Manganese
fullManganese is the groundwater problem that outlasts iron: WHO set a provisional 0.08 mg/L guideline in 2021, the EU lists 50 µg/L as an indicator and the US 0.05 mg/L as a secondary standard, and its removal needs a stronger oxidant or a higher pH than iron because Mn(II) resists oxygen; permanganate and manganese oxide coated media are treatment reagents in their own right.
Typical wastewaters
- coal mine drainage (acid or ferruginous) dissolved Mn²⁺ that stays in solution after the iron has oxidised; 4.0 daily maximum and 2.0 mg/L monthly average
- ferroalloy smelting (open electric furnaces with wet scrubbers) total manganese in furnace off-gas scrubber water from ferromanganese and silicomanganese smelting BPT 0.064 kg/MWh daily maximum and 0.032 kg/MWh 30-day average, with chromium and TSS
- electrolytic manganese and manganese dioxide production dissolved Mn²⁺ with ammonia-N in cell liquor bleed and rinse water BPT 2.771 kg/t product daily maximum and 1.356 kg/t 30-day average for electrolytic manganese, ammonia-N 40.667 kg/t
- battery manufacture (zinc anode and Leclanche cells) manganese from manganese dioxide cathode paste in process wastewater BPT 2.58 mg/kg zinc daily maximum and 1.10 mg/kg monthly average for wet amalgamated powder anodes; NSPS 0.019 mg/kg of cells produced for Leclanche cells
- coal combustion residual leachate (ash landfills and impoundments) dissolved manganese among the BAT treated pollutants in combustion residual leachate; monitored as monthly minimum, maximum and average monitoring table lists Mn with V, As, Se, B and other ash metals
- blast furnace gas scrubbing water Mn 0.48 mg/L average in untreated scrubber water with Fe 6.77, Zn 0.1 to 29.4, NH₄⁺ 2 to 200 and cyanide 0.1 to 50 mg/L six EU blast furnaces, 1990 to 1992 data (Table 6.11)
- steelmaking plant wastewater manganese with iron, zinc and copper in raw steel making wastewater above the Malaysian Standard B limits 0.03 mg/L after an electric arc furnace slag column
- manganese contaminated mine drainage Mn²⁺ persisting after iron removal, precipitated as rhodochrosite, manganite and Mn(III, IV) oxides in steelmaking slag and limestone reactors 316 day pilot in Korea; no raw concentration in the abstract
1 · Identity
- Symbol, number
- Mn, 25
- Oxidation states in water
- +2 as Mn²⁺, the dissolved form of anoxic and acid groundwater and of hypolimnia (WHO: the divalent form predominates in most water at pH 4 to 7); +4 as MnO₂ and hydrous manganese oxides, the black solid that stains, coats mains and is the filter deposit; +7 as permanganate MnO₄⁻, the treatment oxidant, purple, and the species left by an ozone overdose; +3 only as a transient in oxide surfaces and in strong complexes.
- Note
- The element entry covers the eleven oxidation states, pyrolusite and the steel and battery uses. This chapter is about the Mn(II) to Mn(IV) step in water and what it costs to force it.
2 · Occurrence in water
- Natural sources
- Weathering of manganese bearing rock and soil; reductive dissolution of manganese oxides in anoxic aquifers, in lake and reservoir hypolimnia below a thermocline, and in acidic water. WHO: reducing conditions in groundwater and some lakes and reservoirs favour high manganese; in aerobic waters higher levels are usually associated with industrial pollution. Manganese is detected at about 70 percent of US groundwater sites and 97 percent of surface water sites.
