Chromium
fullChromium is regulated everywhere (WHO 50 µg/L total, EU 25 µg/L from 2036, US 0.1 mg/L total, California 10 µg/L hexavalent), and everything about it in water turns on whether it is the soluble, carcinogenic chromate anion Cr(VI) or the insoluble, precipitable Cr(III); tannery, plating and chrome dye effluents are its industrial homes.
Typical wastewaters
- electroplating and metal finishing Cr(VI) as chromate and dichromate from chromic acid baths in plating rinse water; reduced then precipitated as Cr(OH)₃
- leather tanning Cr(III) from basic chromium sulfate tanning floats, precipitated as Cr(OH)₃ at pH 8 or above and recoverable
- textile dyeing with chromium mordant or chromium containing dyes Cr(III) from chrome mordant and metal complex dyeing of wool
- wool scouring total chromium, mass limited per 1000 kg of wool
- cooling tower blowdown (once chromate treated) chromate CrO₄²⁻ from chromate corrosion inhibitors; 0.2 mg/L total chromium limit
- chemical sector effluent (chromium compound production) total chromium 5.0 to 25 µg/L after treatment; may not apply where the load comes from chromium-organic compound production
- steel and pulp mills total chromium, the US EPA source list
1 · Identity
- Symbol, number
- Cr, 24
- Oxidation states in water
- +3 as Cr³⁺ and its hydroxy complexes Cr(OH)n^(3-n)+, precipitating as Cr(OH)₃ between about pH 6 and 8 (the element entry) and redissolving only in strong alkali; +6 as chromate CrO₄²⁻, hydrogen chromate HCrO₄⁻ and, at high concentration, dichromate Cr₂O₇²⁻, soluble at every pH and adsorbed poorly.
- Note
- The element entry already sets out the two states and the reduce-then-precipitate rule. This chapter gives the numbers: the limits, the occurrence, the analytical splits and the reactions.
2 · Occurrence in water
- Natural sources
- Weathering and erosion of chromium bearing rocks; high natural chromium, including Cr(VI), in groundwater from mafic and ultramafic volcanic and metamorphic rocks, ophiolite complexes and serpentine rich units (WHO background document). Uncontaminated water is usually below 1 µg/L.
- Anthropogenic sources
- Metal finishing and chromium plating (chromic acid baths), leather tanning with basic chromium sulfate, chrome mordant and metal complex dyeing of wool and textiles, chromate pigments and corrosion inhibitors, cooling tower blowdown (once chromate treated), steel and pulp mills (US EPA source list), landfill leachate, and chromium chemical plants in the ledger's chemical chapter. Pre-chlorination or pre-ozonation in a treatment plant can oxidise Cr(III) to Cr(VI) (WHO).
| matrix | typical range | note |
|---|---|---|
| uncontaminated fresh water and groundwater | below 1 µg/L | total chromium; UK groundwater below 3 µg/L; Netherlands mean 0.7, maximum 5 µg/L |
| surface water, USA | up to 84 µg/L region-dependent, older surveys | Rhine below 10 µg/L; half of Indian stream waters below 2 µg/L |
| drinking water, general | usually below 5 µg/L | England and Wales 2016, more than 12,000 compliance samples: none above 50 µg/L, maximum 15, 95th percentile 1 µg/L; Canada median 2, maximum 18.9 (groundwater) |
| drinking water, hexavalent chromium, USA (UCMR 3, 2013 to 2015) | 0.057 to 7.51 µg/L | present across all states; the majority of states between 0.1 and 1.0 µg/L; Canada and US averages 0.2 to 2 µg/L; UK background Cr(VI) below 0.1 µg/L |
| seawater | 0.04 to 0.5 µg/L | natural total chromium; 0.7 µg/L in the North Sea; PubChem gives 0.3 µg/L (3 x 10⁻4 mg/L) |
| rainwater | 0.2 to below 1 µg/L | average total chromium |
3 · Speciation
Chromium(VI) is an oxyanion: hydrogen chromate HCrO₄⁻ below about pH 6.5, chromate CrO₄²⁻ above it, dichromate only in concentrated acid solutions. It is soluble across the whole pH range, mobile in groundwater, poorly adsorbed except on iron oxides at low pH, and it is what plating and chromate baths discharge. Chromium(III) is a cation that hydrolyses, precipitates as Cr(OH)₃ between about pH 6 and 8 and is adsorbed at relatively high pH (WHO background document), so it leaves water with the sludge. The distribution between the two depends on redox potential, pH, oxidants (chlorine, ozone, manganese oxides) and reductants (organic matter, iron(II), sulfide); Cr(VI) is easily reduced by organic matter in soil (WHO). Treatment therefore reduces Cr(VI) first, or adsorbs it on iron, and precipitates Cr(III); oxidative pre-treatment in a drinking water plant can do the opposite.
