Palladium

    group 10 · period 5 · d-block · transition metal

    minorPalladium has no water limit and no treatment role; it is the most abundant and the most soluble of the three catalytic converter metals in road dust and runoff, so it is the platinum group element that shows up in urban river sediments, in highway runoff water and in the freshwater fauna that live on it, at nanograms per gram and femtograms to picograms per millilitre.

    Typical wastewaters

    • road runoff and stormwater (automobile catalytic converters) Pd(0) and PdO particles on road dust and runoff solids, with a small fraction solubilised as Pd(II) during transport 5.4 to 61.2 ng/g in Perth runoff basin sediment
    • municipal sewage labile palladium passing sewage works with limited retention, following the traffic metals Cu, Zn and Pb into urban rivers trend only; no concentration in the abstract read

    1 · Identity

    Symbol, number
    Pd, 46
    Oxidation states in water
    0 as metal particles shed by converters; +2 as chloro and hydroxo complexes once solubilised
    Note
    The element entry covers the metal, PdCl₂ and the catalysts. The water chemistry is that of a particle that slowly leaches, and the abstracts read give no dissolved speciation.

    2 · Occurrence in water

    Natural sources
    Negligible; placer and sulfide ores (element entry).
    Anthropogenic sources
    Automobile three-way catalysts, the main source; catalyst and jewellery workshops, pharmaceutical hydrogenation catalysts leaving with waste (element entry); dental alloys. Road dust in Toronto held a geomean 152 µg/kg Pd in the inhalable fraction against 55 Pt and 21 Rh; Canadian road dust averaged 73 ng/g Pd, 23 Pt, 7.1 Rh.
    matrixtypical rangenote
    river, lake, stormwater and snow, Canadabelow method detection
    detection limits not stated in the summary read
    no measurable PGE in water or snow from Montreal, the St Lawrence or Nunavik; the literature values the paper cites run from 35 fg/mL upward, frequently below detection
    urban river water (DGT labile fraction)not quoted as a number abstract onlyZenne (Brussels) higher than Marque (Lille); highest Pd and Rh in water collecting highway runoff; the abstract gives no concentrations
    infiltration basin and wetland sediment receiving road runoff, Perth5.4 to 61.2 ng/gsediment, not waterPd; Pt 9.0 to 103.8, Rh 1.5 to 17.2; highest at basin low points and proportional to road area drained and traffic
    river sediment, Canada3.4 ng/gsedimentaverage Pd; Rh 1.59, Pt 2.35, Ru 29

    3 · Speciation

    Emitted as metal and oxide particles on the catalyst washcoat; in drainage systems a small part of the palladium in road dust is solubilised under natural conditions, which shifts the Pt to Pd ratio between road dust and basin sediment. Dissolved palladium is expected as Pd(II) chloro and hydroxo complexes but no speciation measurement was read.

    conditiondominant speciesnote
    road dust and runoff solidsPd(0) and PdO particlesthe bulk of the load
    drainage watera small solubilised Pd(II) fractioninferred from Pt/Pd ratio shifts (Rauch 2005)
    Solubility
    Low but the highest of the three converter metals.
    Hydrolysis
    Not read.
    Complexation
    Chloride and organic ligands expected; not read.
    Precipitates
    Not relevant.

    4 · Role in treatment

    as a problem
    PGE pass through sewage works
    limited retention of PGEs in wastewater treatment plants raises concentrations in urban rivers downstream (Scheldt tributaries)
    palladium follows the traffic metals Cu, Zn and Pb rather than the hospital platinum

    5 · Removal and control

    stormwater infiltration basins and wetlands
    particulate PGE settle where flow slows; concentrations peak at topographic low points
    Perth road runoff
    Efficiency
    not quoted as a percentage
    Interferences
    partial solubilisation of Pd during transport

    6 · Analytics

    methodstandarddetection limitnote
    ICP-MS after microwave digestion and cation exchange (sediments); ICP-MS/MS (water and biota)research methods; no standard method readng/g in solids; water values frequently below detection at fg to pg/mLmethod detection limits taken as three standard deviations of fifteen spiked measurements in the Canadian study
    diffusive gradients in thin films with chelating resinresearch method (Scheldt study)not readgood interlaboratory agreement for Pt, larger discrepancies for Pd, none possible for Rh at natural levels; anion exchange resin gave lower results
    nickel sulfide fire assay and neutron activationresearch method (Toronto road dust)not readfor solids
    Sampling pitfalls
    Spectral interferences on palladium masses (yttrium, rubidium, strontium, copper, zinc argides and oxides) must be monitored; the isopod study measured Hf, Cu, Y, Rb, Sr and Pb for corrections. The 2025 Canadian study warns that literature reports of high PGE in biota may be analytical artefacts.

