Antimony
fullAntimony is regulated in drinking water (WHO 20 µg/L, EU 10 µg/L, US 6 µg/L) although natural water carries almost none; it arrives from PET bottles, solders and fittings, polyester dyehouses (antimony trioxide is the polyester catalyst), flame retardant finishing, mining and smelting, and it behaves like arsenic in water: an oxo-anion that conventional treatment does not touch and that only iron coagulation at low pH takes out.
Typical wastewaters
- textile dyeing and finishing (polyester) Sb(III) and Sb(V) released from the antimony trioxide polyester catalyst in the dyeing liquor at pH 4 to 5 and 130 C; antimony trioxide flame retardant synergist from finishing ZDHC limits do not yet apply to polyester wet processing, but antimony must be sampled and reported
- mine drainage (antimony mining and smelting districts) Sb(OH)₃ (aq) and thioantimonite complexes in reducing, sulfidic mine water, oxidising slowly to Sb(OH)₆⁻ on aeration US EPA source list for the antimony MCL
- petroleum refining, ceramics, electronics and lead-acid battery manufacture antimonate Sb(OH)₆⁻ in oxic effluent US EPA source list for the antimony MCL; no effluent figure read
1 · Identity
- Symbol, number
- Sb, 51
- Oxidation states in water
- +5 as the antimonate anion Sb(OH)₆⁻ in oxic water, the form WHO identifies for antimony leached from materials and the less toxic one; +3 as the neutral Sb(OH)₃ in reducing water and as the soluble potassium antimony tartrate of the toxicology studies, more toxic and genotoxic in vitro and in vivo; -3 (stibine) has no water chemistry. 0 as the metal in lead alloys and solders.
- Note
- The element entry covers stibnite, the trioxide and the halides. In water antimony is the arsenic analogue one row down: an anion in the +5 state, a neutral hydroxide in the +3 state, both poorly adsorbed at neutral pH.
2 · Occurrence in water
- Natural sources
- Weathering of stibnite and other antimony minerals; hydrothermal and mining districts. WHO: groundwater below 0.001 µg/L and surface water below 0.2 µg/L in general; drinking water appears to be below 5 µg/L. Antimony is not normally a raw water contaminant.
- Anthropogenic sources
- Dissolution from metal plumbing and fittings, the most common source in drinking water (WHO), with antimony solder replacing lead; leaching from PET bottles, which hold antimony trioxide catalyst residues (213 mg Sb per kg plastic in one brand); antimony trioxide in polyester manufacture and hence polyester dyeing effluent (ZDHC); antimony trioxide flame retardant synergist in textile finishing (element entry); antimony mining and smelting, petroleum refineries, ceramics, electronics and lead-acid battery plants (US EPA source list); the ledger's textile, chemical and mining chapters carry the plant figures.
| matrix | typical range | note |
|---|---|---|
| groundwater | below 0.001 µg/L the figure is far below usual detection limits and is quoted as printed | WHO fact sheet general statement |
| surface water | below 0.2 µg/L | |
| drinking water | below 5 µg/L | appears to be; dissolution from plumbing is the usual source |
| bottled water in PET, south western USA | 0.095 to 0.521 µg/L storage temperature and time dependent | nine brands; leaching rises with temperature: the model gives 176 days at 60 C, 2.3 days at 80 C and 1.3 days at 85 C to reach the US 6 µg/L limit |
3 · Speciation
Antimony(V) exists as the antimonate anion Sb(OH)₆⁻ across the whole natural pH range because antimonic acid is a fairly strong acid; antimony(III) is the neutral Sb(OH)₃ up to high pH. Neither is a cation, so neither hydrolyses to a filterable hydroxide, and neither adsorbs well on aluminium hydroxide. Ferric hydroxide adsorbs both: Sb(V) best at pH 4.5 to 5.5 and progressively worse as pH rises, Sb(III) well from pH 4 to 10 (Guo and others 2009). Phosphate and humic acid compete with Sb(V) for the iron surface and barely affect Sb(III). Oxic water holds Sb(V); reducing water and stibnite districts give Sb(III), and the sulfide complexes of Sb(III) keep antimony mobile in sulfidic water. Antimony leached from materials is the Sb(V) oxo-anion (WHO).
