Beryllium

    group 2 · period 2 · s-block · alkaline earth metal

    fullBeryllium is regulated in US drinking water at 4 µg/L, carries a WHO health based value of 12 µg/L without a formal guideline, is a Group 1 carcinogen by inhalation, and is rarely found in water because its hydroxide is insoluble across the normal pH range; the treatment story is coagulation and lime softening of a trace metal that is almost never there.

    Typical wastewaters

    • primary beryllium extraction (bertrandite and beryl ore) Be²⁺ in acid solvent extraction raffinate with fluoride, ammonia, chromium, copper and cyanide; limits are mass based per kg of beryllium carbonate produced
    • industrial effluent near point sources (coal burning, alloy, ceramic and weapons manufacture) 30 to 170 µg/L reported in industrial effluents, industries not named; dissolved Be²⁺ where pH is below 5, hydroxo complexes above 8, adsorbed on turbidity in between
    • metal refineries and coal burning factories; electrical, aerospace and defence industries beryllium as a trace metal discharge, the US NPDWR source list; species not given by the source

    1 · Identity

    Symbol, number
    Be, 4
    Oxidation states in water
    +2 only, as Be²⁺ and its hydrolysis products. The ion is tiny and strongly hydrated, hydrolyses readily, precipitates as Be(OH)₂ near neutral pH and redissolves in strong alkali as hydroxo complexes; of the simple compounds only the chloride, fluoride, nitrate, phosphate and sulfate are soluble at neutral pH (WHO background document).
    Note
    The element entry carries the metal, the alloys, the ores and the berylliosis story. This chapter is beryllium as a dissolved trace metal.

    2 · Occurrence in water

    Natural sources
    Weathering of beryllium bearing rocks and soils (beryllium is concentrated in silicates and feldspars, highest in pegmatites) and atmospheric deposition; in most natural waters the majority is adsorbed to suspended matter or held in sediment rather than dissolved, and sediment concentrations are orders of magnitude above water concentrations (Great Lakes). Concentrations can be elevated where pH is below 5 or above 8 or turbidity is high (WHO).
    Anthropogenic sources
    The primary source appears to be release from coal burning and other industries using beryllium; alloy, ceramic and weapons manufacturing discharges; certain fossil fuels contain beryllium compounds (WHO background document). US NPDWR names discharge from metal refineries and coal burning factories and from electrical, aerospace and defence industries. Primary beryllium extraction from bertrandite and beryl ore is a US effluent guideline subcategory.
    matrixtypical rangenote
    surface waterup to 1000 ng/L
    region-dependent; old compilations
    Great Lakes below 4 to 120 ng/L; Australian rivers below 10 to 120 ng/L (10 to 30 average); geometric mean of US STORET data 1960 to 1988 70 ng/L; US six-year review survey found beryllium above the 1 µg/L MDL in 0.64 percent of surface water samples and never in groundwater
    groundwater8 ng/Lsingle averageaverage in German groundwater; US survey: no detections above 1 µg/L
    drinking wateraverage 0.19, median 0.1, maximum 35 µg/Lregion-dependent19,173 Czech samples 2004 to 2008, 0.53 percent above 2 µg/L; US survey of 1577 samples: detected in 5.4 percent, mean 190 and maximum 1220 ng/L
    industrial effluent30 to 170 µg/Lunspecified sourcesreported in industrial effluents near point sources; industries not named
    seawater0.0000056 mg/Lsingle figureoceanic abundance figure, Jefferson Lab via PubChem, quoted in the element entry (5.6 ng/L)

    3 · Speciation

    At pH 7.5 only a small amount of beryllium is in soluble form; solubility increases to a small extent at lower and higher pH. At neutral pH most soluble beryllium salts hydrolyse to insoluble beryllium hydroxide and only trace quantities remain dissolved; at high pH water soluble hydroxide complexes form and raise solubility and mobility, and detectable dissolved beryllium has been found in acidified waters (WHO background document). In the gut, soluble beryllium precipitates as the phosphate, which is why it is poorly absorbed.

