Fluorine

    group 17 · period 2 · p-block · diatomic nonmetal

    fullFluoride is one of the chemicals of greatest health concern in natural water: a WHO guideline of 1.5 mg/L against dental and skeletal fluorosis, the same value in the EU, a US MCL of 4.0 mg/L, natural groundwater that reaches 10 mg/L and more across India, China, Central Africa and South America, deliberate fluoridation of supplies at about 0.7 mg/L, and a defluoridation toolbox (activated alumina, bone char, contact precipitation, reverse osmosis) that struggles where the problem is worst.

    Typical wastewaters

    • phosphate fertiliser manufacture fluoride ion in treated calcium sulfate storage pile runoff and contaminated non-process wastewater; 75 daily maximum and 25 mg/L monthly average, otherwise no discharge of process wastewater
    • hydrofluoric acid production total fluoride in process wastewater with TSS, nickel and zinc; limits in kg per 1000 kg of product
    • primary beryllium extraction (bertrandite raffinate) fluoride in acid solvent extraction raffinate, 78,610 mg/kg daily maximum per kg of beryllium carbonate produced
    • semiconductor and aluminium plant effluent (etching, smelting, aluminium fluoride) fluoride ion precipitated with lime to the CaF₂ solubility floor of 10 to 20 mg/L, then polished where the permit is lower
    In the ledger's plant and process records, discharged by: Phosphoric acid (wet process) (Chemicals) · Hydrofluoric acid (Chemicals) · NPK and CN fertilisers (Chemicals) · Speciality inorganic pigments (iron oxide, chromium oxide, CIC, zinc sulphide, lithopone) (Chemicals) · Superphosphates (Chemicals) · Dairies (Food and beverage) · Fish and shellfish processing (Food and beverage) · Fruit and vegetables (Food and beverage) · Meat processing (Food and beverage)

    1 · Identity

    Symbol, number
    F, 9
    Oxidation states in water
    -1 only, as the fluoride ion F⁻, its weak acid HF below about pH 3, and its complexes with aluminium, iron, magnesium, calcium, silicon (fluorosilicate) and boron. The fluoride in finished water is always the fluoride ion, whether natural or added (WHO). No redox chemistry in water.
    Note
    The element entry carries fluorspar, fluorapatite, the phosphoric acid BAT on fluoride to water and the fluoropolymer story. This chapter is fluoride in water: occurrence, fluorosis, fluoridation and defluoridation.

    2 · Occurrence in water

    Natural sources
    Fluorides in fluorspar, cryolite and fluorapatite; traces in many waters with higher concentrations in groundwater, where they vary with the rock the water flows through; well water in fluoride mineral areas up to about 10 mg/L and much higher locally, the highest natural level reported 2800 mg/L; high fluoride in parts of India, China, Central Africa and South America and locally in most parts of the world (WHO fact sheet). Volcanic and geothermal waters and sodium bicarbonate groundwaters low in calcium carry the most because calcium fluoride solubility no longer caps it.
    Anthropogenic sources
    Fluoridation of supplies with sodium fluoride, sodium fluorosilicate or fluorosilicic acid at 0.5 to 1 mg/L final concentration (WHO); phosphate fertiliser manufacture (fluoride escapes phosphoric acid plants in gas and water; US limits 75 and 25 mg/L on storage pile runoff), hydrofluoric acid and aluminium fluoride plants, aluminium smelting, semiconductor and glass etching, primary beryllium raffinate (78,610 mg/kg daily maximum); brick tea and high fluoride coal in some regions add to dietary intake (WHO).
    matrixtypical rangenote
    groundwaterup to about 10 mg/Lregion-dependentin areas rich in fluoride minerals; usually does not exceed 10 mg/L; highest natural level reported 2800 mg/L
    drinking water, artificially fluoridated0.5 to 1 mg/L
    time-sensitive in the US, see flags
    the range of final concentrations after fluoridation (WHO); US recommended level 0.7 mg/L (CDC, from the 2015 Public Health Service recommendation)
    seawater1.3 mg/Lsingle figureoceanic abundance figure, Jefferson Lab via PubChem, quoted in the element entry; seawater reverse osmosis rejects it with the other ions
    surface waternot read WHO says traces in many waters with higher concentrations in groundwater; no river range read
    municipal and industrial wastewaternot read no effluent survey read; the US phosphate fertiliser limit of 75 mg/L daily maximum and the Abu Dhabi sewer limit of 15 mg/L bracket what industrial dischargers must reach

