Manganese

    group 7 · period 4 · d-block · transition metal

    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.
    matrixtypical rangenote
    fresh water, typical1 to 200 µg/Lregion-dependentWHO 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 surveyUS 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, treatedbelow 50 µg/Ltypical 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
    seawater0.4 to 10 µg/Laverage 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.

    conditiondominant speciesnote
    anoxic or acid groundwater, hypolimnion, pH 4 to 7Mn²⁺, MnHCO₃⁺; MnCO₃ (s) where carbonate is highWHO: the divalent form predominates in most water at pH 4 to 7
    aerated water, pH 7 to 8, no catalystMn²⁺ 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 dioxideMnO₂ (s), hydrous manganese oxidesthe filterable form; also the coating on greensand and on old mains
    ozone overdose, or permanganate overdoseMnO₄⁻ (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).
    2MnX2++OX2+2HX2O2MnOX2(s)+4HX+\ce{2 Mn^2+ + O2 + 2 H2O -> 2 MnO2 (s) + 4 H+}
    aeration; rate law second order in OH^- and autocatalytic on MnO2, so slow below pH 9 without oxide surfaces (Stumm and Morgan chapter 11, from the chapter, not re-read); stoichiometric demand 0.29 mg O2 per mg Mn (EPA Table 2-7)
    MnX2++HOCl+HX2OMnOX2(s)+ClX+3HX+\ce{Mn^2+ + HOCl + H2O -> MnO2 (s) + Cl^- + 3 H+}
    free chlorine; EPA Table 2-18: optimum pH 7 to 8 with 1 to 3 hours, or pH 9.5 with minutes; kinetics slow, reaction time increases at lower pH. The electron balance above gives 1.29 mg Cl2 per mg Mn; EPA Table 2-7 prints 0.77
    3MnX2++2MnOX4X+2HX2O5MnOX2(s)+4HX+\ce{3 Mn^2+ + 2 MnO4^- + 2 H2O -> 5 MnO2 (s) + 4 H+}
    potassium permanganate; 1.92 mg KMnO4 per mg Mn (EPA Table 2-7), which the equation reproduces; seconds; the product MnO2 is filtered with the manganese it came from
    MnX2++OX3+HX2OMnOX2(s)+OX2+2HX+\ce{Mn^2+ + O3 + H2O -> MnO2 (s) + O2 + 2 H+}
    ozone; 0.88 mg O3 per mg Mn, optimum pH 8 to 8.5 (EPA Table 2-7 and section 3.3.1.2); over-ozonation gives permanganate and resolubilises the manganese
    MnX2++2ClOX2+2HX2OMnOX2(s)+2ClOX2X+4HX+\ce{Mn^2+ + 2 ClO2 + 2 H2O -> MnO2 (s) + 2 ClO2^- + 4 H+}
    chlorine dioxide; 2.45 mg ClO2 per mg Mn (EPA Table 2-7; about 2.5 mg/L per 1.0 mg/L Mn in section 4.3.3); chlorite is the by-product and caps the usable dose at the 1.0 mg/L chlorite limit
    MnX2++COX3X2MnCOX3(s)\ce{Mn^2+ + CO3^2- -> MnCO3 (s)}
    anoxic carbonate rich groundwater; rhodochrosite (Stumm and Morgan chapter 7, from the chapter, not re-read)
    MnX2++2OHXMn(OH)X2(s)\ce{Mn^2+ + 2 OH- <=> Mn(OH)2 (s)}
    manganese(II) hydroxide is far more soluble than the iron(II) hydroxide, so it forms only above about pH 9.5; this is the whole difference between an iron plant and a manganese plant, and the reason aeration at neutral pH removes one and not the other
    MnX2++MnOX2(s)+2HX2O2MnOOH(s)+2HX+\ce{Mn^2+ + MnO2 (s) + 2 H2O -> 2 MnOOH (s) + 2 H+}
    the first half of the autocatalytic loop, written as comproportionation to the Mn(III) oxyhydroxide; Stumm and Morgan write the same loop as adsorption of Mn(II) on the oxide surface followed by its oxidation. Either way it is why a clean water holds Mn^2+ for days and a filter already coated with manganese oxide strips it in seconds
    4MnOOH(s)+OX24MnOX2(s)+2HX2O\ce{4 MnOOH (s) + O2 -> 4 MnO2 (s) + 2 H2O}
    the second half: oxygen reoxidises the surface, regenerating the catalyst; the pair is the mechanism behind manganese oxide coated media and behind the deposits that build in mains
    MnX2++HSXMnS(s)+HX+\ce{Mn^2+ + HS^- -> MnS (s) + H+}
    sulfidic anoxic water; manganese sulfide is orders of magnitude more soluble than iron sulfide, so sulfide reduction that strips iron leaves the manganese dissolved, the classic reason a groundwater is clear of iron and still stains black
    MnX2++Ca(OH)X2Mn(OH)X2(s)+CaX2+\ce{Mn^2+ + Ca(OH)2 -> Mn(OH)2 (s) + Ca^2+}
    lime softening at pH 10.5 to 11 carries manganese out with the calcium carbonate and magnesium hydroxide sludge; 1 mol of lime per mol of manganese on top of the hardness demand

