Technetium
fullTechnetium has no stable isotope and no chemical limit, but technetium-99 is one of the most mobile radionuclides in water: in oxic water it is the pertechnetate anion TcO₄⁻, barely sorbed and carried with groundwater, which is why it defines the plumes under the Hanford and other fuel cycle sites and carries a WHO guidance level of 100 Bq/L and a US derived concentration of 900 pCi/L; treatment means reducing it to insoluble Tc(IV) oxide or catching the anion on an exchanger.
Typical wastewaters
- nuclear fuel reprocessing and uranium enrichment plant discharges technetium-99 as pertechnetate TcO₄⁻, weakly sorbed and mobile
- nuclear site groundwater pump and treat (Hanford tank leaks and disposal cribs) pertechnetate TcO₄⁻ in oxic groundwater above the 900 pCi/L standard in plume areas plume maxima not read
- alkaline nuclear tank waste streams (Hanford, Savannah River) TcO₄⁻ in 1 M sodium hydroxide with nitrate, sulfate and chloride competing removal work uses perrhenate as the surrogate
- hospital effluent and sewage (radiopharmaceuticals) technetium-99m from medical imaging, decaying with a 6 hour half-life; species not given by the source from the element entry; not read from a water source
1 · Identity
- Symbol, number
- Tc, 43
- Oxidation states in water
- +7 as pertechnetate TcO₄⁻ in oxic water; +4 as TcO₂ hydrate (and Tc(IV) sulfides) under reducing conditions
- Note
- The element entry covers the isotopes and the pertechnetate chemistry. Tc-99 is a pure beta emitter with a 210,000 year half-life; Tc-99m (6 h) from medical imaging reaches hospital effluent and sewage but decays away.
2 · Occurrence in water
- Natural sources
- Negligible: traces from spontaneous fission of uranium (element entry); the EPA fact sheet notes very small natural amounts in the crust and very low concentrations in air, seawater, soils and biota from fallout.
- Anthropogenic sources
- Fission product of uranium and plutonium in reactors; atmospheric weapons tests; fuel reprocessing and uranium enrichment plant discharges; groundwater beneath uranium processing facilities at US federal sites; Tc-99m in hospital and laboratory effluent. At Hanford the isotope is present in the vadose zone and groundwater from tank leaks and disposal cribs.
| matrix | typical range | note |
|---|---|---|
| contaminated groundwater, Hanford | above the 900 pCi/L standard in plume areas pCi/Lone site; maxima not quoted | Washington Ecology lists Tc-99 among the eight main Hanford groundwater contaminants, water soluble and highly mobile, with limited methods to capture it in the environment; plume maxima not read |
| contaminated vadose zone sediment, Hanford | 34 to 3800 pCi/gsediment, not water | range of the sediments used in the PNNL gas-phase treatment tests |
3 · Speciation
In oxic water technetium is pertechnetate, TcO₄⁻, a large weakly hydrated anion that is weakly sorbed at neutral and alkaline pH and moves with the water. Under anoxic conditions Fe(II) and sulfide reduce Tc(VII) to Tc(IV), which precipitates as a hydrous TcO₂ phase (and sulfides where sulfide is present) of very low solubility; re-oxidation on return of oxygen remobilises it, so immobilisation may not be permanent. Organic rich soils retain it.
| condition | dominant species | note |
|---|---|---|
| oxic groundwater and surface water, pH 6 to 9 | TcO₄⁻ | highly mobile; radioactive decay does not attenuate a plume over any practical time |
| anoxic, Fe(II) or sulfide bearing sediment | TcO₂.nH₂O (s), Tc(IV) sulfides | immobilised; the basis of reductive treatment |
| organic rich soil | retained Tc, not characterised in the fact sheet | EPA: retained and not highly mobile |
- Solubility
- Pertechnetate salts are freely soluble; TcO₂ hydrate is very insoluble.
- Hydrolysis
- None for TcO₄⁻; Tc(IV) is fully hydrolysed.
- Complexation
- Not read for natural ligands; the anion competes with nitrate, sulfate and chloride on exchangers.
- Precipitates
- TcO₂.nH₂O, Tc(IV) sulfide.
4 · Role in treatment
5 · Removal and control
- Efficiency
- a large fraction of the treated Tc-99 resisted leaching in saturated column tests
- Interferences
- re-oxidation on return of air; alkaline co-contaminants
- Efficiency
- as quoted for the surrogate; no plant performance figure read
- Interferences
- nitrate, sulfate and chloride compete; radiolysis and high alkalinity degrade organic resins
- Efficiency
- not quoted from a read source
- Interferences
- oxygen re-mobilises Tc(IV)
6 · Analytics
| method | standard | detection limit | note |
|---|---|---|---|
| liquid scintillation counting after separation | ISO 22125-1:2019 | about 5 to 20 Bq/kg with 30 min counting of 14 to 40 mL | all water types: drinking, rain, surface, ground, cooling, industrial and domestic wastewater |
| ICP-MS after separation | ISO 22125-2:2019 | not read | catalogue entry only; the separation chemistry and interference handling were not read |
- Sampling pitfalls
- Keep the sample oxic: pertechnetate is dissolved and passes filters, but a sample that goes anoxic in the bottle loses technetium to the walls as Tc(IV). Ruthenium and molybdenum isobars must be separated before ICP-MS.