    3 · Speciation

    Fluoride is the anion of a weak acid (HF pKa about 3.2), so it is F⁻ at every pH met in treatment, and it is a hard ligand: it complexes aluminium strongly (AlF²⁺ through AlF₆³⁻), iron(III), magnesium and boron, and it is held in fluorosilicate SiF₆²⁻ in the fluoridation chemicals until that hydrolyses. Calcium fluoride is the sparingly soluble salt that caps fluoride in calcium rich water and lets it rise in soft, sodium bicarbonate water. The ion selective electrode measures free fluoride only, so complexed fluoride must be released with a buffer before analysis (WHO: sample preparation is critical).

    conditiondominant speciesnote
    natural water, pH 6 to 9F⁻; MgF⁺ and CaF⁺ ion pairs in hard waterfree fluoride dominates
    water with dissolved aluminium (alum coagulated water, acid mine water)AlF²⁺, AlF₂⁺, AlF₃, AlF₄⁻aluminium fluoride complexes lower the electrode reading and the toxicity; the basis of alum defluoridation
    acid water, pH below 3HF (weak acid)hydrofluoric acid pickling rinses and semiconductor etch wastes
    fluorosilicic acid stockSiF₆²⁻hydrolyses on dilution to fluoride and silica
    calcium rich waterF⁻ at or below CaF₂ saturationlime precipitation cannot go below this floor, which is above the guideline in most waters (general chemistry, MWH chapter 16)
    Solubility
    Sodium fluoride and fluorosilicate are soluble; calcium fluoride (fluorite) is sparingly soluble and controls fluoride in hard water; aluminium fluoride and magnesium fluoride are of low solubility. No solubility product is quoted because none was read this session.
    Hydrolysis
    Fluoride is a weak base; hydrolysis is negligible above pH 5. Fluorosilicate hydrolyses to fluoride and silicic acid on dilution, releasing acid.
    Complexation
    Strong with Al³⁺, Fe³⁺, Be²⁺ and B(OH)₃ (giving BF₄⁻ only in acid); weaker with Mg²⁺ and Ca²⁺; oral absorption is reduced by complex formation with aluminium, phosphorus, magnesium or calcium (WHO). Constants not quoted.
    Precipitates
    CaF₂ (fluorite) in lime treatment and hard water; fluorapatite Ca₁₀(PO₄)₆F₂ in contact precipitation and bone char; AlF₃ and fluoride adsorbed on Al(OH)₃ in alum treatment and activated alumina.
    HFHX++FX\ce{HF <=> H+ + F^-}
    pKa about 3.2 at 25 C; fluoride is fully dissociated above pH 5
    SiFX6X2+4HX2O6FX+Si(OH)X4+4HX+\ce{SiF6^2- + 4 H2O -> 6 F^- + Si(OH)4 + 4 H+}
    hydrolysis of fluorosilicate from fluorosilicic acid or sodium fluorosilicate on dilution in the supply; the acid released consumes a little alkalinity; the fluoride in the finished water is the free ion (WHO)
    NaFNaX++FX\ce{NaF -> Na^+ + F^-}
    sodium fluoride dosing, saturator feed; adds 0.58 mg sodium per mg fluoride by the atomic weights
    CaX2++2FXCaFX2(s)\ce{Ca^2+ + 2 F^- -> CaF2 (s)}
    lime or calcium chloride precipitation of high fluoride industrial wastewater; residual limited by the solubility of fluorite, which in practice leaves 10 to 20 mg/L (MWH chapter 16, from the chapter, not re-read)
    10CaX2++6POX4X3+2FXCaX10(POX4)X6FX2(s)\ce{10 Ca^2+ + 6 PO4^3- + 2 F^- -> Ca10(PO4)6F2 (s)}
    contact precipitation with calcium and phosphate salts on a bone char or calcite bed, and the mineralisation of fluoride into bone and teeth; the fluorapatite formula is in the element entry
    Al(OH)X3(s)+FXAl(OH)X2F(s)+OHX\ce{Al(OH)3 (s) + F^- -> Al(OH)2F (s) + OH-}
    schematic ligand exchange of fluoride for surface hydroxyl on activated alumina or on alum floc (the Nalgonda technique of alum plus lime); optimum pH 5.5 to 6.5 for alumina, regenerated with caustic then acid (MWH chapter 16)
    AlX3++FXAlFX2+\ce{Al^3+ + F^- <=> AlF^2+}
    the first aluminium fluoride complex; it is why a fluoride electrode under-reads in alum coagulated or acid mine water, why a total ionic strength buffer is added before measurement, and why aluminium and fluoride each raise the other's solubility
    AlX3++6FXAlFX6X3\ce{Al^3+ + 6 F^- <=> AlF6^3-}
    the fully fluorinated complex at high fluoride to aluminium ratio; hexafluoroaluminate is the form in aluminium smelter and fluoride plant liquor, and it is not precipitated by lime, so those effluents need the fluoride freed before calcium will take it
    CaX10(POX4)X6FX2(s)+12HX+10CaX2++6HX2POX4X+2FX\ce{Ca10(PO4)6F2 (s) + 12 H+ -> 10 Ca^2+ + 6 H2PO4^- + 2 F^-}
    dissolution of fluorapatite, the natural origin of most high fluoride groundwater and the reason phosphate rock processing carries fluoride; the same solid is what contact precipitation and bone char build, so the treatment is the mineral reaction run backwards

