Iodine

    group 17 · period 5 · p-block · diatomic nonmetal

    fullIodine has no WHO, EU or US drinking water limit, but it is a treatment element three times over: iodide in raw water is the precursor of the most toxic disinfection by-products known, elemental iodine is a recognised point of use disinfectant, and iodine-131 from nuclear medicine and reactor releases is a regulated radionuclide with a WHO guidance level.

    Typical wastewaters

    • hospital effluent and municipal sewage (radiopharmaceuticals) iodine-131 excreted by thyroid patients, passing activated sludge and leaving mostly in the effluent at 1.8 to 227 Bq/L one small plant with a thyroid cancer treatment centre in its catchment; earlier studies of larger plants up to 32.2 Bq/L
    • nuclear reactor releases (raw water supplies after an accident) iodine-131; speciation not stated by the source; not detected by gross activity screening removal 10 to 40 percent by coagulation or sand filtration, 40 to 70 by activated carbon or ion exchange, above 70 by reverse osmosis (WHO Table 9.4)
    • oil and gas produced water and hydraulic fracturing flowback iodide up to 56 mg/L in Appalachian brines; brine treatment plant effluents up to 28 mg/L promotes iodinated disinfection by-products at downstream chlorination
    • hospital wastewater (iodinated X-ray contrast media) iodinated contrast media making up 95 percent of the micropollutant mass in biologically treated hospital wastewater; diatrizoate recalcitrant 50 to 65 percent removal by ozone (1.08 g O₃ per g DOC), 23 mg/L PAC or UV 2400 J/m₂
    • municipal wastewater effluent (stable iodine) iodide and iodate; 2 to 25 percent captured in sludge, the rest discharged effluent average 4.0 µg/L (1.0 to 16 µg/L); some effluent streams up to 1,910 µg/L

    1 · Identity

    Symbol, number
    I, 53
    Oxidation states in water
    -1 iodide (I⁻, the natural form in almost all water); 0 molecular iodine (I₂, only when dosed as a disinfectant or formed transiently by oxidants); +1 hypoiodous acid (HOI) and hypoiodite (OI⁻), the reactive intermediates formed by chlorine, chloramine, ozone and permanganate; +5 iodate (IO₃⁻), the stable end product of strong oxidation and the harmless sink. Triiodide I₃⁻ forms when I₂ meets excess iodide (element entry).
    Note
    The element entry covers the hydrolysis to iodide and iodate in alkali and the triiodide equilibrium. This chapter follows iodide into the treatment plant, where the oxidant decides whether it ends as iodate or as an iodinated organic.

    2 · Occurrence in water

    Natural sources
    Iodine occurs naturally in water as iodide (WHO fact sheet). The ocean is the reservoir (element entry), so iodide is highest in seawater, saline groundwater, brines and coastal aquifers with marine intrusion; rivers and lakes carry a few micrograms per litre. Traces of iodine are produced by oxidation of iodide during water treatment (WHO).
    Anthropogenic sources
    Iodine dosed deliberately as a field or emergency disinfectant (WHO 2018: 2.5 to 7 mg/L historically, tablets since the 1940s, about 2 mg/L residual aboard spacecraft); iodine-131 excreted by thyroid patients and reaching sewage (Rose 2012); iodine chemicals manufacture and iodinated X-ray contrast media are in the ledger, not sourced here.
    matrixtypical rangenote
    rivers and lakes0.5 to 20 µg/L
    compilation of averages, not a distribution
    average concentrations quoted by the WHO fact sheet; the background document gives a North American average of 4 µg/L and a maximum of 18 µg/L (ATSDR 2004), presumably mainly iodide
    drinking waterabout 4 µg/Lthe average the WHO background document uses for exposure; drinking water is about 5 percent of iodine intake
    seawater50 to 60 µg/L
    single figure from the book entry
    iodide plus iodate; from the element entry (about 0.05 to 0.06 ppm)
    municipal wastewater effluent, iodine-1311.8 to 227 Bq/L
    single plant with an unusual hospital catchment
    sewage effluent of a small plant serving a thyroid cancer treatment centre (Stony Brook, USA); earlier studies of larger plants reported up to 32.2 Bq/L; activated sludge recycling holds iodine in the plant for a sewage half life of 3 days and most iodine-131 leaves in the effluent, not the sludge
    iodine disinfected water1 to 5 mg/Lbactericidal residual after a 7 to 9 mg/L dose to meet the demand of tap water (Chang and Morris 1953, quoted by WHO 2018); taste threshold 0.147 to 0.204 mg/L

