Activated carbon, also called activated charcoal, is a form of carbon commonly used to filter contaminants from water and air, among many other uses. It is processed ( activated) to have small, low-volume pores that greatly increase the surface area
Because it is so porous on a microscopic scale, one gram of activated carbon has a surface area of over ,
Activated carbon is usually derived from waste products such as coconut husks in addition to other agricultural wastes like olive stones, rice husks and nutshell shells which are also being upcycled into activated carbon, diversifying feedstock supply. Furthermore, waste from paper mills has been studied as a possible source of activated carbon.
Uses
Activated carbon is used in
methane and
hydrogen storage,
,
capacitive deionization, supercapacitive swing adsorption, solvent recovery,
decaffeination, gold purification, metal extraction, water purification,
medicine,
sewage treatment,
in
, filters in compressed air, teeth whitening, production of hydrogen chloride, edible electronics,
and many other applications. These multiuse applications make it a versatile form of carbon that is used daily in many industries.
Industrial
There are many industrial applications of activated carbon and its other forms such as areas like metal extraction, water purification, sewage treatment, metal finishing and more. For example, it is the main purification technique for removing organic impurities from bright nickel plating solutions used for metal finishing plants. Expanding on electroplating, a variety of organic chemicals can be added to the plating solutions for improving their deposit qualities and for enhancing properties like brightness, smoothness, ductility, etc. This is due to the passage of direct current and electrolytic reactions of anodic oxidation and cathodic reduction, organic additives generate unwanted breakdown products in solution. Their excessive build up in the solutions can adversely affect plating quality and physical properties of deposited metal if run untreated by the filters. Activated carbon treatment removes such impurities and restores plating performance to the desired level. Its installation costs may vary according to the volume of water it must process, however the average cost can be around USD 1 - 2 million. Additionally, these filters need replacing over time (typically 6-12 months depending on usage). The cost of replacing the carbon in the GAC filter form is about USD 0.05 - 0.1 per cubic meter of water that is treated in the plant.
Medical
Activated carbon is used to treat
and
following oral
ingestion. Tablets or capsules of activated carbon are used in many countries as an over-the-counter drug to treat
diarrhea,
indigestion, and
flatulence. However, activated charcoal shows no effect on intestinal gas and diarrhea, is ordinarily medically ineffective if poisoning resulted from ingestion of corrosive agents, boric acid, or petroleum products, and is particularly ineffective against poisonings of
strong acids or bases,
cyanide,
iron,
lithium,
arsenic,
methanol,
ethanol, or
ethylene glycol.
Activated carbon will not prevent these chemicals from being absorbed into the human body.
It is on the World Health Organization's List of Essential Medicines.
Incorrect application (e.g. into the lungs) results in pulmonary aspiration, which can sometimes be fatal if immediate medical treatment is not initiated.
Analytical chemistry
Activated carbon, in 50% w/w combination with celite, is used as stationary phase in low-pressure
chromatographic separation of
carbohydrates (mono-, di-, tri-
saccharides) using
ethanol solutions (5–50%) as
Chromatography in analytical or preparative protocols.
Activated carbon is useful for extracting the direct oral (DOACs) such as dabigatran, apixaban, rivaroxaban and edoxaban from blood plasma samples.
Environmental
Carbon
adsorption has numerous applications in removing
from air or water streams both in the field and in industrial processes such as:
During early implementation of the 1974 Safe Drinking Water Act in the US, EPA officials developed a rule that proposed requiring drinking water treatment systems to use granular activated carbon. Because of its high cost, the so-called GAC rule encountered strong opposition across the country from the water supply industry, including the largest water utilities in California. Hence, the agency set aside the rule.[EPA Alumni Association: Senior EPA officials discuss early implementation of the Safe Drinking Water Act of 1974, Video , Transcript (see pages 15-16).] Activated carbon filtration is an effective water treatment method due to its multi-functional nature. There are specific types of activated carbon filtration methods and equipment that are indicated – depending upon the contaminants involved.
Activated carbon is also used for the measurement of radon concentration in air.
Biomass waste-derived activated carbons were also successfully used for the removal of caffeine and paracetamol from water.
Agricultural
Activated carbon (charcoal) is an allowed substance used by organic farmers in both
Animal husbandry and wine making. In livestock production it is used as a pesticide, animal feed additive, processing aid, nonagricultural ingredient and disinfectant.
