What is Activated Carbon and How is it Made?
Activated carbon (also known as active carbon or activated charcoal), is an artificial carbonaceous (carbon-rich) material. It is typically made from wood, but also can be made using bamboo, coconut husk, peat, woods, coir, lignite, coal, pitch, and other dense carbon sources. There are a variety of similar substances that fall under the general classification of activated carbon such as activated coal and activated coke, but they all share the properties of vast surface area per mass, exceptional microporosity, and a composition of almost exclusively elemental carbon.
is characterized through techniques such as electron microscopy and surface area analysis methods and is primarily responsible for its usefulness. Microscopes show a surface honeycombed with holes and crenelated with ridges which join to a similar structure deeper within the carbon. Due to this structure, activated carbon can have surface areas commonly exceeding 500–1500 m²/g, with some grades reaching over 3000 m²/g depending on activation method and feedstock..
These small, low-volume pores allow for increased adsorption capacity (the process of chemical surface bonding, not to be confused with absorption) and allow more reactions between the carbon and other media. Activated carbon is therefore highly valued in filtering, deodorization, medical, and chemical applications, as most contaminants easily bind to it and remain trapped in the carbon microstructure. Adsorption mechanisms may include van der Waals forces, pore filling, electrostatic interactions, and surface chemistry effects..
Activated carbon is produced through carbonization followed by physical or chemical activation processes,making it widely available for many applications; however, activated carbon performance declines as adsorption sites become saturated. Replacement or regeneration frequency depends on application, contaminant load, and operating conditions, and while microbial growth can occur in some wet filtration systems, this is application-specific rather than universal. This demand drives continuous production and regeneration across industrial supply chains.
How to Make Activated Carbon
The production process of activated carbon, or the activation of carbon, exists in two forms. A carbonaceous source such as wood, coal, peat, or any organic carbonaceous material is carbonized, which means the pure carbon is extracted by a heating method known as pyrolysis.
Following carbonization, activation is typically achieved either through physical activation using steam or carbon dioxide at high temperatures, or through chemical activation using agents such as phosphoric acid, potassium hydroxide, or zinc chloride depending on feedstock and process design.
The sections below briefly detail these processes.

Carbonization
Carbonization is the thermal decomposition of carbon-rich material in limited oxygen, producing a char composed primarily of carbon along with ash and residual compounds.. This heating process, called pyrolysis, comes from an ancient technique for making charcoal. Very dense carbonaceous material is used in the beginning, because the result needs to be extra-porous for activated carbon purposes.
Carbonization typically occurs at approximately 400–900°C depending on feedstock and process conditions. What remains is usually 20-30 percent of the beginning weight and consists of mostly carbon with a small percentage of inorganic ash. This differs from metallurgical coking, which generally refers to producing coke from coal rather than charcoal.
Once the porous form of carbon is produced, it needs to undergo oxidization so it can be adsorbent, or “activated”. This can occur in one of two ways: gas or chemical treatment.
Gas Treatment
Physical activation is typically performed by exposing carbonized material to steam or carbon dioxide at elevated temperatures in controlled conditions that partially gasify the carbon structure and expand porosity. After being oxidized, the active carbon gains its good adsorption characteristics and is ready to collect contaminants in liquid/gaseous applications.
For physical gas treatment, the carbonization/pyrolysis process must take place in an inert environment at 600-900 degrees Celsius. Controlled oxidizing gases such as steam or carbon dioxide are introduced which react with portions of the carbon surface to develop pore structure.
Chemical Treatment
In chemical activation, carbonization and activation often occur in a combined process. The precursor material is typically impregnated with activating chemicals such as phosphoric acid, potassium hydroxide, or zinc chloride before heating, rather than simply being submerged in a heated bath. The chemically treated material is then heated, often at lower temperatures than physical activation, commonly around 400–900°C.
This process allows the carbonaceous material to be carbonized and activated efficiently, often with higher yield and lower activation temperatures than physical activation. Post-treatment washing is usually required to remove residual activating chemicals, byproducts, and impurities that could otherwise reduce product purity or performance.
Activated Carbon Regeneration
Soiled activated carbon can be restored to its original adsorptive capacity via regeneration procedures. There are numerous methods of carbon regeneration, but the most common technique is thermal reactivation, where the soiled carbon is dried, heated in an inert atmosphere, and gas treated.
