Iron
fullIron is an indicator parameter in the EU and a secondary standard in the US, the most common groundwater treatment problem after hardness, and the base of the two workhorse coagulants, ferric chloride and ferric sulfate.
Typical wastewaters
- coal mine drainage (acid or ferruginous) Fe²⁺ in acid mine water, oxidising to Fe(OH)₃ ochre on aeration; 7.0 daily maximum and 3.5 mg/L monthly average total iron
- power plant metal cleaning wastes total iron with copper, 1.0 mg/L daily maximum and monthly average
- chromate bearing effluent reduced with ferrous sulfate Fe²⁺ reductant oxidised to Fe³⁺ and precipitated as Fe(OH)₃ with Cr(OH)₃ at pH 8 to 9
- wastewater treated with ferric salts for phosphorus FePO₄ and hydrous ferric oxide in the sludge, more than the 1:1 molar ratio dosed
1 · Identity
- Symbol, number
- Fe, 26
- Oxidation states in water
- +2 (ferrous, Fe²⁺, dissolved in anoxic groundwater and mine water) and +3 (ferric, hydrolysed to Fe(OH)₃ and hydrous ferric oxide in oxic water; the state of coagulant flocs and pipe rust). 0 as the metal of cast iron and steel mains, which corrode to both.
- Note
- Iron(II) salts are unstable in drinking water supplies and precipitate as iron(III) hydroxide, a rust coloured silt (WHO background document). Everything below follows from that switch.
2 · Occurrence in water
- Natural sources
- Dissolution of iron bearing minerals under reducing conditions and low pH; anaerobic groundwater carries iron(II) at up to several milligrams per litre without colour or turbidity until it is pumped and aerated. Lowering the water table or nitrate leaching aerates iron bearing soil layers and changes both groundwater and surface water quality (WHO background document).
- Anthropogenic sources
- Corrosion of cast iron, steel and galvanised iron distribution pipes; carry over of iron coagulants; acid or ferruginous coal mine drainage, regulated in the US at 7.0 mg/L daily maximum; metal cleaning wastes at power plants, regulated at 1.0 mg/L; iron and steel pickling and mine water in the ledger's mining chapter.
| matrix | typical range | note |
|---|---|---|
| natural fresh water | 0.5 to 50 mg/L | range quoted by the WHO fact sheet for natural fresh waters |
| groundwater, anaerobic | 0.5 to 10 mg/Lregion-dependent | as iron(II); up to 50 mg/L is sometimes found |
| surface water, rivers | 0.7 mg/L single median figure, no range given | reported median for rivers |
| drinking water | below 0.3 mg/L | normally; higher where iron salts are used as coagulants and where cast iron, steel and galvanised pipes distribute the water |
| seawater | 0.002 mg/Lsingle figure, no range | oceanic abundance figure, Jefferson Lab via PubChem; open ocean iron is a trace element limited by solubility |
3 · Speciation
Below the oxic boundary, and wherever pH is low, iron is dissolved Fe²⁺, with FeHCO₃⁺ and FeSO₄ ion pairs in mineralised water. In oxic water above pH 6 the equilibrium species is iron(III), and iron(III) is almost entirely solid: Fe(OH)₃ and hydrous ferric oxide, with only nanomolar dissolved hydrolysis products (Fe(OH)₂⁺, Fe(OH)₄⁻) in the neutral range. The practical question is therefore never the equilibrium but the rate of the Fe(II) to Fe(III) step, which is fast above pH 7 in aerated water and slow in acid or organic rich water.
