Content uploaded by Abm Kamrul Hasan
Author content
All content in this area was uploaded by Abm Kamrul Hasan on Jul 14, 2020
Content may be subject to copyright.
INTERNATIONAL JOURNAL OF INTEGRATED ENGINEERING VOL. 12 NO. 5 (2020) 233-244
© Universiti Tun Hussein Onn Malaysia Publisher’s Office
IJIE
Journal homepage: http://penerbit.uthm.edu.my/ojs/index.php/ijie
The International
Journal of
Integrated
Engineering
ISSN : 2229-838X e-ISSN : 2600-7916
*Corresponding author: sumonce@gmail.com; 18h0251@ubd.edu.bn 233
2020 UTHM Publisher. All rights reserved.
penerbit.uthm.edu.my/ojs/index.php/ijie
Abstract: Activated carbon (AC) is an extremely porous carbonaceous adsorptive substance which has a
rigid carbon matrix with high surface area and broad functional groups. The structure is connected by
chemical bonds; arranged irregularly, generating a highly porous arrangement of corners, crevices, claps,
and cracks between the carbon layers. Activated carbons are produced high-temperature and chemical
activation of waste biomass. The pores in the lattice network of activated carbon permit the removal of
impurities from gaseous and liquid medium through adsorption. At present, the COVID-19 disease is the
prime concern around the whole world because of its exponential infections and death rate. There is no medicine
for this virus, and protection is the only remedy to survive from this contagious disease. Using a face mask is one
of the best methods to get rid of COVID-19. The mask combined with activated carbon can be beneficial for
adsorbing and disinfecting the virus as it is the versatile adsorbent for the elimination of the organic,
inorganic, and pathogenic contaminants.
Keywords: Activated carbon, adsorption, recycling/regeneration, COVID-19, coronavirus, SARS-CoV-2.
Analysis on Preparation, Application, and Recycling of
Activated Carbon to Aid in COVID-19 Protection
Md Sumon Reza1*, ABM Kamrul Hasan2, Shammya Afroze1, Muhammad S.
Abu Bakar1, Juntakan Taweekun3, Abul K. Azad1
1Faculty of Integrated Technologies,
Universiti Brunei Darussalam, JalanTungku Link, Gadong, BE 1410, BRUNEI DARUSSALAM
2Department of Anaesthesia, RIPAS Hospital, Jalan Putera Al-Muhtadee Billah,
Bandar Seri Begawan, BA1712, BRUNEI DARUSSALAM
3Department of Mechanical Engineering, Faculty of Engineering,
Prince of Songkla University, Hatyai, Songkla, 90112, THAILAND
*Corresponding Author
DOI: https://doi.org/10.30880/ijie.2020.12.05.029
Received 28 May 2020; Accepted 30 June 2020; Available online 30 June 2020
1. Introduction
Before 3750 BC, the use of carbon was started in the production of bronze of zinc, copper, and tin by the Egyptians
and Sumerians. In 1773, Car Wilhelm had recognized the absorptive capacity of carbonaceous substances from diverse
precursors. The first commercial marketing of manufactured activated carbon (AC) was introduced in 1911 in Austria.
AC has other names with activated coal, activated charcoal, and carbo enables [1]. It is one of the best adsorbents for its
enormous adsorptive capability and a significant amount of porosity. One gram of activated carbon can produce around
400–1000 square meters of the surface area [2]. The most common uses of ACs are for water treatment, gas masks
filter, ventilators, odor control, pathogen removal, metal purification, medicine, sewage management, compressed air
filters [3].
Any material which has a high carbon and less inorganic contents can be utilized as the raw resources of activated
carbon. Waste biomasses are used mainly for the production of AC with better adsorption capability and adequate
mechanical power [4]. Lots of precursors are used for obtaining sufficient activated carbon from waste biomass
M.S Reza et al., International Journal of Integrated Engineering Vol. 12 No. 5 (2020) p. 233-244
234
like Acacia species, paddy straws, coconut, bamboo, bagasse, fruit shell, fruit skins, etc. [5]. The use of waste biomass
for ACs sources is advantageous as it is cheaper, abundant, and non-toxic [6]. Adsorption capacity is the main
characteristic of activated carbon in its porous arrangement and chemical groups in the surface area [7]. The energy that
comes from the burning of fossil fuels creates greenhouse gases that can be minimized by activated carbon [8].
Currently, the novel coronavirus disease 2019 (COVID-19) is a great threat to the whole of humanity. It is an
infective pneumonia illness that occurred by the severe acute respiratory syndrome coronavirus 2 (SARS-CoV-2). This
virus was initially perceived in December 2019 at the Wuhan city, Hubei Province, China [9]. Within a short period, it
was spread in 215 countries and considered as a pandemic disease for infection and mortality rates. COVID-19 is a
novel beta RNA virus of 60-140 nm diameters with spine type projection. It causes a severe syndrome of respiratory
diseases with fever, breathing problems, cough, and a few gastrointestinal symptoms [10]. The coronavirus can spread
by the human-to-human conduction through nose, mouth, and eyes, mainly for coughing and sneezing [11]. To date, no
medicine or vaccine has invented for COVID-19 disease entirely. Protection is the only primary remedy to minimize
the transmission of the virus by wearing a face mask, using hand sanitizer, and maintaining physical distance (Figure 1)
[12]. Since the virus enters the human body through the nose and mouth, it can prevent by wearing a face mask.
Fig.1 - Protection ways from COVID-19 [13]
To reduce the exposure to the virus, numerous types of respiratory safety are used like N95 respirator masks,
surgical masks, cotton cloths, etc. All these masks cannot filter and absorb the virus, bacteria, dust, and toxic gases.
Among them, the N95 respirator mask can filter viruses, bacteria, and dust. But it cannot work appropriately for small
particle size and high breathing rates [14]. It is highly essential to design the respiratory protector properly, which can
filter viruses, bacteria, toxic gases, and dust. Mask s made with activated carbon can filter the pathogens, smokes, dust,
and hazardous gases [15].
2. Preparation of AC
The activated carbon preparation follows two main phases; the first stage is the carbonization, and the second stage
is the activation. The carbonization of the biomass occurs through the pyrolysis process which produces biochar [16].
