Mercury
fullMercury is regulated in drinking water by WHO (6 µg/L inorganic), the EU (1 µg/L) and the US (2 µg/L), in surface water by the strictest EU quality standard of any metal (0.07 µg/L), and in effluents at nanogram per litre levels; its water story is speciation, methylation in sediments, the chlor-alkali legacy, and removal by sulfide and activated carbon.
Typical wastewaters
- chlor-alkali (legacy mercury cells, decommissioning) Hg(II) complexes and dissolved elemental mercury, treated to 3 to 15 µg/L at the outlet of the mercury treatment unit during decommissioning or conversion the mercury cell process was stopped in the EU on 11 December 2017 and cannot be BAT under any circumstances; contaminated sewers and sediments release mercury for years
- coal fired power (flue gas desulfurisation wastewater) Hg(II) in the scrubber purge, treated to 34 ng/L monthly and 103 ng/L daily under the 2020 US BAT limits raw FGD mercury implied in the microgram per litre range; older or smaller units 356 and 788 ng/L
- ore mining and dressing (copper, lead, zinc, gold, silver, molybdenum mines and mills) Hg(II) in mine drainage and mill water, limited at 1 µg/L monthly limit, not a measured concentration
- refineries and factories; landfill and cropland runoff inorganic Hg(II), the US EPA source list for mercury in drinking water no concentration read
- textile and leather wet processing Hg(II) as a ZDHC restricted metal, limited at 0.01 mg/L foundational, 0.005 progressive and 0.001 aspirational, with sludge thresholds of 1 mg/kg textile and 0.2 mg/kg leather a limit, not a measured occurrence
1 · Identity
- Symbol, number
- Hg, 80
- Oxidation states in water
- +2 as Hg²⁺, present in water almost entirely as neutral hydroxide and chloride complexes (Hg(OH)₂, HgClOH, HgCl₂) and, in sulfidic water, as HgS and bisulfide complexes; 0 as dissolved elemental mercury, volatile and lost to air; +1 as Hg₂²⁺ only in unusual chemistry; and organic mercury, above all monomethylmercury CH₃Hg⁺, formed by bacteria in sediments. Almost all mercury in uncontaminated drinking water is thought to be inorganic Hg²⁺ (WHO).
- Note
- The element entry gives the metal's reactions and the calomel, cinnabar and chloride compounds. In water the questions are which complex, whether it has been methylated, and how far below 1 µg/L a treatment can go.
2 · Occurrence in water
- Natural sources
- Weathering of cinnabar and mercury bearing sulfide deposits; local mineral deposits produce higher groundwater levels (WHO); rainwater carries 5 to 100 ng/L, with means as low as 1 ng/L (WHO background document, IPCS 1990). Methylation of inorganic mercury occurs in both fresh water and seawater (WHO).
- Anthropogenic sources
- Chlor-alkali mercury cells, the process the EU stopped on 11 December 2017 and the BAT conclusions declare not BAT under any circumstances; electrical appliances, dental amalgam and mercury compounds (WHO); refineries, factories, landfill and cropland runoff (US EPA source list); flue gas desulfurisation wastewater at coal fired power plants, regulated in the US at 34 ng/L monthly; ore mining and dressing at 1 µg/L monthly; artisanal gold amalgamation in the ledger.
