Selenium
fullSelenium is regulated in drinking water by WHO (40 µg/L provisional), the EU (20 µg/L) and the US (0.05 mg/L), is the pollutant that drove biological treatment of power plant FGD wastewater, and has a treatment chemistry that turns entirely on whether it is selenite, which iron removes, or selenate, which almost nothing removes except reduction and membranes.
Typical wastewaters
- coal power plant flue gas desulfurisation wastewater selenate SeO₄²⁻ with selenite in a high nitrate scrubber water; reduced to elemental Se(0) in anoxic bioreactors BAT limits 70 µg/L daily and 29 µg/L monthly; nitrate is consumed before selenium
- coal gasification wastewater and combustion residual leachate total selenium; gasification wastewater limited to 453 µg/L daily and 227 µg/L monthly a limit, not a measured range
- petroleum refinery effluent dissolved selenium; species not given by the source US EPA source list for the selenium MCL
- mine drainage (coal, phosphate and sulfide mining) dissolved selenium; selenate is favoured where the water is oxic and alkaline, selenite at near neutral and acid pH the US EPA lists mines as a source; no mine water concentration was read
- agricultural drainage from seleniferous soils selenate in high sulfate drainage water, with organic selenium (selenomethionine, dimethylselenide) the case behind the nanofiltration study cited by WHO
- copper refinery anode slime processing selenium in the anode slime processing effluent; species not given by the source
- textile wet processing total selenium, a sample and report only ZDHC parameter; sludge reporting limit 5 mg/kg dry weight
1 · Identity
- Symbol, number
- Se, 34
- Oxidation states in water
- +6 selenate, SeO₄²⁻, the soluble, mobile form of alkaline oxidising water; +4 selenite, H₂SeO₃, HSeO₃⁻ and SeO₃²⁻, the form that adsorbs to iron and aluminium oxides; 0 elemental selenium, insoluble, the product of chemical and biological reduction; -2 selenides and hydrogen selenide in strongly reducing sediments; organic selenium (selenomethionine, dimethylselenide) in biota and drainage water.
- Note
- The element entry covers anode slimes, glass and photovoltaics; this chapter is selenite against selenate.
2 · Occurrence in water
- Natural sources
- Crustal selenium 50 to 90 µg/kg, higher in some volcanic, sedimentary and carbonate rocks; soils 5 to 1,200,000 µg/kg. Selenites and selenates are soluble, so selenium leaches from well aerated alkaline soils; elemental selenium and selenides are insoluble, so it is retained in wet, poorly aerated soils. Dissolved selenium rises at both high and low pH (WHO background document).
- Anthropogenic sources
- Flue gas desulfurisation wastewater, gasification wastewater and combustion residual leachate at coal power plants, regulated in 40 CFR 423.13; discharges from petroleum refineries and mines (EPA NPDWR); copper refinery anode slime processing (element entry); agricultural drainage from seleniferous soils, the case behind the nanofiltration study cited by WHO; coal, phosphate and sulfide mining (element entry, MWEI BREF); selenium is a textile sludge and report only wastewater parameter for ZDHC.
| matrix | typical range | note |
|---|---|---|
| groundwater and surface water | 0.06 to about 400 µg/L region-dependent; 1930s to 1960s US compilations | some groundwater approaches 6,000 µg/L |
| tap water, public supplies worldwide | much less than 10, may exceed 50 µg/Lregion-dependent | 50 to 160 µg/L in a high selenium soil area of China |
| well water in a poisoning case | 9 mg/Lsingle case | a family exposed for about 3 months lost hair and nails and recovered on changing supply |
| seawater | 0.0002 mg/L single abundance figure, no range | estimated oceanic abundance, Jefferson Lab via PubChem |
| industrial wastewater, coal gasification (regulated level) | 453 daily maximum; 227 monthly µg/La limit, not a measured range | the 40 CFR 423.13(j) BAT limits for gasification wastewater, which show the order of magnitude of raw selenium in that stream; raw concentrations were not read |
3 · Speciation
The common forms in water are selenite, Se(IV), and selenate, Se(VI); conversion of selenite to selenate is slow, both exist together, and neither is oxidised or reduced easily under treatment conditions (WHO citing Sorg and Logsdon 1978). Selenate is more soluble and much harder to remove by coagulation than selenite, so oxidising selenite would be a mistake. Acidic and reducing conditions reduce selenite to elemental selenium; alkaline and oxidising conditions favour selenate. Chlorine oxidises selenite to selenate only under harsh conditions and selenium is unlikely to react with ozone, chlorine dioxide or chloramines.
