Ruthenium
fullStable ruthenium is negligible in water (about 5 x 10⁻14 mol/L in the ocean) and unregulated, but ruthenium-106, a 372 day fission product, dominated the beta-gamma activity of reprocessing plant liquid discharges (70 to 80 percent at La Hague, about 10 percent at Sellafield in the 1983 figures), travels as non-reacting nitrosyl complexes with low sediment retention, and carries a WHO guidance level of 10 Bq/L.
Typical wastewaters
- nuclear fuel reprocessing liquid effluent (nitric acid, La Hague and Sellafield) ruthenium-106 as nitrosyl Ru(III) complexes [RuNO(NO₃)x(NO₂)y(OH)z(H₂O)₅-x-y-z]^(3-x-y-z), 30 to 50 percent insoluble 70 to 80 percent of the beta-gamma activity of La Hague liquid discharges in 1983 figures; sediment Kd only 20 to 50
- alkaline and diluted nuclear waste (Savannah River, Oak Ridge waste pits) ruthenate RuO₄²⁻ and perruthenate RuO₄⁻ at high pH; about 60 percent anionic nitrosyl species in diluted waste, the rest neutral
- reactor cooling effluent (Hanford) ruthenium-103, 66 percent particulate, 16 percent cationic, 13 percent anionic and 5 percent nonionic; 91 percent anionic in riverbank springs
1 · Identity
- Symbol, number
- Ru, 44
- Oxidation states in water
- +3 and +4 hydrolysed species Ru(OH)n^(4-n)+ in natural water; nitrosyl Ru(III) complexes RuNO³⁺ with nitrate, nitrite, hydroxide and water ligands in nitric acid effluent; +6 and +7 ruthenate and perruthenate in alkaline waste; +8 as volatile RuO₄ in accidents
- Note
- The element entry covers the metal, RuO₂ and RuO₄. In water the chemistry is complex and ligand driven; the PNNL review is the reference used here.
2 · Occurrence in water
- Natural sources
- Platinum group sulfide ores and ophiolite chromitites (element entry); seawater 1.3 ppt in one Indian Ocean measurement, typical ocean 5 x 10⁻14 M (0.005 ppt) and rivers 4.7 x 10⁻9 M (0.48 ppb) as summarised in the review.
- Anthropogenic sources
- Ru-103 and Ru-106 from fuel reprocessing liquid and gaseous effluents (La Hague, Sellafield, Marcoule, Oak Ridge, Hanford tank leaks), reactor accidents (Chernobyl, the 2017 European Ru-106 release), weapons fallout; stable ruthenium from chlor-alkali anode coatings, chip resistors and catalysts (element entry).
| matrix | typical range | note |
|---|---|---|
| seawater | 5 x 10⁻14 mol/L two very different figures quoted together in the review | typical ocean value summarised in the review (0.005 ppt); 1.3 ppt measured in the Southern Indian Ocean |
| river water | 4.7 x 10⁻9 mol/Lsingle summary value | 0.48 ppb, summarised in the review from Johnson et al. 2011 |
3 · Speciation
In seawater ruthenium is expected as pH dependent hydrolysed species Ru(OH)n^(4-n)+; under strongly oxidising conditions perruthenate RuO₄⁻ can occur, and ruthenate and perruthenate dominate alkaline reprocessing waste, disproportionating to RuO₄ and hydrous RuO₂ on acidification or dilution. In nitric acid reprocessing effluent 30 to 50 percent of the ruthenium is insoluble and the rest is a family of nitrosyl complexes [RuNO(NO₃)x(NO₂)y(OH)z(H₂O)₅-x-y-z]^(3-x-y-z), which are the non-reacting species that let Ru-106 travel from La Hague to the North Sea and Barents Sea. Reactor effluent Ru-103 at Hanford was 66 percent particulate, 16 percent cationic, 13 percent anionic and 5 percent nonionic, but 91 percent anionic in riverbank springs.