| matrix | typical range | note |
|---|---|---|
| surface water and groundwater | below 0.5 µg/L an upper bound, not a distribution | inorganic mercury, usually; local mineral deposits may produce higher levels in groundwater; wells on Izu Oshima Island, Japan, reached 5.5 µg/L |
| drinking water | about 0.025 µg/L1990s compilation | average about 25 ng/L, the same as rain (WHO background document); a small number of US groundwaters exceeded the 2 µg/L MCL |
| rainwater | 0.005 to 0.1 µg/L | 5 to 100 ng/L; means as low as 1 ng/L reported |
| industrial wastewater, flue gas desulfurisation | treated to 34 (monthly) and 103 (daily) ng/L limits, not measured raw concentrations | the 2020 US BAT limits; older or smaller units 356 and 788 ng/L; the limits imply raw FGD mercury in the microgram per litre range |
| industrial wastewater, chlor-alkali decommissioning | 3 to 15 µg/LEU BAT level, not a survey | BAT associated performance level at the outlet of the mercury treatment unit during decommissioning or conversion of mercury cell plants, 24 hour flow proportional composites |
| seawater | not read no figure | methylation occurs in seawater (WHO); no concentration figure was read |
3 · Speciation
Dissolved inorganic mercury in oxic fresh water is not the free ion but neutral Hg(OH)₂, HgClOH and HgCl₂, with the chloride complexes winning as chloride rises (HgCl₃⁻ and HgCl₄²⁻ in seawater); natural organic matter binds Hg(II) strongly at reduced sulfur sites, so most river mercury is organically bound or on particles. In anoxic sulfidic water mercury is HgS, one of the least soluble solids known, unless excess sulfide or organic thiols redissolve it. Bacteria in anoxic sediments methylate Hg(II) to methylmercury, the form that bioaccumulates; the balance between methylation and demethylation sets the methylmercury level (WHO).
| condition | dominant species | note |
|---|---|---|
| oxic fresh water, pH 6 to 9, low chloride | Hg(OH)₂, HgClOH, HgCl₂; Hg bound to natural organic matter and particles | the WHO fact sheet: almost all mercury in uncontaminated drinking water is inorganic |
| brackish water and seawater | HgCl₂, HgCl₃⁻, HgCl₄²⁻ | chloride complexes dominate; anionic complexes sorb poorly |
| anoxic, sulfidic sediment and groundwater | HgS (s), HgS₂²⁻ and HgHS₂⁻ at excess sulfide; CH₃Hg⁺ from bacterial methylation | methylation occurs in fresh water and seawater; bacteria isolated from fish slime and soil methylate mercury (WHO background document) |
| treatment plant with sulfide dosing | HgS (s) | best in the near neutral pH range; efficiency falls above pH 9 and excess sulfide redissolves mercury (EPA capsule report) |
- Solubility
- Mercury(II) chloride and nitrate are soluble; mercury sulfide has a very low solubility (WHO background document). No solubility product is printed in the sources read; the Stumm and Morgan table gives HgS among the least soluble sulfides (from the chapter, not re-read).
- Hydrolysis
- Hg²⁺ hydrolyses at low pH: Hg(OH)₂ is the dominant species above about pH 4 in chloride free water, which is why mercury behaves as a neutral, poorly sorbed molecule rather than a cation (Stumm and Morgan chapter 6, from the chapter).
- Complexation
- Chloride (HgCl⁺, HgCl₂, HgCl₃⁻, HgCl₄²⁻), hydroxide, sulfide and bisulfide, and the reduced sulfur groups of natural organic matter; constants not printed in the sources read.
- Precipitates
- HgS (cinnabar or metacinnabar) from sulfide precipitation and in anoxic sediments; Hg(OH)₂ and HgO only at high pH and high concentration; mercury co-precipitated on Fe(OH)₃ and Al(OH)₃ flocs in coagulation.
4 · Role in treatment
5 · Removal and control
- Efficiency
- 99.9 percent and more from initial mercury above 10 mg/L; the lowest achievable effluent appears to be about 10 to 100 µg/L (EPA after Patterson 1985)
- Interferences
- excess sulfide, high pH, oxidants
- Efficiency
- up to 80 percent inorganic and 20 to 40 percent organic mercury in drinking water treatment (WHO); 94 to 98 percent in the sewage tests
- Interferences
- organic mercury, low solids
- Efficiency
- not quoted as a percentage; part of the route to below 1 µg/L
- Interferences
- natural organic matter competes
- Efficiency
- lowest effluent concentrations of the established technologies (EPA)
- Interferences
- anionic chloride complexes need anion or chelating, not cation, resin
- Efficiency
- typically 80 to 90 percent rejection of mercury (EPA capsule report)
- Interferences
- neutral complexes pass more readily than ions
6 · Analytics
| method | standard | detection limit | note |
|---|---|---|---|