About 5-15% of the original weight of the carbon is lost in thermal regeneration, and this process is very energy-intensive; therefore, smaller companies typically send their used carbon to specialized regeneration facilities instead of performing regeneration onsite. There are numerous other regeneration techniques that aim to reduce both the yield loss and energy expenditure of thermal regeneration.
Alternative regeneration approaches may include chemical, electrochemical, microwave, steam, or biological methods depending on contaminant type and economic feasibility. , .
Post Treatment Activated Carbon
Following oxidization, activated carbon can be processed for many kinds of uses, with several classifiable different properties. For instance, granular activated carbon (GAC) is a sand-like product with bigger grains than powdered activated carbon (PAC), and each is used for different applications.
Other varieties include impregnated carbon, which adds different elements such as silver and iodine, and polymer-coated carbons. Below, the following section provides a brief overview of the different types of available activated carbon and their beneficial qualities.
Types of Activated Carbon
Activated Charcoal
Activated charcoal is synonymous with activated carbon and can be used interchangeably. It is important to note that “charcoal” differs from pure carbon terminology, as charcoal denotes carbonaceous material derived from firing wood and organic substances that still contain hydrogen, oxygen, and other non-carbon elements, while “carbon” in technical contexts may refer to elemental carbon or carbon-rich engineered materials depending on usage..
Do not be concerned if you can only find “activated charcoal” when looking for activated carbon — they are the same type of material.
Powdered Activated Carbon (PAC)
Powdered activated carbon (PAC) typically consists of finely ground particles, often with the majority passing through mesh sizes such as 80 mesh (0.177 mm), though exact sizing standards vary, maximizing surface accessibility and minimizing diffusion distance. PAC is a fine material that will pass through most mesh sleeves.
PAC generally creates higher resistance in fixed-flow systems than GAC and is often dosed or suspended rather than used as a primary packed-bed medium, making it more useful in raw water intakes, rapid mix basins, clarifiers, gravity filters, and other applications where maximum adsorption of contaminants supersedes flow characteristics.
Granular Activated Carbon (GAC)
Granular activated carbon (or GAC) has larger particle sizes than PAC which generally improve hydraulic flow characteristics while increasing diffusion path length within particles.. Gases and vapors can often be processed more effectively through GAC beds in certain applications, as there is more space between granulated carbon particles for gas to flow through; however, there is also less internal surface area in GAC, leading to a necessary balancing act between grain size and adsorption capacity. GAC is typically employed for liquid water treatment, deodorization, and component separation in liquid flow systems.
Extruded Activated Carbon (EAC)
Powdered or finely milled activated carbon feedstock is combined with a binder and extruded into cylindrical-shaped blocks typically in much smaller industrial pellet diameters, often a few millimeters, forming extruded activated carbon (EAC). The benefit of EAC is its low pressure drop, dust content, and high mechanical strength, as well as its more standardized grain shapes. EAC is used in gas-phase applications and places where dust is prohibited, as well as in Chlorine, Taste, Odor (CTO) filters.
Bead Activated Carbon (BAC)
Bead activated carbon (BAC) is manufactured into spherical particles, often through polymer or pitch precursor processing, rather than simply fused carbon.. BAC also sports low pressure drops, low dust content, and high mechanical strength as EAC, but differs in its slightly smaller grain size and its preferential use in fluidized bed applications where water can more easily flow around its spherical form. The choice between EAC and BAC is typically specified by flow regime, where BAC is better suited for high-flow/high-wear liquid systems.
Polymer Coated Carbon
When porous carbon is coated with a biocompatible polymer, it becomes polymer-coated carbon. This activated carbon type has both a smooth, permeable outside and open, available pores, making it highly useful for medical applications dealing with blood filtration known as hemoperfusion.
In hemoperfusion, blood is passed over polymer coated carbon to remove toxins and unwanted media. The polymer prevents the loss of formed elements in the bloodstream and the formation of unwanted clots (charcoal emboli), while its pores can still filter out toxic substances.
Impregnated Carbon
Impregnated carbon is activated carbon that has been treated with additional chemical substances to improve its ability to capture specific contaminants. These additives, known as impregnates, are selected according to the target application. Common examples include sulfur compounds for mercury removal, silver for bacteriostatic water-treatment media, and acid- or alkali-treated carbons for gases such as ammonia, hydrogen sulfide, acid gases, and other industrial pollutants.
