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Biomass and industrial wastes as resource materials for Aerogel preparation: opportunities, challenges and research directions Nilofar Asim, Marzieh Badiei, Mohammad A. Alghoul, Masita Mohammad, Ahmad Fudholi, Md Akhtaruzzaman, Nowshad Amin, and Kamaruzzaman Sopian Ind. Eng. Chem. Res., Just Accepted Manuscript • DOI: 10.1021/acs.iecr.9b02661 • Publication Date (Web): 23 Aug 2019 Downloaded from pubs.acs.org on August 24, 2019
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Biomass and industrial wastes as resource materials for Aerogel preparation: opportunities, challenges and research directions Nilofar Asim1*, Marzieh Badiei2, Mohammad A. Alghoul3, Masita Mohammad1, Ahmad Fudholi1, Md Akhtaruzzaman1, Nowshad Amin4, Kamaruzzaman Sopian1 1
Solar Energy Research Institute, Universiti Kebangsaan Malaysia, Malaysia 2 Independent Researcher: Razavi 16, 91777-35843 Mashhad, Iran 3 Center of Research Excellence in Renewable Energy Research Institute, King Fahd University of Petroleum & Minerals, Saudi Arabia 4 Institute of Sustainable Energy, Universiti Tenaga Nasional, Malaysia * Corresponding author:
[email protected];
[email protected].
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Abstract: Aerogels with extraordinary properties have attracted much attention due to their suitability for different technologies. However, the drawbacks of aerogels, such as expensive raw material and costly preparation methods, have motivated researchers to seek alternative materials. Meanwhile, rapid economic development has driven the generation of massive agricultural, biomass, and industrial wastes. Despite the huge potential of recycling wastes for preparation of various aerogels, related investigations are limited. This study reviews the variety of waste biomasses used for preparation of different types of aerogels and their applications, as well as the technologies used in their preparation. This study will draw the attention of researchers due to the potential of biomass as sustainable resource for the production of aerogels. Future research challenges and directions for the commercial application of aerogels are presented.
Keywords: biomass; industrial wastes; aerogel; sustainable preparation
1. Introduction: The challenge of conventional aerogel preparation has been overcome by extracting pure precursor, mainly polysaccharide-based precursors, and recycling silica precursor from different types of wastes. Bio-based aerogels, a class of porous biodegradable materials, are renowned because of their low density and large specific surface area. The first results of aerogel synthesis were reported by S. S. Kistler 1 and followed by some trials in 1988
2, 3, 4,
which led to the preparation of porous cellulose compounds from cellulose xanthate 5. The utilization of natural renewable polysaccharides in the preparation of bio-based aerogel materials from multiple sources, such as alginate, cellulose, chitosan (CS), lignin, pectin, proteins, and starch, represents an interesting innovation in this field
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6, 7, 8, 9, 10.
The search
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results from Scopus search engine showed the increasing trend for using different waste and biomass as resource materials for aerogel preparation (Figure 1.)
Figure 1. The trend for aerogels utilizing various biomass and waste as resource materials. In fact, natural biopolymers are remarkable precursors for the preparation of bio-based aerogels. The use of these biopolymers potentially adds value to low-cost waste products. Notably, using agricultural and industrial wastes decreases wastes and reduces air and water pollutions by high percentage. The majority of biopolymers are obtained from agricultural wastes like lignocellulosic biomass, including forestry wastes, straws, and stovers of field crops
11,
such as corn and soybean; however, marine biomass
12
and solid urban residues
13
have similar attracted interest. Bio-based aerogels have typical features, such as sustainability, biodegradability, strong hydrophilicity, and large surface area. As-prepared aerogels are potential candidates for thermal insulation adsorbents
16.
14,
drug delivery systems
15,
and
Moreover, environment-friendly production of silica aerogel from wastes,
specifically agricultural residues, like rice and wheat husk 17, has been widely reported. Conversion of biomass wastes as sustainable natural resource into biodegradable aerogels is a significant sustainable process. Biodegradability factor is a substantial characteristic of the aerogel that makes it an eco-friendlier material compared with conventional aerogels. Utilizing biomass and wastes, reduces their negative environmental impacts
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and provides
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sustainability of nature. It also results in resource efficiency as well as lowering waste disposal cost. A series of excellent reviews have summarized the fabrication process, structures, and applications of aerogels, but considerably less attention has been placed specifically on those from wastes. In this review, we provide basic data on various aerogels with emphasis on the most abundant inedible biopolymers, mainly cellulose, lignin, chitin, and chitosan, as well as silica inorganic aerogels obtained from waste resources. The type of waste, type of extracted monomer, monomer structure, modifications and processing method such as drying conditions definitely influence on the physiochemical properties and structure of each individual aerogels. Here, a detailed study of the aerogels prepared from wastes (agricultural, industrial, municipal) based on more than 200 articles and regarding to their preparation, applications, and the technologies used in the preparations of different types of aerogels is surveyed in this article. 2. Aerogel preparation methods: The sol–gel method, as a chemical synthesis route, is a common approach for the preparation of aerogels. Freeze drying is commonly performed to prepare carbon-based aerogels, while ambient pressure drying is mostly conducted to synthesize silica aerogel from waste materials. The preparation of hydrophobic carbon-based aerogel is mostly realized by introducing a hydrophobic function on the surface of the aerogel via chemical modification 18 or pyrolysis
19, 20.
Drying of alcogels is regarded as one of most important step in the
preparation of aerogels 21. Given that freeze drying is not preferred for industrial use, research on the preparation of aerogel by air- and oven-drying methods have been ongoing 22. Loading nanomaterials on aerogel for various applications has been done via different methods, such as atomic layer deposition, hydrothermal, in situ synthesis, and ion exchange 23, 24, 25. Doshi 19
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reviewed bio-based aerogel preparation methods for oil removal application. Cellulose, as one of the most important and abundant sustainable materials in nature, is extensively used to prepare nanocellulose due to its promising properties and potential use in many applications. Groups of nanocellulose, nanofibril cellulose, and nanocrystal nanocelluloses have been used in various applications as renewable and sustainable materials. The huge potential of using agricultural and industrial wastes for preparing nanocellulose render the latter more interesting because its composition is directly dependent on its sources (agriculture biomass, marine animals, algae, fungi, and industrial waste)
26, 27, 28.
Figure 2 shows the different
techniques that could be utilized to prepare cellulose nanofibers, nanocellulose and aerogel from agricultural biomass. Chemical pretreatment in this case include acid hydrolysis, alkaline hydrolysis, oxidation, and organic solvents/ionic liquids. In enzymatic preparation, the enzyme catalyzes the hydrolysis of cellulose fibers
28.
Rajinipriya et al.
28
reviewed the
importance of waste materials in the preparation of nanocellulose. Considering of increasing demand for nanocellulose and environmental concern, they proposed more research concern on sustainable raw materials such as agricultural and industrial wastes as resource materials. Regarding to lignin, Figure 3 shows precipitation of lignin from black liquor obtained from pulp and paper industry through the Sequential Liquid-Lignin Recovery and Purification (SLRP) process. Black liquor that is composed mainly of 10–50% lignin by weight
44.
Furthermore, Figure 4 depicts the schematic of marine waste processing for preparation of proteins, pigments, chitin, CS, and their oligomers. Bernd et al.
29
used pyrolysis to
synthesize carbon nanostructures, such as carbon fiber, nanotubes, and graphite, from wood sawdust. Ravi et al.
30
extensively reviewed the preparation methods of different carbon
nanomaterials using biomass and plastic wastes as potential resource materials. The possibility of syntheses of other carbon allotropes, such as graphitic structure and nanotubes, using cellulose from waste biomass must be considered for the preparation of
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other carbon-based aerogels. Sevilla et al. 31 synthesized graphitic carbon nanostructures with cellulose as its source material. They used hydrothermal treatment, impregnation, and thermal treatment for this preparation. However, Zhang et al. 32 used a one-step simple method using KCl and various ferric salts for preparation of porous graphitic carbon from willow catkins biomass. In this method, graphitization and activation were performed simultaneously. Recently, Yang et al.
33
prepared a graphitic mesopore carbon by catalytic carbonization of
sucrose. Agricultural wastes are not only excellent sources of cellulose but also contain silica and other metal oxides as main constituents. Hence, these wastes can possibly be used for silica and silica aerogel preparations
34, 35.
