Iodine
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.
| matrix | typical range | note |
|---|---|---|
| rivers and lakes | 0.5 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 water | about 4 µg/L | the average the WHO background document uses for exposure; drinking water is about 5 percent of iodine intake |
| seawater | 50 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-131 | 1.8 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 water | 1 to 5 mg/L | bactericidal 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.
| condition | dominant species | note |
|---|---|---|
| raw water, any pH | I⁻ (iodide); iodate only where the water has been oxidised | iodide is the natural form (WHO) |
| iodine dosed, pH 5 to 7 | I₂ dominant, HOI minor; I₃⁻ if iodide is in excess | I₂ is the better sporicide and protozoacide; suitable pH 5 to 7 (WHO 2018 Table 3) |
| iodine dosed, pH 7 to 9 | HOI rising, I₂ falling; OI⁻ appears above pH 8 | HOI 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 water | IO₃⁻ (iodate) | strong oxidants complete the oxidation; iodate has little antimicrobial activity and is the harmless sink (WHO 2018, WHO fact sheet) |
| chloraminated water containing iodide | HOI persisting, then iodinated organics | chloramine 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.
4 · Role in treatment
5 · Removal and control
- Efficiency
- not quoted
- Interferences
- none stated
- Efficiency
- not quoted
- Interferences
- free chlorine contact raises trihalomethane formation, the reason chloramine was chosen
- Efficiency
- not applicable
- 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
| method | standard | detection limit | note |
|---|---|---|---|
| leuco crystal violet colorimetry | Standard 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 |
| titrimetry | Standard 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 iodate | ISO 17294-2 lists iodine among its elements | not read this session | iodine is not among the EPA 200.8 analytes; iodine memory effects in ICP-MS need alkaline rinsing |
| DPD colorimetry for iodine residual | Standard Methods 4500-I C (used for disinfectant residual as for chlorine) | not read | reads I₂ plus HOI; iodate does not respond |
| gamma spectrometry for iodine-131 | WHO Annex 6 (ISO methods for specific radionuclides) | not read | 8.04 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.
| body | limit | note |
|---|---|---|
| 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-131 | 10 Bq/L | guidance level for an individual dose of 0.1 mSv/year; iodine-125 10 Bq/L, iodine-129 1 Bq/L (Annex 6) |
| EU DWD 2020/2184 | not set | iodine is not an Annex I parameter |
| EU Directive 2013/51/Euratom, iodine-131 | 6.2 Bq/L | Annex III derived concentration for the 0.1 mSv indicative dose, not a limit on its own |
| US EPA NPDWR | not regulated | no MCL for iodine or iodide; iodine-131 falls under the beta particle and photon emitter MCL of 4 millirem per year |
| body | limit | note |
|---|---|---|
| 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 |
| sector | body | limit | note |
|---|---|---|---|
| textile | ZDHC 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, 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)
Identity
- Name and symbol
- Iodine, I
- Atomic number
- 53 protons
- Position
- group 17 · period 5 · p-block · diatomic nonmetal
- CAS number
- 7553-56-2
Atomic structure
- Atomic mass
- 126.904 u
- Electron configuration
- 1s² 2s² 2p⁶ 3s² 3p⁶ 4s² 3d¹⁰ 4p⁶ 5s² 4d¹⁰ 5p⁵
[Kr] 5s²⁴d¹⁰⁵p⁵ - Electrons per shell
- 2, 8, 18, 18, 7
- Valence electrons
- 7 outer shell
| isotope | mass (u) | abundance |
|---|---|---|
| 127I | 126.904 47(3) | 100 % |
Physical properties
- State at room temperature
- Solid
- Melting point
- 386.85 K (113.7 °C)
- Boiling point
- 457.55 K (184.4 °C)
- Density
- 4.93 g/cm3
- Appearance
- lustrous metallic gray solid, black/violet liquid, violet gas
- Thermal conductivity
- 0.449 W/(m·K)
- Electrical resistivity
- 1.3×10⁷ Ω·m at 0 °C
- Electrical conductivity
- 7.69e-8 S/m
- Crystal structure
- base-centered orthorhombic
- Molar heat capacity
- not in sources
Chemical properties
- Oxidation states
- +7, +5, +1, -1
- Electronegativity
- 2.66 (Pauling Scale)
- Ionisation energy
- 10.451 eV
1st 1,008.4, 2nd 1,845.9, 3rd 3,180 kJ/mol - Electron affinity
- 3.059 eV
- Atomic radius
- empirical 139, covalent 139, van der Waals 198 pm
- Ionic radius
- I⁻ 220; I⁵⁺ 95; I⁷⁺ 53 pm
- Reactivity
- The least reactive of the stable halogens and the weakest oxidising agent among them, a volatile blue-black solid; it combines with many elements but is displaced from iodides by the lighter halogens and shows some metallic character.
- with water
- Only slightly soluble in water (about 1 g in 3.5 L at 20 C), dissolving far better as triiodide when iodide is present: , and it disproportionates only slightly in neutral water.
