Lithium

    group 1 · period 2 · s-block · alkali metal

    fullLithium is the newest drinking water contaminant of regulatory interest: monitored across every large US system under UCMR 5 (2023 to 2025) against a 10 µg/L health reference level that nearly half of US public supply wells exceed, unregulated everywhere, conservative in water, and growing as an effluent from brine evaporation, hard rock concentrators and battery manufacture and recycling.

    Typical wastewaters

    • lithium carbonate production (brine and trona, spodumene) Li⁺ in residual brine returned to the source water body (trona process); spodumene process wastewater limited on TSS and pH only
    • battery manufacturing and recycling hydrometallurgy Li⁺ with sodium, potassium, boron and sulfate in spent brine, concentrator tailings water and recycling liquors no effluent concentrations were read; the USGS flags battery use and disposal as a future source
    • municipal sewage (pharmaceutical lithium, swimming pool sanitiser) Li⁺, conservative; lithium salts used as a pharmaceutical and lithium hypochlorite as a pool sanitiser are the EPA's named anthropogenic sources no sewage concentration was read

    1 · Identity

    Symbol, number
    Li, 3
    Oxidation states in water
    +1 only, as the small, strongly hydrated Li⁺ ion. It forms no hydrolysis products, no insoluble hydroxide and no significant complexes at natural concentrations, so it behaves as a conservative cation like sodium (book entry: its salts are soluble and it moves freely once in water).
    Note
    The element entry carries the metal's reaction with water, the minerals, the brines and the 2024 production figures. This chapter is about lithium as a dissolved trace cation and as an industrial effluent.

    2 · Occurrence in water

    Natural sources
    Weathering of lithium bearing silicates and evaporite minerals; concentrations are highest in arid regions and in older groundwater, particularly in unconsolidated clastic aquifers and sandstones, and lowest in carbonate rock aquifers; extensive evaporation, mineral dissolution, cation exchange and mixing with geothermal waters or brines account for the observed concentrations (USGS 2021). Geothermal and oilfield brines and the continental salt flat brines of Argentina, Chile and China are the concentrated natural reservoirs (book entry).
    Anthropogenic sources
    Brine evaporation ponds and spent brine, spodumene concentrator and lithium carbonate refinery effluent, battery manufacturing and recycling hydrometallurgy, lithium salts in swimming pool sanitisers and as a pharmaceutical (EPA); the USGS notes that anthropogenic sources may become important because of the rapid increase in battery use and disposal.
    matrixtypical rangenote
    groundwater, US public supply wells (1464 wells, 33 principal aquifers)below 1 to 396, median 8.1 µg/Lregion-dependent; US survey45 percent exceeded the 10 µg/L health based screening level and 9 percent the 60 µg/L drinking water only threshold; High Plains aquifer median 24.6 µg/L, Biscayne aquifer maximum 2.6 µg/L
    groundwater, US domestic wells (1676 wells)below 1 to 1700, median 6 µg/Lregion-dependent; US survey37 percent above 10 µg/L and 6 percent above 60 µg/L
    seawater0.18 mg/Lsingle figure, no rangeoceanic abundance figure, Jefferson Lab via PubChem, quoted in the element entry
    surface waternot read no source read gives a river or lake range; the USGS study is groundwater only
    municipal and industrial wastewaternot read no source read gives lithium in sewage, brine plant or battery plant effluent

    3 · Speciation

    Lithium in water is Li⁺ at every pH and redox condition met in treatment. It does not hydrolyse, does not precipitate as hydroxide or carbonate at trace concentrations, and is not removed by heating, boiling or disinfection (EPA fact sheet). Only in evaporating brines does it reach the solubility of lithium carbonate, which is how it is won from salt flats.

    conditiondominant speciesnote
    all natural and treated water, pH 4 to 12, oxic or anoxicLi⁺ (hydrated)conservative; passes coagulation, filtration, softening and disinfection unchanged
    evaporated continental brineLi⁺ concentrated to the point where Li₂CO₃ precipitates on soda ash additionthe recovery step; the element entry describes it
    Solubility
    Lithium chloride, sulfate, nitrate and hydroxide are freely soluble; lithium carbonate is the least soluble common salt and the one precipitated in production. No solubility figure is quoted because none was read this session.
    Hydrolysis
    Negligible; Li⁺ is not an acid in water at any concentration met in treatment.
    Complexation
    Weak ion pairing with sulfate and carbonate in brines only; not significant in fresh water (general chemistry, not quantified in the sources read).
    Precipitates
    Li₂CO₃ from concentrated brine with sodium carbonate; lithium phosphate and lithium aluminate in recovery processes (not read this session, named only). None in natural water.
    2LiCl+NaX2COX3LiX2COX3(s)+2NaCl\ce{2 LiCl + Na2CO3 -> Li2CO3 (s) + 2 NaCl}
    hot concentrated brine after solar evaporation and removal of magnesium and calcium; the element entry states that continental brines yield lithium carbonate when treated with sodium carbonate
    2LiX++COX3X2LiX2COX3(s)\ce{2 Li^+ + CO3^2- -> Li2CO3 (s)}
    the ionic form of the same step, reached only in evaporated brine after magnesium and calcium have been taken out and run hot because lithium carbonate is the least soluble common lithium salt; no solubility product was read, so no saturation index can be written; nothing like it happens at the microgram per litre concentrations of drinking water