| condition | dominant species | note |
|---|---|---|
| oxic, alkaline water, pH 7 to 9 | SeO₄²⁻ | selenate; mobile, poorly sorbed; passes coagulation, alumina at natural pH and activated carbon |
| oxic water, near neutral and acid pH | HSeO₃⁻ and SeO₃²⁻, sorbed on iron and aluminium oxides | selenite; removed by ferric coagulation below pH 7 and by iron oxide media |
| reducing sediment, anoxic bioreactor, zero valent iron | Se (s), elemental, as nanospheres on bacterial cells or in iron corrosion products | the sink that biological FGD treatment and iron reduction exploit |
| strongly sulfidic, reducing | selenides, HSe⁻ | poorly absorbed, insoluble metal selenides; not covered by the water sources beyond the statement of insolubility |
| biota, drainage water | selenomethionine, selenocysteine, dimethylselenide | teratogenic to birds and fish; the reason the US criterion is a fish tissue value |
- Solubility
- Selenite and selenate salts of the common cations are soluble; elemental selenium and metal selenides are insoluble (WHO). No solubility products are printed in the sources read.
- Hydrolysis
- Selenous acid and selenic acid dissociate stepwise with pH; the sources read do not print the constants, so none are quoted. In the pH 6 to 9 range selenite is HSeO₃⁻ or SeO₃²⁻ and selenate is the divalent anion.
- Complexation
- Selenite sorbs on iron and aluminium oxide surfaces and on iron oxide coated sand (capacity about 1 mg/g); selenate sorbs weakly; nitrate interferes with selenium adsorption on soil (WHO). No constants quoted.
- Precipitates
- Elemental selenium from reduction; selenite carried on ferric hydroxide floc; metal selenides under sulfidic conditions.
4 · Role in treatment
5 · Removal and control
- Efficiency
- moderate for selenite; ineffective for selenate; no percentage printed
- Interferences
- selenate; phosphate and silicate competing for the iron surface
- Efficiency
- 98 percent on activated alumina at pH 5; treatment of 4 µg/L natural water with iron(II) hydroxide at pH 8.8 gave below 1 µg/L
- Interferences
- selenate at natural pH; nitrate; competing anions
- Efficiency
- to the 2020 BAT limits of 70 µg/L daily and 29 µg/L monthly (chemical precipitation plus low residence time reduction); the voluntary incentives limit of 10 µg/L needs more
- Interferences
- nitrate consumed first; cold water; oxidant carry-over; the sludge and spent carbon carry the selenium
- Efficiency
- 4 µg/L to below 1 µg/L in the ferrous hydroxide test
- Interferences
- arsenate, molybdate, oxygen
- Efficiency
- not quantified in the source
- Interferences
- sulfate and nitrate compete, as for arsenate
- Efficiency
- over 95 percent (RO); 95 percent (NF)
- Interferences
- scaling in high sulfate drainage water; concentrate disposal
- Efficiency
- by ratio
6 · Analytics
| method | standard | detection limit | note |
|---|---|---|---|
| hydride generation AAS | Standard Methods 3114 B and C | about 0.5 µg/L with 100 mL samples (WHO) | the most convenient method in the WHO review; hydride generation needs Se(IV), so total selenium requires pre-reduction of selenate |
| ICP-MS | EPA 200.8 (mass 82); ISO 17294-2; Standard Methods 3125 | similar to hydride AAS per WHO; EPA 200.8 instrument detection limit 5 µg/L scanning and 1.3 µg/L selected ion monitoring at mass 82, the poorest in the table | argon dimer at mass 80 and krypton at mass 82 interfere (EPA 200.8 notes the isobaric krypton overlap); collision cell instruments do far better than the 1994 figures |
| speciation, Se(IV) and Se(VI) | no numbered standard read | not read | needed to choose between coagulation and reduction; hydride generation with and without pre-reduction is the classic split |
- Sampling pitfalls
- Acidify for total selenium; filter 0.45 µm in the field for dissolved selenium. Interconversion of selenite and selenate is slow, so speciation samples are less fragile than arsenic, but hydride methods respond only to Se(IV) and undercount selenate unless the sample is pre-reduced. Hydride generation interferences from transition metals are real in FGD and mine water.