Vaibhav et al.
34
used alkali/acid treatment to
prepare pure nanosilica from rice husk, bamboo leaves, sugarcane bagasse, and groundnut shell. Thermal treatment and hydrothermal activation were used to prepare nanosilica from rice husk
36.
Adebisi et al.
37
reviewed the preparation methods for the synthesis of high-
purity silicon nanoparticle using biomass waste materials. Many other industrial wastes consist of a high percentage of silica, alumina, and other metal oxides in their composition, and they can be used to prepare silica and silica aerogel. Waste silicon sludge, fly ash, coal gangue, red mud, copper slug, and mine wastes are some potential industrial wastes that can be used to prepare silica, alumina, and their aerogels
13, 38, 39, 40.
Figure 5 shows some
preparation methods for extracting silica and alumina from silicon sludge and fly ash.
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Figure 2. Different methods of nanocellulose and aerogel production from agricultural biomass (dp is the particle diameter). Adapted in part with permission from 41, 42, 43. Copyright 2015 IntechOpen, 2014 Elsevier, 2017 The Royal Society of Chemistry. 7 ACS Paragon Plus Environment
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Figure 3. Sequential liquid-lignin recovery and purification (SLPR) process. Reproduced with permission from 44 . Copyright 2018 AIMS Press.
Figure 4. Schematic diagram for preparation of chitin and chitosan from marine wastes. Reprinted with permission from 45. Copyright 2014 Springer.
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Figure 5. extracting SiO2 and alumina from (a) sludge, (b) rice husk and (c) fly ash. Adapted in part with permission from 38, 46, 47. Copyright 2015 Elsevier, 2014 Elsevier, 2013 Longdom. Considering almost same sol-gel and freeze-drying methods for preparation of various aerogels, the emphasis will focus on finding more simple and economic methods for extracting the base componenst from different agricultural /industrial wastes for aerogel’s preparation. Then, finding more green and economic pretreatment methods such as liquid hot water
48, 49
to enhance the extraction of main component from waste biomass is very
important. The potential of combining different approaches such as microwave
50
and
ultrasonic to commonly used pretreatments methods to enhance their performance must consider as well
51, 52.
However, the optimum pretreatment method solely depends on the
nature of waste materials and final required components. 3. Aerogels from Cellulose:
The first report on cellulose aerogels was published in 2001 by Tan, et al.
53.
Cellulose
aerogels are novel green biodegradable nanoporous materials that have attracted extensive 9 ACS Paragon Plus Environment
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interest among scientists. Cellulose, as the precursor for the preparation of aerogels, is the most abundant, sustainable, and environment-friendly biopolymer in nature that is available in many biomass wastes and could be regarded as one of the best precursors for the preparation of carbon-based aerogel due to its low cost, sustainability, and environmentfriendly properties 54, 55. Figure 6 compares the chemical structure of cellulose with chitin and chitosan that differ by the group at position C2. These are the main polysaccharides used for the preparation of aerogels. The prepared cellulose aerogels have unique features and excellent properties, such as low density, high porosity, and high specific surface area with cross-linked 3D network 56, 57.
These features makes these aerogels suitable in the preparation of absorbents
10, 14,
membranes 58, filters 59, templates 60, 61, energy storage devices, biomedicine 62, and insulators 63.
Generally, the cellulous gels are formed through dissolution of cellulose fibers in an
aqueous or organic solvent, followed by its regeneration
64.
Several different crystalline
structures of cellulose are known resulting from the biomass source of cellulose, extraction methods and post-treatment processes. Nanocellulose has a higher degree of crystallinity in comparison with other types of cellulose. According to Takeshi and Yoda 65, nanocellulose can be obtained in two forms of cellulose nanocrystals (CNC) and cellulose nanofibrils (CNF) based on separation method. Nanocellulose, with nanoscale dimensions and unique morphology, has distinctive characteristics, mainly high surface area 66, ultra-lightweight 67, and outstanding mechanical strength
68.
The different morphologies, mechanical and surface properties as well as
hydrophilicity of aerogel compounds are due to the presence of nanocellulose and its derivatives derived from biomass resources
69, 70, 71
which directly relate to the pretreatment
and extraction methods 51, 52, 72 .
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However, the economic barrier of the current nanocellulose extraction methods is the cost of chemical reagents and energy required during the separation processes 30. This issue could be considered determining factor that hinders the development of cellulose aerogels. Hence, overcoming all these technical drawbacks are further emphasized to allow Lignocellulosic biomass to be used as sustainable feedstock for various applications. The performance characteristics of cellulose aerogels are greatly influenced by the biomass source of cellulose 73, 74.
The reason is that physical and chemical properties of cellulose fibers like degree of
polymerization (DP) and degree of crystallinity and extraction process conditions
77.
75, 76
are determined by the types of biomass
Additionally, the drying technology that is used to
produce a particular type of cellulose aerogel greatly influences its morphology i.e. specific surface area and pore size distribution 78, 79. Cellulose has been introduced as a promising raw material for the preparation of aerogel via various methods. The different sources of nanocellulose cotton fibers
12, 89
wood chips
84, 85,
and wheat straw
90.
bagasse
86,
80, 81, 82
mainly include rice straw 83,
paper waste and recycled paper
For example, Lin et al.
89
87,
bamboo leaf
88,
fabricated hydrophobic and flexible
cellulose aerogel from cotton linter and was an efficient, renewable, and reusable oil sorbent. Nguyen et al.
87
prepared aerogels from recycled cellulose fibers obtained from paper waste
with a low thermal conductivity of 0.029–0.032Wm−1K−1. These aerogels, which showed satisfactory heat insulation performance, can be used in medium- and low-temperature heat insulation materials. Furthermore, the homogeneous nanoporous cellulose aerogels were synthesized from waste cotton fabrics 91. The prepared composite aerogel exhibited moderate thermal conductivity of 0.081 W m-1 k-1, indicating the excellent heat-insulating performance 92, 93.
In addition, Shi and coworkers 94 utilized cotton linter in the freeze-drying process. The
fabricated cellulose aerogel exhibited low density of around 0.2-0.4 g cm-3 and a low thermal conductivity of up to 0.029 W m-1 k-1 suitable for insulating materials and heat insulation
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applications. Fan et al.
95
prepared cellulose aerogels from newspaper waste, which, as
municipal solid waste, contains cellulose fibers
96.
The mesoporous cellulose aerogels
showed low density of approximately17.4–28.7 mg cm-3 with oil and organic solvent adsorption capacity. Kenawy et al.
97
fabricated highly porous aerogel from nano-fibrillated
cellulose extracted from rice straw. Jian et al.
98
synthesized cellulose aerogel with 3D
network from wheat straw featured with very low density (approximately 40 mg.cm–3) and large specific surface area (approximately 101 m2.g–1). Moreover, cellulose aerogel was modified using trimethylchlorosilane to improve its absorption capability for oil and dye contaminants. In 2013, Nguyen et al.
99
synthesized hydrophobic cellulose aerogel from
waste paper and modified using methyltrimethoxysilane. Seantier et al. 70 used bleached cellulose fibers and cellulose nanofibers (NFC or CNC) from date palm tree (Phoenix dactylifera L). Aerogels were prepared from cellulose nanofibers and exhibited better-quality properties. NFC aerogels are commonly introduced as thermal superinsulating materials
100.
According to results, cellulose nanoparticles are added to the
cellulose fiber to decrease thermal conductivity as a result of the decrease in pore sizes and pore wall thickness in the resulting aerogels. Cellulose nanofibers are flexible and can create 3D networks even at very low concentrations. Numerous studies have focused on the fabrication of nanofibrous aerogels from cellulosic resources. The sustainable amphiphilic cellulose-based aerogels have shown tunable mechanical strength due to the presence of both hydrophilic hydroxyls and hydrophobic pyranose rings. Table 1 summarizes the latest studies on cellulose aerogels from waste materials.
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Figure 6. The structure of cellulose, chitin and chitosan. Reprinted with permission from 101. Copyright 2017 MDPI AG.