Impregnated carbon is used when standard activated carbon does not provide enough adsorption capacity or chemical selectivity for a specific contaminant. It is commonly used in water treatment, industrial air purification, gas scrubbing, odor control, and pollution-control systems. For example, sulfur-impregnated activated carbon is used for mercury capture, while silver-impregnated activated carbon is used in some water filters to inhibit bacterial growth on the carbon media.
What is Activated Carbon Used For?
In addition to its use as a filter, activated carbon is used for a variety of other applications. It can recover valuable solvents and materials from various fluids, remove odors, and alter flavors in gases and liquids. It also has medical uses and can help treat patients who have ingested poisons or overdosed on ingested narcotics.
Activated carbon also finds use in the cleanup of certain hazardous spills. The following sections explore these different applications of activated carbon in a variety of markets.
Filtration
Among other applications, activated carbon is often used to filter contaminants out of drinking water. After water testing, filtration can be manipulated to remove specific contaminants so the water can meet EPA National Drinking Water Standards. Specifically, activated carbon filters are useful for removing organic compounds, which are often the cause of changes in the taste, smell, and appearance of water.
Activated carbon works primarily through adsorption of many organic molecules due to pore structure, surface area, and chemical affinity rather than simply because compounds contain carbon and hydrogen. Filtration can remove harmful chemicals, such as trihalomethanes (THMs), pesticides, polychlorinated biphenyls (PCBs), and polycyclic aromatic hydrocarbons (PAHs). If these chemicals are present in quantities above EPA standards, the water is potentially dangerous to drink.
Despite activated carbon’s usefulness, it is not universally effective for all contaminants. Standard activated carbon is generally limited for dissolved heavy metal removal unless specially modified or combined with additional treatment media. Microbes, nitrates, and fluoride are examples of contaminants that cannot be filtered effectively using active carbon.
Activated carbon can sometimes support bacterial growth if filters are poorly maintained because trapped organic matter and moisture may create favorable conditions for microbial colonization. In public water systems, the water is pre-treated for disease-causing bacteria, so water that enters the home or is used as public drinking water is unlikely to contain such bacteria.
It is common, however, for a fair number of non-pathogenic bacteria to build up inside the active carbon filter. Although these types of bacteria don’t cause disease outright, it’s a good idea to change the filter or clean it on a regular basis.
Common exposure to bacteria means that the human immune system is well-equipped to protect against basic bacteria, but those who have weaker immune systems are more susceptible — either way, regular cleaning of the filter is important in maintaining an effective active carbon system.
Industrial & Chemical Applications
Activated carbon is used in industrial applications to remove organic impurities from bright nickel-plating solutions, as well as to purify and extract precious metals such as gold. When electroplating, operators add a variety of organic materials to plating solutions to improve specific metal properties, but these compounds can break down into unwanted side-products when exposed to electrical current.
Activated carbon is added to remove these impurities and to restore plating solutions to their optimal efficiencies. In analytical chemistry and laboratory processing, activated carbon is more commonly used for purification, decolorization, sample cleanup, or contaminant removal as well as extract certain media from substrates. It is also used to filter and purify certain chemical samples, either as regular activated carbon or as impregnated carbon for specific contaminants.
Medical Applications
As previously stated, polymer-coated carbon is used in hemoperfusion to cleanse blood of unwanted toxic substances; however, activated carbon can also be ingested in tablet form to treat poisoning and overdoses. Activated charcoal has historically been marketed for some gastrointestinal uses, but its evidence base outside poison management is limited and not universally supported for routine gastrointestinal treatment.
Activated charcoal has been included in WHO Essential Medicines guidance for specific toxicological uses, though listing status and recommendations may vary over time,, and it remains an important tool in poison management when clinically appropriate.
Environmental & Agricultural Applications
Activated carbon (specifically impregnated carbon) is used to remove air and water pollutants such as those found in chemical spills, groundwater, drinking water, air, volatile organic compound (VOC) factories, and other sources of pollution.
Activated carbon can be used in certain passive radon test devices as an adsorbent collection medium.. Impregnated carbon infused with sulfur and/or iodine is widely implemented in coal power plants, medical incinerators, and methane wellheads to trap mercury emissions (though, mercury-laden carbon poses a disposal problem of its own).