    4 · Role in treatment

    as a problem
    black staining, discoloured water, encrustation
    Mn(II) oxidised slowly in the distribution system to hydrous MnO₂ that deposits and sloughs off
    complaints above 0.02 mg/L (WHO fact sheet); coatings form at 0.02 mg/L and taste above 0.1 mg/L (WHO background document); many countries set 0.05 mg/L for that reason
    deposit release events
    manganese oxides accumulated in mains are released by mains breaks, hydrant flushing, pH, temperature, chlorine residual or source changes
    WHO fact sheet: arsenic, barium, chromium, lead and uranium deposited with the oxides are released with them; chemical releases of dissolved manganese go unnoticed
    aeration does not work
    Mn(II) oxygenation needs pH above about 9 or an oxide catalyst
    the plant that removes its iron by aeration passes its manganese
    pink water
    permanganate overdose, or permanganate formed by over-ozonation
    EPA section 3.3.1.2; reduce on a filter downstream
    MnOX4X+4HX++3eXMnOX2(s)+2HX2O\ce{MnO4^- + 4 H+ + 3 e- -> MnO2 (s) + 2 H2O}
    the permanganate half reaction, standard potential about +1.68 V in acid; three electrons per manganese, which is why a small overdose colours a large volume and why any reductant on the filter, including the media coating itself, takes the colour out again
    chlorite from chlorine dioxide
    each mg of manganese oxidised by ClO₂ leaves about 2 mg of chlorite
    EPA section 4.3.3: use limited by the 1.0 mg/L chlorite and chlorate by-product ceiling
    manganese in coagulants
    impurity in iron and aluminium coagulants
    WHO fact sheet
    as a reagent
    potassium permanganate, oxidant
    oxidises Fe(II), Mn(II), sulfide and taste and odour compounds and is itself reduced to MnO₂, which is filtered; regenerates manganese oxide coated media continuously
    3MnX2++2MnOX4X+2HX2O5MnOX2(s)+4HX+\ce{3 Mn^2+ + 2 MnO4^- + 2 H2O -> 5 MnO2 (s) + 4 H+}
    1.92 mg KMnO4 per mg Mn, 0.94 mg per mg Fe (EPA Table 2-7); overdose is pink water
    manganese oxide coated media (greensand, pyrolusite)
    adsorbs Mn(II) and Fe(II) and catalyses their oxidation on the MnO₂ surface; the bed is regenerated by chlorine or permanganate fed ahead of it
    WHO fact sheet: manganese greensand filtration with careful operation at the point of entry; the EPA arsenic manual describes the same media for iron and arsenic (see the iron chapter)
    permanganate for iron
    see the iron chapter
    0.94 mg KMnO4 per mg Fe