- Anthropogenic sources
- Acid and ferruginous coal mine drainage (US limit 4.0 mg/L daily maximum); iron and steel and ferroalloy plants and manganese mining in the ledger's chapters; potassium and sodium permanganate used for cleaning, bleaching and water treatment; manganese as an impurity in coagulants (WHO fact sheet); permanganate overdosed in a treatment plant.
| matrix | typical range | note |
|---|---|---|
| fresh water, typical | 1 to 200 µg/Lregion-dependent | WHO fact sheet range; very high concentrations up to 10 mg/L reported in acidic groundwater |
| surface water, USA (USGS NAWQA) | median 16; 99th percentile 400 to 800 µg/L1990s survey | US river survey dissolved manganese below 11 to above 51 µg/L |
| groundwater, USA (USGS NAWQA) | median 5; 99th percentile 5,600 µg/L region-dependent; the median is lower than surface water but the tail far higher | up to 1,300 µg/L in neutral and 9,600 µg/L in acidic groundwater reported by ATSDR |
| drinking water, treated | below 50 µg/L | typical treated water (fact sheet); US groundwater systems 1984 to 1986 median 10 µg/L, detected in 68 percent; Germany 90 percent of households below 20 µg/L |
| seawater | 0.4 to 10 µg/L | average about 2 µg/L |
3 · Speciation
Manganese(II) is soluble and stable in water far longer than iron(II): oxygen alone oxidises it only above about pH 9 at useful rates, and the reaction is autocatalytic on the manganese oxide it produces, so a clean water without oxide surfaces holds Mn²⁺ for days in aerated water at neutral pH (Stumm and Morgan). Chlorine, permanganate, ozone and chlorine dioxide do the step in minutes at pH 7 to 8. The product is a hydrous Mn(IV) oxide, written MnO₂, that is insoluble, black, adsorbs other metals and catalyses further oxidation. In carbonate rich anoxic groundwater rhodochrosite MnCO₃ caps dissolved manganese; in sulfidic water MnS is far more soluble than FeS, so manganese stays dissolved where iron precipitates. Over-oxidation with ozone gives permanganate, which redissolves the manganese as a pink anion until it is reduced on a filter.
| condition | dominant species | note |
|---|---|---|
| anoxic or acid groundwater, hypolimnion, pH 4 to 7 | Mn²⁺, MnHCO₃⁺; MnCO₃ (s) where carbonate is high | WHO: the divalent form predominates in most water at pH 4 to 7 |
| aerated water, pH 7 to 8, no catalyst | Mn²⁺ persists for days; slow conversion to MnO₂ (s) | the reason aeration alone does not remove manganese |
| aerated water above pH 9, or any pH with chlorine, permanganate, ozone or chlorine dioxide | MnO₂ (s), hydrous manganese oxides | the filterable form; also the coating on greensand and on old mains |
| ozone overdose, or permanganate overdose | MnO₄⁻ (pink water) | EPA: over-ozonation resolubilises manganese, which should be reduced to manganese dioxide downstream |
- Solubility
- MnO₂ is the controlling solid in oxic water and holds dissolved Mn(IV) at negligible levels; the practical solubility of manganese is that of Mn²⁺, which is high until it is oxidised. MnCO₃ (rhodochrosite) controls Mn(II) in anoxic carbonate water. No solubility products are quoted; the sources read print none.
- Hydrolysis
- Mn²⁺ hydrolyses only above pH 9 (Mn(OH)₂ is much more soluble than Fe(OH)₂), which is why the oxygenation rate, second order in hydroxide like that of iron, is so slow at neutral pH.
- Complexation
- Bicarbonate and sulfate ion pairs; natural organic matter binds Mn(II) weakly compared with Fe(III). WHO notes that adsorption on soil depends on organic content and cation exchange capacity. Constants not quoted.
- Precipitates
- MnO₂ and hydrous manganese oxides (oxic); MnCO₃ rhodochrosite (anoxic, carbonate); Mn₃O₄ hausmannite and Mn₂O₃ as ageing products; manganese oxide coatings on pipe walls that also hold arsenic, barium, chromium, lead and uranium (WHO fact sheet).