In agriculture, activated carbon may be used in niche applications such as soil remediation, toxin adsorption, feed supplementation under specific formulations, or processing support.
Limitations and Drawbacks of Activated Carbon
Activated carbon is a highly versatile material, but it is not without significant limitations. Understanding where it falls short is essential for selecting the right filtration approach and maintaining system performance over time.
Contaminant Selectivity
Activated carbon excels at capturing organic compounds, chlorine, VOCs,some contaminants depending on formulation, with standard activated carbon generally being less effective for many dissolved heavy metals unless specially modified, but it cannot effectively remove all categories of contaminants. Microbes, nitrates, fluoride, sodium, and dissolved inorganic compounds pass through carbon filters largely unaffected.
When water contamination levels are high, the available surface area fills up rapidly, and if flow rates are too fast, carbon may fail to capture all target contaminants even before saturation occurs.
Filter Saturation and Capacity Limits
All activated carbon filters have a finite adsorption capacity. Once the pore surfaces become saturated with trapped contaminants, the filter stops working and must be replaced.
Once adsorption capacity is exceeded, target contaminants increasingly pass through the filter untreated, though desorption of previously retained substances may occur under certain changing conditions. This makes timely replacement an important performance and safety consideration. This makes timely replacement not just a performance issue, but a safety one.
Typical replacement intervals depend on usage and contaminant load:
- Air purifier filters: every 3 to 12 months under standard conditions
- Point-of-use water filters (countertop, refrigerator): every 2 to 6 months
- Under-sink and whole-house systems: every 6 months to 2 years
- High-contamination industrial environments: significantly shorter replacement cycles
Bacterial Growth Risk
The moist interior of a poorly maintained activated carbon filter can create conditions favorable for microbial colonization or biofilm formation.. While most bacteria that accumulate in consumer filters are non-pathogenic, immunocompromised individuals face elevated risk. Industrial and municipal systems require rigorous replacement and monitoring schedules to prevent biological fouling.
Particle Filtration Limitations
Activated carbon primarily adsorbs chemical contaminants and is not designed as a high-efficiency particulate filtration medium for dust, pollen, or many microorganisms without additional filtration technologies.. In air purification applications, activated carbon must typically be paired with HEPA filtration to address both chemical and particulate contaminants.
Cost and Regeneration Challenges
Activated carbon costs vary widely depending on feedstock, grade, processing, and market conditions, with specialized grades often carrying substantially higher costs. The need for frequent replacement drives ongoing operational costs. Thermal regeneration — the most common method of restoring spent carbon — is highly energy-intensive and often results in some material loss per cycle, commonly in the approximate range of 5–15% depending on contamination and process conditions. Smaller organizations typically cannot justify on-site regeneration equipment and must outsource to specialized facilities, adding logistics costs and potential delays.
Hot Water and Temperature Sensitivity
Many activated carbon filtration systems are designed primarily for cold or moderate-temperature use unless specifically rated for higher temperatures.. Higher temperatures can reduce adsorption efficiency for certain contaminants and may affect system materials or performance depending on design and operating conditions. Carbon filter systems should always be installed on cold water lines before any water heater.
Sustainability and Environmental Impact of Activated Carbon Production
The environmental footprint of activated carbon varies significantly depending on the feedstock used, the production method employed, and whether virgin or reactivated carbon is involved. Life cycle assessment (LCA) research has quantified these differences across feedstock types.
Feedstock Carbon Footprint Comparison
Coal-derived activated carbon often carries a relatively high environmental burden in many LCA scenarios, particularly when fossil energy inputs are significant, while biomass-derived carbons may offer lower greenhouse gas impacts depending on sourcing, processing efficiency, and accounting assumptions. Specific emissions values vary substantially by study design, feedstock, and energy mix.
Coconut shell and other biomass-derived activated carbons are often considered lower-impact options in some environmental categories, particularly when agricultural byproducts are used efficiently, though sustainability outcomes depend on sourcing, transport, and processing practices.
The direct emissions from production furnaces and the electricity consumed to run activation kilns are consistently identified as the largest contributors to environmental impact across all feedstock types.
