Bromine
fullBromide is a harmless conservative ion until the water is disinfected: ozone turns it into bromate, regulated at 10 µg/L by WHO, the EU and the US, and chlorine turns it into brominated trihalomethanes and haloacetic acids, so bromide decides which disinfectant a plant can use.
Typical wastewaters
- coal power plant flue gas desulfurisation wastewater bromide Br⁻ in the scrubber water, limited to 0.2 mg/L daily under the voluntary incentives programme the only bromide effluent limit read
- oil and gas produced water and brines bromide Br⁻ as a conservative anion of the brine WHO names brine and oilfield water, road salt and industrial effluent as anthropogenic bromide sources
- chlor-alkali and hypochlorite production bromide impurity in the salt and caustic, oxidised to bromate BrO₃⁻ in the concentrated high pH hypochlorite; the same in on-site electrolytic hypochlorite from bromide bearing brine a bromate source without ozone
- textile dyeing and finishing organically bound bromine from brominated flame retardant finishing, counted in AOX (BAT-AEL 0.1 to 0.4 mg/L) bromate from sulfur dye dyeing is named by the element entry, not by this source
1 · Identity
- Symbol, number
- Br, 35
- Oxidation states in water
- -1 bromide, Br⁻, the natural form, conservative and unsorbed; +1 hypobromous acid and hypobromite (HOBr, OBr⁻) and bromamines, formed transiently when ozone or chlorine meets bromide; +5 bromate, BrO₃⁻, the stable end product of ozonation; organic bromine in brominated disinfection by-products and in brominated flame retardants; 0 as elemental bromine in the disinfectant chemicals themselves.
- Note
- The element entry covers brine extraction, flame retardants and the chlor-alkali route to bromate; this chapter is the disinfection chemistry.
2 · Occurrence in water
- Natural sources
- Bromide occurs with sodium chloride in smaller amounts: seawater 65 mg/L to well over 80 mg/L in confined seas, fresh water from trace amounts to about 0.5 mg/L, desalinated water up to 1 mg/L (WHO). Bromide in surface water and groundwater fluctuates seasonally and rises with saltwater intrusion in drought and with pollution (WHO brominated acetic acids sheet).
- Anthropogenic sources
- Bromide from brine and oilfield water, road salt and industrial effluent; bromide in flue gas desulfurisation wastewater, limited to 0.2 mg/L under the US voluntary incentives programme for power plants; bromate impurity in sodium hypochlorite made from bromide contaminated salt and caustic, and in on-site electrolytic hypochlorite from bromide bearing brine (WHO); bromate from sulfur dye textile dyeing and permanent wave neutralisers; brominated flame retardants leaching from finished textiles and plastics and bromine impurities in chlor-alkali and EDC production (element entry).
| matrix | typical range | note |
|---|---|---|
| seawater, bromide | 65 to over 80 mg/L | higher in confined sea areas; PubChem gives 67.3 mg/L as the oceanic abundance |
| fresh water, bromide | trace to about 0.5 mg/Lregion-dependent | |
| desalinated water, bromide | up to about 1 mg/L | the reason post chlorination of desalinated water is a brominated DBP problem |
| ozonated drinking water, bromate | below 2 to 293 µg/L the high end comes from laboratory studies with very high bromide | range across source waters, depending on bromide, ozone dose, pH, alkalinity and DOC (IPCS 2000 as cited); European utilities below 2 to 16 µg/L; US finished surface water annual mean 2.9 µg/L, range below 0.2 to 25 |
| ozonated bottled water, bromate | 4.3 to 37.3, mean 18 µg/Lsingle survey | Health Canada survey |
| ozonated water in early studies, bromate | 60 to 90 µg/L | Haag and Hoigne 1983, McGuire 1990 as cited |
3 · Speciation
Bromide is conservative: it neither sorbs nor precipitates in fresh water and survives every conventional process. Ozone oxidises it to hypobromite and hypobromous acid; hypobromous acid brominates natural organic matter and reacts with ammonia to bromamines, while hypobromite is oxidised further by ozone and hydroxyl radicals to bromate. Low pH favours HOBr and the brominated organics, high pH favours OBr⁻ and bromate. Chlorine oxidises bromide to hypobromous acid too, which is why chlorinated bromide waters carry bromoform, bromodichloromethane, dibromochloromethane and brominated acetic acids. Chlorine dioxide does not oxidise bromide and makes no bromate under treatment conditions. Bromate, once formed, is stable, non volatile and only slightly sorbed; its long term fate is slow reduction by organic matter back to bromide (WHO).