| condition | dominant species | note |
|---|---|---|
| seawater | Ru(OH)n^(4-n)+ hydrolysed Ru(IV) | Byrne 2002 as cited in the review |
| nitric acid reprocessing effluent | RuNO³⁺ nitrosyl nitrato, nitro, hydroxo and aqua complexes; 30 to 50 percent insoluble Ru | about 60 percent anionic in diluted Savannah River waste |
| alkaline waste, high pH | RuO₄⁻, RuO₄²⁻ | unstable to dilution |
| reducing sediment, pH 5 to 7 | insoluble sulfide or hydrated oxide | the condition under which minerals removed 74 to 85 percent of Ru-106 from Oak Ridge waste |
- Solubility
- Ligand and oxidation state dependent; hydrous RuO₂ is insoluble, nitrosyl complexes are soluble and mobile.
- Hydrolysis
- Ru(III) and Ru(IV) hydrolyse strongly at natural pH.
- Complexation
- Nitrosyl, nitrate, nitrite, chloride (polychloro complexes in acid); the review notes that complexation constants for environmentally relevant ligands are incomplete.
- Precipitates
- RuO₂.nH₂O, ruthenium sulfides.
4 · Role in treatment
5 · Removal and control
- Efficiency
- about 60 percent
- Interferences
- neutral complexes
- Efficiency
- 74 to 85 percent
- Interferences
- oxidising conditions (pH above 13 with persulfate) gave poorer removal
6 · Analytics
| method | standard | detection limit | note |
|---|---|---|---|
| gamma spectrometry (germanium detector) | routine radiometric method; no standard number read | not read | Ru-106 is measured through its 30 s daughter Rh-106; Ru-103 directly |
| ICP-MS for stable ruthenium isotope signatures | research methods | not read | Ru-99 and Ru-101 are isobars for Tc-99 and other masses |
- Sampling pitfalls
- Speciation decides everything: the La Hague study fractionated effluent mixed with seawater by ultracentrifugation and hollow fibre ultrafiltration with on line ion exchange over 62 hours because particulate, cationic, anionic and neutral fractions behave differently. RuO₄ is volatile and toxic; oxidising sample treatment can lose ruthenium as the tetroxide.
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 Table A₆.1 | 10 Bq/L | ruthenium-106; ruthenium-103 100 Bq/L; guidance levels at 0.1 mSv per year |
| US EPA NPDWR (40 CFR 141.66) | 4 mrem per year | beta particle and photon emitters; no Ru-106 derived concentration was read |
| EU (Euratom Directive 2013/51) | 0.1 mSv per year | indicative dose; gross beta screening 1.0 Bq/L; Ru-106 not among the derived concentrations read |
| WHO GDWQ 4th ed. with addenda (2022), chemical tables | no guideline | stable ruthenium is in neither Table A₃.2 nor A₃.3 |
| EU DWD 2020/2184 | not set | not an Annex I parameter |
| US EPA NPDWR | not regulated | no chemical MCL |
| body | limit | note |
|---|---|---|
| EU CWW BREF BAT-AEL (Decision 2016/902), BAT 12 | not set | not a BAT 12 parameter |
8 · Health and environmental effects
- Toxicity
- Radiological for the fission isotopes; chemically, gaseous RuO₄ is toxic with an ozone-like smell, and hydrous RuO₂ is retained in the deep lung after inhalation. Gastrointestinal absorption of ingested ruthenium is low (about 0.01 for chloro complexes of Ru(III) and Ru(IV), 0.03 for nitrosyl Ru(III), Yamagata 1969 as cited).
- Bioaccumulation
- Ru-106 Kd in soils: 6.6 x 10^3 L/kg inorganic soils, 55 sand, 990 loam, 400 clay (medians), all lower than Cs-137, so Ru-106 is the more mobile; it binds preferentially to organic matter. Brown algae and estuarine saltmarsh sediments in tidally inundated zones accumulate Ru-106 (Ravenglass).
- Ecotoxicity
- Not read.
Flags
- The review is a PNNL manuscript with visible editorial comments; the ocean and river ruthenium figures it summarises differ by orders of magnitude between sources and are quoted as given.