The carbonaceous materials are prepared by eliminating the volatile matters through thermal decomposition in this
stage. Temperature, heating rate, gas flow rate, and the residence period are the main parameters [17]. As biochars
show lower adsorption capability, an activation procedure is important to develop the pore volume and the surface
areas. Initially, the disordered carbon has removed, exposed to the activating agents, and improves the porosity. Lastly,
the existing small pores are broadened to bigger sizes through the burning of pore walls. It increases the in-between
pores and the macro-porosity to reduce the micropores volume [18]. The degree of burn-off and the grade of activation
is a significant extent for preparing the porous AC. The primary activation can be done by a physical, chemical,
physiochemical, or microwave radiation processes [19]. Activated carbon is made from biomass with the following
procedures.
2.1 Pyrolysis/Carbonization
The pyrolysis or the carbonization is a thermal degradation process to decompose the biomass at higher
temperatures under an inert environment. In this process, the volatiles and non-carbons (hydrogen, oxygen, and
nitrogen) are removed and enhanced the fixed carbon content of the biochar [20]. During the de-volatilization process,
small pores are developed, which can be deposited by tarry materials at higher temperatures [21]. This deposition cause
collision in the tarry elements and the pore walls for the hydrocracking of the elements [22]. Table 1 shows the four
phases of the carbonization procedure [4].
2.2 Conventional Heating
One of the most appropriate preparation methods for manufacturing activated carbon is conventional heating.
During conventional heating, heat is shifted to the examples by conduction, convection, and radiation devices [23]. The
particle surface is heated, encouraging a thermal gradient between the core and the surface of each particle.
235
M.S Reza et al., International Journal of Integrated Engineering Vol. 12 No. 5 (2020) p. 233-244
Conventional heating is slow and inhomogeneous in which the surface and corners are much warmer than materials
inside [24].
Table 1 - Four phases of carbonization procedure
Phase
Temperature (°C)
Reaction type
Procedure
1
≤ 200
Endo-thermic
Primary heating of materials to eliminate the moisture content
2
170 - 300
Endo-thermic
Produce pyroligneous liquids, light tars, and gases (non-
condensable)
3
250 - 300
Exo-thermic
Major elimination of the pyroligneous liquid and tars
4
>300
-
Elimination of the volatiles and the non-carbon components to
increase the fixed carbon percentage of the biochar
2.3 Physical Activation
During physical activation, the raw materials undergo carbonization under a temperature of less than 700 °C, in an
oxygen-free environment. The physical activation response occurs between the oxidizing gas and carbon atom, which
produces pores as different portions of the char structure respond quicker than the rest. However, due to the period and
a large amount of energy needed, physical activation is not appropriate all time. Moreover, a massive amount of the
inner carbon mass is demolished to acquire the pore structure [25]. Physical activation has accompanied by two stages.
In the first stage, carbonization proceeds to remove all volatile substances in small temperatures from the precursor.
The activation of the gained carbonized material undergoes at higher temperatures using inert gasses, which are
optional in the second stage. The burning of carbonaceous elements may be prohibited in the existence of steam (H2O),
Nitrogen (N2), CO2, and Argon (Ar) or the combinations of these gases [26].
2.4 Chemical Activation
Chemical activation provides several benefits, because the process is a single step mixture and activation, achieved
at temperatures that are lower than physical activation, and thus, development of a higher quality of porous structure
[25]. Furthermore, the chemicals added for activation can be simply regained. Chemical activation is typically favored
because of its low temperature, uncomplicatedness, well advancing of the porous structure, higher production, and
quicker activation time. But, problems regarding this technique involve the necessity to rinse the final product of the
remaining inorganic substances, which can result in pollution difficulties [27]. Some acids (H3PO4, HCl, HNO3, and
H2SO4), bases (NaOH, KOH, and K2CO3) and few oxidants (H2O2 and KMnO4) are generally used for the activation
procedure. The first benefit is that acid action enhances the properties of AC with the surface area and the porosity that
accredit the removal efficiency of the pollutants to the carbon surface. The second advantage is that it can create or
enhance numerous functional bunches (carboxylic group, amino acids, oxygen cluster, etc.) on the exterior of the
activated carbon [28].
2.5 Physiochemical Activation
In this process, both the physical and the chemical activators are used instantaneously afterward, the carbonization.
The activation mostly happened at a higher temperature of 600 - 850 °C with the existence of chemicals, such as
H3PO4, ZnCl2, KOH, CO2, or H2O (steam). Though it is costly and time-consuming, physiochemical activation can
create activated carbon with significant surface properties. The joint activation process will impose on the pore
opening, which leads to a well-built porous structure. For instance, KOH with CO2 can create higher macropores and
mesopores within the matrix of activated carbon [18].
2.6 Microwave Activation
In the AC production process, the microwave (MW) activation became a feasible substitute than conventional
methods. It has some exceptional features like selective, quick, eventual heating to the sample, prompt response, and
precise regulator. The significant working constraints are MW radiation strength, precursor properties, activation time,
and chemical constituents [27]. In the microwave process, the energy transferred inside the particles as heat through the
dipole alignment and the ionic conduction. The particle with dipole moments is associated with the opposite course
from the force applied for high voltage. Therefore, high-temperature difference developed in the molecules inside and
outside, that make AC more functioning and faster [29].
3. Types of AC
Activated carbons (ACs) are categorized into six classes according to their size, preparation methodology, and
application as follows [1];
M.S Reza et al., International Journal of Integrated Engineering Vol. 12 No. 5 (2020) p. 233-244
236
•
Granular activated carbon (GAC)
•
Powdered activated carbon (PAC)
•
Extruded activated carbon (EAC)
•
Bead activated carbon (BAC)
•
Impregnated activated carbon (IAC)
•
Polymer-coated activated carbon (PCAC)
Activated carbons that are chemically and physically activated, ordinarily present in three shapes, which are
granular AC, powdered AC, and extruded AC. GAC has a rough formed by crushing and sieving, which vary in 0.2 to
5 mm inner dia. GACs are stable and hygienic to grip the amounts of gas and oil to a steady distinction. It can be
reactivated and recycled [30]. PAC owns the particle size of 5 to150 angstroms. It has little production expenses, which
are flexible and improved. Palatable oils are frequently cleansed by PAC and continuously in combination with the
earth. EACs are cylindrical pellets which diameters from 1-9 mm. Significant applications of EACs are in gas
purification, solvent recovery, gold rescue, and automobile discharges regulator [25].