| cold vapour atomic fluorescence after bromine monochloride oxidation, purge and trap | EPA 1631 Revision E; ISO 17852 | MDL 0.2 ng/L, minimum level 0.5 ng/L, range 0.5 to 100 ng/L; 0.05 ng/L with larger volume and lower BrCl | the method behind the ng/L effluent limits; all mercury oxidised to Hg(II) with BrCl before analysis; needs the clean sampling of Method 1669 |
| cold vapour atomic absorption | EPA 245.1; Standard Methods 3112 B; ISO 12846 | 0.05 µg/L (WHO fact sheet) | the ZDHC accepted method with 245.7 and ICP-MS |
| ICP-MS | EPA 200.8 (direct analysis only); ISO 17294-2 | 0.2 µg/L direct analysis in EPA 200.8 Table 7; total recoverable digestion not applicable because it is unsuitable for organomercury; 0.6 µg/L by ICP (WHO) | severe memory effects; 100 µg/L gold in the rinse clears 5 µg/L mercury; keep standards at or below 5 µg/L |
| flame atomic absorption | 5 µg/L (WHO) | too insensitive for drinking water |
- Sampling pitfalls
- Preserve with bromine monochloride (EPA 1631E) or acid; mercury adsorbs to and volatilises from ordinary bottles, so use acid cleaned glass or fluoropolymer and follow Method 1669 clean hands technique. Discrete autosamplers contaminate at the ng/L level (EPA 1631E). Samples above 100 ng/L must be diluted; iodide above tens of µg/L interferes with the purge. Methylmercury needs a separate, unoxidised aliquot.
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) | 6 µg/L | for inorganic mercury, the form found in drinking water; TDI 2 µg/kg body weight from a NOAEL of 0.23 mg/kg per day for kidney effects in rats, uncertainty factor 100; 10 percent allocation, 60 kg, 2 L/day; the previous value applied to total mercury; assessment 2004 |
| EU DWD 2020/2184 | 1.0 µg/L | Annex I Part B chemical parameter; uncertainty of measurement 30 percent of the parametric value (Annex III) |
| US EPA NPDWR | 0.002 mg/L | MCL and MCLG for inorganic mercury; sources listed as erosion of natural deposits, discharge from refineries and factories, runoff from landfills and croplands |
| body | limit | note |
|---|---|---|
| EU CWW BREF BAT-AEL (Decision 2016/902) | not set | mercury is not among the BAT 12 parameters (Cr, Cu, Ni, Zn are the metals with AELs); mercury limits in EU chemical plants come from permits and the chlor-alkali conclusions |
| EU chlor-alkali BAT conclusions (Decision 2013/732/EU), decommissioning or conversion of mercury cell plants | 3 to 15 µg/L | BAT associated environmental performance level at the outlet of the mercury treatment unit, 24 hour flow proportional composite samples taken daily; the mercury cell technique cannot be considered BAT under any circumstances; no AEL for normal production |
| US EPA 40 CFR 415.63, chlor-alkali mercury cell process (BAT) | 0.00023 daily maximum; 0.00010 30-day average kg mercury per kkg of product | a mass based limit for a process the EU has prohibited since 11 December 2017 |
| US EPA 40 CFR 423.13(g)(1)(i), steam electric FGD wastewater (2020 BAT) | 103 daily maximum; 34 30-day average ng/L total mercury time-sensitive: the 2024 steam electric rule changed applicability dates | compliance by 31 December 2025; subcategory (g)(2)(ii) 788 and 356 ng/L; voluntary incentives programme (g)(3)(i) 23 and 10 ng/L by 31 December 2028; gasification wastewater (j)(1)(i) 1.8 and 1.3 ng/L; combustion residual leachate (l)(2)(i)(A) 788 and 356 ng/L by 30 April 2035 |
| US EPA 40 CFR 440.103, copper, lead, zinc, gold, silver and molybdenum ore mines and froth flotation mills (BAT) | 0.002 daily maximum; 0.001 30-day average mg/L | no discharge of process wastewater from mills using cyanidation |
| Abu Dhabi ADS 23/2017, discharge to the marine environment (EAD) | 0.001 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 | 0.5 mg/L region-dependent; sewer discharge, not receiving water; 500 times the marine value | Table A₄ maximum allowable concentration for trade effluent to the sewer network |
| sector | body | limit | note |
|---|---|---|---|
| textile and leather | ZDHC Wastewater Guidelines v₂.1 (2022) | 0.01 foundational; 0.005 progressive; 0.001 aspirational mg/L | methods ISO 17294, EPA 200.8-SIM, 6020A-SIM, 245.1, 245.7, cold vapour AAS; sludge threshold 1 mg/kg textile, 0.2 leather |
8 · Health and environmental effects
- Toxicity
- Inorganic mercury targets the kidney in humans and animals (tubular necrosis, proteinuria); acute oral poisoning causes haemorrhagic gastritis and colitis; mercury(II) chloride can raise benign tumours where tissue is damaged and is weakly genotoxic without point mutations (WHO). Mean dietary intake 2 to 20 µg/day; JECFA PTWI for total mercury 5 µg/kg body weight with no more than 3.3 µg/kg as methylmercury (1972, reassessed 1988 and 2003; WHO background document). Methylmercury is the neurotoxin of Minamata and of fish advisories.
