Rhodium

    group 9 · period 5 · d-block · transition metal

    minorRhodium has no water limit and no treatment role; it is the scarcest of the three catalytic converter metals in road dust, runoff and urban sediment (1.5 to 17.2 ng/g in Perth runoff basins against 5.4 to 61.2 for palladium), too low in natural water for the field methods to compare, and the least bioaccumulated of the three.

    Typical wastewaters

    • road runoff and stormwater (automobile catalytic converters) Rh(0) particles on road dust and runoff solids, settling in infiltration basins and wetlands 1.5 to 17.2 ng/g in Perth runoff basin sediment; no dissolved value read

    1 · Identity

    Symbol, number
    Rh, 45
    Oxidation states in water
    0 as converter particles; +3 as chloro and hydroxo complexes if dissolved
    Note
    The element entry covers the metal, its inertness and Rh₂O₃. No dissolved speciation measurement in natural water was read.

    2 · Occurrence in water

    Natural sources
    Negligible; native and sulfide ores (element entry).
    Anthropogenic sources
    Automobile three-way catalysts (the NOx reduction metal); nitric acid plant gauzes and chemical catalysts (element entry). Toronto inhalable road dust geomean 21 µg/kg Rh (Pd 152, Pt 55); Canadian road dust average 7.1 ng/g Rh.
    matrixtypical rangenote
    river, lake, stormwater and snow, Canadabelow method detection
    detection limits not stated in the summary read
    no measurable PGE in any water or snow sample
    urban river water (DGT)too low for interlaboratory comparison abstract onlyRh followed the traffic metals with the highest values in highway runoff water; no number in the abstract
    runoff basin and wetland sediment, Perth1.5 to 17.2 ng/gsedimentRh; Pd 5.4 to 61.2, Pt 9.0 to 103.8
    river sediment, Canada1.59 ng/gsedimentaverage Rh

    3 · Speciation

    Particulate metal from converters; the abstracts read give no dissolved rhodium speciation, and the Pt/Pd ratio shift seen in drainage was attributed to palladium solubilisation, not rhodium.

    conditiondominant speciesnote
    road dust, runoff solids and sedimentRh(0) particlesessentially all of the load
    Solubility
    Very low.
    Hydrolysis
    Not read.
    Complexation
    Not read.
    Precipitates
    Not relevant.

    4 · Role in treatment

    Not relevant or not given for this element.

    5 · Removal and control

    stormwater infiltration basins and wetlands
    particulate settling; concentration scales with road area drained and traffic volume
    Perth road runoff
    Efficiency
    not quoted as a percentage

    6 · Analytics

    methodstandarddetection limitnote
    ICP-MS after digestion and cation exchange; ICP-MS/MSresearch methods; no standard method readng/g in solids; below detection in waterthe isopod study monitored Hf, Cu, Y, Rb, Sr and Pb to correct spectral interferences on the PGE masses
    DGT with chelating resinresearch methodnot readno interlaboratory comparison was possible for Rh because natural concentrations are too low
    Sampling pitfalls
    Interference correction dominates the rhodium result (Cu, Sr, Rb, Pb monitored in the isopod study); at natural levels the number is mostly blank and correction.

    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/Lrhodium-105; guidance level at 0.1 mSv per year (Rh-106, the Ru-106 daughter, is covered through ruthenium-106 at 10 Bq/L)
    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. Rhodium in inhalable road dust was 14 percent bioaccessible in simulated lung fluid.
    Bioaccumulation
    The least accumulated converter metal: Asellus aquaticus from an urban river held 17.9 plus or minus 12.2 ng/g Rh (Pd 155.4, Pt 38.0) and the 24 h bioaccumulation factor was 7 (Pd 150, Pt 85); Chaoborus assimilated only 1.6 percent of dietary Rh.
    Ecotoxicity
    Not read.

    Flags

    • No dissolved rhodium concentration in water was read as a number.
    • Sediment and dust figures are the only quantitative environmental data and are quoted as such.

    Gaps

    • No dissolved Rh concentration for any water was read.
    • No speciation, solubility or ecotoxicity data were read.
    • No removal efficiency in wastewater treatment was 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 Rh (platinum group metal, inertness, catalysts) (data/elements/Rh.json, data/reference/text/Rh.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.