4. Characteristics of AC
AC is the carbonaceous material of higher porosity and significant surface area with the vast functional area [31].
Different parameters like pore diameter, hardness, density, iodine number, and ash contents make them appropriate for
specific applications. Also, ACs have remediable pores with tunable surface chemistry, chemical/thermal steadiness,
and high accessibility [32]. AC contains different functional groups of aromatic rings that maintain the chemical
properties. These groups can be initiated on carbon structure to work through chemical, thermal, and hydrothermal
treatment. AC by KOH can enlarge the surface area up to 1200 m2 per gram by the elimination of acidic constituents,
which might close the pores [27]. The removal efficiency depends on the pore size, surface area, hardness, and density
of the AC with the concentration, solubility, chemical, and magnetism affection of the pollutants [33].
The most dynamic and thorough requirements for ACs in purification methods are connected to the contented of
inorganic constituents [34]. AC for gas and air purification has a BET surface area between 800 - 1500 m2 per gram,
where for water purification within the range of 500 to 1500 m2/g [35]. Organics has been adsorbed to the exterior of
AC uses for a long time; allow the accommodation of the constituent resulting in biodegradation of organics. ACs can
recollect volatile organic compounds on their surface and stop them from releasing into the atmosphere [36]. The size
of the particles is accountable for guiding the availability of the adsorbate to the pores of AC. In contrast, the solubility
controls the level of hydrophobic connections between adsorbate and the surface of AC [37].
5. Pores of AC
An important characteristic of AC for removing pollutants is their pores. AC involves ‘‘pores’’ with variable sizes
and shapes. According to the IUPAC categorizes pores [38] are
•
Macropores (Diameter > 50 nm)
•
Mesopores (2 ≤ Diameter ≤ 50 nm)
•
Micropores (Diameter < 2 nm)
Fig. 2 - Pores of activated carbon [39]
ACs contains three types of pores (macropore, mesopore, and micropore) that show in Figure 2. In carbonization,
the volume of the micropores increases up to 700 °C than decreases. In the activation process, the reaction occurred
between oxidizing agents and the tar elements mainly. This process helps to open the blocked pores, expands the small
pores, and forms new bigger pores. The resultant is a higher pore volume and a bigger surface area [40]. The
macropores aid to restrain adsorbate substances from the outer surface. Micro-pores have advanced ratios for their
237
M.S Reza et al., International Journal of Integrated Engineering Vol. 12 No. 5 (2020) p. 233-244
surface area to pore volume, compared to mesopores and macropores [41]. Mesopores help transmit the adsorbate
elements to the inner particles where micropores can catch. Macro-pores are utilized in trapping larger impurities, and
micro-pores are applied to captivate the minor molecules [42].
6. Adsorption of AC
AC adsorptions go through three primary stages. First, the materials are adsorbed to the exterior of the carbon
matrix. Second, materials transferred to the inside of the carbon pores, and third, materials adsorb the internal walls of
the carbon [42]. Adsorption occurs when pollutants are fascinated by the carbon pore, which happened if the carbon
pores are slightly bigger than contaminant size [39]. Two types of absorption are usually ensuing, physical adsorption
and chemical adsorption as follows,
6.1 Physical Adsorption
The physical adsorption occurs when the surface of carbon crystal attracts the contaminants via Van Der Waals
force. Contaminants a to the surface of the AC, where large particles were stuck in tinnier holes [39]. Physical
adsorptions are reliant on the concentration of the contaminant in the gas flow, and the pollutant to be adsorbed.
Molecules are fixed to the surface of the carbon by intermolecular attraction forces [43]. This adsorption happens inside
the pores to own radius of a few times larger than the molecular length of the adsorbed molecule. Pores that are tinier
than the molecular impurity sizes are unreachable and do not contribute to the adsorption progress [44].
6.2 Chemical Adsorption
Chemical adsorption is defined as the straight response of the adsorbed molecule to the active surface of the
activated carbon. Chemical bonds are formed between the surface of the char and the adsorbate [45]. The functional
groups of the carbon surface which carry the oxygen and other electrons participate in this process. If the molecules are
adsorbed chemically to the carbon surface, the process is called chemisorption [44]. The adsorption is the combination
of pollutants with the surface of the AC pores. The chemical materials existing on the surface of the openings rely on
the activation method, a natural resource used, and post-treatment of AC [39].
7. Factors Influencing Adsorption
The factors affecting the adsorption are characteristics of adsorbent are as follows
•
The size of the internal surface area
Activated carbon has the high surface areas which provide high adsorptive capabilities for molecules in some
gases and solvents. The more elevated surface is essential for the adsorption of bigger molecules [46].
•
Pore size
Pore sizes affect the adsorption of the pollutants are in two ways. Firstly, adsorption capacity increases with the
reduction of pore size as the contact points increase between the adsorbate and surface. Secondly, the size
rejection confines the pollutant adsorption of a specific type of pores, which are too low [47].
•
Chemical properties
In the activated carbon, the existence of the sulfur and nitrogen groups donated the alkaline behaviors, while the
oxygen and hydrogen groups added the acidic nature. The higher adsorption of the positively charged pollutants
on the AC holding higher O and H groups is constant, where the majority of the negatively charged in acidic
carbon [48].
•
Molecular characteristics (Chemically)
The surface functional groups have an important involvement in the adsorption of activated carbon by strong
chemical interactions, like Lewis acid-base interactions, electrostatic attraction/repulsion, p-p EDA interactions,
hydrogen bonding, and cation–p bonding [49].
•
Molecular structure
Adsorption capability of organic vapors to the activated carbon increased for the higher molecular weight of the
adsorbate [50].