[ Activated Charcoal Review Sheet, USDA Organic Materials Review, February 2002.] In organic winemaking, activated carbon is allowed for use as a processing agent to adsorb brown color pigments from white grape concentrates.
[ Activated Carbon Petition, USDA Organic Materials Review petition, Canadaigua Wine, May 2002.]
It is sometimes used as
biochar.
Distilled alcoholic beverage purification
Activated carbon filters (AC filters) can be used to filter
vodka and
whiskey of
organic compound impurities which can affect color, taste, and odor. Passing an organically impure vodka through an activated carbon filter at the proper flow rate will result in vodka with an identical alcohol content and significantly increased organic purity, as judged by odor and taste.
Fuel storage
Research is being done testing various activated carbons' ability to store
natural gas and
hydrogen gas.
The porous material acts like a sponge for different types of gases. The gas is attracted to the carbon material via Van der Waals forces. Some carbons have been able to achieve binding energies of 5–10 kJ per mol.
The gas may then be desorbed when subjected to higher temperatures and either combusted to do work or in the case of hydrogen gas extracted for use in a hydrogen fuel cell. Gas storage in activated carbons is an appealing gas storage method because the gas can be stored in a low pressure, low mass, low volume environment that would be much more feasible than bulky on-board pressure tanks in vehicles. The United States Department of Energy has specified certain goals
to be achieved in the area of research and development of nano-porous carbon materials. All of the goals are yet to be satisfied but numerous institutions, including the ALL-CRAFT program,
are continuing to conduct work in this field.
Gas purification
Filters with activated carbon are usually used in compressed air and gas purification to remove
oil vapors, odor, and other
from the air. The most common designs use a 1-stage or 2 stage filtration principle in which activated carbon is embedded inside the filter media.
Activated carbon filters are used to retain radioactive gases within the air vacuumed from a nuclear boiling water reactor turbine condenser. The large charcoal beds adsorb these gases and retain them while they rapidly decay to nonradioactive solid species. The solids are trapped in the charcoal particles, while the filtered air passes through.
Chemical purification
Activated carbon is commonly used on the laboratory scale to purify solutions of organic molecules containing unwanted colored organic impurities.
Filtration over activated carbon is used in large scale fine chemical and pharmaceutical processes for the same purpose. The carbon is either mixed with the solution then filtered off or immobilized in a filter.
Mercury scrubbing
Activated carbon, often infused with sulfur
or iodine, is widely used to trap mercury emissions from coal-fired power stations, medical
Incineration, and from
natural gas at the wellhead. However, despite its effectiveness, activated carbon is expensive to use.
Since it is often not recycled, the mercury-laden activated carbon presents a disposal dilemma.[Tim Flannery, Here On Earth: A New Beginning, Allen Lane (2011), p. 186.] If the activated carbon contains less than 260 ppm mercury, United States federal regulations allow it to be stabilized (for example, trapped in concrete) for landfilling. However, waste containing greater than 260 ppm is considered to be in the high-mercury subcategory and is banned from landfilling (Land-Ban Rule). This material is now accumulating in warehouses and in deep abandoned mines at an estimated rate of 100 tons per year.
The problem of disposal of mercury-laden activated carbon is not unique to the United States. In the Netherlands, this mercury is largely recovered and the activated carbon is disposed of by complete burning, forming carbon dioxide ().
Food additive
Activated, food-grade charcoal became a
food trend in 2016, being used as an
food additive to impart a "slightly smoky" taste and a dark coloring to products including hotdogs, ice cream, pizza bases, and bagels.
People taking medication, including birth control pills and
,
are advised to avoid novelty foods or drinks that use activated charcoal coloring since it can render the medication ineffective.
Smoking filtration
Activated charcoal is used in smoking filters
as a way to reduce the tar content and other chemicals present in smoke, which is a result of combustion, wherein it has been found to reduce the toxicants from tobacco smoke, in particular the free radicals.
[
]
Structure of activated carbon
The structure of activated carbon has long been a subject of debate. In a book published in 2006,[H. Marsh and F. Rodríguez-Reinoso, Activated carbon, Elsevier (2006), p. 186.] Harry Marsh and Francisco Rodríguez-Reinoso considered more than 15 models for the structure, without coming to a definite conclusion about which was correct. Recent work using aberration-corrected transmission electron microscopy has suggested that activated carbons may have a structure related to that of the , with pentagonal and heptagonal carbon rings.