    3 · Speciation

    In untreated water iodine is iodide, a conservative, weakly sorbed anion. Added I₂ hydrolyses to HOI and iodide; between pH 5 and 9 the active disinfectant shifts from I₂ (99 percent at pH 5) towards HOI, and at pH 8 and above HOI slowly disproportionates to iodate and iodide (WHO 2018). Chlorine and ozone push iodide all the way to iodate; chloramine stops at HOI, which is why chloraminated coastal supplies form iodinated by-products (WHO fact sheet). Iodate is inert and non toxic; HOI is the species that reacts with natural organic matter.

    conditiondominant speciesnote
    raw water, any pHI⁻ (iodide); iodate only where the water has been oxidisediodide is the natural form (WHO)
    iodine dosed, pH 5 to 7I₂ dominant, HOI minor; I₃⁻ if iodide is in excessI₂ is the better sporicide and protozoacide; suitable pH 5 to 7 (WHO 2018 Table 3)
    iodine dosed, pH 7 to 9HOI rising, I₂ falling; OI⁻ appears above pH 8HOI is 3 to 4 times more effective than I₂ against E. coli and the better virucide (pH 8 to 9); at pH 8 and above HOI decomposes slowly to iodate and iodide (WHO 2018)
    chlorinated or ozonated waterIO₃⁻ (iodate)strong oxidants complete the oxidation; iodate has little antimicrobial activity and is the harmless sink (WHO 2018, WHO fact sheet)
    chloraminated water containing iodideHOI persisting, then iodinated organicschloramine oxidises iodide to HOI but does not take it on to iodate, so HOI reacts with natural organic matter to iodinated DBPs (WHO fact sheet: formed most often during chloramination when complete oxidation is prevented)
    Solubility
    Elemental iodine is only sparingly soluble: 0.34 g/L at 25 C in the WHO background document (about 1 g in 3.5 L in the element entry); a saturated solution made by passing water through an iodine crystal column holds about 200 mg/L at 10 C and 400 mg/L at 30 C and is diluted to the dose (WHO 2018). Iodide and iodate salts are freely soluble; no iodine solid limits iodine in natural water.
    Hydrolysis
    I₂ + H₂O gives HOI, iodide and a proton; the overall stoichiometry holds between pH 2 and 7 (WHO 2018, after Lengyel, Epstein and Kustin 1993). The hydrolysis is less pH sensitive than that of chlorine, which is why iodine keeps its efficacy from pH 4.5 to 8.1 and declines only slowly to pH 10 (WHO 2018).
    Complexation
    Iodide forms the triiodide ion with I₂ (element entry) and is otherwise a free anion; iodine binds covalently to natural organic matter through HOI substitution, which is the by-product route, not a complexation equilibrium. No stability constants are printed in the sources read.
    Precipitates
    None relevant in water treatment. Silver iodide is the analytical and photographic precipitate (element entry) and the reason iodide interferes with silver based disinfection; no iodine solid forms in ordinary treatment.
    IX2+HX2OHOI+IX+HX+\ce{I2 + H2O -> HOI + I^- + H+}
    hydrolysis of dosed iodine, pH 2 to 7 overall stoichiometry; the equilibrium shifts to HOI as pH rises
    3HOIIOX3X+2IX+3HX+\ce{3 HOI -> IO3^- + 2 I^- + 3 H+}
    slow disproportionation of hypoiodous acid at pH 8 and above; slow in the absence of a stronger oxidant (WHO 2018, after Ellis and van Vree 1989); balance written here
    IX+HOClHOI+ClX\ce{I^- + HOCl -> HOI + Cl^-}
    first step when chlorine meets iodide; fast
    HOI+2HOClIOX3X+2ClX+3HX+\ce{HOI + 2 HOCl -> IO3^- + 2 Cl^- + 3 H+}
    chlorine completes the oxidation to iodate, the harmless sink; chloramine does not do this step, so HOI survives to react with organic matter (WHO fact sheet: iodinated DBPs form most often during chloramination); stoichiometry written here as the electron balance
    NHX2Cl+IX+HX2OHOI+NHX3+ClX\ce{NH2Cl + I^- + H2O -> HOI + NH3 + Cl^-}
    monochloramine oxidises iodide to HOI but not further; electron balance written here, not printed by WHO
    IX2+IXIX3X\ce{I2 + I^- <=> I3^-}
    triiodide forms whenever iodide is in excess of the dosed iodine, as it is in a saturated iodine solution or late in a contact tank; triiodide is a poor disinfectant, so iodide accumulation in a recirculating point of use system costs efficacy at constant total iodine
    HOIOIX+HX+\ce{HOI <=> OI^- + H+}
    hypoiodite appears above about pH 8 and, unlike hypochlorite, is not the useful species: it is the entry to the slow disproportionation to iodate and iodide, so the disinfecting window closes above pH 9; the dissociation constant is not printed in the sources read
    IX+3OX3IOX3X+3OX2\ce{I^- + 3 O3 -> IO3^- + 3 O2}
    ozone takes iodide straight through to iodate, the inert sink, in one pass; this is why an ozonated supply forms no iodinated by-products while a chloraminated one does; the electron balance is written here, WHO states the outcome without the stoichiometry
    AgX++IXAgI(s)\ce{Ag^+ + I^- -> AgI (s)}
    silver iodide, the analytical and photographic solid; it is also why iodide bearing water blunts silver based point of use disinfection, the silver being taken out of solution as the halide

