Carbon
fullCarbon is two of the three master variables of water treatment: inorganic carbon (dissolved CO₂, bicarbonate, carbonate) sets pH, alkalinity, buffering, corrosion and scaling, and organic carbon (TOC, DOC, BOD, COD) is the load that biological treatment removes, the precursor that chlorine turns into trihalomethanes and the parameter that EU, US and every discharge permit regulate; carbon dioxide and activated carbon are also treatment reagents.
Typical wastewaters
- municipal sewage biodegradable and refractory organic carbon measured as BOD₅ 110 to 350, COD 250 to 800 and TOC 80 to 260 mg/L, with bicarbonate alkalinity 50 to 200 mg/L as CaCO₃ low to high strength typical composition
- chemical sector effluent dissolved organic carbon, refractory fraction dominant after biological treatment; TOC 10 to 33 and COD 30 to 100 mg/L as yearly averages, halogenated organics as AOX 0.20 to 1.0 mg/L
- textile dyeing and finishing and leather tanning organic load measured as BOD₅ and COD (textile 150, 80, 40 and leather 250, 150, 100 mg/L COD by level), halogenated fraction as AOX in textile
- high strength industrial wastewater and sludge digestion organic carbon converted anaerobically to methane and CO₂ (about 0.35 m₃ methane per kg COD removed); the effluent needs aerobic polishing
1 · Identity
- Symbol, number
- C, 6
- Oxidation states in water
- +4 as dissolved carbon dioxide, carbonic acid, bicarbonate and carbonate (dissolved inorganic carbon, DIC), and as the solid carbonates that scale and dissolve; -4 as methane in anoxic water and digester gas; every state between in dissolved and particulate organic matter, from -3 in methyl groups through 0 in carbohydrate to +3 in carboxylic acids, whose average state sets the ratio of COD to organic carbon; 0 as the activated carbon that adsorbs organics and reduces chlorine.
- Note
- The element entry carries the allotropes, the carbon cycle, CO₂ in the atmosphere and the fossil carbon economy. This chapter is the carbonate system, the organic carbon parameters, the reagents and the limits. Chlorine's by-products are in the chlorine chapter; nitrification's alkalinity demand is in the nitrogen chapter; struvite and calcium carbonate softening chemistry are in the magnesium and calcium chapters, with the carbonate equations kept here.
2 · Occurrence in water
- Natural sources
- Inorganic carbon enters water from atmospheric CO₂ (about 390 ppm by 2013 in the element entry), from respiration of organic matter in soil, where CO₂ partial pressures reach ten to a hundred times atmospheric, and from dissolution of limestone and dolomite by that CO₂; the result is the bicarbonate alkalinity of nearly all fresh water. Organic carbon comes from the decay of vegetation and algae (humic and fulvic acids, the natural organic matter that colours water and reacts with chlorine) and from soil leaching; groundwater usually carries little (the US rule treats source TOC below 2 mg/L as needing no precursor removal), surface water more.
- Anthropogenic sources
- Sewage and industrial organic loads measured as BOD, COD and TOC; methane from landfills, digesters and anoxic sediments; carbon dioxide dosed for recarbonation and pH control; activated carbon and coke; halogenated organics measured as AOX; carbon dioxide from the burning of fossil carbon, which is acidifying the ocean (element entry).
