used in the administration of drugs. The therapeutic efcacy of CBNs-assisted DDSs can be improved through their functionalization with cer­tain targeting ligands such as aptamers and folic acid (FA), which also reduces their cytotoxicity toward healthy cells.
Modest targeting molecules, such as FA [179], which targets folate receptors espoused on the exterior of a range of robust cancerous cells, ligands with an afnity for a particular receptor overexpressed on a particular malignant tumor [10,180], a monoclonal antibody that recognizes tumor-associated antigens [181], and magnetic nanoparticles [100], can also be incorporated with the drug-loaded CBNs. Such tech­niques allow for targeted delivery by receptor-mediated endocytosis or drug aggre­gation at the target region with the use of an externally applied magnetic eld. As a result, functionalized CBNs have found use in the transport of proteins, enzymes, nucleic acids, and biomolecules. CBNshave been used to administer anticancer drugs, uorescent markers for tumor identication, PTT, and othertheranostics [100,178].
For thefunctions like point-of-care detection, the design of precise biosensors is essential. Early and accuratediagnosis of conditions like cancer can increase a patient’s likelihood of surviving [182]. Bioimaging is a technique that allows for the molecular characterization and investigation of biological processes [183]; it may examine a treatment plan in addition to aiding in illness detection. Owing to their superior attributes of having a large surface area, being robust, and having outstand­ing electronic attributes, graphene-based materials were extensivelyemployed in bio­imaging and biosensing applications [182]. The capacity to transport electrons and the amphiphilicity of these nanomaterialsare two important properties that might affect their potential for biosensing [184]. The aws in GO facilitate electron transfer, whereas the functional groups enable surface modication and luminescent compo­nent binding [185]. Proteins, oligonucleotides, and antigens are typical examples of detection molecules [186]. These can be covalently or non-covalently connected to the horizon of graphene derivatives.
To detect CD59, a lung cancer biomarker, Chauhan etal. (2020) loaded anti-CD59 antigens onto graphite electrodes to form an immunosensor. The graphite rods were coated with GO to increase their conductivity. The study provided a quick and noninvasive lung cancer diagnostic method [187]. Arapid and accurate method of detecting the lung cancer (NSCLC) biomarker CK19 in spiking human plasma was
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developed by Chiu et al. (2018) using a carboxyl-GO-modied biomaterial-based SPR biosensor. SuchGO-COOH-based SPRchip, which has a positive linear range (0.001–100 pg/mL) with shorter response times than a conventional SPR chip, out­performed it in terms of detection limits. They later discovered that a biosensor sys­tembased on carboxyl-GO could identify CK19 at levels as low as 0.05 pg/mL in 10% serum proteins and 0.001 pg/mL in PBS solution [188].
CNTs have undergone extensive investigation toward the targeted and con­trolleddelivery of anticancer agents due to their distinct properties. CNTs are drug carriers for several anticancer cancer medicines and efcient phototherapy stim­ulators due to their inherent optical characteristics. Because of their adaptability, CNTs can be used therapeutically for a variety of cancers. At this time, a lot of anticancer treatment strategies are aimed at eradicating tumor cells and the con­ditions that support them. Actively going after cancer cells can effectively remove their parenchyma, but treating the tumor microenvironment unswervingly can stop tumor cells from proliferating and spreading by upsetting their environment, which also indirectly kills cancer cells [189]. Recently, Zhou etal. (2022) synthesized mul­tifunctional and PEGylated MWCNTs for the targeted delivery of the anticancer agent, Doxorubicin (DOX). Adipic acid (AA) was used as a cross-linking agent to bind the targeted ligand of folic acid (FA) to hyperbranched poly-L-lysine (HBPLL). Further, DOX was successfully integrated on the MWCNT-PEG-AA-HBPLL-FA nanocarrier, and thein-vitro release of drugs was examined using a UV-Vis spec­trophotometer. The in-vitro cytotoxicity and anticancer capabilities of DOX-loaded nanocarrier were investigated in the human embryonic kidney (HEK293) and liver cancer (HepG2) cells. The presented nanocarrier demonstrated effective drug loading efciency, pH-responsive and targeteddrug release; this assessment is signicant as it can get around some of the drawbacks of traditional cancer chemotherapy, like the simplicity through which obtained nanoparticles attach to cancerous cells receptors, which then quickly enter receptor-mediated endocytosis and deliver the drug to the affected regions. At acidic pH levels, intracellular endosome surroundings showed a signicant proportion of drug release rate. The nanoparticles have been reported to have signicant cytotoxicity for HepG2 cells and low cytotoxicity for HEK293 cells. [190]. ANovel SWCNTs-based DDS was designed by Yu etal. (2016) for the pro­longed delivery of Paclitaxel (PTX). The sidewalls of SWCNTs were non-covalently linked with chitosan to improve their biocompatibility. To achieve the cell-targeting property, biodegradable hyaluronan was also added into the chitosan’s outer surface. The results showed that PTX release depended on pH and was enhanced at lower pH values (pH 5.5). The improved SWCNTs drastically lowered intracellular reactive oxygen species (ROS), which may have boosted the activation of mitogen-activated protein kinases and greatly facilitated cellular damage. Western blotting results showed that apoptosis-related proteins were highly expressed in A549 cells. The vitality of the A549 cells was decreased by PTX-loaded SWCNTs, as evidenced by cell viability assays and a lactate dehydrogenase (LDH) release experiment [191].