Production
Activated carbon is carbon produced from carbonaceous source materials such as bamboo, coconut husk, willow peat, wood, coir, lignite, coal, and petroleum pitch. It can be produced (activated) by one of the following processes:
-
Physical activation: The source material is developed into activated carbon using hot gases. Air is then introduced to burn out the gases, creating a graded, screened and de-dusted form of activated carbon. This is generally done by using one or more of the following processes:
-
Carbonization: Material with carbon content is pyrolysis at temperatures in the range 600–900 °C, usually in an inert atmosphere with gases such as argon or nitrogen
-
Activation/oxidation: Raw material or carbonization material is exposed to oxidizing atmospheres (oxygen or steam) at temperatures above 250 °C, usually in the temperature range of 600–1200 °C. The activation is performed by heating the sample for 1 h in a muffle furnace at 450 °C in the presence of air.
-
Chemical activation: The carbon material is impregnated with certain chemicals. The chemical is typically an acid, strong Alkali,
The Dutch company Norit NV, part of the Cabot Corporation, is the largest producer of activated carbon in the world. Haycarb, a Sri Lankan coconut shell-based company, controls 16% of the global market share.
Regeneration & Sustainability
After adsorption, spent granular activated carbon can often be regenerated rather than discarded. Thermal reactivation (heating in an inert or steam atmosphere at 800–900 °C) restores much of the pore structure but consumes significant energy, while chemical regeneration (e.g. with dilute acids or bases) can selectively remove fouling compounds under milder conditions. Emerging methods like microwave-assisted reactivation and bio-regeneration using fungi or bacteria show promise for lower-carbon footprints. Choosing the optimal regeneration route balances carbon lifespan, energy use and treatment costs, and helps minimize the volume of hazardous waste sent to landfill.
Classification
Activated carbons are complex products which are difficult to classify on the basis of their behaviour, surface characteristics and other fundamental criteria. However, some broad classification is made for general purposes based on their size, preparation methods, and industrial applications.
Powdered activated carbon (PAC)
Normally, activated carbons (R 1) are made in particulate form as powders or fine granules less than 1.0 mm in size with an average diameter between 0.15 and 0.25 mm. Thus they present a large surface to volume ratio with a small diffusion distance. Activated carbon (R 1) is defined as the activated carbon particles retained on a 50-mesh sieve (0.297 mm).
Powdered activated carbon (PAC) material is finer material. PAC is made up of crushed or ground carbon particles, 95–100% of which will pass through a designated mesh sieve. The ASTM classifies particles passing through an 80-mesh sieve (0.177 mm) and smaller as PAC. It is not common to use PAC in a dedicated vessel, due to the high head loss that would occur. Instead, PAC is generally added directly to other process units, such as raw water intakes, rapid mix basins, clarifiers, and gravity filters.
Granular activated carbon (GAC)
Granular activated carbon (GAC) has a relatively larger particle size compared to powdered activated carbon and consequently, presents a smaller external surface. Diffusion of the adsorbate is thus an important factor. These carbons are suitable for adsorption of gases, vapors and liquids, because these substances diffuse rapidly throughout the filters. Granulated carbons are used for air filter and water treatment, as well as for general deodorization and separation of components in flow systems and in rapid mix basins. GAC can be obtained in either granular or extruded form. GAC is designated by sizes such as 8×20, 20×40, or 8×30 for liquid phase applications and 4×6, 4×8 or 4×10 for vapor phase applications. A 20×40 carbon is made of particles that will pass through a U.S. Standard Mesh Size No. 20 sieve (0.84 mm) (generally specified as 85% passing) but be retained on a U.S. Standard Mesh Size No. 40 sieve (0.42 mm) (generally specified as 95% retained). AWWA (1992) B604 uses the 50-mesh sieve (0.297 mm) as the minimum GAC size. The most popular aqueous-phase carbons are the 12×40 and 8×30 sizes because they have a good balance of size, surface area, and head loss characteristics.