| matrix | typical range | note |
|---|---|---|
| surface water, source water TOC | 2.0 to above 8.0 mg/Lregulatory bands, not a survey | the bands of the US enhanced coagulation table (2 to 4, 4 to 8, above 8 mg/L); source or treated water below 2.0 mg/L is exempt from TOC removal, which is where most groundwater sits |
| fresh water, alkalinity | 0 to above 240 mg/L as CaCO3regulatory bands | the bands of the same table (0 to 60, 60 to 120, 120 to 240, above 240 mg/L as CaCO₃), which are also the practical range of natural water |
| seawater, dissolved inorganic carbon | 28 mg/Lsingle figure | oceanic abundance figure for carbon, Jefferson Lab via PubChem, quoted in the element entry; essentially all bicarbonate and carbonate |
| untreated municipal wastewater | BOD₅ 110 to 350; COD 250 to 800; TOC 80 to 260; alkalinity 50 to 200 mg/L (alkalinity as CaCO3) textbook typical values, not a survey | low, medium and high strength typical composition, Metcalf and Eddy 5th ed. Table 3-18, from the chapter and not re-read |
| industrial wastewater, chemical sector effluent after treatment | TOC 10 to 33; COD 30 to 100 mg/L achievable emission levels, not raw effluent | the CWW BAT-AEL ranges as yearly averages; the upper ends may reach 100 mg/L TOC or 300 mg/L COD where influent TOC exceeds 2 g/L with refractory organics and the abatement efficiency is high |
3 · Speciation
Dissolved CO₂ hydrates slowly to carbonic acid (less than 1 percent of the dissolved gas is H₂CO₃), which dissociates with pKa₁ 6.35 and pKa₂ 10.33 at 25 C when the dissolved gas and the acid are lumped as H₂CO₃*. So below pH 6.3 dissolved CO₂ dominates, between 6.3 and 10.3 bicarbonate, above 10.3 carbonate; nearly all natural water sits in the bicarbonate field, which is why alkalinity and bicarbonate are almost the same number there. In an open system the CO₂ is fixed by Henry's law and the atmosphere; in a closed pipe or aquifer the total inorganic carbon is fixed and pH moves with acid or base added (Stumm and Morgan chapter 4). Organic carbon is not a species but a continuum: dissolved (DOC, through a 0.45 µm filter) and particulate, biodegradable (BOD) and refractory, with the humic fraction that absorbs at 254 nm being the chlorine reactive part.
| condition | dominant species | note |
|---|---|---|
| pH below 6.3 | CO₂ (aq) and H₂CO₃, no carbonate alkalinity | acid mine water, soft upland water, soda water, reverse osmosis permeate before remineralisation |
| pH 6.3 to 10.3 | HCO₃⁻ | all normal natural and treated water; alkalinity equals bicarbonate to within a few percent |
| pH above 10.3 | CO₃²⁻ | lime softening, lime stabilised sludge, caustic effluent; calcium and magnesium precipitate here |
| anoxic sediment, digester, landfill | CH₄ with CO₂ and HCO₃⁻ | the end products of fermentation; digester gas 60 to 70 percent methane (Metcalf and Eddy chapter 10) |
| calcite saturation | CaCO₃ (s) precipitating or dissolving | the Langelier index is the pH difference from saturation; positive scales, negative dissolves (MWH chapter 22) |
- Solubility
- CO₂ dissolves according to Henry's law, about 10⁻1.5 mol per litre per atmosphere at 25 C, so air equilibrated water holds about 10⁻5 mol/L of CO₂ and rain sits near pH 5.6 (Stumm and Morgan chapter 4). Calcium carbonate is sparingly soluble and its solubility rises with CO₂ partial pressure and falls with temperature, the reason boilers, hot water pipes and reverse osmosis concentrates scale. Methane is a sparingly soluble gas that escapes on aeration.
- Hydrolysis
- Carbonate is a base: it takes a proton from water to give bicarbonate and hydroxide, so soda ash solutions are alkaline; bicarbonate is amphoteric and buffers between pH 6 and 10.
- Complexation
- Carbonate and bicarbonate complex calcium, magnesium and the transition metals (CaCO₃ and MgCO₃ ion pairs, uranyl carbonates that keep uranium mobile) and natural organic matter binds iron, aluminium, copper and lead, slowing their precipitation and passing them through filters (iron chapter); constants not quoted.
- Precipitates
- CaCO₃ (calcite, aragonite) the universal scale; MgCO₃ only in brines, Mg(OH)₂ instead at high pH; FeCO₃ siderite in anoxic groundwater; MnCO₃; the metal carbonates of soda ash precipitation of heavy metals (sodium chapter).