| condition | dominant species | note |
|---|---|---|
| oxic water, pH 6 to 9, low organic matter | CrO₄²⁻ (above pH about 6.5) and HCrO₄⁻ | the natural Cr(VI) of serpentine groundwater and the plating rinse anion |
| reducing or organic rich water, pH 6 to 9 | Cr(OH)₃ (s), Cr(OH)₂⁺, Cr bound to organic matter and iron oxides | particulate; passes only as colloid |
| acid effluent, pH below 4 | Cr³⁺ (hexaaqua) dissolved; HCrO₄⁻ and Cr₂O₇²⁻ for Cr(VI) | tannery float and pickle liquors; reduction of chromate is run here |
| strong alkali, pH above 11 | Cr(OH)₄⁻ (chromite anion) | amphoteric redissolution; keep precipitation at pH 8 to 9 |
- Solubility
- Cr(OH)₃ is the controlling solid for Cr(III), least soluble around pH 8 to 9 and redissolving in strong alkali; Cr(VI) has no controlling solid in ordinary water except barium and lead chromate at high concentration. Constants are not quoted because the sources read print none.
- Hydrolysis
- Cr³⁺ hydrolyses to Cr(OH)n^(3-n)+ (WHO notation), so chromium(III) salts are acidic and precipitation consumes alkalinity; HCrO₄⁻ is a weak acid with pKa about 6.5 (Stumm and Morgan chapter 3, from the chapter, not re-read).
- Complexation
- Cr(III) forms inert complexes with organic ligands and adsorbs on iron oxides at higher pH; Cr(VI) adsorbs on ferrihydrite, goethite and iron oxide coated sand, more strongly at low pH (WHO treatment section).
- Precipitates
- Cr(OH)₃ (hydroxide precipitation), chromium in ferric hydroxide sludge after reduction with iron(II), chromite and Cr₂O₃ in aged sludge, barium and lead chromate pigments.
4 · Role in treatment
5 · Removal and control
- Efficiency
- to the BAT-AEL of below 0.3 to 1 mg/L total chromium in tanning and 5 to 25 µg/L in the chemical sector with good solid separation
- Interferences
- excess oxidant, complexing agents holding Cr(III), overshoot to pH above 11
- Efficiency
- not quoted as a figure
- Interferences
- Cr(VI)
- Efficiency
- not quoted
- Interferences
- competing anions
- Efficiency
- 80 to 96 percent (WHO)
- Interferences
- sulfate competition; regenerant brine carries the chromium
- Efficiency
- reverse osmosis 82 to 97 percent; nanofiltration similar
- Interferences
- concentrate disposal
- Efficiency
- not quoted
- Interferences
- oxygen
6 · Analytics
| method | standard | detection limit | note |
|---|---|---|---|
| ICP-MS (total chromium) | EPA 200.8 (mass 52); ISO 17294-2 | EPA 200.8 instrument detection limit 0.07 µg/L scanning, 0.04 µg/L selected ion monitoring; WHO 0.08 to 7 µg/L across ICP-AES, ICP-MS, AES and GFAAS | ArC⁺ and ArO⁺ overlap mass 52 and ArN⁺ mass 54 (EPA 200.8 Table 2); use a collision cell or the correction equations |
| ICP-OES and graphite furnace AAS | EPA 200.7 (205.552 nm); ISO 11885; ISO 15586 | EPA 200.7 instrument detection limit 6.1 µg/L, total recoverable method detection limit 0.004 mg/L; flame AAS 0.5 mg/L (WHO) | WHO recommends FAAS for 0.5 to 20 mg/L and electrothermal AAS below 0.1 mg/L |
| Cr(VI) by ion chromatography with post-column diphenylcarbazide | EPA 218.7; EPA 218.6; ISO 18412 (ZDHC methods list) | EPA 218.7 method detection limits 0.0044 to 0.015 µg/L, lowest concentration minimum reporting levels 0.012 to 0.036 µg/L; WHO 0.0044 to 0.015 µg/L | chromate separated on an anion column, derivatised and read at 530 nm; samples preserved with an ammonium sulfate and ammonium hydroxide buffer above pH 8 with a dechlorinating reagent |
| Cr(VI) by diphenylcarbazide colorimetry | Standard Methods 3500-Cr B; ISO 11083 | ISO 11083 range 0.05 to 3 mg/L | red violet complex at 540 nm; the effluent method |
| speciation by ion chromatography coupled to ICP-MS | no numbered standard read | 0.5 µg/L for Cr(III) and Cr(VI) (WHO) | WHO: reliable validated methods for separate Cr(III) and Cr(VI) analysis are still required |
- Sampling pitfalls
- Acidifying a sample for total chromium destroys the speciation: Cr(VI) samples need the alkaline buffer of EPA 218.7 and prompt analysis, and chlorine residual must be quenched or it keeps oxidising Cr(III). Cr(III) adsorbs on container walls and particles, so total chromium needs digestion of the unfiltered sample.
