Palladium
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.
| matrix | typical range | note |
|---|---|---|
| river, lake, stormwater and snow, Canada | below 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 only | Zenne (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, Perth | 5.4 to 61.2 ng/gsediment, not water | Pd; 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, Canada | 3.4 ng/gsediment | average 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.
| condition | dominant species | note |
|---|---|---|
| road dust and runoff solids | Pd(0) and PdO particles | the bulk of the load |
| drainage water | a small solubilised Pd(II) fraction | inferred 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
5 · Removal and control
- Efficiency
- not quoted as a percentage
- Interferences
- partial solubilisation of Pd during transport
6 · Analytics
| method | standard | detection limit | note |
|---|---|---|---|
| ICP-MS after microwave digestion and cation exchange (sediments); ICP-MS/MS (water and biota) | research methods; no standard method read | ng/g in solids; water values frequently below detection at fg to pg/mL | method detection limits taken as three standard deviations of fifteen spiked measurements in the Canadian study |
| diffusive gradients in thin films with chelating resin | research method (Scheldt study) | not read | good 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 activation | research method (Toronto road dust) | not read | for 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.
| body | limit | note |
|---|---|---|
| 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 2020/2184 | not set | not an Annex I parameter |
| US EPA NPDWR | not regulated | no MCL |
| WHO GDWQ Table A₆.1 (radionuclides) | 1000 Bq/L | palladium-103; guidance level at 0.1 mSv per year |
| body | limit | note |
|---|---|---|
| EU CWW BREF BAT-AEL (Decision 2016/902), BAT 12 | not 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
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)
Identity
- Name and symbol
- Palladium, Pd
- Atomic number
- 46 protons
- Position
- group 10 · period 5 · d-block · transition metal
- CAS number
- 7440-05-3
Atomic structure
- Atomic mass
- 106.42 u
- Electron configuration
- 1s² 2s² 2p⁶ 3s² 3p⁶ 4s² 3d¹⁰ 4p⁶ 4d¹⁰
[Kr] 4d¹⁰ - Electrons per shell
- 2, 8, 18, 18
- Valence electrons
- 28 ns and (n-1)d
| isotope | mass (u) | abundance |
|---|---|---|
| 102Pd | 101.905 632(4) | 1.02 % |
| 104Pd | 103.904 030(9) | 11.14 % |
| 105Pd | 104.905 079(8) | 22.33 % |
| 106Pd | 105.903 480(8) | 27.33 % |
| 108Pd | 107.903 892(8) | 26.46 % |
| 110Pd | 109.905 173(5) | 11.72 % |
Physical properties
- State at room temperature
- Solid
- Melting point
- 1,828.05 K (1,554.9 °C)
- Boiling point
- 3,236 K (2,962.85 °C)
- Density
- 12 g/cm3
- Appearance
- silvery white
- Thermal conductivity
- 71.8 W/(m·K)
- Electrical resistivity
- 105.4 nΩ·m at 20 °C
- Electrical conductivity
- 9.49 MS/m
- Crystal structure
- face-centered cubic
- Molar heat capacity
- 25.98 J/(mol·K)
Chemical properties
- Oxidation states
- +3, +2
- Electronegativity
- 2.2 (Pauling Scale)
- Ionisation energy
- 8.337 eV
1st 804.4, 2nd 1,870, 3rd 3,177 kJ/mol - Electron affinity
- 0.557 eV
- Atomic radius
- empirical 139, covalent 139, van der Waals 202 pm
- Ionic radius
- Pd⁺ 59 (2-coordinate); Pd²⁺ 86; Pd³⁺ 76; Pd⁴⁺ 62 pm
- Reactivity
- The least dense and lowest-melting platinum-group metal, chemically inert in air but the most easily dissolved of the group: nitric acid and aqua regia attack it, and it absorbs up to 900 times its own volume of hydrogen at room temperature.
- with water
- Does not react with water.
- with oxygen, air
- Does not tarnish in air at room temperature; heated in air to about 800 C it forms a layer of palladium(II) oxide: .
- with acids
- Dissolves slowly in concentrated nitric acid and in hot concentrated sulfuric acid, readily in aqua regia at room temperature, and when finely divided in hydrochloric acid: .
- with halogens
- Combines with chlorine on heating to palladium(II) chloride: ; fluorine gives PdF2 and higher fluorides.