    4 · Role in treatment

    as a problem
    an unregulated contaminant that conventional treatment does not touch
    Li⁺ is conservative; coagulation, filtration, softening and disinfection leave it in the water
    EPA: lithium cannot be removed by heating, boiling or disinfecting water; 45 percent of US public supply wells exceed the 10 µg/L screening level (USGS)
    a growing effluent
    spent brine, concentrator tailings water and battery recycling liquors carry lithium with sodium, potassium, boron and sulfate
    no effluent concentrations were read; the USGS flags battery use and disposal as a future source
    occurrence in the West of the United States
    arid climate, old groundwater and clastic aquifers concentrate lithium
    High Plains aquifer public supply median 24.6 µg/L with 86 percent above the screening level
    as a reagent
    none in water treatment
    lithium salts are not treatment reagents; lithium hypochlorite is sold as a swimming pool sanitiser (EPA names the use) and lithium chloride is a conservative tracer in hydraulic studies of reactors (general practice, no source read)
    LiOCl+HX2OHOCl+LiX++OHX\ce{LiOCl + H2O -> HOCl + Li^+ + OH^-}
    swimming pool sanitiser only; the hydrolysis is written by analogy with the sodium and calcium hypochlorite equations in the chlorine chapter, the EPA fact sheet names the pool use without an equation; like every hypochlorite it raises pH

    5 · Removal and control

    ion exchange
    cation exchange resin takes Li⁺ with the other cations; the literature is largely bench and pilot scale
    RNa+LiX+RLi+NaX+\ce{RNa + Li^+ -> RLi + Na^+}
    EPA: ion exchange is effective for removal of lithium from drinking water; competition from calcium, magnesium and sodium at far higher concentrations is the design problem (general, not from the source); the exchange is written in the usual resin notation for a sodium form strong acid bed (R one exchange site), the EPA fact sheet names the process without a stoichiometry
    Efficiency
    not quantified in the source; EPA points to its Drinking Water Treatability Database
    Interferences
    hardness and sodium load the resin
    adsorption on selective media
    lithium selective sorbents (manganese and titanium oxide types, aluminium hydroxide types) developed for brine extraction also take lithium from dilute water
    EPA: adsorption using certain novel media may also be effective
    Efficiency
    not quantified
    reverse osmosis
    Li⁺ is rejected with the other monovalent ions; the removal is by membrane, not by chemistry
    general membrane behaviour, not from a source read this session; the brine then carries the lithium
    Efficiency
    not quantified
    brine evaporation and carbonate precipitation
    the recovery process, not a treatment: solar evaporation concentrates lithium, magnesium and calcium are removed, and sodium carbonate precipitates Li₂CO₃
    2LiCl+NaX2COX3LiX2COX3(s)+2NaCl\ce{2 LiCl + Na2CO3 -> Li2CO3 (s) + 2 NaCl}
    salt flats of Argentina, Chile and China (element entry)
    Efficiency
    not applicable
    Interferences
    magnesium must be removed first
    conventional treatment
    none
    coagulation, filtration, softening, chlorination, boiling do not remove lithium
    Efficiency
    nil

    6 · Analytics

    methodstandarddetection limitnote
    ICP-OESEPA 200.7; Standard Methods 3120 B; ASTM D₁₉₇₆UCMR 5 minimum reporting level 9 µg/Lthe UCMR 5 methods; total lithium from all compounds present
    ICP-MSISO 17294-2; EPA 200.8 (lithium not among its listed analytes, see the iron chapter)not read; below 1 µg/L in practice (general)needed for the sub 10 µg/L range the USGS study reports
    flame emission or atomic absorptionStandard Methods 3500-Li B; 3111 Bnot readthe classical method; lithium's red line
    Sampling pitfalls
    Acidify as for any metal; lithium is conservative and stable in the bottle. Contamination comes from lithium grease, some laboratory glassware and lithium heparin blood tubes if a clinical lab is shared (general practice). The health screening level is close to the reporting limit, so method sensitivity decides what the data can say.