•
Hydrophilic performance
For Log-scale adsorption, the sorption coefficients have a positive correlation for hydrophobic compounds and a
negative association for hydrophilic compounds [51].
M.S Reza et al., International Journal of Integrated Engineering Vol. 12 No. 5 (2020) p. 233-244
238
•
Polarity
The adsorption capacity of AC decreased with the increase of polarity and saturation air pressure [50].
•
Adsorbate concentration
The adsorption capacity of the AC increases exponentially with the initial concentration. The removal
performances were high at a lower level, while the uptake affected the concentrations increased [52].
•
Temperature
The increases in the temperature make the removal efficiency higher by activated carbon. It is the arrangement
of the activated transmission and the rise in surface area. Activated carbon is widening and deepen in micro-
pores, which create more surface area for adsorption [53].
•
Composition of the mixture
AC has the potential to be less expensive for hot gas mixture cleanup sorbent like adsorb H2S from high-
temperature coal gas stream [54].
•
pH value
The pH values play an essential role in the adsorption by activated carbon. It is affecting the solubility of the
adsorbate by changing the surface charge of the adsorbent [55].
•
Relative humidity for the gas phase
Activated carbon performed in a better way for nitric oxide (NO) conversion and adsorption in dry conditions.
Conversion can be compacted up to zero if the relative humidity increased by 50% [56]. The moisture contents
decrease the catalytic adsorption of the NO on activated carbon by lodging the oxidation sites, which reduce the
efficiency of the NO conversion [57].
8. Applications of Activated Carbon
Activated carbon is the cheap and environment-friendly adsorbents for eliminating the contaminants from water
and air in so many sectors as per Figure 3.
Fig. 3 - Applications of AC in different sectors [58]
239
M.S Reza et al., International Journal of Integrated Engineering Vol. 12 No. 5 (2020) p. 233-244
8.1 Water Purifications
AC is one of the best adsorbents to remove pollutants like dyes, metals, pesticides, etc. from wastewater. The
dyeing industries produce around 150,000 tons of dyes into sewage that increases the poisonousness and cancer-
causing assets [59]. Heavy metals are also one of the utmost dangerous water pollutants for the human body. The
elimination of heavy metals by AC is economically promising and requires simple methods; thus, AC is extensively
utilized to process water with heavy metals [37].
8.2 Air Cleansing
Activate carbon can clean the environment by absorbing the harmful gasses (COx, NOx, and SOx) from the air.
These pollutant gases cause respiratory diseases, lung infection, breathing problems, cough, heart disease, and paralysis
[60]. The removal efficiency depends on the characteristics of the feedstock (petroleum coke, coal, biomass), activators
(potassium hydroxide, carbon dioxide, and phosphoric acid), and process variables (activation temperature, the ratio of
activator to feedstock) [32].
8.3 Volatile Organic Compounds (VOCs) Capture
During surgical procedures, strong carcinogen smokes are produced, which have volatile organic compounds
(VOCs). These surgical smokes are risky for the health of surgeons and operation staff. The activated carbon filter can
reduce the adverse effect of surgical smoke effectively [61].
8.4 Pathogen Filtering
Activated carbon can remove the pathogens (virus and bacteria) effectively. The viruses are connected with the AC
through the electrostatic force of attraction between the virus tail and the surface of the carbon. With the higher ionic
strength, more viruses adsorbed [62]. AC can efficiently adsorb bacteria and microorganisms. The activated carbon
masks are used in the hospital for removing bacterial droplets [15].
8.5 Mask Filter Industry
Activated carbon filters are very useful to be used in mask Filter Company to remove the toxic gas, vapors, and
odors. The masks can have the capacity to filter out 95% of the particle with 0.3 microns size. It is eco-friendly and low
breathing resistance [15].
8.6 Medical Uses
AC is thought out as the first-line agent in the treatment of poisons, especially after passing some hours after
poison intake. Numerous forms of ACs are provided with low protein diets to regulate a few signs of uremia amongst
patients by several phases of kidney diseases, tie off urine urea, and the urinary poisons with AC, besides the
defecation, generating a density ascent for the constant dispersal of the toxins. It has also been testified to remove
urinary poisons by charcoals [63].
8.7 Use in Agriculture
Wine and livestock production by farmers are also dependent on charcoal (activated carbon). It is used as an
animal feed, pesticide, and nonagricultural ingredients in livestock production. A processing agent from activated
carbon is used in organic winemaking to adsorb brown color pigments from white grape concentrates [64].
8.8 Purification of Alcoholic Beverages
Activated carbon filters can be used effectively to remove the impurities from vodka and whiskey. An activated
carbon filter can significantly increase organic purity, while organically impure vodka was passing through at the
proper flow rate. As a result, the identical alcohol content in vodka is judged by odor and taste [39].
8.9 Storage of Fuel
Natural gas and hydrogen gas can be stored with the help of activated carbon from the literature. The porosity of
AC performs like foam for the various gases. Van der Waal force is acting between these gases and the carbon. Then
the gas may desorb at higher temperatures for combustion or extracting hydrogen gas for use in fuel cells. It is a
remarkable gas reserving technique as the gases can store at low pressure, small volume, and minor mass [65].
M.S Reza et al., International Journal of Integrated Engineering Vol. 12 No. 5 (2020) p. 233-244
240
9. Recycling and Handling
The recycling of AC is relatively tight and expensive. As the recycling is involved with the elimination of
impurities from AC via hot gas or stem without interrupting the adsorbed pollutants [66]. The AC can be reused once
the contaminants are eliminated from the used AC by recovering up to 80% of its efficiency. Rigid raw materials, like
stone coal, suggestively could retain well and may recycle a hundred times. The two methods of recycling AC as
follows [4],
1)
Thermal Recycling with heat completed in this way,
•
The ACs are dried up.
•
The dried carbons are pre-heated to carbonized the pollutants.
•
Activated carbons are revived with 700-1000 °C temperature to maintain the hollow porosity, and thus,
carbon can be recycled.
2)
Steam Recycling with steam is done as follows,
•
The filters are washed by hot water, descending from above, as these carbons filters continuously progress
upward from below.
•
The steam is connected and imposed through the AC with 120-130 °C temperature.
