Iridium

    group 9 · period 6 · d-block · transition metal

    minorIridium is a platinum group trace with no drinking water guideline, no effluent limit and no treatment role: the most corrosion resistant metal known does not dissolve in water or acid, its compounds are laboratory and catalyst materials, and its only water signal is as a minor member of the platinum group pattern in urban sewage sludge; the one place a water engineer meets it is as the iridium oxide coating on the anodes of electrochlorinators and electrolytic cells, where it is the electrode, not the water.

    Typical wastewaters

    • municipal sewage (platinum group point sources) particulate iridium ending in sewage sludge and incinerator ash, up to 33 µg/kg in 91 UK samples, higher in Sheffield and London ash measured in the sludge, not the water; the converter pattern is Pt, Pd and Rh, so the iridium is attributed to point industrial sources

    1 · Identity

    Symbol, number
    Ir, 77
    Oxidation states in water
    +3 and +4 in the chloro complexes IrCl₆³⁻ and IrCl₆²⁻ of refinery liquors and in the oxide IrO₂; the metal is inert. No natural water speciation was read.
    Note
    The element entry covers the metal, crucibles, spark plugs and the standard metre. This chapter says only where iridium touches water.

    2 · Occurrence in water

    Natural sources
    Native iridium and osmiridium in river placers and platinum group sulfide ores (element entry); dissolved iridium in natural water is at femtomolar levels and no measured value was read.
    Anthropogenic sources
    Automobile catalysts are the main platinum group source to urban drainage and sewage, but the pattern they leave is platinum, palladium and rhodium; iridium in UK sewage sludge and incinerator ash reached 33 ppb and, with osmium and ruthenium, was higher in Sheffield and London ash and attributed to point industrial sources (Jackson 2010). Spent iridium catalysts and iridium oxide anode coatings are recycled, not discharged.
    matrixtypical rangenote
    sewage sludge and sludge incinerator ash (solid, not water)up to 33 µg/kg
    solid matrix; no water concentration was read
    91 samples from 9 UK cities; maxima 602 Pt, 710 Pd, 65 Rh, 100 Ru, 33 Ir, 12 Os

    3 · Speciation

    The metal is attacked by nothing in water. Iridium enters solution only as chloro complexes, IrCl₆³⁻ for Ir(III) and IrCl₆²⁻ for Ir(IV), made with chlorine in hydrochloric acid (element entry); on dilution and neutralisation these hydrolyse slowly to hydrous oxide. IrO₂ is insoluble and is the electrocatalytic coating of mixed metal oxide anodes. No stability constants or natural water speciation were read.

    conditiondominant speciesnote
    refinery liquor, hydrochloric acid with chlorineIrCl₆²⁻, IrCl₆³⁻element entry (hexachloroiridic acid)
    natural waterparticulate metal and oxideno dissolved speciation read
    Solubility
    Metal and IrO₂ insoluble; hexachloroiridates soluble.
    Hydrolysis
    Slow hydrolysis of the chloro complexes on neutralisation; not quantified in the sources read.
    Complexation
    Chloride in acid; nothing sourced for natural water.
    Precipitates
    Hydrous iridium oxide; iridium sulfide in refinery precipitation.
    Ir+OX2IrOX2\ce{Ir + O2 -> IrO2}
    high temperature (element entry); the thermal route to the anode coating

    4 · Role in treatment

    as a reagent
    iridium oxide anode coating in electrochlorination and electrolytic cells
    IrO₂ on titanium is the durable electrocatalyst for chlorine and oxygen evolution; iridium is the electrode, not a dosed reagent, and its loss rate to the water is negligible
    the anode use is textbook electrochemistry and the element entry names IrO2 as a chlorine cell anode coating; no wear rate was read

    5 · Removal and control

    Not relevant or not given for this element.

    6 · Analytics

    methodstandarddetection limitnote
    ICP-MS after fire assay or acid digestionresearch methods (Jackson 2010 for sludge and ash); iridium is not an analyte of EPA 200.8not readiridium is used as an internal standard in some ICP-MS metal methods, which precludes measuring it in the same run
    Sampling pitfalls
    The metal resists digestion; fire assay or a chlorine and hydrochloric acid attack is needed to bring it into solution.

    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 GDWQno guideline iridium does not appear in the Annex 3 chemical summary tables; Annex 6 gives 100 Bq/L guidance levels for iridium-190 and iridium-192, a medical and industrial radiography isotope
    US EPA NPDWRnot regulated no entry in the table of regulated contaminants
    discharge
    bodylimitnote
    EU CWW BREF BAT-AEL (Decision 2016/902)not set BAT 12 metals are Cr, Cu, Ni and Zn only

    8 · Health and environmental effects

    Toxicity
    Low toxicity and no known biological role (element entry); no drinking water assessment exists.
    Bioaccumulation
    Not addressed in the sources read.
    Ecotoxicity
    Not addressed in the sources read.

    Flags

    • The only concentration is a sludge and ash maximum from one UK study; no water value was read.
    • The anode coating note rests on the element entry and textbook electrochemistry; no coating wear or iridium release figure was read.

    Gaps

    • No source read gives iridium in seawater, rivers, groundwater, drinking water or wastewater as a dissolved concentration.
    • EU DWD 2020/2184 Annex I was not read this session.
    • No aquatic or oral toxicity value for iridium was read.
    • No removal study exists in the sources read; the removal list is empty on purpose.
    • No GCC discharge standard was read.

    Sources

    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.