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Table 1.: Overview of studies on cellulose-based aerogels Waste materials
Type of Aerogel
Cellulose aerogel
Cellulose from cotton linter
Potential application
Ref 102
Cellulose oxidation
adsorption and separation of oil as
crosslinking
well as organic solvent
freeze drying
oxidation
CNFs from eucalyptus
Silane-modified CNF
Cellulose oxidation
water treatment & thermal
bleached Kraft pulp
aerogels
crosslinking
insulation
freeze drying
oxidation
Composite hybrid CNF –
freeze drying
Electroactive & supercapacitor
MnOx aerogel
calcination
materials
cellulose / chitosan aerogel
gelation
Adsorption and separation of
freeze-drying
oil/seawater separation
gelation
Adsorption and separation of heavy
freeze drying
metal ions
CNFs from wood flour
cellulose nanofibrils
& chitosan
Preparation process
Waste paper
Cellulose/chitosan
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103
104
105
106
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Wheat straw
Newspaper waste
Waste denim
Waste newspaper
Recycled waste fibers
SnO2–znO - cellulose
NaOH/PEG suspension
photocatalytic degradation of
aerogels
Cellulose hydrogel
rhodamine B
synthesis of SZ@CA
freeze drying
Cellulose composite with
gelation
Adsorption and separation of Congo
Fe3O4 powder
freeze drying
Red
Cellulose aerogel
utilizing ionic liquid solvents through dissolution
Adsorption and separation of oil
108
regeneration
freeze- drying
gelation
Adsorption and separation of organic
95
freeze drying
pollutants
Silylated CNF suspensions
Adsorption and separation of oil
109
freeze-drying 110
Cellulose aerogel
cellulose aerogel
96
Pruning waste of
non-crosslinked and
gelation
Adsorption and separation, heat
blueberry tree
crosslinked cellulose aerogel
Freeze-drying
insulator
Waste box board and
Cellulose aerogel
Gelation
Adsorption and separation of oil
111
freeze drying
silanization
Gelation
Adsorption and separation of organic
112
vacuum freeze drying
pollutants
milk-container Board
107
Paper waste
Cellulose monolite aerogels
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Waste newspaper
Bamboo fibers
Pine needles
Waste paper &
Cellulose aerogel
Cellulose /AlOOH aerogel
cellulose aerogels
Cellulose aerogel
cardboard
Waste cotton fabrics
Wastepaper
Wastepaper
Wheat straw
Wastepaper
Cellulose aerogel
Cellulose aerogel
Cellulose aerogel
Cellulose aerogel
cellulose Aerogel
gelation
Freeze-drying
gelation
Freeze-drying
gelation
Freeze-drying
gelation
Freeze-drying
modification with clay and APP powders
gelation
Freeze-drying
gelation
Freeze-drying
cross-linking
silanization
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Adsorption and separation of oil
113
thermal insulator
24
Adsorption and separation of oil
114
thermal insulator
115
thermal insulator
91
Adsorption and separation of oil
116
gelation
Thermal insulator, Adsorption and
87
Freeze-drying
separation
gelation
Adsorption and separation of oil
117
freeze drying
gelation
crude oil spill cleaning
99
Freeze drying
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Silanization gelation
Seaweeds,
Polysaccharide (cellulose,
wastes of
chitin, chitosan) aerogels
supercritical drying
Cellulose Aerogel
gelation
freeze drying
Catalysis; Adsorption and separation
118
Adsorption and separation
119
the seafood industry
bleached softwood
kraft pulp
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Aerogels from Lignin
Lignin is a natural polymer and a high carbon containing renewable resource with heterogeneous aromatic composition
120.
In plant cell walls, lignin provides regular and
proper connection with other components, especially cellulose 121 . The chemical structure of lignin is not exactly known due to two main reasons. First, the monomers are connected with each other through various inter-unit linkages. Second, lignin is obtained from variety of sources and species. Regardless of the source, all lignins are polymers of 4-hydroxycinnamyl alcohol i.e. pcoumaryl alcohol, its 3-methoxylated derivatives i.e. coniferyl as well as 3,5-methoxylated derivatives that is sinapyl alcohol (Figure 7). Lignin has many covalent bonds in the structure along with some strong noncovalent interactions such as hydrogen bonding that have caused stability and resistivity against degradation and makes the commercial use very difficult
122.
However, the aromatic
structure of lignin and its various chemical functional groups i.e. hydroxyl, methoxyl, carbonyl and carboxyl groups allow it to react with other substances.
Figure 7 : Chemical Structure of monomeric units of lignin. Adapted with permission from 123.
Copyright 2014 Elsevier.
In general, lignin is more normally the massive waste of the pulp and paper industry as well as cellulosic ethanol industry
44
.
It is the main fuel for the energy balance of pulping 18
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process. So one of the major goals in lignin material research is to find high-end uses and high value applications. Regarding their physical and chemical properties, generally, the major difference among types of lignin originates from the pulping process and the minor difference from the plant sources 124 . Kraft lignin is produced from the Kraft pulping process, which produces more than 50 tons per year equals to 85% of world lignin production 122, 125 . However, the utilization of Kraft lignin is limited. Therefore, the aim of researchers is to valorize Kraft lignin to prepare value-added chemicals for large-scale industrial applications 126 . Kraft pulping is characterized by increasing the amount of phenolic hydroxyl group in lignin structure and condensing the structures during the cooking process. Therefore, kraft lignin has high contents of ash and carboxyl group. On the other hand, the lignin obtained from organosolv pulping has high purity with low molecular weight and narrow range of molecular weight distribution. Until now the Kraft process is the leading pulping process all over the world 122 . Lignin-based aerogels are special class of nanostructure materials for the use of lignocellulosics. In the synthesis process, lignin biopolymer with three phenolic monomers is chemically crosslinked to form a 3D network structure gels
127
. Chen et al. (2011)
128
produced a lignin-resorcinol-formaldeyde (LRF) aerogel under supercritical ethanol drying conditions. Grishechko et al. (2013)
129
studied the lignin-phenol-formaldehyde (LPF)
aerogels. Resorcinol has been reported as expensive raw material that contains toxic material. Hence, the use of lignin is considered as an alternative to resorcinol as carbon raw material. In other study
130
synthetic phenol was replaced with tannin that is natural phenolic
compound and further supercritically dried to form aerogels. Tanin can be extracted from leaves of plants, and mainly from wood and bark of several trees
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131
. The goal of the work
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was to replace toxic compounds such as phenol and resorcinol with the natural phenolic compounds for the sustainable production of advanced materials. The problem was that the aforementioned aerogels have fragile structures. Thereby, researchers 132 used bacterial celulose (BC) to toughen the LRF aerogel. Wang et al. (2016) 133
developed lignin aerogels of nanocellulose which acts as an adhesion agent.
Moreover, Quraishi et al. (2015)
60
developed alginate-lignin aerogels that were bioactive
and featured good as scafolds for tissue engineering and regenerative medicine (TERM) 134 . Lignin has outstanding characteristics including ecofriendly nature, availability, low cost, biodegradability and biological effect as well as its reinforcement effect in composite’s structure that has made it an ideal candidate for variety of applications especially in polymer matrices for high performance composites as well as food and other industrial applications 135, 136
. Table 3 presents the studies conducted on preparation of aerogels from Lignin.
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Table 2: Overview of studies on Lignin-based aerogels Waste materials
Type of Aerogel
enzymatically isolated
Lignin-Resorcinol-
lignin
Formaldehyde copolymer aerogel
lignin-derived carbon
Graphene/Lignin- aerogel
(LDC)
Preparation process
polycondensation of resorcinol with
Potential application
Ref
Thermal insulator
128
formaldehyde and ignin
gelation
supercritical ethanol drying
Graphene-oxide / lignin water suspension
Ultrahigh Electromagnetic
freeze drying to form foams
Interference Shielding
137
Performance
alginate–lignin hybrid
lignin, Na-alginate & CaCO3 suspension
scaffolds for
aerogels
CO2 induced gelation
tissue engineering & regenerative
supercritical drying
medicine
lignin-tanin-formaldehyde solution
biomedical and
softwood black liquor &
hydrogel formation
environmental applications.