4 · Role in treatment
5 · Removal and control
- Efficiency
- 85 to 95 percent of BOD₅; COD and TOC less because refractory carbon remains
- Interferences
- toxic loads, low temperature, nutrient deficiency; oxygen transfer is the cost
- Efficiency
- COD removal 70 to 90 percent for suitable wastes; effluent needs aerobic polishing
- Interferences
- sulfate, ammonia, pH below 6.5, temperature
- Efficiency
- 15 to 50 percent required; humic waters give more, low SUVA waters less
- Interferences
- high alkalinity buffers the pH drop; low SUVA carbon is not amenable and can be waived
- Efficiency
- to the µg/L level for target organics while capacity lasts; a fraction of bulk TOC only
- Interferences
- natural organic matter, chlorine, biological growth in the bed
- Efficiency
- not quantified in the source
- Interferences
- bromide gives bromate (bromine chapter)
- Efficiency
- DOC rejection high for NF and RO; not quantified here
- Interferences
- organic fouling of the membrane
- Efficiency
- alkalinity to below 10 mg/L as CaCO₃ with acid and degassing (general)
6 · Analytics
| method | standard | detection limit | note |
|---|---|---|---|
| total and dissolved organic carbon (TOC, DOC) | Standard Methods 5310 B (high temperature combustion), C (persulfate UV), D; ISO 8245 and EN 1484; EPA 415.3 | about 0.1 mg/L in practice (general); not read | DOC after 0.45 µm filtration; inorganic carbon purged after acidification or measured and subtracted; the EU allows TOC in place of oxidisability and the UWWTD in place of COD |
| chemical oxygen demand (COD) | Standard Methods 5220 B, C, D; ISO 6060 (dichromate reflux), ISO 15705 (sealed tube); EPA 410.4 | about 5 mg/L for the low range (general); not read | dichromate in sulfuric acid with silver catalyst and mercury to mask chloride; chloride interferes above the mercury capacity, which is why the CWW BREF prefers TOC (no very toxic reagents) |
| biochemical oxygen demand (BOD₅, CBOD₅) | Standard Methods 5210 B; ISO 5815-1; EPA 405.1 | about 2 mg/L (general); not read | five days at 20 C in the dark; a nitrification inhibitor gives CBOD₅ (the UWWTD reference method adds one); seeded dilution water for disinfected effluent |
| alkalinity | Standard Methods 2320 B; ISO 9963-1 and 9963-2 | about 1 mg/L as CaCO₃ | titration with strong acid to pH 4.5 (total) and 8.3 (carbonate); reported as CaCO₃ |
| free carbon dioxide | Standard Methods 4500-CO₂ C (titration) and D (nomograph from pH, alkalinity, temperature and TDS) | not applicable | measure in the field or calculate from pH and alkalinity; CO₂ is lost from the bottle |
| UV absorbance and SUVA | Standard Methods 5910 B | not applicable | UV₂₅₄ in per metre divided by DOC in mg/L gives SUVA in L per mg per m; 2.0 or below is the US exemption from enhanced coagulation |
| adsorbable organic halogen (AOX) | ISO 9562 | not read | the CWW BAT-AEL and ZDHC textile parameter for halogenated organic carbon |
| methane | headspace gas chromatography | not read | no standard method read |
- Sampling pitfalls
- Fill BOD and TOC bottles without headspace and keep cold; BOD samples must be set up within 48 hours (Standard Methods); TOC bottles must be carbon clean glass with acid preservation for total carbon only where inorganic carbon will be purged. Chlorinated samples need quenching before BOD (and seeding). Alkalinity and CO₂ change with degassing, so titrate promptly or in the field. COD on high chloride samples (seawater, brines) is unreliable; use TOC. Filter for DOC at once, in the field where possible.
7 · Regulatory limits
Limits change, and many are set locally. Treat these as the published values to start from, not as your compliance target: check the standard in force at your site and the numbers written into your own permit.
| body | limit | note |
|---|---|---|
| WHO GDWQ 4th ed. with addenda (2022) | no guideline | no guideline for TOC, alkalinity or carbon dioxide; the chlorination by-products (trihalomethanes, haloacetic acids) have guideline values in the chlorine chapter |
| EU DWD 2020/2184, total organic carbon | not set | Annex I Part C indicator parameter with the parametric value written as no abnormal change; need not be measured for supplies under 10,000 m₃ a day |
| EU DWD 2020/2184, oxidisability | 5.0 mg/L O2 | Annex I Part C indicator parameter (permanganate index); need not be measured if TOC is analysed |