    5 · Removal and control

    chemical oxidation then filtration
    Mn(II) oxidised by chlorine, permanganate, ozone or chlorine dioxide to MnO₂, which is settled and filtered; all the common oxidants except chloramines do it (EPA); reactions take seconds with permanganate, minutes to hours with chlorine at pH 7 to 8
    3MnX2++2MnOX4X+2HX2O5MnOX2(s)+4HX+\ce{3 Mn^2+ + 2 MnO4^- + 2 H2O -> 5 MnO2 (s) + 4 H+}
    oxidant demand per mg Mn: 0.77 mg Cl2 (EPA table; 1.29 by stoichiometry), 1.92 mg KMnO4, 0.88 mg O3, 2.45 mg ClO2, 0.29 mg O2 (EPA Table 2-7); chlorine pH 7 to 8 or 9.5
    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
    adsorption and catalytic oxidation on manganese oxide media
    greensand or pyrolusite pressure filters with continuous chlorine or permanganate feed; Mn(II) adsorbs and is oxidised on the surface
    WHO: adsorption and oxidation; point of entry greensand needs careful operation and maintenance
    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
    biological filtration
    manganese oxidising bacteria on filter media oxidise Mn(II) at neutral pH without chemical oxidant, usually after biological iron removal
    WHO fact sheet lists biological filtration among the methods that lower manganese below 0.05 mg/L; the start-up and pH window are not given in the sources read
    Efficiency
    to below 0.05 mg/L (WHO)
    Interferences
    chlorine residual kills the biofilm; iron must be removed first
    softening and ion exchange
    lime softening precipitates manganese with the calcium carbonate at high pH; cation exchange takes Mn²⁺ with hardness
    2RNa+MnX2+RX2Mn+2NaX+\ce{2 RNa + Mn^2+ -> R2Mn + 2 Na^+}
    WHO fact sheet: softening and ion exchange listed; point of use ion exchange moderately effective. R is the cation exchange site in the sodium form; manganese leaves with the hardness and returns in the brine, and the run ends when hardness breaks through, not when manganese does; the exchange is the standard softening reaction of MWH chapter 16
    Efficiency
    not quoted as a figure
    Interferences
    Mn(II) already oxidised to particulate fouls resin
    reverse osmosis (point of use)
    membrane rejection of Mn²⁺
    WHO fact sheet: the most effective and reliable point of use technology
    Efficiency
    not quoted
    Interferences
    particulate manganese fouls the membrane
    source management
    drill a new well, blend wells, manage reservoir stratification to keep sediment from releasing manganese
    WHO fact sheet practical considerations

    6 · Analytics

    methodstandarddetection limitnote
    ICP-MSEPA 200.8 (mass 55); ISO 17294-20.002 µg/L (WHO fact sheet); EPA 200.8 instrument detection limit 0.1 µg/L scanning, 0.007 µg/L selected ion monitoringArNH⁺ overlaps mass 55 (EPA 200.8 Table 2); none of the methods distinguish oxidation states
    ICP-OES and graphite furnace AASEPA 200.7; ISO 11885; ISO 155860.005 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)
    colorimetryStandard Methods 3500-Mn B (persulfate); the ISO 1986 spectrometric method cited by WHO10 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.

    drinking water
    bodylimitnote
    WHO GDWQ 4th ed. with addenda (2022)0.08 mg/Lprovisional 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, acceptability0.02 mg/Lconcentrations 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 2020/218450 µg/LAnnex I Part C indicator parameter
    US EPA0.05 mg/LNational Secondary Drinking Water Regulation, non enforceable; effects listed as black to brown colour, black staining, bitter metallic taste; no primary MCL
    discharge
    bodylimitnote
    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 manganesewith 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 sewer10 mg/L
    region-dependent; sewer discharge, not receiving water
    Table A₄ Metals, maximum allowable concentration for trade effluent to the sewer network
    industry thresholds
    sectorbodylimitnote
    textile and leatherZDHC 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 Guidelines for Drinking-water Quality, 4th ed. incorporating the first and second addenda (2022), chapter 12 chemical fact sheet, Manganese (pp. 420 to 423, expanded fact sheet)
    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)

    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.