- Bioaccumulation
- Methylmercury bioaccumulates and biomagnifies in aquatic food chains; the EU EQS in biota is 20 µg/kg wet weight, set because the water column value cannot protect predators and humans eating fish (Directive 2013/39/EU). Inorganic mercury in drinking water is not the exposure route of concern; food is (WHO).
- Ecotoxicity
- US EPA aquatic life criteria: freshwater 1.4 µg/L acute and 0.77 µg/L chronic, saltwater 1.8 and 0.94 µg/L (1995), with the caution that they may not protect where methylmercury is a substantial part of total mercury. EU EQS: 0.07 µg/L annual average and maximum in inland and other surface waters, biota 20 µg/kg.
Flags
- The occurrence figures are 1990s IPCS compilations in the WHO 2005 background document; no modern survey was read.
- The FGD and chlor-alkali numbers are limits, not measured effluent concentrations.
- The hydrolysis and chloride speciation equations are cited to Stumm and Morgan chapter 6 from memory of the text; the mechanism of methylation (sulfate reducers, hgcAB genes) is not sourced and is left as 'bacteria in anoxic sediments' as WHO puts it.
- The HgS redissolution equation is written here from the EPA statement about soluble mercury sulfide species at excess sulfide.
- The US steam electric mercury limits carry compliance dates and were revised in 2024; check applicability before quoting.
- Abu Dhabi values cover two media (marine 0.001 mg/L, sewer 0.5 mg/L); other GCC states were not read.
- The Minamata Convention text was not reachable this session; the chlor-alkali ban date is cited to the EU mercury regulation.
Gaps
- No source read gives mercury in seawater, municipal wastewater influent or specific industrial effluents as measured ranges; only limits and 1990s compilations are quoted.
- Solubility products, hydrolysis and chloride complexation constants and methylmercury formation rates are not printed in the sources read.
- The Minamata Convention (adoption, entry into force, Annex B dates) was not read; the EU regulation stands in.
- Mercury removal by chemical reduction (borohydride, stannous chloride) and by membrane extraction, described in the EPA capsule report chapters 5 and 6, was not read in detail.
- EPA 245.1 and 245.7 detection limits were not read; the WHO 0.05 µg/L figure stands for cold vapour AAS.
- Other GCC discharge standards (Saudi, Oman, Qatar) were not read.
- Bacterial methylation of Hg(II) to methylmercury is described by WHO as a pathway and no source read prints a stoichiometry or a rate for it, so no methylation equation is written.
- The thiol resin equation is written in the resin convention from the mechanism the EPA capsule report describes.