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 | 100 Bq/L | technetium-99 guidance level at 0.1 mSv per year; Tc-99m is not listed in the rows read |
| US EPA NPDWR | 900 pCi/L | derived concentration of Tc-99 assumed to yield the 4 mrem per year beta and photon MCL when Tc-99 is the only such nuclide (33 Bq/L, the writer's conversion); with other beta emitters the summed dose applies |
| US EPA 40 CFR 141.66 | 4 mrem per year | MCL for beta particle and photon radioactivity from man-made radionuclides; the section read lists tritium 20,000 and strontium-90 8 pCi/L, not technetium |
| EU (Euratom Directive 2013/51) | 0.1 mSv per year | indicative dose parametric value; gross beta screening 1.0 Bq/L; Tc-99 is not among the derived concentrations listed in the annex read |
| EU DWD 2020/2184 | not set | radioactivity is left to Directive 2013/51/Euratom |
| body | limit | note |
|---|---|---|
| EU CWW BREF BAT-AEL (Decision 2016/902), BAT 12 | not set | radionuclides are outside the CWW BAT conclusions |
8 · Health and environmental effects
- Toxicity
- Radiological, not chemical: Tc-99 is a weak beta emitter, so external exposure is minimal and ingestion of contaminated water and plants is the route; once absorbed it concentrates in the thyroid and gastrointestinal tract and is excreted steadily (half in about 60 hours, Washington Ecology). Risk is an increased chance of cancer.
- Bioaccumulation
- Under aerobic conditions technetium in soil transfers readily to plants; brown algae concentrate Tc-99 from seawater and it transfers to marine animals (EPA fact sheet).
- Ecotoxicity
- Not read.
Flags
- Hanford groundwater maxima were not read; only the standard and the qualitative plume statements are quoted.
- The pertechnetate sorbent capacities are perrhenate surrogate figures from laboratory materials, not plant performance.
- The Fe(II) reduction equation is the writer's balanced statement of the redox pair described in the PNNL report; the original paper was not read.
- The 900 pCi/L to 33 Bq/L conversion is the writer's arithmetic.
Gaps
- Tc-99 concentrations in groundwater (pCi/L) at Hanford or any other site were not read from a primary source.
- Kd values for pertechnetate were not read.
- Tc-99m in hospital effluent and sewage was not read.
- The Euratom Annex III list read did not include Tc-99; the full annex may.
- No GCC standard was read.
- The oxidation product of hydrogen sulfide in the gas phase reduction of pertechnetate is not stated by the PNNL report, so no equation is written for that step.
Sources
Washington State Department of Ecology, Hanford cleanup: groundwater contaminants (technetium-99 entry: 900 pCi/L standard, mobility, half-life, health effects)
Truex, M. J., Szecsody, J. E., Zhong, L. and Qafoku, N., Gas-Phase Treatment of Technetium in the Vadose Zone at the Hanford Site Central Plateau, PNNL-23665 / RPT-DVZ-AFRI-023 (September 2014), summary and introduction
Creation of cationic polymeric nanotrap featuring high anion density and exceptional alkaline stability for highly efficient pertechnetate removal from nuclear waste streams, ACS Central Science (2024) (open access, PMC10906250); and Synthesis of ZnO nanoparticle-anchored biochar composites for the selective removal of perrhenate, a surrogate for pertechnetate, Journal of Hazardous Materials (2020) (abstract, PubMed 31761646)
ISO 22125-1:2019, Water quality. Technetium-99. Part 1: Test method using liquid scintillation counting (scope and detection limit from the catalogue abstract)
ISO 22125-2:2019, Water quality. Technetium-99. Part 2: Test method using inductively coupled plasma mass spectrometry (catalogue entry)
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)
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)
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)
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 Tc (isotopes, pertechnetate chemistry, medical Tc-99m, corrosion inhibition) (data/elements/Tc.json, data/reference/text/Tc.json)
Identity
- Name and symbol
- Technetium, Tc
- Atomic number
- 43 protons
- Position
- group 7 · period 5 · d-block · transition metal
- CAS number
- 7440-26-8
Atomic structure
- Atomic mass
- 98 u
- Electron configuration
- 1s² 2s² 2p⁶ 3s² 3p⁶ 4s² 3d¹⁰ 4p⁶ 5s² 4d⁵