| condition | dominant species | note |
|---|---|---|
| natural water, any pH and Eh | Br⁻ | conservative tracer behaviour |
| during ozonation, pH below about 8 | HOBr, brominated organics, bromamines if ammonia is present | the organic by-product branch |
| during ozonation, pH above about 8 | OBr⁻, then BrO₃⁻ | the bromate branch; alkalinity and temperature raise bromate formation, ozone stability falls |
| during chlorination | HOBr from Br⁻ and HOCl; bromoform, bromodichloromethane, dibromochloromethane, bromoacetic acids | bromine substitutes for chlorine in the THM and HAA series |
| chlorine dioxide | Br⁻ unchanged | no hypobromite or bromate; bromate only under light, thermodynamically unfavourable (WHO) |
| hypochlorite stock solutions | BrO₃⁻ from bromide impurities at high pH | a source of bromate in the finished water independent of ozone |
- Solubility
- Bromide salts of the common cations are very soluble; potassium bromate dissolves at 133 g/L at 40 C and sodium bromate at 275 g/L at 8 C (WHO). Nothing precipitates bromide or bromate in water treatment.
- Hydrolysis
- Hypobromous acid is a weak acid and bromous and bromic acids are weaker than hydrobromic acid (WHO); the HOBr dissociation constant is not printed in the sources read, so none is quoted. Basic hypobromite solutions are stable at 0 C but disproportionate rapidly to bromide and bromate at about 50 C and above (WHO citing Cotton and Wilkinson).
- Complexation
- Bromide forms no complexes of consequence in fresh water; silver ions are sequestered by bromide among other anions (WHO silver document). Not otherwise addressed.
- Precipitates
- None in treatment; silver bromide in the analytical chloride removal cartridge.
4 · Role in treatment
5 · Removal and control
- Efficiency
- bromate below 0.01 mg/L achievable (WHO treatment performance statement)
- Interferences
- high bromide, high pH, high alkalinity and warm water push the other way
- Efficiency
- not established
- Efficiency
- bromate avoided, not removed
- Interferences
- light plus chlorine dioxide can form traces of bromate
- Efficiency
- not read
6 · Analytics
| method | standard | detection limit | note |
|---|---|---|---|
| ion chromatography with suppressed conductivity detection | EPA 300.1 Part B (bromate, bromide, chlorite, chlorate); Standard Methods 4110; ISO 10304 | bromate MDL below 1.5 µg/L, practical quantification level about 5 µg/L (WHO citing EPA 300.1); 1.5 µg/L in the fact sheet | the compliance method for bromate in US systems using ozone (EPA manual section 3.5.3); a silver cartridge removes chloride ahead of the column |
| ion chromatography with post column reaction and UV or visible absorbance detection | EPA 317.0 and 326.0 | bromate MDL below 0.2 µg/L, PQL about 1 µg/L | |
| ion chromatography with ICP-MS detection | EPA 328.1 (WHO citation); EPA 321.8 | bromate MDL 0.3 µg/L, PQL about 1 µg/L | isotope specific bromine detection |
| bromide by ion chromatography | EPA 300.1 Part A; Standard Methods 4110; ISO 10304-1 | not read | bromide should be measured on any source water before an ozone or chlorine decision |
- Sampling pitfalls
- Bromate samples must not be exposed to residual ozone or hypochlorite after collection or bromate keeps forming; quench the oxidant at sampling (EPA 300.1 preservation was not read, so no reagent is named). High chloride and high carbonate mask bromate on the column (WHO). Bromide itself is stable and needs no preservation. Hypochlorite stock solutions should be assayed for bromate separately.