In the family of CBNs, the graphene quantum dots (GQDs) are considered the smallest derivatives of graphene. Owing to their tiny size, GQDs are able to cross the blood-brain barrier (BBB) and deliver nucleic acid cargo to cell cytosols and nuclei. Due to their low toxicity, high solubility, and luminous properties that make
22 Carbon-Based Nanocarriers for Drug Delivery
it straightforward to track drug release, GQDs are a great option for gene carriers. Recently, Ghafary etal. (2017) established a distinctive nanoconjugate consisting of GQDs, the chimeric peptide MPG-2H1, and plasmid DNA (pDNA)that is capable of real-time monitoring and gene delivery [192]. The nanoconjugate was synthesized by non-covalent interactions between each component. The enhanced complex achieved transfection efciency that was approximately eight times greater than the typical peptide-pDNA combination. The results of this study suggest that GQDs could per­form well as a transfection vector for gene delivery applications. Due to the signi­cant presence of the sp2 domain and the possibility for “π-πstacking,” GQDs provide greater drug loading in comparison to certain other nanomaterial drug carrier sys­tems. Because these biomolecules must be covalently bonded to the edge groups, the active sites on the edge of GQDs are unfortunately restricted to ligands, making it doubtful that they will be exploited in gene delivery applications [192]. The promis­ing outcomes of several studies on gene therapy employing CBNs haveboosted the hopes of individuals seeking treatment. However, the regulatory clearances will take a long time, even though this is a very different notion because the technology and its implications for individuals seem mostly unstudied.
Carbon-based nanomaterials, with their superior mechanical and chemical prop­erties, have displayed signicant potential for tissue engineering applications. CNTs were effectively used in the development of medications for bone, cardiac, and neu­rological regeneration. Bone is capable of self-healing and rebuilding after mild trauma or fractures. Nevertheless, in pathogenic injuries, acute bone attrition, or core tumor excision, bone is no longer able to mend itself if the aws are greater than a threshold size (5mm) [193,194]. This case reported a variety of treatments, including xenografts, allografts, and autografts. Unfortunately, these methods have serious disadvantages, including limited availability and donor site morbidity for autografts, the risk of resistance and infection transmission for allografts, and the probability of immunogenicity and a poor clinical prognosis for xenografts [194]. Consequently, a novel and highly promising approach involving the use of 3D con­structions known as tissue-engineered synthetic bone scaffolds hasgained tremen­dous attention, which provides the support required for cell adhesion, growth, and transformation. Tanaka etal. (2017) developed a 3D block construction consisting of CNTs and compared its efciency as a scaffold for bone regeneration to that of PET-reinforced gelatin. The articial structure and rat femoral bone had compres­sive strengths of 62.1 MPa and 61.86 MPa, respectively, and mechanical analysis revealed no discernible differences. Cell adhesion occurred earlier on CNT scaf­folds compared to collagen-reinforced PET scaffolds. Recombinant human BMP-2 was added, which boosted the ALP activity in the CNTs block and showed good osteogenesis properties [195].
Corresponding to this, multiple investigations have shown that GO-based nano­carriers may effectively be used for muscle, skin, and cardiac tissue regeneration [10]. Altogether, CBNs showed excellent efcacy and capacity for drug administration in regenerative medicine, gene therapy, and cancer treatments, which may indicate a exible treatment option for diseasedindividuals. Despite the positive outcomes of CBNsbiocompatibility trials, further research is needed to fully understand the harmful effects and toxicity of carbon-based nanocarriers.