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.
| body | limit | note |
|---|---|---|
| WHO GDWQ 4th ed. with addenda (2022) | 40 µg/L | provisional because of uncertainties in the scientific database; 20 percent of the upper tolerable intake of 400 µg/day allocated to water; most drinking water is far below 10 µg/L; for most Member States a guideline is unnecessary; assessment 2010 |
| EU DWD 2020/2184 | 20 µg/L | Annex I Part B; 30 µg/L applies in regions where geological conditions could lead to high selenium in groundwater; uncertainty of measurement 40 percent of the parametric value (Annex III) |
| US EPA NPDWR | 0.05 mg/L | MCL and MCLG both 0.05 mg/L; health effects listed as hair or fingernail loss, numbness, circulatory problems; sources listed as refineries, natural deposits, mines |
| US EPA health advisory (2018 table) | 0.05 mg/L | lifetime health advisory equal to the MCL; RfD 0.005 mg/kg per day, DWEL 0.2 mg/L |
| body | limit | note |
|---|---|---|
| EU CWW BREF BAT-AEL (Decision 2016/902) | not set | selenium is not a BAT 12 parameter |
| US EPA 40 CFR 423.13(g)(1), steam electric FGD wastewater (2020 BAT) | 70 daily maximum; 29 30-day average µg/L total selenium time-sensitive: the 2024 rule requires no discharge of FGD wastewater by a date no later than 31 December 2034 for most plants | with arsenic 18 and 8 µg/L, mercury 103 and 34 ng/L, nitrate plus nitrite 4 and 3 mg/L as N; technology basis chemical precipitation plus low residence time biological reduction |
| US EPA 40 CFR 423.13(g)(3), FGD wastewater, voluntary incentives programme | 10 µg/L total selenium, daily maximumtime-sensitive | with arsenic 5 µg/L, mercury 23 and 10 ng/L, nitrate plus nitrite 2.0 and 1.2 mg/L, bromide 0.2 mg/L, TDS 306 and 149 mg/L; for discharges generated after 31 December 2023 |
| US EPA 40 CFR 423.13(j)(1), gasification wastewater (BAT) | 453 daily maximum; 227 30-day average µg/L total selenium | with arsenic 4 µg/L, mercury 1.8 and 1.3 ng/L, TDS 38 and 22 mg/L |
| Abu Dhabi ADS 23/2017, discharge to the marine environment (EAD) | 0.02 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 sewer | 10 mg/L region-dependent; sewer discharge, not receiving water | Table A₄ maximum allowable concentration for trade effluent to the sewer network; 500 times the marine value |
| sector | body | limit | note |
|---|---|---|---|
| textile | ZDHC Wastewater Guidelines v₂.1 (2022), Table 2 | not set | selenium is a sample and report only wastewater parameter for textiles (methods EPA 200.8, 6010C, 6020A, HJ 700); sludge total selenium reporting limit 5 mg/kg dry weight (Table 4A) |
8 · Health and environmental effects
- Toxicity
- Essential: about 25 selenoproteins; recommended intakes 26 to 35 µg/day for adults, upper tolerable limit 400 µg/day. Deficiency is Keshan disease and Kaschin-Beck disease; excess is selenosis (brittle hair and nails, skin lesions, nerve changes) at dietary intakes above about 900 µg/day, with symptoms in Chinese villages at about 5 mg/day. Selenite, selenate, selenocysteine and selenomethionine kill laboratory animals at single doses of 1.5 to 6 mg/kg. Not classifiable as a carcinogen; several selenium compounds are anticarcinogenic in animals (WHO).
- Bioaccumulation
- Selenium is taken up into proteins as selenocysteine and selenomethionine and moves through food webs; selenate, selenite and the seleno amino acids are teratogenic in birds and fish, the basis of the aquatic bird deformities in central California cited by WHO and of the fish tissue form of the US criterion.