Reactivation as a Sustainability Strategy
Regeneration or reactivation of spent activated carbon can significantly reduce environmental impact compared with virgin production in many scenarios by lowering raw material demand and reducing lifecycle energy intensity, though exact reductions depend on regeneration efficiency, transport, and contamination profile.. This makes a strong case for circular carbon management: industrial users who implement on-site or outsourced reactivation programs can dramatically reduce both their environmental footprint and material costs.
Emerging Sustainable Production Methods
Growing awareness of the environmental costs of fossil-based activated carbon has accelerated research into agricultural and waste-based precursors. Activated carbon derived from agricultural residues such as coconut husk, rice husk, sugarcane bagasse, and wood waste can be produced at lower energy cost and with significantly reduced greenhouse gas emissions compared to coal-based equivalents.
Energy consumption varies widely depending on activation method, scale, and feedstock, but on commercial scales, pyrolysis off-gases (including CO2, CO, H2, and CH4) can be captured and used for energy recovery, further reducing the net environmental impact.
End-of-Life Disposal
Unused or non-contaminated activated carbon may often be managed as non-hazardous material, but classification depends on jurisdiction and contaminant exposure. However, activated carbon that has adsorbed hazardous substances — mercury, heavy metals, chlorinated compounds — must be disposed of according to applicable hazardous waste regulations at approved facilities.
This end-of-life challenge is particularly acute for mercury-laden carbon from power plants and medical incinerators, which represents an ongoing disposal challenge despite the material’s effectiveness as a mercury sorbent.
Safety Considerations for Activated Carbon
While activated carbon is non-toxic in its pure form, handling and use — particularly in industrial, powdered, or medical contexts — carry specific safety considerations that practitioners should be aware of.
Industrial Handling and Dust Hazards
Activated carbon, especially in powdered form (PAC), generates fine carbon dust during handling. This dust can cause mild irritation to the upper respiratory tract, eyes, and skin. Workers in environments with elevated airborne carbon dust concentrations should use appropriate respiratory protection (NIOSH-approved respirators), safety goggles, and protective clothing.
Specific regulatory guidance may vary, but general particulate or nuisance dust exposure standards are often applied when substance-specific limits are unavailable. Individuals with pre-existing respiratory or cardiovascular conditions are more susceptible to dust-related effects and should take additional precautions.
Fine carbon dust dispersed in air in sufficient concentrations, in the presence of an ignition source, presents a dust explosion hazard. Storage and handling areas should be kept free of ignition sources, including open flames, sparks, and smoking. Carbon is difficult to ignite directly but can smolder slowly without producing visible flames, and smoldering carbon in enclosed spaces can generate dangerous levels of carbon monoxide.
Oxygen Depletion in Confined Spaces
Activated carbon in confined spaces may contribute to oxygen-deficient atmospheres due to adsorption effects or displacement mechanisms under certain storage and process conditions. Workers entering enclosed storage spaces, silos, or vessels containing activated carbon — particularly damp or recently wetted carbon — face a serious oxygen deficiency hazard. All confined space entry procedures should include pre-entry air monitoring for both oxygen levels and carbon monoxide, and appropriate respiratory protection or supplied-air apparatus should be used.
Medical Contraindications for Ingested Activated Charcoal
While activated charcoal is a proven treatment for certain types of poisoning, it is not universally appropriate and carries specific contraindications identified by the American Academy of Clinical Toxicology (AACT):
- Patients with an unprotected airway or depressed level of consciousness (risk of pulmonary aspiration)
- Cases where the ingested toxin is not meaningfully adsorbed by carbon — including metals, acids, alkalis, electrolytes, and alcohols
- Situations where GI perforation or hemorrhage risk is elevated, or where endoscopy is planned
- Ingestion of hydrocarbons with high aspiration potential
- Patients with intestinal blockages or conditions causing slow gut motility
Aspiration is a major medical risk during activated charcoal administration and may cause severe pulmonary complications; airway protection is therefore a critical clinical consideration.
Additionally, activated charcoal binds to many oral medications — including birth control pills, antidepressants, and cardiac medications — reducing their absorption and efficacy. Medication timing and safety should be guided by medical or pharmaceutical advice depending on therapeutic context.. Long-term daily use of oral activated charcoal is not recommended, as it can interfere with nutrient absorption and is associated with an increased risk of bowel obstruction.