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1.4.2 enVironmenTal remeDiaTion
There are signicant environmental degradation concerns as a result of the rise of modern civilization, the expansion of urbanization, the expansion of industrial output, and the intensication of transportation. Human productivity and routine everyday activities are increasingly causing environmental disruption. Antibiotics, pesticides, dyes, heavy metals, greenhouse gases, endocrine disruptors, and organic compounds are just a few of the toxic emissions that are released into groundwater, soil, and air, endangering both human health and the ecosystem [196]. According to the “UN Global Water Development Report,2018,”around 80% of efuent from urban and commercial operations is discharged into the environment without anypretreatment, which either directly or indirectly degrades the quality of the water [197]. Generally, efuent should be processed before being released into the environment because it includes hazardous proportions of metallic ions, organic compounds, dyes, and other cancer-causing substances [198]. Researchers have worked hard to identify a variety of compounds that may effectively eliminate contaminants fromwastewater, includ­ing clay minerals, carbon-based materials, and both organic and inorganic nanoma­terials [199].
Due to their outstanding physicochemical characteristics, CBNs have received a lot of interest in the domain of environmental remediation. These nanomaterials have higherspecic surface areas, superior acid stability, and heat resistance [197]. It has been discovered that CBNs, with adsorption effectiveness > 80% andphotocat­alytic degradation efciency > 98%, may efcaciously eliminate contaminants like heavy metals,nitric oxide, dyes, hydrogen sulde,and pharmaceutical compounds from the surroundings [196]. Throughout the past ten years, studies regarding the utilization of CBNsin the remediation of pollutants have steadily increased (2012–
2021).Porous frameworks and functional units are themajorattributes ofadsorbent in nature, which makes it possible to use CBNsin the prevention of environmental pollution. Particularly at lower concentrations, photodegradation is a useful method for the removal of organic compounds from contaminants. The optimum outcomes in the photocatalytic breakdown of organic compounds are the nal products of car­bon dioxide and water. In the case ofheavy metal ions, in addition to their deposition on CBNs, metal ions may also be immobilized in the surroundings by the photocat­alytic degradation of high-valent components to low-valent ones, followed by the production of in-situ precipitates [197].
Signicant benets and potential for application-driven investigation have been made possible by the distinct physicochemical characteristics of graphene and related materials, specically through graphene oxide (GO). GO, with its2D structure, highersurface area, oxygenatedfunctional entities, andfunctionalization ability, delivered substantial potential for the removal of heavy metal ions, organic pollutants, radioactive pollutants, and agricultural pollutants like pesticides and her­bicides. Nevertheless, the stability and propensity for aggregation of GO in aqueous environments result in a decline in itsperformance efciency. The effective surface area of GO nanostructure tends to decrease with aggregation, which has an impact on the overall effectiveness ofthe water treatment process. These restrictions could be circumvented by functionalizing GO with inorganic nanomaterials as well as
24 Carbon-Based Nanocarriers for Drug Delivery
other functional groups. Recently, a unique nanocomposite based on GOand other functionalized nanostructures has been designed for rapid, inexpensive, and effective methods and used successfully to remove various types of contaminants [138].
To remove lead (Pb (II)) ionsfrom an aqueous system, Zarenezhad etal. (2021) recently synthesized magnetic graphene oxide (MGO) and further functionalized it usingMEA,melamine, andEthylenediamine (EDA).For process improvement, the variables inuencing the adsorption of Pb (II) ions were examined. Acomparison of the adsorption performances for nanocomposites such as MEA-MGO, M-MGO and EDA-MGOrevealed 97.65%, 96.34%, and 98% removal efciency for lead ions, respectively. Moreover, 98% elimination of Pb (II) was seen under ideal circum­stances (Co= 20 ppm, X=40 mg, pH =4, t= 10 min) [200]. Utilizing the free radical reaction approach, Pashaei-Fakhri etal. (2021) were able to effectively pro­duce a nanocomposite hydrogel, particularly acrylamide/GO-bonded sodium algi­nate (AM-GO-SA) and acrylamide bonded sodium alginate (AM-SA) hydrogel. The effectiveness of the developed hydrogel composites was assessed for the adsorption ofcrystal violet dyes. It was discovered that AM-SAand AM-GO-SAeach had the highest capacity for adsorption at 62.07 mg/g and 100.30 mg/g, correspondingly [201]. In a single step, Chen etal. (2019) demonstratedan entirely novel bio-adsorbent for simultaneous photochemical reduction and dye adsorption. The bio-adsorbent was synthesized usingGO, titanium dioxide (TiO2), and corn straw pith (CSP). The GO and CSP serve as coats and stents, respectively. Nevertheless, TiO2 nanoparticles are afxed to the adsorbent’s surface and serve as both an adsorbent with enhanced hydrophilicity and a photochemical dye degradation agent. The direct use of the adsorbent maize straw pith during pyrolysis offered a valuable and economical uti­lization for the agricultural commodity. The adsorption process was accomplished via non-covalent interactions, includingπ–πstackings andelectrostatic interaction. The conguration and structure of the GO loading with 5 weight percent and 20 weight percent TiO2 were excellent, with signicant removal efciency for pollutants [202]. The potential use of GOnanoplatelets for the elimination of carbamazepine was examined by Bhattacharya etal. in 2020. Response surface methodology (RSM) Articial Neural Network modeling was used to signicantly improve the adsorption system for the dosage of adsorbent, initial amount of carbamazepine, temperature, and pH. At adsorbent dosage of 1g/L, pH 2, and 120 minutes of adsorption process, the highest adsorption capacity was reported to be 9.2 mg/g andremoval efciency of99%. [203].
