Tellurium

    group 16 · period 5 · p-block · metalloid

    minorTellurium is not regulated in drinking water or effluent anywhere read and has no treatment role; it behaves as a rarer, less soluble selenium: tellurate and tellurite oxyanions at picomolar levels in the sea, an anthropogenic coastal signal near cadmium telluride and thermoelectric manufacture, and a removal chemistry (bioreduction to insoluble elemental Te(0)) borrowed directly from selenium treatment.

    Typical wastewaters

    • cadmium telluride photovoltaic manufacture and copper refinery anode slime processing tellurite TeO₃²⁻ and tellurate oxyanions, soluble through conventional treatment unless reduced to Te(0) the treatment studies used synthetic tellurite wastewater at 10 to 20 mg/L; no real plant effluent concentration read

    1 · Identity

    Symbol, number
    Te, 52
    Oxidation states in water
    +6 (tellurate, TeO₄²⁻ and its protonated forms) and +4 (tellurite, TeO₃²⁻ and HTeO₃⁻) dissolved; 0 as insoluble elemental tellurium after reduction; -2 telluride only in strongly reducing sulfidic systems
    Note
    The element entry covers the metalloid, TeO₂ and CdTe. In water the exact dissolved species (oxyanion or hydroxide) is still debated in the review.

    2 · Occurrence in water

    Natural sources
    Weathering of tellurides and copper sulfide ores (element entry); the ocean holds tellurate over tellurite with a surface maximum.
    Anthropogenic sources
    Copper refinery anode slime processing, cadmium telluride solar cell manufacture (about 40 percent of demand in the review, 60 percent in the element entry's 2024 figure), thermoelectric production; Chinese coastal water and the Changjiang estuary show the elevated values.
    matrixtypical rangenote
    seawater, open ocean0.46 to 1.39 pmol/LPacific 1.39 (0 to 300 m) falling to 0.46 (2001 to 4000 m); Atlantic 1.03 (0 to 1000 m) to 0.56 (3001 to 5000 m)
    coastal water85 to 305 pmol/LEnglish Channel 305 (70 percent Te(VI)); Chinese coastal waters 85 to 263 (70 to 87 percent Te(VI))
    estuaryTe(IV) 3 to 60; Te(VI) 5 to 330 pmol/LChangjiang estuary
    synthetic tellurite wastewater (treatment studies)10 to 20 mg/L as TeO3^2-
    synthetic, not a plant effluent
    influent to the UASB reactor study; 0.05 to 0.1 mmol/L in the mixed selenite tellurite study

    3 · Speciation

    Oxic water carries mainly Te(VI) as tellurate (70 to 87 percent of the total in coastal water), with tellurite Te(IV) as the minor and more toxic fraction; both are soluble. Reduction, biological or chemical, gives elemental Te(0), which is insoluble and settles or stays inside biomass. The review notes that whether the dissolved forms are oxyanions or hydroxides is still controversial.

    conditiondominant speciesnote
    oxic seawater and coastal watertellurate Te(VI) 70 to 87 percent, tellurite Te(IV) the rest
    anaerobic sludge, lactate fed, pH 7, 30 CTe(0) nanoparticles in extracellular polymer of the granules98 percent removal from 10 mg/L tellurite, 92 percent from 20 mg/L
    Solubility
    Tellurate and tellurite are soluble; Te(0) is insoluble.
    Hydrolysis
    Tellurous and telluric acids are weak acids; the protonation state at natural pH was not read as constants.
    Complexation
    Not read.
    Precipitates
    Te(0); metal tellurides under sulfidic conditions (not read).
    TeOX3X2+4eX+6HX+Te(s)+3HX2O\ce{TeO3^2- + 4 e- + 6 H+ -> Te (s) + 3 H2O}
    tellurite reduction to elemental tellurium, the reaction bacteria in anaerobic granular sludge carry out with lactate or hydrogen as electron donor; Te(IV) reduces seven times faster than Te(VI)

    4 · Role in treatment

    as a problem
    soluble toxic tellurium oxyanions in CdTe and refinery effluent
    tellurite and tellurate stay dissolved through conventional treatment unless reduced
    the treatment literature is at laboratory scale