4 · Role in treatment
5 · Removal and control
- Efficiency
- easily to below 0.05 mg/L (WHO fact sheet); oxidation and filtration usually adequate for 0.05 mg/L (WHO background document)
- Interferences
- organic matter consumes oxidant; low pH slows chlorine; ozone overdose makes permanganate; ammonia turns chlorine into chloramine, which does not oxidise manganese
- Efficiency
- to below 0.05 mg/L (WHO fact sheet lists it among the methods that achieve this)
- Interferences
- iron above the media capacity, silica and organics coat the surface
- Efficiency
- to below 0.05 mg/L (WHO)
- Interferences
- chlorine residual kills the biofilm; iron must be removed first
- Efficiency
- not quoted as a figure
- Interferences
- Mn(II) already oxidised to particulate fouls resin
- Efficiency
- not quoted
- Interferences
- particulate manganese fouls the membrane
6 · Analytics
| method | standard | detection limit | note |
|---|---|---|---|
| ICP-MS | EPA 200.8 (mass 55); ISO 17294-2 | 0.002 µg/L (WHO fact sheet); EPA 200.8 instrument detection limit 0.1 µg/L scanning, 0.007 µg/L selected ion monitoring | ArNH⁺ overlaps mass 55 (EPA 200.8 Table 2); none of the methods distinguish oxidation states |
| ICP-OES and graphite furnace AAS | EPA 200.7; ISO 11885; ISO 15586 | 0.005 to 50 µg/L across ICP-AES and GFAAS (WHO fact sheet); ICP-OES about 1 to 2 µg/L, AAS to 0.01 µg/L (WHO background document) | |
| colorimetry | Standard Methods 3500-Mn B (persulfate); the ISO 1986 spectrometric method cited by WHO | 10 to 70 µg/L (WHO fact sheet); about 10 µg/L (WHO background document) | field kits for operations |
- Sampling pitfalls
- Dissolved and particulate manganese answer different treatment questions (WHO: selection of treatment depends on the form), so filter 0.45 µm in the field for dissolved manganese and acidify both fractions at once; Mn(II) oxidises far more slowly than Fe(II) in the bottle but still deposits on walls over days. A tap sample after a hydraulic disturbance measures the deposit, not the water. Monitor after treatment where manganese is removed (WHO).
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) | 0.08 mg/L | provisional guideline value for total manganese, protective of neurological effects in bottle fed infants; TDI 0.025 mg/kg body weight from a rat LOAEL of 25 mg/kg per day with an uncertainty factor of 1000; 50 percent allocation, 5 kg infant, 0.75 L/day; assessment 2020 |
| WHO GDWQ, acceptability | 0.02 mg/L | concentrations above 0.02 mg/L have caused complaints about discoloured water and staining (fact sheet); 0.05 mg/L usually acceptable (background document) |
| EU DWD 2020/2184 | 50 µg/L | Annex I Part C indicator parameter |
| US EPA | 0.05 mg/L | National Secondary Drinking Water Regulation, non enforceable; effects listed as black to brown colour, black staining, bitter metallic taste; no primary MCL |
| body | limit | note |
|---|---|---|
| EU CWW BREF BAT-AEL (Decision 2016/902) | not set | manganese is not among the metals with a BAT-AEL (Cr, Cu, Ni, Zn) |
| US EPA 40 CFR 434.32, coal mining, acid or ferruginous mine drainage (BPT) | 4.0 daily maximum; 2.0 30-day average mg/L total manganese | with total iron 7.0 and 3.5 mg/L; taken from the book's iron water chapter, section not re-read this session |
| Abu Dhabi ADS 23/2017, discharge to the marine environment (EAD) | 0.2 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 Metals, maximum allowable concentration for trade effluent to the sewer network |
| sector | body | limit | note |
|---|---|---|---|
| textile and leather | ZDHC Wastewater Guidelines v₂.1 (2022) | not set | manganese is not a ZDHC wastewater parameter |
8 · Health and environmental effects
- Toxicity
- Essential trace element; the central nervous system is the target of excess. WHO's provisional guideline rests on neurodevelopmental effects in juvenile rats (LOAEL 25 mg/kg per day) supported by epidemiology of reduced cognitive ability in children drinking manganese rich water; absorption and retention are higher in infants, and bottle fed infants get manganese from both formula and the water; no adequate evidence of oral carcinogenicity (WHO fact sheet). WHO advises exclusive breastfeeding or an alternative safe water for formula where the value is exceeded.