- Ecotoxicity
- US EPA 2016 freshwater criterion: egg or ovary 15.1 mg/kg dry weight, whole body 8.5, muscle 11.3, water column 1.5 µg/L in lentic and 3.1 µg/L in lotic systems (30 day averages), with an intermittent exposure element; fish tissue governs except when selenium inputs are increasing. Saltwater criteria 290 µg/L acute and 71 µg/L chronic (1999).
Flags
- The WHO natural water ranges are US compilations from 1937 to 1968 and vary by region; no recent survey was read.
- The seawater figure (0.2 µg/L) is a single abundance figure from Jefferson Lab via PubChem.
- Dissociation constants of selenous and selenic acid are not printed in the sources read; none are quoted.
- The selenate and selenite reduction half reactions are electron balances written here; the EPA and WHO describe the reductions in words.
- The US FGD limits carry compliance dates and were changed again by the 2024 supplemental rule, which was not read in full.
- Abu Dhabi values cover two media (marine 0.02 mg/L, sewer 10 mg/L); other GCC states not read.
- EPA 200.8 detection limits for selenium are 1994 quadrupole figures without a collision cell.
- The WHO selenium document names a branded activated alumina in the 98 percent figure; the brand is omitted here.
Gaps
- No measured selenium concentrations in FGD wastewater, refinery effluent, mine drainage or municipal wastewater were read; only the regulated levels.
- No removal percentages for full scale biological FGD treatment beyond the limits it was designed to meet.
- Selenium speciation methods (HPLC-ICP-MS, hydride with and without pre-reduction) were not read as numbered standards.
- No solubility products, adsorption constants or acid dissociation constants are printed in the sources read.
- The 2024 steam electric supplemental rule and other GCC discharge standards were not read.
- Selenium in the EU EQS directive and in the AMR or pharma sector lists was not checked.
- The zero valent iron and ferrous hydroxide reductions are written as electron balances from the reagents and pH values WHO gives; neither source prints a stoichiometry, and no carbon source stoichiometry was read for the biological selenate reduction step.
Sources
WHO, Selenium in Drinking-water, background document for development of WHO Guidelines for Drinking-water Quality, WHO/HSE/WSH/10.01/14 (2011), sections 1, 2, 5 and 6
Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Annex I Parts B and C and Annex III Table 1
US EPA, National Primary Drinking Water Regulations (table of MCLs)
US EPA, 2018 Edition of the Drinking Water Standards and Health Advisories Tables, EPA 822-F-18-001 (March 2018)
40 CFR 423.13, Effluent limitations guidelines representing BAT, steam electric power generating point source category (cooling tower blowdown, FGD wastewater, gasification wastewater)
US EPA, Supplemental Technical Development Document for the 2020 Steam Electric Reconsideration Rule, EPA 821-R-20-004 (August 2020), section 4 (biological treatment of FGD wastewater)
US EPA, Aquatic Life Ambient Water Quality Criterion for Selenium in Freshwater 2016, fact sheet (June 2016)
US EPA, National Recommended Water Quality Criteria, Aquatic Life Criteria Table and Appendix B (hardness equations)
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 4 and BAT 12 Table 3 with footnotes 24 to 29
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), Appendix Table A4
ZDHC Wastewater Guidelines Version 2.1 (November 2022), Table 1M (organotins), Table 2 (heavy metals) and Tables 4A and 4B (sludge)
US EPA Method 200.8, Revision 5.4 (1994), Determination of trace elements in waters and wastes by ICP-MS, Table 1 instrument detection limits
Standard Methods (online edition), 3114 Arsenic and Selenium by Hydride Generation/Atomic Absorption Spectrometry
Standard Methods (online edition), 3125 Metals by Inductively Coupled Plasma-Mass Spectrometry
