Potassium

    group 1 · period 4 · s-block · alkali metal

    fullPotassium is a conservative major cation with no drinking water limit anywhere, but it is the counter ion of potassium permanganate, the most used iron and manganese oxidant, and of the potassium chloride that regenerates a growing share of household softeners; both put potassium into drinking water and the second can put in a lot.

    Typical wastewaters

    • potash mining and brine discharge K⁺ with chloride; supplies in Saskatchewan, the largest potash producing area, reach 51 mg/L
    • potassium chloride softener regenerant and softened water K⁺ released at 14 mg per 17 mg/L of hardness removed; softened water 82 to 411 mg/L for hardness of 100 to 500 mg/L as CaCO₃
    • potash mine effluent and runoff (German Werra and Weser catchments) K⁺ in potash mine effluents and runoff; receiving rivers and streams reached 72 g/L total salt (about 149 mS/cm) K⁺ found the most toxic ion to freshwater organisms at equal concentration, calcium ameliorating
    • palm oil mill effluent dissolved K⁺ 9.5 to 29.1 mg/L with nitrogen 7.6 to 20.7 and phosphorus 5.3 to 8.7 mg/L eight smallholder mills, Nigeria
    • distillery spent wash (sugarcane vinasse) dissolved potassium with high COD, nitrogen, phosphorus and sulfur 42.5 percent K removed by microalgal cultivation
    • coal mine water (open cast and underground, Dhanbad) K⁺ and Al the highest of 18 metals measured in mine water, with TDS and COD above drinking water standards
    In the ledger's plant and process records, discharged by: Cleaning-in-place and disinfection (Food and beverage)

    1 · Identity

    Symbol, number
    K, 19
    Oxidation states in water
    +1 only, as the hydrated K⁺ ion; no hydrolysis, no complexes of consequence, no precipitates in treatment. Potassium-40 makes it the largest natural source of beta activity in water.
    Note
    The element entry already says K⁺ passes straight through most treatment plants and counts toward salinity rather than toxicity. This short chapter adds the two treatment reagents that carry it and the one exposure route that matters.

    2 · Occurrence in water

    Natural sources
    Weathering of feldspar and mica and dissolution of evaporites; present in all natural waters at far lower levels than sodium (WHO fact sheet: occurs widely in the environment, including all natural waters).
    Anthropogenic sources
    Potassium permanganate dosing (up to about 10 mg/L potassium added, normally less), potassium chloride softener regeneration (tens to hundreds of mg/L in softened water), potash mining and brine discharge (Saskatchewan supplies reach 51 mg/L), fertiliser runoff and sewage.
    matrixtypical rangenote
    drinking water, United Kingdommean 2.5, 90th percentile 5.2 mg/LRegional Heart Study survey
    raw and treated drinking water, Canadabelow 1 to 8 mg/Lregion-dependentaverage by area; up to 51 mg/L in Saskatchewan, the largest potash producing area
    softened water, potassium chloride regeneration82 to 411 mg/L
    calculated, fully potassium regenerated softener
    calculated by Health Canada for hardness of 100, 200 and 500 mg/L as CaCO₃ (14 mg potassium released per 17 mg/L hardness removed); treated tap water without a softener 8.0 mg/L in the same table
    seawater399 mg/Lsingle figureestimated oceanic abundance, Jefferson Lab figure via PubChem; the Dead Sea holds nearly 2 billion tonnes of potassium chloride (the element entry)

    3 · Speciation

    Potassium is K⁺ at every pH and redox condition water can reach. It forms no hydroxide, carbonate or sulfate precipitate at the concentrations of treatment, only weak ion pairs, and it is taken up and released by clays and ion exchange resins in competition with sodium, calcium and magnesium. Its chemistry in a plant is entirely that of its partner ions: permanganate, chloride, hydroxide.