- Bioaccumulation
- Bioaccumulates in lower organisms (phytoplankton, algae, molluscs, some fish) but not in higher organisms; biomagnification in food chains not expected to be significant (WHO background document).
- Ecotoxicity
- No US EPA national recommended aquatic life criterion for manganese; the harm in mine drainage streams is the oxide coating of the bed, as with iron.
Flags
- The Mn(II) oxygenation rate law and its autocatalysis are cited to Stumm and Morgan chapter 11 from memory of the text, not re-read this session; MnCO₃ likewise to chapter 7.
- EPA Table 2-7 prints 0.77 mg Cl₂ per mg Mn; the Mn(II) to MnO₂ electron balance gives 1.29 mg Cl₂ per mg Mn. Both are given; the EPA figure comes from a 1986 compilation the manual cites.
- The chlorine, ozone and chlorine dioxide equations are electron balances written here; EPA prints the doses and the products, not the equations.
- USGS median and 99th percentile figures are 1990s NAWQA compilations quoted by the 2011 WHO background document; the 2021 WHO background document was not reachable (iris.who.int returned 403).
- The coal mining limit is reused from the book's iron chapter; the CFR section was not re-read this session.
- Abu Dhabi values cover two media (marine 0.2 mg/L, sewer 10 mg/L); other GCC states not read.
- Standard Methods and ISO method numbers other than those in the sources read (EPA 200.8, ISO 17294-2 and the methods the WHO documents cite) are quoted from memory and were not confirmed this session.
Gaps
- Biological manganese filtration design (pH, dissolved oxygen, start-up) is named by WHO but not described in any source read.
- The 2021 WHO background document (WHO/HEP/ECH/WSH/2021.5) behind the provisional guideline was not reachable; occurrence figures are from the 2011 revision.
- EU law was read on legislation.gov.uk mirrors because eur-lex did not respond to scripts; the eur-lex urls are kept for consistency with the other chapters.
- No EQS row: manganese is not an EU priority substance and the directive was not searched for it.
- Other GCC discharge standards (Saudi, Oman, Qatar) were not read.
- No solubility products, hydrolysis constants or rate constants are printed here. The hydroxide, sulfide, autocatalytic surface and permanganate half reaction equations and the lime softening and ion exchange stoichiometry are from Stumm and Morgan chapters 7, 8 and 11 and MWH chapters 16 and 22, from the chapter, not re-read.