ISO 17294-2:2023, Water quality. Application of ICP-MS. Part 2: Determination of selected elements including uranium isotopes
The Element Book, own entry for selenium (data/elements/Se.json and data/reference/text/Se.json)
PubChem element summary for selenium; estimated oceanic abundance 2 x 10^-4 mg/L from Jefferson Lab
Identity
- Name and symbol
- Selenium, Se
- Atomic number
- 34 protons
- Position
- group 16 · period 4 · p-block · polyatomic nonmetal
- CAS number
- 7782-49-2
Atomic structure
- Atomic mass
- 78.971 u
- Electron configuration
- 1s² 2s² 2p⁶ 3s² 3p⁶ 4s² 3d¹⁰ 4p⁴
[Ar] 4s²³d¹⁰⁴p⁴ - Electrons per shell
- 2, 8, 18, 6
- Valence electrons
- 6 outer shell
| isotope | mass (u) | abundance |
|---|---|---|
| 74Se | 73.922 4759(1) | 0.86 % |
| 76Se | 75.919 2137(1) | 9.23 % |
| 77Se | 76.919 9141(5) | 7.6 % |
| 78Se | 77.917 309(1) | 23.69 % |
| 80Se | 79.916 522(6) | 49.8 % |
| 82Se | 81.916 699(3) | 8.82 % |
Physical properties
- State at room temperature
- Solid
- Melting point
- 493.65 K (220.5 °C)
- Boiling point
- 958 K (684.85 °C)
- Density
- 4.809 g/cm3
- Appearance
- grey metallic-looking, red, and vitreous black (not pictured) allotropes
- Thermal conductivity
- amorphous: 0.519 W/(m·K)
- Electrical resistivity
- not in sources
- Electrical conductivity
- not in sources
- Crystal structure
- hexagonal
- Molar heat capacity
- 25.363 J/(mol·K)
Chemical properties
- Oxidation states
- +6, +4, -2
- Electronegativity
- 2.55 (Pauling Scale)
- Ionisation energy
- 9.752 eV
1st 941, 2nd 2,045, 3rd 2,973.7 kJ/mol - Electron affinity
- 2.021 eV
- Atomic radius
- empirical 120, covalent 120, van der Waals 190 pm
- Ionic radius
- Se²⁻ 198; Se⁴⁺ 50; Se⁶⁺ 42 pm
- Reactivity
- A group 16 non-metal below sulfur with several allotropes; grey selenium resists air and non-oxidising acids at room temperature but burns in oxygen and is oxidised by nitric acid, showing the -2, +4 and +6 states.
- with water
- Does not react with water.
- with oxygen, air
- Stable in air at room temperature; burns in oxygen with a blue flame to selenium dioxide: .
- with acids
- Resists non-oxidising acids; nitric acid oxidises it to selenous acid: .
- with halogens
- Burns in fluorine to selenium hexafluoride: ; with chlorine it gives SeCl4 and Se2Cl2.
- Typical compounds
- SeO₂ selenium dioxide polymeric solid, dissolves to selenous acid
- H₂Se hydrogen selenide extremely toxic gas, intolerable at 1.5 ppm
- H₂SeO₃ selenous acid from the dioxide in water; selenite salts
- SeF₆ selenium hexafluoride toxic gas, more reactive than SF6
- ZnSe zinc selenide metal selenide semiconductor
- SeS₂ selenium disulfide anti-dandruff shampoo ingredient
Occurrence, production and use
- Crustal abundance
- 5×10-2 milligrams per kilogram
- Oceanic abundance
- 2×10-4 milligrams per liter
- Occurrence and sources
- selenium in copper sulphide ores recovered from the anode slimes of electrolytic copper refineries; reserves 92,000 tonnes counted as the selenium content of copper reserves, largest in Russia, Peru, the United States, Canada and China
- crooksite, clausthalite and other rare selenium minerals minor; selenium was historically taken from copper smelter flue dust
- selenium in coal, and in lead, nickel and zinc ores coal generally contains significant selenium but recovery from fly ash is not economic; selenium is discharged from base metal, precious metal, industrial mineral, coal and uranium extraction
- Extraction, production
- Recovery from copper anode slimes
Anode slimes are roasted with soda ash or sulphuric acid, or smelted with soda and nitre, to release the selenium, which is then refined to 99.5 percent and higher; two United States refineries produced crude selenium and slimes in 2024 but refined none. The sources name the reagents but no reaction products, so no equation is written. World refinery production about 3,700 tonnes in 2024 (estimate), price about 24 dollars a kilogram in the United States and Europe.