•
Finally, the ACs are back-washed and are ready to use.
No severe human health effects like toxicity or carcinogenicity rise for the contact of a person to the activated
carbon. The recommendation is to throughout the used or fresh AC to non-hazardous wastes as they are non-toxic.
Attention is warned in the repetition of the consumed Activated carbons. The ACs are applying for drinking water
treatments must follow the specification of the World Health Organization (WHO) [36].
10. Activated carbon to aid in COVID-19 protection
The activated carbon filter can protect the COVID-19 disease as it adsorbs virus from polluted deposits. This
adsorption happens due to the electrostatic attraction forces between the virus and the functional groups (carboxyl
groups and amino groups) of AC [67]. The mask equipped with activated carbon can trap and disinfect the coronavirus
by adsorbing the moisture. Once the viruses are caught, the high electropositive ions can disrupt the membrane integrity
and essential proteins, which lose the cell capability. The combined activated carbon mask also can minimize the
spreadability of COVID-19 disease [68]. Some companies even claim that activated carbon filters masks can filter at
least 95% of particles from the air while it fitted tightly [69]. Figure 4 shows the typical diagram of a combined
activated carbon mask.
Fig. 4 - Activated carbon with anti-virus micro particle barrier face mask [70]
The removal of the virus through activated carbon mainly depends on
•
The hydrophobicity of the virus
•
Electrophoretic repulsive force
•
Pore size distribution
•
The negative charge of activated carbon surface
If the hydrophobicity of the virus surface is more, the removal will be more. For the lower electrophoretic
repulsive force between AC and virus, extraction will be higher. Large volume with 20-50 nm pores activated carbons
can remove the virus effectively. With the less negative surface charge, the AC can enhance virus removal efficiency
[71].
241
M.S Reza et al., International Journal of Integrated Engineering Vol. 12 No. 5 (2020) p. 233-244
As the COVID-19 has a spike protein with hydrophobic character, the AC can be an efficient adsorbent and filter
for this virus removal [72]. The SARS-CoV-2 virus can create a bond with the carbon atoms by hydrogen bonds in the
first level, π-π interactions in the second level, and Van der Waals interactions in the third level [73]. In the inhibition
of the SARS-CoV-2 virus by the hydroxychloroquine, activated carbon played a significant role. In this process, AC
removed the pigments, tannins, and fatty acids. [74]. In the membrane process, activated carbon leads to the best
configuration and optimization for eliminating the COVID-19 virus and pathogens from wastewater [75].
There is a significant relationship between death for COVID-19 in the USA and the air pollution associated with
dust, smoke, and toxic gases [76]. It also found that in northern Italy, the affected and mortality rate is high for the
upper level of air pollution [77]. In the era of COVID-19, there is a massive risk for laparoscopic surgery as this
surgical process creates hazardous smokes with volatile organic compounds. It also found that there is a positive
relation between surgical smokes and virus transmission. Activated carbon filters can remove the surgical smokes as it
has the ability to absorb gas, vapor, and strong-smelling gases [78].
There is no direct relation between the transmissions of Covid-19 with the activated carbon using. Also, nobody
has affected in coronavirus while handling the products of activated carbons [79]. Proper care should be taken during
the reuse of AC filters according to the rules and standards [80].
11. Conclusion
The whole world is experiencing environmental, economic, and public health problems for COVID-19 disease, air
pollution, and waste generation. Activated carbon can be the single solution for its adsorbing capacity and environment-
friendly utilizations. It is a cheap, readily available, and versatile adsorbent for filtering viruses, bacteria, metals, dyes,
dust, smoke, and toxic gases effectively. Masks combined with activated carbon, protected from COVID- 19, maybe
the best solution as it can filter and disinfect the virus. The handling of activated carbon products is also risk-free.
Further investigation is necessary to check the performance of activated carbon masks to protect against COVID-19
disease.
Acknowledgement
The UGS award to Md Sumon Reza by Universiti Brunei Darussalam is gratefully acknowledged.
References
[1]
Gupta, T., (2017). Historical Production and Use of Carbon Materials: The Activated Carbon, In Carbon Black,
Gray Transparent, Springer International Publishing, pp: 47–70.
[2]
Ismadji, S., Sudaryanto, Y., Hartono, S.B., Setiawan, L.E.K., & Ayucitra, A., (2005). Activated carbon from
char obtained from vacuum pyrolysis of teak sawdust: Pore structure development and characterization.
Bioresource Technology, 96(12), 1364–1369.
[3]
González-García, P., (2018). Activated carbon from lignocellulosics precursors: A review of the synthesis
methods, characterization techniques and applications. Renewable and Sustainable Energy Reviews, 82, 1393–
1414.
[4]
Reza, M.S., Yun, C.S., Afroze, S., Radenahmad, N., Bakar, M.S.A., Saidur, R., Taweekun, J., & Azad, A.K.,
(2020). Preparation of activated carbon from biomass and its’ applications in water and gas purification, a
review. Arab Journal of Basic and Applied Sciences, 27(1), 208–238.
[5]
Daud, Z., Ahmad, B., Awang, H., Abubakar, M.H., Nasir, N., & Tajarudin, H.A., (2018). Ammoniacal nitrogen
removal using flamboyant pods (Delonix regia) adsorbent for natural rubber wastewater treatment. International
Journal of Integrated Engineering, 10(9), 184–189.
[6]
Reza, M.S., Islam, S.N., Afroze, S., Bakar, M.S.A., Sukri, R.S., Rahman, S., & Azad, A.K., (2020). Evaluation
of the bioenergy potential of invasive Pennisetum purpureum through pyrolysis and thermogravimetric analysis.
Energy, Ecology and Environment, 5(2), 118–133.
[7]
Ahiduzzaman, M., & Sadrul Islam, A.K.M., (2016). Preparation of porous bio-char and activated carbon from
rice husk by leaching ash and chemical activation. SpringerPlus, 5(1), 1248.
[8]
Hossain, M.A., Shams, S., Amin, M., Reza, M.S., & Chowdhury, T.U., (2019). Perception and barriers to
implementation of intensive and extensive green roofs in Dhaka, Bangladesh. Buildings, 9(4), 79.