| US EPA, total organic carbon | not set | treatment technique, not an MCL: Step 1 TOC removal of 15 to 50 percent by enhanced coagulation or enhanced softening for surface water systems with conventional filtration, by source TOC and alkalinity (40 CFR 141.135); TTHM 0.080 and HAA₅ 0.060 mg/L in the chlorine chapter |
| body | limit | note |
|---|---|---|
| EU CWW BREF BAT-AEL (Decision 2016/902), TOC | 10 to 33 mg/L | yearly average, direct discharge to a receiving water; either the TOC or the COD AEL applies, TOC preferred; upper end up to 100 mg/L TOC where influent TOC exceeds 2 g/L with a high proportion of refractory compounds and abatement efficiency is high |
| EU CWW BREF BAT-AEL (Decision 2016/902), COD | 30 to 100 mg/L | yearly average; up to 300 mg/L under the same conditions; no BAT-AEL for BOD, indicative BOD₅ at or below 20 mg/L from a biological plant; TSS 5.0 to 35 mg/L; AOX 0.20 to 1.0 mg/L |
| EU UWWTD 2024/3019, Annex I Table 1, secondary treatment | BOD₅ 25; COD 125; TOC 37; TSS 35 mg/L (BOD and COD as O2) time-sensitive: recast in force with transposition deadlines | or minimum reductions of 70 to 90 percent BOD₅, 75 percent COD or TOC, 90 percent TSS; BOD₅ at 20 C without nitrification; the recast repeals Directive 91/271/EEC |
| US EPA 40 CFR 133.102, secondary treatment | BOD₅ 30 (30-day average), 45 (7-day average), 85 percent removal; or CBOD₅ 25 and 40 mg/L | with suspended solids 30 and 45 mg/L and pH 6.0 to 9.0 |
| Abu Dhabi ADS 23/2017, discharge to the marine environment (EAD) | BOD₅ 30; COD 100; TOC 75 mg/L region-dependent; marine discharge only | Table 1 maximum allowable concentrations |
| Abu Dhabi DoE Trade Effluent Control Regulations 2022, discharge to sewer | COD 1000 mg/L region-dependent; sewer discharge | Table A₁; no BOD or TOC row for sewer discharge |
| sector | body | limit | note |
|---|---|---|---|
| textile and leather | ZDHC Wastewater Guidelines v₂.1 (2022), BOD₅ | textile 30, 15, 8; leather 50, 30, 20 mg/L | Foundational, Progressive, Aspirational; Table 3 |
| textile and leather | ZDHC Wastewater Guidelines v₂.1 (2022), COD | textile 150, 80, 40; leather 250, 150, 100 mg/L | Foundational, Progressive, Aspirational; AOX textile only 3, 0.5, 0.1 mg/L |
8 · Health and environmental effects
- Toxicity
- Organic carbon as a bulk parameter is not toxic; its health significance in drinking water is as the precursor of chlorination by-products and as the substrate for regrowth. Carbon dioxide in water is harmless to drink (carbonated bottled water may sit below pH 4.5 under the EU DWD) but the gas is an asphyxiant in confined spaces such as lime softening and CO₂ dosing rooms; methane is an explosion hazard; carbon monoxide is in the element entry.
- Bioaccumulation
- Not applicable to bulk carbon; the persistent halogenated organics counted in AOX include bioaccumulating substances treated under their own entries.
- Ecotoxicity
- Biodegradable organic carbon kills by oxygen depletion, not by toxicity: the reason for BOD limits, the UWWTD and the secondary treatment rule. US EPA has no numeric aquatic criterion for organic carbon; dissolved oxygen is in the oxygen chapter.
Flags
- The carbonate constants, Henry's constant and the CaCO₃ equations are cited to Stumm and Morgan chapter 4 from memory of the text, not re-read this session.
- The municipal wastewater composition is Metcalf and Eddy Table 3-18 from memory of the chapter; the representative organic formula and the methane yield are from chapters 7 and 10 likewise.
- The TOC and alkalinity bands given as concentrations are the US regulatory bands, not survey data.
- The UWWTD recast values are read from the 2024 Directive; the 1991 Directive tables (BOD₅ 25 mg/L, COD 125, TSS 35, TN 15 and 10, TP 2 and 1) were not re-read and are not quoted.
- Detection limits for the organic carbon methods are general laboratory practice, not read.
- Abu Dhabi values cover two media (marine outfall BOD₅ 30, COD 100, TOC 75 mg/L; sewer COD 1000 mg/L); other GCC states not read.
Gaps
- No survey of TOC, DOC or alkalinity in natural waters was read; regulatory bands stand in.
- No activated carbon isotherm constants, carbon use rates or GAC bed lives are quoted.
- The WHO GDWQ chapter 10 text on organic carbon, taste and odour and the WHO position on TOC were not read.
- Chlorination by-product formation kinetics and the trihalomethane formation potential test are not covered here; see the chlorine chapter.
- The 1991 UWWTD tables, US industrial category BOD and COD limits (OCPSF part 414, textile part 410, pharma part 439) and the EU FDM BREF were not read.
- Other GCC discharge standards were not read.
