Platinum

    group 10 · period 6 · d-block · transition metal

    minorPlatinum has no water limit and no treatment role; its water story is trace emissions from catalytic converters into road runoff and from cisplatin and carboplatin excreted by patients into hospital effluent, both at nanograms per litre.

    Typical wastewaters

    • hospital effluent (cisplatin and carboplatin) hydrolysed Pt(II) cytostatic drugs excreted by patients, dissolved, below 10 to 601 ng/L as daily averages and 20 to 3,580 ng/L in 2 hour composites at five European hospitals 3.3 to 12.3 percent of the estimated catalytic converter emissions in the countries studied
    • road runoff (catalytic converters) platinum metal particles shed by converters, the main source of platinum to urban drainage no runoff concentration was read
    • municipal sewage cytostatic platinum from hospitals and converter particles from road runoff, adsorbed to activated sludge hospital effluents are a minor source compared with cars but should not be disregarded

    1 · Identity

    Symbol, number
    Pt, 78
    Oxidation states in water
    +2 and +4 as chloro and hydroxo complexes (PtCl₄²⁻, PtCl₆²⁻) and as the hydrolysed cytostatic drugs; 0 as the metal particles shed by converters.
    Note
    The element entry covers the metal and its salts. In water platinum is a trace pollutant measured by clean ICP-MS, not a treatment parameter.

    2 · Occurrence in water

    Natural sources
    Negligible; native platinum in river sediments (element entry).
    Anthropogenic sources
    Car catalytic converters, the main source; hospital effluent from cisplatin and carboplatin, which emitted 3.3 to 12.3 percent (1.3 to 14.3 kg per year) of the estimated converter emissions in the European countries studied (Kummerer 1999); refinery and jewellery workshops in the ledger.
    matrixtypical rangenote
    hospital effluentbelow 10 to 601 (daily averages); 20 to 3580 (2 hour composites) ng/Lshort term studyfive European hospitals; the estimate from consumption data is below 10 to 710 ng/L

    3 · Speciation

    Platinum from converters is metallic and particulate; dissolved platinum is chloro or hydroxo complexed Pt(II) and Pt(IV), and the cytostatic drugs hydrolyse to aquated species that bind organic matter. Not sourced beyond the abstract.

    Solubility
    The metal is inert; the chloro complexes are soluble.
    Hydrolysis
    not relevant
    Complexation
    Chloride and amine ligands (the drugs).
    Precipitates
    not relevant

    4 · Role in treatment

    as a problem
    cytostatic platinum in hospital and municipal sewage
    excreted drugs pass to the sewer
    hospital effluents are a minor source of platinum in municipal sewage compared with cars but should not be disregarded (Kummerer 1999)
    as a reagent
    none
    platinum is not dosed
    platinised titanium anodes in electrochlorination are hardware, not a reagent

    5 · Removal and control

    not practised
    adsorption to activated sludge is the fate in sewage treatment
    not sourced
    Efficiency
    not quoted

    6 · Analytics

    methodstandarddetection limitnote
    ICP-MS after preconcentrationno standard method readng/L levels in the cited studyhafnium oxide interference on mass 195
    Sampling pitfalls
    Contamination from jewellery and laboratory ware; 2 hour composites vary 30 fold against daily averages in hospital sewage (Kummerer).

    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 no chemical fact sheet; radionuclide guidance levels, where they exist, are in chapter 9 and Annex 6
    EU DWD 2020/2184not set not an Annex I parameter
    US EPA NPDWRnot regulated no MCL
    discharge
    bodylimitnote
    EU CWW BREF BAT-AEL (Decision 2016/902)not set not a BAT 12 parameter
    industry thresholds
    sectorbodylimitnote
    textileZDHC Wastewater Guidelines v₂.1 (2022)not set not a ZDHC parameter

    8 · Health and environmental effects

    Toxicity
    Platinum salts are respiratory sensitisers occupationally; the cytostatic drugs are the toxic and genotoxic forms in effluent (not sourced beyond the abstract).
    Bioaccumulation
    not relevant
    Ecotoxicity
    not relevant

    Flags

    • Only the abstract of Kummerer 1999 was read.
    • Road runoff platinum concentrations appeared only in search summaries and are not quoted.

    Gaps

    • No source read gives platinum in road runoff, rivers, seawater or municipal effluent as numbers.
    • Speciation and removal of platinum cytostatics in sewage treatment (activated sludge sorption, advanced oxidation) were not read; the open access reviews found were not reachable.
    • No GCC document mentions platinum.

    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.