Sources
WHO, Manganese in Drinking-water, background document for development of WHO Guidelines for Drinking-water Quality, WHO/SDE/WSH/03.04/104/Rev/1 (2011), sections 1.3, 1.5, 3.2, 6.1 and 6.2
Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Annex I Part C (read on the legislation.gov.uk mirror of the directive)
US EPA, Secondary Drinking Water Standards: Guidance for Nuisance Chemicals
US EPA, Alternative Disinfectants and Oxidants Guidance Manual, EPA 815-R-99-014 (April 1999), section 2.2.3 and Table 2-7, Table 2-18, section 3.3.1.2 (ozone) and section 4.3.3 (chlorine dioxide)
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 Table 3 (read on the legislation.gov.uk mirror)
40 CFR 434.32, Effluent limitations for acid or ferruginous mine drainage (BPT), coal mining 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), Appendix Table A4 Metals
ZDHC Wastewater Guidelines Version 2.1 (November 2022), Table 2 heavy metals
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) and Table 2 (molecular ion interferences)
Standard Methods for the Examination of Water and Wastewater (online edition), 3500-Mn Manganese, B. Persulfate Method
US EPA, National Recommended Water Quality Criteria, Aquatic Life Criteria Table (no manganese row)
The Element Book, water chapter for iron (data/water/Fe.json), permanganate and greensand for iron
Stumm, W. and Morgan, J. J., Aquatic Chemistry, 3rd ed. (Wiley, 1996), chapter 11 (oxygenation kinetics of Mn(II), autocatalysis) and chapter 7 (carbonate solids)
40 CFR 424.12, Effluent limitations (BPT), ferroalloy manufacturing point source category, Subpart A open electric furnaces with wet air pollution control devices
40 CFR 424.62, Effluent limitations (BPT), ferroalloy manufacturing point source category, Subpart F electrolytic manganese products
40 CFR 461.71, Effluent limitations (BPT), battery manufacturing point source category, Subpart G zinc subcategory
40 CFR 423.19, Reporting and recordkeeping requirements, steam electric power generating point source category, Table 1 to paragraph (k)(2)(v), BAT treated pollutants in combustion residual leachate
EU Best Available Techniques (BAT) Reference Document for Iron and Steel Production (2013), Table 6.11, composition of waste water from blast furnace gas scrubbing before treatment (read from the Internet Archive copy of the EIPPCB PDF)
Beh C. L., Chuah T. G., Nourouzi M. N., Choong T. S. Y., Removal of heavy metals from steel making waste water by using electric arc furnace slag, Journal of Chemistry 9(4), 2557 to 2564 (2012), doi 10.1155/2012/128275 (abstract)
Im D. G., Kim D. M., Kwon H. L., Lee J. H., Kwon O. H., Yun S. T., Pilot-scale assessment of slag reactors for manganese removal from mine drainage, Environmental Geochemistry and Health 48, 173 (2026), doi 10.1007/s10653-026-03079-x (abstract)
40 CFR 461.43, New source performance standards, battery manufacturing point source category, Subpart D Leclanche subcategory
MWH, Water Treatment: Principles and Design, 3rd ed. (Wiley, 2012), chapter 16 (ion exchange: softening) and chapter 22 (lime soda softening)
Identity
- Name and symbol
- Manganese, Mn
- Atomic number
- 25 protons
- Position
- group 7 · period 4 · d-block · transition metal
- CAS number
- 7439-96-5
Atomic structure
- Atomic mass
- 54.938 u
- Electron configuration
- 1s² 2s² 2p⁶ 3s² 3p⁶ 4s² 3d⁵
[Ar] 4s²³d⁵ - Electrons per shell
- 2, 8, 13, 2
- Valence electrons
- 7 ns and (n-1)d
| isotope | mass (u) | abundance |
|---|---|---|
| 55Mn | 54.938 043(2) | 100 % |
Physical properties
- State at room temperature
- Solid
- Melting point
- 1,519 K (1,245.85 °C)
- Boiling point
- 2,334 K (2,060.85 °C)
- Density
- 7.3 g/cm3
- Appearance
- silvery metallic
- Thermal conductivity
- 7.81 W/(m·K)
- Electrical resistivity
- 1.44 µΩ·m at 20 °C
- Electrical conductivity
- 694,444.444 S/m
- Crystal structure
- body-centered cubic
- Molar heat capacity
- 26.32 J/(mol·K)
Chemical properties
- Oxidation states
- +7, +4, +3, +2
- Electronegativity
- 1.55 (Pauling Scale)
- Ionisation energy
- 7.434 eV
1st 717.3, 2nd 1,509, 3rd 3,248 kJ/mol - Electron affinity
- 0 eV
- Atomic radius
- van der Waals 197 pm
- Ionic radius
- Mn²⁺ 67 low spin; Mn³⁺ 58 low spin; Mn⁴⁺ 53 low spin; Mn⁵⁺ 33 (4-coordinate) low spin; Mn⁶⁺ 26 (4-coordinate) low spin; Mn⁷⁺ 46 low spin; Mn²⁺ 83 high spin; Mn³⁺ 65 high spin pm
- Reactivity
- A group 7 transition metal ([Ar] 3d5 4s2) with the widest range of oxidation states in the first row (+2, +4 and +7 the common ones); the hard, brittle metal is chemically reactive, a little less so toward air than its neighbours, and comparable to zinc in the reactivity series.