| condition | dominant species | note |
|---|---|---|
| anoxic groundwater or sediment pore water, pH 6 to 8 | Fe²⁺, FeHCO₃⁺; FeCO₃ (siderite) and FeS where carbonate or sulfide is high | iron(II) persists for as long as the water is kept away from air |
| oxic water, pH 6 to 9 | Fe(OH)₃ (s) and hydrous ferric oxide colloids; dissolved Fe(OH)₂⁺ and Fe(OH)₄⁻ at trace level; Fe(III) complexed by natural organic matter | dissolved iron above about 0.1 mg/L in such water is either colloidal or organically complexed |
| acid mine drainage, pH below 3 | Fe²⁺ and Fe³⁺ both dissolved; Fe³⁺ hydrolyses and precipitates as pH is raised | the reason lime neutralisation of mine water produces iron rich high density sludge |
- Solubility
- Iron(III) hydroxide is the controlling solid in oxic water and keeps dissolved iron(III) far below 0.1 mg/L between pH 6 and 9; iron(II) is soluble at mg/L levels until it is oxidised. The sources read give no solubility products, so none are quoted.
- Hydrolysis
- Fe³⁺ hydrolyses stepwise to Fe(OH)₂⁺, Fe(OH)₃ and Fe(OH)₄⁻; the hydrolysis releases protons, which is why ferric coagulants consume alkalinity and depress pH.
- Complexation
- Bicarbonate and sulfate ion pairs with Fe(II); natural organic matter binds Fe(III) and slows its oxidation and settling. Constants are not quoted because the sources read do not print them.
- Precipitates
- Fe(OH)₃ and hydrous ferric oxide (oxic); FeCO₃ siderite and FeS (anoxic, carbonate or sulfide rich); FePO₄ with phosphate; Fe₃O₄ magnetite and Fe₂O₃ hematite as ageing products and pipe tubercles.
4 · Role in treatment
5 · Removal and control
- Efficiency
- to below the 0.3 mg/L acceptability level in normal practice; no percentage is printed in the sources read
- Interferences
- natural organic matter complexes slow oxidation and hold colloidal iron; low pH slows aeration; manganese needs a stronger oxidant or higher pH
- Efficiency
- not quoted
- Interferences
- organic matter consumes permanganate
- Efficiency
- not quoted
- Interferences
- bromide forms bromate with ozone
- Efficiency
- iron: not quoted; arsenic riding on the iron: 80 to 95 percent
- Interferences
- natural organic matter, orthophosphate and silicate compete for the iron hydroxide surface
- Efficiency
- not quoted
- Interferences
- organically bound iron passes filters
6 · Analytics
| method | standard | detection limit | note |
|---|---|---|---|
| 1,10-phenanthroline colorimetry | Standard Methods 3500-Fe B; ISO 6332 | colorimetric methods about 5 µg/L (WHO); ISO 6332 applies from 0.01 to 5 mg/L | gives total iron after digestion, total dissolved iron after filtration, and iron(II) directly; the orange red complex is read at 510 nm |
| atomic absorption spectrometry | Standard Methods 3111 (flame); WHO cites AAS | about 1 µg/L (WHO background document) | |
| ICP-OES | EPA 200.7; ISO 11885 | not read in the sources this session | iron is not among the analytes of EPA 200.8 (ICP-MS), whose Table 1 lists 21 elements without iron; ICP-MS for iron needs interference removal at mass 56 |
| ICP-MS | ISO 17294-2 | not read | ISO 17294-2 covers iron among its elements; use a collision cell mode for the argon oxide interference |
- Sampling pitfalls
- Iron(II) in an anaerobic groundwater sample oxidises and precipitates in the bottle on contact with air (WHO: iron(II) salts are unstable in supplies). Filter 0.45 µm in the field and acidify at once for dissolved iron; acidify unfiltered samples for total iron; measure iron(II) on site. Rust from the sampling tap and the mains is a total iron artefact.