Sources
Metcalf and Eddy, Wastewater Engineering: Treatment and Resource Recovery, 5th ed. (McGraw-Hill, 2014), chapter 2 (BOD, COD, TOC), chapter 3 Table 3-18 (typical composition of untreated wastewater), chapter 7 (stoichiometry of aerobic oxidation) and chapter 10 (anaerobic digestion)
MWH, Water Treatment: Principles and Design, 3rd ed. (Wiley, 2012), chapter 15 (adsorption), chapter 16 (ion exchange, decarbonation), chapter 17 (reverse osmosis), chapter 22 (corrosion indices, lime softening, recarbonation)
Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Annex I Parts B and C
40 CFR 141.135, Treatment technique for control of disinfection byproduct precursors (Step 1 TOC removal table, enhanced coagulation target pH)
Commission Implementing Decision (EU) 2016/902 establishing BAT conclusions for common waste water and waste gas treatment/management systems in the chemical sector (CWW), BAT 12 Tables 1 and 2 with footnotes
Directive (EU) 2024/3019 concerning urban wastewater treatment (recast), Annex I Part B Tables 1 and 2
40 CFR 133.102, Secondary treatment (BOD5, suspended solids, pH)
Abu Dhabi Specification ADS 23/2017, Environmental Specifications for Land-Based Liquid Discharges to the Marine Environment (Environment Agency Abu Dhabi), Table 1
Abu Dhabi Department of Energy, Trade Effluent Control Regulations 2022 (DoE/PD/R01/005, effective 1 January 2022), Schedule A Tables A1, A2 and A4
ZDHC Wastewater Guidelines Version 2.1 (November 2022), Table 3 conventional parameters and anions
US EPA, Alternative Disinfectants and Oxidants Guidance Manual, EPA 815-R-99-014 (April 1999), chapter 3 (ozone by-products, AOC and BDOC)
WHO GDWQ 4th ed. with addenda (2022), chapter 12 fact sheets read this session (pp. 350, 402, 452, 462, 470): no TOC guideline; GAC as achievable treatment in the organic chemical sheets
Standard Methods for the Examination of Water and Wastewater (online edition), 2320 alkalinity, 4500-CO2, 5210 BOD, 5220 COD, 5310 TOC, 5910 UV absorbance
The Element Book, entries for carbon (atmospheric CO2, carbonates, activated charcoal, BOD and COD narrative) (data/elements/C.json, data/reference/text/C.json)
Identity
- Name and symbol
- Carbon, C
- Atomic number
- 6 protons
- Position
- group 14 · period 2 · p-block · polyatomic nonmetal
- CAS number
- atomic carbon: 7440-44-0; graphite: 7782-42-5; diamond: 7782-40-3
Atomic structure
- Atomic mass
- 12.0107 u
- Electron configuration
- 1s² 2s² 2p²
[He] 2s²²p² - Electrons per shell
- 2, 4
- Valence electrons
- 4 outer shell
| isotope | mass (u) | abundance |
|---|---|---|
| 12C | 12.0000000(00) | 98.93 % |
| 13C | 13.00335483507(23) | 1.07 % |
Physical properties
- State at room temperature
- Solid
- Melting point
- 3,823 K (3,549.85 °C)
- Boiling point
- 4,098 K (3,824.85 °C)
- Density
- 2.267 g/cm3
- Appearance
- graphite: black, metallic-looking; diamond: clear
- Thermal conductivity
- graphite: 119 to 165 W/(m·K)
- Electrical resistivity
- graphite: 7.837 µΩ·m
- Electrical conductivity
- 127,599.847 S/m
- Crystal structure
- simple hexagonal
- Molar heat capacity
- 8.517 J/(mol·K)
Chemical properties
- Oxidation states
- +4, +2, -4
- Electronegativity
- 2.55 (Pauling Scale)
- Ionisation energy
- 11.26 eV
1st 1,086.5, 2nd 2,352.6, 3rd 4,620.5 kJ/mol - Electron affinity
- 1.263 eV
- Atomic radius
- van der Waals 170 pm
- Ionic radius
- C⁴⁺ 16 pm
- Reactivity
- A nonmetal with four valence electrons that chains into millions of compounds, yet the element itself (graphite, diamond) is comparatively unreactive at room temperature and resists all but the strongest oxidisers; graphite is the more reactive form.
