Bromine

    group 17 · period 4 · p-block · diatomic nonmetal

    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
    In the ledger's plant and process records, discharged by: Cleaning-in-place and disinfection (Food and beverage)

    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).
    matrixtypical rangenote
    seawater, bromide65 to over 80 mg/Lhigher in confined sea areas; PubChem gives 67.3 mg/L as the oceanic abundance
    fresh water, bromidetrace to about 0.5 mg/Lregion-dependent
    desalinated water, bromideup to about 1 mg/Lthe reason post chlorination of desalinated water is a brominated DBP problem
    ozonated drinking water, bromatebelow 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, bromate4.3 to 37.3, mean 18 µg/Lsingle surveyHealth Canada survey
    ozonated water in early studies, bromate60 to 90 µg/LHaag 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).

    conditiondominant speciesnote
    natural water, any pH and EhBr⁻conservative tracer behaviour
    during ozonation, pH below about 8HOBr, brominated organics, bromamines if ammonia is presentthe organic by-product branch
    during ozonation, pH above about 8OBr⁻, then BrO₃⁻the bromate branch; alkalinity and temperature raise bromate formation, ozone stability falls
    during chlorinationHOBr from Br⁻ and HOCl; bromoform, bromodichloromethane, dibromochloromethane, bromoacetic acidsbromine substitutes for chlorine in the THM and HAA series
    chlorine dioxideBr⁻ unchangedno hypobromite or bromate; bromate only under light, thermodynamically unfavourable (WHO)
    hypochlorite stock solutionsBrO₃⁻ from bromide impurities at high pHa 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.
    BrX+OX3OBrX+OX2\ce{Br^- + O3 -> OBr^- + O2}
    first step of ozonation of bromide water; Figure 3-12 of the EPA manual shows the pathways; the stoichiometry is written here
    HOBrOBrX+HX+\ce{HOBr <=> OBr^- + H+}
    the branch point: low pH keeps HOBr, which brominates organics; high pH gives OBr^-, which goes to bromate
    OBrX+2OX3BrOX3X+2OX2\ce{OBr^- + 2 O3 -> BrO3^- + 2 O2}
    molecular ozone and hydroxyl radical pathways to bromate; formation rises with bromide, ozone dose, pH, temperature and alkalinity and falls with a low ozone to DOC ratio
    HOBr+NHX3NHX2Br+HX2O\ce{HOBr + NH3 -> NH2Br + H2O}
    ammonia addition with a short ozone contact time diverts hypobromous acid to monobromamine, cutting both bromate and brominated organics; the monobromamine can be oxidised on to nitrate (WHO)
    BrX+HOClHOBr+ClX\ce{Br^- + HOCl -> HOBr + Cl^-}
    chlorination of bromide water; the hypobromous acid then forms brominated trihalomethanes and haloacetic acids with natural organic matter
    BrX2+HX2OHOBr+HX++BrX\ce{Br2 + H2O <=> HOBr + H+ + Br^-}
    hydrolysis of bromine when it is used as a disinfectant; the equilibrium is in the element entry
    3OBrXBrOX3X+2BrX\ce{3 OBr^- -> BrO3^- + 2 Br^-}
    disproportionation of basic hypobromite; stable at 0 C, rapid at about 50 C and above; the WHO document states the behaviour citing Cotton and Wilkinson without printing the stoichiometry, which is the same three to one disproportionation as hypochlorite
    BrX+3OClXBrOX3X+3ClX\ce{Br^- + 3 OCl^- -> BrO3^- + 3 Cl^-}
    bromide impurity in salt and caustic oxidised inside concentrated, high pH hypochlorite stock and in on-site electrolytic generators fed with bromide bearing brine; a bromate source in the finished water with no ozone anywhere in the plant; the stoichiometry is the electron balance, WHO names the source without printing it
    NHX2Br+3OX3NOX3X+BrX+2HX++3OX2\ce{NH2Br + 3 O3 -> NO3^- + Br^- + 2 H+ + 3 O2}
    the ammonia lever delays bromine rather than removing it: monobromamine formed at short ozone contact is oxidised on to nitrate and the bromide is released again; written as the electron balance, WHO names the reaction without printing it
    AgX++BrXAgBr(s)\ce{Ag^+ + Br^- -> AgBr (s)}
    silver form cartridge used in ion chromatography to strip chloride from a high chloride sample before the bromate peak; bromide is lost with the chloride, so bromide and bromate cannot both be measured on a cartridge treated aliquot