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), bromate | 10 µg/L | provisional because of limitations in analytical and treatment methods; the health based value is 2 µg/L at 10⁻5 excess cancer risk (cancer potency 0.19 per mg/kg body weight per day); assessment 2003 |
| WHO GDWQ, bromide | no guideline | occurs at concentrations well below health concern; ADI 0 to 0.4 mg/kg body weight gives health based values of 6 mg/L for adults and 2 mg/L for a 10 kg child; assessment 2009 |
| WHO GDWQ, brominated trihalomethanes | 100 bromoform; 100 dibromochloromethane; 60 bromodichloromethane µg/L | individual guideline values; the sum of the ratios of each THM to its guideline value should not exceed 1 |
| EU DWD 2020/2184, bromate | 10 µg/L | Annex I Part B; uncertainty of measurement 40 percent of the parametric value (Annex III) |
| US EPA NPDWR, bromate | 0.010 mg/L | MCL under the Stage 1 Disinfectants and Disinfection Byproducts Rule (40 CFR 141.64); MCLG zero; systems using ozone must monitor bromate |
| US EPA health advisory table (2018), bromate | 0.005 mg/L at 10^-4 cancer risk | one day health advisory 0.2 mg/L, RfD 0.004 mg/kg per day, DWEL 0.14 mg/L; cancer group B₂ |
| body | limit | note |
|---|---|---|
| EU CWW BREF BAT-AEL (Decision 2016/902), AOX | 0.20 to 1.0 mg/L | adsorbable organically bound halogens (EN ISO 9562) count organically bound bromine with chlorine and iodine; applies if the emission exceeds 100 kg/yr; no bromide or bromate AEL |
| EU textiles BAT-AEL (Decision 2022/2508), AOX | 0.1 to 0.4 mg/L | all processes, direct and indirect discharge; brominated flame retardant finishing contributes |
| US EPA 40 CFR 423.13(g)(3), FGD wastewater, voluntary incentives programme, bromide | 0.2 mg/L daily maximum time-sensitive: steam electric limits carry compliance dates | the only bromide effluent limit read; with selenium 10 µg/L, arsenic 5 µg/L, mercury 23 and 10 ng/L |
| Abu Dhabi ADS 23/2017 and DoE Trade Effluent Control Regulations 2022 | not set region-dependent | neither bromide nor bromate appears in the tables read |
| sector | body | limit | note |
|---|---|---|---|
| textile | ZDHC Wastewater Guidelines v₂.1 (2022) | not set | bromide and bromate are not ZDHC wastewater parameters; brominated flame retardants are MRSL substances |
| surface water (EU) | Directive 2013/39/EU priority substances | not set | brominated diphenylethers are a priority hazardous substance group (sum of congeners 28, 47, 99, 100, 153 and 154) with biota and water standards not transcribed here; bromide and bromate are not listed |
8 · Health and environmental effects
- Toxicity
- Bromide: sedative at pharmacological doses; JMPR ADI 0 to 1 mg/kg body weight (1966, 1988) and a conservative human NOEL of 4 mg/kg per day giving 0 to 0.4 mg/kg; dietary intake 2 to 9 mg/day. Bromate: IARC Group 2B, mutagenic in vitro and in vivo, kidney tumours, mesotheliomas and thyroid tumours in rats; drinking water at 20, 2 and 0.2 µg/L corresponds to 10⁻4, 10⁻5 and 10⁻6 upper bound risks; if ozone is used, bromate intake could be 120 to 180 µg/day in early estimates (WHO).
- Bioaccumulation
- Not addressed for bromide or bromate in the sources read; brominated flame retardants bioaccumulate, which is why brominated diphenylethers carry an EU biota standard.
- Ecotoxicity
- Not addressed for bromide or bromate in the sources read; no US EPA aquatic criterion appears in the table for either.