Sources
WHO, Mercury in Drinking-water, background document for development of WHO Guidelines for Drinking-water Quality, WHO/SDE/WSH/05.08/10 (2005), sections 1.4, 2.2, 6.1, 6.2 and 7
Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Article 11, Annex I Part B, Annex II Part D and Annex III
US EPA, National Primary Drinking Water Regulations (table of MCLs and MCLGs, inorganic chemicals and radionuclides)
Directive 2013/39/EU amending Directives 2000/60/EC and 2008/105/EC as regards priority substances, Annex I Part A (environmental quality standards)
US EPA, National Recommended Water Quality Criteria, Aquatic Life Criteria Table
Regulation (EU) 2017/852 on mercury, Article 7 and Annex III Part I (manufacturing processes in which the use of mercury is prohibited)
Commission Implementing Decision 2013/732/EU establishing BAT conclusions for the production of chlor-alkali, BAT 1 and the BAT on decommissioning of mercury cell plants
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
40 CFR part 415 subpart F (chlor-alkali), section 415.63, mercury cell process BAT effluent limitations
40 CFR 423.13, Effluent limitations (BAT), steam electric power generating point source category
40 CFR 440.103, Effluent limitations (BAT), copper, lead, zinc, gold, silver and molybdenum ores subcategory
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 Tables A2 and A4
ZDHC Wastewater Guidelines Version 2.1 (November 2022), Table 2 heavy metals and Table 4 sludge parameters
US EPA, Capsule Report: Aqueous Mercury Treatment, EPA/625/R-97/004 (July 1997), chapters 1 to 4
US EPA Method 1631, Revision E (2002), Mercury in water by oxidation, purge and trap, and cold vapor atomic fluorescence spectrometry, sections 1.2 to 1.4 and 2
US EPA Method 200.8, Revision 5.4 (1994), Determination of trace elements in waters and wastes by ICP-MS, Table 7 (method detection limits)
Standard Methods for the Examination of Water and Wastewater (online edition), 3112 B Metals by cold-vapor atomic absorption spectrometry (mercury)
ISO 12846:2012, Water quality. Determination of mercury. Method using atomic absorption spectrometry with and without enrichment
ISO 17852:2006, Water quality. Determination of mercury. Method using atomic fluorescence spectrometry
ISO 17294-2:2023, Water quality. Application of ICP-MS. Part 2: Determination of selected elements including uranium isotopes
Stumm, W. and Morgan, J. J., Aquatic Chemistry, 3rd ed. (Wiley, 1996), chapter 6 (metal ions in aqueous solution, hydrolysis and complex formation) and chapter 7 (precipitation and dissolution, solubility products)
The Element Book, element entry and reference text for Hg (data/elements/Hg.json, data/reference/text/Hg.json)
Identity
- Name and symbol
- Mercury, Hg
- Atomic number
- 80 protons
- Position
- group 12 · period 6 · d-block · transition metal
- CAS number
- 7439-97-6
Atomic structure
- Atomic mass
- 200.592 u
- Electron configuration
- 1s² 2s² 2p⁶ 3s² 3p⁶ 4s² 3d¹⁰ 4p⁶ 5s² 4d¹⁰ 5p⁶ 6s² 4f¹⁴ 5d¹⁰
[Xe] 6s²⁴f¹⁴⁵d¹⁰ - Electrons per shell
- 2, 8, 18, 32, 18, 2
- Valence electrons
- 12 ns and (n-1)d
| isotope | mass (u) | abundance |
|---|---|---|
| 196Hg | 195.965 83(2) | 0.15 % |
| 198Hg | 197.966 769(3) | 10.04 % |
| 199Hg | 198.968 281(4) | 16.94 % |
| 200Hg | 199.968 327(4) | 23.14 % |
| 201Hg | 200.970 303(5) | 13.17 % |
| 202Hg | 201.970 644(5) | 29.74 % |
| 204Hg | 203.973 494(3) | 6.82 % |
Physical properties
- State at room temperature
- Liquid
- Melting point
- 234.32 K (-38.83 °C)
- Boiling point
- 629.88 K (356.73 °C)
- Density
- 13.5336 g/cm3
- Appearance
- shiny, silvery liquid
- Thermal conductivity
- 8.30 W/(m·K)
- Electrical resistivity
- 961 nΩ·m
- Electrical conductivity
- 1.04 MS/m
- Crystal structure
- rhombohedral
- Molar heat capacity
- 27.983 J/(mol·K)
Chemical properties
- Oxidation states
- +2, +1
- Electronegativity
- 2 (Pauling Scale)
- Ionisation energy
- 10.438 eV
1st 1,007.1, 2nd 1,810, 3rd 3,300 kJ/mol - Electron affinity
- 0 eV
- Atomic radius
- empirical 132, covalent 132, van der Waals 209 pm
- Ionic radius
- Hg⁺ 119; Hg²⁺ 102 pm
- Reactivity
- The only metal liquid at room temperature, mercury sits between the noble metals and its group 12 relatives zinc and cadmium in reactivity: it does not tarnish in dry air or react with water or non-oxidising acids, but it dissolves in oxidising acids, combines directly with sulfur and the halogens, and forms Hg(I) dimers as well as Hg(II) compounds.