- Typical compounds
- PdCl₂ palladium(II) chloride principal starting material for palladium compounds and catalysts
- PdO palladium(II) oxide oxide layer formed above 800 C
- Pd(O₂CCH₃)₂ palladium(II) acetate versatile coupling-reaction catalyst
- H₂PdCl₄ tetrachloropalladic acid product of dissolving the metal in aqua regia
- PdH₀.7 palladium hydride non-stoichiometric hydride from absorbed hydrogen
Occurrence, production and use
- Crustal abundance
- 1.5×10-2 milligrams per kilogram
- Oceanic abundance
- Not Applicable
- Occurrence and sources
Discovered in 1803 by Wollaston, Palladium is found with platinum and other metals of the platinum group in placer deposits of Russia, South America, North America, Ethiopia, and Australia. It is also found associated with the nickel-copper deposits of South Africa and Ontario. Palladium's separation from the platinum metals depends upon the type of ore in which it is found.
- braggite and other PGM sulfides in layered intrusions Norilsk (Russia), Bushveld (South Africa), Great Dyke (Zimbabwe), Sudbury (Canada), Stillwater (Montana)
- native palladium and palladium-gold alloy Brazil
- crustal abundance 0.000037 ppm (BGS group figure for all PGMs via RSC); 0.015 mg/kg crust (PubChem)
- Extraction, production
- Mined PGM concentrate and by-product of nickel, copper and zinc refining
world mine production about 190,000 kg in 2024; about 120,000 kg of palladium plus platinum recovered globally from scrap in 2024; no refining chemistry stated
- Uses
Palladium is used to make springs for watches, surgical instruments, electrical contacts and dental fillings and crowns. Finely divided palladium acts as a catalyst and is used in hydrogenation and dehydrogenation processes. Palladium at room temperature can absorb up to 900 times its own volume of hydrogen. Hydrogen will easily pass through heated palladium, a property that allows for the easy purification of hydrogen. Palladium alloys are used to make jewelry and, when alloyed with gold, forms a material known as white gold.
Palladium dichloride (PdCl2), a palladium compound, can absorb large amounts of carbon monoxide (CO) gas and is used in carbon monoxide detectors.
Finely divided palladium is a good catalyst and is used for hydrogenation and dehydrogenation reactions. It is alloyed and used in jewelry trades.
White gold is an alloy of gold decolorized by the addition of palladium. Like gold, palladium can be beaten into leaf as thin as 1/250,000 in. The metal is used in dentistry, watch making, and in making surgical instruments and electrical contacts.
- Automotive catalysts: catalytic converters, the leading domestic use of PGMs; palladium substitutes for platinum in most gasoline-engine converters
- Pharmaceuticals and fine chemicals: palladium hydrogenation and dehydrogenation catalysts in multipurpose batch synthesis; spent catalyst and metal residues leave with the waste
- Chemicals and refining: catalysts for bulk-chemical production and petroleum refining; palladium membranes for hydrogen purification
- Electronics: multilayer ceramic capacitors in phones and laptops; hybridised integrated circuits
- Jewellery and dentistry: white gold alloying, jewellery, dental crowns and fillings, investment
- Mining: PGM mining in Russia, South Africa, Zimbabwe, Canada, United States
- Safety, toxicity
- GHS classification, signal word Danger
- H228 Flammable solid Flammable solids
- H315 Causes skin irritation Skin corrosion/irritation
- H319 Causes serious eye irritation Serious eye damage/eye irritation
- H335 May cause respiratory irritation Specific target organ toxicity, single exposure; Respiratory tract irritation
- H413 May cause long lasting harmful effects to aquatic life to the aquatic environment, long-term hazard
Discovery and name
- Discovered by
- William Hyde Wollaston
- Discovered
- 1802
- First isolated
- not in sources
- Named by
- not in sources
- Origin of the name
- after asteroid Pallas, itself named after Pallas Athena
The element is a silvery-white metal, it does not tarnish in air, and it is the least dense and lowest melting of the platinum group of metals. When annealed, it is soft and ductile; cold-working greatly increases its strength and hardness. Palladium is attacked by nitric and sulfuric acid.
At room temperatures, the metal has the unusual property of absorbing up to 900 times its own volume of hydrogen, possibly forming Pd2H. It is not yet clear if this is a true compound. Hydrogen readily diffuses through heated palladium, providing a means of purifying the gas.
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.