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) | no guideline | not of health concern at levels found in drinking water; may affect acceptability; a 10 percent allocation of the JECFA PMTDI of 0.8 mg/kg body weight gives about 2 mg/L, below which there is no health hazard, but taste and appearance are usually affected below that level; assessment 1993 |
| WHO GDWQ, acceptability | 0.3 mg/L | the level above which laundry and plumbing stain and taste is noticeable (background document); turbidity and colour can appear in piped systems above 0.05 to 0.1 mg/L |
| EU DWD 2020/2184 | 200 µg/L | Annex I Part C indicator parameter; uncertainty of measurement 30 percent of the parametric value (Annex III) |
| US EPA | 0.3 mg/L | National Secondary Drinking Water Regulation, non enforceable; effects listed as rusty colour, sediment, metallic taste, reddish or orange staining |
| body | limit | note |
|---|---|---|
| EU CWW BREF BAT-AEL (Decision 2016/902) | not set | iron is not among the BAT 12 parameters (TOC, COD, TSS, TN, Ninorg, TP, AOX, Cr, Cu, Ni, Zn); iron limits in the EU come from national permits |
| US EPA 40 CFR 434.32, coal mining, acid or ferruginous mine drainage (BPT) | 7.0 daily maximum; 3.5 30-day average mg/L total iron | with manganese 4.0 and 2.0 mg/L, TSS 70 and 35 mg/L, pH 6.0 to 9.0 |
| US EPA 40 CFR 423.12(b)(5), steam electric metal cleaning wastes (BPT) | 1.0 mg/L total iron | same value for daily maximum and 30-day average; with copper 1.0 mg/L |
| Abu Dhabi ADS 23/2017, discharge to the marine environment (EAD) | 2.0 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 | 50 mg/L region-dependent; sewer discharge, not receiving water | Table A₄ maximum allowable concentration for trade effluent to the sewer network |
| sector | body | limit | note |
|---|---|---|---|
| textile | ZDHC Wastewater Guidelines v₂.1 (2022) | not set | iron is not a ZDHC wastewater parameter |
8 · Health and environmental effects
- Toxicity
- Essential nutrient; minimum daily requirement about 10 to 50 mg depending on age, sex and bioavailability; JECFA PMTDI 0.8 mg/kg body weight (1983) as a precaution against iron storage; 0.3 mg/L in drinking water contributes about 0.6 mg to daily intake. No health based guideline is proposed (WHO).
- Bioaccumulation
- Not addressed in the sources read; iron is regulated by uptake in animals and is not a bioaccumulating contaminant in the sense used for metals such as mercury.
- Ecotoxicity
- US EPA national recommended aquatic life criterion, freshwater chronic 1000 µg/L (1986); no acute freshwater and no saltwater criterion. The harm in rivers is usually physical: ochre precipitates smother the bed.
Flags
- The 0.5 to 10 mg/L groundwater range and the 0.7 mg/L river median are WHO 1990s compilations and vary strongly by aquifer and region.
- The seawater figure (0.002 mg/L) is a single abundance figure from Jefferson Lab via PubChem, not a range.
- The Fe(II) oxygenation rate constant is cited to Stumm and Morgan chapter 11 from memory of the text, not re-read this session.
- The chromate and chlorite reduction stoichiometries are electron balances written here; the sources name the reagent but do not print the equation.
- The EPA oxidant doses per mg Fe come from a 1986 and 1991 compilation quoted by the 1999 EPA manual; the brief's own example gives 0.64 mg Cl₂ per mg Fe, the EPA table 0.62.
- Abu Dhabi values are two different media (marine outfall 2.0 mg/L, sewer 50 mg/L); other GCC states were not read.
- No detection limit was read for EPA 200.7 or ISO 17294-2 this session.
Gaps
- No source read gives iron concentrations in municipal or industrial wastewater; the mining and steel figures are in the ledger's own chapters, not here.
- No solubility products or hydrolysis constants are quoted; Stumm and Morgan has them but was not re-read.
- No removal percentage for iron is printed in the sources read; the EPA doses and the WHO acceptability level stand in for it.
- Lime softening, ion exchange softening, sequestration with polyphosphate and biological iron filtration are not covered because no read source describes them.
- The phosphorus precipitation and chromate reduction equations are cited to a textbook chapter and the CWW BREF technique description, not to a printed equation read this session.
- Other GCC discharge standards (Saudi, Oman, Qatar) were not read.