Tanin from barks of
solvent exchange
wattle trees
supercritical drying
lignin from wheat straw
kraft lignin from
Tannin-lignin aerogels
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60
130
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kraft lignin from
Lignin–phenol–
softwood black liquor
formaldehyde aerogels
lignin from crop wastes
kraft and organosolv
Lignin-based aerogels
lignin-based aerogels
sol-gel polymerization of lignin and phenol with
Page 22 of 80
Thermal insulation
129
138
formaldehyde
solvent exchange
supercritical drying
sol-gel polymerization of lignin and resorcinol
carbon electrodes for
with formaldehyde
supercapacitors
solvent exchange
ambient drying process
pyrolysis up to 1050 C
sol-gel polycondensation of lignin with
lignins
formaldehyde
solvent exchange
freeze drying
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supercapacitors
139
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alkali lignin (MW 10000)
wheat straw lignin
Wheat Straw lignin (AS
BC-LRF aerogel
Lignin aerogel
Lignin aerogel
lignin)
Hardwood lignin from beech chips
Lignin aerogel
lignin-resorcinol-formaldeyde (LRF) gel
oil/water separation,
impregnated BC gel with LRF gel by sonication
supercapacitors and sensors
CO2 supercritical drying
lignin crosslinking & gelation
solvent exchange
supercritical drying of lignin gels
Fenton‐type pre‐activation of lignin
crosslinking of oxidized lignin
solvent exchange
supercritical CO2 drying in N2
Fenton‐type pre‐activation of lignin
crosslinking of oxidized lignin
solvent exchange
supercritical CO2 drying in N2
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132
Thermal insulator
127
Electrochemical applications
140
Electrochemical applications
140
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softwood lignin from
Fenton‐type pre‐activation of lignin
crosslinking of oxidized lignin
solvent exchange
supercritical CO2 drying in N2
Lignin – graphene oxide
catalytic graphitization of kraft lignin
(LGO) – CNF aerogel
oxidation of lignin graphene oxide
reduced lignin graphene oxide
assembly of LGO & CNF
freeze drying
Lignin aerogel
pine kraft lignin
kraft lignin
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Electrochemical applications
140
Water resistance, thermal stability
141
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5. Aerogels from Chitin and Chitosan: 5.1.
Chitin:
Chitin -based aerogels fabricated from abundant natural macromolecules of chitin as raw material, have been widely studied. Next to cellulose, chitin is the most abundant (1011 tons produced annually) renewable biopolymers on earth
142.
In fact, the major material obtained
from marine biomass is the biopolymer chitin with molecular structure consisting of β-(1,4)linked linear chains of N-acetyl-d-glucosamine. Isolated chitin chains have different degrees of acetylation depending on their sources of origin and process of extraction
143.
Chitin is
converted to chitosan through different degrees of deacetylation. The utilization of chitin in aerogel preparation has attracted interest because of its low cost, abundancy of waste material resources, and significant characteristic properties, such as biocompatibility, non-toxicity, as well as thermal and chemical stability. Different size distributions of chitin ( nanocrystals ChNCs and nanofibers ChNFs ) can be generated from the same resource while they can been utilized as raw materials for aerogel preparation 4. Chitin nanofibers and nanocrystals, as renewable resources with unique structures and properties, can be isolated from the shells of crustaceans, i.e., crab, shrimp, and lobster, and in fish waste via different methods 6. It is also found in fungi, insects (ants), annelids, cephalopods (squid and octopus), and so on. However, the most common industrial renewable resource for chitin is mainly seafood-processing residues, i.e., crab and shrimp shells
5, 7, 8, 16, 53.
According to reports, an enormous quantity of crustacean shell wastes
(approximately more than 6 mega tons) are produced every year 33. Disposal of these wastes has been a real challenge for industry; hence, production of chitin, chitosan and their derivatives for utilization in various value-added industrial platforms has extreme importance. It should be mentioned that extraction process and treatment conditions would extremely influence on morphological appearance and physicochemical characteristic of resulting chitin. Development of profitable technology for extraction of chitin and its derivatives is of great interest among academic and industries 144. Several publications have reported the production of chitin aerogels and their potential applications in different areas. For example, Tsutsumi and coworkers
56
prepared highly
porous aerogels with high specific surface area (up to 289 m2 g–1) from squid pen chitin nanofibrils through freeze-drying process. The numbers of recent publications on the fabrication of chitin aerogels are presented in Table 3.
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5.2.
Page 26 of 80
Chitosan:
Nevertheless, extensive removal of acetyl groups of chitin produces chitosan that is a natural polyamine. Chitosan is a biocompatible polycationic biopolymer obtained via alkaline deacetylation of chitin. It is a long-chain copolymer of β-(1→4)-linked 2-acetamido-2-deoxyβ-D-glucose units with acetamide groups in the C2 position. The source of origin, variables of deacetylation process and purification conditions can influence the characteristics of final product, resulting in chitosan molecules with different chemical and physical qualities 145. The physicochemical properties of chitosan are characterized by its deacetylation degree and molecular weight. Among many characteristics, the degree of deacetylation, which defines the content of free amino groups in the polysaccharides, is one of the more important chemical characteristics, which influences the performance of chitosan in many of its applications
146, 147.
During deacetylation process, acetyl groups of chitin are replaced with
amino groups. The chemical structures of chitin and chitosan were compared with that of the cellulose in Figure 6. Given its mechanical and structural properties, chitosan has gained interest as a polysaccharide for synthesis of different types of nanostructured porous materials in different fields. The main characteristic of chitosan -based aerogel is its highly porous structure with extended surface area. The presence of amino groups allows chitosan to react easily with electrophilic reagents like aldehydes and acids. chitosan has many distinctive physicochemical and biological properties, such as the formation of gels with polyanions 3. Fabricating chitosan aerogels could improve the availability of chitosan functional groups for chemical reactions. For example, Ricci et al.
148
successfully prepared chitosan aerogel
microspheres from marine crustaceans with high surface areas of up to 350 m2g-1 and were applied as catalysts in asymmetric aldol reactions. Similarly, Quignard and his coworkers
12
used squid pen and crab shell chitosan with high degrees of amine groups to prepare chitosan aerogel particles, which demonstrated highly porous and fibrous microstructures. This was followed by thermal decomposition of aerogel into N-doped carbonaceous /carbon aerogels /equivalent. However, chitosan has some weaknesses that limit its applications. These mainly include weak chemical stability, poor mechanical strength, low surface area, and dissolution only in acidic solution
87;
chitosan is insoluble in many solvents. Numerous chitosan modification
methods were found to be effective and harmless to the environment and which improved the 26 ACS Paragon Plus Environment
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Industrial & Engineering Chemistry Research
inherent properties of chitosan. Two biopolymer functional groups are responsible for the different chemical modifications, resulting in materials with more desirable characteristics. Chemical modifications of chitosan, typically either at the amino group (the secondary C2 NH2 group) or the hydroxyl group (the primary C6 OH and secondary C3 OH groups), aim to produce derivatives with enhanced properties to widen its applications. These derivatives are considerably easier to fabricate into aerogels because they are water or acid soluble 149. One physical method for improving the mechanical strength of chitosan aerogels involves blending of cellulose nanofibers into a biopolymer matrix. This method resulted in greater mechanical strength and thermal insulation, along with higher adsorption capacity of composites. Cellulose and chitosan are abundant natural, renewable, biocompatible, and biodegradable polymers. Zhang et al.
105
prepared reinforced nanofibrilated cellulose
composite aerogels by integrating NFC into chitosan matrix via the freeze-drying method. chitosan –cellulose composite aerogels have also presented improved adsorption ability
88.
Moreover, organic–inorganic hybrid aerogels are another group of aerogels with improved thermal characteristics 88, 89, 150. Ebisike and his coworkers 86 prepared chitosan –silica hybrid aerogels from the biomass waste of crab shell and bamboo leaves to fabricate chitosan –silica hybrid aerogel [(chitosan) hA]. CS biopolymer was hybridized with varieties of inorganic compounds, such as silica 85 and chondroitin sulfate (ChS) 82. Various applications, such as adsorption 94, catalysts 77, 80, biosensors 81, tissue engineering 82, 151,
and controlled release of bioactive molecules 6, have been reported for chitosan aerogels.