| condition | dominant species | note |
|---|---|---|
| oxic water, pH 4 to 10 | Sb(OH)₆⁻ | the drinking water and PET leachate form; the less toxic state (WHO) |
| reducing water, mine water, stibnite districts | Sb(OH)₃ (aq); thioantimonite complexes where sulfide is present | the more toxic state; oxidises to Sb(V) on aeration, slowly |
| ferric coagulation at pH 4.5 to 5.5 | Sb(V) adsorbed on ferric hydroxide floc | the removal window (Guo and others 2009) |
| polyester dyeing liquor, pH 4 to 5, 130 C | antimony released from the polymer catalyst as Sb(III) and Sb(V) | the ZDHC polyester exemption exists because this source is in the fibre, not the dyehouse's chemistry |
- Solubility
- No controlling solid in ordinary water; Sb₂O₃ and Sb₂S₃ are the sparingly soluble source minerals and iron antimonates the proposed treatment solids. No solubility products quoted; the sources read print none.
- Hydrolysis
- Both states are fully hydrolysed hydroxo species at natural pH; Sb(OH)₅ is a stronger acid than Sb(OH)₃, hence the anion for Sb(V) and the neutral molecule for Sb(III). The pKa is not printed in the sources read and is not quoted.
- Complexation
- Sulfide (thioantimonites), tartrate (potassium antimony tartrate), organic matter; phosphate and humic acid compete at the iron surface rather than complexing antimony (Guo and others 2009).
- Precipitates
- Antimony adsorbed on and co-precipitated with ferric hydroxide; Sb₂S₃ in sulfidic sediments; iron antimonate proposed in the coagulation literature.
4 · Role in treatment
5 · Removal and control
- Efficiency
- effective for both states with ferric chloride; percentages not printed in the abstract read
- Interferences
- phosphate and humic acid markedly impede Sb(V) removal, insignificant effect on Sb(III); aluminium sulfate gives very low removal of both
- Efficiency
- not quoted
- Interferences
- as above
6 · Analytics
| method | standard | detection limit | note |
|---|---|---|---|
| ICP-MS | EPA 200.8 (mass 123); ISO 17294-2; Standard Methods 3125 | 0.1 to 1 µg/L (WHO); EPA 200.8 instrument detection limit 0.08 µg/L scanning, 0.008 µg/L selected ion monitoring | hydrochloric acid needed for stability; apply the chloride interference corrections (EPA 200.8 section 7.1) |
| electrothermal AAS | ISO 15586 | 0.01 µg/L (WHO); graphite furnace 0.8 µg/L | |
| hydride generation AAS | no numbered standard read (WHO cites hydride generation AAS; Standard Methods 3114 covers arsenic and selenium, not antimony) | 5 µg/L (WHO) | prereduction to Sb(III) needed for total antimony |
- Sampling pitfalls
- Preserve with hydrochloric acid, not nitric alone: antimony is unstable in nitric acid solutions and adsorbs out (EPA 200.8). Speciation (Sb(III) against Sb(V)) needs prompt analysis; oxic storage converts Sb(III). PET sample bottles are an antimony source; use glass or polyethylene. Bottled water results depend on storage temperature and age.