Sources
WHO, Iron in Drinking-water, background document for development of WHO Guidelines for Drinking-water Quality, WHO/SDE/WSH/03.04/08 (2003; text of 1996)
Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Annex I Part C and Annex III
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 (oxidant doses for iron and manganese)
US EPA, Arsenic Treatment Technology Design Manual for Small Systems, draft for peer review (June 2002), sections 2.5.2 (Table 2-3), 2.7.1 and 2.7.3
40 CFR 434.32, Effluent limitations for acid or ferruginous mine drainage (BPT), coal mining point source category
40 CFR 423.12, Effluent limitations guidelines representing BPT, steam electric power generating point source category
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
Best Available Techniques Reference Document for Common Waste Water and Waste Gas Treatment/Management Systems in the Chemical Sector (CWW BREF 2016), chapter 3, chemical reduction
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), conventional parameters and metals tables
US EPA, National Recommended Water Quality Criteria, Aquatic Life Criteria Table (iron, 1986)
Standard Methods for the Examination of Water and Wastewater (online edition), 3500-Fe Iron, B. Phenanthroline Method
ISO 6332:1988, Water quality. Determination of iron. Spectrometric method using 1,10-phenanthroline
ISO 17294-2:2023, Water quality. Application of ICP-MS. Part 2: Determination of selected elements including uranium isotopes
US EPA Method 200.8, Revision 5.4 (1994), Determination of trace elements in waters and wastes by ICP-MS, Table 1 (iron not listed)
PubChem element summary for iron; oceanic abundance 2 x 10^-3 mg/L from Jefferson Lab
WHO, Chlorine Dioxide, Chlorite and Chlorate in Drinking-water, background document, WHO/FWC/WSH/16.49 (2016), section 4.2 (chlorite reduction with ferrous iron)
Stumm, W. and Morgan, J. J., Aquatic Chemistry, 3rd ed. (Wiley, 1996), chapter 11 (kinetics of redox processes, oxygenation of Fe(II)) and chapter 7 (precipitation and dissolution)
Metcalf and Eddy, Wastewater Engineering: Treatment and Resource Recovery, 5th ed. (McGraw-Hill, 2014), chapter 6 (chemical precipitation of phosphorus with iron)
Identity
- Name and symbol
- Iron, Fe
- Atomic number
- 26 protons
- Position
- group 8 · period 4 · d-block · transition metal
- CAS number
- 7439-89-6
Atomic structure
- Atomic mass
- 55.845 u
- Electron configuration
- 1s² 2s² 2p⁶ 3s² 3p⁶ 4s² 3d⁶
[Ar] 4s²³d⁶ - Electrons per shell
- 2, 8, 14, 2
- Valence electrons
- 8 ns and (n-1)d
| isotope | mass (u) | abundance |
|---|---|---|
| 54Fe | 53.939 608(3) | 5.8 % |
| 56Fe | 55.934 936(2) | 91.7 % |
| 57Fe | 56.935 392(2) | 2.1 % |
| 58Fe | 57.933 274(3) | 0.2 % |
Physical properties
- State at room temperature
- Solid
- Melting point
- 1,811 K (1,537.85 °C)
- Boiling point
- 3,134 K (2,860.85 °C)
- Density
- 7.874 g/cm3
- Appearance
- lustrous metallic with a grayish tinge
- Thermal conductivity
- 80.4 W/(m·K)
- Electrical resistivity
- 96.1 nΩ·m at 20 °C
- Electrical conductivity
- 10.41 MS/m
- Crystal structure
- body-centered cubic
- Molar heat capacity
- 25.1 J/(mol·K)
Chemical properties
- Oxidation states
- +3, +2
- Electronegativity
- 1.83 (Pauling Scale)
- Ionisation energy
- 7.902 eV
1st 762.5, 2nd 1,561.9, 3rd 2,957 kJ/mol - Electron affinity
- 0.163 eV
- Atomic radius
- van der Waals 194 pm
- Ionic radius
- Fe²⁺ 61 low spin; Fe³⁺ 55 low spin; Fe⁴⁺ 59 low spin; Fe⁶⁺ 25 (4-coordinate) low spin; Fe²⁺ 78 high spin; Fe³⁺ 65 high spin pm
- Reactivity
- A group 8 transition metal ([Ar] 3d6 4s2), by far the most reactive of its group: the pure metal corrodes rapidly in moist air because its oxide is porous and flakes off rather than passivating, it is pyrophoric when finely divided, and its chemistry runs on the +2 and +3 states.