    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 not in Table A₃.3 (guideline values) nor in Table A₃.2 (chemicals considered but not given a value)
    EU DWD 2020/2184not set not an Annex I parameter
    US EPA NPDWRnot regulated no MCL
    WHO GDWQ Table A₆.1 (radionuclides)1000 Bq/Lpalladium-103; guidance level at 0.1 mSv per year
    discharge
    bodylimitnote
    EU CWW BREF BAT-AEL (Decision 2016/902), BAT 12not set Tables 1 to 3 carry TOC, COD, TSS, TN, Ninorg, TP, AOX, Cr, Cu, Ni and Zn only

    8 · Health and environmental effects

    Toxicity
    No human health guideline anywhere read. Palladium in inhalable road dust is only 3.4 percent bioaccessible in simulated lung fluid, against 16 percent for platinum and 14 percent for rhodium.
    Bioaccumulation
    Asellus aquaticus from an urban river held 155.4 plus or minus 73.4 ng/g Pd dry weight (Pt 38.0, Rh 17.9); 24 h bioaccumulation factors from standard solutions 150 for Pd, 85 for Pt, 7 for Rh, time dependent and higher for materials of higher PGE content. Chaoborus, by contrast, assimilated only 19 percent of dietary Pd and excreted it fast (efflux 0.69 per day), so trophic transfer is low.
    Ecotoxicity
    Not read.

    Flags

    • No dissolved palladium concentration in water was read as a number; the Scheldt abstract gives trends only and the Canadian water samples were below detection.
    • Bioaccumulation evidence conflicts between the 2001 isopod field data and the 2025 predator-prey experiments; both are quoted.

    Gaps

    • No dissolved Pd concentration for river water, road runoff, sewage or seawater was read as a number.
    • No speciation or solubility data were read.
    • No removal efficiency for Pd in wastewater treatment was read; the Scheldt abstract says retention is limited.
    • No ecotoxicity data were read.
    • No GCC standard was read.

    Sources

    Autocatalyst-derived platinum, palladium and rhodium (PGE) in infiltration basin and wetland sediments receiving urban runoff, Science of the Total Environment (2005), doi 10.1016/j.scitotenv.2004.09.030 (abstract, PubMed 15833252)
    Bioaccumulation of palladium, platinum and rhodium from urban particulates and sediments by the freshwater isopod Asellus aquaticus, Water Research (2001), doi 10.1016/s0043-1354(01)00136-1 (abstract, PubMed 11791847)
    Distribution of platinum (Pt), palladium (Pd), and rhodium (Rh) in urban tributaries of the Scheldt River assessed by diffusive gradients in thin films technique (DGT), Science of the Total Environment (2021), doi 10.1016/j.scitotenv.2021.147075 (abstract, PubMed 33905928)
    Biodynamics and Environmental Concentrations of the Platinum Group Elements in Freshwater Systems, Environmental Science and Technology (2025), doi 10.1021/acs.est.4c08750 (open access, PMC11966755)
    An assessment of the inhalation bioaccessibility of platinum group elements in road dust using a simulated lung fluid, Environmental Pollution (2018), doi 10.1016/j.envpol.2018.06.043 (abstract, PubMed 30029308)
    WHO Guidelines for Drinking-water Quality, 4th ed. incorporating the first and second addenda (2022), Annex 3 chemical summary tables: Table A3.2 chemicals for which guideline values have not been established and Table A3.3 guideline values for chemicals of health significance
    WHO Guidelines for Drinking-water Quality, 4th ed. incorporating the first and second addenda (2022), Annex 6 Table A6.1 guidance levels for radionuclides in drinking-water (individual dose criterion 0.1 mSv per year, levels rounded to the nearest order of magnitude)
    Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Annex I Parts B, C and D (annexes read on legislation.gov.uk)
    US EPA, National Primary Drinking Water Regulations (table of MCLs; inorganic chemicals and radionuclides; beta particle and photon emitters 4 millirem per year)
    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 to 3 (TOC, COD, TSS, TN, Ninorg, TP, AOX, Cr, Cu, Ni, Zn) (annex read on legislation.gov.uk)
    The Element Book, element entry and reference text for Pd (platinum group metal, PdCl2, catalysts, hydrogen absorption) (data/elements/Pd.json, data/reference/text/Pd.json)

    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.