    5 · Removal and control

    anaerobic bioreduction in an upflow granular sludge bed reactor
    tellurite reduced to Te(0) deposits associated with the granules; recoverable by extracting the extracellular polymer
    30 C, lactate at 0.6 g COD per L per day, 10 then 20 mg/L tellurite
    Efficiency
    98 percent (10 mg/L) and 92 percent (20 mg/L); up to 78 percent of retained Te recovered from the sludge
    simultaneous selenite and tellurite bioreduction
    methanogenic granular sludge reduces both oxyanions to Se(0), Te(0) and mixed nanostructures capped in extracellular polymer
    12 h hydraulic retention, pH 7, 30 C, 0.05 then 0.1 mmol/L each
    Efficiency
    93 to 96 percent, dipping to 81 percent after the load step and recovering to 97 percent or more
    Interferences
    load increase depressed removal for about 20 days
    redox-mediated microbial reduction
    riboflavin raised the Te(IV) reduction rate eleven fold and the extracellular Te(0) fraction from 21 to 64 percent; lawsone raised Te(VI) reduction five fold
    methanogenic consortium, sulfur free medium, hydrogen as donor
    Efficiency
    not quoted as a percentage

    6 · Analytics

    methodstandarddetection limitnote
    ICP-MS with preconcentration and Te(IV)/Te(VI) separationresearch methods behind the review; no standard method readsub-pmol/L in the ocean dataspeciation needs hydride generation or selective coprecipitation, as for selenium
    Sampling pitfalls
    Acidification and storage can shift the Te(IV) to Te(VI) ratio; the review's coastal speciation data depend on prompt separation (writer's caution from the selenium analogy, not sourced for Te).

    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/Ltellurium-132, a short lived fission product; guidance level at 0.1 mSv per year
    discharge
    bodylimitnote
    EU CWW BREF BAT-AEL (Decision 2016/902), 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 human health guideline for tellurium in water anywhere read. Tellurite Te(IV) is the more toxic and more reactive form (the treatment papers call the oxyanions toxic and soluble and Te(0) less toxic and insoluble).
    Bioaccumulation
    Fish 1 to 12 ng/g (mean 2 to 3), mussels below 1.4 to 5.9, oysters 1.18 to 3.48, squid tissues 0.9 to 3.4 ng/g with bioaccumulation factors of 6 x 10^3 to 2 x 10^4 (review).
    Ecotoxicity
    No aquatic ecotoxicity value was read; the statement that Te(IV) is about ten times as toxic as Te(VI) appeared only in a search summary and is not quoted as data.

    Flags

    • All removal figures are laboratory reactors on synthetic wastewater.
    • The share of demand going to CdTe differs between the 2019 review (40 percent) and the element entry's 2024 USGS figure (60 percent).

    Gaps

    • No river, groundwater, municipal wastewater or real industrial effluent concentration was read.
    • No pKa values for tellurous or telluric acid were read.
    • No aquatic ecotoxicity data were read.
    • No GCC discharge standard was read.
    • No standard analytical method text for tellurium was read.

    Sources

    Less-Studied Technology-Critical Elements (Nb, Ta, Ga, In, Ge, Te) in the Marine Environment: Review on Their Concentrations in Water and Organisms, Frontiers in Marine Science 6 (2019) 532 (open access)
    Continuous removal and recovery of tellurium in an upflow anaerobic granular sludge bed reactor, Journal of Hazardous Materials (2017), doi 10.1016/j.jhazmat.2016.12.052 (abstract, PubMed 28043045)
    Recovery of elemental tellurium nanoparticles by the reduction of tellurium oxyanions in a methanogenic microbial consortium, Environmental Science and Technology (2016), doi 10.1021/acs.est.5b04074 (open access, PMC4738100)
    Formation of Se(0), Te(0), and Se(0)-Te(0) nanostructures during simultaneous bioreduction of selenite and tellurite in a UASB reactor, Applied Microbiology and Biotechnology (2018), doi 10.1007/s00253-018-8781-3 (abstract, PubMed 29399711)
    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 entry and reference text for Te (metalloid, TeO2, CdTe, anode slime source, 2024 use shares) (data/elements/Te.json, data/reference/text/Te.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.