- with water
- Does not react with water.
- with oxygen, air
- Does not tarnish in dry air at room temperature; heated near its boiling point it slowly oxidises to the red oxide: , which decomposes back to the elements near 400 C.
- with acids
- Unaffected by hydrochloric acid or dilute sulfuric acid; hot concentrated sulfuric acid dissolves it: , and nitric acid gives the nitrate: , with excess mercury giving the Hg(I) salt instead.
- with halogens
- Combines directly with the halogens on gentle heating; chlorine gives the sublimable mercury(II) chloride: , while excess mercury gives calomel Hg2Cl2.
- Typical compounds
- HgCl₂ mercury(II) chloride corrosive sublimate, violently poisonous white solid
- Hg₂Cl₂ mercury(I) chloride calomel, Cl-Hg-Hg-Cl with a metal-metal bond
- HgS mercury(II) sulfide cinnabar, the ore, and the pigment vermilion
- HgO mercury(II) oxide red oxide of mercury batteries, decomposes near 400 C
- Hg(CNO)₂ mercury fulminate primary explosive once used in detonators
- Hg(NO₃)₂ mercury(II) nitrate soluble salt from the metal and nitric acid
Occurrence, production and use
- Crustal abundance
- 8.5×10-2 milligrams per kilogram
- Oceanic abundance
- 3×10-5 milligrams per liter
- Occurrence and sources
- cinnabar (HgS), with droplets of native mercury China, Kyrgyzstan, Tajikistan, Spain (Almaden, closed 2003), Slovenia, Mexico, Peru, Ukraine; Alaska, Arkansas, California, Nevada, Texas
- by-product of gold-silver ore processing and of colonial silver-mining waste Nevada mines; Mexico reclaims mercury from Spanish colonial residues
- crustal and oceanic abundance about 0.03 ppm crust (BGS via RSC); 0.085 mg/kg crust and 0.00003 mg/L seawater (PubChem)
- Extraction, production
- Roasting cinnabar in a current of air and condensing the vapour
RSC states cinnabar is heated in air and the mercury vapour condensed; sulfur dioxide as the sulfur product is implied by roasting, not named
Secondary mercury by retorting of lamps, batteries, amalgam, switches, thermostats and contaminated soilseight US facilities of six companies in 2024; LED replacement of fluorescent lamps is increasing the recycled flow
- Uses
Mercury can be used to make thermometers, barometers and other scientific instruments. Mercury conducts electricity and is used to make silent, position dependent switches. Mercury vapor is used in streetlights, fluorescent lamps and advertising signs.
Mercury easily forms alloys with other metals, such as gold, silver, zinc and cadmium. These alloys are called amalgams. Amalgams are used to help extract gold from its ores, create dental fillings (in the case of silver) and help extend the life of dry cell batteries (in the case of zinc and cadmium).
Mercury forms useful compounds with other elements. Mercuric chloride (HgCl2) is a very poisonous salt and was once used to disinfect wounds. Mercurous chloride (Hg2Cl2), also called calomel, is an antiseptic used to kill bacteria. Mercuric sulfide (HgS) is used to make a red paint pigment called vermilion. Mercuric oxide (HgO) is used to make mercury batteries.
Mercury is poisonous and can enter the body through the respiratory tract, the digestive tract or directly through the skin. It accumulates in the body, eventually causing severe illness or death.
The metal is widely used in laboratory work for making thermometers, barometers, diffusion pumps, and many other instruments. It is used in making mercury-vapor lamps and advertising signs, etc. and is used in mercury switches and other electronic apparatus. Other uses are in making pesticides, Mercury cells for caustic soda and chlorine production, dental preparations, anti-fouling paint, batteries, and catalysts.