[9]
Wang, C., Horby, P.W., Hayden, F.G., & Gao, G.F., (2020). A novel coronavirus outbreak of global health
concern. The Lancet, 395(10223), 470–473.
[10]
Tay, M.Z., Poh, C.M., Rénia, L., MacAry, P.A., & Ng, L.F.P., (2020). The trinity of COVID-19: immunity,
inflammation and intervention. Nature Reviews Immunology, 1–12.
[11]
Singhal, T., (2020). A Review of Coronavirus Disease-2019 (COVID-19). Indian Journal of Pediatrics, 87(4),
281–286.
[12]
Chang, D., Xu, H., Rebaza, A., Sharma, L., & Dela Cruz, C.S., (2020). Protecting health-care workers from
M.S Reza et al., International Journal of Integrated Engineering Vol. 12 No. 5 (2020) p. 233-244
242
subclinical coronavirus infection. The Lancet Respiratory Medicine, 8(3), e13.
[13]
https://www.tinkerfcu.org/covid-19/. Accessed May 18, 2020.
[14]
Bałazy, A., Toivola, M., Adhikari, A., Sivasubramani, S.K., Reponen, T., & Grinshpun, S.A., (2006). Do N95
respirators provide 95% protection level against airborne viruses, and how adequate are surgical masks?
American Journal of Infection Control, 34(2), 51–57.
[15]
Khayan, K., Anwar, T., Wardoyo, S., & Puspita, W.L., (2019). Active Carbon Respiratory Masks as the
Adsorbent of Toxic Gases in Ambient Air. Journal of Toxicology, 2019, 1–7.
[16]
Radenahmad, N., Tasfiah, A., Saghir, M., Taweekun, J., Saifullah, M., Bakar, A., Reza, S., & Kalam, A., (2020).
A review on biomass derived syngas for SOFC based combined heat and power application. Renewable and
Sustainable Energy Reviews, 119(March), 109560.
[17]
Reza, M.S., Afroze, S., Bakar, M.S.A., Saidur, R., Aslfattahi, N., Taweekun, J., & Azad, A.K., (2020). Biochar
characterization of invasive Pennisetum purpureum grass: effect of pyrolysis temperature. Biochar, 1–13.
[18]
Ahmed, M.J., (2016). Preparation of activated carbons from date (Phoenix dactylifera L.) palm stones and
application for wastewater treatments: Review. Process Safety and Environmental Protection, 102, 168–182.
[19]
Temdrara, L., Addoun, A., & Khelifi, A., (2015). Development of olivestones-activated carbons by physical,
chemical and physicochemical methods for phenol removal: a comparative study. Desalination and Water
Treatment, 53(2), 452–461.
[20]
Reza, M.S., Ahmed, A., Caesarendra, W., Abu Bakar, M.S., Shams, S., Saidur, R., Aslfattahi, N., & Azad, A.K.,
(2019). Acacia Holosericea : an Invasive Species for Bio-char , Bio-oil and Biogas Production. Bioengineering,
6(2), 33.
[21]
Reza, M.S., Islam, S.N., Afroze, S., Bakar, M.S.A., Taweekun, J., & Azad, A.K., (2020). Data on FTIR, TGA –
DTG, DSC of invasive Pennisetum purpureum grass. Data in Brief, 30, 105536.
[22]
Yahya, H.S.M., & Amin, N.A.S., (2019). Catalytic steam reforming of toluene for hydrogen production over
nickel-cobalt supported activated carbon. International Journal of Integrated Engineering, 11(7), 209–218.
[23]
Razali, Y.S., Tajarudin, H.A., & Daud, Z., (2018). Extraction of volatile fatty acids from leachate via liquid-
liquid extraction and adsorption method. International Journal of Integrated Engineering, 10(9), 79–84.
[24]
Ahmed, M.J., (2016). Application of agricultural based activated carbons by microwave and conventional
activations for basic dye adsorption: Review. Journal of Environmental Chemical Engineering, 4(1), 89–99.
[25]
Hales, R., (2002). Activated carbon adsorbers. Metal Finishing, 100(8), 59.
[26]
Danish, M., & Ahmad, T., (2018). A review on utilization of wood biomass as a sustainable precursor for
activated carbon production and application. Renewable and Sustainable Energy Reviews, 87, 1–21.
[27]
Ao, W., Fu, J., Mao, X., Kang, Q., Ran, C., Liu, Y., Zhang, H., Gao, Z., Li, J., Liu, G., & Dai, J., (2018).
Microwave assisted preparation of activated carbon from biomass: A review. Renewable and Sustainable Energy
Reviews, 92(May), 958–979.
[28]
Thwe, L.K., Phyo, S.W., & Khin, T.N., (2018). Effectiveness of prepared corn husk activated carbon on the
abatement of sodium chloride content in fish sauce. Universal Journal of Agricultural Research, 6(2), 91–97.
[29]
Pathak, P.D., & Mandavgane, S.A., (2015). Preparation and characterization of raw and carbon from banana peel
by microwave activation: Application in citric acid adsorption. Journal of Environmental Chemical Engineering,
3(4), 2435–2447.
[30]
Shepherd, A., (2001). Activated Carbon Adsorption for Treatment of VOC Emissions. CARBTROL
Corporation.
[31]
Daud, Z., Rahman, S.E.A., Awang, H., Abubakar, M.H., Ridzuan, M.B., & Tajarudin, H.A., (2018). Utilization
of waste paper sludge as an alternative adsorbent for the adsorption of ammonia nitrogen and COD in stabilized
landfill leachate. International Journal of Integrated Engineering, 10(9), 105–109.
[32]
Li, D., Zhou, J., Wang, Y., Tian, Y., Wei, L., Zhang, Z., Qiao, Y., & Li, J., (2019). Effects of activation
temperature on densities and volumetric CO 2 adsorption performance of alkali-activated carbons. Fuel,
238(October 2018), 232–239.
[33]
Ng, C.A., Wong, L.Y., Bashir, M.J.K., & Ng, S.L., (2018). Development of hybrid polymeric polyerthersulfone
(PES) membrane incorporated with powdered activated carbon (PAC) for palm oil mill effluent (POME)
treatment. International Journal of Integrated Engineering, 10(2), 137–141.