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Table 3.: Overview of studies on chitin and chitosan-based aerogels Waste materials
Aerogel
Preparation process
Potential application
Ref
crab shell
Chitosan / silica hybrid aerogel
sol-gel method by combining an inorganic network
Adsorption & separation of Cd2+ &
85
bamboo leaves
in the presence of an organic polymer
heavy metal
Chitosan
Prawn chitin nanofiber
wood cellulose nanofiber
Chitosan
Ultrapure chitosan
Chitosan /graphene oxide aerogel
Chitin nanofibril aerogel
Cu-chitosan aerogel
Chitosan/ chondroitin sulfate (chs)
Chitosan
chitosan aerogels
gelation
crosslinking
freeze drying
aq. suspension
solvent exchange
freeze drying
gelation
supercritical CO2 drying
gelation
freeze drying
gelation
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adsorption of CO2 molecules
150
Catalysis
57
Heterogeneous Catalyst
80
wound healing
82
nanomedicine applications
83
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Chitosan and cellulose from cotton
chitosan/oxidized cellulose
linter
aerogel
wastepaper & chitosan
Chitosan & Nanofibrillated
Wastepaper/chitosan aerogel
chitosan/ cellulose aerogel
cellulose
Chitosan
chitosan aerogel modified with Au+2
Chitosan & medical adsorbent
Chitosan/cellulose aerogel
cotton
Chitosan from crab & shell
Chitosan/silica hybrid aerogel
supercritical CO2 drying
Cellulose hydrogel formation
cellulose hydrogel oxidation
Schiff base reaction of hydrogel and chitosan
freeze drying
Modification
Wastepaper/chitosan hydrogel formation
freeze drying
gelation
freeze drying
Wet gel preparation
freeze drying
gelation
freeze drying
gelation
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Adsorption & separation of oil
102
Adsorption & separation of cu+2 &
106
heavy metals
Adsorption & separation of oil
105
Catalysis
68
Adsorption & separation of Congo
88
Red (CR)
thermal insulators, catalysis and
86
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silica from bamboo leaves
Chitin from carapace powders
Nanofibrillated chitin/Ag2O aerogel
partially deacetylated α-chitin
α-chitin nanofiber/nanowhisker
nanofiber/nanowhisker (DEChN)
(DEChN) aerogels
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ambient pressure drying
biomedical materials
gelation
Adsorption & separation of
Freeze drying
58
radioiodine anions
Alkali deacetylation
solvent exchange
freeze drying
Hydrothermal gelation of chitin aqueous
Biomedicine, photocatalysis, gas
suspensions
sensing
thermal insulators, catalysis and
59
biomedical materials
from Crab shell from food waste (Nantong, China)
chitin nanocrystals from dried
Chitin aerogel
crab shells
Chitin from shrimp shells
CNFs from corn husks and
CNCs from shrimp shells
Chitosan powder
freeze drying
chitin nanowhisker aerogel
surface modification of chitin nanowhiskers
chitin nanowhisker/ carbon
CNC3 & CNT hybrid aerogel
freeze drying
nanotubes hybrid aerogel
Chitin/cellulose hybrid aerogel
translucent and ultralight
gelation
Freeze drying
gelation through cross-linking with
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thermal insulators, catalysis and
60
152
biomedical materials
anti-bacterial and anti-oxidant
61
thermal insulators
63
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Chitosan aerogel
formaldehyde
Chitosan powder
chitosan/carbon nanotubes aerogel
α-chitin powder
Chitosan powder
α-chitin aerogel
translucent and ultralight
supercritical CO2 drying
CNTs & CS aq. Suspension
Crosslinking
Freeze-drying
gelation with ethanol
supercritical CO2 drying
gelation through cross-linking with
Chitosan powder
fiber reinforced silica / chitosan nanocomposite aerogel
Chitosan powder
Chitosan–silica composite aerogels
81
adsorption & energy materials
catalyst supports, biomedical
2
materials
thermal insulators
65
formaldehyde
chitosan aerogel in the visible region
sensors, medical restorative,
supercritical CO2 drying
gelation of sodium silicate & chitosan
supercritical drying
gelation
supercritical CO2 drying
thermal insulation, sorption, catalysis
Adsorption & separation of Congo
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red
153
67
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Chitosan
Bamboo powder
chitosan aerogel beads supported by microfibrilated cellulose
agarose from red seaweed &
chitosan powder
Chitin nanofibers from squid-pen
Gelation through ball dropping method
freeze drying
Chitosan/agarose composite aerogel
Chitin aerogel
(Sepioteuthis lessoniana)
Chitosan from shrimp
hybrid monolith aerogel of chitosan (CTS) - Graphene Oxide
Chitin powder
Chitosan
Chitin nanofiber aerogels
Chitosan / montmorillonite hybrid
cross-linked gel formation
Freeze drying
Gelation
freeze drying
Gelation
freeze drying
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Adsorption & separation of
89
formaldehyde in indoor air
Adsorption & separation of oil
154
catalysis of aqueous Knoevenagel
56
condensation reaction
Adsorption & separation of CO2
65
aqueous NaOH–urea suspension
biomaterials,
155
gelation from ethanol
heat or sound insulators, catalysis
supercritical CO2 drying
gelation of an intercalated “chitosan–
Adsorption & separation of
montmorillonite” solution,
methylene blue
aerogel microspheres
super-critical CO2 drying
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156
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chitosan (79% DD) from India
Chitosan Aerogel
Sea Food Products
Chitosan nanofibers from
Chitosan aerogel
crustaceans
α-chitin from crab shell
β-chitin from squid pen
Chitosan
Chitosan aerogel
chitosan aerogel
gelation
supercritical CO2 drying
gelation
supercritical CO2 drying
gelation
supercritical CO2 drying
gelation
crosslinking
biomedical
66
Heterogeneous Catalyst
148
Catalysis
12
adsorption & separation of anionic
157
surfactant sodium dodecylbenzenesulfonate (SDBS)
Chitosan from squid pen
Chitosan aerogel
Supercritical CO2 fluid extraction.
Wet gel formation,
freeze drying
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catalysis or adsorption & separation
158
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6. Aerogels from Pectin: Pectin is a linear polysaccharide found as a primary constituent of plant cell walls and is responsible for the rigidity and cohesion between cells. It is an abundant and inexpensive commercial product, and its chemical structure is composed of linear polymers of galacturonic acid linked by 1,4 glycosidic bonds. Carboxylic acid functional groups are found in galacturonic acid chains that are partially esterified on the C6 position using methanol. The percentage of methyl-esterified groups in the pectin chain is referred to as degree of methylation or degree of esterification (Figure 8).
Figure 8: Chemical structure of pectin molecule. Reprinted with permission from 159. Copyright 2010 MDPI AG.
Pectin is a major industrial waste biomass polysaccharide that is mainly obtained from fruit juice industries as abundant, inexpensive, and high-volume commercial waste product. The main sources are apple pomace and citrus peel because of their abundance and rich protopectin content. Pectin has the ability to form gels, and pectin aerogels are excellent thermal-insulating compounds that are commonly fabricated through dissolution–gelation– coagulation process, followed by supercritical drying. Thermal conductivity increases with increasing pectin concentrations. According to reports
160, 161,
the obtained thermal
conductivity values are in the range of 0.016–0.020 W m−1K−1. Moreover, pectin aerogels have been reported to have considerable mechanical strength. The first pectin aerogel or 34 ACS Paragon Plus Environment
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aeropectin preparation has been reported by White and his coworkers
162.