    conditiondominant speciesnote
    acid water, pH below 5Be²⁺ and BeOH⁺; BeF⁺ and BeSO₄ ion pairs where fluoride or sulfate is highthe condition under which WHO expects elevated natural concentrations
    pH 6 to 8Be(OH)₂ (s), adsorbed to clay and suspended matterdissolved beryllium at trace level only
    alkaline water, pH above 8 to 9Be(OH)₃⁻ and Be(OH)₄²⁻ hydroxo complexessolubility and mobility rise again (WHO); the amphoterism is in the element entry
    any water with phosphateberyllium phosphate precipitatethe reason for poor gut absorption (WHO)
    Solubility
    Beryllium oxide and hydroxide are insoluble across the normal pH range, which keeps natural water at trace levels; chloride, fluoride, nitrate, phosphate and sulfate are the soluble salts (WHO). No solubility product is quoted because none was read.
    Hydrolysis
    Be²⁺ hydrolyses more readily than magnesium because of its small radius, releasing protons, which is why beryllium sulfate solutions are acidic (element entry).
    Complexation
    Hydroxide complexes at high pH (WHO); fluoride complexes are strong in beryllium chemistry and are the basis of beryllium fluoride processing, but no aqueous constant was read this session; adsorption to clay dominates transport in natural water.
    Precipitates
    Be(OH)₂ near neutral pH; beryllium phosphate; co-precipitation on Al(OH)₃, Fe(OH)₃ and CaCO₃ in treatment.
    BeX2++2OHXBe(OH)X2(s)\ce{Be^2+ + 2 OH- -> Be(OH)2 (s)}
    neutral pH; most soluble beryllium salts hydrolyse to insoluble hydroxide and only trace quantities stay dissolved (WHO background document)
    Be(OH)X2(s)+2OHXBe(OH)X4X2\ce{Be(OH)2 (s) + 2 OH- -> Be(OH)4^2-}
    high pH; WHO describes water soluble hydroxide complexes that increase solubility and mobility, the element entry calls the hydroxide amphoteric; the tetrahydroxo stoichiometry is written here as the limiting complex, not printed by WHO
    BeX2++HX2OBeOHX++HX+\ce{Be^2+ + H2O <=> BeOH^+ + H+}
    first hydrolysis step in acid to neutral water; the reason beryllium salt solutions are acidic
    Be(OH)X2(s)+2HX+BeX2++2HX2O\ce{Be(OH)2 (s) + 2 H+ -> Be^2+ + 2 H2O}
    acid water below about pH 5; the acid limb of the amphoteric solubility curve, the alkaline limb being the hydroxo complexes above pH 8 to 9; WHO expects elevated natural beryllium exactly here
    3BeX2++3HX2OBeX3(OH)X3X3++3HX+\ce{3 Be^2+ + 3 H2O -> Be3(OH)3^3+ + 3 H+}
    the polynuclear hydrolysis product that dominates concentrated beryllium solutions in the weakly acid range; not reached at the sub microgram per litre concentrations of natural water, where BeOH^+ and Be(OH)2 govern; Baes and Mesmer, The Hydrolysis of Cations (1976), beryllium chapter, from the chapter, not re-read
    3BeX2++2POX4X3BeX3(POX4)X2(s)\ce{3 Be^2+ + 2 PO4^3- -> Be3(PO4)2 (s)}
    phosphate bearing water and the gut; WHO records that soluble beryllium precipitates as the phosphate, which is why it is poorly absorbed, and names the precipitate without a formula, so the tribasic stoichiometry is written here
    BeX2++FXBeFX+\ce{Be^2+ + F^- -> BeF^+}
    fluoride waters; the beryllium fluoride complexes are strong and hold beryllium in solution where the hydroxide would otherwise take it out; Stumm and Morgan chapter 6, from the chapter, not re-read, and no constants are quoted

    4 · Role in treatment

    as a problem
    a regulated trace metal that is almost never present
    insolubility of the oxide and hydroxide keeps natural water below trace levels; the occurrence database is limited
    US survey: 0.64 percent of surface water samples above 1 µg/L, none in groundwater; WHO set no formal guideline for that reason
    mobilisation at low or high pH and with turbidity
    acid water dissolves beryllium, alkaline water forms hydroxo complexes, turbid water carries adsorbed beryllium
    WHO: elevated concentrations possible where pH is below 5 or above 8 or turbidity is high
    coal ash and industrial point sources
    coal burning releases beryllium; intake through air and dust rises two to three orders of magnitude near a coal fired plant (WHO)
    the water pathway near ash ponds is the ledger's concern, not sourced here
    as a reagent
    none
    beryllium has no use in water treatment; in official methods it is recommended as an ICP internal standard at 5 ng/L because it is not normally measured (WHO)