Flags
- The bromate formation and bromamine equations are stoichiometries written from the EPA pathway figure and WHO text; neither source prints them.
- The HOBr dissociation constant is not printed in the sources read; the pH 8 branch point is stated qualitatively by the EPA manual.
- The 0.18 mg/L bromide threshold is one 1993 study cited by WHO, not a design rule.
- The bromate occurrence range up to 293 µg/L includes laboratory studies at unrealistic bromide.
- The US FGD bromide limit belongs to the voluntary incentives programme and carries compliance dates.
- The WHO supporting document on bromine, iodine and silver as alternative disinfectants was not read; the bromine disinfectant row rests on the element entry.
- No GCC discharge standard lists bromide or bromate; the row records the absence.
Gaps
- No bromide concentrations in municipal or industrial wastewater were read; only the FGD bromide limit.
- The HOBr pKa, the ozone and hydroxyl radical rate constants and the bromate formation models (von Gunten) were not read; the EPA manual cites them.
- No bromide removal process was read; reverse osmosis and anion exchange are named by analogy only.
- EPA 300.1 preservation and the bromate MDL table were not extracted from the method text read.
- The EU total THM parametric value and the US TTHM MCL were not transcribed here; they belong to the chlorine entry.
- The WHO bromine disinfectant document and the WHO reference numbers of the bromate and bromide background documents were read from the file headers only.
- Other GCC discharge standards were not read.
- The bromate, bromide and bromamine equations added here are electron balances written from the pathways the WHO background document describes in words; no rate constants or yields were read.
- No balanced equation is written for the bromination of natural organic matter to bromoform and the brominated acetic acids: natural organic matter has no formula and no source read prints a model compound stoichiometry.
Sources
WHO Guidelines for Drinking-water Quality, 4th ed. incorporating the first and second addenda (2022), chapter 12 chemical fact sheets, Bromide and Brominated acetic acids (pp. 352 to 353)
WHO Guidelines for Drinking-water Quality, 4th ed. incorporating the first and second addenda (2022), chapter 12 chemical fact sheet, Trihalomethanes
WHO, Bromate in Drinking-water, background document for development of WHO Guidelines for Drinking-water Quality, WHO/SDE/WSH/05.08/78 (2005), sections 1, 2, 6 and 7
WHO, Bromide in Drinking-water, background document for development of WHO Guidelines for Drinking-water Quality, WHO/HSE/WSH/09.01/6 (2009), sections 1 and 2
US EPA, Alternative Disinfectants and Oxidants Guidance Manual, EPA 815-R-99-014 (April 1999), sections 2.3, 3.4 (bromate formation, Figure 3-12), 3.5.3 and 7.4 (peroxone)
US EPA Method 300.1, Revision 1.0 (1997), Determination of inorganic anions in drinking water by ion chromatography, Part B (bromate, bromide, chlorite, chlorate)
40 CFR 141.64, Maximum contaminant levels for disinfection byproducts (bromate and chlorite)
US EPA, 2018 Edition of the Drinking Water Standards and Health Advisories Tables, EPA 822-F-18-001 (March 2018)
Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Annex I Parts B and C and Annex III Table 1
40 CFR 423.13, Effluent limitations guidelines representing BAT, steam electric power generating point source category (cooling tower blowdown, FGD wastewater, gasification wastewater)
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 4 and BAT 12 Table 3 with footnotes 24 to 29