The pectin
extracted from citrus peel was fabricated through thermal gelation of pectin solution, dissolving in acidic solution, solvent exchange with ethanol, and finally drying with supercritical CO2. The recent reports on the preparation of pectin-based aerogels are summarized in Table 4
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Table 4.: Overview of studies on Pectin-based aerogels Waste materials
Aerogel
Preparation process
Potential application
Ref
magnetic pectin aerogel
Gelation
magnetic targeting drug delivery vehicles
163
supercritical CO2 drying
aq. suspension,
chromatography, heterogeneous catalysis
164
freeze drying
and large molecule adsorption
Polymerization,
thermal insulator
Coagulation,
supercritical CO2 drying
gelation,
freeze-drying
modification with nanoclay
pectin from apple–citrus and citrus peel
Pectin (from citrus fruit peel)
Apple pomace Pectin
Pectin from citrus
Pectin from citrus peel
Pectin from apple pomace
High methoxyl pectin
Pectin aerogel
Polyaniline/Pectin Aerogels
Pectin/Clay Aerogels
Monolithic pectin aerogel
methoxyl pectin–xanthan aerogel
62
165
Dissolution
thermal
gelation
super insulator
coagulation
supercritical CO2 drying
ethanol-induced gelation
coating on medical-grade
Supercritical CO2 drying
stainless steel
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160
166
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High-methoxyl (Pectin)
Dissolution in water,
gelation of pectin in ethanol
supercritical CO2 drying
Dissolution in water
Solvent Exchange
supercritical CO2 drying
pectin-TiO2 nanocomposite
aerogels
Pectin aerogel
and low-methoxyl
Citrus pectin
Amidated pectin
Pectin Aerogel
Thermal insulator
161
Thermal insulator
167
Gelation
potential
168
supercritical CO2 drying
insulated food packaging porous carriers in oral drug delivery
169
packaging and insulation materials
170
low-methoxyl citrus
amidated low-methoxyl apple (AF)
cationic gelation
apple pectins
and citrus (CF) pectin aerogels
supercritical CO2 drying
Pectin from apples
Pectin/ Boron nitride nanosheets
Gelation
(BNNSs) aerogel
freeze-drying
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7. Carbon Aerogels: After the initial synthesis of carbon aerogels
171,
the field largely became popular. This
exceptional class of materials, with its high surface area, electrical conductivity, chemical inertness, and compatibility with the environment makes it suitable for energy storage, absorbent, supercapacitors, and catalysts. Carbon-based aerogels are unique carbonaceous materials with unique high-surface-area. They are prepared through hydrothermal carbonization of carbonaceous precursor; this is a method wherein hydrothermal treatment process is followed by pyrolysis of biomass carbon in the presence of N2 or Ar at temperatures above 600 °C to obtain extremely pure carbon structure
25.
Sol–gel and
pyrolysis are common methods for preparing carbon aerogel. Chandrasekaran et al.
172
reviewed many carbon-based aerogel preparation methods, such as inkjet and 3D printing, which make them an attractively growing field for study and various applications. Despite the synthesis of carbon nanotube aerogel in the last decade using surfactants and via freeze drying and critical point drying 173, its preparation is regarded as very challenging. Although carbon is the main element in all agricultural, plastics and other biobased waste materials, mostly its proper extraction isn’t easy and economical, and more research must be conducted in this field. This material has become even more attractive due to its unique thermomechanical and electrical properties. Their unique characteristics, such as biodegradability, environmental compatibility, and high surface area, have made them special porous materials for applications such as adsorption
155,
environmental desalination
174,
and energy storage
62.
While common adsorbents, such as activated carbon, have sorption capacity less than 100 g. g-1, carbon aerogels, as important solid adsorbents, have shown unique adsorption capacity of up to 900 g. g-1 20, 175, 176. Their hydrophobic surfaces allow selective and effective adsorption of oils, organic pollutants, and heavy metals from wastewater
106.
Moreover, their unique
electrical conductivity is beneficial in electrical/electrochemical applications, such as super capacitors 177, electrocatalysis and electrosensing 178, as well as batteries 104. Since the sol-gel reaction chemistry control the morphology and properties of carbon aerogels, aerogels with specified applications and properties could develop considering sol-gel precursors, polymerization catalyst and reaction solvent (Figure 9)
179.
As shown, the Carbon aerogel
(CA) structure can be modified either during the sol–gel polymerization step, through the introduction of additives or templates to the reaction mixture, or through gas- or solutionphase reactions on the surfaces of the CA framework after the pyrolysis step. 38 ACS Paragon Plus Environment
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Figure 9. Synthetic scheme showing the versatility associated with carbon aerogel synthesis. (Reprinted with permission from ref. 179. Copyright 2011 Royal Society of Chemistry.) Using carbon allotropes, various carbon-based aerogel with different properties could be developed. Traditional carbon aerogel consists of 3D network of interconnected amorphous carbon
163, 172.
Chandrasekaran et al.
172
reviewed many carbon-based aerogel preparation
methods, such as inkjet and 3D printing, which make them an attractively growing field for study and various applications. The most common carbon-based aerogels that have been introduced as novel porous materials are carbon nanotube (CNT) 173, 180, graphene 181, 182, and carbon nanofiber aerogels
183.
Moreover, various types of carbonaceous wastes have been
used as raw materials to prepare carbon-based functional materials due to their carbon richness, low cost, and natural abundance. They mainly consist of abundant agricultural byproducts e.g., grass, leaves, rice husks and straws, coconut coirs, and shells, as well as municipal solid wastes, such as waste paper and newspaper. The second group is non-
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degradable municipal and industrial wastes, including different industrial polymeric products, such as plastic bottles, plastic bags, and industrial wastewaters. Graphene 184, 185, 186 and graphite aerogels are other carbon-based aerogels that are of interest to researchers due to their attractive properties. However, only limited studies have been published on the syntheses of CNT and grapheme aerogels materials. For example, Wang and his coworkers
188
187
from carbonaceous waste raw
prepared grapheme aerogels using
cigarette filters. The fabricated composite aerogels area ultralight (ρ=7.6 mg cm-3) and have high mechanical strength (0.07 MPa), and they are used as electromagnetic wave absorbers. Nevertheless, plenty of reports have utilized natural biofibers, mostly cellulose nanofibers, as starting materials for the preparation of emerging carbon nanofiber aerogels
189.
Cellulose
aerogels, with cross-linked 3D network, could be pyrolyzed into carbon aerogels to make composites
43, 190.
Cellulose-nanofiber aerogels have been used as the main source for novel
carbon aerogels produced via pyrolysis. Carbon nanofiber aerogels can be derived from several sources, mainly nanocelluloses and nanochitins, as the most abundant biopolymer nanofibril
97.
In fact, cellulose fiber has been introduced as precursor for the preparation of
porous cellulose aerogels, making it a special candidate for carbon aerogel preparation For example, low-cost and abundant bamboo pulp fibers
192
191.
were used as promising
precursors for the preparation of a novel lightweight carbon aerogel (5.65 mg cm-3) with excellent mechanical property, high hydrophobicity, and large specific surface area (379.39 m2g-1). Moreover, its excellent absorption behavior allows it to be used in future water treatment applications. In another case, waste paper or cotton, as raw material, was used to fabricate sponge-like hydrophobic and porous carbon microbelt aerogels and carbon fiber aerogels via a facile route
193.
Waste newspaper is extensively used as raw material for
fabricating carbon-based aerogel. Bi and coworkers (2013) 20 used twisted carbon fibers from cotton fibers and carbon microbelts from waste paper to produce porous and hydrophobic aerogels to adsorb a variety of organic solvents and oils in water purification systems. The latest publications on carbon aerogels from waste materials are listed in Table 5.