    5 · Removal and control

    coagulation with aluminium sulfate or ferric chloride
    adsorption and co-precipitation on the hydroxide floc; removal rises with pH from 6 to 9 and is independent of initial concentration from 5 to 50 µg/L
    jar tests on river water with 18 µg/L beryllium: 85 percent with 2.5 mg/L Al as aluminium sulfate and 80 percent with 10 mg/L Fe as ferric chloride, both at final pH 6.5; 28 percent with no coagulant; US BAT 2 (coagulation and filtration, not for systems under 500 connections)
    Efficiency
    80 to 85 percent in jar tests; 94 to 98 percent in wastewater with higher doses
    Interferences
    low pH
    lime softening
    precipitation as Be(OH)₂ and co-precipitation with CaCO₃ and Mg(OH)₂ at high pH
    BeX2++2OHXBe(OH)X2(s)\ce{Be^2+ + 2 OH- -> Be(OH)2 (s)}
    groundwater spiked to 20 µg/L: removal rose with lime dose from 75 to 450 mg/L, 99 percent at the maximum dose; wastewater with lime 415 mg/L at pH 11.5: 99.4 percent from 100 µg/L; US BAT 6
    Efficiency
    99 percent
    Interferences
    hydroxo complexes at very high pH (not quantified)
    activated alumina, ion exchange, reverse osmosis
    adsorption on alumina, cation exchange, membrane rejection of the divalent ion
    US BAT 1, 5 and 7 for beryllium in 40 CFR 141.62(c); no performance data read
    Efficiency
    not read
    zeolite adsorption
    natural and synthetic aluminosilicate zeolites, including greensand, adsorb beryllium; equilibrium within about an hour
    groundwater at 1.6 µg/L and tap water at about 2 µg/L with 0.1 to 0.2 g/L zeolite
    Efficiency
    50 to 80 percent
    activated carbon
    marginal
    only slightly increased removal with lime and alum systems; raised cumulative removal to 98.7 percent with ferric chloride in wastewater
    Efficiency
    marginal

    6 · Analytics

    methodstandarddetection limitnote
    ICP-MSEPA 200.8; ISO 17294-2minimum quantification limit 0.000005 to 0.001 mg/L (WHO)the method of choice at guideline levels
    ICP-OESEPA 200.7; Standard Methods 3120 B; ISO 11885minimum quantification limit 0.002 to 0.2 mg/L (WHO)graphite furnace AAS gives a slightly better limit than EPA 200.7 (WHO); all methods reach below 1 µg/L
    graphite furnace AASStandard Methods 3113 Bbelow 1 µg/L (WHO)
    Sampling pitfalls
    Filter 0.45 µm in the field before acidifying if dissolved beryllium is wanted, because most beryllium in natural water is on suspended matter (WHO); acidify to pH below 2 for total. Beryllium dust is the hazard in the laboratory, not the solution; the 1 µg/L method detection limit of the US survey is a quarter of the MCL, so the reporting limit matters.

    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 considered necessary to set a formal guideline value because beryllium is rarely if ever found at concentrations of concern; a health based value of 12 µg/L can be calculated from 20 percent of the TDI of 2 µg/kg body weight (dog small intestine lesions), 60 kg adult, 2 L/day; assessment 2009
    EU DWD 2020/2184not set beryllium is not in Annex I
    US EPA NPDWR0.004 mg/LMCL and MCLG both 0.004 mg/L; intestinal lesions; BAT: activated alumina, coagulation and filtration, ion exchange, lime softening, reverse osmosis
    discharge
    bodylimitnote
    EU CWW BREF BAT-AEL (Decision 2016/902)not set beryllium is not among the BAT 12 parameters
    US EPA 40 CFR 421.152 and 421.153, primary beryllium subcategory, solvent extraction raffinate from bertrandite oreBPT 2763 daily maximum, 1235 monthly average; BAT 1842 daily maximum, 831 monthly average mg/kg of beryllium carbonate produced from bertrandite ore as berylliumproduction normalised unitsmass based, not concentration; the same tables limit chromium, copper, cyanide, ammonia (299,400 and 131,600 mg/kg as N), fluoride (78,610 and 44,700 mg/kg) and TSS, with pH 6.0 to 9.0
    Abu Dhabi ADS 23/2017, discharge to the marine environment (EAD)0.05 mg/L
    region-dependent; marine discharge only
    Table 1 maximum allowable concentration at the point of discharge
    Abu Dhabi DoE Trade Effluent Control Regulations 2022, discharge to sewer5 mg/L
    region-dependent; sewer discharge
    Table A₄
    industry thresholds
    sectorbodylimitnote
    textileZDHC Wastewater Guidelines v₂.1 (2022)not set beryllium is not a ZDHC parameter