- with water
- Rusts in water and moist air to brown-to-black hydrated iron(III) oxides; red-hot iron decomposes steam to iron oxide and hydrogen, the reaction Lavoisier used in
- with oxygen, air
- Reacts readily with oxygen, especially in moist air or when hot, to oxides that offer no protection; finely divided iron is pyrophoric:
- with acids
- Dissolves easily in dilute acids to iron(II) salts and hydrogen, but is passivated by concentrated nitric acid and other oxidising acids:
- with halogens
- Reacts with fluorine, chlorine and bromine to the iron(III) halides:
- Typical compounds
- Fe₂O₃ iron(III) oxide hematite, the main ore; rust and ochre pigments
- Fe₃O₄ iron(II,III) oxide magnetite; black magnetic ore
- FeS₂ iron pyrite fool's gold; iron(II) polysulfide
- FeCl₃ iron(III) chloride water and sewage coagulant; circuit-board etchant
- FeSO₄ iron(II) sulfate green vitriol; precursor to other iron compounds
- Fe(CO)₅ iron pentacarbonyl volatile carbonyl; source of carbonyl iron powder
Occurrence, production and use
- Crustal abundance
- 5.63×104 milligrams per kilogram
- Oceanic abundance
- 2×10-3 milligrams per liter
- Occurrence and sources
Iron is a relatively abundant element in the universe. It is found in the sun and many types of stars in considerable quantity. Its nuclei are very stable. Iron is a principal component of a meteorite class known as siderites and is a minor constituent of the other two meteorite classes. The core of the earth 2150 miles in radius is thought to be largely composed of iron with about 10 percent occluded hydrogen. The metal is the fourth most abundant element, by weight that makes up the crust of the earth.
The most common ore is hematite, which is frequently seen as black sands along beaches and banks of streams.
- haematite (Fe2O3), magnetite (Fe3O4) and low grade taconite mined in Australia, Brazil, China, India, Russia, Ukraine, South Africa, Canada, Iran and the United States; world resources above 800 billion tonnes of ore with more than 230 billion tonnes of iron
- pyrite (FeS2) sulphide ore roasted for sulphuric acid, leaving iron oxide; one tonne of acid needs 0.5 tonne of pyrite
- dissolved iron(II) and particulate iron(III) anoxic groundwater and mine water; a measured parameter in water from base metal, precious metal, uranium, iron ore and bauxite extraction
- Extraction, production
- Blast furnace reduction of ore with coke
Haematite or magnetite is heated with coke and limestone in a blast furnace to pig iron with about 3 percent carbon, then converted to steel. The equation given is the main ore reduction step of the blast furnace, taken from the added secondary source. World pig iron 1.3 billion tonnes in 2024 (estimate); direct reduced iron and scrap feed electric arc furnaces.
Iron oxide pigments by aqueous oxidation of iron(II) saltsThe SIC BREF describes the precipitation and Penniman-Zoph processes (iron(II) sulphate oxidised with air over seed crystals to yellow, red and black oxides), the Laux process (nitro compound reduction with metallic iron steered to pigment grade oxide) and dry calcination of iron sulphate to Fe2O3 and SO3. No stoichiometry is stated, so no equation.