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Table 5.: Overview of studies on Carbon-based aerogels Waste materials
Bagasse from sugarcanes
Type of Aerogel Carbon aerogel
lignin-derived carbon
Graphene/Lignin-
(LDC)
Derived Carbon aerogel
Preparation process
Potential Application
Ref
supercapacitor electrode
178
Gelation
Freeze-drying
Carbonization
chemical activation
Graphene-oxide / lignin water
Ultrahigh Electromagnetic
suspension
Interference Shielding
freeze drying to form foams
carbonization at 900 C at Ar
137
Performance
alkali lignin (MW
BC-LRF carbon
lignin-resorcinol-formaldeyde (LRF) gel
oil/water separation,
10000)
aerogel
impregnated BC gel with LRF gel by
supercapacitors and sensors
132
sonication
CO2 supercritical drying
kraft and organosolv
lignin-based carbon aerogels
Carbonization
sol-gel polycondensation of lignin with formaldehyde
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supercapacitors
139
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lignins
lignin from crop wastes
Lignin-based carbon
solvent exchange
freeze drying
carbonization at 1100 ̊C T N2
sol-gel polymerization of lignin and resorcinol
carbon electrodes for
with formaldehyde
supercapacitors
aerogels
Wheat Straw lignin (AS
Lignin carbogel
lignin)
Hardwood lignin from beech chips
Lignin carbogel
Page 42 of 80
solvent exchange
ambient drying process
pyrolysis up to 1050 C
Fenton‐type pre‐activation of lignin
crosslinking of oxidized lignin
solvent exchange
supercritical CO2 drying in N2
carbonization
Fenton‐type pre‐activation of lignin
crosslinking of oxidized lignin
solvent exchange
supercritical CO2 drying in N2
carbonization
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138
Electrochemical applications
140
Electrochemical applications
140
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Fenton‐type pre‐activation of lignin
from pine kraft
crosslinking of oxidized lignin
lignin
solvent exchange
supercritical CO2 drying in N2
carbonization
softwood lignin
Lignin carbogel
Waste newspaper
Waste pomelo peels
Cellulose from cotton linter
Carbon aerogel
Carbon aerogel
Cellulose/carbon aerogels
Gelation
Freeze drying
pyrolysis
hydrothermal carbonization
freeze-drying
pyrolysis
Gelation
Carbonization
activation
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Electrochemical applications
140
Adsorption & separation of oil
54
Adsorption & separation of oil
194
Adsorption & separation of CO2
195
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eggplant
Animal skin waste
Carbon aerogel
Collagen-polypyrrole hybrid
Gelation
Freeze drying
Carbonization & post-pyrolysis
In situ oxidative polymerization
gelation
Freeze drying
air-limited calcination method
NaOH/urea aqueous solutions
freeze drying
carbonization
Activation
gelation
freeze-drying
pyrolysis
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Adsorption & separation of oils and
195
organic solvents
Biosensor, tissue engineering
196
Adsorption & separation of methylene
197
aerogels
Cotton fibers
bamboo cellulose fibers
Waste durian shell
carbon aerogel
carbon aerogel
Carbon aerogel
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blue (MB)
supercapacitor electrodes
Adsorption & separation of organic solvents /oil
148
163
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Wood-derived nanofibers
Ultrathin Carbon nanofiber
gelation
aerogel
Supercritical CO2 drying
pyrolysis
supercapacitor electrodes
164
Adsorption & separation of dye
62
Adsorption & separation of oil and
165
under flowing inert
gas
Nitrogen-enriched
chitin powder
carbon
nanofiber aerogels
Nitrogen-doped
Waste cabbage leaves
carbon aerogels
typha
orientalis
cellulose
Carbon aerogel
fibers
porous
gelation
Supercritical CO2 drying
Carbonization
Hydrothermal gelation
freeze-drying
carbonization
gelation
Supercritical CO2 drying
Carbonization
organic solvents
Adsorption & separation of colored
198
diesel
under N2 atmosphere
Plastic waste PET, HDPE, LDPE, waste
municipal
Polymeric aerogel
solid
mixed with Xylene and antioxidant
precipitation,
freeze-drying
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Adsorption & separation of oil
166
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Sisal leaves
Carbon
Aerogel/TiO2
Nanorods
gelation
freeze-drying
carbonization
Bamboo cellulose
cellulose nanofibers
CNF gels
nanofibers
(CNFs)/multi-walled
freeze-drying
carbon nanotubes
CNF aerogels dipped in
(MWCNTs) carbon aerogels
carbonization
banana peel
banana peel/wastepaper
gelation
wastepaper
(BPWP) hybrid aerogel
freeze-drying
carbonization
In-situ oxidation
Cattail biomass
Carbon aerogel
Adsorption & separation of oil
199
Adsorption & separation of oil
200
energy storage, sensors and pressure-
169
MWCNT solution
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sensitive electronics.
Supercapacitor
170
Adsorption & separation of oil &
167
polymerization method
leaves of Premna
carbon@SiO2@MnO2
gelation
microphylla (PM)
aerogel
freeze-drying
carbonization in N2 atmosphere
self-templated N-doped
gelation
carbon aerogel
freeze-drying,
carbonization in
Sisal leaves
Banana
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organic solvents
supercapacitors
201
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argon (Ar) atmosphere,
watermelon
activation by CO2
magnetite carbon aerogels (MCAs)
bleached softwood kraft
Carbon aerogel
pulp (BSKP)
puffed rice Popcorn
Natural apple pectin
premna microphylla leaves
Magnetic carbon aerogel
Carbon aerogel
Carbon aerogel
gelation freeze drying incorporating Fe3O4 nanoparticles into the networks calcination
NaOH/urea/H2O suspension
vacuum freeze-drying
carbonization
gelation
freeze-drying
carbonization
magnetization of popecorn
surface modification
Wet gel formation
ambient pressure drying
carbonization
activation
gelation
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Supercapacitors
Adsorption & separation of oil &
202
203
organic solvents
selective Adsorption & separation of
158
oil & organic solvents
Adsorption & separation of
204
pharmaceutical contaminants
Adsorption & separation
205
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sisal fiber
biomass of apples (Malus
carbons aerogels
pumila Mill)
Waste newspaper
Bamboo pulp fibers
Waste cabbage
Carbon aerogel
Carbon aerogel
Nitrogen-doped
carbon
aerogel
cotton
Carbon fiber aerogel
freeze-drying
carbonization
gelation
freeze-drying
carbonization
gelation
freeze-drying
post-pyrolysis
gelation
freeze-drying
post-pyrolysis
Hydrothermal gelation
freeze-drying
carbonization
cotton calcination in air-limited
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electrochemical sensing
206
Adsorption & separation of organic
54
solvents
Adsorption & separation of Oil
192
Adsorption & separation of Oil;
207
supercapacitor
Adsorption & separation of dye
197
Adsorption & separation of Oils &
176
atmosphere
Wastepaper
Carbon Microbelt Aerogel
gelation
freeze-drying
pyrolysis
Organic Solvents under
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argon
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Industrial & Engineering Chemistry Research
atmosphere
waste of shaddock (Citrus
carbon
maxima) peels
(CNANAs)
Cigarette filters
nanoballs
aerogels
graphene aerogels
gelation
freeze-drying
carbonization
carbonization
of
celluloses
electrocatalysis and electro sensing
108
electromagnetic wave absorption
188
Adsorption & separation of oil
162
Lithium Ion Storage
208
Supercapacitor electrode
206
fibers into CFs
Chitosan
reduction of GO into grapheme
graphene
carbonization of fibers
oxide/polydopamine
reduction of GO into graphene
gelation
freeze-drying
carbonization
gelation
freeze-drying
carbonization
activation
composite aerogel reinforced by chitosan
Waste seaweed
Nano
Fe2O3
/
/N-doped
graphene aerogel
chitosan
Graphene-based
nitrogen
self-doped carbon aerogels
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8. Aerogel from Silica: Silica aerogels
209
with nanosized, open foam-like structures exhibit extremely low density
(containing up to 95% air in their volume), high specific area, high porosity, low thermal conductivity, and optical transparency, rendering them very attractive for a multitude of technological applications 210, 211. The capability to control the polarity of the surface between hydrophilic and hydrophobic properties, as well as excellent access option to its inner surface due to the open porous network, result in exceptional physico-chemical properties, rendering them suitable for thermal insulators, catalysts, adsorbents, and drug delivery 211. In nature, silica exists as sand, glass, quartz, and so on. Naturally occurring silica has crystalline structure, while synthetic silica, which is usually obtained from silicate solution, has amorphous structure 174. Silica aerogel is commonly produced using expensive and toxic precursors, such as tetramethoxysilane [Si(OCH3)4, TMOS] and tetraethoxysilane [Si(OC2H5)4, TEOS] 189. However, industrial and agricultural wastes containing silica in their respective compositions can be used as precursors for the preparation of silica-based aerogels. As an example, rice husk
212
has been abundantly reported to be one of the potential bioresources of silica.
According to literatures, rice husk ash, which is obtained from agricultural wastes and residues and is abundantly produced in the rice industry, consists of 92% amorphous pure silica. The composition of rice husk as an organic biomass consists of silica, lignin, cellulose, and hemicelluloses
175.
After burning the husk under controlled combustion, rice husk ash,
which contains approximately 90% to 98% silica, and some amount of metallic impurities are generated
176, 177
Utilization of these agricultural wastes could considerably reduce the high
cost of disposal and environmental problems because the extraction process of silica is cost effective. Rice husk is an abundant recyclable waste product, and its ash contains considerable levels of high-quality silica. Most importantly, pure silica obtained from rice
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husk ash exists in an amorphous state with high surface area applications of silica aerogels include drug delivery systems
Page 52 of 80
178. 213,
The common practical adsorbent for pollution
treatment 214, and filler material for thermal management solution 212. Numerous reports have been made on silica aerogels prepared from rice husk ash
181.
For
example, silica was extracted from rice husk ash to prepare SiO2 aerogel via sol–gel process and supercritical drying of ethanol
215.