- with water
- Does not react at ordinary temperatures; red-hot carbon reacts with steam to carbon monoxide and hydrogen, the coal-gas reaction:
- with oxygen, air
- Stable in air at room temperature; at high temperature it burns to carbon dioxide (or monoxide when oxygen is short) and strips oxygen from metal oxides, the basis of iron smelting:
- with acids
- No reaction with hydrochloric or sulfuric acid; graphite is oxidised by hot concentrated nitric acid to mellitic acid.
- with halogens
- No reaction with chlorine; fluorine attacks lamp black at room temperature to carbon tetrafluoride and graphite above
- Typical compounds
- CO₂ carbon dioxide product of combustion and respiration; carbonic acid in water
- CO carbon monoxide toxic gas that binds haemoglobin; smelting reductant
- CH₄ methane simplest hydrocarbon; natural gas
- CaCO₃ calcium carbonate limestone, the great carbon store in rocks
- CCl₄ carbon tetrachloride chlorinated solvent; does not hydrolyse
- C₂H₂ acetylene triple-bonded fuel gas for oxy-acetylene welding
Occurrence, production and use
- Crustal abundance
- 2.00×102 milligrams per kilogram
- Oceanic abundance
- 2.8×101 milligrams per liter
- Occurrence and sources
- dissolved in seawater about 28 mg/L; crustal estimate 200 mg/kg (Jefferson Lab figures via PubChem)
- hydrocarbons: natural gas, crude oil, oil shale, coal fossilised organic matter; mostly used as fuel, a small fraction as petrochemical feedstock
- carbonates: limestone, chalk, dolomite, magnesite, siderite great rock masses; limestone is the raw material for lime and cement
- natural graphite (flake, amorphous, lump) China, Madagascar, Mozambique, Brazil, Tanzania, Canada, India; world resources exceed 800 million tonnes
- carbon dioxide atmosphere at about 390 ppm (2013) and dissolved in all natural waters
- Extraction, production
- Steam reforming of natural gas to synthesis gas, the gateway from fossil carbon to ammonia, methanol and hydrogen
Delta H0 = 206 kJ/mol, endothermic, over nickel catalyst at 400 to 600 degrees C inlet (AAF BREF, PDF p68); the carbon monoxide is then shifted, p69), and the CO2 removed, which is where the fertiliser industry's process CO2 comes from.
Mining and beneficiation of natural graphite; spherical graphite for lithium-ion anodesPhysical processing. New flake mines opened in Brazil and Tanzania in 2024 and spherical graphite plants in the United States (USGS, printed pp. 84 to 85).
- Uses
Amorphous carbon is formed when a material containing carbon is burned without enough oxygen for it to burn completely. This black soot, also known as lampblack, gas black, channel black or carbon black, is used to make inks, paints and rubber products. It can also be pressed into shapes and is used to form the cores of most dry cell batteries, among other things.
Graphite, one of the softest materials known, is a form of carbon that is primarily used as a lubricant. Although it does occur naturally, most commercial graphite is produced by treating petroleum coke, a black tar residue remaining after the refinement of crude oil, in an oxygen-free oven. Naturally occurring graphite occurs in two forms, alpha and beta. These two forms have identical physical properties but different crystal structures. All artificially produced graphite is of the alpha type. In addition to its use as a lubricant, graphite, in a form known as coke, is used in large amounts in the production of steel. Coke is made by heating soft coal in an oven without allowing oxygen to mix with it. Although commonly called lead, the black material used in pencils is actually graphite.
Diamond, the third naturally occurring form of carbon, is one of the hardest substances known. Although naturally occurring diamond is typically used for jewelry, most commercial quality diamonds are artificially produced. These small diamonds are made by squeezing graphite under high temperatures and pressures for several days or weeks and are primarily used to make things like diamond tipped saw blades. Although they posses very different physical properties, graphite and diamond differ only in their crystal structure.
A fourth allotrope of carbon, known as white carbon, was produced in 1969. It is a transparent material that can split a single beam of light into two beams, a property known as birefringence. Very little is known about this form of carbon.
Large molecules consisting only of carbon, known as buckminsterfullerenes, or buckyballs, have recently been discovered and are currently the subject of much scientific interest. A single buckyball consists of 60 or 70 carbon atoms (C60 or C70) linked together in a structure that looks like a soccer ball. They can trap other atoms within their framework, appear to be capable of withstanding great pressures and have magnetic and superconductive properties.