Reduction of aromatic nitro compounds with iron4 Ar-NO₂ Ar-NH₂ + 3 Fe₃O₄Equation as stated by the OFC BREF for the fine chemical route to aromatic amines: the nitro compound is added to iron, water and acid with 15 to 50 percent excess iron; 97 to 98 percent of the hydrogen comes from the water, the acid only activates the iron. The iron oxide sludge is a waste stream in the pharma chapter.
- Uses
Huge amounts of iron are used to make steel, an alloy of iron and carbon. Steel typically contains between 0.3% and 1.5% carbon, depending on the desired characteristics. The addition of other elements can give steel other useful properties. Small amounts of chromium improves durability and prevents rust (stainless steel); nickel increases durability and resistance to heat and acids; manganese increases strength and resistance to wear; molybdenum increases strength and resistance to heat; tungsten retains hardness at high temperatures; and vanadium increases strength and springiness. Steel is used to make paper clips, skyscrapers and everything in between.
In addition to helping build the world around us, iron helps keep plants and animals alive. Iron plays a role in the creation of chlorophyll in plants and is an essential part of hemoglobin, the substance that carries oxygen within red blood cells. Iron sulfate (FeSO4) is used to treat the blood disease anemia.
Iron is a vital constituent of plant and animal life and works as an oxygen carrier in hemoglobin.
Taconite is becoming increasingly important as a commercial ore. The pure metal is not often encountered in commerce, but is usually alloyed with carbon or other metals.
- Steel and construction: carbon steel (0.1 to 2 percent carbon), alloy steels with nickel, chromium, vanadium, tungsten and manganese, stainless steel with at least 10.5 percent chromium; cast iron (3 to 5 percent carbon) for pipes, valves and pumps; reinforced concrete and girders construction took 28 percent of United States steel shipments in 2024, service centres 23 percent, automotive 15 percent (USGS, US figures)
- Chemicals: iron catalyst for ammonia synthesis at 100 to 250 bar and 350 to 550 degrees C; iron oxide and chromium oxide shift catalyst; pyrite roasting for sulphuric acid; iron oxide pigments from scrap iron and iron sulphate
- Pharmaceuticals and fine chemicals: metallic iron as the reducing agent for aromatic nitro compounds, giving amines and an iron oxide sludge
- Food and beverage: ferric chloride and iron based coagulants and flocculants for effluent treatment and sludge conditioning; iron oxides as the colour additive E172
- Mining: iron ore extraction, tailings and heaps are a sector of the MWEI BREF; ferric chloride as a flotation depressant and iron salts as coagulants in mine water treatment; iron cyanide complexes and high density sludge are waste streams
- Safety, toxicity
- GHS classification, signal word Danger
- H228 Flammable solid Flammable solids
- H251 Self-heating; may catch fire Self-heating substances and mixtures
- H319 Causes serious eye irritation Serious eye damage/eye irritation
- H335 May cause respiratory irritation Specific target organ toxicity, single exposure; Respiratory tract irritation
Discovery and name
- Discovered by
- not in sources
- Discovered
- before 5000 BC
- First isolated
- not in sources
- Named by
- not in sources
- Origin of the name
- probably from a PIE root meaning 'blood', for the color of its oxides
The pure metal is very reactive chemically and rapidly corrodes, especially in moist air or at elevated temperatures. It has four allotropic forms or ferrites, known as alpha, beta, gamma, and omega, with transition points at 700, 928, and 1530C. The alpha form is magnetic, but when transformed into the beta form, the magnetism disappears although the lattice remains unchanged. The relations of these forms are peculiar. Pig iron is an alloy containing about 3 percent carbon with varying amounts of sulfur, silicon, manganese, and phosphorus.
Iron is hard, brittle, fairly fusible, and is used to produce other alloys, including steel. Wrought iron contains only a few tenths of a percent of carbon, is tough, malleable, less fusible, and usually has a "fibrous" structure.
Carbon steel is an alloy of iron with small amounts of Mn, S, P, and Si. Alloy steels are carbon steels with other additives such as nickel, chromium, vanadium, etc. Iron is a cheap, abundant, useful, and important metal.
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.