Likewise, Kumar and his coworkers
213
prepared
biocompatible silica aerogel microparticles from rice husk ash as promising drug delivery vehicles because of their large surface area and open pore structures. They used water-inmineral oil emulsion for sol–gel preparation, followed by supper critical drying with CO2. Other examples on the utilization of rice husk ash as silica resource for aerogel preparation are listed in Table 6. Other reports have proven that rice hull 216, wheat husk 17, and Bagasse 217
from agricultural wastes can be used for the production of silica aerogels. Considering of
using other resulted byproduct such as lignin, cellulose and hemicellulose during extraction and purification of silica from waste biomass as co product for different application could add more value for its commercialization. These silica aerogels have also been prepared from industrial wastes, mostly gold mine wastes and coal gangue. Details of these reports are explained in Table 6.
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Industrial & Engineering Chemistry Research
Table 6.: Overview of studies on Silica-based aerogels Waste precursor
Type of Aerogel
Preparation method
Application
Ref
Silica aerogel
gelation
Thermal insulator in cement-based
142
solvent exchange
mortar
drying at ambient pressure
gelation
solvent exchange
surface modification
ambient pressure drying
Water glass preparation
gelation
solvent exchange
ambient pressure drying
Rice husks
Rice husk
Rice husk
Rice husk
Rice husk from Mazandaran
Silica aerogel
silica aerogel
γ-Fe2O3/ SiO2 aerogel
Silica microspheres
lands
Rice Husk
Silica aerogel
thermal insulator
151
thermal insulator
218
Gelation
photoFenton- like degradation of
214
drying at 60oC
rhodamine B (RhB)
Silica gel formation
HPLC stationary phase
180
calcination at 550 oC
sol-gel method
thermal insulation,
212
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Rice husk
Rice husk
silica aerogel beads
silica aerogel
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solvent exchange
chemical sensors, and energy storage
surface modification
devices
ambient pressure drying
ball dropping method
Adsorption and separation of oil; filler
surface modification (silylation)
material for thermal insulation
ambient pressure drying
Silica aerogel nanoparticles incorporated
219, 220
Microwave and RF application
221
drug delivery
213
55
into poly(butylene succinate)
Rice husk
Rice husk
Bagasse
Fly ash
silica aerogel
gelation
microparticles
supercritical CO2 drying
TEOS-doped silica
gelation
thermal insulation, catalysis, acoustic
aerogel
atmospheric pressure drying
delay, drug delivery
Silica aerogel
gelation
thermal insulation, catalysis, acoustic
ambient pressure drying
delay, drug delivery
Silica aq. gel
thermal insulation, catalysis, acoustic
surface modification
delay, drug delivery
ambient pressure drying
Silica aerogel
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222
223
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Bagasse
Wheat husk
Gold mine waste
Coal gangue
Coal gangue
Coal gangue
Coal gangue
Silica aerogels
Silica aerogel
Silica aerogel
SiO2-Al2O3 aerogel
SiO2-Al2O3 aerogel
Silica aerogel
Silica aerogel
wet gel formation
surface modification
ambient pressure drying
gelation
ambient pressure drying
gelation
ambient pressure drying
Strong hydrophobic
224
Adsorption and separation
225
Thermal insulator for insulating plaster
226
gelation
Adsorption and separation; thermal
227
ambient pressure drying
insulator
gelation
Adsorption and separation of organic
ambient pressure drying
solvents
gelation
Thermal insulator
229
surface silylation
ambient pressure drying
gelation
Thermal insulator
230
hydrophobization
ambient pressure drying
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silicon tetrachloride (SiCl4)
Silica aerogel
from polysilicon industry
Fly ash acid sludge
Rice hull
Rice hull
Bamboo leaf
silica aerogels
Silica aerogel
Silica aerogel
silica aerogel
gelation
ambient pressure drying
gelation
surface silylation
ambient pressure drying
gelation
drying at atmospheric pressure
gelation
solvent exchange
super critical drying
Preparation of water glass as a precursor
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thermal insulation
231
Strong hydrophobic material
232
Thermal insulator
222
thermal insulation, catalysis
216
Thermal insulator
233
for silica aerogel synthesis
Rice husk ash
Silica aerogel
sol-gel
solvent exchange
vaccum oven drying
234
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9. Discussion and Future prospect of research: In the last decade, interest in developing aerogels for diverse applications, such as thermal insulator, catalysts, sensors, environmental, and biological applications, has increased. The unique properties of these aerogels and their preparations via flexible methods, such as sol– gel method, play important roles for their industrialization. The potentials of various materials for aerogel preparation show the importance of a fundamental understanding of materials science to design the optimized synthesis conditions and processes. One of the most important challenges that is still an active area of research is the complete study of the waste materials with variable composition and properties to determine the best design for the better utilization of natural resource and preparation of these aerogels while considering functionalization and making composite for their specified application. Since the sol-gel and freeze-drying methods are almost commonly used methods in the preparation of various aerogels, exploration of new, more green and economical methods such as liquid hot water for extraction and purification of waste materials for commercialization of aerogel production is very imperative. Meanwhile, the potential of combining different approaches such as microwave, ultrasonic and so on to commonly used pretreatments methods to modify their performance is very promising study concept. However, it is important to keep in mind that optimum pretreatment method strictly depend on waste materials characteristic as well as the components to be isolated. The separation of base materials from wastes is currently a major challenge in this field. For example, despite of presence of carbon as the base element in all agricultural, plastics and other biobased waste materials, proper and cheap extraction of carbon is still challenging subject that need more study. Techno-economic evaluation of monomer isolation from waste and biomass, which is a preliminary evaluation of mass and energy balances, has been performed by some authors. But there are not published data from economic standpoint on the cost of production of aerogels from varieties of industrial wastes and agricultural biomass in any of recorded articles in this review paper. This issue remains open and rich to researchers for the future development of aerogel production. Moreover, the potential of utilization of biowastes and industrial wastes for the synthesis of silica, alumina, and other metal oxides cannot be ignored as it provides inexpensive and sustainable resource materials for the preparation of metal oxide aerogels. Despite various research on the utilization of waste materials for aerogel preparation, extensive studies must 57 ACS Paragon Plus Environment
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be conducted in this field to address them as industrial potential precursors for this application. Utilizing different byproducts such as lignin, hemicellulose and silica that made during extraction of specified materials such as cellulose from waste biomass must not be ignored. It could provide more value for their commercialization. Considering the promising development in the preparation of different carbon nanostructures, such as carbon fiber, nanocellulose, nanotube, graphite, and so on, from cellulose and lignocellulose biomass, which are the most abundant biomass on earth, their future use in the preparation of aerogel is extremely promising. 10. Conclusion: Despite the recent studies on aerogel preparation methods and precursor materials, the stateof-the-art aerogels cannot satisfy huge application demands. This contribution aimed to provide an overview of the utilization of waste biomass and industrial wastes by researchers and industries through categorizing the source of precursors, fabrication, synthesis process, and applications to emphasize the improvement of green and effective aerogel preparation methods. The limitations of these products and recommendations in future works are also detailed. The aforementioned natural resources are abundant and inexpensive, making it economical and sustainable for the preparation of aerogels while also addressing waste management problems. The conducted research and studies on this subject could definitely develop new reliable, cost-effective, and sustainable pathways for aerogel preparation. Future works must conduct in-depth study to provide the appropriate knowledge for understanding and establishing the relation between waste materials with variable composition and aerogels with specific requirements, considering different modifications, such as functionalization and making composite. Considering the direct dependence of characteristic such as morphology, surface and mechanical properties of prepared aerogels to its components derived from waste resources, developing optimum pretreatment and extraction methods is the most important future challenge. Waste materials are believed to have promising future as potential materials in aerogel preparation.
Acknowledgment: This study was partially supported by the Universiti Kebangsaan Malaysia’s grants (GUP2018-129 and GP-K019259). 58 ACS Paragon Plus Environment
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Graphical abstract 337x111mm (96 x 96 DPI)
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Figure 3 317x138mm (96 x 96 DPI)
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Figure 4 322x233mm (96 x 96 DPI)
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Figure 5 353x319mm (96 x 96 DPI)
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Figure 6 104x57mm (300 x 300 DPI)
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Figure 7 161x89mm (96 x 96 DPI)
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Figure 8
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Figure 9
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