- with water
- Decomposes slowly in cold water at most, giving hydrogen; under normal conditions the attack is negligible.
- with oxygen, air
- Somewhat less reactive to air than its neighbours; heated in oxygen the metal burns to the mixed oxide
- with acids
- Dissolves in dilute acids to pale pink manganese(II) salts and hydrogen:
- with halogens
- Combines with the halogens to manganese(II) halides, chlorine giving manganese(II) chloride and fluorine reacting similarly:
- Typical compounds
- MnO₂ manganese dioxide pyrolusite; dry-cell depolariser, glass decolouriser, oxidiser
- KMnO₄ potassium permanganate purple oxidiser for analysis, medicine, water treatment
- MnCO₃ manganese(II) carbonate rhodochrosite, a main ore
- MnSO₄ manganese(II) sulfate pale pink salt of the aquo ion; fertiliser additive
- MnCl₂ manganese(II) chloride from the metal and chlorine
- Mn₃O₄ trimanganese tetroxide hausmannite; the oxide from burning the metal
Occurrence, production and use
- Crustal abundance
- 9.50×102 milligrams per kilogram
- Oceanic abundance
- 2×10-4 milligrams per liter
- Occurrence and sources
Manganese minerals are widely distributed, with oxides, silicates, and carbonates being the most common. Large quantities of manganese nodules are found on the ocean floor and may become a source of manganese. These nodules contain about 24% manganese, together with many other elements in lesser abundance.
Most manganese today is obtained from ores found in Russia, Brazil, Australia, South Africa, Gabon, and India. Pyrolusite and rhodochrosite are among the most common manganese minerals. The metal is obtained by reduction of the oxide with sodium, magnesium, aluminum, or by electrolysis.
- pyrolusite (MnO2) and rhodochrosite (MnCO3) the most common ore minerals, widely distributed; main mining areas in South Africa, Gabon, Australia, Ghana, India, China and Brazil
- manganese ore (35 to 54 percent manganese) land based resources large but irregular, South Africa about 70 percent of world resources; United States ores very low grade and not mined since 1970
- manganese nodules the deep ocean floor, about 24 percent manganese with cobalt, nickel and copper
- Extraction, production
- Smelting of manganese ore to ferromanganese and silicomanganese
Ore is reduced with carbon in furnaces to ferromanganese (74 to 95 percent manganese) or with silicon bearing charge to silicomanganese, the forms that steelmakers buy; the United States imports ferromanganese mainly from Malaysia, Australia, Norway and South Africa. The equation given is the carbothermic reduction step of ferromanganese smelting, taken from the added secondary source. World mine production about 20 million tonnes of manganese content in 2024 (estimate).
Electrolytic manganese metal and metallothermic reductionThe metal is obtained by electrolysis of manganese sulphate solution or by reducing the oxide with sodium, magnesium or aluminium; electrolytic manganese production consumes selenium dioxide as a yield additive. Battery grade high purity manganese is a growing product. Reactants only are stated, so no equation is written.
- Uses
Nearly 90% of all of the manganese produced each year is used in the production of steel. Manganese is added to molten steel to remove oxygen and sulfur and is alloyed with steel to make it easier to form and work with and to increase steel's strength and resistance to impact. Railroad tracks, for example, are made with steel that contains as much as 1.2% manganese. Manganese is also used to give glass an amethyst color and is responsible for the color of amethyst gemstones.