    4 · Role in treatment

    as a problem
    iodinated disinfection by-products
    iodide oxidised to HOI by chlorine or chloramine reacts with natural organic matter; chloramination is the worst case because it stops short of iodate
    occasionally detected in drinking water from plants in coastal saltwater areas; the remedy is removing natural organic matter before disinfection without compromising disinfection (WHO fact sheet)
    taste and odour of iodine residual
    free iodine residual
    taste threshold 0.147 to 0.204 mg/L, nearly independent of pH, versus 0.075 to 0.45 mg/L for chlorine depending on pH (WHO 2018)
    thyroid exposure from long term iodine disinfection
    iodine and iodide intake from water on top of diet
    WHO does not recommend iodine as a primary disinfectant and cautions against long term point of use disinfection in susceptible individuals; upper intake levels 500 to 1100 µg/day (WHO fact sheet and background document)
    iodine-131 in sewage effluent
    excreta of thyroid patients pass through activated sludge plants largely untouched
    1.8 to 227 Bq/L in one plant's effluent (Rose 2012); the WHO guidance level is 10 Bq/L for drinking water, so downstream intakes should know about upstream hospitals
    as a reagent
    point of use disinfectant (iodine tablets, iodine solutions, iodine resin columns)
    I₂ and HOI oxidise cell components; HOI is the better virucide and bactericide, I₂ the better sporicide and protozoacide
    IX2+HX2OHOI+IX+HX+\ce{I2 + H2O -> HOI + I^- + H+}
    dose 7 to 9 mg/L to leave a 1 to 5 mg/L residual in tap water (Chang and Morris 1953); best at pH 7 to 7.5 where both I2 and HOI are present; higher doses at low temperature; 2.5 to 7 mg/L used since the early 1900s, about 2 mg/L residual aboard spacecraft; not recommended by WHO for primary or long term disinfection
    iodometric analysis of oxidants
    chlorine, ozone and other oxidants liberate I₂ from added iodide, which is titrated with thiosulfate
    HOCl+2IX+HX+IX2+ClX+HX2O\ce{HOCl + 2 I^- + H+ -> I2 + Cl^- + H2O}
    the iodometric titrations of Standard Methods 4500-Cl B and C; iodine here is a reagent, never a residual; stoichiometry written here
    thiosulfate titration of the liberated iodine
    the iodine released by the oxidant is titrated with standard sodium thiosulfate to a starch or amperometric end point; iodine is the electron shuttle between the oxidant and the titrant
    IX2+2SX2OX3X22IX+SX4OX6X2\ce{I2 + 2 S2O3^2- -> 2 I^- + S4O6^2-}
    acidified sample, Standard Methods 4500-Cl B and C; the same thiosulfate is the quenching agent that stops the oxidant in a preserved sample; the stoichiometry is the standard iodometric one, the normality and factors of the method were not read