    4 · Role in treatment

    as a problem
    bromate formation during ozonation
    ozone and hydroxyl radicals oxidise bromide through hypobromite to bromate
    bromide at or above 0.18 mg/L is the level flagged by WHO (Krasner 1993); other drivers are ozone dose and CT, pH, temperature, alkalinity and DOC; peroxone generally makes more bromate than ozone at the same residual, comparable in some studies (EPA)
    bromate cannot be removed
    stable, soluble, unsorbed anion
    WHO: no practical removal method; ion exchange and membranes suggested for evaluation; control is by limiting formation, and below 0.01 mg/L is achievable by control of disinfection conditions
    brominated disinfection by-products with chlorine
    HOBr from bromide oxidation brominates natural organic matter
    WHO guideline values bromoform 100 µg/L, dibromochloromethane 100 µg/L, bromodichloromethane 60 µg/L; brominated acetic acids have no guideline for lack of data; the levels of bromide that form these by-products are far below any bromide health value
    the control measures conflict
    low pH cuts bromate but raises bromoform and other brominated organics and hurts corrosion control; ammonia diverts HOBr to bromamine
    WHO and EPA both say the balance must be struck plant by plant
    bromate in hypochlorite
    bromide in salt and caustic is oxidised in the concentrated, high pH hypochlorite; on-site electrolytic generators with bromide bearing brine do the same
    a bromate source without ozone; the chlor-alkali chapter of the ledger carries bromate for the same reason
    BrX+3OClXBrOX3X+3ClX\ce{Br^- + 3 OCl^- -> BrO3^- + 3 Cl^-}
    concentrated hypochlorite stock at high pH, warm storage; controlled by low bromide salt and caustic, cool dark storage and short stock life, the same controls as chlorate
    desalinated and saline source water
    bromide up to 1 mg/L in desalinated water and higher in intruded coastal wells
    post chlorination of such water is bromine dominated DBP chemistry
    as a reagent
    bromine and bromine releasing chemicals as disinfectants
    hypobromous acid is the active species, as hypochlorous acid is for chlorine
    BrX2+HX2OHOBr+HX++BrX\ce{Br2 + H2O <=> HOBr + H+ + Br^-}
    used in water treatment and sanitation where chlorine and iodine can substitute (element entry, USGS); WHO treats bromine in its supporting document on alternative disinfectants (bromine, iodine and silver), which was not read

    5 · Removal and control

    bromate control by disinfection conditions
    limit formation rather than remove: pH below 8, ammonia addition with a short ozone contact time, lower ozone dose and CT, low ozone to DOC ratio, staged ozone addition
    HOBr+NHX3NHX2Br+HX2O\ce{HOBr + NH3 -> NH2Br + H2O}
    WHO and EPA list the same levers; each has a cost in organic by-products, disinfection credit or corrosion 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
    bromate removal after formation
    none practical; ion exchange and membrane filtration suggested for evaluation
    RCl+BrOX3XRBrOX3+ClX\ce{RCl + BrO3^- -> RBrO3 + Cl^-}
    WHO 2003 statement; no full scale process read. R is a strong base anion exchange site in the chloride form; WHO suggests ion exchange and membranes for evaluation only, and sulfate and nitrate compete for the same sites
    Efficiency
    not established
    chlorine dioxide instead of ozone or chlorine
    chlorine dioxide does not oxidise bromide, so no hypobromite, brominated organics or bromate form
    the trade is chlorite and chlorate (WHO chlorine dioxide document, cited in the chlorine entry of this book)
    Efficiency
    bromate avoided, not removed
    Interferences
    light plus chlorine dioxide can form traces of bromate
    bromide removal
    no conventional process removes bromide; reverse osmosis and anion exchange are the candidates by analogy with other monovalent anions
    RCl+BrXRBr+ClX\ce{RCl + Br^- -> RBr + Cl^-}
    the sources read describe no bromide removal process. The exchange is written from the standard chloride form anion exchange of a monovalent anion (MWH chapter 16, from the chapter, not re-read); bromide sits just above chloride and well below sulfate and nitrate in resin selectivity, so a bromide run is short and sulfate rich water is not a candidate
    Efficiency
    not read

    6 · Analytics

    methodstandarddetection limitnote
    ion chromatography with suppressed conductivity detectionEPA 300.1 Part B (bromate, bromide, chlorite, chlorate); Standard Methods 4110; ISO 10304bromate 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 sheetthe 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 detectionEPA 317.0 and 326.0bromate MDL below 0.2 µg/L, PQL about 1 µg/L
    ion chromatography with ICP-MS detectionEPA 328.1 (WHO citation); EPA 321.8bromate MDL 0.3 µg/L, PQL about 1 µg/Lisotope specific bromine detection
    bromide by ion chromatographyEPA 300.1 Part A; Standard Methods 4110; ISO 10304-1not readbromide 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.

    drinking water
    bodylimitnote
    WHO GDWQ 4th ed. with addenda (2022), bromate10 µg/Lprovisional 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, bromideno 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 trihalomethanes100 bromoform; 100 dibromochloromethane; 60 bromodichloromethane µg/Lindividual guideline values; the sum of the ratios of each THM to its guideline value should not exceed 1
    EU DWD 2020/2184, bromate10 µg/LAnnex I Part B; uncertainty of measurement 40 percent of the parametric value (Annex III)
    US EPA NPDWR, bromate0.010 mg/LMCL 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), bromate0.005 mg/L at 10^-4 cancer riskone day health advisory 0.2 mg/L, RfD 0.004 mg/kg per day, DWEL 0.14 mg/L; cancer group B₂
    discharge
    bodylimitnote
    EU CWW BREF BAT-AEL (Decision 2016/902), AOX0.20 to 1.0 mg/Ladsorbable 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), AOX0.1 to 0.4 mg/Lall processes, direct and indirect discharge; brominated flame retardant finishing contributes
    US EPA 40 CFR 423.13(g)(3), FGD wastewater, voluntary incentives programme, bromide0.2 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 2022not set region-dependentneither bromide nor bromate appears in the tables read
    industry thresholds
    sectorbodylimitnote
    textileZDHC 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 substancesnot 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 sheet, Bromate (pp. 351 to 352)
    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

    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.