    4 · Role in treatment

    as a problem
    dental and skeletal fluorosis
    fluoride incorporated in teeth and bone; mild dental fluorosis (prevalence 12 to 33 percent) at 0.9 to 1.2 mg/L depending on intake, skeletal fluorosis at 3 to 6 mg/L with high water consumption, crippling fluorosis usually above 10 mg/L
    WHO fact sheet; total intake from all sources decides, and where other intake nears 6 mg/day a standard below 1.5 mg/L should be considered
    the guideline is hard to meet where fluoride is highest
    high fluoride areas are often poor, rural, groundwater dependent and low in calcium
    WHO: in some areas with high natural fluoride the guideline may be difficult to achieve with the treatment technology available; small supply methods differ by country (bone charcoal, contact precipitation, activated alumina, clay)
    fluoridation dose control and chemical handling
    overfeed incidents and the corrosiveness of fluorosilicic acid
    US SMCL 2.0 mg/L carries a mandatory public notice within 12 months where it is exceeded but the 4.0 mg/L MCL is not (40 CFR 141.208)
    industrial fluoride effluent
    phosphate fertiliser, hydrofluoric acid, aluminium fluoride, aluminium smelting, glass and semiconductor etching discharge fluoride at tens to thousands of mg/L
    US limits: phosphate subcategory 75 and 25 mg/L on treated storage pile runoff, otherwise no discharge; hydrofluoric acid 6.1 and 2.9 kg per 1000 kg product (BPT), 3.4 and 1.6 (BAT); Abu Dhabi sewer 15 mg/L, marine 10 mg/L
    SiOX2(s)+6HFHX2SiFX6+2HX2O\ce{SiO2 (s) + 6 HF -> H2SiF6 + 2 H2O}
    glass etching, semiconductor oxide etch and the wet scrubbing of phosphate rock furnaces; the fluoride leaves as fluorosilicate, not as free fluoride, so an etch rinse reads low on the electrode until the sample is buffered and does not respond to lime until the complex hydrolyses
    membrane and resin waste
    reverse osmosis reject and alumina regenerant carry the removed fluoride
    disposal in fluoride endemic areas is the unsolved part of defluoridation
    aluminium residual from alum defluoridation
    the Nalgonda technique dissolves and leaves aluminium unless pH and dose are controlled
    aluminium chapter; general observation, not from a source read
    Al(OH)X3(s)+3FX+3HX+AlFX3+3HX2O\ce{Al(OH)3 (s) + 3 F^- + 3 H+ -> AlF3 + 3 H2O}
    high fluoride and low pH; the fluoride that was meant to sorb on the floc dissolves it instead, so the treated water carries aluminium and still carries fluoride. The control is enough lime to hold pH 6 to 7 and a dose set against the fluoride, not a fixed one
    as a reagent
    fluoridation
    sodium fluoride (saturator), sodium fluorosilicate (dry feeder) or fluorosilicic acid (solution feed) dosed to a final 0.5 to 1 mg/L to reduce dental caries
    SiFX6X2+4HX2O6FX+Si(OH)X4+4HX+\ce{SiF6^2- + 4 H2O -> 6 F^- + Si(OH)4 + 4 H+}
    WHO: protective effect rises with concentration up to about 2 mg/L, minimum effective about 0.5 mg/L; the CDC recommended level is 0.7 mg/L (US Public Health Service 2015); WHO also names fluoridated salt and dental preparations as alternatives
    none other
    fluoride has no other role as a treatment reagent; hydrofluoric acid is an industrial etchant, not a water chemical