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), total chromium | 50 µg/L | based on achievability by treatment, measurability and toxicology; for total chromium because reliable routine speciation is not available; hyperplasia of the small intestine the most sensitive end point; Cr(VI) compounds IARC Group 1 by inhalation; assessment 2020 |
| EU DWD 2020/2184 | 25 µg/L | Annex I Part B; the 25 µg/L value shall be met at the latest by 12 January 2036, until then the parametric value is 50 µg/L; uncertainty of measurement 30 percent (Annex III) |
| US EPA NPDWR, total chromium | 0.1 mg/L | MCL and MCLG 0.1 mg/L; health effect listed as allergic dermatitis; sources discharge from steel and pulp mills and erosion of natural deposits |
| California SWRCB, hexavalent chromium | 0.010 mg/L | MCL of 10 µg/L effective 1 October 2024; public health goal 0.02 µg/L (2011) |
| body | limit | note |
|---|---|---|
| EU CWW BREF BAT-AEL (Decision 2016/902), chromium | 5.0 to 25 µg/L | applies if the emission exceeds 2.5 kg/yr; may not apply when the main load originates from the production of chromium-organic compounds |
| EU tanning BAT conclusions (Decision 2013/84/EU), total chromium | below 0.3 to 1 mg/L | direct and indirect discharge, monthly average of 24 hour composite samples |
| EU textiles BAT conclusions (Decision 2022/2508), chromium | 0.01 to 0.1 mg/L footnote on applicability not read | direct and indirect discharge, dyeing with chromium mordant or chromium containing dyes |
| US EPA 40 CFR 433.15, metal finishing PSES, chromium (total) | 2.77 daily maximum; 1.71 monthly average mg/L | pretreatment standard for discharge to sewer |
| US EPA 40 CFR 425.15, leather tanning PSES, total chromium | 12 daily maximum; 8 monthly average mg/L | subpart A; facilities processing fewer than 275 hides a day are exempt from the chromium limit |
| US EPA 40 CFR 410.12, textile mills wool scouring BPT, total chromium | 0.10 daily maximum; 0.05 30-day average kg per 1000 kg of woolproduction normalised | mass based |
| US EPA 40 CFR 423.13(d)(1), steam electric cooling tower blowdown (BAT), total chromium | 0.2 mg/L | daily maximum and 30-day average; with total zinc 1.0 mg/L |
| Abu Dhabi ADS 23/2017, discharge to the marine environment (EAD) | total chromium 0.2; chromium(VI) 0.15 mg/L region-dependent; marine discharge only | Table 1 maximum allowable concentrations |
| Abu Dhabi DoE Trade Effluent Control Regulations 2022, discharge to sewer | 5 mg/L region-dependent; sewer discharge | Table A₄ chromium (total) |
| sector | body | limit | note |
|---|---|---|---|
| textile and leather | ZDHC Wastewater Guidelines v₂.1 (2022), total chromium | textile 0.2 foundational, 0.1 progressive, 0.05 aspirational; leather 1.5, 0.8, 0.3 mg/L | ISO 17294, EPA 200.8, 6010C, 6020A; sludge total chromium 50 mg/kg (textile) |
| textile and leather | ZDHC Wastewater Guidelines v₂.1 (2022), chromium(VI) | textile 0.05 foundational, 0.005 progressive, 0.001 aspirational; leather 0.15, 0.05, 0.02 mg/L | ISO 18412, EPA 218.6, GB 7467; the aspirational value must meet the reporting limit; sludge Cr(VI) 20 mg/kg textile, 2 mg/kg leather |
8 · Health and environmental effects
- Toxicity
- Chromium(VI) is more toxic than chromium(III) and is a human carcinogen by inhalation (IARC Group 1); orally it is rapidly and efficiently reduced to Cr(III) in the gut, though a proportion may remain available. In two year drinking water studies tumours of the oral cavity in rats and small intestine in mice appeared at 0.77 and 0.38 mg/kg body weight per day, attributed to a threshold mode of action; environmental Cr(VI) levels are orders of magnitude below the doses tested, so WHO kept 50 µg/L total chromium (fact sheet, 2020). Chromium(III) is an essential trace element (the element entry).