    conditiondominant speciesnote
    all natural and treated waterK⁺ (aq), minor KSO₄⁻ ion pair in sulfate rich waterconservative; passes coagulation, filtration, softening by lime and disinfection unchanged
    cation exchangeK⁺ held on resin or clay, displaced by Ca²⁺ and Mg²⁺the basis of potassium chloride softener regeneration and of potassium retention in soils
    Solubility
    Potassium chloride, sulfate, nitrate, carbonate and hydroxide are among the most soluble inorganic salts (the element entry); no solid controls potassium in water.
    Hydrolysis
    None; K⁺ does not hydrolyse and potassium hydroxide is a strong base used for pH correction where sodium must be kept low.
    Complexation
    Weak ion pairs only; no complexation of treatment significance.
    Precipitates
    None in water treatment; potassium leaves evaporation ponds as sylvite and carnallite (the element entry).
    KMnOX4KX++MnOX4X\ce{KMnO4 -> K^+ + MnO4^-}
    dissolution of the oxidant; each mg/L of permanganate dosed adds 0.25 mg/L potassium (39 over 158)
    KX++SOX4X2KSOX4X\ce{K^+ + SO4^2- -> KSO4^-}
    the one association worth naming, and a weak one: it takes a sulfate rich water such as seawater or a gypsum bearing groundwater to bind a few percent of the potassium, and it changes nothing in a treatment plant (Stumm and Morgan chapter 6, from the chapter, not re-read; no constant is quoted)

    4 · Role in treatment

    as a problem
    potassium intake from softened water
    potassium chloride regenerated softeners exchange calcium and magnesium for potassium; at 200 mg/L hardness the softened water carries about 164 mg/L potassium
    WHO: a concern only for high risk groups (kidney dysfunction, heart disease, hyperkalaemia, certain medications, the elderly and infants); bypass a share of the water round the softener or do not drink softened water
    2RK+CaX2+RX2Ca+2KX+\ce{2 RK + Ca^2+ -> R2Ca + 2 K^+}
    the service run of a potassium chloride regenerated softener, written in the usual resin notation (R one exchange site); two moles of potassium go into the water for every mole of hardness taken out, which is the 164 mg/L potassium at 200 mg/L hardness in the WHO fact sheet; the fact sheet describes the exchange without an equation
    potassium as a salinity and conductivity contributor
    conservative cation adding to TDS
    the element entry: counts toward salinity and conductivity rather than toxicity
    permanganate overdose
    pink water and manganese dioxide particulates when permanganate is not fully consumed before the filters
    the manganese, not the potassium, is the problem (EPA oxidant manual)
    as a reagent
    potassium permanganate as oxidant for iron and manganese, taste and odour, arsenic(III) and sulfide
    permanganate is reduced to manganese dioxide, which precipitates and is filtered; the potassium stays in solution
    3MnX2++2KMnOX4+2HX2O5MnOX2(s)+2KX++4HX+\ce{3 Mn^2+ + 2 KMnO4 + 2 H2O -> 5 MnO2 (s) + 2 K^+ + 4 H+}
    stoichiometric dose 1.92 mg KMnO4 per mg Mn(II) and 0.94 per mg Fe(II); alkalinity consumed 1.21 mg/L as CaCO3 per mg/L Mn and 1.49 per mg/L Fe; oxidation in 5 to 10 minutes at pH above 7; in practice less than stoichiometric is needed because MnO2 catalyses the reaction; taste and odour doses 0.25 to 20 mg/L; the EPA manual prints this equation
    potassium permanganate for iron
    same reduction to MnO₂ with ferric hydroxide
    3FeX2++KMnOX4+7HX2O3Fe(OH)X3(s)+MnOX2(s)+KX++5HX+\ce{3 Fe^2+ + KMnO4 + 7 H2O -> 3 Fe(OH)3 (s) + MnO2 (s) + K^+ + 5 H+}
    the EPA manual prints this equation; 0.94 mg KMnO4 per mg Fe
    potassium chloride for softener regeneration
    replaces sodium chloride so that softened water carries potassium instead of sodium
    RX2Ca+2KCl2RK+CaClX2\ce{R2Ca + 2 KCl -> 2 RK + CaCl2}
    WHO fact sheet: used in some countries in place of, or mixed with, sodium chloride; potassium ions exchange with calcium and magnesium; the regeneration written in the usual resin notation, the same equation the sodium chapter carries with sodium chloride
    potassium hydroxide for pH correction
    strong base alternative to sodium hydroxide where sodium is limited
    KOHKX++OHX\ce{KOH -> K^+ + OH-}
    the element entry lists caustic potash; no dose read; the dissolution is written for the dosing arithmetic it carries, 56 g of potassium hydroxide for the mole of hydroxide that 40 g of sodium hydroxide gives, so about 1.4 times the mass, and 0.70 mg/L of potassium per mg/L of KOH dosed (39 over 56)