[34]
Marichelvam, M.K., & Azhagurajan, A., (2018). Removal of mercury from effluent solution by using banana
corm and neem leaves activated charcoal. Environmental Nanotechnology, Monitoring and Management,
10(August), 360–365.
[35]
Morlay, C., Gasperi, J., Guillossou, R., Mailler, R., Le Roux, J., Rocher, V., Vulliet, E., & Nauleau, F., (2019).
Organic micropollutants in a large wastewater treatment plant: What are the benefits of an advanced treatment
by activated carbon adsorption in comparison to conventional treatment? Chemosphere, 218, 1050–1060.
[36]
Baker, F.S., Miller, C.E., Repik, A.J., & Tolles, E.D., (2003). Carbon, Activated, In Kirk-Othmer Encycl. Chem.
Technol., John Wiley & Sons, Inc., pp: 1–34.
[37]
Dias, J.M., Alvim-Ferraz, M.C.M., Almeida, M.F., Rivera-Utrilla, J., & Sánchez-Polo, M., (2007). Waste
materials for activated carbon preparation and its use in aqueous-phase treatment: A review. Journal of
Environmental Management, 85(4), 833–846.
243
M.S Reza et al., International Journal of Integrated Engineering Vol. 12 No. 5 (2020) p. 233-244
[38]
Zdravkov, B.D., Čermák, J.J., Šefara, M., & Janků, J., (2007). Pore classification in the characterization of
porous materials: A perspective. Central European Journal of Chemistry, 5(2), 385–395.
[39]
Strand, G., (2001). Activated carbon for purification of alcohol-and some useful distillation tips-Macro pores
Meso pores Micro pores. Gert Strand.
[40]
Hadi, P., To, M.-H., Hui, C.-W., Lin, C.S.K., & McKay, G., (2015). Aqueous mercury adsorption by activated
carbons. Water Research, 73, 37–55.
[41]
Ahmed, M.J., (2017). Adsorption of quinolone, tetracycline, and penicillin antibiotics from aqueous solution
using activated carbons: Review. Environmental Toxicology and Pharmacology, 50, 1–10.
[42]
Siong, Y.K., Idris, J., & Atabaki, M.M., (2013). Performance of activated carbon in water filters. Water
Resources, 1–19.
[43]
Menya, E., Olupot, P.W.W., Storz, H., Lubwama, M., & Kiros, Y., (2018). Production and performance of
activated carbon from rice husks for removal of natural organic matter from water: A review. Chemical
Engineering Research and Design, 129, 271–296.
[44]
Koehlert, K., (2017). Activated carbon : fundamentals and new applications. www.chemengonline.com.
[45]
Rosli, M.A., Daud, Z., Latiff, A.A.A., Rahman, S.E.A., Oyekanmi, A.A., Zainorabidin, A., Awang, H., & Halim,
A.A., (2017). The effectiveness of Peat-AC composite adsorbent in removing color and Fe from landfill
leachate. International Journal of Integrated Engineering, 9(3), 35–38.
[46]
Rodrıguez-Reinoso, F., & Molina-Sabio, M., (1998). Textural and chemical characterization of microporous
carbons. Advances in Colloid and Interface Science, 76–77, 271–294.
[47]
Li, L., Quinlivan, P.A., & Knappe, D.R.U., (2002). Effects of activated carbon surface chemistry and pore
structure on the adsorption of organic contaminants from aqueous solution. Carbon, 40(12), 2085–2100.
[48]
Zhang, K., Cheung, W.H., & Valix, M., (2005). Roles of physical and chemical properties of activated carbon in
the adsorption of lead ions. Chemosphere, 60(8), 1129–1140.
[49]
Liu, H., Zhang, J., Ngo, H.H., Guo, W., Wu, H., Guo, Z., Cheng, C., & Zhang, C., (2015). Effect on physical and
chemical characteristics of activated carbon on adsorption of trimethoprim: Mechanisms study. RSC Advances,
5(104), 85187–85195.
[50]
Li, L., Sun, Z., Li, H., & Keener, T.C., (2012). Effects of activated carbon surface properties on the adsorption of
volatile organic compounds. Journal of the Air and Waste Management Association, 62(10), 1196–1202.
[51]
Nam, S.-W., Choi, D.-J., Kim, S.-K., Her, N., & Zoh, K.-D., (2014). Adsorption characteristics of selected
hydrophilic and hydrophobic micropollutants in water using activated carbon. Journal of Hazardous Materials,
270, 144–152.
[52]
Inam, E.I., Etim, U.J., Akpabio, E.G., & Umoren, S.A., (2016). Simultaneous adsorption of lead (II) and 3,7-
Bis(dimethylamino)-phenothiazin-5-ium chloride from aqueous solution by activated carbon prepared from
plantain peels. Desalination and Water Treatment, 57(14), 6540–6553.
[53]
Yavuz, R., Orbak, I., & Karatepe, N., (2006). Factors affecting the adsorption of chromium (VI) on activated
carbon. Journal of Environmental Science and Health - Part A Toxic/Hazardous Substances and Environmental
Engineering, 41(9), 1967–1980.
[54]
Cal, M.., Strickler, B.., & Lizzio, A.., (2000). High temperature hydrogen sulfide adsorption on activated carbon:
I.
Effects of gas composition and metal addition. Carbon, 38(13), 1757–1765.
[55]
Xiang, Y., Xu, Z., Wei, Y., Zhou, Y., Yang, X., Yang, Y., Yang, J., Zhang, J., Luo, L., & Zhou, Z., (2019).
Carbon-based materials as adsorbent for antibiotics removal: Mechanisms and influencing factors. Journal of
Environmental Management, 237, 128–138.
[56]
Abdulrasheed, A.A., Jalil, A.A., Triwahyono, S., Zaini, M.A.A., Gambo, Y., & Ibrahim, M., (2018). Surface
modification of activated carbon for adsorption of SO2 and NOX: A review of existing and emerging
technologies. Renewable and Sustainable Energy Reviews, 94, 1067–1085.