    5 · Removal and control

    removal of natural organic matter before disinfection (coagulation, activated carbon)
    iodide itself is not removed; taking out the organic precursor cuts iodinated by-product formation
    the WHO advice for all DBPs, provided disinfection is not compromised
    Efficiency
    not quoted
    Interferences
    none stated
    choice of oxidant
    chlorine or ozone ahead of chloramination oxidises iodide to inert iodate instead of leaving HOI for the organics
    HOI+2HOClIOX3X+2ClX+3HX+\ce{HOI + 2 HOCl -> IO3^- + 2 Cl^- + 3 H+}
    iodinated DBPs form most often during chloramination when complete oxidation is prevented (WHO fact sheet); the operating consequence is a free chlorine contact before ammonia addition in iodide bearing supplies
    Efficiency
    not quoted
    Interferences
    free chlorine contact raises trihalomethane formation, the reason chloramine was chosen
    treatment of iodide as a contaminant
    not applicable in normal practice
    WHO: treatment performance not applicable as occurrence in drinking water is usually low
    Efficiency
    not applicable
    radioiodine removal
    iodine-131 in a supply after a release
    RCl+IXRI+ClX\ce{RCl + I^- -> RI + Cl^-}
    WHO Table 9.4: coagulation 10 to 40 percent, sand filtration 10 to 40, activated carbon 40 to 70, precipitation softening 0 to 10, ion exchange 40 to 70, reverse osmosis above 70 percent; iodine and tritium are not detected by gross activity screening and need specific analysis (Table 9.2 note). R is a strong base anion exchange site in the chloride form; the exchange is what stands behind the 40 to 70 percent WHO figure, and it acts on iodide, not on iodate, which is the speciation caveat
    Efficiency
    activated carbon and ion exchange 40 to 70 percent, reverse osmosis above 70 percent
    Interferences
    speciation: iodide passes filters, iodate is retained differently; not stated by WHO

    6 · Analytics

    methodstandarddetection limitnote
    leuco crystal violet colorimetryStandard Methods 4500-I B (iodine) and 4500-I- (iodide)10 µg/L for iodine; applicable to iodide at 50 to 6000 µg/L (WHO background document)the method WHO quotes for its limit of detection
    titrimetryStandard Methods 4500-I- (iodide, titrimetric)iodide at 2 to 20 mg/L (WHO background document)for brines and disinfectant stock, not raw water
    ICP-MS for total iodine; ion chromatography for iodide and iodateISO 17294-2 lists iodine among its elementsnot read this sessioniodine is not among the EPA 200.8 analytes; iodine memory effects in ICP-MS need alkaline rinsing
    DPD colorimetry for iodine residualStandard Methods 4500-I C (used for disinfectant residual as for chlorine)not readreads I₂ plus HOI; iodate does not respond
    gamma spectrometry for iodine-131WHO Annex 6 (ISO methods for specific radionuclides)not read8.04 day half life; count promptly
    Sampling pitfalls
    Iodide is stable in a clean bottle but oxidises to I₂ and volatilises if the sample is chlorinated or acidified in air; quench disinfectant residuals and keep samples cool and dark. Iodine residual is measured on site. Iodine-131 samples decay by half every 8 days, so the count must be corrected to sampling time.