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) | 0.02 mg/L | 20 µg/L from a TDI of 6 µg/kg body weight (NOAEL 6.0 mg/kg per day for reduced weight gain in a 90 day rat study with potassium antimony tartrate, uncertainty factor 1000), 10 percent allocation, 60 kg, 2 L/day; assessment 2003 |
| EU DWD 2020/2184 | 10 µg/L | Annex I Part B |
| US EPA NPDWR | 0.006 mg/L | MCL and MCLG 0.006 mg/L; health effects listed as increase in blood cholesterol and decrease in blood sugar; sources listed as petroleum refineries, fire retardants, ceramics, electronics, solder |
| body | limit | note |
|---|---|---|
| EU CWW BREF BAT-AEL (Decision 2016/902) | not set | antimony is not among the metals with a BAT-AEL |
| US EPA 40 CFR 433.14, metal finishing (BAT) | not set | antimony is not among the regulated pollutants of the metal finishing category |
| Abu Dhabi ADS 23/2017, discharge to the marine environment (EAD) | 0.1 mg/L region-dependent; marine discharge only | Table 1 maximum allowable concentration at the point of discharge |
| Abu Dhabi DoE Trade Effluent Control Regulations 2022, discharge to sewer | not set region-dependent | antimony has no row in Table A₄ Metals |
| sector | body | limit | note |
|---|---|---|---|
| textile and leather | ZDHC Wastewater Guidelines v₂.1 (2022), Table 2 | 0.1 foundational; 0.05 progressive; 0.01 aspirational mg/L | textile and leather; footnote a: for polyester wet processing facilities the limits do not yet apply unless required by law or adopted voluntarily, but antimony must be sampled and reported, with limits intended by 2025; methods ISO 17294, EPA 200.8, 6010C, 6020A; sludge threshold 5 mg/kg dry weight, textile only (Table 4A) |
8 · Health and environmental effects
- Toxicity
- TDI 6 µg/kg body weight from a 90 day rat study with the soluble potassium antimony tartrate; the form decides the toxicity: Sb(V) leached from materials is the less toxic, antimony trioxide has low bioavailability, soluble Sb(III) salts are genotoxic in vitro and in vivo. Antimony trioxide is possibly carcinogenic by inhalation (IARC 2B), the trisulfide not classifiable (Group 3); there are no data indicating carcinogenicity by the oral route (WHO fact sheet). US health effects listed: increased blood cholesterol, decreased blood sugar.
- Bioaccumulation
- Not addressed in the sources read; total exposure from environment, food and drinking water is very low compared with occupational exposure (WHO).
- Ecotoxicity
- No US EPA national recommended aquatic life criterion for antimony and no EU EQS; not addressed in the sources read.
Flags
- The Sb(OH)₆⁻ and Sb(OH)₃ formulas and the antimonic acid dissociation are textbook speciation, not printed in the WHO text, which names only the antimony(V) oxo-anion; cited to Stumm and Morgan chapter 6 from memory, not re-read.
- The WHO groundwater figure of below 0.001 µg/L is below the detection limits WHO itself lists and is quoted as printed.
- Guo and others 2009 was read as the abstract only; removal percentages are in the paper, not the abstract.
- The pre-oxidation and neutral pH iron removal item is a consequence drawn from the pH dependence, not a design rule read.
- Westerhoff and others 2008 was read as the abstract; the temperature model figures are from it.
- EU law was read on legislation.gov.uk mirrors because eur-lex did not respond; eur-lex urls kept for consistency.
- Abu Dhabi marine value 0.1 mg/L; the sewer regulation has no antimony row; other GCC states not read.
- Standard Methods and ISO method numbers other than those in the sources read (EPA 200.8, ISO 17294-2 and the methods the WHO documents cite) are quoted from memory and were not confirmed this session.
Gaps
- No seawater, municipal wastewater, mine water or polyester dyehouse antimony concentration was read.
- No pKa, solubility product or adsorption constant is quoted.
- Adsorbents (iron oxide media, activated alumina), reverse osmosis and ion exchange for antimony are not covered because no read source gives figures.
- The WHO 2003 background document on antimony was not read; the fact sheet was.
- The EU textiles BAT conclusions (2022/2508) were not read for an antimony BAT-AEL.
- EU law was read on legislation.gov.uk mirrors; other GCC discharge standards were not read.
- No surface complexation constants or surface species formulas for antimony on ferric hydroxide were read; the ligand exchange equation is written by analogy with arsenate.
