Osmium

    group 8 · period 6 · d-block · transition metal

    minorOsmium is a platinum group trace with no drinking water guideline, no effluent limit and no treatment role; the metal is inert and insoluble, and the water story is confined to laboratory waste, where the volatile, water soluble and very toxic tetroxide OsO₄ must be reduced before it goes down a drain, and to sewage sludge, where osmium is the lowest of the platinum group metals.

    Typical wastewaters

    • laboratory waste (osmium tetroxide stain and oxidant) OsO₄ (aq), a volatile molecular oxide dissolved without ionising; reduced in the fume hood to insoluble OsO₂ before disposal as heavy metal waste, never poured to sewer the reductant is not specified by the sources read
    • municipal sewage (platinum group point sources) particulate osmium ending in sewage sludge and incinerator ash, up to 12 µg/kg in 91 UK samples, higher in Sheffield and London ash measured in the sludge, not the water; attributed to point industrial sources

    1 · Identity

    Symbol, number
    Os, 76
    Oxidation states in water
    +8 as osmium tetroxide OsO₄, a volatile molecular oxide that dissolves in water without ionising; +6 as osmate from OsO₄ and alkali; +4 and +3 in the chlorides and the insoluble OsO₂. The metal does not dissolve.
    Note
    The element entry covers the metal, its density and the tetroxide hazard. This chapter is about OsO₄ in laboratory drains and the platinum group signal in sludge.

    2 · Occurrence in water

    Natural sources
    Native osmium and osmiridium in platinum group deposits and river placers (element entry); dissolved osmium in natural water is at femtomolar levels and no measured value was read.
    Anthropogenic sources
    Laboratory use of OsO₄ as a biological stain and as a diol forming oxidant in organic synthesis; catalyst waste; platinum group metal refining. UK sewage sludge and incinerator ash reached 12 ppb osmium against 602 ppb platinum and 710 ppb palladium, and the osmium, iridium and ruthenium in Sheffield and London ash were higher than elsewhere and attributed to point industrial sources (Jackson 2010).
    matrixtypical rangenote
    sewage sludge and sludge incinerator ash (solid, not water)up to 12 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

    Osmium tetroxide is a molecular oxide, soluble in water to about 6 percent at room temperature and volatile from solution (NIOSH); it does not hydrolyse to an anion at neutral pH but is reduced by any oxidisable organic matter to black OsO₂ and lower oxides. In alkali it forms the +6 osmate K₂OsO₂(OH)₄ (element entry). The metal, OsO₂ and the sulfides are insoluble. No natural water speciation study was read.

    conditiondominant speciesnote
    OsO₄ solution, neutral pHOsO₄ (aq), molecularvolatile; the laboratory hazard
    OsO₄ in alkaliOsO₂(OH)₄²⁻ (osmate)element entry
    OsO₄ with reductant (organic matter, sulfite, corn oil, thiosulfate)OsO₂ (s) and lower oxidesthe basis of laboratory neutralisation before disposal; reagent choice not sourced
    Solubility
    OsO₄ 6 percent in water at 25 C (NIOSH); the metal, OsO₂ and the sulfides insoluble.
    Hydrolysis
    OsO₄ stays molecular in neutral water.
    Complexation
    Chloro complexes in hydrochloric acid; not relevant to natural water.
    Precipitates
    OsO₂ from reduction; osmium sulfide from sulfide precipitation of refinery liquors.
    Os+2OX2OsOX4\ce{Os + 2 O2 -> OsO4}
    powdered or spongy osmium in air, slowly at room temperature (element entry); the source of the fume hazard

    4 · Role in treatment

    as a problem
    osmium tetroxide in laboratory waste
    OsO₄ is volatile from water and attacks eyes, skin and the respiratory tract; the NIOSH REL is 0.002 mg/m₃ as a time weighted average and 0.006 mg/m₃ short term, the OSHA PEL 0.002 mg/m₃ and the IDLH 1 mg/m₃, all air limits, not water
    OsO₄ solutions are reduced in the fume hood to insoluble OsO₂ before disposal as heavy metal waste; they must not be poured to sewer, and the reductant is not specified by the sources read

    5 · Removal and control

    chemical reduction then solids removal
    OsO₄ reduced to OsO₂ (s) by organic matter or a reducing agent, then settled or filtered
    laboratory and refinery waste only; no municipal or industrial treatment study read
    Efficiency
    not read
    Interferences
    oxidants regenerate the tetroxide

    6 · Analytics

    methodstandarddetection limitnote
    ICP-MS after fire assay or acid digestionresearch methods (Jackson 2010 for sludge and ash); osmium is not an analyte of EPA 200.8not readosmium is lost as OsO₄ in oxidising acid digestion unless the sample is kept reduced or the tetroxide is trapped
    Sampling pitfalls
    Any oxidising preservation or digestion volatilises osmium as OsO₄; keep samples reduced or distil and trap the tetroxide on purpose. Osmium-187 interferes with rhenium-187 in ICP-MS.

    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 osmium does not appear in the Annex 3 chemical summary tables; Annex 6 gives 100 Bq/L guidance levels for osmium-185, -191 and -193
    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
    The metal is not toxic; the tetroxide is very toxic to lungs, skin and eyes (element entry, NIOSH). No oral or drinking water assessment was read.
    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 NIOSH and OSHA numbers are workplace air limits and are placed under problems, not limits.
    • The reduction step for OsO₄ waste is standard laboratory practice; the reagent and stoichiometry were not read and are not written.

    Gaps

    • No source read gives osmium 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 toxicity or oral toxicity value for osmium or OsO₄ was read.
    • 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.