Extruded activated carbon (EAC)
Extruded activated carbon (EAC) combines powdered activated carbon with a binder, which are fused together and extruded into a cylindrical shaped activated carbon block with diameters from 0.8 to 130 mm. These are mainly used for gas phase applications because of their low pressure drop, high mechanical strength and low dust content. Also sold as CTO filter (Chlorine, Taste, Odor).
Bead activated carbon (BAC)
Bead activated carbon (BAC) is manufactured from carbonizing petroleum pitch and then activating it into uniform spheres in diameters from approximately 0.35 to 0.80 mm. BAC typically exhibits a surface area in the range of 800–1 200 m2/g, comparable to or exceeding many granular carbons, enhancing its capacity for dissolved organics. Similar to EAC, it is also noted for its low pressure drop, high mechanical strength and low dust content, but with a smaller grain size. Its spherical shape makes it preferred for fluidized bed applications such as water filtration.
Impregnated carbon
Porous carbons containing several types of inorganic impregnate such as iodine and silver. such as aluminium, manganese, zinc, iron, lithium, and calcium have also been prepared for specific application in air pollution control especially in museums and galleries. Due to its antimicrobial and antiseptic properties, silver loaded activated carbon is used as an adsorbent for purification of domestic water. Drinking water can be obtained from natural water by treating the natural water with a mixture of activated carbon and aluminium hydroxide (Al(OH)3), a Flocculation. Impregnated carbons are also used for the adsorption of hydrogen sulfide (H2S) and . Adsorption rates for H2S as high as 50% by weight have been reported.
Polymer coated carbon
This is a process by which a porous carbon can be coated with a biocompatible polymer to give a smooth and permeable coat without blocking the pores. The typical film thickness ranges from 50 to 200 nm, which strikes a balance between preserving pore access and ensuring mechanical stability in the material. The resulting carbon is useful for hemoperfusion. Hemoperfusion is a treatment technique in which large volumes of the patient's blood are passed over an adsorbent substance in order to remove toxic substances from the blood. In clinical trials, polymer-coated carbons have achieved over 80% removal of toxins such as bilirubin and certain drug metabolites in a single pass!
Woven carbon
There is a technology of processing technical rayon fiber into activated carbon cloth for carbon filtering. Adsorption capacity of activated cloth is greater than that of activated charcoal (BET theory) surface area: 500–1500 m2/g, pore volume: 0.3–0.8 cm3/g). Thanks to the different forms of activated material, it can be used in a wide range of applications (supercapacitors, odor absorbers, CBRN defense industry etc.).
Properties
A gram of activated carbon can have a surface area in excess of , with being readily achievable.
Under an electron microscope, the high surface-area structures of activated carbon are revealed. Individual particles are intensely convoluted and display various kinds of porosity; there may be many areas where flat surfaces of graphite-like material run parallel to each other,
James Dewar, the scientist after whom the Dewar (vacuum flask) is named, spent much time studying activated carbon and published a paper regarding its adsorption capacity with regard to gases.[The separation of the most volatile gases from air without liquefaction] In this paper, he discovered that cooling the carbon to liquid nitrogen temperatures allowed it to adsorb significant quantities of numerous air gases, among others, that could then be recollected by simply allowing the carbon to warm again and that coconut-based carbon was superior for the effect. He uses oxygen as an example, wherein the activated carbon would typically adsorb the atmospheric concentration (21%) under standard conditions, but release over 80% oxygen if the carbon was first cooled to low temperatures.
Physically, activated carbon binds materials by van der Waals force
Activated carbon does not bind well to certain chemicals, including alcohols, , strong and bases, and most , such as lithium, sodium, iron, lead, arsenic, fluorine, and boric acid.
Activated carbon can also adsorb iodine very well. The iodine capacity, mg/g, (ASTM D28 Standard Method test) may be used as an indication of total adsorption over the surface area of the testing material.
Carbon monoxide however, is not very well adsorbed by activated carbon. This should be of particular concern to those using the material in filters for respirators, fume hoods, or other gas control systems because the gas is undetectable to the human senses, toxic to the metabolism, and neurotoxic which creates concern.
Substantial lists of the common industrial and agricultural gases adsorbed by activated carbon can be found online.
Activated carbon can be used as a substrate for the application of various chemicals to improve the adsorptive capacity for some inorganic (and problematic organic) compounds such as hydrogen sulfide (H2S), ammonia (NH3), formaldehyde (HCOH), mercury (Hg) and radioactive iodine-131(131I). This property is known as chemisorption.