Sources
Westerhoff, P., Prapaipong, P., Shock, E. and Hillaireau, A., Antimony leaching from polyethylene terephthalate (PET) plastic used for bottled drinking water, Water Research 42(3), 551 to 556 (2008), abstract (PMID 17707454)
Guo, X., Wu, Z. and He, M., Removal of antimony(V) and antimony(III) from drinking water by coagulation-flocculation-sedimentation (CFS), Water Research 43(17), 4327 to 4335 (2009), abstract (PMID 19595424)
Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Annex I Part B (read on the legislation.gov.uk mirror of the directive)
US EPA, National Primary Drinking Water Regulations (table of MCLs and treatment techniques)
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 Table 3 and footnotes c, d and g (read on the legislation.gov.uk mirror)
40 CFR 433.14, Effluent limitations (BAT), metal finishing 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 Table A4 Metals
ZDHC Wastewater Guidelines Version 2.1 (November 2022), Table 2 heavy metals and Table 4A sludge
US EPA Method 200.8, Revision 5.4 (1994), Determination of trace elements in waters and wastes by ICP-MS, sections 1.7 and 7.1, Table 1 (instrument detection limits)
US EPA, National Recommended Water Quality Criteria, Aquatic Life Criteria Table
Standard Methods for the Examination of Water and Wastewater (online edition), 3111 (flame AAS), 3120 (ICP-OES), 3125 (ICP-MS)
Stumm, W. and Morgan, J. J., Aquatic Chemistry, 3rd ed. (Wiley, 1996), chapter 6 (metal ions in aqueous solution: hydrolysis and complexation) and chapter 7 (precipitation and dissolution)
Identity
- Name and symbol
- Antimony, Sb
- Atomic number
- 51 protons
- Position
- group 15 · period 5 · p-block · metalloid
- CAS number
- 7440-36-0
Atomic structure
- Atomic mass
- 121.76 u
- Electron configuration
- 1s² 2s² 2p⁶ 3s² 3p⁶ 4s² 3d¹⁰ 4p⁶ 5s² 4d¹⁰ 5p³
[Kr] 5s²⁴d¹⁰⁵p³ - Electrons per shell
- 2, 8, 18, 18, 5
- Valence electrons
- 5 outer shell
| isotope | mass (u) | abundance |
|---|---|---|
| 121Sb | 120.903 81(2) | 57.21 % |
| 123Sb | 122.904 21(1) | 42.79 % |
Physical properties
- State at room temperature
- Solid
- Melting point
- 903.78 K (630.63 °C)
- Boiling point
- 1,860 K (1,586.85 °C)
- Density
- 6.685 g/cm3
- Appearance
- silvery lustrous gray
- Thermal conductivity
- 24.4 W/(m·K)
- Electrical resistivity
- 417 nΩ·m at 20 °C
- Electrical conductivity
- 2.4 MS/m
- Crystal structure
- rhombohedral
- Molar heat capacity
- 25.23 J/(mol·K)
Chemical properties
- Oxidation states
- +5, +3, -3
- Electronegativity
- 2.05 (Pauling Scale)
- Ionisation energy
- 8.64 eV
1st 834, 2nd 1,594.9, 3rd 2,440 kJ/mol - Electron affinity
- 1.07 eV
- Atomic radius
- empirical 139, covalent 139, van der Waals 206 pm
- Ionic radius
- Sb³⁺ 76; Sb⁵⁺ 60 pm
- Reactivity
- A brittle group 15 metalloid, a poor conductor, stable in air at room temperature and attacked only by oxidising acids; it shows the +3 and +5 states and, like arsenic, is toxic.
- with water
- Does not react with water.
- with oxygen, air
- Stable in air at room temperature; on heating it burns to antimony trioxide, which forms as Sb4O6 in the vapour: .
- with acids
- No reaction with non-oxidising acids; oxidising acids such as nitric acid attack it, and concentrated nitric acid takes the trioxide on to the pentoxide.
- with halogens
- Combines with the halogens to the trihalides: ; with excess chlorine or fluorine the pentahalides form: .
- Typical compounds
- Sb₂O₃ antimony trioxide flame-retardant synergist, glass fining agent
- Sb₂S₃ stibnite the principal ore; kohl, safety-match heads
- SbCl₃ antimony trichloride from stibnite in hydrochloric acid; Lewis acid
- SbF₅ antimony pentafluoride with HF gives fluoroantimonic superacid
- SbH₃ stibine unstable toxic hydride, semiconductor dopant
- InSb indium antimonide infrared detector semiconductor
Occurrence, production and use
- Crustal abundance
- 2×10-1 milligrams per kilogram
- Oceanic abundance
- 2.4×10-4 milligrams per liter
- Occurrence and sources
Antimony is not abundant, but is found in over 100 mineral species. It is sometimes found natively, but more frequently it is found as the sulfide stibnite.