Carbon-14, a radioactive isotope of carbon with a half-life of 5,730 years, is used to find the age of formerly living things through a process known as radiocarbon dating. The theory behind carbon dating is fairly simple. Scientists know that a small amount of naturally occurring carbon is carbon-14. Although carbon-14 decays into nitrogen-14 through beta decay, the amount of carbon-14 in the environment remains constant because new carbon-14 is always being created in the upper atmosphere by cosmic rays. Living things tend to ingest materials that contain carbon, so the percentage of carbon-14 within living things is the same as the percentage of carbon-14 in the environment. Once an organism dies, it no longer ingests much of anything. The carbon-14 within that organism is no longer replaced and the percentage of carbon-14 begins to decrease as it decays. By measuring the percentage of carbon-14 in the remains of an organism, and by assuming that the natural abundance of carbon-14 has remained constant over time, scientists can estimate when that organism died. For example, if the concentration of carbon-14 in the remains of an organism is half of the natural concentration of carbon-14, a scientist would estimate that the organism died about 5,730 years ago, the half-life of carbon-14.
There are nearly ten million known carbon compounds and an entire branch of chemistry, known as organic chemistry, is devoted to their study. Many carbon compounds are essential for life as we know it. Some of the most common carbon compounds are: carbon dioxide (CO2), carbon monoxide (CO), carbon disulfide (CS2), chloroform (CHCl3), carbon tetrachloride (CCl4), methane (CH4), ethylene (C2H4), acetylene (C2H2), benzene (C6H6), ethyl alcohol (C2H5OH) and acetic acid (CH3COOH).
- Petrochemicals and polymers: hydrocarbon feedstock for polymers, fibres, paints, solvents and plastics; ethylene chlorination to , and cracking to p528); ethylene oxidation to ethylene oxide, C2H4 + 1/2 p400); methanol oxidation to formaldehyde, CH3OH + 1/2 p375); process CO2 with ammonia to urea, , then p352)
- Iron and steel: coke and charcoal as reductant and fuel in smelting; natural graphite in refractories, steelmaking, brake linings, lubricants and powdered metals
- Batteries: spherical and synthetic graphite anodes for lithium-ion batteries; US natural graphite consumption fell 21 percent in 2024 as Chinese synthetic graphite undercut it
- Mining and energy: coal, oil and natural gas extracted as fuels; combustion raised atmospheric CO2 from 280 ppm to 390 ppm
- Phosphorus and inorganic chemicals: coke as reductant in the electric phosphorus furnace, p279)
- Water treatment: activated carbon adsorption and filtration of organics in industrial waste water and air; carbon dioxide dosed to lower pH in neutralisation
- Advanced materials: carbon fibre for aircraft, rockets and sports goods; industrial diamond for cutting and drilling, diamond films
- Safety, toxicity
- GHS classification, signal word Warning
- H319 Causes serious eye irritation Serious eye damage/eye irritation
- H335 May cause respiratory irritation Specific target organ toxicity, single exposure; Respiratory tract irritation
Discovery and name
- Discovered by
- Egyptians and Sumerians
- Discovered
- 3750 BCE
- First isolated
- not in sources
- Named by
- not in sources
- Origin of the name
- from the Latin carbo for coal and charcoal
Conventions
Valence electrons are counted by the usual convention: the outer shell for s- and p-block elements, ns and (n-1)d for the d-block, ns, (n-1)d and (n-2)f for the f-block. Lanthanides and actinides are placed in the f-block with no group number. Electrical conductivity is the reciprocal of the printed resistivity. Ionic radii are Shannon effective radii, six-coordinate unless noted. Where a field reads “not in sources” the value was not found; it is a gap, not a zero. Regulatory limits are the published values and change often, so check the standard in force at your site and the numbers written into your own permit before you design to them.
Data
Element records, isotopes, radii and the descriptive text come from PubChem (NCBI), the Los Alamos National Laboratory periodic table, IUPAC CIAAW and the IAEA Atomic Mass Data Center. Appearance, thermal conductivity, electrical resistivity, crystal structure, discovery and the origin of each name come from Wikipedia and Periodic-Table-JSON, used under CC BY-SA 4.0. Hazard classifications come from the ECHA C&L inventory via PubChem. Ionic radii follow R. D. Shannon (1976). The water chapters cite their own sources at the foot of each entry, and are written to the level of Snoeyink and Jenkins, Stumm and Morgan, MWH's Water Treatment and Metcalf and Eddy.