- Bioaccumulation
- Cr(VI) is reduced in gastric fluid (70 percent within a minute at pH 2) and Cr(III) is poorly absorbed; no bioaccumulation concern is raised in the sources read.
- Ecotoxicity
- US EPA aquatic life criteria (1995): chromium(VI) freshwater 16 µg/L acute and 11 µg/L chronic, saltwater 1,100 and 50 µg/L; chromium(III) freshwater 570 µg/L acute and 74 µg/L chronic, expressed as a function of hardness.
Flags
- The EU 25 µg/L value applies only from 12 January 2036; 50 µg/L until then.
- The California Cr(VI) MCL is a state standard effective 1 October 2024; no federal Cr(VI) MCL exists.
- The HCrO₄⁻ pKa and the dichromate condensation are cited to Stumm and Morgan chapter 3 from memory.
- The reduction equations are electron balances; the CWW BREF names ferrous sulfate and sulfite without printing them.
- The occurrence figures are 1980s to 2010s surveys compiled by WHO; the UCMR 3 Cr(VI) range is quoted through WHO, not from the EPA data files.
- The textile BAT-AEL footnote 8 on chromium was not read.
- The tannery pretreatment exemption and the wool scouring mass based limit are not comparable with concentration limits.
- Abu Dhabi values cover two media (marine 0.2 and 0.15 mg/L; sewer 5 mg/L); other GCC states not read.
- Tannery and plating raw effluent chromium concentrations were not read; only the limits are quoted.
Gaps
- No raw effluent chromium concentrations for tanneries, plating shops or dye houses were read; the ledger's chapters hold them.
- No solubility product for Cr(OH)₃ or adsorption constants on iron oxides were read.
- The WHO 80 to 96 percent ion exchange figure is quoted as printed without the matrix it refers to.
- EPA 218.6 and ISO 18412 are cited by number from the ZDHC methods table; their texts were not opened.
- Other GCC discharge standards (Saudi, Oman, Qatar) were not read.
- The dichromate half reaction potential, the Cr(III) hydrolysis step and the lime stoichiometry are from Stumm and Morgan chapters 3, 6 and 8 and Metcalf and Eddy chapter 6, from the chapter, not re-read.
- The manganese oxide oxidation, the chlorine oxidation of Cr(III) and the chromate ligand exchange on ferrihydrite are electron and mass balances written from mechanisms the WHO background document describes in words; no rate constants, surface constants or yields were read.