- Chemicals (chlor-alkali mercury cell, VCM catalysts): flowing mercury cathode of the mercury-cell chlor-alkali process; anode: ; cathode: Na+ + e- + Hgx -> NaHgx; decomposer: 2 NaHgx Hgx; overall: (cak-bref-2014, PDF p40); one US mercury-cell plant still ran in 2024; not BAT in the EU since 2017; mercury(II) catalysts for coal-based (acetylene) vinyl chloride monomer in China; mercury carried in mercury-cell caustic into steam-cracker scrubbing liquor about 163 t of elemental mercury circulates in US manufacturing processes (catalysts, cell cathodes), almost all reused (usgs-mcs2025-mercury)
- Electrical devices: relays, sensors, switches, valves, rectifiers relays, sensors, switches and valves 65 percent of US end use (usgs-mcs2025-mercury)
- Dentistry and medicine: dental amalgam (mercury and silver as biocides against recurrent decay); formulated products: buffers, fixatives, vaccine preservatives dental amalgam 27 percent, formulated products 7 percent of US end use (usgs-mcs2025-mercury)
- Pharmaceuticals (fine-chemical synthesis): mercury reagents in reductions and other unit processes of organic fine-chemical synthesis
- Lighting: fluorescent and compact fluorescent lamps, being replaced by LEDs bulbs, lamps and lighting 1 percent of US end use (usgs-mcs2025-mercury)
- Mining (gold amalgamation): mercury amalgamation of gold in artisanal and small-scale mining, the largest anthropogenic emission source; mercury reported in extractive-waste water at four precious-metal sites; by-product recovery at large gold-silver mines
- Pigments and consumer products (legacy): vermilion (HgS) pigment, now rarely used; button batteries, skin-lightening creams, folk medicines, fireworks, pesticides in some countries
- Safety, toxicity
- GHS classification, signal word Danger
- H330 Fatal if inhaled Acute toxicity, inhalation
- H400 Very toxic to aquatic life Hazardous to the aquatic environment, acute hazard
- H410 Very toxic to aquatic life with long lasting effects Hazardous to the aquatic environment, long-term hazard
- H290 May be corrosive to metals Corrosive to Metals
- H300 Fatal if swallowed Acute toxicity, oral
- H360 May damage fertility or the unborn child Reproductive toxicity
- H360D May damage the unborn child Reproductive toxicity
- H372 Causes damage to organs through prolonged or repeated exposure Specific target organ toxicity, repeated exposure
- H317 May cause an allergic skin reaction Sensitization, Skin
- H319 Causes serious eye irritation Serious eye damage/eye irritation
- H370 Causes damage to organs Specific target organ toxicity, single exposure
- H341 Suspected of causing genetic defects Germ cell mutagenicity
- H360FD May damage fertility; May damage the unborn child Reproductive toxicity
Discovery and name
- Discovered by
- Ancient Egyptians
- Discovered
- before 1500 BCE
- First isolated
- not in sources
- Named by
- not in sources
- Origin of the name
- from the planet Mercury, with which it was associated in medieval alchemy
It is a heavy, silvery-white metal; a rather poor conductor of heat, as compared with other metals, and a fair conductor of electricity. It easily forms alloys with many metals, such as gold, silver, and tin, which are called amalgams. Its ease in amalgamating with gold is made use of in the recovery of gold from its ores. The most important salts are mercury chloride (corrosive sublimate - a violent poison), mercurous chloride (calomel, occasionally still used in medicine), mercury fulminate, a detonator widely used in explosives, and mercuric sulfide (vermilion, a high-grade paint pigment). Organic mercury compounds are important. It has been found that an electrical discharge causes mercury vapor to combine with neon, argon, krypton, and xenon. These products, held together with van der Waals' forces, correspond to HgNe, HgAr, HgKr, and HgXe. Mercury is a virulent poison and is readily absorbed through the respiratory tract, the gastrointestinal tract, or through unbroken skin. It acts as a cumulative poison and dangerous levels are readily attained in air. Air saturated with mercury vapor at 20°C contains a concentration that exceeds the toxicity limits. The danger increases at higher temperatures. It is important therefore that mercury be handled with care. Containers of mercury should be securely covered and spillage should be avoided. If it is necessary to heat mercury or mercury compounds, it should be done in a well-ventilated hood. Methyl mercury is a dangerous pollutant and is now widely found in water and streams. The triple point of mercury, -38.8344C, is a fixed point on the International Temperature Scale (ITS-90).
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.