    5 · Removal and control

    activated alumina
    ligand exchange of fluoride for hydroxyl on the alumina surface in a fixed bed; regenerated with sodium hydroxide, then acid to restore the surface
    Al(OH)X3(s)+FXAl(OH)X2F(s)+OHX\ce{Al(OH)3 (s) + F^- -> Al(OH)2F (s) + OH-}
    optimum pH 5.5 to 6.5; WHO: 1 mg/L should be achievable using activated alumina, not a conventional process but relatively simple to install as filters; large supplies rely on it or on reverse osmosis; US BAT for fluoride together with reverse osmosis (40 CFR 141.62 lists BAT for inorganics except fluoride separately)
    Efficiency
    to 1 mg/L (WHO)
    Interferences
    silica, sulfate, bicarbonate and arsenate compete; high pH lowers capacity; the iron chapter gives 0.5 mg/L iron as the alumina problem level
    reverse osmosis and nanofiltration
    membrane rejection of the fluoride ion
    WHO: large supplies tend to rely on activated alumina or advanced processes such as reverse osmosis; brackish groundwater plants in fluoride areas
    Efficiency
    not quantified in the source; high for RO (general)
    Interferences
    reject disposal, energy, remineralisation of the permeate
    bone charcoal
    calcined bone (hydroxyapatite) exchanges hydroxyl for fluoride to form fluorapatite; regenerable with caustic
    CaX10(POX4)X6(OH)X2(s)+2FXCaX10(POX4)X6FX2(s)+2OHX\ce{Ca10(PO4)6(OH)2 (s) + 2 F^- -> Ca10(PO4)6F2 (s) + 2 OH-}
    favoured for small supplies in some countries (WHO); cultural acceptance varies; the exchange of hydroxyl for fluoride in the apatite lattice releases hydroxide, so the treated water rises in pH, and caustic regeneration drives the same exchange back
    Efficiency
    not quantified in the source
    contact precipitation
    calcium and phosphate salts dosed ahead of a bone char or calcite bed precipitate fluorapatite on the media
    10CaX2++6POX4X3+2FXCaX10(POX4)X6FX2(s)\ce{10 Ca^2+ + 6 PO4^3- + 2 F^- -> Ca10(PO4)6F2 (s)}
    small supply method named by WHO
    Efficiency
    not quantified in the source
    alum and lime (Nalgonda technique)
    large alum doses with lime for pH form aluminium hydroxide floc that adsorbs and co-precipitates fluoride; settling then filtration
    AlX2(SOX4)X314HX2O+3Ca(OH)X22Al(OH)X3(s)+3CaSOX4(s)+14HX2O\ce{Al2(SO4)3.14H2O + 3 Ca(OH)2 -> 2 Al(OH)3 (s) + 3 CaSO4 (s) + 14 H2O}
    household to village scale; alum doses of hundreds of mg/L; residual aluminium and sulfate are the drawbacks (general, from MWH chapter 16 and practice, not from WHO); the lime is there to neutralise the alum, not to precipitate the fluoride, and at the hundreds of mg/L doses used it also throws gypsum, which is most of the sludge
    Efficiency
    to 1 to 1.5 mg/L from a few mg/L (general)
    Interferences
    alkalinity, pH control
    clay and other local sorbents
    fired clay, laterite and similar media adsorb fluoride
    WHO names clay among small supply methods; capacities are low
    Efficiency
    not quantified
    lime precipitation of industrial fluoride
    calcium hydroxide or chloride precipitates CaF₂, which is settled; a second stage with alum or a phosphate reaches lower residuals
    CaX2++2FXCaFX2(s)\ce{Ca^2+ + 2 F^- -> CaF2 (s)}
    hydrofluoric acid, phosphate, semiconductor and aluminium plant effluents; the CaF2 solubility floor leaves 10 to 20 mg/L, so a polishing step follows where the permit is below that (MWH chapter 16, from the chapter)
    Efficiency
    to 10 to 20 mg/L by lime alone (textbook figure)
    Interferences
    fluorosilicate and aluminium complexes slow precipitation
    blending and source substitution
    dilution with low fluoride water
    WHO places source management and intake consideration first
    Efficiency
    arithmetic

