Aguato

    Rubidium

    group 1 · period 5 · s-block · alkali metal

    minor Rubidium is potassium's heavier shadow. It substitutes for potassium in feldspars and micas, weathers out of them as Rb⁺, and then behaves as that ion and nothing else: no hydrolysis, no complexation of note, no redox chemistry, and no solid that would take it back out of solution. Conventional treatment leaves it where it is, and no drinking water or effluent standard consulted for this chapter sets a chemical value for it, though WHO gives rubidium-86 a radionuclide guidance level, so there is no treatment role to describe. What rubidium is good for is measurement. Blood and urine are rubidium rich relative to strontium, so sewage effluent leaves a works with a dissolved Rb to Sr ratio unlike that of the river it enters, and because both ions are conservative that ratio survives downstream and traces the plume.

    Typical wastewaters

    • municipal sewage
      Rb⁺, conservative and enriched relative to Sr²⁺ because blood and urine are rubidium rich; the dissolved Rb to Sr ratio traces the effluent plume
    • geothermal brine and lithium mica processing
      Rb⁺, the hydrated ion, no complexation or hydrolysis
      named as industrial sources by the element chapter

    1 · Identity

    Symbol, number
    Rb, 37
    Oxidation states in water
    +1 only, the hydrated Rb⁺ ion; no hydrolysis, no complexation of note, no redox chemistry
    Note
    The element chapter covers the metal and its violent reaction with water; dissolved rubidium is simply the ion left behind.

    2 · Occurrence in water

    Natural sources
    Weathering of potassium feldspars and micas, in which rubidium substitutes for potassium; potash brines and evaporites (element chapter). It stays in solution like potassium and is taken up by plants and animals with it.
    Anthropogenic sources
    Sewage effluent carries rubidium enriched relative to strontium because blood and urine are Rb enriched; the dissolved Rb to Sr ratio traced the Blue Plains outfall plume in the tidal Potomac. Geothermal brines and lithium mica processing are the industrial sources (element chapter).
    matrixtypical rangenote
    seawater0.12 mg/LPubChem figure carried in the element chapter
    municipal wastewater effluentnot recordedabstract onlythe tracer paper's abstract gives the Rb to Sr enrichment, not concentrations

    3 · Speciation

    Rb⁺ throughout; no hydrolysis, no significant ion pairing, no redox change. It follows potassium through water treatment and the environment and is taken up by ion exchange onto clays somewhat more strongly than potassium, by analogy with caesium.

    conditiondominant speciesnote
    all natural watersRb⁺conservative
    Solubility
    All common salts are freely soluble.
    Hydrolysis
    None.
    Complexation
    Negligible.
    Precipitates
    None.

    4 · Role in treatment

    Not relevant or not given for this element.

    5 · Removal and control

    not practised
    a conservative monovalent cation passes coagulation and filtration; only cation exchange, reverse osmosis or the general alkali removal of demineralisation would take it out
    writer's statement from the potassium analogy, not sourced
    Efficiency
    not recorded
    Interferences
    potassium and sodium compete on every exchanger

    6 · Analytics

    methodstandarddetection limitnote
    ICP-MSnot recordednot recordedrubidium is routinely measured in ICP-MS trace element suites and was used as an interference monitor in the PGE isopod study (see Pd)
    Sampling pitfalls
    Rb is conservative and easy; only the Rb to Sr ratio, not the concentration, carries the sewage signal, so measure both on the same filtered, acidified sample.

    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)100 Bq/Lrubidium-86; guidance level at 0.1 mSv per year
    discharge
    bodylimitnote
    EU CWW BREF BAT-AEL 1, 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 drinking water guideline. The US EPA provisional (PPRTV, 2016) assessment derived only a screening subchronic reference dose of 5 x 10⁻3 mg/kg per day for rubidium chloride (human LOAEL 5.3 mg/kg per day in small antidepressant trials: weight gain, diarrhoea, nausea, polyuria, confusion, agitation; uncertainty factor 1000), no chronic value, and found no IRIS, HEAST or drinking water health advisory value. Rats given 1,200 mg/L rubidium chloride in drinking water (167 mg/kg per day) for 10 days showed altered saliva flow and composition; mice at 299 to 896 mg/kg per day in drinking water for 3 weeks developed sound-induced convulsive seizures and deaths, worse when dietary potassium and magnesium were deficient. Rat studies indicated that lower doses take longer to produce toxicity, so no chronic value was derived.
    Bioaccumulation
    Taken up with potassium by all organisms; blood and urine are Rb enriched relative to Sr, which is the basis of the effluent tracer.

    Read these with care

    • The PPRTV screening value is a Superfund risk assessment number, not a limit, and the document itself labels it as carrying considerably more uncertainty than a full provisional value.
    • No river or groundwater concentration was read; the Gaillardet world river average and the Turkish spring range seen in search summaries are not written.

    What this chapter does not cover

    • No river, groundwater, drinking water or effluent concentration was read from a primary source.
    • No aquatic ecotoxicity data were read.
    • No GCC discharge standard was read.
    • The clay ion exchange selectivity for Rb⁺ over K⁺ is asserted from the caesium analogy, not read.
    • Ecotoxicity: No aquatic ecotoxicity value is quoted for rubidium.

    Notes

    1. Decision 2016/902

    Sources

    US EPA, Provisional Peer-Reviewed Toxicity Values for Rubidium Compounds (rubidium, rubidium chloride, rubidium hydroxide, rubidium iodide), EPA/690/R-16/012F, final 2 September 2016, Tables 3 and 4, Appendix A
    Dissolved rubidium to strontium ratio as a conservative tracer for wastewater effluent-sourced contaminant inputs near a major urban wastewater treatment plant, Water Research (2021), doi 10.1016/j.watres.2021.117691 (abstract, PubMed 34619608)
    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 chapter and reference text for Rb (alkali metal chemistry, reaction with water, potassium mineral hosts, crust and seawater abundance)

    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.