Iodine number
Many carbons preferentially adsorb small molecules. Iodine value is the most fundamental parameter used to characterize activated carbon performance.
It is a measure of activity level (higher number indicates higher degree of activation
Iodine number is defined as the milligrams of iodine adsorption by one gram of carbon when the iodine concentration in the residual filtrate is at a concentration of 0.02 normal (i.e. 0.02N). Basically, iodine number is a measure of the iodine adsorbed in the pores and, as such, is an indication of the pore volume available in the activated carbon of interest. Typically, water-treatment carbons have iodine numbers ranging from 600 to 1100. Frequently, this parameter is used to determine the degree of exhaustion of a carbon in use. However, this practice should be viewed with caution, as chemical interactions with the adsorbate may affect the iodine uptake, giving false results. Thus, the use of iodine number as a measure of the degree of exhaustion of a carbon bed can only be recommended if it has been shown to be free of chemical interactions with adsorbates and if an experimental correlation between iodine number and the degree of exhaustion has been determined for the particular application.
Molasses
Some carbons are more adept at adsorbing large molecules.
Molasses number or molasses efficiency is a measure of the mesopore content of the activated carbon (greater than 20 Å, or larger than 2 nanometre) by adsorption of molasses from solution.
A high molasses number indicates a high adsorption of big molecules (range 95–600). Caramel dp (decolorizing performance) is similar to molasses number. Molasses efficiency is reported as a percentage (range 40%–185%) and parallels molasses number (600 = 185%, 425 = 85%).
The European molasses number (range 525–110) is inversely related to the North American molasses number.
Molasses Number is a measure of the degree of decolorization of a standard molasses solution that has been diluted and standardized against standardized activated carbon. Due to the size of color bodies, the molasses number represents the potential pore volume available for larger adsorbing species. As all of the pore volume may not be available for adsorption in a particular waste water application, and as some of the adsorbate may enter smaller pores, it is not a good measure of the worth of a particular activated carbon for a specific application. Frequently, this parameter is useful in evaluating a series of active carbons for their rates of adsorption. Given two active carbons with similar pore volumes for adsorption, the one having the higher molasses number will usually have larger feeder pores resulting in more efficient transfer of adsorbate into the adsorption space.
Tannin
are a mixture of large and medium size molecules.
Carbons with a combination of and mesopores adsorb tannins.
The ability of a carbon to adsorb tannins is reported in parts per million concentration (range 200 ppm–362 ppm).
Methylene blue
Some carbons have a mesopore (20 Å to 50 Å, or 2 to 5 nm) structure which adsorbs medium size molecules, such as the dye methylene blue.
Methylene blue adsorption is reported in g/100g (range 11–28 g/100g).
Dechlorination
Some carbons are evaluated based on the dechlorination half-life length, which measures the chlorine-removal efficiency of activated carbon. The dechlorination half-value length is the depth of carbon required to reduce the chlorine concentration by 50%. A lower half-value length indicates superior performance.
Apparent density
The solid or skeletal density of activated carbons will typically range between 2000 and 2100 kg/m3 (125–130 lbs./cubic foot). However, a large part of an activated carbon sample will consist of air space between particles, and the actual or apparent density will therefore be lower, typically 400 to 500 kg/m3 (25–31 lbs./cubic foot).[TIGG Corporation. Granular activated carbon selection . Published 2012-05-8, retrieved 2012-09-21.]
Higher density provides greater volume activity and normally indicates better-quality activated carbon.
ASTM D 2854 -09 (2014) is used to determine the apparent density of activated carbon.
Hardness/abrasion number
It is a measure of the activated carbon's resistance to attrition.
It is an important indicator of activated carbon to maintain its physical integrity and withstand frictional forces which would cause the material to be defective. There are large differences in the hardness of activated carbons, depending on the raw material and activity levels (porosity) it is created for.
Ash content
Ash reduces the overall activity of activated carbon and reduces the efficiency of reactivation. The amount is exclusively dependent on the base raw material used to produce the activated carbon (e.g., coconut, wood, coal, etc.).