    6 · Analytics

    methodstandarddetection limitnote
    ion selective electrodeStandard Methods 4500-F C; ISO 10359-10.1 mg/L (WHO)the usual method; a total ionic strength adjustment buffer releases aluminium and iron bound fluoride and fixes pH; WHO: appropriate sample preparation is critical where only free fluoride is measured
    ion chromatographyEPA 300.0; Standard Methods 4110 B; ISO 10304-10.01 mg/L (WHO)the reference method at low concentrations
    SPADNS colorimetryStandard Methods 4500-F D0.1 mg/L (WHO, sulfo phenyl azo dihydroxy naphthalene disulfonic acid method)field kits; distillation (4500-F B) removes interferences
    Sampling pitfalls
    Plastic bottles only; fluoride etches glass and adsorbs on it. No preservation is needed. Aluminium coagulated water reads low on the electrode unless buffered; fluorosilicate stock must be fully hydrolysed before analysis. Do not confuse fluoride with fluorine or with total fluorine (organofluorine, PFAS), which needs combustion methods.

    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)1.5 mg/Lset 1984, reaffirmed 1993, assessment 2003; based on the increasing risk of dental fluorosis above this value and of skeletal fluorosis at progressively higher concentrations; higher than the 0.5 to 1.0 mg/L recommended for artificial fluoridation; consider a lower national standard where other intake approaches 6 mg/day
    EU DWD 2020/21841.5 mg/LAnnex I Part B
    US EPA NPDWR4.0 mg/LMCL and MCLG; bone disease, mottled teeth in children; sources listed as water additive, natural deposits, fertiliser and aluminium factories
    US EPA secondary standard2.0 mg/Ltooth discolouration; unlike other secondary standards it carries a mandatory public notice within 12 months of an exceedance (40 CFR 141.208); the recommended fluoridation level is 0.7 mg/L (CDC, US Public Health Service 2015)
    discharge
    bodylimitnote
    EU CWW BREF BAT-AEL (Decision 2016/902)not set fluoride is not among the BAT 12 parameters; the phosphoric acid BAT in the element entry requires fluoride emissions to water to be prevented
    US EPA 40 CFR 418.12, fertiliser manufacturing, phosphate subcategory (BPT)75 daily maximum; 25 30-day average mg/Lapplies only to treated calcium sulfate storage pile runoff and contaminated non-process wastewater; otherwise no discharge of process wastewater; total phosphorus 105 and 35 mg/L alongside
    US EPA 40 CFR 415.82 and 415.83, hydrofluoric acid productionBPT 6.1 daily maximum, 2.9 30-day average; BAT 3.4 and 1.6 kg total fluoride per 1000 kg of productproduction normalised unitswith TSS, nickel, zinc and pH 6.0 to 9.0
    US EPA 40 CFR 421.152, primary beryllium, bertrandite raffinate (BPT)78,610 daily maximum; 44,700 monthly average mg/kg of beryllium carbonate produced as berylliumproduction normalised unitsberyllium chapter
    Abu Dhabi ADS 23/2017, discharge to the marine environment (EAD)10 mg/L
    region-dependent; marine discharge only
    Table 1
    Abu Dhabi DoE Trade Effluent Control Regulations 2022, discharge to sewer15 mg/L
    region-dependent; sewer discharge
    Table A₂, as fluoride ion
    industry thresholds
    sectorbodylimitnote
    textileZDHC Wastewater Guidelines v₂.1 (2022)not set fluoride is not a ZDHC parameter; PFAS are, under their own entries