Commission Implementing Decision (EU) 2022/2508 establishing BAT conclusions for the textiles industry, BAT 8 and Tables 1.3 and 1.4 (BAT-AELs for direct and indirect discharges) with footnotes 31, 34 and 41
Directive 2013/39/EU amending Directives 2000/60/EC and 2008/105/EC as regards priority substances in the field of water policy, Annex I (environmental quality standards) and Annex II
Abu Dhabi Specification ADS 23/2017, Environmental Specifications for Land-Based Liquid Discharges to the Marine Environment (Environment Agency Abu Dhabi), Table 1
ZDHC Wastewater Guidelines Version 2.1 (November 2022), Table 1M (organotins), Table 2 (heavy metals) and Tables 4A and 4B (sludge)
The Element Book, own entry for bromine (data/elements/Br.json and data/reference/text/Br.json)
PubChem element summary for bromine; estimated oceanic abundance 6.73 x 10^1 mg/L from Jefferson Lab
Identity
- Name and symbol
- Bromine, Br
- Atomic number
- 35 protons
- Position
- group 17 · period 4 · p-block · diatomic nonmetal
- CAS number
- 7726-95-6
Atomic structure
- Atomic mass
- 79.904 u
- Electron configuration
- 1s² 2s² 2p⁶ 3s² 3p⁶ 4s² 3d¹⁰ 4p⁵
[Ar] 4s²³d¹⁰⁴p⁵ - Electrons per shell
- 2, 8, 18, 7
- Valence electrons
- 7 outer shell
| isotope | mass (u) | abundance |
|---|---|---|
| 79Br | 78.9183376(14) | 50.69 % |
| 81Br | 80.9162897(14) | 49.31 % |
Physical properties
- State at room temperature
- Liquid
- Melting point
- 265.95 K (-7.2 °C)
- Boiling point
- 331.95 K (58.8 °C)
- Density
- 3.11 g/cm3
- Appearance
- reddish-brown liquid
- Thermal conductivity
- 0.122 W/(m·K)
- Electrical resistivity
- 7.8×10¹⁰ Ω·m at 20 °C
- Electrical conductivity
- 1.28e-11 S/m
- Crystal structure
- orthorhombic
- Molar heat capacity
- not in sources
Chemical properties
- Oxidation states
- +5, +1, -1
- Electronegativity
- 2.96 (Pauling Scale)
- Ionisation energy
- 11.814 eV
1st 1,139.9, 2nd 2,103, 3rd 3,470 kJ/mol - Electron affinity
- 3.365 eV
- Atomic radius
- empirical 120, covalent 120, van der Waals 183 pm
- Ionic radius
- Br⁻ 196; Br³⁺ 59 (4sq-coordinate); Br⁵⁺ 31 (3py-coordinate); Br⁷⁺ 39 pm
- Reactivity
- The only liquid non-metal, a halogen between chlorine and iodine in reactivity: a strong oxidising agent that combines readily with most elements, weaker than chlorine but stronger than iodine.
- with water
- Dissolves readily in water to a red solution and partly disproportionates to hypobromous acid and bromide: , a reversible equilibrium.
- with oxygen, air
- Does not react with oxygen directly; the oxides and bromates are made by other routes and are strong oxidising agents.
- with acids
- No reaction with acids; in alkali it disproportionates to hypobromite and bromide: .
- with halogens
- Forms interhalogen compounds with the other halogens, for example bromine trifluoride: , and bromine pentafluoride BrF5.
- Typical compounds
- HBr hydrogen bromide hydrobromic acid; source of inorganic and alkyl bromides
- AgBr silver bromide light-sensitive salt of photographic film
- KBr potassium bromide historic sedative, infrared optics
- BrF₃ bromine trifluoride interhalogen fluorinating agent
- NaBrO₃ sodium bromate bromate oxidising agent
- C₂H₄Br₂ 1,2-dibromoethane organobromine; flame retardants use most bromine
Occurrence, production and use
- Crustal abundance
- 2.4 milligrams per kilogram
- Oceanic abundance
- 6.73×101 milligrams per liter
- Occurrence and sources
A member of the halogen group, bromine is obtained from natural brines from wells in Michigan and Arkansas. Some bromine is extracted today from seawater, which contains only about 85 ppm.