- The discharge shares (70 to 80 percent at La Hague, 10 percent at Sellafield) are 1983 figures and do not describe current discharges.
- No Bq/L concentration of Ru-106 in seawater or effluent was read.
Gaps
- No measured Ru-106 activity concentration in seawater, river water or effluent was read.
- No stable ruthenium data for groundwater, municipal or industrial wastewater were read.
- No complexation constants; the review itself states they are incomplete.
- No standard method number for Ru-106 in water was read.
- No GCC standard was read.
- No balanced equation is written: the sources read describe ruthenium hydrolysis and nitrosyl complexes in words only, without stoichiometry.
Sources
Radionuclide speciation in effluent from La Hague reprocessing plant in France, Health Physics (2003), doi 10.1097/00004032-200309000-00007 (abstract, PubMed 12938721)
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)
40 CFR 141.66 Maximum contaminant levels for radionuclides (beta particle and photon radioactivity 4 mrem/year; gross alpha 15 pCi/L; combined radium 5 pCi/L; uranium 30 µg/L)
Council Directive 2013/51/Euratom on radioactive substances in water intended for human consumption, Annex I (radon 100 Bq/l, tritium 100 Bq/l, indicative dose 0.1 mSv), Annex III screening (gross alpha 0.1 Bq/l, gross beta 1.0 Bq/l) and derived concentrations (annexes read on legislation.gov.uk)
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
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 Ru (platinum group metal, RuO2 anode coatings, RuO4, catalysts) (data/elements/Ru.json, data/reference/text/Ru.json)
Identity
- Name and symbol
- Ruthenium, Ru
- Atomic number
- 44 protons
- Position
- group 8 · period 5 · d-block · transition metal
- CAS number
- 7440-18-8
Atomic structure
- Atomic mass
- 101.07 u
- Electron configuration
- 1s² 2s² 2p⁶ 3s² 3p⁶ 4s² 3d¹⁰ 4p⁶ 5s¹ 4d⁷
[Kr] 5s¹⁴d⁷ - Electrons per shell
- 2, 8, 18, 15, 1
- Valence electrons
- 8 ns and (n-1)d
| isotope | mass (u) | abundance |
|---|---|---|
| 96Ru | 95.907 589(1) | 5.54 % |
| 98Ru | 97.905 29(5) | 1.87 % |
| 99Ru | 98.905 930(3) | 12.76 % |
| 100Ru | 99.904 211(3) | 12.6 % |
| 101Ru | 100.905 573(3) | 17.06 % |
| 102Ru | 101.904 340(3) | 31.55 % |
| 104Ru | 103.905 43(2) | 18.62 % |
Physical properties
- State at room temperature
- Solid
- Melting point
- 2,607 K (2,333.85 °C)
- Boiling point
- 4,423 K (4,149.85 °C)
- Density
- 12.1 g/cm3
- Appearance
- silvery white metallic
- Thermal conductivity
- 117 W/(m·K)
- Electrical resistivity
- 71 nΩ·m at 0 °C
- Electrical conductivity
- 14.08 MS/m
- Crystal structure
- hexagonal close packed
- Molar heat capacity
- 24.06 J/(mol·K)
Chemical properties
- Oxidation states
- +3
- Electronegativity
- 2.2 (Pauling Scale)
- Ionisation energy
- 7.361 eV
1st 710.2, 2nd 1,620, 3rd 2,747 kJ/mol - Electron affinity
- 1.05 eV
- Atomic radius
- empirical 146, covalent 146, van der Waals 207 pm
- Ionic radius
- Ru³⁺ 68; Ru⁴⁺ 62; Ru⁵⁺ 57; Ru⁷⁺ 38 (4-coordinate); Ru⁸⁺ 36 (4-coordinate) pm
- Reactivity
- A hard platinum-group metal that is inert at room temperature: it does not tarnish, resists all common acids including aqua regia, and is attacked only by strong oxidants, the halogens on heating, and fused alkalis.
- with water
- Does not react with water.
- with oxygen, air
- Does not tarnish at room temperature; on heating to about 800 C it oxidises to the dioxide: .