It is critical to distinguish between medical-grade activated charcoal and common grilling charcoal. Charcoal briquettes contain additives and binders that are toxic if ingested. Only specifically manufactured, food- or pharmaceutical-grade activated charcoal should ever be consumed.
Performance Data and Quantitative Benchmarks
The original article describes the structural properties of activated carbon qualitatively. The following benchmarks provide concrete performance reference points drawn from published industrial and research data.
Surface Area
High-quality activated carbon commonly exhibits internal surface areas in the range of roughly 500–1500 m²/g, with some specialized grades exceeding this depending on precursor and activation method.. Activated carbon surface area varies widely by material and process, and many commercial or research materials span broad ranges both below and above 1000 m²/g, with pore volume and pore size distribution highly dependent on feedstock and activation process . This extraordinary surface area per unit mass is what makes activated carbon one of the highest-performing adsorbents known to materials science.
Contaminant Removal Efficiency
Activated carbon can achieve high removal efficiency for many VOCs and organic contaminants under properly designed conditions, though actual performance varies substantially by compound chemistry, humidity, residence time, carbon type, and system design.. For drinking water applications, activated carbon can be highly effective for chlorine and many organic contaminants, but reported efficiencies depend heavily on specific contaminant properties, contact time, carbon condition, and operational parameters. However, these figures are highly dependent on contaminant type, contact time, carbon quality, and system design. Excessive flow rates or insufficient carbon bed depth will significantly limit effectiveness even with appropriate carbon selection.
Filter Lifespan Summary
The table below summarizes typical activated carbon filter lifespans by application type under normal usage conditions:
- Residential water pitcher filters: 40-100 gallons, or approximately 2-3 months
- Refrigerator water filters: approximately 6 months (manufacturer-recommended)
- Under-sink point-of-use filters: 6 months to 1 year
- Whole-house water systems: 1-2 years
- Air purifier carbon filters: 3-12 months depending on VOC load
- High-contamination industrial systems: significantly shorter; monitoring-based replacement recommended
These figures represent guidelines only. Higher contaminant concentrations, elevated flow rates, and continuous operation all accelerate saturation and reduce effective service life. Many modern filtration systems incorporate performance sensors or indicator systems to signal replacement based on actual usage rather than fixed time intervals.
Market Size and Industry Context
Activated carbon is a substantial and growing global industry driven by increasingly stringent environmental regulations, expanding water treatment infrastructure, and rising industrial demand across multiple sectors.
Global Market Overview
Global activated carbon market estimates vary significantly depending on source, segmentation methodology, and forecast model, but most industry analyses project substantial long-term growth driven by environmental and industrial demand. Water treatment is widely recognized as one of the dominant application segments globally.
Asia-Pacific is generally recognized as the largest regional market due to industrialization, population growth, and environmental infrastructure expansion, while North America and Europe remain major markets supported by regulatory frameworks and established industrial demand.
Key Demand Drivers
Several macro trends are accelerating activated carbon demand globally:
- Tightening regulations on industrial air and water pollution in North America and Europe, requiring broader use of activated carbon in flue gas treatment, municipal water, and wastewater processing
- Growing municipal water treatment infrastructure in developing economies
- Rapidly expanding PFAS (per- and polyfluoroalkyl substance) remediation requirements, which have identified activated carbon as a primary treatment technology
- Growth in food and beverage processing applications, where activated carbon is used for color, odor, and taste removal in products such as fruit juices and sugar processing
- Pharmaceutical and healthcare sector growth, driving demand for high-purity activated carbon in drug production and medical applications
- Increasing consumer awareness and residential demand for home water and air filtration products
Feedstock and Product Trends
Coal-based activated carbon has historically represented a major share of global production due to established supply chains and industrial scale, though exact market share varies by source and region.
Biomass-derived carbons such as coconut shell-based products are often associated with growing demand in certain markets due to sustainability considerations and performance advantages for some applications..
PAC and GAC both represent major product categories, with market distribution varying by application, geography, and industry sector.
Reactivated carbon is an emerging growth area as operators seek to reduce both costs and environmental footprint through circular carbon management.
Summary
This article briefly explored what activated carbon is, how it is made, and how it is used in industry. We hope that this article helped readers understand the vital importance of activated carbon in our modern lives and how such a simple material can create cleaner air, water, and consumables. To learn more, visit the Thomas Network, where we have over 550 activated carbon suppliers listed.