- bromide in seawater about 65 parts per million, an estimated 100 trillion tonnes; recovered as a co product of solar salt
- bromide in evaporitic lakes and underground brines the Dead Sea (Israel, Jordan; about 1 billion tonnes of bromine), petroleum associated brines in Arkansas and Michigan, brines in China
- Extraction, production
- Chlorine displacement from bromide brine
Balanced from the reactants and product stated by the RSC account of Balard's discovery (chlorine passed into concentrated brine liberates bromine), with chloride as the only possible co product; the same displacement, followed by steaming out and condensing the bromine, is the industrial route from Arkansas and Dead Sea brines. The RSC also describes extraction by electrolysis. World production about 400,000 tonnes in 2024 (estimate) excluding the United States.
Bromine recycling from hydrogen bromideHydrogen bromide emitted as a by product of organic brominations is recycled with virgin brine as a source of bromine; the OFC BREF lists recovery of bromine and HBr from exhaust gases as a technique. No reaction is stated.
- Uses
Elemental bromine is a hazardous material. It causes severe burns when it comes in contact with the skin and its vapor irritates the eyes, nose and throat. Most of the bromine produced in the United States was used in the manufacture of ethylene dibromide(C2H4Br2), a chemical added to leaded gasolines that prevented the accumulation of lead compounds within the engine. With the discontinuation of leaded gasolines in favor of unleaded gasolines, the demand for bromine has been greatly reduced. Silver bromide (AgBr), a chemical used in photography, now accounts for the largest use of bromine. Other bromine compounds are used in fumigants, in flameproofing agents and in some compounds used to purify water. Tyrian purple, an expensive purple dye known to ancient civilizations, was produced from an organic bromine compound secreted from a sea mussel known as the murex.
Bromine is used in making fumigants, flameproofing agents, water purification compounds, dyes, medicines, sanitizers, inorganic bromides for photography, etc. Organic bromides are also important.
- Flame retardants and plastics: brominated flame retardants (tetrabromobisphenol A, decabromodiphenyl oxide and others) in electronics casings, furniture foam and construction plastics; bromine in recycled plastics tends to be carried into new products brominated flame retardants and clear brine fluids are the leading global applications (USGS, ranking only)
- Textiles: brominated flame retardants applied in flame retardant finishing of cotton, viscose, polyester and other fabrics for upholstery, carpets, curtains and transport; decaBDE and related brominated compounds are discharged from that process (Textiles BREF)
- Oil and gas: calcium, zinc and sodium bromide clear brine drilling and completion fluids, for which there is no comparable substitute in well completion and packer applications
- Chemicals: bromide in salt and brine is oxidised in chlor-alkali cells to bromate, a compound of the chlor-alkali chapter; bromine impurities in cell room chlorine give brominated by products in EDC direct chlorination unless purified liquid chlorine is used (LVOC BREF); brominated intermediates, dyestuffs and agricultural chemicals
- Pharmaceuticals and fine chemicals: bromine as a halogenating agent in fine chemical synthesis, used less than chlorine because of its price; recovery of bromine and hydrobromic acid from exhaust gases
- Food and beverage: brominated vegetable oil (E443), used since the 1920s to stabilise fruit flavour oils in beverages at up to 15 parts per million; the United States FDA revoked its authorisation in July 2024 because a safe dietary level could not be established
- Water treatment and batteries: bromine compounds for water treatment and sanitation, where chlorine and iodine can substitute; zinc bromine flow batteries, from which bromine is fully recoverable; silver bromide in photography
- Safety, toxicity
- not in sources
Discovery and name
- Discovered by
- Antoine Jérôme Balard and Carl Jacob Löwig
- Discovered
- 1825
- First isolated
- not in sources
- Named by
- not in sources
- Origin of the name
- from Ancient Greek βρῶμος, 'stench', for its sharp and pungent smell
Bromine is the only nonmetallic liquid element. It is a heavy, mobile, reddish-brown liquid, volatilizing readily at room temperature to a red vapor with a strong disagreeable odor, resembling chlorine, and having a very irritating effect on the eyes and throat; it is readily soluble in water or carbon disulfide, forming a red solution, is less active than chlorine but more so than iodine; it unites readily with many elements and has a bleaching action; when spilled on the skin it produces painful sores. It presents a serious health hazard, and maximum safety precautions should be taken when handling it.
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.