    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)no guideline available data inadequate for a health based value and occurrence usually low; JECFA PMTDI 1000 µg/day (17 µg/kg body weight) from all sources; iodine not recommended as a primary disinfectant but usable at the point of use; assessment 2020
    WHO GDWQ chapter 9, iodine-13110 Bq/Lguidance level for an individual dose of 0.1 mSv/year; iodine-125 10 Bq/L, iodine-129 1 Bq/L (Annex 6)
    EU DWD 2020/2184not set iodine is not an Annex I parameter
    EU Directive 2013/51/Euratom, iodine-1316.2 Bq/LAnnex III derived concentration for the 0.1 mSv indicative dose, not a limit on its own
    US EPA NPDWRnot regulated no MCL for iodine or iodide; iodine-131 falls under the beta particle and photon emitter MCL of 4 millirem per year
    discharge
    bodylimitnote
    EU CWW BREF BAT-AEL (Decision 2016/902)not set iodine is not among the BAT 12 parameters
    US EPA effluent guidelines (40 CFR)not regulated no iodine limitation found in the parts read (414, 423, 433, 440)
    Abu Dhabi ADS 23/2017 (marine outfall) and DoE Trade Effluent Control Regulations 2022 (sewer)not set
    region-dependent; other GCC states not read
    iodine is not a listed parameter in either table
    industry thresholds
    sectorbodylimitnote
    textileZDHC Wastewater Guidelines v₂.1 (2022)not set iodine is not a ZDHC parameter

    8 · Health and environmental effects

    Toxicity
    Essential for thyroid hormones; WHO/FAO recommended intakes 90 to 200 µg/day, JECFA PMTDI 1000 µg/day, upper intake levels 500 to 1100 µg/day. Excess causes hypothyroidism with or without goitre, hyperthyroidism and changes in thyroid malignancies; no threshold for thyrotoxicosis could be identified, and iodine and iodide differ in their thyroid effects, which is why no guideline exists (WHO). Iodinated DBPs are the concern in treated water; iodine-131 is a thyroid dose.
    Bioaccumulation
    Iodine concentrates in seaweed (0.1 to 0.2 percent iodide by weight) and seafood (200 to 1000 µg/kg), the natural dietary sources (WHO background document); iodine-131 concentrates in thyroid tissue.
    Ecotoxicity
    Not addressed in the sources read; no EPA aquatic life criterion or EU EQS exists for iodine.

    Flags

    • The 0.5 to 20 µg/L river and lake figure is a WHO compilation of averages; coastal and saline groundwaters run far higher and were not sourced.
    • The seawater figure is the book's own element entry, not a water chemistry source.
    • The iodine-131 effluent range is one plant with a thyroid cancer centre in its catchment (Rose 2012).
    • The WHO 2018 disinfectant document prints an iodine solubility of 0.03 mg/L at 20 C, which contradicts the background document (0.34 g/L at 25 C) and the element entry; the g/L figure is used and the mg/L figure treated as a misprint.
    • The iodate formation, chloramine and iodometric equations are electron balances written here; WHO describes the pathways without printing equations.
    • The Standard Methods 4500-I method numbers are cited from memory of the method index, not re-read; no DOI was obtained.
    • Iodine detection limits by ICP-MS and ion chromatography were not read.