- with oxygen, air
- Does not react with oxygen directly; the pentoxide I2O5 is made by dehydrating iodic acid.
- with acids
- No reaction with acids; in alkali it disproportionates to iodide and iodate: .
- with halogens
- Combines with the lighter halogens to interhalogens such as iodine monochloride: , and with fluorine to IF5 and the heptafluoride IF7.
- Typical compounds
- HI hydrogen iodide hydroiodic acid, strong acid used in acetic acid manufacture
- KI potassium iodide iodised salt; dissolves iodine as triiodide
- AgI silver iodide yellow photographic halide
- I₂O₅ iodine pentoxide oxidises carbon monoxide; CO detection reagent
- KIO₃ potassium iodate stable iodate salt; iodate minerals are an ore
- CHI₃ iodoform organoiodine from the iodoform test
Occurrence, production and use
- Crustal abundance
- 4.5×10-1 milligrams per kilogram
- Oceanic abundance
- 6×10-2 milligrams per liter
- Occurrence and sources
Ultrapure iodine can be obtained from the reaction of potassium iodide with copper sulfate. Several other methods of isolating the element are known.
- iodate in nitrate (caliche) ores Atacama desert, Chile; the leading world source
- iodide in oilfield, gasfield and salt-well brines Chiba, Japan; north-western Oklahoma; Turkmenistan, Azerbaijan, Iran
- seawater (0.05 to 0.06 ppm) and Laminaria seaweeds (up to 0.45 percent dry) oceans hold about 90 billion t; seaweed was the source before 1959
- crustal and oceanic abundance about 0.71 ppm (BGS figure via RSC); 0.45 mg/kg crust and 0.06 mg/L seawater (PubChem)
- Extraction, production
- Release of iodine from iodate recovered from nitrate ores
RSC states iodine is liberated from the iodate of nitrate ores but names no reductant, so no equation is written
Extraction of iodine vapour from processed brineRSC states iodine is stripped as vapour from brine after processing; the oxidant that converts iodide to iodine is not named, so no equation is written
Courtois, 1811 (historical)sulfuric acid added to seaweed ash released purple iodine vapour; stoichiometry not stated
- Uses
Iodine is used as a test for starch and turns a deep blue when it comes in contact with it. Potassium iodide (KI) is used to make photographic film and, when mixed with iodine in alcohol, as an antiseptic for external wounds. A radioactive isotope of iodine, iodine-131, is used to treat some diseases of the thyroid gland.
Care should be taken in handling and using iodine. It can burn the skin and damage the eyes and mucous membranes. Pure iodine is poisonous if ingested.
Iodine compounds are important in organic chemistry and very useful in medicine. Iodides, and thyroxine which contains iodine, are used internally in medicine, and as a solution of KI and iodine in alcohol is used for external wounds. Potassium iodide finds use in photography. The deep blue color with starch solution is characteristic of the free element.
- Pharmaceuticals (contrast media and drugs): iodinated X-ray contrast media, the leading world use of iodine; iodide salts and alkyl iodides in drug synthesis; iodine recovered from mother liquors; iodine-131 for thyroid therapy X-ray contrast media and pharmaceuticals rank first and second worldwide by quantity (usgs-mcs2025-iodine)
- Food and beverage (sanitisers, feed, supplements): iodophor and polyvinylpyrrolidone-iodine disinfectants in cleaning-in-place; animal feed iodine supplements; iodised salt and food supplements
- Electronics (LCD polarisers): iodine-doped polarising films for liquid crystal displays
- Chemicals: fluorochemical intermediates; catalysts; nylon; printing inks and dyes; photographic silver iodide inorganic iodine compounds about 80 percent and organic about 20 percent of US consumption in 2024 (usgs-mcs2025-iodine)
- Medicine and biocides: disinfectants and biocides; antibiotics, bromine or chlorine are the only partial substitutes
- Mining (brines and nitrate ores): by-product of Chilean nitrate mining and of oil and gas brine production
- Safety, toxicity
Care should be taken in handling and using iodine, as contact with the skin can cause lesions; iodine vapor is intensely irritating to the eyes and mucus membranes. The maximum allowable concentration of iodine in air should not exceed 1 mg/m3 (8-hour time-weighted average - 40-hour).
Discovery and name
- Discovered by
- Bernard Courtois
- Discovered
- 1811
- First isolated
- not in sources
- Named by
- not in sources
- Origin of the name
- from the Ancient Greek ιώδης, "violet", for the color of its vapor
Iodine is a bluish-black, lustrous solid, volatizing at ordinary temperatures into a blue-violet gas with an irritating odor; it forms compounds with many elements, but is less active than the other halogens, which displace it from iodides. Iodine exhibits some metallic-like properties. It dissolves readily in chloroform, carbon tetrachloride, or carbon disulfide to form beautiful purple solutions. It is only slightly soluble in water.
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.