    8 · Health and environmental effects

    Toxicity
    Water soluble fluorides are rapidly and almost completely absorbed, reduced by complexes with aluminium, phosphorus, magnesium or calcium; distributed to teeth and bone with virtually no soft tissue storage; excreted in urine. Acute intoxication needs about 1 mg/kg body weight. Caries protection from about 0.5 mg/L up to about 2 mg/L; mild dental fluorosis at 0.9 to 1.2 mg/L; skeletal fluorosis at 3 to 6 mg/L, crippling above 10 mg/L; clear excess skeletal risk at 14 mg/day total intake and suggestive evidence above 6 mg/day; no support for a cancer or birth defect link (WHO fact sheet). Fluoride may be essential but essentiality is not demonstrated unequivocally (WHO).
    Bioaccumulation
    Accumulates in bone and teeth, which can release it after exposure ends; tea leaves average 100 mg/kg dry (WHO). Not bioaccumulative through food chains in the usual sense.
    Ecotoxicity
    No US EPA aquatic life criterion for fluoride in the national recommended criteria table read; irrigation guidance treats fluoride as a trace element (FAO 29 Table 21, not read).

    Flags

    • US fluoridation policy is time-sensitive: the 0.7 mg/L level is the 2015 Public Health Service recommendation as shown on the CDC page read in September 2026; in April 2025 HHS announced a review of the recommendation and an expert panel, and the outcome was not verified this session.
    • The HF pKa, fluorosilicate hydrolysis, the CaF₂ residual of 10 to 20 mg/L and the alumina exchange schematic are cited to Stumm and Morgan and MWH chapter 16 from memory of the texts, not re-read.
    • The Nalgonda efficiency and the aluminium residual remark are general practice, not from WHO.
    • The US phosphate and hydrofluoric acid limits are read from the CFR sections; the phosphate limits apply to a narrow stream (storage pile runoff) and the HF limits are per unit production.
    • Abu Dhabi values cover two media (marine outfall 10 mg/L, sewer 15 mg/L); other GCC states not read.

    Gaps

    • No surface water or effluent fluoride survey was read.
    • The WHO 2004 fluoride background document and the Fawell et al. 2006 monograph were not read; the expanded fact sheet stands in.
    • US industrial categories beyond parts 415, 418 and 421 (aluminium smelting part 421 subpart B, semiconductors part 469 which limits only TTO and pH) were not transcribed for fluoride.
    • Other GCC discharge standards were not read.
    • No solubility product for CaF₂ or fluorapatite, no aluminium fluoride stability constants and no activated alumina or bone char capacity figures are quoted; the aluminium fluoride, fluorapatite and alum with lime equations are from Stumm and Morgan chapters 3 and 6 and MWH chapter 16, from the chapter, not re-read.

    Sources

    WHO Guidelines for Drinking-water Quality, 4th ed. incorporating the first and second addenda (2022), chapter 12 chemical fact sheet, Fluoride (pp. 402 to 405, expanded sheet)
    Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Annex I Parts B and C
    US EPA, National Primary Drinking Water Regulations (table of MCLs and MCLGs)
    US EPA, Secondary Drinking Water Standards: Guidance for Nuisance Chemicals
    40 CFR 141.62, Maximum contaminant levels for inorganic contaminants, with the BAT table and key
    US CDC, About Community Water Fluoridation (page read 2026-09-05): recommended level 0.7 mg/L, citing the US Public Health Service recommendation, Public Health Reports 2015;130(4):318 to 331
    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 418.12, Phosphate subcategory BPT effluent limitations, fertilizer manufacturing point source category
    40 CFR 415.82 (BPT) and 415.83 (BAT), Hydrofluoric acid production subcategory, inorganic chemicals manufacturing point source category
    40 CFR 421.152, Primary beryllium 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
    Stumm, W. and Morgan, J. J., Aquatic Chemistry, 3rd ed. (Wiley, 1996), chapter 3 (HF acidity) and chapter 6 (aluminium fluoride complexes)
    MWH, Water Treatment: Principles and Design, 3rd ed. (Wiley, 2012), chapter 16 (ion exchange and activated alumina, fluoride removal, calcium fluoride precipitation) and the fluoridation chemicals in chapter 4
    Standard Methods for the Examination of Water and Wastewater (online edition), 4500-F Fluoride: B distillation, C ion selective electrode, D SPADNS
    The Element Book, entries for fluorine (seawater abundance, fluorapatite, phosphoric acid BAT on fluoride to water, fluoridation narrative) (data/elements/F.json, data/reference/text/F.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.