    8 · Health and environmental effects

    Toxicity
    Poorly absorbed orally because it precipitates as phosphate in the intestine; no reliable human oral data. Chronic dog feeding study: NOAEL about 0.1 mg/kg per day, gastrointestinal lesions at 12 mg/kg per day, BMD₁₀ 0.46 mg/kg per day; oral tolerable intake 0.002 mg/kg per day with an uncertainty factor of 300. By inhalation the lung is the target: chronic beryllium disease (granulomas, immune mediated) and lung cancer; IARC Group 1, for the inhalation route; the oral carcinogenicity database is inadequate. Estimated US daily intake 423 ng, mostly food and water; a smoker of 20 cigarettes may inhale about 1.5 µg/day (WHO background document).
    Bioaccumulation
    Plants below 1 mg/kg dry weight; up to 100 µg/kg fresh weight in fish and marine organisms (WHO). Not described as bioaccumulative.
    Ecotoxicity
    No US EPA aquatic life criterion for beryllium in the national recommended criteria table; sediment concentrations of 1.4 to 7.4 mg/kg in Illinois lakes (WHO).

    Flags

    • WHO occurrence figures are 1960s to 2000s compilations quoted by the 2009 background document; the six-year review survey MDL of 1 µg/L hides everything below it.
    • The tetrahydroxo complex and first hydrolysis equations are general beryllium chemistry; WHO describes hydroxide complexes without printing formulas.
    • The US primary beryllium limits are mass per unit production, not concentrations, and are quoted only for bertrandite raffinate; the beryl ore and other waste streams in 421.152 and 421.153 were not transcribed.
    • Removal percentages are jar test and laboratory results reported by WHO, not full scale.
    • Abu Dhabi values cover two media (marine outfall 0.05 mg/L, sewer 5 mg/L); other GCC states not read.

    Gaps

    • No solubility product, hydrolysis constants or fluoride complex constants were read; Stumm and Morgan and Baes and Mesmer have them.
    • No municipal wastewater concentration was read; the WHO wastewater removal figures are spiked studies.
    • No performance data for activated alumina, ion exchange or reverse osmosis on beryllium were read; only the BAT listing.
    • Coal ash pond leachate and beryllium alloy plant effluent concentrations belong to the ledger and were not sourced here.
    • Other GCC discharge standards were not read.
    • The Be₃(OH)₃³⁺ trimer is cited to Baes and Mesmer by chapter, from the chapter, not re-read; no formation constant is quoted.
    • The beryllium phosphate is written as the tribasic salt; WHO names the precipitate without a formula.

    Sources

    WHO Guidelines for Drinking-water Quality, 4th ed. incorporating the first and second addenda (2022), chapter 12 chemical fact sheet, Beryllium (p. 350)
    WHO, Beryllium in Drinking-water, background document for development of WHO Guidelines for Drinking-water Quality, WHO/HSE/WSH/09.01/5 (2009), sections 1 to 5
    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)
    40 CFR 141.62, Maximum contaminant levels for inorganic contaminants, with the BAT table and key
    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 421.152 (BPT) and 421.153 (BAT), Primary beryllium subcategory, nonferrous metals manufacturing point source category
    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 6 (metal ions in aqueous solution, hydrolysis)
    The Element Book, entries for beryllium (amphoteric hydroxide, acidic sulfate solutions, seawater abundance, ores) (data/elements/Be.json, data/reference/text/Be.json)
    Baes, C. F. and Mesmer, R. E., The Hydrolysis of Cations (Wiley, 1976), chapter on beryllium (mononuclear and polynuclear hydrolysis)

    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.