Sources
WHO, Chromium in Drinking-water, background document, WHO/HEP/ECH/WSH/2020.3 (2020), sections 1.5, 2.1 and 7
Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Annex I Parts B and C and Annex III
US EPA, National Primary Drinking Water Regulations (table of MCLs and treatment techniques)
California State Water Resources Control Board, Division of Drinking Water, Hexavalent Chromium MCL page (read 2026-09-05)
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
Best Available Techniques Reference Document for Common Waste Water and Waste Gas Treatment/Management Systems in the Chemical Sector (CWW BREF 2016), chapter 3 (chemical reduction, chemical precipitation)
Commission Implementing Decision 2013/84/EU establishing BAT conclusions for the tanning of hides and skins, BAT 10 to 12, BAT 24 and Tables 3 and 4
Commission Implementing Decision (EU) 2022/2508 establishing BAT conclusions for the textiles industry, BAT-AELs for direct and indirect discharges (OJ L 325, 20.12.2022, pp. 141 to 142)
40 CFR 433.15, Pretreatment standards for existing sources (PSES), metal finishing point source category
40 CFR 425.15, Pretreatment standards for existing sources (PSES), leather tanning and finishing, subpart A (hair pulp, chrome tan, retan-wet finish)
40 CFR 410.12, Effluent limitations representing BPT, textile mills, subpart A (wool scouring)
40 CFR 423.13, Effluent limitations guidelines representing BAT, steam electric power generating point source category
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), Appendix Tables A2 and A4
ZDHC Wastewater Guidelines Version 2.1 (November 2022), conventional parameters, anions and metals tables and sludge Table 4A
Directive (EU) 2024/3019 concerning urban wastewater treatment (recast), Annex I Table 1 (COD reference method with potassium dichromate)
US EPA, National Recommended Water Quality Criteria, Aquatic Life Criteria Table (chromium III and chromium VI, 1995)
US EPA Method 200.8, Revision 5.4 (1994), Determination of trace elements in waters and wastes by ICP-MS, Table 1 (instrument detection limits) and Table 2 (molecular ion interferences)
US EPA Method 200.7, Revision 4.4 (1994), Determination of metals and trace elements in water and wastes by ICP-AES, Table 1 (wavelengths and instrument detection limits), Table 4 (method detection limits) and Table 5 (argon plasma conditions)
US EPA Method 218.7, Determination of hexavalent chromium in drinking water by ion chromatography with post-column derivatization and UV-visible spectroscopic detection, EPA 815-R-11-005 (November 2011), sections 1.2, 2 and 8
ISO 17294-2:2023, Water quality. Application of ICP-MS. Part 2: Determination of selected elements including uranium isotopes
ISO 11885:2007, Water quality. Determination of selected elements by inductively coupled plasma optical emission spectrometry (ICP-OES)
ISO 15586:2003, Water quality. Determination of trace elements using atomic absorption spectrometry with graphite furnace (Ag, Al, As, Cd, Co, Cr, Cu, Fe, Mn, Mo, Ni, Pb, Sb, Se, Tl, V, Zn)
ISO 11083:1994, Water quality. Determination of chromium(VI). Spectrometric method using 1,5-diphenylcarbazide
Standard Methods (online edition), 3500-Cr Chromium (B. colorimetric diphenylcarbazide method, C. ion chromatographic method)
PubChem element summary for chromium; estimated oceanic abundance 3 x 10^-4 mg/L (PUG View, reference 5, Jefferson Lab)
The Element Book, layer 1 entry for chromium (data/elements/Cr.json and data/reference/text/Cr.json)
The Element Book, water chapter for iron (data/water/Fe.json), chromate reduction with ferrous iron
Stumm, W. and Morgan, J. J., Aquatic Chemistry, 3rd ed. (Wiley, 1996), chapter 3 (acids and bases: chromic acid) and chapter 7 (precipitation: chromium hydroxide)
Metcalf and Eddy, Wastewater Engineering: Treatment and Resource Recovery, 5th ed. (McGraw-Hill, 2014), chapter 6 (chemical precipitation of heavy metals: lime and caustic dose, hydroxide solubility versus pH)
Identity
- Name and symbol
- Chromium, Cr
- Atomic number
- 24 protons
- Position
- group 6 · period 4 · d-block · transition metal