Manganese dioxide (MnO2), the most common compound of manganese, makes up about 0.14% of the Earth's crust. It is used in dry cell batteries to prevent the formation of hydrogen, to remove the green color in glass that is caused by the presence of iron contaminants, and as a drying agent in black paints.
The dioxide (pyrolusite) is used as a depolarizer in dry cells and is used to "decolorize" glass that is colored green by impurities of iron. Manganese by itself colors glass an amethyst color and is responsible for the color of true amethyst. The dioxide is also used in the preparation of oxygen and chlorine and in drying black paints. The permanganate is a powerful oxidizing agent and is used in quantitative analysis and in medicine.
Manganese is widely distributed throughout the animal kingdom. It is an important trace element and may be essential for utilization of vitamin B1.
- Steel: about 1 percent manganese in ordinary steel for strength, workability and wear resistance; manganese steel with about 13 percent manganese for railway track, safes and rifle barrels; manganese dioxide for pig iron manufacture (three United States consumers) consumption closely follows the steel industry; manganese has no satisfactory substitute in its major applications (USGS)
- Batteries: manganese dioxide in dry cell batteries; high purity battery grade manganese for lithium ion cathodes, a strategic raw material under the EU Critical Raw Materials Act (in force May 2024)
- Chemicals: manganese containing catalyst for the transesterification step of PET made from dimethyl terephthalate, which ends up in the product (POL BREF); manganese(IV) oxide as a catalyst, rubber additive and glass decolouriser; potassium permanganate as an oxidant in synthesis and treatment
- Agriculture and food: manganese sulphate in fungicides and fertilisers for manganese poor soils; manganese as a mineral supplement in animal feed and in brick colorants (USGS lists animal feed among non metallurgical ore uses)
- Aluminium alloys: drinks can alloy with 1.5 percent manganese for corrosion resistance; highly magnetic alloys with aluminium, antimony and copper
- Mining: manganese ore extraction is grouped with iron ore in the MWEI BREF; manganese is a measured parameter in water discharged from base metal, precious metal, industrial mineral and coal extraction
- Safety, toxicity
Exposure to manganese dusts, fume, and compounds should not exceed the ceiling value of 5 mg/m3 for even short periods because of the element's toxicity level.
GHS classification, signal word Danger- H228 Flammable solid Flammable solids
- H319 Causes serious eye irritation Serious eye damage/eye irritation
- H411 Toxic to aquatic life with long lasting effects to the aquatic environment, long-term hazard
- H412 Harmful to aquatic life with long lasting effects to the aquatic environment, long-term hazard
- H360 May damage fertility or the unborn child Reproductive toxicity
- H372 Causes damage to organs through prolonged or repeated exposure Specific target organ toxicity, repeated exposure
- H401 Toxic to aquatic life to the aquatic environment, acute hazard
- H316 Causes mild skin irritation Skin corrosion/irritation
- H320 Causes eye irritation Serious eye damage/eye irritation
- H370 Causes damage to organs Specific target organ toxicity, single exposure
Discovery and name
- Discovered by
- Carl Wilhelm Scheele
- Discovered
- 1774
- First isolated
- Johann Gottlieb Gahn
- Named by
- not in sources
- Origin of the name
- after Magnesia, Greece
It is gray-white, resembling iron, but is harder and very brittle. The metal is reactive chemically and decomposes slowly in cold water. Manganese is used to form many important alloys. Manganese improves rolling and forging qualities in steel, along with adding strength, stiffness, wear resistance, hardness.
With aluminum and antimony, and especially with small amounts of copper, it forms highly ferromagnetic alloys.
Manganese metal is ferromagnetic only after special treatment. The pure metal exists in four allotropic forms. The alpha form is stable at ordinary temperature; gamma manganese, which changes to alpha at ordinary temperatures, is said to be flexible, soft, easily cut, and capable of being bent.
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.