[Kr] 5s²⁴d⁵ - Electrons per shell
- 2, 8, 18, 13, 2
- Valence electrons
- 7 ns and (n-1)d
| nuclide | half-life | decay |
|---|---|---|
| 97Tc | 4.21 My | ε=100% |
| 98Tc | 4.2 My | β-=100%; β+=0% |
| 99Tc | 211.1 ky | β-=100% |
| 97Tcm | 91.1 d | IT=96.06±1.8%; ε=3.94±1.8% |
Physical properties
- State at room temperature
- Solid
- Melting point
- 2,430 K (2,156.85 °C)
- Boiling point
- 4,538 K (4,264.85 °C)
- Density
- 11 g/cm3
- Appearance
- shiny gray metal
- Thermal conductivity
- 50.6 W/(m·K)
- Electrical resistivity
- 200 nΩ·m at 20 °C
- Electrical conductivity
- 5 MS/m
- Crystal structure
- hexagonal close packed
- Molar heat capacity
- 24.27 J/(mol·K)
Chemical properties
- Oxidation states
- +7, +6, +4
- Electronegativity
- 1.9 (Pauling Scale)
- Ionisation energy
- 7.28 eV
1st 702, 2nd 1,470, 3rd 2,850 kJ/mol - Electron affinity
- 0.55 eV
- Atomic radius
- empirical 147, covalent 147, van der Waals 209 pm
- Ionic radius
- Tc⁴⁺ 65; Tc⁵⁺ 60; Tc⁷⁺ 56 pm
- Reactivity
- A radioactive group 7 metal whose chemistry resembles rhenium: it tarnishes slowly in moist air, is dissolved by oxidising acids but not hydrochloric acid, and under oxidising conditions exists as the pertechnetate ion TcO4-.
- with water
- Does not react with water; the pertechnetate ion is its stable form in aerated water.
- with oxygen, air
- Tarnishes slowly in moist air; the powder burns in oxygen to the volatile heptoxide: .
- with acids
- Dissolves in nitric acid, aqua regia and concentrated sulfuric acid, but not in hydrochloric acid of any strength.
- with halogens
- Combines with the halogens on heating; fluorine gives the hexafluoride: , and chlorine the tetrachloride: .
- Typical compounds
- KTcO₄ potassium pertechnetate pertechnetate, the common Tc(VII) form; steel corrosion inhibitor
- Tc₂O₇ technetium heptoxide pale yellow volatile oxide, hydrolyses to pertechnetic acid
- TcO₂ technetium dioxide reduction product of the heptoxide
- TcF₆ technetium hexafluoride highest binary fluoride
- TcCl₄ technetium tetrachloride chain-structured chloride
- Tc₂S₇ technetium heptasulfide precursor to the disulfide
Occurrence, production and use
- Crustal abundance
- Not Applicable
- Oceanic abundance
- Not Applicable
- Occurrence and sources
- trace fission product in uranium ores about 1 milligram per tonne of uranium
- synthesis separated from fission products of spent nuclear fuel in tonne quantities
- Extraction, production
- Separation from spent uranium fuel
no reaction stated by the source
- Uses
Small amounts of technetium can retard the corrosion of steel, although this protection can only be applied to closed systems due to technetium's radioactivity. Technetium can also be used as a medical tracer and to calibrate particle detectors.
- Medicine: technetium-99m radiopharmaceuticals for diagnostic imaging of many organs
- Nuclear (closed systems): pertechnetate as a corrosion inhibitor for steel where radioactivity can be contained
- Safety, toxicity
It is reported that mild carbon steels may be effectively protected by as little as 55 ppm of KTcO4 in aerated distilled water at temperatures up to 250°C. This corrosion protection is limited to closed systems, since technetium is radioative and must be confined. 98Tc has a specific activity of 6.2 x 108 Bq/g. Activity of this level must not be allowed to spread. 99Tc is a contamination hazard and should be handled in a glove box.
Discovery and name
- Discovered by
- Carlo Perrier and Emilio Segrè
- Discovered
- 1937
- First isolated
- not in sources
- Named by
- not in sources
- Origin of the name
- after Greek τεχνητός, 'artificial', for being the first artificially produced element
Technetium is a silvery-gray metal that tarnishes slowly in moist air. The common oxidation states of technetium are +7, +5, and +4. Under oxidizing conditions technetium (VII) will exist as the pertechnetate ion, TcO4-. The chemistry of technetium is said to be similar to that of rhenium. Technetium dissolves in nitric acid, aqua regia, and concentrated sulfuric acid, but is not soluble in hydrochloric acid of any strength. The element is a remarkable corrosion inhibitor for steel. The metal is an excellent superconductor at 11K and below.
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.