    5 · Removal and control

    reverse osmosis and electrodialysis
    monovalent cation rejected with sodium by the membrane
    the only practical removal; potassium is not a target of treatment
    Efficiency
    not quoted for potassium
    Interferences
    none specific
    cation exchange
    K⁺ exchanges onto hydrogen or sodium form resin in demineralisation; a sodium regenerated softener also removes it
    RNa+KX+RK+NaX+\ce{RNa + K^+ -> RK + Na^+}
    WHO: technologies are available to remove potassium but are generally more expensive and redundant when combined with softening; bypassing part of the flow is the recommended way to limit potassium from potassium chloride softeners; the exchange written in the usual resin notation for a sodium form bed, which is why a sodium regenerated softener trades the potassium straight back for sodium
    Efficiency
    not quoted
    Interferences
    competes with sodium, calcium and magnesium

    6 · Analytics

    methodstandarddetection limitnote
    ICP-OESEPA 200.7 (766.491 nm); ISO 11885EPA 200.7 instrument detection limit 700 µg/L (footnoted as a high value), total recoverable method detection limit 0.3 mg/Lpotassium is not an analyte of EPA 200.8
    flame photometry and flame AASStandard Methods 3500-K (flame photometric and flame AAS methods)not readthe routine method; the standard is cited from the Standard Methods table of contents
    ion chromatography of cationsno numbered standard readnot readsodium, potassium, calcium, magnesium and ammonium in one run
    Sampling pitfalls
    Potassium is stable in a sample; the only pitfall is contamination from potassium bearing glassware and reagents at low levels. Report whether the sample is upstream or downstream of a permanganate dose or a softener.

    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 occurs at concentrations well below those of health concern; recommended daily requirement above 3000 mg; assessment 2009; advice for high risk groups on potassium chloride softeners
    EU DWD 2020/2184not set potassium is not in Annex I; Annex IV lists potassium among the dissolved minerals (with calcium and magnesium) on which consumers are to be informed
    US EPAnot regulated absent from the primary and secondary standards
    discharge
    bodylimitnote
    EU CWW BREF BAT-AEL (Decision 2016/902)not set not a BAT 12 parameter
    Abu Dhabi ADS 23/2017 (marine) and DoE Trade Effluent Control Regulations 2022 (sewer)not set region-dependentpotassium is not listed in either table
    industry thresholds
    sectorbodylimitnote
    textileZDHC Wastewater Guidelines v₂.1 (2022)not set potassium is not a ZDHC parameter

    8 · Health and environmental effects

    Toxicity
    Essential; daily requirement above 3000 mg; no evidence that potassium in municipally treated water, even with permanganate, poses a risk (WHO). Hyperkalaemia is possible in susceptible individuals (kidney dysfunction, heart disease, hypertension, diabetes, adrenal insufficiency, pre-existing hyperkalaemia, interfering medications, the elderly and infants) drinking potassium chloride softened water.
    Bioaccumulation
    Not applicable; potassium is homeostatically regulated.
    Ecotoxicity
    No US EPA aquatic life criterion; potassium contributes to salinity toxicity in brine discharges but no figure was read.

    Flags

    • The softened water potassium figures are Health Canada calculations for a fully potassium regenerated softener, not measurements.
    • The seawater figure is a single PubChem abundance figure.
    • The 0.25 mg potassium per mg permanganate is arithmetic on the formula weights, not a source figure.
    • The permanganate equations are as printed by the EPA manual; the doses come from a 1986 compilation quoted there.
    • The potassium-40 remark is from the element entry; the WHO radiological screening treatment of potassium-40 was not re-read.
    • Standard Methods 3500-K is cited from the table of contents; the method text was not opened.