    Gaps

    • No source read gives iodide in groundwater, seawater as a range, municipal wastewater or industrial wastewater; only the WHO averages and one iodine-131 effluent study are quoted.
    • Iodinated DBP occurrence data (iodoacetic acid, iodinated trihalomethanes in µg/L) were not read; the WHO fact sheet only states that they occur in coastal plants.
    • Rate constants for iodide oxidation by chlorine, chloramine and ozone are not in the sources read.
    • The GCC tables list no iodine; other GCC states not read.
    • Iodine resin disinfection is not covered; iodide removal by anion exchange is written as the standard halide exchange behind the WHO radioiodine table, no resin capacity or selectivity figure was read, and silver impregnated carbon is not covered.
    • The HOI dissociation constant, the iodide ozonation rate and the thiosulfate titration factors are not in the sources read; the triiodide and silver iodide equations come from the book's own iodine entry.

    Sources

    WHO Guidelines for Drinking-water Quality, 4th ed. incorporating the first and second addenda (2022), chapter 12 chemical fact sheet, Iodine (pp. 413 to 414)
    WHO, Iodine in Drinking-water, background document for development of WHO Guidelines for Drinking-water Quality, WHO/HEP/ECH/WSH/2020.5 (2020), sections 1, 2, 7.2 and 7.3
    WHO, Alternative drinking-water disinfectants: bromine, iodine and silver (2018), Part II Iodine as a drinking-water disinfectant, sections 1, 2.1 and 2.2
    WHO Guidelines for Drinking-water Quality, 4th ed. incorporating the first addendum, chapter 9 Radiological aspects (sections 9.2 to 9.7, Tables 9.2 and 9.4, Box 9.5)
    WHO Guidelines for Drinking-water Quality, 4th ed. incorporating the first and second addenda (2022), Annex 6 Supporting information on radionuclides, Table A6.1 guidance levels
    Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Article 11, Annex I Part B, Annex II Part D and Annex III
    Council Directive 2013/51/Euratom laying down requirements for the protection of the health of the general public with regard to radioactive substances in water intended for human consumption, Annex I (parametric values and notes) and Annex III (screening, derived concentrations, performance characteristics)
    US EPA, National Primary Drinking Water Regulations (table of MCLs and MCLGs, inorganic chemicals and radionuclides)
    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
    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 2 heavy metals and Table 4 sludge parameters
    Rose, P. S., Swanson, R. L. and Cochran, J. K., Medically-derived 131I in municipal sewage effluent, Water Research 46 (2012) 5663 to 5671, doi 10.1016/j.watres.2012.07.045 (abstract)
    Standard Methods for the Examination of Water and Wastewater (online edition), 4500-I Iodine and 4500-I- Iodide (leuco crystal violet, catalytic reduction, voltammetric methods)
    ISO 17294-2:2023, Water quality. Application of ICP-MS. Part 2: Determination of selected elements including uranium isotopes
    The Element Book, element entry and reference text for I (data/elements/I.json, data/reference/text/I.json)
    Harkness J. S., Dwyer G. S., Warner N. R., Parker K. M., Mitch W. A., Vengosh A., Iodide, bromide, and ammonium in hydraulic fracturing and oil and gas wastewaters: environmental implications, Environmental Science and Technology 49(3), 1955 to 1963 (2015), doi 10.1021/es504654n (abstract)
    Kovalova L., Siegrist H., von Gunten U., Eugster J., Hagenbuch M., Wittmer A., Moser R., McArdell C. S., Elimination of micropollutants during post-treatment of hospital wastewater with powdered activated carbon, ozone, and UV, Environmental Science and Technology 47(14), 7899 to 7908 (2013), doi 10.1021/es400708w (abstract)
    ATSDR, Toxicological Profile for Iodine (2004), section 6.2.2 releases to water and section 6.4.2 water (read from the Internet Archive copy of the PDF)

    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.