- with acids
- Not attacked by acids or by aqua regia alone; it dissolves in fused alkalis to ruthenates and is oxidised by sodium hypochlorite at room temperature.
- with halogens
- Attacked by the halogens at elevated temperature; chlorine gives the trichloride: , and fluorine the hexafluoride RuF6.
- Typical compounds
- RuO₂ ruthenium dioxide stable oxide; photocatalyst on CdS for splitting H2S
- RuO₄ ruthenium tetroxide volatile, toxic, explosive strong oxidant
- RuCl₃ ruthenium trichloride brown solid, the usual synthetic starting material
- K₂RuO₄ potassium ruthenate Ru(VI) product of fused alkali
- RuF₆ ruthenium hexafluoride highest halide, hydrolyses violently
Occurrence, production and use
- Crustal abundance
- 1×10-3 milligrams per kilogram
- Oceanic abundance
- 7×10-7 milligrams per liter
- Occurrence and sources
A member of the platinum group, ruthenium occurs native with other members of the group in ores found in the Ural mountains and in North and South America. It is also found along with other platinum metals in small but commercial quantities in pentlandite in the Sudbury, Ontario nickel-mining region, and in the pyroxinite deposits of South Africa.
- with other platinum-group metals in pentlandite and pyroxenite; occasionally native Bushveld Complex (South Africa), Norilsk (Russia), Sudbury (Canada), Great Dyke (Zimbabwe), Stillwater (Montana)
- crustal and oceanic abundance 0.000037 ppm (BGS group figure for all PGMs via RSC); 0.001 mg/kg crust and 7 x 10^-7 mg/L seawater (PubChem)
- Extraction, production
- By-product of nickel and platinum refining
recovered from the wastes of nickel refining; no separation chemistry is stated by either source
- Uses
Ruthenium is primarily used as an alloying agent. Adding 0.1% ruthenium to titanium makes titanium 100 times more resistant to corrosion. Small amounts of ruthenium are added to platinum and palladium to strengthen them. These alloys are used in jewelry and in electrical contacts that must resist wear.
- Electronics: thick-film chip resistors and electrical contacts; most ruthenium goes here; hard-disk and multilayer capacitor applications shared with other PGMs
- Chemicals: ruthenium oxide coating on dimensionally stable anodes for chlorine production; ruthenium catalysts for ammonia synthesis and for acetic acid production
- Jewellery and alloys: hardener for platinum and palladium; wear-resistant contact alloys; platinum-ruthenium jewellery alloys
- Energy: ruthenium dye complexes in dye-sensitised solar cells
- Mining: co-product of platinum-group and nickel-copper sulfide mining
- Safety, toxicity
- GHS classification, signal word Danger
- H228 Flammable solid Flammable solids
- H413 May cause long lasting harmful effects to aquatic life to the aquatic environment, long-term hazard
Discovery and name
- Discovered by
- Karl Ernst Claus
- Discovered
- 1844
- First isolated
- not in sources
- Named by
- not in sources
- Origin of the name
- from Latin Ruthenia for Russia
Ruthenium is a hard, white metal and has four crystal modifications. It does not tarnish at room temperatures, but oxidizes explosively. It is attacked by halogens, hydroxides, etc. Ruthenium can be plated by electrodeposition or by thermal decomposition methods. The metal is one of the most effective hardeners for platinum and palladium, and is alloyed with these metals to make electrical contacts for severe wear resistance. A ruthenium-molybdenum alloy is said to be superconductive at 10.6 K. The corrosion resistance of titanium is improved a hundredfold by addition of 0.1% ruthenium. It is a versatile catalyst. Hydrogen sulfide can be split catalytically by light using an aqueous suspension of CdS particles loaded with ruthenium dioxide. It is thought this may have application to removal of H2S from oil refining and other industrial processes. Compounds in at least eight oxidation states have been found, but of these, the +2, +3, and +4 states are the most common. Ruthenium tetroxide, like osmium tetroxide, is highly toxic. In addition, it may explode. Ruthenium compounds show a marked resemblance to those of cadmium.
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.