- stibnite (Sb2S3) China (Hunan), Tajikistan, Russia, Myanmar, Bolivia, Turkey, Australia; Stibnite district, Idaho
- native antimony and more than 100 other minerals minor
- crustal and oceanic abundance about 0.2 ppm (BGS figure via RSC); 0.2 mg/kg crust and 0.00024 mg/L seawater (PubChem)
- Extraction, production
- Roasting of stibnite to antimony(III) oxide
RSC states the sulfide is roasted to the oxide; sulfur dioxide as the sulfur product is implied by roasting in air, not named
Carbon reduction of the oxide to metalRSC states the oxide is then reduced with carbon; The added secondary source prints the carbon dioxide form, which is the equation given.
Secondary antimony as antimonial leadrecovered at secondary lead smelters from spent lead-acid batteries and returned to battery grids; about 3,500 t in the United States in 2024
- Uses
Antimony is a brittle metal and is a poor conductor of heat and electricity. Very pure antimony is used to make certain types of semiconductor devices, such as diodes and infrared detectors. Antimony is alloyed with lead to increase lead's durability. Antimony alloys are also used in batteries, low friction metals, type metal and cable sheathing, among other products. Antimony compounds are used to make flame-proofing materials, paints, ceramic enamels, glass and pottery. The ancient Egyptians used antimony, in the form of stibnite, for black eye make-up.
Antimony is finding use in semiconductor technology for making infrared detectors, diodes and Hall-effect devices. It greatly increases the hardness and mechanical strength of lead. Batteries, antifriction alloys, type metal, small arms and tracer bullets, cable sheathing, and minor products use about half the metal produced. Compounds taking up the other half are oxides, sulfides, sodium antimonate, and antimony trichloride. These are used in manufacturing flame-proofing compounds, paints ceramic enamels, glass, and pottery.
- Lead alloys and batteries: antimonial lead for lead-acid battery grids; ammunition, cable sheathing, type metal, bearing alloys metal products 40 percent of US antimony use in 2024 (usgs-mcs2025-antimony)
- Textiles (flame-retardant finishing, polyester dyeing): antimony trioxide synergist in flame-retardant finishes; antimony BAT-AEL applies; antimony released from polyester in pretreatment and disperse dyeing (BAT-AEL 0.1 to 0.2 mg/l, up to 1.2) flame retardants 39 percent of US antimony use in 2024, across all substrates (usgs-mcs2025-antimony)
- Chemicals (polyester catalyst, pigments, glass): antimony trioxide polycondensation catalyst for PET; antimony in lead-chromate and complex inorganic colour pigment effluent (Pb, Sb pretreatment by precipitation); enamels, paints, glass, pottery nonmetal products including ceramics, glass and rubber 21 percent of US use in 2024 (usgs-mcs2025-antimony)
- Electronics: indium antimonide and other semiconductors for infrared detectors and diodes
- Mining: stibnite mining and gold-antimony deposits; antimony reported in extractive-waste water at base-metal and precious-metal sites
- Safety, toxicity
- GHS classification, signal word Danger
- H301 Toxic if swallowed Acute toxicity, oral
- H302 Harmful if swallowed Acute toxicity, oral
- H332 Harmful if inhaled Acute toxicity, inhalation
- H351 Suspected of causing cancer Carcinogenicity
- H373 May causes damage to organs through prolonged or repeated exposure Specific target organ toxicity, repeated exposure
- H411 Toxic to aquatic life with long lasting effects to the aquatic environment, long-term hazard
- H315 Causes skin irritation Skin corrosion/irritation
- H319 Causes serious eye irritation Serious eye damage/eye irritation
- H335 May cause respiratory irritation Specific target organ toxicity, single exposure; Respiratory tract irritation
- H370 Causes damage to organs Specific target organ toxicity, single exposure
- H372 Causes damage to organs through prolonged or repeated exposure Specific target organ toxicity, repeated exposure
- H401 Toxic to aquatic life to the aquatic environment, acute hazard
Discovery and name
- Discovered by
- Arabic alchemists
- Discovered
- before AD 815
- First isolated
- not in sources
- Named by
- not in sources
- Origin of the name
- Uncertain. Possibly from Greek anti ("not") + monos ("alone"), for not occurring alone in nature
Antimony is a poor conductor of heat and electricity. Antimony and many of its compounds are toxic.
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.