Protactinium
fullProtactinium is not relevant to ordinary water treatment: protactinium-231, the only long lived isotope, is a trace daughter of uranium-235 present at attograms per litre in seawater and is so strongly hydrolysed and particle reactive that it is used as a scavenging tracer of ocean circulation; it has a WHO guidance level of 0.1 Bq/L, the lowest in the annex, is caught by gross alpha screening, and appears in water only at uranium mill and legacy nuclear sites.
Typical wastewaters
- uranium ore refining raffinate (pitchblende, St. Louis airport site and Weldon Spring raffinate pits) Pa-231 following Th-230 into the raffinate solids and slurry left after ether extraction of uranium, with Ac-227 growing in from it source term for ore in equilibrium: Pa-231 at 0.02 of the uranium activity, 0.01 of total alpha; NIOSH found dose reconstruction for raffinate workers exposed to Th-230, Pa-231 and Ac-227 not feasible; a residue slurry rather than a discharged liquid, and no activity per litre was read
1 · Identity
- Symbol, number
- Pa, 91
- Oxidation states in water
- +5 as hydrolysed hydroxo oxo species that adsorb to vessel walls and particles at any pH above strong acid; +4 under strongly reducing conditions (element entry). Protactinium-231 (half life 32,500 years, alpha, uranium-235 chain) and the short lived protactinium-234 and -233 are the isotopes; the element has no stable form.
- Note
- The element entry covers the discovery and the fluoro complexes. This chapter says only that Pa(V) is among the most particle reactive actinides and how it is regulated.
2 · Occurrence in water
- Natural sources
- Decay of uranium-235 in uranium ores and in seawater, where protactinium-231 is present at tens of attograms per litre in filtered water and is detectable in about 2 L of surface seawater for the particulate fraction (Shen 2003); it is removed onto sinking particles and is used together with thorium-230 as a tracer of ocean circulation.
- Anthropogenic sources
- Uranium mill tailings and spent fuel; neptunium-237 in waste decays to protactinium-233, which was removed from solution together with neptunium by bioprecipitation in one laboratory study (EPA Kd volume III). No effluent figure was read.
| matrix | typical range | note |
|---|---|---|
| seawater | tens of attograms per litre ag/Lanalytical paper, not a survey | protactinium-231 in filtered (below 0.4 µm) seawater; detection limits 38 and 49 ag in particulate and dissolved fractions by isotope dilution TIMS; 1 ag is 10⁻18 g |
3 · Speciation
Pa(V) hydrolyses at once to hydroxy oxide species that stick to vessel walls, so aqueous protactinium is kept only in strong acid or as fluoride complexes such as PaF₈³⁻ (element entry). In natural water it is therefore almost entirely on particles and is removed from the water column by scavenging; the dissolved remainder is a hydrolysed Pa(V) species whose formula was not given by any source read.
| condition | dominant species | note |
|---|---|---|
| natural water, any pH | hydrolysed Pa(V) hydroxo oxo species, mostly particulate | particle reactive; measured in both dissolved and particulate fractions (Shen 2003) |
| hydrofluoric acid | PaF₈³⁻ and other fluoro complexes | element entry; the only way to hold it in solution |
- Solubility
- Pa₂O₅ and the hydrous oxide are insoluble; the dioxide resists nitric, hydrochloric and sulfuric acid and dissolves in hydrofluoric acid (element entry).
- Hydrolysis
- Immediate and complete in dilute acid and above (element entry).
- Complexation
- Fluoride; nothing sourced for carbonate or organics.
- Precipitates
- Hydrous protactinium oxide on any surface or particle.
4 · Role in treatment
Not relevant or not given for this element.
5 · Removal and control
Not relevant or not given for this element.
6 · Analytics
| method | standard | detection limit | note |
|---|---|---|---|
| isotope dilution thermal ionisation mass spectrometry after chemical separation | research method (Shen 2003) | 38 to 49 ag per sample; 100 to 1000 ag needed for 4 to 12 percent uncertainty | the only way to see natural levels; blank 16 plus or minus 15 ag |
| gross alpha screening | ISO 9696, ISO 10704; WHO Table 9.3 | 0.02 to 0.1 Bq/L; Euratom 0.04 Bq/L | protactinium-231 counts in gross alpha; WHO screening level 0.5 Bq/L, Euratom 0.1 Bq/L, US 15 pCi/L |
- Sampling pitfalls
- Protactinium adsorbs to every surface it meets; samples must be acidified hard at collection and spiked with tracer before any handling, and filtration separates a particulate fraction that holds most of it.