    Gaps

    • No source read gives potassium in groundwater, surface water, municipal or industrial wastewater as ranges; potash and brine effluents belong to the ledger's mining chapter.
    • No cation chromatography standard or flame photometry detection limit was read.
    • Reverse osmosis and ion exchange removal figures for potassium are not printed in the sources read; the textbook chapters are cited from memory.
    • The potassium permanganate reactions with sulfide and with arsenite are not written here because the reagent row already carries the iron and manganese equations the EPA manual prints; they belong to the sulfur and arsenic chapters.

    Sources

    WHO GDWQ 4th ed. with addenda (2022), chapter 12 fact sheet, Potassium (pp. 412 to 413)
    WHO, Potassium in Drinking-water, background document, WHO/HSE/WSH/09.01/7 (2009), sections 2 and 6
    Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Annex I and Annex IV point 3(b)
    US EPA, National Primary Drinking Water Regulations (table of MCLs and treatment techniques)
    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 and 2
    Abu Dhabi Specification ADS 23/2017, Environmental Specifications for Land-Based Liquid Discharges to the Marine Environment (Environment Agency Abu Dhabi), Table 1
    ZDHC Wastewater Guidelines Version 2.1 (November 2022), conventional parameters, anions and metals tables and sludge Table 4A
    US EPA, Alternative Disinfectants and Oxidants Guidance Manual, EPA 815-R-99-014 (April 1999), section 5.3.1.1 (permanganate reactions with iron and manganese, alkalinity consumption, doses), 5.3.1.2 and 5.7
    US EPA Method 200.7, Revision 4.4 (1994), Determination of metals and trace elements in water and wastes by ICP-AES, Table 1 (wavelengths and instrument detection limits), Table 4 (method detection limits) and Table 5 (argon plasma conditions)
    ISO 11885:2007, Water quality. Determination of selected elements by inductively coupled plasma optical emission spectrometry (ICP-OES)
    Standard Methods for the Examination of Water and Wastewater (online edition), table of contents (Part 3000 metals, including 3500-K Potassium and 3500-V Vanadium)
    PubChem element summary for potassium; estimated oceanic abundance 3.99 x 10^2 mg/L (PUG View, reference 5, Jefferson Lab)
    The Element Book, layer 1 entry for potassium (data/elements/K.json and data/reference/text/K.json)
    Crittenden, J. C. et al., MWH's Water Treatment: Principles and Design, 3rd ed. (Wiley, 2012), chapter 16 (ion exchange) and chapter 17 (reverse osmosis)
    Schulz C. J. and Canedo-Argueelles M., Lost in translation: the German literature on freshwater salinization, Philosophical Transactions of the Royal Society B 374, 20180007 (2018), doi 10.1098/rstb.2018.0007 (abstract)
    Ohimain E. I., Seiyaboh E. I., Izah S. C., Oghenegueke E. V., Some selected physico-chemical and heavy metal properties of palm oil mill effluents (2012), Zenodo record 3441038, doi 10.5281/zenodo.3441037 (abstract)
    Vasistha S., Balakrishnan D., Manivannan A., Rai M. P., Microalgae on distillery wastewater treatment for improved biodiesel production and cellulose nanofiber synthesis: a sustainable biorefinery approach, Chemosphere 315, 137666 (2023), doi 10.1016/j.chemosphere.2022.137666 (abstract)
    Vetrivel S. A., Diptanghu M., Ebhin M. R., Sydavalli S. and others, Green algae of the genus Spirogyra: a potential absorbent for heavy metal from coal mine water, Remediation Journal 27(3), 81 to 90 (2017), doi 10.1002/rem.21522 (abstract)
    Stumm, W. and Morgan, J. J., Aquatic Chemistry, 3rd ed. (Wiley, 1996), chapter 6 (ion pairs of the major ions in seawater)

    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.