- Uses
Selenium's resistance to the flow of electricity is greatly affected by the amount of light shining on it. The brighter the light, the better selenium conducts electricity. This property has made selenium useful in devices that respond to the intensity of light, such as electric eyes, photo cells, light meters for cameras and copiers. Selenium can also produce electricity directly from sunlight and is used in solar cells. Selenium is also a semiconductor and is used in some types of solid-state electronics as well as in rectifiers, devices which convert alternating current electricity into direct current electricity. In addition to its use in electrical devices, selenium is also used to make a ruby-red color in glasses and enamels, as a photographic toner and as an additive to stainless steel.
Selenium forms few inorganic compounds, none of which are commercially important. They include selenious acid (H2SeO3), selenium dichloride (SeCl2) and selenium oxychloride (SeOCl2).
Selenium is used in Xerography for reproducing and copying documents, letters, etc. It is used by the glass industry to decolorize glass and to make ruby-colored glasses and enamels. It is also used as a photographic toner, and as an additive to stainless steel.
- Metallurgy: selenium dioxide additive to raise yields in electrolytic manganese metal production; free machining copper, lead and steel alloys; gun bluing and plating solutions metallurgy including electrolytic manganese 40 percent of global consumption in 2024 (USGS, world figure)
- Agriculture and food: dietary supplement for livestock and humans as an essential micronutrient; fertiliser additive to raise plant tolerance of stress agriculture and animal health 20 percent of global consumption in 2024 (USGS)
- Glass: decolourising the green iron tint of container and soda lime glass; red and bronze tinted architectural glass glass 20 percent of global consumption in 2024 (USGS)
- Electronics and photovoltaics: copper indium gallium diselenide thin film solar cells, photocells and rectifiers electronics and photovoltaics 10 percent of global consumption in 2024 (USGS)
- Chemicals: cadmium sulphoselenide red pigments for ceramics, paint and plastics; catalysts for selective oxidation, rubber vulcanising agents, antidandruff shampoo actives, blasting cap delays chemicals and pigments 5 percent of global consumption in 2024 (USGS)
- Mining: selenium is listed among substances discharged from base metal, precious metal, industrial mineral, coal and uranium extraction (MWEI BREF)
- Safety, toxicity
Hydrogen selenide at a concentration of 1.5 ppm is intolerable to man. Selenium occurs in some solid in amounts sufficient to produce serious effects on animals feeding on plants, such as locoweed, grown in such soils. Exposure to selenium compounds (as Se) in air should not exceed 0.2 mg/m3 (8-hour time-weighted average - 40-hour week).
GHS classification, signal word Danger- H301 Toxic if swallowed Acute toxicity, oral
- H331 Toxic if inhaled Acute toxicity, inhalation
- H413 May cause long lasting harmful effects to aquatic life to the aquatic environment, long-term hazard
- H373 May causes damage to organs through prolonged or repeated exposure Specific target organ toxicity, repeated exposure
- H370 Causes damage to organs Specific target organ toxicity, single exposure
- H372 Causes damage to organs through prolonged or repeated exposure Specific target organ toxicity, repeated exposure
- H361 Suspected of damaging fertility or the unborn child Reproductive toxicity
Discovery and name
- Discovered by
- Jöns Jakob Berzelius and Johann Gottlieb Gahn
- Discovered
- 1817
- First isolated
- not in sources
- Named by
- not in sources
- Origin of the name
- after Selene, Greek goddess of the moon
Selenium exists in several allotropic forms, although three are generally recognized. Selenium can be prepared with either an amorphous or a crystalline structure. The color of amorphous selenium is either red (in powder form) or black (in vitreous form). Crystalline monoclinic selenium is a deep red; crystalline hexagonal selenium, the most stable variety, is a metallic gray.
Selenium exhibits both photovoltaic action, where light is converted directly into electricity, and photoconductive action, where the electrical resistance decreases with increased illumination. These properties make selenium useful in the production of photocells and exposure meters for photographic use, as well as solar cells. Selenium is also able to convert a.c. electricity to d.c., and is extensively used in rectifiers. Below its melting point, selenium is a p-type semiconductor and has many uses in electronic and solid-state applications.
Elemental selenium has been said to be practically nontoxic and is considered to be an essential trace element; however, hydrogen selenide and other selenium compounds are extremely toxic, and resemble arsenic in their physiological reactions.
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.