- CAS number
- 7440-47-3
Atomic structure
- Atomic mass
- 51.9961 u
- Electron configuration
- 1s² 2s² 2p⁶ 3s² 3p⁶ 4s¹ 3d⁵
[Ar] 3d⁵⁴s¹ - Electrons per shell
- 2, 8, 13, 1
- Valence electrons
- 6 ns and (n-1)d
| isotope | mass (u) | abundance |
|---|---|---|
| 50Cr | 49.946 041(3) | 4.3 % |
| 52Cr | 51.940 505(3) | 83.7 % |
| 53Cr | 52.940 647(3) | 9.5 % |
| 54Cr | 53.938 878(3) | 2.3 % |
Physical properties
- State at room temperature
- Solid
- Melting point
- 2,180 K (1,906.85 °C)
- Boiling point
- 2,944 K (2,670.85 °C)
- Density
- 7.15 g/cm3
- Appearance
- silvery metallic
- Thermal conductivity
- 93.9 W/(m·K)
- Electrical resistivity
- 125 nΩ·m at 20 °C
- Electrical conductivity
- 8 MS/m
- Crystal structure
- body-centered cubic
- Molar heat capacity
- 23.35 J/(mol·K)
Chemical properties
- Oxidation states
- +6, +3, +2
- Electronegativity
- 1.66 (Pauling Scale)
- Ionisation energy
- 6.767 eV
1st 652.9, 2nd 1,590.6, 3rd 2,987 kJ/mol - Electron affinity
- 0.666 eV
- Atomic radius
- empirical 139, covalent 139, van der Waals 189 pm
- Ionic radius
- Cr²⁺ 73 low spin; Cr³⁺ 62 low spin; Cr⁴⁺ 55 low spin; Cr⁵⁺ 49 low spin; Cr⁶⁺ 44 low spin; Cr²⁺ 80 high spin pm
- Reactivity
- A group 6 transition metal ([Ar] 3d5 4s1) whose thin, corundum-structured oxide film passivates it against air and acids, which is why it is plated onto steel and makes steel stainless; its compounds are all coloured, in the +3 and +6 states above all.
- with water
- Does not react; the passivating oxide film keeps the metal bright and untarnished in water and moist air.
- with oxygen, air
- Passivated by a thin chromium(III) oxide layer at room temperature; on strong heating the oxide scale grows, and above 950 C volatile chromium trioxide is lost from it:
- with acids
- Passivated chromium is stable against acids, and nitric acid strengthens the passivation; once the film is removed the metal dissolves readily in hydrochloric or sulfuric acid to chromium(III) salts and hydrogen:
- with halogens
- Combines with fluorine at 400 C and 200 bar to the volatile pentafluoride; the trihalides CrX3 are the common halides and give tetrahalides with more halogen at elevated temperature:
- Typical compounds
- Cr₂O₃ chromium(III) oxide green pigment; corundum-structured oxide, reduced by aluminium to the metal
- FeCr₂O₄ chromite the ore; refractory bricks, ferrochromium
- K₂Cr₂O₇ potassium dichromate orange oxidiser for analysis and tanning
- Na₂CrO₄ sodium chromate from roasting chromite with soda ash
- CrO₃ chromium trioxide chromic acid of electroplating; substance of very high concern
- PbCrO₄ lead chromate chrome yellow pigment
Occurrence, production and use
- Crustal abundance
- 1.02×102 milligrams per kilogram
- Oceanic abundance
- 3×10-4 milligrams per liter
- Occurrence and sources
The principal ore is chromite, which is found in Zimbabwe, Russia, New Zealand, Turkey, Iran, Albania, Finland, Democratic Republic of Madagascar, and the Phillippines. The metal is usually produced by reducing the oxide with aluminum.
- chromite (iron chromium oxide, FeCr2O4 spinel) layered igneous complexes and podiform deposits; 95 percent of world resources in Kazakhstan and southern Africa, mined in South Africa, Kazakhstan, Turkey, India, Finland, Brazil and Zimbabwe; United States resources in the Stillwater Complex, Montana
- crocoite (lead chromate) the Siberian red lead of the 1798 discovery; a mineralogical curiosity, not an ore
- trace chromium(III) in silicates the colour of emerald and ruby; chromium is a substance discharged from base metal, iron ore and industrial mineral extraction
- Extraction, production
- Carbothermic smelting of chromite to ferrochromium
Chromite is reduced with carbon in an electric arc furnace to high carbon ferrochromium, the form in which chromium enters stainless steel; China is the leading ferrochromium producer. Chromium metal is made by reducing chromium(III) oxide with aluminium or silicon. Reductants are named but not the product set, so no equation is written. World chromite production about 47 million tonnes gross weight in 2024 (estimate).