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 Annex 6, Table A₆.1 | 0.1 (protactinium-231); 100 (protactinium-230 and -233) Bq/L | guidance levels; protactinium-231 is marked natural and shares the lowest level in the table with lead-210, polonium-210, radium-228 and thorium-229; not in the chapter 9 short table |
| EU Directive 2013/51/Euratom, Annex III | not set | no protactinium isotope in the derived concentration table; caught by the 0.1 Bq/L gross alpha screening level |
| US EPA NPDWR | 15 pCi/L | gross alpha MCL excluding radon and uranium; no protactinium specific MCL |
8 · Health and environmental effects
- Toxicity
- Toxic through its radioactivity (element entry); an alpha emitter with no chemical toxicity relevant at these masses. No dose coefficient was read.
- Bioaccumulation
- Not addressed in the sources read.
- Ecotoxicity
- Not addressed in the sources read.
Flags
- The seawater level is quoted from an analytical method paper, not a survey.
- Speciation is qualitative from the element entry; no hydrolysis constants or a formula for the dissolved species were read.
- The Euratom table was read from the retained UK copy on legislation.gov.uk.
Gaps
- No source read gives protactinium in fresh water, groundwater, drinking water, wastewater or uranium mill effluent.
- No removal study exists in the sources read; the removal list is empty on purpose.
- No dose coefficient or toxicity value for protactinium-231 was read.
- The CWW BAT conclusions have no radioactivity parameter; no discharge row is written.
- The relative particle reactivity of protactinium and thorium, the basis of the protactinium-231 to thorium-230 circulation tracer, was not read this session and is not stated.
- No balanced equation is written: protactinium hydrolysis is described qualitatively in the sources read; no constant or stoichiometry was printed.
Sources
WHO Guidelines for Drinking-water Quality, 4th ed. incorporating the first and second addenda (2022), Annex 6 Supporting information on radionuclides, Table A6.1 (NCBI Bookshelf)
WHO Guidelines for Drinking-water Quality, 4th ed. incorporating the first addendum, chapter 9 Radiological aspects (screening levels, Table 9.3)
Council Directive 2013/51/Euratom, Annex III (screening levels, derived concentrations, limits of detection), read in the retained UK copy on legislation.gov.uk
US EPA, National Primary Drinking Water Regulations (table of MCLs and MCLGs, radionuclides)
US EPA, Understanding Variation in Partition Coefficient, Kd, Values, Volume III: Review of Geochemistry and Available Kd Values for Americium, Arsenic, Curium, Iodine, Neptunium, Radium and Technetium, EPA 402-R-04-002C (July 2004), section 5.6.2 (protactinium-233 bioprecipitation with neptunium)
The Element Book, element entry and reference text for Pa (data/elements/Pa.json, data/reference/text/Pa.json)
ORAU Team Dose Reconstruction Project for NIOSH, Basis for Development of an Exposure Matrix for the Mallinckrodt Chemical Company St. Louis Downtown Site and the St. Louis Airport Site, St. Louis, Missouri, ORAUT-TKBS-0005 Rev. 03 (2010), sections 1 to 2 (raffinate residues) and Appendix A total alpha source term factors
Identity
- Name and symbol
- Protactinium, Pa
- Atomic number
- 91 protons
- Position
- no group (f-block) · period 7 · f-block · actinide
- CAS number
- 7440-13-3
Atomic structure
- Atomic mass
- 231.035 u
- Electron configuration
- 1s² 2s² 2p⁶ 3s² 3p⁶ 4s² 3d¹⁰ 4p⁶ 5s² 4d¹⁰ 5p⁶ 6s² 4f¹⁴ 5d¹⁰ 6p⁶ 7s² 5f² 6d¹
[Rn] 7s²⁵f²⁶d¹ - Electrons per shell
- 2, 8, 18, 32, 20, 9, 2
- Valence electrons
- 5 ns, (n-1)d and (n-2)f
| isotope | mass (u) | abundance |
|---|---|---|
| 231Pa | 231.035 88(1) | 100 % |
Physical properties
- State at room temperature
- Solid
- Melting point
- 1,845 K (1,571.85 °C)
- Boiling point
- 4,027 K (3,753.85 °C)
- Density
- 15.37 g/cm3
- Appearance
- bright, silvery metallic luster
- Thermal conductivity
- 47 W/(m·K)
- Electrical resistivity
- 177 nΩ·m at 0 °C
- Electrical conductivity
- 5.65 MS/m
- Crystal structure
- body-centered tetragonal
- Molar heat capacity
- not in sources
Chemical properties
- Oxidation states
- +5, +4
- Electronegativity
- 1.5 (Pauling Scale)
- Ionisation energy
- 5.89 eV
1st 568 kJ/mol - Electron affinity
- not in sources
- Atomic radius
- empirical 200, covalent 200, van der Waals 243 pm
- Ionic radius
- Pa³⁺ 104; Pa⁴⁺ 90; Pa⁵⁺ 78 pm
- Reactivity
- A dense, silvery-gray actinide that keeps its luster in air for a while but is chemically reactive; the +5 state dominates its solid compounds (5f2 6d1 7s2 configuration), with +4, +3 and +2 also known.