In addition, to GO, other CBNs such as carbon quantum dots (CQDs) [204], CNTs [197], and fullerene [24] have also been extensively utilized for environmental reme­diation applications. For instance, with their distinct PL attributes and signicant conversion abilities, CQDs have delivered tremendous potential for the degradation of dyes and other organic contaminants along with active pharmaceutical agents [205]. Recently, Zhou etal. (2019) used a microwave-assisted technique to produce carbon dots (CDs), which were then divided into three distinct size fractions using size exclu­sion chromatography. The lack of a link between CD size and PL emission wavelength demonstrates that the PL process is notdependent on quantum size. The light absorp­tion characteristics and band gap of the CDs altered with particle size, as evidenced by UV/vis absorption and diffuse reectance spectrometry. The photodegradation of
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organic dyes was carried out independently using each of the three CDs segments beneath simulated sunlight exposure. It was discovered that as the dimension of the particles reduced, the reactivity of the CDs wasincreased. The 2-nm CDs were able to completely degrade both methylene blue (MB) andrhodamine B (RhB) in 150 minutes. The scavenger experiments revealed that the major components engaged in the photodegradation of the dyes by the 2-nm CDs aresuperoxide radicals andholes. Throughout the several cycles of dye degradation, these CDs demonstrated excellent stability. The 2-nm CDs have alsodemonstrated decent p-nitrophenol photodegra­dation. For the rst time, thendings of this study describedthat bare carbon dots might be used to degrade environmental pollutants [206].
Astudy done byQi etal. (2016) describedthat a facile solution-phase approach could be used to effectively synthesize a variety of fullerene (C60)-modied anatase TiO2 (a-TiO2) nanostructures of varied C60 proportions. Under UV-A light irradiation, the photodegradation ofMBby pristine a-TiO2 and C60@a-TiO2 nanostructures was evaluated, revealing that C60 signicantly improves the photocatalytic performance of a-TiO2 nanoparticles with an ideal level of 2.0 wt%. They looked into the elec­tronic conguration of the C60@a-TiO2 hetero-interfaces in conjunction with the den­sity functional theory (DFT) computations to unveil the fundamental mechanism of the C60 stacking on the photocatalytic performance. It was discovered that introduc­ing C60 to the interface of a-TiO2 not only reduced the energy gap but also established a new doping state across the valance and conduction band. As a consequence, the C60@a-TiO2 nanocomposites would exhibit better photocatalytic activity due to the effective charge separation and greater light adsorption caused by the existence of a transitional electronic state [207].
The photocatalytic breakdown of organic contaminants is still a “black box” technique, particularly in terms of the study of reactive component activity and the determination of intermediate compounds, both of which are useful in evaluating the catalytic characteristics of nanomaterials. The quantitative measurements of intermediates online remain quite challenging. Future research may focus on devel­oping quick online analysis to comprehend how organic contaminants degrade through photocatalysis. The majority of nanostructures are still being developed in laboratories and are thus difcult to produce and utilize on a large scale. CBNs continue to struggle with high manufacturing costs and challenges with large-scale production. To safeguard the homeland of mankind, environmental remediation isreceiving a growing amount of attention worldwide. In the future, mass man­ufacturing and cost-reduction strategies will likely receive increased emphasis in the R&D of CBNs. The advancement of methodologies might enable the mass pro­duction of inexpensive CBNs. Since CBNsare eventually discharged into the eco­system, their toxicity in the natural surroundings must additionally be taken into account [197].
It is unavoidable that a certain amount of CBNs would be discharged into the atmosphere through their production operations when those are employed forenvironmental remediation; hence, environmental nanoparticle residues need to be factored in. Despite the fact that the study on the toxicity of nanostructures in the ecosystem is still in its early stages, it is important to considerthe toxicity of CBNs.