Chromium(III) oxide pigment from sodium dichromateIn the SIC BREF's solid state process sodium dichromate (Na2Cr2O7) is mixed with sulphur and calcined in a rotary kiln to chromium(III) oxide, then washed and milled; the sulphur co product is not stated, so no equation. The wash water carries chromate, and the BREF lists chromium removal from waste water for the pigment sector.
- Uses
Chromium is a blue-white metal that is hard, brittle and very corrosion resistant. Chromium can be polished to form a very shiny surface and is often plated to other metals to form a protective and attractive covering. Chromium is added to steel to harden it and to form stainless steel, a steel alloy that contains at least 10% chromium. Other chromium-steel alloys are used to make armor plate, safes, ball bearings and cutting tools.
Chromium forms many colorful compounds that have industrial uses. Lead chromate (PbCrO4), also known as chrome yellow, has been used as a yellow pigment in paints. Chromic oxide (Cr2O3), also known as chrome green, is the ninth most abundant compound in the earth's crust and is a widely used green pigment. Rubies and emeralds also owe their colors to chromium compounds. Potassium dichromate (K2Cr2O7) is used in the tanning of leather while other chromium compounds are used as mordants, materials which permanently fix dyes to fabrics. Chromium compounds are also used to anodize aluminum, a process which coats aluminum with a thick, protective layer of oxide. Chromite, chromium's primary ore, is used to make molds for the firing of bricks because of its high melting point, moderate thermal expansion and stable crystal structure.
Chromium is used to harden steel, manufacture stainless steel, and form many useful alloys. It is mostly used in plating to produce a hard, beautiful surface and to prevent corrosion. Chromium gives glass an emerald green color and is widely used as a catalyst.
The refractory industry uses chromite for forming bricks and shapes, as it has a high melting point, moderate thermal expansion, and stability of crystalline structure.
- Stainless steel and alloys: ferrochromium for stainless and heat resisting steel, which contains at least 10.5 percent chromium; superalloys, the major strategic use; chromium plating for a mirror finish on steel and plastics chromium has no substitute in stainless steel, the leading end use; recycled stainless scrap supplied 23 percent of United States apparent consumption in 2024 (USGS)
- Textiles: chrome (mordant) dyeing of wool: the dye is applied from an acidic bath and the fibre is then chromed with dichromate in the afterchrome process, so exhausted baths carry chromium(VI) and chromium(III); 1:1 and 1:2 metal complex dyes with chromium bound inside the dye molecule; the BREF answers with low chrome afterchroming and reactive dyeing of wool without chrome (BAT 42a)
- Chemicals: chromium(III) oxide green pigments from sodium dichromate; Phillips chromium catalysts for high density polyethylene; iron oxide and chromium oxide shift catalyst in ammonia plants; chromium discharged from pigment and phosphoric acid plants
- Pharmaceuticals and fine chemicals: metallisation of azo dyes with chromium(III) oxide or chloride to form 1:1 and 1:2 chelated complexes; dichromate as an inorganic oxidant
- Leather: about 90 percent of all leather is tanned with chromium(III) salts; the effluent is toxic
- Mining: chromite extraction is grouped with iron ore in the MWEI BREF; chromium is among the substances discharged from ore processing
- Safety, toxicity
Chromium compounds are toxic and should be handled with proper safeguards.
GHS classification, signal word Danger- H317 May cause an allergic skin reaction Sensitization, Skin
- H319 Causes serious eye irritation Serious eye damage/eye irritation
- H334 May cause allergy or asthma symptoms or breathing difficulties if inhaled Sensitization, respiratory
- H335 May cause respiratory irritation Specific target organ toxicity, single exposure; Respiratory tract irritation
- H320 Causes eye irritation Serious eye damage/eye irritation
- H341 Suspected of causing genetic defects Germ cell mutagenicity
- H371 May cause damage to organs Specific target organ toxicity, single exposure
- H400 Very toxic to aquatic life Hazardous to the aquatic environment, acute hazard
- H410 Very toxic to aquatic life with long lasting effects Hazardous to the aquatic environment, long-term hazard
Discovery and name
- Discovered by
- Louis Nicolas Vauquelin
- Discovered
- 1794
- First isolated
- not in sources
- Named by
- not in sources
- Origin of the name
- from the Greek χρῶμα, "color", because many chromium compounds are intensely colored
Chromium is used extensively in automobile trim as chromium metal because of its shiny finish and corrosion resistance.
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.