- with water
- Attacked by water vapor; in solution Pa(V) hydrolyzes at once to hydroxy-oxide species that stick to vessel walls, so aqueous protactinium is kept in strong acid or as fluoride complexes.
- with oxygen, air
- Reacts readily with oxygen; the stable oxide is the white pentoxide Pa2O5, the black dioxide PaO2 is made from it by hydrogen reduction, and the monoxide PaO exists only as a surface film on the metal.
- with acids
- Dissolves in inorganic acids to Pa(V); the dioxide resists dilute and concentrated nitric, hydrochloric and sulfuric acid but dissolves easily in hydrofluoric acid, which forms fluoro complexes such as PaF8^3-.
- with halogens
- Combines with iodine at about 600 C to give iodides, and pentahalides are known for all four halogens (white PaF5, yellow PaCl5, brown PaBr5, PaI5); PaCl5 hydrolyzes readily in water.
- Typical compounds
- Pa₂O₅ protactinium(V) oxide white, the most stable oxide, from igniting the hydroxide in air
- PaO₂ protactinium(IV) oxide black, from hydrogen reduction of the pentoxide
- PaF₅ protactinium(V) fluoride white solid, made from the oxide with bromine fluorides
- PaCl₅ protactinium(V) chloride yellow, volatile, hydrolyzes in water
- Na₃PaF₈ sodium octafluoroprotactinate cubic PaF8 unit, from hydrofluoric acid solutions
Occurrence, production and use
- Crustal abundance
- 1.4×10-6 milligrams per kilogram
- Oceanic abundance
- 5×10-11 milligrams per liter
- Occurrence and sources
Protactinium is one of the rarest and most expensive naturally occurring elements. The average concentrations of protactinium in the Earth's crust is typically on the order of a few parts per trillion, but may reach up to a few parts per million in some uraninite ore deposits. The element occurs in pitchblende to the extent of about 1 part 231Pa to 10 million parts of ore. Ores from Zaire have about 3 ppm. In 1959 and 1961, it was announced that the Great Britain Atomic Energy Authority extracted by a 12-stage process 125 g of 99.9% protactinium, the world's only stock of the metal for many years following. The extraction was made from 60 tons of waste material at a cost of about $500,000.
- protactinium-231 in uranium ores small amounts, from the decay of uranium-235; also in spent fuel rods
- Extraction, production
- not in sources
- Uses
Due to its scarcity, high radioactivity and toxicity, there are currently no uses for protactinium outside of basic scientific research.
Because of its scarcity, high radioactivity and high toxicity, there are currently no practical uses for protactinium other than that of basic scientific research, and for this purpose, protactinium is generally extracted from spent nuclear fuel.
- Safety, toxicity
- not in sources
Discovery and name
- Discovered by
- Kasimir Fajans and Oswald Helmuth Göhring
- Discovered
- 1913
- First isolated
- Aristid von Grosse
- Named by
- Otto Hahn and Lise Meitner
- Origin of the name
- means "(nuclear) precursor of actinium," since some of its isotopes decay into actinium
Protactinium metal is a dense, silvery-gray material with a bright metallic luster which it retains for some time in air but it does readily react with oxygen, water vapor and inorganic acids to form various compounds. In solid compounds protactinium is most stable in the oxidation state +5, but it also exists in the +4, +3 and +2 oxidation states. In solution the +5 state rapidly hydrolyzes by combining with hydroxide ions to form soluble or insoluble hydroxy-oxide solids which have a tendency to stick to the surfaces of vessels in which it is contained. A number of protactinium compounds are known, some of which are colored. The element is superconductive below 1.4K.
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.