    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 lithium has no chemical fact sheet in the 2022 series (the fact sheet URL pattern returns no document) and no guideline value was found; treated here as not assessed
    EU DWD 2020/2184not set lithium is not in Annex I
    US EPAnot regulated on CCL 5; UCMR 5 monitoring 2023 to 2025 with a 9 µg/L minimum reporting level and final dataset released August 2026; CCL 5 health reference level 10 µg/L (screening, not a standard) from a provisional reference dose of 2 µg/kg per day with 20 percent allocated to water; no health advisory; USGS drinking water only benchmark 60 µg/L
    discharge
    bodylimitnote
    EU CWW BREF BAT-AEL (Decision 2016/902)not set lithium is not among the BAT 12 parameters
    US EPA 40 CFR 415.452, lithium carbonate production (BPT)no limit trona process: no discharge of process wastewater except return of residual brine to the source water body; spodumene process: TSS 2.7 kg/kkg daily maximum, 0.90 30-day average, pH 6.0 to 9.0; lithium itself is not a limited parameter
    Abu Dhabi ADS 23/2017, discharge to the marine environment (EAD)not set
    region-dependent; marine discharge only
    lithium is not in Table 1
    Abu Dhabi DoE Trade Effluent Control Regulations 2022, discharge to sewer2.5 mg/L
    region-dependent; sewer discharge
    Table A₄ maximum allowable concentration for trade effluent to the sewer network
    industry thresholds
    sectorbodylimitnote
    textileZDHC Wastewater Guidelines v₂.1 (2022)not set lithium is not a ZDHC parameter

    8 · Health and environmental effects

    Toxicity
    No recommended dietary allowance and differing views on whether lithium is a micronutrient (EPA). Therapeutic doses of 600 to 1200 mg/day of lithium compound treat bipolar disorder and carry renal effects (dilute urine, thirst, kidney disease at higher long term doses), neurological effects (lethargy, tremor, cognitive impairment) and thyroid and parathyroid effects; the EPA provisional reference dose of 2 µg/kg per day is a LOAEL from patients divided by 1000, so risk between 10 µg/L and therapeutic levels cannot be confidently estimated (EPA fact sheet).
    Bioaccumulation
    Not addressed in the sources read; lithium is present in cereal grains, leafy vegetables and root crops (EPA).
    Ecotoxicity
    No US EPA aquatic life criterion; lithium does not appear in the national recommended criteria table.

    Flags

    • The WHO row is an absence: no fact sheet or guideline was found, but the full GDWQ table of guideline values was not re-read this session.
    • US occurrence is a 1991 to 2018 USGS compilation of untreated groundwater; the UCMR 5 national dataset (August 2026) was not read.
    • The reverse osmosis and tracer statements are general practice, not from a source read.
    • No effluent concentration for brine, concentrator or battery plants was read; the ledger's mining chapter, not this entry, is where they should sit.
    • Abu Dhabi sewer value 2.5 mg/L; marine outfall has no lithium row; other GCC states not read.

    Gaps

    • No surface water, sewage or industrial effluent concentrations were read.
    • No solubility of lithium carbonate and no ion exchange selectivity data were read.
    • No removal percentages for ion exchange, adsorption or reverse osmosis; the EPA fact sheet defers to its treatability database, which was not opened.
    • Battery manufacturing and recycling effluent chemistry (lithium with fluoride, cobalt, nickel, sulfate) is not sourced here.
    • Other GCC discharge standards were not read.
    • No stoichiometry was read for the lithium selective sorbents (manganese and titanium oxide ion sieves, the lithium aluminate intercalation), so no equation is written for the adsorption row.

    Sources

    US EPA, Technical Fact Sheet: Lithium in Drinking Water, A Resource for Primacy Agencies, EPA 815-F-23-007 (October 2023)
    US EPA, Fifth Unregulated Contaminant Monitoring Rule (UCMR 5) page, Table 2 (lithium MRL 9 µg/L, EPA 200.7, SM 3120 B, ASTM D1976) and lithium questions, read 2026-09-05
    Lindsey, B. D., Belitz, K., Cravotta, C. A., Toccalino, P. L. and Dubrovsky, N. M. (2021), Lithium in groundwater used for drinking-water supply in the United States, Science of the Total Environment 767, 144691 (abstract read on the USGS publications page)
    WHO GDWQ 4th ed. with addenda (2022), chapter 12 fact sheets, beryllium and boron pages (pp. 350 to 351), read to confirm that no lithium sheet sits in the series
    Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Annex I Parts B and C
    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 with footnotes
    40 CFR 415.452, Lithium carbonate production subcategory, BPT effluent limitations
    Abu Dhabi Specification ADS 23/2017, Environmental Specifications for Land-Based Liquid Discharges to the Marine Environment (Environment Agency Abu Dhabi), Table 1
    Abu Dhabi Department of Energy, Trade Effluent Control Regulations 2022 (DoE/PD/R01/005, effective 1 January 2022), Schedule A Tables A1, A2 and A4
    ZDHC Wastewater Guidelines Version 2.1 (November 2022), Table 3 conventional parameters and anions
    US EPA, National Recommended Water Quality Criteria, Aquatic Life Criteria Table
    Standard Methods for the Examination of Water and Wastewater (online edition), 3120 B (ICP-OES), 3500-Li B (flame emission)
    The Element Book, entries for lithium (brine carbonate precipitation, seawater abundance, minerals and production) (data/elements/Li.json, data/reference/text/Li.json)

    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.