The metal oxides (Fe2O3) can leach out of activated carbon resulting in discoloration. Acid/water-soluble ash content is more significant than total ash content. Soluble ash content can be very important for aquarists, as ferric oxide can promote algal growths. A carbon with a low soluble ash content should be used for marine, freshwater fish and reef tanks to avoid heavy metal poisoning and excess plant/algal growth.
ASTM (D2866 Standard Method test) is used to determine the ash content of activated carbon.
Carbon tetrachloride activity
Measurement of the porosity of an activated carbon by the adsorption of saturated carbon tetrachloride vapour.
Particle size distribution
The finer the particle size of an activated carbon, the better the access to the surface area and the faster the rate of adsorption kinetics. In vapour phase systems this needs to be considered against pressure drop, which will affect energy cost. Careful consideration of particle size distribution can provide significant operating benefits.
However, in the case of using activated carbon for adsorption of minerals such as gold, the particle size should be in the range of . Activated carbon with particle size less than 1 mm would not be suitable for elution (the stripping of mineral from an activated carbon). Researchers at Cornell University synthesized an ultrahigh surface area activated carbon with a BET area of 4800 m2 g–1 and a total pore volume of 2.7 cm3 g–1.
Modification of properties and reactivity
Acid-base, oxidation-reduction and specific adsorption characteristics are strongly dependent on the composition of the surface functional groups.[Philippe Serp, José Luis Figueiredo, Carbon Materials for Catalysis, Wiley, – 2009, – 550 p.]
The surface of conventional activated carbon is reactive, capable of oxidation by atmospheric oxygen and oxygen plasma
Oxidation in the liquid phase is caused by a wide range of reagents (HNO3, H2O2, KMnO4).
Through the formation of a large number of basic and acidic groups on the surface of oxidized carbon to sorption and other properties can differ significantly from the unmodified forms.
Activated carbon can be nitrogenated by natural products or
Activated carbon can interact with chlorine,
Surface of activated carbon, like other carbon materials can be fluoralkylated by treatment with (per)fluoropolyether peroxide
Sulfonic acid functional groups can be attached to activated carbon to give "starbons" which can be used to selectively catalyse the esterification of fatty acids.[
] It is reported about synthesis of activated carbon with chemically grafted superacid sites –CF2SO3H.
Some of the chemical properties of activated carbon have been attributed to presence of the surface active carbon Alkenes.
The Polyani adsorption theory is a popular method for analyzing adsorption of various organic substances to their surface.
Examples of adsorption
Heterogeneous catalysis
The most commonly encountered form of chemisorption in industry, occurs when a solid catalyst interacts with a gaseous feedstock, the reactant/s. The adsorption of reactant/s to the catalyst surface creates a chemical bond, altering the electron density around the reactant molecule and allowing it to undergo reactions that would not normally be available to it.
Reactivation and regeneration
The reactivation or the regeneration of activated carbons involves restoring the adsorption of saturated activated carbon by desorbing adsorbed contaminants on the activated carbon surface.
Thermal reactivation
The most common regeneration technique employed in industrial processes is thermal reactivation.
-
Adsorbent drying at approximately
-
High temperature desorption and decomposition () under an inert atmosphere
-
Residual organic gasification by a non-oxidising gas (steam or carbon dioxide) at elevated temperatures ()
The heat treatment stage utilises the exothermic nature of adsorption and results in desorption, partial cracking and polymerization of the adsorbed organics. The final step aims to remove charred organic residue formed in the porous structure in the previous stage and re-expose the porous carbon structure regenerating its original surface characteristics. After treatment the adsorption column can be reused. Per adsorption-thermal regeneration cycle between 5–15 wt% of the carbon bed is burnt off resulting in a loss of adsorptive capacity.
Other regeneration techniques
Current concerns with the high energy/cost nature of thermal regeneration of activated carbon has encouraged research into alternative regeneration methods to reduce the environmental impact of such processes. Though several of the regeneration techniques cited have remained areas of purely academic research, some alternatives to thermal regeneration systems have been employed in industry. Current alternative regeneration methods are:
-
TSA (thermal swing adsorption) and/or PSA (pressure swing adsorption) processes: through convection (heat transfer) using steam,
-
MWR (microwave regeneration)
-
Chemical and solvent regeneration
-
Microbial regeneration
-
Electrochemical regeneration
-
Ultrasonic regeneration
-
Wet air oxidation
See also
External links