[57]
Ghafari, M., & Atkinson, J.D., (2016). Catalytic NO Oxidation in the Presence of Moisture Using Porous
Polymers and Activated Carbon. Environmental Science and Technology, 50(10), 5189–5196.
[58]
http://borovljany.com/top/. Accessed June 23, 2019.
[59]
Jiang, W., Xing, X., Li, S., Zhang, X., Wang, W., Jiang, W., & Xing, X., (2019). Synthesis, characterization and
machine learning based performance prediction of straw activated carbon. Journal of Cleaner Production, 212(x),
1210–1223.
[60]
Guan, W.J., Zheng, X.Y., Chung, K.F., & Zhong, N.S., (2016). Impact of air pollution on the burden of chronic
respiratory diseases in China: time for urgent action. The Lancet, 388(10054), 1939–1951.
[61]
Choi, S.H., Choi, D.H., Kang, D.H., Ha, Y.S., Lee, J.N., Kim, B.S., Kim, H.T., Yoo, E.S., Kwon, T.G., Chung,
S.K., & Kim, T.H., (2018). Activated carbon fiber filters could reduce the risk of surgical smoke exposure during
laparoscopic surgery: application of volatile organic compounds. Surgical Endoscopy, 32(10), 4290– 4298.
[62]
Cookson, J.T., (1969). MECHANISM OF VIRUS ADSORPTION ON ACTIVATED CARBON. Journal -
American Water Works Association, 61(1), 52–56.
M.S Reza et al., International Journal of Integrated Engineering Vol. 12 No. 5 (2020) p. 233-244
244
[63]
Alkhatib, A.J., & Zailaey, K. Al, (2015). Medical and environmental applications of activated charcoal: review
article. European Scientific Journal, 11(3), 50–56.
[64]
https://www.ams.usda.gov/?dDocName=STELPRDC5067194&acct=nosb. Accessed June 24, 2019.
[65]
Foo, K.Y., & Hameed, B.H., (2011). The environmental applications of activated carbon/zeolite composite
materials. Advances in Colloid and Interface Science, 162(1–2), 22–2q8.
[66]
Chowdhury, Z.K., Summers, R.S., Westerhoff, G.P., Leto, B.J., Nowack, K.O., Corwin, C.J., & Passantino,
L.B., (2013). Activated Carbon: Solutions for Improving Water Quality. American Water Works Association.
[67]
Tang, C.-S., Paleologos, E.K., Vitone, C., Du, Y.-J., Li, J.-S., Jiang, N.-J., Deng, Y.-F., Chu, J., Shen, Z., Koda,
E., Dominijanni, A., Fei, X., Vaverková, M.D., Osiński, P., Chen, X., Asadi, A., Takeuchi, M.R., Bo, M.W.,
Abuel-Naga, H., Leong, E.-C., Farid, A., Baser, T., O’Kelly, B.C., Jha, B., Goli, V.S.N.S., & Singh, D.N.,
(2020). Environmental Geotechnics: Challenges and Opportunities in the Post COVID-19 World. Environmental
Geotechnics, 1–21.
[68]
Pradhan, D., Biswasroy, P., Kumar naik, P., Ghosh, G., & Rath, G., (2020). A Review of Current Interventions
for COVID-19 Prevention. Archives of Medical Research, 1–42.
[69]
Mejova, Y., & Kalimeri, K., (2020). Advertisers Jump on Coronavirus Bandwagon: Politics, News, and
Business.
[70]
https://www.holygadgetstore.com/products/n95-pm2-5-anti-virus-micro-particle-barrier-face-mask-reusable-
with-activated-carbon-filter. Accessed May 16, 2020.
[71]
Matsushita, T., Suzuki, H., Shirasaki, N., Matsui, Y., & Ohno, K., (2013). Adsorptive virus removal with super-
powdered activated carbon. Separation and Purification Technology, 107, 79–84.
[72]
Ibrahim, I.M., Abdelmalek, D.H., Elshahat, M.E., & Elfiky, A.A., (2020). COVID-19 spike-host cell receptor
GRP78 binding site prediction. Journal of Infection, 80(5), 554–562.
[73]
Aanouz, I., Belhassan, A., El-Khatabi, K., Lakhlifi, T., El-ldrissi, M., & Bouachrine, M., (2020). Moroccan
Medicinal plants as inhibitors against SARS-CoV-2 main protease: Computational investigations. Journal of
Biomolecular Structure and Dynamics, 1–9.
[74]
Moussa, S., & Smain, C., (2020). In-silico Studies of Antimalarial-agent Artemisinin and Derivatives Portray
More Potent Binding to Lys353 and Lys31-Binding Hotspots of SARS-CoV-2 Spike Protein than
Hydroxychloroquine: Potential Repurposing of Artenimol for COVID-19. ChemRxiv, 1–12.
[75]
Ghernaout, D., & Elboughdiri, N., (2020). Disinfecting Water: Plasma Discharge for Removing Coronaviruses.
OALib, 07(04), 1–29.
[76]
Wu, X., Nethery, R.C., Sabath, B.M., Braun, D., & Dominici, F., (2020). Exposure to air pollution and COVID-
19 mortality in the United States. MedRxiv, 2020.04.05.20054502.
[77]
Conticini, E., Frediani, B., & Caro, D., (2020). Can atmospheric pollution be considered a co-factor in extremely
high level of SARS-CoV-2 lethality in Northern Italy? Environmental Pollution, 261, 114465.
[78]
Mowbray, N.G., Ansell, J., Horwood, J., Cornish, J., Rizkallah, P., Parker, A., Wall, P., Spinelli, A., Torkington,
J., & Mowbray, M.N.G., (2020). Safe management of surgical smoke in the age of COVID-19. British Journal
OfSurgery, 1–8.
[79]
https://activated-carbon.com/2020/03/16/covid-19-situation/. Accessed May 10, 2020.
[80]
El Gamal, M., Mousa, H.A., El-Naas, M.H., Zacharia, R., & Judd, S., (2018). Bio-regeneration of activated
carbon: A comprehensive review. Separation and Purification Technology, 197, 345–359.